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PHONE (80S) 323-0211
2000 EAST BRUNDAGE LANE
POST OFFICE BOX 4087
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BAKERSFIELD, CALIFORNIA 93307
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WEST
TANK
1000 Gals.
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BSK Job B93229
January, 1994
Figure 3
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500 Gals.
156 Feet to
Wood Fence at
Daniels Lane
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BORING LOCATIONS
UST SITE SOIL CHARACTERIZATION
K & D SALVAGE, 600 SOUTH UNION A VENUE
BAKERSflELD,CALWORN[A
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BSK Job B93229
January, 1994
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January, 1994
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VICINITY MAP
UST SITE SOIL CHARACTERIZATION
K & D SALVAGE, 600 SOUTH UNION AVENUE
BAKERSFIELD, CALIFORNIA
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BSK Job 893229
October, 1993
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Scale (Miles)
VICINITY MAP
UST SITE SOIL CHARACTERIZATION
K & D SALVAGE, 600 SOUTH UNION AVENUE
BAKERSFIELD, CALIFORNIA
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BSK Job 893229
October, 1993
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Scale: 1 Inc" = 50 Feet
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Wood Fence
FORMER TANK
LOCATIONS
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TANK TANK
1000 Oals. 500 Oals.
Wood Fence
Daniels Lane
SITE PLAN
UST SITE SOIL CHARACTERIZATION
K & D SALVAGE, 600 SOUTH UNION A VENUE
BAKERSFIELD, CALIFORNIA
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~
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BSK Job 893229
October, 1993
Fløure 3
i I
08-4
200 feet to
South Union
Avenue Curb
FORMER TANK LOCATIONS
WEST ~ ~ EAST
TANK ~2 ~~lTANK
1000 Gals. 500 Gals.
08-5
08-3
156 Feet to
Wood Fence at
Daniels Lane
o Proposed Test Boring
o 10 20 30
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Scale 1 inch = 20 Feet
PROPOSED BORING LOCATIONS
UST SITE SOIL CHARACTERIZATION
K & D SALVAGE, 600 SOUTH UNION A VENUE
BAKERSFIELD, CALIFORNIA
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BSK Job 893229
October, 1993
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HOSPITAL LOCATION MAP
UST SITE SOn. CHARACTERIZATION
K & D SALVAGE, 600 SOUTH UNION A VENUE
BAKERSFIELD, CALIFORNIA
~
& Ac;sociatf'S
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PUBLIC· COMMENT PERIOD ON A
PROPOSED CLEANUP PLAN FOR
THE K&D SALVAGE YARD SITE
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DEPARTMENT OF TOXIC
SUBSTANCES CONTROL
INTRODUCTION
The Former K&D Salvage Yard Site
(Site) is located at 600 South Union
Avenue, Bakersfield, California, Kern
County. From 1958 through 1989, the
Site was used as a metal recycler and
storage facility. Over the last several
years, the Department of Toxic
Substances Control (DTSC) has been
conducting investigations to determine
what kind and how much contamination
exists on site soil and groundwater. This
fact sheet provides information on what
was discovered during the
investigations, proposed cleanup
options, and public participation
activities planned for the community.
Public Review and
Comment Period
The Department ofToxic Substances Control
(DTSC) is seeking review and comment on
the draft Removal Action Work Plan (RAW)
and proposed draft Negative Declaration for
tl£K&DSalvage Yard-sité during a 30-day
public comment period.
Comment Period
February 26 - March 26,2003
Send Comments To
Maria Gillette
Site Mitigátion Program
Department of Toxic Substances Control
8800 Cal Center Drive
Sacramento, CA 95826
(916)255-3953
mgillett@dtsc.ca.gov
SITE DESCRIPTION
AND BACKGROUND
The Site encompasses approximately
10 acres of fenced, vacant land, and is
located in an area of town that houses
light industrial, commercial businesses,
and some residences. Directly south of
the Site is the abandoned Benham and
, -Johnson/Double "D" metal recycling
facility. Though the sites are adjacent,
they are being dealt with as two
separate projects due. to the different
industrial activities that occurred at
each of them.
Information Repository
Copies of the draft RAW, Negative
Declaration and other Site-related documents
are available for review at:
Holloway-Gonzales Public Library
506 E, Brundage Lane
BakerSfield; CA93307
805-861-2083
And
Department of Toxic Substances Control
Attn: Librarian
8800 Cal Center Drive
Sacramento, CA 95826
(916)255-3758
The Site was used for storage and
recycling of metal from 1958 until 1989, ,
when it was abandoned by its owners.
For the next ten years the Site was
subject to unauthorized dumping and occupied by transients. In October 1998, DTSC
removed debris, such as household items and furniture, in preparation of conducting
preliminary soil sampling in the winter of 1999. Analyses of the sampling confirmed
that Site soil is contaminated with polychlorinated biphenyls (PCBs) and heavy metals
The energy challenge facing Cal(fornia is real. Every Californian needs to take immediate action to reduce ene/xy
consumption. For a list qfsimple wa}~\' you can reduce demand and cut your ene/xy costs, see our .vebsite (I{ www.dtsc.ca.gov.
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PLAZO PARA EL COMENTARIO DEL PUBLICO
ACERCA DEL PROPUESTO PLAN DE LIMPIEZA
PARA EL SITIO K&D SALVAGE YARD
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DEPARTMENT OF TOXIC
SUBSTANCES CONTROL
BAKERSFIELD, CALIFORNIA
INTRODUCCION
El antiguo sitio K&D Salvage Yard (el
Sitio) se encuentra ubicado en South
Union Avenue No. 600 en Bakersfield,
California, Municipio de Kern. Desde
el año 1958 hasta 1989, el sitio fue
utilizado como una instalación para el
reciclaje yalmacenamiento de metales. .
Durante varios de los años recientes,
DTSC (Departamento de Control de
Sustancias Tóxicas) ha estado
realizando investigaciones para
detenninar la cantidad y el tipo de
contaminación que existe en el suelo y
en las aguas subterráneas en el Sitio.
El objetivo del presente folleto es
infonnarles acerca de los resultados de
dichas investigaciones, las alternativas
de limpieza propuestas, y las
actividades que se han planificado para
tanto la participación del público como
la de la comunidad.
ANTECEDENTES Y
DESCRIPCION DEL SITIO
El Sitio abarca aproximadamente 10
acres de un terreno baldío y cercado, el
cual está situado en un sector de la
ciudad donde existen locales
comercia)e.s y .~~. in.dustria ligera y._
algunas viviendas, Justo al sur del
terreno se encuentra la instalación ya
abandonada de reciclaje Benham and
Johnson/Double "D" Metal. Aunque
los terrenos se encuentran uno allado
del otro, se considera los mismos
como dos proyectos separados debido
a que las actividades industriales que
se desarrollan en ambos difieren las
unas de las otras.
. .
Plazopara los Comentarios y
Revisión del Público
EI Departamento de Control de Sustancias
Tóxicas (DTSC) está solicitando los comentarios
y la r.evisión acerca del borrador del Plan de
Trabajo de Elimináción (RAW) y del borrador
de la Declaración.de Jmpacto Negativo para el
sitio K&D Salvage Yard durante el plazo de 30
días para que el público presente sus
comentarios,
Plazo para los Comentarios del Público
26 de Febrero del 2003 hasta Marzo 26 del 2003
Sìrvase Enviar sus Comentarios A
María Gillette
Programa de Mitigación de Sitios
Departamento de Control de Sustancias
Tóxicas
Cal Center Drive No,· 8800
Sacramento, CA 95826
(916)255-3953
. mgillett@dtsc.ca.gov
Buzones de Información
Las copias del borrador RAW, de la DeclaÍ'ación
de Impacto Negativo y documentos relacionados
con el mismo se encuentran a su disposición para
su revisión en:
Biblioteca Pública Holloway-Gonzales
E. Brundage Lane No. 506
Bakersfield, CA 93307
805-861"2083
Yen
Departamento de Control de Sustancias
Tóxicas
Atn.: Bibliotecaria
Cal Center Drive No. 8800
Sacramento, Ca
(916)255-3758
Desde 1958 hasta 1989, el Sitio fue
utilizado para el almacenamiento y el reciclaje de metales. En 1989 sus dueños dejaron
abandonado el sitio, Durante los diez años siguientes se utilizó el Sitio como un
basurero ilegal y también como albergue utilizado por vagabundos. En Octubre de 1998,
DTSC procedió a remover desperdicios del Sitio, tales como muebles y enseres, para
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el consumo de enel;giä, Para vel' una /ista de cÓmo usted puede reducir la demanda y sus costos de energia. visite nuestro sitio
en/a red en WWH: dIsc. ca. g"OV.
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including lead and zinc.
Studies have shown that PCBs can cause cancer in
animals and are probable carcinogins (cancer causing)
to humans. Exposure to high levels of lead ,can be
harmful to children, causing seizures, unconsciousness,
and in some cases, death. In adults, high lead levels
can cause increased chance ofillness during
pregnancy, fertility problems (in men and women), and
memory and concentration problems,
PROPOSED REMEDIAL ALTERNATIVES
Details of sampling and analysis of a site is compiled
during the Remedial Investigation (Rl) phase.
Alternatives on ways to cleanup the site are also
,analyzed during this phase. . Dnce the Rl phase is
completed, a document known as a draft Removal
Action Workplan (RAW) is developed and made
available to the public for review and comment. The
draft RAW summarizes the information obtained during
the Rl phase and makes a proposal on how to best
cleanup the site. All of the potential cleanup options
outlined during the Rl phase are evaluated against
three general criteria of effectiveness, ease of .
implementation, and cost. The best remedy is then
selected.
With these criteria in mind, the following five
alternatives were evaluated: .
maintained continuously, This alternative was not
chosen, in part, because it would not be effectÍve in
protecting public health over a long period of time,
#3) Excavation and Off-site Disposal
This alternative involves excavating contaminated soil
and transporting it to an off-site disposal facility. This
alternative was not chosen, in part, because although it
would essentially achieve the same results as option
#5, it would require a greater cost.
#4) Stabilization and Offsite Disposal
This alternative involves treating the contaminated soil
prior to excavating it and transporting it to an off-site
disposal facility. This alternative was not chosen, in
part,-because it would require a greater cost than
option #5.
#5) On-site Disposal and Capping
This alternative would involve consolidating the
contaminated soil, covering it with an engineered cap
(asphalt), and placing a deed restriction on the
property. The land use on the Site would be limited to
commercial and industrial uses.
CHOSEN REMEDIAL ALTERNATIVE
The alternative proposed in the draft RAW is option
#5, On-site Disposal and Capping, This proposed
alternative is effective in removing the risk and hazard
posed by the contamination without adversely affecting
on-site workers and off-site residents.
#1) No Further Action
This alternative means that nothing would be done to
treat, contain, or remove any of the contamination. The draft RAW and the draft California Environmental
This alternative was discounted for several reasons, QualityAct (CEQA) Negative Declaration will be
including that it would not reduce the toxicity or volume available for public review and comment during a 30-
of cQntaD1il1ation and that it would limit futureJand . _ _day public comment period.. -The-comment period is -.
usage. held so that the public's concerns are considered
before DTSC makes a final decision to either approve
or deny the draft RAW. The Negative Declaration
states that the proposed remedy will not negatively
impact the environment.
#2) Institutional/Engineering Controls
This alternative would involve the placement of a deed
restriction on the property that"would limit its use. It
would also require that the site fencing and signage be
Hearin!! Impaired
You can obtain additional information by using the California State Relay Service at 1-888-877-5378 (TDD).
Ask them to contact Maria Gillette at 916-255-3953 regarding the K&D Salvage Yard site.
.
d.~
poder lIevar a cabo un muestreo preliminar de suelos, 10
que ocurrió en el invierno de 1999, Los análisis de
muestreo realizados confirmaron que elsuelo del Sitio está
contaminado con binéfi]os policlorinados (PCBs) y metales
densos que incluyen plomo y zinc.
Los estudios efectuados han demostrado que los PCBs
pueden causar cáncer en los animales y son posiblemente
carcinógenos (que causan cáncer) a los seres humanos. La
exposición a altos niveles de plomo puede ser dañino para
los niños, provocando convulsiones (apoplejía), pérdida del
conocimiento y en algunos casos, la muerte, En los adultos,
los altos niveles de plomo pueden causar un aumento en la
probabilidad de contraer enfermedades durante el
embarazo, problemas de fertilidad (en hombres y mujeres),
y problemas de concentración y retención de memoria,
ALTERNATIVAS PROPUESTAS PARA MEDIDAS
CORRECTIVAS
Los pormenores del muestro-y de los análisis efectuados en
un terreno se recopilan durante la etapa denominada
Investigación Correctiva (RI). Asimismo, durante esta
misma etapa se analizan las alternativas para proceder a la
limpieza del sitio. Una vez que el RI se haya completado,
se prepara un documento denominado borrador RAW, el
cual se pone a disposición del público para sus comentarios
y estudio, El borrador RAW resume la información
obtenida durante la etapa RI y prop one las mejores
alternativas para proceder a la limpieza del terreno. Todas
las posibles alternativas de limpieza indicadas en la etapa
RI son evaluadas comparando tres puntos en general:
eficacia, facilidad para su implementación y costo.
Entonces, se selecciona la mejor de las medidas correctivas.
Considerando 10 anterior, se evaluaron las siguientes cinco
alternativas:
No, I) No se tomará ninguna acciónfutura
Esta alternativa significa que no se tomará ninguna medida
para tratar, contener 0 remover nada de la contaminación.
Se descartó esta aIternativa por varias razones, incluyendo
el hecho de que no reduciría la toxicidad ni el volumen de
contaminación y que limitaría el futuro uso de las tierras,
No, 2) Con troles de lngeniería e lnstitucionales
Esta alternativa involucraría la implementación de una
restricción en la escritura del bien raíz, la cuallimitaría el
uso del mismo. Asimismo, requeriría que se cercara la
Aviso a Personas con Problemas Auditivos
,.-;.
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propiedad y que se mantuvieran letreros en el terreno en
forma continua, Se descartó esta alternativa en parte dado
que no sería efectiva para proteg~r la salud pública a largo
plazo.
No.3) Excavación y Eliminación Fuera del Sitio
Esta opción incIuye excavar el suelo contaminado y
transportarlo a una instalación fuera del sitio. No se escogió
esta alternativa ya que aunque básicamente se conseguiría
el mismo resultado de la alternativa No.5, su costo sería
mucho más alto.
No, 4) Estabilización y Eliminación Fuera del Sitio
Esta alternativa contempla el tratamiento del suelo
contaminado previa a su excavación y su transporte a una
instalación fuera del sitio. No se escogió esta alternativa ya
que su costo es mucho más alto que la alternativa No.5
No, 5) Eliminación y Cubierta Protectora en el Sitio
Esta aIternativa involucraría consolidar el suelo
contaminado, instalar una capa protectora (asfalto) para
posteriormente fijar una restricción en el titulo de
propiedad de la misma. El uso de la propiedad en el Sitio
estaría limitada solamente para el uso industrial y
comercial.
ALTERNATIVA QUE SE SELECCIONO PARA LA
ACCION CORRECTIVA
La alternativa propuesta el borrador RAW es la No.5,
Eliminación y Cubierta Protectora en Terrreno, La eficacia
de esta alternativa que se prop one es que se eliminará el
riesgo que involucra la contaminación sin que afecte a los
trabajadores en terreno y alas personas que residen en las
afueras del sitio.
El borrador RAW y el borrador de la Declaración de
Impacto Negativo conforme al Acta de Calidad Ambiental
de California (CEQA) estarán a disposición del público
para su estudio y comentarios durante el plazo para los
comentarios del público el cual es de 30 días. La finalidad
de este último es para que se consideren las inquietudes del
público previo a que DTSC tome una decisión final para ya
sea aprobar 0 denegar el borrador RAW. La Declaración de
Impacto Negativo indica quela medida correctiva
propuesta no tendrá un imp acto negativo en el medio
ambiente,
Pueden obtener información adicionalllamando alServicio de Relevo del Estado de California, 1-888-877-5378
(TDD) Y solicitar que se les comunique con María Gillette al número 916-255-3953 con respecto al sitio K&D
Salvage Yard.
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FUTURE ACTIVITIES
After the public comment period has ended, DTSC will
review all comments received and make a final
determination to either accept or deny the RAW and
draft Negative Declaration. At the same time DTSC
announces the acceptance or denial of the draft RAW,
anyone who submitted either verbal or written
comments will receive DTSC's Response to
Comments document. This document provides all of
the comments submitted during the public comment
period and DTSC's response to those comments. The
Response to Comments will be availaþle in the
repositories that have been established for the site.
CONTACTS
If you would like additional copies of this fact sheet or
more information concerning the site, please contact:
Ms. Maria Gillette
Project Manager
Site Mitigation Program
Department of Toxic Substances Control
8800 Cal Center Drive
Sacramento, CA 95826
mgillett@dtsc.ca.gov
(916) 255-3953
Ms. Heidi Nelson
Public Participation Specialist
Department of Toxic Substances Control
8800 Cal Center Drive
Sacramento, CA 95826
hnelson@dtsc,ca.gov
(916)255-3575
Mediã Contact ~- - .
Ron Baker
Public Information Officer
Department of Toxic Substances Control
1001 I Street
Sacramento, CA 94814
rbaker@dtsc.ca,gov
(916) 324-3142
GLOSSARY
California Environmental Quality Act: The statutory act
that requires decision-makers to conduct an evaluation
of the environmental impact of proposed projects under
their jurisdiction. The Act also requires the department
or agency to provide the opportunity for public
comment.
Draft Negative Declaration: A document issued by the
regulatory agency when an initial environmental study
reveals no substantial evidence that the proposed
project will have any significant effect on the
environment. Meets the requirements set forth in the
California Environmental Quality Act.
Draft Removal Action Work Plan (draft RAW): A plan
in draft form that outlines a specific program leading to
cleanup of a contaminated site.
Metals: A group of elements that can be toxic at
relatively low concentrations.
Polvchlorinated Biphenyls: PCBs are mixtures of
synthetic organic chemicals and can range from oily
liquids to waxy solids. PCBs were used in hundreds of
industrial and commercial applications including
electrical equipment, plasticizers in paints, plastics and
rubber products; in pigments, dyes and carbon less copy
paper. PCBs are believed to be carcinogenic' (cancer
causing) to humans.
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ACTIVIDADES FUTURAS
Después que haya finalizado el plazo para los comentarios
del público, DTSC procederá a revisar todos los
comentarios recibidos y tomará una determinación fmal de
ya sea aceptar 0 no el borrador RAW y la Declaración de
Impacto Negativo, AI mismo tiempo en que DTSC anuncia
la aceptación 0 la denegación del borrador RAW, todos
aquéllos que hayan presentados sus comentarios ya sea por
escrito u oral recibirán el documento titulado Respuesta a
los Comentarios de parte de DTSC, el cual indica todos los
comentarios presentados durante el plazo de comentarios
por parte del público y la respuesta de DTSC a los mismos.
Este documento estará disponible en los buzones que han
sido establecidos para el sitio.
PERSONAS CON QUIENES COMUNICARSE
Si desea recibir copias adicionales acerca de este folleto
informativo 0 alguna otra información con respecto a este
sitio, sírvase comunicarse con:
Sra. María Gillette
Gerente de Proyecto
Programa Mitigación de Sitios
Departamento de Control de Sustancias Tóxicas
Cal Center Drive No. 8800
Sacramento, CA 95826
mgillett@dtsc.ca,gov
(916) 255-3953
. Sra. Heidi Nelson
Especialista en Participación Pública
Departamento de Control de Sustancias Tóxicas
Cal Center Drive No. 8800
Sacramento, Ca 95826
hnelson@dtsc.ca.gov
(916) 255-3575
Medios Informatives
Ron Baker
Información al Público
Departamento de Control de Sustancias Tóxicas
Calle 1 No, 1001
Sacramento, Ca 94814
rbaker@dtsc.ca.gov
(916) 324-3142
.~
GLOSARJO
Acta de Calidad Ambiental de California: Acta legalla cual
. requiere que las personas que toman decisiones en
proyectos bajo su jurisdicción, efectúen una evaluación del
impacto que aquellos propuestos proyectos causarían al
medio ambiente, Dicha Acta requiere asimismo que el
departamento 0 la agencia a cargo del proyecto dé al
público la oportunidad para que éste presente sus
respectivos comentarios.
Plan de Trabaio de Acción de Eliminación (borrador RAW):
Un plan en forma de borrador el cual destaca un programa
específico que Ilevará a la implementación de la limpieza
de un sitio contaminado.
Metales: Un grupo de elementos que pueden ser tóxicos en
concentraciones relativamente bajas.
Bifenilos Policlorinados (PCBs): son una mezcla de
sustancias sinteticas orgánicas químicas que varían de
liquídos aceitosos a sólidos como cera, PCBs fueron
utilizados en cientos de aplicaciones industriales y
comenciales, incluyendo el uso de plastificadores en
productos de pinturas, plástico y hule; en pigmentos,
tinturas y papel de copias sin carbón. Se cree que los PCBs
son cancerígenos (que causan cáncer) al ser humano,
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Mailing List Coupon
If you have any comments concerning the Former K&D Salvage Yardsite or if you would like to be put on the
site specific mailing list, please take a moment to fill out the infonnation below and mail it to Ms. Heidi Nelson,
DTSC, 8800 Cal Center Drive, Sacramento, California, 95826. DTSC mailing lists are solely for the purpose of
keeping persons informed ofDTSC activities, Mailing lists are not routinely released to outside parties. However,
they are considered public records, and, if requested, may be subject to release.
Name:
Address:
City, State, Zip Code
Phone Number:
Fax Number:
E-Mail:
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Cupón Lista de Direcciones
En el caso que usted desee presentar algún comentario con respecto al Antigua Sitia K&D Salvage Yard 0 si desea
que su nombre se inc1uya en la lista de direcciones del sitio específico, tenga la bondad de completar la informacÍón
que se indica a continuación y envíe la misma a la Sra. Heidi Nelson, DTSC, Cal Center Drive No, 8800, Sacra-
mento, California, 95826, Las listas de direcciones de DTSC son de uso exclusivo de este departamento y su única
finalidad es"mantenerlos informados acerca de las actividades que desarrolla DTSC. Estas listas no son divulgadas
a terceros. Sin embargo, ya que se considera que son documentos públicos y si así se solicita, podrían estar sujetas a
su divulgación.
Nombre:
Dirección:
Ciudad, Estado, Código Postal:
Número de Teléfono:
Número de FAX:
Correo Electrónico:
Comentarios/Preguntas:
L¡{1.
I
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THE FORMER K&D SALVAGE YARD SITE
June 19991
mSTORY OF THE SITE
1958 through 1989
K&D operates as a metal recycler and storage facility at 600 South
Union Avenue, Bakersfield, CA.
l2.8.2
The property owners abandon the Site.
1989 through 1999
Illegal dumping of debris such as old appliances, tires and household
items occurs. The Site is also frequented by the homeless.
Summer 1998
The Department of Toxic Substances Control (DTSC) issues an
Imminent and Substantial Endangennent Determination and Order
(Order) to the potentially responsible parties stating that they must
conduct and pay for an environmental investigation and eventual
cleanup of the Site.
Fall 1998
Responsible parties do not comply with the Order. DTSC agrees to
conduct and pay for the necessary environmental investigations and
eventual Site cleapup,
Winter 1999
DTSC removes visible debris, fences perimeter of the 10 acre Site,
and performs soil gas sampling. Preliminary investigations reveal
soil contaminated with heavy metals, waste oils, and polychlorinated
biphenyls (PCB's), however, DTSC determines that further
investigation is needed to fully characterize the Site.
~
DTSC begins public participation activities including developing a
Site specific mailing list, community questionnaire, and public
participation plan in preparation· of further environmental
investigations at the Site.
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Quiero agradècerle con anticipación por tomarse el tiempo para
llenar ia encuesta ad junta, y si usted tiene cualquier pregunta con
respecto al antiguo local de K&D Salvage Yard, por favor
comuníquese conmigo, llamando al (916) 324-3108, ó con Eric
Wallberg,. Administrador de Proyectos del Departamento,
llamando al (916) 255-3749 ó con Heidi Hansen al (916) 324-
3108. ~
FUTURE OF THE SITE
..1
The following infonnation represents the next steps to be taken on I
the Fonner K&D Salvage Yard project: ~
1
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Phase 1- Technical Activities
Remedial Investigation
Remedial Investigation: An in-depth investigation to
determine the nature and extent of contamination in order to
evaluate the need to treat site contamination and to identify
potential methods of treatment.
Feasibility Study
A study to identify and evaluate treatment methods proposed
in the Remedial Investigation.
Phase I - Public Participation Activities
+Public Participation Plan
-community interviews
-site tour
+Mailing List Development
+Establish a Repository
+Fact Sheet
* Other
Phase II- Technical Activities
Draft Remedial Action Plan
A document describing the proposed alternative for treating
soil and/or groundwater contamination at a hazardous waste
site.
Phase II - Public Participation Activities
+30-Day Public Comment Period
+Public Notice
+Public Meeting
+Fact Sheet
+Response to Comments
* Other
*Depending on the level of community interest, other public
participation activities may occur. Activities may include, but are
not limited to: public meetings, workshops, briefmgs, and
additional fact sheets.
For More Infonnation, please contact one of the following
DTSC representatives:
Eric Wallberg
DTSC
Project Manager
(916)255-3749
ewallberg@dtsc.ca.gov
Heidi Hansen
DTSC
Project Manager
(916)324-3108
hhansen@dtsc.ca.gov
You can obtain additional information by using the California
State Relay Service at 1-888-877-5378 (TDD). Ask them to
contact Eric Wallberg at (916) 255-3749 or Heidi Hansen at
(916) 324-3108 regarding the Fonner K&D Salvage Yard site.
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PUBLIC COMMENT PERIOD ONr~ r ~
PROPOSED CLEANUP PLAN FOR----- = -=-,-'
THE K&D SALVAGE YARD SITE ':r:~~1"f ~I:;,~1'S' .
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DEPARTMENT OF TOXIC
SUBSTANCES CONTROL
INTRODUCTION
The Former K&D Salvage Yard Site
(Site) is located at 600 South Union
Avenue, Bakersfie]d, California, Kern
County. From 1958 through ]989, the
Site was used as a metal recycler and
storage facility. Over the last several
. years, the Department of Toxic
Substances Control (DTSC) has been
conducting investigations to determine
what kind and how much contamination
exists on site soil and groundwater. This
fact sheet provides information on what
was discovered during the
investigations, proposed cleanup
options, and public participation
activities planned for the community.
Public Review and
Comment Period
The Department of Toxic Substances Control
(DTSC) is seeking review and comment on
the draft Removal Action Work Plan (RAW)
and proposed draft Negative DecJarat!~pXor .'-
. the K&D-Salvage Yard site during a 30-däý
public comment period.
Comment Period
February 26 - March 26,2003
Send Comments To
Maria Gillette
Site Mitigation Program
Department of Toxic Substances Control
8800 Cal Center Drive
Sacramento, CA 95826
(916)255-3953
mgillett@dtsc.ca.gov
SITE DESCRIPTION
AND BACKGROUND
Information Repository
Copies of the draft RAW, Negative
Declaration and other Site-related documents
are available for review at:
The Site encompasses approximately
10 acres of fenced, vacant land, ahd is
located in an area of town that houses
light industrial, commercia] businesses,
and some residences. Directly south of
the Site is the abandoned Benham -and
Johnson/Doub]e "D" metal recycling
facility. Though the sites are adjacent,
they are being dealt with as two
separate projects due to the different
industrial activities that occurred at
each of them.
Holloway-Gonzales Public Library
506 E, Brundage Lane
Bakersfield, CA 93307
805-861-2083
And
Department of Toxic Substances Control
Attn: Librarian
8800 Cal Center Drive
Sacramento, CA 95826
(916)255-3758
The Site was used for storage and
recycling of meta] from 1958unti] 1989, ,
when it was abandoned by its owners.
For the next ten years the Site was
subject to unauthorized dumping and occupied by transients. In October 1998, DTSC
removed debris, such as household items and furniture, in preparation of conducting
preliminary soil sampling in the winter of 1999. Analyses of the sampling confirmed
that Sitesoil is contaminated with polychlorinated biphenyls (PCBs) and heavy metals
The eller,'.,T)' challenge facing CalUÓrnia is real. Every Californian needs to tàke immediate action to reduce ener,'.,')'
consumption. For a list C?fsimple ways you can reduce demand and cut your enel:gy costs, see our ,vebsite at w,vw.dtsc.ca.gov,
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PLAZO PARA EL COMENTARIO DEL PUBLICO
ACERCA DEL PROPUESTO PLAN DE LIMPIEZA
PARAELSITIO K&D SALVAGE YARD
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INTRODUCCION
EI antiguo sitio K&D Salvage Yard (el
Sitio) se encuentra ubicado en South
Union Avenue No. 600 en Bakersfield,
California, Municipio de Kern. Desde
el año 1958 hasta 1989, el sitio fue
utilizado como una instalación para el
recicIaje y almacenamiento de metales..
Durante varios de los años recientes,-·
DTSC (Departamento de Control de
Sustancias Tóxicas) ha estado
realizando investigaciones para
detenninar la cantidad y el tipo de
contaminación que existe en el suelo y
en las aguas subterráneas en el Sitio.
EI objetivo del presente foIleto es
infonnarles acerca de los resultados de
dichas investigaciones, las alternativas
de limpieza propuestas, y las
actividades que se han planificado para
tanto la participación del público como
la de la comunidad.
ANTECEDENTES Y
DESCRIPCION DEL SITlO
EI Sitio abarca aproximadamente 10
acres de un terreno baldío y cercado, el
cual está situado en un sector de la
ciudad don de existen locales
comerciales y de industria ligera y
algunas viviendas. JUsto al sur del
terreno se encuentra la instalación ya
abandonada de recicIaje Benham and
Johnson/Double "D" Metal. Aunque
los terrenos se encuentran uno allado
del otro, se considera los mismos
como dos proyectos separados debido
a que las actividades industriales que
se desarroIlan en ambos difieren las
unas de las otras.
DE~ARTMENT OF TOXIC
SUBSTANCES CONTROL
Plazo para los Comentariosy
Revisión delPúblico
EI Departamento de Control de Sustancias
Tóxicas (DTSC) está solicitando 105 comentarios
Ý la revisión acerca del borrador del Plan de
Trabajo de Eliminación (RAW) y del borrador
de la Declaracióry. de Impacto Negativo. para ,el
sitio K&D Salvage Yard ~urante el plazo de 30
días para que el público presente sus
comentarios.
Plazo para los Comentarios del Público
26 de Febrero del 2003 hasta Marzo 26 del 2003
Sìrvase Enviar sus Comentarios A
María Gillette .
ProgramadeMitigación de Sitios
Departamento de Control deSustancias
Tóxicas
Cat Center Drive No, 8800
Sacramento, CA 95826
(916) 255~3953
mgillett@dtsc.ca.gov
Buzones de Información
. Las copias del börrador RAW, de la DeclaÌ'ación
de ImpactoNegativo y documentos relacionados
con elmismo se encuentran a su disposición para
su revisión en:
I
Biblioteca Pública Holloway-Gonzales
E. Brundage Lane No. 506
Bakersfield, CA 93307
805-861 c2083
Yen
Departamento de Control de Sustancias
Tóxicas
Atn,: Bibliotecaria
Cal Center Drive No, 8800
Sacramento, Ca
(916)255-3758
Desde 1958 hasta 1989, el Sitio fue
utilizado para el almacenamiento y el recicIaje de metales. En 1989 sus dueños dejaron
abandonado el sitio, Durante los diez años siguientes se utilizó el Sitio como un
basurero ilegal y también como albergue utilizado por vagabundos. En Octubre de 1998,
DTSC procedió a re~over desperdicios del Sitio, tales como muebles y enseres, para
La crisis de energia que enfrenta Caltlornia es un hecho real, Cada Cáliforniano debe lomar medidas ¡nmediataspara I'educ¡r
el consun/o de ene/:gia, Para vel' una /ista de cÔmo listed puede reduc¡1' la demanda Y SILl' costos de energia. )'¡site nuestro s¡t¡o
enla red ell W,VH: dIsc. CC/. go)',
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including lead and zinc,
Studies have shown that PCBs can cause cancer in
animals and are probable carcinogins (cancer causing)
to humans. Exposure to high levels of lead can be
harmful to children, causing seizures, unconsciousness,
and in some cases, death. In adults, high lead levels
can cause increased chance of illness during
pregnancy, fertility problems (in men and women), and
memory and concentration problems.
PROPOSED REMEDIAL ALTERNATIVES
Details of sampling and analysis of a site is compiled
during the Remedial Investigation (RI) phase,
Alternatives on ways to cleanup the site are also.
. analyzed during this phase. Once the RI phase is
completed, a document known as a draft Removal
Action Workplan (RAW) is developed and made
available to the public for review and comment. The
draft RAW summarizes the information obtained during
the RI phase and makes a proposal on how to best
cleanup the site. All of the potential cleanup options
outlined during the RI phase are evaluated against
three general criteria of effectiveness, ease of
implementation, and cost. The best remedy is then
selected.
With these criteria in mind, the following five
alternatives were evaluated: .
#1) No Further Action
This alternative means that nothing would be done to
treat, contain, or remove any of the contamination.
This alternative was discounted for several reasons,
including that it would not reduce the toxicity or volume
.of contamination and that it wouldJimit future land.
usage.
#2) Institutional/Engineering Controls
This alternative would involve the placement of a deed
restriction on the property that would limit its use. It
would also require that the site fencing and signage be
maintained continuously. This alternative was not
chosen, in part, because it would not be effective in
protecting public health over a long period of time.
#3) Excavation and Off-site Disposal
This alternative invälves excavating contaminated soil
and transporting it to an off-site disposal facility, This
alternative was not chosen, in part, because although it
would essentially achieve the same results as option
#5, it would require a greater cost.
#4) Stabilization and Offsite Disposal
This alternative involves treating the contaminated soil
prior to excavating it and transporting it to an off-site
disposal facility. This alternative was not chosen, in
part, because it would require-a'greater cost than
option #5.
#5) On-site Disposal and Capping
This alternative would involve consolidating the
contaminated soil, covering it with an engineered cap
(asphalt), and placing a deed restriction on the
property. The land use'on the Site would be limited to
commercial and industrial uses.
CHOSEN REMEDIAL ALTERNATIVE
The alternative proposed in the draft RAW is option
#5, On-site Disposal and Capping. This proposed
alternative is effective in removing the risk and hazard
posed by the contamination without adversely affecting
on-site workers and off-site residents.
The draft RAW and the draft California Environmental
Quality Act (CEQA) Negative Declaration will be
available for public review and comment during a 30-
day public commentpedod. The comment periodjs _
held so that the public's concerns are considered
before DTSC makes a final decision to either approve
or deny the draft RAW. The Negative Declaration
states that the proposed remedy will not negatively
impact the environment.
Hearinl! Impaired
You can obtain additional information by using the California State Relay Service at 1-888-877-5378 (TDD),
Ask them to contact Maria Gillette at 916-255-3953 regarding the K&D Salvage Yard site,
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poder llevar a cabo un muestreo preliminar de suelos, 10
que ocurrió en el invierno de 1999. Los análisis de
muestreo realizados confirmaron que el suelo del Sitio está
contaminado con binéfilos policlorinados (PCBs) y metales
densos que incluyen plomo y zinc,
Los estudios efectuados han demostrado que los PCBs
pueden causar cáncer en los animales y son posiblemente
carcinógenos (que causan cáncer) a los seres humanos. La
exposición a altos niveles de plomo puede ser dañino para
los niños, provocando convulsiones (apoplejía), pérdida del
conocimiento y en algunos casos, la muerte. En los adultos,
los altos niveles de plomo pueden causar un aumento en la
probabilidad de contraer enfermedades durante el
embarazo, problemas de fertilidad (en hombres y mujeres),
y problemas de concentración y retención de memoria.
ALTERNATIVAS PROPUESTAS PARA MEDIDAS
CORRECTIVAS
Los pormenores del muestro y de los. análisis efectuados en
un terreno se recopilan durante la etapa denominada
Investigación Correctiva (RI), Asimismo, durante esta
misma etapa se analizan las alternativas para pro ceder a la
limpieza del sitio. Una vez que el RI se haya completado,
se prepara un documento denominado borrador RAW, el
cual se pone a disposición del público para sus comentarios
y estudio. EI borrador RAW resume la información
obtenida durante la etapa RI y propone las mejores
alternativas para proceder a 1a limpieza del terreno, Todas
las posibles alternativas de limpieza indicadas en la etapa
RI son evaluadas comparandö tres puntos en general:
eficacia, facilidad para su implementación y costo.
Entonces, se selecciona la mejor de las medidas correctivas.
Considerando 10 anterior, se evaluaron las siguientes cinco
alternativas:
No.1) No se tomará ninguna acciónfutura
Esta alternativa significa que no se tomará ninguna medida
para tratar, contener 0 remover nada de la contaminación.
Se descartó esta alternativa por varias razones, inc1uyendo
el hecho de que no reduciría la toxicidad ni el volumen de
contaminación y que limitaría el futuro uso de las tierras,
No.2) Controles de 1ngeniería e Institucionales
Esta alternativa involucraría la implementación de una
restricción en la escritura del bien raíz, la cuallimitaría el
uso del mismo. Asimismo, requeriría que se cercara la
Avisoa Personas con Problemas Auditivos
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,
propiedad y que se mantuvieran letreros en el terreno en
forma continua. Se descartó esta altemativa en parte dado
que no sería efectiva para proteger la salud pública a largo
plazo.
No, 3) Excavación y Eliminación Fuera del Sltio
Esta opción inc1uye excavar el suelo contaminado y
transportarlo a una instalación fuera del sitio. No se escogió
esta altemativa ya que aunque básicamente se conseguiría
el mismo resultado de la alternativa No.5, su costo sería
mucho más alto.
No.4) Estabilización y Eliminación Fuera del Sitio
Esta alternativa contempla el tratamiento del suelo
contaminado previo a su excavación y su transporte a una
instalación fuera del sitio. No se escogió esta alternativa ya
que su cósto es mucho más alto que la alternativa No.5
No.5) Eliminación y Cubierta Protectora en el Sitio
Esta alternativa involucraría consolidar el suelo
contaminado, instalar una cap a protectora (asfalto) para
posteriormente fijar una restricción en el título de
propiedad de la misma. EI uso de la propiedad en el Sitio
estaría limitada solamente para el uso industrial y
comercial.
ALTERNATIVA QUE SE SELECCIONO PARA LA
ACCION CORRECTIVA
La alternativa propuesta el borrador RAW es la No, 5,
Eliminación y Cubierta Protectora en Terrreno. La eficacia
de esta alternativa que se prop one es que se eliminará el
riesgo que involucra la contaminación sin que afecte a los
trabajadores en terreno y alas personas que residen en las
afueras del sitio,
EI borrador RAW Y el borrador de la Dec1aración de
Impacto Negativo conforme al Acta de Calidad Ambiental
de California (CEQA) estarán a disposición del público
para su estudio y comentarios durante el plazo para los
comentarios del público el cual es de 30 días, La finalidad
de este último es para que se consideren las inquietudes del
público previo a que DTSC tome una decisión fmal para ya
sea aprobar 0 denegar el borradorRA W. La Declaración de
Impacto Negativo indica que la medida correctiva
propuesta no tendrá un imp acto negativo en el medio
ambiente,
Pueden obtener información adicionalllamando alServicio de Re1evo del Estado de California, 1-888-877-5378'
(TDD) Y solicitar que se les comunique con María Gilletteal número 916-255-3953 con respecto al sitio K&D
Salvage Yard.
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FUTURE ACTIVITIES
After the public comment period has ended, DTSC will
review all comments received and make a final
determination to either accept or deny the RAW and
draft Negative Declaration. At the same time DTSC
announces the acceptance or denial of the draft RAW,
anyone who submitted either verbal or written
comments will receive DTSC's Response to
Comments document. This document provides all of
the comments submitted during the public comment
period and DTSC's response to those comments. The
Response to Comments will be available in the
repositories that have been established for the site.
CONTACTS
- If you would 1ike addít{onaÏ copies õ(Ùl1s fact sheet or
more information concerning the site, please contact:
Ms. Maria Gillette
Project Manager
Site Mitigation Program
Department of Toxic Substances Control
8800 Cal Center Drive
Sacramento, CA 95826
mgillett@dtsc.ca,gov
(916)255-3953
Ms. Heidi Nelson
Public Participation Specialist
Department of Toxic Substances Control
8800 Cal Center Drive
Sacramento, CA 95826
hnelson@dtsc.ca.gov
(916)255-3575
MèaiäCöntad
Ron Baker
. Public Information Officer
Department of Toxic Substances Control
100 I I Street
Sacramento, CA 94814
rbaker@dtsc.ca.gov
(916) 324-3142
GLOSSARY
California Environmental Quality Act: The statutory act
that requires decision-makers to conduct an evaluation
of the environmental impact of proposed projects under
their jurisdiction. The Act also requires the department
or agency to provide the opportunity for public
comment.
Draft Negative Declaration: A document issued by the
regulatory agency when an initial environmental study
reveals no substantial evidence that the proposed
project will have any significant effect on the
environment. Meets the requirements set forth in the
California Environmental Quality Act.
... '-- ~ . ~.
._ -. __T .-. ..... ..-_-, ......':'"--- ~. - ~ -
...... ~- .- ,
Draft Removal Action Work Plan (draft RAW): A plan
in draft form that outlines a specific program leading to
cleanup of a contaminated site.
Metals: A group of elements that can be toxic at
relatively low concentrations.
Polvchlorinated Biphenyls: PCBs are mixtures of
synthetic organic chemicals and can range from oily
liquids to waxy solids. PCBs were used in hundreds of
industrial and commercial applications including
electrical equipment, plasticizers in paints, plastics and
rubber products; in pigments, dyes and carbon less copy
paper. PCBs are believed to be carcinogenic'(cancer
causing) to humans.
-. .... ,,-~ -..---
jÇ:.
ACTIVIDADES FUTURAS
Después que haya finalizado el plazo para los comentarios
del púbIico, DTSC procederá a revisar todos los
comentarios recibidos y tomará una determinación fmal de
ya sea aceptar 0 no el borrador RAW Y la Declaración de
Impacto Negativo, Al mismo tiempo en que DTSC anuncia
la aceptación 0 la denegación del borrador RAW, todos
aquéllos que hayan presentados sus comentarios ya sea por
escrito u oral recibirán el documento titulado Respuesta a
los Comentarios de parte de DTSC, el cual indica todos los
comentarios presentados durante el plazo de comentarios
por parte del público y la respuesta de DTSC a los mismos.
Estedocumento estará disponible en los buzones que han
sido establecidos para el sitio,
PERSONAS CON QUIENES COMUNICARSE
Si desea recibir copias adicionales acerca de este folleto
-inforinativo 0 alguna otra información con respecto a este
sitio, sírvase comunicarse con:
Sra. María Gillette
Gerente de Proyecto
Programa Mitigación de Sitios
Departamento de Control de Sustancias Tóxicas
Cal Center Drive No. 8800
Sacramento, CA 95826
mgillett@dtsc.ca.gov
(916) 255-3953
. Sra. Heidi Nelson
Especialista en Participación Pública
Departamento de Control de Sustancias Tóxicas
Cal Center Drive No, 8800
Sacramento, Ca 95826
hnelson@dtsc.ca.gov
(916) 255-3575
Medios Informatives
Ron Baker
Informacíón al Público
Departamento de Control de Sustancias Tóxicas
Calle 1 No. 1001
Sacramento, Ca 94814
rbaker@dtsc.ca.gov
(916) 324-3142
J
....
GLOSARJO
Acta de Calidad Ambiental de California: Acta legalla cual
requiere que las personas que toman decisiones en
proyectos bajo sujurisdicción, efectúen una evaluación del
impacto que aquellos propuestos proyectos causarían al
medio ambiente, Dicha Acta requiere asimismo que el
departamento 0 la agencia a cargo del proyecto dé al
público la oportunidad para que éste presente sus
respectivos comentarios.
Plan de Trabaio de Acción de Eliminación (borrador RAW):
Un plan en forma de borrador el cual destaca un programa
específico que llevará a la implementación de la limpieza
de un sitio contaminado,
Metales: Un grupo de elementos que pueden ser tóxicos en
concentraciones reIativamente bajas. -
Bifenilos Policlorinados (PCBs): son una mezcla de
sustancias sinteticas orgánicas químicas que varían de
liquídos aceitosos a sólidos como cera. PCBs fueron
utilizados en cientos de aplicaciones industriales y
comenciales, incluyendo el uso de plastificadores en
productos de pinturas, plástico y hule; en pigmentos,
tinturas y papel de copias sin carbón. Se cree que los PCBs
son cancerígenos (que causan cáncer) al ser humano,
?D
..
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Mailing List Coupon
If you have any comments concerning the Former K&D Salvage Yardsite or if you would like to be put on the
site specific mailing list, please take a moment to fill out the infonnation below and mail it to Ms, Heidi Nelson,
DTSC, 8800 Cal Center Drive, Sacramento, California, 95826. DTSC mailing lists are solely for the purpose of
keeping persons infonned ofDTSC activities. Mailing lists are not routinely released to outside parties. However,
they are considered public records, and, if requested, may be subject to release,
Name:
Address:
City, State, Zip Code
Phone Number:
Fax Number:
E-Mail:
~--"'--"--'-'-----'--'-"'-"'------------'----""'-----......--...........................--------.-.-....--.....------................._---
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._._...._...___.____.__............_....__.___..__._.__............___......_......._._.............._....___._.___.....________.____.n....
..................................
.................................................... ................................. .....................................-...............................................
----- ~
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- - --~-
--------
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Comments/Questions: ---------.--------------------.-.--------.--------..-----------.--------------------.-------
.................................--.........» ._..........._.__..........._~...... .....»....................-.........-....-
... ............................- ...........-.......-...-..........-..... ...........~....~..~~......~ ...................-......-......-........
........-..........._.....~ ..................................-....--.-.......
........~.......__..._..... ......._........~..._......- ...~..._.......~..............
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-- - --- ---
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Cupón Lista de Direcciones
En el caso que usted de see presentar algún comentario con respecto al Antiguo Sitio K&D Salvage Yard 0 si desea
que su nombre se incluya en la lista de direcciones del sitio especítico, tenga la bondad de completar la información
que se indica a continuación y envíe la misma a la Sra. Heidi Nelson, DTSC, Cal Center Drive No. 8800, Sacra-
mento, California, 95826, Las listas de direcciones de DTSC son de uso exclusivo dè este departamento y su única
tinalidad es mantenerlos infonnados acerca de las actividades que desarrolIa DTSC, Estas listas no son divulgadas
a terceros, Sin embargo, ya que se considera que son documentos públicos y si así se solicita, podrían estar sujetas a
su divulgación.
Nombre:
Dirección:
Ciudad, Estado, Código Postal:
Número de Teléfono:
Número de FAX:
Correo Electrónico:
Comentarios/Preguntas:
.
.
.
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-
BAKERSFIELD
FIRE DEPARTMENT
MEMORANDUM
DATE: June 7, 1999
TO: Ron Fraze, Chief
FROM: Ralph E. Huey, Director Office of Environmental Services 4
SUBJECT: Hazardous Waste Site at 340 Daniels Lane
Ron, This site is the former D & D Auto Dismantler and Metal Recycler and is located
adjacent to the former K & D Auto Dismantler which has an address of at 600 S Union. Both the
K & D site and the D & D site are state clean-up sites and are being investigated by California
Department of Toxic Substance Control (DTSC). Eric Wallberg is the project manager for
DTSC and will be conducting a limited site assessment including soil sampling and analysis on
both sites this summer. The sites are being handled separately because of funding. The K & D
site is a California only site however, the former D & D site is being funded through a federal
grant.
We met with Eric Wallberg and Heide Hanson on Friday (6-4-99) for an update on both
of these contaminated sites. The area was annexed into the city on November 10, 1994. At that
time the K & D site had been abandoned however, the D & D site was still operating. There is a
third site adjacent to D & D on the east side that is also under investigation. This property is the
former K & D Solid Landfill site and is currently under investigation by the Regional Water
Quality Control Board and the local implementing agency for solid waste (Kern County). The
three sites form a complete boundary along the north side of Daniels Lane from S Union to the
end of Daniels Lane and the solid waste landfill extends beyond Daniels Lane to the east, an area
of approximately 30 acres.
~e & D site as well as the K & D dismantling site has soil contaminated with lead as
well as P 's, PCB's and various hydrocarbon constituents including Benzene, Toluene, Ethyl
Benze an Xylenes. A more complete profile ofthe extent ofthe contamination will be
completed over the next few months. .
Pamela McCarthy's memo, reporting the Prop 65 notification of this site states that "The
property is occupied by a resident who has daily visits by a friend with a child..." This occupant
has now moved and the site is vacant. Both the former K & D salvage yard and the D & D
salvage yard are currently fenced. The gates at the D & D site are not in the best shape however.
'Y~de W~ ~.A0Pe ~ A W~ II
/'
We will be working with DTSC to attempt to maintain security on these sites.
In our meeting Friday the state was interested in conducting public informational
meetings with local residents. We will also be working with them to find a suitable location - - -
in the area - - - for this meeting. DTSC was not interested in having the meeting at a city
government building.
Inna Carson has requested that I summarize the status of the contamination at the K & D
site as well as the meeting with DTSC. That summary should be completed today, you will of
course get a copy.
REH/ed
cc: K. Blair
H. Wines
a
CallEPA
DepaT1ment of
Toxic Substances
Control
10151 Croydon Way
Suite 3
Sacramento. C4
95827-2106
tM I It:e è. - 'P(.r-;I
"August 2, 1996
Mr. steve McCally, R.E.H.S.
Director
Kern County Environmental Health
Services Department
2700 M Street, suite 300
Bakersfield, California 93301
II! 1,\
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-.........-
---
K & D SALVAGE YARD, 600 SOUTH UNION AVENUE,
BAKERSFIELD, CALIFORNIA 95678
Dear Mr. Mccally:
The letter you sent to the Department of Toxic
substances Control's (DTSC's) Clovis office requesting
action on the subject property (Site) was recently
referred to DTSC's Sacramento office. DTSC is aware of
the nature of the contamination at the site and
recommends the next phase of investigation to be
completed be a Preliminary Endangerment Assessment
(PEA). The PEA will assess the nature and extent of
onsite contamination and estimate the potential threat
posed to human health and the environment.
DTSC does not have a schedule for requiring
completion of a PEA at the site and was not aware that
access to the site was unrestricted. Until the PEA and
any required remediation is completed, it will be
necessary to restrict access to the Site. DTSC will be
coordinating with your office in the future to conduct
a site visit and explore viable alternatives for
stabilizing the Site. Recent discussions with
Mr. Brian pitts of your office indicate that DTSC's
planned activities will satisfy the concerns expressed
in your letter.
If you have any questions please contact me at
(916) 255-3709.
sincerely,
~¡;~
Eric J. Garcia
site Evaluation Lead
Central California
Cleanup Operations Branch
EG.dm
c:\EG47W.076
~
.
Pete Wilson
Governor
James M. Strock
Secretary for
Environmental
. Protection
."
. .
....
Primed on Recycled Pepe,
STATE OF l.ALlFORNIA - ENVIRONMENTAL PROTECTION AGENCY
PETE WilSON, Governor
DEPARTMENT OF TOXIC SUBSTANCES CONTROL
"'GION 1
151 CROYDON WAY, SUITE 3
SACRAMENTO, CA 95827-2106
(916) 255-3549
_.
Miy 20, 1996
I -.~,'"
Mr. steve McCalley, Director
Kern County Department of Environmental
2700 "M" street
Bakersfield, CA 93305
.', "
----
. -----...
Hè-a-l-th
--------
K & D SALVAGE, 600 SOUTH UNION AVENUE, BAKERSFIELD, CA
Dear Mr. McCalley:
This letter is to notify you and your Department that
the above subject has been assigned to the Central California
Cleanup Operations Branch for mitigation. Mr. Eric Garcia
will be the project manager overseeing the security,
stabilization and mitigation of the site. Mr. Garcia can be
reached at (916) 255-3709, Dept. of Toxic Substances Control,
Region 1, 10151 Croydon Way, suite 3, Sacramento, CA 95827~2106.
If you have any questions or if I can be of further
assistance, please call Bruce Butterfield of my staff at (209)
297-3942.
Sincerely,
(7tl~~/dL
Charles A. McLaughlin
Chief, Northern California Branch
State Regulatory Programs Division
cc: See next page
.,
. .
....
Printed on Recycled PStxJf
Mr. steve McCalley
Page 2
cc: Mr. Brian Pitts
Kern County Department of Environmental Health
2700 "M" street
Bakersfield, CA 93305
Mr. Robert Taylor
Regional Water Quality Control Board
Central Valley Region
3614 E. Ashlan Ave.
Fresno, CA 93726
Mr. Eric Garcia
Department of Toxic Substances Control
Central California Cleanup Operations Branch
10151 Croydon Way, suite 3
Sacramento, CA 95827-2106
Ms. . Astrid Johnson
Department of Toxic Substances Control
1515 Tollhouse Road
Clovis, CA 93611
Mr. James Tjosvold
Department of Toxic Substances Control
Central California Cleanup Operations Branch
10151 Croydon Way, suite 3
Sacramento, CA 95827-2106
Hollowell met me at the site on March 6, 1996. He directed me to
an area between the RR tracks and Madison Street. I saw piles of
dirt ,that appeared similar to the piles of dirt in Hollowell's
yard. Hollowell said that the piles were much larger last summer
and that people commonly pulled their trucks into the field and
took dirt.
The piles of dirt on Daniels property that Hollowell claims to be
the source of the dirt that he took appears to have been dumped
onto Daniels property. The presence of hydrocarbons in the dirt
indicates that it is from another source. The dirt is similar to
but may not be part of the K&D Salvage operation.
On March 8, 1996 I spoke with Daniel's consultant, Bob Crewdson,
and advised him of the investigation. He said that he would advise
the Daniels and would forward analytical data to me from a SWAT
assessment.
To date this data has not been received.
Status To Date
1. John Hovannisian (owner of the property at 1906 Filson) has
not been contacted.
2. Daniels (owner of the property suspected of being the source
of the contaminated dirt) has not been directly contacted.
His consultant has been advised of the situation and said that
he will relay it to his client. He added that Daniels is
eighty-five years old and in failing health.
3. The field where the dirt is reputed to have come from has been
inspected but not sampled.
4. RWQCB has been notified and advised of this Department' s
concern's.
5. CALEPA-DTSC has been notified and advised of this Department's
concern's.
6. Prop. 65 form has been filed.
Complications
1. Hollowell has no money for clean-up.
2. Hollowell's neighbor at 1904 Filson Street, Paul Saunders, is
coincidentally under an abatement order from the Integrated
Waste Management Board for operating an illegal tire recycling
facility. Saunders has made threats to kill a building
inspector and anyone else that he perceives to be causing him
legal problems. We have been advised that a warrant has been
issued for Sander's arrest.
Issues
1. A public health threat from contaminated soil exists at
Hollowell's yard. The same soil appears to be located in an
open field west of Madison Street on property owned by
Daniels. However the dirt may not have ultimately originated
at the Daniels property.
2. This investigation revealed that an assessment to determine if
hazardous waste occurs at the K&D Salvage (west) yard is
lacking. A public health threat may exist at K&D Salvage
yard. The yard is in a residential neighborhood and open to
unrestricted access. Part of it is recognized to be a threat
and has been fenced. However, large areas are open to public
access and may pose a threat to the health of the residents in
the area.
cc:
complain\Hollo.mem March 25, 1996
ENVIRONMENTAL HEALTH SERVICES DEPARTMENT
STEVE McCALLEY, R.E.H.S., Director
2700"M" STREET, SUITE300
BAKERSFIELD, CA 93301
10ne: (805) 862-8700
. AX:(805)862-8701
Ifl'!~\'\/~';~'í.~"""-,
0:::t)
-'" ()!-("-':'\ \\\""
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RESOURCE MANAGEMENT AGENCY
DA VlD PRICE III, RMA DIRECTOR
Engineering" Survey Services Department
Environmental Health Services Department
PlannIng Department
Roads Department
NARRATION FOR A COMPLAINT INVESTIGATION
WORK ORDER: 5918
TRACKING #: 96-
DATE OF INCIDENT: 02-07-96
DATE OF NARRATION: 02-08-96 (updated as needed)
NARRATION BY: Brian Pitts (KCEHSD)
RESPONDERS: Brian Pitts
Dan Starkey
COMPLAINANT:
l.
2 .
confidential
Kern County Waste Management Dept.
COMPLAINT:
Hollowell is scavenging metal from contaminated
dirt and dumping the dirt in the landfill.
LOCATION:
Charles Hollowell residence
1906 Filson Street
Bakersfield, CA 93307
805-831-1065
Prop. OWner:
John Hovannisian
500 Mooney Boulevard
Tulare, CA 93274
(owner listed for the property at 1906 Filson)
MATERIAL:
Dirt contaminated with unknown material.
Analytical results from one composite sample
indicate that the dirt has hazardous levels of
copper, lead and PCB. Other metals are elevated
including mercury. The dirt has contamination from
hydrocarbons.
RESPONSIBLE PARTY: 1.
Charles Hollowell
1906 Filson Street
Bakersfield, CA 93307
805-831-1065
SUSPECT:
NA
CONTACTS:
1.
Charles Hollowell
NARRATION:
02-08-96
At approximately 930 Dan Starkey and I drove to Filson and met
Hollowell. We identified ourselves and explained the complaint to
him. His yard is a residential sized yard in a residential arèa.
I saw a backhoe and other equipment consistent with light
construction. Three piles of dirt could be seen from the street.
They appeared oily and dark. It was difficult to tell because
recent rains got everything in the yard wet. When we entered the
yard to speak with Hollowell we could smell a distinct odor similar
to oil or petroleum. A screen was set on the east side of the yard
and it appeared that, they had been dumping soil through the screen.
Three other men were milling around the yard watching us.
Hollowell told us the following in summary:
He had some spare time and wanted to make extra money. He has
seen scrap metal in the dirt at the old K&D Salvage yard. He
went to the old K&D Salvage yard near the intersection of
South Union Avenue and Daniels Street and took dirt off of the
vacant lot. He took the dirt to the Filson Street yard and
has been pouring it through screens to remove scrap metal.
He sells some of the metal to recyclers and some of the
material he scavenges he takes and sells at the swapmeet.
When they accumulate enough dirt they take it to the landfill
and dump it.
I told him that part of our concern was prompted by a complaint
from one of the landfills that they might be trying to take
contaminated dirt to the landfill. I explained that the landfills
cannot take contaminated dirt and that he might get in trouble if
he tried. Hollowell then said that he has never taken dirt to any
landfill. After further questioning he admitted that he has never
received permission from the property owner to take the dirt. He
said that he figured that it was "ok" because he has seen others
take dirt from the yard. He also wanted to clarify his earlier
statement about where the dirt came from. He said that they loaded
it from the east side of the lot at a location near RR tracks west
of Madison and north of Belle Terrace.
I asked for and received permission to collect soil samples for
analyses. I donned appropriate protective equipment and collected
samples as follows:
Filson #1 Sampled from the southern-most soil pile in the yard.
Sample is a composite of dirt from two points dug
approximately three inches into the pile. One point was
near the upper third of the pile on the south site and
the other was from a similar location on the east side of
the pile. Photographed.
Filson #2 Composite sample of dirt from two piles. One part of the
sample is from dirt under the shaker (screen). The other
part is from the low pile on the north end of the yard.
Photographed.
We told Hollowell that the analyses should take about two weeks and
that we would call him with the results. He said that he would not
do anything with the soil until we advised him.
We left ar approximately 1030 and drove to the K&D yard. The dirt
in the yard was similar in appearance to the dirt in Hollowell's
yard.
We took the samples to BC Laboratories for analyses.
I briefed Canas on the case when we returned to the office.
02-15-96
Received analytical from BC Labs.
and lead with elevated levels
Advised Canas.
Soil tested hazardous for copper
for mercury, nickel and zinc.
02-16-96
Called DTSC and left a message with Fujitsubo requesting
information on K&D Salvage.
Spoke with O'Rullian about the site. He informed me that the case
is being handled by the RWQCB and he directed me to Dianne Wilson.
She had their file and loaned it to me to read.
I discovered that the contact at the RWQCB is Scott Moore. I
called his number and left a message for him to call me. Canas
wanted to see the site. We drove to Hollowell's house on Filson in
eh afternoon. The gate was locked and no one was home.
02-20-96
"
Drove to Filson and met Hollowell. Hollowell described the
location where he took the dirt from. He described it as a
location west of Madison Street, north of Belle Terrace and south
of where the RR crosses Madison. He said it was from an area east
of the large fenced area in the field. He was not sure of the
exact location and directed me to circle two areas on a map that I
had with me. I asked him to go with me to the site and show me the
exact location. He said that he was too busy at the time and said
that he would at a later time. I told him that the initial
analytical results indicate that the soil is hazardous for copper
and lead and that other metals were elevated. I told him to keep
people, especially children away from the dirt. He said that he
would. Hollowell said that the dirt has been in the yard since
last summer and he was not concerned about having ita while
longer.
02-22-96
I called Scott Moore.
interest in the case.
I explained the case and told him about my
I faxed analytical results to him.
I received a call from Bob Turner of the RWQCB ((209) 445-6185).
He said that he was interested in the case because of a pending
SWAT. I explained the situation to him. He said that the DTSC was
interested in the site and suggested that I call Claudia Johansen
or Bruce Butterfield.
I called Hollowell to try to set up an appointment to meet me at
the site. Dan Starkey informed me that he heard that a neighbor of
Hollowell, Paul Saunders, threatened to kill someone from the Solid
Waste Department. That Department, coincidentally, has an
enforcement action with the IWMB against Saunders.
02-23-96
I called Bruce Butterfield and left a message requesting that he
call me.
I received analytical r.esults that showed hazardous levels of
metals and PCB.
I called and spoke with Hollowell. He was unable to meet with me
today and said that he would meet with me early next week. I asked
him to again describe the site where he got the dirt. He
reiterated his earlier description and upon questioning insisted
that he took it from the lot west of Madison, south of where the,RR
tracks cross Madison. I asked him if he remembers seeing the large
fenced area in the field described. He said "yes" and said that he
did not go into the fenced area. He said that the dirt piles are
now overgrown with grass, but he is confident that he could
relocate the spot. I told him about the analytical results.
02-29-96
George Evans told me that Paul Sanders, Hollowell's next door
neighbor, been threatening to kill one of the Department's building
inspectors and anyone else from the Department that crosses him.
Apparently a warrant has been issued for Sanders for making
terrorist threats. He wanted to advise me so that I would be
careful if I was in the neighborhood. I asked Evans to send a copy
of Sanders' "mug shot" when they arrest him.
I called and spoke with Butterfield. He said that he was familiar
with the KD Salvage yard and described it as very contaminated. He
was not su~e what the status of the case ié or which agency had
l.ead status. We discussed disposal options for the soil at
Hollowell's yard. He expressed a possibility that the state may
pay for emergency clean-up to get the hazardous waste out of the
neighborhood. Butterfield said that my supervisor would need to
make the request. I told him that an additional concern was that
the residents in the area have unrestricted access to an area
contaminated with hazardous waste. He said that he noted that
scavengers were in the area when he inspected it several years ago,
and was unsure why his Department did not act at that time.
I noted that Hollowell hadn't called me.
and had no answer.
I called his residence
03-01-96
I concluded the primary portion of my investigation and issued
"Prop. 65" notifications.
03-04-96
I called and left a message for Hollowell to call me.
03-06-96
Hollowell called at approximately 0810. He said that he could meet
with me at the site now. I left the office and met with Hollowell
and another man. We walked into the field and they directed me to
where they took the dirt from. I saw dirt piles that appeared very
similar to the dirt in Hollowell's yard. I photographed the dirt
and discussed the situation with the two men. Hollowell agreed to
leave the dirt in his yard alone until I advise him. Both said
that they were sorry for any trouble that has been caused and said
that they do not want to go to jail over this. I told them that I
had no intention of putting them in jail. Both said that they were
poor and could not pay any fines. They said that they have to dig
through dirt to get scrap metal and that they are worried sick over
this problem. They told me that the dirt piles used to be much
bigger and that "lots of people" have been hauling it off over the
months.
03-08-96
I called and spoke with Crewdson. I explained the sequence of
events to him that prompted my interest in the Daniels site. He
gave his perspective on the development of the case and made a case
that Butterfield's samples were "worthless" because bits of metal
are to be expected at a scrap yard and that their presence did not
make the soil hazardous.
He said that he had some SWAT material that he would forward to me
and advise the Daniels of my investigation.
03-18-96
I called Robert Turner (RWQCB) and left a message requesting
information on the status of the order from RWQCB to Daniels dated
November 1990 that requires Daniels to characterize the possible
hazardous waste at the site. This order appears to have been
prompted by the sampling by Butterfield.
I called Butterfield and left a message requesting information on
the DTSC precedents for classifying soils at recyclers.
Specifically, what precautions are taken to ensure that high levels
of metals dó not actually reflect pieces of wire, or lead weights,
etc. that would not normally classify as hazardous.
03-21-96
Butterfield called back and he said that he does not know of any
specific cases of legal precedent regarding sampling and analyses
at recyclers.
03-25-96
I called and spoke with Bob Turner (RWQCB) about the directive from
the RWQCB to Daniels that appears to require an assessment of the
western portion of the Daniel's property prompted by the samples
collected by Butterfield. He said that at the time they thought
that the samples collected by Butterfield were from the eastern
portion of the yard. He said that they did not actually know where
they were collected. The letter directs the Daniels to assess the
area that is currently fenced and no other area. Turner said that
they have no intention of requiring an assessment of any other area
and that was under the purview of "toxic's."
03-27-96
Joe Canas called the DTSC site mitigation branch and spoke with
Ivan Rodriguez to attempt to acquire funding for clean-up.
Rodriguez discussed the case with his staff and agreed to fund the
clean-up.
03-28-96
Dan Starkey and I went to the lot and collected composite samples
from each of four contaminated piles of dirt. I then composited
samples from piles 1 and 2 into one samples and samples from piles
3 and 4 into another. I transported the composite samples from 1
piles 1/2 and 3/4 to Zalco labs to have them analyzed for PCB. I
did this to verify that the soil piles were from the same waste
stream as the dirt in Hollowell's yard. PCB is a relatively quick
test and a positive result would support Hollowell's claim that it
is the same dirt.
Rodriguez said that they hired KES and that Charlie Heard is the
contact. I met Heard at Hollowell's house for a "job walk." We
then went to the open lot and he examined the additional dirt.
Heard said that they planned to begin at 0900 the next morning.
03-29-96
I met Heard and his crew at 0900. It became apparent that
additional roll-off bins would be necessary for the job. ~his was
because the contractor cannot fill a bin to capacity because of
vehicle code weight restrictions. Additionally, the dirt looses
compaction and "fluffs" when it is moved. Heard and Canas relayed
the situation to Rodriguez and received additional funding to cover
the cost overruns. The job was finished at 1615.
Complaint\Hollowell - April 11, 1996
KD Salvage
Chronology
06-12-72 RWQCB issued an Ind~strial Waste Discharge Requirements
to K&D Salvage Company. The disposal point appears to be
a large pit on the east side of the property, near
Madison.
1977 Site appears to have closed. Apparently, the western
portion of the facility was used as i scrap yard and a
large pit on the eastern portion was used as a solid
waste disposal facility.
07-28-77 K&D Salvage at 600 South Union Avenue was issued a solid
waste facilities permit. Permit states that the facility
accepts "commercial solid wastes," and" shredded material
from automobiles and Dirt." Owners are listed as Robert
I .and Sol B Daniels.
12-26-84 Clair Binder of the KCEHSD sampled three unspecified
areas at K&D Salvage. Analytical results indicated that
the samples are hazardous for metals.
04-22-87 RWQCB determines that the Toxic Pits Cleanup Act (TPCA)
applies to the site.
06-22-87 RWQCB reevaluated the site and determined that the site
is not subject to the TPCA. However, the RWQCB is
concerned that the site may pose a threat to water
quality.
11-19-90 RWQCB issues an order requiring a site assessment.
02-19-90' Don Ferguson (KCEHSD) inspects the site.
08-15-90 Bruce Butterfield, CALEPA-DTSC, inspected the western
side of the K&D Salvage yard due to a complaint. He
collected'two composite samples and had them analyzed for
metals. The analyses indicated that they had hazardous
levels of copper, lead, and zinc. DTSC notified the
RWQCB.
11-19-90 RWQCB directs the Daniels' to submit a workplan to assess
the lateral and vertical extent of metal contamination at
the site. This order appears to have been prompted by
samples collected by Butterfield on 8-15-90.
03-06-92 RWQCB inspected the site and found it in compliance with
the WDR.
12-06-93 Conditional Use Permit was issued to reopen part of the
site for continued recycling. Bakersfield City
recommended against issuance.
01-18-94 RWQCB memorandum accepts portions of K&D Salvage's SWAT
report and requires additional work in specified areas.
04-13-95 RWQCB sent a letter to Roberta Daniels requiring a
complete SWAT report.
Summer 95 Hollowell claims that he removed soil from Daniels
property sometime during the summer of 1995.
06-21-95 Bob Crewdson, consultant for K&D Salvage, met with the
RWQCB to discuss requirements for completion of the SWAT.
02-08-96 Starkey and Pitts inspect and sample soil at 1906 Filson
Street. The responsible party, Charles Hollowell,
admitted taking the soil from piles at the K&D Salvage
yard near Madison Street.
02-15-96 Analytical results indicated the soil has hazardous
levels of copper, lead, and PCB's.
Partial Summary of Analytical Results Showing Hazardous Levels
(All in PPM)
KCCB 10 KCCB 11 KCCB 12 KDOOl KD002 Filson 2 Regulatory
12-26-84 12-26-84 12-26-84 08-15-90 08-15-90 02-13-96 Threshold
"Metals "Metals Method TTLC - Metals
Scan" Scan" 6010
Copper 4,500 5,080 6,250 2,580 4,430 33,800 2,500
Lead 1,450 1,370 1,040 5,170 4,740 4,670 1,000
Mercury NA NA NA NA NA 14 20
Zinc 4,400 45,200 360,000 19,700 17,800 2,510 5,000
;
Nickel 222 1,160 6,250 565 818 439 2,000
PCB NA NA NA NA NA 120 50
TRPH NA NA NA NA NA 41,000 - - --
Pitts/complain/hollo3
Notes on samples:
KD001 Composite surface soil sample collected by Bruce
Butterfield (CALEPA-DTSC) during a complaint inspection
in 1990. Composite area is near and east of a concrete
pad on the west end of the property (see map for
approximate location) .
KD002 Composite surface soil sample collected by Bruce
Butterfield (CALEPA-DTSC) during a complaint inspection
in 1990. Composite area is near an "old shredder area"
in the western portion of the K&D Salvage Yard (see map
for approximate location).
Filson 2 Composite surface soil sample collected by Brian Pitts
(KCEHSD) during a complaint inspection in 1996. The
sample is from soil piles found at 1906 Filson Street.
The soil is reputed to have come from the K&D Salvage
Yard near Madison Street; east of the fenced area (see
map for approximate location) .
KCCB 10 Soil sample collected by Claire Binder (KCEHSD) in 1984.
File notes describe the sample as a "soil sample taken
from discarded soil in pit."
KCCB 11 Soil sample collected by Claire Binder (KCEHSD) in 1984.
File notes describe the sample as a "soil sample taken
from covered pit."
KCCB 12 Sample collected by Claire Binder (KCEHSD) in 1984. File
notes describe the sample as a "solid sample of solid
chunks from open pit."
complain \Hollo2 March 8, 1996
J
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1I.¡':'.Jnjuus M.J tl.:1" 1.1 1 ~ l..1bur.H ur,? Sect iun
LABORAT1RY REPORT FOR TOTAL METAL ANALYSIS
:o,.'s Name
C., ß i lv' ,::.. r= ~
Locat i on ji J llfl11L{ Dr? tL,l~ DUt-.{ f'..;/ ~
~. rtl 11 ¡ Itr IV( Bn I.:.f./5 FI0 Lf) C:~n--
j ,
ical Samples are digested wit~ concentrated nitric acid over a hot
Jre; samples are filtered and made to lOOrnL with 5~ nitric acid in
water. Metal analysis of the digest is by ICPAES. Results are
or's
1/
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reported
a s .!!.!).i!J..
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LADORA'J"ORY REPORT
Priority PollutAnts--Base-Ncutrals
(! b, ljJ/1) Date Received .{ 1/ ((<
Jr's Name I 'by Laboratory
. ea. tion /}v, : /ll n .10< /./Yf1 1. J ~ Collector's Sa.mp~e # ffW/)"'OI û
ÞÝ1 ke f)J.tJ!(J (J 1/ .. /{¿t./5 0 I~
Afy; ¡; /v1 ""'A H r; ¡fA ,,- ' . , /I 'H' '7l,
;al.Procedure: 'LL/Y YI . .: id;¡:(l(' --rrï/1 J. 1M/- ~ Á- cA~
-- r !hi; ~ lfJ. '7./' {j...f ~I /J /í1J "vi ~L., 'L /J--IL .IF" ~ tl.h,i1{1(JAu LJ~ d
1 .::::nn( J (;{!. ,1>
Concentra.tion Uni t5: ¡solids: - UR 1ft: (j I \JF,/L / rr
Licuids:
11 ;/ / / /î _C::: V!-/l/q(,., ~/t/ 9'1 I
"I' ï 7_ Detection
Jr' 5 SEUD'Ple # IkCèP. /)/0 ~~~ðIJ I~," 1') (,)~:7 Limi t
- - - ¡Q ui.
.:hloro-ethyl) ether -. - villi
- ;1....) l~ 'a
11orobenzene - - - . 10 () Õ
,
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-
--- -..
llorobenzene - - :--- 10
.:hloro-iso'Pro'Oyl} ether . . -'. - -
-, - -
Jroethane
50di-n-'Pro'Pylamine - -
- - -
:1zene
. , - -
ne -
h' )ethoxy)methane - - -
-
richlorobenzene - - -
lene -- - -
--
ona'Phthalene - - -
. thyl ene ..~. - - I
- - - - ~
-1 'Phthalate -
-,i trotoluene - - - .
.
thene - - - -
:i treteluene ---. - -
'-e - - -
butadiene - . - --
.ore
-o-nhenvl 'Phenvl ether ~ - -
''Phenvl 'Phenyl ether -. - -
.oro cyclopentadicne - - -
.
. -- I,.
_crobel"zene - - J I
~~ (
to
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~
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(-) = Net detected
(ble.nk) "" Uot determined
,e
Continued. on page 2
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CALÏFORNtA DEPARTMENT OF HEALTH SERVICES
HAZARDOUS MATERIALS LABORATORY
2151 aERk£LEY WAY. BERKELEY, CA,94704
PHONE: (415)540-3003
LABORATORY REPORT FOR TOTAL METAL ANALYSIS
HHLR.'1 ffl ~ ~ ¡?>ttJ
HMl R ,<1 d2lr,l ð ¡~ ,,, .
,
,
'I
COLLECTOR'S NAME: BUTTERFIELD.
SAMPLE LOCATION : K & D SALVAGE
BAKERSFIELD
COLLECTOR'S SAM~lE NO. k & D 001
ACTtVITY : ENFORCEMENt
DATE COLLECTED: e/15/S0
DATE RECEIVED: ä/22/90
ANALYTICAL
PROCEDURE =
ËPA-S~ 848
SAMPLES ARE DIGESTED WITH 1:1 HN03 (AND 301. H202, AND 1:1 HCL
IF APPLICABLE) OVER Po HOT PLATE. THE DIGESTATES ARE FILTERED
fiND HADE TO FINAL VOLUME ~ITH DEIONIZED H20. METAL ANALYSIS
OF THE DIGEST IS BY ICPAES. RESULTS ARE REPORTED AS HG/KG;
f1EtHOD:
3050 FOR SOLIDS; 3010 FOR lIQUIDS; 3005 FOR CLEAN ~AT£R
HML NUI'IBER . 800433 900434
.
CbllEtt SAHp t: KDo01 KD002
SAI'IPLE tYPE SOIL SOIL
AS-ARSEN1C 37.2 < ä.o
SÁ-BAR1UM 2010 USO
SE-BERYLUUI't 0.24 0.31
CD-CADMIUM 48.4 52.4
CO-COBALT 32.4 21.ê
CR-CHROMIUM 161 118
CU-COPPER 2580 r/ 4430 ~
HO-MOLYBDENUM 12.9 S.B!
Nt-NICKEL 565 818
PB-LEAD 5170 V 4740 V
SE-SELEN!UM < 8,0 < 8,0
TL-THALLIUM < 8.1 < 8.1
I) -VANADIUH 24.3 25.7
2N-ZINC '8400 V *' 15300 ~
Y 4.28 3.58
NOTE: < = BELOW DETECTION LIMIT OF tNSTRUMENT (+++)=NOT DETERHINEU ~y ICP
~4:~_cal~~;211;y of ~~~/1~~__b_:_ tO~~;11
7a~ALYST'5 SIGNATURE DATE MILAD S. ISKANDER, SUPERVISOR DATE
v
~ ([ C4') 1/ vl&'~
~ t,6.v) 1/rJ,,/70
.
cöttÈc-rdi~, t S NAMg ~ BUTTERFIEtD
rDCAT!ON: t{ AND D SALVAGE
600 S. UNION. BAKERSFIELD
. .>'.... ,¡t:, "', "-:fU',);~',
,,,,"': -- .. ~ ,t·-:-...
: . .:~, . ..,';;-", : .
,. .,.,',~,_~","':''':''f.~~,~~.~I¡;,.:,'f: ., ':l;~:-' ,"~.
7.'}·' , .,~.;;,\,t -, ';~^
~J: " ... 'J" , . '. ~ . ;¡¡.:
cAttFOtUUA bEPAA'1'MÈMf ð, tI~ALfÛ~¡~ftV'f~~§^;~t :~;',f'
ItAZÄRDoUS MATÈttíAt§ L!M6ftA'f~~Y>,~~ð'ff,~ft ,:t
LABoRATO~'l 1tËtJtl\rtrð~~Ü!;ti'f~~~ ~~.~ "" .
~" , ,,< .~~~.'.; ~~p:.; ,t}:~+:':., :;. : ..-:tj:
eoLfÆelfð'ft' ~ f ,. {"~ßððL:' ,
. ---'liB! .J(ðOtl2, ,-
AtTíVí~~! !NröftetM~Nf
.
. -
ANALYTICAL
PROCEDURE:
The samples are digested with HMo3. Ü202, artd Mel bVät
a ho~ plate. The digested sám~l~s áre filterêd ähð màdé
to 100 ml with 5% HN03 irt distil1ed deldtli~ed Wäter.
Results are reported às Mg/k~. Ref. ÈPÁ Method 3050.
o. C./ Metal analysis of the di~ests is by FÂAS.
HML NUMBER 900433 900434
COßLECT No. KD 001 1<0 002
SAMPLE TYPE SOIL SOIL
Z:ENC (ZN) 19;700 17;800
.}.,.:.:~
."..~: ."
SIGNATURES:
9~d~
~
///~~
Date
1/14/71'
S'¿t
·
LABORATORIES
Page
1
TOTAL CONCENTRATIONS
(California Code of Regulations, Title 22, Section 66261)
KERN COUNTY ENVIRONMENTAL HEALTH DEPT.
2700 M STREET, STE 300
BAKERSFIELD, CA 93301
Attn: BRIAN PITTS 862-8700
Date Reported: 02/13/96
Date Received: 02/07/96
Laboratory No.: 96-01531-2
Sample Description: FILSEN #2 SAMPLED BY BRIAN PITIS
Sampling Date/Time: 02/07/96 @ 10:30AM
Title 22 Waste Type: Type i: Millable Solid - No Free Liquid
Regulatory
Criteria
Method STLC TTLC,
Constituents Sample Results Units P.O.L. Method mq/L mq/kq
Antimony None Detected mg/kg 25. SW-6010 15. 500.
Arsenic 14. mg/kg 2.5 SW-6010 5.0 500.
Barium 523. mg/kg 2.5 SW-6010 100. 10000.
Beryllium None Detected mg/kg 2.5 SW-6010 0.75 75.
Cadmium 7.0 mg/kg 2.5 SW-6010 1.0 "'~;i þO-:-
Chromium 236. mg/kg 2.5 SW-6010 560. 2S00~
Cobalt None Detected mg/kg 12.5 SW-6010 80. 8000.
Copper 33800. mg/kg 2.5 SW-6010 25. 2500.
Lead 4670. mg/kg 12.5 SW-6010 5.0 1000.
Mercury 14. mg/kg 2.0 SW - 7471 0.2 20.
Molybdenum 23. mg/kg 12.5 SW-6010 350. 3500.
'~~,-.-;-< ~,-'" '..'
Nickel 439. mg/kg 12.5 SW-6010 20. '2000.
Selenium None Detected mg/kg 2.5 SW-6010 1.0 100.
Silver 11. 'mg/kg 5.0 SW-6010 5.0 500.
Thallium None Detected mg/kg 25. SW-6010 7.0 700.
Vanadium 48. mg/kg 2.5 SW-6010 24. 2400.
Zinc 2510. mg/kg 12.5 SW-6010 250. 5000.
Comment: All above constituents are reported on an as received (wet) sample basis.
Results reported represent totals (TILC) as sample subjected to appropriate
techniques to determine total levels.
P.Q.L. = Practical Quantitation Limit (refers to the least amount of analyte
quantifiable based on sample size used and analytical technique employed) .
STLC Soluble Threshold Limit Concentration
TTLC Total Threshold Limit Concentration
REFERENCES:
SW = "Test Methods for Evaluating Solid Wastes Physical/Chemical Methods",
EPA-SW-846, September, 1986.
r"
~7~
Dan Schultz
Laboratory Director
--
All results listed in this report are for the exclusive use of the submitting party, BC Laboratories, Inc, assumes no responsibility for repo!t .lteratlon, separation, detachment or third party Interpretation,
4100 Atlas Ct. . Bakersfield, CA 93308· [805) 327-4911 . FAX [805) 327-191 8
·
LABORATORIES
Page
1
Total Petroleum Hydrocarbons
KERN COUNTY ENVIRONMENTAL HEALTH DEPT.
2700 M STREET, STE 300
BAKERSFIELD, CA 93301
Attn: BRIAN PITTS 862-8700
Date Reported: 02/13/96
Date Received: 02/07/96
Laboratory No.: 96-01531-2
Sample Description: FILSEN #2 SAMPLED BY BRIAN PITTS
Sampling Date/Time: 02/07/96 @ 10:30AM
Constituents
Sample Results
Units
Method
P.O.L.
Method
Total Recoverable Petroleum
Hydrocarbons
43000.
mg/kg
10000.
EPA-418.1
Note: PQL's were raised due to high concentration of target analytes requiring
sample dilution.
California D.O.H.S. Cert. #1186
~~
Stuart G. Buttram
Department Supervisor
All results listed in this report are for the exclusive use of the submitting party. BC Laboratories, Inc, assumes no responsibility for repon IIIenItlon, separation, detachment or third party interpretation.
4100 Atlas Ct. . Bakersfield, CA 83308 . (805J 327-4811 . FAX (805J 327-1 91 8
·
LABORATORIES
Page
1
PCB Analysis
(EPA Method 8080)
KERN COUNTY ENVIRONMENTAL HEALTH DEPT.
2700 M STREET, STE 300
BAKERSFIELD, CA 93301
Attn: BRIAN PITTS 862-8700
Date Reported: 02/20/96
Date Received: 02/07/96
Laboratory No.: 96-01531-2
Sample Description: FILSEN #2 SAMPLED BY BRIAN PITTS
Sample Matrix:
Soil
Date Collected:
Date Extracted:
Date Analyzed:
02/07/96 @'10:30AM
02/16/96
02/20/96
Reporting
Units
Practical
Quantitation
Limit
Constituents
Analysis
Results
PCB-1016
PCB-1221
PCB-1232
PCB-1242
PCB-1248
PCB-1254
PCB-1260
Total PCB's (Summation)
None Detected
None Detected
None Detected
120.
None Detected
None Detected
None Detected
120.
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
20.
20.
20.
20.
20.
20.
20.
20.
Quality Control Data
Surroqates %' Recovery Control Limits
Decachlorobiphenyl Not Reportable 60-140
Note: PQL's were raised due to high concentration of target analytes requiring
sample dilution.
California D.O.H.S. Cert. #1186
~/L
Stuart G. Buttram
Department Supervisor
All results listed in this repon are for the exclusive use 01 the submitting party, BC Laboratories, Inc. assumes no responsibility lor report alteration, separation, detachment or third party interpretation,
4100 Atlas Ct, . Bakersfield, CA 83308· (805) 327-4811 . FAX (805) 327-1818
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California Regional Water Quality Control Board
Central Valley Region
Steven T. Butler, Chair
.
Fresno Branch Office
Internet Address: http://www.swrcb.ca.gov/-rwqcb5
3614 East AsbIan Aveòue, Fresno, California 93726
Phone (559) 445-5116· FAX (559) 445-5910
Gray Davis
Governor
Winston H. Hickox
Secretary for
Environmental
Protection
17 February 2000
Ms. Daphne H. Washington
Kern County Waste Management Department
2700 M Street, Suite 500
Bakersfield, Ca 93301
TRANSMITTAL OF ADOPTED WASTE DISCHARGE REQillREMENTS FOR OPERATION
AND CONSTRUCTION, ARVIN SANITARY LANDFILL, KERN COUNTY
Enclosed is an official copy of Order No. 5-00-023 as adopted by the California Regional Water Quality
Control Board, Central Valley Region, at its 28 January 2000 meeting.
~.IÎ~
DANE S. JO~~N .
. Senior Engineering Geologist
CRG No. 4239
Enclosure:
Adopted Order
Standard Provisions
cc: U.S. Environmental Protection Agency, Region 9, San Francisco
Mr. Tim Regan, Office of Chief Counsel, State Water Resources Control Board, Sacramento
Ms, Elizabeth Haven, Division of Clean Water Programs, State Water Resources Control Board,
Sacramento
California Integrated Waste Management Board, Sacramento
Department of Health Services, Office of Drinking Water, Fresno
Department of Fish and Game, Region IV, Fresno
Department of Water Resources, San Joaquin District, Fresno
Kern County Department of Environmental Health Services, Bakersfield
Kern County Department of Planning and Development Services, Bakersfield
Kern County Air Pollution Control District, Bakersfield
Kern County Water Agency, Bakersfield
Mr. Howard Wines, City of Bakersfield, Bakersfield
California Environmental Protection Agency
#r>
~J Rervcled Paper
~
CALIFORNIA REGIONAL WATER QUAUTY CONTROL BOARD
CENTRAL V ALLEY REGION
ORDER NO. 5-00-023
WASTE DISCHARGE REQUIREMENTS
FOR
COUNTY OF KERN
FOR
OPERATION AND CONSTRUCTION
ARVIN SANITARY LANDFILL
KERN COUNTY
The California Regional Water Quality Control Board, Central Valley Region, (hereafter Board)
finds that:
1. The County of Kern (hereafter Discharger) owns and operates a municipal solid waste
landfill approximately five miles west of the City of Arvin, in Section 31, TI1S, R29E,
MDB&M, as shown in Attachment A, which is incorporated herein and made part of this
Order.
2. The waste management facility contains one existing unlined waste management unit
covering 127 acres, as shown in Attachment B, which is incorporated herein and made part
of this Order. The facility is comprised of Assessor's Parcel Number (APN) 189-330-20-
00-0.
3. The Discharger may expand the waste management unit for the discharge of municipal
solid waste to an area of approximately 15 acres within the SW 1/4 of the NW 1/4 of
Section 31, T31S, R29E, MDB&M.
4. On 14 August 1992, the Board adopted Order No. 92-163, which prescribes waste
discharge requirements for the existing waste management unit. The facility is cJassified as
a Class ill landfill which accepts municipal solid waste in accordance with Title 27,
California Code of Regulations, §20005, et seq. (Title 27).
5. On 17 September 1993, the Board adopted Order No. 93-200, amending Order No. 92-163
and implementing State Water Resources Control Board Resolution No. 93-62, Policy for
Regulation of Discharges of Municipal Solid Waste.
6. ThisOrder updates the waste discharge requirements for the facility in conformance with
the California Water Code and Title 27, and the revisions and policies adopted hereunder,
and removes the facility from Attachment 1 of Order No. 93-200. This Order also
addresses operation of the unlined waste management unit and construction of any lateral
expansion or new waste management unit.
..
WASTE DISCHARGE REQUIREMENTS, ORDER NO. 5-00-023
COUNTY OF KERN
FOR OPERATION AND CONSTRUCTION
ARVIN SANITARY LANDFll.L
KERN COUNTY
-2-
7. Based on 1998 data, the waste management facility receives approximately 267 tons of
municipal solid waste per day with an estimated remaining capacity of 550,393 cubic yards
as of January 1, 1999. Final capacity is anticipated by September 2001. Waste diversion
alternatives are being considered by the Discharger. If one of these alternatives is selected,
the anticipated final capacity date would be April 2003.
SITE DESCRIPTION
8. The facility is in a topographically flat region of the Tulare Lake Hydrologic Basin of the
San Joaquin Valley. The native ground surface elevation ranges between approximately
360 feet above mean sea level at the northeast boundary of the facility and 345 feet abòve
mean sea level at the southwest facility boundary. The ground surface slopes
approximately 22 feet per mile toward the southwest.
9. The waste management facility is on Quaternary alluvial deposits. The soils underlying the
facility are unconsolidated soils, consisting of interbedded gravels, sands, silts, and clays.
10. The measured hydraulic conductivity of the native soils underlying the waste management
unit range between 9 x 10-4 and 4 x 10-7 em/sec.
11. The waste management facility is not within a fault hazard zone. The closest Holocene
fault is the White Wolf Fault, approximately five miles to the south. A Richter scale
magnitude 7.7 earthquake occurred along the White Wolf Fault in 1952.
12. An abandoned non-hazardous oil field waste processing facility, formerly operated by
V en Virotek, is on a 5-acre parcel within the southwest comer of the waste management
facility property. An estimated 75,000 cubic yards of impacted soil, and other processing
equipment remain. Waste Discharge Requirements Order No. 92-199 was adopted naming
both VenVirotek and Kern County as co-dischargers for the waste processing facility.
13. Land within 1,000 feet of the facility is used for cultivated crops and vacant land. A former
residence domestic well (California State Well No. 3l/29-30POl) is located approximately
150 feet north of the facility. The Discharger has identi.fied well 31129-30POl as a potential
source of additional water for operations at the waste management facility. Well 31/29-
30PO 1 is shown on Attachment B.
14. The facility receives an average of 6.1 inches of precipitation per year as determined from
data collected by the Department of Water Resources. The mean evaporation is 87 inches
per year as determined from evaporation data collected by the Department of Water
Resources between 1967 and 1978.
WASTE DISCHARGE REQUIREMENTS, ORDER NO. 5-00-023
COUNTY OF IŒRN
FOR OPERATION AND CONSTRUcnON
ARVIN SANITARY LANDFllL
KERN COUNTY
-3-
15. . The lDO-year, 24-hour precipitation event for the facility is estimated to be 2.5 inches, as
detennined from data furnished by the National Weather Service.
16. The waste management facility is within a l00-year floodplain based on the Federal
Emergency Management Agency's (FEMA) Flood Insurance Rate Map, COminunity-Panel
Number 060075 l3ooB, dated 29 September 1986.
17. There are ten municipal, domestic, industrial, or agricultural supply wells within a I-mile
radius of the site. No surface springs or other sources of groundwater supply have been
observed.
18. The landfill water supply well (California State Well No. 31/29-31DI) is at the northwest
comer of the waste management unit. The well was drilled to a total depth of 320 feet
below ground surface. A surface seal reportedly exists to 50 feet below ground surface.
The remainder of the borehole is gravel packed.
SURFACE AND GROUND WATER CONDITIONS
19. The Board adopted the Water Quality Control Plan for the Tulare Lake Basin; Second
Edition (hereafter Basin Plan), that designates beneficial uses and contains water quality
objectives for all waters ofthe Basin. This Order implements the Basin Plan.
20. Surface drainage is toward the Kern Lake Bed in the Kern Delta Hydrologic Area (557.10)
of the Tulare Lake Basin.
21. There are no identified surface water bodies within one mile of the facility.
22. The first encountered areal groundwater is approximately 59 to 80 feet below the native
ground surface. Groundwater elevations range from 280 feet MSL to 288 feet MSL.
23. Monitoring data indicates that the groundwater is unconfined. The depth to groundwater
fluctuates seasonally as much as 11 feet.
24. The current direction of groundwater flow beneath the waste management facility is from
the northwest toward the south. The average groundwater gradient is approximately 0.004
feet per foot. The groundwater velocity has been reported as seven to ten feet per year.
The direction of groundwater flow has varied between southeast and southwest.
25. Monitoring data from upgradient monitoring well ARI-Ol indicates that groundwater
collected from this well from 1989 through 1998 has a specific electrical conductivity that
ranges from 863 to 1;540 micromhoslcm, and Total Dissolved Solids ranging from 507 to
WASTE DISCHARGE REQUIREMENTS, ORDER NO. 5-00-023
COUNTY OF KERN
FOR OPERATION AND CONSTRUcnON
ARVIN SANITARY LANDFllL
KERN COUNTY
-4-
680 mgll. The quality of groundwater from ARI-Ol exceeds the secondary drinking water
standards established by the Department of Health Services for electrical conductivity and
TotaJ Dissolved Solids.
Three additional background monitoring wells were installed in November 1997. Wells
ARI-06 and ARI-22 were installed upgradient from the landfill. Well ARl-21 was
installed sidegradient from the landfill. Wells ARl-21 and ARl-22 monitorf1rst
encountered groundwater, while well ARI-06 was completed approXimately 80 feet below
first encountered groundwater.
Monitoring data from deep upgradient well ARI-06, upgradient well ARl-22, and
sidegradient well ARl-21 indicate that groundwater collected from these wells from May
1998 through January 1999 have electrical conductivity ranges from 434 to 617; 4,240 to
5,070; and 644 to 1,034 micromohs/cm, respectively. The range of Total Dissolved Solids
in wells ARI-06, ARI-21, and ARI-22 for the same time period is 272 to 294; 3,120 to
3,880; and 436 to 493 mgll, respectively. The quality of groundwater from ARI-06 meets
the secondary drinking water standards established by the Department of Health Services
for electrical conductivity and Total Dissolved Solids. The quality of groundwater in well
ARI-21 exceeds the secondary drinking water standards for electrical conductivity and
Total Dissolved Solids. The quality of groundwater in well ARl-22 exceeds the secondary
drinking water standard for electrical conductivity and meets the secondary drinking water
standard for Total Dissolved Solids.
26. The designated beneficial uses of the groundwater, as specified in the Basin Plan, are
domestic and municipal, agricultural, and industrial supply.
27. State Water Resources Control Board Order No. 97-03-DWQ (General Permit No.
CASOOOOO1), amended 17 April 1997, specifies waste discharge requirements for
discharges of storm water associated with industrial activities, excluding construction
activities, ánd requiring submission of a Notice Of Intent by industries to be covered under
the pennit. Waste disposal at landfills, including inert disposal facilities, is considered an
industrial activity requiring submittal of a Notice Of Intent for coverage under the general
pennit if storm water is to be discharged off-site. The Discharger submitted a Notice of
Intent on 27 August 1997, and a Stonn Water Pollution Prevention Plan and Monitoring
Program Reporting Requirements on 12 June 1998. Stonn water runoff is proposed to be
impounded or temporarily detained in an excavation located adjacent to the unlined waste
management unit in the SWII4 of the NWl/4 of Section 31, TIIS, R29E, MDB&M.
WASTE DISCHARGE REQUIREMENTS, ORDER NO. 5-00-023
COUNTY OF KERN
FOR OPERATION AND CONSTRUCTION
ARVIN SANITARY LANDFll..L
KERN COUNTY
-5-
WASTE AND SITE CLASSIFICATION
28. The discharge consists of putrescible and nonputrescible municipal solid wastes and non-
friable asbestos. These wastes are classified as 'nonhazardous solid waste' or 'inert waste'
using the criteria set forth in Title 27.
29. The site characteristics where the waste management unit is located (see Finding No. 10)
do not meet the siting criteria for a Class ill landfill contained in §20260(a) and (b)(l) of
Title 27. As such, the site is not suitable for the discharge and containment of Class ill
wastes. Therefore, in order to discharge the wastes described in Finding No. 28, additional
waste containment measures are required in accordance with §20260(b)(2) of Title 27 and
State Water Resources Control Board Resolution No. 93-62 for any lateral expansion of the
waste management unit.
30. The Discharger may construct a lateral expansion within the waste management facility
property. The liner system will need to be designed, constructed, and operated to prevent
migration of wastes from the waste management unit to adjacent natural geologic materials,
groundwater, or surface water during disposal operations, closure, and the post-closure
maintenance period in accordance with the criteria set forth in Title 27 for a Class ill
landfill, and the provisions in State Water Resources Control Board Resolution No. 93-62
for municipal solid wastes.
GROUNDWATER MONITORING
31. The DisCharger is required to monitor the groundwater and vadose zone in accordance with
Title 27.
32. This Order requires that the groundwater and vadose zone detection monitoring devices be
installed, operational, and the first round of samples analyzed prior to the discharge of
waste to any waste management unit expansion.
33. Ten groundwater monitoring wells have been installed at the waste management facility for
detection monitoring purposes. The existing groundwater detection monitoring system
consists of downgradi'ent monitoring wells ARl-02, ARl-03, ARl-04, ARl-05, ARl-23,
ARl-24, upgradient monitoring wells ARI-Ol, ARl-06, ARl-21, and sidegradient well
ARI-22. The elevation of static groundwater in wells ARI-Ol, ARI-02, ARI-03, ARl-04,
and AR 1-05 exceeds the elevation of the top of screened interval in each well. The
elevation of groundwater above the screened interval currently ranges from one to twenty
one feet. Excluding well ARl-23, completed approximately ninety-five feet bèlow the
elevation of static groundwater when drilled, the elevation of the pump intakes in each
WASTE DISCHARGE REQUIREMENTS, ORDER NO. 5-OO"()23
COUNTY OF KERN
FOR OPERATION AND CONSTRUCTION
AR VIN SANITARY LANDFll.L
KERN COUNTY
-6-
downgradient well is below the elevation of static groundwater by a range of eleven to fifty-
six feet.
34. The vadose zöne monitoring system for the unlined waste management unit consists of two
moisture block/gas probe clusters (ARI-07 and ARl-08), installed at the base of refuse.
35. The Discharger has implemented an Evaluation Monitoring Program for the existing waste
management unit, but has not completed the delineation of the vertical and lateral extent of
the groundwater degradation in accordance with the time schedule in Title 27. Details of
the work accomplished and the work remaining to complete the Evaluation 'Monitoring
Program will be addressed in a subsequent Cleanup and Abatement Order.
36. The Discharger's detection monitoring program for groundwater does not satisfy the
requirements contained in Title 27 due to an insufficient number of groundwater
monitoring wells and no established concentration limits. A subsequent Cleanup and
Abatement Order will require the Discharger to bring the Detection Monitoring Program
into full compliance with Title 27 in accordance with an approved time schedule.
GROUNDW A TER DEGRADATION
37. Groundwater monitoring performed at the landfill has detected volatile organic compounds
(VOCs) in samples conected from on-site monitoring wells since 1990. Groundwater
analyses have repeatedly detected the following waste constituents at concentrations above
water quality objectives (primary Maximum Contaminant Level): benzene; 1,1-
dichloroethane; methylene chloride; tetrachloroethene (PCE); trichloroethene (TCE); and
vinyl chloride. Other constituents repeatedly detected in wells at concentrations below
water quality goals include: acetone; bis (2-ethylhexyl) phthalate; benzyl butyl phthalate;
. chlorobenzene; chloroditluoromethane; chlorotluoromethane; chloroform;
dichlorodifluoromethane (Freon 12); 1, l-dichloroethene; cis-l ,2-dichloroethene;
dichlorofluoromethane; l,2-dichloropropane; ethylbenzene; isopropylbenzene; p-isopropyl
toluene; pentane; toluene; I ,I, I-trichloroethane; trichlorofluoromethane (Freon 11);
l,2,4-trimethylbenzene; 1,3,5-trimethylbenzene; and total xylenes.
38. Constituents detected in samples from evaluation monitoring hydropunch borings include:
acetone; benzene; bromodichloromethane; bromoform; chloroform; chloromethane;
dibromochloromethane; dichlorodit1uoromethane (Freon 12); 1, l-dichloroethane;
isopropylbenzene; methyl ethyl ketone; methylene chloride; naphthalene; n-propylbenzene;
PCB; I ,1 ,I-trichloroethane; TCE; trichlort1uoromethane (Freon 11);
1.2,4-trimethylbenzene; l,3,5-trimethylbenzene; and toluene.
WASTE. DISCHARGE REQUIREMENTS, ORDER NO. 5-00-023
COUNTY OF KERN
FOR OPERATION AND CONSTRUCTION
ARVIN SANITARY LANDFIll.
KERN COUNTY
-7-
39. Constituents detected in samples from downgradient monitoring well ARl-23, completed
100 feet below the depth of first continuous groundwater, include: chlorofonn;
dichlorodit1uoromethane (Freon 12); 1, l-dichloroethane; isopropylbenzene; methylene
chloride; tetrachJoroethene (PCE); toluene; trichloroethene (fCE); and 1,1,2-trichloro-
1,2,2-trifluoroethane.
40. Constituents detected in a sample collected from the landfill water supply well include
dichlorodifluoromethane (Freon 12) and methylene chloride. The compounds benzidine
and endrin aldehyde were tentatively identified.
CONSTRUcnON AND ENGllŒERED ALTERNATIVE
41. On 17 June 1993, the State Water Resources Control Board adopted Resolution No. 93-62
implementing a State Policy for the construction, monitoring, and operation of municipal
solid waste landfills that is consistent with the federal municipal solid waste regulations
promulgated under Title 40, Code of Federal Regulations, Part 258 (Subtitle D).
42. Resolution No. 93-62 requires the construction of composite liner systems at municipal
solid waste landfills that receive wastes after 9 October 1993. The prescriptive standard for
a composite liner system consists of a minimum 40-mil thick (60 mil for HDPE) upper
synthetic flexible membrane component and lower soil component of compacted clay a
minimum of two feet thick with a hydraulic conductivity not to exceed 1 x 1O-7.cmlsec.
43. Resolution No. 93-62 also allows the Board to consider the approval of engineered
alternatives to the prescriptive standard. Section ill.A.b. of Resolution No. 93-62 requires
that the engineered alternative be of a composite design similar to the prescriptive standard.
44. Section 20080(b) of Title 27 allows the Board to consider the approval of an engineered
alternative to the prescriptive standard. In order to approve an engineered alternative in
accordance with §20080(c)(1) and (2), the Discharger must demonstrate that the
prescriptive design is unreasonably and unnecessarily burdensome and will cost
substantially more than an alternative which will meet the criteria contained in §20080(b),
or would be impractical and would not promote attainment of applicable perfonnance
standards. The Discharger must also demonstrate that the proposed engineered alternati ve
is consistent with the perfonnance goal addressed by the particular prescriptive standard,
and provides protection against water quality impainnent equivalent to the prescriptive
standard in accordance with §20080(b)(2) of Title 27.
45. Section 1336O(a)(I) of the California Water Code allows the Board to specify the design,
type of construction, and/or particular manner in which compliance must be met in waste
~
WASTE DISCHARGE REQUIREMENTS, ORDER NO. 5-00-023
COUNTY OF KERN
FOR OPERATION AND CONSTRUCTION
AR VIN SANITARY LANDFilL
KERN COUNTY
-8-
discharge requirements or orders for the discharge of waste at solid waste disposal
facilities.
46. The Discharger has not yet submitted a design plan for an expansion of the Arvin Sanitary
Landfill.
47. Prior to an expansion of the existing waste management unit, the Discharger will need to
submit for Executive Officer approval, design and construction CQA plans for expansion of
the waste management unit.
48. An unsaturated zone monitoring system will need to be installed beneath the composite
liner system of any lateral expansion in accordance with §20415 (d) of Title 27.
49. Construction will proceed only after all applicable design, construction plans, and
construction quality assurance plans have been approved by the Executive Officer.
CEQA CONSIDERATIONS
50. The action to update waste discharge requirements for this facility is exempt from the
provisions of the California Environmental Quality Act (CEQA), Public Resource Code
§21000, et seq., and the CEQA guidelines. in accordance with Title 14, CCR, §15301, et
seq.
OTHER CONSIDERATIONS
51. On 9 October 1991, the United States Environmental Protection Agency (USEPA)
promulgated regulations (Title 40, Code of Federal Regulations, Parts 257 and 258.
"federal municipal solid waste [MSW] regulations" or "Subtitle D") that apply, in
California, to dischargers who own or operate Class n or Class ill landfill units at which
municipal solid waste is discharged. The majority of the federal MSW regulations became
effective on the "Federal Deadline", which was 9 October 1993. The USEPA has deemed
the State of California to be an approved state, meaning that compliance with the applicable
state regulations constitutes compliance with the federal Subtitle D regulations. These
,requirements implement the appropriate 'state regulations in lieu of Subtitle D.
52. These requirements implement the prescriptive standard and performance goals of Title 27,
California Code of Regulations, §20005 et seq. (Title 27).
53. These requirements implement the Basin Plan.
54. The requirements implement State Water Resources Control Board Resolution No. 93-62,
Policy for Regulation of Discharges of Municipal Solid Waste, which implement the
federal Subtitle D regulations.
~
WASTE DISCHARGE REQUIREMENTS, ORDER NO. 5-00-023
COUNTYOFlŒRN
FOR OPERATION AND CONSTRUcnON
AR VIN SANITARY LANDFILL
KERN COUNTY
-9-
55. All local agencies with jurisdiction to regulate land use, solid waste disposal, air pollution,
and to protect public health have approved the use of this site for the discharges of waste to
land stated herein.
56. The Board has notified the Discharger and interested agencies and persons of its intention
to update the waste discharge requirements for this facility.
57. In a public hearing, the Board heard and considered all comments pertaining to this facility
and discharge.
IT IS HEREBY ORDERED.that Order No. 92-163 is rescinded, and Attachment 1 of Order No.
93-200 is amended to delete the Arvin Sanitary Landfill, which is on line No. 55, and that the
County of Kern, Kern County Waste Management Department, its agents, successors, and
assigns, in order to meet the provisions of Division 7 of the California Water Code and the
regulations adopted hereunder, shall comply with the following:
A. PROHIBITIONS
1. The discharge of 'hazardous waste' at this facility, except waste that is hazardous
due only to its friable asbestos content, is prohibited. The discharge of 'designated
waste' at this facility is prohibited. For the purposes of this Order, the tenn
'hazardous waste' is as defined in Title 23 California Code of Regulations, Section
2510 et seq., and 'designated waste' is as defined in Title 27.
2. The discharge of wastes outside of a waste management unit or portions of a waste
management unit specifically designed for their containment is prohibited.
3. The discharge of solid waste, liquid waste, leachate, or waste constituents to
surface waters, ponded water, surface water drainage courses, or groundwater is
prohibited.
4. The discharge of liquid or semi-solid waste (i.e., waste containing less than 50
percent solids), except dewatered sewage or water treatment sludge, or on-site
generated leachate or landfill gas condensate, above a composite liner as provided
in §20220(c) of Title 27, is prohibited.
5. The discharge of solid waste containing free liquid or moisture in excess of the
waste's moisture holding capacity is prohibited.
6. The discharge of waste within 100 feet of surface waters is prohibited.
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COUNTY OF KERN
FOR OPERATION AND CONSTRUcnON
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7. The discharge shall not cause the pollution or degradation of groundwater via the
release of waste constituents in either liquid or gaseous phase.
8. The discharge of wastes shall not cause the pollution or degradation of any water
supply.
9. The discharge of wastes which have the potential to reduce or impair the integrity
of containment structures or which, if commingled with other wastes in the waste
management unit, could produce violent reaction, heat or pressure, fire or
explosion, toxic by-products, or reaction products, which, in turn:
a. require a higher level of containment than provided by the unit; or
b. are 'restricted hazardous wastes'; or
c. impair the integrity of containment structures;
is prohiþited.
10. The discharge shall not cause any increase in the concentration of waste
constituents in soil or other geologic materials outside of the waste management
unit if such waste constituents could migrate to waters of the State and cause a
condition of degradation, pollution, or nuisance.
11. The discharge of any additional waste to a waste management unit after it is closed
is prohibited. -
B. DISCHARGE SPECIFICATIONS
1. Wastes shall only be discharged to either:
a. that portion of an existing waste management unit that was pennitted and/or
received wastes prior to the Federal Deadline of9 October 1993; or
b. to an area equipped with a composite liner containment system that meets
the requirements for both liners and leachate collection and removal systems
specified below.
WASTE DISCHARGE REQUIREMENTS, ORDER NO. 5-00-023
COUNTY OF KERN
FOR OPERA nON AND CONSTRUCTION
ARVIN SANITARY. LANDFILL
KERN COUNTY
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2. A minimum separation of 5 feet shall be maintained between the base of the wastes
and the highest anticipated elevation of underlying groundwater, including the
capillary fringe.
3. Water used for facility maintenance shall be limited to the minimum amount
necessary for dust control, construction, and, after closure, to the minimum amount
necessary to irrigate cover vegetation or for other uses approved by the Executive
Officer.
4. Leachate collected from the landfill shall be discharged to an appropriate waste
management unit in accordance with Title 27 and in a manner consistent with the
waste classification of the leachate, or discharged on-site to a waste management
unit or portion of a waste management unit that has a composite liner and a leachate
collection and removal system.
5. Gas condensate collected from any landfill gas control systems installed at the waste
management unit and proposed for discharge to land. shall be discharged to an
appropriate waste management unit in accordance with Title 27 and in a manner
consistent with the waste classification of the condensate, or discharged on-site to a
waste management unit or portion of a waste management unit that has a composite
liner and a leachate collection and removal system.
6. Neither the treatment nor the discharge of wastes shall cause a pollution or nuisance
as defined by the California Water Code, § 13050.
7. The Discharger shall, in a timely manner, remove and relocate any wastes
discharged at this facility in violation of this Order.
C. FACILITY SPECIFICATIONS
1. Waste management 'units and containment structures shall be designed and
constructed to limit, to the greatest extent possible, ponding, infiltration,
inundation, erosion, slope failure, washout, and overtopping as a result of a
100-year, 24-hour precipitation event.
2. Precipitation and drainage control systems shall be designed, constructed, and
maintained to accommodate the anticipated volume of precipitation and peak flows
from surface runoff under the 100-year, 24-hour precipitation conditions.
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FOR OPERATION AND CONSTRUCflON
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KERN COUNTY
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3. Cover materials shall be graded to divert precipitation from the waste management
unit, to prevent the ponding of surface water over wastes, and to resist erosion as a
result of a l00-year, 24-hour precipitation event.
4. Interim cover placed over wastes discharged to any waste management unit shall
be designed and constructed to minimize the percolation of liquids through wastes.
5. Waste management units or portions of waste management units shall be designed,
constructed, and operated in compliance with precipitation and flood conditions
contained in the Standard Provisions and Reporting Requirements referenced in
Provision F.5 below.
6. All drainage control systems shall be designed and constructed to prevent the
ponding of water above wastes.
7. SUlface drainage from tributary areas and internal site drainage from surface or
subsurface sources shall not contact or percolate through wastes.
8. Areas with slopes greater than ten percent, sUlface drainage courses, and areas
subject to erosion by wind or water shall be designed and constructed to prevent
such erosion.
9. An earthen cover shall be maintained over all but the active disposal area of the
waste management unit. This area shall be properly graded and drained to prevent
ponding and infiltration. The cover over the waste management unit shall be
approved by the California Integrated Waste Management Board in accordance
with §20680 of Title 27. Any alternative daily cover material shall be approved by
the Executive Officer to ensure that it will be protective of water quality.
10. The Discharger shall submit information that demonstrates for Executive Officer
review and approval, that the waste management unites) will not restrict the flow of
the l00-year flood, reduce the temporary water storage capacity of the floodplain,
or result in washout of solid waste so as to pose a hazard to human health or the
environment.
11. The Discharger shall submit information that demonstrates for Executive Officer
review and approval, that flood protection devices (e.g., floodwalls, dikes) are
installed at the waste management unit and will be maintained to prevent
inundation or washout and divert surface drainage from the unit for floods with a
lOO-year return period. If the flood protection devices have not been installed, the
WASTE DISCHARGE REQUIREMENTS, ORDER NO. 5-00-023
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FOR OPERATION AND CONSTRUCTION
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Discharger shall submit a work plan for their installation to the Executive Officer
for review and approval.
12. The Discharger shall submit an Interim Drainage Plan demonstrating adequate
design, construction, and operation of a facility liquid management system for
protection from storm events, including precipitation and drainage controls,
consistent with the development ofa closure and post-closure maintenance plan
and Facility Specifications C.l through C.S.
13. The Discharger shall immediately notify the Board of any flooding, unpermitted
offsite discharge, equipment failure, slope failure, or other change in site
conditions, which could impair the integrity of waste or leachate containment
facilities or precipitation and drainage control structures.
14. The Discharger shall appropriately revise the Stonn Water Pollution and
Prevention Plan and Interim Drainage Plan to reflect site design modifications
prior to the discharge of wastesJo a newly constructed waste management unit or
to an expansion of an existing waste management unit.
D. CONSTRUCTION SPECIFICATIONS
1. Materials used to construct liners shaH have appropriate physical and chemical
properties to ensure containment of discharged wastes over the operating life,
closure, and post-closure maintenance period of a waste manàgement unit or portion
of a waste management unit.
2. Materials used to construct the leachate collection and removal system shall have
appropriate physical and chemical properties to ensure the required transmission of
leachate over the operating life, closure, and post-closure maintenance period of a
waste management unit or portion of a waste management unit.
3. The Discharger shall submit for Execut~ve Officer review and approval prior to
construction, design plans and specifications for new waste management units and
expansions of existing waste management units that include the following:
a) A demonstration that new waste management units and expansions of
existing waste management units shall not be located in a wetland, unless
demonstrated that:
(1) There is no practical alternative;
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(2) Steps have been taken to achieve no net loss of wetlands, pursuant
to §404 of the Federal Clean Water Act; and
(3) The landfill will not do any of the following:
(a) Degrade the wetland;
(b) Jeopardize threatened or endangered species or produce
adverse modification of a critical habitat protected under
the Endangered Species Act of 1973; or
(c) Violate any requirement under the Marine Protection,
Research, and Sanctuaries Act of 1972 for the protection
of.a marine sanctuary.
b) A Construction Quality Assurance Plan demonstrating that the proposed
waste management unit will be constructed according to the approved
specifications and plans, and shall provide quality control on the materials
and construction practices used in construction and prevent the use of
inferior products and/or materials which do not meet the approved design
plans or specifications; and
c) A geotechnical evaluation of the area soils, evaluating their use as the
foundation layer; and
d) A vadose zone monitoring system that meets the criteria contained in
§20415 (d) of Title 27, and is installed beneath the composite liner system.
4. If clay layers are used in a liner system, then the hydraulic conductivities for the
clay determined through laboratory methods shall be confirmed by a Sealed Double-
Ring Infi1trometer (SDRI) field test, or an equivalent field test method approved by
the Executive Officer, of a test pad constructed in a manner duplicating the clay \
liner construction of the waste management unit or expansion portion of the waste
management unit. Test pad construction methods, quality assurance/quality control
procedures, and testing shall be in accordance with a construction quality assurance
plan approved by the Executive Officer and shall be sufficient to ensure that all
parts of the liner meet the hydraulic conductivity and compaction requirements.
5. Both the bottom liner and side slope liner of all new waste management units andsexpansion areas of existing waste management units shall be constructed in
accordance with one of the foJlowing composite liner designs:
WASTE DISCHARGE REQUIREMENTS, ORDER NO. 5-00-023
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FOR OPERATION AND CONSTRUCTION
AR VIN SANITARY LANDFITL
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a) The prescriptive standard design which consists of a lower compacted soil
layer that is a minimum of two feet thick with a hydraulic conductivity of 1
x 10-7 cm/see or less and a minimum relative compaction of 90%.
Immediately above the compacted soil layer, and in direct and uniform
contact with the soil layer, shall be a synthetic flexible membrane
component that shall be at least 4O-mil thick (or at least 6O-mil thick if
composed of high density polyethylene [HDPE]); or
b) An engineered alternative liner system that is comprised, in ascending order,
of the following:
1) A twelve-inch thick engineered soil foundation layer that shall be
constructed of select fine-grained soil materials which shall be
compacted in lifts of six inches or less to 90% of maximum dry density
and at 0% to 4% wet of optimum moisture content, in accordance with
the approved construction quality assurance plan, and shall be
compacted to attain a hydraulic conductivity of 1 x 1O-s cm/see or less,
or meet the following gradation criteria:
(a) A maximum size of 3/8-inch;
(b) At least 30% of the material, by dry weight, passing the No. 200
U.S. Standard sieve; and
(c) A gradation series (i.e., well graded) that is amenable to
compaction.
2) A nonwoven bottom geotextile, which may be part of the geosynthetic
clay layer (GCL).
3) A GCL that shall exhibit appropriate strength characteristics (hydrated)
to accommodate stresses associated with specific landfill design
parameterS, with particular attention to interface, long-term creep
shear, and bearing capacity.
4) A 6O-mil thick synthetic flexible membrane of HDPE; or
c) An engineered alternative liner system as provided by §20080(b) and (c) of
Title 27, which must be a composite liner that meets the performance goals
of the prescriptive design in option a) above, and has been approved by the
Executive Officer.
WASTE DISCHARGE REQUIREMENTS, ORDER NO. 5-00-023
COUNTY OF KERN
FOR OPERATION AND CONSTRUCTION
ARVIN SANITARY LAND~
KERN COUNTY
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6. If the Discharger proposes to construct a liner system in which a GeL is placed on
top of the subgrade, the subgrade for the bottom and the side slopes of the waste
management unit shall be prepared in an appropriate manner using accepted
engineering and construction methods so as to provide a smooth swface that is free
from rocks, sticks, or other debris that could damage or otherwise limit the
performance of the GCL.
7. Hydraulic conductivities of liner materials shall be det~rmined by laboratory tests
using solutions with similar properties as the fluids that will be contained.
Hydraulic conductivities of cover materials shall be determined by laboratory tests
using water. Hydraulic conductivities determined through laboratory methods shall
be confinned by field testing in accordance with the approved Construction Quality
Assurance Plan. Construction methods and quality assurance procedures shall be
sufficient to ensure that all parts of the liner and cap meet the hydraulic conductivity
and compaction requirements.
8. All new waste management units or lateral expansions of existing waste
management units shall have a blanket-type leachate collection and removal system.
The leachate collection and removal system shall be designed, constructed,
maintained, and operated to collect twice the anticipated daily volume of leachate
generated by the waste management unit. The leachate collection and removal
system shall be designed and operated to maintain less than a 30 cm depth of
leachate over the liner.
9. Leachate generated by any waste management unit or portion of a waste
management unit shall not exceed 85% of the design capacity of the leachate sump.
H leachate generation exceeds this value, or if the depth of fluid in the leachate
collection and removal system exceeds 30 cm,or if the monitoring reveals
substantial or progressive increases above the design anticipated daily volume of
leachate generated by the waste management unit or portion of the waste
management unit, the Discharger shall immediately notify the Board in writing
within seven days. The notification shall include a timetable for remedial or
corrective action necessary to reduce leachate production.
10. Following the completion of construction of a waste management unit or portion of
a waste management unit, ahd prior to discharge onto the newly constructed liner
system, a construction report shall be submitted for Executive Officer review and
approval. The "report shall be certified by a registered civil engineer or a certified
engineering geologist. It shall contain sufficient infonnation and test results to
verify that construction was in accordance with the design plans and specifications,
and with the· prescriptive standards andperfonnance goals of Title 27.
WASTE DISCHARGE REQUIREMENTS, ORDER NO. 5-00-023
COUNTY OF KERN
FOR OPERATION AND CONSTRUCTION
ARVIN SANITARY LANDFITl...
KERN COUNTY
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The report for the waste management unit shall include as a minimum, but not be
limited to, the following:
a) Test results on the chemical and geotechnical properties of materials used in
the containment structure, as specified in these waste discharge
requirements.
b) Test results on the penneability of the clay liner if the prescriptive standard
clay layer is used in the liner system.
c) Test ~sults on the compatibility of the waste ~ith the liner system.
d) Construction quality assurance and quality control procedures and results for
all aspects of liner construction.
e) A geologic map and geologic cross-sections which show mappable
lithologic units and structural features in relation to the waste management
unit.
11. Partial or final closure of new, existing, or portions of a classified waste
management unit shall be in compliance with the applicable provisions of Title 27.
Classified waste management units or portions of waste management units shall be
closed in accordance with a closure and post-closure maintenance plan approved by
the Executive Officer, and closure waste discharge requirements adopted by the
Board. In addition to the applicable provisions of Title 27, the closure and/or the
post-closure maintenance plan shall include the following:
a) A final cover design with a minimum I-foot thick erosion resistant layer;
b) An estimate of the largest area of the waste management unites) ever
requiring a final cover at any time during the active life of the unites);
c) An estimate of the maximum inventory of wastes ever on-site over the
active life of the waste management facility;
d) Initiation of closure activities within 30 days of final waste receipt, or within
one year of receipt of most recent waste if additional capacity remains;
e) Completion of closure activities within 180 days of the beginning of closure
activities;
WASTE DISCHARGE REQUIREMENTS. ORDER NO. 5-00-023
COUNTY OF KERN
FOR OPERATION AND CONSTRUCTION
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f) Notifying the Executive Officer that the deed to the landfill facility property,
or some other instrument that is nonnally examined during a title search. has
been recorded and a copy placed in the operating record. The notation on
the deed shall in perpetuity notify any potential purchaser of the property
that the land has been used as a landfill facility and that use of the land is
restricted to the planned uses described in the post-closure maintenance
plan.
12. The Discl}arger shall notify the Executive Officer that a closure and post-closure
maintenance plan has been prepared in accordance with Construction Specification
D. 11 and placed in the operating record by the date of initial receipt of waste at any
new waste management unit or lateral expansion of any existing waste management
uni t.
13. Closure shall not proceed in the absence of closure waste discharge requirements.
E. DETECTION MONITORING SPECIFICATIONS
1. The Discharger shall submit a groundwater detection monitoring report
demonstrating compliance with Title 27 for the existing waste management unit and
any waste management unit expansion. The program is subject to approval by the
Executive Officer.
2. The Discharger shall submit a Sample Collection and Analysis Plan. which includes
quality assurance/quality control standards and the analysis of unfiltered samples,
for approval by the Executive Officer.
3. The Discharger shall comply with the detection monitoring provisions of Title 27
for groundwater and the unsaturated zone. and in accordance with Monitoring and
Reporting Program No. 5-00-023. Detection monitoring for a new waste
management unit or an expansion of an existing waste management unit shall be
installed, operational, and the first round of samples collected prior to the discharge
of wastes.
4. The Water Quality Protection Standard, as defined in §20390 of Title 27, shall
consist of constituents of concern. their concentration limits, the point of
compliance. and all water quality monitoring points. Constituents of concern shall
include all waste constituents. their reaction products. ånd hazardous constituents
that are reasonably expected to be in or derived from waste contained in the landfill.
Concentration limits shall consist of the background concentrations of each
WASTE DISCHARGE REQUIREMENTS, ORDER NO. 5-00-023
COUNTY OF KERN
FOR OPERATION AND CONSTRUCTION
AR VIN SANITARY LANDFIlL
KERN COUNTY
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constituent of concern established in accordance with a data analysis method that
meets the applicable criteria of §20415(e) of Title 27.
'5. The Discharger shall comply with the Water Quality Protection Standard which is
specified in Monitoring and Reporting Program No. 5-00-023 and the Standard
Provisions and Reporting Requirements, dated August 1997, which are attached to
and made part of this order.
6. Organic compounds that are not naturally occU1TÎng have a background value of
zero. The Water Quality Protection Standard for volatile organic compounds shall
be taken as the detection limit of the analytical method used (i.e., USEPA Methods
8260 and 8270). Evidence of exceeding the standard occurs when the constituent is
detected by the appropriate method.
7. The concentrations of the constituents of concern in waters passing the Point of
Compliance shall not exceed the concentration limits established pursuant to
Monitoring and Reporting Program No. 5-00-023.
8. For each monitoring event, the Discharger shall determine whether the landfill is in
compliance with the Water Quality Protection Standard using procedures specified
in Monitoring and Reporting Program No. 5-00-023 and §20415(e) of Title 27.
9. Methane and other landfill gases shall be adequately vented, removed from the
waste management unit, or otherwise controlled to prevent adverse health effects,
nuisance conditions, or the impairment of the beneficial uses of surface water or
groundwater due to migration through the vadose (unsaturated) zone.
F. PROVISIONS
1. The Discharger shall maintain legible records of the volume and type of each waste
discharged at each waste management unit or portion of a waste management unit,
and the manner and location of the discharge. The Discharger shall maintain such
records until the beginning of the post-closure maintenance period. These records
shall be available for review by representatives of the Board and of the State Water
Resources Control Board at any time during normal business hours. At the
beginning of the post-closure maintenance period, copies of these records shall be
properly stored for future reference.
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COUNTY OF KERN
FOR OPERATION AND CONSTRUcnON
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2. The Discharger shall maintain a copy of this Order at the facility and make it
available at all times to facility operating personnel, who shall be familiar with its
contents, and to regulatory agency personnel upon request.
3. The Discharger shaH comply with all applicable provisions of Title 27 that are not
specifically refeITed to in this Order.
4. The Discharger shall comply with Monitoring and Reporting Program
No. 5-00-023, which is incorporated into and made part of this Order. This
compliance includes, but is not limited to monitoring of: the maintenance of waste
containment facilities, precipitation and drainage controls, the groundwater
monitoring system, leachate from the waste management unit(s), and the vadose
zone and surface water monitoring systems throughout the active life of the waste
management unit and the post-closure maintenance period.
5. The Discharger shall comply with the applicable portions of the Standard
Provisions and Reporting Requirements, dated August 1997. which are hereby
incorporated into this Order.
6. . A violation of any of the applicable portions of the Standard Provisions and
Reporting Requirements or the Monitoring and Reporting Program is a violation of
these waste discharge requirements.
7. Monitoring wells, piezometers, and other measurement, sampling, and analytical
devices shall be operated and maintained so that they perform to design
specifications throughout the life of the monitoring program.
8. The Discharger or persons employed by the Discharger shall comply with all notice
and reporting requirements of the State Department of Water Resources with regard
to the construction, alteration, destruction, or abandonment of all monitoring wells
used for compliance with this Order as required by § 13750 through § 13755 of the
California Water Code.
9. The Discharger shan submit documentation to the Executive Officer that all
persons who own or reside on the land that directly overlies any portion of the
contaminant plume that has migrated off-site have been notified.
10. The Discharger shall have the continuing responsibility to assure the protection of
the beneficial uses of ground and surface waters from gases and leachate generated
by discharged waste during the active life, closure and post-closure maintenance
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COUNTY OF KERN
FOR OPERATION AND CONSTRUCflON
ARVIN SANITARY LANDFILL
KERN COUNTY
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period of the waste' management unit(s) and during the subsequent use of the
property for other purposes.
11. In the event of any change in control or ownership of the land or waste discharge
facilities described herein, the Discharger shall notify the succeeding owner or
operator of the existence of this Order by letter, a copy of which shall be
immediately forwarded to this office.
12. To assume operation under this Order, the succeeding owner or operator must apply
in writing to the Board requesting transfer of the Order within 14 days of assuming
ownership or operation of this facility. The request must contain the requesting
entity's fun legal name, the State of incorporation if a corporation, the name and
address and telephone number of the persons responsible for contact with the .
Board, and a statement. The statement shall comply with the signatory
requirements contained in Reporting Requirements No.5 of the Standard
Provisions and Reporting Requirements and state that the new owner or operator
assumes full responsibility for compliance with this Order. Failure to submit the
request shaH be considered a discharge without requirements, a violation of the
California Water Code. Transfer shall be approved or disapproved by the Board.
13. The Discharger shall notify the Boardin writing of any proposed change in
ownership or responsibility for construction or operation of the waste management
unit. The Discharger shall also notify the Board of a material change in the
character, location or volume of the waste discharge and of any proposed
expansions or closure plans. This notification shall be given 90 days prior to the
effective date of the change and shall be accompanied by an amended Report of
Waste Discharge and any technical documents that are needed to demonstrate
continued compliance with these waste discharge requirements.
14. The Discharger shall, by 30 April of each year, submit for approval by the
Executive Officer, plans with detailed cost estimates and a demonstration of
assurances of financial responsibility for initiating and completing corrective action
for all known and reasonably foreseeable releases from the waste management unit.
The Discharger shall provide the assurances of financial responsibility to the
California Integrated Waste Management Board as required by Title 27 CCR,
Division 2, Subdivision 1, Chapter 6. The assurances of financial responsibility
shall provide that funds for corrective action shall be available to the Regional
Board upon the issuance of any order under California Water Code, Division 7,
Chapter 5. The Discharger shall adjust the cost annual.ly to account for inflation
. and any changes in facility design, construction, or operation. '
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15. The Discharger shall, by 30 April of each year, submit for approval by the
Executive Officer, ,a demonstration of assurances of financial responsibility to
ensure closure and post-closure maintenance of each waste management unit in
accordance with its approved closure and post-closure maintenance plans. The
Discharger shall provide the assurances of financial responsibility to the California
Integrated Waste Management Board as required by Title 27 CCR, Division 2,
Subdivision I, Chapter 6. The assurances of financial responsibility shall provide
that funds for closure and post-closure maintenance with respect to water quality
shall be available to the Regional Board upon the issuance of any order under
California Water Code, Division 7, Chapter 5. The Discharger shall adjust the cost
annually to account for inflation and any changes in facility design, construction, or
operation.
i6. If a single mechanism of financial assurance is used for both corrective action and
closure and post-closure maintenance, the financial assurance must be sufficient for
both requirements.
17. The Board will review this Order periodically and will revise thèse waste discharge
requirements when necessary.
18. The Discharger shall complete the tasks contained in these waste discharge
requirements in accordance with the following time schedule:
Task
COIIi~liance Date
(a) Submit for Executive Officer
review and approval, a
demonstration that the waste
management unit will not restrict
the 100-year flood, reduce the
storage capacity of the floodplain,
or result in washout of solid waste.
(Facility Specification C.W)
30 April 2000
(b) Submit Interim Drainage Plan
, (Facility Specification C.I2)
30 April 2000
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WASTE DISCHARGE REQUIREMENTS, ORDER NO. 5-00-023
COUNTY OF KERN
FOR OPERA nON AND CONSTRUCTION
AR VIN SANITARY LANDFIll..
KERN COUNTY
Task
(c) Submit for Executive Officer
review and approval, design
plans and specifications for new
waste management units
and expansions of existing
waste management units.
(Construction Specification D.3)
(d) Submit for Executive Officer
review and· approval, a revised
closure and post-closure
maintenance plan.
(Construction Specification D.II)
(e) Submit Sample Collection and
Analysis Plan
(Detection Monitoring
Specification E.2)
Compliance Date
Prior to Construction
No Later Than One
Year Prior to the
Anticipated Date of
Closure
30 April 2000
I, GARY M. CARLTON, Executive Officer, do hereby certify that the foregoing is a full, true,
and correct copy of an Order adopted by the California Regional Water Quality Control Board,
Central Valley Region, on 28 January 2000.
RCS/REH
CALIFORNIA REGIONAL WATER QUAUfY CONTROL BOARD
CENTRAL V ALLEY REGION
MONITORING AND REPORTING PROGRAM NO. 5-00-023
FOR
COUNTY OF KERN
KERN COUNTY WASTE MANAGEMENT DEPARTMENT
FOR
OPERATION AND CONSTRUcnON
ARVIN SANITARY LANDFUL
KERN COUNTY
Compliance with this Monitoring and Reporting Program, with Title 27, California Code of
Regulations, Section 20005, et seq. (hereafter Title 27), and with the Standard Provisions and
Reporting Requirements dated August 1997, is ordered by Waste Discharge Requirements Order
No. 5-00-023.
Failure to comply with this Program, or with the Standard ProvisiQns and Reporting
Requirements, constitutes noncompliance with the Waste Discharge Requirements and
with the California Water Code, which can result in the imposition of civil monetary
liability.
A. REQUIRED MONITORING REPORTS
Report Due
1. Groundwater Monitoring (Section D.l) See Table I
2. Annual Monitoring Summary Report Annually
(Standard Provisions and Reporting Requirements)
3. Unsaturated Zone Monitoring (Section D.2) See Table II
4. Leachate Monitoring (Section D.3) See Table ill
5. Facility Monitoring (Section D.5) As necessary ,
6. Response to a Release As necessary
(Standard Provisions and Reporting Requirements)
B. REPORTING
The Discharger shall report monitoring data and information as required in this Monitoring
and Reporting Program and as required in the Standard Provisions and Reporting
Requirements. Reports which do not comply with the required format will be REJECTED
and the Discharger shall be deemed to be in noncompliance with the waste discharge
requirements. In reporting the monitoring data required by this program, the Discharger
MONITORING AND REPORTING PROGRAM
ORDER NO. 5-00-023
COUNTY OF KERN
KERN COUNTY WASTE MANAGEMENT DEPARTMENT
FOR OPERATION AND CONSTRUCTION
ARVIN SANITARY LANDFll.L
KERN COUNTY
2
shall arrange the data in tabular form so that the date, the constituents, the concentrations,
and the units are readily discernible. Data shall also be submitted in a digital database
format acceptable to the Executive Officer. The data shall be summarized in such a manner
so as to illustrate clearly the compliance with waste discharge requirements or the lack
thereof. A short discussion of the monitoring results, including notations of any water
quality violations, shall precede the tabular summaries.
Field and laboratory tests shall be reported in each monitoring report. Monthly, quarterly,
semiannual, and annual monitoring reports shall be submitted to Board staff in accordance
with the following schedule for the calendar period in which samples were taken or
observations made. The results of any monitoring done more frequently than required at
the locations specified herein shall be reported to Board staff.
Sampling Reporting
Frequency Frequency
Monthly Quarterly
Quarterly Quarterly
Semi-Annually
Semi-Annually
Annually
Annually
Reporting
Periods End
Last Day of Month
31 March
30 June
30 September
31 December
30 June
31 December
31 December
Report
Date Due
by Quarterly Sch~ule
31 May
31 August
30 November
28 February
31 August
28 February
30 April
The annu~ report to be submitted to Board staff shall contain both tabular and graphical
summaries of the monitoring data obtained during the previous twelve months, so as to
show historical trends at each weH. The report shall include a discussion of compliance
with the waste discharge requirements and the water quality pro~ection standard.
A transmittal letter explaining the essential points shall accompany each report. At a
minimum, the transmittal letter shaH identify any violations found since the last report was
submitted, and if the violations were corrected. If no violations have occurred since the last
submittal, this shall be stated in the transmittal letter. The transmittal letter shall also state
that a discussion of any violations found since the last report was submitted, and a
description of the actions taken or planned for correcting those violations, including any
references to previously submitted time schedules, is contained in the accompanying report.
MONITORING AND REPORTING PROGRAM
ORDER NO. 5-00-023
COUNTY OF IŒRN
KERN COUNTY WASTE MANAGEMENT DEPARTMENT
FOR OPERATION AND CONSTRUCTION
ARVIN SANITARY LANDFllL·
KERN COUNTY
3
c. WATER QUALITY PROTECTION STANDARD AND COMPLIANCE PERIOD
1. Water Quality Protection Standard Report
For each waste management unit, the water quality protection standard consists of a
list of constituents of concern and monitoring parameters, concentration limits for
each constituent of concern, the point of compliance, and all monitoring points.
The Discharger shall submit a proposed water quality protection standard for review
and approval in accordance with a Cleanup and Abatement Order which will be
adopted following adoption of this Order. The Executive Officer shall review the
data and the proposed water quality protection standard in determining the final water
quality protection standard for each monitored medium.
The report shall:
a) Identify aD distinct bodies of surface and ground water that could be affected
in the event of a release from a waste management unit or portion of a waste
management unit. This list shall include at least the uppermost aquifer and any
permanent or ephemeral zones of perched groundwater underlying the waste
management facility.
b) Include a map showing the monitoring points and background monitoring points
for the surface, saturated, and unsaturated zones and showing the point of
compliance in accordance with §20405 of TitJe 27.
c) Evaluate the perennial direction(s) of groundwater movement within the
uppermost groundwater zone(s).
If subsequent sampling of the background monitoring point(s) indicates significant
water quality changes due to either seasonal fluctuations or other reasons unrelated to
waste management activities at the site, the Discharger may request modification of
the water quality protection standard
2. Constituents or Concern
The constituents of concern are the waste constituents, reaction products, and
hazardous constituents that are reasonably expected to be in or derived from waste
contained in the waste management unit. The constituents of concern for all waste
management units at the facility are those listed in Table VI. The Discharger shall
monitor all constituents of concern in Table VI every five years, or more frequently as
required in accordance with a Corrective Aétion Program.
MONITORING AND REPORTING PROGRAM
ORDER NO. 5-00-023
COUNTY OF KERN
KERN COUNTY WASTE MANAGEMENT DEPARTMENT
FOR OPERATION AND CONSTRUCTION
ARVIN SANIT J\RY LANDFlll...
KERN COUNTY
4
a. Monitoring Parameters
Monitoring parameters are the waste constituents, reaction products, hazardous
constituents, and physical parameters that provide a reliable indication of a
release from a waste management unit. The monitoring parameters for all waste
management units are those listed in Tables I through V for the specified
monitored medium.
3. Concentration Limits
The concentration limits for each constituent of concern are as follows:
a. for naturally occuning constituents of concern, the concentration limit shall be
the calculated statistical concentration limit.
b. for anthropogenic (not naturally 9Ccurring) constituents, which have no natural
and. therefore, no background values, the concentration limit (water quality
protection standard) shall be the detection limit of the analytical method(s) used.
The Discharger shall use the data analysis method approved by the Executive Officer,
and the groundwater quality data obtained from the detection monitoring program to
update the concentration limits annually in accordance with §20415(e)(1O)(B) of Title
27. The Discharger shall submit the updated concentration limits to the Executive
Officer for review and approval in the annual monitoring report. The Discharger
shall be allowed to make a demonstration to establish concentration limits based upon
reference to historical data in accordance with §20415(e)(lO)(A) of Title 27. The
demonstration is subject to the statistical analysis criteria contained in §20415(e) of
Title 27, and shall be reviewed and approved by the Executive Officer. If the
demonstation is approved, the Discharger shall submit the historical concentration
limits to the Executive Officer for reveiw and approval in the annual monitoring
report. For successive annual monitoring reports having the same constituent
concentration Jimits as the previous year, the Discharger shall include a
demonstration to justify the unchanged values. Any annual demonstrations shall be
reveiwed and approved by the Executive Officer.
4. Point of Compliance
The point of compliance for each waste management unit is the vertical surface
located at the hydraulically downgradient limit of the waste management unit that
extends through the uppennost aquifer underlying the unit.
MONITORING AND REPORTING PROGRAM
ORDER NO. S-OO-mJ
COUNTY OF KERN
KERN COUNTY WASTE MANAGEMENT DEPARTMENT
FOR OPERATION AND CONSTRUCTION
ARVIN SANlT ARY lANDFILL
KERN COUNTY
S
a. Monitoring Points
All downgradient wells established for groundwater monitoring shall constitute
the monitoring points for the groundwater quality protection standard. All
approved monitoring wells, unsaturated zone monitoring devices, leachate, and
sulface water monitoring points shall be sampled and analyzed for monitoring
parameters and constituents of concern as indicated and listed in Tables I
through IV.
S. Compliance Period
The compliance period for each waste management unit shall be the number of years
equal to the active life of the waste management . unit plus the closure period. The
compliance period is the minimum period during which the Discharger shall conduct
a water quality monitoring program subsequent to a release from the unit. The
compliance period shall begin anew each time the Discharger initiates an evaluation
monitoring program.
D. MONITORING
The Discharger shall comply with the detection monitoring provisions of Title 27 for
groundwater, surface water, and the unsaturated zone, in accordance with Detection
Monitoring Specifications E.2 and E.3 of waste discharger requirements Order
No. 5-00-023. Detection monitoring for a new facility, a new waste management unit, or
an expansion of an existing waste management unit shall be installed, operational, and the
first round of samples collected prior to the discharge of wastes. All monitoring shall be
conduCted in accordance with a Sample Collection and Analysis Plan, which includes
quality assurance/quality control standards and the analysis of unfiltered samples. that are
acceptable to the Executive Officer.
Method detection liniits and practical quantitation limits shall be reported. All peaks, shall
be reported, including those which cannot be quantified and/or specifically identified.
Metals shall be analyzed in accordance with the methods listed in Table VI.
The, Discharger may use alternative analytical test methods, including new EPA approved
methods, provided the methods have method detection limits equal to or lower than the
analytical methods specified in this Monitoring and Reporting Program.
MONITORING AND REPORTING PROGRAM
ORDER NO. 5-00-023
COUNfYOFKERN
KERN COUNTY WASTE MANAGEMENT DEPARTMENT
FOR OPERATION AND CONSTRUCTION
AR VIN SANITARY lANDFllL
KERN COUNTY
6
1. Groundwater
The Discharger shall install and operate a groundwater detection monitoring system
that complies with the applicable provisions of §20415 and §20420 of Title 27 in
accordance with a Detection Monitoring Plan approved by the Executive Officer. The
Discharger shall collect, preserve,. and transport groundwater samples in accordance
with the approved Sample Collection and Analysis Plan.
The Discharger shall determine groundwater flow rate and direction in the uppermost
aquifer and in any zones of perched water and in any additional zone of saturation
monitored pursuant to this Monitoring and Reporting Program, and report the results
semi-annually, including the times of highest and lowest elevations of the water levels
in the wells. The groundwater elevation in each well shall be measured prior to
purging, each time the well is sampled. Groundwater elevations in wells that monitor
the same waste management facility shall be measured within a period of time short
enough to avoid temporal variations in flow which could preclude accurate
groundwater flow rate and direction detennination. Additionally, hydrographs of
each well shall be prepared showing the elevation of groundwater with respect to the
elevations of the top and bottom of the screened interval and the elevation of the
pump intake. Hydrographs of each well shall be prepared quarterly and submitted
annually.
Groundwater samples shall be collected from the point of compliance wells,
background wells, and any additional wells added as part of the approved
groundwater monitoring system. Samples shall be collected and analyzed for the
monitoring parameters in accordance with the methods and frequency specified in
Table I. In each monitoring report, all monitoring parameters shall be graphed so as
to show historical trends at each well. In lieu of graphs in each semiannual '
monitoring report, the Discharger may include a detailed discussion of constituent
trends. The discussion shall include listings of constituents displaying increasing
and/or decreasing trends; newly identified detections of VOCs; newly identified
detections of inorganic constituents at or above established concentration limits; and
detections of constituents at or above MCLs. The monitoring parameters shall also be
evaluated with regards to the cation/anion balance, and the results shall be graphically
presented using a Stiff diagram or a Piper graph. Stiff diagrams or Piper graphs shall
be prepared for all groundwater monitoring well~ every five years. Samples for the
constituents of concern specified in Table I shall be collected and analyzed in
accordance with the methods listed in Table VI every five years.
MONITORING AND REPORTING PROGRAM
ORDER NO. 5..()(M)23
COUNTY OF KERN
KERN COUNTY WASTE MANAGEMENT DEPARTMENT
FOR OPERATION AND cONSTRUCflON
ARVIN SANlT ARY lANDFllL
KERN COUNTY
7
2. . Unsaturated Zone Monitoring
The Discharger shall install and operate an unsaturated zone detection monitoring
system that complies with the applicable provisions of §20415 and §20420 of Title 27
in accordance with a detection monitoring plan approved by the Executive Officer.
The Discharger shall collect, preserve, and transport samples in accordance with the
quality assurance/quality control standards contained in the approved Sample
C:Ollection and Analysis Plan.
Unsaturated zone samples shall be collected from the monitoring devices and
background monitoring devices of the approved unsaturated zone monitoring system.
Samples shall be collected and analyzed for the listed constituents in accordance with
the methods and frequency specified in Table II. All monitoring parameters shall be
graphed so as to show historical trends at each monitoring point. Samples for the
constituents of concern specified in Table II shall be collected and analyzed in
. accordance with the methods listed in Table VI every five years.
The pan lysimeters shall be checked monthly for liquid and monitoring shall include
the volume of liquid recovered. Unsaturated zone monitoring reports shall be
included with the corresponding semi-annual groundwater monitoring and shall
include an evaluation of potential impacts of the facility on the unsaturated zone and
compliance with the water quality protection standard.
3. Leachate Monitoring
All waste management unit leachate collection and removal system sumps shall be
.
inspected weekly for leachate generation. Upon detection of leachate in a previously
dry leachate collection and removal system, leachate shall be sampled and analyzed
for the constituents listed in Table m. Leachate monitoring shall be conducted as
specified in Table ill in accordance with the methods listed in Table VI. The
constituents of concern list shall include all constituents listed in Table VI. The
quantity of leachate pumped from each sump shall be measured weekly and reported
as Leachate Flow Rate (in gallons/day).
Upon detection of any leachate seeps at the unlined waste management unit, the
leachate shall be sampled and analyzed for the constituents listed in Table m in
accordance with the methods listed in Table VI. The quantity of Jeachate shall be
estimated and reported as Leachate Flow Rate (in gallons/day).
MONITORING AND REPORTING PROGRAM
ORDER NO. 5-00-023
COUNTY OF KERN
KERN COUNTY WASTE MANAGEMENT DEPARTMENT
FOR OPERATION AND CONSTRUCTION .
AR VIN SANITARY LANDFIll..
KERN COUNTY
8
4. Facility Monitoring
a. Facility Inspection
Annually, prior to the anticipated rainy season, but no later than 30 September,
the Discharger shall conduct an inspection of the facility. The inspection shall
assess damage to the drainage control system, groundwater monitoring
equipment (including. wells, etc.), and shall include the Standard Observations
defined in the Standard Provisions and Reporting Requirements (Definition 24).
Any necessary construction, maintenance, or repairs shall be completed by
31 October. By 15 November of each year, the Discharger shall submit an
annual report describing the results of the inspection and the repair measures
implemented,
b. Storm Events
The Discharger shall inspect all precipitation, diversion, and drainage facilities
for damage within 7 days following major stonn events. Necessary repairs shall
be completed within 30 days of the inspection. The Discharger shall report any
damage and subsequent repairs within 45 days of completion of the repairs.
The Discharger shall implement the above monitoring program on the effective date of this
Program.
Ordered by:
28 J anuarv 2000
(Date)
RCS/REH
MONITORING AND REPORTING PROGRAM
ORDER NO. 5-00-023
COUNTY OF KERN
KERN COUNTY WASTE MANAGEMENT DEPARTMENT
FOR OPERATION AND CONSTRUCTION
ARVIN SANITARY LANDFIlL
KERN COUNTY
9
T ABLE I
GROUNDWATER DETECTION MONITORING PROGRAM
Parameter Units Frequency
Field Parameten
Groundwater Elevation Ft & hundredths, M.S.L. Quarterly
Temperature Of Semi-annual
Specific Conductance µmhoslcm Semi-annual
pH pH units Semi-annual
Turbidity Turbidity units Semi-annual
Monitoring Parameten
Total Dissolved Solids (TDS) mgIL Semi-annual
Chloride mgIL Semi-annual
Carbonate mgIL Semi-annual
Bicarbonate mgIL Semi-annual
Nitrate - Nitrogen mgIL Semi-annual
Sulfate mgIL Semi-annual
Calcium mg/L Semi-annual
Magnesium mg/L Semi-annual
Potassium mg/L Semi-annual
Sodium mgIL Semi-annual
V olatile Organic Compounds µgIL Semi-annual
(USEP A Method 8260, see Table V)
Constituents of Concern (see Table VI)
Total Organic Carbon mg/L 5 years
Inorganics(düssolved) mg/L 5 years
Volatile Organic Compounds µgIL 5 years
(USEPA Method 8260, extended list)
Semi-Volatile Organic Compounds µgIL 5 years
(USEP A Method 8270)
Chlorophenoxy Herbicides µgIL 5 years
(USEPA Method 8150)
Organophosphorus Compounds µgIL 5 years
(USEP A Method 8141)
MÖNITORlNG AND REPORTING PROGRAM
ORDER NO. 5-00-023
COUNTY OF KERN
KERN COUNTY WASTE MANAGEMENT DEPARTMENT
FOR OPERATION AND CONSTRUCI10N
ARVIN SANITARY LANDFITl
KERN COUNTY
10
TABLE n
UNSA TURA TED ZONE DETECTION MONITORING PROGRAM
SOIL-PORE GAS
Parameter Units Frequency
Monitoring Parameters
Volatile Organic Compounds µgfcmJ Semi-annual
(USEPA Method To..14)
Methane % Quarterly
"
PAN LYSIMETERS (or other vadose zone monitoring device)
Parameter Units Frequency
Field Parameters
Specific Conductance µmhoslcm Semi-annual
pH pH units Semi-annual
Monitoring Parameters
Total Dissolved Solids (IDS) mg/L Semi-annual
Carbonate mg/L Semi-annual
Bicarbonate Alkalinity mg/L Semi-annual
Chloride mgIL Semi-annual
Sulfate mgIL Semi-annual
Nitrate - Nitrogen mgIL Semi-annual
Volatile Organic Compounds µgIL Semi-annual
(USEPA Method 8260, see Table V)
Constituents of Concern (see Table VI)
Total Organic Carbon mgIL 5 years
Inorganics (dissolved) mgIL 5 years
Volatile Organic Compounds µgIL 5 years
(USEPA Method 8260, extended list)
Semi-Volatile Organic Compounds µgIL 5 years
(USEPA Method 8270)
Chlorophenoxy Herbicides µgIL . 5 years
(USEPA Method 8150)
Organopb~phorus Compounds µgIL 5 years
(USEP A Method 8141)
MONITORING AND REPORTING PROGRAM
ORDER NO. 5-00-023
COUNTY OF KERN
KERN COUNTY WASTE MANAGEMENT DEPARTMENT
FOR OPERATION AND CONSTRUcnON
ARVIN SANITARY LANDFIlL
KERN COUNTY
11
TABLE In
LEACHA TE DETECTION MONITORING PROGRAM
Parameter
Field Parameten
Total Flow
Flow Rate
Specific Conductance
pH
Monitoring Parameters
Total Dissolved Solids (TDS)
Carbonate
Bicarbonate Alkalinity
Chloride
Sulfate
Nitrate - Nitrogen
V olatile Organic Compounds
(USEPA Method 8260, see Table V)
Constituents of Concern (see Table VI)
Total Organic Carbon
Inorganics (dissolved)
V olatile Organic Compounds
(USEPA Method 8260, extended list)
Semi-Volatile Organic Compounds
(USEPA Method 8270)
Chlorophenoxy Herbicides
(USEP A Method 8150)
Organophosphorus Compounds
(USEP A Method 8141)
Units
Frequency
Gallons
GallonslDay
µmhoslcm
pH units
Monthly
Monthly
Monthly
Monthly
mgIL
mgIL
mgIL
mgIL
mgIL
mgIL
µgIL
Quarterly
Quarterly
Quarterly
Quarterly
Quarterly
Quarterly
Quarterly
mgIL
mgIL
µgIL
µgIL
µgIL
µgIL
5 years
5 years
5 years
5 years
5 years
5 years
MONITORING AND REPORTING PROGRAM
ORDER NO. 5-00-023
COUNTY OF KERN
KERN COUNTY WASTE MANAGEMENT DEPARTMENT
FOR OPERATION AND CONSTRUCTION
ARVIN SANITARY LANDFILL
KERN COUNTY
12
TABLE IV
MONITORING PARAMETERS FOR DETECTION MONITORING
Surrogates for Metallic Constituents:
pH
Total Dissolved Solids
Specific Conductivity
Chloride
Sulfate
Nitrate nitrogen
Constituents included in VOC:
USEPA Method 8260
Acetone
Acrylonitrile
Benzene
Bromochloromethane
Bromodichloromethane
Bromoform (Tribromomethane)
Carbon disulfide
Carbon tetrachloride
Chlorobenzene
Chloroditluoromethane
Chlorofluoromethane
Chloroethane (Ethyl chloride)
Chloroform (Trichloromethane)
Dibromochloromethane (Chlorodibromomethane)
1,2-Dibromo-3<hJoropropane (DBCP)
1,2-Dibromoethane (Ethylene dibromide; EDB)
o-Dichlorobenzene (1,2-Dichlorobenzene)
p-Dichlorobenzene (I ,4-Dichlorobenzene)
Dichloroditluoromethane (CFC-12)
Dichlorotluoromethane
trans- I ,4-Dichloro-2-butene
1,I-Dichloroethane (Ethylidene chloride)
1,2-Dichloroethane (Ethylene dichloride)
1,I-Dichloroetbylene (1,1 -Dichloroethene; Vinylidene chloride)
cis-I,2-Dichloroethylene (cis- I ,2-Dichloroethene)
trans-l,2-Dichloroethylene (trans-l,2-Dichloroethene)
1,2-Dichloropropane (Propylene dichloride)
cis-l,3-Dicbloropropene
trans- 1,3-Dichloropropene
Ethylbenzene
2-Hexanooe (Methyl butyl ketone)
Isopropylbenzene
MONITORING AND REPORTING PROGRAM
ORDER NO. 5-00-023
COUNTY OF KERN
KERN COUNTY WASTE MANAGEMENT DEPARTMENT
FOR OPERATION AND CONSTRUCTION
ARVIN SANITARY LANDFllL
KERN COUNTY
13
TABLE IV
MONITORING PARAMETERS FOR DETECTION MONITORING
Continued
p-Isopropyltoluene
Methyl bromide (Bromomethene)
Methyl chloride (Chloromethane)
Methylene bromide (Dibromomethane)
Methylene chloride (Dichloromethane)
Methyl ethyl ketone (MEK: 2-Butanone)
Methyl iodide Oodomethane)
Methyl tert-Butyl Ether
4-Methyl-2-pentanone (Methyl isobutylketone)
Pentane
Styrene
1,1,1,2- Tetrachloroethane
1,1.2,2- Tetrachloroethane
Tetrachloroethylene (Tetrachloroethene; Perchloroethylene)
Toluene
1,1, I-Trichloethane (Methylchloroforrn)
1,1,2- Trichloroethane
Trichloroethylene (Trichloroethene)
Trichlorofluoromethane (CFC-ll)
1,2,3- Trichloropropane
1,2,4- Trimethylbenzene
1,3,5- Trimethylbenzene
Vinyl acetate
Vinyl chloride
Xylenes
MONITORING AND REPORTING PROGRAM
ORDER NO. 5'()()-023
COUNTY OF KERN
KERN COUNTY WASTE MANAGEMENT DEPARTMENT
FOR OPERATION AND CONSTRUCTION
ARVIN SANITARY LANDFllL
KERN COUNTY
14
TABLE V
CONSTITUENTS OF CONCERN & APPROVED USEPA ANALYTICAL METHODS
Aluminum
Antimony
Barium
Beryllium
Cadmium
Chromium
Cobalt
Copper
Silver
Tin
Vanadium
Zinc
Iron
Manganese
Arsenic
Lead
Mercury
Nickel
Selenium
Thallium
Cyanide
Sulfide
USEPA Method
6010
6010
6010
6010
6010
6010
6010
6010
6010
6010
6010
6010
6010
6010
7061
7421
7470
7520
7741
7841
9010
9030
Inommics (dissOlved):
Volatile Organic Compounds:
USEPA Method 8260
Acetone
Acetonitrile (Methyl cyanide)
Acrolein
Acrylonitrile
Allyl chloride (3-ChJoropropene)
Benzene
Bis(2~thylhexyl) phthalate
Bromochloromethane (Chlorobromomethane)
Bromodichloromethane (Dibromochloromethane)
Bromoform (Tribromomethane)
Carbon disulfide
Carbon tetrachloride
CbIorobenzene
CbIorodifluoromethane
CbIorofluoromethane
Cbloroethane (Ethyl chloride
~
MONITORING AND REPORTING PROGRAM
ORDER NO. 5-00-023
COUNTY OF KERN
KERN COUNTY WASTE MANAGEMENT DEPARTMENT
FOR OPERATION AND CONSTRUCflON
ARVIN SANITARY LAND~
KERN COUNTY
15
TABLE V
CONSTITUENTS OF CONCERN & APPROVED USEPA ANALYTICAL
METHODS
Continued
Chloroform (Trichloromethane
Chloroprene
Dibromocbloromethane (Chlorodibromomethane)
1,2-Dibro~3<hloropropane (DBCP)
l,2-Dibromoethane (Ethylene dribromide; EDB)
o-Dichlorobenzene (1 ,2-Dichlorobenzene)
m-Dichlorobenzene (1 ,3-Dichlorobenzene)
p-Dichlorobenzene (1,4-Dichlorobenzene)
trans-l ,4-Dichloro- 2-butene
Dichlorodit1uoromethane (CFC-12)
Dichlorot1uoromethane
1,I-Dichloroethane (Ethylidene chloride)
1,2-Dichloroethane (Ethylene dichloride)
1,1-Dichloroethylene (1, I-Dichloroethene; Vinylidene chloride)
cis-I ,2-Dichloroethylene (cis- l,2-Dichloroethene)
trans-I ,2-DichJoroethylene (trans- 1,2-Dichloroethene)
l,2-Dichloropropane (Propylene dichloride)
1,3-Dichloropropane (Trimethylene dichloride)
2,2-Dichloropropane (Isopropylidene chloride)
l,l-Dichloropropene
cis-} ,3-Dichloropropene
ttans-I ,3-Dichloropropene
EthyIbenzene
Hexachlorobutadiene
2-Hexanone (Methyl butyl ketone)
Isobutyl alcohol
Isodrin
Isopropylbenzene
p-Isopropyltoluene
Methacrylonitrile
Methyl bromide (Bromomethane)
Methyl chloride (Chloromethane)
Methyl ethyl ketone (MEK; 2-Butanone)
Methyl iodide (Iodomethane)
Methyl methacrylate
Methyl ten-Butyl Ether
4-Methyl-2-pentanone (Methyl isobutyl ketone)
Methylene bromide (Dibromomethane)
Methylene chloride (Dichloromethane)
Naphthalene
Pentane
Propionitrile (Ethyl cyanide)
MONITORING AND REPORTING PROGRAM
ORDER NO. 5-00-023
COUNTY OF KERN
KERN COUNTY WASTE MANAGEMENT DEPARTMENT
FOR OPERATION AND CONSTRUCTION
ARVIN SANlT ARY LANDFIlL
.KERN COUNTY
16
TABLE V
CONSTITUENTS OF CONCERN & APPROVED USEPA ANALYTICAL
MEmODS
Continued
Styrene
1,1,1,2- Tetrachloroethane
1,1,2,2- Tetrachloroethane
Tetrachloroethylene (Tetrachloroethene; Perchloroethylene; PCE)
Toluene
1,2,4- Trichlorobenzene
l,t,I-Trichloroethane, Methylchloroform
1, I ,2- Trichloroethane
Trichloroethylene (Trichloroethene; TCE)
Trichlorofluoromethane (CFC-Il)
1,2,3- Trichloropropane
1,2,4- Trimethylbenzene
1,3,5-Trimethylbenzene
Vinyl acetate
Vinyl chloride (Chloroethene)
Xylene (total)
Semi-Volatile Organic Compounds:
USEPA Method 8270 - base. neutral. & acid extractables
Acenaphthene
Acenaphthylene
Acetophenone
2-Acetylaminofluorene (2-AAF)
Aldrin
4-Aminobiphenyl
Anthracene
Benzo[ a]anthracene (Benzanthracene)
Benzo[b]fluoranthene
Benzo[k]fluoranthene
Benzo[g,h,i]perylene
Benzo[ a]pyrene
Benzyl alcohol
alpha-BRC
beta-BHC
delta-BRC
gamma-BRC {Lindane}
Bis(2-chloroethoxy)methane
Bis(2-chloroethyl) ether (Dichloroethyl ether)
Bis(2-chloro-l-methyethyl) ether (Bis(2-chloroisopropyl) ether; DC1P)
4-Bromophenyl phenyl ether
Butyl benzyl phthalate (Benzyl butyl phthalate)
MONITORING AND REPORTING PROGRAM
ORDER NO. 5-00-023
COUNTY OF KERN
KERN COUNTY WASTE MANAGEMENT DEPARTMENT
FOR OPERATION AND CONSTRUCTION
ARVIN SANITARY LANDFILL
KERN COUNTY
17
TABLE V
CONSTITUENTS OF CONCERN & APPROVED USEPA ANALYTICAL
METHODS
Continued
Chlordane
p-Chloroaniline
Chlorobenzilate
p-Chloro-DKresol (4-Chloro-3-methylphenol)
2-011oronaphthalene
2-Oll0r0phenol
4-ChIorophenyl phenyl ether
Chrysene
o-Cresol (2-methylphenol)
m-Cresol (3-methylphenol)
p-Cresol (4-methylphenol)
4,4':.DDD
4,4'-DDE
4.4'-DDT
Diallate
Dibenz[ a.b ] anthracene
Dibenzofuran
Di-n-butvl phthalate
o-Dichlorobenzene (1,2-Dichlorobenzene)
m-Dichlorobenzene (I ,3-Dichlorobenzene)
p-Dicblorobenzene (1 ,4-Dichlorobenzene)
3,3'-Dichlorobenzidine
2,4-Dichlorophenol
2.6-Dichlorophenol
Dieldrin
Diethyl phthalate
p-{Dimethylamino )azobenzene
7, 12-Dimethylbenz[ a]anthracene
3,3'-Dimethylbenzidine
2,4-Dimehtylphenol (m-Xylenol)
Dimethvl phthalate
m-Dinitrobenzene
4,6-Dinitro-o-cresol (4,6-Dinitro-2-methylphenol)
2,4-Dinitrophenol
2,4-Dinitrotoluene
2,6-Dinitrotoluene
Di-n-<>Ctyl phthalate
Diphenylamine
Endosulfan I
Endosulfan n
Endosulfan sulfate
Endrin
..
MONITORING AND REPORTING PROGRAM
ORDER NO. 5-00-023
COUNTY OF KERN
KERN COUNTY WASTE MANAGEMENT DEPARTMENT
FOR OPERATION AND CONSTRUCfION
ARVIN SANITARY LANDFllL
KERN COUNTY
18
TABLE V
CONSTITUENTS OF CONCERN & APPROVED USEPA ANALYTICAL
METHODS
Continued
Endrin aldehyde
Ethyl methacrylate
Ethyl methanesulfonate
Famphur .
Fluoranthene
Fluorene
Heptachlor
HeptachJor epoxide
HexachJorobenzene
HexachJorobutadiene
HexachJorocyclopentadiene
Hexachloroethane
Hexachloropropene
Indem)( 1.2,3<.d)pyrene
Isophorone
Isosafrole
Kepone
MethapyriJene
Methoxychlor
3-Methylcholanthrene
Methyl methanesulfonate
2-Methylnaphthalene
Naphthalene
1,4-Naphthoquinone
I-Naphthylamine
2-Naphthylamine
o-Nitroaniline (2-Nitroaniline)
m-Nitroaniline (3-Nitroaniline)
p-Nitroaniline (4-Nitroaniline)
Nitrobenzene
o-Nitrophenol (2-Nitrophenol)
p-Nitrophenol (4-Nitrophenol)
N-Nitrosodi-n-butylamine (Di-n-butylnitrosamine)
N-Nitrosodiethylamine (DieØ1ylnitrosamine)
N-Nitrosodimethylamine (Dimethylnitrosamine)
N-Nitrosodiphenylamine (Diphenylnitrosamine)
N-Nitrosodipropylamine (N-Nitroso-N~ipropylamine; Di-n-propylnitrosamine)
N-Nitrosometbylethylamine (Methylethylnitrosamine)
N-Nitrosopiperidine
N-Nitrosospyrrolidine
5-Nitro-o-toluidine
Pentachlorobenzene
;
MONITORING AND REPORTING PROGRAM
ORDER NO. 5-00-023
COUNTY OF KERN
KERN COUNTY WASTE MANAGEMENT DEPARTMENT
FOR OPERATION AND CONSTRUCTION
ARVIN SANITARY LANDFILL
KERN COUNTY
19
TABLE V
CONSTITUENTS OF CONCERN & APPROVED USEPA ANALYTICAL
METHODS
Continued
Pentachloronitrobenzene (PCNB)
Pentachlorophenol
PhenaCetin
Phenanthrene
Phenol
p-Phenylenediamine
Polychlorinated biphenyls (PCBs; Aroclors)
Pronamide
Pyrene
Safrole
1,2,4,5- T etrachlorobenzene
2,3,4,6- Tetrachlorophenol
0- Toluidine
Toxaphene
1,2,4- Trichlorobenzene
2.4.5- Trichloropheno
12,4,6-Trichlorophenol
0,0,0- Triethyl phosphorothioate
sym- Trinitrobenzene
Chlorophenoxy Herbicides:
USEP A Method 8150
2,4-D (2,4-Dichlorophenoxyacetic acid)
Dinoseb (DNBP; 2-sec-ButyI4,6~initrophenol)
Silvex (2,4,5-Trichlorophenoxypropionic acid; 2,4,5-TP)
2,4,5- T (2,4,5- Trich1orophenoxyacetic acid)
Organophosphorus Compounds:
USEPA Method 8141
O,O-Diethyl 0-2-pyrazinyl phosphorothioate (Thionazin)
Dimethoate
Disulfoton
Methyl parathion (parathion methyl)
Parathion
Phorate
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o Waste Management Facility Boundary
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ATTACHMENT A
FACILITY LOCATION MAP
ARVIN SANITARY LANDFILL
COUNTY OF KERN
(2125198 )
Existing Monitoring Well
Existing Vadose Zone Monitoring Point
Landfill Water Supply Well
Waste Management Facility Boundary
aAR1-22
AR1.06
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. lEGEND
AnACHMENT B
SCHEMATIC REPRESENTATION
of the -
ARVIN SANITARY LANDFILL
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Waste Management Unit
COUNTY OF KERN
Approximate Scale: 1- = 600'
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INFORMATION SHEET
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ORDER NO. 5-00-23
COUNTY OF KERN
FOR OPERATION AND CONSTRUCflON
ARVIN SANITARY LANDFIIL
KERN COUNTY
The County of Kern owns and operates the Arvin Sanitary Landfill. The facility was originally operated
as a bum dump as early as 1949, and was converted to a landfill in August 1971. Based on 1998 data,
the waste management facility receives approximately 267 tons of municipal solid waste per day with an
estimated remaining capacity of 550,393 cubic yards. Final capacity is anticipated by September 2000.
It is approximately five miles west of Arvin and receives waste from the greater Arvin area, portions of
Bakersfield, the communities of Lamont, Weedpatch, Greenfield, and Pumpkin Center, and the Lebec
transfer station.
A 127-acre unlined waste management unit exists within the 170-acre waste management facility
property. The site is within a l00-year floodplain according to FEMA maps. Soils underlying the site
are unconsolidated, consisting of interbedded gravels, sands, silts, and clays.
Depth to groundwater is approximately 59 to 80 feet below the native ground surface, and exhibits a
gradient toward the south. Monitoring data from one background well indicates that groundwater has a
total dissolved solid range of 507 to 680 mgll, which exceeds the secondary drinking water standard
established by the Department of Health Services. Groundwater monitoring has detected volatile
organic compounds at concentrations in excess of the primary maximum contaminant levels for drinking
water.
Evaluation monitoring to determine the extent óf groundwater degradation has been implemented at the
site. Completion of the evaluation monitoring program, modification of the detection monitoring
program for full compliance with Title 27, and implementation of a corrective action program will be
addressed in a subsequent Cleanup and Abatement Order.
This Order implements groundwater detection monitoring and operation of the facility in accordance
with the provisions contained in Title 27.
RCS/REH: 1/2812000
o
California Regional Water Quality Control Board
Central Valley Region
Steven T. Butler, Acting Chair
@
~
Winston H;.}Iickox
Secreta!; for
Environmental
Prnl,rtinn
Fresno Branch Office
Internet Address: hltp:/fwww.swrcb.ca.gov/-rwqcb5
3614 East Ashlan Avenue. Fresno. California 93726
Phone (559) 445-5116' FAX (559) 445-5910
Gray Davis
Govemor
19 November 1999
Ms. Daphne H. Washington
Kern County Waste Management Department
2700 M Street, Suite 500
Bakersfield, CA 93301
, , - "-,
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NOTICE
TENTATIVE WASTE DISCHARGE REQUIREMENTS
FOR
COUNTY OF KERN
FOR
OPERATION AND CONSTRUCTION
ARVIN SANITARY LANDFILL
KERN COUNTY
Any comments or recommendations you may have concerning this tentative Order should be submitted
to this office in writing by 31 December 1999 in order that consideration may be given them prior to the
meeting of the Regional Board.
If you have any questions, please call Ronald Holcomb of this office at (559) 445-6050.
~(}~
DANE S. JO~ON
Senior Engineeririg Geologist
CRG No. 4239
Enclosure
cc: U.S. Environmental Protection Agency, Region 9, San Francisco
Mr. Tim Regan, Office of Chief Counsel, State Water Resources Control Board, Sacramento
Ms. Elizabeth Haven, Division of Clean Water Programs, State Water Resources Control Board,
Sacramento
California Integrated Waste Management Board, Sacramento
Department of Health Services, Office of Drinking Water, Fresno
dsjlrehlu: landfilVrehlkemnowl Arvinlaslwdr/asltncl.doc
California Environmental Protection Agency
o Recycled Paper
TENTATIVE
WASTE DISCHARGE REQUIREMENTS
ARVIN SANITARY LANDFILL
KERN COUNTY
-2-
~
Department of Fish and Game, Region IV, Fresno
Department of Water Resources, San Joaquin District, Fresno
Kern County Department of Environmental Health Services, Bakersfield
Kern County Department of Planning and Development Services, Bakersfield
. Kern County Air Pollution Control District, Bakersfield
Kern County Water Agency, Bakersfield
Mr. Howard Wines, City of Bakersfield, Bakersfield
ds j/rehlu :landfilllrehlk&dII 999/wdr/kdnphcl.doc
California Environmental Protection Agency
Recycled Paper
19 November 1999
i'
CALIFORNIA REGIONAL WATER QUALITY CONTROL BOARD
CENTRAL V ALLEY REGION
ORDER NO.
WASTE DISCHARGE REQUIREMENTS
FOR
COUNTY OF KERN
FOR
OPERATION AND CONSTRUCTION
ARVIN SANITARY LANDFILL
KERN COUNTY
The California Regional Water Quality Control Board, Central Valley Region, (hereafter Board)
finds that:
1. The County of Kern (hereafter Discharger) owns and operates a municipal solid waste
landfill approximately five miles west of the City of Arvin, in Section 31, T31S, R29E,
MDB&M, as shown in Attachment A, which is incorporated herein and made part of this
Order.
2. The existing waste management unit consists of one existing unlined waste management
unit covering 127 acres, as shown in Attachment B, which is incorporated herein and made
part of this Order. The facility is comprised of Assessor's Parcel Number (APN) 189-330-
20-00-0.
3. The Discharger may expand the waste management unit for the discharge of municipal
solid waste to an area of approximately 15 acres within the SW 1/4 of the NW 1/4 of
Section 31, T31S, R29E, MDB&M.
4. On 14 August 1992, the Board adopted Order No. 92-163, which prescribes waste
discharge requirements for the existing waste management unit. The facility is classified as
a Class ill landfill which accepts municipal solid waste in accordance with Title 27,
California Code of Regulations, §20005, et seq. (Title 27).
5. On 17 September 1993, the Board adopted Order No. 93-200, amending Order No, 92-163
and implementing State Water Resources Control Board Resolution No. 93-62, Policy for
Regulation of Discharges of Municipal Solid Waste.
6. This Order updates the waste discharge requirements for the facility in conformance with/
the California Water Code and Title 27, and the revisions and policies adopted hereunder,
and removes the facility from Attachment 1 of Order No. 93-200. This Order also
DRAFT
WASTE DISCHARGE REQUIREMENTS, ORDER NO.
COUNTY OF KERN
.
FOR OPERATION AND CONSTRUCTION
l' ARVIN SANITARY LANDFll.L
KERN COUNTY
-2-
addresses operation of the unlined waste management unit and construction of any lateral
expansion or new waste management unit.
7. Based on 1998 data, the waste management facility receives approximately 267 tons of
municipal solid waste per day with an estimated remaining capacity of 550,393 cubic yards.
Final capacity is anticipated by September 2000.
'. .~
SITE DESCRIPTION
8. The facility is in a topographically flat region of the Tulare Lake Hydrologic Basin of the
San Joaquin Valley. The native ground surface elevation ranges between approximately
360 feet above mean sea level at the northeast boundary of the facility and 345 feet above
mean sea level at the southwest facility boundary. The ground surface slopes
approximately 22 feet per mile toward the southwest.
9. The waste management facility is on Quaternary alluvial deposits. The soils underlying the
facility are unconsolidated soils, consisting of interbedded gravels, sands, silts, and clays.
10. The measured hydraulic conductivity of the native soils underlying the waste management
unit range between 9 x 10-4 and 4 x 10-7 cm/sec.
11. The waste management facility is not within a fault hazard zone. The closest Holocene
fault is the White Wolf Fault, approximately five miles to the south. A Richter scale
magnitude 7.7 earthquake occurred along the White Wolf Fault in 1952.
12. An abandoned non-hazardous oil field waste processing facility, formerly operated by
V en Virotek, is located on a 5-acre parcel within the southwest comer of the waste
management facility property. An estimated 200,000 cubic yards of impacted soil, and
other processing equipment remain. Waste Discharge Requirements, Order No. 92-199,
were adopted naming both VenVirotek and Kern County as co-dischargers for the waste
processing facility.
13. Landwithin 1,000 feet of the facility is used for cultivated crops and vacant land. A former
residence domestic well (California State Well No. 31129-30POl) is located approximately
150 feet north ofthe facility. The Discharger has identified well 31129-30POl as a potential
source of additional water for operations at the waste management facility. Well 31/29-
30POl is shown on Attachment B.
14. The facility receives an average of 6.1 inches of precipitation per year as determined from
data collected by the Department of Water Resources. The mean evaporation is 87 inches
DRAFT
WASTE DISCHARGE REQUIREMENTS, ORDER NO.
COµNTY OF KERN
FOR OPERA nON AND CONSTRUCTION
" ARVIN SANITARY LANDFILL
KERN COUNTY
-3-
per year as determined from evaporation data collected by the Department of Water
Resources between 1967 and 1978.
15. The 1oo-year, 24-hour precipitation event for the facility is estimated to be 2.5 inches, as
determined from data furnished by the National Weather Service.
16. The waste management facility is within a 100-year floodplain based on the Federal
Emergencý Management Agency's (FEMA) Flood Insurance Rate Map, Community-Panel
Number 060075 BOOB, dated 29 September 1986.
17. There are ten municipal, domestic" industrial, or agricultural supply wells within a I-mile
, radius of the site. No surface springs or other sources of groundwater supply have been
observed.
18. The landfill water supply well (California State Well No. 31/29-31D1) is located at the
northwest comer of the waste management unit. The well was drilled to a total depth of
320 feet below ground surface. A surface seal reportedly exists to 50 feet below ground
surface. The remainder of the borehole is gravel packed.
SURFACE AND GROUND WATER CONDITIONS
19. The Board adopted the Water Quality Control Plan for the Tulare Lake Basin; Second
Edition (hereafter Basin Plan), that designates beneficial uses and contains water quality
objectives for all waters of the Basin. This Order implements the Basin Plan.
20. Surface drainage is toward the Kern Lake Bed in the Kern Delta Hydrologic Area (557.10)
of the Tulare Lake Basin.
21. The designated beneficial uses of surface waters on the valley floor, as specified in the
Basin Plan, are agricultural supply, industrial service and process supply, contact and
noncontact water recreation, wann fresh water habitat, preservation of rare, threatened and
endangered species, and groundwater recharge.
22. The first encountered areal groundwater is approximately 59 to 80 feet below the native
ground surface. Groundwater elevations range from 280 feet MSL to 288 feet MSL.
23. Monitoring data indicates that the groundwater is unconfined. The depth to groundwater
fluctuates seasonally as much as 11 feet.
24. The current direction of groundwater flow beneath the waste management facility is from
the northwest toward the south. The average groundwater gradient is approximately 0.004
DRAFT
WASTE DISCHARGE REQUIREMENTS, ORDER NO.
COUNTY OF KERN
.
FOR OPERATION AND CONSTRUCTION
" ARVIN SANITARY LANDFILL
KERN COUNTY
-4-
feet per foot. The groundwater velocity has been reported as seven to ten feet per year.
The direction of groundwater flow has varied between southeast and southwest.
25. Monitoring data from upgradient monitoring well AR1-01 indicates that groundwater
collected from this well from 1989 through 1998 has a specific electrical conductivity that
ranges from 863 to 1,540 micromhos/cm, and Total Dissolved Solids ranging from 507 to
680 mgll. The quality of groundwater from AR1-01 exceeds the secondary drinking water
standards established by the Department of Health Services for electrical conductivity and
Total Dissolved Solids.
Three additional background monitoring wells were installed in November 1997. Wells
AR1-06 and ARI-22 were installed upgradient from the landfill. Well ARl-21 was
installed sidegradient from the landfill. Wells ARl-21 and ARl-22 monitor first
encountered groundwater, while well ARI-06 was completed approximately 80 feet below
first encountered groundwater.
Monitoring data from deep upgradient well AR1-06, upgradient well ARl-22, and
side gradient well ARI-21 indicate that groundwater collected from these wells from May
1998 through January 1999 have electrical conductivity ranges from 434 to 617; 4,240 to
5,070; and 644 to 1,034 micromohs/cm, respectively. The range of Total Dissolved Solids
in wells ARI-06, ARl-21, and ARl-22 for the same time period is 272 to 294; 3,120 to
3,880; and 436 to 493 mgll, respectively. The quality of groundwater from AR1-06 meets
the secondary drinking water standards established by the Department of Health Services
for electrical conductivity and Total Dissolved Solids. The quality of groundwater in well
ARl-21 exceeds the secondary drinking water standards for electrical conductivity and
Total Dissolved Solids. The quality of groundwater in well ARl-22 exceeds the secondary
drinking water standard for electrical conductivity and meets the secondary drinking water
standard for Total Dissolved Solids.
26. The designated beneficial uses of the groundwater, as specified in the Basin Plan, are
domestic and municipal, agricultural, and industrial supply.
27. State Water Resources Control Board Order No. 97-03-DWQ (General Permit No.
CASOOOOO 1), amended 17 April 1997, specifies waste discharge requirements for
discharges of storm water associated with industrial activities, excluding construction
activities, and requiring submission of a Notice Of Intent by industries to be covered under
the permit. Waste disposal at landfills, including inert disposal facilities, is considered an
industrial activity requiring submittal of a Notice Of Intent for coverage under the general
permit if storm water is to be discharged off-site. The Discharger submitted a Notice of
Intent on 27 August 1997, and a Storm Water Pollution Prevention Plan and Monitoring
Program Reporting Requirements on 12 June 1998. Storm water runoff is proposed to be
DRAFT
WASTE DISCHARGE REQUIREMENTS, ORDER NO.
COUNTY OF KERN
.
FOR OPERATION AND CONSTRUCTION
í' ARVIN SANITARY LANDFilL
KERN COUNTY
-5-
impounded or temporarily detained in an excavation located adjacent to the unlined waste
management unit in the SW 1/4 of the NW1/4 of Section 31, T31 S, R29E, MDB&M,
WASTE AND SITE CLASSIFICATION
28. The discharge consists of putrescible and nonprutrescible municipal solid wastes and non-
friable asbestos, These wastes are classified as 'nonhazardous solid waste' or 'inert waste'
using the criteria set forth in Title 27.
29. The site characteristics where the waste management unit is located (see Finding No. 10)
do not meet the siting criteria for a Class ill landfill contained in §20260(a) and (b)(1) of
Title 27. As su~h, the site is not suitable for the discharge and containment of Class ill
wastes. Therefore, in order to discharge the wastes described in Finding No. 28, additional
waste containment measures are required in accordance with §20260(b)(2) of Title 27 and
State Water Resources Control Board Resolution No. 93-62 for any lateral expansion of the
waste management unit.
30. The Discharger may construct a lateral expansion within the waste management facility
property. The liner system will need to be designed, constructed, and operated to prevent
migration of w~tes from the waste management unit to adjacent natural geologic materials,
groundwater, or surface water during disposal operations, closure, and the post-closure
maintenance period in accordance with the criteria set forth in Title 27 for a Class ill
landfill, and the provisions in State Water Resources Control Board Resolution No. 93-62
for municipal solid wastes.
GROUNDWATER MONITORING
:u. The Discharger is required to monitor the groundwater and vadose zone in accordance with
Title 27.
32. This Order requires that the groundwater and vadose zone detection monitoring devices be
installed, operational, and the first round of samples analyzed prior to the discharge of
waste to any waste management unit expansion.
33. Nine groundwater monitoring wells have been installed at the waste management facility
for detection monitoring purposes. The existing groundwater detection monitoring system
consists of down gradient monitoring wells ARI-02, ARI-03, ARI-04, ARI-05, ARl-23,
upgradient monitoring wells ARI-Ol, ARI-06, ARl-21, and sidegradient well ARl-22.
The elevation of static groundwater in wells ARI-Ol, ARI-02, ARI-03, ARI-04, and ARl-
DRAFT
WASTE DISCHARGE REQUIREMENTS, ORDER NO.
COUNTY OF KERN
,
FOR OPERATION AND CONSTRUCTION
i' ARVIN SANITARY LANDFILL
KERN COUNTY
-6-
05 exceeds the elevation of the top of screened interval in each well. The elevation of
groundwater above the screened interval currently ranges from one to twenty one feet.
Excluding well ARl-23, completed approximately ninety-five feet below the elevation of
static groundwater when drilled, the elevation of the pump intakes in each downgradient
well is below the elevation of static groundwater by a range of eleven to fifty-six feet.
34. The vadose zone monitoring system for the unlined waste management unit consists of two
moisture block/gas probe clusters (ARl-07 and ARl-08), installed at the base of refuse.
35. The Discharger has implemented an Evaluation Monitoring Program for the existing waste
management unit, but has not completed the delineation of the vertical and lateral extent of
the groundwater degradation in accordance with the time schedule in Title 27. Details of
the work accomplished and the work remaining to complete the Evaluation Monitoring
Program will be addressed in a subsequent Cleanup and Abatement Order.
36. The Discharger's detection monitoring program for groundwater does not satisfy the
requirements contained in Title 27 due to an insufficient number of groundwater
monitoring wells and no established concentration limits. A subsequent Cleanup and
Abatement Order will require the Discharger to bring the, Detection Monitoring Program
into full compliance with Title 27 in accordance with an approved time schedule.
GROUNDWATER DEGRADATION
37. Groundwater monitoring performed at the landfill has detected volatile organic compounds
(VOCs) in samples collected from on-site monitoring wells since 1990. Groundwater
analyses have repeatedly detected the following waste constituents at concentrations above
water quality objectives (primary Maximum Contaminant Level): benzene; 1,1-
dichloroethane; methylene chloride; tetrachloroethene (PCE); trichloroethene (TCE); and
vinyl chloride. Other constituents repeatedly detected in wells at concentrations below
water quality goals include: acetone; bis (2-ethylhexyl) phthalate; benzyl butyl phthalate;
chlorobenzene; chlorodit1uoromethane; chlorot1uoromethane; chloroform;
dichlorodit1uoromethane (Freon 12); 1, l-dichloroethene; cÏs-l ,2-dichloroethene;
dichlorot1uoromethane; 1,2-dichloropropane; ethylbenzene; isopropylbenzene; p-isopropyl
toluene; pentane; toluene; 1,1, I-trichloroethane; trichlorotluoromethane (Freon 11);
1,2,4-trimethylbenzene; 1,3,5-trimethylbenzene; and total xylenes.
38. Constituents detected in evaluation monitoring hydropunch borings include: acetone;
benzene; bromodichloromethane; bromoform; chloroform; chloromethane;
dibromochloromethane; dichloroditluoromethane (Freon 12); 1, I-dichloroethane;
DRAFT
WASTE DISCHARGE REQUIREMENTS, ORDER NO.
COJJNTY OF KERN
FOR OPERATION AND CONSTRUCTION
ARVIN SANITARY LANDFll..L
KERN COUNTY
-7-
isopropylbenzene; methyl ethyl ketone; methylene chloride; naphthalene; n-propylbenzene;
PCE; 1,1, I-trichloroethane; TCE; trichlort1uoromethane (Freon 11); 1,2,4-
trimethylbenzene; 1,3,5-trimethylbenzene; and toluene.
39. Constituents detected in down gradient monitoring well ARl-23, completed 100 feet below
the depth of first continuous groundwater, include: chloroform; dichlorodifluoromethane
(Freon 12); 1,I-dichloroethane; isopropylbenzene; methylene chloride; tetrachloroethene
(PCE); toluene; trichloroethene (TCE); and 1,1 ,2-trichloro-1 ,2,2-trifluoroethane.
40. Constituents detected in a sample collected from the landfill water supply well include
dichlorodifluoromethane (Freon 12) and methylene chloride. The compounds benzidine
and endrin aldehyde were tentatively identified.
CONSTRUCTION AND ENGINEERED ALTERNATIVE
41. On 17 June 1993, the State Water Resources Control Board adopted Resolution No. 93-62
implementing a State Policy for the construction, monitoring, and operation of municipal
solid waste landfills that is consistent with the federal municipal solid waste regulations
promulgated under Title 40, Code of Federal Regulations, Part 258 (Subtitle D).
42. Resolution No. 93-62 requires the construction of composite liner systems at municipal
solid waste landfills that receive wastes after 9 October 1993. The prescriptive standard for
a composite liner system consists of a minimum 40-mil thick (60 mil for HDPE) upper
synthetic flexible membrane component and lower soil component of compacted clay a
minimum of two feet thick with a hydraulic conductivity not to exceed 1 x 10-7 em/sec.
43. Resolution No. 93-62 also allows the Board to consider the approval of engineered
alternatives to the prescriptive standard. Section ill.A.b. of Resolution No. 93-62 requires
that the engineered alternative be of a composite design similar to the prescriptive standard.
44. Section 20080(b) of Title 27 allows the Board to consider the approval of an engineered
alternative to the prescriptive standard. In order to approve an engineered alternative in
accordance with §20080(c)(l) and (2), the Discharger must demonstrate that the
prescriptive design is unreasonably and unnecessarily burdensome and will cost
substantially more than an alternative which will meet the criteria contained in §20080(b),
or would be impractical and would not promote attainment of applicable performance
standards. The Discharger must also demonstrate that the proposed engineered alternative
is consistent with the performance goal addressed by the particular prescriptive standard,
and provides protection against water quality impairment equivalent to the prescriptive
standard in accordance with §20080(b )(2) of Title 27.
DRAFT
WASTE DISCHARGE REQUIREMENTS, ORDER NO.
COµNTY OF KERN
FOR OPERATION AND CONSTRUCTION
, ARVIN SANIT AR Y LANDFllL
KERN COUNTY
-8-
45. Section 1 3360(a)(1) of the California Water Code allows the Board to specify the design,
type of construction, and/or particular manner in which compliance must be met in waste
discharge requirements or orders for the discharge of waste at solid waste disposal
facilities.
46. The Discharger has not yet submitted a design plan for an expansion of the Arvin Sanitary
Landfill.
47. Prior to an ex.pansion of the existing waste management unit, the Discharger will need to
submit for Executive Officer approval, design and construction CQA plans for expansion of
the waste management unit.
48. An unsaturated zone monitoring system will need to be installed beneath the composite
liner system of any lateral expansion in accordance with § 20415 (d) of Title 27.
49. Construction will proceed only after all applicable design, construction plans, and
construction quality assurance plans have been approved by the Executive Officer.
CEQA CONSIDERATIONS
50. The action to update waste discharge requirements for this facility is exempt from the
provisions of the California Environmental Quality Act (CEQA), Public Resource Code
§21000, et seq., and the CEQA guidelines, in accordance with Title 14, CCR, §15301, et
seq.
OTHER CONSIDERATIONS
51. On 9 October 1991, the United States Environmental Protection Agency (USEPA)
promulgated regulations (Title 40, Code of Federal Regulations, Parts 257 and 258,
"federal municipal solid waste [MSW] regulations" or "Subtitle D") that apply, in
California, to dischargers who own or operate Class II or Class III landfill units at which
municipal solid waste is discharged. The majority of the federal MSW regulations became
effective on the "Federal Deadline", which was 9 October 1993. The USEPA has deemed
the State of California to be an approved state, meaning that compliance with the applicable
state regulations constitutes compliance with the federal Subtitle D regulations. These
requirements implement the appropriate state regulations in lieu of Subtitle D.
52. These requirements implement the prescriptive standard and performance goals of Title 27,
California Code of Regulations, §20005 et seq. (Title 27).
53. These requirements implement the Water Quality Control Plan for the Tulare Lake Basin,
Second Edition, 1995.
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WASTE DISCHARGE REQUIREMENTS, ORDER NO.
COUNTY OF KERN
,
FOR OPERATION AND CONSTRUCTION
, ARVIN SANITARY LANDFILL
KERN COUNTY
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54. The requirements implement State Water Resources Control Board Resolution No. 93-62,
Policy for Regulation of Discharges of Municipal Solid Waste, which implement the
federal Subtitle D regulations.
55. All local agencies with jurisdiction to regulate land use, solid waste disposal, air pollution,
and to protect public health have approved the use of this sitc~ for the discharges of waste to
. land stated herein.
56. The Board has notified the Discharger and interested agencies and persons of its intention
to update the waste discharge requirements for this facility.
57. In a public hearing, the Board heard and considered all comments pertaining to this facility
. and discharge.
IT IS HEREBY ORDERED that Order No. 92-163 is rescinded, and Attachment I of Order No.
93-200 is amended to delete the Arvin Sanitary Landfill, which is on line No. 55, and that the
County of Kern, Kern County Waste Management Department, its agents, successors, and
assigns, in order to meet the provisions of Division 7 of the California Water Code and the
regulations adopted hereunder, shall comply with the following:
A. PROHIBITIONS
1. The discharge of 'hazardous waste' at this facility, except waste that is hazardous
due only to its friable asbestos content, is prohibited. The discharge of 'designated
waste' at this facility is prohibited. For the purposes of this Order, the tt~rm
'hazardous waste' is as defined in Title 23 California Code of Regulations, Section
2510 et seq., and 'designated waste' is as defined in Title 27.
2. The discharge of wastes outside of a waste management unit or portions of a waste
management unit specifically designed for their containment is prohibited.
3. The discharge of solid waste, liquid waste, leachate, lOr waste constituents to surface
waters, ponded water, surface water drainage courses, or groundwater is prohibited.
4. The discharge of liquid or semi-solid waste (i.e., waste containing less than 50
percent solids), except dewatered sewage or water treatment sludge, or on-site
generated leachate or landfill gas condensate, above a composite liner as provided
in §20220(c) of Title 27, is prohibited.
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5. The discharge of solid waste containing free liquid or moisture in excess of the
waste's moisture holding capacity is prohibited.
6. The discharge of waste within loo feet of surface waters is prohibited.
7. The discharge shall not cause the pollution or degradation of groundwater via the
release of waste constituents in either liquid or gaseous phase.
8. The discharge of wastes shall not cause the pollution or degradation of any water
supply.
9. The discharge of wastes which have the potential to reduce or impair the integrity of
. containment structures or which, if commingled with other wastes in the waste
management unit, could produce violent rèaction, heat or pressure, fire or explosion,
toxic by-products, or reaction products, which, in turn:
a. require a higher level of containment than provided by the unit; or
b. are 'restricted hazardous wastes'; or
c. impair the integrity of containment structures;
is prohibited.
10. The discharge shall not cause any increase in the concentration of waste constituents
in soil or other geologic materials outside of the waste management unit if such
waste constituents could migrate to waters of the State and cause a condition of
degradation, pollution, or nuisance.
11. The discharge of any additional waste to a waste management unit after it is closed
is prohibited.
B. DISCHARGE SPECIFICATIONS
1. Wastes shall only be discharged to either:
a. that portion of an existing waste management unit that was permitted and/or
received wastes prior to the Federal Deadline of 9 October 1993; or
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b. to an area equipped with a composite liner containment system that meets
the requirements for both liners and leachate collection and removal systems
specified below.
2. A minimum separation of 5 feet shall be maintained between the base of the wastes
and the highest anticipated elevation of underlying groundwater, including the
capillary fringe.
3. Water used for facility maintenance shall be limited to the minimum amount
necessary for dust control, construction, and, after closure, to the minimum amount
necessary to irrigate cover vegetation or for other uses approved by the Executive
Officer.
4. Leachate collected from the landfill shall be discharged to an appropriate waste
management unit in accordance with Title 27 and in a manner consistent with the
waste classification of the leachate, or discharged on-site to a waste management.
unit or portion of a waste management unit that has a composite liner and a leachate
collection and removal system.
5. Gas condensate collected from any landfill gas control systems installed at the waste
management unit and proposed for discharge to land, shall be discharged to an
appropriate waste management unit in accordance with Title 27 and in a manner
consistent with the waste classification of the condensate, or discharged on-site to a
waste management unit or portion of a waste management unit that has a composite
liner and a leachate collection and removal system.
6. Neither the treatment nor the discharge of wastes shall cause a pollution or nuisance
as defined by the California Water Code, § 13050.
7. The Discharger shall, in a timely manner, remove and relocate any wastes
discharged at this facility in violation of this Order.
C. FACILITY SPECIFICATIONS
1. Waste management units and containment structures shall be designed and
. constructed to limit, to the greatest extent possible, ponding, infiltration, inundation,
erosion, slope failure, washout, and overtopping as a result of a 1oo-year, 24-hour
precipitation event.
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2. Precipitation and drainage control systems shall be designed, constructed, and
maintained to accommodate the anticipated volume of precipitation and peak flows
from surface runoff under the lOG-year, 24-hour precipitation conditions.
3. Cover materials shall be graded to divert precipitation from the waste management
unit, to prevent the ponding of surface water over wastes, and to resist erosion as a
result of a lOO-year, 24-hour precipitation event.
4. Interim cover placed over wastes discharged to any waste management unit shall be
designed and constructed to minimize the percolation of liquids through wastes.
5. Waste management units or portions of waste management units shall be designed,
constructed, and operated in compliance with precipitation and flood conditions
contained in the Standard Provisions and Reporting Requirements referenced in
Provision F.5 below.
6. All drainage control systems shall be designed and constructed to prevent the
ponding of water above wastes.
7. Surface drainage from tributary areas and internal site drainage from surface or
subsurface sources shall not contact or percolate through wastes.
8. Areas with slopes greater than ten percent, surface drainage courses, and areas
subject to erosion by wind or water shall be designed and constructed to prevent
such erosion. .
9. An earthen cover shall be maintained over all but the active disposal area of the
waste management unit. This area shall be properly graded and drained to prevent
ponding and infiltration. The cover over the waste management unit shall be
approved by the California Integrated Waste Management Board in accordance with
§20680 of Title 27. Any alternative daily cover material shall be approved by the
Executive Officer to ensure that it will be protective of water quality.
10. The Discharger shall submit information that demonstrates for Executive Officer
review and approval, that the waste management unites) will not restrict the flow of
the l00-year flood, reduce the temporary water storage capacity of the floodplain, or
result in washout of solid waste so as to pose a hazard to human health or"the
environment.
11. the Discharger shall submit information that demonstrates for Executive Officer
review and approval, that flood protection devices (e.g., floodwalls, dikes) are
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installed at the waste management unit and will be maintained to prevent inundation
or washout and divert surface drainage from the unit for floods with a lOO-year
return period. If the flood protection devices have not been installed, the Discharger
shall submit a work plan for their installation to the Executive Officer for review
and approval.
12. The Discharger shall submit an Interim Drainage Plan demonstrating adequate
design, construction, and operation of a facility liquid management system for
protection from stonn events, including precipitation and drainage controls,
consistent with the development of a closure and post-closure maintenance plan and
Facility Specifications e.1 through e.g.
13. The Discharger shall immediately notify the Board of any flooding, unpermitted
offsite discharge, equipment failure, slope failure, or other change in site conditions,
which could impair the integrity of waste or leachate containment facilities or
precipitation and drainage control structures.
14. The Discharger shall appropriately revise the Storm Water Pollution and Prevention
Plan and Interim Drainage Plan to reflect site design modifications prior to the
discharge of wastes to a newly constructed waste management unit or to an
expansion of an existing waste management unit.
D. CONSTRUCTION SPECIFICATIONS
1. Materials used to construct liners shall have appropriate physical and chemical
properties to ensure containment of discharged wastes over the operating life,
closure, and post-closure maintenance period of a waste management unit or portion
of a waste management unit.
2. Materials used to construct the leachate collection and removal system shall have
appropriate physical and chemical properties to ensure the required transmission .of
leachate over the operating life, closure, and post-closure maintenance period of a
waste management unit or portion of a waste management unit:
3. The Discharger shall submit for Executive Officer review and approval prior to
construction, design plans and specifications for new waste management units and
expansions of existing waste management units that include the following:
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CQUNTY OF KERN
FOR OPERA nON AND CONSTRUCTION
ARVIN SANITARY LANDFllL
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a) A demonstration that new waste management units and expansions of
existing waste management units shall not be located in a wetland, unless
demonstrated that:
(1) There is no practical alternative;
(2) Steps have been taken to achieve no net loss of wetlands, pursuant
to §404 of the Federal Clean Water Act; and
(3) The landfill will not do any of the following:
(a) Degrade the wetland;
(b) Jeopardize threatened or endangered species or produce
adverse modification of a critical habitat protected under
the Endangered Species Act of 1973; or
(c) Violate any requirement under the Marine Protection,
Research, and Sanctuaries Act of 1972 for the protection
of a marine sanctuary.
b) A Construction Quality Assurance Plan demonstrating that the proposed
waste management unit will be constructed according to the approved
specifications and plans, and shall provide quality control on the materials
and construction practices used in construction and prevent the use of
inferior products and/or materials which do not meet the approved design
plans or specifications; and
c) A geotechnical evaluation of the area soils, evaluating their use as the
foundation layer; and
d) A vadose zone monitoring system that meets the criteria contained in
§20415 (d) of Title 27, and is installed beneath the composite liner system.
4. If clay layers are used in a liner system, then the hydraulic conductivities for the
clay detennined through laboratory methods shall be confirmed by a Sealed Double-
Ring Infiltrometer (SDRI) field test, or an equivalent field test method approved by
the Executive Officer, of a test pad constructed in a manner duplicating the clay
liner construction of the waste management unit or expansion portion of the waste
management unit. Test pad construction methods, quality assurance/quality control
procedures, and testing shall be in accordance with a construction quality assurance
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I
-,
plan approved by the Executive Officer and shall be sufficient to ensure that all
parts of the liner meet the hydraulic conductivity and compaction requirements.
5. Both the bottom liner and side slope liner of all new waste management units and
expansion areas of existing waste management units shall be constructed in
accordance with one of the following composite liner designs:
a) The prescriptive standard design which consists of a lower compacted soil
layer that is a minimum of two feet thick with a hydraulic conductivity of 1
x 10-7 cm/sec or less and a minimum relative compaction of 90%.
Immediately above the compacted soil layer, and in direct and uniform
contact with the soil layer, shall be a synthetic flexible membrane
component that shall be at least 40-mil thick (or at least 60-mil thick if
composed of high density polyethylene [HDPE]); or
b) An engineered alternative liner system that is comprised,. in ascending order,
of the following:
1) A twelve-inch thick engineered soil foundation layer that shall be
constructed of select fine-grained soil materials which shall be
compacted in lifts of six inches or less to 90% of maximum dry density
and at 0% to 4% wet of optimum moisture content, in accordance with
the approved construction quality assurance plan, and shall be
compacted to attain a hydraulic conductivity of 1 x 10-5 cm/sec or less,
or meet the following gradation criteria:
(a) A maximum size of 3/8-inch;
(b) At least 30% of the material, by dry weight, passing the No. 200
U.S. Standard sieve; and
(c) A gradation series (i.e., well graded) that is amenable to
compaction.
2) A nonwoven bottom geotextile, which may be part of the geosynthetic
clay layer (GCL).
3) A GCL that shall exhibit appropriate strength characteristics (hydrated)
to accommodate stresses associated with specific landfill design
parameters, with particular attention to interface, long-term creep
shear, and bearing capacity.
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4) A 60-mil thick synthetic flexible membrane of HDPE; or
c) An engineered alternative liner system as provided by §20080(b) and (c) of
Title 27, which must be a composite liner that meets the performance goals
of the prescriptive design in option a) above, and has been approved by the
Executive Officer.
6. If the Discharger proposes to construct a liner system in which a GCL is placed on
top of the subgrade, the subgrade for the bottom and the side slopes of the waste
management unit shall be prepared in an appropriate manner using accepted
engineering and construction methods so as to provide a smooth surface that is free
from rocks, sticks, or other debris that could damage or otherwise limit the
performance of the GeL.
7. Hydraulic conductivities of liner materials shall be determined by laboratory tests
using solutions with similar properties as the fluids that will be contained.
Hydraulic conductivities of cover materials shall be determined by laboratory tests
using water. Hydraulic conductivities determined through laboratory methods shall
be confIrmed by field testing in accordance with the approved Construction Quality
Assurance Plan. Construction methods and quality assurance procedures shall be
sufficient to ensure that all parts of the liner and cap meet the hydraulic conductivity
and compaction requirements.
8. All new waste management units or lateral expansions of existing waste
management units shall have a blanket-type leachate collection and removal system.
The leachate collection and removal system shall be designed, constructed,
maintained, and operated to collect twice the anticipated daily volume of leachate
generated by the waste management unit. The leachate collection and removal
system shall be designed and operated to maintain less than a 30 cm depth of
leachate over the liner.
9. Leachate generated by any waste management unit or portion of a waste
management unit shall not exceed 85% of the design capacity of the leachate sump.
If leachate generation exceeds this value, or if the depth of fluid in the leachate
collection and removal system exceeds 30 cm, or if the monitoring reveals
substantial or progressive increases above the design anticipated daily volume of
leachate generated by the waste management unit or portion of the waste
management unit, the Discharger shall immediately notify the Board in writing
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within seven days. The notification shall include a timetable for remedial or
corrective action necessary to reduce leachate próduction,
10. Following the completion of construction of a waste management unit or portion of
a waste management unit, and prior to discharge onto the newly constructed liner
system, a construction report shall be submitted for Executive Officer review and
approval. The report shall be certified by a registered civil engineer or a certified
engineering geologist. It shall contain sufficient information and test results to
verify that construction was in accordance with the design plans and specifications,
and with the prescriptive standards and performance goals of Title 27.
The report for the waste management unit shall include as a minimum, but not be
limited to, the following:
a) Test results on the chemical and geotechnical properties of materials used in
the containment structure, as specified in these waste discharge
requirements.
b) Test results on the permeability of the clay liner if the prescriptive standard
clay layer is used in the liner system.
c) Test results on the compatibility of the waste with the liner system.
d) Construction quality assurance and quality contÍ'ol procedures and results for
all aspects of liner construction.
e) A geologic map and geologic cross-sections which show mappable
lithologic units and structural features in relation to the waste management
unit.
11. Partial or final closure of new, existing, or portions of a classified waste
management unit shall be in compliance with the applicable provisions of Title 27.
Classified waste management units or portions of waste management units shall be
closed in accordance with a closure and post-closure maintenance plan approved by ,
the Executive Officer, and closure waste discharge requirements adopted by the
Board. In addition to the applicable provisions of Title 27, the closure and/or the
post-closure maintenance plan shall include the following:
a) A final cover design with a minimum I-foot thick erosion resistant layer;
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b) An estimate of the largest area of the waste management unites) ever
requiring a final cover at any time during the active life of the unites);
c) An estimate of the maximum inventory of wastes ever on-site over the
active life of the waste management facility;
d) Initiation of closure activities within 30 days of final waste receipt, or within
Qt¡e year of receipt of most recent waste if additional capacity remains;
e) Completion of closure activities within 180 days of the beginning of-closure
activities;
t) Notifying the Executive Officer that the deed to the landfill facility property,
or some other instrument that is normally examined during a title search, has
been recorded and a copy placed in the operating record. The notation on
the deed shall in perpetuity notify any potential purchaser of the property
that the land has been used as a landfill facility and that use of the land is
restricted to the planned uses described in the post -closure maintenance
plan.
12. The Discharger shall notify the Executive Officer that a closure and post-closure
maintenance plan has been prepared in accordance with Construction Specification
D. 11 and placed in the operating record by the date of initial receipt of waste at any
new waste management unit or lateral expansion of any existing waste management
unit.
13. Closure shall not proceed in the absence of closure waste discharge requirements.
E. DETECTION MONITORING SPECIFICATIONS
1. The Discharger shall submit a groundwater detection monitoring report
demonstrating compliance with Title 27 for the existing waste management unit and
any waste management unit expansion. The program is subject to approval by the
Executive Officer.
2. The Discharger shall submit a Sample Collection and Analysis Plan, which includes
quality assurance/quality control standards and the analysis of unfiltered samples,
for approval by the Executive Officer.
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3. The Discharger shall comply with the detection monitoring provisions of Title 27
for groundwater, surface water, and the unsaturated zone, and in accordance with
Monitoring and Reporting Program No. _. Detection monitoring for a new
waste management unit or an expansion of an existing waste management unit shall
be installed, operational, and the fIrst round of samples collected prior to the
discharge of wastes.
4. The Water Quality Protection Standard, as defIned in §20390 of Title 27, shall
consist of constituents of concern, their concentration limits, the point of
compliance, and all water quality monitoring points. Constituents of concern shall
include all waste constituents, their reaction products, and hazardous constituents
that are reasonably expected to be in or derived from waste contained in the landfIll.
Concentration limits shall consist of the background concentrations of each
constituent of concern established in accordance with a data analysis method that
meets the applicable criteria of §20415(e) of Title 27.
5. The Discharger shall comply with the Water Quality Protection Standard which is
specifIed in Monitoring and Reporting Program No. and the Standard
Provisions and Reporting Requirements, dated August 1997, which are attached to
and made part of this order.
6. Organic compounds that are not naturally occurring have a background value of
ze!o. The Water Quality Protection Standard for volatile organic compounds shall
be taken as the detection limit of the analytical method used (i.e., USEP A Methods
8260 and 8270). Evidence of exceeding the standard occurs when the constituent is
detected by the appropriate method.
7. The concentrations of the constituents of concern in waters passing the Point of
Compliance shall not exceed the concentration limits established pursuant to
Monitoring and Reporting Program No._.
8. For each monitoring event, the Discharger shall determine whether the landfIll is in
compliance with the Water Quality Protection Standard using procedures specifIed
in Monitoring and Reporting Program No._ and §20415(e) of Title 27.
9. Methane and other landfIll gases shall be adequately vented, removed from the
waste management unit, or otherwise controlled to prevent adverse health effects,
nuisance conditions, or the impairment of the benefIcial uses of surface water or
groundwater due to migration through the vadose (unsaturated) zone.
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F. PROVISIONS
1. The Discharger shall maintain legible records of the volume and type of each waste
discharged at each waste management unit or portion of a waste management unit,
and the manner and location of the discharge. The Discharger shall maintain such
records until the beginning of the post-closure maintenance period. These records
shall be available for review by representatives of the Board and of the State Water
Resources Control Board at any time during normal business hours. At the
beginning of the post-closure maintenance period, copies of these records shall be
properly stored for future reference.
2. The Discharger shall maintain a copy of this Order at the facility and make it
avaiiable at all times to facility operating personnel, who shall be familiar with its
contents, and to regulatory agency personnel upon request.
3. The Discharger shall comply with all applicable provisions of Title 27 that are not
specifically referred to in this Order.
4. The Discharger shall comply with Monitoring and Reporting Program No. _,
which is incorporated into and made part of this Order. This compliance includes,
but is not limited to monitoring of: the maintenance of waste containment facilities,
precipitation and drainage controls, the groundwater monitoring system, leachate
from the waste management unit(s), and the vadose zone and surface water
monitoring systems throughout the active life of the waste management unit and the
post-closure maintenance period.
5. The Discharger shall comply with the applicable portions of the Standard Provisions
and Reporting Requirements dated August 1997, which are hereby incorporated into
this Order.
6. A violation of any of the applicable portions of the Standard Provisions and
Reporting Requirements or the Monitoring and Reporting Program is a violation of
these waste discharge requirements.
7. Monitoring wells, piezometers, and other measurement, sampling, and analytical
devices shall be operated and maintained so that they perform to design
specifications throughout the life of the monitoring program.
8. The Discharger or persons employed by the Discharger shall comply with all notice
and reporting requirements of the State Department of Water Resources with regard
to the construction, alteration, destruction, or abandonment of all monitoring wells
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used for compliance with this Order as required by § 13750 through § 13755 of the
California Water Code.
9. The Discharger shall maintain waste containment facilities and precipitation and
drainage controls. and shall continue to monitor groundwater in accordance with
Monitoring and Reporting Program No. throughout the active life of the
waste management unit and the post-closure maintenance period.
10. The Discharger shall submit documentation to the Executive Officer that all persons
who own or reside on the land that directly overlies any portion of the contaminant
plume that has migrated off-site have been notified.
11. The Discharger shall have the continuing responsibility to assure the protection of
the beneficial uses of ground and surface waters from gases and leachate generated
by discharged waste during the active life, closure and post-closure maintenance
period of the waste management unit( s) and during the subsequent use of the
property for other purposes.
12. In the event of any change in control or ownership of the land or waste discharge
facilities described herein, the Discharger shall notify the succeeding owner or .
operator of the existence of this Order by letter, a copy of which shall be
immediatelý forwarded to this office.
13. To assume operation under this Order, the succeeding owner or operator must apply
in writing to the Board requesting transfer of the Order within 14 days of assuming
ownership or operation of this facility. The request must contain the requesting
entity's full legal name, the State of incorporation if a corporation, the name and
address and telephone number of the persons responsible for contact with the Board,
and a statement. The statement shall comply with the signatory requirements
contained in Reporting Requirements No.5 of the Standard Provisions and
Reporting Requirements and state that the new owner or operator assumes full
responsibility for compliance with this Order. Failure to submit the request shall be
considered a discharge without requirements, a violation of the California Water
Code. Transfer shall be approved or disapproved by the Board.
14. The Discharger shall notify the Bóard in writing of any proposed change in
ownership or responsibility for construction or operation of the waste management
unit. The Discharger shall also notify the Board of a material change in the
character, location or volume of the waste discharge and of any proposed
expansions or closure plans. This notification shall be given 90 days prior to the
effective date of the change and shall be accompanied by an amended Report of
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Waste Discharge and any technical documents that are needed to demonstrate
continued compliance with these waste discharge requirements.
15.
The Discharger shall, by 30 April of each year, submit for approval by the
Executive Officer, plans with detailed cost estimates and a demonstration of
assurances of financial responsibility for initiating and completing corrective action
for all known and reasonably foreseeable releases from the waste management unit.
The Discharger shall provide the assurances of financial responsibility to the .,,, '..
California Integrated Waste Management Board as required by Title 27 CCR,
Division 2, Subdivision 1, Chapter 6. The assurances of financial responsibility
shall provide that funds for corrective action shall be available to the Regional
Board upon the issuance of any order under California Water Code, Division 7,
Chapter 5. The Discharger shall adjust the cost annually to account for inflation and
any changes in facility design, construction, or operation.
'.
. ,
16. The Discharger shall, by 30 April of each year, submit for approval by the
Executive Officer, a demonstration of assurances of financial responsibility to
ensure closure and post-closure maintenance of each waste management unit in
accordance with its approved closure and post-closure maintenance plans. The
Discharger shall provide the assurances of financial responsibility to the California
Integrated Waste Management Board as required by Title 27 CCR, Division 2,
Subdivision 1, Chapter 6. The assurances of financial responsibility shall provide
that funds for closure and post-closure maintenance with respect to water quality
shall be available to the Regional Board upon the issuance of any order under
California Water Code, Division 7, Chapter 5. The Discharger shall adjust the cost
annually to account for inflation and any changes in facility design, construction, or
operation.
17. IT a single mechanism of financial assurance is used for both corrective action and
closure and post-closure maintenance, the financial assurance must be sufficient for
both requirements.
18. The Board will review this Order periodically and will revise these waste discharge
requirements when necessary.
19. The Discharger shall complete the tasks contained in these waste discharge
requirements in accordance with the following time schedule:
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Task
Compliance Date
(a) Submit for Executive Officer
review and approval, a
demonstration that the waste
management unit will not restrict
the lOO-year flood, reduce the
storage:capacity of the floodplain,
or result in washout of solid waste.
(Facility Specification C.1O)
30 April 2000
(b) Submit Interim Drainage Plan
(Facility Specification C.12)
30 April 2000
(c) Submit for Executive Officer
review and approval, design
plans and specifications for new
waste management units
and expansions of existing
waste management units.
(Construction Specification D.3)
Prior to Construction
(d) Submit for Executive Officer
review and approval, a revised
closure and post-closure
maintenance plan.
(Construction Specification D.II)
30 April 2000
(e) Submit Sample Collection and
Analysis Plan
(Detection Monitoring
Specification E.2)
30 April 2000
(f) Submit documentation to the
Executive Officer that all persons
have been notified that own or
reside on land overlying any
portion of a contaminant plume.
(Provision F. 10)
30 April 2000
DRAFT
WASTE DISCHARGE REQUIREMENTS
COUNTY OF KERN
. FOR OPERATION AND CONSTRUCTION
ARVIN SANITARY LANDFll.L
KERN COUNTY
-24-
I, GARY M. CARLTON, Executive Officer, do hereby certify that the foregoing is a full, true,
and correct copy of an Order adopted by the California Regional Water Quality Control Board,
Central Valley Region, on
" } ~
GARY M. CARLTON, Executive Officer
RCSIREH: 11120/99
Attachments
DRAFT
CALIFORNIA REGIONAL WATER QUALITY CONTROL BOARD
CENTRAL V ALLEY REGION
MONITORING AND REPORTING PROGRAM NO.
. FOR
COUNTY OF KERN
KERN COUNTY WASTE MANAGEMENT DEPARTMENT
FOR
OPERATION AND CONSTRUCTION
ARVIN SANITARY LANDFILL
KERN COUNTY
Compliance with this Monitoring and Reporting Program, with Title 27, California Code of
Regulations, Section 20005, et seq. (hereafter Title 27), and with the Standard Provisions and
Reporting Requirements dated August 1997, is ordered by Waste Discharge Requirements Order
No. 97-
Failure to comply with this Program, or with the Standard Provisions and Reporting
Requirements, constitutes noncompliance with the Waste Discharge Requirements and
with the California Water Code, which can result in the imposition of civil monetary
liability.
A. REQUIRED MONITORING REPORTS
Report Due
1. Groundwater Monitoring (Section D.l) See Table I
2. Annual Monitoring Summary Report Annually
(Standard Provisions and Reporting Requirements)
3. Unsaturated Zone Monitoring (Section D.2) See Table II
4. Leachate Monitoring (Section D.3) See Table ill
5. Surface Water Monitoring (Section D.4) See Table IV
6. Facility Monitoring (Section D.5) As necessary
7. Response to a Release As necessary
(Standard Provisions and Reporting Requirements)
B. REPORTING
The Discharger shall report monitoring data and information as required in this Monitoring
and Reporting Program and as required in the Standard Provisions and Reporting
Requirements. Reports which do not comply with the required format will be REJECTED
and the Discharger shall be deemed to be in noncompliance with the waste discharge
requirements. In reporting the monitoring data required by this program, the Discharger
DRAFT
MONITORING AND REPORTING PROGRAM
ÇOUNTY OF KERN
KERN COUNTY WASTE MANAGEMENT DEPARTMENT
FOR OPERA nON AND CONSTRUCTION
ARVIN SANrr AR Y LANDFill...
KERN COUNTY
2'
shall arrange the data in tabular form so that the date, the constituents, the concentrations,
and the units are readily discernible. Data shall also be submitted in a digital database
format acceptable to the Executive Officer. The data shall be summarized in such a manner
so as to illustrate clearly the compliance with waste discharge requirements or the lack
thereof. A short discussion of the monitoring results, including notations of any water
quality violations, shall precede the tabular summaries.
Field and laboratory tests shall be reported in each monitoring report. Monthly, quarterly,
semiannual, and annual monitoring reports shall be submitted to Board staff in accordance
with the following schedule for the calendar period in which samples were taken or
observations made. The results of any monitoring done more frequently than required at
the locations specified herein shall be reported to Board staff.
Sampling Reporting
Frequency Frequency
Monthly Quarterly
Quarterly Quarterly
Reporting
Periods End
Last Day of Month
31 March
30 June
30 September
31 December
Semi-Annually
Semi-Annually
30 June
31 December
Annually
AnnuaIiy
31 December
Report
Date Due
by Quarterly Schedule
31 May
31 August
30 November
28 February
31 August
28 February
30 April
The annual report to be submitted to Board staff shall contain both tabular and graphical
summaries of the monitoring data obtained during the previous twelve months, so as to
show historical trends at each well. The report shall include a discussion of compliance
with the waste discharge requirements and the water quality protection standard.
A transmittal letter explaining the essential points shall accompany each report. At a
minimum, the transmittal letter shall identify any violations found since the last report was
submitted, and if the violations were corrected. If no violations have occurred since the last
submittal, this shall be stated in the transmittal letter. The transmittal letter shall also state
that a discussion of any violations found since the last report was submitted, and a
description of the actions taken or planned for correcting those violations, including any
references to previously submitted time schedules, is contained in the accompanying report.
DRAFT
MONITORING AND REPORTING PROGRAM
. COUNTY OF KERN
KERN COUNTY WASTE MANAGEMENT DEPARTMENT
FOR OPERA nON AND CONSTRUCTION
ARVIN SANITARY LANDFlLL
KERN COUNTY
3
C. WATER QUALITY PROTECTION STANDARD AND COMPLIANCE
PERIOD
1. Water Quality Protection Standard Report
, .
For each waste management unit, the water quality protection standard consists of a
list of constituents of concern and monitoring parameters, concentration limits for
each constituent of concern, the point of compliance, and all monitoring points.
The Discharger shall submit a proposed water quality protection standard for review
and approval in accordance with a Cleanup and Abatement Order which will be
adopted following adoption of this Order. The Executive Officer shall review the
data and the proposed water quality protection standard in determining the final water
quality protection standard for each monitored medium.
The report shall:
a) Identify all distinct bodies of surface and ground water that could be affected
in the event of a release from a waste management unit or portion of a waste
management unit. This list shall include at least the uppermost aquifer and any
permanent or ephemeral zones of perched groundwater underlying the waste
management facility.
b) Include a map showing the monitoring points and background monitoring points
for the surface, saturated, and unsaturated zones and showing the point of
compliance in accordance with §20405 of Title 27.
c) Evaluate the perennial direction(s) of groundwater movement within the
uppermost groùndwater zone(s).
If subsequent sampling of the background monitoring point(s) indicates significant
water quality changes due to either seasonal fluctuations or other reasons unrelated to
waste management activities at the site, the Discharger may request modification of
the water quality protection standard.
2. C<)llstituents of Concern
The constituents of concern are the waste constituents, reaction products, and
hazardous constituents that are reasonably expected to be in or derived from waste
contained in the waste management unit. The constituents of concern for all waste
management units at the facility are those listed in Table VI. The Discharger shall
monitor all constituents of concern in Table VI every five years, or more frequently as
required in accordance with a Corrective Action Program.
a. Monitoring Parameters
Monitoring parameters are the waste constituents, reaction products, hazardous
constituents, and physical parameters that provide a reliable indication of a
release from a waste management unit. The monitoring parameters for all waste
DRAFT
MONITORING AND REPORTING PROGRAM
.COUNTY OF KERN
KERN COUNTY WASTE MANAGEMENT DEPARTMENT
FOR OPERATION AND CONSTRUCTION
ARVIN SANITARY LANDFILL .
KERN COUNTY
4
management units are those listed in Tables I through V for the specified
monitored medium.
3. Concentration Limits
The concentration limits for each constituent of concern are as follows:
a. for naturally occurring constituents of concern, the çoncentration limit shall be
the calculated statistical concentration limit.
b. for anthropogenic (not naturally occurring) constituents, which have no natural
and, therefore, no background values, the concentration limit (water quality
protection standard) shall be the detection limit of the analytical methodes) used.
The Discharger shall use the data analysis method approved by the Executive Officer,
and the groundwater quality. data obtained from the detection monitoring program to
update the concentration limits annually in accordance with §20415(e)(10)(B) of Title
27. The Discharger shall submit the updated concentration limits to the Executive
Officer for review and approval in the annual monitoring report. The Discharger shall
be allowed to make a demonstration to establish concentration limits based upon
reference to historical data in accordance with §20415(e)(10)(A) of Title 27. The
demonstration is subject to the statistical analysis criteria contained in §20415(e) of
Title 27, and shall be reviewed and approved by the Executive Officer. If the
demonstation is approved, the Discharger shall submit the historical concentration
limits to the Executive Officer for reveiw and approval in the annual monitoring
report. For successive annual monitoring reports having the same constituent
concentration limits as the previous year, the Discharger shall include a demonstration
to justify the unchanged values. Any annual demonstrations shall be reveiwed and
approved by the Executive Officer.
4. Point of Compliance
The point of compliance for each waste management unit is the vertical surface
located at the hydraulically downgradient limit of the waste management unit that
extends through the uppermost aquifer underlying the unit.
a. Monitoring Points
All downgradient wells established for groundwater monitoring shall constitute
the monitoring points for the groundwater quality protection standard. All
approved monitoring wells, unsaturated zone monitoring devices, leachate, and
surface water monitoring points shall be sampled and analyzed for monitoring
parameters and constituents of concern as indicated and listed in Tables I
through IV.
5. Compliance Period
DRAFT
MONITORING AND REPORTING PROGRAM
,COUNTY OF KERN
KERN COUNTY WASTE MANAGEMENT DEPARTMENT
FOR OPERATION AND CONSTRUCTION
ARVIN SANITARY LANDFILL
KERN COUNTY
5
The compliance period for each waste management unit shall be the number of years
equal to the active life of the waste management unit plus the closure period. The
compliance period is the minimum period during which the Discharger shall conduct
a water quality monitoring program subsequent to a release from the unit. The
compliance period shall begin anew each time the Discharger initiates an evaluation
monitoring program.
D. MONITORING
The Discharger shall comply with the detection monitoring provisions of Title 27 for
groundwater, surface water, and the unsaturated zone, in accordance with Detection
Monitoring Specifications E.2 and E.3 of waste discharger requirements Order No.
Detection monitoring for a new facility, a new waste management unit, or an expansion of
3Il existing waste management unit shall be installed, operational, and the first round of
samples collected prior to the discharge of wastes. All monitoring shall be conducted in
:accordance with a Sample Collection and Analysis Plan, which includes quality
assurance/quality control standards and the analysis of unfiltered samples, that are
:acceptable to the Executive Officer.
Method detection limits and practical quantitation limits shall be reported. All peaks shall
be reported, including those which cannot be quantified and/or specifically identified.
Metals shall be analyzed in accordance with the methods listed in Table VI.
The Discharger may use alternative analytical test methods, including new EP A approved
methods, provided the methods have method detection limits equal to or lower than the
analytical methods specified in this Monitoring and Reporting Program.
1. Groundwater
The Discharger shall install and operate a groundwater detection monitoring system
that complies with the applicable provisions of §20415 and §20420 of Title 27 in
accordance with a Detection Monitoring Plan approved by the Executive Officer. The
Discharger shall collect, preserve, and transport groundwater samples in accordance
with the approved Sample Collection and Analysis Plan.
The Discharger shall detennine groundwater flow rate and direction in the uppermost
aquifer and in any zones of perched water and in any additional zone of saturation
monitored pursuant to this Monitoring and Reporting Program, and report the results
semi-annually, including the times of highest and lowest elevations of the water levels
in the wells. The groundwater elevation in each well shall be measured prior to
purging, each time the well is sampled. Groundwater elevations in wells that monitor
the same waste management facility shall be measured within a period of time short
enough to avoid temporal variations in flow which could preclude accurate
groundwater flow rate and direction determination. Additionally, hydrographs of
each well shall be prepared showing the elevation of groundwater with respect to the
elevations of the top and b9ttom of the screened interval and the elevation of the
pump intake. Hydrographs of each well shall be prepared quarterly and submitted
annually. .
DRAFT
MONITORING AND REPORTING PROGRAM
·COUNTY OF KERN
KERN COUNTY WASTE MANAGEMENT DEPARTMENT
FOR OPERATION AND CONSTRUCTION
ARVIN SANITARY LANDFILL
KERN COUNTY
6
Groundwater samples shall be collected from the point of compliance wells,
background wells, and any additional wells added as part of the approved
groundwater monitoring system. Samples shall be collected and analyzed for the
monitoring parameters in accordance with the methods and frequency specified in
Table I. All monitoring parameters shall be graphed so as to show historical trends at
each well. The monitoring parameters shall also be evaluated with regards to the
. cation/anion balance, and the results shall be graphically presented using a Stiff
diagram or a Piper graph. Stiff diagrams or Piper graphs shall be prepared for all
groundwater monitoring wells every five years. Samples for the constituents of
concern specified in Table I shall be collected and analyzed in accordance with the
methods listed in Table VI every five years.
2. Unsaturated Zone Monitoring
The Discharger shall install and operate an unsaturated zone detection monitoring
system that complies with the applicable provisions of §20415 and §20420 of Title 27
in accordance with a detection monitoring plan approved by the Executive Officer.
The Discharger shall collect, preserve, and transport samples in accordance with the
quality assurance/quality control standards contained in the approved Sample
Collection and Analysis Plan.
Unsaturated zone samples shall be collected from the monitoring devices and
background monitoring devices of the approved unsaturated zone monitoring system.
Samples shall be collected and analyzed for the listed constituents in accordance with
the methods and frequency specified in Table n. All monitoring parameters shall be
graphed so as to show historical trends at each monitoring point. Samples for the
constituents of concern specified in Table n shall be collected and analyzed in
accordance with the methods listed in Table VI every five years.
The pan lysimeters shall be checked monthly for liquid and monitoring shall include
the volume of liquid recovered. Unsaturated zone monitoring reports shall be
included with the corresponding semi-annual groundwater monitoring and shall
include an evaluation of potential impacts of the facility on the unsaturated zone and
compliance with the water quality protection standard.
3. Leachate Monitoring
All waste management unit leachate collection and removal system sumps shall be
inspected weekly for leachate generation. Upon detection of leachate in a previously
dry leachate collection and removal system, leachate shall be sampled and analyzed
for the constituents listed in Table m. Leachate monitoring shall be conducted as
specified in Table ill in accordance with the methods listed in Table VI. The
constituents of concern list shall include all constituents listed in Table VI. The
quantity of leachate pumped from each sump shall be measured continuously and
reported as Leachate Flow Rate (in gallons/day).
DRAFT
MONITORING AND REPORTING PROGRAM
·COUNTY OF KERN
KERN COUNTY WASTE MANAGEMENT DEPARTMENT
FOR OPERATION AND CONSTRUCTION
ARVIN SANITARY LANDFILL
KERN COUNTY
7
Upon detection of any leachate seeps at the unlined waste management unit, the
leachate shall be sampled and analyzed for the constituents listed in Table ill in
accordance with the methods listed in Table VI. The quantity of leachate shall be
estimated and reported as Leachate Flow Rate (in gallons/day).
4. Surface Water Monitoring
The Discharger shall install and operate a surface water detection monitoring system
where appropriate that complies with the applicable provisions of §20415 and §20420
of Title 27 and has been approved by the Executive Officer.
For all monitoring points and background monitoring points assigned to surface water
detection monitoring, samples shall be collected and analyzed for the monitoring
parameters in accordance with the methods and frequency specified in Table IV. All
surface water monitoring samples shall be collected and analyz~d for the constituents
of concern specified in Table IV every five years. All monitoring parameters shall be
graphed so as to show historical trends at each sample location.
5. Facility Monitoring
a. Faci~ty Inspection
Annually, prior to the anticipated rainy season, but no later than 30 September,
the Discharger shall conduct an inspection of the facility. The inspection shall
assess damage to the drainage control system, groundwater monitoring
equipment (including wells, etc.), and shall include the Standard Observations
defined in the Standard Provisions and Reporting Requirements (Definition 24).
Any necessary construction, maintenance, or repairs shall be completed by 31
October. By 15 November of each year, the Discharger shall submit an annual
report describing the results of the inspection and the repair measures
implemented.
b. Storm Events
The Discharger shall inspect all precipitation, diversion, and drainage facilities
for damage within 7 days following major storm events. Necessary repairs shall
be completed within 30 days of the inspection. The Discharger shall report any
damage and subsequent repairs within 45 days of completion of the repairs.
The Discharger shall implement the above monitoring program on the effective date of this
Program.
Ordered by:
GARY M. CARLTON, Executive Officer
DRAFT
MONITORING AND REPORTING PROGRAM
·COUNTY OF KERN
KERN COUNTY WASTE MANAGEMENT DEPARTMENT
FOR OPERATION AND CONSTRUCTION
ARVIN SANITARY LANDFILL
KERN COUNTY
8
RCS
DRAFT
(Date)
MONITORING AND REPORTING PROGRAM
.COUNTY OF KERN
KERN COUNTY WASTE MANAGEMENT DEPARTMENT
FOR OPERATION AND CONSTRUCTION
ARVIN SANITARY LANDFllL
KERN COUNTY
9
TABLE I
GROUNDWATER DETECTION MONITORING PROGRAM
Parameter
Field Parameters
Groundwater Elevation
Temperature
Specific Conductance
pH
Turbidity
Monitoring Parameters
Total Dissolved Solids (IDS)
Chloride
Carbonate
Bicarbonate
Nitrate - Nitrogen
Sulfate
Calcium
Magnesium
Potassium
Sodium
Volatile Organic Compounds
(USEP A Method 8260, see Table' V)
Constituents of Concern (see Table VI)
Total Organic Carbon
Inorganics (dissolved)
V olatile Organic Compounds
(USEPA Method 8260, extended list)
Semi-Volatile Organic Compounds
(USEPA Method 8270)
Chlorophenoxy Herbicides
(USEPA Method 8150)
Organophosphorus Compounds
(USEP A Method 8141)
Units
Ft. & hundredths, M.S.L.
of
µmhos/cm
pH units
Turbidity units
mgIL
mgIL
mgIL
mgIL
mgIL
mgIL
mg/L
mgIL
mg/L
mgIL
µgIL
mg/L
mg/L
µg/L
µg/L
µgIL
µgIL
DRAFT
Frequencv
Quarterly
Semi-annual
Semi-annual
Semi-annual
Semi-annual
Semi-annual
Semi-annual
Semi-annual
Semi~annual
Semi-annual
Semi-annual
Semi-annual
Semi-annual
Semi-annual
Semi-annual
Semi-annual
5 years
5 years
5 years
5 years
5 years
5 years
MONITORING AND REPORTING PROGRAM
COUNTY OF KERN
KERN COUNTY WASTE MANAGEMENT DEPARTMENT
FOR OPERATION AND CONSTRUCTION
ARVIN SANITARY LANDFILL
KERN COUNTY
10
TABLE II
UNSA TURA TED ZONE DETECTION MONITORING PROGRAM
SOIL-PORE GAS
Parameter
Monitoring Parameters
V olatile Organic Compounds
(USEPA Method TO-14)
Methane
Units
µgIcm3
%
PAN LYSIMETERS (or other vadose zone monitoring device)
Parameter
Field Parameters
Specific Conductance
pH
Monitoring Parameters
Total Dissolved Solids (IDS)
Carbonate
Bicarbonate Alkalinity
Chloride
Sulfate
Nitrate - Nitrogen
Volatile Organic Compounds
(USEP A Method 8260, see Table V)
Constituents of Concern (see Table VI)
Total Organic Carbon
Inorganics (dissolved)
Volatile Organic Compounds
(USEP A Method 8260, extended list)
Semi-Volatile Organic Compounds
(USEP A Method 8270)
Chlorophenoxy Herbicides
(USEP A Method 8150)
Organophosphorus Compounds
(USEP A Method 8141)
Units
µmhos/cm
pH units
mgIL
mgIL
mgIL
mgIL
mgIL
mgIL
µgIL
mgIL
mgIL
µgIL
µgIL
µgIL
µgIL
DRAFT
Frequency
Semi-annual
Quarterly
Frequency
Semi-annual
Semi-annual
Semi-annual
Semi-annual
Semi-annual
Semi-annual
Semi-annual
Semi-annual
Semi-annual
5 years
5 years
5 years
5 years
5 years
5 years
MONITORING AND REPORTING PROGRAM
.COúNTY OF KERN
KERN COUNTY WASTE MANAGEMENT DEPARTMENT
FOR OPERATION AND CONSTRUCTION
ARVIN SANITARY LANDFllL
KERN COUNTY
11
TABLE ill
LEACHA TE DETECTION MONITORING PROGRAM
Parameter Units Frequency
Field Parameters
Total Flow Gallons Monthly
Flow Rate Gallons/Day Monthly
Specific Conductance µmhos/cm Monthly
pH pH units Monthly
Monitoring Parameters
Total Dissolved Solids (IDS) mgIL Quarterly
Carbonate mgIL Quarterly
Bicarbqnate Alkalinity mgIL Quarterly
Chloride mgIL Quarterly
Sulfate mgIL Quarterly
Nitrate - Nitrogen mgIL Quarterly
Volatile Organic Compounds µgIL Quarterly
(USEP A Method 8260, see Table V)
Constituents of Concern (see Table VI)
Total Organic Carbon mgIL 5 years
Inorganics (dissolved) mgIL 5 years
Volatile Organic Compounds µgIL 5 years
(USEPA Method 8260, extended list)
Semi-Volatile Organic Compounds µgIL 5 years
(USEP A Method 8270)
Chlorophenoxy Herbicides µgIL 5 years
(USEPA Method 8150)
Organophosphorus Compounds µgIL 5 years
(USEP A Method 8141)
DRAFT
MONITORING AND REPORTING PROGRAM
.COUNTY OF KERN
KERN COUNTY WASTE MANAGEMENT DEPARTMENT
FOR OPERATION AND CONSTRUCfION
ARVIN SANITARY LANDFILL
KERN COUNTY
12
TABLE IV
SURFACE WATER DETECTION MONITORING PROGRAM
Parameter Units Frequency
Field Parameters
Temperature °C Semi-annual
Specific Conductance µmhos/cm Semi-annual
pH pH units Semi-annual
Turbidity Turbidity units Semi-annual
Monitoring Parameters
Total Dissolved Solids (TDS) mgIL Semi-annual
Carbonate mgIL Semi-annual
Bicarbonate mgIL Semi-annual
Chloride mgIL Semi-annual
Nitrate - Nitrogen mgIL Semi-annual
Sulfate mgIL Semi-annual
Calcium mgIL Semi-annual
Magnesium mgIL Semi-annual
Potassium mgIL Semi-annual
Sodium mgIL Semi-annual
Volatile Organic Compounds µgIL Semi-annual
(USEPA Method 8260, see Table V)
Constituents of Concern (see Table VI)
Total Organic Carbon mgIL 5 years
Inorganics (dissolved) mgIL 5 years
Volatile Organic Compounds µgIL 5 years
(USEPA Method 8260, extended list)
Semi-Volatile Organic Compounds µgIL 5 years
(USEP A Method 8270)
Chlorophenoxy Herbicides µgIL 5 years
(USEPA Method 8150)
Organophosphorus Compounds µgIL 5 years
(USEP A Method 8141)
DRAFT
MONITOR1NG AND REPORTING PROGRAM
COUNTY OF KERN
KERN COUNTY WASTE MANAGEMENT DEPARTMENT
FOR OPERATION AND CONSTRUCTION
ARVIN SANITARY LANDFILL
KERN COUNTY
13
TABLE V
MONITORING PARAMETERS FOR DETECTION MONITORING
Surrogates for Metallic Constituents:
pH
Total Dissolved Solids
Specific Conductivity
Chloride
Sulfate
Nitrate nitrogen
Constituents included in VOC:
USEPA Method 8260
Acetone
Acrylonitrile
Benzene
Bromochloromethane
Bromodichloromethane
Bromoform (Tribromomethane)
Carbon disulfide
Carbon tetrachloride
Chlorobenzene
Chlorodifluoromethane
Chlorofluoromethane
Chloroethane (Ethyl chloride)
Chloroform (Trichloromethane)
Dibromochloromethane (Chlorodibromomethane)
1,2-Dibromo-3-chloropropane (DBCP)
1,2-Dibromoethane (Ethylene dibromide; EDB)
o-Dichlorobenzene (l,2-Dichlorobenzene)
p-Dichlorobenzene (1 ,4-Dichlorobenzene)
Dichlorodifluoromethane (CFC-12)
Dichlorofluoromethane
trans-l,4-Dichloro-2-butene
1, I-Dichloroethane (Ethylidene chloride)
1,2-Dichloroethane (Ethylene dichloride) .
l,l-Dichloroethylene (1,1 -Dichloroethene; Vinylidene chloride)
cis-l,2-Dichloroethylene (cis- 1 ,2-Dichloroethene)
trans-l,2-Dichloroethylene (trans-l ,2-Dichloroethene)
1,2-Dichloropropane (propylene dichloride)
cis-l,3-Dichloropropene
trans- 1,3-Dichloropropene
Ethylbenzene
2-Hexanone (Methyl butyl ketone)
Isopropylbenzene
DRAFT
MONITORING AND REPORTING PROGRAM
COUNTY OF KERN .
KERN COUNTY WASTE MANAGEMENT DEPARTMENT
. FOR OPERATION AND CONSTRUCTION
ARVIN SANITARY LANDFILL
KERN COUNTY
14
TABLE V
MONITORING PARAMETERS FOR DETECTION MONITORING
Continued
p-Isopropyltoluene
Methyl bromide (Bromomethene)
Methyl chloride (Chloromethane)
Methylene bromide (Dibromomethane)
Methylene chloride (Dichloromethane)
Methyl ethyl ketone (MEK: 2-Butanone)
Methyl iodide (Iodomethane)
Methyl tert-Butyl Ether
4-Methyl-2-pentanone (Methyl isobutylketone)
Pentane
Styrene
1,1,1,2- Tetrachloroethane
1,1.2,2- Tetrachloroethane
Tetrachloroethylene (Tetrachloroethene; Perchloroethylene)
Toluene
1,1,1- Trichloethane (Methylchloroform)
1,1,2- Trichloroethane
Trichloroethylene (Trichloroethene)
Trichlorofluoromethane (CFC-II)
1,2,3- Trichloropropane
1,2,4- Trimethylbenzene
1,3,5- Trimethylbenzene
Vinyl acetate
Vinyl chloride
Xylenes
DRAFT
MONITORING AND REPORTING PROGRAM
.COUNTY OF KERN
KERN COUNTY WASTE MANAGEMENT DEPARTMENT
FOR OPERATION AND CONSTRUCTION
ARVIN SANITARY LANDFilL
KERN COUNTY
. 15
TABLE VI
CONSTITUENTS OF CONCERN & APPROVED USEPA ANALYTICAL METHODS
Inof2anics (dissolved):
USEP A Method
Aluminum
Antimony
Barium
Beryllium
Cadmium
Chromium
Cobalt
Copper
Silver
Tin
Vanadium
Zinc
Iron
Manganese
Arsenic
Lead
Mercury
Nickel
Selenium
Thallium
Cyanide
Sulfide
6010
6010
6010
6010
6010
6010
6010
6010
6010
6010
6010
6010
6010
6010
7061
7421
7470
7520
7741
7841
9010
9030
Volatile Organic Compounds:
USEPA Method 8260
Acetone
Acetonitrile (Methyl cyanide)
Acrolein
Acry lonitrile
Allyl chloride (3-Chloropropene)
Benzene
Bis(2-ethylhexyl) phthalate
Bromochloromethane (Chlorobromomethane)
Bromodichloromethane (Dibromochloromethane)
Bromoform (Tribromomethane)
Carbon disulfide
Carbon tetrachloride
Chlorobenzene
Chlorodifluoromethane
Chlorofluoromethane
Chloroethane (Ethyl chloride
Chloroform (Trichloromethane)
DRAFT
MONITORING AND REPORTING PROGRAM
·COUNTY OF KERN
KERN COUNTY WASTE MANAGEMENT DEPARTMENT
FOR OPERATION AND CONSTRUCTION
ARVIN SANITARY LANDFILL
KERN COUNTY
16
TABLE VI
CONSTITUENTS OF CONCERN & APPROVED USEPA ANALYTICAL
METHODS
Continued
Chloroprene
Dibromochloromethane (Chlorodibromomethane)
1.2-Dibromo-3-chloropropane (DBCP)
1.2-Dibromoethane (Ethylene dribromide; EDB)
o-Dichlorobenzene (1 ,2-Dichlorobenzene)
m-Dichlorobenzene (1,3-Dichlorobenzene)
p-Dichlorobenzene (1,4-Dichlorobenzene)
trans-1,4-Dichloro-2-butene
Dichlorodifluoromethane (CFC-12)
Dichlorofluoromethane
1.1-Dichloroethane (Ethylidene chloride)
1.2-Dichloroethane (Ethylene dichloride)
1.1-Dichloroethylene (1,I-Dichloroethene; Vinylidene chloride)
cis-I,2-Dichloroethylene (cis- l,2-Dichloroethene)
trans-I,2-Dichloroethylene (trans- 1,2-Dichloroethene)
l,2-Dichloropropane (Propylene dichloride)
1.3-Dichloropropane (Trimethylene dichloride)
2,2-Dichloropropane (Isopropylidene chloride)
1.1-Dichloropropene
cis-1,3-Dichloropropene
trans-l ,3-Dichloropropene
Ethylbenzene
Hexachlorobutadiene
2-Hexanone (Methyl butyl ketone)
Isobutyl alcohol
Isodrin
Isopropylbenzene
p-Isopropyltoluene
Methacrylonitrile
Methyl bromide (Bromomethane)
Methyl chloride (Chloromethane)
Methyl ethyl ketone (MEK; 2-Butanone)
Methyl iodide (Iodomethane)
Methyl methacrylate
Methyl tert-Butyl Ether
4-Methyl-2-pentanone (Methyl isobutyl ketone)
Methylene bromide (Dibromomethane)
Methylene chloride (Dichloromethane)
Naphthalene
Pentane
Propionitrile (Ethyl cyanide)
Styrene
DRAFT
MONITORING AND REPORTING PROGRAM
COUNTY OF KERN
KERN COUNTY WASTE MANAGEMENT DEPARTMENT
FOR OPERATION AND CONSTRUCTION
ARVIN SANITARY LANDFilL
KERN COUNTY
17
TABLE VI
CONSTITUENTS OF CONCERN & APPROVED USEPA ANALYTICAL
METHODS
Continued
1,1, 1,2- Tetrachloroethane
1,1,2,2- Tetrachloroethane
Tetrachloroethylene (Tetrachloroethene; Perchloroethylene; PCE)
Toluene
1,2,4- Trichlorobenzene
1,1, I -Trichloroethane, Methylchloroform
1,1,2- Trichloroethane
Trichloroethylene (Trichloroethene; TCE)
Trichlorofluoromethane (CFC-II)
1,2,3- Trichloropropane
1.2,4- Trimethylbenzene
1,3,5- Trimethylbenzene
Vinyl acetate
Vinyl chloride (Chloroethene)
Xylene (total)
Semi-Volatile Organic Compounds:
USEPA Method 8270· base. neutral. & acid extractables
Acenaphthene
Acenaphthylene
Acetophenone
2-Acetylaminofluorene (2-AAF)
Aldrin
4-Aminobiphenyl
Anthracene
Benzo[a]anthracene (Benzanthracene)
Benzo[b ]fluoranthene
Benzo[k ]fluoranthene
Benzo[g,b,i]perylene
Benzo[a]pyrene
Benzyl alcohol
alpha-BHC
beta-BHC
de lta-BHC
gamma-BHC (Lindane)
Bis(2-chloroethoxy)methane
Bis(2-chloroethyl) ether (Dichloroethyl ether)
Bis(2-chloro-I-methyethyl) ether (Bis(2-chloroisopropyl) ether; DClP)
4-Bromophenyl phenyl ether
Butyl benzyl phthalate (Benzyl butyl phthalate)
Chlordane
p-Chloroaniline
DRAFT
MONITORING AND REPORTING PROGRAM
. COUNTY OF KERN
KERN COUNTY WASTE MANAGEMENT DEPARTMENT
FOR OPERA nON AND CONSTRUCTION
ARVIN SANITARY LANDFILL
KERN COUNTY
18
TAnLE VI
CONSTITUENTS OF CONCERN & APPROVED USEPA ANALYTICAL
METHODS
Continued
Chlorobenzilate
p-Chloro-m-cresol (4-Chloro-3-methylphenol)
2-Chloronaphthalene
2-Chlorophenol
4-Chlorophenyl phenyl ether
Chrysene
o-Cresol (2-methylphenol)
m-Cresol (3-methylphenol)
p-Cresol (4-methylphenol)
4,4'-DDD
4,4'-DDE
4,4'-DDT
Diallate
Dibenz[ a,h ]anthracene
Dibenzofuran
Di-n-butvl phthalate
o-Dichlorobenzene (1,2-Dichlorobenzene)
m-Dichlorobenzene (I ,3-Dichlorobenzene)
p-Dichlorobenzene (I ,4-Dichlorobenzene)
3,3 '-Dichlorobenzidine
2,4-Dichlorophenol
2,6-Dichlorophenol
Dieldrin
Diethyl phthalate
p-(Dimethylamino )azobenzene
7 , 12-Dimethylbenz[ a]anthracene
3,3'-Dimethylbenzidine
2,4-Dimehtylphenol (m-Xylenol)
Dimethvl phthalate .
m-Dinitrobenzene
4,6-Dinitro-o-cresol (4,6- Dinitro-2-methylphenol)
2,4-Dinitrophenol
2,4-Dinitrotoluene
2,6-Dinitrotoluene
Di-n-octyl phthalate
Diphenylamine
Endosulfan I
Endosulfan II
Endosulfan sulfate
Endrin
Endrin aldehyde
Ethyl methacrylate
DRAFT
MONITORING AND REPORTING PROGRAM
.cOUNTY OF KERN
KERN COUNTY WASTE MANAGEMENT DEPARTMENT
FOR OPERATION AND CONSTRUCTION
ARVIN SANITARY LANDFILL
KERN COUNTY
19
TABLE VI
CONSTITUENTS OF CONCERN & APPROVED USEPA ANALYTICAL
METHODS
Continued
Ethyl methanesulfonate
Famphur
Auoranthene
Fluorene
Heptachlor
Heptachlor epoxide
Hexachlorobenzene
Hexachlorobutadiene
Hexachlorocyclopentadiene
Hexachloroethane
Hexachloropropene
Indeno( 1 ,2,3-c,d)pyrene
Isophorone
Isosafrole
Kepone
Methapyrilene
Methoxychlor
3-Methylcholanthrene
Methyl methanesulfonate
2-Methylnaphthalene
Naphthalene
1,4-Naphthoquinone
I-Naphthylamine
2-Naphthylamine
o-Nitroaniline (2-Nitroaniline)
m-Nitroaniline (3-Nitroaniline)
p-Nitroaniline (4-Nitroaniline)
Nitrobenzene
o-Nitrophenol (2-Nitrophenol)
p-Nitrophenol (4-Nitrophenol)
N-Nitrosodi-n-butylamine (Di-n-butylnitrosamine)
N-Nitrosodiethylamine (Diethylnitrosamine)
N-Nitrosodimethylamine (Dimethylnitrosamine)
N-Nitrosodiphenylamine (Diphenylnitrosamine)
N-Nitrosodipropylamine (N-Nitroso-N-dipropylamine; Di-n-propylnitrosamine)
N-Nitrosomethylethylamine (Methylethylnitrosamine)
N-Nitrosopiperidine
N- Nitrosospyrro I idine
5-Nitro-o-toluidine
Pentachlorobenzene
Pentachloronitrobenzene (PCNB)
Pentachlorophenol
Phenacetin
DRAFT
MONITORING AND REPORTING PROGRAM
. COUNTY OF KERN
KERN COUNTY WASTE MANAGEMENT DEPARTMENT
FOR OPERATION AND CONSTRUCTION
ARVIN SANITARY LANDFILL
KERN COUNTY
20
TABLE VI
CONSTITUENTS OF CONCERN & APPROVED USEPA ANALYTICAL
METHODS
Continued
Phenanthrene
Phenol
p-Phenylenediamine
Polychlorinated biphenyls (PCBs; Aroclors)
Pronamide
Pyrene
Safrole
1,2,4,5- Tetrachlorobenzene
2,3,4,6- Tetracblorophenol
o-Toluidine
Toxaphene
1,2,4- Trichlorobenzene
2,4,5- Trichloropheno
I 2,4,6- Trichlorophenol
0,0,0- Triethyl phosphorothioate
sym- Trinitrobenzene
Chlorophenoxy Herbicides:
USEPA Method 8150
2,4-D (2,4-Dichlorophenoxyacetic acid)
Dinoseb (DNBP; 2-sec-Butyl-4,6-dinitrophenol)
Silvex (2,4,5-Trichlorophenoxypropionic acid; 2,4,5- TP)
2,4,5- T (2,4,5- Trichlorophenoxyacetic acid)
Organophosphorus Compounds:
USEP A Method 8141
O,O-Diethyl 0-2-pyrazinyl phosphorothioate (Thionazin)
Dimethoate
Disulfoton
M~thyl parathion (Parathion methyl)
Parathion
Phorate
DRAFT
/
/
/
/
IIGEND
ATTACHMENT A
D
Waste Management Facility Boundary
FACILITY LOCATION MAP
.
1445 FEET
N
i
ARVIN SANITARY LANDFILL
. VenVirotek Lease
Scale: 1 w = 1445'
r---....-
o
COUNTY OF KERN
BASE MAP SOURCE: USGS 7.5' WEED PATCH QUAORANGLE
(RCS)
(2125198 )
ßAR1.22
AR1.œ
AR1-o1
AR1·21
$
AR1-o2
& AR1-05
VenVirotek
1-03
$
.
Existing Vadose Zone Monitoring Point
Landfill Water Supply Well
Waste Management Facility Boundary
AnACHMENT B
SCHEMATIC REPRESENTATION
of the
lEGEND
& Existing Monitoring Well
o
D
L£ - ì
\.. I
", ,
~
ARVIN SANITARY LANDFILL
Waste Management Unit
N
i
COUNTY OF KERN
Approximate Scale: 1" :: 600'
-...--- .
o 600 FEET
(RCS)
(2125/98 )
.
INFORMATION SHEET
.
COUNTY OF KERN
FOR OPERA nON AND CONSTRUCTION
ARVIN SANITARY LANDFILL
KERN COUNTY
The County of Kern owns and operates the Arvin Sanitary Landfill. The facility was originally operated
as a bum dump as early as 1949, and was converted to a landfill in August 1971. Based on 1998 data,
the waste management facility receives approximately 267 tons of municipal solid waste per day with an
estimated remaining capacity of 550,393 cubic yards. Final capacity is anticipated by September 2000.
It is approximately five miles west of Arvin and receives waste from the greater Arvin area, portions of
Bakersfield, the communities of Lamont, Weedpatch, Greenfield, and Pumpkin Center, and the u:bec
transfer station.
A 127-acre unlined waste management unit exists within the 170-acre waste management facility
property. The site is within a 100-year floodplain according to FEMA maps. Soils underlying the site
are unconsolidated, consisting of interbedded gravels, sands, silts, and clays.
Depth to groundwater is approximately 59 to 80 feet below the native ground surface, and exhibits a
gradient toward the south. Monitoring data from one background well indicates that groundwater has a
total dissolved solid range of 507 to 680 mgll, which exceeds the secondary drinking water standard
established by the Department of Health Services. Groundwater monitoring has detected volatile
organic compounds at concentrations in excess of the primary maximum contaminant levels for drinking
water.
Evaluation monitoring to determine the extent of groundwater degradation bas been implemented at the
site. . Completion of the evaluation monitoring program, modification of tbe detection monitoring
program for full compliance with Title 27, and implementation of a corrective action program will be
addressed in a subsequent Cleanup and Abatement Order.
This Orderimplements groundwater detection monitoring and operation of the facility in accordance
with the provisions contained in Title 27.
,
'i
S
California Regional Water Quality Control Board
Central Valley Region
Steven T. Butler, Chair
Q
'~,
Winston H. Hickox
Secretary for
Environme1l1al
Pr"'IJrtinn
Fresno Branch Office
Internet Address: http://www.swrcb.ca.gov/-rwqcb5
3614 East Ashlan Avenue. Fresno. California 93726
Phone (559) 445-5116' FAX (559) 445-5910
Gray Davis
Governor
19 November 1999
-, \
J \:J :~ ,':I~;"i-'
f~fJf/ ) c' ~,<~'
, f¡{i'r.-..
~ u:;~~9
Ms. Daphne H. Washington
Kern County Waste Management Department
2700 M Street, Suite 500
Bakersfield, CA 93301
'~ -
",
. J ;.~::,
NOTICE OF' PUBLIC MEETiNG
Three (3) copies of a Notice of Public Meeting concerning your waste discharge requirements and one
(1) of a Proof of Posting form are enclosed. Regulations require you to comply with the items checked
below:
[X] By 30 November 1999, post one (1) copy ofthe Notice at the nearest city hall or county
courthouse; and one (1) copy at the post office nearest the facility.
[X] By 10 December 1999, file with this office Proof of Posting, using the enclosed form.
DANE S. JOHN ON
Senior Engineering Geologist
CRG No. 4239
Enclosure
cc: U.S. Environmental Protection Agency, Region 9, San Francisco
Mr. Tim Regan, Office of Chief Counsel, State Water Resources Control Board, Sacramento
Ms. Elizabeth Haven, Division of CleanW ater Programs, State Water Resources Control Board,
Sacramento
California Integrated Waste management Board, Sacramento
Department of Health Services, Office of Drinking Water, Fresno
Department ofFish and Game, Region IV, Fresno
Department of Water Resources, San Joaquin District, Fresno
Kern County Department of Environmental Health Services, Bakersfield
Kern County Department of Planning and Development Services, Bakersfield
dsjlrehlu:landfiWrehlkemnowl Arvinlaslwdr/aslnphcl.doc
California Environmental Protection Agency
o Recycled Paper
7
NOTICE OF PUBLIC HEARING
ARVINS~TARYLAND~L
KERN COUNTY
-2-
Kern County Air Pollution Control District, Bakersfield
Kern County Water Agency, Bakersfield
Mr. Howard Wines, City of Bakersfield, Bakersfield
dsj/rehlu :landfiJJJrehJk&dII999/wdrlkdnphcJ. doc
California Environmental Protection Agency
Recycled Paper
19 November1999
~
CALIFORNIA REGIONAL WATER QUALITY CONTROL BOARD
CENTRAL V ALLEY REGION
3614 E. Ashlan Avenue
Fresno, California 93726
NOTICE OF PUBUC MEETING
and
Notice of Consideration of Waste Discharge Requirements
for
COUNTY OF KERN
FOR
OPERATION AND CONSTRUCTION
ARVIN SANITJ'~Y LANDFILL
KE~ COUNTY
Nathan Daniels, Roberta Daniels, et al. own a solid waste landfill approximately three miles southeast of
downtown Bakersfield. The existing 24-acre facility contains one 8-acre unlined waste management unit
that received nonhazardous and inert solid waste from 1968 to 1974. These updated waste discharge
requirements require post-closure maintenance of the facility in accordance with the provisions of
Division 7 of the California Water Code.
The County of Kern owns and operates the Arvin Sanitary Landfill. A 127-acre unlined waste
management unit exists within the 170-acre waste management facility property. Based on 1998 data,
the waste management facility receives approximately 267 tons of municipal solid waste per day with an
estimated remaining capacity of 550,393 cubic yards. Final capacity is anticipated by September 2000.
It is approximately five miles west of Arvin and receives waste from the greater Arvin area, portions of
Bakersfield, the communities of Lamont; Weedpatch, Greenfield, and Pumpkin Center, and the Lebec
transfer station.
A public meeting concerning this matter will be held as follows:
DATE:
\Friday, 28 January 2000
,TIME:
9:00 a.m.
PLACE:
Regional Water Quality Control Board
3443 Routier Road, Suite A
Sacramento, California
Persons who want to submit written comment or evidence on this item must provide such written
documents so that they are received at this Regional Board office by 31 December 1999. Written
documents may be submitted by fax to (559) 445-5910, but it is the responsibility of the commenter to
ensure that the documents are received by the deadline. Comments received by this deadline will be
included in the administrative record before the Board. Staff may provide responses to the comments.
Written testimony or comments submitted after the noticed deadline will not be accepted and not
Notice of Public Meeting
incorporated into the administrative record unless allowed by the Board Chair, based on extreme
hardship or unusual circumstances.
All interested persons may speak at the Board meeting, and may orally summarize their written
submittals. Oral testimony at the Board meeting will be limited in time by the board Chair (typically not
more than 15 minutes for dischargers and 3 minutes for other interested parties). Oral testimony must be,
relevant. Groups of speakers will be expected to select a spokesperson and not be repetitive.
Copies of the proposed requirements and related documents are available for review and may be
obtained from the Regional Board office on weekdays, between 8:00 AM and 5:00 PM. Anyone having
questions regarding these requirements should contact Ronald Holcomb at (559) 445-6050.
~
W~
WILLIAM F. PFISTER
Supervising Engineering Geologist
CEG No. 931
Dated: 19 November 1999
~'
~
California Environmental Protection Agency
Department of Toxic Substances Control
Fact Sheet #2
RECETfV~
'''- Jf:'-1D
AUG 1 2 1999
BY:
===--
WHAT Is THE PURPOSt: ÛF THIS FLYER?
August 1999
This flyer has been developed to inform you
about site investigation activities that will be
performed at the former K&D Salvage Yard
site in August 1999.
WHAT IS THE FORMER K&D SALVAGE
Y ARD'S HISTORV?
1935 throuah 1989: The 1 a-acre former
K&D Salvage Yard (Site), located at 600 S.
Union Ave, Bakersfield, California, operates
as a metal recycler and storage facility.
October 1998: The Department of Toxic
Substances Control (DTSC) takes over
responsibility to perform environmental
investigations and eventual cleanup of the
Site as part of its orphan site program.
December 1998: DTSC removes non-
hazardous debris from the Site surface,
starts contamination investigation activities,
and places a fence around the perimeter of
the Site.
Julv 1999: DTSC begins the Remedial
Investigation/Feasibility Study (RI/FS)
phase of the project.
WHAT Is A REMEDIAL
INVESTIGATION/FEASIBILITY STUDV?
In genera', a Remedial Investigation is
conducted to determine the types of
chemicals present and where they are
located. This is done by coiiecting soil
samples and having them analyzed by a
laboratory .
Following the Remedial Investigation, a
Feasibility Study is conducted to determine
cleanup options, including treating and
removing soil or groundwater. This
evaluation of several cleanup options
çonsiders the human health and
environmental risk posed by the
contamination and the costs of each option.
Even though prior preliminary environmental
investigations have shown that soil at the
Site is contaminated with heavy metals
including lead and zinc, waste oils, and
polychlorinated biphenyls (otherwise known
as PCBs), it is important to conduct further
investigations so that DTSC has all of the
facts when selecting the best possible
cleanup option fOí the Site.
/
W HAT CAN I ExPECT To S EE IN M V
NEIGHBORHOOD?
As a safety precaution, workers performing
sampling activities will be wearing
protective clothing and possibly air
purification equipment. The protective
clothing will safeguard workers from contact
with contaminated soil. Since workers will
be very close to the contamination , state
and federal regulations require that they
wear air purification equipment and
protective clothing.
Departamento para el Control de Substancias T óxicas
Agencia para la Protección del Medio Ambiente de California
T
Actividades de Investigación del Lugar en el
Antiguo Local deK & D Salvage Yard
Hoja Informativa #2
Agosto de 1999
¿CUÁL ES EL PROPÓSITO DE ESTE VOLANTE?
Este volante se ha elaborado para informarle sobre
las actividades de investigación del lugar que se
llevarán a cabo en el antiguo local de K& D Salvage
Yard, en agosto de 1999.
I- -
- "_.~--- -- ._,...----~-----~-,-.,-..----~--------~-~-..,----
¿ CUÁLES SON LOS ANTECEDENTES DEL ANTlGUO
LOCAL DEK & D SALVAGE YARD?
De 1935 a 1989: El antiguo local de K & D Salvage
Yard, con una extensión de 10 acres, ubicado en el
600 S. Union Ave., en Bakersfield, California,
opera un establecimiento de reciclaje y
almacenamiento de metales.
Octubre de 1998: El Departamento para el Control
de Substancias Tóxicas (Department of Toxic Sub-
stances Control - DTSC) asume la responsabilidad
de llevar a cabo investigaciones del medio ambiente
y la limpieza eventual del Local, como parte de su
programa de locales huérfanos.
i__
Diciembre de 1998: El DTSC remueve los
escombros no peligrosos de la superficie del Local,
. ~eomienza-las-actividades de-investigación-sobre la-
contaminación y coloca un cerco alrededor del
perímetro del Local.
Julio de 1999: El DTSC comienza la fase del
Estudio de Viabilidad/Jnvestigación de Medidas
Correctivas (Remedial Investigation/Feasibility
Study - RI/FS) del proyecto.
¿ QUÉ ES EL ESTUDIO DE VIABILIDAD DE MEDIDAS
CORRECTlV AS?
En general, una Investigación de Medidas Corree-
tivas se lleva a cabo para determinar las c1ases de
químicos que están presentes, y en dónde se loca~
lizan. Esto se hace tomando muestras del suelo, y
haciendo que se analicen en un laboratorio.
Después de la Investigación de Medidas
Correctivas, un Estudio de Viabilidad se lleva a
cabo para determinar las opciones de limpieza,
---'-inc1uyendo el tratainiento yextracciònaetferra -0--
agua subterránea, Esta evaluación de varias
opciones de limpieza toma en consideración el
riesgo que la contaminación significa para la salud
del ser humane y del medio ambiente, así como 105
costos de cada opción.
Aunque las investigaciones preliminares pre vias
han indicado que el suelo del Local está
contaminado con metales pesados, entre los que se
inc1uyen el plomo y el cine, aceites desechados y
bifenilos polic1orinados (polychlorinated biphenyls)
(conocidos de otra forma como PCB s), es
importante llevar a cabo investigaciones
adicionales, a fin de que el DTSC tenga todos los
datos al seleccionar la mejor opcÎón de limpieza
posible para el Local.
¿ QUÉ PUEDO ESPERAR VER EN MI VECINDARIO?
__ ____-_____. ____A~____·_
- ----- - ----
Como una precaución de seguridad, los trabajadores
que tomen las muestras llevarán puesta ropa protec-
tora y posiblemente equipo para la purificación del
aire. La ropa protectora protegerá a los trabajadores
del contacto con tierra contaminada. Puesto que los
trabajadores estarán muy cerca de la contaminación,
los reglamentos estatales y federales exigen que
lleven equipo para la purificación del aire y ropa
protectora.
,
All investigative activities will occur Monday
through Friday, from 5:00 a.m. until 5:00
p.m., and will last approximately one week.
Equipment will be coming in the gate on
Daniels Lane and out the gate on Union
Avenue. Other than delivery of the
backhoe, heavy truck traffic is not
anticipated. However, if unknown Site
conditions require the use of heavy
equipment, It is DTSC's goal to keep truck
traffic and parking to a minimum in order to
reduce any inconvenience to the
neighborhood.
WHAT HAPPENS ONCE THE REMEDIAL
INVESTIGATION/FEASIBILITY STUDY ARE
OVER?
Once DTSC has fully investigated the Site,
the results of the findings and proposed
cleanup strategy will be made available to
the public for a 30-day review and comment
period. Flyers like this one will be sent to
you announcing when the 30-day public
comment period will begin. The flyer will
also tell you when and where you can
attend a public meeting to discuss DTSC's
proposed cleanup plan.
Mailing List
~
If you would like to be added to, or know
of an individual or group that would like to
be added to the former K&D Salvage
Yard site specific mailing list, please
notify one of the contacts listed on this
page.
WHO SHOULD I CONTACT IF I HAVE
QUESTIONS OR CONCERNS?
If you find that you have questions or
concerns at any time during this project, you
are encouraged to contact the Project
Manager or Public Participation Specialist
listed below, Mr. Wallberg will be present
when field activities are scheduled at the
Site, however, Site access is restricted.
During these times, he can be contacted by
calling the number below. The following
individuals can assist you with any
questions you might have:
Eric Wallberg
Project Manager
Department of Toxic Substances Control
10151 Croydon Way, Suite 3
Sacramento, California 95827
(916) 255-3749
or
Heidi Hansen
Public Participation Specialist
Department of Toxic Substances Control
P.O. Box 806 - HQ15
Sacramento, California 95812-0806
(916) 324-3108
I NOTICE TO THE HEARING IMPAIRED
~
You can obtain additional information by
using the California State Relay Service at
1-888-877-5378 (TDD). Ask them to
contact Heidi Hansen at 916-324-3108
regarding the Former K&D Salvage Yard
site.
.
Todas las actividades investigativas se llevarán a
cabo de lunes a viernes, de 5:00 de la mañana a 5:00
de la tarde, y durarán aproximadamente una
semana. El equipo llegará por la entrada en Daniels
Lane y saldrá por la entrada en Union Avenue.
Aparte de la entrega de la retroex:cavadora, no se
anticipa tráfico de camiones pesados. Si las
condiciones inesperadas en el Local requieren el
uso de equipo pesado, el objetivo del DTSC es
minimizar el tráfico y estacionamiento de camiones,
a fin de reducir cualquier inconveniencia 'al
vecindario.
¿ QUÉ SUCEDE UNA VEZ QUE SE CONCLUY A EL
ESTUDIO DE VIABILIDADIINVESTlGACIÓN DE
MEDIDAS CORRECTlV AS?
Una vez-qûè -él btSChaya invèstigado ëfLoéãl põr
completo, los resultados de la investigación y la es-
trategia propuesta para la limpieza se pondrán a la
disposición del público, por un período de 30 días
para su análisis y comentarios. Se Ie enviarán
volantes como éste, anunciando cuándo comenzará
el período de 30 días para comentarios del público.
Además, el volante indicará cuándo y dónde usted
puede asistir a una reunión abierta al público para
hablar sobre el propuesto plan de limpieza del
DTSC.
Lista de Correspondencia
~
Si Ie gustaría que a usted se Ie agregara, 0 si
sabe de algún individuo 0 grupo al que Ie
gustaría que se Ie agregara a una lista de
correspondencia específica para el antiguo local
de K & Ð Salvage Yard, por favor notifíquese1o
a una de las personas que sirven como contacto
que se indican en esta página.
I .
¿ CON QUIÉN DEBO COMUNICARME SI TENGO
PREGUNTAS 0 PREOCUPACIONES? rl
Si se da cuenta que tiene preguntas 0
preocupaciones en cualquier momento durante este
proyecto, se Ie recomienda que se comunique con el
Administrador de Proyectos 0 con el Especialista
Encargado de la Participación del Público que se
indica a continuación. EI Sr. Wall berg estará
presente cuando se programe llevar a cabo
actividades en el Local. Sin embargo, el acceso al
Local está limitado. En esos momentos, puede
comunicarse con él, llamándole al número a
continuación. Las personas siguientes pueden
ayudarle con cualesquier preguntas que podría
tener:
-- ~- --~-<'- -~-- ---Ene Wallbéig---
Administrador del Proyecto
del Departamento para el Control
de Substancias Tóxicas
10151 Croydon Way, Suite 3
Sacramento, California 95827
(916) 255-3749
ó
Heidi Hansen
Especialista Encargada de la Participación del
Público del
Departamento para el Control
de Substancias T óxicas
P.O. Box 806 - HQ15
Sacramento, California 95812-0806
(916) 324-3108
-_.
A VISO PARA LAS PERSONAS CON
IMPEDIMENTOS DEL OIDO
1:r
Usted puede obtener información adicional
utilizando el Servicio Auxiliar (Relay Service)
del Estado de California, llamando al
1-888-877-5378 (TDD). Pídales que se
comuniquen con Heidi Hansen al
916-324-3108, con respecto al antiguo local de
K & D Salvage Yard.
,~;
"
11
Mailing List Coupon
If you have any comments concerning the Former K&D Salvage Yard site or if you would like to be
put on the site specific mailing list, please take a moment to fill out the information below and mail
it to Heidi Hansen, DTSC, P.O. Box 806 - HQ15, Sacramento, CA 95812-0806.
MAILING LISTS ARE CONSIDERED PUBLIC RECORD.
Name:
Address:
City/State:
Zip Code:
Comments:
Cupõn para la Lista de Correspondencia
Si usted tiene cualesquier comentarios con respecto al Antiguo local de K&D Salvage Yard, 0 si Ie
gustaría que se Ie agregara a la lista de correspondencia pertinente específicamente allocal, por
favor tómese unos minutos para lIenar la información a continuación, y envíeselo por correo a
Heidi Hansen, DTSC, P.O. Box 806 - HQ15, Sacramento, CA 95812-0806.
LAS LIST AS DE CORRESPONDENCIA SE CONSIDERAN REGISTROS PÚBLlCOS·.
, I
Nombre:
Dirección:
Ciudad/Estado:
Código Postal:
Comentarios:
06/07/99 MON 12:09 FAX 805 326 3098
COB WTR RESRCS
II ·
.
I'
I
CITY OF BAKERSFIELD WATER QUALITY REPORT 1998
Pr1mar~ standards
+1.
'''lI~ETI'I!i'' "
- Mandator~ Health-Related Standards
" , ,,:,; 1 "" ~~~~j,' 'cõHiW'¡'¡4MT," ~~~"",::, '·¡'¡:'::":GIi:aUHÐVÄt~:,I.;:";:.¡..
¡ .. . . I~~II~~: l"~~), I!, '(PHGt '. ',IWI~:.':;"~:;:'" ~~~~~', ::¡'I
NTU S. nong 0.01-1.10 0.21
~ Sa.plos P sitiv~ S. 0 0-1.4 0.1
MCL Wiol~tlon5 0 0
m§/L 0.002 0.004) M.D.
m~/L O.OO~ 0.005 N.D.
us/L 0.018 none N.D.
ms/L 0.001 0 N.D.
DU/~ 0.0002 .00000 > N.D.
as/l 0.018 O.O~ N.D.
as/l O.oooS 0 N.D.
møll 0.0001 .00003 N.D.
_S/l 0.07 0.07) N.D.
ms/L 0.2 0.79) N.D.
.S/l 0.4 0.' N.D.
as/l O.oo~ 0.012) H.D.
.S/L 0.0002 0 M.D.
_S/L 0.6 D.'> H.D.
DilL O.oos 0.006) N.D.
ms/l 0.005 ~One N.D.
.S/L 0.006 0.007 N.D.
ai/l 0.005 0 M.D.
mS/l 0.006 o.o? N.D.
ms/l 0.01 0.1 N.D.
.~/L o.ooS 0 H.D.
~/L o.~:.:!s ,',on" N.D.
-S/l 0.007 0.01~) N.D.
.O/l 0.00000003 0 N.D.
8S/l 0.02 0.02 N.D.
D~/L 0.1 0.58) N.D.
a~/L O.OOl 0.002 N.D.
milL 0.70 0.3) N.D.
ms/L 0.00005 0 N.D.
a9ll 0.15 0.7) N.D.
.S/L 1.2 (41 N.D.
8g/L 0.7 (1) N.D.
m9/L 0.00001 0 N.D.
au/L 0.00001 0 H.D.
au/L 0.001 0 H.D.
.S/L O.os 0.05 N.D.
me/L 0.0002 0.0002 N.D.
ms/l O.O~ 0.04 N.D.
89/L 0.005 0 N.D.
.9fL 0.02 none N.D.
.g/L 0.07 0.1 H.D.
.s/l O.Z 0.05) N.D.
.9/l 0.001 0.0004 N.D.
ms/l 0.5 O.S) H.D.
(PCls) 80/L 0.0005 0 N.D.
8S/L 0.05 O.o~ N.D.
moll 0.004 0.004 N.D.
mS/l 0.1 0.1 N.D.
8S/L 0.001 nonO N.D.
a~/L O.OOS 0 N.D.
agll 0.07 none N.D.
mS/l 0.15 none N.D.
ms/l 0.003 0 N.D.
Dg/L 0.07 0.005) N.D.
m~/l 0.2 0.,00 M.D.
m~/L 0.005 0.003 N.D.
D~/L O.OOs 0 H.D.
mulL 0.1 none H.D.
ms/l 0.0005 0 H.D.
moIL 1.75 1.6001 N.D.
. ,"
.1
TurbIdIty
Coliform laçterla
ORGANIC CHEMICALS
Alli1chlor
Atra;¡<~ne
IIgntilzon
Benz.n.
aenzo (a) p~r.ne
t"rÞofuran
C"rÞon Tgtrachlorldo
Chlordane
;;:,~-p
Dlllapon
Di lZ-.thylhekyl) èdipat. \DEHA)
Dl (2-e!hy1haxyl) pnthill~t. (DE~
Dlb~o.ochloroprQP~ne (DIICP)
1,2-DiohloroQ8nzene
l,4-DiçnloroÞenzene
l,l-Dich1or~thanQ
1,I·Dlchloroeth~lene
l,Z-Dichloroetnang
tI1-1,Z-Dlchloraeth~lonQ
Tran5-1,~-DichloruetnYlgne
1,Z-Dicnloropropane
à1~;~~~hlur"'p,'o"-
Dlo.Jn (2.3.7.ð~TCDD)
Diaust
Endotha11
~ndr¡n
Etl'l:rlÞenz8ng
Etnylene Dlbrobld8 (EDB)
Freen 11
Frean 113
Gly)\o$.~e
leptilçhLor
Ieptachlor fpo.lde
H8.achloroDenzene
He.Bchlorocyclo~.ntadiDno
lindlime
I16tl\o>l\lchlor
Nøthyløng Chloride (PC")
""'Hnote
"onochlorobenzene
0"8m,1 (\I"da'.)
Pentachlorophenol
Piçlora.
Pol,chlorinat.d liphe~y15
Silve. (2.~.S-TP)
Sllllazin.
St,rone
1,1,Z,l-Tetrachloroethane
Tetrachloroetnylene (PCE)
Thloboincarb
T olu,,"e
rCI1<.phooe
1,Z.4-Triçhloroþgnzene
l,l,l-Triçnloroethane (TCA)
1.I.Z-Tricnleroethane
1ricnloromtft\llen. (TCE)
Total Trlh5loa.Lhano5
'''In,l Chlodde
Jt.J' }o.ne5
I"OPQ~NIC CHEnlcALS
aluainum
Antllllon.J'
4r5enjc
ASbestos
8er.lIJa
16..311111.1.
C.doi.iUD
ChroOlil.lØl
FluorIde
Lelld
Meraury
Nickel
Hitrate tas M03)
Selenlu.,
11'1&11ium
RADIOACTIII ITY
GrO$5 Alpha Activity
UnniWII
'5ecQl1dar'.;j 5tandardS
1.
0.1106
0.05
7
,
0.Q04
0.005
O.OS
1.4 - Z."
0.015 ¡ilL
O.QO?:
0.1
"5.
0.05
O.OO?:
<1<Jne
ð.020)
none
7
Z
O.oo~
0.005
0.1
(1)
O.OOZ)
0.002
none
("5)
a.oJ;
.0005
0-0.09 <0.01
N.D.
0-0.01 <O.O~
N.D.
0-(1.' <n,.'
o~O.ool <0.00
N.D.
M.D.
o-o.?: 0.1
0-0.019 0.00/
N.D.
0-0.010 0.00
;:-33 5
N.D.
H.D.
N.t>.
0-Q.07 <0.01
o·n Z
0-D_29 0.9
0-0.06 cO.Ol
0-0.25 0.02
N.D.
N.D.
N.D.
N.D. <0_01
10·145 Z6
174-S22 Z83
0-0.07 <0.01
~S-132 83
9·1!o~ 29
Z,5·J9Z 86
oY8 30
7.69-1.96 8.09
1.0-3.4 Z."
.g/L
./L
.g/l
IIFl
~:J/L
IliIl
.ø/l
.!l/l
"g/L
-ø/l
'"IIIL
IIs/l
m9fl
m5l/l
.g/l
pCi/L IS none
pCi/l 20 none
- Aest1Jet,c 5t~nd~rd5
NTU . M.p~lo..trio Turbidity Units
T_O.N . T~res~ld Odor HumDer
~ W~YA~ .~~Dn~l"ð arl ,~~~. ~o~~_~
15.
1.3 Al
0.5
0.5
o.oS
0.005
3.
0.1
500.
none
nonQ
nonA
nune
none
none
none
non_
non.
none
none
nong
orl e
Calor
Co~ø..r
Foaming Agent~ (1IIaS>
Iron
IÌèIn¡¡ana&e
N8t~~1 tert-ß~~y1 ~tß.r (NT6E)
Odor-Threshold
SH"er
Sulfet.
Specific Condl.lçtançe
U.\C
AdditionaZ Constituents
al~alinity (é~ço~)
cillçiWl
Hardnmss (C8C03
1Ia!ll/'l.sl....
11M
Potl!'ssiu.
none
Ran.
nonll
none
none
none
N.D.
IIFL
DC:i/l
. M01: DetecteCl
s "lll1ðn Fibers pAr LitDr
. Di~a ~uriQc nor li~or
H.T. . Not Tested
AL . Action IDyol
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(QOlll\)
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State of California
. cr" rnia Environmental Protection Agency
àerdrtment of Toxic Substances Control
Northern California Region
Sacramento Office
Site Mitigation Program
Case Development Unit
10151 Croydon Way, Suite 3
Sacramento, CA 95827-2106
.(916) 255-3749"
Eric Wallberg 8-494-3749
Hazardous Substances Scientist TELEFAX (916) 255-3696
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.-- - - ----
RPR-28-1999 10:36
;. >r
.~
DTSC-EXT.RFFRIRS
-
916 327 0978
P.01/02
.
FAX TRASMITTAL
To:
Howard Wines
805-326-0576
Amy Green
661-826-8701
Jim Ellis
661-862~860 1
From:
Heidi Hansen
Department of Toxic Substances Control
Public Participation Specialist
916-324-3108
Date:
4/28/99 @ 10:31 a.m.
Subject:
INFORMATION ON THE FORMER K&D SALVAGE YARD
Attached is a one~page fact sheet that was sent to nearby residents of the Site back in
December. It provides a brief description of the Department's involement with the Site and is
supplemental to the more extensive cOnllnWlity outreach that we are begiIU1ing to conduct now.
In brief, what I'm hoping to do is meet with appropriate representatives of the affected
community to answer questions and obtain infonnation regarding how best to involve the
community in the decision-making aspects of this project.
After you have had a chance to review the attached, I would appreciate a few moments of
your time to set-up an appointment, convenient to you, to meet and discuss tlùs project in a bit
more detail.
Thank you for taking the time to respond to this matter. It is much appreciated.
Attaclunent
APR-28-1999
10:37
DTSC-EXT.AFFAIRS
e·-:·:
.., '
.. ,
l:.ùiI'Clrni;¡ l\n'''~nl"J Prul~"li"n AI!~ncy
1).:pal'ml<I,1 "1'_ Sub:iiM.:." COIIINI
.
916 327 0978
Oecember '998
P.02/02
~~
~
The Former K&D Salvage Yard Site
W1 IA T [S TI IE PURPOSE OF THIS FLYER?
This flyer l'Ias been developed to inform you about activities at the _et..Ka.o.~~1x¡ilge..:r:ilr.d sile, localed at6QO
.¡..JJtIion,AIte, Balc.erstield, California.
¡lOW DOES TI !IS AFFECT ME?
As you mayor may not know. tne former K&D Salvage Yard (Site) opør~...i!~_~m auto dismantler and storage
f~y .n 1ILAç~.s' b.dWeen 1958 and ~989~ Previous In\lestigations at the S~8 four'ld tnat K&D's ~C?_rmer..
operations resulted in soil contamination witn nea'l.Y ,.roetals . ladudIøg," lead ;.,d~¡tinè~~astè "oils,'-ãnd'
ggJ~c/'lÇld.,.ale~ þiphenyls (otherwise 1u'10wn à:o PCBs),
Cl.IlTently, the Sile is abandoned and because it was never adeCluBtely fenced, is access able for unauthorized
disposal of debrts. such as tires, old appliances and other househøld item6.
1o:À.~.Á.\Jst ,t99ß, the Department of Toxic Substances ContRIl CDrsC) IS$Ueclan-mminent.:.~nd Substantial
endangerment Determination and Order (otherwise known ta8 an Order) to those parties found responsible for
çontaminatir'lg the Site, The Order stated, that under [)"IS:; aversight, the responsible parties were to conduct
and pay for an investigatiQn and eventual cleanuþ of the Site,
Unfortunately, U'!e I:ç.spcn,ible.parties did 110t comply with ~e Order, IInd in Od:ober 199B, OTSC determÍl'led that
it would take responsibility for cQnducting and paying før ¡"ve.tis.ticn and clean LIp of the Site.
WI AT CA;\; I UXPGCT TO SeE IN MY NEIGHBORHOOD?
even tl'lougli OTSC has already concluded th¡¡at conl.tmlinBdon dess exist at tne Site, fu.,her investIgation is
needed to ð@terminé éxactly what kind and how much contamination .till remains. /It, c:ontraètor has been hired
by DTSC 10 remove the debris and ;nstall a new fence around the Site. Once the Site l'Ias be,,!n cleared of aU
debris, soil samples will be collec:ted. These activities are upec:\ed to last approximately 7 to 14 days, with
work occurring Monday through Friday, 8:00 a,m. to 5:00 p.m. Curing this time. you may notic;e trucks hauling
off debris. It is DTSC's 9Q4I1 to keep truck traffic: and par1t;ing to a minimum in order to reduce any inconvenience
to t~e neigl'lborhood.
Once tne Site Mas been fully investigated. the results of OTSC's findi"gs and cleanup strategy will be made
available to tl'\e public: for review and comment. Flyers like this one will be provided tQ keep you Informed as
activities progress.
I row (' AN r GET INVOL vrm
OTSC's PQlicy is 10 encourage community involllement in !tie decisiQn.making process and two-way
c:ommunication, AS þart of DTSC's PUblic Participation strategy for this Síte, a public partic:ipatlon plan will be
developed by meeting with members of the éJPfec:ted communÎt'i to formall~ document their questions arid
c:øncer"s, Other strategies for this síte include, but are "crt limilBd to; dS\lslopl",g a site specific mailing líst
è$taÞishi/'l9 ,al'l infQrmation reposilo/)' to provide community access to OTSC docf,jments related !o tnls "roJecl;
and distnbution of fact sheets ugdatÎng the affected commul'ljty throughQut the project
WHAT HAPC.JENS NEXT?
Once this pnase of the project has been C:Qm~leted, a fad snaet may be distributed to the site specIfic mailíng
list announcing the next technical Md participation steps in the PrQject.
If you find, however, that you would Ii)ca mom information prior to being contacted by On>c. your are
enc:oul'3ged to ccntac:t:
Megan Cambridge
Department of Toxic SubstanC:ès Control
10151 Croydc" Way, Suite 3
Sacramento, Califomie 95827
(916) 255·3727
Of
Heidi Hansen
Department of TO:lic Substanc.es Control
P,O. Bcx806· HQ15
Sac:l'8mento, Callfomla 9581Z-0806
(916) 324-3108
M~iling List Coupon
Il'yolol haY\: ..,.)' "'Ulnr'l¢nt~ ~"'I\c~"'¡n~ Ih~ Former K&D SaIl/age Yard~¡!C t:It ¡(yO\! would like!Q be pUII'n \I,.: ~II~
~flc~ilïe ",:¡ilin¡; h~l. fllo.:.~o.: 1:010;0.: Ii murncnl tu fill .....t Ihe inrormari"" b!:lo...... Il\d mail it 10 He,dl Hansen. 1).,.:0;('_
I'.V. !.SOX !IOu - IIQIS. S~<;I'¡men;o. CA 95812-0806. MAIL.Iì'lCI LISTS AJl£ COlSmHREI' ^ 1'11111,1(' '(',~'tJtU>
N¡'c:
A.sdr,,~:
Cil)'~
Cnm",c"t~'
SloIte:
Zip Cede;
TOTAL P.02
"
.
s
Californiaþgional Water Qualitøcontrol Board
Central Valley Region
Steven T. Butler, Acting Chair
~
--
Winston H. mckox
Secrermy for
Environmental
Prnt,rti""
Fresno Branch OfDce
Internet Address: http://www.swrcb.ca.gov/-rwqcb5
3614 East Ashlan Avenue. Fresno. California 93726
Phone (559) 445-5116· FAX (559) 445-5910
Gray Davis
Governor
23 March 1999
Mrs. Roberta Daniels
c/o Mr. Marcus Daniels, Agent
408 Quailridge Drive
Bakersfield, CA 93309
Mr. Nathan Daniels
3318 Harmony
Bakersfield, CA 93306
NOTICE OF PUBLIC MEETING
Three (3) copies of a Notice of Public Meeting concerning your waste discharge requirements and one
(1) of a Proof of Posting form are enclosed. Regulations require you to comply with the items checked
below:
[X] By 31 March 1999, post one (1) copy of the Notice at the nearest city hall or county courthouse;
and one (1) copy at the post office nearest the facility.
[X] By 9 April 1999, file with this office Proof of Posting, using the enclosed form.
~-
DANE S. JOHNSO
Senior Engineering Geologist
CRG No. 4239
Enclosure
cc: U.S. Environmental Protection Agency, Region 9, San Francisco
Ms. Lori Sennitte, Office of Chief Counsel, State Water Resources Control Board, Sacramento
Ms. Elizabeth Haven, Division of Clean Water Programs, State Water Resources Control Board,
Sacramento
California Integrated Waste management Board, Sacramento
Department of Health Services, Office of Drinking Water, Fresno
Department of Fish and Game, Region N, Fresno
Department of Water Resources, San Joaquin District, Fresno
dsjlrehlu:landfilVrehlk&dl1999/wdrlkdnphcl.doc
California Environmental Protection Agency
o Recycled Paper
"
NOTICE OF PUBLIC IlilWUNG
K&DSALVAGELANDftfL
KERN COUNTY
-2-
e
Kern County Department of Environmental Health Services, Bakersfield
Kern County Department of Planning and Development Services, Bakersfield
Kern County Air Pollution Control District, Bakersfield
Kern County Water Agency, Bakersfield
Mr. Howard Wines, City of Bakersfield, BakersfièIct..¡
dsj/rehlu:landfiWrehlk&dlI 999/wdrlkdnphcl,doc
California Environmental Protection Agency
Recycled Paper
23 March 1999
e
e
CALIFORNIA REGIONAL WATER QUALITY CONTROL BOARD
CENTRAL V ALLEY REGION
3614 E. Ashlan Avenue
Fresno, California 93726
NOTICE OF PUBUC MEETING
and
Notice of Consideration of Waste Discharge Requirements
for
NATHAN DANIELS, ROBERTA DANIELS, et al.
FOR
POST -CLOSURE MAINTENANCE OF
K&D SALVAGE COMPANY SOLID WASTE LANDFILL
KERN COUNTY
Nathan Daniels, Roberta Daniels, et al. own a solid waste landfill approximately three miles southeast of
downtown Bakersfield. The existing 24-acre facility contains one 8-acre unlined waste management unit
that received nonhazardous and inert solid waste from 1968 to 1974. These updated waste discharge
requirements require post-closure maintenance of the facility in accordance with the provisions of
Division 7 of the California Water Code.
A public meeting concerning this matter will be held as follows:
DATE:
Friday, 11 June 1999
TIME:
9:00 a.m.
PLACE:
City Council Chambers
1313 California Street
Redding, California
Persons who want to submit written comment or evidence on this item must provide such written
documents so that they are received at this Regional Board office by 5 May 1999. Written documents
may be submitted by fax to (559) 445-5910, but it is the responsibility of the commenter to ensure that
the documents are received by the deadline. Comments received by this deadline will be included in the
administrative record before the Board. Staff may provide responses to the comments. Written
testimony or comments submitted after the noticed deadline will not be accepted and not incorporated
into the administrative record unless allowed by the Board Chair, based on extreme hardship or unusual
circumstances.
All interested persons may speak at the Board meeting, and may orally summarize their written
submittals. Oral testimony at the Board meeting will be limited in time by the board Chair (typically not
more than 15 minutes for dischargers and 3 minutes for other interested parties). Oral testimony must be
relevant. Groups of speakers will be expected to select a spokesperson and not be repetitive.
¡¡
Notice of Public Meeting e
e
Copies of the proposed requirements and related documents are available for review and may be
obtained from the Regional Board office on weekdays, between 8:00 AM and 5:00 PM. Anyone having
questions regarding these requirements should contact Ronald Holcomb at (559) 445-6050.
0~~
Wll...LIAM F. PFISTER
Supervising Engineering Geologist
CEG No. 931
Dated: 23 March 1998
~ CaliforniaBegional Water QualitI.. Control Board
~ . _ Central Valley Region.
Wlru¡,ton H. HIckox Steven T. Butler, Acting Chair
S,creÌiJry for
Environmental Fresno Branch Omce
Pr"t"rti"n Internet Address: http://www.lwrcb.ca.gov/-rwqcbS
3614 East Asbian Avenue. fresno. California 93726
Phone (SS9) 44S-S116' FAX (SS9) 44S-S910
@I
--
Gray Davis
Gavemor
Mr. Nathan Daniels
3318 Harmony
Bakersfield,CA 93306
23 March 1999
Mrs. Roberta Daniels
c/o Mr. Marcus Daniels, Agent
408 Quailridge Drive
Bakersfield, CA 93309
NOTICE
TENT A TNE WASTE DISCHARGE REQUIREMENTS
FOR
NATHAN DANIELS, ROBERTA DANIELS, et al.
FOR
POST-CLOSURE MAINTENANCE OF
K&D SALVAGE COMPANY SOLID WASTE LANDFilL
KERN COUNTY
Any comments or recommendations you may have concerning this tentative Order should be submitted
to this office in writing by 5 May 1999 in order that consideration may be given them prior to the
meeting of the Regional Board.
If you have any questions, please call Ronald Holcomb of this office at (559) 445-6050.
~.
DANE S. JOHNS N
Senior Engineering Geologist
CRG No. 4239
Enclosure
cc: U.S. Environmental Protection Agency, Region 9, San Francisco
Ms. Lori Sennitte, Office of Chief Counsel, State Water Resources Control Board, Sacramento
dsj/rehlu :landfilllrehlk&dlI999/wdr/kdtnc\.doc:
California Environmental Protection Agency
o Recycled Paper
TENTATIVE
WASTE DISCHARGE.QUlREMENTS
K&D,SAL V AGE LANiJIlIIILL
KERN COUNTY
-2-
e
23 March 1999
Ms. Elizabeth Haven, Division of Clean Water Programs, State Water Resources Control Board,
Sacramento
California Integrated Waste Management Board, Sacramento
Department of Health Services, Office of Drinking Water, Fresno
Department of Fish and Game, Region IV, Fresno
Department of Water Resources, San Joaquin District, Fresno
Kern County Department of Environmental Health Services, Bakersfield
Kern County Department of Planning and Development Services, Bakersfield
Kern County Air Pollution Control District, Bakersfield
Kern County Water Agency, Bakersfield
Mr. Howard Wines, City of Bakersfield, Bakersfield
dsjlrehlu:landfilllrehlk&.di 1999/wdrlkdnphc1.doc:
California Environmental Protection Agency
Recycled Paper
e
e
CALIFORNIA REGIONAL WATER QUALITY CONTROL BOARD
CENTRAL V ALLEY REGION
ORDER NO.
WASTE DISCHARGE REQUIREMENTS
FOR
NATHAN DANIELS, ROBERT A DANIELS, et al.
FOR
POST-CLOSURE MAINTENANCE OF
K&D SALVAGE COMPANY SOLID WASTE LANDFILL
KERN COUNTY
The California Regional Water Quality Control Board, Central Valley Region, (hereafter Board)
finds that:
1. Nathan Daniels, Roberta Daniels, et al. (hereafter Discharger) own a solid waste landfill
approximately three miles southeast of the downtown area of Bakersfield in Section 5,
T30S, R28E, MDB&M, as shown in Attachment A, which is incorporated herein and
made a part of this Order.
2. The 24-acre facility contains one existing unlined waste management unit covering eight
acres, as shown in Attachment B, which is incorporated herein and made part of this
Order. The facility is identified by Assessor's Parcel Number (APN) 169-150-07.
3. On 23 June 1972, the Board adopted Order No. 72-292, which prescribes waste discharge
requirements for the waste management unit. The facility was classified as a Class ll-2
landfill that accepted nonhazardous and inert solid waste in accordance with the
regulations that were in effect at the time Order No. 72-292 was adopted.
4. The site was utilized from 1968 to 1974 for the disposal of automobile shredder waste by
K&D Salvage Company. The site was not available for public waste disposal.
5. Waste disposal ceased in 1974, prior to the effective dates of Title 23, California Code of
Regulations, §251O et seq. (Chapter 15; 27 November 1984) and Title 27, California
Code of Regulations, §20005 et seq. (Title 27, 18 July 1997). The closure and post-
closure maintenance requirements contained in Chapter 15 and Title 27 are not applicable
to this site.
6. The volume of wastes in the existing waste management unit is approximately 50,000
cubic yards. '
TENT A TIVE
WASTE DISCHARcAEQUIREMENTS e
NATHAN DANIELS~OBERT A DANIELS, et al.
FOR POST-CLOSURE MAINTENANCE OF
K&D SALVAGE COMPANY SOLID WASTE LANDFllL
KERN COUNTY
-2-
SITE DESCRIPTION
7. The facility is in a topographical flat region of the Tulare Lake Hydrologic Basin of the
San Joaquin Valley. The native ground surface elevation is approximately 395 feet above
mean sea level.
8. The waste management facility is on non-marine fluvial deposits of the Kern River
Series. The soils underlying the facility consist of fine-to-coarse-grained sands
interbedded with silts and clays.
9. The hydraulic conductivity of the native soils underlying the waste management unit
range between 1 x 10-5 and 1 x 10-3 centimeters per second.
10. The waste management facility is not within a fault hazard zone. The closest active fault
is the Kern Front Fault approximately 7 miles to the north. Recorded magnitudes of
seismic events along this fault range between 4 and 4.5 on the Richter scale.
11. Land within 1,000 feet of the facility is used for commercial, industrial, and rural
residential purposes.
12. The facility receives an average of 5.75 inches of precipitation per year and has a mean
evaporation of 62.6 inches per year as measured at the Bakersfield Station.
13. The lOO-year, 24-hour precipitation event for the facility is estimated to be 2 inches, as
determined by data furnished by the National Weather Service.
14. The waste management facility is not within a loo-year floodplain based on the Federal
Emergency Management Agency's (FEMA) Aood Insurance Rate Map, Community-
Panel Number 06oo75-1020B, dated 29 September 1986.
15. There are 109 municipal. domestic, industrial, or agricultural groundwater supply wells
within a I-mile radius of the site. No surface springs or other sources of groundwater
supply have been observed.
TENTATIVE
WASTE DISCHAR.QUIREMENTS e
NATHAN DANIELS, ROBERTA DANIELS, et aI.
FOR POST-CLOSURE MAINTENANCE OF
K&D SALVAGE COMPANY SOLID WASTE LANDFILL
KERN COUNTY
-3-
SURFACE AND GROUND WATER CONDITIONS
16. The Board adopted the Water Quality Control Plan for the Tulare Lake Basin, Second
Edition (hereafter Basin Plan) which designates beneficial uses and contains water quality
objectives for all waters of the Basin. This order implements the Basin Plan.
17. Surface drainage is towards the Kern Lake Bed in the Kern Delta Hydrologic Area
(557.10) of the Tulare Lake Basin.
18. The designated beneficial uses of surface waters on the valley floor, as specified in the
Basin Plan, are agricultural supply, industrial service and process supply, contact and
noncontact water recreation, warm fresh water habitat, preservation of rare, threatened
and endangered species, and groundwater recharge.
19. The first encountered groundwater is approximately 170 to 205 feet below the native
ground surface. Groundwater elevations range from 192 feet above mean sea level
(MSL) to 231 feet MSL.
20. Monitoring data indicates that the groundwater is unconfined. The depth to groundwater
fluctuates seasonally as much as 10 feet.
21. The direction of groundwater flow in the immediate vicinity of the site is toward the
southeast. The average groundwater gradient is approximately 0.005 feet per foot.
Groundwater velocity data is not available.
22. Monitoring data indicates that Total Dissolved Solids in background groundwater ranges
from 127 to 375 milligrams per liter (mgll) and Specific Conductance ranges from 215 to
560 micromhos per centimeter (µ/cm). Title 22, California Code of Regulations, §64449
establishes the drinking water Secondary Maximum Contaminant Level for Total
Dissolved Solids as 500 mgll and for Specific Conductance as 900 µ/cm.
23. The designated beneficial uses of the groundwater, as specified inthe Basin Plan, are
domestic and municipal, agricultural, and industrial supply.
WASTE AND SITE CLASSIFICATION
24. The Discharger has disposed of nonprutrescible solid wastes. The wastes are classified as
'nonhazardous solid waste' or 'inert waste' using the criteria set forth in Title 27 for a
Class ill landfill.
TENTATIVE
WASTE DISCHAR.QUIREMENTS e
NATHAN DANIELS, ROBERTA DANIELS. et al.
FOR POST -CLOSURE MAINTENANCE OF
K&D SALVAGE COMPANY SOLID WASTE LANDFILL
KERN COUNTY
-4-
25. The waste management unit may be reclassified as a Class ill landfill for nonhazardous
solid wastes in accordance with the siting criteria of §20260 of Title 27.
GROUNDWATER QUALITY
26. Groundwater monitoring was conducted in October 1990 and November 1991 as part of
the Solid Waste Water Quality Assessment (SWAT) investigation. Groundwater samples
were collected from a monitoring well installed in the southern area of the waste
management unit during October 1990. Background data was gathered from seven water
supply wells located in the vicinity of the site. The closest background well is
approximately 600 feet northeast of the landfill. No construction or water level data was
provided for the background wells.
27. A vadose zone monitoring system was not installed at the site. Vadose zone sampling
was conducted in October 1990 as part of the SW AT investigation. Three soil borings
were drilled through the waste management unit and two additional soil borings were
drilled on the facility outside the waste management unit.
28. Results of the groundwater monitoring detected no organic waste constituents in the on-
site well. Concentrations of inorganic constituents in the on-site well appeared to be
consistent with the background water supply wells.
29. Results of the vadose zone sampling conducted as a part of the SW AT investigation
detected no organic waste constituents. The concentrations of inorganic constituents
detected in vadose zone samples from beneath the waste management unit appeared to be
consistent with those detected in background vadose zone samples.
30. The landf1l1 has been closed for approximately 25 years. There is no evidence of the
presence of waste constituents in the vadose zone or groundwater at concentrations
greater than background levels and the probability of the waste degrading the
groundwater is very low. Therefore, a groundwater monitoring program is not warranted
at this site. .
LANDFILL COVER
31. The landf1ll cover was constructed in accordance with the regulations that were in effect
at the time the landfill stopped receiving waste (California Water Code § 13360). Wastes
are covered by two feet of compacted soil. The waste management unit cover was graded
TENTATIVE
WASTE DISCHARcaEQUIREMENTS . e
NATHAN DANIELS~OBERTA DANIELS, et aI.
FOR POST-CLOSURE MAINTENANCE OF
K&D SALVAGE COMPANY SOLID WASTE LANDFnL
KERN COUNTY
-5-
so that runoff water was channeled to an onsite evaporation pond outside the waste
management unit (see Attachment B).
CEQA CONSIDERATIONS
32. The action to revise waste discharge requirements for this facility is exempt from the
provisions of the California Environmental Quality Act (CEQA), Public Resource Code
§21000, et seq., and the CEQA guidelines, in accordance with Title 14, CCR, §15000, et
seq.
OTHER CONSIDERATIONS
33. These requirements implement the prescriptive standard and performance goals of Title
27, California Code of Regulations, §20005 et seq. (Title 27).
34. These requirements implement the Water Quality Control Plan for the Tulare Lake
Basin, Second Edition, 1995.
35. All local agencies with jurisdiction to regulate land use, solid waste disposal, air
pollution, and protect public health have approved the use of this site for the discharges of
waste to land stated herein.
36. The Board has notified the Discharger and interested agencies and persons of its intention
to update the waste discharge requirements for this facility.
37. In a public hearing, the Board heard and considered all comments pertaining to this
facility and discharge.
IT IS HEREBY ORDERED that Order No. 72-292 is rescinded, and that Nathan Daniels,
Roberta Daniels, et aI., their agents, successors, and assigns, in order to meet the provisions of
Division 7 of the California Water Code and the regulations adopted thereunder, shall comply
with the following:
A. PROHIBITIONS
1. The discharge of waste at this facility is prohibited.
TENTA TIVE
WASTE DISCHAR.QUIREMENTS e
NATHAN DANIELS, ROBERTA DANIELS, et aI.
FOR CLOSURE OF
K&D SALVAGE COMPANY SOLID WASTE LANDFILL
KERN COUNTY
·6-
2. The discharge shall not cause the pollution or degradation of groundwater or surface
water via the release of waste constituents in either liquid or gaseous phase.
3. The discharge shall not cause any increase in the concentration of waste constituents
in soil or other geologic materials outside the waste management unit if such waste
constituents could migrate to waters of the State and cause a condition of degradation,
pollution, or nuisance.
4. The discharge or storage of liquid over the waste is prohibited.
5. The erosion of deposited waste from the waste management unit is prohibited.
B. DISCHARGE SPECIFICATIONS
1. W aste sh~l be confined to the existing waste management unit.
2. A minimum separation of 5 feet shall be maintained between the base of the wastes
and the highest anticipated elevation of underlying groundwater, including the
capillary fringe.
3. Water used for facility maintenance shall be limited to the minimum amount
necessary for dust control and to the minimum amount necessary to irrigate cover
vegetation or for other uses approved by the Executive Officer.
4. Neither the treatment nor the discharge of wastes shall cause a pollution or nuisance
as defmed by the California Water Code, § 13050.
5. The Discharger shall, in a timely manner, remove and relocate any wastes discharged
at this facility in violation of this Order.
C. POST ·CLOSURE MAINTENANCE SPECIFICATIONS
1. Waste management units and containment structures shall be graded and maintained
to limit, to the greatest extent possible, ponding, infiltration, inundation, erosion,
slope failure, washout, overtopping, and divert precipitation from the waste
management unit as a result of a l00-year, 24-hour precipitation event.
2. Precipitation and drainage control systems shall be maintained to accommodate the
TENT A TIVE
WASTE DISCHARceEQUIREMENTS e
NATHAN DANIELS, ROBERTA DANIELS. et al.
FOR CLOSURE OF
K&D SALVAGE COMPANY SOLID WASTE LANDFß...L
KERN COUNTY
-7-
anticipated volume of precipitation and peak flows from surface runoff under the 100-
year. 24-hour precipitation conditions.
3. Cover materials shall be graded to divert precipitation from the waste management
unit, to prevent ponding of surface water over wastes, and to resist erosion.
4. The waste management unit shall be maintained in compliance with precipitation and
flood conditions contained in the Standard Provisions and Reporting Requirements
referenced in Provision D.I below.
5. All drainage control systems shall be maintained to prevent the ponding of water
above wastes.
6. Surface drainage from tributary areas and internal site drainage from surface or
subsurface sources shall not contact or percolate through wastes.
7. Areas with slopes greater than ten percent, surface drainage courses. and areas subject
to erosion by wind or water shall be maintained to prevent such erosion.
8. Annually, prior to 1 October of each year. the Discharger shall conduct an inspection
of the waste management unit cover. By 31 October of each year. any necessary
construction, or repairs of the waste management unit cover shall be completed to
limit, to the greatest extent possible. ponding. infiltration, inundation, erosion. slope
failure, washout, overtopping. and divert precipitation from the waste management
unit.
9. By IS November of each year, the Discharger shall submit a report to the Board
describing the results of the inspection(s) and measures taken to maintain the waste
management unit cover.
10. Annually, prior to 1 October and within 7 days following a major storm event, the
Discharger shall conduct an inspection of the facility. All precipitation and drainage
control systems shall be inspected and standard observations made in accordance with
Definition 24 of the Standard Provisions and Reporting Requirements referenced in
Provision D.2 below.
11. By 31 October of each year, or within 30 days of a major storm event. any necessary
construction, maintenance, or repairs of precipitation and drainage control facilities
shall be completed to prevent erosion or flooding of the facility and to prevent surface
drainage from contacting or percolating through wastes.
TENTATIVE
WASTE DISCHAR.QUIREMENTS e
NÀ THAN DANIELS, ROBERT A DANIELS. et al.
FOR CLOSURE OF
K&D SALVAGE COMPANY SOLID WASTE LANDFILL
KERN COUNTY
-8-
12. By 15 November of each year. or within 45 days of a major storm event. the
Discharger shall submit a report to the Board describing the results of the
inspection(s) and standard observations, and the measures taken to maintain the
precipitation and drainage control systems.
13. The Discharger shall immediately notify the Board of any flooding. unpermitted off-
site discharge. equipment failure, slope (ailure. or other change in site conditions
which could impair the integrity of waste containment facilities or precipitation and
drainage control structures.
D. PROVISIONS
I. The Discharger shall comply with the applicable portions of the Standard Provisions
and Reporting Requirements dated August 1997, which are hereby incorporated into
this Order.
2. A violation of any of the applicable portions of the Standard Provisions and Reporting
Requirements is a violation of these waste discharge requirements.
3. The Discharger shall have the continuing responsibility to assure the protection of the
beneficial uses of ground and surface waters from gases and leachate generated by
discharged waste during the post-closure maintenance period of the waste
management unit and during the subsequent use of the property for other purposes. .
4. In the event of any change in control or ownership of the land or waste discharge
facilities described herein, the Discharger shall notify the succeeding owner or
operator of the existence of this Order by letter, a copy of which shall be immediately
forwarded to this office.
5. To assume operation under this Order, the succeeding owner or operator must apply
in writing to the Board requesting transfer of the Order within 14 days of assuming
ownership or operation of this facility. The request must contain the requesting
entity's full legal name, the State of incorporation if a corporation, the name and
address and telephone number of the persons responsible for contact with the Board,
and a statement. The statement shall comply with the signatory requirements
contained in Reporting Requirements No. 5 of the Standard Provisions and Reporting
Requirements and state that the new owner or operator assumes full responsibility for
compliance with this Order. Failure to submit the request shall be considered a
discharge without requirements, a violation of the California Water Code. Transfer
shall be approved or disapproved by the Board.
TENT A TIVE
WASTE DISCHAR.QUIREMENTS e
NÀTHAN DANIELS, ROBERTA DANIELS, et aI.
FOR CLOSURE OF
K&D SALVAGE COMPANY SOLID WASTE LANDFILL
KERN COUNTY
-9-
6. The Discharger shall notify the Board in writing of any proposed change in ownership
or responsibility for construction or operation of the waste management unit. The
Discharger shall also notify the Board of a material change in the character,location
or volume of the waste discharge and of any proposed expansions or closure plans.
This notification shall be given 90 days prior to the effective date of the change and
shall þe accompanied by an amended Report of Waste Discharge and any technical
documents that are needed to demonstrate continued compliance with these waste
discharge requirements.
7. The Discharger shall, by 30 April of each year, submit for approval by the Executive
Officer, plans with detailed cost estimates and a demonstration of assurances of
financial responsibility for initiating and completing corrective action for all known
and reasonably foreseeable releases from the waste management unit. The Discharger
shall provide the assurances of financial responsibility to the Executive Officer. The
assurances of financial responsibility shall provide that funds for corrective action
shall be available to the Regional Board upon the issuance of any order under
California Water Code, Division 7, Chapter 5. The Discharger shall adjust the cost
annually to account for inflation and any changes in facility design or construction.
8. The Discharger shall, by 30 April of each year, submit for approval by the Executive
Officer, a demonstration of assurances of financial responsibility to ensure post-
closure maintenance of the waste management unit in accordance with its approved
closure and post-closure maintenance plans. The Discharger shall provide the
assurances of financial responsibility to the Executive Officer. The assurances of
financial responsibility shall provide that funds for closure and post-closure
maintenance with respect to water quality shall be available to the Regional Board
upon the issuance of any order under California Water Code, Division 7, Chapter 5.
The Discharger shall adjust the cost annually to account for inflation and any changes
in facility design or construction.
9. If a single mechanism of financial assurance is used for both corrective action and
closure and post-closure maintenance, the financial assurance must be sufficient for
both requirements.
10. The Board will review this Order periodically and will revise these waste discharge
requirements when necessary.
TENTATIVE
WASTE DISCHAR.EQUIREMENTS e
NATHAN DANIELS. ROBERTA DANIELS. et al.
FOR CLOSURE OF
K&D SALVAGE COMPANY SOLID WASTE LANDFll..L
KERN COUNTY
-10-
11. The Discharger shall complete the tasks contained in these waste discharge
requirements in accordance wi~ the following time schedule:
Task
(a) Inspection Report of Waste Management
Unit Cover
Submit a report to the Board describing
the results of the inspection(s) and the measures
taken to maintain the waste management unit
cover.
(Post-Closure Maintenance Specification C.8)
(b) Inspection Report of Precipitation and
Drainage Control Systems
Submit a report to the Board describing the
results of the inspection(s) and the measures
taken to maintain the precipitation and drainage
control systems.
(post-Closure Maintenance Specification C.9)
(c) Financial Assurances for Corrective Action
Submit an annual status report regarding the
financial assurances for corrective action.
(Provision C.9)
(d) Financial Assurances for Post-Closure
Maintenance
Submit an annual status report regarding the
financial assurances for post-closure maintenance.
(Provision C.l 0)
TENTA TIVE
Compliance Date
By 15 November of
each year
By 15 November of
each year or within
45 days of a major
storm event
By 30 April each
year
By 30 April each
year
W ASTE DISCHAR~QUIREMENTS e
NATHAN DANIELS. ROBERTA DANIELS. et al.
FOR CLOSURE OF
K&D SALVAGE COMPANY SOLID WASTE LANDFll..L
KERN COUNTY
-11-
I, GARY M. CARLTON, Executive Officer. do hereby certify that the foregoing is a full, true,
and correct copy of an Order adopted by the California Regional Water Quality Control Board,
Central Valley Region, on
GARY M. CARLTON, Executive Officer
_: _1_/97
Attachments
TENTA TIVE
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EXPLANATION
ATTACHMENT A
c:J Waste Manag~ Facility Boundary
FACILllY LOCATION MAP
J
2,200 FEET
,
N
K&D SAlVAGE SOLID WASTE LANDFILL
SCALE: 1"'"2,200'
1__
~--
o 1,100
NATHAN DANIELS, ROBERTA DANIELS, et III.
IOUItCE: USGS LAMONT, CA 7.1...un TOPOGRAPHIC~
S.P.R.R. TRACKS
-.-.-.-.-.-.-.-.-.-.---.-.-.-.
,
\
DANIELS LANE
./
./
/
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./.
./
./
,/
EXPLANATION
ATTACHMENT B
WASTE MANAGEMENT UNIT
,
N
STORMWATER EVAPORATION POND
IIW
.
SITE MAP
GROUNDWATER MONITORING WELL
SCALE: 1"-300'
10.1""_-_
o 150
K&D SALVAGE
SOLID WASTE lANDFILL
NATHAN DANIELS, ROBERTA DANIELS, et 81
I
300 FEET
(REH 3/2199)
· e
INFORMATION SHEET
WASTE DISCHARGE REQUIREMENTS
NATHAN DANIELS, ROBERTA DANIELS, et al.
K&D SALVAGE COMPANY SOLID WASTE LANDFll..L
KERN COUNTY
The K&D Salvage Company Solid Waste Landfill is approximately three miles southeast of the
downtown area of Bakersfield in Section 5, T30S, R28E, MDB&M. The 24-acre facility is owned and
maintained by Nathan Daniels and Roberta Daniels, et aI. (Discharger) and includes one 8-acre unlined
waste management unit that contains approximately 50,000 cubic yards of waste. The landfill stopped
receiving waste in 1974. The facility was classified as a Class ll-2landfill that accepted nonhazardous
and inert solid waste in accordance with the regulations that were in effect at the time that Order No. 72-
292 was adopted.
Surface drainage is towards the Kern Lake Bed in the Kern Delta Hydrologic Area (557.10) of the Tulare
Lake Basin.
Monitoring data indicates that groundwater is unconfined. The first encountered groundwater is
approximately 170 to 205 feet below the native ground surface. Monitoring data indicates that Total
Dissolved Solids in background groundwater ranges from 127 to 375 milligrams per liter and Specific
Conductance ranges from 215 to 560 micromhos per centimeter.
The landfill has been closed for approximately 25 years. There is no evidence of vadose zone or
groundwater degradation. Groundwater sampling has not detected volatile organic compounds and the
concentrations of inorganic constituents in the onsite monitoring well appear to be consistent with
background concentrations in the upgradient well. The probability of the waste degrading the
groundwater is very low; therefore, a groundwater monitoring program is not warranted at this site.
This Order updates the waste discharge requirements for post-closure maintenance and annual
monitoring of the waste management facility.
TENTATIVE
~!
FROM : CRWQC - Central v~ Region
TEL: 209 445 5910
-
MAR. 8.1999 10:41 AM
P 1
-
,
IFAX
I Date
03/08199
I Number of pages InelL/ding cover sheet 1
TO:
Howard Wines
City of Bakersfield
FROM:
Ron Holcomb ~
RWQCB Central Valley
Region
3614 East Ash/an Avenue
Fresno, CA 93726
Phone
Fax Phone
Phone
Fax Phone
(559) 445·6050
559 445-5910
I CC:
REMARKS: 0 Urgent 181 For your review 0 Reply ASAP 0 Please Comment
Attached are tables listing analytical results of groundwater sampling at the K&D Salvage
Company Solid Waste Disposal Facility In Bakersfield. Also attached is a location map showing
the monitoring well on the subject property and a well construction diagram.
Please notice that groundwater analytical data for a CWS well in the vicinity of the site was also
included, Sample analyses from CWS Well No. 133-01 were used for background groundwater
quality data.
Do not hesitate to call if you have any questions.
FROM : CRWQC - Central vaJllr Region
TEL: 209 445 5910
4IÞ MAR. 8.1999 10:42 AM P 2
.-. ----------
--....---------.
DANIELS
LANE
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Ce~ ¡I Eng ¡neer ing) Inc.
K&D SALVAGE LANDFILL
MONITOR WELL
........ "u .,.... , ..,...,. _ .. /"'., In·,
FROM : CRWQC - Central uaJìlÞ~ Region
'.
TEL: 209 445 5910
4IÞ MAR. 8.1999 10:42 AM P 3
CO~RETE 9..AB 8-5/8" WNLMENf
With Lock Cap
3 IX 3 IX 611
o 1-19 ': Sa1:I. crs orn ,/
œøt-ølt ana shredded
f ¡ber . wood t nJber
II '-36 ': Sad. crs..f/1 gm.
slty. 'I pebbles
36 '-51': Sad, IIId-fn gm.
. slUy sHy
51'-71': Scn1. rItId grn
71'-91': Sad, fn1ed gm
91 '-111 I: Sard. rœd grn
11' '-131 I: Sad, crs-fn grn.
tre silt
\31'-171 ': Scni.lJted-fn ~.
tn: sit.
boulder' 171'
171 '-1U ': ~. ers,
slty a: cly
'S3 '.2M ': CIØ.f ,/ as sbrd
20J '-206 ': Sad. crs-tlCd grn
GROUND LEVEL
4" nan I'VC PIPE
(4-1/211 od) Sch 40
Landed at 206 I
w/ bull plug on bottom
111 cub ic feet CÐ.ENT GROUf
I 64- sx AP I C I ass A Cement
1886 Hi Yield Benton ita
and Potable Water
pran ¡xed at 13 .51/gollon
(16,; excess)
frcm 174 I to Surface
II~
BENTON ITE SEAL 174 1-178 I
FILTER PAa<
8-20 Mesh Sand
fi II 1781-206'
1961
O.020IlX 2" Slots
~
DR ILLED ~E
, 11" d ianeter
Total Depth
206'
Cec i I Eng ineer ing, Inc.
K&D LANDF ILL SNA T
GMN-1 PROF I LE
StJJ.E VERT: 1"=30'
lI"ð I~. 11"'C:" NTC'· a/"Ft/r/I
TEL: 209 445 5910
.
P 4
~
FROM :CRWQC.~ Central va~ Region
E/iV/lfØNMENTAL
CHEMICAL ~NALrslS
PETROLEUM
MAR. 8.1999 10:43 AM
LABORATORIES. INC.
J. J. co'",". AIIO. CH!M. EtIOR.
4100 ATLAS CT., BAKERSFIELD, CALIFORNIA 93308 PHONE (808) 327-4811 FAX (80S) 321.1818
1601 "H" Street Bakersfield, CA 93301
cecil Engineering
'ate of Report: 10-15-99
r..aboratory
~ame: B C Laboratories
~ame of
;ampler:
'at.e/Time Sample
:o11ected: 10-3-90
rest Methods:
PURGEABL! ORGANIC ANALYSIS
(Volatiles)
EPA
Lab Sample ID
Signature Lab
Director
Sampler
Employed By:
Date/Time Sample Were Holding
Received ø Lab: 10-4-90 Times Observed? YES
Were all the Constituents listed
601/~9~ below quantified? YES
____~__-__-_--------a---.---øa---a----------------
System
Number:
No. 8691-"
J)cu.., W,.A" a. ("
/
..DD___a________~__
;ystem
lame:
>eacription of
¡Ðmplinq Point: ___
lame/No. Of Sample
iourc::e:
)ate &
~iJne of
:ample:
County Name:
station
Number:
. I_'_I_ILI_I_I_I..:..'_I_'_I_I_I_'_'
1_'_1_'_1_1_1_'_'_1_'
Y Y M H D D T T T T
User' I I' I
---
IC:
SUbmitted to SWQIS
By:
W~ter 1 ,
Type GIS
)lace an "XU in box to delete all data tor this station/date/time 1=1
REPORTINGICONSTITUENT
!lNITS I
, ,
Q~te Apalvsis ComDleted
Jer/L
Jq[{¡
Jg/L
Jg/tt
JaIL
..JaiL
J5Itt.
Jq/tI
JaIL
Jc:r/L
J.cr/L
Jc:;/L
Jc:r/L
JaiL
AnalyzinQ Acencv Code (Lab)
Intensive Survey ~~~ber
e§O;~ne
Bt:OJ'ftodichloromethac!
Brornofor~
Bromometlu~n~
Carbon ~etrachloriåe
Ch19J;obenzene
chloroetb~ne
2-Chloro~~þvlvinv1 ether
Ch1orofor1,!l
Chloromethane
p~bromochloromethane
li2-C1chlor~~,nzene
~,3-Diohlorobenz8ne
1.4-Dichlorobenz,ne
ITI STORETI ANALYSIS 1 DETECTION
I.I.I CODE 1 RESULTS I LIMIT
I 'I I ,
, I '..2..1..ºJ..1J...2J..2.1~'_'_I_I_I_I_1
,-, I Y Y M M D C I, I
I_I 1 " 1
'_' ,_I..~..I..§).,QJ.§..J_'_I_I_I_I_I_'
, I I I 1 I , I I I , I I , I
1=1 340~Q 1=1=(iÐ])='=I=,=,:Q:CII(Q)
I I 32101 1_1_lli'J2.'_I_I_'_'..º.J..:-'_~J.Q;.I
I_I 32104 1_'_llLlJ;L'_I_I_I_I.Q..I_t-'..~..I..Q.I
I_I 34413 '_'_llil.l2.I_I_I_I_I.Q.I..,.J.2J.Q.1
I I 32102 1_1_lliIj2J_I_I_I_I..QJ..&..I.~J..Q)
1=1 34301 1_1_lliJ..Q.I_'_I_I_I.Q.J...~.JáJJ2.I
I I 34311 1_1_1J!1J2.1_1_'_I_I.2J_&..I~..I...QJ
1=' 345' 6 '_I_llf..lJ2J_I_I_'_I~I""",I~'.Q.1
1 , 32106 '_I_'li.I~I_I_I_I_I..Q.I""",I~I.Q.1
I-I 34418 1_'_lli'j¡I_I_I_I_I..Q.I""",'.1.I.Q.1
I-I 321Q~ '_I_llLlJ2.I_I_I_I_I"p"'I..,-'.~..I.9.1
I-I 34536 1_1_llilJ2.I_I_t_I_I..Q.I-,-I~I.2.1
I-I 34566 '_'_llLlJ2.I_I_I_'_I.Q)""",I.å.I..Q.1
1=1 3'4571 1_1_1.tL1.l2.'_'_I_I_I..Q.I""",I.1.I.Q..'
" FROM : ,.CRWQC ,~ Central val. Region
TEL: 209 445 5910
.
MAR. 8.1999 10:43 AM
P 5
'.
INYIRONMENTAL
CHEMlCAlA/iALTSIS LABORATORIES, INC.
PETROLEUM J. J. IOUH, AIO. CHIM. ¡NOR.
purgeable Organic Analysf¿OO (C~If~"4ä'RSFIELD, CALIFORNIA 93308 PHONE (805) 327·4911 FAX (805) 327·1911
Lab #:8691-1 (Cant.)
SYSTEM NAME & NUMBER
I REPORTING! CONSTITUENT
I UNITS I
1- µ~/L Ipichlorodifluoromethane
IJa/L I ¡., :¡'-Dichloroethane (L I-DCA)
l--Pq/L Il,2-DichloroetbDn, (l,2-DCA)
IJ9!L Il.l-Dichloroethene (1 t 1-PÇ~)
I µ3/~ Itrans-l,2-Dichloroethene
1--µqJ~ Il.2-D,ichloroorooane
I~~q/L cis-l,3-DichlorODrocene
I--Ya/L t~~ns-l,3-D1chlorQD~9cene
I IJa/L ~thYl Benz~De
I--yg/~ Methy~ene chloride
1--y~/L !,lß2.2-Tetrachlç~oethane
l--Ya/L Tetrachloroethane (PCE)
IJ~/L Tolu~ne
'--lalt 1,l,l-Trich~9rgethane
'--ya/L ~,1,2-Tri9þloroethane
I--Yq/L Trich~9roethQnQ (TÇE)
'--YqLL Tricþlorofluoromethane
IJa/L VinYl chloride
'IJg,(L xvlen~s
l--Ya/L Total Trihalo~,thanes
California D.O.H.S. Cart. #1186
ITI STORETI ANALYSIS I DETECTION I
I~' CODE I RESULT~ I LIMIT I
I_I 346 68 1_1_lliJ~I_'_I_I_I..Q..I...t.J..2.1Jl.1
I I 34496 1_1_lli.lJ2J_I_I_I_IJl.'-:.J..~..I..2J
I-I 34511 1_1_1l:!.I..Q.I_I_I_I_ljtl...-I.ã,I-º-1
I-I 34501 1_1_1J:!.1..Q.1_1_1_'_I.2..'-:..'i'..Q..1
I-I 34546 1_1_ll:I..l..Q.I_I_I_I_I..Q..I~I~I..2.1
1"':"""1 34 54 ~ 1_'_'£I..Q.I_I_I_'_'..Q.I..:,..'.20I..Q..1
1=1 347 04 '_I_llf.l..Q.'_'_'_I_I.2.I...t...I~U~J
I_I ,~4699 1_1_llil.g.I_I_I_'_I~I...s-'.ã.I..s2.1
I_I 3437 + 1_1_1 JiJ..Q..I_I_I_I_I..Q.I..:..'.,iI.2..1
I_I 344~~ 1_1_1li.1'p'1_1_1_1_1~1..J.1.2J..QJ
I_' 3451 Õ 1:-1_I.H.I..Q.I_I_I_I_I..Q..I..:-'..2J~1
I_I 3447~ 1_1_llil.!2.I_I_I_I_I..Q.I..:...I~I..QJ
I_I 34010 1_1....JB.I.I2.I_'_I_I_I..Q..I...lil.Q.1
I_I 34506 1_1_IJiJJ2J_I_I_I_'J2..I..:...I~1.2J
I_I 345 t 1 1_1_lJiJ.g.I_I_I_I_'.2..I..I~I..Q..1
I_I ,39~80 1_1_llil..Q.'_I_I_I_I..QJ..:..t.20I.Q.I
I_I 344 88 1_'_ljiJ.Q.I_I~I_I':""1J2..1...:..J..2.1.2..1
I_I 3 91 7 ~ 1_1_lliJJ2..I_I..:....I_I_I...Q.I...I~.I..Q.I
I_I 81551 1_1_I,.N.I..Q.J_I_I_1_ljtl..,.J.2.1..Q.I
'_I 820~Q 1_1_1.1i.1J2.1_1_1_1_1~1...a..1~1..Q..1
~ote any unidentified Qea~~ below.
rOTE ND - NONE DETECTED
r
I
I
I
TABLE A.. WATER GEOCHEM1STRY.
TOIaJ CaIc:iIUIa a.c.p.. ..Sod-. ,.... Tca1 TGIaI .... WfIfa 0ai0riIk NÍIRf& F'-* TaAI Caed. SaiidI TIØI W".
\D Hacd.. CA MG NA Ie. CaIiœs AIIIaL HCOJ SCM CL NO) F Aaiœs pH EC TÐS w-k Typo II
a.. JII&II mall ~ ~
:E
CI
-.;r
-.;r
(S)
<M
0"\ UW\-t, * '51 0 4S 13 10 482 eo 35 . 8 ·0 11 \2 2300 610 3841 HCœ-tMGH
0"\ MW1-9C1 III 590 tIT 214 80 III 111 III r¡r IV nr nr ft( 7.8 nr ØI 13352 HC03-HJGK
0"\
<M
CD TABLE B. WATER- HEAVY METALS.
ÅIIÎIII. ~ 8Irña 8ctyI. c.d.. 011-. CabW Cappel bœ Lca4 Wuaa Wuaay )4aIyb. N"1CIrcl Sdra- sa- T\aIIiKa v..... 2iDc Aba
SB AS SA BE CD ca. Co cu FE PI MN HG Yo Ni SE AG n Va ZN AI.
.." D&J' aan II ^ DJI1 V3II aaJI JIll' val'
(S)
<M
0"\
It)
It) -t1 0
:! '1IW1-tO 0
0"\
(S)
N
.. 'WEU.
mGROUP
I-
c.u.
.~~P1
~ 3AOUP2
a::~A0UP3
.-11
:> 4W1-tO
I'll
~
+'
C
II
U
I
U
~
a::
u
:E
o
a::
lJ...
7 0 4'0 0 185 3DOO 0 71 0 0 0 0 0 0 0 176 0
6 801 0 nr 60 0 704 9580 ,- m ... 0 S5 fill ,., 0 0 554 ...
TABLE C. WATER- CATION/ANION EQUIVALENTS. TABLE7D. TERNARY PROPORTIONS.
CMÏI:IaI ...... SocIiam .... Teal s.öte Cb)ariðo ~ Auariðt: T4Id Totd Cak:àD Mat- Wt-Poe. BØb. ~ 0II0ridc
CA NCi NA K c.õc. ØC03 S04 a. NOJ f AÜQIø BtStC CA JdG NA..X øem S(M CL
æeqII meçJI mcqIJ -.4 IDÞVI seqA IIIDCIII ~
5.2
7..
0.0
a.o
7..9
2.1
0.14 0.10
0.77 0.00
0.25
0..23
0-25
0.61
o.5fì
0..34
0-\9
0.Q5
1.5
0.1
Q.2
G.1
8.1
2.3
G..
0.0
1.9
2.0
0.'
G.!
...
10.'
1.t
U
....
0.7
..,.
\"AL!t'VNrtll\ VVI\ I en .;;)cnv,\.I1;;. \.IVIVU nn. .-),- .,.-- \ J ..
BAKERSFIELD, CALIFORNiA -'-.. ;..........'
-l '
I"-
a..
\"ÆU. SoWI'lE M Sa Cd Cr eM F. Pb Ma Ho Se As ZA AI . P , fa U
E STATION DATE JAJIL moIL mgIL mgIl. mgA. IftØIl moIL moil meIL JIIOI\. mgIL mgA. tngII.. m¡IL. m¡IL ~ maJl. JI'oGIL
<I -
'<:t ~, O9I09Iaa <0.05 <0.05 <0.05 <0..05 24 0.08 0.061
'<:t 17-41 03I2:9t..
G;) 16-01 03l2Il11
~
I8-Ot G3t28IN
(J\ ao-o 1 1:l1'"'' II <0.0, 0.041
(J\
(J\ 82-4 , 03t28IU
~
13-01 03l2III8O <6 t» <I < I <¡o <.50 c; to <2 < , <2 < t <50 2& G..04 o.ou
CD
84-41 03t2aIU <, 50 <I <. 1 <50 <50 < iO 2110 < t <2 < 1 <50 2t U2 0.G38
0:: I5-4t 03I2IIIM CIO 130 <1 < 10 <50 <50 < $0 <30 < 1 <, <10 <50 30 0.03 0.013
<I 81~1 03t2II&I <$ <50 70 ~ <1 < I <50 II O.OG 0. 178
E UiIO <\ <. I < 10 < 1
8&-01 0312116t
e~1 03l28I8l
01-41 ~ <, 110 < , <: t ~ ,~ 13 <2 < 1 <2 < I 80 30 0.G2 0.013
102-41 03I2Mt <$ I. <1 < \ eo ~ <.0 <2 <1 <2 < 1 130 :rl om ð..ooa
'œ-ol 11118115
G;) 105-41 01I2IIa <f <50 <I < 1 <50 <:50 <10 <2 < . <2 < I <60 41 QJI4 o.ou
~
(J\ I~t 03I2IIIIa <, <50 <I < I <50 <50 <10 <2 < 1 <2 < 1 <50 .e 0.06 0.012
I/)
I07~1 03t2IIM <5 110 <I < I <50 <50 <10 70 < 1 <2 < 1 <50 .a 0.0. 0.O:D
I/)
'<:t 110-01 ØII05II5 17 G...OIiI 0.051
'<:t- <50 o..cø 4.055
...-41 03I2aIU <5 <50 <t < I <50 <50 < 10 <2 < 1 <2 < , II
(J\ 112-41 CMlt" <5 150 <50 <50 < '0 <1 < 1 <2 < I <$0 36 o..cø 0.011
G;) <1 < 1
N 1~1 CMltW66 <10 no < . * <50 17 <2 <. 1 <2 < I <50 32 0..G2 o.ooe
< I
....J n4-41 04/tMl <to <100 <I <10 <so 110 <\0 <30 <1 <5 <'0 <50 43 Q.44 O.GOI
W na-e. WI"
I-
n~1 ~ o.o¡ <0.02 401 <0.0 I 30 o.œ 6.020
C I2D-OI CMltftIM
0 121-41 CMlI_ <5 130 <I < 1 <!O 100 <10 70 < 1 <'2 < t <50 It om 0.D:22
(11 12:).41 0411.. <I 130 <, < , <50 <50 <60 <2 < I <2 < I <50 211 o.cø 0.008
tI
0:: 1211-41 CMW5II5
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FAX No. (805) 326-0576 · Bus No. (805) 326-3979
1715 Chester Ave. · Bakersfield, CA 93301
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03/05/99
16:16
'5'805 326 0576
BFD HAZ MAT DIV
~001
e
e
***************************
*** ACTIVITY REPORT ***
***************************
TRANSMISSION OK
TX/RX NO.
CONNECTION TEL
CONNECTION ID
START TIME
USAGE TIME
PAGES
RESULT
0650
19162553696
03/05 16:15
01'20
2
OK
Acres
KEY DATA PROHPT
P22241
Roll 1 Use Code 3100
AG Presy NO
CPest
BPS SO 5 UF NT
NEXT-FUNC:
KIPS #ROllINQ
ATN 169 140 02 00 7
File No 19nd
APN 169 140 02 7 19l S 5 T 30 R 28
SITE 340 DANIELS lN BAKERSFIELD
Ouner DANIELS NATHAN TR ET Al
tþ Bill 2609 "OFFITT ~Y BAKERSFIELD CA 93309
R.B.P. 99 98-1107538-00-2
001 409 001 409
KEY:
SECURED ROll INQUIRY
ACTIVE
Doc
TRA-No
CHG DT
Chg Type
"ineral
land/PI
Impryment
e Other Imp
Pers Prop
Exmp Amt
Net Value
97-1107114-00-5
001 409
22,221
18 ,470
21,786
18 , 1 08
21,359
17,753
40,691
39,894
39 , 112
PFI=HElP 2="ENU 3=RTRN 4=TOG 5=FUTR 9=BIll 10=UFl 11=BUS 12=EVTSEl
PF13=NE~ 14=APN HIST 15=O~NERS 16=EXEHPT 17=SUPPl 18=ADDR 19=ROll CORR
PF20=PREV YR 21=NEXT YEAR 22=PRT 23=NEXT 24=PREV 03/05/99 09:37
MAR-04-1999 11:35
DTSC CROYDON OFFICE
916 255 3697 P.01/04
DA 1'£:
TELECOPIER MESSAGE
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I
-
DEPARTMENT OF
TOXIC SUBSTANCES CONTROL
101S1 CROYDON WAY. SUITE 3
SACRAMENTO. CA.I..IFOR.N1A 95827-2106
(916)':55-3545
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MAR-04-1999 11:35
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DTSC CROYDON OFFICE
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916 255 3697 P.02/04
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GORE-SORBER~ Screening Survey
Final Report
· QA/QC trip blank modules were provided to document contamination occurring that was not part of
the soil gas signal of interest (i.e., impact during module shipment, installation and retrieval. and
storage). The trip blanks are identically manufactured and packaged soil gas modules to those
modules placed in the subsurface. However, the trip blanks remain unopened during all phases of
the soil gas survey. Levels reported on the trip blanks may indicate potential impact to modules
other tha.n the contaminant source of interest.
· Unresolved peak envelopes (UPEs) are represented as a series of compound peaks clustered together
around a central GC elution time in the total ion chromatogram. Typical1y, UPEs are indicative of
complex. fluid mixtures that are present in the subsurface. UPEs observed early in the
chromatogram are considered to indicate the presence of more volatile fluids, while UPEs observed
later in the chromatogram may indicate the presence of less volatile fluids. Multiple UPEs may,
indicate the presence ofmultÎple complex fluids. Attenuation of the VOC/SVOC soil gas
components may suggest the presence of a less volatile fluid, when in fact, a more volatile fluid
existed but the volatile components have weathered away.
Project Specific: Comments:
· The minimum (gray) contour level, for each mapped analÝ'te or group of analytes, was set at the
maximum blank level observed or the method detection limit, whichever was greater. The
maximum c:ontour-level was set at the maximum value observed.
· Stacked total ion chromatograms (TICs) are included in Appendix A. TI1e last four digits of each
module number are incòrporated into the TIC identification (e.g.: A VZ2563TC.D represents module
#172563).
· Nominal trip blank levels were reported for some target analytes. No detectable levels of target
analytes were reported in the method blanks.nn our experience, TPH present in the blanks at these
, low levels can be considered «background:' Thus, target analyt:e levels, reported for the field-
installed modules, that exceed trip and method blank levels, have a high probability of originating
from on-site sources.
. The mapped spatial patterns for those compounds selected for mapping, were composed of
continuous and isolated soil gas plumes. However, for th~etrOleum-related compounds, elevaTfI'd,..
levels fonnins defined plum~ were apparent in the southwest corner of the area sampled. BTEX
was also observed to be widely distributed in the eastern half of the area sampled; however, these
mass levels were tow. PCE was observed in four distinct areas where elevated soil gas mass levels
~ ~,
defined soil ~as ~Iumes.
· -,;wo PCB c:o~ners (di- and trichlorobiphenyl) were detected at module # 172468 (C 19) at levels
'~above the method detection limit, and trichlorobiphenyl was detected at module locations #172477
(CI~ and -489 (£16) although the levels were below the method detection level. The spatial
relationship of these sampling locations suggests that it may be prudent to evaluate further the
. extent of the PCBs around the '.·Crushing Area.t '
. At some locations, the soil gas plumes appear to extend into areas of the site that were not sampled
for soil gas. Ifthe objective of the soil gas survey was to delineate the narore and extent ofthe
conbmination. then additional soil gas sampling is recommended in those areas. Subsequent soil
gas sampling events can be combined onto one set of maps providing increased resolution oftbe
subsurface impact.
CiORE·SORBER is a ~gis(et'ed trademm. ofW. L. Gore &: Associarcs, Inc:.
FORM IJ Jt3
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'HO . ..__ "__."_"H'"
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MRR-04-1999 11:36
DTSC CROYDON OFFICE
916 255 3697 P.03/04
e
.
, ATrACHMENTC
RESULTS OF PREVIOUS SITE INVESTIGATIONS
Table c:-l AnaJ~caJ results of~il samples coIJected by DTSC on August 15, 1990 at the K&D
SaI S'
.' vaile ltc.
Contaminant mglkg Threshold (TTLC)
Copper .' . 4.430 2,500
Lead " 5,170 1,000
linc , 16.400 5,000
Table C-2' Results of soil sample analyses. Sampled March 4, 1993 by BSK & Associates
( in rndke:)
Tanks Depth (ft) TPH·G Benzene Toluene Ethyl· Total
BfB '.., .', .,... ..' --- benzene. Xylene
East Tank 2 840 ND 1.9 1.4 18
(500 Gal) 6 1000 . ND ND ND 20
West Tank 2 ND ND ND ND ND
(1000 Gal) 6 ND ND ND ND ND
" . .--
BTB - Below Tank Bottom
.
.. ,.._-,.. ....
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T
able C-) Analytical results on the soil and black material (Sludge) samples col]ected·by DTSC on 9/30198 in inglkg.
Chemical KDOO1 KDOO2 KDOO3 KDOO4 KDOO5 KDOO6 KDOO7 KDOO8 KDOO9 KDOtO'· TTLC
SOIL SOIL SOIL SOIL SOIL Sludge Sludge Sludge SOil Sludge
Copper 22.8 54,5 23.7 28.1 281 989 2260 1470 170 N/A 2500
Lead 88.7 572 92.5 112 422 1900 2ð70 1980 237 N/A 1000
Zinc 459 743 526 209 1670 8400 12800 11600 1330 N/A 5000
TPH 13 65 <4 27 110 1200 1300 700 2000 3200 N/A
PCB NO 3 NO NO NO 13 9.2 11 1.6 8.2 50
Pesticides NO ND ND NO NO ND ND NO ND ND N/A
Sludge samples were collected from different waste piles localed at the Sile.
Nt A - Not available
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California EnVirflntal Protection Agency
Department of Toxic Substances Control
.-
December 1998
The Former K&D Salvage Yard Site
WHAT IS THE PURPOSE OF THIS FLYER?
This flyer has been developed to inform you about activities at the former K&D Salvage Yard site, located at 600
S. Union Ave., Bakersfield, California.
HOW DOES THIS AFFECT ME?
As you mayor may not know, the former K&D Salvage Yard (Site) operated as an auto dismantler and storage
facility on 10 acres between 1958 and 1989. Previous investigations at the Site found that K&D's former
operations resulted in soil contamination with heavy metals including lead and zinc, waste oils, and
polychlorinated biphenyls (otherwise known as PCBs).
Currently, the Site is abandoned and because it was never adequately fenced, is accessable for unauthorized
disposal of debris, such as tires, old appliances and other household items.
In August 1998, the Department of Toxic Substances Control (DTSC) issued an Imminent and Substantial
Endangerment Determination and Order (otherwise known as an Order) to those parties found responsible for
contaminating the Site. The Order stated, that under DTSC oversight, the responsible parties were to conduct
and pay for an investigation and eventual cleanup of the Site,
Unfortunately, the responsible parties did not comply with the Order, and in October 1998, DTSC determined that
it would take responsibility for conducting and paying for investigation and cleanup of the Site.
WHAT CAN I EXPECT TO SEE IN MY NEIGHBORHOOD?
Even though DTSC has already concluded that contamination does exist at the Site, further investigation is
needed to determine exactly what kind and how much contamination still remains, A contractor has been hired
by DTSC to remove the debris and install a new fence around the Site. Once the Site has been cleared of all
debris, soil samples will be collected. These activities are expected to last approximately 7 to 14 days, with
work occurring Monday through Friday, 8:00 a.m. to 5:00 p,m. During this time, you may notice trucks hauling
off debris, It is DTSC's goal to keep truck traffic and parking to a minimum in order to reduce any inconvenience
to the neighborhood.
Once the Site has been fully investigated, the results of DTSC's findings and cleanup strategy will be made
available to the public for review and comment. Flyers like this one will be provided to keep you informed as
activities progress.
HOW CAN I GET INVOLVED?
DTSC's policy is to encourage community involvement in the decision-making process and two-way
communication. As part of DTSC's Public Participation strategy for this Site, a public participation plan will be
developed by meeting with members of the affected community to formally document their questions and
concerns. Other strategies for this site include, but are not limited to: developing a site specific mailing list;
establishing an information repository to provide community access to DTSC documents related to this project;
and distributing fact sheets updating the affected community throughout the project.
WHAT HAPPENS NEXT?
Once this phase of the project has been completed, a fact sheet may be distributed to the site specific mailing
list announcing the next technical and participation steps in the project.
If you find, however, that you would like more information prior to being contacted by DTSC, you are
encouraged to contact:
Megan Cambridge
Department of Toxic Substances Control
10151 Croydon Way, Suite 3
Sacramento, California 95827
(916) 255-3727
or
Heidi Hansen
Department of Toxic Substances Control
P.O. Box 806 - HQ15
Sacramento, California 95812-0806
(916) 324-3108
Mailing List Coupon
If you have any comments concerning the Former K&D Salvage Yard site or if you would like to be put on the site specific
mailing list, please take a moment to fill out the information below and mail it to Heidi Hansen, DTSC, P,Q. Box 806 - HQ15,
Sacramento, CA 95812-0806.
MAILING LISTS ARE CONSIDERED A PUBLIC RECORD,
Name:
Address:
City:
Comments:
State:
Zip Code:
Agencia para la prot.n ~el Medio Ambiente de California
Departamento para el Control de Substancias Tóxicas
.\
Oiciembre de 1998
El Antigua Local de K&D Salvage Yard
¿CUÁL ES EL PROPÓSITO DE ESTE VOLANTE?
Este volante se ha desarrollado para informarle sobre las actividades que se lIevan a cabo en el antiguo local de
K&O Salvage Yard, localizado en el 600 S. Union Ave., Bakersfield, California.
¿DE QUÉ MANERA ME AFECTA ESTO?
Como usted sa be 0 quizás no 10 sepa, de 1958 a 1989, en el local de K&O Salvage Yard operaba un
establecimiento de desmantelamiento y almacenamiento de autom6viles, en una extensi6n de 10 acres. En
investigaciones previas del Local se descubri6 que las antiguas operaciones de K&O contaminaron el suelo con
metales pesados, entre los que se incluyen el zinc, desechos de aceite y bifenilos policlorinados (polychlorinated
biphenyls) (conocidos como PCBs).
Actualmente, el Local está abandon ado, y puesto que nunca se cerc6 adecuadamente, da cabida a que se tiren,
de manera desautorizada, desechos como lIantas, aparatos electrodomésticos viejos y otros artículos del hogar.
En agosto de 1998, el Departamento para el Control de Substancias T6xicas (Oepartment of Toxic Substances
Control-OTSC) emiti6 una Determinaci6n y Orden de Peligro Substancial e Inminente (Imminent and Substantial
Endangerment Oetermination and Order) (a la que se refiere como Orden) a aquellas partes que se determin6 eran
responsables de contaminar el Local. La Orden estipulaba que, bajo la supervisi6n del OTSC, las partes
responsables deberlan lIevar a cabo y pagar el costo de una investigaci6n y limpieza eventual del Local.
Desafortunadamente, las partes responsables no acataron la Orden, y en octubre de 1998, el OTSC determin6 que
éste se haria responsable de lIevar a cabo y pagar el costa de la investigaci6n y limpieza del Local.
¿QUÉ PUEDO ESPERAR VER EN MI VECINDARIO?
Aunque el OTSC ya ha concluido que la contaminaci6n en el Local existe, se necesitan realizar investigaciones
adicionales para determinar exactamente qué clase y cuánta contaminaci6n resta aún. EI OTSC ha empleado a
un contratista para que extraiga los desechos e instale una nueva cerca alrededor del Local. Una vez que sa
hayan eliminado todos los desechos del Local, se tomarán muestras del suelo, Se espera que estas actividades
duren aproximadamente de 7 a 14 dlas, realizándose trabajo de lunes a viernes, de 8:00 de la mañana a 5:00 de
la tarde. Durante este tiempo, es posible que usted note que camiones transporten los desechos fuera del local.
EI objetivo del OTSC es minimizar el tráfico y estacionamiento de camiones, a fin de reducir cualquier
inconveniencia al vecindario,
Una vez que el Local se haya investigado a fondo, 105 resultados de 105 hallazgos y la estrategia de limpieza del
OTSC se pondrán a la disposici6n del público para que los analice y haga sus comentarios al respecto, A medida
que avancen las actividades, se proporcionarán volantes como éste para mantenerle informado.
¿CÓMO ME PUEDO INVOLUCRAR?
La polltica del OTSC es alentar el involucramiento de la comunidad en el proceso de la toma de decisiones, y
facilitar la comunicaci6n abierta entre todas las partes involucradas. Como parte de la estrategia del OTSC para
la Participaci6n del Público, se desarrollará un plan de participaci6n del público, lIevando a cabo reuniones con
los residentes de la comunidad afectada para documentar formalmente sus preguntas y preocupaciones, Otras
estrategias para este local incluyen, pero no se limitan a: desarrollar una lista de correspondencia especifica a
este local; establecer un dep6sito de informaci6n para proporcionar a la comunidad acceso a 105 documentos del
OTSC relacionados a este proyecto; y distribuir hojas informativas para poner al día a la comunidad afectada a 10
largo del proyecto,
¿QUÉ SUCEDERÁ DESPUÉS?
Una vez que se haya completado esta fase del proyecto, es posible que se distribuya una hoja informativa alas
personas de la lista de correspondencia especifica a este local, anunciando los pasos técnicos y de participaci6n
siguientes que se tomarán con relaci6n al proyecto.
Sin embargo, si a usted Ie gustaria recibir más informaci6n antes de que el OTSC se comunique con usted, se Ie
_~ reC9!T1ien9-ª_qu-ª-J~_Eu:~ongª--eRçQJltÇlct_~LÇ-º!l: __ _ ________ ___ = -_ - - __ _-_ -~_______~____ ----
Megan Cambridge
Department of Toxic Substances Control
10151 Croydon Way, Suite 3
Sacramento, California 95827
(916) 255-3727
o
Heidi Hansen
Department of Toxic Substances Control
P.O. Box 806 - HQ15
Sacramento, California 95812-0806
(916) 324-3108
Cupón para la Lista de Correspondencia
Si tiene algún comentario con relación al Antiguo Local de K&D Salvage Yard, 0 si Ie gustaría que se Ie incluyera en la lista de
correspondencia específica a este local, por favor tómese unos momentos para anotar la información a continuación y envíela por
correo a Heidi Hansen, DTSC, P,O. Box 806 - HQI5, Sacramento, CA 95812-0806.
LAS LIST AS DE CORRESPONDENCIA SE CONSIDERAN REGISTROS PÚBLICOS.
Nombre:
Dirección:
Ciudad:
Comentarios:
Estado:
Zona Postal:
_- ì
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RECORD OF TELEPHONE CONVERSATION
Location:
Gee) S UN'wJ
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Business Name: ~~-'L ~Dt:.-J 'ST'A--re ~(.s
Contact Name: br (c- LA J=. (b~
Business Phone: '7 (b J 2. 55".. 3> 70/1
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Inspector's Name: ~
Time of Call: Date: ('2-/'?/4 ~ Time: 1(0() # Min:
, !
Type of Call: Incoming [ ]
Outgoing ~
Returned [ ]
Content of Call:
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Actions Required: ~c1vG-~" G~ - ftb If
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1_.17VSlreel
: . .. · Bakersfield, CA 93304
(805) 327-0671
(805) 324-4218 FAX
& Associates
.
February 11, 1994
BSK JOB B93229
Mr. Nathan Daniels
3318 Harmony Drive
Bakersfield, California 93306
SUBJECT:
UST Site Assessment Report
K & D SALVAGE
Bakersfield, California
Dear Mr. Daniels:
BSK & Associates is pleased to submit this report for the above-referenced project. This report includes
background information, purpose and scope, findings, and our evaluation of the findings. Appendix "A"
presents soil boring logs, Appendix "B" presents results of chemical analyses of soil samples, and
Appendix "C" presents a description of our investigative procedures,
The work was conducted in conformance with guidelines of the Kern County Environmental Health
Services Department. We recommend that you submit a copy of this report to the KCEHSD.
Findings of the investigation did not reveal the presence of gasoline in the subsurface soils at the location
of the former USTs. Based on our evaluation of the findings, we recommend that no further action be
taken.
We appreciate the opportunity to be of service to you on this project. If you have questions regarding
this report, please contact our Bakersfield office.
Respectfully submitted,
BSK & Associates ,
b····~ ///
. .
7 /7
. Bruce M. BI~
{ieOlogi?
Ivan D, Sanderson, Ph.D.
Registered Geologist No. 4514
Project Manager
BMB/IDS:ds
Distribution: Mr. Nathan Daniels (2 copies)
Geotechnical Engineering' Engineering Geology' Environmental Services' Construction Inspection & Testing· Analytical Testing
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TABLE OF CONTENTS
Page
INTRODUCTION
. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .
PURPOSE AND SCOPE . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .
BACKGROUND INFORMATION .................................. 2
Project Location . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .. 2
Site Description . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .. 2
Site Geology and Hydrogeology ............................... 2
Site History ........................................... 2
INVESTIGATIVE PROCEDURES. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .. 4
Exploratory Boring and Sampling Locations . . . . . . . . . . . . . . . . . . . . . . .. 4
Laboratory Analysis of Soil Samples ............................ 4
FINDINGS ...............,................................ 5
Soil Profile . . . . . . . . . . , . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .. 5
Results of Soil Sample Analyses . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .. 5
EVALUATION ...... '. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .. 6
Evaluation of Analytical Results of Soil Samples .... . . . . . . . . . . . . . . . .. 6
Extent of Soil Contamination . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .. 6
Potential Environmental Impacts . . . . . . . . . . . . . . . . . . . . . . . . . . . . . ., 6
Recommendations . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .. 6
CONCLUSIONS . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .. 7
LIMITATIONS ...................,.....,................... 7
TABLES
Table t ....... Results of Soil Sample Analyses - March 4, t 993
Table 2 ....... Results of Soil Sample Analyses - January 19, 1994
BSK JOB B93229 - Febmary 14, 1994
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FIGURES
Figure 1 . . . . . . . Vicinity Map
Figure 2 . . . . . . . Site Plan
Figure 3 . . . . . . . Exploratory Boring Locations
APPENDICES
Appendix A . . . . . Log of Borings
Appendix B . . . . . Analytical Results
Appendix C . . . . . Field Sampling and Testing Procedures
BSK JOB B93229 - February 14, 1994
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UST SITE ASSESSMENT REPORT
K & D SALVAGE
BAKERSFIELD, CALIFORNIA
INTRODUCTION
This report presents findings of an investigation to assess the extent of gasoline migration
beneath a 500-gallon underground storage tank (UST), formerly located at the former K & D
Salvage facility in Bakersfield, California.
PURPOSE AND SCOPE
Purpose of the investigation was to assess the extent of gasoline migration in the subsurface soil
at the location of the former 500-gallon UST in conformance with requirements of the Kern
County Environmental Health Services Department (KCEHSD).
ßSK & Associates' (BSK) scope of work for this investigation induded:
o A workplan and health and safety plan, dated October 1,
1993 (BSK Report 893229), was prepared and submitted to
the KCEHSD for review and approval. The workplan, as
amended, was approved in writing by Mr. Joe Canas of
KCEHSD on December 9, 1993.
o Three exploratory soil borings were drilled on the site and
soil samples were collected on January 19, 1994.
o Selected soil samples were analyzed for BTEX and total
petroleum hydrocarbons as gasoline by 8SK Analytical
Laboratories.
o This report was prepared presenting our evaluation of the
findings of our field and laboratory inve~jtigations and our
recommendations as to further action.
BSK JOB B93229 - Fehruary 14, 1994
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UST Site Assessment Report - K & D Salvage
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Page 2
BACKGROUND INFORMATION
Project Location
The project site is located at 600 South Union Avenue, Bakersfield, Kern County, California.
The site is within the southwest quarter of the northwest quarter of Sec. 5, T.30 South, R.28
East, MDBM and is east of Union Avenue and north of Daniels Lane (see Vicinity Map,
Figure 1).
Site Description
The site is level, partially paved with asphalt and concrete pavement, and is fenced on the north,
south, and east property boundaries. The site is bounded on the north by a motel, on the south
by Daniels Lane, on the west by Union Avenue, and on the east by undeveloped land. The
USTs were located in the central portion of the site. There are presently no structures on the
site. A large pile of wood and concrete debris is present in the area of the site southwest of the
area of investigation. Weeds and trash were observed throughout the site. According to the
owner there are no water wells, dry wells, or drainage sumps on the site. The Kern Island
Canal runs approximately 1/8 mile south of the site.
Site Geology and Hydrogeology
The site is located within the San Joaquin Valley of the Great Valley geomorphic province of
California. Near-surface site soils consist predominantly of fine to coarse sand, which are
Quaternary alluvial deposits. Water well information obtained from Kern County Water Agency
indicates that first-encountered groundwater occurs in unconfined aquifer conditions at a depth
of approximately 220 feet in the vicinity of the site.
Site History
Information concerning the history of the site was provided by Mr. Nathan Daniels, the
responsible party and owner of the site since 1982. The site was used until 1968 as a scrap
metal recycling facility. In 1968, operations were transferred to an off-site location and only
nonferrous materials were recycled at the site. Site operations were discontinued completely in
1981 or 1982. No other information was available concerning past uses for the site.
8SK J08 893229 - Febmary 14, 1994
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UST Site Assessment Report - KtD Salvage
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Page 3
A SOD-gallon UST was removed from the site by M Construction on March 4, 1993. At that
time a 1,ODO-gallon UST was discovered and also removed. Information obtained from Allen
Daniels indicates that the 1,000-gallon UST was installed sometime during the late 1970s when
use of the SOD-gallon UST was discontinued. At the time of the tank removals there was no
product dispenser on the site. Because the USTs were not used for commercial purposes, it is
likely that the product dispenser was previously located at or near the position of the USTs and
that no extensive underground product lines existed. No other USTs or above-ground fuel tanks
are known to have existed on the site.
At the time of the UST removals, soil samples were obtained from beneath the USTs by BSK
and analyzed for benzene, toluene, ethylbenzene, and total xyJenes (BTEX), and total petroleum
hydrocarbons - Gasoline (TPH-G). Test results indicated detectable concentrations of BTEX and
TPH-G in soil at depths of two and six feet beneath the SOD-gallon UST. Results of soil samples
obtained from beneath the 1,000-gallon UST were non-detectable for BTEX and TPH-G.
Laboratory results of the preliminary site assessment are presented in Table I.
Based on the findings of the preliminary site assessment, KCEHSD requested that a site
characterization study be conducted to assess the extent of gasoline migration in soil beneath the
former SOD-gallon UST.
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Page 4
. ... ..
H.·....·. .>i ....... ..> TABLEt<>. ....
.. H ·.··.·RESUI.;'rSO~S()ILSA,."PLÊÅNAL YSES;t(&þ$ALVAGESITE
... ..... ... · ············>······.·.~~~~ê~lW~I~~n~y~{;:Yür:hreh~,G~~~~:/.
. .. Sámpl~dl'Aätch.~;1993 by Bs.t<&.Ašs~c.i.åtê.t;.
Depth, ft TPH...G, Benzene,
BTB mg/kg rng/kg ..
Total Xylene!;,
mg/kg
East Tank 2 840 NO 1,9 1.4 18
(500 Gals.) 6 1,000 NO NO NO 20
West Tank 2 NO NO NO NO NO
(1,000 Gals.) 6 NO NO NO NO NO
Abbreviations:
BTB = Below Tank Bottom
TPH-G = Total Petroleum Hydrocarbons - Gasoline
ND = None Detected
mg/kg = Milligrams per kilogram (Parts per million)
INVESTIGA TIVE PROCEDURES
Exploratory Boring and Sampling Locations
Following approval of the workplan by the KCEHSD, a field investigation was conducted by
BSK on January 19, 1994. Three exploratory borings were drilled on the site. Boring B-1 was
drilled at the former location of the 500-gallon UST to a depth of 37 feet, Boring B-2 was
drilled 10 feet west of Boring B-1 near the former location of the I ,ODD-gallon UST to a depth
of 25 feet, and Boring B-3 was drilled 10 feet south of Boring B-1 to a depth of 20 feet. Boring
locations are shown on Figure 3. Soil samples were collected at five foot intervals commencing
at a depth of ten feet to total exploration depth at each exploratory boring location.
Laboratory Analysis of Soil Samples
Soil samples, collected from Boring B-1 at 10, IS, 20, 25, 30, and 35 feet, from Boring B-2 at
10 and 25 feet, and from Boring B-3 at IS and 20 feet, were analyzed for TPH-G by EPA
Method 8015 and BTEX by EPA Method 8020.
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UST Site Assessment Report - K & D Salvage
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FINDINGS
Page 5
Soil Profile
Subsurtàce soils generally consist of silty sand to a depth of 8 feet underlain by poorly graded
sand and sandy silt to a depth of approximately 30 feet. Silty clay exhibiting moderate plasticity
was encountered at a depth of 30 feet at the location of Boring B-1. Detailed descriptions of soil
types are included in the Logs of Borings (Appendix A).
Results of Soil Sample Analyses
Results of analyses of soil samples collected by BSK on January 19,1994 for BTEX and TPH-G
are presented in Table 2. Laboratory documentation is provided in Appendix B.
. . .."'.'.. ..,. .. .... ....' ..., .,.,
TABLE 2 .. .'y»,).,../.......
-: - '", . :.'-:<-:-:'-;'.--: .:::: :-:::->..:...:.:-::.,.-:-:-.... .;:"';"-::'-:"-"
RESUL TS QFSOIL SAMPLE ANAL Y5E$, t<~D SALVAßI:Sr'l~n
. . Total P~troleum Hydrocé)rbon$ ~. Gé)fiOlinf!i)n
Benzene, Toluene, Ethylbenzf!ne, Xylem~~ .> ,in ,.
. .. .....
SamplE!dJanuary19, 1994 by BSK &A~$ocj,tf!$<>
Sample Boring .. Depmr ··TPH-:G, i3enzel1e,
Location ftBSG mg/kg .. . mg/kg
...,. .. I·· ... ....
S-1 8-1 10 NO NO
5-2 8-1 15 NO NO
5-3 8-1 20 NO NO
5-4 8-1 25 NO NO
5-5 8-1 30 NO NO
5-6 8-1 35 NO NO
5-7 8-2 10 NO NO
5-10 8-2 25 NO NO
5-12 8-3 15 NO NO
5-13 8-3 20 NO NO
Abbreviations:
B5G
TPH-G =
NO
mg/kg =
TOIQ~I1~, t:thYlb~rii!n!'
019/kg mg/kg)
NO NO
NO NO
NO NO
NO NO
,005 NO
NO NO
NO NO
NO NO
NO NO
NO NO
·.t9('''XYI¡Òi~~
'.·.../.........mQ/~~/...·...·..·.·
NO
NO
NO
NO
NO
NO
NO
NO
NO
NO
= Below 5ite Grade
Total Petroleum Hydrocarbons - Gasoline
= None Detected (Below Method Detection Limit)
Milligrams per kilogram (Parts per million)
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Page 6
EVALUA TION
Evaluation of Analytical Results of Soil Samples
Results of analyses of soil samples collected on January 19, 1994 did not reveal the presence
of BTEX or TPH-G in the subsurface soils at the former location of the 500-gallon UST to a
depth of 35 feet. Results of soil samples obtained at the time of the UST removal on March
4, 1993 indicated that lów levels of TPH-G (1,000 ppm or less) were present at depths of 2
and 6 feet beneath the UST (10 to 15 feet beneath site grade at the location of Boring B-1).
During drilling of B-1 gasoline vapor was noticed by the field geologist at a depth of
approximately 10 feet.
Extent of Soil Contamination
BTEX and TPH-G were not detected in the soil samples collected and analyzed by BSK as
part of this investigation. BTEX and TPH-G detected in samples obtained at the time of the
preliminary site assessment on March 4, 1993 appear to have been localized, perhaps
resulting from minor spillage during tank removal.
Potential Environmental Impacts
Based on the findings of this investigation, no subsurface conditions in the vicinity of the
former USTs were identified that could impact the groundwater or the public health and
safety.
Recommendations
Because no fuel contamination was found at the site, no further action is indicated.
BSK JOB B93229 - Fehruary 14, 1994
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UST Sile Assessmenl Report - K & D Salvage
Page 7
CONCLUSIONS
On the basis of our evaluation of the findings, we present the following conclusions:
o Soil profile in the vicinity of the former SOD-gallon UST
consists of silty sand underlain by poorly graded sand and
silty clay to the maximum explored depth of 37 feet.
o First encountered groundwater is reported to occur in
unconfined conditions at a depth of approximately 220 feet.
o No measurable levels of petroleum hydrocarbons as
gasoline were detected in the soil samples obtained by BSK
to a depth of 37 feet BSG.
o No subsurface conditions resulting from the former USTs
were identified in the borings that present potential impacts
to the environment or the public health and safety.
o No further action is indicated.
LIMITATIONS
Findings presented in this report are based on data obtained from our field and laboratory
investigations. The report does not retlect variations which may exist between exploratory
boring locations and sampling points. Such variations cannot be anticipated nor may they be
entirely accounted for in spite of exhaustive additional testing. This study was limited to
characterizing the extent of gasoline migration in soil beneath USTs removed from the site on
March 4, ·1993.
This report is valid as of the present. The passage of time, natural processes or human
intervention on the property or adjacent properties, or changes in government regulations can
cause changed conditions which may invalidate the findings and conclusions presented in this
report.
ßSK JOB 893229 - Pebruary 14. 1994
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UST Site Assessment Report - K & D Salvage
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Page 8
BSK has prepared this report in accordance with generally accepted engineering and geological
practices for the area, based on the guidelines of local and state jurisdictions. No warranties,
either express or implied, are made. This report has been prepared for the exclusive use of the
client. Use of or reliance upon this report or its contents by others, without express written
consent by BSK, is strictly prohibited.
BSK & Associates
BSK JOB B93229 - Fehruary 14, 1994
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APPENDIX A
LOG OF BORINGS
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SOIL LOG LEGEND
tit
UNIFIED SOil CLASSIFICATION SYSTEM
MAJOR DIVISIONS
(Standard ASTM Test Method D2487 For Classification Of Soils For Engineering Purposesl
GRA VEL
AND
GRAVEllY
SOILS
COARSE
GRAINED
SOilS
CLEAN GRAVELS
(less than 6% fines)
More than 60% of
coarse fraction
retained on No.4 sieve (More than 12% finesl
GRAVELS WITH
FINES
More than 60%
retained on the No.
200 sieve
SAND AND
SANDY
SOILS
60% or more of
coarse fraction passes
No,4 sieve
FINE
GRAINED
SOILS
SilTS
AND
ClA YS
liquid limit less
Than 60
60% or more
passes the No. 200
sieve
SILTS
AND
ClA YS
liquid limit 60 or
More
HIGHLY ORGANIC SOILS
CLEAN SANDS
(less than 6% flnesl
SANDS WITH
FINES
(More then 12% finesl
INORGANIC
ORGANIC
INORGANIC
ORGANIC
NOTE: Dual symbols are used to Indlcete borderline soli cllllslflcatlons
SYMBOLS
GRAPH lETTER
VOv'OvOv
o 0 0 0 GW
C) C) C)
':"t':"t':"t':"
---
. .I~ t~ t ~
Þ .IÞ liÞ ..
.
/)/ '/)/
:.-~~~"
... ...
... ...
.. .
.. .
..... .
.. ..
. .
. . .".
~~
. II
.
- --
-
-
//'>/ // //
~;//;//;/~/
///////~(;
SAMPLER SYMBOLS
GP
GM
GC
SW
SP
SM
SC
ML
CL
OL
MH
CH
OH
PT
TYPICAL
DESCRIPTIONS
Well-graded gravel. gravel-sand mixtures.
little or no fines
Poorly-graded gravel. gravel-sand mixtures.
little or no fines
Silty gravel. gravel-sand-slit mixtures
Clayey gravel. gravel-sand-clay mixtures
Well-graded sand. gravelly sand. little or no
tines
Poorly graded sand. gravelly send. little or no
fines
Silty sand. sand-silt mixtures
Clayey sand. sand-clay mixtures
Inorganic silt and very fine sand. rock flour.
silty or clayey fine sand or clayey silt with
sUcht nløsticitv
lean clay-low to medium plasticity. gravelly
clay. sandy clay. silty clay
Organic silt and organic silty clay of low
plasticity
Elastic ailt. micaceous or diatomaceous fine
sand or silty soil
Fat clay-high plasticity
Organic clay-medium to high plasticity:
organic silt
Peat. humus. awamp soil with high organic
content
[I] Auger Cuttings IQ] No Recovery
I2J Disturbed Sample DI Shelby Tube
[I Rock Core B Hand Auger/Sampler
. California Sampler ~ Standard Penetration Test
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LOG OF BORING B-1 BSK JOB NO: B93229
FIGURE NO: 4
ffi DATE: 1/19/94 SHEET 1 of 2
~ LOGGED BY: Blythe
~ ~
~ :I.o WATER LEVEL: No Groundwater Encountered
:::E E-< ~
:::E ~ 0 ELEVATION: none
ti: Z 0 CI) ~ EQUIPMENT: B-50
:I.o ~ ~ ~
:I.o
~ ~ CI) 0 CI) 0 LOCATION: East UST
Z :I.o g ~ u ~
..... :::E :::E
:I.o 0 Ë ~
~ .( ~ >-
0 ..... ~ ~ DESCRIPTION REMARKS
:I.o CI) CI)
SM SILTY SAND: Dark yellow brown; fine grained; Boring commenced at 0918
moist; with 5 percent 3116-inch rounded gravel. Hrs
5_
SP SAND POORLY GRADED: light yellow brown;
loose; fine grained; slightly silty,
10 --
S-I 12 I Slight gasoline odor on
sample.
15 I Becoming very fine grained; color change to
S-2 22 Faint gasoline odor on
grey-black. sample.
-
20 Becoming medium grained; color change to grey.
S-3 35 No gasoline odor on .
- sample.
-
25 I Color change to light yellow brown.
5-4 42 No gasoline odor on
-
Continued Next Page
The described soil conditions may not be representative of those at different locations and times, ~
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LOG OF BORING B-1 BSK JOB NO: B93229
FIGURE NO: 4
~ DATE: 1/19/94 SHEET 2 of 2
~ LOGGED BY: Blythe
:Q ø.. WATER LEVEL: No Groundwater Encountered
~ E-< ~
~ ::J 0 0( ELEVATION: none
E-< Z 0 en ~ EQUIPMENT: B-50
¡¡., ø.. ~ ~ ¡¡.,
ø..
~ en 0 en 0 LOCATION: East UST
E-< Z ø.. ~ ¡.L u :Q
..... ~ ~
ø.. 0 ~ en
¡.L 0( ,...:¡ >-
0 ..... ::> DESCRIPTION REMARKS
ø.. en :Q en
3Q I
S-5 32 SM SILTY SAND: yellow brown; clayey; moist; grades No gasoline odor on
to plastic silty clay. sample.
35 I
S-6 10 SC '//% SILTY CLAY: yellow brown; plastic. No gasoline odor on
</; /
... /// sample.
// Boring terminated at 37 feet
///
/:// at tooo Hrlt.
,
The described soil conditions may not be representative of those at different locations and times. ~
& Associates
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LOG OF BORING B-2 BSK JOB NO: B93229
FIGURE NO: 5
~ DATE: 1/19/94 SHEET 1 of 1
ffi LOGGED BY: Blythe
~ ~ WATER LEVEL: No Groundwater Encountered
~ ~ ~
Ii ~ ::> 0 ELEV A TION: none
Z 0 tI) ~ EQUIPMENT: B-50
~ 5 ~ ~
~ --
is tI) 0 tI) 0 LOCATION: West UST
Z ~ ~ w u ~
...... ~ ~
~ 0 g ~ tI)
w ...... :>< DESCRIPTION REMARKS
0 ~ tI) ~ ~ ::> tI)
SM SILTY SAND: dark yellow brown; moist; with 5 Boring commenced at 1025
percent 3/16-inch gravel. Hrs.
5
SP SAND POORLY GRADED: light yellow brown;
loose.
10 I
S-7 12 No gasoline odor on
sample.
·
..
·
15 I . . Becoming finer grained; color change to grey black.
$-8 16 · No gasoline odor on
sample.
...
.
20 No gasoline odor on
$-9 18
sample.
No gasoline odor on
25 I sample.
S-IO 30 Boring terminated at 25 feet
lal 1047 Hr!l
The described soil conditions may not be representative of those at different locations and times. ~
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LOG OF BORING B-3 BSK JOB NO: B93229
FIGURE NO: 6
~ DATE: 1/ 19/94 SHEET I of 1
f;J LOGGED BY: Blythe
I:Q ø.. WATER LEVEL: No Groundwater Encountered
~ f-< ~
ti ~ ;::¡ 0 ELEV A TION: none
Z 0 tI) ~ EQUIPMENT: B-50
ø.. ~ ~ ~
ø..
::I: tI) 0 tI) 0 LOCATION: 5 feet South of Boring B-1
f-< Z ø.. ::: J..I.j u I:Q
- ~ ~
ø.. 0 9 ø.. tI)
J..I.j -« ~ >-
0 - ;:¡ DESCRIPTION REMARKS
ø.. tI) I:Q tI)
SM SILTY SAND: Dark yellow brown; with 5-10 Boring commenced at liB
percent 3!l6-inch gravel Hrs.
S
SP SAND POORLY GRADED: light yellow brown;
loose; fine grained; slightly silty,
'.
W I
S-ll 20 No gasoline odor on
sample.
15 I
S-12 20 No gasoline odor on
sample.
.
. . No gasoline odor on
20 sample. ,
I .
5-13 34 Boring tenninated at 20 feet
. . lalll1"'\Hr!l
The described soil conditions may not be representative of those at different locations and times. ~
& Associates
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APPENDIX B
ANALYTICAL RESULTS
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~
& Associates
ANALYTICAL
~
lAßORATORIES
1414 Slanislaus se
Fresno, California 93706
Telephone (209) 497-2889
FAX (209) 485-6935
1-800-877-8310
.
Date Sampled
Time Sampled
Date Received
Date of Analysis
Report Issue Date:
BSK-Bakersfield
Nathan Daniels
Case Number
Lab ID Number
Project Number
Sample Description:
Ch940212
0212-1
B93229
K & D Salvage
S-1; B-1 @ 10'
Sample Type
Analyses for BTEX by EPA Method 8020
and TPH (G) by EPA Method 8015
Results Reported in Milligrams per Kilogram (mg/kg)
Compound
Results DLR
ND 0.005
ND 0.005
ND 0.005
ND 0.005
ND l.
DLR Multiplier = 1
: 01/19/94
0925
: 01/20/94
01/20/94
01/25/94
SOLID
NOTE:
Hydrocarbons in the gasoline boiling point range are reported, in accordance with the
method, as Qasoline.
Benzene ........................
Toluene ........................
Ethylbenzene ...................
Total Xylene Isomers ...........
Total Petroleum Hydrocarbons (G)
Sample DLR = DLR x DLR Multiplier,
~
DLR: Detection Limit tor the Purposes of Reporting.
Exceptional sample conditions or matrix interferences
may result in higher detection limits.
ND: None Detected
Cynthia
R930106 BTPSO.t
an, QA/QC Supervisor
4'- ~
Jeffr~Creager, Organics Manager
1414 Stanislaus St.
Fresno, California 93706
Telephone (209) 497-2889
FAX (209) 485-6935
H()(}'8 77-8310
e
ANAL YTICAL
~
LABORATORIES
BSK-Bakersfield
Nathan Daniels
Date Sampled
Time Sampled
Date Received
Date of Analysis
Report Issue Date:
Ch940212
: 0212-2
B93229
K & D Salvage
S-2; B-1 @ 15'
Case Number
Lab ID Number
Project Number
Sample Description:
Sample Type
Analvses for BTEX bv EPA Method 8020
and TPH (G) bv EPA Method 8015
Results Reported in Milligrams per Kilogram (mg/kg)
compound
Results
OLR
Benzene ........................
0.005
0.005
0.005
0.005
1.
Toluene ........................
Ethylbenzene ...................
Total Xylene Isomers ...........
Total Petroleum Hydrocarbons (G)
NO
NO
NO
NO
NO
Sample OLR = OLR x OLR Multiplier,
DLR Multiplier = 1
01/19/94
0936
01/20/94
01/20/94
01/25/94
SOLID
NOTE:
Hydrocarbons in the gasoline boi1ing point range are reported, in accordance with the
method, as qaso1ine.
LEGEND :
DLR: Detection Limit for the Purposes of Reporting.
Exceptional sample conditions or matrix interferences
may result in higher detection limits.
ND: None Detected
Cynthia
R930106 BTPSO.t
4l ~
Jeffrep7creager, Organics Manager
ANALYTICAL
g
1414 Stanislaus St.
Fresno, California 93706
Telephone (209) 497-2889
FAX (209) 485-6935
1-800877-8310
LABORATORIES
~~
BSK-Bakersfield
Nathan Daniels
Case Number
Lab ID Number
Project Number
Sample Description:
e
Date Sampled
Time Sampled
Date Received
Date of Analysis
Report Issue Date:
Ch940212
0212-3
B93229
K & D Salvage
5-3; B-1 @ 20'
Sample Type
Analvses for BTEX bv EPA Method 8020
and TPH (G) bv EPA Method 8015
Results Reported in Milligrams per Kilogram (mg/kg)
Compound
Results DLR
ND 0.005
ND 0.005
ND 0.005
ND 0.005
ND 1.
DLR Multiplier = 1
Benzene ........................
To 1 uene ........................
Ethy lbenzene ...................
Total Xylene Isomers ...........
Total Petroleum Hydrocarbons (G)
Sample DLR = DLR x DLR Multiplier,
01/19/94
0938
01/20/94
01/20/94
01/25/94
SOLID
ROTE:
Hydrocarbons in the gasoline boiling point range are reported, in accordance with the
method, as qasoline.
~
DLR: Detection Limit for the Purposes of Reporting.
Exceptional sample conditions or matrix interferences
may result in higher detection limits.
NO: None Detected
Cynthia
:19]0106 BTPSO. t
4 L _-
Jeffre~creager, Organics Manager
1414 51anislaus 51_
Fresno, California 93706
Telephone (209) 497-2889
FAX (209) 485-6935
1-8()().8 77-8310
e
ANAL YTICAl
~
LABORAroRILS
~~
BSK-Bakersfield
Nathan Daniels
Date Sampled
Time Sampled
Date Received
Date of Analysis :
Report Issue Date:
Case Number
Lab ID Number
Project Number
Sample Description:
Ch940212
0212-4
B93229
K & D Salvage
S-4; B-1 @ 25'
Sample Type
Analvses for BTEX by EPA Method 8020
and TPH (G) by EPA Method BOIS
Results Reported in Milligrams per Kilogram (mg/kg)
Compound
Results DLR
ND 0.005
ND 0.005
ND 0.005
ND 0.005
ND 1.
DLR Multiplier = 1
Benzene ........................
Toluene ........................
Ethylbenzene . ..................
Total Xylene Isomers ...........
Total Petroleum Hydrocarbons (G)
Sample DLR = DLR x DLR Multiplier,
01/19/94
: 0939
01/20/94
01/20/94
01/25/94
SOLID
ROTE:
Hydrocarbons in the gasoline boiling point range are reported, in accordance with the
method, M! Qasoline.
~
DLR: Detection Limit for the Purposeø of Reporting.
Exceptional saøple conditions or matrix interferences
may result in higher dstection limitø.
ND: None Detected
~
~
-#cL
Jeffr Creager, Organics Manager
Cynthia
1\')30106 BTPSO. t
QA/QC Supervisor
LABORArORllS
1414 Stanislaus SIr.
Fresno. California 93706
Telephone (209) 497·2889
FAX (209) 485-6935
1-8ro877-831O
e
ANAL YTlCAl
~
é~~
BSK-Bakersfield
Nathan Daniels
Date Sampled
Time Sampled
Date Received
Date of Analysis
Report Issue Date:
Case Number
Lab ID Number
Project Number
Sample Description:
Ch940212
0212-5
B93229
K & D Salvage
S-5; B-1 @ 30'
Sample Type
Analvses for BTEX bv EPA Method 8020
and TPH (G) bv EPA Method 8015
Results Reported in Milligrams per Kilogram (mg/kg)
Compound
Results
DLR
Benzene ........................
To 1 uene ........................
Ethylbenzene ...................
Total Xylene Isomers ...........
Total Petroleum Hydrocarbons (G)
0.005
0.005
0.005
0.005
1.
ND
0.005
ND
ND
ND
Sample DLR = DLR x DLR Multiplier,
DLR Multiplier = 1
: 01/19/94
0945
01/20/94
01/20/94
01/25/94
SOLID
NOTE:
Hydrocarbons in the gasoline boiling point range are reported, in accordance with the
method, as qasoline.
LEGEND :
DLR: Detection Limit for the Purposes of Reporting.
Exceptional sample conditions or matrix interferencee
may result in higher detection limits.
ND: None Detected
A'L ---
~ I"
Jeffr~creager, Organics Manager
'''~0106 BTPSO. t
e
1414 Stanislaus Streel
Fresno, California 93706
Telephone (209) 497-2889
FAX (209) 485-6935
1-800-877-8310
e
ANALYTICAL
~
LAßORAfORllS
~~
BSK-Bakersfield
Nathan Daniels
Date Sampled
Time Sampled
Date Received
Date of Analysis
Report Issue Date:
Case Number
Lab ID Number
Project Number
Sample Description:
Ch940212
0212-6
B93229
K & D Salvage
5-6; B-1 @ 35'
Sample Type
Analvses for BTEX bv EPA Method 8020
and TPH (G) bv EPA Method 8015
Results Reported in Milligrams per Kilogram (mg/kg)
Compound
Results DLR
ND 0.005
ND 0.005
ND 0.005
ND 0.005
ND 1.
DLR Multiplier = 1
Ben zene ........................
Toluene ........................
Ethylbenzene ...................
Total Xylene Isomers ...........
Total Petroleum Hydrocarbons (G)
Sample DLR = DLR x DLR Multiplier,
01/19/94
1000
01/20/94
01/20/94
01/25/94
SOLID
NOTE:
Hydrocarbons in the gasoline boiling poi.nt range are reported, in accordance with the
method, 'ªª qasoline.
LEGEND :
DLR: Detection Limit for the Purposes of Reporting.
Exceptional sample conditions or matrix interferences
may result in higher detection limits.
ND: None Detected
Cynthia pi
it - 0106 BTPSO. t
n, QA/QC Supervisor
4L .ø-
Jeffr~ Creager, Organics Manager
ANAL YTICAL
r;m
LABORATORIES
, e
1414 Stanislaus Street
Fresno, California 93706
Telephone (209) 497-2889
FAX (209) 485-6935
1.w0-877-831O
e
Date Sampled
Time Sampled
Date Received
Date of Analysis
Report Issue Date:
BSK-Bakersfield
Nathan Daniels
Case Number
Lab ID Number
Project Number
Sample Description:
Ch940212
0212-7
B93229
K & D Salvage
S-7; B-2 @ 10'
Sample Type
Analvses for BTEX by EPA Method 8020
and TPH (G) bv EPA Method 8015
Results Reported in Milligrams per, Kilogram (mg/kg)
Compound
Results DLR
ND 0.005
ND 0.005
ND 0.005
ND 0.005
ND 1.
DLR Multiplier = 1
01/19/94
1034
01/20/94
01/20/94
01/25/94
SOLID
NOTE:
Hydrocarbons in the gasoline boiling point range are reported, in accordance with the
method, ªª qasoline.
Benzene ........................
To 1 uene ........................
Ethylbenzene ...................
Total Xylene Isomers ...........
Total Petroleum Hydrocarbons (G)
Sample DLR = DLR x DLR Multiplier,
~
DLR: Detection Limit for the Purpoøeø of Reporting.
Exceptional øample condltionø or matrix interferenceø
may reøult in higher detection limitø.
ND: None Detected
Cynthia
R930106 BTPSO.t
an, QA/QC Supervisor
41 ~
Jeffr1Ø'Creager, Organics Manager
e
1414 Stanislaus Street
Fresno, California 93706
Telephone (209) 497-2889
FAX (209) 485-6935
1-800877-8310
e
ANALYTICAL
~
LABORATORIES
BSK-Bakersfield
Nathan Daniels
Date Sampled : 01/19/94
Time Sampled : 1045
Date Received : 01/20/94
Date of Analysis : 01/20/94
Report Issue Date: 01/25/94
Case Number
Lab 10 Number
Project Number
Sample Description:
Ch940212
0212-8
B93229
K & D Salvage
S-lO; B-2 @ 25'
Sample Type
SOLID
Analvses for BTEX bv EPA Method 8020
and TPH (G) bv EPA Method 8015
Results Reported in Milligrams per Kilogram (mg/kg)
Compound
Results
DLR
Benzene ........................
To 1 uene ........................
Ethylbenzene ...................
Total Xylene Isomers ...........
Total Petroleum Hydrocarbons (G)
ND
ND
ND
ND
ND
0.005
0.005
0.005
0.005
1.
Sample DLR = DLR x DLR Multiplier,
DLR Multiplier = 1
NOTE:
Hydrocarbons in the gasoline boiling point range are reported, in accordance with the
method, 'ªª aasoline.
~
DLR: Detection Limit for the Purposes of Reporting.
Exceptional sample conditions or matrix interferences
may result in higher detection limits.
ND: None Detected
Cynthia Pigman
RQ't0106 BTPSO.t
Supervisor
. -ß. L ".
Jeffreþfcreager, Organics Manager
ANALYTICAL
~
LAßORATOR I E 5
1414 Slanislaus SI.
Fresno, California 93706
Telephone (209) 497-2889
FAX (209) 485-6935
1-800-877 -S31O
e
Date Sampled
Time Sampled
Date Received
Date of Analysis
Report Issue Date:
BSK-Bakersfield
Nathan Daniels
Case Number
Lab ID Number
Project Number
Sample Description:
Ch940212
0212-9
B93229
K & D Salvage
S-12; B-3 @ 15'
Sample Type
Analvses for BTBX by BFA Method B020
and TFH (G) by BFA Method B015
Results Reported in Milligrams per Kilogram (mg/kg)
Compound
Results
DLR
: 01/19/94
1120
01/20/94
01/20/94
01/25/94
SOLID
NOTE:
Hydrocarbons in the gasoline boiling point range are reported, in accordance with the
method, .!!!! qasoline.
Benzene ........................
ND
ND
ND
ND
ND
0.005
0.005
0.005
0.005
1.
Toluene ........................
Ethylbenzene ...................
Total Xylene Isomers ...........
Total Petroleum Hydrocarbons (G)
Sample DLR = DLR x DLR Multiplier,
DLR Multiplier = 1
~
DLR: Detection Limit tor the Purposes of Reporting.
Exceptional sample conditions or matrix interferences
may result in higher detection limits.
ND: None Detected
Cynthia
30106 BTPSO. t
an, QA/QC Supervisor
4,L /
Jeffr~Creager, Organics Manager
e
1414 Stanislaus Street
Fresno, California 93706
Telephone (209) 497-2889
FAX (209) 485-6935
1-80C}877-831O
e
ANAL YTlCAL
~
LABORATORIES
BSK-Bakersfield
Nathan Daniels
Date Sampled
Time Sampled
Date Received
Date of Analysis
Report Issue Date:
Case Number
Lab ID Number
Project Number
Sample Description:
Ch940212
0212-10
B93229
K & D Salvage
S-13; B-3 @ 20'
Sample Type
Analyses for BTEX by EPA Method 8020
and TPH (G) by EPA Method 8015
Results Reported in Milligrams per Kilogram (mg/kg)
Compound
Results DLR
ND 0.005
ND 0.005
ND 0.005
ND 0.005
ND 1-
DLR Multiplier 1
Benzene ........................
To 1 uene ........................
Ethylbenzene ...................
Total Xylene Isomers ...........
Total Petroleum Hydrocarbons (G)
Sample DLR = DLR x DLR Multiplier,
01/19/94
: 1137
01/20/94
01/20/94
01/25/94
SOLID
NOTE:
Hydrocarbons in the gasoline boiling point range are reported, in accordance with the
method, 'ªª Qasoline.
LEGEND :
DLR: Detection Limit.for the Purposes of Reporting.
Exceptional sample conditions or matrix interferences
may result in higher detection limits.
ND: None Detected
Cynthia
R9J0106 BTPSO.t
AL .-
~ -
Jeffr~ Creager, Organics Manager
Shaded areas forLABuscooly
]
BSK Log Number:O 2 Î 2
, ¡
~
y
Ana1YÙcalD\aeDate:li~zlt',..CrtJ.ijl
Requested Analyses
. - -
ANALYTICAL
tl;_I~
LABORATORIES
1414 Stanislaus Street
Fresno, CA 93706
(209) 485-8310
(800) 877-8310
(209) 485-6935 FAX
Analyses Request / Chain of Custody
&rwitt".",e.t.e S~
Cücut"ame Report Anenlion: -r- Pbone # ~
" ~ - /,., /J¿;] " " ~ ¿ r'" .fA A/'/J,Æfi r-f1!':./ ~
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A~ Proje<;t . QuOle or PO A FAX#
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c~e. Zip c1þJ opy to: System # ~ '\
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1YPii.....f..; Sampled Sampled Samp¡{' DescriptionlLocation Station Code :y;
...:.:~.::.:., ··:·,:::{:::.t&¡t' ; ~
~~ht/ /J ¡P..2S /<~z:; .;$/9 ¿. i/~6 ~ (/I~' $/,1~~
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fcþ·..:.: ) // -?7 <Ç-/; A- $~--" ;I l
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Payment Received with Delivery .
Date:. .. .:~unt: S
Chtck'# ... . . InitíiIš' .
n-_" ~. . . ." '::::" <:.:-::>::::>: .:. ""'<'::}\;::}« :.:: :::::.{} :-::.:'
.F.f~9~:<:'····· . "',.. .,.:.:.:.::...,.........-:..,.:-...:...
Tune
Matrix Type: l· liquid S· Solid G - Gas Additional Services:
Type of Hazards Associated with Samples: Rush Priority: [] - 2 Day [] . 5 Day
[ ] - Fonnal Chain of Custody [] - QC Data package
Additional Services Authorized by:
Print Name
(Signature)
Company
;S-.1D
Received I ReliDquisbed by:
Rec0ive4lll.oIiDquiobcct by:
,f,mr.fl'~in~i ,"
',(;j....
.
.
APPENDIX C
FIELD SAMPLING AND TESTING PROCEDURES
~
& Associates
e
e
APPENDIX C
FIELD SAMPLING AND TESTING PROCEDURES
TABLE OF CONTENTS
Page
INTRODUCTION . . . . , . . , . . , . . . . . , . . . . . . . , . . , , . . . , . , . . . . . . , . . . . . . . 1
SOIL SAMPLING .,.....,...,.,...,.,.,..,......................, 1
Exploratory Boring Locations .....,...",..."...,.,........"., 1
Soil Sampling Methods ,...,........,.,....,...."........,... 1
Equipment Decontamination, . , . . , . . . . . . , , , , . , , . . . . . . , . . . . . . . . . . 2
Soil Cuttings Disposition . . , . . , , . . . . . . . , , . . . , . . . , , , . . . . , . . , . . . . . 2
Field Logs/Documentation ",.....,....",..,.................. 3
LABORATORY TESTING ,..,.....",.".......,.....,....,......,. 3
Laboratory Analyses ..,...,......,.,.......,...........,...,. 3
Laboratory Quality Control . . . . . , . , . . . . . . . . . , . , . , . , . . . . . . , . . , . . . 3
BSK Job 893229 - Fehmmy 11, 1994
~
& Associates
.
.
APPENDIX C
FIELD SAMPLING AND TESTING PROCEDURES
INTRODUCTION
This appendix presents soil sampling and analytical procedures utilized during a site
characterization study to assess the presence and extent of gasoline constituents (TPH-G and
BTEX) in soil beneath the former site of a 500-gallon underground storage tank (UST) at
K & D Salvage, 600 South Union Avenue, Bakersfield, California. Field and laboratory
investigations were conducted in accordance with the procedures described below.
SOIL SAMPLING
Exploratory Boring Locations
Exploratory soil borings were located as described in the project workplan with the exception
that proposed Borings B-4 and B-5 were not drilled. Two working days prior to commencement
of the work, Underground Services Alert was notified and on-site underground utilities were
identified and indicated.
Undisturbed soil samples were obtained at each boring location at five-foot depth increments
beginning at a depth of 10 feet BSG.
Soil Sampling Methods
A BSK geologist was on site to coordinate the work, to take custody of the soil samples, and
to log soil types encountered during boring operations. Soil types were visually described in
accordance with the Unified Soil Classification System and noted on boring logs with penetration
blow counts and other pertinent data.
BSK Job B93229 - Felmwry 11, 1994
~
& Associates
Appendix C - Pield Sampling Testing Procedures
Page 2
Drilling was performed by BSK using a truck-mounted drill rig equipped with hollow~stem
augers. Soil samples were collected with a California split spoon sampler lined with stainless
steel tubes and driven through the center of the auger. The lowermost sample tube collected in
the sampler was retained for chemical analyses. Ends of the sample tubes were sealed with
Teflon film, covered with plastic caps, labeled, and sealed with waterproof tape having
non-petroleum adhesive. Samples were identified by project number, sample number, date and
time of sampling, and name of sampling personnel. Soil samples were stored in an ice chest
mainta'ined at or near a temperature of 4°C and shipped to BSK's California Department of
Health Services certified laboratory in Fresno, California. Samples were accompanied by a
chain-of-custody form. Chain-of-custody documentation include sampler's name, sample
identification information, requested chemical analyses, and times and dates of custody transfers.
Equipment Decontamination
Drill bits, auger flights, and other ancillary equipment were cleaned with a high pressure hot
water washer prior to drilling and between each boring location. Between soil sampling events,
samplers were disassembled and washed in a solution of laboratory grade detergent, rinsed with
clean water, and reassembled with clean sample tubes to minimize the potential for cross
contamination between sampling events.
Soil Cuttings Disposition
Soil cuttings generated from Borings B-2 and B-3 were used to backfill the boreholes. Soil
cuttings generated from Boring B-1 were spread on site for aeration under the approval of the
KCEHSD on-site representative. The borehole for Boring B-1 was backfilled with a
sand/cement slurry. Spent soil samples from laboratory analyses were retained for a period of
30 days from the date of analysis and will be disposed of in accordance with applicable state and
federal regulations after that time period has elapsed.
8SK lob 893229 - Febmary II. 1994
~
& Associates
Appendix C - Field Sampling -¡¡resting Procedures
Page 3
Field Logs/Documentation
Soil sampling operations, site and equipment conditions, variances from specified sampling
procedures, field observations, instrument readings and measurements, equipment and personnel
decontamination procedures, and soil sampling depths and locations were documented by the
field geologist on prepared BSK forms. These forms are retained in the project records.
LABORATORY TESTING
Laboratory Analyses
Soil samples were analyzed for TPH-G and BTEX by EPA Methods 8020M and 8015M.
Laboratory Quality Control
Internal quality control checks used by the analytical laboratory to validate data included the
foJlowing:
Calibration Check Standard - A calibration check standard containing all of the
analytes to be measured, internal standard, and surrogates was performed at the
beginning of each day.
Instrument Performance Criteria - Instrument performance criteria was
demonstrated every 12 hours in conformance with performance criteria defined
in EPA methods.
Matrix Spike - Matrix spikes to measure analytical accuracy were analyzed at a
rate of one for every ten samples analyzed. If calculated spike recoveries did not
fall within acceptable ranges, corrective action was taken before further analyses
was performed.
Analysis of Duplicate Samples - Duplicate samples were run at a rate of one for
every ten samples analyzed to measure analytical precision.
Control Charts - Control charts prepared for each parameter determined by a
method were supplied to each laboratory analyst to assess whether recoveries
were within acceptable limits.
Internal Standards - A known concentration of internal standard was added to
every standard, blank, and sample analyzed for organic parameters to compensate
for minor fluctuations in instrument response.
Surrogate Standards - Samples were spiked with a surrogate closely related to the
compound of interest before sample preparation.
8SK loh 893229 - Fehrum}' 1 I, 1994
~
& Associates
--
-
·
-
BSK JOB B93229
SITE ASSESSMENT WORKPLAN AND
HEALTH AND SAFETY PLAN
K & D SALVAGE
600 SOUTH UNION AVENUE
BAKERSFIELD, CALIFORNIA
_... - ..........~ .. .~. - -_"___"~_M_____ .-t
:", ...' \ . .::..~ ;: '\ /n-: ;'=, "I'" "
, , -- I __ " \,', :'~ "\
,'~~ -=- ~.:::.--~~~_.:,? ! :1 i I
_.II9m
..._---_.-....-_..-.. .- -...
-..~ ._._~~-_.
~
& Associates
I~~
& Associates
117 "V" Street
Bakersfield, CA 93304
(805) 327-0671
(805) 324-4218 FAX
e
October 1, 1993
Mr. Nathan Daniels
3318 Harmony Drive
Bakersfield, California 93306
BSK JOB B93229
SUBJECT: Site Assessment Workplan
K & D Salvage
600 South U nion Avenue
Bakersfield, California
Dear Mr. Daniels:
BSK & Associates is pleased to present this workplan for the above-referenced project. It
will be your responsibility to transmit a copy of the workplan to Ms. Flora Darling of Kern
County Environmental Health Services Department for approval prior to commencement of
our field investigation.
We appreciate the opportunity to be of service to you on this project. If you have questions
regarding this workplan, please contact our Bakersfield office.
Distribution: Client (2 copies)
Respectfully submitted,
Ivan D. Sanderson, Ph.D.
Registered Geologist No. 4514
Geotechnical Engineering' Engineering Geology' Environmental Services' Construction Inspection & Testing' Analytical Testing
·
.J
TABLE OF CONTENTS
Page
INTRODUCTION . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .. 1
PURPOSE AND SCOPE . . . . . . . . . . . . . . . . . . . . . . . . . . . . . ... . . . . . . . .. 1
BACKGROUND INFORMATION . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .. 2
Project Location . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .. 2
Site Description . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .. 2
Site History ........................................... 2
Site Geology and Hydrology ................................. 4
TECHNICAL WORKPLAN . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .. 4
Field Exploration . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .. 4
Laboratory Investigation . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .. 5
Site Characterization Report . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .. 6
Project Schedule . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .. 6
LIMITATIONS ............................................. 6
TABLES
Table 1 ............ Preliminary Analytical Results
Table 2 . . . . . . . . . . . . Project Schedule
FIGURES
Figure 1 ........... Vicinity Map
Figure 2 ........... Site Plan
Figure 3 ........... Proposed Boring Locations
Figure 4 ........... Hospital Location Map
APPENDICES
Appendix A ......... Laboratory Results
Appendix B ......... Field Sampling and Testing Procedures
Appendix C ......... Health and Safety Plan
BSK Job B93229 - October 1, 1993
~
& Associates
e
.
SITE ASSESSMENT
WORKPLAN AND HEALTH AND SAFETY PLAN
K & D SALVAGE
600 SOUTH UNION A VENUE
BAKERSFIELD, CALIFORNIA
INTRODUCTION
This report presents a Workplan and Health and Safety Plan for a proposed site assessment to
characterize soil beneath a former underground storage tank site (UST site) at 600 South Union
Avenue in Bakersfield, California. Preparation of this workplan was authorized by Mr. Nathan
Daniels on September 23, 1993.
Contents of this workplan include purpose and scope, background information, and a technical
approach of our proposed field and laboratory investigations. Three report appendices contain
Analytical Results (Appendix A), Field Sampling and Testing Procedures (Appendix B) and a
Health and Safety Plan (Appendix C).
PURPOSE AND SCOPE
Purpose of this workplan is to provide Kern County Environmental Health Services
Department (KCEHSD) with a description of the methodology and technical procedures to be
utilized by BSK and Associates (BSK) during the proposed site assessment. Scope of BSK's
work includes preparation of this workplan and health and safety plan, a field investigation
consisting of sampling soil beneath the UST site, analytical testing of soil samples for
gasoline constituents, and preparation of a site assessment report.
BSK Jvb B93229 - October 1, 1993
~
& Associates
. .
Workplan and Health and Safety Plan - K & D Salvage, 600 South Umon Avenue
Page 2
During preparation of this workplan the following tasks were performed:
. Mr. Nathan Daniels was interviewed on September 27 and 29, 1993, who
provided background information.
. This Workplan and Health and Safety Plan was prepared.
BACKGROUND INFORMATION
Project Location
The project site is located at 600 South Union Avenue, Bakersfield, Kern County, California.
The site is bounded on the west by South Union Avenue, on the south by Daniels Lane, and
on the north and east by developed property. The site is within Section 5, Township 30
South, Range 28 East, Mount Diablo Baseline and Meridian (see Vicinity Map, Figure 1).
Site Description
The site is level, is unpaved in the vicinity of the proposed site characterization, and is
bounded on the west by a discontinuous brick wall. Portions of the site are paved with
asphaltic and Portland cement concrete, remnants of surface improvements now mostly
removed. The site is bounded on the north and south by wood fences. There are presently
no structures on the site (see Site Plan, Figure 2). A large pile of wood and concrete debris
from demolition of site buildings is present southwest of the area on the site to be
investigated.
/
Site History
Information concerning the site history was provided by Mr. Nathan Daniels, site owner.
This site, the former location of K & D Salvage, was used for many years as a recycling
facility for scrap iron and other metals. In 1968, operations involving ferrous metals and
automobiles were transferred to Golden State Metals, leaving scrap nonferrous metal
operations only at this site. Operations ceased in 1981 or 1982. A Solid Waste Assessment
BSK Job B93229 - OClober I, 1993
~
& Associates
. -
Workplan and Health and Safety Plan - K & D Salvage, 600 South Union Avenue Page 3
metallic and other contaminants in site soil and groundwater in the eastern portion of the site
were investigated. A test well was drilled that encountered groundwater at a depth of
220 feet. According to Mr. Daniels, slight concentrations of heavy metals were detected in
groundwater in the well, but other wells in the neighborhood were tested and found to have
similar background levels of heavy metals.
During its operation as K & D Salvage (1935-1982), the property was owned by Mr. Nathan
Daniels' brother, Robert Daniels. Upon the death of Robert Daniels in 1982, the property
was inherited by his wife, ISabelle Daniels, who died in 1984. The property was then
¡ ,
purchased by Mr. Nathan Daniels from the estate of his brother's wife, for which Mrs. Joyce
Clarke, a daughter of Robert and Isabelle Daniels, was acting as trustee. Mr. Daniels
. p
reports that at the time of his obtaining ownership, salvage operations had ceased. He had
no knowledge at that time of the presence of USTs on the site.
A SOD-gallon gasoline UST was used on-site for refueling a forklift used in the salvage
operation. Mr. Nathan Daniels became aware of the existence of a UST at the site in 1989,
when notified by KCEHSD of the need for its removal. Mr. Nathan Daniels did not know of
any leakage from any USTs, nor was he aware of installation of a second UST, which was
found by M Construction at the time of removal in 1993. According to Alan Daniels,
Nathan Daniels' nephew, the 1, ODD-gallon UST was installed sometime in the late 1970s and
the SOD-gallon UST was taken out of service,
On March 4, 1993, two USTs - one of 500 gallons capacity and one of 1,000 gallons
capacity - were removed from the western portion of the site by M Construction Co. (see
Figure 2). At the time of the UST removal, BSK & Associates obtained soil samples from
beneath the USTs and analyzed for benzene, toluene, ethylbenzene, and total xylenes
(BTEX), and total petroleum hydrocarbons-gasoline (TPH-G). Preliminary site assessment
results indicated detectable concentrations of gasoline and gasoline constituents in soil at
BSK Job B93229 - October 1, 1993
~
& Associates
. -
Work plan and Health and Safety Plan - K & D Salvage, 600 South Union Avenue Page 4
depths of approximately two and six feet below the former position of the 500-gallon UST.
Results are shown in Table 1 and Appendix A.
At the time of the tank removals, no evidence was seen above ground for a fuel dispenser.
Since the USTs were not used for commercial sale of fuel, it is likely that the fuel dispenser
was located at or near the position of the USTs and that no extensive underground fuel lines
were present.
Based on results of the preliminary sample analyses, Kern County Environmental Health
Services Department (KCEHSD) requested that a Site Characterization Study be conducted to
assess the vertical and lateral extent of gasoline migration in soil beneath the former UST
. - ~ ~~ ~ w.rIJP, "
site. ~tþQ. hott--~- '¡ ~-, /"'--1
~ ~tGa.~, ~
Site Geology and Hydrology
The site is located within the San Joaquin Valley of the Great Valley geomorphic province of
California. Near-surface site soils consist predominantly of fine to coarse sand, which are
Quaternary alluvial deposits. Water well information obtained from Kern County Water
Agency indicates that first-encountered groundwater occurs in unconfined aquifer conditions
at a depth of approximately 220 feet in the vicinity of the site. Î
TECHNICAL WORKPLAN
Upon approval of this workplan by KCEHSD, BSK will conduct a field exploration to obtain
soil samples and a laboratory investigation to test the samples. The object of these efforts is
to assess the extent of migration and concentration of gasoline constituents (BTEX and
TPH-G) and presence of soluble lead in subsurface soils at the former UST site. Results will
be summarized in a Site Characterization Report. These phases of work are described
below.
Field Exploration
BSK Job B93229 - October 1, 1993
\~
Th~ field exploration will consist of drilling a maximum of five soil borings in the vicinity of
the former USTs to a maximum depth of 50 feet below site grade (BSG) or until auger
refusal or groundwater is encountered. Soil borings will be drilled with a Mobile B-50 drill
rig equipped with eight-inch hollow-stem augers. Encountered soils will be field-screened
for gasoline vapors using a photo ionization detector (PID). Depths to which drilling will be
advanced will be based on PID readings. ,_ _ _ ~ ~ ~
~~~~1=r
A soil boring will be located at the cent of the former position of the 500-gallon UST to
assess the vertical extent of contaminatio . Additional soil borings will be located at
distances of ten feet from the center of the former UST position in various directions to
assess the lateral extent of product migration. A proposed configuration for test borings is
shown in Figure 3, but this configuration may be modified depending on site conditions
encountered during the exploratio Undisturbed soil samples will be retrieved at five-foot
increments commencing at a depth of 10 feet BSG, for field screening and laborator~ :::iÃ-Ù
analysis-~"l\~~~.A:t~~ud"..Lt ~~~
ú.&a.~ ~ cn~~I6.. uL.1I D8ff-5 ~~
~ÐtßL.,.. - - 0 U ~
Soil will be sampled, stored, and transported in accordance with guidelines outlined in U.S.
EPA Test Methods for Evaluating Solid Waste, Physical/Chemical Methods: SW-846, Third
Edition. Chain-of-Custody documentation will be maintained during the sample
transportation and handling process. <:)~..sU2.Q çU..t:r/l..·~~.~ Cl.J..~ ~
s(Q~ ~ ~ r1] Rf ' ~\~~
A BSK geologist will be on site to UdT:a~ ~nd log soil types encountered during
boring operations. Soil types will be described in accordance with the Unified Soil
Classification System. Drill cuttings will be screened with the PID for gasoline constituents
and segregated based on the PID readings. Cuttings will be stored on site in D.O.T.
approved drums. Following completion of drilling and sampling operations, the boreholes
will be backfilled with a bentonite/cement slurry.
Laboratory Investigation
BSK Job B93229 - October I, 1993
~
& Associates
· .
Workplan and Health and Safety Plan - K & D Salvage. 600 South UlÚon Avenue Page 6
Selected soil samples will be transported to BSK Analytical Laboratories in Fresno,
California and analyzed for BTEX and TPH-G by EPA Methods 8020M and 80l5M. In
addition, because of the apparent age of the former UST and the likelihood that leaded
gasoline was previòusly stored in the UST, a selected soil sample will be tested for tota1lead
by an approved DHS method.
Site Characterization Report
Upon completion of the field and laboratory phases of the investigation, a Site
Characterization Report will be prepared presenting our findings, evaluation, and
conclusions. The report will be prepared in accordance with guidelines set forth in
KCEHSD Document UT-35, Site Characterization and Site Remediation, and will include a
summary of analytical data, boring logs, the extent of contamination (if present), estimates of
cost for at least three alternative remediation methods including the no-action alternative, and
a workplan for additional site characterization (if necessary).
Project Schedule
We anticipate that approximately four to five weeks, exclusive of agency review time, will
be required to complete the investigation and report after approval of this workplan by
KCEHSD.
It is anticipated that the field investigation will commence within one week after agency
approval. Laboratory analysis of soil samples will require approximately ten working days
from the time of submittal. A site assessment report will be submitted to the client
approximately two weeks after receiving results of the soil analyses. The preliminary project
schedule is presented in Table 2.
LIMITATIONS
The scope of work presented in this workplan is based on the assumption that site features
and conditions do not deviate significantly from the information provided to BSK by the
BSK Jvb B93229 - October I, 1993
~
& Associates
· .'
Workplan and Health and Safety Plan - K & D Salvage, 600 South Union Avenue
Page 7
client. This workplan is presented with the understanding that it is the client's (property
owner's) responsibility to transmit the information contained herein to the appropriate
regulatory agency for approval prior to commencement of our investigation. It will be the
responsibility of the client to identify existing underground systems and features prior to
commencement of drilling operations. BSK will not be responsible for damage to subsurface
features or to the environment resulting from our drilling at locations approved by the
property owner.
Execution of the scope of work outlined in this proposal may result in the generation of
hazardous materials. BSK will not be responsible for the generation, manifestation,
transportation, or disposal of hazardous materials. Hazardous materials generated by the
work will remain the responsibility of the property owner.
This workplan has been prepared in accordance with generally accepted engineering practices
for the area, based on the guidelines of federal and local jurisdictions. This workplan has
been prepared for the sole use of BSK and our client. No warranties, express or implied,
are made.
BSK & Associates
8SK Job 893229 - October 1, 1993
~
& Associates
.
e
Workplan and Health and Safety Plan - K & D Salvage, 600 South Union Avenue
Page 8
·········DšûLTšôFSOmŠAMPmANALYŠÊŠK&DSÂ1LVÂGÊ'šì~î~·" , .....,.,
1'O'I'ÀLiETRfiLÊûMffimR~êARíl6~ši~AsÖLíNi·<·I'¡¡··::
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.".... .. . . .....",,--.
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.....
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· , ))~¡!H<... ftBTH
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...
East Tank 2
(500 Gals.) 6
West Tank 2
(1,000 Gals.) 6
··""·:TA.8tJtT" .'.,' ,', .,
..
-, .........
................................. "
.."....... ,..,..... .". .
.;.:.'...-:.;...;.....;.;-:;-::-.:-..;.. .
......:.'....................,........-...... .
.,...,......."....:...............'.... ...
:::::';";;:;:::;:;:;:,:;::::.:,;:::;:;:::::; .. ....,.
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.·..·..·B:ii~~e,.........· ··.......~!:~~0...:.·..... .......~.~t.........
,. .. ·········..7If········
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1 9 1 4
.·..¡.·.I~f\I~....··..
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. ... .. . ........
.. -. ". .....
18
....
. .
840 NO
1,000 NO
NO NO
NO NO
ND
NO
NO
NO
NO
NO
20
NO
NO
Abbreviations:
BTB - Below Tank Bottom
TPH-G - Total Petroleum Hydrocarbons - Gasoline
ND - None Detected
mg/kg - Milligrams per kilogram (pans per million)
...... ....... ..... ......... ....' .1i' ....... . ... ..' A K.l
" /., ..... .... ....../ ...... . .. H
....,..... .......... ............... ......, ....... ... ".
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Submit Work plan for Agency jil~ l~ ~~i ;~~~ ¡~¡;
".0:'" ~@~' ,~.. ,..::-;
Approval i~ ~ ~ t.~ ¡~
......'.....
.............
......
...."..
...........
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Field Investigation
Analytical Testing
Final Report
BSK Jùb B93229 - OClober 1, 1993
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............../..
..............~......... ~...
. .......\ .. (f1W.~~/'<""
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~.;§ ·fJJ :¡m: :. .
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& Associates
.
.
Workplan and Health and Safety Plan - K & D Salvage, 600 South Union Avenue
Page 3
Test (SWAT) was conducted thereafter, in which the presence, concentration, and extent of
metallic and other contaminants in site soil and groundwater in the eastern portion of the site
were investigated. A test well was drilled that encountered groundwater. at a depth of
220 feet. According to Mr. Daniels, slight concentrations of heavy metals were detected in
groundwater in the well, but other wells in the neighborhood were tested and found to have
similar background levels of heavy metals.
During its operation as K & D Salvage (1935-1982), the property was owned by Mr. Nathan
Daniels' brother, Robert Daniels. Upon the death of Robert Daniels in 1982, the property
was inherited by his wife, Isabelle Daniels, who died in 1984. The property was then
purchased by Mr. Nathan Daniels from the estate of his brother's wife, for which Mrs. Joyce
Clarke, a daughter of Robert and Isabelle Daniels, was acting as trustee. Mr. Daniels
reports that at the time of his obtaining ownership, salvage operations had ceased. He had
no knowledge at that time of the presence of USTs on the site.
A 500-gallon gasoline UST was used on-site for refueling a forklift and other vehicles used
in the salvage operation. Mr. Daniels has no recollection of when the 5OO-gallon UST was
installed. When this UST began to leak, it was taken out of service and a 1,0oo-gallon UST
was installed adjacent to it. According to Alan Daniels, Nathan Daniels' nephew, the 1,000-
gallon UST was installed sometime in the late 1970s. Currently Alan Daniels is doing
business as Double D Recycling on the eastern portion of the property.
~ March 4, 1993, two USTs - one of 500 gallons capacity and one of 1,000 gallons
capacity - were removed from the western portion of the site by M Construction Co. (see
Figure 2). At the time of the UST removal, BSK & Associates obtained soil samples from
b~neath the USTs and analyzed for benzene, toluene, ethylbenzene, and total xylenes
(BTEX), and total petroleum hydrocarbons-gasoline (TPH-G). Preliminary site assessment
results indicated detectable concentrations of gasoline and gasoline constituents in soil at
BSK Jub B93229 - October 1, 1993
~
& Associates
e e
Workplan and Health and Safety Plan - K & D Salvage, 600 South Union Avenue Page 3
wt
Here. 15 c.orf'€C!---tI CH15 ich the presence, concentration, and extent of
5D( sc+e).pet" O"~SI reQut5+J groundwater in the eastern portion of the site
It encountered groundwater at a depth of
rcentrations of heavy metals were detected in
I neighborhood were tested and found to have
I
Te~
me
22C
gro
slm
i
DUI ! 982), the property was owned by Mr. Nathan
Dar þth of Robert Daniels in 1982, the property
was _, .. __6 died in 1984. The property was then
purchased by Mr. Nathan Daniels from the estate of his brother's wife, for which Mrs. Joyce
Clarke, a daughter of Robert and Isabelle Daniels, was acting as trustee. Mr. Daniels
reports that at the time of his obtaining ownership, salvage operations had ceased. He had
no knowledge at that time of the presence of USTs on the site.
A 500-gallon gasoline UST was used on-site for refueling a forklift used in the salvage
operation. Mr. Nathan Daniels was aware of the existence of a UST at the site, but did not
know of any leakage or installation of a second UST, which was found by M Construction at
the time of removal. According to Alan Daniels, Nathan Daniels' nephew, the I,OOO-gallon
UST was installed sometime in the late 1970s when the original UST began to leak and was
taken out of service.
On March 4, 1993, two USTs - one of 500 gallons capacity and one of 1,000 gallons
capacity - were removed from the western portion of the site by M Construction Co. (see
Figure 2). At the time of the UST removal, BSK & Associates obtained soil samples from
beneath the USTs and analyzed for benzene, toluene, ethylbenzene, and total xylenes
(BTEX), and total petroleum hydrocarbons-gasoline (TPH-G). Preliminary site assessment
results indicated detectable concentrations of gasoline and gasoline constituents in soil at
BSK Job B93229 - October 1, 1993
~
& Associates
e
APPENDIX A
ANALYTICAL RESULTS
-
~.
& Associates
^N"L YT IC"l
œ
l^ßOR^fORIf:S
&..\r...rIAI ~
1414 Stanislaus 5t.'-
Fresno, California ~6
Telephone (209) 485-8310
FAX (209) 485-6935
1-800-877-8310
e',..
BSK-Bakersfield
K & D Salvage
Date Sampled
Time Sampled
Date Received
Date of Analysis
Report Issue Date:
Case Number
Lab ID Number
Project Number
Sample Description:
Ch930557
0557-1
B93039
East Tank
(500 Gal) 2'
Sample Type
Analvses for BTEX bv EPA Method 8020
and TPH (G) bv EPA Method 8015
Results Reported in Milligrams per Kilogram (mg/kg)
Compound
Results
DLR
Benzene ........................
ND
1.9
1.4
18
840
0.005
0.005
0.005
0.005
1.
Toluene ........................
Ethylbenzene ...................
Total Xylene Isomers ...........
Total Petroleum Hydrocarbons (G)
Sample DLR = DLR x DLR Multiplier,
DLR Multiplier = 1
DLRI Detection Limit for the Purpose. of Reporting.
Bxceptional sample condition. or ~trix interferences
may result in higher detection limits.
1m: None Detected
Cynthia
>,930106 BTPS.t
: 03/04/93
1250
03/05/93
03/11/93
03/11/93
SOLID
an, QA/QC Supervisor
~L--/
Jeffr Creager, Organics Manager
1414 Stanislaus se --'
Fresno, California 93706
Telephone (209) 485-8310
FAX (209) 485-6935
1-800-877-8310
,e-
^N^L YTICM
œ
L^ßORAroRIES
6,wWIØJfI¡J ......
BSK-Bakersfield
K & D Salvage
Date Sampled
Time Sampled'
Date Received
Date of Analysis
Report Issue Date:
Case Number : Ch930557
Lab ID Number 0557-2 Sample Type
Project Number : B93039
Sample Description: East Tank (500 Gal) 6'
Analyses for BTBX by BFA Method 8020
and TFH (G) by BFA Method 8015
Results Reported in Milligrams per Kilogram (mg/kg)
, Compound
Results DLR
ND 0.005
ND 0.005
ND 0.005
20 0.005
1000 1-
DLR Multiplier = 500
Benzene ........................
Tol uene ........................
Ethylbenzene ...................
Total Xylene Isomers ...........
Total Petroleum Hydrocarbons (G)
Sample DLR = DLR x DLR Multiplier,
DLR: Detection Limit for the Purposes of Reporting.
Exceptional sample conditions or matrix interferences
may result in higher detection limits.
RD: None Detected
Cynthia
'{!'~,)106 BTPs.t '
: 03/04/93
: 1255
03/05/93
03/11/93
03/11/93
SOLID
---
L/'
~t
Jeffr Creager, Organics Manager
QA/QC Supervisor
ANAL YTlc'!\l
~
lADORATORIES
¿;..,.\-....., ~
1414 Stanislaus se-,
Fresno, California 93706
Telephone (209) 485-8310
FAX (209) 485-6935
1-800-877-8310
e---,
BSK-Bakersfield
K & D Salvage
Date Sampled
Time Sampled
Date Received :
Date of Analysis :
Report Issue Date:
Case Number : Ch930557
Lab ID Number : 0557-3 Sample Type
Project Number B93039
Sample Description: West Tank (1000 Gal) 2'
Analyses for BTEX by EPA Method B020
and TPH (G) by EPA Method BOIS
Results Reported in Milligrams per Kilogram (mg/kg)
Compound
Results
DLR
Benzene ........................
ND
ND
ND
ND
ND
0.005
0.005
0.005
0.005
1.
Toluene ........................
Ethylbenzene ...................
Total Xylene Isomers ...........
Total Petroleum Hydrocarbons (G)
sample DLR = DLR x DLR Multiplier,
DLR Multiplier = 1
DLR: Detection Limit for the Purposes of Reporting.
Exceptional sample conditions or ~trix interferences
may result in higher detection limits.
RD: lIone Detected
Cynthia Pigman, QA/QC Supervisor
F-10106 BTPS.t
-ill --
Jeffr~ creager,POrganics Manager
: 03/04/93
1305
03/05/93
03/0B/93
03/11/93
: SOLID
1414 Stanislaus se,,-,,!
Fremo, California 93706
Telephone (209) 485-8310
FAX (209) 485-6935
1-800-871-8310
A\,
.-
ANAL YT ICt.l
œ
lABORATORIES
&MI....., ......
BSK-Bakersfield
K & D Salvage
Date Sampled
Time Sampled
Date Received
Date of Analysis :
Report Issue Date:
Case Number Ch930557
Lab ID Number : 0557-4 Sample Type
Project Number B93039
Sample Description: West Tank (1000 Gal) 6'
Analvses for BTBX by BPA Method 8020
and TPH (G) by BPA Method 8015
Results Reported in Milligrams per Kilogram (mg/kg)
Compound
Results DLR
ND 0.005
ND 0.005
ND 0.005
ND 0.005
ND L
DLR Multiplier = 1
Benzene ........................
Toluene ........................
Ethylbenzene ...................
Total Xylene Isomers ...........
Total Petroleum Hydrocarbons (G)
Sample DLR = DLR x DLR Multiplier,
DLR: Detection Limit for the Purposes of Reporting.
Exceptional sample conditions or matrix interferences
may result in higher detection limits.
ND: None Detected
Supervisor
#it ,-
Jeffr creager,~organics Manager
Cynthia Pigman,
: g. 1106 BTPS.t
03/04/93
1315
03/05/93
03/0B/93
03/11/93
SOLID
BSK Log Number
¿IIJ ~- J--;
\
ANALYSIS REQUEST ¡CHAIN OF CUSTODY RECORD
'I uLJO -' q. d 7 '::1
Client blame ~
K ~ ~ S-olva~e.
Aáaress C"? ~. .V,~ 1""'+- -
/c .(;_ ~ //7 --//" J. ( /J::e.:
City,.5tate, Zip r/ ,-, :;17"";; I Repon. ~enllon
~~·...s{,r::¡d) - "( Y.).)V"ý- .L.to-.
Sampled by __ r-,
Time ~ .L.~-- ..y-::r.., t:lc.-;C''''-
sampled See....1
below)
I Pro)eC<l..,or P.Q." - 9
k'ç';sC ~
¡Phone /I _....-= _;
~'S - :-,.;:,./-~/
Date
sampled
~-
y~
Sample deSCription
Number
of
::ontaíners
Lab
Sample
number
/ Analysis reQuired
Lab Use Only I (I
In this V
section ~ ,#
" ~ ?!' /,
Sample
Seals
(See key ¡¡
belOw) ~ c-;~ RemarICS
V .>(
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X
)(
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S' ø;..~~
./~ 7.'~')~ 5'0 £ÔŸ
J/¢ /;: $",.1'.... :>0 ¡; ar1'
J4 /."() ') /- St> tVdl
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IMPORTANT NOTICE: No samples will be analyzed without an authorized signature in this section,
I am hereby requesting BSK's Normal Chai~ustody Procedures tor the:tzPI I understand that
these proceòures are generally COI\SISIen! with ZCh08e . d In I 77.""""E';'. 846 d that there is no
extra charge for this service.
, ~
By:
.r /' Signature
§.jønature II /
ReIinQuistMId tr¡ Æ- /f ~Æ""¡'
r /{)'h~ Lt 'A ì ~ ()
I am hereby requesting BSK's Formal Chaì~USIOdy Procedures tor the above samples. I understand that
these procedures are generally consistent with those outlined in U.s. EPA Conlnld L.BbcnIoIy Program SUIte-
men! of Work. Section F, and that there is a charge of $50.00 per work order or ss.oo a bailie, whicheIIer is
grøaler,
By:
Authorized Signature
Date
Tuœ .
I
Print Name
Company
.ðJF. i?' 4' .!rfa-.lt"1-j
P£?t:--.
j'/~hJ' ;;Cb /J-.
3~5~., ì~}D
Received tr¡
;z;..~~ D. S" Q-d~1-
h. (Q¡(2P.{n
~
~
Relinquished by
Received by
Relinquished tr¡
ReceMId tr¡
..
ßSI< & Associates
Chemical Laboratories,
~ Type: AO-AQueous Sl-8ludge SQ-So PE-PøtroIeum m-other
Seals: P-PnIeenI A-AbIent 8-BrokIIn
DISTRIBUTION: WHITE, CANARY . LABORATORY PINK· ORIGIN,(TOR
NOI8:
Samples are discarded 14 days after results are reported unless other arrangements are made.
Hazardous samples will be returned to client or disposed of at client expense.
1414 Stanislaus Street Fresno. Califomia 93706
Telephone (209) 485-8310 . Fax (209) 485-7427
e
e
APPENDIX B
FIELD SAMPLING AND TESTING PROCEDURES
~
& Associates
e
e
APPENDIX B
FIELD SAMPLING AND TESTING PROCEDURES
TABLE OF CONTENTS
Page
INTRODUCTION . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .. 1
SOIL SAMPLING ........................................... 1
Exploratory Boring Locations . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .. 1
Soil Sampling Methods .................................... 1
Equipment Decontamination ................................. 2
Soil Cuttings Disposition ................................... 2
Field Logs/Documentation .................................. 2
LABORATORY TESTING ...................................... 3
Laboratory Analyses ...................................... 3
Laboratory Quality Control . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .. 3
BSK Jvb B93229 - October 1, 1993
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APPENDIX B
FIELD SAMPLING AND TESTING PROCEDURES
INTRODUCTION
This appendix presents soil sampling and analytical procedures to be utilized for a site
characterization to assess the presence and extent of gasoline constituents (TPH-G and BTEX)
and soluble lead in soil beneath the former site of a 500-gallon and a 1,OOO-gallon UST at K &
D Salvage, 600 South Union Avenue, Bakersfield, California. Field and laboratory
investigations will be conducted in accordance with the procedures described below.
SOIL SAMPLING
Exploratory Boring Locations
Exploratory soil borings will be located as described in the project workplan. Two working
days prior to commencement of the work, Underground Services Alert will be notified and on-
site underground utilities will be identified and indicated.
Undisturbed soil samples will be obtained at each boring location at five-foot depth increments
beginning at a depth of 10 feet BSG.
Soil Sampling Methods
A BSK geologist will be on site to coordinate the work, to take custody of the soil samples, and
to log soil types encountered during boring operations. Soil types will be visually described in
accordance with the Unified Soil Classification System and noted on boring logs with penetration
blow counts, PID readings, and other pertinent data.
Drilling will be performed by a truck-mounted drill rig equipped with hollow-stem augers. Soil
samples will be collected with a California split spoon sampler lined with stainless steel tubes
BSK Job B93229 - October 1, 1993
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Appendix B - Field SamPlingtt Testing Procedures
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Page 2
and driven through the center of the hollow-stem auger. The lowermost sample tube collected
in the split spoon sampler will be retained for chemical analyses. Ends of the sample tubes will
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be sealed with Teflon film, covered with· plastic caps,· labeled; and sealed with.~waterproof.tape
having non-petroleum adhesive. Samples will be identified by project number, sample number,
date and time of sampling, sampling personnel initials, and requested analyses. Soil samples
will be stored in an ice chest maintained at or near a temperature of 4°C and shipped to BSK's
California Department of Health Services certified laboratory in Fresno, California. Samples
will be accompanied by a chain-of-custody form. Chain-of-custody documentation will include
sampler's name, sample identification information, requested analyses, and times and dates of
custody transfers.
Equipment Decontamination
Drill bits, auger flights, and other ancillary equipment will be cleaned with a high pressure hot
water washer prior to drilling and between each boring location. Between soil sampling events,
samplers will be disassembled and washed in a solution of laboratory grade detergent, rinsed
with clean water, and reassembled with clean sample tubes to minimize the potential for cross
contamination between sampling events. Decontamination methods and equipment used will be
documented by the field geologist.
Soil Cuttings Disposition
Soil cuttings generated during boring operations will be used to backfill the boreholes upon
completion of each boring. Spent soil samples from laboratory analyses will be retained for a
period of 30 days from the date of analysis and will be disposed of in accordance with applicable
state and federal regulations after that time period has elapsed.
Field Logs/Documentation
Soil sampling operations, site and equipment conditions, variances from specified sampling
procedures, field observations, instrument readings and measurements, equipment and personnel
decontamination procedures, and soil sampling depths and locations will be documented by the
field geologist on prepared BSK forms. These forms will be retained in the project records.
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Appendix B - Pield Sampling .Testing Procedures
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Page 3
LABORATORY TESTING
Laboratory Analyses
Soil samples will be analyzed for TPH-G and BTEX by EPA Methods 8020 M and 80l5M, and
for soluble lead by the California Waste Extraction Test (WET) method set forth in Cal.Code
Regs.,tit.3,§66261.126 Appendix II.
Laboratory Quality Control
Internal quality control checks that will be used by the analytical laboratory to validate data will
include the following:
Calibration Check Standard - A calibration check standard containing all of the
analytes to be measured, internal standard, and surrogates will be performed at
the beginning of each day.
Instrument Performance Criteria - Instrument performance criteria will be
demonstrated every 12 hours in conformance with performance criteria defined
in EP A methods.
Matrix Spike - Matrix spikes to measure analytical accuracy will be analyzed at
a rate of one for every ten samples analyzed. If calculated spike recoveries do
not fall within acceptable ranges, corrective action will be taken before further
analyses are performed.
Analysis of Duplicate Samples - Duplicate samples will be run at a rate of one
for every ten samples analyzed to measure analytical precision.
Control Charts - Control charts prepared for each parameter determined by a
method will be supplied to each laboratory analyst to assess whether recoveries
are within acceptable limits.
Internal Standards - A known concentration of internal standard will be added
to every standard, blank, and sample which is analyzed for organic parameters
to compensate for minor fluctuations in instrument response.
Surrogate Standards - Samples will be spiked with a surrogate which is closely
related to the compound of interest before sample preparation.
BSK Job B93229 - October 1, 1993
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& Associates
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RECORDING REQUEITED BY
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RECORDED BY
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AND WHEN RECORDED MAIL TO
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NATHAN DANIELS
3318 Harmony Drive
¡~:~ Bakersfield, California
030960
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City II
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SPACE ABOVE THIS LINE FOR RECORDER'S USE-
Individual Grant Deed
THI. FO''''. ,"URN'SWED .,. TICOII TITL& 'MSU""".
The undersigned grantor(s} dec1ar§~~
Documentary transfer tax is $ .00- .
(XX) computed on full value of property conveyed, or \
.C. ) computed on full value less value of liens and eÌlcumbrances remaining at time of Sale,
tx ) Unincorporated area: ( ) City of , and
FOR A VALUABLE CONSIDERATION, receipt of which is hereby acknowledged,
ISABELLE DANIELS, a widoW1 and ISABELLE DANIELS, as Trustee of the
DANIELS QTIP TRUST
NA'l'HAN DANIELS, TruBtee of the NA'l'HAN DANIELS SURVIVORS
TRUST, Dated September 19, 1980
the following described real pro~ in the unincorporated area of the
County of Item . State of California:
FOR LEGAL DESCRIPTION, SEE EXHIBIT · A· A'l"l'ACBED BERETO AND MADE A
PART BEREOF.
hereby GRANT(S} to
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ISABELLE DANIELS
STATE OF CALlFORNtA -}
COUNTVOF RIVERSIDB ss. ~ ~...r ~
On MARCH 21. 1984 before u ~
me, the undcrsiped, . Notary Public in and for said State, '
penona1ly appeared
ISABELLE DANIELS
/,,:nollally luwwn to me or proved ro me on the basis of sat·
ISfactory evidence to be the penon_ ,mose name 18
subscribed to the within instrument and acknowleð¡;ed
that she executed the same.
.'TN"'çC'.w& _ A(þ
Signature t"'\ ..,(\ 1 ß ,
Dated:
March 16, 1984
(This arca for official notar¡d ~aI)
Title Order No.
Escrow r: Loan No.
MAIL TAX STATEMENT: AS DIRECTED ABOVE
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APPENDIX C
HEALTH AND SAFETY PLAN
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APPENDIX C
HEALTH AND SAFETY PLAN
TABLE OF CONTENTS
Page
INTRODUCTION . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .. 1
PURPOSE OF HEALTH AND SAFETY PLAN ......................... 1
APPLICABILITY OF THE PLAN . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .. 1
RESPONSIBILITIES .......................................... 2
Project Manager (BSK & Associates) . . . . . . . . . . . . . . . . . . . . . . . . . . ., 3
Site Safety Officer (BSK & Associates) . . . . . . . . . . . . . . . . . . . . . . . . . ., 3
Branch Health and Safety Officer (BSK & Associates) . . . . . . . . . . . . . . . . .. 4
Project Personnel (BSK & Associates) . . . . . . . . . . . . . . . . . . . . . .. 5
Subcontractor's Safety Representative . . . . . . . . . . . . . . . . . . . . . . . . . . .. 5
JOB HAZARD ANALYSIS .. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . ., 6
Gasoline Constituents . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .. 6
Lead . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .. 6
Noise Hazards. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .. 7
Drill Rig Hazards . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .. . . . . .. 7
Underground Utilities and Overhead Obstructions. . . . . . . . . . . . . . . . . . . .. 9
Traffic Hazards ......................................... 9
Personal Protective Equipment (PPE) . . . . . . . . . . . . . . . . . . . . . . . . . . .. 9
Heat Stress Recognition and Control ........................... 10
EXPOSURE MONITORING PLAN . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .. 11
DECONTAMINATION PROCEDURES ............................. 11
SITE CONTROL ........................................... 12
SAFE WORK PRACTICES . . . . . . . . . . . . . . . . . . . . . . . , . . . . . . . . . . . .. 12
HEALTH AND SAFETY EQUIPMENT LIST ......................... 13
EMERGENCY RESPONSE PLAN ................................ 14
Fire and Fire Extinguishers . . . . . . -. . . . . . . . . . . . . . . . . . . . . . . . . ., 14
Communication (Telephones) . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . ., 14
BSK Job B93229 - Oerobe,l, 1993
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TABLE OF CONTENTS (CONTINUED)
Incident Report ........................................ 14
Operation Shutdown ..................................... 15
SIGNATURE PAGE ......................................... 16
FIGURES
Figure 4 . . . . . . . . . Hospital Location Map
BSK Job B93229 - October 1, 1993
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& Associates
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APPENDIX C
HEALTH AND SAFETY PLAN
INTRODUCTION
This plan has been prepared to provide health and safety guidelines for conducting a site
characterization at 600 South Union Avenue, Bakersfield, California. Purpose of the proposed
investigation is to assess the presence and extent of gasoline constituents (TPH-G and BTEX)
and soluble lead in subsurface soils at a former UST site.
PURPOSE OF HEALTH AND SAFETY PLAN
Purpose of this plan is to assign responsibilities, establish personal protection standards and
safety procedures, and provide for contingencies that may arise during proposed project
operations at the site. This plan complies with, but does not replace, Federal Health and Safety
regulations as set forth in 29 CFR 1910 and 1926, California Health and Safety Regulations as
set forth in Title 8, California Code of Regulations, and guidance established by the California
Department of Health Services. This plan is to be used by BSK & Associates (BSK) personnel
as a supplement to such rules, regulations, and guidelines.
APPLICABILITY OF THE PLAN
Provisions of this plan are mandatory for on-site BSK employees engaged in hazardous material
management activities including but not limited to initial site reconnaissance, preliminary field
investigations, mobilization, project operations, and demobilization. Invasive work will be
limited to exploratory soil borings with hollow-stem augers. Changing or unanticipated site
conditions may require modification of this plan to maintain a safe work environment.
Modifications to the plan should be recorded in field notes and reviewed with site personnel.
Under no circumstances will modifications to this plan conflict with federal, state, or local health
and safety regulations. Daily tailgate meetings will be held to emphasize work site hazards,
safety procedures, and concerns of on-site personnel.
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Appendix C - Health and safetAtn
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Page 2
If applicable, BSK will provide a copy of this plan to a representative of each on-site BSK
subcontractor in compliance with 29 CFR 1910.120 and will inform subcontractors of potential
site hazards. Each subcontractor shall provide a health and safety plan to its employees covering
exposure to hazardous materials and shall complete work in accordance with that plan. BSK
reserves the right to review each subcontractor's plan for applicability to potential site hazards.
BSK reserves the right to suspend its subcontractor's site work and ask the subcontractor's
personnel to evacuate the exclusion zone in the event of deficient health and safety procedures
on the part of the subcontractor or if the subcontractor's personnel are, or may be, exposed to
an imminent health hazard.
The subcontractor shall provide its own safety equipment in accordance with its health and safety
plan requirements. The subcontractor will comply with all regulations, including OSHA 29 CFR
1910.134 (Respiratory Protection), Title 8, CCR, Section 5192 (Hazardous Waste Operations
and Emergency Response), and 29 CFR 1910.120 (Hazardous Waste Operations), and 29 CFR
1910.95 (Noise Hazards and Hearing Protection).
RESPONSIBILITIES
BSK will maintain site health and safety oversight and coordinate responsibilities for BSK
employees; however, each subcontractor will be held accountable for the safe and healthful
performance of work by each of their employees, subcontractors, or support personnel who may
enter the site.
Subcontractors involved in handling contaminated soils and groundwater shall require their
employees, visitors, subcontractors, and their suppliers/vendors to comply with the minimum
standards set forth by OSHA and the subcontractor's site health and safety plan while on the
work site and during the performance of their contractual duties. Specific operations not covered
in this plan will be governed by other applicable federal, state, and local regulations. The
subcontractors are required to know and comply with the safety regulations that apply to their
operations.
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Appendix C - Health and sar-,an
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Provisions of this plan combined with applicable regulations issued by governmental entities will
be strictly adhered to by BSK.
Project Manager (BSK & Associates)
The Project Manager (PM) will direct the on-site investigation and BSK personnel. The PM
may delegate all or part of these duties to the Site Safety Officer (SSO).
At the site, the PM and/or the SSO has primary responsibility for:
· The availability, maintenance, and proper use of appropriate
personal protective equipment (PPE).
· Familiarity of on-site BSK personnel of the provisions of this plan,
instruction of on-site BSK personnel in the work practices necessary to
maintain safety, and instructing on-site BSK personnel of emergency
procedures.
· Ascertaining that BSK field personnel have requisite 40 hour health and
safety training, 8-hour annual updates, and have been fit tested for the
appropriate respirators.
· Advising on-site BSK personnel of potential hazards associated with site
operations.
· Monitoring the performance of personnel regarding safe work practices.
· Removing BSK or subcontractor employees who do not comply with safe
work practices.
· Correcting unsafe work practices or hazardous conditions that may result
in personal injury or exposure to hazardous substances.
· Directing emergency response operations.
· Preparing accidentlincident reports.
· Halting site operations, if necessary, to correct unsafe work practices.
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Appendix C - Health and safetyln
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Page 4
Site Safety Officer (BSK & Associates)
The Site Safety Officer's (SSO) duties may be carried out by the PM or other site manager. To
protect the health and safety of BSK personnel, the SSO shall:
· Implement project health and safety plans, and report changes from the
anticipated conditions described in the plan to the PM, and, if necessary,
the Branch Health and Safety Manager (BHSM).
· Verify that monitoring equipment is calibrated daily.
· Maintain air quality monitoring equipment and verify that it is operating
correctly.
· Identify site personnel with special medical problems (e.g., allergies,
perforated eardrum, etc.) and confirm their suitability to work based on
physician's recommendations.
· Monitor workers for signs of physical stress such as heat exhaustion,
fatigue, or chemical exposure.
· Conduct daily tailgate safety meetings.
· Approve selection of personal protective equipment and monitor its
maintenance and proper use.
· Monitor decontamination procedures used by site personnel.
· Monitor exposure to chemical and physical hazards.
· Control entry and exit to work site during site operations.
· Coordinate emergency medical care in the event of an accident.
· Be aware of emergency procedures, emergency telephone numbers, and
hospital location.
Branch Health and Safety Officer (BSK & Associates)
The Branch Health and Safety Officer (BHSO) shall:
· Review this plan for appropriateness prior to commencement of work.
· Audit on-site operations for compliance with this plan.
· Provide health and safety support as requested by the SSO and PM.
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Project Personnel (BSK & Associates)
Project personnel involved in on-site investigations and operations are responsible for:
· Taking reasonable precautions to prevent injury to themselves and to their
fellow employees.
· Performing only those tasks that they believe they can do safely.
· Immediately reporting accidents and/or unsafe conditions to the SSO, PM,
or BHSO.
· Following procedures set forth in this plan, and reporting any deviations
from the procedures described in the plan to the SSO or PM for corrective
action.
· Notifying the PM and SSO of medical problems or symptoms of exposure
to hazardous materials or conditions.
BSK personnel associated with the field operations of the project include:
Branch Health and Safety Officer. . . . . . . . . . . . . .Ivan D. Sanderson
(805) 327-0671
Project Manager. . . . . . . . . . . . . . . . . . . . . .Ivan D. Sanderson
(805) 327-0671
Site Manager/Site Safety Officer
. . . . . . . . . .
. . .Ivan D. Sanderson
Subcontractor's Safety Representative
Each subcontractor is required to designate an on-site safety representative. That individual is
responsible for safe work practice by his work force and subcontractors. During the
subcontractor's activities on site, the safety representative will perform work area safety
inspections, conduct daily safety meetings, and orient new employees to safe work practices and
site conditions. He will attend daily safety meetings with the SSO. The subcontractor's
representative will also investigate accidents involving the subcontractor's personnel and report
accidents to the SSO.
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Appendix C - Health and safety.n
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JOB HAZARD ANALYSIS
Potential chemical hazards include those associated with exposure to gasoline constituents and
lead in soil. Physical hazards that may be encountered on site include those from drill rig
operations, cold or heat stress, noise, underground and overhead utilities, on-site traffic, and
equipment failures.
Gasoline Constituents
Workers may be exposed to gasoline and its constituents at this UST removal site. Of these
benzene, a carcinogen, is considered the greatest potential health risk. Principal routes of
absorption are inhalation, absorption, skin and/or eye contact, and ingestion. Protective
measures include respirators, safety glasses and face shields, disposable protective clothing, and
disposable protective gloves. Decontamination is by washing with soap and water.
First aid for exposure to gasoline is:
Eye: Flush eyes immediately with fresh water for at least 15 minutes while holding the eyelids
open. Remove contact lenses if worn. No additional first aid should be necessary. However,
if irritation persists, see a doctor.
Skin: No first aid procedures are required. As a precaution, wash skin thoroughly with soap
and water. Remove and wash contaminated clothing.
Inhalation: If respiratory irritation or any signs or symptoms of nervous system toxicity occur
(headache, dizziness, loss of appetite, weakness, loss of coordination, loss of consciousness,
coma), move the person to fresh air. If any of these effects continue, see a doctor.
IF VICTIM IS NOT BREATHING OR IF BREATHING DIFFICULTIES
DEVELOP ARTIFICIAL RESPIRATION OR OXYGEN SHOULD BE
ADMINISTERED BY QUALIFIED PERSONNEL.
Ingestion: If swallowed, give water or milk to drink and telephone for medical advice. DO
NOT make person vomit unless directed to do so by medical personnel. If medical advice
cannot be obtained, take the person and product container to the nearest medical emergency
treatment center or hospital.
Lead
Workers may be exposed to lead in soil and dust generated from drilling and sampling
operations. Exposure to lead should be minimized because of its toxic effect on humans. The
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current National Institute For Health and Safety (NIOSH) Permissible Exposure Level (PEL) for
lead in the breathing atmosphere is < 0.01 mg/m3 based on a lO-hour time weighted average
(TW A). Principal exposure routes for lead are inhalation, skin or eye contact, and ingestion.
Symptoms of lead exposure include: eye irritation, lassitude, and pallor.
Skin contact with potentially contaminated soil or groundwater will be minimized by wearing
personal protective clothing. Ingestion of contaminated materials will be minimized by good
personal hygiene during work (i.e., thoroughly washing face and hands with soap and water
before eating or drinking).
First aid for exposure to lead is:
Eye: Flush the affected eye with water and seek medical assistance if irritation develops.
Skin: Remove contaminated clothing and flush contact areas with water and then thoroughly
cleanse contact area by washing with soap and water. If irritation develops seek medical
attention.
Breath: IF VICTIM IS NOT BREATHING OR IF BREATHING DIFFICULTIES
DEVELOP ARTIFICIAL RESPIRATION OR OXYGEN SHOULD BE
ADMINISTERED BY QUALIFIED PERSONNEL.
Swallow: Seek immediate medical assistance.
Noise Hazards
The primary noise hazard at this site is from the drilling equipment which may produce
continuous and impact noise at or above the OSHA PEL in the immediate proximity of the
equipment. Personnel within 25 feet of drill rigs shall wear hearing protective devices (either
muffs or plugs).
Drill Rig Hazards
Safe work practices for drill rig operation include:
. When moving a drill rig off-road, pay particular attention to
obstacles in the route of travel. Walk the route first.
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Appendix C - Health and Safeten
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· Providing an assistant to guide the driver when in close proximity to
hazards or if clearance is at a minimum.
· Setting the brakes and/or blocking the wheels when the mast is raised.
· Lowering the mast when moving the rig.
·
Confirming the status of utilities (energized, charged, etc.) prior to
drilling. Call Underground Service Alert (800-642-2444) to locate
underground utilities.
I -
· Considering overhead lines to be energized. Watching for low
overhead lines when entering a site; and call the utility for assistance
in moving them.
· Operating the drill rig at least 15 feet from overhead lines; checking
with local utility companies to confirm line voltage and distance
requirements .
· Clearing the site of obstructions, debris, etc., prior to setting up the
drill rig.
· Maintaining proper "housekeeping" around and on the drill rig at all
times. Tools should be stored in a manner that permits convenient
access but also provides for personnel safety.
· Keeping platforms, walkways and scaffolding free of obstructions and
excess grease or oil that could cause a surface to become slick and
dangerous.
· Storing gasoline and other flammable substances only in approved
storage containers equipped with spark arresters.
· Inspecting drill rig equipment prior to starting work; repairing or
replacing faulty items.
· Handling augers with care. Using proper lifting technique; use a tool
hoist for large or heavy augers. Staying clear of rotating augers and
machinery.
· Leveling and stabilizing the drill rig prior to raising the mast and prior
to drilling.
· Watching for slippery surfaces when mounting or dismounting the
platform.
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Appendix C - Health and Safet.
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Page 9
· Covering or barricading unattended boreholes.
· Avoiding drilling during electrical storms.
Underground Utilities and Overhead Obstructions
BSK will attempt to locate underground utilities prior to the commencement of drilling activities.
Resources will include site plans, underground utility diagrams provided by the owner, and hand
augering prior to drilling. Care will be exercised when moving the drill rig and other equipment
in areas where overhead obstructions are present.
Traffic Hazards
Traffic cones and/or barricades shall be used to delineate the work/exclusion zone.
Personal Protective Equipment (PPE)
Minimum PPE for Site Personnel:
· Hard hat
· Steel-toed boots or shoes
· Safety glasses with side shields
Work/Exclusion Zone PPE Requirements:
· Hard hat
· Eye protection (face shield or safety glasses with side shields)
· Steel-toed work boots
· Hearing protection within 25 feet of operating drilling rig
· Work gloves
· Coveralls or long-sleeved shirts
Based on subjective evidence of contamination, the following would be donned at the discretion
of the SSG or PM:
· Tyvek coveralls
· Chemical-resistant steel-toed boots
· Nitrile gloves (drillers can wear under work gloves)
· Surgical latex or vinyl gloves (inner)
· Half or full face respirators with organic vapor cartridges.
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PPE may be downgraded from Level "C" to Level "D" at the discretion of the 8S0.
Heat Stress Recognition and Control
Heat stress is likely to be a significant hazard when ambient temperatures exceed 85°P. Some
effects of heat stress include flushed skin, rash, irritability, faintness, or dry, cool skin.
Wearing PPE can place a worker at an elevated risk of developing heat stress. This can result
in health effects ranging from transient heat fatigue to serious illness or death. Heat stress is
caused by a number of interacting factors including environmental conditions, clothing, work
load, and the physical condition of the worker. Because heat stress is one of the most common
(and potentially serious) illnesses at hazardous waste sites, rest periods, adequate drinking water
intake, and regular monitoring for signs and symptoms of distress are vital.
Heat-stress monitoring should be conducted if personnel are wearing PPE (including Tyvek-type
coveralls) and the ambient temperature exceeds 70 degrees Fahrenheit. If impermeable garments
are not worn, monitoring should commence when ambient temperatures exceed 85 degrees.
Heat-stress monitoring should be conducted by measuring worker's heart rate at the beginning
of each rest period (i.e. during the first minute). The worker's heart rate should not exceed 110
beats per minute during the first minute, and should decrease by 10 beats per minute for each
of the following three minutes. If the heart rate exceeds this amount, shorten the next work
cycle by a factor of one third and maintain the same rest period. Suggested monitoring
frequencies are shown in the following table.
Ambient Temp (oF) Not Wearing PPE Wearing PPE
77.5 - 77.5 After each 150 minutes of work After each 120 minutes of work
77 ,5 - 82.5 After each 120 minutes of work After each 90 minutes of work
82.5 - 87.5 After each 90 minutes of work A fter each 60 minutes of work
87.5 - 90 After each 60 minutes of work After each 30 minutes of work
90 and above After each 45 minutes of work After each 15 minutes of work
When wearing PPE during warm weather conditions, a personal cooling vest or equivalent is
recommended. To help prevent heat stress, site personnel shall drink a sufficient quantity of
BSK l()b B93229 - October 1, 1993
~
& Associates
Appendix C - Health and safeten
e
Page 11
water to maintain their body fluids at normal levels. Daily fluid intake must be approximately
equal to the amount of water lost through perspiration. The normal thirst mechanism is not
sensitive enough to provide for sufficient consumption of water to replace lost fluids. The
following is recommended during warm or hot weather conditions:
· Maintain an adequate supply of drinking water at a temperature of 50°
to 60°F.
· Drink at least 16 ounces of fluid (preferably water or electrolyte
replenishing drink) before beginning work.
· Drink a cup or more of water or equivalent fluid every 15 to 20
minutes, or during each rest period. A total of 1 to 1.5 gallons of
fluid per day are recommended, but more may be necessary depending
on physical condition of the worker and ambient temperature.
EXPOSURE MONITORING PLAN
Heat stress, nOIse, and chemical exposures may be encountered at this site. Monitoring
procedures for these conditions are presented above. Noise levels will not be monitored;
personnel will wear hearing protection.
Drilling operations are not expected to generate a sustained dust cloud. If necessary, a water
mist may be applied to reduce dust. Unusual or unrecognized odors or other chemical warnings
noticed during work activities will result in cessation of work until the hazard is identified and
the risk assessed by the SSO.
DECONTAMINATION PROCEDURES
A high-pressure hot water washer will be used for decontamination of shovels, auger flights, and
other equipment.
Rubber boots and gloves will be cleaned with a stiff bristle brush, detergent, and water. Tyvek
coveralls, disposable gloves, and spent respirator cartridges should be bagged on site and
disposed of with drill cuttings.
BSK Job B93229 - October 1, 1993
~
& Associates
Appendix C - Health and safeta
e
Page 12
Respirators will be washed, sanitized, and stored in a clean plastic bag or case after each day's
work. Each employee will be responsible for cleaning and maintaining his/her respirator.
SITE CONTROL
Entry into hazardous areas shall be limited to individuals who must work in those areas and are
qualified to do so. Authorized visitors may be allowed to enter the exclusion zone only if they
have read and understand this document and have agreed to abide by the requirements set forth,
have the requisite health and safety requirements, are willing to follow the instructions of the
SSG, and have been informed of the potential hazards and risks associated with them.
Traffic cones, barricades, and warning tape will be used to delineate an exclusion zone around
the drill rig and work area. The exclusion zone should encompass a 25-foot radius around the
rig and work area.
SAFE WORK PRACTICES
The following generai guideiines are presented.
· Eating, drinking, chewing gum or tobacco, and smoking are
prohibited within the exclusion zone.
· Avoid contact with potentially contaminated substances. Do not walk
through puddles, pools, mud, etc. Avoid, whenever possible,
kneeiing on the ground, leaning or sitting on equipment or ground.
Do not place monitoring equipment on potentially contaminated
surfaces.
· Field crew members should remain aware of potentially dangerous
situations (i.e., presence of strong, irritating or nauseating odors).
· Prevent, to the extent possible, spillage. In the event that a spill
occurs, contain liquid if possible.
· Prevent splashing of contaminated materials.
· The number of personnei and equipment in the exclusion zone should
be minimized, but oniy to the extent consistent with work force
requirements for safe site operations.
8SK Job 893229 - October 1, 1993
~
& Associates
Appendix C - Health and safety.n
e
Page 13
· Only personnel trained (Title 8, CCR, Sec. 5192) and authorized will
be permitted to work in or enter the exclusion zone.
· Personal protective equipment shall be used as specified by the 550.
During drilling and sampling activities, the following safe work practices shall be employed:
· Drilling and sampling equipment will be decontaminated before
proceeding to the drill site.
· At the drilling or sampling site, sampling equipment will be
decontaminated after each use.
· Work in areas of low expected contamination levels should be
conducted first where practical. Work upwind of the contaminated
area, if possible.
· The minimum number of personnel necessary to achieve the objectives
shall be allowed within the exclusion zone.
· If emergency and backup subcontracted personnel are at the site, they
will remain 25 feet upwind from the exclusion zone, where practical.
· Unauthorized personnel will remain outside the exclusion zone at all
times.
HEALTH AND SAFETY EQUIPMENT LIST
· Hard hats
· Safety glasses with side shields
· Ear plugs or muffs
· Tyvek coveralls
· Chemical resistant steel-toed boots or steel-toed boots with chemically
resistant boot covers
· Work gloves
· Nitrile gloves
· Surgical vinyl inner gloves
· Half or full face respirators with orgamc vapor cartridges
and dust and mist prefilters
· Traffic cones and/or barricades
· Wash tubs, scrub brushes, and detergent
· First aid kit
· Drinking water or electrolyte replenishing-type beverage
· Type ABC fire extinguishers
BSK Job B93229 - October J, 1993
~
& Associates
APpendi; C - Health and Safet~n
e
Page 14
EMERGENCY RESPONSE PLAN
In the event of a fire or medical emergency, the following numbers may be called for assistance:
BAKERSFIELD FIRE DEPARTMENT. . . . . . . 911
AMBULANCE ..................... 911
BAKERSFIELD MEMORIAL HOSPITAL
420 34TH Street, Bakersfield, CA .......... (805) 327-1792
BAKERSFIELD POLICE DEPARTMENT 911
POISON CONTROL CENTER .. . . . . . . . . . . (800) 642-2442
Bakersfield Memorial Hospital, located approximately 2 112 miles north from the project site at
420 34th Street in Bakersfield, is the closest general receiving emergency hospital (Hospital
Location Map, Figure 4). A first aid kit will be available at the site for use in case of minor
injuries. If direct contact with contaminants occurs, affected skin areas shall be immediately
washed with soap and water.
Fire and Fire Extinguishers
Type ABC fire extinguishers will be available on site to contain and extinguish small fires. The
local fire department will be summoned (911) in the event of a fire on site.
Communication (Telephones)
The nearest telephone is available at the eastern portion of the site at the office of Double D
Recycling.
Incident Report
In the event of an incident resulting in injury or illness, work is to be stopped until the SSG has
determined the cause of the incident and has taken appropriate action. An injury or illness,
regardless of severity, is to be reported to the SSO or PM. The SSO will be responsible for
completion of an accident report.
BSK Job B93229 - OClober 1, 1993
~
& Associates
Appendix C - Health and safet.
e
Page 1 S
Operation Shutdown
If conditions arise which could result in physical injury or chemical exposure the PM, SSO, or
subcontractor's safety representative shall request that operations be suspended until the
condition is corrected or controlled. The SSG will have ultimate authority for operation
shutdown and restart of operations.
8SK Job 893229 - October 1, 1993
~
& Associates
Appendix C - Health and safety.
e
Page 16
.
SIGNATURE PAGE
HEALTH AND SAFETY PLAN - SITE CHARACTERIZATION
600 SOUTH UNION A VENUE
BAKERSFIELD, CALIFORNIA
The undersigned employees of BSK & Associates have read this Site Health and Safety Plan in
conjunction with the project described above, on the date(s) indicated.
Department Manager: Date:
Project Manager: Date:
Staff Engineer/Geologist: Date:
Driller: Date:
Helper: Date:
Technician: Date:
Other: Date:
Other: Date:
Other: Date:
Other: Date:
Other: Date:
BSK Job B93229 - Oc/ober 1, 1993
~
& Associates
e
e
ENVIRONMEt" AL HEALTH SERVIC~· DEPARTMENT
STEVE McCALLEY, R.E.H.S.
DIRECTOR
2700 -M- Street. Suite 300
Balterlfield, CA 93301
(805) 861-3636
(805) 861-3429 FAX
FebruélI)' 24, 1994
REMEDIAL ACTION COMPLETION CERTIFICATION
Nat Daniels
K & D Salvage (formerly Golden State Metals)
600 Union Avenue
Bakersfield, CA 93307
SUBJECT:
Location:
Known As:
Site No.:
600 Union Avenue, Bakersfield, CA
Golden State Metals
250011
Dear Mr. Daniels:
This letter confirms the completion of site investigation and remedial action for the
underground storage tank(s) at the above site. Thank you for your cooperation throughout
this investigation. With the provision that the information provided to this agency was
accurate and representative of site conditions, no further action related to the underground
tank release is required based on the available information as set forth in California Code
of Regulations, Title 23, Division 3, Chapter 16, Article 11, Section 2721(e) (Underground
Storage Tank Corrective Action Regulations).
If you have any questions regarding this matter, please contact Flora Darling at (805)
861-3636, Extension 549.
Steve McCalley, Director
Environmental Health Services D
SMc:FD:ch
dar1ing\250011.a
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ENVIRONMENTAL HEALTH SERVICES DEPARTMENT
STEVE McCALLEY, R.E.H.S.
DIRECTOR
2700 -M- Street. Suite 300
Bakersfield. CA 93301
(805) 861-3636
(805) 861-3429 FAX
December 9, 1993
Ivan Sanderson
BSK & Associates
117 "V" Street
Bakersfield, CA 93304
SUBJECf:
Workplan for K & D Salvage
Dear Mr. Sanderson:
This Department· has once again closely reviewed your workplan for assessment of soil
contamination at the above-mentioned facility and have reconsidered our position. The
workplan is adequate for implementation.
I believe a misunderstanding as a result of different interpretations of language used in the
workplan is the reason for not receiving initial approval. In the future please do not
hesitate to call me if an issue cannot be resolved with the person assigned a case.
Thank you for your patience in resolving the perceived problem. Please contact Flora
Darling forty-eight (48) hours in advance of the proposed drilling date.
Sincerely,
Steve McCalley, ~ctor
I ~ L'dA.--- ~
By:/JOe Cañas, R.E.H.S.
Interim Program Supervisor
Hazardous Materials Management Program
JC:ch
cc: Nat Daniels
canas\sanderso.let
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ENVIRONMENTAL HEALTH SERVICES DEPARTMENT
STEVE McCALLEY. R.E.H.S.
DIRECTOR
2700 -M- Street, Suite 300
Bake~fi~,CA 93301
(805) 881-3636
(805) 881-3429 FAX
November 1, 1993
BSK and Associates
117 "V' Street
Bakersfield, CA 93304
A TIN: Ivan Sanderson
K. & D. Salvage
600 Union Avenue
Bakersfield, CA 93307
Permit #: 250011
Dear Mr. Sanderson:
SUBJECT:
This office is in receipt of your letter dated October 27, 1993, addressed to Mr. Nathan
Daniels. Your comments are appreciated; however, five (5) test holes are considered
excessive. Three (3) test holes should be adequate to determine the vertical and lateral
extent of the petroleum hydrocarbon plume. One test hole should be placed at the center
of the former underground tank location to define the vertical extent of the contamination.
To define the lateral extent of the plume, one test hole should be located within a fifteen
(15) foot radius of the vertical test hole. If contamination is found to be present, one
additional test hole selected to define the lateral migration of the plume should be
adequate. Additional test holes in excess of three (3) must have the concurrence of the
hazardous materials specialist present on site during the investigation and the owner
(responsible party).
Please submit an addendum plan view of the site depicting the test hole locations. Upon
receipt of the additional information, this office will continue its review.
Contact me at (805) 861-3636, Ext. 549, if you have any questions.
Sincerely,
Steve McCalley, or
By: Flora ¿~.s., R.EA
Hazardous Materials Specialist III
Hazardous Materials Management Program
FD:ch
cc: Mr. Nathan Daniels
3318 Harmony Drive
Bakersfield. CA 93306
-
.
& AssOCiates
.
-
( . "v" St t
~_. ree
BakerSfield, CA 93304
(805) 327-0671
(805) 324-4218 FAX
~,
....
October 27, 1993
l~ ." q
Mr. Nathan Daniels
3318 Harmony Drive
Bakersfield, Califotnia 93306
~
R.epon 2
Dear Mr. Daniels:
SlIBJECT: Site Assessment W orkplao Addendum
K & D Salvage
600 South Union A venue
Bakersfield, California
1.
:SK & ASSOCiates is in receipt of a letter (attached) &om Ms. Flora Darling of Kern C ty
nYlr°lUnentaJ Health Services DepartnJent (KCEHSD) requesting 1J1inor chan es in ouroun
W orkplao that We sUbmItted on OctOber I, 1993. This addend"", to the Wor~lao addresses
the ISSUes raIsed. Please SUbmit one COpy to KCElfSD.
FiYe test holes /]Jay not be excessive, aod three test holes /]Jay not be adequate EsK
reserves the right to modify the n""'ber of test holes On the basis of findings d~ring
he held InYestlgatIon, WIth the concurrence of the on-site Hazardous Materials
pecIabst.
A spacing in increments of ten feet radially arOUnd the f011)]er lJST center is
reaS?nable because the contanunatlOn may be laterally extensive. Where the
stratIficatIon sequence cOnsists of POrous sand underlain by silty Clay, ao incleased
~otentlal for lateral mIgratIOn of contaQ¡inants mUst be cOnsidered. To restrict test
.onngs to fifteen feet from the center of the contan,¡nation zOne Places ao unneeded
1111l1tatIon On the SIte characteriza.tion effort. BSK reserves the right to change lateral
spacIng of the bonngS On the baSIs of f111d111gS during the field investigation with the
concurrence of the Hazardous Materials SPecialist from KCElfSD Who tr, .11 'b
present. wI e
The secOnd sentence in the secOnd paragraph On page 5 should read, "Addif 1 '1
borlIlgS w1lJ be located at 10, 20, 3D, aod 40 feet from the center oi the forn:~~:~'
POSd'tron to the. West, south, nort¡ aod east, resPectively, to assess the lateral extent of
pro Uct mIgratIOn. "
Site Geology: The Property oWner repOrts that there are no SUmps Or dry WelJs On
the SIte. The Kern 1s1_ Canal (l11]jined) is preSent about II, mile south of the lJST
SIte.
1229 - October 27, 1993
'!ering . Engineerinq G",,,,__
e _
ENVIRONMENTAL HEALTH SERVICES DEPARTMENT
STEVE McCALLEY. R.E.H.S.
DIRECTOR
2700 -M- Street, Suite 300
Bakersfield, CA 93301
(805) 881-3838
(805) 881-3429 FAX
October 20, 1993
BSK & Associates
117 "V" Street
Bakersfield, CA 93304
Attn: Ivan Sanderson
SUBJECf: K & D Salvage
600 Union Avenue, Bakersfield, CA
Permit # 250011
Dear Mr. Sanderson:
The proposed site characterization workplan prepared by your firm for the above-noted
facility has been reviewed. Our review has revealed several items that must be clarified
prior to this Department granting approval for work to begin. The items of concern are
listed below. Please provide this office with the addendum information within thirty (30)
days of the date of this letter.
1. Site geology (p. 4): In regard to the local topography, describe any sumps, dry
wells and adjacent wateIWays that are present at the site.
2. Field exploration (p. 5): Five (5) test holes are excessive. Delete two (2) test
holes. The distances between the test holes do not correspond with the
locations depicted on the plan view. Lateral test holes should remain within
fifteen (15) feet of the test hole selected to define the vertical depth of the·
contamination plume. Vertical depths of all test holes must be advanced until
field observation and field instrument readings indicate "nondetect" (N.D.)
from a minimum of two (2) consecutive five (5) feet of soil samþles.
Describe the rationale for the selection of the proposed test holes.
3. The abandonment of completed test holes (p. 5) does not agree with the
procedures described in Appendix B, p. 2: Please be specific.
Any modification in the field of an approved workplan must have concurrence from the
Hazardous Materials Specialist present during the field investigation. In addition, the
number of soil samples selected from each test hole for laboratory analyses must be
adequate to obtain a representative profile of the contamination.
-
e e
BSK & Associates
Subject: 600 Union Avenue, Bakersfield, CA - Permit #250011
- October 20, 1993
Page 2
Upon the receipt of the addendum information addressing the above items, this office will
be able to continue our review.
If you have any questions, you may contact me at (805) 861-3636, extension 549.
Sincerely,
FD:cas
cc: Nat Daniels
K & D Metals
3318 Harmony Drive
Bakersfield, CA 93306
\t1ora\250011.1tr
-
ENVIRONME'TAL HEALTH SERVIC'S ;~EPARTMENT
STEVE McCALLEY, R.E.H.S.
DIRECTOR
2700 -M- Street, Suite 300
Bakersfield, CA 93301
(805) 861-3636
(805) 861-3429 FAX
July 22, 1993
Nat Daniels
K & D Metals
3318 Harmony Drive
Bakersfield, CA 93306
SUBJECT:
Location:
Known As:
PERMIT #:
600 Union Avenue, Bakersfield, CA
K & D Salvage
250011
Dear Mr. Daniels:
The intent of this letter is to inform you of the necessary deadlines for work required at the
property described above. As a responsible party for a leaking underground storage tank, you
have previously received a letter from this Department notifying you of the required work
necessary to identify the extent of the contamination. We are now requesting that this work,
outlined in UT-35 , be done in a timely manner.
In accordance with California Health and Safety Code, Chapter 6.7, and Kern County Ordinance
Code, Chapter 8.48, the Kern County Environmental Health Services Department requires a
determination of the threat to the environment. Accordingly, you must select an environmental
contractor and submit a site characterization workplan proposal to this office by August 23, 1993.
The workplan must be approved by this Department before any work is started.
If you should have any questions regarding this matter, please contact me immediately at (805)
861-3636, Ext. 549.
Sincerely,
FD:ch
darling\250011.121
Jo
STEVE McCALLEY. R.E.H.S.
DIRECTOR
2700 -M- Street, Suite 300
Bakersfield, CA 93301
(805) 861-3636
(805) 861-3429 FAX
April 7, 1993
...
Nat Daniels K ~ 0 M-e"tI'\c....5
Golden State Metals
3318 Harmony Drive
Bakersfield, CA 93306
SUBJECf: Location: 600 Union Avenue
Bakersfield, CA 93306
Known as: Golden State Metals
PERMIT #: 250011
Dear Mr. Daniels:
This letter is an official notice to inform you that the property described above has been
determined by Kern County Environmental Health Services Department to be the site of
an unauthorized release of hazardous materials from an underground storage tank. This
notice is sent to you because our records indicate that you are a responsible party for this
property .
As a responsible party, you must provide for all studies and work relating to the above·
described property and the cost for oversight of these activities. California Health and
Safety Code, Chapter 6.7, and Kern County Ordinance Code, Chapter 8.48, require a
determination of the threat to the environment as a result of this release. THE
RESPONSffiLE PARTY SHALL, ON A TIMELY BASIS, DEVELOP A SITE
CHARACfERIZATION, FEASIBILITY STUDY AND REMEDIAL ACfION PLAN
FOR KERN COUNTY ENVIRONMENTAL HEALTH SERVICES DEPARTMENT'S
REVæW AND APPROVAL BEFORE THE WORK IS INITIATED. Enc1,?sed you will
find Attachment "A", Handbook UT-35, which states the minimum required site work plan
activities, the necessary requirements for selecting environmental contractors qualified to
perform this work, a glossary of terms, example illustrations, and a section discussing the
answers to commonly asked questions.
The cost incurred by Kern County Environmental Health Services Department for tlíe
oversight of the work for the site characterization, feasibility study, remediation action plan,
site remediation, and ongoing monitoring is not covered þy any fees or permits. These costs
are recovered by Kern County Environmental Health Services Department in one of the two
methods described below. It is your responsibility to select the method of oversight cost
recovery under the terms of (A) State contract or (B) County of Kern Local Agreement
Option. These options pertain only to costs associated with oversight.
e
-,
Nat Daniels
April 7, 1993
Page 3
It is necessary for you to respond, in writing, within ten (10) calendar days of receipt of this
letter to advise Kern County Environmental Health Services Department of your choice:
either the State contract or the County's Local Agreement Option. If you select the
County's Local Agreement, please complete and sign the Local Agreement (Attachment B),
and return it with your check for $1,000.00 (one thousand doUars) made payable to the
County of Kern, addressed to Kern County Environmental Health Services Department,
2700 M Street, Suite 300, Bakersfield, CA 93301, Attention: Accounting - Local Agreement
Option. If you select the State contract, please indicate, in writing, that you have made this
selection and that you have read the above official notification.
Failure to respond within ten (10) calendar days to this notice will automatically result in
oversight cost recovery for your site( s) to be placed under the terms of the State contract
for Leaking Underground Storage Tanks.
If you should have any questions regarding this matter, please contact Susan Gonzales at
(805) 861-3636, Extension 510.
~
Steve McCaUey, Director .
Environmental Health Services.
SMc:ch
Attachments
colt\250011.a
Attachment "B"
e
e
KERN COUNTY LOCAL AGREEMENT OPTION
BETWEEN
KERN COUNTY ENVIRONMENTAL HEALTH SERVICES DEPARTMENT
(Kern County Underground Storage Tank Permitting Authority)
AND
Nat Daniels
Responsible Party for Underground Storage Tank
for: Golden State Metals
Permit #250011
This facility has experienced an unauthorized release of hazardous substances from an underground storage
tank. Action is necessary to protect the public health and the environment of the County, pursuant to Chapter
6.7 of the California Health and Safety Code and Chapter 8.48 of the Kern County Ordinance Code.
TIm WITNESS FOR TIm COUNTY AND SIGNATURE(S) FOR A RESPONSIBLE PARTY OF mE
SUBJEcr FACILITY DESCRIBED ABOVE DO HEREBY AGREE mAT:
Kern County Environmental Health Services Department shall act as the lead agency for regulatory oversight
for the:
a)
Site characterization: the study of a site, including sampling of subsurface soil and water
where contamination is found in order to fully assess its extent and threat to the environmenL
It shall include a discussion of the relative risk to biological receptors and possible pathways
of exposure. It may include removal or in-place closure of the tank, disposal or on-site
treatment of contaminated backfill or adjacent soil, removal of hazardous substances floating
on groundwater, and the drilling of groundwater monitor wells.
b)
Feasibility study: the identification and evaluation of feasible alternatives for cleaning up the
site and remedying threats to public health and safety.
c)
Remedial action plan: the most cost-effective, appropriate plan to lessen, alleviate, abate,
correct or clean-up the effects that a release of hazardous substances may have on the
environment, based on the feasibility study.
d)
Remediation: the action chosen by the responsible party and approved by Kern County
Environmental Health Serviœs Department for the mitigation and clean-up of contamination
resulting from an unauthorized release of hazardous materials and any ongoing monitoring
of the site. . .
e
e
The responsible party shall do the following:
a. Conduct all work as directed by Kern County Environmental Health Services Depanment '
pursuant to State and local law and in conformance with appropriate regulaûons to assess
and remediate the contaminated site.
b. Deposit with the Kern County Environmental Health Leaking Underground Storage Tank
Local Option Trust Fund the sum of $1,000.00. The Depanment's oversight activiûes will
be charged against this account at the rate prescribed by Kern County Ordinance Code
Chapter 8.04 ($80.00 per hour). Monthly statements will be prepared detailing the acûviûes
and services provided and the remaining credit balance.
Kern County Environmental Health Services Depanment shall provide the following services:
a. Oversight of all activiûes to characterize the site's threat to the environment and/or the
groundwater, and coordination with the appropriate State, County and local regulatory
agencies.
b. Serve as the single contact point for the responsible party's representatives and other
regulatory agencies for the activities described in Dall above. If during the Depanment's
review of the site characterization/remedial action plan, it is determined that a permit may
be required by another agency, the responsible party shall be referred to that permitting
agency.
c. Review reports, conduct inspections, and oversee monitoring until the site poses no funher
environmental or public health threat An official certification letter shall be given to the
responsible party when the site is determined to no longer pose a significant threat to the
environment
d. The responsible party will be officially notified by Kern County Environmental Health
Services Depanment when:
1. Necessary oversight is completed. A final statement will be provided to the
responsible party. If there remains an unexpended balance of the deposit made by
the responsible party in the Leaking Underground Storage Tank Trust Fund, a
refund for the unexpended balance will be issued;
- or -
2. Founeen (14) hours of billable time has been reached. This will give notice that the
available funds will be exhausted after six (6) additional hoUlS of billable time, at
which time the agreement will expire. A statement estimating the amount of time
necessary to complete any remaining oversight work will be sent The responsible
party will then have another opponunity to renew his agreement with the County.
3. Failure to enter into another agreement shall require Kern County Environmental
Health Services Department to utilize the State Water Resources Conuol Board
Local Oversight Program for which the responsible party may be billed by the State
directly for the cost of County services as well as State costs.
-- -
e
e
Kern County Environmental Health Services Depanment reseJVeS the right to cancel this agreement at any
time for any reasons, including groundwater contamination or a uniquely complex hydrogeological condition.
If an unexpended balance remains on deposit from the responsible party under the terms of this agreement,
a refund for the unexpended balance will be issued and the agreement terminated. Once the agreement is
cancelled, you, as a responsible party, will be enrolled in the State Leaking Underground Storage Tank Local
Oversight Program.
This agreement may be cancelled any time by either party by cenified registered return receipt letter to the
other party within ays of said notification.
;/
/"7/ / / 1þ
I,/ Æ:. :-/ / , '. "/'. (responsible party), have read and agree to the conditions of this
agreement for the' contaminated site'described as:
\.A /) I. ) -!~ ~f1 ,~/
Site Name " 'ÇJ U--k-1l-ÆAA.. i8-L.-4.£L ",'Í'·!.NrA,.).x/
Site Address
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Zip 9 'Z.'? 0 2--
Owner
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NAT DANIELS
GOLDEN STATE METALS
3318 HARMONY DRIVE
BAKERSFIELD,CA 93306
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Golden State ,y.etals. Inc;~'\
SaaP Metals. Processins " RecYdins ,;4;S/~~?.'~\
Post Office Box lOlS8 .ß:./;// ,/ \,:\j \
Bakersfield. California 93387 (' <"¿~// \"/_:;. \
r805) 327-3559. fAX r805) 321-5749 ~\ ~. ,è' ';.:
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June 25, 1993
Mr. Steve McCalley, R.E.H.S.
Directc.'t'
Environrn~ntal Health Services Department
2700 M Stre~t, Suite 300
Bakersfield, CA 93301
RE: Nat Daniels
K &- D Salvage
Dear Mr. McCalley:
We recently received a lette:J:' (copy attached) addressed to Nat
Daniels at Golden State Metals. This is to inform you that
ML. Daniels is no longer associated with Golden State Metals in any
way, haviI.g sold the business in 1989.
I believe the address given, 600 Union Avenue, is ~orrect for Mr.
Daniels' new business, K & D Salvage. We have forwarded the
original of the attached letter to Mr. Daniels at his home address.
Thank you for your attention to this matter.
SinCerelY,%; ,
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Dawn Fields
Executive Secretary
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ENVIRONMENTAL HEALTH SERVICES DEPARTMENT
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(805) 861-3636
(805) 861-3429 FAX
STEVE McCALLEY, R.E.H.S.
DIRECTOR
April 7, 1993
Nat Daniels
Golden State Metals
3318 Harmony Drive
Bakersfield, CA 93306
SUBJECf: Location: 600 Union Avenue
Bakersfield, CA 93306
Known as: Golden State Metals
PERMIT #: 250011
Dear Mr. Daniels:
This letter is an official notice to inform you that the property described above has been
determined by Kern County Environmental Health Services Department to be the site of
an unauthorized release of hazardous materials from an underground storage tank. This
notice is sent to you because our records indicate that you are a responsible party for this
property.
As a responsible party, you must provide for all studies and work relating to the above-
described property and the cost for oversight of these activities. California Health and
Safety Code, Chapter 6.7, and Kern County Ordinance Code, Chapter 8.48, require a
determination of the threat to the environment as a result of this release. THE
RESPONSIBLE PARTY SHALL, ON A TIMELY BASIS, DEVELOP A SITE
CHARACTERIZATION, FEASIBILITY STUDY AND REMEDIAL ACTION PLAN
FOR KERN COUNTY ENVIRONMENTAL HEALTH SERVICES DEPARTMENT'S
REVIEW AND APPROVAL BEFORE THE WORK IS INITIATED. Enc1,?sed you will
find Attachment "A", Handbook UT-35, which states the minimum required site work plan
activities, the necessary requirements for selecting environmental contractors qualified to
perform this work, a glossary of terms, example illustrations, and a section discussing the
answers to commonly asked questions.
The cost incurred by Kern County Environmental Health Services Department for the
oversight of the work for the site characterization, feasibility study, remediation action plan,
site remediation, and ongoing monitoring is not covered þy any fees or permits. These costs
are recovered by Kern County Environmental Health Services Department in one of the two
methods described below. It is your responsibility to select the method of oversight cost
recovery under the terms of (A) State contract or (B) County of Kern Local Agreement
Option. These options pertain only to costs associated with oversight.
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Nat Daniels
April 7, 1993
Page 2
(A) STATE CONTRACT
The State Leaking Underground Storage Tank Local Oversight Program provides a
mechanism for the State to reimburse the County for County oversight. The County will
conduct the necessary oversight and biII the State Water Resources Control Board under this
State contract. The State will then charge you, a responsible party, for the costs incurred
by both the County and the State, pertaining to your site, under the State terms explained
below:
Whereas the federal Petroleum Leaking Underground Storage Tank Trust Fund provides
funding to pay the local and state agency administrative and oversight costs associated with
the cleanup of releases from underground storage tanks; and Whereas the Legislature has
authorized funds to pay the local and state agency administrative and oversight costs
associated with the cleanup of releases from underground storage tanks; and Whereas the
direct and indirect costs of site inv~tigation or remedial action at the above site are funded,
in whole or in part, from the federal Trust Fund; and Whereas the above individual(s) or
entity(ies) have been identified as the party or parties responsible for investigation and
cleanup of the above site; YOU ARE HEREBY NOTIFIED that pursuant to Title 42 of the
United States Code, Section 6991b(h)(6) and Section 25360 of the Health and Safety Code,
the above Responsible Party or Panies shall reimburse the State Water Resources Control
Board not more than 150 percent of the total amount of site-specific oversight costs actually
incurred while overseeing the cleanup of the above underground storage tank site, and the
above Responsible Party or Parties shall make full payment of such costs within 30 days of
receipt of a detailed invoice from the State Water Resources Control Board.
(B) COUN'IY OF KERN LOCAL AGREEMENT OPTION
Kern County Environmental Health Services Department is providing this option for those
who prefer to pay the County directly and avoid the addition of State costs. Prior to the
County's performance of services, this option requires your deposit of $1,000.00 (one
thousand dollars) with the County to be held in the Local Option Trust Account. Charges
for County oversight are made against this account. In this option, a responsible party must
enter into a County agreement, Attachment "B".
The environmental sensitivity (Attachment lie') of this site has been reviewed by
Environmental Health Services Department to determine the potential threat for
groundwater contamination. Only sites determined to be non-environmentally sensitive may
enroll in the Local Option Agreement. The site described above is not in an
environmentally sensitive area and may be enrolled in the Local Agreement Option;
however, the County of Kern reserves the right to cancel any Local Agreement Option
should it be discovered that groundwater contamination or a unique, complex
hydrogeological condition exists. In such cases, Environmental Health will utilize the State
contract to pay for County oversight activities. The County of Kern reserves this right for
any site even when the site is located in a non-environmentally sensitive area.
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Nat Daniels
April 7, 1993
Page 3
It is necessary for you to respond, in writing, within ten (10) calendar days of receipt of this
letter to advise Kern County Environmental Health Services Department of your choice:
either the State contract or the County's Local Agreement Option. If you select the
County's Local Agreement, please complete and sign the Local Agreement (Attachment B),
and return it with your check for $1,000.00 (one thousand dollars) made payable to the
County of Kern, addressed to Kern County Environmental Health Se1VÎces Department,
2700 M Street, Suite 300, Bakersfield, CA 93301, Attention: Accounting - Local Agreement
Option. If you select the State contract, please indicate, in writing, that you have made this
selection and that you have read the above official notification.
Failure to respond within ten (10) calendar days to this notice will automatically result in
oversight cost recovery for your site( s) to be placed under the terms of the State contract
for Leaking Underground Storage Tanks.
If you should have any questions regarding this matter, please contact Susan Gonzales at
(805) 861-3636, Extension 510.
~
Steve McCalley, Director
Environmental Health Se1VÎces.
artment
SMc:ch
Attachments
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Attachment "B"
KERN COUNTY LOCAL AGREEMENT OPTION
BETWEEN
KERN COUNTY ENVIRONMENTAL HEALTH SERVICES DEPARTMENT
(Kern County Underground Storage Tank Permitting Authority)
AND
Nat Daniels
Responsible Party for Underground Storage Tank
for: Golden State Metals
Permit #250011
This facility has experienced an unauthorized release of hazardous substances from an underground storage
tank. Action is necessary to protect the public health and the environment of the County, pursuant to Chapter
6.7 of the California Health and Safety Code and Chapter 8.48 of the Kern County Ordinance Code.
THE WITNESS FOR TIlE COUNTY AND SIGNATURE(S) FOR A RESPONSIBLE PARTY OF THE
SUBJEcr FACILITY DESCRIBED ABOVE DO HEREBY AGREE mAT:
Kern County Environmental Health SelVÍces Depanment shall act as the lead agency for regulatory oversight
for the:
a) Site characterization: the study of a site, including sampling of subsurface soil and water
where contamination is found in order to fully assess its extent and threat to the environment.
It shall include a discussion of the relative risk to biological receptors and possible pathways
of exposure. It may include removal or in-place closure of the tank, disposal or on-site
treatment of contaminated backfill or adjacent soil, removal of hazardous substances floating
on groundwater, and the drilling of groundwater monitor wells.
b) Feasibility study: the identification and evaluation offeasible alternatives for cleaning up the
site and remedying threats to public health and safety.
c) Remedial action plan: the most cost-effective, appropriate plan to lessen, alleviate, abate,
correct or clean-up the effects that a release of hazardous substances may have on the
environment, based on the feasibility study.
d) Remediation: the action cposen by the responsible party and approved by Kern County
Environmental Health Services Depanment for the mitigation and clean-up of contamination
resulting from an unauthorized release of hazardous materials and any ongoing monitoring
of the site./-
1
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The responsible party shall do the following:
a. Conduct all work as directed by Kern County Environmental Health Services Depanment
pursuant to State and local law and in conformance with appropriate regulations to assess
and remediate the contaminated site.
b. Deposit with the Kern County Environmental Health Leaking Underground Storage Tank
Local Option Trust Fund the sum of $1,000.00. The Department's oversight activities will
be charged against this account at the rate prescribed by Kern County Ordinance Code
Chapter 8.04 ($80.00 per hour). Monthly statements will be prepared detailing the activities
and services provided and the remaining credit balance.
Kern County Environmental Health Services Department shall provide the following services:
a. Oversight of all activities to characterize the site's threat to the environment and/or the
groundwater, and coordination with the appropriate State, County and local regulatory
agencies.
b. Serve as the single contact point for the responsible party's representatives and other
regulatory agencies for the activities described in ftaft above. If during the Department's
review of the site characterization/remedial action plan, it is determined that a permit may
be required by another agency, the responsible party shall be referred to that permitting
agency.
c. Review reports, conduct inspections, and oversee monitoring until the site poses no further
environmental or public health threat. An official certification letter shall be given to the
responsible party when the site is determined to no longer pose a significant threat to the
environmenL
d. The responsible party will be officially notified by Kern County Environmental Health
Services Department when:
1. Necessary oversight is completed. A final statement will be provided to the
responsible party. If there remains an unexpended balance of the deposit made by
the responsible party in the Leaking Underground Storage Tank Trust Fund, a
refund for the unexpended balance will be issued;
- or-
2. Fourteen (14) hours of billable time has been reached. This will give notice that the
available funds will be exhausted after six (6) additional hours of billable time, at
which time the agreement will expire. A statement estimating the amount of time
necessary to complete any remaining oversight work will be senL The responsible
party will then have another opportunity to renew his agreement with the County.
3. Failure to enter into another agreement shall require Kern County Environmental
Health Services Department to utilize the State Water Resources Control Board
Local Oversight Program for which the responsible party may be billed by the State
directly for the cost of County services as well as State costs.
2
.
.
Kern County Environmental Health Services Depanment reserves the right to cancel this agreement at any
time for any reasons, including groundwater contamination or a uniquely complex hydrogeological condition.
If an unexpended balance remains on deposit from the responsible party under the terms of this agreement,
a refund for the unexpended balance will be issued and the agreement terminated. Once the agreement is
cancelled, you, as a responsible party, will be enrolled in the State Leaking Underground Storage Tank Local
Oversight Program.
This agreement may be cancelled any time by either party by certified registered return receipt letter to the
other party within five days of said notification.
I, (responsible party), have read and agree to the conditions of this
agreement for the contaminated site described as:
Site Name
Site Address
City
Owner
Owner's Address
City
Telephone
Operator
Telephone
Billing Address Attn:
Zip
Zip
Permit #
In order for this agreement to be executed, it must be signed aod accompanied by the deposit of one-thousand
dollars ($1000.00),
Responsible Party:
Date:
For the County of Kern:
Date:
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NAT DANIELS
GOLDEN STATE METALS
3318 HARMONY DRIVE
BAKERSFIELD,CA 93306
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EN~IRONM~T AL HEALTH SERVIC~ DEPARTMENT
STEVE McCALLEY, R.E.H.S.
DIRECTOR
2700 -M- Street, Suite 300
Bakersfield, CA 93301
(805) 861-3636
(805) 861-3429 FAX
PERMIT FOR PERMANENT CLOSURE
OF UNDERGROUND HAZARDOUS
SUBSTANCES STORAGE FACILI1Y
PERMIT NUMBER A 1837·25
FACILTIY NAMFJADDRESS:
OWNER(S) NAMFJADDRESS:
CONTRACTOR:
Old K & D Salvage
600 So. Union
Bakersfield, CA 93307
Nat Daniels
3318 Harmony Drive
Bakersfield, CA 93306
M Construction Company
340 Industrial Street
Bakersfield, CA 93307
License #414695
Phone: (805) 324-1760
Phone: (805) 871-4884
PERMIT FOR CLOSURE OF
PERMIT EXPIRES
May 24. 1993
~ TANK(S) AT ABOVE
APPROVAL DATE February 25. 1993
APPROVED BY ~~ ~ -
Carrie Georgi Î
Hazardous Materials Specialist
LOCATION
................................ .......... ................................ ..................... PO ST 0 N PREMISES.................................. ............ ..... .............................................
CONDITIONS AS FOLLOWS:
1. It is the responsibility of the Permittee to obtain permits which may be required by other regulatory agencies prior to beginning work (i.e" City Fire and Building
Departments).
2. Permittee must notify the Hazardous Materials Management Program at (805) 861-3636 two working days prior to tank removal or abandonment in place to
arrange for required inspections(s).
3. Tank closure activities must be per Kern County Environmental Health and Fire Department approved methods as described in Handbook UT-30.
4. It is the contractor's responsibility to know and adhere to all applicable laws regarding the handling, transportation or treatment of hazardous'materials.
5. The tank removal contractor must have a qualified company employee on site supetvising the tank removal. The employee must have tank removal experience
prior to working unsupervised.
6. If any contractors other than those listed on permit and permit application are to be utilized, prior approval must be granted by the specialist listed on the
permit. Deviation from the submitted application is not allowed,
7. Soil Sampling:
a, Tank size less than or equal to 1,000 gallons - a minimum of two samples must be retrieved from beneath the center of the tank at depths of
approximately two feet and six feet.
b. Tank size greater than 1,000 to 10,000 gallons - a minimum of four samples must be retrieved one-third of the way in from the ends of each tank
at depths of approximately two feet and six feet.
c, Tank size greater than 10,000 gallons - a minimum of six samples must be retrieved one-fourth of the way in from the ends of each tank and beneath
the center of each tank at depths of approximately two feet and six feet.
8, Soil Sampling (piping area):
A minimum of two samples must be retrieved at depths of approximately two feet and six feet for every 15 linear feet of pipe run and under the dispenser area,
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PERMIT FOR PERMANENT CLOSURE
OF UNDERGROUND HAZARDOUS
SUBSTANCES STORAGE FACILITY
PERMIT NUMBER A 1837·25
ADDENDUM
9. Soil Sample analysis:
a. All soil samples retrieved from beneath gasoline (leaded/unleaded) tanks and appurtenances must be analyzed for benzene, toluene, xylene, and total
petroleum hydrocarbons (for gasoline).
b. All soil samples retrieved from beneath diesel tanks and appurtenances must be analyzed for total petroleum hydrocarbons (for diesel) and benzene,
c, All soil samples retrieved from beneath waste oil tanks and appurtenances must be analyzed for total organic halides, lead, oil and grease.
d. All soil samples retrieved from beneath crude oil tanks and appurtenances must be analyzed for oil and grease.
e. All soil samples retrieved from beneath tanks and appurtenances that contain unknown substances must be analyzed for a full range of substances
that may have been stored within the tank.
10. The following timetable lists pre- and post-tank removal requirements:
ACTIVITY
DEADLINE
Complete permit application submitted
to Hazardous Materials Management Program
At least two weeks prior to closure
Notification to inspector listed on permit of date
and time of closure and soil sampling
Two working days
Transportation and tracking forms sent to Hazardous
Materials Management Program. All hazardous waste
manifests must be signed by the receiver of the
hazardous waste
No later than 5 working days for transportation and 14 working
days for the tracking form after tank removal
Sample analysis to Hazardous Materials Management
Program
No later than 3 working days after completion of analysis
11. Purging/Inerting Conditions:
a. Liquid shall be pumped from tank prior to purging such that less than 8 gallons of liquid remain in tank. (CSH&SC 41700)
b, Tank shall be purged through vent pipe discharging at least 10 feet above ground level. (CSH&SC 41700)
c. No emission shall result in odors detectable at or beyond property line. (Rule 419)
d, No emission shall endanger the health, safety, comfort or repose of any person. (CSH&SC 41700)
e. Vent lines shall remain attached to tank until the inspector arrives to authorize removal.
RECOMMENDATIONS/GUIDELINES FOR REMOVAL OF UNDERGROUND STORAGE TANKS
This department is responsible for enforcing the Kern County Ordinance Code, Division 8 and state regulations pertaining to underground storage tanks,
Representatives from this department respond to job sites during tank removals to ensure that the tanks are safe to remove/close and that the overall job performance
is consistent with permit requirements, applicable laws and safety standards. The following guidelines are offered to clarify the interests and expectations for this
department.
1.
Job site safety is one of our primary concerns. Excavations are inherently dangerous, It is the contractor's responsibility to know and abide by CAL-OSHA
regulations. The job foreman is responsible for the crew and any subcontractors on the job. As a general rule, workers are not permitted in improperly sloped
excavations or when unsafe conditions exist in the hole. Tools and equipment are to be used only for their designed function. For example, backhoe buckets
are never substituted for ladders.
2.
l
Properly licensed contractors are assumed to understand the requirements of the permit issued, The job foreman is responsible for knowing and abiding by
the conditions of the permit. Deviation from the permit conditions may result in a stop-work order.
3.
Individual contractors will be held responsible for their post-removal papelWork. Tracking forms, hazardous waste manifests and analyses documentation are
necessary for each site in order to close a case file or move it into mitigation. When contractors do not follow through on necessary papelWork, an
unmanageable backlog of incomplete cases results. If this continues, processing time for completing new closures will increase.
Accepted Bv:
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GIBSOM OIL·AND REFINING
END or COJØŒRCIAL DR
BAKER8FIILD,CA 93308
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16. GENERATOR'S CERTIFICATION: I hereby declare that the contents of the consignment are fully and accurately described above by proper:shìp~;~Wáí;t:dassmed'-::
packed, marked, and labeled, and are in all respects in proper condition for transport by highway according to applicable federOl, state:andínte~·,~,i:j:i~~:;:;!~1¡·::¡}"'. ¡.::!.
. ; .~' .' ~' :":""'~.;··f:...:/~JlLt~:~'si¡:.~~~t~¡:_~?;<i~<~:~;·j:":i.;~~·~:~~.:,:£"~·
If I am a large quantity generator, I certify that I have a program in place' fO reduce the volume and loxicity of waste g~raied to ti..i,~ree-:(hCNe.:~'tò,~~·.', .
economically proc1icable and that I have !iOlected the practicoble method of t'!Qtn1ent, "orage, or disposal currently ovailabHl'to me which mi"Í!ftÍ2eÍ:the,¡~'aìid:futu!l!l'_'..(:
threa1,I.> humc," newlh'.tlnd the ,·nvironment; OR, if I am a small quantity generotor, I have made a good faith effort to minimize my wCHte.get!OraIiori:ànd',selec(t!wI"best, "-
waste:ma mean metnod lhdt-ìs available to me and that I can afford. '. ~..~; :,:..._ .,...7.::.':. :. ':.: ~..::.~~::-,-~..-:.')~'~~~~;f*~~~~:~~':~:,": .\:"..... "'''-q..'~
Prinled/Typed Name Signature .. .:::ManIh':;;";:)·:'I:'9Y,. ,y'G~;:-:::
"0 ". "'dr'~¡ . ,,2
I of Materials
19. Discrepancy Indication Space
Yellow: TSDF SENDS THIS COPY TO GENERATOR WITHIN 30 DAYS:;.·.
(Generators who 5ubmit hazarc:lauswasfe·.for'trOnsport out-of1tate,
produce completed copy of this copy øncI.~ ,to DTSC within 30 days,)
DTSC 8022A (12/91)
EPA 8700-22
"I~ ',. ""_,:- '''¡';~.,.'..~;,;':~';¡';'~ p....
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'. VV\....L.O ...;. , (Jv 1..,/ I' Yl..o..:I l,A."h (/ JA-TV., '::..~ .' '. :
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, " :¡.' I,' ~'~' ~., \'J?-¡' "1 t t".- '1" :v~' ~ . t !' I"¡\':~ ~'in, 'l'lt '<V;'1i\\.. -'If"".' , (;I, ,:'> ':
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-./YYLJL
Gibson'-
Environmental
Màrch 09," 19:sr.'3-'·' . .
NATT DANIELS
600 SUNION AVENUE
BAKERSFIELD,CA 93304
EPA# CAC000837376
(017925)
This letter is to inform you that Gibson Environmental has
accepted your material for recycling.
Gibson certifies that the material received on the manifests
indicated below has been properly treated and recycled.
Date
03/04/93
Manifest
92226894
Movement
00072212
Quantity
200
UOM
GAL
If this information does not agree with your records, please notify
us within ten days so we can resclve any discrepancies.
Generators, know your wastestream. Gibson Bakersfield is only
permitted to accept the following wastes that are varying
combinations of oil, water and solids under California Waste Codes
221, 222, 223, 241. In addition, Gibson at Bakersfield may accept
waste codes 0004 through 0043.
For information as to approved codes for Gibson's Wilmington and
Redwood City facilities, please call (800) 582-3935.' '
This notice is required by the Department of Toxic Substance Control.
Gibson Environmental
Customer Service
3300 Truxtun Avenue suite 200
Bakersfield, CA 93301
(805) 327-0413
A Subsidiarj' of V.L.S.. Inc.
3300 Truxtun Avenue. Suite 200 . Bakersficld.CA 9330J' S05/32ì-0413· 800/582-3935' Fax 805/861-0229
o Recycled Paper
e
.--
'-_.:
FILE CONTENTS SUMMARY
FACILITY: Gðld~Y1 ~~ M4 (s.
ADDRESS: (p ()O [1 () ìò n AIJ-eV1 ue..
PER!-fIT #: ó< '5 ()() II ENV. SENSITIVITY: -11E'~
A.CTIVITY DATE ;; OF TANKS COHHE.YTS
appJ i Ca-J-¡, 0 n 7jc2sj~5 J opera-k
r2,:;>'OO/IC 7/ I / 5'0 J I'
f I
o.ppiCaf/t)'I] 0?'21/93 / rem¿:; Va.. r
Ii /837rQ5" ~f:;~/93 J II
Job resu/fs 3/"f /9.3
&/)(t;~J- ,3/30/93
.3/3ð/93
CONTRACTOR NO:
SITE NO:
SITE NAME:
ADDRESS:
CITY/ZIP:
.
,--
WATER RESOURES CONTROL BOARD
DIVISION OF WATER QUALITY
UST CLEANUP PROGRAM
SITE SPECIFIC QUARTERLY REPORT
15000 SOURCE OF FUNDS:
250011 FEDERAL EXEMPT:
GOLDEN STATE METALS
600 UNION AVENUE
BAKERSFIELD, CA 93306
N
SUBSTANCE: 8006619
PETROLEUM: Y
DATE REPORTED:
DATE CONFIRMED:
MULTIPLE R.P's:
03/30/93
03/30/93
N
----------------------------- SITE STATUS ----------------------------
RP SEARCH:
PRELIMINARY
ASSESSMENT:
REMEDIAL
INVESTIGATION:
REMEDIAL ACTION:
POST REMEDIAL
ACTION MONITORING:
ENFORCEMENT ACTION
TAKEN:
LUFT FIELD MANUAL CONSIDERATION
(CATEGORY 1, 2, 3, PLUS H, S, C, A,
CASE CLOSED:
DATE EXCAVATION STARTED:
CASE TYPE:
2, S, C, A.
R, W, G, OR 0 AS APPLICABLE)
DATE CLOSED: /
REMEDIAL ACTIONS TAKEN:
S
CONTRACT STATUS:
/
/
/
4
/
/
/
EMERGENCY
RESPONSE:
DATE COMPLETED:
DATE COMPLETED:
03/30/93
04/01/93
S
DATE UNDERWAY: 03/30/93
DATE UNDERWAY: 03/18/93
DATE COMPLETED: / /
DATE COMPLETED: / /
DATE COMPLETED:
DATE TAKEN:
/
-------------------------- RESPONSIBLE PARTY -------------------------
CONTACT NAME:
COMPANY NAME:
ADDRESS:
CITY/ZIP:
PHONE #:
CONTACT NAME:
COMPANY NAME:
ADDRESS:
CITY/ZIP:
PHONE #:
CONTACT NAME:
COMPANY NAME:
ADDRESS:
r'T'TV/7TD·
C
DATE UNDERWAY:
DATE UNDERWAY:
DATE UNDERWAY:
TYPE:
/
/
NAT DANIELS
GOLDEN STATE METALS
3318 HARMONY DRIVE
BAKERSFIELD, CA 93306
( )
SPECIALIST:
SENSITIVITY: NES
ABANDONMENT #: A1837-25
DATE OF REPORT: 04/01/93
LEAK REPORT: Y
CONTACT NAME:
COMPANY NAME:
ADDRESS:
CITY/ZIP:
PHONE #:
CONTACT NAME:
COMPANY NAME:
ADDRESS:
r. prv / 7 T P ~
. .'
-'~ATE OFCAUFORNlA./·:ar";
~./ STATE WATER RESOURCES CONTRoL 8OARD.~:~--{.
. . -. f . , "
UNDERGROUND STORAG'E TANK PERMIT APPLICATION· FORMA. ," :,
.: " ':t ~ "'. :..'" . ::.. .' .~.-'\.;..
, , .
.;', 'COMPLETE'THIS FORM 'FOR EACH FAetutYlSlTE';:::-"2;:;:'J.lç :.:: .
,D 3 RENEWAL P,ERMIT 0 5 + OFINFø~MATlÒN:'iiT:7"~ÀM~ýClOseDSìrE"
o 4 AMENDED PERMIT 0 8 TEMPORÂRY'SITE'Ci.oSURE· :: ': "~:~\~" ;"~.'-. " ":' . '. .."
MARK ONLY 0 1 NEW PERMIT
ONE ITEM · 0 2 INTERIM PERMIT
. \"
. , ,>f~ ::'::~)~ '..~
I. FACILITYISITE INFORMATION & ADDRESS· (MUST BE COMPLETED) "
DBA OR FACILITY NAME NAME OF OPERATfj .. '.
,j. - "" ""1" .
! :\... "^-..
ADDRESS NEA¡¡EST CROSS STREET
t. ,~~ ~...... (\ e ". ~ t.s
CITY NAME ZIP CODE
1330b
.- '1.-.'
"I ~ ;~. .:" ~;. ·.~",:..s~ " .":
. .: .il· ç'~," 1 ~ i.'
~. \ .,
o CORPORATION
It!iCl!NDIVIDUAL
o PARTNERSHIP
o LOCAL·AGENCY " 0 COUNTY.,\GENCY
DISTRICTS
D ./ IF INDIAN /I OF TANKS AT SITE E. P. A. L 0,/1 (optiaJa/)
RESERVATION ì
OR TRUST LANDS t
o STATE.,\GENCY
o FEDERAl.,\GENCY
TYPE OF BUSINESS 0 1 GAS STATION 0 2 DISTRIBUTOR
D 3 FARM D 4 PROCESSOR ~: 5 OTHER
EMERGENCY CONTACT PERSON (SECONDARY). optional
DAYS: NAME (lAST, FIRST) PHONE /I WITH AREA CODE
NIGHTS: NAME (LAST, FIRST)
PHONE /I WITH AREA CODE
II. PROPERTY OWNER INFORMATION· MUST BE COMPLETED
~
..,.
CARE OF ADDRESS INFORMATION
~~;..
ST.ATE~.
...""
......
~'
./ box Ð Indicate
,0 STATE·AGENCY
""";' .
III. TANK OWNER INFORMATION· (MUST BE COMPLETED)
NAM, OF OWNER , CARE OF ADDRESS INFORMATION
). /, :. '. " -
MAILING OR ST.!J.E. ADDRESS ~ ./ box Ð Indicate 0 INDIVIDUAl 0 LOCAl-AGENCY
-", ~ </ \
,.' ' ,,^__ ~ V e 0 CORPORATION 0 PARTNERSHIP 0 COUNTY.,\GENCY 0 FEDERAl-AGENCY
CITY¡ NAME '.,-- r, ZIP CODE PHONE /I WITH AREA CODE
6'i.i.. ~g ..~- (~é{d {.' 33Ò b Ò', ì - "iSSt¡.
IV. BOARD OF EQUALIZATION UST STORAGE FEE ACCOUNT NUMBER· Call (916) 739-2582 if questions arise.
TY (TK) HQ @EJ·CIITrIJ
V. LEGAL NOTIFICATION AND BILLING ADDRESS
o STATE·AGENCY
Legal notification and billing will be senllo Ihe lank owner unless box I or II is checked.
"
CHECK ONE BOX INDICATING WHICH ABOVE ADDRESS SHOULD BE USED FOR LEGAL NOTIFICATIONS AND BilLING:
1.0
II.CiQ 111.0
THIS FORM HAS BEEN COMPLETED UNDER PENALTY OF PERJURY, AND TO THE BEST OF MY KNOWLEDGE. IS TRUE AND CORRECT
APPLlCANrs NAME (PRINTED & SIGNATURE)
APPLlCANrs TITLE
DATE
MONTHlDAYIYEAR
LOCAL AGENCY USE ONLY
COUN'7Y #
C2EJ
JURISDICTION #
~
lUJ.UL.W
FACILITY #
[I[5IaillDJ
LOCATION CODE . OPTIONAL
rCENSUS TRACT. . OPTIONAL
J ..--
/\ "::>
I SUPVISOR - DISTRICT CODE - OPTIONAL
THIS FORM MUST BE ACCOMPANIED BY AT LEAST (1) OR MORE PERMIT APPLICATION· FORM B, UNLESS THIS IS A CHANGE OF SITE INFORMATION ONLY.
FOROO33A-R2
FORM A (9-90)
,.1 .;
COMPLETE A SEPARATE FORM FOR EACH TANK SYSTEM. ' "
'. '(~.f-'\'t': .:',": "A:'~
_~ ~ ... u" "
.... ."......
.. ' , STATEOFCAUFORtIA" ,',-,' l'
STATE WATER RESOURCES CONTROL BOARD < " "', '., "I'·r. ',',,', ¡... .
UNDERGROUND STORAGE TANK PERMIT,' APPLICATION . FORM; ~;~~.;xc,;~,' \.6Z~.
MARK ONLY
ONE ITEM
o 1 NEW PERMIT
o 2 INTERIM PERMIT
o 3 RENEWAl PERMIT
o 4 AMENDED PERMIT
"
o 5 CHANGE OF INFORMATION
o 6 TEMPORARY TANK CLOSURE
I I""rf--'
fij';,7 PERMANENTLY CLOSED ON SITE
o 8 TANK REMOVED
DBA OR FACILITY NAME WHERE TANK IS INSTALLED: \Jt>..., C (, ......·t
I. TANK DESCRIPTION
COMPLETE ALL ITEMS - SPECIFY IF UNKNOWN
A. OWNER'S TANK L D. #
B, MANUFACTURED BY:
1A..,;y-,Y-
C. DATE INSTALLED (MOIDAYIYEAR) '\ ''\ t- r....:¡ c! l.L~ '\
D. TANK CAPACITY IN GAlLONS:
II. TANK CONTENTS
IFA·1ISMARKED,COMPLETEITEMC,
~.1 MOTOR VEHICLE FUEL 0 4 OIL B. C. ~ 1aREGULAR B 3 DIESEL o 6 AVIATION GAS
A. . UNLEADED
02 PETROLEUM 0 EMPTY .Cd 1 PRODUCT o 1b PREMIUM 4 GASAHOL o 7 METHANOL
80 o 5 JET FUEL
03 0 0 UNLEADED
CHEMICAL PRODUCT 95 UNKNOWN 2 WASTE o 2 LEADED o 99 OTHER (DESCRIBE IN ITEM D. BELOW)
D. IF (A.1) IS NOT MARKED, ENTER NAME OF SUBSTANCE STORED C.A.S.#:
III. TANK CONSTRUCTION
MARK ONE ITEM ONLY IN BOXES A, B. AND C, AND ALL THAT APPLIES IN BOX D
A, TYPE OF 0 1 DOUBLE WALL 0 3 SINGLE WALL WITH EXTERIOR LINER 0 95 UNKNOWN
SYSTEM ø 2 SINGLE WALL 0 4 SECONDARY CONTAINMENT (VAULTED TANK) 0 99 OTHER
.~ 1 BARE STEEL 0 2 STAINLESS STEEL 0 3 FIBERGLASS 0 4 STEEL CLAD WI FIBERGLASS REINFORCED PLASTIC
B. TANK
MATERIAL 0 5 CONCRETE 0 6 POLYVINYL CHLORIDE 0 7 AlUMINUM 0 8 100% METHANOL COMPATIBLEWIFRP
(Primary Tank) 0 9 BRONZE 0 10 GALVANIZED STEEL 0 95 UNKNOWN 0 99 OTHER
01 RUBBER LINED 0 2 AlKYD LINING 0 3 EPOXY LINING 0 4 PHENOLIC LINING
C. INTERIOR 0 5 GLASS LINING 0 6 UNLINED 0 95 UNKNOWN 0 99 OTHER
LINING .'
IS LINING MATERIAL COMPATIBLE WITH 100% METHANOL? YES_ NO_
D. CORROSION 0 1 POLYETHYLENE WRAP o 2 COATING o 3 VINYL WRAP 0 4 FIBERGLASS REINFORCED PLASTIC
PROTECTION D 5 CATHODIC PROTECTION !:23 91 NONE o 95 UNKNOWN D 99 OTHER
IV. PIPING INFORMATION
CIRCLE A IF ABOVE GROUND OR U IF UNDERGROUND, BOTH IF APPLICABLE
A, SYSTEM TYPE A U 1 SUCTION A U 2 PRESSURE A U 3 GRAVITY A,'Ú 99 OTHER
B. CONSTRUCTION A U 1 SINGLE WALL A U 2 DOUBLE WALL A U 3 LINED TRENCH A '!!J 95 UNKNOWN AU, 99 OTHER
C. MATERIAL AND A U 1 BARE STEEL A U 2 STAINLESS STEEL A U 3 POLYVINYL CHLORIDE (PVC) A U 4 FIBERGLASS PIPE
CORROSION A U 5 ALUMINUM A U 6 CONCRETE A U 7 STEEL WI COATING A U 8 100% METHANOL COMPATIBLE W/FRP
PROTECTION A U 9 GALVANIZED STEEL A U 10 CATHODIC PROTECTION ,. li"')5 UNKNOWN A U 99 OTHER
_.......
D. LEAK DETECTION D 1 AUTOMATIC LINE LEAK DETECTOR D 2 LINE TIGHTNESS TESTING D 3 INTERSTITIAL 0~99 OTHER ¡..J (\;JL
MONITORING
V. TANK LEAK DETECTION
o 1 VISUAL CHECK 0
o 6 TANK TESTING 0
2 INVENTORY RECONCILIATION 0 3 VAPOR MONITORING 0 4 AUTOMATIC TANK GAUGING 0 5 GROUND WATER MONITORING
7 INTERSTITIAL MONITORING ,~91 NONE 0 95 UNKNOWN 0 99 OTHER
VI. TANK CLOSURE INFORMATION
1. ESTIMATED qATE LAST USED (MO/DAYIYR)
t ...t'-,,~ 'I: ~,) <~, ...U I'I.J
2. ESTIMATED QUANTITY OF
SUBSTANCE REMAINING
3. WAS TANK FILLED WITH
GALLONS INERT MATERIAL?
YES 0 NO GJ
THIS FORM HAS BEEN COMPLETED UNDER PENAL TY OF PERJURY, AND TO THE BEST OF MY KNOWLEDGE, IS TRUE AND CORRECT
APPLICANT'S NAME DATE
(PRINTED & SIGNATURE)
LOCAL AGENCY USE ONLY THE STATE I.D. NUMBER 15 COMPOSED OF THE FOUR NUMBERS BELOW
STATE I.D,#
COUNTY #
[2EJ
JURISDICTION #
[21QI}]
FACILITY # TANK #
~~
I PERMIT EXPIRATION DATE
PERMIT NUMBER
.1 ¡-:::
l.. II
I PERMIT APPROVED BY/DATE
FORM B (9-90)
THIS FORM MUST BE ACCOMPANIED BY A PERMIT APPLICATION· FORM A, UNLESS A CURRENT FORM A HAS BEEN FILED.
FOROD34B-R4
e
'.
Perm.:lt
Quest.:lonna.:lre
Normally, permits are sent to facility Owners but since many
Owners live outside Kern County, they may choose to have the permits
sent to the Operators of the facility where they are to be posted.
Please fill in Permit # and check one of the following before
returning this form with payment:
For PERMIT # ~~o'l c....,
~1.
Send All information to Owner at the address
listed on invoice (if Owner is different than
Operato!'. it will be Owner's responsibIlity
to provide Operator with pertInent
information) .
2. Send all information to Owner at the
following corrected address:
3. Send all information to Operator:
Name:
Address:
(Operator can make copy of permit for
Owner) .
, .~i
ENVìRON~'E~ L\kHEALTH SERVICt:'bEcè~~i~E~~"
. ,. .,_~~,.'. .:--~ ,r. ';:^, ~,. ,< ,~'-
,- ,
STEVE McCALLEY.. R.E.H.S."
I ( '. DIRECTOR "
"
", \ \. ¡ ;'. .......
". . ",~..,·~?~,~M~: Stt~e¿S~té 300..
, "', ..' " '<'i;",:\;¡,ít.(¡¡.af¡!ld~,~~f,.933Òr',
~ '::,':'. . ,"},;(à9S)S$~t.-3S38~,'\: "
" ,:. ' . " '~'·:,ì805)f861-3429;j:AX·
'. . ,~š1:~1~¡:r B·;,(' .
.
: ' ~ .
.~.[ ....
. ' ..:. .
Faci l1ty Name: . J
DLD k ~ f) ~~"a..; ~
Address: bD l> 0, fA. ~~ A-V~~
~ ~ers -ß.~ C-A..!J 3 3 ()-::r
**UNDERGROUND TANK DISPOSITION TRACKING RECORD** .
:KemCounty Permit #:
·.··,AIg3'?--25
county.: ~
This form 1S to be returned to the Kern County Environmental Heaîth' Services
Department within 14 days of acceptance of the tank(s) by an approved disposal
or recycling facility. The holder of the permit with the number noted above is
responsible for insuring that this fonm is completed and returned~ .
Section 1 To be filled out by tank removal contractor:
Tank Removal COntractor:...M-C"'~"'''¡ I'<"}" 'NG . .'
Address: ~ð IN ou ~-t=2I~ ~eE-r" . Phone": 80S· !%4:J"1~
BA.Œ&SF1ËU> ("AL.aC:ð2ðl!Å~ Zip: q~SO'·. . '.'<
Date Tank(s) Removed: No. of Tank(s):,·, ,.' ...~
.
_.
_t" ".'.
" "." ,
"'.;... '
ìection % To be filled out by contractor "decontaminating" tank(s): .'.,"
"
. "
..', -~
.-
Tank "Decontamination" Contractor: M.P. VAC:~&JM ."
Address: g4ðð No2'1'P{ M~ðe ~~ET' Phone ':JOS'¡~
AA"ERSFIfL.D ~.ÀlI~ðQN1Â Zip: ~"""
Tank Size L.E.L. Tank Size L.E.L...
:It 1 lAOe'>O 6L\L. 0 "
.2. taðeð4A1.. 0
--
.'.
. .... ."... "~
,.... . 'Authorizëërrepnrsentat1vé:'o'f'the contractor certifies by signing below that t'he
..... . .,
, tank(s) have· been decontam1'nated in accordance with Kern County Environmental'~
. Hea!~!t!!erv ce. 8IIIrtfmt ""!.u1rements. .12'- .
~ . .\"" ~.
.".... J..!" -+ _; ~ " ~ . , .
.' it l,e~~'j¡; , . L;'
',(".
ection 'ª To be filled out and signed by an authorized repre,~entat1ve,of:the
approved disposal or recycling facility åccepting the tank(s):
.,
Facility Name:
Add
"
Phone .: . ~~1;"~C:¡
Zip: Ci'?:i:2~'\ '
No. of Tan~s)·..a: <j
Title: ?--'!L/.ïq~.
700 "M"'::' I ~1 t SUITE 300
BAKERSFlì :'¡~. CALIFORNIA 93301,
(805) 861·3636
I-a 117"V"Streel
. .- . Bakersfield, CA 93304
(805) 327-0671
(805) 324-4218 FAX
& Associates
li.~~~¡:µTIj 'r,:
{'I' / i :¡; /i :'
, " ' . ,'I
! f 'r-.r"·v"',', ¡
'11\ \ ¡ : \1l~R J 7 L:"" !! i ' '!
d J \ \ : ~:; ! ¡ J
¡'Iii' 1Vi!
¡' U W i.-_____ I ,/ !
¡ --'-----.1 I
March 12, 1993
Mr. Jim Mitchell
M Construction Co.
340 Industrial Street
Bakersfield, California 93307
SUBJECT:
r jt p, If3"7-Z-S
UST Soil Sampling and Analysis ~.rm ,,,
K&D Salvage, 600 South Union Avenue
Bakersfield, California
Dear Mr. Mitchell:
Pursuant to our agreement, BSK & Associates is pleased to present analytical results for the
above-referenced project. Four soil samples were collected for analysis during removal of two
underground storage tanks (USTs) on March 4, 1993. Two soil samples were collected for
analysis at each UST site at depths of two and six feet below the tank bottom.
The USTs were located at the property known as K&D Salvage, 600 South Union Avenue,
Bakersfield, California. See Site Plan, Figure 1. The center of the west tank (1,000 gallons
capacity) was located at a point 207 feet east of the east curb on South Union Avenue and 179
feet north of the wooden fence bounding the property on the south. The center of the east tank
(500 gallons capacity) was located 216 feet east of the South Union Avenue curb and 180 feet
north of the south boundary wooden fence. Nearby floor slabs from fonner buildings at the site
have been spray-painted with arrows to indicate positions of the fonner tank sites.
The samples were collected from relatively undisturbed soil brought from depths of two and six
feet beneath the tank bottoms in the bucket of a backhoe. Soils sampled were predominantly
poorly-graded sand. Samples were collected in stainless steel tubes, six inches in length and two
inches diameter, using a slide-hammer sampler. Sample tube ends were covered with Teflon
film, capped with pressure-fitted plastic caps, sealed with transparent packing tape, and labeled
following collection of each sample. Portions of the sampling equipment that make contact with
soil were decontaminated before and after each sampling event. Sampling, decontamination, and
sample preservation were conducted in accordance with procedures described in BSK &
Associates, Soil and Groundwater Sampling Procedures, a document on file at Kern County
Environmental Health Services Department (KCEHSD). Chain-of-Custody documentation was
maintained during sample collection and transport.
BSK Job B93039 - March 12, 1993
Geotechnical Engineering· Engineering Geology' Environmental Services' Construction Inspection & Testing' Analytical Testing
UST Soil Sampling and Anall- K&D Salvage, 600 South Union A
e
Page 2
The four samples were analyzed for Total Petroleum Hydrocarbons - Gasoline (TPH - G) and
for Benzene, Toluene, Ethylbenzene, and Xylenes (BTEX) using EPA Methods 8020M and
8015M, by BSK Analytical Laboratories in Fresno, California. BSK Analytical Laboratories is
a State-certified lab.
Results are summarized in Table 1. Copies of the analytical results and chain-of-custody
documentation are attached. Please have the property owner submit this report to KCEHSD.
We appreciate the opportunity to be of service. If you have questions regarding this report, please
contact our Bakersfield office.
Respectfully submitted,
BSK & Associates
4?
Ivan D. Sanderson, Ph.D.
Registered Geologist No. 4514
IDS:wp
Distribution: 4 copies to M Construction Co.
BSK Job B93039 - March 12, 1993
~
& Associates
UST Soil Sampling and Anal. K&D Salvage. 600 South Union A
¡-
Page 3
....................-............ .........................................'.....'.._..............-.....-...-..-.-_....-,.........-.-.-_..-.-..............
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}~:t~~~t~;t;~;;t:t~?t;:~:I:;f;{ttt/??:t:::·:·:·:·:·:·:·:·:·:({::t:~:::::;:;:::::;:::::::::::::::;::::::~::::;::{:' :;:;:;:;:;:;:;:;:;:::::::::;:;:;:;:;:.;.;.::: ............: ............ :.:::':':;';::::::';:;:;:;:::;:::":':::::::::::::::::::::';::::':':"':':';":'..:: >::::::::::::::::::::;:;;;;;:::::;:;:::::;:;:::;:;:;:::;::::;:;:: . ...
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:.;.:.:.;.;.;-:.:.;-:-:.::::::::::.:.;.;.:::-:.:.' ..:.:.:-;.;.;.:.;.;.;.;,;.;.:...:.....:.;.;'.'..;.:.:.:: :.:-:-:-:.;.:.;.;.....;..::-;.....-:-.'.;.-;-::;.:.... ....;.;.:-:-;-:';..-:-:...;.-;.:-:...;...;.,...;.;.;.;.;.;. ......,...,.......................-..,.,._;.._....-.-...'. ._.:-;..-:-.-.-;.:-:.;..:--;.:;.;.:;.:-:'.......... .-.... .." --. ,..-.."
.:::!:::æ~/ .. ·:pjpm;·~Jl*ø;!!~~~~H . . To]uene,····~myHrtøiåt
.·:·,·I1~gf·«..):.ttBm:'6:î(v~gW~g\i~¡¡þêijiÇijt$; . ···X· I·'
J¡tffii!®!iii,ii .... . . . ¡¡!Xi . ..' .ii;·~i I~liiì!i~
East Tank 2 840 ND 1 9 1 4 18
($00 Gals.) 6 1,000 NO ND NO 20
West Tank 2 NO NO NO NO NO
(1,000
Gals.)
6
NO
NO
NO
ND
NO
Abbreviations:
BTB = Below Tank Bottom
TPH-G = Total Petroleum Hydrocarbons - Gasoline
ND = None Detected
mg/kg = Milligrams per kilogram (parts per million)
BSK Job B93039 - March 12, 1993
~
& Associates
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8SK Job 893039
March, 1993
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Brick Wall
Wood Fence
FORMER TANK
LOCATIONS
WEST 0 II EAST
TANK TANK
Qon Gnls. 500 Gals.
Wood Fence
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50
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Scale: 1 Inch = 50 Feet
Figure 1.-- Site Plan.
Curb
100
,
Daniels Lnnc
PHASE I UST SOIL SAMPLING AND ANALYSIS
K&D SALVAGE, 600 S. UNION A VENUE
BAKERSFIELI), CALIFORNIA
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ANAL YTICAl
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LABORATORIES
ÞrM_-.YI.IJ .......
1414 Stanislaus 5t'
Fresno, California 93706
Telephone (209) 485-8310
FAX (209) 485-6935
1-800-877-8310
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BSK-Bakersfield
K & D Salvage
Date Sampled
Time Sampled
Date Received
Date of Analysis
Report Issue Date:
Case Number
Lab ID Number
Project Number
Sample Description:
Ch930557
0557-1
B93039
East Tank
(500 Gal) 2'
Sample Type
Analvses for BTEX bv EPA Method 8020
and TPH (G) by EPA Method 8015
Results Reported in Milligrams per Kilogram (mg/kg)
compound
Results DLR
ND 0.005
1.9 0.005
1.4 0,005
18 0.005
840 1.
DLR Multiplier 1
Benzene ........................
Toluene ........................
Ethylbenzene ...................
Total Xylene Isomers ...........
Total Petroleum Hydrocarbons (G)
Sample DLR = DLR x DLR Multiplier,
DLR: Detection Limit for the Purposes of Reporting.
Exceptional sample conditions or matrix interferences
may result in higher detection limits.
ND: None Detected
Cynthia
R930106 BTPS.t
03/04/93
1250
03/05/93
03/11/93
03/11/93
SOLID
-#~
Jeffry Creager, Organics Manager
.-
ANAL YTlCAl
-
lABORATORIES
&rw..,,¡¡,¡ &tMw
1414 Stanislaus S.
Fresno, Callfomia 93706
Telephone (209) 485-8310
FAX (209) 485-6935
1-800-877-8310
BSK-Bakersfield
K & D Salvage
Date Sampled
Time Sampled
Date Received
Date of Analysis
Report Issue Date:
Case Number
Lab ID Number :
Project Number :
Sample Description:
Ch930557
0557-2
B93039
East Tank
( 500 Gal) 6'
Sample Type
Analvses for BTEX bv EPA Method 8020
and TPH (G) by EPA Method 8015
Results Reported in Milligrams per Kilogram (mg/kg)
compound
Results
DLR
Benzene ........................
ND
ND
ND
20
1000
0.005
0.005
0.005
0.005
1.
Toluene ........................
Ethylb~nzene ...................
Total Xylene Isomers ...........
Total Petroleum Hydrocarbons (G)
Sample DLR = DLR x DLR Multiplier,
DLR Multiplier = 500
DLR: Detection Limit for the Purposes of Reporting.
Exceptional sample conditions or matrix interferences
may result in higher detection limits.
ND: None Detected
03/04/93
1255
03/05/93
03/11/93
03/11/93
SOLID
--
£/
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Jeffr Creager, Organics Manager
Cynthia Pi
R930l06 BTPS.t
QA/QC Supervisor
ANAL YT ICAL
[;m
LABORATORIES
~&Miw
1414 Stanislaus St.
Fresno, Califomia 93706
Telephone (209) 485-8310
FAX (209) 485-6935
1-800-877-8310
--
BSK-Bakersfield
K & D Salvage
Date Sampled
Time Sampled
Date Received
Date of Analysis
Report Issue Date:
Case Number
Lab ID Number
Project Number
Sample Description:
Ch930557
0557-3
B93039
West Tank
(1000 Gal) 2'
Sample Type
Analvses for BTEX by EPA Method 8020
and TPH (G) bv EPA Method 8015
Results Reported in Milligrams per Kilogram (mg/kg)
compound
Results
OLR
Benzene ........................
NO
NO
NO
NO
NO
0.005
0.005
0.005
0.005
1.
Toluene ........................
Ethylbenzene ...................
Total Xylene Isomers ...........
Total Petroleum Hydrocarbons (G)
Sample OLR = OLR x OLR Multiplier,
OLR Multiplier
DLR: Detection Limit for the Purposes of Reporting.
Exceptional sample conditions or matrix interferences
may result in higher detection limits.
ND: None Detected
Cynthia Pigman, QA/QC Supervisor
R930l06 BTPS.t
-ß.l --
Jeffr~ creager,Porganics Manager
: 03/04/93
1305
: 03/05/93
03/08/93
03/11/93
SOLID
1
1414 Stanislaus St. '
Fresno, California 93706
Telephone (209) 485-8310
FAX (209) 485-6935
1-800-877-8310
e
ANAL YT ICAl
-
lABORATORIES
,&",u-.YIJJ AeMw
BSK-Bakersfield
K & D Salvage
Date Sampled
Time Sampled
Date Received
Date of Analysis :
Report Issue Date:
Case Number : Ch930557
Lab 1D Number 0557-4 Sample Type
Project Number B93039
Sample Description: West Tank (1000 Gal) 6'
Analvses for BTEX bv EPA Method 8020
and TPH (G) by EPA Method 8015
Results Reported in Milligrams per Kilogram (mg/kg)
Compound
Results DLR
ND 0.005
ND 0.005
ND 0.005
ND 0.005
ND 1-
DLR Multiplier 1
Benzene ........................
To 1 uene ........................
Ethylbenzene ...................
Total Xylene Isomers ...........
Total Petroleum Hydrocarbons (G)
Sample DLR = DLR x DLR Multiplier,
DLR: Detection Limit for the Purposes of Reporting.
Exceptional sample conditions or matrix interferences
may result in higher detection limits.
lID: None Detected
03/04/93
1315
03/05/93
03/08/93
03/11/93
: SOLID
Cynthia Pigman, A/QC Supervisor
R930106 BTPS.t
# ~r-
Jeffr Creager, Organics Manager
BSK Log Number
~D55¡
clienKl11ec1 D
Address % .&-~
City~tate"Zip
~~rS{¡r::¡d)
Date
sampled
Ç'!
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.i~UiShed by
Received by
Relinquished by
Received by
Relinquished by
Received by
Time
sampled
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,BSI( & Associates
ANALYSIS REQUEST ¡CHAIN OF CUSTODY RECORD
1000- 4879
ProjecLpr P.O,# <; / A I· . /
4' ç':3 0 5" ' na yslS reqUIred
Lab Use Only
Phone # _....., ....; in this (J
~V S -- .f.4./ -::-% I section ~ ,þ
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Sample
Seals
(See key
below) ~ 0<1. Remarks
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Sampled by ~ r-.
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of Sample
containers number
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below)
Sample description
£057
Gar"
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IMPORTANT NOTICE: No samples will be analyzed without an authorized signature in this section.
Print Name
bC?'-. /7 . S- a......d ~/-.
n. ,Q¡@tn
Co;"
.
I am hereby requesting BSK's Formal Chain-of-Custody Procedures for the above samples. I understand that
these procedures are generally consistent with those outlined in U.S. EPA Contract Laboratory Program State-
ment of Work, Section F, and that there is a charge of $50.00 per work order or $5,00 a bottle, whichever is
greater,
By:
Company
Authorized Signature
Date
Time
I am hereby requesting BSK's Normal Chain-of-Custody Procedures for the ab~ve rle I understand that
these procedures are generelly consistent with ZEhose ou ' ed int;:?:h .. .. 846 d that there is no
extra charge for this service. _ _
By: ' .,// - z.---
,r /' Almíorized Signature
§jønature II /
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, .I{)'h~ L( f1 ì ~ 0
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KEY: Type: AQ-Aqueous SL-Sludge SO-Soil PE-Petroleum OT-Other
Seals: P-Present A-Absent B-Broken
DISTRIBUTION: WHITE, CANARY - LABORAlORY PINK - ORIGINAlOR
Note:
Samples are discarded 14 days after results are reported unless other arrangements are made.
Hazardous samples will be returned to client or disposed of at client expense.
Chemical Laboratories
1414 Stanislaus Street Fresno, California 93706
Telephone (209) 485-8310 · Fax (209) 485-7427
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Fresno
Visalia
Bakersfield
Pleasanton
Sacramento
--. ._,,~_. --
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IVAN D. SANDERSON, PhD, RG
Senior Geologist
Environmental! Geoscien :es Manager
GEOTECHNICAL ENGINEERING
ENGINEERING GEOLOGY
ENVIRONMENTAL SERVICES
CONSTRUCTION INSPECTION & TESTING
ANALYTICAL LABORAIDRIES
117 "V" Street
Bakersfield. CA 93304
(805) 327-0671
FAX: (805) 324-4218
-------------
Ofpce '-Memorandum
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PROM : ~
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KERN
COUNTY
DATE: 6-;)....'t-C; ~
Telephone No. (316)
SUBJECl': ;1500 t \ ~ ~ ~
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KC 96-5004
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"IæIL~ c;oUNTY RESOURCE MANAG~-' . AGRNCY
ENVIRONMEmAL HEALTH SEi\ViI.·F~· DEP..!ütTMENT
27QO "M" STREET, SUITE 300
BA1ŒRSFŒLD, CAIJPORNlA 93301
(805)861-3636
:FIlJ.. OUT ~ APPLICATION PER FAClUTY)
, ,\PPLlCATIOIIJ FOR PERMIT FOR PERW.ANENT CLOSURE/ABANDONMENT OF UNDERGROUND
HAZARDOUS SUBSTANCE STORAGE FACUlTY
:'HIS APPUCAT10N IS FO~MOVAL, OR 0 ABANDONMENT IN P~Œ
A:FACUJTYINFORMATION
¡:, . ;::
INTERNAL U , LY: PTA: fJ¡tß1"'~~
APP1JCA110N OP DAT!f2 ·2'3 .ra' ,
,; OF TANKS TO ABANDON:~ .'
PIPING FT. TO ABANDON; -
PTo: J, ()()I{
f '
ProJettContlct: J,'m P M 1Tc~ell I Phone: 3-;).4-J~601 TIRISEC (RuralLocationa):f~t.5 ~ø~ R28£
Fa(:üity Name:C)lJ ~. g V S'q. \\I(\"~ Add....·1!I$: 600 s, U;I\ )1 0"" Nearest Cross .
-,....- " City: Bø, /<,.pl''¡ A't ( JJ Zip: C¡~30? Street: DQ. nI ~ i l' L., j
Phone #·NcY\t.. $I~ J I1Ø~
. - V<lCA,,'r
Own.!r: IV'lT D"" ~"t..I.s I Addrcss: '33 ~ H q 07"10,,", Y 1)" , SQce: ßo,kvJ-{;y IcR ("fIll-
Phone: ¥ /'o¡ --4 rf 8' i City: 'Bqk.("n~ ("f c..9 Zip: c¡ 330'
B:CONTRACTORIN¡ORMATION
Tank Removal Contr~ctor: M ,CO;1 rrrv C.:1"t """ C \J '/ ~....., I Address: '3;';0 x.".,,¡;VI'7'nfJ' (T State: C9 ¡
Phone #: 3f).;'¡- /"''760 ' I Cfry: (3", k..~ -A~ reQ zip:93~oI
Proposed Start Date: Califorrna License Type & #: A I G /1.1 Co 2.1, Hu Worker's Compensation #:
ASft.f' J.f Ii-{ 6' "f 5 vue 6 8'o¿.¡ 8Z8'3 '7
Conttactor Retrieving Samplea: ß.$ Ie:: cwt£) As.s C1 c.. " Address: ,,? V ~. I S~ate: ~ ,
I
Phone II: 3 7-?- 06')1
Worker's Compensation #: W è. G 3 I' I 5" A
Laboratory c.."lat wUl a...'1Q.Ìÿze '>d.:ü1jJLi:ti; 85' I< Á.tQI yl't' c€¡ ,-~ Lo¡bs,
Phone #: /- S'QO- 8 ??- II 31 0
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! City: 'Ï3Cf \c:.-v\~" (JJ i ZlP:<ß30"f I
¡ Insurer: S JfU'\'or N~'h'o",4'\' I
¡ Addreu: I ï.J i~ <;'ht. .ds /CHJS í'ry Scate: C~
! City: p"1'I" ó Zip: C¡3~o6
~; aæMICAL INFORMATION
Chemkal Composition of Mareri.Üs Stored:
Tank# Vcrhrme Chf.1micai Stored
~ /000 <; '" \ ¿:;a)() I,,,,-t.
J.. 100(1560 , GQ) <J F"'~
~ ::. -
Dates Stored
? Iff60 To IY~'O ?
?~QTo P~s~'1r
To
To
-~ 7
C.hemic:al Formerly Stored
/Vo.u íî
/1...;1 <:J.lVl£.
-,
-:-
-
): Environmentallnfol'T!121dcm
Water to facility provided by: lCf i W':t 't<-r ¡ :¡~ gIoundwateI' '..vithin 50 feet? Y o(N) /8" fef!7: ePee þ
Nearest water we1J-Gh'e cii5rart~e if withi.'1~5ôo feet: /5'00.... rš;il t"'j'p'3 at {adUty: fVt L ~¡~ CWlllOo'\"'/ s<:!... q~JJ SP
....1""'11.-.... L "'"'<¡¡.
Basi. for soil type anci gr"U.r.j-;N2.¡:~r &ep~~ dftermin~'n:,....[,'~eM~ I" <:{t'V~ t' (tit Woe. 7"C.r
Total number of samples \:0 be am:!yud: ~ j SmllÚii ro be aruûyzeci f.)r: ß TX q",tJ TPH _CJ"'Jù/''",t
.. ~.....
~: Disposallnformarlon
Deco~taminationprocedu.re: Tr I " j e r t '" S\L ro L t= L <. g; ï (>
Decontaminaåon Contractor: M. P E Y'I" \ re '" ,., (' .,,, I 7.., c I Disposallo<::¿¡tìon far ri.l1,eate:
Phone #: 3'3 --1/5 ì._ __ i Gi.bJ v...... I::..., 1/',' (cJY7 ;?- ~ J'7""'" } '._ \
Dis!08al method for tank(s): R('- c y(. J,~ ,_,___ ¡ Disposallo:::ation for tU'..k(s): Go (cYP-"1 ,Ç"~,.. f11" "" J oS
Disposal method for piping: R "t_ ~'y c I''':f- ~ I D~yo¡o;u 1 c>cation 20: pipinö: 60 í.Q-, S.,..., ~ M ~ ~ ) J
....Please ~~~ç,W.ß.ev~rs~ S.ir:i~ .QLT.IDr,A~t9re Submirr~ FOT R..e~
rus t.orm .h¡s Þt!!t!n cOJ':p;e~td !J.:~0/~;:,,~.Üv,;f pelj1.i.ry a.."ld ~(¡ d:~ bEst of:nY. k..."1¢IHiccið~ i~ true .md correct, .
jign.a,ture~ ~ ....~ . ....:....__ ~~.;_t:,,:: _Prt'J¡j)l"""~_"_ Dare: ~~L2...3/9 3
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CASH KEn I Sn=R
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Irwo'ice Nbr. 1
90401
KERN CO RESOURCE MANAGEMENT AGENCY
2'100 't9'l1 Stre(';:t
Bakersfield. CA 93301
( B 0 5 ) 8 6 1 -. 3 [) 0 ?
. .. .... '. .............,. ··.·..·.·r··.···..·'.···_·· ..........,.............._.........."
......<0.......... .,., ,........ ._...
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Wtn By ¡Order Date I
f:3A~3 I 02/23/93 !
... .,......... !......,...,..,.... I
..... p........... ...'
:..'j ne i)~)SC r'j pt'f on
4751U~OERGROU~OTANKS CLOSE/A8AND
1)31'002
THANK YOUl
Type ef Or'del"
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,.. ,., ..., . , ,.. _.. ... .... ... ... .., ... _.. ... .... .... _.._. ..' .., _.. .... ._. .., ,_, ... .., .... ,... .., .., ... ... ... .... I
¡
NATHAN DANIELS & SARA LEE I
¡
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Sh-¡ p Date ¡ V·, a ¡ Terms I
02/2,¡/9:) IOF I NT I
. .... ,.......,.. I.. ,.......... ...... ...... .... ........ ..... ¡ ....................... ,. ,. ¡
Quentity Price Unit Disc Tetal
EH 1 1100.00 E 1100.00
O,..da,.. Tota"1
1100.()0
Amount Due
1100.00
Payment Made By Check
1 '100.. 00
· e
ENVIRONMENTAL HEALTH SERVICES DEPARTMENT
STEVE McCALLEY, R.E.H.S.
DIRECTOR
2700 -M- Street, Suite 300
Bakersfield, CA 93301
(8051 861-3636
(8051861-3429 FAX
February;),
1993
Nathan Daniels
3318 Harmony Drive
Bakersfield, CA 93306
RE: Underground Storage Tanks, Monitoring, Repair, Abandonment and
Tightness Test Requirements. Permit to Operate Underground
Storage Tanks Number 250011.
Dear Mr. Daniels:
In regard to the underground storage tank facility located at 600
Union Avenue in Bakersfield, California you are currently in
violation of the following:
NOTICE OF VIOLATION
1. Section 8.48.030 (A) of the Kern County Ordinance Regulating
Underground Storage Tanks: No person sha.ll .., abandon. . . a
tank, . . ,at a facili ty for the underground storage of
hazardous substances within the unincorporated and
incorporated areas of the count:v unless by authori ty of a
"'a1 id, unexpired unrevoked permi t issued to the owner pursuant
to the provisions of within this chapter...
2. Section 8.48.120 IC) of the Kern County Ordinance Regulating'
Underground Storage Tanks: That the holder of the permit ha.s
violated one or more conditions upon which the permit has been
issued.
Permit to Operate #250011, Conditions/Prohibitions ï. The
facili ty underground storage tanks must be moni tored,
utilizing the option approved b:v the permitting authority,
until the tank is closed under a ,,-alid, unexpired permit for
closure. and 8. An,Y inacti ve underground storage tank which
is not being monitored, as approved by the permitting
authority, is considered improperl;t- closed. Proper closure is
required and must be completed under a permit issued by the
permitting authority. Monitoring Requirements 1 a and b
e
;.
Page 2
Nathan Daniels
3318 Harmony Drive
Bakersfield, CA 93306
Standard Inventory Control Moni toring , . . shall be
utilized.. .in accordance with requirements summarized in
Handbook UT-1 O. All tanks shall be tested annually utilizing
a tank integri t.v test.,. The first test shall be completed
before December 31, 1991, and subsequent tests completed each
calendar year thereafter, All tank integri t,v tests. . . shall be
completed under a valid, unexpired Permit to Test issued by
the Environmental Health Services Department.
3. Section 8,48.170 (B)(3)(g) Owners shall repair or close any
underground storage tank for which an approved moni toring
program is not promptly obtained, ,.,
The department has not received an application for
modification or abandonment for this UST system. Several
attempts by telephone and office meetings with Amy Green have
not resulted in the submittal of any application.
ORDER TO CORRECT
1. Submit a completed application for a modification or
abandonment permit along with permit application fees to this
department by March 1, 1993,
Failure to comply with this ORDER TO CORRECT may result in
revocation of your Permit to Operate and referral to the Office of
the District Attorney. As prescribed by the County Ordinance, a
per-hour fee for extended services will be charged for any work
required to bring this facility into compliance. If you have any
questions please contact me at (805) 861-3636, extension 589 or Amy
Green at extension 576.
Sincerely,
Steve McCalley, Director
By:
~.~'
Carrie Georgi
Hazardous Materials Specialist
Hazardous Materials Management Program
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WOKK OBDD LOG SBBBr
Date: d.-. - ~ - 1,3-
Tracking #:
APN:
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Work Order #: RHO ? .s- o-.s-"
WO Category: Hazmats
WO Type: :¡::v
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RP Code:
WORK ORDER NAME: ;'00 (,Lr-\;" A~ )-!l",--~_L..-t
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PARTY (RP) NAME: IV~ L)~\-e \.$
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PROGRAM:
DESCRIPTION:
LOCATION:
FACILITY
NAME:
REPORTING PERSON:
PHONE NO.
COMMENTS:
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.UNDERG~Q~,~D.HAZARDOUS SUBSTANCE STORAGE: FACILITY
* INSPECTION RËPORT *
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PERMIT# 250011C' TIME IN ¡:éZ') TIME OUT NUMBER OF TANKS: 1
? E RM I T P CST E D 7 Y E S...................::....··Ñï::· .,,_:~.:=._... '-"'-'-""'ÏÑ 5 P EC T I ON DA T E :u..9..... --¡;¡::::«Fl..?
TYPE OF INSPECTION: ROUTINE,_....._~~..._ REINSPECTION _..........___ COMPL~ .~_..-:_:-:
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F AC I L I TY N AM E : ,Y..ð.º~.~J_.b.QJ_........_..............,_......_...._....._.._........,.............................................._....__.._,..._...__..__...__..___
F AC I L I TY ADDRESS: &.0 a._Y.N Lº.tLAY~N1U;:..........._.._........................,_.._...._.._.._._...___.....,,___.__.._..._,_
8AKERSF I ELD f (-:A
OWN E RS NAME: .Q.ðN.lg.b§..I...,..~I.t!.~..'~..........._.__..........................................,...............,......_.....___...._..._.___...___.._____.._
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GOMMENTS~
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ITEM VIOLATIONS/OBSERVATIONS
1- µRIMARYCONiAINMENT MONITORING: ../ ---
~. Ir,tercepting an directing system <
b. St~ndard Inventory Control . ,
c, ~odified Inventory C~'trol .~~--
d. [~-tank Level Sensing Oav;ce !.
e, Groundwater Monitoring /. ./ ..
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.. Vðdose Zone ~onitorin9
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), ~Ar~TENANCE, GENERAL SAFETY, AND !
OPERATING CONDITION OF FACILITY ¡
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REI..ÑS·p..~·C'T-ÚJr;¡~_·šc·H¡ªï5.(iLEÕ?:::::~~::~-;Ç";~'~.._~~~::~=~·;;..·..A·p·pï~Ò·x'i"r;ïÄ-T·E·.....RË·T~¡s..p·ËC·TTõ·N DA T E : _htt:~ ~'7 2 -/ s: '1
fNSPECTOR: / . ,.<:..Le..~ 1 REPORT RECEIVED BY:
....',.,................-=-".....'...........-'J"...................-........................... ........;\:)'0 6 ï\f E,----¡J¡,r" s ~-a7..
2-. SECONDARY CONTAINMENT MONITORING:
'/!; Liner '"
b. Double-Walled tðnk
c. Vauìt
! 3. PIPING MONITORING:
1J. Pressurized
b, Suction
c. Gravity
4, OVERFILL PROTECTION:
5, TIGHTNESS TESTING
6. NEW CONSTRUCTION/MODIFICATIONS
--
CLOSURE/ABANDONMENT
8, UNAUTHORIZED RELEASE
RE~URCE MANAGEMENT A'r.NCY
RANDALL L. ABBOTT
DIRECTOR
DAVID PRICE III
ASSISTANT DIRECTOR
Environmental Health Services Department
STEVE McCALLEY, REHS, DIRECTOR
Air PoUution Control District
WILLIAM J. RODDY, APeO
Planning & Development Services Deparunent
TED JAMES, AlCP, DIRECTOR
ENVIRONMENTAL HEALTH SERVICES DEPARTMENT
July 22, 1992
DANIELS, NA1HAN
3318 HARMONY DRIVE
BAKERSFIELD, CA 93306
Re: VACANT LOT
Permit #: 2500l1C
Dear Sir/Madam:
The Kern County Environmental Health Services Department has completed a file review and was
not able to fmd an application for a permit to complete an integrity test, or the results of an
integrity test, for the underground storage tank(s) located at the facility sited above. The
monitoring requirements developed for the facility tank(s) require that integrity tests be completed
within the 1991 calendar year. Please review your records to determine whether a tank integrity
test was performed at your facility between January 1, 1991, and December 31, 1991. Please copy
any test results and submit the copy to this department within 14 days of this letter. The results
will be reviewed and placed within your permit file.
After August 10, 1992, all facilities which have not submitted proof of the integrity tests required
by their permits shall receive a notice of violation for noncompliance with permit testing
requirements for Calendar Year 1991. Facility owners or operators who receive a notice of
violation for noncompliance with the testing requirements for the calendar years 1991 and 1992 may
be cited into court for violation of permit conditions and state and local underground storage tank
laws. The facility owner/operator could be liable for a penalty of not less than one hundred dollars
($100) or more than one thousand dollars ($1,000) for each underground storage tank for each day
of violation for failure to test the tanks at frequencies specified within the permit to operate.
All integrity tests completed after September 16, 1991, are required to be completed under permit. '
Any test submitted which was completed without a valid testing permit after September 16, 1991,
was completed in violation of the Kern County Ordinance Code which regulates underground
storage tanks. The facility, and possibly the tester, shall be subject to fines/penalties.
If you have any questions regarding this matter, please feel free to call me at (805) 861-3636.
AG:jIW:ch
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2700 "M" STREET, SUITE 300
BAKERSFIELD, CALIFORNIA 93301
(805) 861-3636
FAX: (805) 861-3429
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FEBRUARY 12, 1992
KERN COUNTY
ENVIRONMENTAL HEALTH SERVICES
2700 M ST., BAKERSFIELD, CA.
RE: 600 S. UNION
BAKERSFIELD, CA.
TO WHOM IT MAY CONCERN,
tit" .
IN RESPONSE TO YOUR INQUIRY REGARDING THE POSSIBLE EXISTENCE
OF UNDERGROUND STORAGE TANKS, PLEASE BE AWARE THAT TO THE
BEST OF MY KNOWLEDGE, THERE IS ONE TANK THAT HAS NOT BEEN
USED FOR SEVERAL YEARS.
, ~.~
AT THIS TIME I AM TRYING TO SELL THIS PROPERTY~THEREFORE I
RESPECTFULLY REQUEST THAT I BE, GRANTED A eJ. ~ EXTENSION
TO COMPLY WITH WHATEVER ORDINANCES AND REGULATIONS MAY BE
APPLICABLE.
SINCERELY, ~~
NATHAN DANIELS
3318 HARMONY DR.
BAKERSFIELD, CA. 93306
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·21700 -M-" STREET, SUITE 300, BAKERSFIELD, CA.93301 .
. ' . (80S}861-3636 . . r
'. . UNDERGROUND 'HAZARDOUS SUBSTANCE STORAGE 'FAClLITY
* INSPECTION REPORT *
PERMIT. 250011C
PERMIT POSTED?
TYPE OF INSPECTION:
TIME IN ._._....._ TIME OUT NUMBER OF TANKS:
YES.__ NO ....____... INSPECTION DATE:
ROUTINE._...__ REINSPECTION ___ COMPLAINT
1
.-....-.------
F AC I L I TY N AM E : .§ 0 L D EN §.T~ T E ..J1.E T..~JJL....J..~.º..:.._..........__
FA C I L I TY ADD RES S : .~ 0 0 ..l! N I ON....A V E.t~'-~.!;........._.__._.._.....................___.._...___....._.....
BAKERSFIELD, CA
I OWN E RS N AM E : .ºA~l_g LS r ~ A TH AN...._._.___._......__._..........._.........
OPERATORS NAME:DANIELS NATHAN
COMMEN TS : .-..,....r;oj~çf..)~~::=:=·2..~·~"A=;::=~~=:"i5.D~:::~-.l;;~j£"¿~~ ~---.-_.-
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ITEM tI I\tl·~~ VIOLATIONS/OBSERVATIONS
~2-A£-¡¡: ~ ~ ~~
1. PRIMARY CONTAINMENT MONITORING: I
a. Intercepting an directing system
b. Standard Inventory Control I
c. Modified Inventory Control
d. In-tank Level Sensing Device
e. Groundwater Monitoring
f. Vadose Zone Monitoring
2. SECONDARY CONTAINMENT MONITORING:
3
a. Liner
b. Double-Walled tank
c. Vault
PIPING MONITORING:
a. Pressurized
b. Suction
c. Gravity
OVERFILL PROTECTION:
TIGHTNESS TESING
,
NEW CONSTRUCTION/MODIFICATIONS
CLOSURE/ABANDONMENT
UNAUTHORIZED RELEASE
MAINTENANCE, GENERAL SAFETY. AND
OPERATING CONDITION OF FACILITY
4
5
6
7
8
9
COMM EN T51 R ECOMMEN DA T I ON 5...........~::r.I4t...y_............2..L.....-5.¡~........~.....a~AJL
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LOCATION: (~o-~ 1\Jc;-:J- f) ~~~ ~ .
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FACILITY
NAME:
Revised 11/04/91
et:RN COUNTY HEALTH DEPARTME. -'
2700 M Street
Bakersfield, Cålifornia
Mailing Address:
. 1415 Truxtun Avenue
Båkersfield, California 93301
(805) 861-3636
ENVIRONMENTAL HEALTH DIVISION
HEALTH OFFICER
Leon M Hebertson, M.D.
DIRECTOR OF ENVIRONMENTAL HEALTH
Vernon S. Reichard
Mr. Nathan Daniels
P. O. Box 67
Bakersfield, California 93302
Dear Mr. Daniels:
This letter is an official notice of your non-compliance with
state and county laws relating to underground tanks.
Upon review of our records, it was discovered that the 1988
Permit to Operate fees for Golden State Metals, Inc., 600 Union
Avenue, Bakersfield, California were not paid. Enclosed is a copy
of 1988 I S invoice plus the 50% late penal ty required by county
ordinance. The second invoice is for this year I s Permi t to
Operate fees. These invoices must be paid within 30 days to avoid
further penalties and/or legal action.
Be advised that these fees must be paid even if the tanks are
no longer in use. I f the tanks are not in use, a permi t for
permanent closure must be obtained from this off ice. Permanent
closure requires either removal or closure in place of your tanks
and assessment by soil sampling to determine whether there has been
environmental damage as a resul t of unauthorized releases Ç)f
hazardous substances from your tank site. The specific
requirements for these activities are in Handbook #UT-30, available
with your application. No closur~ activity can begin prior to the
issuance of ~ ~mit from this office.
If you have any questions or feel this assessment is in error, ,
or if you would like an application and our handbook on permanent
closure please call me at (805}861-3636. Your prompt attention to
this very important matter is appreciated.
Sincerely,
;)l'l« ¿J~
Jane Warren
Hazardous Materials Inspector
Hazardous Materials Management Program
DISTRICT OFFICES
--,--__ - . ----a _ '_1.._ I. .&...._11_ a .......i......~ . Di,.f,..n,....ftf"o. . C':h'!:llltar . T.oIft
2700 M Street
Bakersfield, California
Mailing Address:
1415 Truxtun Avenue
Bakersfield, California 93301
(805) 861-3636
e. .~N COUNTY HEALTH DEPARTMe4t
ENVIRONMEN TAL HEALTH DIVISION
HEALTH OFFICER
Leon M Hebertson, M.D.
DIRECTOR OF ENVIRONMENTAL HEALTH
Vernon S. Reichard
June
Mr. Nathan Dani81s
cia Gyrum Kimball
1515 20th Street
Bakersfield, California 93301
Dear Sir:
This letter is an official notice of your non-cumpliance with
state and county laws relating to underground tanks.
Upon review of our records, it was discovered that the 1988
Permit to Operate fees for Golden State Metals, Inc" 600 Union
Avenue, Bakersfield, California were not paid. Enclosed is a copy
of 1988 I S invoice pIus the 50?f; late penal ty required by county
ordinance. The second .invo.Lce is for thi s year f s Permi t to
Operate fees. These invoices must be paid within 30 days to avoid
further penalties and/or legal action.
Be advised that these fees must be paid even if the tanks are
no longer in use. If Ule tank!:.~ are not in use, a permi t for
permanent ,.::losure must be obts.1.ned from this office. Permanent
clos11re requires either removal ü1' closure in place of your tanks
and asspssmen t by sO.ll samp.1i n~j to determine Nh~ tl.H-.r there has been
environment8.1 dam~ge as a result: of unauthorized releases of
h2.zard.ot1S substances f""u\fi 'i0u.I' tank site. The specific
requirements for these activities are in Handbook #UT-30, available
\ldth YOlU' ê\pplicatioH. Er¿ _(.:1.t,1f~~\~L~ §~~:!::)vity :;an beuin prior to the
lssuallÇe of -ª Q..§J~}~.:Lt;. .frolll .!:chi.§ .'.21Lif'§:·
If you h<'1ve any qnF'st:ions 01::' fr:,'el this assessment is in error,
or if you \.'JOuJ.d like 2.n '~L1plir:::;3.tion ;::J.nd 01..1.1:' handbook on permanent
c 108ure plpa!':;e (:;:'1.11 me i'd (80S) 8Gl--3G36, Your prompt attention to
tillS vC'ry .lmportant In;,,(-f-"'1" js appl'ecì.::¡ted.
S:inc:eTely, .
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&-r:e y.]arrl~n
Hw,~a:n1c.nH~ H<=t1:erials Inspector
Hazardous Materials Management Program
DISTRICT OFFICES
Delano . Lamont . Lak" 'nella. Mojave . Ridgecrest . Shaffer . Taft
ot Enviromaental HealtJ;t Application Da~
.r Street, Bakersfi. CA 93305 It .
APPLICATION FOR PERMIT TO OPERATE UNDEÆ;ROUND
HAZARDOUS SOBSTANCES S'l'ORAGE FACILITY
~ of Application (check):
CNiW Facility []flÐdification of Facility ØEKisti~ Facility
. "'I'jency 24-tÐut Contact (name, area code, ¡tlone): Days
, Niqhts
'.cUlty Name Golden State Metals Inc. ~. 0 or )
'J'ype of Business (check): [JGaso\ine Station gOther (describe)
J Ia Tank(a) Located on an Agricultural Farm? Dyes §lNo
'~ Is Tank(s) Used Primarily for Agricultural ~rposes~ DYes .. No . (\......01 e,ls "
t' 'acUity Address 2eOn 1:_ ~~m'lellUr-e ~ Ii/I~) !I¡J{(J(] f1 Nearest Cross St..g:-, erDQI1 A.a.
) ,tp T R S Rura Locations 0'11y)
1 ~Hathan Daniels Contact Person
Jy 1'318 Har.ony Dr.. Bakersfield. Ca Zip 93306 Tele¡h)ne 1if'7/- ~ rtrr-;.¡.
'r//! Opera or Ç2..,r¡ YYJ fJ Contact Person If/an OCi'/1 ,·e/s
Address Zip Telephone S<' '33 - 3 [? 7<2. '
8. Water to FacUity Provided by California Water Service Depth to' Grol.Diwater
Soil Characteristics' at facility
Basis for Soil Type and GroLRtwater Depth Deteœlnations
CA Contractor I s License No.
Zip Telephone
Proposed Caapletlon Da"
Insurer
C. Contractor
Address
Proposed Startl~ Date
Wbrker's Compensation ~ertification .
D. If This Permit Is For Modification Of An EKisti~ FacUity, Briefly Dascrlbe Modifications
proposed
E.
Tank(s) Store (check all that apply) :
~! Waste Product Motor Vehicle Unleaded Regular Pr_i~ Diesel Waste
Fuel on
~#( [] [] ~ ~ -
[] ~ 8 8
[] [] []
(] [] D 8 8 8 8
[] [J IJ
r. Ch_lcal CaDpoai tion of Materials Stored (not necessary for mtor vehicle fuels)
TanK . Ca-w-ic&l Stored (non-cOllDBrcial name) CAS . (if known)_ ct.aical Prevloual¥ Stored
(if different)
..
,G. Transfer of OWnership
Date of Transfer Previous OWner
Previous Facility Name
I, accept fully all obliqations of Permit No. issued to
. I understand that the Permittiß} Authority may review and
modify or terminate the transfer of ,the Permit to Operate this Wldergroœd storage
facility upon receiving this completed form.
'Ibis form has been canpleted under penal ty of
true and correct.
Signature Ilt~~~
perj ury and to the best of my knowledqe is
Title Office Nanager
Date 7-25-85
rc:u.:J..LH.y NC::UIæ ~H ~'t'UC¿SJé- L-\...)_ s, permlt NO.
TANK! L (FILL OUT SEPARATE FORM .. wACH ~)
FOR EACH SECTION, CHECK ALL APPROPRIATE BOXES
H. 1. Tank is: DVau1ted ONcm-Vau1ted DDoub1e-Wall Ø5ingle-wall
2. Tank Material
gcarbon Steel 0 Stainless Steel 0 Polyvinyl Chloride 0 Fiberglass<lad Steel
Fiberglass-Reinforced Plastic 0 Concrete 0 AllDinLIR 0 Bronze DUnknown
Other (describe)
3. primary Containment
IBte Installed 'ft1ickness (Inches) Capacity (Gallons) Manufacturer
CUt LI1·¡;;w v'\
4. Tank Secondary Containment
ODouble-Wall--r:JSynthetic Liner OLined Vault DNone ~O\«1
DOther (describe): Manufacturer:
DMaterial Thickness (Inches) Capacity (Gals.)
5. Tank Interior Lining
-¡:jRubber 0 Alkyd OEp>xy OPhenolic OGlass OClay ~lined Ot1'lkncM1
OOther (describe):
6. Tank Corrosion Protection
-UGalvanlzed DFlberglass-Clad OPolyethylene Wrap OVinyl Wrapping
~ar or Asphalt OUnknown ONone DOther (describe): .
Cathodic Protection: o None OImpressed CUrrent System [JSacr1flclal 1ftode SystsD
Describe System & Equipnent:
7. Leak Detection, Monitoring, and Interception
~Tank: DVisual (vaulted"tãnks only) (jGrouOOwater Mon i tori 11)' Well (8)
o Vadose Zone Moni toriD:j Well (s) 0 u-Tube Without Liner
o U-Tube with Canpatible Liner Directi~ Flow to Moni torl 11) Well(s) ·
o Vapor Detector· 0 Liquid Level Sensor 0 ConductivitX- Sensor·
o Pressure Sensor in Annular Space of Double Wall Tank
o Liquid Retrieval & Inspection Fran U-Ttt>e, Moni toriD:j well or Annular Space
o Daily Ga~iD:j & Inventory Reconciliation 0 Periodic Tightne_ T_tiD:j
~one 0 UnknO\«1 0 Other
b. P{pi~: Flow-RestrictiD:j Leak Detector(s) for pressurized Piping-
o Moni torlD:j Slap wi th Raceway 0 Sealed Concrete Raceway
o Hal f-cut Compatible Pipe Raceway 0 Synthetic Liner Raceway 0 HonII
aUnknO\«1 0 Other
*Deseribe Make & Model:
8. Tank Tightness
HaS 'Ibis Tank Been Tightness Tested? DYes ONe> ~\«1
Date of Last Tightness Test Resul ts of Test
Test Name Testil'¥J Canpany
9. Tank Repair
Tank Repai red? 0 Yes ~ Olk\known
Date(s) of Repair(s)
Describe Repairs
10. Overfill Protection
~ator Fills, Controls, & Visually Monitors Level
OTape Float Gauge OFloat Vent Valves 0 Auto Shut- Off Controls
BCapacitance Sensor OSealed Fill Box ONe>ne Ot1'1knO\«1
Other: List Make & Model For Above Devices
~
11. Piping
a. lklderground PipiD:j: ~es ONe> Dunknown Material
Thickness (inches) Diameter Manufacturer
OPressure (2lSuction C]Gravity - Approximate Len:)th of Pipe Ra.n
b. Underground prping CorrosIon Protection :
DGalvanized OFiberglass-Clad DImpr-essed current DSacrlficial Anode
gpolyethylene Wrap OElectrical Isolation OVinyl Wrap OTar or Asphalt
~Unknown o None OOther (describe):
c. Underground Pipirg, Secondary Contairment:
DDouble-wall DSynthetic Liner System ONone ~knO\«1
DOther (describe):
·
t
~URCE MANAGEMENT A~NCY
RANDALL L. ABBOTT
DIRECTOR
DAVID PRICE m
ASSISTANT DIRECTOR
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Environmental Health Services Department
STEVE McCALLEY, RÐfS, DIRECTOR
Air Pollution Control District
WILUAM J. RODDY, APCO
Planning & DeYeIopment Services Department
1E) JAMES, AlCP, DIRECTOR
ENVIRONMENTAL HEALTH SERVICES DEPARTMENT
PERMIT TO OPERATE UNDERGROUND
HAZARDOUS STORAGE FACILI'IY
Permit No.:
250011C
State ID No.: 250011
Issued to:
GOLDEN STATE METALS, INC.
No. of Tanks: 1
Location:
600 UNION A VENUE
BAKERSFIELD, CA
Owner:
DANIELS, NATIIAN
3318 HARMONY DRIVE
BAKERSFIELD, CA 93306
Operator:
DANIELS, NATIIAN
Facility Profile:
Substance Tank Tank Year Is piping
Tank No. Code Contents Capacity Installed Pressurized?
1 MVF3 REGULAR UNKNOWN UNKNOWN NO-SUCTION
This permit is granted subject to the conditions and prohibitions
listed on the attached summary of conditions/prohibitions
By:
Issue Date: November 4, 1991
Title: Director, Environmental Health S
Expiration Date: November 4, 1996
-- POST ON PREMISES--
NONTRANSFERABLE
2700 "M" STREET, SUITE 300
BAKERSFIELD, CALIFORNIA 93301
(805) 861·3636
FAX: (805) 861-3429
-
-
e
e.
HAZARDOUS UNDERGROUND STORAGE FACllJ'IY PERMIT
SUMMARY OF CONDmONSIPROHIBmONS
CONDmONSIPROHIBmONS:
1. The facility owner and operator must be familiar with all conditions specified within this permit and
must meet any additional requirementS to monitor, upgrade, or close the tanks and associated piping
imposed by the permitting authority.
2. If the operator of the underground storage tank is not the owner, then the owner shall enter into a
written contract with the operator, requiring the operator to monitor the underground storage tank;
maintain appropriate records; and implement reponing procedures as required by the Department.
3. The facility owner and operator shall ensure that the facility has adequate financial responsibility
insurance coverage, as mandated for all underground storage tanks containing petroleum, and supply
proof of such coverage when requested by the permitting authority.
4. The facility owner must ensure that the annual permit fee is paid within 30 days of the invoice date.
5. The facility will be considered in violation and operating without a permit if annual permit fees are not
received within 60 days of the invoice date.
6. The facility owner and/or operator shall review the leak detection requirementS provided within this
permit. The monitoring alternative shall be implemented within 60 days of the permit issue date.
7. The facility underground storage tanks must be monitored, utilizing the option approved by the
permitting authority, untü the tank is closed under a valid, unexpired permit for closure.
8. Any inactive underground storage tank which is not being monitored, as approved by the permitting
authority, is considered improperly closed. Proper closure is required and must be completed under
a permit issued by the permitting authority.
9. The facility owner/operator must obtain a modification permit before:
a. Uncovering any underground storage tank after faüure of a tank integrity test.
b. Replacement of piping.
c. Uning the interior of the underground storage tank.
10. The tank owner must advise the Environmental Health Services Depanment within 10 days of transfer .
of ownership.
11. Any change in state law or local ordinance may necessitate a change in permit conditions. The
owner/operator will be required to meet new conditions within 60 days of notification.
12. The owner and/or operator shall keep a copy of all monitoring records at the facility for a minimum
of three years, or as specified by the permitting authority. They may be kept off site if they can be
obtained within 24 hours of a request made by the local authority.
13. The owner/operator must report any unauthorized release which escapes from the sea>ndary
containment, or from the primary containment if no secondary containment existS, which increases the
hazard of fire or explosion or causes any deterioration of the secondary containment within 24 hours
of discovery.
AEG:jrw (greeø\penDiLp2)
2
_.
e'
MONITORING REQUlREMENTS:(MVF2Spr)
1. All underground storage tanks designated as MVF 2 within Page 1 of this permit shall be
monitored utilizing the following method:
a. Standard Inventory Control Monitoring (Tank gauging five to seven days per week).
Kern County Environmental Health Services Department forms shall be utilized
unless a facility form can provide the same information and has been reviewed and
approved by the Environmental Health Services DepartmenL (Monitoring shall be
completed in accordance with requirements summarized in Handbook UT-lO.)
AND
b. All tanks shall be tested annually utilizing a tank integrity test which has been
certified as being capable of detecting a leak of 0.1 gallon per hour with a
probability of detection of 95 percent and a probability of false alarm of 5 percent.
The first test shall be completed before December 31, 1991, and subsequent tests
completed each calendar year thereafter. All tank integrity tests completed after
September 16, 1991, shall be completed under a valid, unexpired Permit to Test
issued by the Environmental Health Services Department.
c. All pressurized piping systems shall install pressurized piping leak detection systems
and ensure that they are capable of functioning as specified by the manufacturer.
The mechanical leak detection systems must be capable of alerting the
owner/operator of a leak by restricting or shutting off the flow of hazardous
substances through the piping, or by triggering an audible or visual alarm, detecting
three gallons or more per hour, per square inch, line pressure within one hour.
d. All pressurized piping systems shall be tested annually unless the facility has
installed the following:
1. A continuous monitoring system within secondary containment.
2. The continuous monitor is connected to an audible and visual alarm system
and the pumping system.
3. The continuous monitor shuts down the pump and activates the alarm
system when a release is detected.
4. The pumping system shuts down automatically if the continuous monitor
fails or is disconnected.
The first test shall be completed before December 31, 1991, and subsequent tests completed
each calendar year thereafter.
2. All underground storage tanks shall be retrofitted with overspill containers which have a
minimum capacity of 5 gallons; be protected from galvanic corrosion, if made of metal; and
be equipped with a drain valve to allow the drainage of liquid back into the tank by
December 1998, or as specified by the Environmental Health Services Department.
3. All equipment installed for leak detection shall be operated and maintained in accordance
with manufacturer's instructions, including routine maintenance and service checks (at least
once per year) for operability or running condition.
4. An annual report shall be submitted to the Kern County Environmental Health Services
Department each year after monitoring has been initiated. The owner/operator shall use
the form provided within the Handbook UT-lO.
3
Facility:
-
e
PERMIT CHECKLIST
~1~*
GOLDEN STATE METALS, INC.
600 UNION AVENUE
BAKERSFIELD, CA
This checklist is provided to ensure that all necessary packet enclosures were received
and that the permittee has obtained all necessary equipment to implement monitoring
requirements described within the permit to operate.
Please complete this form and return to the Kern County Environmental Health
Services Department, in the self-addressed envelope provided, within 60 days of the permit
issue date.
CHECK:
YES NO
A. The packet received contained the following items:
1. A cover letter, a Permit to Operate the Underground
Hazardous Storage Facility, and a return envelope.
2. (if ordered) Handbook UT-lO, 12 recording,
reconciliation and trend analysis forms, and an action
chart (for standard inventory control monitoring).
3. (if ordered) Handbook UT-15, 12 recording forms,
along with an action chart (for modified inventory
control monitoring).
4. an order/request form for UT monitoring manuals - if
the manuals were not ordered when the monitoring
alternatives fact sheets were returned.
B. I have reviewed the information provided within the Permit
and find the owner's name and address, facility name and
address, operator's name and address, substance codes, and
number of tanks to be accurately listed. (If uno" is checked,
note appropriate corrections on the back side of this sheet.)
C. I have the following required equipment (as described on page
. 5 of UT-15, or page 6 of UT-IO).
1. Acceptable gauging instrument
2. "Striker Plate(s)" in tanks
3. Water-finding paste
e
e
Permit Checklist
Page 2
YES NO
D. I have read the information within the permit to operate
pertaining to the agreement between the owner and operator
and hereby state that the owner of this facility is the operator.
(If "no" is checked, attach a copy of agreement between the
owner and the operator.)
E. I have enclosed a copy of Calibration Charts for ª-Ü tanks
which will be monitored utilizing manual or electronic gauging
at this facility. (If the tanks are identical, one chart will
suffice; label chart(s) with corresponding tank numbers listed
on permit.)
F. Manual Gauging, utilizing Standard Inventory Control (UT-lO)
or Modified Inventory Control (UT-I5), was started at this
facility in accordance with procedures described within the
appropriate handbook.
Date Started
Signature of Person Completing Checklist:
Title:
Date:
/1---4"-q¡ . (Ò./:!, ,
Na1-/XJJL) DOJJ/e/(] caIne If), C¡he nQI77f?/ ()çF)
CJhs pen71!~b IS !nCOr'íe(l{ Tef-- ~,kY--91 &/-
vaDe ':f' IS I1Co:'J 0- vo.,c,CV?<t 10'/ 'He
do~kdf p/CU7 </0 ùf'£ ~/72 cfa~~- .oJ; ¿RJI!(
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HM8
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KERN COUNTY HEALTH DEPARTMENT
\}\~
¡,'BILLING DATE
. OS/20/RÇ
I'·;;; AMOUNT DUE
. 150,00
r 'MlQUNHNCLOSED
Iv\ailing Address:
1415 Truxtun Avenue
Bakersfield, CA 93301
2700 M Street, Bakersfield
(805) 861-3636
Office Address:
DETACH HERE--.
'\ )
r /
DANIELS. NATHAN I
P.O. BOX 67 ~ ~
BAKERSFIELD. CA 93302 .~
) ï I .
'--J I \
\
PLEASE RETURN THIS PORTION TO INSURE <:ORRECT PAYMENT IDENTIFICATlON_ __ _ _ _ _ _ _ __ _ _ _ _ _ C_ DET~~~ HER
CHARGES PAST DUE ARE SUBJECT TO PENALTY
I
I;':>
DUEDATE .
06/19/89
L
h¡)\MOlJNT
OS/20/89 PERMIT/INVOICE # 250011C-88
FISCAL YEAR 87/88 FEE FOR PERMIT TO OPERATE UNDERGROUND STOR GE FACILIT
WITH 1 TANK(S) LOCATED AT:
600 UNION AVENUE
BAKERSFIELD. CA
1 0 0'. 0 0
50% PENALTY FOR LATE PAYMENT OF ORIGINAL INVOICE
50.00
.. <ERN COUNTY HEALTH DEPARTMENT
SECTION 3807 PENAlTIES. If any fee required by this division is nOI paid prior to the
delinquency dOle, in addITion 10 such fefit, the applicant shaH pay 0 penalty equal 10 fifty
pe'cont 150~.~f t~e fee. The te,m 'd~l;nguenH dote' 'h<¡II <:>eo-" 'Q ,"¡ '9'1',oiPU"I'l"Q, Tr\TAl AMOU NT DUE
July 31, on:-;, h\(·,*.l Kn*'Ke}oóiN'~d^"*e)t ª'ì:o~H\Í N'l1\:~eÆ~1',d~'}I,ltt\ X ~
commencemen ê:t'llie éûslOoss or oá~v~.
150.00
-~- ---.--- -
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.-+---- -----
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Mailing Address:
1415 Truxtun Avenue
Bakersfield, CA 93301
2700 M Street, Bakersfield
BILLING D TE
OS/Z0/89
(805) 861-3636
Office Address:
AMOUNT DUE
100,00
DETACH HERE.._
PERMIT/INVOICE #250~11C~.~11C- 9
n1}Ø
PLEASE RETURN THIS PORTION TO I~SU CORRECT PAYMENT IDENTIFICATION
: AMOUNT ENCLOSED
I
CHARGES PAST DUE ARE SUBJECT TO PENALTY
CA
DUE DATE
06/19/89
L
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_ __ _ __ __ __ __ _ _ _ _ _ ___ r __ _ _. _ '
,ERVI I
ATE
SEND PAYMENT WITHIN 30 DAYS TO AVOID
DESCRIPTION
AMOUNT
OS/20/89 PERMIT/I~VOICE # 250011C-89
ANNUAL FEE FOR PERMIT TO OPERATE UNDERGROUND STORAGE FACILIT
WITH 1 TANK(S) LOCATED AT:
600 UNIO~ AVENUE
BAKERSFIELD. CA
. 100.0
i5AKERSFIELD, CALIFORNIA 93305
SECTION 3801 PENALTIES. If any tee reql.ured by 'nt$ division is not paid prior 10 the
delinquency dOle, in oddlhon 10 such fee, ,he applicant sholl pay 0 penalty equal to fifty
'!~r;~7: ~';X'~~~~~:X:~"~~"f~~~~;(~~~~~ Xl'OT Al AMOUNT DUE
commencement of rhe businen or activity.
100.0
I
/
---_.~ -.-
- - - -- --- - -- --- -
----- .--------
---. -----.-----------
2700 M Street
~ersfield,&California
Mailing Address:
1415 Truxtun Avenue
Bakersfield, California 93301
(805) 861-3636
. . :RN COUNTY HEALTH DEPARTMe...
"
ENVIRONMENTAL HEALTH DIVISION
HEALTH OFFICER
Leon M Hebertson, M.D.
DIRECTOR OF ENVIRONMENTAL HEALTH
Vernon S. Reichard
May 20, 1989
Mr. Nathan Janiels
P. O. Box 67
Bakersfield, California 93302
Dear Mr. Daniels:
This letter is an official notice of your non-compliance with
state and county laws relating to underground tanks.
Upon review of our records, it was discovered that the 1988
Permit to Operate fees for Golden State Metals, Inc., 600 Union
Avenue, Bakersfield, California were not paid. Enclosed is a copy
of 1988 s invoice pI us the 50% late penal ty required by county
ordinance. The second invoice is for this year IS Permit to
Operate fees. These invoices must be paid within 30 days to avoid
further penalties and/or legal action.
Be advised that these fees must be paid even if the tanks are
no longer in use. If the tanks are not in use, a permit for
permanent closure must be obtained from this off ice. Permanent
closure requires either removal or closure in place of your tanks
and assessment by soil sampling to determine whether there has been
environmental damage as a resul t of unauthorized releases of
hazardous substances from your tank site. The specific
requirements for these activities are in Handbook #UT-30, available
with your application. No closure activity can begin prior to the
issuance of ~ permit from this office.
If you have any questions or feel this assessment is in error"
or if you would like an application and our handbook on permanent
closure please call me at (805)861-3636. Your prompt attention to
this very important matter is appreciated.
Sincerely,
~è(
Jane Warren
Hazardous Materials
Hazardous Materials
¿J~
Inspector
Management Program
DISTRICT OFFICES
np'~nn . Lamont . Lake Isabella . Moiave . Ridaecrest . Shatter . Tatt
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. E'kP±R~S:,~: ".JutY,l/i989 ,.
,,' ;'.."\'.'....):;::':::'....:..:::..<.:' " , .
NUMBER"'OF ,'TÄNKS*='.l . ,
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UNDE~GROUND,.HAZAlmOUS;_:S,UB$',l'~éES
STORAG~ -:&'ACILI~Y' ,
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----'-'----'-~----:---'---'-- - - - - ---'-------:;-'-..;------:;---':;-'-.-'-'--"',..;-'-'-.'-,..:.. - - --: -:-
FACILITY:: , ' . I OWNER:,." '!';' :.:',
GOLDEN 'STATE METALS" IÑC ~ IDÀNIELS,:NATHAN:'"
600 UNION'AVENUE.· I. . P.O. BOX' 6'7; '~.d'.. '\' .
BAKERSFIELD, CA 'BAKERSFIELD,' ÓA,:::"::93302;",
--- ---'---- - --- ---- -- - -- - - ----------- - - ---'- -- --- - ~ -..:':' .l_;;.,._.:;.:;....;..;:.:.:;...::.._.. __ _ ' , ,
. '., '.,:.. ....:',./.:--'< "
TANK #
1
AGECIN'YRSl
UNK
SUBSTANCE CODE
MVF3
, .~.. .-, . . :: '- "
PRESSURIZED;:P'IPING?:: '
NO '. ','
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NOTE:
ALL INTERIM REQUIREMENTS ESTABLISHED BY' THE 'PERMr~TtNâ',"'"
AUTHORITY MUST BE MET DURING THE TERM OF ,'l'HIS "PE}{MI,T<'>~.",.,:.
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***
NON-'TRANSFERABLE
,,; .
DATE PERMIT MAILED:'
SEP 1 5 1986
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