HomeMy WebLinkAboutUST-C-1/21/91CONTRACT OPTIONS FOR LEAKING TANKS
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'KERN COUNTY HEALTH DEpAI~TI~ENT
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NA/GRO~WAT
iRES .. ER
;' RESOURCES, INC.
Working to Restorb NatUre BAKERSFIELD, CALIFORNIA 93307
General Engineering Contractor
Class A/Haz License No. 520768
¥.
,.:,
I " " SEQUOIA PAINT
, · _ _. 700 Baker Street
........... " Bakersfield, California
SITE ASSESSMENT REPORT
January 22, 1991
MAILING ADDRESS: P. O. BOX 9383, BAKERSFIELD, CA 93389 (805) 835-7700
FAX (805) 835-7717.
.RESOURCE MANAGEMENT AGENCY
Environmental Health Sen~ces Department
RANDALL g ABBO'iT STEVE M~C,u~,, R~S, DmECTOe
DIRECTOR ~ ~o~o~ co.~o~ ~
DAVID PRICE [] ~ J' RODD¥, ~CO
ASSISTANT DIRECTOR Planning & Development Senates Department
· ~ .... : .-:- ._"~ '.': .... . ....................... TED JAMES, AICP, DIRECTOR
ENVIRONMENTAL HEALTH SERVICES DEPARTMENT
January 29, 1991
Jim Elder
......... Sequoia Paints ............... "
700 Baker Street
Bakersfield, CA 93305
SUBJECT: Location : 700 Baker Street, Bakersfield, CA
Known As : Sequoia Paints
Permit # : 150075
Dear Mr. Elder:
This letter confirms the completion of site investigation and
remedial action at the above'site. With .the provision that the
.information provided to this agency was accurate and representative
of existing conditions, it is the position of this office that no
further action is required at this time.
Please be advised that this letter does not relieve you of any
liability under the California Health and Safety Code or.Water Code
for past, present, .or future operations at the site. Nor does it
relieve you of the responsibility to clean up existing, additional,
or previously unidentified conditions at the site which cause or
threaten to cause pollution or nuisance or otherwise pose a threat
to water quality or Public health.
'Additionally, be advised that changes in the present or ·proposed
use of the site may require further site characterization and
mitigation activity. It is the Property owner's responsibility to
notify this agency of any changes in report content, future
contamination findings, or site usage.
If you have any questions regarding this matter, please contact
Flora Dariing at (805) 861-3636, Extension 549.
........................................ ' .......... Chris Burger, RiE.H.S.
Hazardous Materials Specialist IV
Hazardous Materials Management Program
CB: cas
\150075. tit '
2700 "M" STREET, SUITE 300 BAKERSFIELD, CALIFORNIA 93301 (805) 861-3636
FAX: (805) 861-3429
RESNA/GROU WATER
RESOURCES, INC.
Working to Restore'Nature BAKERSFIELD, CALIFORNIA 93307
General Engineering Contractor
Class A/Haz License No. 520768
.~.
County of Kern
Department of Environmental
Health Services
Bakersfield, CA 93301
Re: SITE ASSESSMENT
Sequoia Paint
700 Baker Street
Bakersfield, California
Dear Ms. Flora Darling,
Enclosed please find the Site Assessment Report for the above referenced site for your
review and approval.
If you have any questions or require further infomation, please don't hesitate to call me at
our main office at (805) 835-7700.
Very truly yours,
Claus L. Engelhardt
Project Geologist
CLE:tab:macpvt
cc: Jim Elder, Sequoia Paint
MAILING ADDRESS: P. O. BOX 9383, BAKERSFIELD, CA 93389 (805) 835-7700
FAX (805) 835-7717
· SEQUOIA PAINT
700 Baker Street
t Bakersfield, California
SITE ASSESSMENT REPORT
January 22, 1991
TABLE OF CONTENTS
1.0 INTRODUCTION
! ~ 2.0 BACKGROUND
"~ ..... - ........... ~3.0 ' PROCEDURES"
~ ' 4.0 FINDINGS
I 4.1 Borings
! 4.2 Geology and Hydrogeology
5.0 DISCUSSION
5.1 Extent of Gasoline Contamination in the Soil
5.2 Groundwater Risk
5.3 Risks to the Surface Environment
6.0 RECOMMENDATIONS
6.1 No Action
6.2 Vapor Extraction
6.3 Excavation
7.0 REFERENCES
8.0 LIMITATIONS
ILLUSTRATIONS
Plate 1 Location Map
Plate 2 Plot Plan
Plate 3-4 Cross-Sections
Plate 5-6 Logs of Borings
APPENDICES
Appendix A Chain of Custody and Laboratory Analysis
Appendix B . LUFT Worksheets
.......... Appendix C - Risk Analysis .............. '"'
SEQUOIA PAINT
1.0 INTRODUCTION
This report presents the results of a Leaking Underground Fuel' Tarik Site Assessment conducted by
i Groundwater Resources Inc. (GRI), a RESNA company, at Sequoia Paint, a retail and wholesale paint
....... business operating at 700 Baker Street in Bakersfield, California (Plate 1). Risks'to groundwater and
the surface environment posed by the presence of gasoline in the soil were found to be very low. No
~t' ~' further assessment or remediation is recommended.
2.0 BACKGROUND
On January 25, 1990 GRI removed tWo underground' storage tanks, a 4000 gallon gasoline tank and
' .... :~' .... a 200 gallon~waste oil tank, from the Sequoia Paint property at 700 Baker S~eiin Bakersfield. The
tanks were reportedly installed in 1982 and remained in service until 1987 at the former WallYTucker
automobile dealership.
Soil was sampled at a depth of two and six feet beneath each tank, beneath the gasoline dispenser and
under the product line halfway between the dispenser and the tank (see Plot Plan, Plate 2). The
dispenser was located in a closet at the west side of the main building on the site which necessitated
using a hand auger to obtain samples beneath the concrete floor of the structure.
All samples were analyzed by BC Laboratories in Bakersfield. Those associated with the gasoline
system were tested for BTXE and TPH (gasoline). No hydrocarbons were detected except in the
sample from six feet beneath the dispenser which contained 32.55 ppm total xylenes and 935 ppm TPH
(gasoline). The waste oil samples were analyzed for TPH (oil and grease), total lead and total
halogenated hydrocarbons (TOX). No halogenated hydrocarbons and.background levels of total lead
and TPH (oil and grease) were reported.
A site assessment of the contamination indicated by the six foot dispenser sample was required by the
Kern County Department of Environmental Health Services. Two attempts were made to determine
the vertical extent of the gasoline plume under the dispenser using a hand auger. On March 9, 1990
GRI obtained samples at a depth of 8, 11 and 14 feet, all of which contained significant leVels of
gasoline constituents. On July 25th Duane R. Smith and Associates augered a hole to 25 feet which
was later deepened to 35 feet and collected samples at 20, 25, 30 and 35 feet. Low to moderate
concentrations of gasoline constituents were'present in these samples. The results for all sampling
efforts at the dispenser are listed below in Table 1.
TABLE 1
ANALYTICAL RESULTS FOR DISPENSER SAMPLES (in ppm)
Depth Benzene Toluene Ethylbenzene Total Xylencs TPH (gasoline)
6 FT ND ND ND 32.55 935.
................ ~-'FT ..... ND .... 2.2 .......... 4.4 311.8 .... -4100
11 FI' ND 1.0 1.4 169 1700
JANUARY 22, 1991/Page 1 GROUNDWATER.RESOURCES INC.
SEQUOIA PAINT
TABLE 1 (continued)
ANALYTICAL RESULTS FOR DISPENSER SAMPLES (in ppm)
._ ........................ . Depth.. .... Benzene ..... Toluene ..:.;:~-Ethylben-zene-.-T°tal Xylenes TPH (gasoline_):~:.. '...~
14 FT ND 1.4 I~7 ........... Y63 ............... 1900
20 FT ND ND 0.10 1.66 15
'- 25 FI' ND 0.26 ND 14.8 250
30 FI' ' 0.10 2.4 4.4 76 520
~ 35 Fl' ND 0.68 2.0 28.8 310
.......... ~ ..... . ..... The contamination extended.beyond-the reaeh..of a hand auger and a truck mounted auger drilling rig ....
I was required to complete the characterization of.this site.
3.0 PROCEDURES
A hollow stem auger drilling rig, owned by RESNA Industries, was used to drill two borings, both'
directed at a 10 degree angle beneath the building. Cores Were retrieved at five foot intervals with
a California split-spoon sampler. A representative sample of each core was sealed in a brass sleeve
with duct-taped teflon-lined plastic caps and chilled on ice. The other sections of each core were
described lithologically, checked for pe_~oleum odors and screened with a photoionization detector
(PID) for volatile hydrocarbons. Upon completion of drilling operations, the sealed cores were
transported to SMC Laboratory in Bakersfield under a chain of custody for chemical analysis. Selected
samples were analyzed for BTXE and TPH (gasoline). Cores retrieved at depths and locations
previously sampled with hand augers were not chemically analyzed to avoid duplicating earlier results.
Augers were decontaminated by high pressUre steam cleaning between borings to prevent cross-
contamination. Both borings were abandoned by filling with a neat cement slurry emplaced by the
tremie method.
4.0 FINDINGS
4.1 Borings
Boring S-1 (Plate 5) was placed three feet from the clOset which formerly housed
the fuel dispenser. The hole was drilled at a ten degree angle beneath that room
under the the building to a depth of 60 feet (see the Plot Plan, Plate 2 and the Cross
Section, Plate 4).
The boring essentially twinned, to a depth of 35 feet, the hand-augered holes
completed earlier; Moderate to strong gasoline odors and elevated PID readings
......................................... '- (112-460 units) were-recorded during this interval.. No..samples~ were submitted to ..........
the laboratory for analysis.. The results of the previous sampling efforts at these
JANUARY 22, 1991/Page 2 GROUNDWATER RESOURCES INC.
SEQUOIA PAINT
depths are listed in Table 1. Note the very low BTXE concentrations and the virtual
absence of benzene.
' 'Gasoline contamination at 40 feet was found to be comparable to levels enc0un_-
- .... ~ :'::- ..... ~"~"':'::[~red"at ShallOwer horizons. Strong 'odors 'and a 500 unit PID response were
recorded. The 3500 ppm TPH value reported by the laboratory was within the
expected range, however, BTXE concentrations were also high, the only sample
in
which these constituents .were .detected at elevated levels.
·
Below 40 feet field indications of contamination decreased. No odors were noted
...... .~...~ ...... ~' :~_.:~.below 50 feet and PID readings declined although they were still above background
levels when drilling was'terminated at 60 feet. The lab reported minute quantities
of gasoline constituents at 45 and 55 feet. Hydrocarbons were absent at 50 feet and
at 60 feet only xylenes at minimum detection levels (.005 to .007 ppm) were
present. Laboratory results for the samples from Boring S-1 are listed below:
~ TABLE 2
ANALYTICAL RESULTS FOR BORING S-1 (in ppm)
Depth Benzene Toluene Ethylbenzene Total Xylenes TPH (gasoline)
40 Fl' 20 48 100 430 3500
45 FT .012 .058 .023 .215 1.8
50 FT ND ND ND ND ND
55 FT ND .018 .011 .095 1.2
60 Er ND ND ND .012 ND
Boring S-2 (Plate 6) was drilled at a 10 degree angle under the showroom building
at a location 12 feet north of Boring S-1. The hole was advanced to 45 feet,
penetrating the equivalent interval in which contamination was found in S-1. A
slight petroleum odor was noted at 25 feet, but no hydrocarbons were 'detected in
the core from this, depth or in samples from 20, 35 and 45 feet which were also
analyzed (Appendix A).
4.2 Geology and Hydrogeology
The Sequoia Paint property lies in a residential and business district in East
Bakersfield within two and one-half miles of the Kern River to the north. In the
shallow subsurface the area is underlain by unconsolidated ailuviai sand-rich
sediments deposited by the Kern River during recent geologic time1. The borings
encountered eight to nine feet of silts and silty sands at the surface, underlain by a
i . sequence of predominantly coarse sands with occasional gravelly.intervals which
i persisted to about 35 feet where a transition to mostly fine grained, silty and clayey
........ :., ...... ......... sandsoccurred._~This lithology was still present at 60 feet, the lowest level, reached ....
(See Boring Logs and Cross Sections Plates 3-6). The change from highly porous
JANUARY' 22, 1991/Page 3 GROUNDWATER RESOURCES INC.
SEQUOIA PAINT
sands to less permeable material corresponds with the base of significant contami-
nation indicating that stratigraphy may have played a role in limiting downward
migration of contaminants.
· -.. <'~:'::"According:to' maps'published by the Kern .County-Water 'Agency2' 'depth 'to .... ::~'
groundwater of the regional unconfined aquifer is approximately 160 feet. Shallow
perched groundwater of limited areal extent also occurs in the vicinity where clay
layers interrupt the downward movement of water. The most recent map for the
Summer of 1989 shows the northern lobe of regional perched water to be situated
south of Bakersfield. No groundwater was encountered in this assessment
DISCUSSION
As a result of the various assessment efforts at the Sequoia Paint site, the vertical and lateral extent.
of soil contamination has been delineated and threats to the surface environment as well as
groundwater resources can be evaluated. The vertical extent of the plume is depicted on the Cross
Sections (Plate 3 and 4) and the maximum lateral dimension of the plume is shown on the Plot Plan
(Plate 2). The interpretations assume the plume to be essentially symmetrical and centered on the
dispenser location.
5.i Extent of Gasoline Contamination in the Soil
Boring S-1 and the hand-augered holes were centered as closely as possible to the
dispenser point of origin of the gasoline leak in order to determine the vertical
extent of the gasoline plume. Moderate levels of gasoline contamination are present
between 6 and 40 feet. TPH (gasoline) concentrations range between 935 and 4100
ppm from 6 and 14 feet and 3500 ppm is present at 40 feet; at other horizons, values
of several hundred Ppm are the norm. BTXE concentrations are very low or absent
except at the 40 foot inte~wal. The base of the plume occurs just below 40 feet. Only.
trace amounts of gasoline constituents are detectable below that depth.
Boring S-2 was drilled 12 feet from S-1 to gain information on the lateral spread
of the gasoline plume with depth. Minimal horizontal migration was anticipated
because of the porous nature of sediments which characterize the area. No gasoline
Constituents were detected by the lab in the samples tested. The slight odor detected
at 25 feet indicates that this boring was 'at the outer margins of the plume and that
its maximum lateral extent is less than 12 feet.
5.2 Groundwater Risk
Groundwater occurs at approximately 160 feet in the vicinity of the site. It is not
considered to be at risk. The source of the. gasoline contamination has been
removed. The base of the plume at 40 feet lies 120 feet above the water table and
................. as. discuss~d-~i-e~iously, theclayey int~iS/iil'~Which .develOPs 'at 55 feet' like]y''
impeded downward movement of the hydrocarbons.
JANUARY 22, 1991/Page 4 GROUNDWATER RESOURCES INC.
SEQUOIA PAINT
The General Risk Appraisal Method as presented in the Leaking Underground Fuel
Tank Manual (LUFT)3 was used to evaluate threats to the groundwater resource.
~.-'. · This apProach uses informatiOn on a site's environment and environmental fate and
. -.:_-:, - ....... ::-:-:.'-'-':- :::::-'--:--::: ..:chemistry data for the more. volatile and dangerous-.BTXE components of gasoline.
' to evaluate risks. The only environmental aspect of this site which could inc~ase
t '-' risks is the porous nature of much ~f the underlying
, worksheets used in the LUFT manual to analyze' data on the site's contamination
~'" with depth and rainfall are presented in Appendix B. No groundwater threat is
'' '~ indicated for benzene and toluene. Individual field samples did exceed 40 ppm for
ethylbenzene and total xylenes precluding use of the worksheets for these sub-
'' 5.3 ks to the Surface Environment · -.
- Risks to people and the surface environment from vapors migrating upward from ·
I the contaminated soil mass are also considered to be low. The assessment shows the
affected area to be half under the Sequoia Paint building and half under the
,~. .adjoining driveway. Presently a strip of soil is exposed along the side of the
i building where the piping connecting the dispenser and fuel tank was removed.
When this section is paved the entire outside portion of the contaminated area will
' be isolated from the surface. The concrete floor of the building will effectively
prevent most vapors from entering the building. The~hole in th_._e floor through
which the i in ched the dispenser must be sealed.
Another factor which further reduces the risks associated with this site is the very
low concentrations of BTXE, the constituents of fuel which engender the most
concern, particularly benzene,' a proven carcinOgen. These components were either
not detected or they were present at very low concentrations above a depth of 40
feet. The._e~4.0,.foot Lam~ple was the onl~ted concentrations of these
substances w'a~-f~und (see Table 1 and 2). ~ ~'~
An effort was made to evaluate the health risks due to exposure to benzene
volatilizing from the soil and entering the Sequoia Paint building. Outside exposure
to vapors was considered to be virtually nil. BenZene was used because it is the only
identified carcinogen present. The highest concentration, 20 ppm, occurs at 40 feet
and this value and depth v0ere used in the calculations. Laboratory determined
values for soil properties at the site were not available. Assuming a sediment matrix
consisting primarily of unconsolidated medium to coarse sand with a low moisture
content, the following parameters were estimated:
Porosity .35
Bulk Density 2.0
........................................ MiSisture 'Content ....... ~ 15 ......................
[ANUARY 22, 1991/Page 5 GROUNDWATER RESOURCES INC.
SEQUOIA PAINT
· The approach used for the risk assessment is based in part on the methods and logic
presented in The California Site Mitigation Decision Tree Manual4, but was pri-
marily modeled after a report submitted to thc Orange County Health Care Agency
..... by ChemRisk entitled Screening Level .Risk Assessment For Benzene, Toluene,
Xylene, And Ethylbenzene In Indoor Air At The Former Shell Station Site At Costa
Mesa5. This document was made available to GRI by the Agency as an example of
. a state of the art health assessment. The steps followed and.the conclusions of this
study are outlined below. A more complete discussion and the calculations are
included in Appendix C.
The first step in the risk evaluation process is the calculation of the steady state flux
of benzene through the soil matrix assuming a non-diminishing source at some
distance below the ground level. This determination requires the knowledge of
benzene's coefficients of diffusion in air and through the soil as well as the vapor
phase concentration of the substance at the source.
Knowing the vapor phase flux through the soil, the volume of air within the
building, a ventilation rate and assuming a leakage rate through the structure's
foundation, a benzene vapor concentration within the building can be predicted.
Then, taking a._~..orse~ase ~cenari~o of a person working their entire 45 year
occupational lifetime at the business, a lifetime average daily dose (LADD)
received by inhalation can be derived.'
Values of indoor vapor concentrations and LADDs can then be compared to
regulatory guidelines to evaluate degree of exposure and risks. In this instance, the
indoor concentration of benzene was calculated to be 2~0x10-7 mg/m~3. The DHS
, Applied Action Level for benzene in ambient air is ~.2x~10~m. 3. The air
concentration for lifetime cancer risk due to benzene exp6~ure 6.6x10-4 mg/m3 can
also be used (DHS E-05 excess lifetime cancer risk level for benzene). Based on
a individual who worked at the site for 45 years, a LADD of 1.25x10-8mg/kg-day
was calculated. This result can be compared to 3.0x10'4 mg/kg-day which is
considered to result in a 1 and 100,000 excess cancer risk under CDHS Proposition
65 guidelines. In all cases, calculated values are well below established guidelines.
The potential for carcinogenic health effects can also be evaluated by multiplying
the lifetime benzene exposure (inhaled volume times concentration) with an
"adjusted potency factor' (USEPA)6 to derive a carcinogenic risk associated with
a specific exposure to benzene. In general, regulatory agencies have found that a
risk in excess of 1 in 1 million is acceptable. In some instances risks of 1 in 100,000
are used in setting environment standards. At Sequoia Paint a risk of 6.0x10'10 was
derived, ~well in-excess' of the 1 in 1;000,000 criteria. -
..
JANUARY 22, 1991/Page 6 GROUNDWATER RESOURCES INC.
SEQUOIA PAINT
In conclusion, based on this risk assessment exercise, no significant health hazards
exist at the Sequoia Paint site.
"6.0 --' REcoMMEND.~Ti0NS
Based on the information obtained and analyzed during the site assessment process, risks to
groundwater resources and the public health are considered to be very low. ,btoX~er as~essment~or
.~ ~_e_ site i_~s deemed neees__~.L~ and site closure is recommended. In addition to the "no
action" alternative, the excavation and vapor e~ re~nedial action option~ are discussed below.
6.1 No Action
Under the "no action" alternative, no further assessment or remediafion to mitigate
the contamination characterized in this study will be required. The.gasoline
constituents will be allowed to remain in the soil to slowly dissipate and degrade
with~ time. This course of action is considered justified by the demonstrated very
low risks'to the groundwater resource and to the people employed in the building
partially overlying the site. Alternative approaches are either not feasible or are too
costly.
To insure isolation of the contaminated mass from the surface, the driveway will
have to be completely paved and the piping passageway through the building
flooring must be sealed.
6.2 VaPor Extraction
Gasoline contaminated soils have been successfully cleansed using vapor extraction
technology. In this approach vadose weils screened through the contaminated soil
interval are installed in the plume. They are attached at the .surface to a blower or
air pump. A vacuum is created and soil gas is drawn to the well bore carrying along
gasoline volatiles which are stripped from the soil. At thesurface hydrocarbons are
thermally destroyed in an internal combustion engine, catalytic oxidizer or they are
adsorbed in carbon filters. This method should work satisfactorily at this site
because of the porous nature of the affected soils. Because of its limited, siz. e, one
well centered in the gasoline plume may be sufficient to effect complete cleanup
in a matter of several months.
The construction of one vadose well will cost $3000. A' tyPical treatment system
using an engine and catalytic converter to bum the liberated volafiles can be leased
for $8000 per month including fuel and maintenance costs. Installation and startup
fees add $2000. Carbon filters are used where concentration of the hydrocarbons
are low due to high carbon replacement costs. Installation of a system using four
................ ~ ...... carbon canisters will cost about$25,000.00. Addition costs will be incurred for~
studies required to design an appropriate system.
JANUARY 22, 1991/Page 7 GROUNDWATER RESOURCES INC.
SEQUOIA PAINT
The vapor extraction alternative is not recommended in this instance due to its high
costs relative to the low environmental risks posed by this situation.
6.3 Excavation
..... : -: ':'-' Excax;ati°n-~f~0~thmifiated soils is ii' 9iiible option When the material ig'
to earth moving equipment 'and the plume does not extend much beyond 20 feet in
depth. Clearly, the at Sequoia precludes consideration of this.
situation
Paint
method. The contamination occurs in pan under the building where the retail
business of the farm is conducted. Excavation would undermine and threaten the
integrity of the building without the construction of supporting structures. Business
.~.~ :. ..... ..would be disrupted. . The deeper potions 9f_~e.plume occur beyond .the reach of~ -,-:.,.-. ......
excavators and complete removal of affected material is not Possible.
7.0 REFERENCES
1. Dale, R.H., French, James J. and Gordon, G.V., June 20, 1966. Ground-water
Geology and Hydrology of the Kern River Alluvial-Fan Area, California: U.S.G.S.'
Open-File Report 66-21
2.' Pyle, Smart T., Clark, Thomas N. and Ribble, George E., May 1990. Kern County
Water Agency Water Supply Report 1989
3. State of California Leaking Underground Fuel Task Fome, October 1989. Leaking
Underground Fuel Tank Manual: Guidelines For Site Assessment, Cleanup, And
· Underground Storage Tank Closure
4. State of California Department of Health Services Toxic Substances Control
Division, Alternative Technology and Policy Development Section, May 19ff.6.
The California Site Mitigation Decision Tree Manual.
(/5.) ChemRisk, A McLaren Company, September 19, 1989.; Sc~:eening Level Risk
Assessment for Benzene, Toluene, Xylene, and Ethylbenzene in Indoor Air at the
Former Shell Gasoline Station Site at Costa Mesa.
6. U.S. Environmental Protection Agency, 1988. Update of the Risk CharacteriZation
Tables in SPHEM (Toxicity Data for Potential Carcinogenic Effects and Non-
Carcinogenic Effects).
7. Thibodeaux, L.J. and Hwang, S.T., 1982. Landfarming of Petroleum Wastes -
Modeling the Air Emission Problem: Environ. Prog. 1:42-46'.
8. Millington, N.J. and Quirk, J.M.; 1961. Permeability of?Porous Solids: Trans.
Faraday Soc. 57: 1200-1207.
9.Fuller, E.N., Schettler, P.D., and Giddings, .J.C., 1966. A New Method for
Prediction of Binary Gas Phase Diffusion Coefficients: Ind. Eng. Chem 58: 19-27.
10. Grimsrud, D.T., Sonderegger and Sherman, R.C., 1983. A Framework of a
Construction Quality Survey for Air Leakage in Residential Buildings: Proceed-
....................................... ings of Thermal Performance of External Env..elppes .0fBui!dings. Pages 422-452 ............
published by ASHRAE.
JANUARY 22, 1991/Page 8 GROUNDWATER RESOURCES INC.
SEQUOIA PAINT
11. Fisk, W.J., Spencer, R.K., Grimsrud, D.T., Offerman, F.J., Pedersen, B, and Sextro,
R., 1987. 'Indoor Air Quality Control Techniques, Radon, Formaldehyde, Combus-
tion Products: .Pollution Tech. Review No. 44. Noyes Data Corp.
This report was prepared for the exclusive use of. Sequoia Paint as it relates to the property described.
The discussion and conclusions presented in this report are based on:
- The test borings performed at this site.
_.,.~.,~ ._.,~_..The obse~ations of.field personnel ............... ,... ......... · ............ _ ...............
=Our understanding of the regulations of Kern County and the California Regional
Water Quality Control Board,
Possible variations in the soil or g~ndwater conditions which may exist beyond the points explored
in this investigation might effect the validity of this report unless those variations or conditions come
to our attention and' are reviewed and assimilated into the conclusions and recommendations of this
report. Also, changes in the hydrologic conditions found could occur with time due to variations in
rainfall, temperature, regional water usage, or other factors, any of which could effect this report.
The services performed by GRI have been conducted in a manner consistent with the levels of care
and skill ordinarily exercised, by professionals currently practicing under similar conditions in
California. The absence of contamination on or beneath the l~roperty cannot be' guaranteed by this
report. GRI is not responsible for any contamination or hazardous material found on the property. No
other warranty expressed or implied, is made.
Respectfully submitted,
GROUNDWATER RESOURCES INC.
Claus L. Engelhardt . Rex J. Young, R.G. #720 ~
Project Geologist Principal Geologist ~,~ ~,~gED
CLE:tab:macpvt ' ~ ~"~
JA~ARY 22, 199 l~age 9, GROU~WA~R ~U~CES ~C.
L
~,: ' * · FOUR'
~.. ~,,. ·
i ~ · QOW
I"
II
HospHa
~ SEQUOIA PAINT PLATE
groundwater resources, inc. 700 BAKER SREEET
BAKERSFIELD, CALIFORNIA 1
envioronmental/geotechnical services
P.OJECT.UMBE.: ~500-3 LOCATION.MAP '
200 GALLON 4000 GALLON
WASTE OIL TANK "" FANK
(removed) "
POLES (removed)
GATE ........ FENCI
~'-~"~ .... PRODUCT LINE~. I UTILITY LINES
ASPHALT DRIVE
t
I
... CLOSET
MAXIMUM
.' METAL LATERAL EXTENT
OF PLUME
LEGEND
X PRELIMINARY SAMPLE
LOCATION
· HANDAUGE ~! :
LOCATIONI~1 SCALE
O----~ ANGLE BORING I I INCH = 20 FEET
LOCATIONI I
..,mm... LINE OFSECTION
EAST 19TH STREET
~ ~ ~, SEQUOIA PAINT PLATE
groundwater resources, inc.. 700 BAKER STREET
........... , ~ ....... BAKERSFIELD, CALIFORNIA 2
: environmental/geotechnical services PLOT PLAN
DISPENSEI: SEQUOIA PAINT
CLOSET SHOWROOM
HAND AUGERED
15
. 20
4O
45
50 20 Benzene - ppm
3500 TPH (gasoline) - ppm
~ Hand augered samples-
55 '' lab results shown in
Contours of Equal
60 SCALE TPH Concentration
..... > 4000 ppm
VERTICAL AND HORIZONTAL ~ > 2000 ppm
ONE INCH = 10 FEET -~ ................ >1000 ppm
I I -- 0 ppm
~ SEQUOIA PAINT PLATE.
groundwater resources, inc. 700 BAKER STREET
BAKERSFIELD, CALIFORNIA
environmental/geotechniCal services
N-S
CROSS
Project Number: 1500-3
SEQUOIA PAINT
I = SHOWROOM
HAND AUGERED
'= 5
_ 10
. 3O
· 50 20 Benzene-pprn
3500 TPH (gasoline) - ppm
~' Hand augered samples-
. 55 ' ' lab results shown In italic.,
Contours of Equal
.. 60 TPH Concentration
SCALE > 4000 ppm
VERTICAL AND HORIZONTAL ,,,..-,--- > 2000 ppm
ONE INCH = 10 FEET. · ................. >1000 ppm
~ 0 ppm
~/~ ~' SEQUOIA PAINT .PLATE
groundwater resources, inc. 700 BAKER STREET
BAKERSFIELD, CALIFORNIA
envir°nmental/geotechnical services
Project Number: 1500-3 " E-W CROSS SECTION
ANALYSES SAMPLE
°
Lab" Field
WELL ud
ABANDONMENT Benzene Hnu
_: SOIL DESCRIPTION
TPH P.I.D. ~ ~ ~ z
ppm ppm.
% ~ ~ ~ ~ No Sample
--
,~,~,~ -10 -- NO Sample ..
,,,,,, _ 320 10 _ _~ S-1-15 ?????;~?;~ ........ SP SAND- ~e-w ~e, qua~ose, loose, yell-bm,
',',', -- i5 -- -- :~:~:~:~:~:~:~:~: damp, mod odor
.~,~,~ -- -- _ ::::::::::::::::::::::
,,,,,, -- 112 23 -~0 --~ S-1-20.:.:.:.:.:.:.:.::::??:::???:: ........ SP SAND- ~e-~ ~e, o~ ~bbles to 1/4 in,
.-,,,,, _ ~ _ _ ??:~?:?:~ qua~ose, orange feld, ~ bm, damp, si to mod 0do
~0- 28 -25 -- ~ S-1-25 ???~. SP SAND- fn~e, prod fn grained, loose, E brn,
'??;~ Neat ~0 38 -- -- ?~?~?~ moist, strong odor
18
I
I S-1-30 SP SANg- W ~e with Inte~als of G~VEL corn
~ '-- --m ~ ~ ~bbles to 1/2 in, qua~zose, igneous, loose,
.',',¥ -- ~ -- -- ?::??::::::?:: damp, stong to mod odor
_ _ S-1-35 ::~:?:~?:~ SM SAND- fn-~e gr, o~ pebbles to 1/4 in, slay,
',',','. _ ,35 -- -- ~ mod clayey, cohesive, yell-brn, moist, strong odor
,,,,., -- -- _ ::::::::::::::::::::::
.,,,,,,. _ 2o ~o. ~ ~ -- S-l~O ~ SP SANe- ~d-w ~e, o~ ~bbles, loose, damp,
.,;,;,; - 3500 ~o ~ _ _m SM st~ odor, grades to SANO- ~gr to sil~, yell-bm,
,,,,,,. -- 60 -- -- damp, st~ odor
.,~,~,~ .012 ~0- I S-145 SM 8g~D- fn-m~d, ~igy, yoll-~m, damp, mod odor at
~,?~, -- 1.8 '~ -- -- center of corn, slight odor at base
[~,~,~, of core I ~0
SURFACE ELEVATION: 410 FEET LOGGED BY: CLE
DATE DRILLED: 12-11-90 * DIAMETER OF BORING: 8 INCH
TOTAL DEPTH: 60 FEET WATER ENCOUNTERED AT: NONE
GROUNDWATER RESOURCES, INC. BORING LOCATION: SEQUOIA PAINT PLATE
(805)835-7700 700 BAKER STREET, BAKERSFIELD CALIFORNIA ~
env_lm_.nmen_t_al_/geote._=c~h_n.~iF_.a.!.,S~.!c_e_~ ............ ~o DEGREE ANGLE BORING UNDER DISPENSER CLOSET
PROJECT NUMBER: 1500-3 LOG OF BORING S,1 page.1 of 2
ANALYSES SAMPLE
'~ Lab" Field ~ --- -~ ~
WELL oo
ABANDONMENT Benzene Hnu ~ X mm ~ '~ SOIL DESCRIPTION
· TPH P.I.D. ~ ~ :~
z '~ ~
ppm ppm ca r~ - ~
· ..... _ :. _-;c~: '/"% , ...... -- - ND 25- .. 30 --. ~~· S-1-50 ..-- ~!i SM SAND- fn-med gr, vy silty, faidy loose, yell-bmi
"~'% ........ -; ' ND- 102 i'00~ rusty, pos SI odor-no odor,-grades to SAND- vy fn
,,,', -- 1013 gr, silty, yell-bm, damp, "sour' odor
',',',Cement ND 40- '50 --$· S-1-55 SM SAND-.vy fn gr, silty, yell-bm, si moist, no odor
'"'"
· .,,,,,, _ ND 7-22 40- 8-1-60 SM SAND- vy fn gr, silty, si claye, yel-bm, damp,
~ ~ ~ ~ TVD 59.1 FT' ..'
SURFACE ELEVATION: 410 FEET LOGGED BY: CLE
DATE DRILLED: 12-11-90 DIAMETER OF BORING: 8 INCH
TOTAL DEPTH: 60 FEET WATER ENCOUNTERED AT: NONE
GROUNDWATER RESOURCES, INC. BORING LOCATION: SEQUOIA PAINT PLATE
(805)835-7700 700 BAKER STREET, BAKERSFIELD CALIFORNIA
enYJron, mental/geotechnical services 1_0 DEGREE ANGLE BORING UNDER DISPENSER CLOSE'[
PROJECT NUMBER= 1500-3 LOG OF BORING S-1 page2of2
ANALYSES SAMPLE
WELL ~ uJ~ '~.~
ABANDONMENT Benzene Hnu ~ ~ I'~ ml::l::
~ SOIL DESCRIPTION
z o..
ppm ppm m ~ ~
',',', 2.0- 6 ~ ~ S-2-5 SM SAND- prod fn gr, W sil~, ~m ~e gr, poorly
,,,,,, _ 3.6 10 ~ -- so~d, damp, no odor, 5 In m~ no sample
,',','i ~ 2.4 10, ~ S-2-10 SP SAND- fn~e gr; sil~, poody so~, yell-bm, si
........ ,~,-,,' ... ..... - ............... · .... 15 .... - ..... . ...... . _~ moist, no odor, grad~.to SAN~
,,; -- 20 -- ~ ~ sil~, loose, damp, no odor
,',','. 0.8 20 ~15 --~ . S-2-15 SP SAND- ~d- W ~e gr, ~bbly, ~ ~bbles to
,,,,,, ~ ~ _ _ 1/2 in, loose, E bm, damp, no ~or
ND ~.o- ~o s-=-2o ~?~ SP SAND- ~a- ~ ~ gr, ~oos~,, b=, d=~p, no odo~
';';';""" ~ntNeat ND 1.2- 25 -25- ~ S-2-25 ~ SM SAND- W fn- fn gr, siEy, E bm, d~p, no odor,
,,-,,,' -- ND 9.6 ~ ~ ~ ~? ~ grades to SAND- fn-~d gr. loose, E bm, damp, si
,,,,,, _ 1.8 30 _ _ S-2-30 SP SAND- me-~ me gr, ~ gray-bm, loose, damp, no
,',',~ ~ ~??~?~:~ odor to W si odor In one po~lon of corn
~ -- 70 ~ ~ %::::::?:?::::
~ ~.]:~:~:~:~:~:?:?:
~/~l ~';'"'~'.'~'
,-,,,, _ ND 1.0 15~5 -- ~ S-2-35 ~::~::~ SM SAND- siRy, mod clayey, corn reed- ~e gr, yell-
,',',' -- ND ~ -- -- brn. moist, no odor
,;,;,; _ ~.o* _~_-~ s-=.o ~ ?~ s. s..o- m~U-W ~ g~,,oo.~, ~a~.,.o oUo~,
............ ~:~ ~ grades to SAND- fn gr, sil~, si clayey, cohesive,
_- _--_
,,,,,,~'~'~'_ ND 1.6 ~ ~_ _-- ~ S-2~5 SM SAND- fn-med gr, W siEy, si clayey, bm, moist, no
-- .ND 100-- -- odor
-- -- -- TO 45 ~
50 ~D ~.3 ~
SURFACE ELEVATION: 410 FEET LOGGED BY: CLE
DATE DRILLED: 12-11-90 DIAMETER OF BORING: 8 INCH
TOTAL DEPTH: 45 FEET WATER ENCOUNTERED AT: NONE
GROUNDWATER RESOURCES, INC. BORING LOCATION: SEQUOIA PAINT PLATE
(805)835-7700 700 BAKER STREET, BAKERSFIELD, CALIFORNIA
10 DEGREE ANGLE BORING 12 FEET NORTH OF S-1 ~'t
environmental/geotechnical
services
PROJEC~TNUMBER: 1500-3 'LOG OF BORING S-2 page 1 of 1
APPENDIX A
Chain of Custody and Laboratory Analyses
GROUNDWATER RESOURCES INC, · ,~. P.O Box 9383 '
~ Bakersfield, California
' Telephone: (805) 835-7700
A RESNA Company CHAIN OF CUSTODY RECORD __ Tole-Fax: (805)835-7717
LAB DESTINATION: PROJECT NUMBER:
SAMPLER(S): (Signature) ~-- '
~ ; S/~tPLE O SAMPLE COR'~AINER
,
NUMBER ~ NUMBER DATE TIME SAMPLE LOCATION O REQUESTED' " 'I'~PE 'D'PE
.
SPECI~ INDUCTIONS:
~I~ES~PLE H~RDS: · ~ ."
.;
1. ~i~h~ by: DatUm: R~ by: Da~me:
Laboratory Analytical Chemistry
Client Name: Groundwater Resources, Inc.
Address : 1500 South Union Ave.
Bakersfield, CA 93307
:-.Attention.-: Mr. Claus~--Engelhardt
~Date samples received : 12-12-90
Date analysis completed: 12-14-90
Date of report : 12-14-90
Project Name: Kern County
....................... Pro3ect ~ :~-1500-5 ·
P.O. % ': 5318-G
RESULTS OF ANALYSIS:
~4510 ID:'S-1-40 ugm/gm MDL,ugm/gm
Benzene 20. 0.005
Toluene 48. 0.005
Ethylbenzene 100. 0.005
p-Xylene 250. 0.005
m-Xylene 180. 0.005
o-Xylene ND 0.005
Isopropylbenzene 1.6 0.005
TPH (Gasoline) 3500 1.0
Method of Analysis for BTX/TPH (Gasoline): 3810/8020 (FID)
MDL = Minimum Detection Level
TPH = Total Petroleum Hydrocarbons
ugm/gm = micrograms per gram (ppm)
ND = None Detected
........................ Stan Comer .... . ...........................................
Analytical Chemist
3155 ~gasus Drive · Bakersfiel~ CA 93308 · (805) 393-3597
BO. Box 80835 ° . ~akersfield, CA 93380 · FAX (805) 393-3623
RESULTS OF ANALYSIS:
~4511 ID: S-1-45 ugm/gm MDL,ugm/gm
Benzene .012 0.005
Toluene .058 0.005
:~ ..-Ethylbenzene .................. ........... .023 ....... . .... 0.005
p-Xylene .037 0.005
m-Xylene .093 0.005
o-Xylene .085 0.005
Isopropylbenzene .016 0.005
'~ TPH (Gasoline) 1.8 1.0
%4512 'ID: S-l-50 ugm/gm MDL,ugm/gm
Benzene ND 0.005
Toluene ND. 0 .005
Ethylbenzene .ND 0.005
p-Xylene ND 0.005
m-Xylene ND 0.005
o-Xylene ND 0.005
Isopropylbenzene ND 0.005
TPH (Gasoline) ND 1.0
%4513 ID: S-1-55 ugm/gm MDL,ugm/gm
Benzene. ND 0.005
Toluene .018 0.005
Ethylbenzene .011 0.005
p-Xylene .014 0.005
m-Xylene .029 0.005
o-Xylene .052 0.005
Isopropylbenzene ND 0.005
TPH (Gasoline) 1.2 1.0
......................... Stan ...Comer
Analytical Chemist
RESULTS OF'ANALYSIS:
%4514 ID: S-l-60 ugm/gm 'MDL,ugm/gm
Benzene ND 0.005
Toluene ND 0.005
.. p-Xylene .007 0.005
-. m-Xylene .005 0.005
o-Xylene ND 0.005
.~, Isopropylbenzene ND 0.005
I '~ TPH (Gasoline) ND 1.0
~4515 ID:'S-2-20- ugm/gm MDL,ugm/gm
Benzene ND 0.005
Toluene ND 0.005
Ethylbenzene ND 0.005
p-Xylene ND 0.005
m-Xylene ND 0.005
o-Xylene ND 0.005
Isopropylbenzene ND 0.005
TPH (Gasoline) ND . 1.0
%4516 ID: S-2-25 ugm/gm MDL,ugm/gm
Benzene ND 0.005
Toluene ND 0.005
Ethylbenzene ND 0.005
p-Xylene ND 0.005
m-Xylene ND 0.005
o-Xylene ND 0.005
Isopropylbenzene ND 0.005
TPH (Gasoline) ND 1.0
Stan Comer-----~-i
Analytical Chemist'
RESULTS OF ANALYSIS:
%4517 ID: S-2-35 ugm/gm MDL,ugm/gm
Benzene ND 0.005
Toluene ND 0.005
p-Xylene . ND 0.005
m-Xylene ND 0.005
o-Xylene ND ., 0.005
Isopropylbenzene ND 0.005
~ TPH (Gasoline) 'ND 1.0
%4518 ID: S-2-45 ugm/gm MDL,ugm/gm
Benzene ND 0.005
Toluene ND 0.005
Ethylbenzene ND 0.005
p-Xylene ND 0.005
m-Xylene ND 0.005
o-Xylene ND 0.005
Isopropylbenzene ND 0.005
TPH (Gasoline) ND 1.0
....... Start-.~ Comer ..................................................
Analytical Chemist
APPENDIX B
LUFT Worksheets
IROIIMEN[AL FA1*E liORKSFlEET FUEL CI3NSI*ITUEN!)
,,,,,,,,,,,,,,
'~ /ill 1111111111
',4 ~ C O E F G
5ftI
I
5ftI C.C.L. ~
I · ft S~PLE 5 ft = C.C.t. 5 . -.
: 5it C.C.L. 5 -
v ft S~PLE 8 ~ft ~ C.C.L. ~ .......... ye5 ~_~
: 5ftI C.C.L. a
I
· S~PLE 9
v ft SAMPLE 9 ~ft = C.C.L. 9 ........... yes ~.~
· : 5ftl ' C.C.L. 9
'' Y ft ~PLE 10 ~ft aC.C.L. 10 ~ye~
tt - feet ~n ~ ~rts ~r
'~:' e NOTE: CONCENTRATIONS EOR_ANX.._SINGL~SOIL.S~PLE~,CANNOT_~X~ED lO0~a ~0~ BENZENE, 80~n ~0~ TOLUENE~.~O~_.I_~,_X~
THE LA~I S~PLE ~0 BE INCLUBEO IN l~E ~L~LATIONS F~ CU~LAII~E CONIAHI~A~ION MUST
[ OETECIION LiHll; O0 NO~ INCL~E BOTI~ S~PLES ~ilCH HAgE CONCENIIAIION5 LESS IHAN
" 42
,.. TABLE 2-3
':ti:'l~ ENVIRONMENTAL FATE I,K)RKSHEET fOg~_( FUEL CONSTITUENT)
.-J A L
III/i1111/1111
C O E ~ G
· . · SOIL
~tIRFArE
I
' ,' t * SAMPLE'S
) SAMPLE
I
. 5ltl C.C.L. 6
5ft~ C.C.L. Z
t SAHPLE 9
· ~ft SAMPLE 9 ~ft o= C.C.L. 9 ~yes
.. 5ftI C.C.L. 9
I
· S~PLE 10 ~n
.T ft ~PLE 10 ft =C.C.L'. 10 ~ye~
'"' "::' :':.~ ft S~PLE 11' ft. , =C.C.L. 11 ~yes
:.
}':i ....':"':.'":."':":... ........ . ' :.:.:. ::.': :'":::" ~ :' ,* ft S~PLE. 12 ft" ..'=C.C.L. 12 --yes.' '__~
~~: ;.:~:~ ~ ........... :~;.:: :~.:~..,~.~.~;~ .~.~.~ ...... ':,.'' ,:.:,:~:/ ,', ',;~:~~:~.~:~.:,,
ft = feet ~ = ~rt~ ~r
....... N TE.- CONCENT~T[ONS FOR ANY. SINGLE._SOIL ~PLE ~HNOT EXCEEO ).O0~n..EOR.,~NZEHErBO~o-~--I~UENE,-~--I~.XILEM
ANO ~0~ FOR ETHYLBENZENE IN ORDER TO BE USEO ~ITH THE GENERAL RIS~ APPHAISAL.
THE LASt S~PLE 10 BE IHCL~D IN THE CALCULATIONS F~ CU~LAIIVE CONI~INAIIOM MUST BE AT OR A~VE THE
DETECTION LINII; DO NOT INCL~E 80Tl~ S~PLES ~HICFl HAVE CONCENTRArIONS LESS THAN THE DETECTION LIMIT.
4 2
t
~ENVIRONHENTAL FATE UORKSHEET FOR d-~.~"~,,/qi~A~J~ .~1~? .~..3.. *UEL CONSTITUENT)
L
I .............
Illlll!lllllll
C D E f .. G
& ~IL ~JRFACE
:. ' ~f~] C.C.L. 2
" ' t S~PLE S O. J .fq~a
5tt~ C.C.L. ~
~ :: ,.. 5f~l~ c.c.c. ~
J ,f~ s~Pc~ 7 fZO ft : c.c.c. ~-..11~ ..... ~. ~Y"~
5ft C.C.L. Z
5ftI. C.C.L. 8
· S~PLE 9 .....
· ft SAMPLE 9 ~t : C.C.L. 9 ........... yes ~.~
' *S~PLE lO__~a
' . v ft S~PLE 10 __ft ;C.C.L. 10 __yes
". lO
· . 2~' .. ~
' 7' 2..'.G2 ::.iX'4 + '..... '2 v. '." ~ -. '~ } ' · - ,. . . . 2.
r;:
..:.:. ' ,:-.. - .,...;: , .:. :..::::',.. '...:,:.::.::.' .::..::;:::. . . .,., .,...-, . .... . -. ,',. .. . ,,
:::-'.. ......................................... ..~.:':'::.::':~:'~:?::: :::::::::::::::::::::::::::::::::::::::::::::::::::::::: ,. .,y:..:,?.(::~::..:.... ..::::: ?..'¥: ,..:, ..'.:.:.:: :...::':.,.: .':..,.,'..,:' :. , .,.. ....
~ :"";'"';'" :":'"~';:; .......... :" """;""': ";W ~ ....................... ';";'"'"':~'"": ............. :'~"~"'""':"~"'"'"?'"""'? = ............... :': ........... ; ........................ ::: .......... : .............. ~':: ..............................
.... ;;% ;..';',:..'..'-..:'..L:: :.:: .:;4 ~, ';:'~.;.:J.. ;.;.'.: ::~ ,: ;::..:.'... ," :a¢:',,,;~ ~ ..... .'. ......... ~~ ~ ~% ............. ,,...r:;;.,,,. ......
~I~ ~ tt ~ feet ~a = ~rts ~r mittiml
. ~? ..........................NOTE:.~CEH~MT [ OHS FOR AHY S.[ HG~E~J~L _~LE ~.NOT. ~CEEOAOO~E~.BENZEME r-~OR ..TOLUENE
ANO ~0~ FOR ET~YLOENZEHE I~ OaOEa TQ HE USED ~ITH THE GEHERRL RISE APPRAISAL.
THE LAST S~PLE TO BE INCL~ED IN THE CAL~LATIOHS F~ ~LATIVE CQHT~INArIOH MUST BE AT OR A~VE THE
DETECTION LIMIT; O0 NOT INCL~E UO'fl~ SAMPLES ~HICH HAVE CONCENIRATIOHS LESS THAN THE OEIECII~ LIMIT.
,- 42
IABLE 2-3
ENVIRONMENTAL FATE IdORKSHEET fOR"f~.r~ll.~.'~? .(FUEL CONSTITUENT)
5ltl C.C.L. 3
I
sftI c.c.L. ~
sft C.C.L. S
f[ SAMPLE 6 ~ ft = C.C.L. ~.-~:q. ~00~ ye5
" : ~f=7 c.c.~. ~ '
/
5ftI C.C.L. 8
· f~ SAHPLE 9 ft ~ C.C.LJ 9 · _ ....... .- __yes
"" ": · +S~PLE lO ~n
? ft S~PLE 10 ft =C,C.L. 10 ~yes
~::,:..
: +S~PLE
'.". ' '. : I · ' '
· :4' ':.: :.v'":.::' :'":'.: ... v' :::::::::::::::::::::::::..:.:::::'.::::. : :','. .'" :.: '.. "::' . .' ' . .,:¥..'. ::.. .' ::"': . ' '" "'- ' ' "' '
::::::::::::::::::::::::::::::::::::: :,:':'.:.::'::.::. '..:.:.'..,:'.'.,.::::::..:, =============================., .,: ~ ..:..,:..: :":',. ,,.:..... : , . . · .., ...
ft = feet ~ = ~rts ~r miLLi~
e NOTE: C~CEH[~TIONS F~ ANY SINGLE.SOIL S~PLE-~NNOT EXCEEO lO0~n FOR BEHZENE,-~a ~-TOLUENE, &0~
.. AND ~0~ f~ ETHYLUENZEHE 'Iff ORDER TO BE USED alT~ TaR GENERAL RISK APPRAISAL.
THE LAST S~PLE TO BE INCL~ED IN THE CALCULATIONS F~ ~LATIVE C~[~IMATIOM ~ST BE Ar OR A~VE THE
DETECTIO~ LINIr; DO NOT INCL~E 80rT~ S~PLES MHICH HAVE CONCEMTRArlONS LESS THAN THE DEIECIIOM
APPENDIX C
Risk Analysis
RISK ASSESSMENT FOR BENZENE AT SEQUOIA PAINT
STEADY STATE VAPOR FLUX
The fu:st step in determining the benzene exposure t° occupants of the building is the
calculation of the rate of emission of the chemical from the soil. This rate is influenced by
such factors as the degree of partitioning of benzene between vapor, soluble and non-
aqueous phases, the rate and degree of movement of the various phases throUgh the.soft,
soft properties, and' environmental factOrs'-such as' temperature, moisture and surface
conditions. The general approach used, is to take the dominant transport mechanism, in
this case vapor diffusion, and model the process. The model used is based on one
developed to predict emissions from landfills by Thibodeaux and Hwang7. It assumes
steady-state fluxes for a non-diminishing source at a specific depth below the ground
~urface. The applicable equation is:
~ CvDs
F- H
Where:
F-- Steady-state vapor flux through a soil-matrix, from a non-
diminishing source - mg/m2'-day
Cv = Vapor phase concentration of benzene at the source - mg/m3
Ds = ~ Vapor phase diffusion coefficient through soil - m2/day
H= depth below ground surface of the contamination - 40 ft (12.19m)
xPMw
.Cv- RT
Where:
x = Mole fraction of benzene in the free liquid hydrocarbon phase. It is assumed
to be approximately equal to the weight fraction of benzene in the residual
20 ppm benzene
4100 ppm TPH The TPH value is the highest concentration encountered
at the site.
. P = Pure component vapor pressure (arm) at temperature T - (0.10 atm)
T = Temperature (o K) - 298 OK
Mw = Molecular weight of benzene - mg/mole - 78000
R = Universal gas constant - 8.21x10-5 m3-amx/mole-OK
xPMw 4~00(0'10)(78000)
Cv- RT - (8.21x10-5)(298),
1555mg/m3
(Oa)(a3.33).
Ds = T2 , a = E-MB
Equation. derived from Millington-Quirk8
Da = diffusion coefficient of benzene in air - 0.32 m2/hr = 0.77 m2/day.
Value can ,be calculated (Fuller et al)9.
a = Soft air content
M = Soil moisture content . 15
:' E = ....... "- ....... Total'porosity- .35
B = Soil bulk density 2.0
a = E-MB = .35-(.15)(2) = .05
(0 77)( 053.33) 10.4 rn2/day
Ds = ' ' = 2.92x
Substituting Cv, Ds and H into the equation for steady-state flux:
F---~---CvDs (1555)(2.92x104)12.19 = 3'72x10'2 mg/m2'day
BENZENE CONCENTRATION IN INDOOR AIR
Knowing the vapor flux through the soft, an estimate can be made of the concentration of
benzene in the indoor air of the overlying building which contains a volume of 12000 cubic
feet (1116 cubic meters). Benzene reaching the surface under the structure may enter the
building through openings in the floor, for example, cracks, joints and loose fitting pipes.
The ratio of leakage to total floor area in the average California home is 2-10cm/m2 of floor
area (Grimsrud et al)10. Commercial buildings built on doncrete slabs would experience
less leakage then residences with crawl spaces, therefore, the lower range value of 2cm/m2
is used in this analysis;
The ventilation rate for the building is based on the studies of Fisk et allL They estimated
that the average air exchange rate for residences at 0.5-0.9 air changes per hour. The most
conservative low end value 0.5 is used. A retail business with numerous customers
entering and leaving and equipped with modem ventilation systems would experience much
higher exchange rates.
The concentration of benzene in the indoor air is predicted by the equation:
FA
Q,- Q
Where:
Cb = Indoor air concentration of benzene due to volatilization from the
.. soil- mgtm3
F= vapor flux through'openings in the foundation - mg/m2-hr·
3.72x.10-2mg/m2-day x 1 day/24hr = 1.55x10-3 mg/m2-hr
A = Leakage area = 0.0002m2openings/m2 floor area x 372 m2 floor
................................. area = .0744 m2
Q = ~ Ventilation rate in building - m3far = 0.5 exchange rate/hr x 1116
m3 building vOlume =558m3/hr
Cb = . 558 .= 2.0xi0-7 mg/m3
RISK BY EXPOSURE
tn order to estimate the health risks associated with~exposure to benzene,-.a very
conservative approach was used based on a individual working at the company for an entire
occupational lifetime of 45 .years, 5 days a week and 50 weeks a year with an inhalation
rate of 10 m3faour.
.:'rotal lifetime inhaled volume ' 1.13xi05 m3
Average daily volume = 4.4 m3/day
'~xposure is the product of contaminant concentration (Cb) and air volume breathed
calculated by the following equation:
LADD--- Bw
LADD = Lifetime average daily dose - mg/kg-day
Cb = concentration of benzene in air = 2.0x10'7 mg/m3
A = Inhalation bioavailability (fraction of benzene inhaled) 100%
B = average daily volume inhaled = 4.4 m3/day
Bw = Body weight = 70 kg
(2.0x10'7)(1)(4.4)
LADD = · '70 - 1.25x10-8 rog~kg-day
The carcinogenic risk associated with a specific exposure can be estimated by the
fonowing:
R=P'E'
Where:
R = Risk associated with a specific exposure
P'= Benzene adjusted pOtency factor [mg/lifetime exposure]-1 = 1.63x10-8
USEPA6 - derived from epidemiological, studies on cancer induced
E = Exposure = inhaled volume m3/lifetime exposure x concentration
R = (1.63xlO'8)(1.13xlOS)(2.0xlO'7)= 6.0x10'10
Environmemal Health Ser~ces Department
RANDALL L. ABBOTT STEVE McCALLEY, REHS, DIRECTOR
DIRECTOR Air Pollution Control District
DAVID PRICE ili W~LLb~ ,J. RODDY, APCO
ASSISTANT DIRECTOR ~ PlanningTED & .IAMEs,Devel°pment AICP,S~:vicesDIRECTORDepartment
ENVIRONMENTAL HEALTH SERVICES DEPARTMENT
November 19, 1990
Seq.uoia Paint
700 Baker Street
Bakersfield, CA 93305
SUBJECT: Location : 700 Baker Street, Bakersfield, CA
Known As : Sequoia Paint
Permit # : 150075
Dear Mr. Elder:
Our Department has reviewed the site characterization workplan submitted.
by Groundwater Resources, Inc. The workplan addressing soil sampling
constituents to be analyzed, and health and safety considerations are acceptable
for continuing investigation of extent of contamination present at this former
underground tank site.
Please notify this office 48 hours prior to retrieving soil samples. Within
thirty (30) days after sampling and laboratory analyses are completed, a compre-
hensive report describing extent of the site' contamination must be submitted to
this office for review. The report must describe remedial alternatives available
and professional recommendations for the most feasible one.
If you have any questions you may contact me at (805) 861-3636.
Flora Darling, R.E.H.S.
Hazardous Materials Specialist
Hazardous Materials Management Program
FD:cas .... . ..................... ~ .......................
1-$00?$-h.m 14
2700 "M" STREET, SUITE 300 BAKERSFIELD, CALIFORNIA 93301 (805) 861-3636
FAX: (8-05) 85!-34~9
RANDALL L. ABBOTT I · 2700 M Street, Suite 300
Agency Director Bakersfield, CA 93301
(805) 861-3502 ..... Telephone (805) 861-3636
· ' Telecopier (805) 861-3429
STEVE Mc CALLEY
Oirector RESOURCE MAN.AG E..M E NT AGENCY
DEPARTMENT' OF 'ENVIRONMENTAL
HEALTH'SERVICES
- - ". .... '
October 10, 1990
~im ~Elder
'~,.. 'Sequoia Paint
~" -. 700 Baker S~reet
;' '" "'"'Bakersfield, CA 93305' ..... ~'~'~' .... '~ .........' ...... ' ....... ' ..... '" ...... "-~ ......... ' ...... ~-~' ......................
';' Subject: Location: 700 Baker Street, Bakersfield, CA
~" Known As: Sequoia Paint
Permit #: 150075
De'ar Mr. Elder:
Our Department has reviewed the site characterization progress report
,, submitted by Duane R. Smith and Associates October 9, 1990, for the above
referenced site.
The preliminary hand auger boring to a depth of 35 feet below'grade has not
adequately defined the vertical and horizontal limits of contamination present
beneath the former gasoline dispenser.
Duane R. Smith and Associates have proposed a Phase 2 boring using different
equipment capable of defining the contaminant limits. Our Department is agreeable
to the Phase 2 workplan.
Work should commence within 30 days. Upon receipt of Phase 2 reports our
Department will be able to continue our review and move toward closure of this
site.
Contact me at (805) 861-3636, extension 54g if you have any questions.
Sincerely,~ ~ .~
Hazardous Materials Sp,edialist
Hazardous Materials Mahagement Program
FD:cas
\150075.1tr
RANDALL L. ABBOTT ~'., ; 2700 M Street. Suite 300
Agency Director Bakersfield, CA 93301
(805) 861-3502 Telephone (805) 861-3636
· ' Telecopier (805) 861-3429
STEVE Mc CALLEY
Director REsoURCE' MANAGEMENT AGENCY
DEPARTMENT OF ENVIRONMENTAL
HEALTH SERVICES
September 14, 1990
Jim Elder ..- ............ _...~-,_.. ...... .~.~
Sequoia Paint
700 Baker Street
Bakersfield, CA 93305
SUBJECT: Location: 700 Baker Street
Known As: Sequoia Paint
Permit #: 150075
Dear Mr. Elder:
On July 25, 1990, Duane R. Smith and Associates performed Phase 1 site
characterization by hand augering at the above referenced site. To date we have
not received the soil sample laboratory reports nor a time schedule for Phase 2
augering.
Handbook UT-35 sets forth the time restraints for initiation and completion
of needed work in order to move this facility toward closure.
Please contact your environmental contractor with instructions'to forward all
reports to this office and a time schedule for completion of Phase 2 augering.
'Sincerely, ' :' ..
'.Flora Darling, R.E.H.S.
Hazardous Materials Specialist
Hazardous Materials Management Program
FD:ch
dar, lins\elder, let
UkCE .MANAGEMENT
RANDALL L. ABBOTT' ~ E,wironmental H,.,,Ith Services
Director ~ STYE McC~, R~S, DIRE~OR
Planning& DevehH)m~'~l ~,rvices
T~ J~ES, AICP, DIRE{~'OR.
Bakersfield, CA 93305
.Subject: Location : 700 Baker St., Bakersfield, CA
~own As : Sequoia Paint .,
Permit g : 150075 .'
Dear Mr. Elder:
This Department-has reviewed the workplan addendum submitted by
Duane' R. Smith and Associates, for the above'named facility. T~e workplan is
acceptable for investigation of contamination at this former underground tank
site.
Please notify .this DePartment 24 48 hours prior to Soil sampling. After
completion of sampling and analyses, a complete report describing the extent of
contamination, remedial alternatives, and professional recommendations must be
submitted .to. this Department for 'evaluation within. 30 days.
If you have any questions you may contact me at (805) 861-3636 Ext. 572.
Sincerely,
Hazardous Materials Sp~alist
Hazardous Material Management Program
FD:ch
cc: Duane. 'R'. Smith and Assiciates
............ darling[elder'.m41 .......................
2700 "M" STREET, SUITE 300 BAKERSFIELD, CALIFORNIA 93301 (805) 861-3636
RECYCLED pAPER 'FAX: (805) 861-3429
DUANE R. SMITH
AND
ASSOCIATES
Registered Geologist No. 3584
7201 Fruitvale Extension
Bakersfield, California 93308
Telephone (805) 589-7861
__J~e._.13
Ms. Flora Darling
Department of Environmental Health Services
Resource Management Agency, County of Kern
.._.
.... 2.700 M Street, Suite--.3.00 .... ~ "~-" ..... -'~-':: .... --~"~'-~:-:---, .........
Bakersfield, California · 93301 " . ~..
· . : . .. ' ' .....~. :-'' .':.: :'.-. "',i :"::'.::~ .:..
Re: . Sequoia Paint Company : " . ...' :-'.''':I'''': ~:''`:'''. .... ~:":'.'~:">.:
700 Baker Street ' ~ ..':c'.. ",.-'"'.'~:
Bakersfield, California 93305 '
Permit No. 150075
Dear Ms. Darling: "
As requested in your. letter dated May'31, 1990, a slant-boring
will be drilled beneath the showroom building at the above referenced
site. Test Hole No. 4 will be located as shown on the attachment.
The boring will be drilled at an angle of 20° from vertical to a
minimum depth of 20 feet. 'At a depth of 20 feet, the boring will
be located 8.5 feet east of the surface location and 6.5 feet east
of the west .edge of the building. Sample collection and preservation
will be as described in the original work plan.
If you.have any questions, please feel free to call.
Yours truly,
Thomas F. Gutcher .-
Staff Geologist
TFG/jk
cc: Mr. Jim Elder, sequoia Paint Company
TE OLE LOCATION MAI~
. .. SEQUOIA PAINT
700 BAKER STREET
BAKERSFIELD . CALIFORNIA
OV~RH~O ~rtLzrz~$ : .,
C~NOPy
5~o w~oo~ ~
ASP~AL~
k Lot .
~ ·
W~oo~ r I~oN F~c6
Cu~o'
.- ~ASr 19fy 9r~ear I" = ~o'
TEST HOLE LOCATION
DUANE R. SMITH & ASSOCIATES -- JUNE 1990
Attachment
GARY J. WICKS 2700 M Street, Suite 300
Bakersfield, CA 93301
Agency Director
Telephone
(805)
861-3636
(805) 861-3502 .
.//~?'f;__~,.~*~~'~V~ ' TelecopJer (805) 861-3429
sTEvE
McCALLEY
U,re to, R ESOU RC E AG ENCY
........... . _" ._...: ': .......................... .... : .... ..._. ,~~//~.~.,..-i ~. . £~ ._~..£ ........ .j.. ............
May 31, 1990
Jim Elder
Sequoia Paint
:. 700 Baker Street -' '
Bakersfield, CA 93305
SUBJECT: Location: 700 Baker Street; Bakersfield, CA
Known As: Sequoia Paint
Permit #: 150075
Dear Mr. Elder:
Our Department has reviewed the si.re characterization workplan
submitted by Duane R. Smith and Associates for the above-referenced
site.
Duane R. Smith and Associates proposes three hand auger test
holes to determine depth and lateral extent of the site's
contaminant plume~ Our Department is agreeable to the proposed
hand auger test holes #1, #2, and #3 at the dispenser area.
However, an additional slant augering will be required to explore
the possibility of contaminant migration beneath the existing
.showroom and office building.
Previous hand augering 'on March 9, 1990, performed by
Groundwater'Resources, Inc. showed soil consistencies to be silty
sand progressing to a gravely coarse sand. At the 14 foot depth
hand augering became increasingly difficult.
In view of this, it may not be possible to adequately define'
the contaminant plume by hand augering. Additional boring
techniques may be required.
Jim Elder
Page Two
May 31, 1990
Please have your environmental contractor forward to this
office an additional plot plan depicting the required slant auger
test hole.
~ Upon receipt of the addendum information, our office will
continue the workplan review. If you have any questions, you may
contact me at (805) 861-3636.
Flora Darling, ~
Hazardous Materials .~ecialist
Hazardous Materials 'Management Program
FD: jg
cc: Duane R. Smith & Associates
i GARY J. WICKS
~ 2700 M Street, Suite 300
: Agency Director .. Bakersfield, CA 93301
~: (805) 861-3502 ,.~.~-~.:,~.~.~..:~.~ Telephone (805) 861-3636 ''
STEVE McCALLEY ~'~r,t'*~' -..-'~.. Telecopler (805) 861-3429
~,';: Director N
RESOURCE 'Jill T' AGENCY
DEPART~. i~ MENTAL
............................... ~.- ...... - ..... ~-: * --':"---' ~:-~-"..':"-' - ........ :_.:' ' .. '_ + ........ m* ~ ''/'::'~::.::--: '--'----'~ ...... 7'-~
March 28, 1990
Jim Elder
~" ......... ' .... Sequoia 'Paint ...............................
~' 711 East 19th Street
Bakersfield, CA 93305
SUBJECT: Location : 711 East 19th Street, Bakersfield, *CA
Known As : Sequoia Paint
Permit # : 150075
Dear'Mr. Elder:
Our Department has reviewed the additional soil sample reports of March 9,
1990, submitted by Groundwater Resources, Inc. (G.R.I.) for the above referenced
site.
Laboratory analyses reveals contamination exists at the 14 foot depth.
Therefore, our Department will require a site characterization, feasibility study,
and remedial action plan to be submitted for the above facility.
Please have your Environmental Contractor forward to our office a site
characterization workplan for review and approval - the workplan should be
submitted within 30 days of receipt of this letter.
If you have any questions you may contact me.at (805) 861-3636.
Sincerely,
'~-Pqora Darling, R.E.H.S.~
Hazardous Materials Speciali~sd~
Hazardous Materials Management Program
FD:cd
cc: G.R.I.
darling\elder.let
groundwater resources inc. BAKERSFIE ,C~Oia~l~3 ~
Gen era' En g'n~~k~r ~l
Ha~ch 19, 1990 '"'~,` ~%~'
~ _Kern...:Coun~y Department of .Envi~onment~ Health .Services ...... . ' . . ·
; 2700 "M" Street, Suite 300
) Bakersfield, CA 93301
RE: Sequoia Paint
700 Baker Street
Bakersfield, CA
'~ Permit ~A-1118-15
Dear'Ms. Darling:
On January 25, 1990, Groundwater Resources, Inc. (GRI) removed ~wo
underground fuel tanks from the referenced pcoper%y and conducted
soil sampling as required for the preliminary .assessment. The
samples were analyzed by BC Laboratories of Bakersfield for several
fuel constituents. No evidence of contamination was found except
for the sample taken six feet beneath the dispenser which contained
32.55 ppm total xy]enes and 935 ppm TPH (gasoline). These results
were reported to the Department on February 12, 1990.
At the request of Hr. Jim Elder, owner of Sequoia Paint and with
the concurrence of your Department, GRI, on the 9%h of March,
obtained additional soil samD]eS beneath the disoenser using a hand
auger. SamD]es were collected at a depth of~~ee%.
At sampling points, %he auger bit was reD]aced by a clean brass
sampling.tube and a slide hammer 'was used to drive the tube into
the soil. The tubes were then sea]ed and chilled for transport to
BC Laboratories '~nder a chain of custody document. Analysis for
BTXE and TPH (gasoline) were requested.
While augering petroleum odors were noted between 5 and.14 feet.
Hydrocarbon were found by the lab in all samD]es. No benzene was
detected as in the previous six foot sample, but toluene,
ethy]benzene and higher concentration of total xy]enes were
present. TPH (gasoline) levels were also higher, ranging from 1700
to 4100 ppm. The complete lab results are attached.
If you require further'information,, please call (805)835-7700.
Sincerely yours,
Claus Engelhardt
PFo~ect Geologist
CLE~amp~rep~O11.rep ~.
....... ~ ............ Enc.losu.~e
cc- J~m Elder, Sequoia Paint
MAILING ADDRESS:P.O. BOX9383, BAKERSFIELD, CA93389 (805) 835-7700
-. LOSANGELES(213) 724-3147
EN¥1RON~ENT~L
P~ROLEU~/ d.J. EGLIN, ~EG. CHEM. ENG..
4100 PIERCE RD., ~KERSFIELD, CALIFORNIA 93308 PHONE 327-4911
~geable ~o~tics
(SOIL)'
5400 A~in Ct. 'Re~: 16-M~-90
~ersfield, CA 93313
At~ntion: Cla~ ~leY~t
~b No.: 2077-~
~le ~sc: Proj~t ~1500~0-2 ~
09-~90 09-~-90 15-~r~90
~ti~ent U~ Res~ ~vel
~ene u~g none de~~ 0.7
Toluene ~/g 2.2 0.7
Et~l ~ene ~/g 4.4 0.7
p-Xylene ~/g ~ 14 0.7
m-Xylene ~/g 7.8 0.7
o-~lene ug/g 290 0.7
To~l Pet~le~
(Gasoline) "
TEST ME~I~tOD:. TPH by D.O.H.S. / L.U.F.T. ~thod.
Individual constituents by Modified EPA ~rethod 5020/8020.
As Received Basis
Corm~ent.~:
California D.O.H.S. Cert. ~102
ENVIROI~MENTAL
LABORATORIES, INC.'
PETROLEU/iI J.J. EGLIN, REG. CHEM. ENGR.
4100 PIERCE RD., BAKERSFIELD, CALIFORNIA 93308 PHONE 327-4911
~geable ~o~tics
(~IL)
~ 5400' Al~ ~ ~ Re~: 16-~-90
~ersfield, CA 93313
At~ntion: Claus ~ ~le~t
~b No.: 2077-2
~le ~sc: ~ject $150010-2
~ ~-~11 3/09/90 1:40 Di~er~ ~' ~. '-~:.~. - ·
~ ~le ~ ~le ~ ~lysis
~ll~: R~eiv~ ~ ~b: '~
09-~90 09-~90 · 15-~-90
~ni~~
Re~~ ~ySis Re~rti~
~ti~ent Uni~ Resul~ Level
~nzene ~/g none de~ 0 6
Toluene ~/g 1.0 0 6
Et~l ~nzene ug/g 1.4 0 6
p-Xylene ~/g 27 0 6~
~lene ~/g 50 0 6
o-Xylene ~/g 92 0 6
To~l Pet~le~
~~'~ns ~/g ~ 20
(Gasoline)
TEST METHOD: TPH by D.O.H.S. / L.U.F.'T.
Individual constituents by Modified EPA ~f~th¢~l 5020/8020.
As Received -Basis
Corf~nts:
California D.O.H.S. Cert. S102
ENVIRO~iMENTAL
LABORATO RI ES, IN C.
J..J. EGLIN, REG. CHEM. ENGR.
PETROLEUM
4100 PIERCE RD., BAKERSFIELD, CALIFORNIA 93308 PHONE 327-4911
Purgeable Aror~tics
(SOIL)
.... -~-_ -'~ '~?~ ...... L~ ~-- ' ~-'~ .~-~--2--~'~-~---~-'~ "-'~J ~'~?-~'"~--~ ."- ,
Gro~dwa~r Resoles, Inc. ~ of
5400 AlVin Ct. 'Re~: 16~E~'-90 .-
~ersfield, CA 93313
At~ntion: Claus ~le~t
~b No.: 2077-3
~ple ~sc: P~j~t $150010-2
- ............ S-~14 3/09/90 2:20 Dis~e~
~ ~le ~ ~le ~ ~mlysis
~11~: R~eiv~ ~ ~b: . ~le~:
09-~-90 09-~-90 15-~-90
M~i:~
' Re~i~ ~lysis Re~i~
~%i~ent Uni~ Res~ ~vel
~ene ug/g none de~c~d 0.6
Toluene ~/g 1.4 0.6
E%~i ~ene ~/g 1.7 0.6
p-Xylene ~/g 27 0.6
~Xylene ~/g 55 0.6
o-Xylene ~/g 81 0.6
To~l Pet~ie~
~ar~rm ~/g ~ 20
(G~ol~e)
TEST METHOD: TPH by D.O.H.S. / L.U.F.T.
Individual cor,~ti~ents by Modified EPA ~th~l 5020/8020.
As Received -Basis
Co~nts:
C-~iifornia D.O.H.S. Cert. $102
ENVIRON. MENTAL
~,~,,~,~ LABO R~TO RIES. INC.
J. J. EGLIN, REG. CHEM. ENGR.
PETROLEUM
4100 PIERCE RD., BAKERSFIELD, CALIFORNIA 93308 PHONE 327-4911
BTXE/TPH GASOLINE
Quality Control Datm
5400 Aldrin Ct. Analysis Date: 15-Mar-90
-Bakersfield, CA 93313 S~,ple Matrix: soil
Attention: Claus F~elhardt Units: ug/g
for Lab Nos: 2077-1, 2077-2, 2077-3
Dup
Spike Spike Spike
Constituent % Rec' % Rec RPD
Benzene 87.37 84.22 3.67
Toluene 89.64 87.34 2.60
EthYl Benzene 92.96 89.32 3.99
groundwater resources, inc. Bakersfield, CallfornJa 93313
~: Telephone: (805) 835-7700
" '~. Tele-Fax. (805) 835'-7717
iii ~. CHAIN OF CUSTODY RECORD
LAB DESTINATION: iJ. PROJECT NUMBER:_/'_5_-z2_0,0-2- PROJECT CONTACT: ~--lct~ EPI~__ [/14
SAMPLER(S):...(~i gnatu i x ~
~U
LAB SAMPLE :i: zrr ANALYSIS SAMPLE CONTAINER
NUMBER NUMBER DATE TIME SAMPLE LOCATION ~°z
o REOUESTED TYPE i TYPE
SPECIAL INSTRUCTIONS:_ .0 5.o- 5'~ /'~t,~.~ ~
POSSI~.LE SAHPLE ~AZARDS' ; .....
I Relinquished by: i(~r'z~£ ~~t4~'~Z'Date/TIm ~'0 Received by: Date/Time:
I. Relinquished by: ~' ~'" Date/Time: Received by' Date/Time:
1. Relinquished by: ,. Date/Time: Received by' Date/Time:
1. Relinquished by: Date/Time: · Received by. Date/Time: ,,
CCR (Rev. 10/89) ' WHITE: LABORATORY PINI~ JOB FILE YELLOW: SAMPLE LOG
SEQI iA PAINT coMP
Hanutacturer~ at Quality. Paints SinCe 1962 _,
71~ East 19th Street · Ba~erstietd, Calit. 305
Phone: (805) 323-7948
March 6, 1990
. '.'" . ._.ZZ~7.'"-'2~"-'~T"~"E~":' '-~Z~-':'~. £_..: L}i.:-' ~.'~Z~E-'~'Z-]-7"7~:--~ .... .Z-'ETZ. _:C"~]'~Z T.~"--~_'~-" ..' -' .._.'L ~..' · ]-'V'~'ZZ"'. ....... ~'.'>] - '~%~:]£'-'f"-:Li'-i/L ......
Kern County Resources Management Agency'
2700 'M' Street.Suite 300
Bakersfield, CA 93301
ATTENTION: Flora Darling R'E: Permit ~Al118-15
Befo~re i'bought' 'the Tucker property at 19th and Baker I .wrote %he .""."
.... Department o.f .Environmental Health_.._~er~ices fOr .informa~ion_~n '~he..~'~.~;:::;-.~..~
underground tanks. I received a reply alon~ with a diagram of a '-'...
4,000 and a 200 gallon tank. We checked with the construction
· company that installed the ~anks and we were told that %hey had. '
been in'for eight years. Tucker Auto's vacated the property three -" '
years after they had been installed, so they had very little use.
we further checked with the city building department and they had
no negative findings.
In April 1989 we had a preliminary site assessment and had our
tanks removed at 711 East 19th Street. William H. Park, Geologist
at thattime ~lso did a site characterization.
Flora, where I need your help is supplying me with your department
needs, but at the same time helping us so that we do not have.any
unnecessary expenses that we cannot afford. The last time we went
through this, we were m'isinformed and we ended up getting ripped off.
Flora, any guidance that you can give us to expedite this matter
would be greatly appreciated.
Thank you.
Sincerely, -'
P 540 625 760
GARY J. WICKS RECEIPT FOR CERTIFIED MAIL
NO INSURANCE COVERAGE PROVIDED
l'~ency Director ('~ NOT.FOR INTE~]fl0_N~ ~A~,
(805) 861-3502 ..... :,~ :~:
Director R E S 0 U'R C E E N T
DEPART MENTAi ~ P~'/~. ~q~,: '"
~ Postage : · , . ~ S ·
Special Delivery Fee
Febr'uary 27, l, gg0 Restricted Delivery Fee
; · - Return Receipt showing ;. ' ·
, tO whom and Date Delivered
Return Receipt showing to whom, .,,...:.
Date, and Address of Delivery · -
Jim .Elder ....
.... Sequoia Paint' ' . ...... - ..... :-:-:- ~..~ TOTAL' Postage :a'nd Fees.... . . .......... S ...............
711 East lgth Street
BakerSfield, CA 93305 . . ~, ~ ~,-..~ ,- ·
SUBJECT: Location: -700 Baker Street '~'
.. Bakersfield, CA 93305
Known As: Sequoia Paint
PERMIT #.: 150075
Dear'Mr. Elder:
This letter is an official notice to inform you that the property described above has
been determined by Kern County Environmental Health 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'S
REVIEW AND APPROVAL BEFORE THE WORK IS INITIATED. Enclosed 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 for the over§ight of the work
for the site characterization, feasibility study., remediation action plan, site
remediation, and ongoing monitorin~ is not covered by any fees or permits. These
costs are recovered by Kern County Environmental Health 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 only pertain to costs associated with oversight.
(A) STATE CONTRACT
The State Leaking Underground Storage Tank Pilot Program provides a mechanism for the
State to reimburse the County for County oversight. The County will conduct the
necessary oversight and bill the State Water Resources Control Board~under this State
contract. The State will then charge you, a responsible party, for both the costs
incurred by the County and the State,' pertaining to your site, under the State terms
explained below: ·
Whereas the Legislature has appropriated funds from theCalifornia Hazardous Substance Clean-up Fund to pay the local and state
agency administrative and oversight costs associaled with the cleanup of releases from underground storage tanks; and Whereas the
direct and indirect costs of overseeing removal or remedial'action at the above site are funded, in whole or in part., from the Hazardous
Substance Cleanup Fund; and Whereas ~he 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 HI~REBY NOTIFIED that pursuant to Section 25360 of the Health and
Safety code, the Above Responsible Par, y or P:~rlics sh;tll reimburse the State Water Resources Control Board for all direct and
indirect cosls incurred by any and all state and loc~t agencies while overseeing the cleanup of the above underground, storage tank
site, and the above Responsible Party or Part i¢...a shall make full payment of such costs within .30 days of receipl of a detailed invoic~
(B) COUNTY OF KERN LOCAL AGREEMENT OPTION
Kern County Environmental Health 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 Trus% Account. Charges for
County oversight are made against this account. In this option, a responsible party
must enter into a County agreement, attachment "B".
Yhe environmental sensitivity (attachment "C") of this -site has been reviewed by
Environmental Health 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.
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 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 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 ofthe
State contract for Leaking Unqerground Storage Tanks.
If you should have any questions.regarding this matter, please contact Susan Gonzales
at (805) 861-3636.
: '-"St~ve McCalley, Director[ /
~ Environmental Health Serve? Department
.... attachments "' .........."~ ..... ' '-~ ~-~' ......
UNDERGROUND STORAGE TANK UNAUTHORIZED RELEASE (LEAK) / CONTAMINATION SITE REPORT
"~ REPORT BEEN FILED ?
~G~N~ ~A~ P~E
~ME
(1) · QU~T~ L~T (G~NS)
~U~ OF DI~HAR~ C~(S)
~ T~K~ ~ UN~O~ ~ OVERF~ ~ ~P~R~NLURE "~ SPl~ ". ':
~E~ONEONLY : '.
~UNDE~RMINED ~ ~ILONLY ~ GROU~WA~R ~ DRINKINGWA~R-(CHECKONLYIFWA~R~SHAvEAC~LYBEENAFFEC~D)
~ NO A~ON T~ PR~IMINA~ Si~ ~E~ME~ ~R~ ~BM~D ~ ~LLUTION C~C~R~N
~ ~BEI~IRMED ~PR~INA~S~E~ME~DERWAY : ~ ~ST~N~MON~R~G~P~GRE~
~ REMEOIA~ONP~ ;.- ~ CA~mEO(C~mMPm~ORUNNECE~AR~ ~ ~ ~PUNDERWAY " :.
CHE~PROPRIA~TION(S) ~ ~CAVA~&DISPO~(ED) ~ ~MO~F~EP~CT(F~ ~ ~H~C~B~GR~ATION(I~
~ C~SI~(CD) ~ ~VA~&TREAT(~ ~ ~MP&T~ATG~UNDWA~R(G~ ~ R~SUPPLY(R~
:emovaI'Co~tractc
~i_~ectton 2 ..~.,To be filled out by contrac '"- .... "'
groundwater resources inc. .'BAKERSFIELD CALI_F~RNI^ 93313 ,
· ~ .-'.2 :* ~ ~
~. . /,,~,..:. (y~aera,,~ineer~Contractor
· /~y Cla%~ Ucense'~'Nq. 5207~
-' Ms. Turonda Crumpler
..... Kern CountyHealthDepart~ent_.. .... . ...... '
2700 M Street, Suite 300
Bakersfield, CA 93301
RE: Sequoia Paint
700 Baker Street
Bakersfield, California
Permit #Al118-15
Dear Ms. Crumpler,
Enclosed are copies of the Tank Disposal Form, the tank tracking
record, and the manifest for the above referenced site. These
documents were not included in the closure report sent to your
attention on February 12, 1990.
! apologize for any inconvenience that this ommission may have
caused you.
Very truly yours,
C.laus L. Engel~a~rdt
Project Geologist
CLE-tab
MAILING ADDRESS: P.O. BOX 9383, BAKERSFIELD, CA 93389 (805) 835-7700
LOS ANGELES 1213~ 724-3147
-~./RECYCLING, INC)/ TANK .... DISPOSAL FORM
2202 South Milliken Avenue ,. Date: ~"AI~, oq..~, ,19
Ontario, CA 91761 Job If
(714) 98a-8000
RO. If
DESTINATION:
A.M.R. 2202 ~. Milliken Ave., Ontario, 'CA 91761
TIME
OU~
5
~ Se~ices Rendered Cost -- ~% '
~ Disposal F~ ~ TAN~ REC~VED
QTY. GAL~Nfi TYPE NET TONS T~AL
~ Extensive ~adingTime 1~ F' S' ~
~ Fiberglass Tank Disposal Fee ~r Tank ~.~ 1~- ~2 ft. D ~ .44
Fiberglass Tank Delivered 2~.~ 1~ ~ ~ .87
__ Bobtail Disposal Fee 250.00 ~ OO~ 1.32
TOTAL CHARGES $ ~ 7~ ~ 0 3.26
~0 D ~ 3.82
All fees incurred are per load unless specified. ~ D ~ 4.33
Terms are net 30 days from date of invoice, 12000 ~ ~ 4.93
Contractor's signature represents acceptance
of terms for payment, and confirms that'tank NO. OF TANKS T~AL NET TONS
removal complies with State laws. ~ /'7~
CONTRA~OR'S,SIGNATURE *F -- FIBERG~SS
/ 1~ / ) ~BE~ COMPLETELY DESTROYED FOR SCRAP .UAPOSES ONLY. '
CONT~CTOR COPY
~7oo ~ su.t ' KERN COUNTY HEALTH DEPARTMENT
' ~ele~e (~5) ~ 1-3~e EH~ROHME~L H~ DIVISION DIRE~OR OF EN~HMEN~L H~
Facility Nane __ ~~~ ~ern County Per. it
* * UNDERGROU~ TARK DISPosITIoN T~CKIRG RECO~
This fo~a Ii t~ b~ returned to the Kern County Health Department !~lthln 14
....... ,~.-.~ ..:0~ --acceptanta ~f--tank(s). ,bF:dtsposal -'=Or' recycltn~ ta-eiltty, '
:~'; ................... holdee of the pee~lt ~lth numbee noted above Is responsible foe insuring
that this form Is co~pl~ted and returned.
Section I - To 'be filled out ~ tank re~oval contractoe:
Tank Removal Contractor: .... ~ _c~4 ~---y
~ctlon a - Io
Tank "~econta~tnatlon' Contractor ,,,~" --~/? ~ ~
~ddress ...... ':' Phone
.... . Zip
Authorized representative of contractor certifies by signing belo~ that
tank(s) have been decontaminated In accordance with Kern County Health
Department requirements. . '5>'-.-. '~..:...::'
..,, .' -:" _
Section 3 -mT° ~be filled _out_ _and :si~ned _by ~an u r z re r sentative of the · · treatmenl, _storaRe_, or disposal facility ,accePttnE _tank(s_)_:
Date Tanks Received.... ~., ~&/:-/q?~ .... ' ac. or Tanks ~':."-,
...................... ; ................ -(Authorized Representative)
* * * HAILING INSTRUCT'IONS: ' Fold In half and staple. '
. Department of Heallh Service~
Form Approved OMB No. 2050---0039 iEx~ir'e~' 9-30-9 t) Toxic Subalances Conlrol Divisio,
Sacramento, Califomi~
UNIFORM HA~RDOU/;' c::::"~' us EPA ID No. Maml[ 2, Page I [
3. Oeneral~'a Name and Mailing Addreel A. 8tate Manileal Oocumenl Number
I
5. Trafllpoflg 1 C~pafly N~I O. US ~A ID N~ C. Still Trlnapofler'a ID
r 7. T~~pany ~o ........ 8. US EPA ~ N~b~ ; E. 81ilo Traflap~er'8 iD
Quafltily ~flit Waste No.
~ 11. US DOT Do~pt~ (~l~hO Pro~ Shipping ~o. ~md CI088. 8~ ID
T~pe
R
A EPA/~her
T
, EPA/~ar
~ " I! ! IIII
EPA/~her
GENE~TOR'S CE~I~ON: I hereby d~l t~l t~ ~t~tl Of thil c~e,I .ri fully and Icc~lely de~b~ above by proper shipping name
~ II I lm a large quantily g~eral~, I ce~i~ thai I h~ve ~ ~am In pl~ce to r~uce the volume and loxicity el waate generaled to the degree I have determined
O I~ be economica~y praclicable and I~t I have ~cted I~ ~cticable melhod el Ire~tmenl, alorage, ~ diapoaal currenlly available to me which minimizes Ihe
U generation arid select tho boot waste management mol~ t~l ko avai~Olo to me and t~al I can ailed.
ZI Print,d/Typed N,m, I..flal.o~ / ~ .onthO.yY..r
T 17. Tr8napo~ I Ackflowledgem~t of R~oipl of ~lofiM8 ' '
R .
Month O~y
O I~r~fllport~r 2 ~w~dg;m~l of Receipt of Materials · -- -- I -
~ Priflto~/Typed Name I ~gflaluro Month Day Year
E
19. Dilcropancy ~O~atiofl Space
I 2~. Facilely Owfl~ or OperM~ Ce~iflcaliofl of receipt of hazardous maleri8ll covered by this mamfest e~cepl 88 flole~ iff Item 19.
T
d '~-'' Printed/Typed-Name .................. . ......IJ Sig~l~e "' J J J J J JM°nfh Day Year
DHS 8022 * (I/~) ~ Not Write ~low ~;s Line ·
EPA 87~22
(Rev. 9-eS) P,avio.. editions are obaobte. ~lue: GENE~A~O~ SEND5 THIS COPY ~O DOH$ WffHIN 30 DAY5
To: P.O. ~x 4~, Socromcflm, CA ~812-0400
~ 5400 ALDRIN CT.
... groundwater resources inc. BAKERSFIELD. CALIFORNIA 93313
~ General Engineering Contractor
Class A/Haz License No. 520768
February 12, 1990
Ms. T uronda C rumpler · .
Kern County Health Department
Division of Environmental Health - ~ ~~ ~/
2700 M Street, Suite 300
Bakersfield, CA 93301
700 Baker Street
Bakersfield, California
Permit ~Al118-15
Dear Ms. Crumpler,
On January 25, 1990, Groundwater Resources, Inc. (GRI) removed the
· following underground tanks from the referenced property:
One 4,000 Gallon Unleaded Tank
One 200 Gallon Waste Oil Tank
The tanks were decontaminated on site using a high pressure steam
cleaner and inerted with dry ice. Rinsate was disposed of at
Gibson Oil and Refining in Bakersfield under manifest ~88524447.
The tanks were removed to American 'Metal Recycling, Inc. in
Ontario, California.
Soil samples were retrieved under Kern' County Department of Health.
Services direction (see plot plan for locations). The gasoline
tank was sampled one third.of the way in from each end at two and
s.ix feet beneath the tank bottom. Samples were also obtained at
two and six feet beneath the fuel dispenser and under the piping
half way between the tank and dispenser. A two and six foot sample
were taken from beneath the center of the waste oil tank.
All samples were analyzed by B.C. Laboratories in Bakersfield.
Those associated with the gasoline tank were anlayzed for BTXE and
TPH (gasoline). 'No hydrocarbons were detected except in the sample
taken six feet under the dispenser which contained 32.55 ppm,total
xylene and 935 ppm TPH.
The waste oil sample' was tested for total lead,'total halogenated
hydrocarbons (TOX) and oil and grease, as follows:
TOTAL LEAD. TOX OIL & GREASE
Six Feet Beneath Tank 7.21 ND 152
MAILING ADDRESS: P.O. BOX 9383, BAKERSFIELD, [A 93389 {805J 835-77~
LOS ANGELES (213} 724-3147
Ms. Turonda Cru~Jr
Kern County Health Department
Division of Environmental Health
,February 12, 1990
The lab results, Chain of custody, a plot plan, manifest, and the
.tank..disposal. form arC-.enclosed. Please contact our-main, office '-~ ........
at (805) 835-7700 if you have any .questions or require further
information.
Very truly yours,
Project Geologist
CLE:tab:O89.rep
Enclosures.
cc: Jim Elder, Sequoia Paint
BAKER STREET
G/g..RCUNE TANK
.......... ~.~ - .... '~ ........ ~;;~ ---. 4000 GALLON,-'~-~-:'~'--~'':~ ..... ~'~'::' ~ ;~ '";~: .... -:~-'"-':'~'~' '-'~:~-:' ~-' '
'~ '~'" ' .... ~ _/,_/, (REMOVED) ' .
.,., BUILDING
[".~,.'"'".'""
PLATE SEQUOIA PAINTING
700 BAKER STREET groundwater resources, inc.
'I BAKERSFIELD, CALIFORNIA
........ .. , PLAN
PLOT Proiect Number: ~$oo~o-2
EIVVIRONllIEIVTAL
LABORATORIES, INC.
PETROLEUIiI ~ J' EGLIN, REG. CHEM. ENGR.
4100 PIERCE RD., BAKERSFIELD, CALIFORNIA 93308 PHONE 327-4911
Purgeable Aromatics
(SOIL)
Groundwater ReS~-'' indUStrieS._ .::. - .......... :=:~': ......... ::':-:.-----..--:_::._-__._-.-:- :. :.- _:_:__.:_ ._.::.-
Date of
5400 Aldrin Ct Report: 05-~eb-90
~Bakersfield, CA 93313
Attention:
L~b No.: 776-1
' Sa~le Desc: S-D-2 Dispenser 2' 1/25/90 @ 11:22
Date Sample Date S~le Date Analysis
Collected: Received @ Lab: Completed:
25-Jan-90 25-Jan-90 02-Feb-90
Mird~,
Reporting Analysis Reporting
Constituent Units Results Level
Benzene ug/g none detected 0.03
Toluene ug/g none detected 0.03
~.thyl Benzene ~g/g none detected 0.03
p-Xylene ug/g none 'detected 0.03
m-Xylene' ug/g none detected 0.03
o-Xylene ug/g none detected 0.03
Total Petroleum
Hydrocarbons ug/g none detected 2.00
TEST METHOD: TPH fOr gasoline by D.O.H.S.L.U.F.T. ~thod.
Individual cor,-~ti~ents by Modified EPA .~thod 8020.
As Received Basis
California D.O.H.S. Cert. ~102
ENVIRONMENTAL
LABO RATO R! ES, IN C.
PETROLEUM J' J' EGLIN, REG. CHEM. ENGR.
4100 PIERCE RD., BAKERSFIELD, CALIFORNIA 93308 PHONE 327-4911
Purgeable Aromatics
(SOIL)
5400 Aldrin Ct Report: 05-Feb-90
Bakersfield, CA 93313
Attention:
' Lab No.: 776-2
· S~ole Desc: S-D-6 Disperser 6' 1/25/90 @ 11:38
Date Sample Date Sample Date Analysis
Collected: Received @ Lab: Completed:
25-Jan-90, 25-Jan-90 02-Feb-90
Mir~im~,
Reporting Analysis Reporting
Constituent Units Results Level
Benzene ug/g none detected O. 30
Toluene ug/g none detected O. 30
Ethyl Benzene ug/g none de~ected O. 30
p-Xylene ug/g 3.04 O. 30
m-Xylene ug/g
~~-4~5~-- O. 30 '
o-Xylene
~/g
24.56 ~ O. 30
Total Petroleum /" '~,
Hydrocarbons
ug/g (,,..935. O0 .~ '20. O0
TEST METHOD: TPH for gasoline by D.O.H.S.L.U.F.T. ~ethod.
Individual constituents by Modified EPA method 8020,
As Received Basis
Co~nents:
California D.O.H.S. C~rt. ,102
· ENVIRONMENTAL
PETROLEUM J' J' EGLIN, REG. CHEM. ENGR.
4100 PIERCE RD., I~KERSFIELD, CALIFORNIA 93308 PHONE 327-4911
Purgeable Aromatics
(SOIL)
:': ~ .... _'"~"i~'~ . "~ -~> ~---'~'~ ~ ~'~---?' '--~ '~-~
__'~ Groundwater Resource. ~ndu~ries
5400 Aldrin Ct Report: 05-Feb-90
-Bakersfield, CA 93313
Attention:
,La.-~'~ No.: 776-3
,..Sample Desc: S-P-2 Piping. 2' 1/25/90 ~ 11:55
Date Sample Date Sample Date Analysis
Collected: Received @ Lab: Completed:
25-Jan-90 25-Jan-90 02-Feb-90
Mini~m
Reporting Analysis Reporting
Constituent Units Results Level
Benzene ug/g none detected ~ 0.03
Toluene ug/g none detected 0.03
Ethyl Benzene ug/g none detected 0.03
p-Xylene ug/g none detected 0.03
m-Xylene ug/g none detected 0.03
o-Xy!ene ug/g. none detected 0.03
Total Petroleum
Hydrocarbons ug/g none deteot~d 2.00
TEST METHOD: TPH for gasoline by D.O.H.S.L.U.F.T. ~thod.
Individual cor~tituents by Mollified EPA ~thod 8020.
As Received Basis
California D.O.H.S. C~rt. ~102
ENVIRONMENTAL
LABORATORIES, INC.
PETROLEUM J' J' EGLIN, REG. CHEM. ENGR.
4100 PIERCE RD., BAKERSFIELD, CALIFORNIA 93308 PHONE 327-4911
Purgeable Aro~mtics
(SOIL)
5400 Aldrin Ct Report: 05-Feb-90
BakerSfield, CA 93313
Attention:
L~b No.: 776-4
.Sample Desc: S-P-6 Piping 6' 1/25/90 @ 12:09
Date Sample Date Sample Da~e Analysis
Collected: Received @ Lab: Completed:
25-Jan-90 25-Jan-90 02-Feb-90
Reporting Analysis Reporting
Constituent Units .~ Results Level
Benzene ug/g none detected 0.03
Toluene ug/g none detected 0.03
Ethyl ~nzene ug/g none de%ected 0.03
p-Xylene ug/g none detected 0.03
m-Xylene ug/g none detected 0.03
o-Xylene ug/g none detected 0.03
Total Petroleum
Hydrv~.arbons ug/g ~ none detected 2.00
TEST METHOD: TPH for gasoline by D.O.H.S.L.U.F.T. method.
Individual constituents by Modified EPA ~ethod 8020.
As Received ~asis
Comments:
California. D.O.H.S. Cert. ~102
ENVIRONMENTAL
LABORATORIES,. INC.
PETROLEUM J- J' EGLIN, REG. CHEM. ENGR.
4100 PIERCE RD., BAKERSFIELD, CALIFORNIA 93308 PHONE 327-4911
Purgeable Aromatics
(SOIL)
." ':.~' .":-' "~ .~'--~'~-'~Groundwater:, Resource I~ustries ~ ~ ~- ~ '~-~ ~-~- ''~ ...... ~ Date 6f" ": .......... r~ .... ...... ~ -~ .....
5400 Aldrin Ct Report: 05-Feb-90
Bakersfield, CA 93313
Attention:
~L~b No.: 776-7 '
~ Sample Desc: S-GE-2 Gasoline Tank East End 2' 1/25/90 @ 1:48
Date' Sample Date Sample .Date Analysis
Collected: Received @ Lab: Completed:
25-Jan-90 25-J~,-90 02-Feb-90
Minirmm~
Reporting Analysis Reporting
Constituent Units Results Level
"BenZene ug/g none detected 0.03
Toluene ug/g none detected 0.03
Ethyl Benzen~ ug/g none detected 0.03
p-Xylene ug/g none detected 0.03
m-Xylene ug/g none detected 0.03
o-Xylene, ug/g none detected 0.03
Total Petroleum
Hydrocarbons ug/g none detected 2.00
TEST METHOD: TPH for gasoline by D. O,H. S. L, U. F. T.
Individual constituents by Modified EPA method 8020,
As Received -Basis
Comments:
California D.O.H.S. Cert. #102
£NVIRONI~£NTAL e
LABORATORIES, INC.
PETROLEUM J. · EGLIN, REG. CHEM. ENGR.
4100 PIERCE RD., ~KERSFIELD, CALIFORNIA 93308 PHONE 327-4911
Purgeable Aromatics
(SOIL)
~a~kersfield, CA 93313 Re~°~t: 05-Feb-90
.Attention:
Lab No.: 776-8
~m~le ~esc: S-GE-6 Ga-~.oline T~ ~a~t ~ 6' 1/25/90 @ 1:50
Date 'Sample Date Sample Date Analysis
Collected: Received @ -Lab: Completed:
25-Jan-90 25-Jan-90 02-Feb-90
Miniz~n
Reportin~ Analysis Reporting
Constituent Unit~ ReSults Level
Benzene ug/g none detected 0.03
Toluene ug/g none detected 0.03
Ethyl Benzene ug/g none detected 0.03
p-Xylene ug/g none detected 0.03
m-Xylene ug/g none detected 0.03
o-X¥1ene ug/g none detected 0.03
Total Petroleum
Hydrocarbons ug/g none detected ' ' 2.00
TEST METHOD: TPH for gasoline by D.O.H.S.L.U.F.T. method.
Individual consti%uents by Modified EPA method 8020.
As Received Basis
Cotr~nents:
California D.O.H.S. C~rt. ~102
ENVIRONMENTAL ~
PETROLEUM J- J. EGLIN, REG. CHEM. ENGR.
· 4100 PIERCE RD., BAKERSFIELD, CALIFORNIA 93308 PHONE 327-4911
Purgeable Aromatics
(~L)
5400 ~ Ct Re~: 05-Feb-90
~ersfield, CA 93313
At~ntion:
~b No.: 776-9
~ple ~sc: S~-2 G~ol~e T~ West ~d 2' 1/25/90 ~ 2:O0
Date S~le Date S~le Date Analysis
Collected: Received @ Lab: Complet~=d:
25-Jan-90 25-Jan-90 02-Feb-90
. Minitel,
Reporting Analysis Reporting
Constituent. Units Results Level
~enzene ug/g none detected O. 03
Toluene ug/g none detected O. 03
Ethyl Benzene ug/g none detected O. 03
p-Xylene ug/g none detected O. 03
m-Xylene ug/g none detected 0.03
o-Xylene ug/g none detected O. 03
Total Petroleum
Hydrocarbons ug~g none detected 2. O0
'TEST METHOD: TPH for gasoline by D.O.H.S.L.U.F.T. ~t~.
Individual cons%ituents by Modified EPA r~thod 8020.
As Received -Basis
California D.O.H.S. Cert. $102
ENVIRONMENTAL
LABORATORIES, INC.
PETROLEIJ¥
J. J. EGLIN, REG. CHEM. ENGR.
4100 PIERCE RD., BAKERSFIELD, CALIFORNIA 933O8 PHONE 327-4911
Purgeable Aromatics
(SOIL)
.... Groundwater' 'Resole indust~ie.~ ........ ~--'~ .: ~- ~-'. ........ ' ..................................... ' .....
5400 Aldrin Ct Date 'of
Bakersfield, CA 93313 Report: 05-Feb-90 '
Attention:
'Lab No'.: 776-10
S~mple Desc: S-GW-6 Gasoline Tank West End 6' 1/25/90 @ 2:07
Date S~r~le Date Sample Date Analysis
Collected: Received @ Lab: - Completed:
25-Jan-90 25-J~n-90 02-Feb-90
Reporting Analysis Reporting
Constituent Units Results Level
Benzene ug/g none detected O. 03
Toluene ug/g none detected O. 03
Et?~l Benzene ~g/g none detected O. 03
p-Xylene ug/g none detected O. 03
m-Xylene ug/g none detected O. 03
o-Xylene ug/g none detected O. 03
Total Petroleum
Hydrocarbons ug/g none detected 2. O0
TEST METHOD: .TPH for gasoline by D.O.H.S.L.U.F.T. r~t?~d.
Individual constituents by M~ified EPA r~t?~x~ 8020.
As Received Basis
Co~nts:
California D
.O.H.o. C~rt. ~102
ENVItTONI~£NTAL
LABORATORIES, INC.
PETROLEUtl J.J. EGLIN, REG. CHEM. ENGR.
· ~ 4100 PIERCE RD., BAKERSFIELD, CALIFORNIA 93308 PHONE 327-4911
BTXE/TPH GASOLINE
Quality Control Data
~d~t~: Res~rce';~lndus~tries ?.~'?~--~ ...... : ........... :::-~':;SPi~-"-~.3:'~76_8::~': .... ~ ..... .--?'=---=--:::::'~' ~
5400 Aldrin Ct Analysis Date: 02-Feb-90
Bakersfield, CA 93313 Sample Matrix: Soil
Attention: Units: ug/g
,Quality Control
for Lab Nos: 776-1, 776-2, 776-3, 776-4, V76-7, 776-8, 776-9
776-10
Dup
Spike Spike Spike
Constituent % Rec % Rec RPD
"Benzene 71.77 75.61 5.21
Toluene 72.62 75.97 4.51
Ethyl Benzene 74.14 78.47 5.67
ENVIRONMENTAL
LABORATORIES, INC.
PETROLEUM J' J' EGLIN, REG. CHEM. ENGR.
4100 PIERCE RD., BAKERSFIELD, CALIFORNIA 93308 PHONE 327-4911
GROUNDWATER RESOURCE.INDUSTRIES Date Reported: 02/07/90 Page 1
P. O. BOX 9383 Date Received: 01/25/90
5400 ALDRIN COURT Laboratory No.= 776-5
BAKERSFIELD, CA 93389
Sample DescriPtion: PROJECT #150010-2:S-WO-2 WASTE OIL TANK 2' 1/25/90 @ '1:38 SAMPLE
COLLECTED BY: CLAUS ENGELHARDT
~ TOTAL CONTAMINANTS
.i-' (Title 22, Article II, California Administrative Code)
Constituents sampl~ Results P.O.L. Units Method Ref.
Lead F/ 9.81 3.5 mg/kg 6010 1
TOX None Detected 20. mg/kg 9020 1
Oil & Grease 70. 20. mg/kg 413.1 2
Requlator¥ Criteria
Constituents STLC, mq/L TTLC, mq/kq
Lead 5.0 10001
Comment: Ail constituents reported above are in mg/kg (unless otherwise stated) on
an as received .(wet) sample basis. Results reported represent totals
(TTLC) as sample subjected ~o appropriate techniques to determine total levels.
P.Q.L. = Practical Quantitation Limit (refers to the least amount of analyte detectable
based on sample size used and analytical technique employed.
N.D. = None Detected (Constituent, if present, would be less than the method P.Q.L.).
I.S. = Insufficient Sample
STLC = 'Soluble Threshold Limit Concentration
TTLC = Total Threshold. Limit Concentration
REFERENCES:
(1) "Test Methods for Evaluating Solid Wastes", SW 846, July,' 1982.
· (2) "Methods for Chemical Analysis of Water and Wastes", EPA-600, 14-79~020.
ENVIRON¥£NTAL
LABORATORIES, INS.
PET/~OLEU, M J' J' EGUN, REG. CHEM. ENGR.
4100 PIERCE RD., BAKERSFIELD, CALIFORNIA 93308 PHONE 327-4911
GROUNDWATER RESOURCE INDUSTRIES Date Reported: 02/07/90 Page 1
P. O. BOX 9383 Date Received: 01/25/90
5400 ALDRIN COURT Laboratory No. = 776-6
BAKERSFIELD, CA 93389 .
Sample Description: PROJECT $150010-2:S-wo-6 WASTE OIL TANK 6' 1/25/90 ,'@ 1=40 SAMPLE
COLLECTED BY: CLAUS ENGELHARDT
TOTAL CONTAMINANTS
(Title 22, Article II, California Administrative Code)
Const£tuents Sample Results P.Q.L. Un£ts ~[ethod Re~ ·
Lead ?. 2! 3.5 mg/kg 6010 1
TOX None Detected :20. mg/~g 9020 1
Oil & Grease 152. ~0. mg/kg 4~3.
Requlator¥ Criteria
Constituents STLC, mq/L TTLC, mq/kg
Lead 5.0 1000.
Comment: Ail constituents reported above are in mg/kg (unless otherwise stated) on
an as received (wet) sample basis. Results reported represent totals
(TTLC) as .sample subjected to appropriate techniques to determine total Levels.
P.Q.L. = Practical Quantitation Limit (refers to the least amount of analyte detectable
based on sample size used and analytical technique employed.
N.D. = None Detected (Constituent, if present, would be'less than the method P.Q.L.).
I.S. = Insufficient Sample
STLC = Soluble Threshold Limit Concentration
TTLC = Total Threshold Limit Concentration
REFERENCES:
(1) "Test. Methods for Evaluating Solid Wastes", SW 846, July, 1982.
(2) = "Me~hods,~foD Chemical Analysis of Water and Wastes", EPA-600, 14-79-020.
I>, 5400 Aldrin Court
~ groundwater resources, inc. Bakersflield, Califorhia 93313
~:. TelephOne: (805) 835-7700
CHAIN OF CUSTODY RECORD ' Tele-;Fax: (805) 835-7717
LAB DEST~INATION: IpROJECT NUMBER.J~_~O/O~._~_ : --
'i ....... PROJECT CONT',CT: ...~ C-(r.~ .
SAMPLER(S)i (SIo~ture) z ~ :,
~ ~ ~ ~ · COUNTY: ~ ~
LAB ~ SAMPLE z ~ ANALYSIS i,i ISAMPLE coNTAINER
NUMBER~ NUMBER DATE TIME SAMPLE LOCATION ~z
o REQUESTED ~ TYPE TYPE
.~. r-,~-a /~o I,'~> ~,~.~.~~a~ CF~. ~ ~-0/,~ ~ .z~,/
_lo. 5-~w-~ /-~r-¢o 4:07~rolt~,~?~,g~' ,, ~' ,, ? ~ ~ ro, i
': ~" I
.SPECIAL INSTRUCTIONS:_ U~ ~
,,.;
POSS I BUE SAMPLE HAZARDS" ',t~
1. RelinqOlshed by: ~L. atelTlme:l-~-~O Received by: -~ ~; Date/Time:
1. Rellnq~she~ ~: Date/llme: Recelve~ ~: '~ :~ Date/lime:
1. Rellaqb~sheO ~: ~ate/l~me:. Recelved ~~ ~:~ ~ate/llme:
1. Rellnq~lsheO ~y: ~ate/llme: ~ecelve~ ~: [~ Date/lime:
CCR (Rev. ~1 A/SO) ~ITE: LABORATORY PINK: ,~AR FII F YFt I AW: 'SAMPl F I AG ~ ,..~ ,.~, ~ ~"r~r~. ~,~
'~'~ ~;~r'~'~ ~'~'~ Toxic ............................... Subnlancns Con.ol
~[: "'~'-~,- and Front of Pi 7 Sac,amenlo. California
~k UNIFORM HAZARDOUS ~aner. Iof'. U~ EPA 'D No. ' ~ M.nile., 2. P.,.S ~
' D u n o ~ Inlormalion ~ I~e s~e~e~ area~
WASTE MANIFEST ~ ~ ~101012~ 12i71611 Ol~i~l~ I o,
10 ! i~ eel ,equ~e~ ~ F~de~al law.
71 I' EAST 19~ ST~ET, B~FIELD, CA 93305 e. smnaa,,,,~o,',~ '.
5. Tranlpo~.l t C~pany Name 8. US EPA ID Number C. Slate Trans~er'l ID ~
OUAY, T~ VACU~ SERVICE, INC. lC IA ID 19 18 l0 18 I ! 18 17 10 12 0. Trmnn~o..,',P~n, 805=589=674 1
I I I I I I I I II~1 F. Trlnnp~.'l P~ne
.. ~.. Di~i~lle4 F~ay N~me and Sile Add,ertl : .:~.. ~::-T::::T~.:j:!O.-:=:~.-T-:EUS EPA ID .................... Numbet:__~ :___...:__:._ ~ SlnllFiclil~'&~-
C~SON 0~ & ~N~NG CO. ~ ~ ~ IDg ~ I~1~1~ 1~171
B~RSFIELD! CA 93308 ]CIAIDI9181018,18131,11117 805-327-0413
12. Conli~ell 13. ToIli 14. I.
11. US DOT Dem~ipli~ (Including Proper ~hipping Neme, ~zar~ Gll{I, i{ I~ NumbeO Qu~nlil~ Unil Wa~le N~.
No. Type . ,, WI/Vol
C~IFO~ ~G~TED ~ 0~Y
E b. ~lala
A. EPA/~h~
T
o I I I I I I I
R c.
EPA/~h~
I I I I!11
EPAI~
J. ~dili~ll De~ipt~l I~ MiI~Itl Llated ~ove ~ ~lmg C~ea I~ Wnnlel LiaI~ Above
5Z - WAS~ OIL/GA~OLI~ c. d..
15. Special Handling I~~lional Inl~mnli~
PROFILE ~( 8245~ '
· GENERATOR'S CERTIFICA~ON: I hereby declatl thel I~ coallBII Of Ihil c~ignment are lully a~d accu, alely de,cribe4 above by prope~ shipping name
nalionil govel~enl iegulelionl.
If I am a le~ge quanlily generaIol, I ce~ily lhal I have I protein in place lo reduce the vol~e an~ loxicily el wasll generale~ to Ihe deglee I have detelmine~
lO be OGOflomicifly p~nCliCiDIo arid thai I have lOliclld I~ pflGliClblo melh~ of Iroalmonl, IIO[lgl, ~ dilpOlll CUfllfllly available to me which minimsze8 tho
prlll~l lfld lutwo Ihroll Io hu~la health and the eflvifo~eflt; OR, ii I am I small quialily oefleralor, I have ~ide i good leilh ollofl Io miflimtze my wasle
oeflefilion end 8elecl lbo best wa~le menaobmefll method that i8 ivlilibtl Io me and Ihal I clfl iliad.
Prinledllyped Naml I ~ignalure ~ Monlh Day Year
' ,ll
T 17. Trana~o~er t ~knowled0emenl el Receipl el MeleJiali
0 18. Tlanspo~el 2 Ac[;lowiedgemenl of Receipl el Maietilil 'v ---
~ ~rinled/Typed Name ] Sionalu~l Month Day Year
E
~. , I I I ~ I I
19. Discrepancy Indicalion Space
I
L
I 20. Facility Ownef ~ Operalo~ Codification of ;eceip{ el haza;doul male;iala covered by Ihil manileal excepl aB holed in Item I~.
T
~ ' PHnled/Typed'Naml '" ] St~aI~t ........ ~ ." .......... : ........ ~ ......... Month Day Year
OHS a022 A (=/~) ~ Not Wrile ~low ~i~ Line
EPA ~7~22
(Rev. a-88) P~evioua edilio~s are obsolele. ~Jle= ISDF SENDS THIS COPY TO ~HS WITHIN 30 DAYS
..... '~" '. '.';' :~:~'-i:'¥~:''::~ Bakerlfleld, CA 93301
'~"q '~" :,Agency Director '. '.~"' - :': ':i':'~:,' ~ . ":: :" · 'i :' i~':: ::':~':~ ::::': '::.' ' ':: ..... '":
:: .',-. '~q~:i:'.~?i!:,':,,'(605) 661-3502 .'. ;. ':' .' .'.., ? ' -:,',!,.; ~:: :-~ ...... '::'~.:,.~:i"-'i:~:~:..:;.~,": ,;:':*' ..........' "' - ' ::" :~ :.': ?: :':~..L:~:~:~:~:-Telepho~ (605) 861-~
· ~:~..~?..~ :: ~...~ ~,~ ?:. ~-: ~..::: :..:.~:...'-~ .~: :-:-::~'.....~' ~ :~,':.~,?'~.-. --~... '~. :'~:: _ '?:'.. ~:f~:~'.~:~?Telecopler.~...;.,,.., (805) 861-3429
A
R. Crumpler;
- r 2. ' Permitt~ must notify the Hazardous Materials Management Prog~m at (805) 861-36~ two working days prnor to tank ~moval or abnndonmen
,3. -Tank cl~ure nctiviti~ must be per K~n County Environmenlnl H~lth and Fire Department approved meth~s as d~b~ in Handb~k UT
.:.L;' %':-::[4. [::':' It is ~hc ~ntractor's r~p0nsibility to know and adhere to all applicable la~ regardin~ the handling, t~nsportation or t~tmcnt of hazardou:
.2. :: ',~ ~. ",::~ Thc tank removal contractor must have a quailed ~mpany cmploy~ onsite sup~ising the tank removal. The employ~ must have tank ~mova.
6. . ~ any contractom oth~ than thee listed on permit and permit application are to be utilized, ~gor approval m~t ~ ~anted by the specialis
:~: :', '-.: ?.' a. t.:[~..:~,., Tank s~ze 1~ than or ~ual to 1,000 gallons - a mm~mum of t~ samplm must be retg~ed [rom ~ncagh thc'~nt~ of the tank at depth:
[;,:~:..::"t~ ?'::,i~C,~'~:b. :~,~lt:';Tank size ~t~ than 1.~0 to 10.~0 halloas - 'a. minimum' ~ four samvl~ must ~ retgeved one-third ~ the way in from the ends o
I ' ',', .: .',:~[" ':" c.' ': :'.? ~[~" Tank size ~eat~ than 10,~ gaHo~ - a minimum of six sampl~ must ~ retg~cd on-fourth of thc way in from ihe en~ of each tan~
PERMIT FOR PERMANENT CLOSURE "' -
range of
C' .:'-.~.""; "'"' -;:~':' --. ;~;: a .... ',.?,.~!Z'.'~'Liquid shall be pumped from tank prior, t0. purging, such that less than S 'gallons_ 0f li'q0'id ~emnin'i~ ~nk" '. (CSH&SC
.,.?~,~ .~;~i,;~,.~i~,?,.b. ~;~;~.,! ~ank shall ~ pur~d through vent p~ dlschar~ng at least 10 f~t a~ve ~und level. (CSH&SC 41700)
~:~.'~. :~e. ".~'~.::~. No emi~ion shall ~uit in odo~ det~table at or ~vond nro~v ~-~ ~o.,,, ~.o, : ~='~:'~ ~-.-'.::.?~
..:., 5~,~L~;~.~ 57,~d. ,~,~, :No emerson shall endang~ the h~llh, safety, comfort of rede of any ~n. (CSH&SC 41700) '~;~'~:~
.. ,. :; ~.....=. ..= :~; :.Veal hn~ shall remmn attach~ to tank until the msp~tor a~v~ to authorize ~movaL . ;',~ ~,~??~;
':(~ ~CO~A~ONS/GUID~S FOR ~MOV~ OF U~ERGRO~ STOOGE T~S '~
.?-2~ Th~ department is r~ponsible for enforcing the Ke~n County Ordinanc~e~ Div~ion 8 ~nd state ~gulntions p~taining to und~0und storage tanks.
...'~.?(~(~.'Repr~enlativ~ {rom this department ~nd to job sit~ during tank removals to ensu~ that the tanks n~:safe to ~move/clme and t~nt 'lhe overall
-": :~.':~';' job ~fformance is consistent with permit r~uirements, applicable la~ and safety standards. The follo~ng guidelin~ n~ offered to ~aflfy theinl~ts
and exp~tations for this department. .. .. ...~ ..,~...
' 1.. Job site safety is one of our prima~ conc~ Excavations a~ ~nh~ntl' ' -dan ~o ' ' '" ~ ''~ ...... ~' '- ": '~:':;~'~'~'
'?' ' ' ': C~ ..... ' y g us. It ~ the ~ntractor s ~po~ibility to know and abide by
?~ ~:~=~?;.:~ -~ ~gmations. The job foreman is ~ponsible for the crew and any subcontracto~, on the job.. ~ a general rule worke~ are not
' .~",,'~ "/'~ ~:-~ permitted in impro~ly sloped excavatio~ or when unsafe conditions exist in the hole. T~ls and ~uipment~ are to be used only for the~
d~igned
'~,~ ..~;~"~ ~: . :function. For example, backh~ buckets are never substituted for ladder. '-' ::'... ...... ~ .-? .;~' .., ,~ ~. ~:.:~?~, :;
2 Prop~ly h~nsed contracto~ are assumed to unde~tand the r~mrements of the permit ~ssued. The job foreman ~s r~pons~ble for knowing and
~...': -.... ,. ~:~ abiding by the conditio~ ~ the permit. Deviation from the p~mit conditions may r~ult in a stop=work' ord~.
~.,,/=.....- :=.+,...,..=,. . .~.~.,-;:: .. ,.....~.y??~.~ ~- .~:~=~....~, .. .-~..>~?~,,......-.......~.~.,.~:~., ....... ~:~`:.~..?~?~:~=;~.:~.a~?.~.=~;~.~.-~?.:~?~.:..~.~
~,,~:~.~.~....::..I~d~v,dua! ~nt[acto~ will be held ~pon~ble for the,r p~t-removal pape~ork. ~raeking Iorm,, ha~a~ou~-~te
~:~*->9,~:~,,~[~ :~?~umentat~on ~ n~a~ for ~aeh ~ite in ord~ to cl~e a ca~e file or move it int~ mitigation~ ~'Wh~n ~ntraeto~ do not foilo~ throu h on
~;'t~5~}~':?5}~:~:'nec~ary papemor~, an unmanageable ~acklog ~ incomplete ca~ r~ulu. I~ thi~ ~ntinu~~, pr~ing tim· for mm~letin n~w ~l~ur~ ~il
.. . , . · ' . ' '..' ' - '-'" ' · ". ",. '~.:~-~'L.- ...~':-~:~:::,?.
· · . ....... ,+ '~., ..... : . , '-'.'? ,' ~'. ~., ..~:','~' X',Y,~ ~-~," .,~:.: ~;~ 'L'. ,,Z~.'.. ',' '-. , , :;. ~ =:.-~ '-L;-(J.:-~ ., ' .2,..:.~"/~;~...-..'~..C~.,C~:-~ .:,~,~-%~;~y.=~:~;~-~.
APPLICATION FOR PERMIT POR PERCENT
HAZARDOU~ SUBST~CE8 ~TORAOE ~FACILITY .....
I
~ Jim Elder 711 E. 19th Street Bkfd.'
I '
1-2 -9o / 520768 ! 0793S~9 I State Fund
~ Groundwater Resources, inc. 5600 Aldr{n'CC., Bakers~{eld ~805~835- 7700
' ~RKER'9 ~P~SATION ~ IN$~ PHONK
4~000 Unleaded Gasolio~ ~~ 1987
' 200 Waste Oil 19~2 ,~ 1987 Waste Oil
Southern California Water Agency ! 200'
Well at Truxtun & Kern (+500.') I Alluvial Sands & .Silts
Site inspecti'on & Kern Co..Water AsencY
~~~m~~ ~m'~~~: Gas: BTX&E and TPH (Gas) 12 ~ W.O. Oil & Grease~ Tox~ Lead
~R, Ontario, California
· z~ Pro~ect Manager DA~ 1'-16-90
PROVIDE DRAWING OF P '
ALL OF THE FOILING INFORMII?ION MUST BE INCLUDED IN ORDER F~APPLICATION E
PROCESSED: .-
TANK(S)', PIPING & DISPENSeR(S), INCLUDING LENGTHS AND DIMENSIONS
PROPOSED SAMPLING LOCATIONS DESIGNATED BY THIS' SYMBOL "(~"
NEAREST S~ OR INTERS~.CTION ·
ANY WATER WELLS OR SURFACE WATERS WITHIN 100' RADIUS OF FACILITY
NORTH ARROW .... · ..... :~,...-... ~',_~ .................. ~ .........................
FENCE
· 4,000 GALLON
' ~ I , STORAGE TANK
· - 200 GALLON
CONCRETE SLAB [ 12
20'
BUILDING
OFFICE BUILDING
~) VENT ------ PRODUCT LINE
· BORING LOCATIONS ..... · VENT LINE
[] FILLBOX
E. 19TH sTREET
PLATE SEQUOIA PAINT
groundwater resources, inc.
~! 700 BAKER STREET
.... .. . ~ , ~ BAKERSFIELD CALIFORNIA .......... environmental/geotechnic~,sefviceS
PI,OT PLAN , ,Project Number: 150010-2
· i: 0.!/17"zg0 :" .... :.....; .-.
' '1 4 ;'05 '~P~" :.': :KERN" COUNTY P'EA~N ~NG & 'DEVELOPNENT" ": '::: .:'.:":' : .' h . ...... ':. :.:" .'"~":"? ~/'~:::'"'::~'..' ":~.'~'?:~;'~:"1"
' I- .'- :."?'"::' ' ': -. '~ 2,00 ~: st~.~t · .' .... '.:':'-::"."~.':'.'::;::~:..:..'. ~ :.:'::'.:-~-.;;~':....~"'.:~7:'~'....:.?.':[:::
. : "'~:~::?~:;~:~?' :: :' ' '".. "." B,'~eesf ~ eld ," 'CA' :.,.:9:330.1 .' .. "?~: ~' ~.-Ty.~®.~:0~ ( Order -..' :"--.::?~::~(:~ ~,,."..: '?.':"(-~':~'~ ?':-'.
' .-': ":::;;~'~'~,?~L
- ..... I '-"~
' . ~ . ~. ~ ~.~%~:J;~4:~,:"~...':,:~.,-.:..? .~ ~ ..... ~'] -' .... -'?-t:"'~ ...... :' ':c ~: -:'.??~:'~t-'-"-':. ,:~.,~.~:;:: .... . - :'~'~"- :'.,:~z~-.-~/,.~,~';)~.':~:::~:~ ':~,~,;.:.' :.-"~, -:~,?.:'"m:,:-'?,~" .~:~';~'~"~2C?~,- ..' ·
' ~,.? .:~-'~'~ :~.~ ~ ~':~ ,~','
. ~ --: ':,-~:.~¢'~7:~:~.:?'
HOl1790-3 ' I NDJ I 01/'17/90 I 01/17/90 '. - . ' .... I... N~ .. : . I
·-I
*a~ ~La~' C,~C~ .. ..- .~ ~ '.~:..,~:..~ ~ ~.'"',~:0'0.00,.~:.~~ ....4'..:.(?~.'~:.~00. ,00
~70~ ' ''
O~de~ Total 100,00
Amount Du~ ..100.00
I~ P~yment N,de By Check i00 O0
THANK YOUI , .. -:,
DUANE R. SMITH
AND ASSOCIATES
'Registered Geologist No. 3584
7201 Fruitvale Extension
Bakersfield, California 93308
Telephone (805) 589-7861
May. 23, 1990
Ms.~Flora Darling
Department of Enviro~ental Health Services
2700 M Street, Suite.300.
Bakersfield, California 9~3'01. ' ...... '" .... '" ...... "~ ....... '
Dear Ms. Darling:
Enclosed please find one (1) copy of the Site Characterization
Work Plan, Sequoia Paint Company, 700 Baker .Street,.Bakersfield,
California, May 1990. The facility permit number is 150075.
If you have any questions, please feel free to call.
Yours truly,
Thomas F. Gutcher
Staff Geologist
TFG/jk
Enclosure
DUANE R. SMITH
AND ASSOCIATES
7201 Fruitvale Extension ..... ',.
· .. o ............................. ~_. Bakersfield, California 93308 " '
~-- ~:--~ ..... (805)'~ '589-7861 .........................................................................
~..
TABLE OF CONTENTS
Pa~e
Site Background ................... · . .1 - 2
Preliminary Site Assessment Results ........ . . 3 - 4
Soil Sampling Plan .................... ~ - 9
Phase I .... , ....... . ' 5 - 7
Health and Safety Considerations ............. 9 , '"":'
Exhibits
Figure 1 Location Map -.-
Figure 2 Plot Plan
Figure 3 Site Map
Figure 4 Test Hole Location Map
Appendix A Preliminary ,Site Assessment Results
Appendix B Health and Safety Considerations
SITE CHARACTERIZATION WORK PLAN
SEQUOIA PAINT COMPANY SITE
SITE BACKGROUND
The Sequoia Paint Company site is located at 700 Baker Street in.
Bakersfield, California. The-site is situated in Section 29,
· T.29S., R.28E.., M.D.B.&'M. (see Figure 1). The site is used for
the distribution of paint and related products. The general area
is commercial and residential~ The facility permit number is
150075.
The Sequoia Paint Company moved their showroom facilities to the
property during the past several months. Mr. Jim Elder of Sequoia
Paint researched past building permits and reports that Wally
Tucker Datsun constructed the current buildings in 1966. Wally
Tucker Datsun occupied the site from about 1952 to 1985. The
property was vacant after 1985. The property reportedly was vacant
prior to 1952 except for a small fast food outlet which may have
occupied the site in the 1940s.
Two underground storage tanks were removed from the property on
January 25, 1990 by Groundwater Resources, Inc. (GRI). A 4,000
gallon unleaded gasoline tank and a 200 gallon waste oil tank were
situated on the property approximately as~shown on Figure 2. The
gasoline dispenser was located in a small closet along the west
................ ~g~_g~__t_he.~ain ~ui~dingis~e_Figure__2) ........ Theproduc~_!iDe,_ran ...........
3EZ]E]
SCALE 1:24000
I ½ 0 I MILE
ll~O ' 0 1000 ' 2000 3000 4000 5000 6000 7000 FEET
J 5 0 ! KILOMETER
.............. 7 0 0 BAKER STRgt~.T
BAKERSFIELD, CALIFORNIA
Source: U.S.G.S. Oildale, Oil Center, Gosford, and Lamont 7½ Minute Quadrangles.
- Figure 1
GASOUNE TANK
,,~,,._~ 4000 ~LLON
E OV
_. _ -T~ Z'Z ". '~ -. '"_L....'_ -L- . - -
~:.:~.:~``:~....~.:.~.~`~`:.:~````~.`~....`.~`.~`.:.:.:.x...:.:`.~:<~.>:<.::::...q~:~.:~.:.:<`.:...~.:.:.:.:.:.>:.:.:.:.:<.:.:.:.:~.:.:.:<.:.::.:... ....
'' Ij~:~:~:~:~.:~.]~.~....~[~:`~:~::.~::.~[:...:~`~:~..`:~:::~..i~L.~*~===============================================================
.,. ,, ,, , .......... ,; .............. ....... ....................... ...............................................
I: :::::~--':.':., ~ ~ :: ::; :-':::::': ~ :.'::: .':::::.,' .~,~,-~..~ ~:N..~:~: ::~?~:~B':.'.i::..~ f: .".'.::~. :::-'::S::.~-~;.': S::'.L-.': :: :::$ :-'::: ::::: ::::.-::-'::::::: ::;::::: :::::: ::::~ :~-:: :::;:;:;:.:
. l f l ~ Ij · I ::-:~::~:"-:-':~-""~s'-'~ ~::~.~!~::""~ :;:-~:-: .... .-:::.-.-::,,:::.::~::~.::::.,.':.~:s,.,,...-~:.-:::::::.~:::s- :.:,~::::~:::~: ,,~::~::~: :::., ~:s:~mm~:,::::~,::::~' ::::::: ::: {!:i~ii~i:. .....................
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~~ ~ WASTE OILTANK
200 GALLON
(REMOVED)
1 IN = 12 FT ::~:.-.~::.::...',~:~,~.~:~:.m:~.:.'.::~:::::::::::::m::::::: .............. .-...:..:~::m:::::::.,. ..................... .s:::::::::::::::::::::::::::::::..~::;.:::::::::::~.::.t.`:::*:~`.m:*::::::::::.:.:~;: ............... .~::..:
· :::"::::"'::::':'"':¢::':':':":;:::::: ::::::::::::::::::::::::::::::::::::::::::::::::::::: ..................................... I:, ~ ~L ' ..... ..~i.~i?~.i~.:~..~.!ij.~.i~.i.~.i~.!E.!.~.......~.......~....~.....~..~...~.~.~....v.....~.....~..~...~ ......
~.:....+:.::..:~.~>:.....>:.x....[~.:'.x..*..`:::~.~..`.:~::..`:.:.:.::::::::::::.:.~.:.:.:.:.:.:::...:~...:::::.:.:..::::.:.:.:.:..:.:..:......:::.::.~:::....:::.:[.~...:.:...>.q~.>*:~.>~::~:: ~:::...:..' :.< ....... :.:.........-_.,:.:..:....:. ................... > ...........
~i:,-.'?,:,:,:'-:: :,.,'>' i.,:,:,:,.:':'.'~ ::.-": ::-:-':~::-<:: .~::..-~..':*":.'~.-...:. !.?:. :. !. :. !. !.:. :. !. :-~, ~ ~ ~. !.~. >~-> ~-~.!.!-!.!. !.!.!.~. :. ~. :-~. ~. ~.?. :. ?:. !.:-:. :. !.~. !. !. !.~.':.~-~'.:': ~. :. ~.~.'.:. [-:. :. :.7:[. :. :.':.:~.:. :':'..?..~: [.'." !. > ~ :. :. !:!:!~ ~: !::)::: :"-::::!:::": :: :::::::: :: :: ::: 5: :: :: ::::: :: ::::::: ::: :::: ::::: ::: ::::::: :: :::::::: ::: :::::::::::::::::::::::
SEOUOIA ~AI~TI~G
700 B^KER $1Rfi~l groundwator r~our¢o$, inc.
BAKERSFIELD, CALIFOFINI^
........... on¥imnmontal/gootochnicat
....... PLOT PLAN ~roiect Number:~s0o,0-2
: Fi guro 2
directly between the tank and the dispenser as shown on Figure 2.
The tanks were made of steel and reportedly were installed in 1982~
and removed from service in 1985. Figure 3 shows a more extensive~
and.more detailed map of the site'
· There are no known rePorts of discrepancies or reportable variations
in inventory monitoring, failed tightness tests, repairs to tanks
or piping, or past leaks.
According to the Geol°gic.Map of California, Bakersfield Sheet,
the sediments underlying the site consist of Quaternary fan deposits
comprised of sediments deposited from streams emerging from
highlands surrounding the Great Valley. In general, these deposits
consist of unconsolidated, poorly sorted sitt, sand, and gravel.
According to the General Soil MaP of Kern County, published by the
Soil Conservation Service, U.S.D.A., the site is underlain by
soiis of the Delano association. In general, "t'his association
consists of well drained moderately fine textured soils developed
in sandy granitic alluvium.
Based on the 1988 Report on Water Conditions, Improvement District
No. 4, published by the Kern County Water Agency, the depth to
groundwater beneath the site is approximately 220 feet. No perched
groundwater is known to exist beneath the site.
SITE MAP
.- SEQUOIA PAINT
700 BAKER STREET
BAKERSFIELD . CALIFORNIA
CANOPy --CUffs
NOTES: 1. Both .tanks, dispenser, and product line removed from site.
......................... 2._._Gasoline tank had a,-4,000 gallon capacity ......................
3. Waste oil tank had a ?-00 gallon capacity.
DUANE R. SMITH & ASSOCIATES -- lW~t~Y 1990
FigUre 3
SITE SPECIFIC PLOT PLAN
The site specific pl°t plan (Site Map) is included as Figure 3.
· The analytical results and chain of custody record from the Prelim-
inary Site Assessment are included in Appendix A, pages A-1 through
Laboratories for analyses. Samples associated with the gasoline
tank were analyzed for T.P.H. gasoline and B.T.X.& E. Samples
associated with the waste oil tank were analyzed for T.O.X., total.
lead, and oil and grease. The sample'locations are shown on
Figure 2.
Sample S-D-2 was collected at a depth of 2 feet beneath the
dispenser. No T.P.H. gasoline or B.T.X.& E. were detected in this
sample. Sample S-D-6 was collected at a depth of 6 feet beneath
the dispenser. This sample reportedly contained 935 ppm T.P.H.
gasoline and moderate levels of xylene.
Samples S-P-2 and S-P-6 were collected at depths of 2 feet-and 6
feet beneath the piping, respectively." No T.P.H. gasoline or
B.T.X.& E. were detected in these samples.
Samples S-GE-2 and S-GE-6 were collected at depths of 2 feet and 6
feet beneath'the east end of the gasoline .tank,._respectively ........
3
Samples S-GWU2 and S-GW-6 were collected at depths of 2 feet and 6
.feet beneath the west end of the gaoline tank, respectively. 'No
T.P.H. gasoline or B.T.X.& E. were detected in any of these samples.
~:":~pi-e~s::'¥~'2Wo-2'and S2WO~6 were Collected at depths of 2 feet and 6
feet beneath the waste oil tank, respectively. Sample s-we-2
reportedly~contained 9.81 ppm total~lead and 70 ppm oil and grease.
'~.[
Sample S-WO-'~ reportedlY contained 7.'21 ppm total lead and 152 ppm
'~:~"i-a~d gf~a~'}- .... N6T:,o.x. was detected'in either sample.
These results indicate no significant contaminatiOn beneath either
tank °r beneath the gasoline piping. However, significant gasoline
contamination is indicated beneath the former dispenser location.
Subsequent to receiving the Preliminary Site Assessment results,
one hand auger boring was drilled by GRI at the former dispenser
location to a depth of 14 feet. Soil samples were collected at
depths of 8, 11, and 14 feet. Details of the sample methodology
are not known. The 8 foot sample reportedly contained 4,100 ppm
T.P.H. gasoline and moderate levels of B.T.X.& E. The 11 foot
sample reportedly contained 1,700 ppm T.P.H. gasoline and moderate
levels of B.T.X.& E. The 14 foot sample reportedly contained
1,900 ppm T.P.H. gasoline.and moderate levels of B.'T.X.& E. The
analytical results and chain of custody record from this test hole
are included in Appendix A, pages A-13 through A-17.
SOIL SAMPLING PLAN
· Phase I
Since the tanks and plumbing were relatively new and were in use
for only three years, we feel there is a good chance that the
contamination is not very 'extensive. For this and o~her reasons,
......................... ' ' ' " er test _~
The other reasons include difficult drilling rig access .(see Figure
3) and the proven ability to drill with a hand auger at this site.
Furthermore, recent drilling experience nearby suggests that the
sediments to a depth of 35 or '40 feet can be readily penetrated.
Three soil borings are proposed to assess the vertical and horizontal
extent and the' degree of contamination at the former dispenser.
location. Figure 4 shows the locations 'of the three test holes.
Test Hole No. 1 is .located near the presumed center of the
contamination. The intent of this test hole is to provide data
necessary to determine the vertical extent of the contaminant
.plume. The other tWo test holes are perimeter borings to provide
data necessary to ~determine the horizontal extent of the contaminant
plume. The exact locations of Test Hole Nos. 2 and 3 may vary
slightly depending on the results of Test Hole No. 1. Test Hole
lOcations 'at the site are limited because ~f structures.
The borings will be drilled until the maximum vertical extent of
~ontami~ti°n 'is 'exceeded or "to ~e maximum p~et~able depth. If
5
TEST HOLE LOCATION MAP
,' SEQUOIA PAINT
7 O0 BAKER S~TREET
BAKERSFIELD. CALIFORNIA
~'AS7' 19rt.l ~rRg&r I" = 30'
TEST HOLE LOCATION
DUANE R. SMITH & ASSOCIATES -- MAY 1990
Figure 4
it is determined from T.H. No. 1 that the vertical extent of
contamination cannot be exceeded with a hand, auger, Phase II of
this work plan'will be'implemented.
..... Soil samples will be collected at 5 foot intervals.. Since a boring
has already been sampled at a depth of 14 feet in the immediate
'vicinity of T.H. No. 1, samples will be collected from T.H. No. 1
starting at a depth of 20 feet. Sample collection will start at'a
depth of 5 feet in T.H. Nos. 2 and 3.
The borings will be drilled with a 2 inch diameter hand auger
using 4 and 5 foot extensions. Soil samples will' be collected
with a hand driven core sampler. The core sampler contains one 2
inch diameter by 2 or 6 inch long brass liner. After advancing
the test hole to the proper sample depth with the hand auger, the
hand auger will be carefully removed and the core sampler inserted
into the boring. The core sampler will then'be driven into the
soil using a hand actuated impact hammer. The brass liner will
then be removed from the sampler and immediately coVered with
Teflon seals and polyethylene caps and taped shut with duct tape.
Each brass liner, after being sealed and taped, will be labeled
and placed in a polyethylene sample bag which will then be. labeled
and sealed. Each sample will be placed in an ice chest and retained
in a chilled state on'blue ice for transport ~o B. C. Laboratories.
The drive sampler will be thoroughly scrubbed, washed, and rinsed
between sample collections.
6
Selected soil' samples will be submitted to B. C. Laboratories and
analyzed for T.P.H. gasoline and B.T.X.& E. The quality assurance
and quality control of the laboratory is available from B..C.
Laboratories on request. Chain of custody records documenting
~a~Pi-e~-~andii~g- wi'li--~6~u~ed-.-~-~ ·~ ~ ·~-~-~.~-~.~.~ ....... ~.~ ........ ~ ............. ~ ........
· In addition, a second sample will be collected from each sample
depth for field screening and soil descriptions. Field screening
---'~"~"~i~-~6~S~S%~'~f'a'h~adspaCe . reading for hydrocarbon vapors with an.
Hnu PID meter calibrated to a.benzene standard. In addition to
the headspace readings, hydrocarbon odors, if 9resent, will be.
noted.
The test holes will be backfJlled with a cement-sand slurry mix.
Contaminated drill cuttings, as identified by field screening,
will be placed in DOT drums for future treatment or disposal.
Phase II
If it is determined that the methodology of Phase I cannot· provide
adequate data to characterize the contamination, Phase II will be
implemented. Phase II will consist of the same three boring
locations as Phase I, but the drilling methodology will be different.
The borings will be drilled to a maximum depth of 50 feet each.
If field screening indicates that the vertical extent of contamination
is less'than 50 feet, the boring depths will be decreased accordingly.
7
If the vertic-al extent of contamination is found to be significantly
greater than 50 feet, additional'borings will be proposed in a
Phase II work plan. Based on the judgement of the on-site geologist,
the borings proposed herein may be drilled slightly deeper than 50
feet-'if ~it '-appears'that the~ v~rtical--~'~~
only slightly greater than 50. feet. Groundwater should not'be
encountered in any of these borings and will not be considered in
th~s work plan.
soil samples will 'be collected every 5 feet starting at a depth of
5 feet except at T.H. No. 1 where sampling will begin at a depth
of 20 feet. Selected soil samples will be submitted for analyses.
The samples will be analyzed for T.P.H. gasoline and B.T.X.& E. by
B. C. Laboratories. The quality assurance and quality control of
the laboratory is available from B. C. Laboratories on request.
Chain of custody records documenting sample handling will be
included.
Soil samples will be collected using a split-spoon sampler driven
into the soil utilizing a truck-mounted continuous flight hollow
stem auger rig (Mobile Drill B-53). The split-spoon sampler
contains three two and one-half inches diameter by six inches long
~rass tubes.
The sampler will be driven through the proper sampling interval
after the hole is drilled with the hollow stem auger. The sampler
will then be removed from the drilling equipment and the brass
tubes removed from the sampler.
8
The ends of. ~ne tube from each sample depth will be covered with
Teflon seals and polyethylene caps and then sealed with duct tape.
The tube will then be labeled and placed in a polyethylene sample
bag and the bag sealed and labeled. Each bagged tube will be
....... L . -'2 ..... ~"~ '22z:: -~ ....
Laboratories for analyses.
Another soil sample from each sampl~ ~epth will be retained for
consist of a headsPace reading for hydrocarbon vapors with an Hnu
PID meter calibrated to a benzene standard. In addition to the
headspace readings, hydrocarbon odors, if present, will be no~ed.
The augers witl be steam cleaned between the drilling of each
borehole to avoid cross contamination. The sampling equipment
will be scrubbed, washed, and thoroughly rinsed between each sample
collection.
The test holes will be backfilled with a cement-sand slurry mix.
Contaminated drill cuttings, as identified by field screening,
will be placed in DOT drums for fdture treatment or disposal.
HEALTH AND SAFETY CONSIDERATIONS
The Health and Safety Considerations are included as Appendix B.
S~mitted by:
~ %~t - '' I IDuane R.. Smith
% ~ ~. , . / ; Registered Geologist
.. California.. 3584
~' Thomas F. Gutcher ·
Staff Geologist
SITE CHARACTERIZATION WORK PLAN
SEQUOIA PAINT~'COMPANY
700 BAKER STREET
BAKERSFIELD, CALIFORNIA
MAY 1990
10
. APPENDIX' A
PRELIMINARY SITE ASSESSMENT RESULTS
ENVIRONMENTAL
LABORATORIES, INC.
PETROLEU/~ J' J' EGLIN, REG. CHEM. ENGR.
· 4100 PIERCE RD., BAKERSFIELD, CALIFORNIA 93308 PHONE 327-491'1
Purgeable Aromatics '
(SOIL)
Groundwater Resource Industries'...:. ......... _.._ ...... Date~..of
.~::~.-m~.:_:--:'::::'--_-5400-. Aldrin Ct ........ :- ........ -'~ :~''~--'-':- -- ....... : ................ ' ............... : ..... RePOrt: 05-Feb-90
-Bakersfield, CA 93313
Attention:
~Lab No.: 776-1
S~r~le Desc: S'D-2 Disper,-~er 2' 1/25/90 @ 11:22
Date Sa~le Date ~le Date Ar,~lysis
Collected: Received@ Lab: ~ Co~leted:
25-Jan-90 25-Jan-90 02-Feb-90
Mini~a~.
Reporting Analysis Reporting
Constituent Units Results Level
Benzene ug/g none detected O. 03
-.- Toluene ug/g none detected 0.03
Ethyl Benzene ug/g none detected 0.03
p-Xylene ug/g none detected 0.03
m-X¥1ene ug/g none detected 0.03
o-Xylene ug/g none detected 0.03
· Total Petroleum
Hydrocarbons ug/g none detected '2.00
TEST METHOD: TPH for gasoline by D.O.H.S.L.U.F.T. rrethod.
Individual cor,-~tituents by Modified EPA :~t~d 8020.
AS Received Basis
California D.O.H.S. Cert. ~102
~ ~ ' ~°~ F~S
~,~,~ LABO RATO , I N C.
4100 PIERCE RD., BAKERSFIELD, CALIFORNIA 93308 PHONE 327-4911
Purgeable Aromatics-
(SOIL)
GrOundwater Resource Ir~lustries Date of
5400 Aldrln Ct ............................... ~: ....... ~-:. ~:-:. ~--,-?~ ..... -<.::Report:~-_~05-Feb~90' -..:-':: ....... :'~=-~ '- ~"'
':-::'~ 'Bakers field,'- C~ .... 93313 ............... '
Attention: ·
Lab No.: 776-2
~ -Sa~le Desc: S-D-6 Disperser 6' 1/25/90 @ 11:38
. t~
Collected: Received @ Lab: Completed:
25-Jan-90 25-Jan-90 ' 02-Feb-90
Reporting Analysis Reporting
Constituent Units Resulta Level
Benzene ug/g .... none detected O. 30
Toluene ug/g none detected O. 30
Eth~l Benzene ug/g '~ none detected O. 30
p-X,ylene ug/g 3.04~ O. 30
m-Xylene ug/g 4.95 O. 30
o-X¥1ene ug/g 24.56 O. 30
Total Petroleum
H~drocarbons ~_/g 935. O0 J 20. O0
'TEST METHOD: TPH for gasoline by D.O.H.S.L.U.F.T. method.'
Ir~!vidual cor~tituents by Modified EPA ~r~thod 8020.
As Received Basis
Co~r~nts:
Califorr~ia D.'O.H.S. Cert. ,102
A-2
I ES
LABO RATO , INC.
PETROLEU~ J' J' EGLIN, REG. CHEM. ENGR.
' 4100 PIERCE RD., B~KERSFIELD, CALIFORNIA 93308 PHONE 327-49~
~g~ble Ar~tic~ '
(~In)
G~wa~r R~~ In~stries ~ of
5400 Ai~.C% ....... ~~ ..... 05~Feb~90 .... ~<~:-r- .... ~---~--
~rsfield, ~ 93313 ........................ :
At~n~ion:
~b ~.: 776-3
~le ~sc: S-P-2 Pipi~ 2' 1/25/90 ~. 11:55
~" ' ........ - ........ ' ....... [Jax~e' S~ple Date Sample Date Analysis
25-Jan-90 .~ 25-Jan-90 02-Feb-90
Repor%ir~ Analysis Reporting
Constituent Uni%s Results Level
Benzene ug/g none detected 0 03
Toluene ug/g none detected 0 03
Et~,l Benzene ug/g none detected 0 03
p-Xylene ug=/g none detected 0 03
m-Xylene ug/g none detected 0 03
o-Xylene ug/g none detected 0 03
Total Petroleum
Hydrocarbons ug/g , none detected 2. O0
TEST METHOD: TPH for gasoline by D.O.H.S.L.O.F.T. rrethod.
Individnal cor~tituents by Mollified EPA r~tf~] 8020.
As Received Basis
California D.O.H.S. Cert. ~102
A-3
~'' ~°~ ~ i~ES
~,~,~ LABO RATO , INC.
PETROLEU¥ J' J' EGL~, REG. CHEM. ENGR.
4100 PIERCE RD., BAKERSFIELD, CALIFORNIA 93308 PHONE 327-4911
Purgeable A~¥~:rmtics -
(SOIL)
Grour~water Resource I~ustries Date of
.r Attention:
Lab No.: 776-4
.... S~ple Desc: . S-P-6 Pipir~ 6' 1/25/90 ¢.~ 12:09
Lk~te Sa~le Date S~le Date AD~]ysis
C/~llected: Received (,~ Lab: . C~pleted:
25-J~-90 25-Jan-90 02-Feb-90
., Reporting Analysis Re~rting
Constituent Units Results Level
Benzene ug/g none detected O. 03
Tol~uene ug/g none detected O. 03
Ethyl Benzene ug/g none detected O. 03
p-X¥1ene ug/g none detected O. 03
m-Xylene ug/g none detected O. 03
o-Xylene· ug/g none detected O. 03
Total Petroleum
Hyc~bons ug/g none detected ~.o 00
TEST METHOD: TPH for gasoline by D.O.H.S.L.U.F.T. ~thod.
Ir~ividual cor~tituen%s by Modified EPA ~thod 8020.
A~ Received -Basis
CaIifornia D.O.H.S. Cert. ~102
ENVIRONMENTAL
PETROL£U¥ ~ J' EGLIN. REG. CHEM. ENGR.
4100 PIERCE RD., BAKERSFIELD, CALIFORNIA 93308 PHONE 327-491'1
I. Purgeable Arc.tics
(soil)
~ersfield, CA 93313
At~ntion:
~b ~.: 776-7
25-J~-90 25-J~-90 02-Fe~90
M~i~r~
~ Re~i~ ~alysis Re~i~
~ti~ent Uni~ Res~ ~vel
~ene ~/g none de~ O. 03
Toluene ~/g none de~ '~ O. 03
Et~l ~nzene ~/g none de~ 0.03
p-~lene ~/g none de~ O. 03
m-Xyl~e ~/g none de~ O. 03
o-Xylene ~/g none de~ O. 03
To~l Pet~le~
Hy~-~~ ~g none de~ 2. O0
TEST METHOD: TPH for gasoline by D.O.H.S.L.U.F.T. ~ret~'~d.
Ir~ividual constituents by Modified EPA ~%~d 8020.
As Received Basis
Oomrr.enl:~:
California D.O.H.S.. Cert. ~102
· ENVIRON~ENTA~
' LABO RATO S, INC.
PETROLEU# J.J. EGLIN, REG. CHEM. ENGR.
· 4100 PIERCE RD., BAKERSFIELD, CALIFORNIA 93308 PHONE 327-4911
Purgeable Aror~mtics
(SOIL)
Groundwater Resource Industries Date of
5400 Aldrin Ct ...... ~ ............
Bakersfi~id, -- CA -93313 ........... '
Attention:
Lab No.: 776-8
S~,ple Desc: S-GE-6 Gasoline Tar~ East End 6' 1/25/90 e 1:50
Collected: R~eiv~ ~ ~b: ~mple~:
25-J~-90 25-J~-90 · 02-Feb-90
~nsti~ent Uni~ Resul~ ~vel
~ene ~g none de~ O. 03
Toluene ~g none de~ O. 03
Ertl' '~nzene ~/g none de~ O. 03
p-Xylene ~/g none de~ O. 03
m-Xylene ~g none de~ O. 03
o-Xylene ug/g none de~ O. 03
To~l Pet~le~
~~ns ~g none de~c~ 2.00
'rEST METHOD: TPH for gasoline by D.O.H.S.L.U.F.T. ~mt~d.
Individual constituents by M~ified EPA ~mth~t' 8020.
As Received Basis
California D.O.H.S. Cert.'.102
' RATO ES'I
LABO , INC.
,OETROLEU¥ J.J. EGLIN, REG. CHEM. ENGR.
.. , 4100 PIERCE RD., BA~(ERSFIELD, CALIFORNIA 93308 PHONE 327-4911
Purgeable Arc.tics ·
(~)IL)
Groundwater Resource Industries Date of
._~m.~?.:.::::~:-_::::.~.:5400.:.Aldrin Ct -.:-:-_'-:'-?-.~-~'-::.:'-:'~:~:-: ~ ~;~:-:-:-_ __. ~_.. :~:. :.:~..:n .... Report: 05-Feb-96-''~-:~mn~:::-:--::~-n':-~ ..........
~Bakers£~e~d, CA 93313
Attention:
~b N0.: 776-9
~p~e ~se: S~-2 ~o~e T~ Hest ~d 2' 1/25/90
,
Date S~nple Date S~le Date Analysis
Collected: Received @ Lab: i:. Completed:
· 25-Jan-90 25-Jan-90 02-Feb-90
Mini~.
Reporting Analysis Reporting
Cons%ituent Units Results Level
Benzene ug/g none detected 0.03
Toluene ug/g none detected 0.03
Ethyl Benzene ug/g none detected 0.03
p-Xylene ug/g none detected 0.03
m-Xylene · ug/g none detected 0.03
o-Xylene ug/g none detected 0.03
Total Petroleum
Hydrocarborm ug/g none detected .2.00
TEST METHOD: TPH for gasoline by D.O.H.S.L.U.F.T.
Individual cor~tituents by Modified EPA ~thod 8020. '
As Received -Basis
Coffn~nts:
California D.O.H.S. Cert. ~102
~ ' ~ ~f' E~n" ~/
i.
3.-7
ENVIRONMENTAL
LABORATORIES, INC.
/~ETROL£U/; J' J' EGLtN, RE~ CHEM. ENGR.
4100 PIERCE RD., BAKERSFIELD, ~LIFORNIA 93308 PHONE 327-4911
· ~ Purgeable A~omatics
(SOIL)
Groundwater Resource Industries Date .of
'Bakersfield, CA 93313
Attention:
Lab No.: 778-10
Sample Desc: S-GW-6 Gasoline Tar~ West Er~ 6' 1/25/90 8 .9.:07
Date S~ple Date Sable Date
'"- Collected: Received @ Lab: Completed:
25-Jar~-90 25-Jan-90 02-Feb-90 ·
Reporting Analysis Reporting
Constituent Unita Results Level
..... Benzene ug/g none detected .0.03
..- Toluene ug/g none. detected 0.03
Et?~/1. Benzene ug/g .none detected O. 03
p-Xylene ug/g none detected O. 03
] m-Xylene u~/g none detected 0.03
o-Xylene ug/g none detected 0.03
Total Petroleum
Hydrocarbons ug/g 'none detected 2.00
TEST METHOD: TPH for
Individual constituents by M~ified EPA ,mtt~x~ 8020.
As Received -Basis
Co~ents:
California D.O.H.S. Cert. ~102
~ ~ ' ~°~'~ i~S
~ ~,~,~ LABO RATO- , I N C.
· 4100 PIERCE RD., BAKERSFIELD, CALIFORNIA 93308 PHONE 327-4911
BTXE/TPH GASOLINE
Quality Con%rol B~ta
Groundwater Resource Industries Spike ID: 776-8
A~tention: Units: ug/g
Quality Control
?for Lab Nos: 776-1, 776-2, 776-3, 776-4, 776-7, 776-8, 776-9
Dup
Spike Spike Spike]
. Constituent % Rec % Rec RPD
Benzene 71.77 75.61 .5.21
Toluene 72.62 75.97 4.51
Ethyl Bermene 74.14 78.47 5.67'
QC Co~nents:
LABO RATO , INC.
P£TROL£U¥ J' J' EGLIN, REG. CHEM. ENGR.
.- 4100 PIERCE RD.,. BAKERSFIELD, CALIFORNIA 93308 PHONE 327-4911
GROUNDWATER RESOURCE INDUSTRIES Date.Reported: 02/07/90 Page 1
P. O. BOX 9383 Date Received: 01/25/90
5400 ALDRIN COURT Laboratory No.: 776-5
BAKERSFIELD, CA 93389
Attn.: CLAUS ENGELHARDT 835-7700
Sample Description:.·PROJECT $150010-2= 'S-WO-2 WASTE OIL TANK '2' 1/25/90 @ 1=38 SAMPLE
COLLECTED BY: CLAUS ENGELHARDT.
g.' TOTAL CONTAMINANTS
~ (Title 22, Article II, California Administrative Code)
Method '.
-'.(- ............. Constituents ........................... .... '-·Sample Results ...... P-.Q.L. '~'units ......... ' ..... '='Method '"'~R~'. ........
Lead 9.81 3.5 mg/kg 6010 1
TOX None Detected 20. mg/kg 9020
Oil & Grease 70. 20. mg/kg 413.1 2
Requlator¥ Criteria
Constituents STLC, mq/L TTLC. m~/kq
Lead 5.0 1000.
Comment: Ail constituents reported above are in mg/kg (Unless otherwise stated) on
an as received (wet) sample basis. Results reported represent totals
(TTLC) as sample subjected to appropriate techniques to determine total levels.
P.Q.L. = Practical Quantitation Limit (refers to the leas.t amount of analyte detectable
based on Sample size used and analytical technique employed.
N.D. = None Detected (Constituent, if present, would be less than the method P.Q.L.).
I.e. = Insufficient Sample
STLC - Soluble Threshold Limit Concentration
· TTLC = Total Threshold Limit Concentration
REFERENCES: re' (1) "Test Methods for Evaluating Solid Wastes", SW 846, July, 1982.
(2) "Methods for Chemical Analysis of Water and Wastes", EPA-600, 14-79-020.
A-10
o ENVIRONMENTAL
PETROLEU~ · J. EGLIN, REG. CHEM. ENGR.
.. · 4100 PIERCE RD., ~KERSFIELD, CALIFORNIA 93308 PHONE 327-4911
GROUNDWATER ~SOURCE INDUSTRIES Date Re. fred: 02/07/90 Page 1
P. O. BOX 9383 Date Received= 01/25/90
5400 ~DRIN COURT
B~RSFIELD, ~ 93389 Laborator~ No.= 776-6
A[tn. = C~US ENGE~T 835-7700
S=ple 'Deacrip[~6,-' 'pR~Ec= $i50010-2= SLWOL6-'-~S~E- ~iL T~K 6' 1/25/90 ~ 1:40 S~PLE
CO~EC~ED BY= C~US ENGEL~T
· ~- . TOTAL CONTAMINANTS
'J. (Title 22, Article II, California Administrative Code)
Method
Constituents ..... .- .~= Sample Results ...... ='.P.O. L< ........ Units ........... "~Het h0~
Lead' '7.21 3.5 mg/kg 6010 1
TOX ' . None Detected 20
Oil & G~ease ' mg/kg 9020 1
152. 20. .mg/kg 413.1 2
_Requlatory Criteria
Lead 5.0 1000.
Comment: Ail constituents reported above are in mg/kg (unless otherwise stated) on
an as received (wet) sample basis. Results reported'represent totals
(TTLC) as sample subjected to appropriate techniques to determine total levels.
P.Q.L. = Practical Quantitation Limit (refers to the least amount of analyte detectable
based on sample size used and analytical technique employed.
N.D. " None Detected (Constituent, if present, would be less than the method P.Q.L ).
I.S. ~ Insufficient Sample ·
STLC - Soluble Threshold Limit Concentration
· TTLC - Total Threshold Limit Concentration
REFERENCES: -:.
(1) "Test Methods for Evaluating Solid Wastes", SW 846, Suly, 1982.'
(2~_'M~,ho~..~hemical Analysis of Water and Wastes', EPA-600, 14-79-020.
BY ,
~0. d4
A-ii
~ ~i 5400 Aldrin Cour. t
~ groundwater resources, inc. Bakersfield, California 933 ! 3
TelePhone: (805) 835-7700
: CHAIN OF 'CUSTODY RECORD , Tele-Fiax: (805) 835-7717
LAB DESTINATION: PROJECT NUMBER:-/,-~'~'O/O'"~_
BC- p.o..U.BER___S_P_~_5__C- PROOECT CONTACT:
SAMPLER(S): (Sion. ature) z ~-
~ ,'7;, COUNTY: l/'/,"I i~ :
LAB SAMPLE 'z a::
ANALYSIS S-AMPLE CONTAINE~
NUMBER NUMBER DATE TIME SAMPLE LOCATION o°z
O REQUESTED TYPE TYPE
--?~7(:, .. i ~'-~-A. t.~.~o ii.,~ p,~r,,,~, .~' b'z-':z~ -Tpt~-C~,.,,,/,.,~.~. '.so, i -//,~....~-
..-z_ .~-p-~. /~r-r~. //.'~ ,,),~,,,,..- ,' .. ~rx~ "T?,¢ O~,:,i,;,d -- ' :"-,,.i '/,',~-~,-~.--
.3?-P-a. /~s"~o /I.'y~' tt ,, ,, '
P'?,") -,~',: -sbt I //,%/~-
- ~ s-P-.C ~ar-¢o /z.'c,,~ n?,,? c ' ~' ~, ,. '" .so,, / ?/,-~j:,,,_
SPECIAL INSTRUCTIONS' U.~ ,,,¢-A~ ' '" '~ '
POSSIBLE SAMPLE HAZARDS'
1. Rellnquls"hed by: ~_z.c~L ~--~,~/~~ate/Tlme:/-~_fO3''0~ $,.2.f~ -
Received. by:~l(,~.~ (c/,._.~_ Date/Time: .I-LC-~/¢
1.'Relinquished by: Date/lime: Recelved by' * ;Date/llme:,
I. ,Rellnquished by: · Date/l'lme: RecelveO b~:. iDate/llme: .
1 Relinquished-by: Date/Time: Received by:
· 'Date/Time:
'- LABORATORIES, INC.
P£TROLEU)~ J.J. EGLIN, REG. CHEM. ENGR.
· 4100 PIERCE RD., BAKERSFIELD, CALIFORNIA 93308 PHONE 327-49].
Purgeable Arouatics
(SOIL)
Groundwater Resolves, Inc. Date of
· :"..:'-.: '.:':--:::--~.-.:~ _5400--Aldrin Ct. :.._:_ ~- --~. :..:.~._.:":::--::'.~:.:~'-':::---:~:":~":-~
~:~kersfield,. CA 93313
At~ntion: Cla~ ~le~t
. ~b No.: 2077-i
S~nple ~sc: Project ~150010-2
S-D-8 3/09/90 1: 15 Di~nser 8'
~ ~le ~ S~,ple ~ ~ly~i~
~llec~d: ' Receiv~
09-~90 09-E~-90 15-~90
Mir~
Re~i~ ~alysis Re~rting
Cor~ti~ent Uni~ Resul~ ~vel
~nzene u~g none de~c~ 0.7
Toluene u~g 2.2 0.7 '"
Et~l ~nzene ~./g 4.4 0.7
p-Xylene ~/g 14 0.7
m-Xylene ~/g 7.8 0.7
o-~lene ~/g 290 0.7
To~l. Pet~le~
~~rm ~./g 4100 20
(Gasoline)
TEST METIIOD: TPH bi D.O.H.S. / L.U.F.T. u~thc~]. '
Individual constituents by Modifi~] EPA u~.t?~x2 5020/8020.
As Received Basis
Cor~r~nts:
California D.0.H.S. (~rt..102
A-13
PETROLEU¥ J. J,. EGUN, REG. CHEM. ENGR.
;, , 4100 PIERCE RD., BA~(ERSFIELD, CALIFORNIA 93308 PHONE 327-4911
Purgeable Aror~tics
(SOIL)
Gz¥~undwater Re$oua~es, Inc.
· 5400 Aldrin Ct. Date of
Attention: Claus Englehardt
Lab No.: · 2077-2
. Sa~?~le DeAc: Project $150010-2
,,~ S-D-11 3/09/90 1:40 Dispenser 11'
Collected: Received @ Lab: Completed:
. :. 09-Mar-90 09-Mar-90 "15-Mar-90
Repor~ir~ Analysis Re[~r tir~
Constituent Units Results Level
Benzene ug/g none detected O. 6
.... Toluene ug/g 1.0 O. 6
.~ Eth~l Benzene ug/g 1.4 O. 6
p-X¥1ene ug/g 27
O. 6
m-X¥1ene ug/g 50 O. 6
o-X¥1ene ug/g 92 O. 6
Total Petroleum
Hydrocarbons ug/g 1700
(Gasoline) 20
TEST METHOD: TPH by D.O.H.S. / L.U.F.T.
Individ,z~l cormtituents by Modified EPA ~mt?md 5020/8020.
As Received g~sis
Co~r~nts:
California D..O.H.~. Cert. ~102
A-14
LABORATORIES' INC.
· J. J. EGLIN, REG. CHEM. ENGR.
· 4100 PIERCE RD., BAKERSFIELD, CALIFORNIA 93308 PHONE 327-49]]
Purgeable Az~:~mtics
(SOIL)
Groundwater Res9 .u~q~.~s_~.i Inq.~_ ........................................ . ...... Date of '
~rsfield, CA 93313
At~ntion: Claus ~le~t
~b No.: 2077-3 '
~r~ple ~sc: P~ject ~150010-2
S-~14 3/09/90 2:20 Dish, er 14'
09-~r-90 09-~r-90 15-~'-90
Re~rtin~ ~alysis Re~r'ti~
~r~ene ~/g none de~c~ O. 6
Toluene ~'/~ -.-1.4 0.6
Ethyl ~r~ene ug/g 1. ? 0. ~
p-Xylene ug/g 27 0.6
m- Xy 1 ene ~/g' 55 0. ~
o-Xylene ~/g 81 0. ~
To~l Pet~le~n
Hy~ar~ns ug/g 1900 20
(Gasoline)
TEST Mk~I'HOD: TPH by D.O.H.S. / L.U.F.T. r~et?~].
Individual cor,-~.tit~ents by Modified EPA ~t~.~] 5020/8020.
As ReCeived Basis
Cormorants: )
California D.O.H.S. Cert. ~102
A-15
LABORATORIES, INC.
PETROLEUU J' J' EGMN. REG. CHEM, ENGR.
~ · 4100 PIERCE RD., BAKERSFIELD, CALIFORNIA 93308 PHONE 327-49~
~~H G~LI~ '
~lity ~nt~l
Gro~dwa~r Resoles, Inc. Spi~ ID: 2051-1
~rsfield, CA 93313 - ~rple ~trix: soil
c A~ntion: Cla~s ~el~t Ur~ts:
Q.~lity Control
..... ' .....' ..... - ........ for- Lab' Nos: 2077-1,- -2077-2,_____ _____ __
D~p
Spike SPiP.~- Spike
COr~tituent % Rec % Rec RPD .....
Benzen~ 87.37 84.22 3.67
Toluene 89.64 87.34 2.60
Ethyl Benzene 92.96 89.32 3.99
A-16
' Bakers f ie'ld,' Cai i fornia 93313
groundwater reSources, inc.
Telephone' (805) 835-7700"
CHAIN OF CUSTODY RECORD Tele-F~x: (805) 835-7717
LAB DESTINATION: PROJECT NUMBER:~°/c'-~ PROJECT CONTACt'
~ ~.0. NUMBER_-~J2--
I~ COUNTY:
LAB SAMPLE zm ANALYSIS 'SAMPLE 20NTA'INER
NUMBER NUMBER DATE TIME SAMPLE LOCATION ~z
· o REQUESTED TYPE TYPE
i '2' ':' ';'~'
SPECIAL INSTRUCTIONS'
1. Relinquished by: Date/Time: Received by: ~,: Date/Time:
:.1..Rel'inqulshed by: Date/Time: Received by: .: ~ Date/Time:
APPENDIX B .... '-.C:.'"
HEALTH AND SAFETY CONSIDERATIONS '
HEALTH AND SAFETY CONSIDERATIONS
The responsible party for the work will be Duane R. Smith and
Associates personnel. The possible hazardous materials encountered
will .be petroleum.~products ('typically.-gasoline, diesel
waste oil). These constituents should occur at relatively low
levels The constituents will be blended with soil.
........ D.Dring. alloperations-that might release-airborne-vaporS,~"an Hn~
PID meter will be used to monitor vapors in the breathing zone of
workers. If there are significant.readings for a sustained period,
the drilling operations will be suspended and the wdrk reevaluated.
Recognition of hazards, whether it be from instrument readings,
'odor, irritation, visibility, headache, dizziness, or fatigue, is
important, but it is equally important to take appropriate action
when a hazard is recognized. If the problem cannot be promptly
corrected, we will back off from the exposure source and obtain
assistance to solve the problem. Work practices and engineering
controls will be devised to minimize potential exposures.. For
example, we will work upwind of any potential exposure source.
Air-purifying respirators with combination organic vapor/acid,
gas/dust, fume, and mist cartridges will be on location. These
will be worn when Hnu readings persist above significant levels in
the breathing zone. If there is eye irritation, full-face
respirators will be used.
Tyvek coveralls will be worn as necessary to avoid skin contact.
with contaminated soils. Chemical resistant gloves and boots will
also be worn as necessary to avoi~ hand and foot contact with
contaminants. All personnel will wear hard hats when w~rking near
~_~he ~drilling~ -rig,~- ~ll personnel~i-involved i~
retrieval have received training as sPecified in the OSHA Hazardous
Waste Operations end.Emergency Response Standard [~9CFR 1910.120].
-.The-physical ~hazards associated ~with operating '~'drill~'~~
sampling equipment must be recognized. ~Individuals not directly
involved in drilling Shall stand back at least the distance of the
vertical boom.
The potential hazards involved in the job will be reviewed with
all personnel including subcontractors working on site.
Prior to commencement of work, emergency evacuation routes will be
established. A "safe zone" location will be established taking
into account weather conditions, site activities, and other factors,
as necessary.
Duane R. Smith and Associates personnel will coordinate activities
in an emergency situation. Arrangement will be made for transportation
to a hospital in the event of an accident or exposure to hazardous
materials that produce organic symptoms in the exposed party.
B-2
SEQUOIA PAINT "COMPANY
',~L~;-~' ~',~~ ... .'~' ~'.7-~','~'.:~'~. - '- 4,~"~ ~'~? ~~ ~' ~' ~t~-~ ~ ~.'~.,'~v, .'~'
-.' ~'~' ~'~ ' ~ .. ', . , ,~' ' ~, . ~, . ~, . . .,.,: ~i'~ . . . '.' . ; ~'~ '~ ~' ~>
· ,. . '..~'..:...'
'.'' . ' Consulting Geologists- "
' ..... ~' ................... - 7201' Prultv~e- -E~tensidn
Bakersfield, ~ii~rnla 9~08
. c8o~) s.-78e~ ~
TABLE OF CONTENTS
Page
2 3
Site GeOlogy -
eeeeeeeleeeeeleeeeeleee
Preliminary Site Assessment Results ............ 3 - 5
~ 5 10
Soil Sampling ' -
eeeeeeeeelee-lee~eeeeee
Supplemental Work Plan 8 - 10
Health and Safely Considerations... · · · · · · · · · .· 10
Exhibits
Figure 1 Location Map
'Figure 2 Plot Plan
Figure 3 Site Map
Figure 4 Log of Test Hole
Figure 5 Test Hole Location Map
Table i Summary of Analytical Results, Samples
Beneath Dispenser Location
Appendix A Analytical Results and Chain of Custody
Records - Preliminary Site Assessment
Appendix B Analytical Results and Chain of Custody
Records - Test Hole No. 1
Appendix C Health and Safety Condiderations
PROGRESS REPORT AND SUPPLEMENTAL WORK PLAN
SEQUOIA PAINT COMPANY SITE-
SITE BACKGROUND
The Sequoia Paint Company is located at 700 Baker Street in
Bakersfield, California. The site is situated in Section 29,
T.~gs., R.28E., M.D.B. & M. (see Figure 1). The site is used for
the dist ibu:tio f:-'paiht'~'~nd '~eT~'~'d~"~'6:~:6'ts'~ ........ Th~he~'~'~:~
is commercial and residential. The facility permit number is
150075.
The Sequoia Paint Company moved their showroom facilities to the
property early in 1990. Mr. Jim Elder of Sequoia Paint re-
searched past building permits and reports that Wally Tucker
Datsun constructed the current building in 1966. Wally Tucker
Datsun occupied the site from about 1952 to 1985. The property
was vacant after 1985. The property reportedly was vacant prior
to 1952 except for a small fast food outlet which may have
occupied the site in the 1940s.
Two underground storage tanks were removed from the property on
January 2'5, 1990 by Groundwater Resources, Inc. (GRI). A 4,000
gallo~ unleaded gasoline tank and a 200 gallon waste oil tank .
were situated on the property approximately as shown on Figure 2.
The gasoline dispenser was located in a small closet along the
west edge of the main building (see Figure 2). The product l%ne
1
%~,.~,?~ /.~', ~ '~,~0~,~ ~ "'~[~~~~~~;{~*~'%'~ ~ : ';~' "~ '~ ~-[~1 '~ ~ ~~~~' : ' I' ~ % ~.~ ~-.~
fei ' (l~l -' > , ' .;.,- ~"' ., '~.~~"~/~~ ' *,', ·
.... ~'~i~ .e ~ ~ --' ; .~
mm ~ ~ . ";'~ ;~I~.~t'" ~. ~
i~ '~";' ~ :: ~ ~' '~' ';~: ¢'; fi" ~' ~ %'> '~' " , : ~ ' ' ~ e -. ~'"
,~_>: ~:::,~ ~1~~~~ :74 ~m~mmS ~ ......... -
-.,5~ ~ ~~ ~...~ ~,.~, ,.:~
;, m, m =Ill. - Im
SCALE ]:24 000
~ 0 ~ M~LE
~ ' 5 ~ ~ K~LONETER
' Figure 1
GASOIJNE TANK
' .4000 GALLON
(REMOVED) ~ -- ~ ,~ ..,
- - ' :7.'--' . ....... :-'~- ......... . -'~' ---'" ' ._ 7"'_..2..~ ' ' '
- - ~ :~ ~<. ~ .~, ,~:" - .. .. . ~:~:::::;:::~:
~ WASTE OILT~K
2O0 ~L~ON
~ S~P~L~AT~N ~ ~ (REMOVED)'
,~:~.~ ~:~.~.~ ~. ~R~,. ~.<.~.~.,:~.~...:.~<.~.:.~ ...... m m n~ ~ ~ .............. ~ ......... .:, ~<¢ .... >;':' ~"~ ...............................................
.:;:<?~:,~¢ ~ >:.:.~>x~ ~ ~x~ ~:;;>;::i::::::~::.:;~:~:~;:~.:~:~::..~ ::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::
SEQUOIA PAINTING
' d resources,
700 BAKER STREET groun water inc.
BAKERSFIELD, C~IFORNIA
.... e,nVironmental/geotechnical services
PLOT PLAN PrOject Number:15oo,o-2
Figure 2 '.
ran directly"between the tank and the dispenser as shown on
Figure 2. The tanks were made of steel and reportedly were
installed in 1982 and removed in 1985. Figure 3 shows a more
extensive and more de.tailed map of'the' site.
There are no known reports of discrepancies or reportable varia-
tions in inventory monitoring, failed tightness tests, repairs to
tanks or piping, or past leaks.
SITE GEOLOGY
According to the Geologic Map of California, Bakersfield Sheet,
the sediments underlying the site consist of Quaternary fan
deposits comprised of sediments dePosited, from streams emerging
from highlands surrounding'the Great Valley. In general, these
deposits consist of unconsolidated, poorly sorted silt, sand, and*
gravel.
According to the General Soil Map of Kern County, published by
the Soil Conservation Service, U.S.D.A., the site is underlain by
soils of the Delano association. In general, "this association
consists of well drained moderatelY fine textured soils developed
in sandy granitic alluvium.
Based on the 1988 Report on Water Conditions, Improvement Dis-
trict No. 4, published by the Kern County Water Agency, the depth
2
S I TE MAP
· ' SEQUOIA PAINT
7OO BAKER STREET
BAKERSFIELD , CALIFORNIA
= - ...... ' ............... ~,~ dU'rI'L'CHAIN- L,NI~ F~NC~' I~' ' '
r': E-- ~ ~ - --~ --E ...... -TI-E-
l I
I ~~
~o~ .......
FENCE
~'AST 19~ g~r I" = 30'
'NOTES: l. Both tanks, dispenser, and product line removed from site.
........... 2. Gasoline tank had_a 4,000 gallon capacity.. ~ ....
3. Waste oil tank had a 200 gallon capacity.
DUANE R. SMITH & ASSOCIATES -- OCTOBER 1990 ·
Figure 3
to groun, dwa~erbeneath the site is approximate~9.0fee/.t No
perched groundwater is known to exis't beneath the s~-i-~e.
Three types of sediments were encountered in one on-site test
feet, the sediments consist of a dark brown silt with minor sand
and clay content. From 9.5 feet to 32 feet, the sediments
consist of a light brown to tan silt~ sand. Gravel is rare to
common in this unit from 13 feet.to 3Z feet. A thin silt layer
was encountered between 32 feet and 34 feet. This unit is. a .:.-. ....
brown sandy silt with minor clay content. Below 34 feet, to an
unknown maximum depth, the sandy unit reappears. Ail of the
sediments, encountered were loose to poorly indurated and slightly
moist to very moist. A detailed description of these sediments
is shown on the log of Test Hole No. ! (see Figure 4).
PRELIMINARY SITE ASSESSMENT RESULTS
The analytical results and chain of custody record from the
Preliminary S~te Assessment are included in Appendix A, pa~es A-1
through A-12. Ten soil samples were collected and submitted to
B. C. Laboratories for analyses. Samples associated with the
~asoline tank were analyzed for T.P.H. gasoline and B.T.X.& E.
S~mp'les associated with the waste oil tank were analyzed for
T.O.X., total lead, and oil and grease. The sample locations are
shown on Figure 2.
OF TEST
= = m = D. R. SMITH & ASSOCIATES
O ~ ..~
· ~ ~ ~ ~ ~ ~ ~LOCATION: SEQUOIA PAINT SHOWROOM
~ ~ ~ ~ o ~ ~.~iTEST HOLE ID NTIFICATION: T.H. NO 1
~ o ~ ~ ~ o ~ ~ DATE DRILLED. 07/25/90 ~~ 412~'
~ ~ ., m~ ~ RIG TYPE: HAND 'AUGER '
m ~ ~ {XI Lithologic Description
....... Silt, dark brown, slightly'clayey, slightly
I~ . ...... sandy, very fine grained, poorly indurated,
....... very moist, gasoline odor.
_ ..' Sand, light bro*m to tan, silty, fine to very
.. '' coarse grained, poorly sorted, loose, moist.
o · o gravel common
o ... gravel rare
o slight decrease.in odor
.... fine gravel common
- . -~- ~ 0'.2 15 slight odor
-~: ' sampling difficulties
-.. '. (~ 320 250 09/19/90 - collected sample, moderate odor
- o... (~) 620 520 moderate odor
-17'2'/. Silt, ~brown, sandy, fine to coarse grained,
7'~'~'i slightly clayey, rust stains common, poorly
~ indurated, slightly moist, slight odor.
-"""~ (~) 720 310
Sand, tan, silty, fine to very coarse grained,
- poorly sorted, loose, moist, moderate odor.
Total Depth: 35' * - Sample Depth ~- Sample Analyzed Sheet 1 of 1
Figure 4
Sample S-D-2'was collected at a depth of 2 feet beneath the
dispenser. No T.P.H. gasoline or'B.T.X.& E. were detected in
this sample. Sample S-D-6 was collected at a depth of 6 feet
beneath the dispenser. This sample reportedly contained 935 ppm
..... -'~' ....... ':'-::-:: ':T'~'~:H~'~-~s~l'ine-':a~d moderat~ 'levels of xylene~' '-::'--'-"':::~::" ...... : ........ :' ...................
Samples S-P-2 and S-P-3 were collected at depths of .2 feet and 6
feet beneath the piping, respectively'. .No T.P.H. gasoline or
Samples S-GE-2 and S-GE-6 were collected, at depths of 2 feet and
6 feet beneath the east end of the ~asoline tank, respectively.
Samples S-GW-2 and S-GW-6 were collected a% depths of 2 feet and
6 feet beneath the west end of the gasoline tank, respectively.
No T.P.H. gasoline or B.T.X,& E. were detected in any of these
samples.
Samples s-we-2 and s-we-6 were collected at depths of 2 feet and
6 feet beneath the waste oil tank,, respectively. Sample s-we-2
reportedly contained 9.81 ppm total lead and 70 ppm oil and
grease. Sample s-we-6 reportedly contained 7.21' ppm total lead
and 152 ppm oil and grease. No ~T.O.X. was detected in either
sample'.
These results indicated no significant contamination beneath
either tank or beneath the gasoline piping. HOwever, significant
4
gasoline contamination is indicated beneath the former dispenser
location.
Subsequent to receiving the Preliminary Site Assessment results,
lo~ation to a depth of 14 feet. Soil samples were collected at
depths of 8, 11, and 14 feet.' Details of the sampling methodolo-
gy are not known. The 8 foot sample'reportedly contained 4,100
foot sample reportedly contained 1,700 ppm T.P.H. gasoline and'
moderate levels of B.T.X.& E. 'The 14 foot sample reportedly
contained 1,900.ppm T.P.H. gasoline and moderate levels of.
B.T.X.& E. The analytical results and chain of custody record
from this test hole are included in Appendix.A, pages A-13
through A-17.
SOIL SAMPLING
Pro~ress Report
Test Hole No. 1, as proposed in the original site characteriza-
tion work plan submitted in May'1990, was drilled with a hand
auger to a depth of 25 feet on July 25, 1990. This test hole was
deepened to 35 feet on September 19, 1990. The location of T.H.
No. 1 is shown on Figure 5.
TEST HOLE LO C ~.T I ON
· .- SEQUOIA PAINT
700 BAKER STREET
BAKERSFIELD . CALIFORNIA
~AST' /~r~ ~r~r If' = So'
TEST HOLE LOCATION
SLANT BORING
DUANE R. SMITH & ASSOCIATES -- OCTOBER 1990
Figure 5
Test Hole NO2 1 was drilled with a 2 inch diameter hand auger
using Z, 4., and § foot extensions. Soil samples were collected
with a hand driven core sampler. Depending on sampling condi-
tions, the core sampler contained one or more 2 inch diameter by
-2 :'~'Ch-10ng brass liners. After-advancing the test hole to the
proper sample depth with the hand auger, the hand auger was
carefully removed and the core sampler inserted into the boring.
The core sampler was t~hen driven into the soil using a hand
~-='.~t~a~="i~-hammer. The bra~s liner was then removed from
the sampler and immediately covered with Teflon seals and poly-
ethylene caps and taped shut with duct tape. Each brass liner,
after being sealed and taped, was labeled and placed in a poly-
ethylene sample b~g w.hich was then labeled and sealed. Each .
Sample was placed in an ice chest and retained in a chilled state
on blue ice for transport to SMC Laboratory. The drive sampler
was thoroughly scrubbed, washed, and rinsed between sample
collections.
Four soil samples from T.H. No. 1 were submitted for chemical
analyses. The samples were analyzed for T.P.H. g~soline and
B.T,X.& E. by SMC Laboratory in Bakersfield. . The analytical
~methods utilized by SMC Laboratory are listed on the laboratory
reports included in Appendix B. The quality assurance and
quality control of t~e laboratory are available from SMC Labora-
tory on request.. The analytical results of the four samples
submitted for analyses along with the appropriate chain of
.custody_ records~.are:~-included in Appendix---B. ~ .................... ; ......................................
6
Another soil ~ample from each sample depth was collected for
field screening and soil descriptions. ,Field screening consisted
of a headspace reading for hydrocarbon vapors with an Hnu PID
meter calibrated to a benzene standard. In addition to the
headspace readings'- ~h~dr0C-"rb6h~'~ 0dbms-,~ 'if de~e~t~d, were noted.
Field screening results are shown on Figure 4. Drill cuttings
were placed in a DOT drum and retained on-site.~J
Soil samples were c~iiec from T.H. No. ! at depths of 20, 25,
30~ and 35 feet.. Since a hand auger boring' had already been . .. ..
sampled at depths of 8, 11~ and 14 feet in the immediate vicinity
of T.H. No. 1~ samples were.not collected above 20 feet. The
delay in advancing this test hole to 35 feet was' due to sampling
difficulties at 25 feet. A core sampler with a built-in sand
catch was ultimately used to collect samples at 25, 30, and 35
feet.
The 20 foot sample from T.H. No. 1 reportedly contained 15 ppm
T.P.H. gasoline and traces of ethylbenzene, xyl'enes, and isoprop-
ylbenzene. The 25 foot sample from T.H. No. 1 reportedly con-
tained 250 ppm T.P.H. gasoline, traces of toluene, and low levels
of xylenes. The 30 foot-sample from T.H. No. 1 reportedly
contained 520 ppm T.P.H. gasoline and moderate levels of B.T.X.&
E. The 35 foot sample from T.H. No. 1 reportedly contained 310
ppm T.P.H. ~asoline and low to moderate levels of toluene,
ethylbenzene, xylenes, and isopropylbenzene. Table ! summarizes
the analytical results of all ~of the samples collected-beneath
?
SUMMARY OF ANALYTICAL RESULTS
SAMPLES BENEATH DISPENSER LOCATION
SEQUOIA PAINT SHOWROOM
DEPTH T.P.H, BENZENE TOLUENE ETHYLBENZENE P-XYLENE N-XYLENE O-XYLENE ZSOPROPYLBENZENE
/2' N.D. N.D. N.D. N.D. N;D. 'N.D. N.D. "-"-
6' ~935.00 N.B. N.D. N.B. 3.04 4.95 24,56 ....
8' 4100 N.D. 2.2 4.4. 14 7.8 290 ....
Il' ~I?00 N.D. l.O 1.4
14' '1900 N.D. 1.4 I.? Z? SS 81 ....
20'. 15 N.D. N.D. .lO .33 .63 .70 .lO
25' 250 N.D. 0.26 N,D. 2.! 2.5 9.6 N.D.
30' 520 0.10 2.4 4.4 20. 20. 36. N.D.
35' 310 H.P. 0.68 2.0 7,9 7.9 13.0 2;0
NOTES:
1. Depths in feet below ground surface.
2. T.P.H. is total petroleum hydrocarbons '(gasoline).
3. All results in pg/g (~ppm).
4. First five samples, not analyzed for isopropylbenzene.
SEQUOIA. RES
Table 1
the former dispenser location. Clearly, the vertical extent of
contamination has not been defined even though the results of the
20 foot sample suggested that the maximum contamination was not
much deeper than 20 feet.
· ' .... . . .- ~.3~.~i.~_~i~ ....................... YUi . './'£7""~%~Z:-~-~-~'~'~-J='-'.-. '7 ~- 3' _ . ! C ....~'3--" .-~7"-~ .... £.'- ........... ~--~ .......
Supplemental Work Plan
SinCe it was determined that hand augering cannot provide ade- .
quate data to characterize the contamination,.Phase II will be
implemented. Phase II will consist of the same boring locations·
as Phase I (see Figure 5), but the drilling methodology will be
different. Test Hole No. 4 will be slant drilled at an angle of
20' from vertical under the building as shown on Figure 5. Test
Hole No. 3 may be omitted if the lateral extent of contamination
can be defined by T.H. No.
The borings will be drilled to a maximum depth of 75 feet each.
If field screening indicates'that the vertical extent of contami-
nation is less than 75 feet, the boring depths will be decreased
accordingly. If the vertical extent of contamination is found to
be significantly greater than 75 feet, additional borings, will be
· proposed in a Phase III work plan. Based on the judgement of the
on-site geologist, the borings proposed herein may be drilled
slightly d~eper than 75 feet if it appears that the Vertical
extent of contamination is only slightly greater than 75 feet.
Groundwater should not be encountered in any of these borings and
will not be'Considered in this w°rk'~lanl
8
Soil samples will be collected every 5 feet starting at a depth .
of § feet except at T.H. No. 1 where sampling will begin at a
depth of 40 feet. Selected soil samples will be submitted for
analyses. The samples will be analyzed for T.P.H. gasoline and
B.T.X.&'E. by SMC Laboratory. The quality assurance and quality
control of the laboratory is available from SMC Laboratory on
request. ~ 'Chain of custody records documenting sample handling.
~ill be included.
~Soil samples will be collected using a split-spoon sampler driven
into the soil utilizing a truck-mounted continuous flight hollow"
stem auger rig (Mobile Drill B-§3). The split-spoon sampler
contains three two and one-half inches diameter by six inches
long brass tubes.
The sampler will be driven through the proper sampling interval
after the hole is drilled with the hollow stem auger. The
sampler will then be removed from .the drilling equipment and the
brass tubes removed from the sampler.
The ends of one tube from each sample depth will be covered with
Teflon seals and polyethylene caps and then sealed with du~t
~ape. The tube will then be labeled and placed in apolyethYlene
sample bag and the bag sealed and labeled. Each bagged tube will
be retained in a chilled state on blue ice. Selected samples
will be delivered to SMC Laboratory for analyses.
9
Another soil' ~ample from each sample depth will be retained for
field screening and soil descriptions. Field screening will
consist of a headspace reading for hydrocarbon vapors with an Hnu
PID meter calibrated to a benzene standard. In addition to the
headspace readings, hydrocarbon odors, if present, wilI be noted.
The'augers will be steam cleaned between the drilling of each
borehole to avoid cross contamination· .The sampling equipment
will be scrubbed, washed, and"~horoughl¥ rinsed between each
sample collection.
The test holes will be backfilled with a cement-sand slurry mix.
Contaminated drill cuttings, as identified by field screening,
will be placed in DOT drums for future treatment or disposgl.
HEALTH AND SAFETY CONSIDERATIONS
The Health and Safety Considerations are included in Appendix C.
Submitted by:
.~ ~0. 3584: Duane R. Smith
Registered Geologist
.,~ State of California No. 3584
Thomas F. Gutcher
Staff Geologist
.... SI~QUOIA. PLN ........................... ~ ........ - ~
10
APPENDIX A
CHAIN OF CUSTODY RECO~S
PRELIMIN~Y SITE ASSESSMENT
PETROLEUM J' J' EGLIN. REG. CHEM. ENGR.
'4100 PIERCE RD., ~KERSFIELD, ~LIFORNIA 93308 PHONE 327-4911
G~wa~r Res~e In, tries ~ of
~rsfield, ~ 93313
At~ntion:
~ns ti~ent U~ Resul~ ~vel
~ene ~g none de~ O. 03
Toluene ~/g none de~ 0.03
E~I ~ene ~g none de~ 0.03
p-Xylene ~g none de~ 0.03
r~lene ~g none de~ 0.03
o-~l~e ~g none de~ 0.03
.To~l Pet~le~
~d~~ ~g none de~ 2.00
TEST METHOD: TPH for gasoline by' D.O.H.S2 L.U.F.T. rr~thod.
Individual constituents by Modified EPA met~c~d 8020.
As Received Basis
California D.O.H.S. Cert. ~102
' LABO RATO INC
P£TROLEU¥ J; J' EGLIN, REG. CHEM. ENGR.
4100 PIERCE RD., BAKERSFIELD, CALIFORNIA 93308 PHONE 327-4911
Purgeable A~tics·
(SOIL}
Groundwater Resource I~-~tries Date of
...... 5400.~Aldrin Ct. -..:-: ................... ..-_ ...... ~_- ....... ~--~-~.~--.: .......... : ...... :. - Report: 05-Feb-90 ...........:~- ................
Bekersfield, CA 93313
Attention:
Lab No.: 776-2
Sample Desc: S-D-6 Disper,-~er 6' 1/25/90 '~ 11:38
Date Sample Date Sample Date Analysis
Collected: Received @ Lab: C~;~leted:
25-Jan'90 25-Jan-90 02-Feb-90
Reporting Analysis Reporting
Constituent Units Results Level
Benzene ug/g none detected O. 30
Toluene ug/g none detected O. 30
Ethyl Benzene ug/g none detected O. 30
p-Xylene ug/g 3.04 O. 30
.~Xylene ug/g 4.95 O. 30 .
o-Xylene ug/g 24.56 O. 30
Total Petroleum
Hydrocarbons ug/g 935. O0 .~0. O0
TEST METHOD: TPH for gasoline by D.O.H.S.L.U.F.T. rf~t~d.
Ir~ividual constituents by Modified EPA r~thod 8020.
As Received Basis
Califor~ia D.O.H.S. Cert. ~102
~ ~mlyst
ENVIROtVYE#T,41.
~RO~E~ ~ ~ EGLIN, REG. CHEM. ENGR.
4100 PIERCE RD., ~KERSFIELD, CALIFORNIA 93308 PHONE 327-4911
~g~ble A~tics '
G~wa~r Res~ I~ies ~ of
~rSfie~d, ~ 93313
At~ntion:
~b ~.: 776-3
~le ~sc: S-P-2 Pip~ 2' 1/25/90 ~ 11:55
~ ~,ple ~ ~le ~ ~lysis
~11~: R~iv~ ~ ~b: ~le~: ·
25-J~-90 25-J~-90 02-Fe~90. .~.
Re~i~ ~alysis Re~~
~ti~ent Uni~ Resul~ ~vel ·
~e ~g · none de~ 0.03
Toluene ~g none de~ O. 03
E~i ~ene ~g none de~ O.
p-Xylene ~g none de~ O. 03
~Xylene ~g none de~ O. 03
o-~l~e ~g none de~ O. 03
To~ Pet~l~
~~~ns ~g none de~ 2. O0
T~ST METHOD: TPH for gasoline by D.O.H.S.L.U.F.T. ,~th~d.
Individual cor,-~tituents by Mollified EPA met¥~d 8020.
As Received Basis . ,
California D.O.H.S. Cert. ~102
LA B ORATOR , I N C.
· P£TROL£il¥ J' J' EGLIN, REG. CHEM. EHGR.
4100 PIERCE RD., BAKERSFIELD, CALIFORNIA 93308 PHONE 327'-4911
Purgeable Ar~mtics .
(SOIL)
flrour~iwater Resource Ina-.~rEes · Date o£
5400" Aldrin- Ct. - .........: ............ . ............ : , '--:~"-:-- Report;:"'--052Feb-90 · ..:+-~ ....
Bakersfield, CA 93313
Attention:
Lab No.: 776-4
~ple Desc: S-P-6 Piping 6' 1/25/90 ~ 12:09
Date San~le Date S~f~ale Date A~-~lysis
C~llected: Received @ Lab: Co~,pleted:
25-Jan-90 25-Jan-90 02-Feb-90
Minimum, _
Reporting Analysis Reporting
Constituent Units Results Level
Benzene ug/g none detected O. 03
Toluene ug/g none detected O. 03
Ethyl Benzene ug/g . none detected O. 03
p-Xylene ug/g none detected O. 03
m-Xylene ug/g none detected O. 03
o-Xylene ug/g none detected O. 03
Total Petroleum
Hydrocarbons ug/g ' none detected
2. O0
TEST METHOD: TPH for gasoline by D.O.H.S.L.U.F.T. ~thod.
Individual constituents by Modified EPA ~t?~d 8020.
As ReCeived -Basis
Co.~ents:
California D.O.H.S. Cert. #102
LABO RATO , INC.
PETROLEUM J* J' EGLIN, REG. CHEM. ENGR.
4100 PIERCE RD., BAKERSFIELD, CALIFORNIA 93308 PHONE 327-4911
Purgeab'l e Arorr~ti¢-~ '
G~wa~r Resole I~tries
............................ ~ersfield, CA 93313
At~ntion:
~b ~.: 776-7
~le ~sc: S~E-2 ~oline T~ ~t ~ 2' 1/25/90 · 1:48
~ ~le ~ ~le ~ ~ysis
~ll~: R~eiv~ ~ ~b: ~le~:
25-J~-90 25-J~-90 02-Fe~90
Mini~,
Re~i~ ~lysis Re~~
~~ent U~ ReS~ ~vel
~ene ~g none de~ O. 03
Tolu~e ~g none de~ O. 03
Et~l ~nzene ~g none de~ O. 03
~lene ~g none de~ O. 03
m-Xyl~e ~g none de~ O. 03
o-~lene ~/g none de~ O. 03
To~l Pet~le~
~~ ~g none de~ 2. O0
TEST METHOD: TPH for gasoline by D.O.H.S.L.U.F.T. r~mt~od.
Ir~ividual constituents by Modified EPA m~thod 8020.
As Received Basis
California.D.O.H.S. Cert. ~102
A-5
PETROLEUI~ J' d' EGUH, REG. CHEM. EHGR.
4100 PIERCE RD., BAKERSFIELD, CALIFORNIA 93308 PHONE 327-49tl
Purgeable Arc~aatics
(SOIL)
Groundwater Resource ,Industries Date of
5400 Aldrin Ct - .... -:-~--~-::'--~-' -: .... ::~: ...... ~-;--::: ...... :- ......... ~ ~'Re~Pt: ' 05F~b-90~:' z- ~:.-~-. ~- :_- '---- :- :::: ..... -~-
Bakersfield,' CA 93313
Attention:
Lab No.: 776-8
S~,ple Desc: S-GE-6 'Gasoline Tank -East End 6' 1/25/90 @ 1:50
Date Sample Date Sa.~le Date Analysis
Collected: Received @ Lab: Cc~pleted: o ~:
25-Jan-90 25-Jan-90 02-Feb-90
Reporting Analysis Reporting
Constituent Units Results Level
Benzene ug/g none detected 0.03
Toluene ug/g none detected 0.03
Ethyl Benzene ug/g none detected 0,03
p-Xylene ug/g none detected 0.03
m-Xylene ug/g none detected 0.03
o-Xylene ug/g none detected 0.03
Total Petroleum
Hydrocarbons ug/g none detected 2.00
TEST METHOD: TPH for gasoline by D.O.H.S.L.U.F,T. ,~t[~d.
Individnal constituents by Mcx~ified EPA, method 8020.
As Received Bali's
California D,O.H.S. Cert. ~102
P£TROLfU¥ J' J' £GLIN, REG. CHEM. ENGR.
, 4100 PIERCE RI:)., BAKERSFIELD, CALIFORNIA 93308 PHONE 327-4911
Purgeable Aromatics ·
(SOIL)
Groundwater Resource Industries Date of
5400 Aldrin Ct ......... Report: .... 05-Feb-90 ....... - ......................
Attention:
Lab No.: 776-9
Sample Desc: S-GW-2 C~8oline Tank West· End 2' 1/25/90 @ 2:O0
Date S~ple Date S~r~le Date Analysis
Collected: Received @ Lab: Completed: ' -
25-Jan-90 25-Jan-90 02-Feb-90
Reporting Analysis Reporting
Constituent Units Results Level
Benzene ug/g none detected O. 03
Toluene ug/g none detected O. 03
Ethyl Benzene ug/g none detected O. 03
p-Xylene ug/g none detected O. 03
. . m-Xylene .ug/g none detected O. 03
o-Xylene ug/g none detected O. 03
Total PetrOleum
Hydrocarborm ug/g none detected 2. O0
TEST METHOD: TPH for gasoline by D.O.H.S.L.U.F.T..~thod.
Individual constituents by Modified EPA t~thod 8020.
As Received -Basis
California D.O.H.S. Cert. #102
LABORATO- , INC.
PETROLEUII J' J' EGLIN, REG. CHEM. ENGR.
4100 PIERCE RD., BAKERSFIELD, CALIFORNIA 93308 PHONE 327-4911
Purgeable Aromatics '
(SOIL)
Groundwater Resource Ir~iuatries Date'of
'~'~ ~:-..~:~:~=~5400~.kldrin--Ct - ...................... c- _-.-~'>. ....... ~ .........--:~'~'- ...... Report:'-~=05=Feb~90-:=.~ ~-~r--'-_:-;--.~-~-
Bakersfield, CA 93313
Attention:
Lab No.~: 776-10
Sa~p, le Desc: S~-6 Gasoline Tar~ West End 6' 1/25/90 @ 2:07
Date F~le Date S~ple Date Analysis
Collected: Received @ Lab: Completed:
25-Jan-90 25-Jan-90 02-Feb-90 ' ' '" · ..
Minirr~.
Reporting Ahalysis Reporting
Constituent Units Results Level
~enzene ug/g none detected O. 03
Toluene ug/g none detected O. 03
Et?~l Benzene ug/g none detected O. 03
p-Xylene ug/g none detected O. 03
m-Xylene ug/g none detected. O. 03
o-X~lene ug/g none detected O. 03
Total Petroleum
Hydrocarbons ug/g none detected 2.00
TEST METHOD: TPH for gasoline by D.O.H.S.L.U.F.T. ~t?~d.
Individual constituents by ~kxlified EPA .~-t~xi 8020.
· As Received Basis
California D.O.H.S. Cert. ~102 !..
~- ,~, ~ RI~/~S
LABORATO. , INC.
PETflOLEIJ¥ J' J' EGLIN, REG. CHEM. ENGR.
4100 PIERCE RD., BAI~ERSFIELD, CALIFORNIA 93308 PHONE 327-4911
BTXE/TPH GASOLINE
Quality Control Data
Groundwater Resource Indus%ties Spike ID: 776-8
'Bakersfield, -CA '-93313 ................. Sample Matrix: Soil
Arran%ion: Units: u~/~
~uali%¥ Con%rol
...~for Lab Nos: 776-1, 776-2, 776.3, 776-4, 776-7, 776-8, 776-9
776-10
Dup
Spike Spike Spike
Constituent % Rec % Rec RPD
Benzene 71.77 75.61 5.21
Toluene 72.62 75.97 4.51
Ethyl Ber~ene 74.14 78.47 5.67
, LABO RATO'RI ES, INC.
P~LEU~ J' J' EGUN, REG. CHEM. ENGR.
4100 PIERCE RD., ~KERSFIELD, ~LIFORNIA 93308 PHONE 327-4911
GROUNDWATER ~SO~CE' INDUSTRIES Date .Re~ted~ 02/07/90 Page 1
P. O. BOX 9383 Date Rece~vedz 01/25/90
5400 ~DRIN ~T L~oratory No. ~ 776-5
8~FIE~, ~ 93389
Attn. ~ C~US ENGE~T ..... 835-7.700
~!__..~.~_._ .~_ -~" ._ .. ~ :__5 ....... - .......... "~- ':~ -:--: .... - ......:'- ~ ...... - 'i.~ -"~"-~ i-~'?--7 .U '-'~i-'~i'..' .... ~" -'~ ......
S~ple Description= pROjECT $150010-2~ S-WO-2 WASTE OIL T~K 2' 1/25/90 ~ 1~38 S~PLE .
CO~ECTED BY: ~US ENGEL~T
** ~ TOTAL CONTAMINANTS
'~ (Title 22, Article II, Californ£a Administrat£ve Code)
~a~plp ~esu~ts P.O.L. -'-'Units ................. ~ethod
Lead 9.81 3.5 mg/kg -6010
TOX None Detected 20. mg/kg *9020 I *'
Oil & Grease 70. 20. mg/kg 413.1 2
Requlatory C~£ter£a
Constituent~ STLC, mq/L TTLC~ m~/k~
Lead 5.0 1000.
Comment: All constituents reported above are in mg/kg (unless otherwise stated) on
an as received (wet) sample basis. Results reported represent totals
(TTLC) as sample subjected to appropriate techniques to determine total levels.
P.Q.L. - Practical Quantitation Limit (refers to the least amount of analyte detectable
based on sample size used and analytical technique employed.
N.D. - None Detected (Constituent, if present, would be less than the method P.Q.L.).
I.S. - Insufficient Sample
STLC - Soluble Threshold Limit Concentration
TTLC - Total Threshold Limit Concentration
REFERENCES: ;~":' (1) #Test Methods for Evaluating Solid.Wastes", SW 846, July, 1982.
(2) 'Methods for Chemical Analysisof Water. and Wastes', EPA-600, 14-79-020.
A-10
LABORATO , INC.
PETROI. EU¥ d' J' EGUN, REG. CHEM. ENGR.
4100 PIERCE RD., BAKERSFIELD, CALIFORNIA 93308 PHONE 327-4911
GROUNDWATER RESOURCE INDUSTRIES Date Reported~ 02/07/90 Page
P. O. BOX 9383 Date Received~ 01/25/90
5400 ALDRIN COURT Laboratory No.~ ?76-6
BA/CERSFIE~, CA 93389
Attn.: CLAUS ENGELHARDT 835-7700
..... ' F- . ' ~* ~ *~'- '. T ' :?'::~* --:--~i .... 7U~*~-*"*i~--~T~'-*:~==~-=~:=~=~~= ............. : ....... ~ii_i ~ ........... ~ .*-*~i =~
Sample Descr£ption; PROJECT #150010-2= S-WO-6 WASTE OIL TANK 6, 1/25/90 @ 1:40 SAMPLE
COLLECTED BY~ CLAUS ENGELHARDT
CONTAMINANTS
California Administrative COde)
Method
..... ~.* .... ~ ........... .Conet£tuente_... ............. **~_~ .............. Sample Results P.Q.L .... Units ............... Method ........... ~-Ref*';
Lead 7.21 3.5 mr/kg 6010 1
TOX None Detected 20. mr/kg 9020
Oil & Grease 152. 20. mr/kg 413.1 2
Regulatory Cr~teFia
Constituent~. STLC, mq[L TTLC. m~/k~
Lead 5.0 1000.
Comment: All constituents reported above are in mg/kg (unless otherwise stated) on
an as received (wet) sample basis. Results reported represent totals
(TTLC) as sample subjected to appropriate techniques to determine total levels.
P.Q.L. - Practical Quantitation Limit (refers to the least amount of analyte detectable
based on sample size used and analyt£cal technique employed.
N.D. - None Detected (Constituent, if present, would be less than the method P.Q.L.).
!. S. - Insufficien~ Sample
STLC - Soluble Threshold Limit Concentration
TTLC - Total Threshold Limit Concentration
REFERENCES: i :~,"
(1) 'Test Methods for Evaluating Solid Wastes', SW 846, July, 1982.
(2)~ *M~hod~_~ .C .heroical Analy,i, of Water and Wa,tee*, EPA-6OO, 14-79-020.
A-il ~ '
" i 5400 Aldrin Court
i: Bakersfield, California 933t'3
. oUndwater resources, inc. i TelephOne: (805) 835-7.700
" Tele.-Fax: (805) 835r7717
CHAIN OF CUSTODY RECORD !: ..
LAB DESTINATION: PROJECT NUMBER:L~bO/O"~_ "'C4f_~.~
/3C P.O. NUMBER~~~ PROJECT CONTACT:
SAMPLER(S): (Sto~ture) z ~ ~
~ ~' COUNTY: I~v~
LAB SAMPLEz~. ANALYSI'S SAMPLE CONTAINER
NUMBERNUMBER DATE TIME SAMPLE LOCATION~z
0 REQUESTED TYPE TYPE
- ~ s-~-,c /~r-~o /z.'o~Bp,7 c" ~' - '" Yor/ //~j~
-lo S-aw-6 l-~r-fo~:o7 i~rd/~.k ~?,.4.~' l, '~ ~, lo, I .
sPECIAL INsTRuCTIONs: U~ ~~ .
POSSIBLE SAMPLE HAZARDS: _
1, Relinquished by:'~~' ate/Ti . ReceiVed by:' .~ "Date/Tlme:
I. Rellnqulshe~ ~y: ~ate/llme: Recelve~ B~: :
1. Rel~nqu~she~y: ~ate/llme: Received ~-." ' Date/lime:
!. ~ellnqu~shed ~y: ~ate/llme: Roce~ve~ ~y. ~; ~:
BWItION~£NTAL
r'
LABORATORIES, INC.
~O~E~ ~ ~ EGUN, REG. CHEM. ENGR.
4100 PIERCE RD., ~KERSFIELD, CALIFORNIA 93308 PHONE
Purgeable Aromatics
(SOIL)
, Gz~undwater ResoL~ces, Inc. Date of'
Bakersfield, CA 93313
Attention: Claus Engle~ -~dt
Lab No.: 2077-1
.~S~.ple Desc: Project ~150010-2
S-D-8 3/09/90 1:15 Dispenser 8'
Date. F~le Date ~.ple ~ Date Analysis
Collected: Received @ Lab: Completed: '
09-Mar-90 09-Mar-90 15-Mar-90 ':' '.
Re~orting Analysis Reporting
Constituent Units Results Level
Benzene ug/g none detected 0 7
Toluene ug/g 2.2 0 7
Ethyl Benzene ug/g 4.4 0 7
p-Xylene 1 ug/g 14 0 7
m-Xylene ug/g 7.8 0 7
o-Xylene ug/g 290 0 7
Total Petroleum
H~drocarbons ug/g 4100 20
(Gasoline)
TEST METHOD: TPH by D.O.H.S. / L.U.F.T. ~t?~d.
Individual constituents by Modified EPA ~%hod 5020/8020.
As Received Basis
Comments:
California D.O.H.S. Cert. ~102
.- 'A-i3
~"~,. ,~ · F. JWIFIOI~¥ENTAL
~,.,.,,~.,. LA B O R AT O R I E S, I N C.
P£TROL£U¥ J' J' EGLIN, REG. CHEM. ENGR.
· 4100 PIERCE RD., BA~(ERSFIELD, CALIFORNIA 93308 PHONE 327-4911
Purgeable Aro.mtics
(SOIL)
G~dwater Resouz~es, Inc. Date of
5400 Aldrin Ct ....................... RePO_..r~:' 16-Mar-90 ._. ~ ....
Attention: C~aus Engle -hardt
~ab Ho.: 2077-2
Sable Desc: Project #1500~0-2
-~ S-D-l! 3/09/90 1:40 Dispenser 11' ~
09- -Ha~-90 09- 'Ma~90 15-M~c-90
Miniature.
Reportir~ Analysis Reporting
Constituent Units ' Results Level
Benzene ug/g none detected O. 6
Toluene ug/g 1.0 O. 6
Ethyl Benzene ug/g 1.4 O. 6
p-Xylene ug/g 27 O. 6
m-Xylene ug/g 50 O. 6
o-Xylene ug/g 92 O. 6
Total Petroleum
Hydr~ar~ns ug/g 17 O0 20 ~
(Gasoline)
TEST METHOD: TPH by D.O.H.S. / L.U.F.T.
Individ,zal cor,-~tituents by Modified EPA ,mth¢~l 5020/8020.
As Received B~is
Co.~nts:
California D.O.H.S.'Cert. ~102
A-14
LABORATORIES. INC.
o' d. J. EGLIN, REG. CHEM. ENGR.
PETROLEUM ' 4100 PIERCE RD., ~KERS~IE~D, CALIFORNIA 93308 PHONE 327-49tl
~geable ~.~tics
(~IL)
....... G~=~dwa~r Res~es ,..!nc.~-~ .... ~--~-'-[~ ....... = ~'~" ~' ~:'-Re~:' 16-~[~z90' ~ .... ~.~--
5400 Aldrin Ct. .
~rsfield, CA 93313
At~ntion: Claus ~le~t
~ No.: 2077-3
~ple ~sc: P~ject ,150010-2
S-~14 3/09/90 2:20 Dish. er 14'
~ ~le ~ ~le ~ ~lysis
~ll~d: R~eiv~ ~ ~b:
09-~-90 09-~r-90 15-~-90
Ming~,
Re~rting ~alysis .. Re~i~
~ti~ent Uni~ Res~' ~vel
~r~ene ~/g none de~ O. 6
Toluene ' ~/g 1.4 O. 6
Et~l ~ene ~/g 1.7 O. 6
p-Xylene ug/g 27 O. 6
~Xylene ~/g 55 O. 6
o-Xylene ~/g 81 O. 6
To~l Pet~le~
Hy~ar~ns . ~/g 1900 20
(Gasoline)
TEST MfTHOD: TPH by D.O.H.S. / L.U.F.T.
Individual cormtituents by Modi£ied ~PA .mt~l~. 5020/8020.
As Received Basis
Comments:
Califor~ia D.O.H.S. Cert. ~102 ..,
A-15
LABO RATO RI ES, IN C.
J. J. EGLIN, REG~ CHEM. ENGR.
PETROLEU¥
· 4100 PIERCE RD., BAKERSFIELD, CALIFORNIA 93308 PHONE 327-4911
BTXE/TPH GASOLINE.
Quality Control
Groundwater Resources, Inc. Spike ID: 2051-1
.... :-': "' :- ' ~ 5400'A~cbrin Ct. :'~: :-:----'~:~:<-~'r~__~u~:::~'----r. '-.:~_~:~__~--. -:---': -r'-: Ar~lysis-Dat~-:--,~lS-Ha~9O~-: ...... --. ......... = ....
~ -Bakersfield, CA 93313 S~.ple Matrix: soil
Attention: Claus En~el~rdt Units: u~/g
~. Quality Control
' ...... - .... ' ................. -fO~' 'Lab 'Nos: ' 2077- I -, ~2077-2, -2077-3 ........... · .....
Dup
Spike Spike SpiP~
Cor~tituent % Rec % Rec RPD
Benzene 87.37 84.22 3.67
Toluene , 89.64 87.34 2.60
Ethyl Benzene 92.96 89.32 3.99
QC Co.~nts:
A-16
Bakersfield, California 93313
groundwater resources, inc. ~ Telephone: (805) 835-770~
'~ CHAI~ OF CUSIO~ ~[CO~O ~ lele-Fa~' (805) gJ5-7717
LAB DESTINATION: PROJECT NUMBER:~Oz6,-~ PROJECT CONTACT: .~~ ~*/40~.
z~
~ L. ~ ~-- u COUNTY: ~ ,
LAB SAMPLE LOCATION Qz A~ALY$1S: SAHPL[ CO~TAI.NE~
NUMBER NUMBER DATE TIME SAMPLE u
o REOUESTED TYPE TYPE
-~~-I1 t-f-Y9 /.'fro r)~r~ ii~~ ~0~1 ~//
1. RelinquiShed by: 6'~aof ~~4~Date/Tlme:' 3--?[70 Received by: ,. ~ Date/Time:
t RelinquiShed by: Date/Time: Received by: ~, Date/Time:
1. Relinquished by' Date/Time: Recelved byi Date/Time:
~. , :~-- ~.~ ~ ,: ~ ,'. '.~-~ ~',1 ~ ~/~1 f ~I. ~ ~',.~1 ~" ,~
APPENDIX B
ANALYTICAL RESULTS
CHAIN OF CUSTODY RECORDS
TEST HOLE NO. 1
SMC Laborator Analytical £hemistr
(
Client Name~ D.R. Smith & Associates
Address = 7201 Fruitvale Ext.
Bakersfield, CA 93308
~- - ~-' -?~: .... : i UU '. ' ' '__: ~ ~':'i"E?i~?~ ..... .'-'71~i~-~51~''~?~?~?~'~-'~-:~:~=: "= ~'~= ~ .......... '. -~ "~- ~- -~-~ i_ '. ' .->- ~= ~ ' -'~': ~- ....
~ Date samples received ~ 07-25-90
Date analysis completed= 07-26-90.
Date of report ~ 07-26-90
Job Site~ Sequoia Paint Attn~ Tom Gutcher.
RESULTS OF ANAL¥SIS~
%2428 ID~ %1 ugm/gm MDL,ugm/gm
Benzene ND 0.1
Toluene ND 0.1
Ethylbenzene .10 0.1
p-Xylene .33 0.1
m-Xylene .63 0.1
o-Xylene .70 0.1
Isopropylbenzene .10 0.1
TPH (Gasoline) 15 1.0
Method of'Analysis for BTX/TPH (Gasoline)= 3810/8020 (FID)
MDL = Minimum Detection Level
TPH = Total Petroleum Hydrocarbons
ugm/gm = micrograms per gram
ND = None Detected
Brian
Laboratory Supervisor
3155 Pegasus Drive · Bakersfield, CA 93308 · (805) 393-3597
P.O. Box 80835 · Bakersfield, CA 93380 · FAX (805) 393-3623
B-1
' CHAIN OF CUSTODY RECORD
LOcation of Sampling Collector., ~Client
Name: · i Name:
Company{ 'g~dD~O//~ P/~/~7- company: D.R. Smith & Associates Company:
Address:~700 ~~ ~r~~ Address: 7201 Fruitvale Ext. ~ddress:~O~
Telephone: ( ) Telephone: (805) 589-7861 Telephone: ( , )
Bill to ~Property ~er ( ) Bill eo Collector Bill to Clien~ ( )
Laboratory No.
S~ple No. Date Time Description Analysis Requested ~ -
Relinquished By: ~~ ~~ . Company: D, L .f~,'r~] C Jrt
~-- Company: S~C A~ ': Date:
Receive~ By: ~ ~
· ~ ~. Date:
Re linqu~shed By: Company:
' ' Date:
Received By: Company:.,
Relinquished By: Company: ,.. .. Date:
Received By~ Company: :~ Date:
DUANE R. SMITH AND ASSOCIATES ., Sheet
SMC Lab~rato~ ~ Anai~ical Chemist~
Client Name: D.R. Smith & Associates
Address : 7201Fruitvale Ext.
Bakersfield, CA ~ 93308
Attention : Mr. Tom Gutcher
(. Date Samples received : 9-20-90
Date analysis completed: 9124-90
Date of report : 9-24-90
Project Name : Sequoia Paint
~3377 ID: ~2 THl~25' ugm/gm MRL,ugm/gm
Benzene ND 0.1
Toluene 0.26 0.1
Ethylbenzene ND 0.1
p-Xylene 2.7 0.1
m-Xylene 2.5 0.1
· o-Xylene 9.6 0.1
Isopropylbenzene ND 0.1.
TPH (Gasoline) 250. 1.0
~3378 ID: ~3 THI~30.' ugm/gm MRL,ugm/gm
Benzene 0.10 0.1
Toluene 2.4 0.1
Ethylbenzene 4.4 0.1
p-Xylene 20. 0.1
m-Xylene 20. 0.1
o-Xylene 36. 0.1
.Isopropylbenzene ND 0.1
TPH (Gasoline) 520. 1.0
~3379 ID: ~4 THl~35' ugm/gm MRL,ugm/gm
Benzene ND 0.1
TOluene 0.68 0.I
Ethylbenzene 2.0 0.1
p-Xylene 7.9 0.1
m-Xylene 7.9 0.1
o-Xylene 13.0 0.1
Isopropylbenzene 2.0 0.1
TPH (Gasoline) 310. 1.0
Method of Analysis.: 3810/8020 (FID)
MRL = Minimum Reporting Level
TPH = Total Petroleum Hydroca6bons
ugm/gm = micrograms per gram'(ppm)
ND = None Detected
Brian T~;~psoff
Laboratory Supervisor
3155 ~gasusDrive · Ba~rsfield, CA93308 ° (805)393-3597
EO. Box80835 · Bakersfield, CA93380 · FAX(805)393-36~
B-3
~* CHAIN OF CUSTODY RECORD !i
,i Client
Location of Sampling Collector
Company~ ~E0~ P~H~/T' Company: D.R. Smith &' AssOciates Compa'~y: S~40/;~
Address~ '700 ~~ ~r~~ Address: 7201 Fruitvale' Ext. ~d~ress: 700
Telephone: ( ) Telephone: (805) 589-7861 Telephone: ( )
Bill to:Property ~ner ( ) Bill to Collector ~ Bill to Client ( )
Laboratory
No.
S~ple No. Date Time Description ~a~ ~- ~u~d
Received By: ~ /~.~ Company.: ~~ ~ .
~ Date:
Relin~ished By: Company:
~ Date:
Received By: Company:
~ Date:
Relin~ished By: Company:
Received By: Company: Date:
', DU~E R. SMITH ~ ASSOcIATEs Sheet
APPENDIX C .....
HEALTH AND SAFETY CONSIDERATIONS
.' HEALTH AND SAFETY CONSIDERATIONS
The responsible party for the work will be Duane R. Smith and
Associates personnel. The possible hazardous materials encountered
.... ~ii 1' -~e"~'e'~:~0ieU~-' pr-~u~t i% :'Ttypicatly .gasoline ,'. :~ies~l ::~f:u~'~-,-:----~hd ~--: ...... :. '"
waste oil). These constituents should occur at. relatively Iow
levels. The constituents will be blended With soil.
PID meter will be used to monitor vapors in the breathing zone of
workers. If there are significant readings for a sustained period,
the drilling operations will be suspended and the work reevaluated.
Recognition of hazards,'whe~her it be from instrument readings,
odor, irritation, visibility, headache, dizziness, or fatigue, is
important, but it is equally important to take appropriate aCtion
when a hazard is recognized. If the problem cannot be promptly
corrected, we will back off from the exposure source and obtain
assistance to solve the problem. Work practices and engineering
controls will be devised to minimize potential exposures. For
example, we will work upwind of any Potential exposure source.
Air'purifying respirators with combinatiOn organic vapor/acid,
gas/dust., fume, and mist cartridges will be on location. These
will be worn when Hnu readings persist above significant levels in
the breathing zone. If there is eye irritation, fUll-face'
........... r. espirato~s.will be_used~ ...... .
C-1
Tyvek coveralls will be worn as necessary to avoid skin contact
with contaminated soils. Chemical resistant gloves and boots will
also be worn as necessary to avoid hand and foot contact with
contaminants. All personnel will wear hard hats when working near
--the drilling-rig.-~, All personnel involved in~drilling.-.and~-~sampLe
retrieval have received training as specified in the OSHA Hazardous
Waste Operations and Emergency Response Standard [29CFR 1910.120].
......... The.~physical,~hazards associated with operating adrilling..~rig and_ '
sampling equipment must be recognized. Individuals not directly
involved in drilling' shall stand back at least the distance of the
vertical boom.
The potential hazards involved in the job will be reviewed with
all personnel including subcontractors working on site.
Prior to commencement of .work, emergency evacuation routes will be
established. A "safe zone" location will be established taking
into account weather conditions, site activities,, and other factors,
as necessary.
'Duane R. Smith and Associates personnel will coordinate activities
in an emergency situation. Arrangement will be made for transportation
to a hospital in the event of an accident or exposure to hazardous
materials that produce organic symptoms in the exposed party.
C-2
5400 ALDEIN CT.
groundwater resources in¢ BAKERSFIELD, CALIFORNIA93313
Class A/Haz License No. 520768
Ii" '~'") ' '
'~'~'- '~'"'"'~ - ........ ~UZff? '__ _,_~_Z ?'-; .L.--:Novel?~her~. ~-~7 z .... D~- ~'~-''~:~-''~=:~-':~''~0 .-.c~- L-~--''~ .... -~-~ ...... ~~~~.~/. ~~.~ ~,~q~. ~..~ ~&,.F~_.~.~uz2~z~-'-- ...... ~,~ ~-~ '
Co~ of Kcm
~p~en~ of ~~en~ HeM~ S~s
27~ M S~t, S~m 3~
. ~B~emfiel~ C~o~a 93301
': ....................... S~uo~a P~ ..................... ~'~'~'~' .................................. '
7~ B~er
B~mfiel~ ~~a
De~ Ms. D~g,
Gro~dwa~r Resoles Mc. (G~), a ~SNA ~dus~s comply, h~ been m~ed m c~ out
a site ~sessment a~ ~e Sequoia P~ f~ a~ 7~ B~er Sm~ ~ B~ersfield. ~p follow~g
wor~l~ is sub~ f~ yo~ approvM.
BACKGROUND
On 1~u~ 25, 1990 G~ mmov~ ~o ~der~und fuel ~, a ~ g~on gaso~e ~ ~d a
2~ g~lon w~e oH ~, ~m ~e Sequoia P~ pm~ a~ 7~ B~r S~et ~ B~emfiel~ ~e
~s were repone~y ~s~ ~ 1982 ~d rem~ed in se~ice un~ 1987 a~ ~e foyer W~lY
Tucker automobile ~Mcmhip.
Soil was s~pled at a dep~ of ~o ~d sk feet benea~ ~avh ~, benea~ ~e gasoline ~spens~r
~d un~r ~e pr~uct ~e h~ay be~n ~e ~spenser ~d ~e ~ (see plot pl~, Pla~ 1). Th~
~spenser w~ l~amd ~ a close~ a~ ~e wes~ side of ~e m~ b~l~g on ~e sim wMch necessita~
us~g a h~d auger to ob~ s~ples benea~ ~e contra fl~r of ~e s~c~.
~1 s~pl~s we~ ~Myzcd by BC Laboratories in B~cmfield. ~ose ~s~ia~ed wi~ ~c gasol~
system were msmd for B~ ~d ~H (g~o~e). No hy~bons were ~ected ~xcept in ~
s~pl~ ~m sk fee~ benea~ ~e ~spenser which con~ed 32.55 ppm to~ xylenes ~d 93~ ppm
~H (g~o~e). ~e waste oH s~les were ~My~ f~ ~H (o~ ~d ~ase), to~ le~ ~d
hMogenated hy~bons (TOX). No h~og~na~d hy~bons ~d back~ound levels of to~M
le~ ~d ~H (oil ~d ~ase) were mpom~.
A ske assessment of ~e con,nation ~camd by ~e sk f~ ~spenser s~ple was mqu~d by
~e Kem County Dep~en~ of Bn~o~en~ He~ Se~c~s. Two attempts wer~ mad~ to
dete~n~ ~ ve~c~ ex~en~ of ~e gasol~e plum~ un~r ~e ~spenser us~g a h~d auger. On
M~ch 9, 1990 GRI ob~ned s~ples a~ a depth of 8, 11 and 14 fee~, M1 of wMch contained
sig~c~ lewls of g~oHne constituents. On July 25~ Du~e R. S~ ~d Ass~iams augured a
hole to 25 fee~ wMch w~ lamr ~e~n~ ~o 3~ feet ~d collected s~ples a~ 20, 2~, 30 ~d 35 f~t.
~w to m~cra~c oon~cn~afions of ~on~nafion wer~ prcscn~ in ~s~ samples. ~ msuks for
'~ ...................... ~-'-~ s~pHng ~ffO~ a~ ~e ~s~ns~r ~ Hst~d'~low ~-Tabl~ 1.~
MAILING ADDRESS: P.O.' BOX 9383, BAKERSFIELD, CA 93389 (805) 835-7700
LOS ANGELES 1213) 724-3147
Ms. Flora Darling
County of Kern ·
Department of Environmental Health Services
November 8~. 1990
Page Two
TABLE 1
ANALYTICAL RESULTS FOR DISPENSER SAMPLES (in ppm)
DePth Benzene Toluene Ethlybenzene Xylenes TPH
(gasoline)
6 FT ND ND ND 32.55 935
~8Fr · ND 2.2 4.4 311.8 4100
11 FI' .ND 1.0 1.4 169 1700
14 FT .... ND 1.4 1.7 .... 163 1900
20 FT .................... ND ......' .... ' .......... ND .............. ........ 0:1'0 ................. 1~66 ............. -'-- 15'~'-~''''' --'-~
25 l:rr ND 0.26 ND 14.8 250
30 Fr 0.10' 2.4 4.4 76 520
35 Fl' ND 0.68 2.0 28.8 310
The contamination extends beyond the reach of a hand auger and a Ixuck mounted auger drilling
rig will be required to complete the characterization of this site.
GEOLOGY AND HYDROGEOLOGY
The site lies in a residential and business district in East Bakersfield within two and one-half miles
of the Kern River to the north. It is underlain by unconsolidated alluvial sediments deposited by
the Kern River through time1. Due to the location's, proximity to the river and its Sierra Nevada
Mountain source area, the soils in the area are expected to consist mostly of coarse quartz-rich
sands and gravels. Nine and one-half feet of surface silts underlain by sands and gravels were
logged in the test hole augered by Duane R. Smith and Associates (Appendix 1).
According to maps published by the Kern County Water Agency2 depth to groundwater of the
regional unconfined aquifer is approximately 160 feet. A body of shallow perched groundwater
· also occurs in the vicinity where clay layers interrupt the downward movement of water. The most
recent map for the Summer of 1989 shows the northern lobe of this perched water to be situated
south of Bakersfield, although in the past it did extend into the area3. This information and the lack
of groundwater occurrence in the D. R. Smith auger hole indicates that no perched water is to be
expected.
PROPOSED BORINGS
Two borings are proposed to complete the characterization of this site (see plot plan, Plate 1).
Boring #1 will be located at the gasoline dispenser and it will be angle drilled under the dispenser
and the building in which it is located. It will be advanced to a depth beyond 35 feet and at least
ten feet deeper than the last detected contamination as indicated in the field by odors and readings
recorded by a photoionization meter. Its objective will be to determine the vertical extent of the
gasoline plume.
Ms. Flora Darling
County of Kern
Department of Environmental Health Services
November 8~ 1990
page Ttn'ee
Boring $$2 will also be angle drilled beneath the building, but at a location 12 feet north of Boring
#1. It will be drilled 10 feet beygnd the last detected contamination. Its purpose will be to
delineate the lateral extent of the plume. Because of the localized .origin of the leak and because of
the porous nature-of' the underlying sOils, 'it is anticipated 'that the'lateral Spread of the"
contamination will be limited. Drilling the second hole with a 12 foot offset should be sufficient to
intersect the outer margins of the plume. Should high levels of hydrocarbons in the secOnd boring
indicate the lateral extent of contamination is greater than anticipated, a third boring will be made.
pROCEDURES
.......... The"borin~s Will be made by RESNA Industries' uSin~ a holl0v~~ s~e~: ~/ii'ger drilling rig. Samples
will be obtained every five feet with a California split-spoon sampler. A GRI geologist will
describe the samples, screen them with a photoionization detector and seal them in brass sleeves
with teflon lined caps. The samples will be labeled and chilled on ice and then taken to SMC
Laboratory, 3155 Pegasus Drive, Bakersfield, for analysis under a chain o.f custody document.
Selected samples will be analyzed for BTXE and TPH (gasoline).
Augers will be steam cleaned between holes to prevent mss-contamination. Contaminated soll
brought to the surface by the drilling operations will be place on plastic sheeting and covered for
later disposal at a proper facility. Holes in which contamination is found will be abandoned by
filling them with cement slurry by the ~emie method. If no contamination is indicated, the borings
will be backfilled with clean soil brought to the surface during the drilling operation.
After field operations are completed and samples analyzed, a report will be prepared for your office
with all results, interpretations and recommendations for remedial action ff required.
HEALTH AND SAFETY
All GRI employees have received the Health and S~ety training required by OSHA for hazardous
waste site operations (29 CFR 1910.120). While conducting the borings, personnel will be
equipped with a photoionization detector and LEL-oxygenmeter with Which to monitor the air for
organic vapors and combustible gases. Personnel are also issued air-purifying respirators (APR)
with organic vapor canisters which can be donned if conditions warrant. One self-contained
breathing apparatus (SCBA) is also available on location.
Gasoline fuel constituents are the identified hazardous substances at the Sequoia Paint site. The
more volatile components, especially benzene, pose the greatest health hazard. The permissible
exposure limit for benzene is 10 ppm, which was not exceeded in any of the soil samples.
Because of the outdoor location and the intermittent nature of drilling operations, it is not
considered likely that personnel will be exposed to elevated levels of hydrocarbon vapors for any
length of time. Under these conditions personnel will work under "Class D" protection.. If odors
and elevated readings are noted on air monitoring equipment, APRs will be put on and operations
suspended till site safety is evaluated. Colorimeter tubes can be used to determine the
concenlrations of specific contaminants in the air.
A "tailgate" safety meeting will be held at the site prior to commencing operations at which all site
hazards and procedures to follow in event of an accident will' be reviewed.
Ms. Flora Darling
County of Kern
. Department of Environmental Health Services
November 8, I990 :
Page Four '
REFERENCES
..... :-'~-' '" ..... '~-- ":"-'~'"---i:~': ': Daie;"R]~I]~, French, James' J. 'and Gordon,'G.V.~ J~rie~ 20, ~i966]
water Geolo~ md Hy~ology of.~e Kern ~ver Alluvi~-Fm ~ea,
C~o~a: U.S.G.S. ~en-F~e Repon 66-21.
2. Pyle, Stum T., CI~, ~omas N. md Ribble, George E., May 1990.
.. Kern Co~ Wat~ Agency Water Supply Rep~ 1989.
........ 3. ~le, Stum T., md ~bble, George E, May 1988. K~m_Coun~...~ater.
...... ' ....... ':-~ ..... '" ..................................... AgencY Wa~r SuPply Re~n'1987: ....... ~ '" ~' ' ..... -
~ you have my questions ~ ~e ~ ~fion, plebe c~ me at 805-835-77~.
Ve~ ~y yom,
~oj~t ~ologst Re~stem~ol/~t ~20
m: ~. J~ Elder, Sequoia P~t ~.~ ~ REX j. YOUNG
200 GALLON 4000 GALLON
WASTE OIL TANK .' rANK ·
(removed) .. POLES (removed)
GATE
PRODUCT LINE , UTIUTY LINES
ASPHALT DRIVE
BORING # 1
CLOSET
LEGEND
PRELIMINARY
SAMPLE
LOCATION N SCALE
PROPOSED I 1 INCH = 20 FEET
ANGLE BORING
LOCATION ·
EAST 19TH STREET
~ SEQUOIA PAINT PLATE
groundwater; resources, inc. 700 BAKER STREET
BAKERSFIELD, CALIFORNIA 1
~envi~r°r~m~ntal/ge0t~ch-n~icalse-r~i~ ............. PLOT pLAN '"
ENVIRONMENTAL
LABORATORIES, INC.
PETROLEUM J' J° EGLIN, REG. CHEM. ENGR.
4100 PIERCE RD., BAKERSFIELD, CALIFORNIA 93308 PHONE 327-4911
· ' Purgeable Arc,tics
(SOIL)
.~_3~. ~_ /_-'~_ '~£iJ-~3-. ~-- £L2-*---~.-..-~~.-~-~I~ ......... ?~--. ~'"'i ' -- .7 . . -. ~ ~L.'7'.- ~' ~ . - . _ L .' .... ' ..~ "_ _~ ~.3 '~ -. -- ..... ~ ' '=~" i~L~"L~"~--- ~ ..... ~_
G~wa~r Resole Ind~tries ' ~ of
5400 AlVin Ct Re~: 05-Feb-90
~rsfield, CA 93313
At~ntion:
~b No.: 776-1
~le ~sc: S-~2 Dis~er 2' 1/25/90 8 11:22
Date Sample Date S~ple Date Ar~alysis
Collected: Received @ Lab: Completed:
25-Jan-90 25-Jan-90 02-Feb-90
MinJgm~n
Reporting Analysis .Reporting
Constituent Units Results Level
Benzene ug/g none detected 0· 03
Toluene . ug/g ' none detected 0.03
Ethyl Benzene ug/g none detected 0.03
p-Xylene ug/g none detected 0.03
m-X¥iene ug/g none detected 0.03
o-Xylene ug/g none detected 0.03
Total Petroleum
Hydrocarbons ug/g r~ne detected 2.00
TEST METHOD: TPH for gasoline by D.O.H.S.L.U.F.T.' r~mthod.
Individual cormtituents by Modified EPA r~mthod 8020·
As Received -Basis
California D.O.H.S. Cert..~102
ENVIRONMENTAL
LABORATO RI FF;_, INC.
PETROLEUM J' J' EGLIN, REG. CHEM. ENGR.
4100 PIERCE RD., BAKERSFIELD, CALIFORNIA 93308 PHONE 327-4911
Purgeable Aromatics
(SOIL)
5400 Aldrin Ct Report: 05-Feb-90
-Bakersfield, CA 93313
Attention:
Lab No.: 776-2
Sample Desc: S-D-6 Dispenser 6' 1/25/90 @ 11:38
Date Sample Date Sample Date Analysis
Collected: Received @ Lab: Completed:
25-Jan-90 25-Jan-90 02-Feb-90
Reporting Analysis Reporting
Constituent Units Results Level
Benzene ug/g none detected 0.30
Toluene ug/g none detected 0.30
Ethyl Benzene ug/g none' detected 0.30
p-Xylene ug/g 3.04 0.30
m-Xylene ug/g 4.95 0.30
o-Xylene ' ug/g 24.56 0.30
Total Petroleum
Hydrocarbons ug/g 935.00 20.00
TEST METHOD: TPH for gasoline by D.O.H.S.L.U.F.T. ~r~thod.
Individual constituents by Modified EPA ~ethod 8020.
As Received Basis
Comments:
California D.O.H.S. Cert. ~102
ENVIRONIItEIVTAL ~
LABORATORIES, INC.
P~TRO/.~t,/~ J. 'J. £GLIH, REG. CHEM. ENGR.
4100 PIERCE RD., BAKERSFIELD, CALIFORNIA 93308 PHONE 327-4911
Purgeable Aro~mtics
'...: .... . ...... ::-_:.-:: .:-:::-: ..... --.: ...... ~ .......................... (SOIL) ...... . :.:::_:-..~ ......................................................
........
Groundwater Resource Industries Date of
~5400 Aldrin Ct Report: 05-Feb-90
Bakersfield, CA 93313
Attention:
Lab No.: 776-3
Sample Desc: S-P-2 Piping 2' 1/.,.5/90 @ 11:55
Date Sample Date ,~k~ple Date Analysis
Collected: Received @ Lab: Completed:
25-Jan-90 25-Jan-90 02-Feb-90
Reporting Analysis Reporting
Constituent Units Results Level
Benzene ug/g none detected O. 03
Toluene ug/g none detected O. 03
Ethyl Benzene ug/g none detected O. 03
p-Xylene ug/g none detected O. 03
m-X¥1ene ug/g none detected O. 03
o-Xylene ug/g none detected O. 03
Total Petroleum
Hydrocarbons ug/g none detected 2. O0
TEST METHOD: TPH for gasoline by D. 0. H.g.L.U.F.T. rr~thod.
Individual cor~tituents by Mc~dified EPA rrethod 8020.
As Received Basis
California D.O.H~S. Cert. $102
.ENVIRONMENTAL
LABORATORIES, INO.
PETROLEUM J' J' EGLIN, REG. CHEM. ENGR.
4100 PIERCE RD., I~KERSFIELD, CALIFORNIA 93308 PHONE 327-4911
Purgeable Aro~mtics
(SOIL)
-Groundwater Resource Industries .....
5400 Aldrin Ct Report: 05-Feb-90
Bakersfield, CA 93313
Attention:
'Lab No.: , 776-4
Sample Desc: S-P'6 Piping 6' 1/£5/90 @ 12:09
Date Sa~le Date Sa~le Date Analysis
Collected: Received @ Lab: Completed:
25-Jan-90 25-Jan-90 02-Feb-90
Reporting Analysis Reporting
Constituent Units Results Level
Benzene ug/g none detected 0.03
Toluene ug/g none ~etected 0.03
Ethyl Benzene ug/g none' detected 0.03
p-Xylene ug/g none detected 0.03
m-Xylene ug/g none detected 0.03
o-Xylene dg/g none detected 0.03
Total petroleum
Hydrocarbons ug/g none detected 2.00
TEST METH6D: TPH for gasoline by D.O.H.S.L.U.F.T. method,
Individual cor~tituen'~s by Modified EPA ~thod 8020,
As Received -Basis
California D.O.H.S. Cert. ~102
· ENVIRONMENTAL
LABORATORIES, INO.
PETROLEU~I J' J' EGLIN, REG. CHEM. ENGR.
4100 PIERCE RD., BAKERSFIELD, CALIFORNIA 93308 PHONE 327-4911
Purgeable Aror~tics
(.SOIL)
Groundwater-Resource Industries' ~-~-~ - --- ~ ' ~. :.-:~Date-of--~-~- ......
5400 Aldrin Ct , Report: 05-feb-9O
Bakersfield, CA 93313
Attention:
La~ No.: 776-7
Sample Desc: S-GE-2 Gasoline Tank East End 2' 1/25/90 @ 1:48
Date Sample Date Sample Date Analysis
Collected: Received ~ Lab: Cor~leted:
25-Jan-90 25-Jm,~-90 02-Feb-90
l~nir~m
Reporting Analysis Reporting
Constituent Units Results Level
Benzene ug/g none detected O. 03
Toluene ug/g' none detected O. 03
Ethyl Benzene ug/f none' detected 0.03
p-Xylene ug/g none detected O. 03
m-Xylene ug/g none detected O. 03
o-Xylene ug/g none detected 0.03
Total Petroleu~
· . Hydrocarbons . ug/g none detected 2.00
TEST METHOD: TPH for gasoline by D.O.H.S.L.U.F.T. ~etf~d.
Individual constituents by Modified EPA r~thod 8020.
As Received Basis
Comments:
California D.O.H.S.~Cert.~ ~102
· ENVIRONMENTAL
L NBO RATO RIES, INC.
PETROLEUM J' J' EGLIN, REG. CHEM. ENGR.
4100 PIERCE RD., BAKERSFIELD, CALIFORNIA 93308 PHONE 327-4911
Purgeable Aromatics
(SOIL)
5400 Aldrin Ct Report: 05-Feb-90
Bakersfield, CA 93313
Attention:
· ~
Lab No.: 776-8
S~le Desc: S-GE-6 Gasoline T~ East'End 6' 1/25/90 @ 1:50
Date Sample Date ,~r~le Date Analysis.
Collected: Received @ Lab: Co, fpleted:
25-Jan-90 25-Jan-90 02-Feb-90
Minimum
Reporting Analysis Reporting
Constituent Units Results Level
~enzene ug/g none detected 0.03 ,
Toluene ug/g none detected 0.03
Ethyl Benzene ~g/g none· de~ec~ 0.03
p-Xylene ug/g none detected 0.03
m-Xylene ug/g none detected 0.03
o-Xylene ug/g none detected 0.03
Total Petroleum
Hydrocarbons ug/g none detected 2. O0
TEST METHOD: TPH for gasoline by D.O.H.S.L.U,F.T. ~tf~.
Individual constituents by Modified EPA rr~thod 8020.
As Received ~is
Compliants:
California D.O.H.S. Cert. ~102
'ENVIRONMENTAL
LABORATORIES, INC.
PETROLEUM J' J' EGLIN, REG. CHEM. ENGR.
4100 PIERCE RD., BAKERSFIELD, CALIFORNIA 93308 PHONE 327-4911
Purgeable An~tics
(SOIL)
_ _-.....:::: _.~..~ ~ ~GrOundwater Resource .~ Industries-~.:~-~ .._-.~ ...... _:_: .... -'- Date ~'of ".~-
5400 Aldrin Ct Report: 05-Feb-90
Bakersfield, CA 93313
Attention:
LaG' No.: 776-9.
Sample Desc: S-GW-2 Gasoline Tank West End 2' '1/25/90 @ 2:O0
Date S~le Date S~ple Date Analysis
Collected: Received @ Lab: Completed:
25-Jan-90 25-Jan-90 02-Feb-90
Minimu~a
Reporting Analysis Reporting
constituent Units .Results Level
Benzene ug/g none detected' O. 03
Toluene ug/g none detected O. 03
Ethyl Benzene ug/g none' detected O. 03
p-Xylene ug/g none detected O. 03
m-Xylene ug/g none detected O. 03
o-Xylene ug/g none detected O. 03
Total Petroleu~
Hydrocarbons ug/g none detected 2. O0
TEST METHOD: TPH for gasoline by D.O.H,S. L.U,F.T. ~r~t~x~,
Individual constituents by Modified EPA ~r~thod 8020.
As Received -Basis
Comments:
-California D.O,H.S. Cert. ~102
ENVIRONMENTAL
LABO RATO RI ES, .I N C.
,OETROLEUltl J.J. EGLIN, REG. CHEM. ENGR.
4100 PIERCE RD., BAKERSFIELD, CALIFORNIA 93308 PHONE 327-4911
Purgeable Aror~tics
(SOIL)
5400 Aldrin Ct Report: 05-Feb-90
-Bakersfield, CA 93313
Attention:
Lab No.: 776-10
SamPle Desc: S-GW-6 Gasoline Tank West End 6' 1/25/90 @ 2:07
Date S~le Date Sample Date Analysis
Collected: Received @ Lab: Completed:
Reporting Analysis Reporting
Constituent Units Results Level
~enzene ug/g none detected 0.03
Toluene ug/g none detected 0.03
Ethyl ~enzene ug/g none detected 0.03
p-Xylene ug/g none detected 0.03
m-Xylene ug/g none detected 0.03
o-Xylene ug/g none detected 0.03
Total Petroleum
Hydrocarbons ug/g none detected 2.00
TEST METHOD: TPH for gasoline by D.O.H.S.L.U.F.T. rrethod.
Individual constituents by Modified EPA ,et?~ed 8020.
As Received B~is
California D.O.H.S. Cert. ~102
ENVIRONMENTAL
LABORATORIES, INC.
PETROLEUB J' J' EGLIN, REG. CHEM. ENGR.
4100 PIERCE RD.; BAKERSFIELD, CALIFORNIA 93308 PHONE 327-4911
BTXE/TPH GASOLINE
Quality Control Data
................ L------'~-7-+'~ ............. ~-'~ ~-- ~ '--~' ........ -~ .................... 7- "Z_L-~ Z~'~-'L2~'~-~Z--~
Gr0undWater-~R~s6urce':Industries ......... SPike- ID'~-. 776-8 ......
5400 Aldrin Ct Analysis Date: 02-Feb-90
Bakersfield, CA 93313 . Sample Matrix: Soil
Attention: Units: ug/g
~ality Control
for Lab Nos: 776-1, .776-2, 776-3, 776-4, 776-7, 776-8, 776-9
776-10
Dup
Spike Spike Spike
conStituent % Rec % Rec RED
Benzene 71.77 75.61 5.21
Toluene 72.62 75.97 4.51
Ethyl Benzene 74.14 78.47 5.67
QC Co~m~ents: '
E~IVIRON/~ENTAL
PETROLEUI~ J.J. EGUN, REG. CHEM. ENGR.
4100 PIERCE RD., ~KERSFIELD, CALIFORNIA 93308 PHONE 327-4911
GROUNDWATER ~SO~CE INDUSTRIES Date Re,fred: 02/07/90 Page 1
P. O. BOX 9383 Date Received: 01/25/90
5400 ~DRIN COURT Laboratory No.: 776-5
'-Attn.: C~US ENGEL~T 835-7700
S~ple Description: PROJECT ~150010-2:S-WO-2 WASTE OIL T~K 2' 1/25/90 ~ 1:38 S~PLE
COLLECTED BY: C~US ENGEL~T
TOT~ CONT~IN~TS
(Title 22, Article IZ, California A~inistrative C°de)
,
Method
Constituents $~ple Results ~ Units Method Ref.
Lead 9.81 3.5 mg/kg 6010 1
TOX None Detected 20. mg/kg 9020 1
Oil a Grease · 70. 20. mg/kg 413.1 2
~equlator¥ Criteria
Constituents ~ TTLC, mq/kg
Lead 5.0 1000.
Comment: Ail constituents reported above are in mg/kg (unless otherwise stated) on
an as received (wet) sample basis. Results reported represent totals
(TTLC) as sample subjected to appropriate techniques to determine total levels.
P.Q.L. = Practical Quantitation Limit (refers to the least amount of analyte detectable
based on sample size used and analytical technique employed.
N.D. ~ None Detected (Constituent, if present, would be less than the method P.QiL.).
I.S. = Insufficient Sample
STLC = Soluble Threshold Limit Concentration
TTLC = Total Threshold LimitConcentration
REFERENCES: (1) "Test Methods for Evaluating Solid Wastes", SW 846, July, 1982.
(2) "Methods for Chemical Analysis of Water and Wastes", EPA~600, 14-79-020.
, ~VVIRONMENTAL
LABORATORIES, INC.
PETROLEUItl J' J' EGLIN, REG. CHEM. ENGR.
4100 PIERCE RD., ~KERSFIELD, CALIFORNIA 93308 PHONE 327-4911
GRO~DWATER ~soURCE .INDUSTRIES Date Re~rted: 02/07/90 Page 1
P. O. BOX 9383 .. Date Received: 01/25/90
5400 ~DRIN COURT L~oratory No. ~ 776-6
~RSFIELD,_. ~ 93389 ~_
......... '-- ' 835-7700 ..... ~. *,::~..~:_::~:~-.<z:;:--::~_::_~:: .... ~'-~.c.:.*~-~*~"-.~ :'z'".-~** '~¥-~':~ .... ~:--.~-~
'Attn.: C~US ENGE~T ' :~ ................
S~ple Description: PROJECT $150010-2:S-WO-6 WASTE OIL T~K 6' 1/25/90 ~ 1:40 S~PLE
COLLECTED BY: C~US ENGEL~T
'TOT~ CONT~IN~TS
'(Title 22' ~ticle II, California A~inistrative Cod~)
........ '~'~ ~'-*~* ........ ' ..... * ....... ' ....... -~' ~=' *--~ "~ ~'~"-=- ................. "~- '- ~:--" '~':~* '*~" ~ Method
Constituents Sample Results P.O.L. Units Method Ref.
Lead 7.21 3.5 mg/kg 6010 1
~X None Detected 20. mg/kg 9020 1
Oil & Grease 152. 20. mg/kg 413.1 2
Requlator¥ Criteria
Constituents STLC, mq/L TTLC, mq/kg
Lead 5.0 1000.
Comment: All constituents reported above are in mg/kg (unless otherwise stated) on
an as received (wet) sample basis. Results reported represent totals
(TTLC) as sample subjected to appropriate techniques to determin~ total levels.
.P.Q.L. = Practical Quantitation Limit (refers to the least amount of analyte detectable
based on sample size used and analytical technique employed.
N.D. = ,None Detected (Constituent, if present, would be less than the method P.Q.L.).
I.S. = Insufficient Sample
STLC = Soluble Threshold Limit Concentration
TTLC = Total Threshold Limit Concentration
REFERENCES: (1) "Test Methods for Evaluating Solid Wastes", SW.846, July, 1982.
(2) "M~£hods~fo~ Chemical Analysis of Water and Wastes", EPA-600, 14-79-020.
0 ~ ' $400 Aldrin Cb{~'rt
' undwater resources iRC ~,. Bakersfield, California 93313
' ' : Telephone. (805) 835-7.7.00
~" Telex-Fax: (805) 835-7717
i CHAIN OF CUSTQDY RECORD
LAB DESTINATION: PROJECT NUMBER:.L~O[O'"~x PROJECT CONTACT:~' .v C-[Cu~ !~----~[~tt, Ul4'7L--
{ ~C P.O. NUHBER_. 3~55C :
SAMPLER S): e o ~ ~
Z~
LAB SAMPLE ANALYSIS : SAMPLE CONTAINER
NUMBER. NUMBER DA~E TIME SAMPLE LOCATION ~ ' '
o REQUESTED ~' TYPE TYPE
SPECIAL~ NSTRUCTIONS:. U~ f~ .
POSSIBLE SAMPLE HAZARDS:__- ....... 3.'~ '~ ; 3'.Z~
1. Relinquished by: ate/Ti . Received bY: . Date/Time:
1. RelinqUished by: Date/Time: Receivod b~: ': ' Date/Tim~'
1. ~ellnq~lsheO b~: Date/llme: Recelve~ ~: ' Date/lime:
CCR('Rev. ~i0/89) ~ITE: L~RATORY PlN~ JOBFILE YELLOW: S~PLELOG J,e~t,)(~:~ ~;~ 27[-~_
LABORATORIES, INC.
PETFIOLEUI4 J' J' EGLIN, REG. CHEM. ENGR. ·
4100 PIERCE RD., BAKERSFIELD, CALIFORNIA 93308 PHONE 327-4911
":" ~ ' '". ': .:'~ '~i-~'.~/-.
Purgeable Aromatics · ·
(SOIL) : '
5400 Aldrin Ct Report: 16-Mar-90
Bakersfield, CA 93313 ...... '
-...'., ':/.
Attention: Claus Englehardt
.. '.ii! ...-'::.
Sa~le Desc: Project ~150010-2
..... · ....... " '" ~;~'S-D-8.3/09/90' 1:15 D~spen~er 8"' · ~ ' ': : ':"~ ..... ' ........ '-~-.'."-
Date Sample Date Sample Date tmalysis"e:':
09- -90, 09- -90 15- -90 " ..-.
Re~~ ~ysis Re~~ · .-. -~.
~ti~ent U~ Res~ ~vel
~ene ~g none de~ ' 0.7
Toluene ~/g 2.2 0.7
Et~l ~ene ~'/g 4.4 0.7
~-Xyl'ene ~/g 14 0.7
m-Xylene ~/g 7.8 0.7
o-~lene ~/g 290 0.7
To~l Pet~le~
~~~ ~/g 4100 20
(Gasoline)
TEST ME. tOD: TPH by D.O.H.S. / L.U.F.T. ~f~thod.
Individual constituents by M~]ified EPA :~thod 5020/8020.
As Received Basis
California D.O.H.S. Cert..102
., EN¥1ROI~t, IENT,~L
LABORATORIES, INC.
~ PETROLEUlll J' J' EGLIN, REG. CHEM. ENGR.
4100 PIERCE RD., I~KERSFIELD, CALIFORNIA 93308 PHONE 327-4911
Purgeable Aro;~mtics
(SOIL)
..... ~ ........... -.._Groundwater ResoUrCes,-~--tnc.:: ...... ?:-::~-~.:~..:.-~.~..==-?~=.:_=~ ~_Date of_~_~_~:::_.
5400 Aldrin Ct. Report: 16-Mar-90
-Bakersfield, CA 93313
Attention: Claus Engle -hardt
Lab No.: 2077-2 ........
Sample Desc: Project $150010-2 · ' .....
'-' S-D-ii 3/09/90 1: 40 Dispense~: 11'~ · - .... ' '"'"'"'
' . · ~.. ' ....
Date S~le Date Sample Date AnalYsis
Collected: Received @ Lab: Completed:
09-Mar-90 09-Mar-90 15-Mar-90
Reporting Analysis Reporting
Constituent Units Results Level
Benzene ug/g none detected 0.6
Toluene ug/g 1.0 0.6
Ethyl Benzene ug/g 1.4 0.6
p-Xylene ug/g ' 27 0.6
m-Xylene ug/g 50 0.6
o-Xylene ug/g 92 0.6
Total Petroleum
Hydrocarbor~ ug/g ' 1700 20
(Gasoline)
TEST METHOD: TPH by D.O.H.S. / L.U.F.T. ~thod.
Individual cormtituents by Modified EPA ~t?~d 5020/8020.
As Received Basis
Co~r,~nts:
California D.O.H.S. Cert. $102
,' EN¥1RO~¥BVT4L
LABO RATO R! F?,, INC.
PETROLEUJI J' J' EGLIN. REG. CHEM. ENGR.
,, 4100 PIERCE RD., BAKERSFIELD, CALIFORNIA 93308 PHONE 327-4911
Purgeable Aromatics
(.SOIL)
5400 Aldrin Ct. Relw.,rt: 16-Mar-S0
Bakersfield, CA . 93313
Attention: Claus Engle[mrdt
- Lab No.: 2077-3
sample Desc: Project ~150010-2
'~ S-D-14 3/09/90 2:20 Dispenser 14" '.'. -~' - :~'""::"f:':'~:~':'i":'i~'("-
Date Sa[~ple Date -Sa~le Date Analysis
Collected: Eece±ved @ Lab: . Completed:
09-Ea~-90 09-Ma~-90 15-~a~-90 ....
Re~orting Analysis Reporting
Constituent Units Results Level
Benzene ug/g none detected 0.6
Toluene ug/g 1.4 0.6
Ethyl Benzene ug/g 1.7 0.6
p-Xylene ug/g 27 0.6
m-Xylene ug/g 55 0.6
o-Xylene u~/g 81 0.
Total Petroleum
Hydrocarbons ug/g 1900 20
(Gasoline)
TEST METHOD: TPH by D.O.H.S. / L.U.F.T.
Individual ¢ormtituents by. Modified EPA .et?~d 5020/802.0.
As Received Basis
Co~nts:
California D.O.H.S. Cert. ~102
'~ ENVIRO~tMENTAL
LABORATORIES, INC.
~ROLEUM J' ~' EGLtN, REG. C~EM. ENGR.
4100 PIERCE RD., BAKERSFIELD, CALIFORNIA 93308 PHONE 327-4911
BTXE/TPH GASOLINE
Quality Control Data
. .~..~ ..... ~-~-~...~Groundwater~Resources,. I.nc .. ~ ~. ~.~. ~_-_-~?~.~-:~..-_-~_~-~?~. Spike 'ID':~2051~1
5400 Aldrin Ct. Analysis Date: 15-Mar-90
Bakersfield, CA 93313 S~ple Matrix: soil
Attention: Claus Engelhardt Units: ug/g
-. ...... . ,.. ................... ',..~.~ .......... = ........... . .~ . ~..L~~ ,
for Lab Nos: 2077-1, 2077-2, 2077-3
D~p
Spike Spike Spil~
Constituent % Rec % Rec RPD
Benzene 87.37 84.22 3.67
Toluene 89.64 87.34 2.60
Ethyl Be. nzene 92.96 89.32 3.99
'. i.':'":..i~:..:. ~..!!~':..:]:-~.!~, Bakersfield, California 83313
.-j. groundwater resources,~inc? . ' ' .~.....:'..":"i::}:' '(..i~iii;.!~!~7." '" :. TelephOne:'i (805) 835-770.0
.'' REcoRD,'.I'' "'. ':!:i-!}}(?:'.",.".:. Tele-'Fax:;'~ (805) 835-7717
.' ~' CHAIN OF CUSTODY ':.? ' ,::'.,?~?:~i~.:~.'. '.. . -
~" ~-~---~ p.O. NUMBER ~_~'__~_L :
nature
. . · ~ .'~ .:
LAB SAMPLE . ANALYSIS . ~:~ :SAMPLE CONtaINER
NUMBER NUMBER DATE TIME SAMPLE LOCATION '~z .: .... :'": · - -'
o '.. 'REQUESTED'~ :'
~ ':'".~.,-- .' .~':- :..~ ~' ., :,
;
. .;
SPECIAL,INSTRUCTIONS: O~ ~L~ ,~ .~..~ ~M% . ..
!. RelinqUished by: ~1 &~~Date/T .. :'
~' , Ime:' 3-~/~ Received
I. Relinqffished by: Date/Time' Received by:' '. '~ Date/Time:
,- ~ · Recelved"fi~-;-:/:~.~.' ' ..
1. RellnquJshed by: Date/Time: ~, : ': Date/Time:
CC~ (~ev. I~/gg) ' .WHIT[: kA~O~A/O~Y PI~K: ~OgFIk[ Y[kkOW:
mt° " " An lyti al
· Labo .. -. . a c Chemis
'. -; ;"'', ,,'" ..... - · ' .' : ,' '.' · ' .~' ' '. i '''"' '" · !,.
"C~en~,;,N'ame~ D.:R.~ Sm~h'& °c'~a~es":' · '
.t... ~. .... . :..
.' .... Address .... ,','. t 7201'.'FrUi~vale Ex~.~'.,: ~.
· /;,.. -.:'..~;..[-..{ :.[:.~b~t,..'i~ :. Bakersfield, 'CA ~ 93308 i'..., ~ '
, ; :- .. ~.. [ ;'%., ~. ; '.,. .- . .... .,... . . , : . ;, ., ., , , , : ~,,'..--;:. ,.r,~,
...' ',..,Date; samples 'received t 07-25-90 '.~ ~ , ....
.:' ',..~.Da~e'..o~ .report ~ .~. ,.-~, t 07-26-90 . ;.... :. · · . . :
,: ;"-' ,' : .;;~":: 'f.'.' ' ~-' t': .. " .- '' ' ~ ' ' '- · ': ':-'""~ · ' -~--"
': :. '.¢~ ;-.'~,.';"'~:~..~' · .''' .. ; - ' ~ :'~ ~ ' [ · ; ' .'. : '.:',''~: '- : " .
.... · ' ' .'~ j' 't. ;~ .' ..= ~"-'~,~ {'' : .'-:' · ....... ' ....... ~ ' · ' ,- .... - -.' "
~ , t ; ; · : ~ ..
.'. ~"'.t".:,'.-.~'.'.~,'~,~ ".~; ".'-"~ :'- ::: ...' " ,. ;[!~,q--:.~ ' .' ,'...;. .U' .... ,'
.'....~ ~" ':.:' ~/4'"~" .,.4. ;'"~ :.'.:- '. : [,.;:.: "-' '." ' ' ~ .'-.'.i'.-' :':.:'-d'-t ".: ':':'. . .'
'~ '"]':5:~.~i74 Toluene' : .: '?.[:: {"" ' ~ NDe"" i .. :' · ' : ;' :':-."-':[ ::['..:,. :'.'.:...:.
, ., ,~.., :.Z~( , ., · ;,. · : .- .
..-j.. ,-t. ~ B2h~lbenzene.. '.
: .zo -. o.
' "...'i";i',~:;'J'p-xylene':. ' · ~ ' ~ .33 .. .0.1
."d..~ ~. :,. ·
~" ,_'L ~_.~ :'.,.: ..'.).....~. · ..... ., . , ......
.,... ;.,;,::: " 63 . '''; :' ~' '
'~,"-.:.'"'.r ~" ': '" , . .' .
.'.,.'-'[.1~2,.~ '~" '.:J~o-X~lene.~ '":' .~ ~0 .-;: '10 1
~ · h' :.t' . ' ..'.,'. "" · ;( : . ~ . . ; . : .... .'::'-
i'..:"-,J'
~' ~.:.~ .'.... ,. ,. ._
. .. ~,.j.-~:.. : ..,
i '...' ', ~.: ~.( . : . .:.
.:' , ~[ · ·
,:. ... ;.~.., ~.~. .,] . . ,. .... ~ ..'.' ~ : ,.
,.~ ' .'::ff. ['.:;..,~.~ ...:.. : ~....: ..... .. ~.: .. . ..~ ~
~. ":'~tj,.(~. ':..';' .:. ,t ; .,;, . ~ : .i ~..,("~
:' ~ . ~.:. f.~ .-.' . . ~', ¢ ...: .: . : ; . .....
~ {..,..:Re~hod of ~nalysi~ fo~. BT'X/TPR (~a~oline)~ 3810/8020 (FI~) ' ' ....
"' :MDL =;Minimum De%ection Level
~ '.TPH. = ~Total Petroleum Hydrocarbons
- ' '"~.'::,:ug:m/gm'=. micrograms' per gram /~ " .,"
" ~ :'"'ND =.:N°ne:De~ec~ed : ~ ~ . ,... , . ~ :
~..,~ ,~,..;.,:.t .:.~ ~-...~... ~. .,. . ....,., .,~,'" ~ .. .=... ::.'
'" ' ' '"' '"~'" ' ' ~ ~ ~ ": : ' : ':; ."
.""':.'r':';'"..":{ -'.' '
.. ...... , ~ . . .... [: . ~ ..
' f:,~ t :,; ".[, ' } '. ,'". . , ~ ~ · .'.'.
/ ~':.:)...... .. '.~'. ',.. .. -.=.:: ...
. . .., ..':..,: ' ,. [ : .~ . [. :f : .' ." . ,.. '...
'.:~"[ rian .... ,
~ : .i . ,. :
~-,:~tabora~orv_ _ _ , Supervisor " . '
~ '~.'. i ' ~: t..'' :;
' ~ f';f" .''~-'~.~ ;~:~,, ,/ .-., .';'.',":' ~'":'t';': ['"-;',', ; ,,: -: ~' ,.' .,
,,;~.':..-.'.~'f':'; ~ ' ~... ..... , .; .......; ..... ... ... .. ....
. . ~ .-~,.. ~ ~,, ; , , ~ ,, .:., . , .... ,, ['. ,..' ... : , '.
.................. ~-f-~?,..~-.~::~v~ ,/ . .. .... ',~e'~'~'~ ~;;r:'~:~ ...... ' ~
~: ' .. ~,, ('" .' .. · : · :'~.'..,'.;.'):t.':.l.:' [ '. .' · :.. : '' .-
~, .. '..:~.. ~ ' .
.; .. ,...' :i( . .:;.:. :. .:. . ::.:. ,.., ...
: .... . ....... ',,. ,, . , '.~. ~ :.'..', ,, . . ..
' '"' asus (805) 393-3597
"~'".: ' :' ~ ~:{ ' :' 3155 Pe Drive .. Bakersfield, CA 93308
. ~ . ":; P.O. ~x 80835 · Bakersfield. CA 93380 ' · F~ (805) 393.3623
Client
Company~ ~6~'O/~ P~/Wr Company: D.R. 'Smith &' Associates' C~PahY:'::E~o~,.
Address} 7Od ~~n Srm~ Address: 7201 Fruitvale Ext.~ ~,~..u~ '" Addre'~-7OO ~
TelephOhe:.( ) .. Telephone: (805) 589-7861/~.~,(~...
.... No__
S~ple N°. Date Time Description Analysis~ Requested Laboratory __
Relinquished By: ~~ ~~ ..... Company: D, ~ :~ "F~ '~f~OC/W~IDate:
Received By: B~~ . Company: 3~ & t~ ;:'~: .:~t,., .Date:
Re li'n~shed Company: Date:
ReceiVe~ By: Company:.' ~ ~('~ Date:
'%.-ASS'O'CI'ATES :
~ DUANE R- SMITH AN :. ::,~;~ ' Sheet
.. : ' " ..... ' :"- . :" .i . '
.i ~]~!~ ..'..' ' ~ .... ". '. ':'... , '.,'.'
· ~.,.,.,.. ~. ;.. ~ .....~ ,-....~ .;~ ;. . ..~..., ....... . .... ~ ..~.~ ~... ,..- .... , ,....-~
' '~ '~ : '. · . ~' "~'::~:/~ ~::..'~'::.:~
. · :'~?:.~:~ ..:L~..'~,,.: ~,,~'..-?.::...:~."u .':~ .-~. .~ .... . .'-.::.'."~:-??::¥:';:~?.~.?'. " ~:~::'.:~::".:"."~'.:'~'~:'~':?q..?":'~'?~'t-.~:':~'/~-:~?~::¥.':' '~:'~
..... .~:?':~'~..':..,..ua~e 'Samples~ecei'Ved ':'-'=' 9;20-;90"
.... :,-. Da~e o~-repor~,.. , .... 9-24-90 .. : . . .: - ...... ~ ..... .;:- .
~..';':,~ ..-..~ . :- .::~.. .: . . '.~.: :' :-;.:.~. .:.. .. ,.~,.', .~ .,. . . ..,.. . ': ......: .... .... ::~.~..'., :::[.~.:...: ..:..:..--,'
;;..~,: ~',[':.' ': ..... ~" ' ' ': '"':~' :' ' ..... '" :~':'~'~:~':'%.? ".'. ?; - ' .: · :' '..";-..,' '~',:.,:~[..:~::-'~:;-:~'::-':~'.~::t" .'.
, '...,. ~'.~:..,.~Protec~..Name '. Seauoia Pain~ ,.:-,-"u'~:.~ .::~.. -. . , ..., .,~. ,., ,: ...... ~-~,~,'....,~:~.~.;~¥ :~.,, .; ....
- ' ;~.¥'~[::.:~'{.'""f'~ ":4 ~" ': ,:'::~ ." :{" ' ' ::'. .:. · "~ .... :'~ ~'1'
,. ~;'~. ' , .. · · .; ~: .~ .-. · .-.. , · . '. t ~ /- .:-]" ':~ :-:~;~;.{,.~:' :,'~ ./;: 'V,~.:~' :-
," .-'r .:'." ~ '.".', ,_.~: .... ' : ['~ ..... : : ..... ' :'..': ;'~: ?'.~..;~:*.
'.." ::..-]:~f::)..~3377 .'+.I~=. ~2 ;. -' ~H'i"~-2:5',' "". ":'.-:'~g~gm
· ' .'.' ' ~ ~ --- ' . ...... ..'. :;'..~.:'.:-~-:L/; '..'.1:~'.; -..' .
Benzene ..:: ~':;., . ' (.;~.::".:;-,... ND ·
:":[ :'~.? ":" ~:..::~"~ "Toluene :, i "~, ~' -'. :" .... ~." :, ~'?[:~"0.26
::;"~:',':;~'::~".".;:': ~'.".~'f 'p-Xylene . · ~ ' '" ' . "'~: 2.7
':"~'~ ..... ':':'"'":m" - ~ ~'' ' ' 0
.F':e'""":~"~. Isopropylbenzene . - ....
..'~¥'~ ::jr ..:",:', .. ~- . q., .
,..:: . :'' , Benzene 0.10. 0 1 -. .'"
...... v . : , ' . ;' .. '.":'.['. ':",.::
.,.:~ ,...... , Toluene' ~ 2.4 0.1 ...... "...,'..'.;-,...' ..... '.
':"~ ', ! "'.~ .,Ethylbenzene 4.4 '1 , O. 1 '"' ' ~': ..... "':':~'" "'
.'~ :' ;.'. p-Xy~ene ' ':20.
' .":; : m-XT~ene 20, · 0 1 ...
.. ; .: ;' o-Xylene :36. 0.1 '~ ".'"
~ ~ ~sopropF1benzene ; ND 0
TPH (Gasoline) 520.' 1.0' ' . ":'
~:... .. . . .:
:~-...
~ . . ~: .., ..
~ ...... %3379 ID:' '$4 THl~35 ' ,, ugm/gm MRL, u'gm/gm .... -' '
. ,. ,: : Benzene , . . ' ND 0.1. ':' " '
~,. ~ :. :Toluene ., : 0.68 0.1
~ ' ~ ~ Ethylbenzene :' ; ':: % 2.0 0.1 .': :- ' "'
f../,j . : -.'~.:..v
~""'' "';,~.~.Meehod of Analysis: 3810/8020..(FfD):' "
.... . . ... ; .::...-{ .
.~/'). M~L := ~inimum Reporting Leve~'. ;:: '.', ,'~ ~ ~' '
.'
:[:,:~j. TPH =' To~al Petroleum HydrOcarbons
~[.~ · . . ~ - . .[ .
i,',:'~t"ug~/g~' ='~icrogra~s per gra~ {(pp~) .'~:.'
· ~:'.f~ "~D .= ~°ne ~eeeceed ~ .~. ~:'~.~,':..~,,-'?:~;-..~
Brian TI :, ~ ~.-~...[
.
'l ":; " 3155 Pegasus Drive · ~kersfield~ CA 93308 · (805) 393-3597 .....
" P.O. ~x 80835 · ~kem~eld, ~ 93380 · F~ (805) 393.3623
B-3
Company~'~SOUO,~ ~Mr~ Company: D.R. Smith & Associates Company:~, .
Address! 70~ ~~ ~F~~. Address: 7201 Fruitvale Ex:. :-'._ Ad~ess:.7OO
, Telephone: ('~.~ )
Telephone' ( ) Telephone: (805) 589-7861):?...,.,.~/;/.~/.~ :
No~
Laborat~v
3 Company:~ , ,,~ Date:
~; Date:
Received By: Company: ., ... : ~ [.[
: Date:
-.' I~ Date:
~ DU~E R S~ITH ~ As'~O:CI~TES' d Sheet [ of
[ ~ APPENDIX I
LOG OF TEST HOLE
= : ~ = D. R. SMITH & AssoCIATES
o ~ '~ ~ o ~ · LOCATION' SEQUOIA PAINT SHOWROOM
'~ ~ ~ ~ ~ O ~ ~ ' '
~ ~ ~ ~ s ~-- ~ ~.,~ ~ ~ ~ TEST HOLE IDENTIFICATION'. T.H. NO. 1
~ o · ~ o~ o DATE DRILLED: 07/25/90 ELEVATION: 412±'
o u m ' ,.mm ~ RIG TYPE: HAND AUGER
m z m[X[ Llthologic Description
2 ..... Silt, dark brown, slightly clayey, slightly
..... sandy, very fine grained, poorly indurated,
........ very moist, gasoline odor.'
· -' Sand, light brown to tan, silty, fine to very:
· coarse grained, poorly sorted, loose, moist.
· ' o gravel common
~'o · gravel rare
i ..'~ slight decrease in odor
fine gravel Common
.-- ~ 0.2 15 slight odor
· ... sampling difficulties
--..~_... ~ 320 250 09/19/90 - collected sample, moderate odor
~'o
~ %'~."~ 620 520 moderate odor
~ .
~ ........ Silt, brown, sandy, fine to coarse grained,
....... ._. .... ' slightly clayey, rust stains common, poorly
-'..-~-7~-~.. indurated, slightly moist, slight odor.
------- ® ?2o 10.
Sand, tan, silty, fine to very coarse grained,
- poorly sorted, loose, moist, moderate odor.
Total Depth: 35' * - Sample. Depth ®- Sample Analyzed Sheet 1 of 1
Figure 4
5400 ^LDRIN CT.
groundwater resources inc. B^KERgFIELE). CALIFOI~NI^ 93313
General Engineering Con[rac[or
Class AJHaz License No. 520768
GROUNDWATER RESOURCES INC.
Bakersfield, California
HEALTH AND sAFETY pLAN ' "
A RESNA Company
MAILING ADDRESS: P.O. BOX 9383, BAKERSFIELD, CA 93389 (805) 835-7700
LOS ANGELES {213) 724-3147
HEALTH AND SAFETY PLAN
1.0 PURPOSE
The purpose of this Plan is to assign responsibilities, establish personnel protection standards and
mandatory safety procedures, and provide for contingencies that may arise while operations are
being conducted at the site.
i:i ':~ :~-'.c.- ~ £~ :-~ ....... ~ .... ': ....................... --'~. -~ - '~ .... ~-'-~£:~: ....... ? ~ T -~--'~--~T~:--:''~-- ? ' .~ ~-'--".~?T'" ~'~-'~ ~'~%:"~L-~.~-~-~
2.0' APPLICABILITY
The provisions of the Plan are mandatory for all on-site Groundwater Resources Inc. (GRI)
'employees and subcontractors engaged in hazardous material management activities including, but
not limited to, initial site reconnaissance, preliminary field investigation, mobilization, project
operations, and demobilization.
Subcontractors shall provide a Health and Safety Plan for their employees covering any exposure
to hazardous materials and shall complete all work in accordance with that plan. The sub-
contractor may choose to use the GRI Health and Safety Plan as a guide in developing its own plan
or may chose to adopt GRI's Plan. In either case, thc subcontractor shall hold GRI harmless from,
. and indemnify it against, all liabilities in thc case of any injury. GRI rcscrvcs thc right to review
and approve the subcontractor's plan at any time.
Grossly inadequate Health and Safety practices on the part of the subcontractor or the belief that
the subcontractor's personnel are or may be exposed to an immediate health hazard, shall be cause
for GRI to suspend the subcontractors site work and ask the subconu'actor's personnel to evacuate
the hazard area.
The Subcontractor shall provide its own safetY equipment in accordance with Health and Safety
Plan requirements. The sub- contractor shall comply with all regulations including OSHA 29 CFR
1910.134 (Respiratory Protection).
3.0 RESPONSII~ILITIES
3.1 Safety Coordinator
The Safety Coordinator (SC) generally shall not be involved directly in onsite
activities. However, the SC shall provide the following functions in support of the
field activities:
1. Maintain an adequate inventory of equipment in good working
order.
2. · Maintain all necessary files and records.
3. Ensure that all monitOring equipment is calibrated on a regular basis
and that the results are properly recorded and f'ded.
4. Ensure monitoring equipment is operating correctly and provide for
maintenance if it is not.
5. Be available, for consultation by the Project Manager or Safety
............................... " ................................................ Officer. -~
PAGE .1 GROUNDWATER RESOURCES, INC.
.- HEALTH AND SAFETY PLAN
3.2 Project Manager
The Project Manager (PM) shall direct on-site investigation operational efforts. At
the site the PM, assisted by the. Safety Officer (SO), shall have the primary
responsibility for:.
...... ~ '-~'-' '~L: ~L'7£TC.-Z~ -~-. ~ .....
".:..£ .... ~..~_-. ~- ~ ' - .'~'.~_ -.'?'--':~ - -7 ..... '52.~77L~' LC'-'.£ ........ .: .... ~ '7.' "~ '.T7~_~_._-"-'~.7
1. Ensuring that appropriate personal protective equipment is available
and properly utilized by all on-site personnel.
2. Ensuring that personnel are aware of the provisions of this plan, are
instructed in the work practices necessary to insure safety, and in
planned procedures for dealing with emergencies.
· -~ 3~~' --- Ensuring-that pers0nnel~ are aware-of the-potential~ hazards associated ...... with on-site operations.
4. Monitoring the safety pefformar~ce of all personnel to ensure that the
required work practices are employed.
5. Correcting any work practices or conditions that may result in injury
or exposure to hazardous substances.
3.3 Safety Officer
The Safety Officer (SO) shall:
1. Implement project Health and Safety Plans, and report any
deviations from the anticipated conditions described in the plan.
2. Ensure that all'on-site personnel tiave a minimum of 24 hours safety
training.
3. Ensure that all monitoring equipment is' recently calibrated.
4. Ensure monitoring equipment is operating correctly (report to Safety
Coordinator if it is not.)
'5. Be responsible for identifying all site personnel with special medical
problems.
6. Preparing any accident/incident report..
7. Assume any other duties as directed by the PM.
3.4 Project Personnel
Project personnel involved in on-site operations shall be responsible for:
1. Taking all reasonable precautions to prevent injury to themselves
and to their fellow employees.
-: ................................. .~2.' ..... --~Performing'only those tasks'that-they believe can be done safely; .........................
PAGE 2 GROUNDWATER RESOURCES, INC.
HEALTH AND SAFETY PLAN
and mediately reporting any accidents and'~r unsafe conditions to
the SO or PM.
3. Implementing the procedures set forth in the Health and Safety Plan,
:.:.-.-:: .... : ~.~-::-:::- -: :-'" '-"::::' '-'-:~'. ..... : . ':--': -'and reporting any deviations-from'the'procedures-described in-the -
Plan to the SO or PM for action.
4.0 :~. BACKGROUND
All ~ersonn¢l shall be knowledgeable concerning the following topics on a site specific basis
including, but not limited to:
Site History
Prior Activity '
Suspected Hazards ' ''~
EMERGENCY CONTACTS AND PROCEDURES . L
5.1 Contacts
Should any situation or unplanned occurrence require outside or support services,
the appropriate contact from the following list should be made:
Agency Contact Person' Telephone
Police
Fire
Ambulance
Hospital
Project Manager
Safety Coordinator
Safety Officer
Client Contact
5.2 Procedures
In the event that an emergency develops on site, the procedures described below are
to be immediately followed. Emergency conditions are considered to exist if:.
-- Any of the project personnel are involved in an accident or experiences any
adverse effects or symptoms of exposure while on site; or
A condition is discovered that suggests the existence of a situation more
hazardous than anticipated.
PAGE 3 ' GROUNDWATER RESOURCES, INC.
· ' HEALTH AND SAFETY PLAN
The following emergency procedures shall be followed:
~ -~ .......... Z?-~-~ ............. ~ '~ '!'-' ~- Z:' -:~'.--.-- ..... . ...... "Z£~.- ............ '
1. Personnel onsite shall use the "buddy" system (pairs). Personnel
shall pre-arrange hand signals or other means of emergency signals
for communication in case of lack of radios or radio breakdown.
The following hand signals are suggested:
-- Hand gripping throat: out of air, can't breathe
............. ~ ...... Grip partner's-wrist or place .both hands-around own waist:.-. .......... -
leave area immediately
Hands on top of head: need assistance
Thumbs up: OK, I'm all right, I understand
Thumbs down: No, negative
2. The Safety Officer shall establish emergency evacuation mutes and
shall make all project.personnel aware of these mutes prior to the
fa'st onsite activities. In the event of an emergency, selection of the
escape route shall be based on the nature of the emergency and wind
direction.
3. Visual contact shall be maintained between on-site personnel.
Support personnel shall remain in close proximity in order to assist
in case of emergencies.
4. In the event that any of the personnel experiences any adverse
effects or symptoms of exposure while on site all personnel shall
immediately halt work and act according to the instructions provided
by the Safety Officer.
5. Wind indicators, visible to all on-site personnel, shall be provided
by the Safety Officer to indicate possible mutes for upwind escape.
6. The discovery of any condition that would suggest the existence of a
situation more hazardous than anticipated shall result in the
evacuation of the on-site personnel and re-evaluation of the hazard
and the level of protection .required.
7. In the event that an accident occurs, the SO shall complete an
Accident Report Form for submittal-to the Safety Coordinator (SC).
The SC shall initiate action to correct the situation that caused the
accident.
PAGE 4 GROUNDWATER RESOURCES, INC.
HEALTH AND SAFETY PLAN
6.0 HAZARD CHARACTERISTICS, MONITORING METHODS AND PROTEC-
TION REQUIRED
All personnel shall be knowledgeable concerning the following topics on a site specific basis
including, but not limitedlo: -~.'~ ~. "-': ':~"~' -
Exposure Limits
Recognizable Characteristics
Symptoms of Overexposure
'~ Potential Chronic Effects
~ First Aid Treatment
· Monitoring Methods
..................... -:- ..... -.~- ............. ' ..... · ...... ':-:--~-' ......... Action Levels ................
Protection Measures
7.0 STANDARD SAFE WORK PRACTICES
7.1 General
1. Eating, drinking, chewing gum or tobacco, and smoking shall be
prohibited in the contaminated or potentially contaminated area or
where the possibility for the transfer of contamination exists.
2. Avoid contact with potentially contaminated substances. Do not
walk through puddles, pools, mud, etc. Avoid, whenever possible,
kneeling on the ground, leaning or sitting on equipment or ground.
Do not place monitoring equipment on potentially contaminated
surface (i.e., ground, etc.).
3. All field personnel .shall make use of all their senses to alert them to
potentially dangerous situations which they should avoid (i.e.
presence of strong, irritating or nauseating odors).
4. Prevent spillages to the extent possible. In the event that a spillage
Occurs, contain liquid immediately.
5. Prevent splashing of the contaminated materials.
6. Field personnel shall be familiar with the physical characteristics of
the investigation site, including:
Wind direction
Accessibility to associates, equipment, vehicles
Communications
Hot zone (areas of known or suspected contamination)
Site access
Nearest clean water sources
PAGE 5 GROUNDWATER RESOURCES, INC.
HEALTH AND SAFETY PLAN
7. -~ e number of personnel and equipment in the contaminated
area shall be minimized, but only to the extent consistent with
Workforce requirements of safe site Operations.
8.. _-- ~ All wastes generated during, on,site activities-shall be disposed of in accordance with all applicable laws and regulations.
7.2 Excavation and Well Installation Practices
For all excavation and well installation activities, the folloWing standard safety
procedures shall be employed:
..... · ....... .:_1. ....... Allequipment shallbe cleaned_before·proceeding to site, and after ..... ~-.-~..-
the excavation and/or well installation has been completed.
2. Only the minimum number of personnel necessary to achieve the
· objectives shall be within 25 feet of the excavation and/or drilling
activity.
3. If the emergency and backup subconu'acted personnel arc at the site,
they shall remain 25 feet from the excavation and/or drilllug activity,
where practical.
4. Exclusion zones shall be established with designated hot lines.
Delineation of a hot line shall reflect the interface between areas at
and below a predetermined threshold contaminant concenu'ation
based on available data. This determination shall be made by the
Safety Officer.
5. All unauthorized Personnel shall remain outside exclusion zones at
all times.
8.0 SITE SAFETY PLAN
The personnel on site will be equipped with a draeger PA-80 air pack, gastech D-Il vapor testor
or an equivalent, a photoionization meter, fire extinguishers and any additionally required
equipment for health and safety considerations.
PAGE 6 GROUNDWATER RESOURCES, INC.
~ ' 5400 ^LDRIN CT.
groundwater resources inc. BAKERSFIELD. CALIFORNIA 93313
General Engineering Contr,~c[or
Class A/Haz License No. 520768
SAMPLING PROTOCOL
MAILING ADDRESS: P.O. BOX 9383, BAKERSFIELD, CA 93389 (805) 835-7700
- LOS ANGELES (213) 724-3147
SAMPLING PROTOCOL
TEST BORING PROCEDURES
L · Soil Sampling Protocol
The following procedures axe following during soil sampling operations utilizing the hollow
A. Hollow Stem Auger
1. Soil borings drilled by the hollow stem auger utilize continuous flight
hollow stem augers.
2. Augers, samplers and all downhole equipment are steam cleaned prior to
................ - ...... = ..... -:,=- ............... -: .......... - ................ use.. In...the_field steam: cleaning is-done' between~borings-,to.minimize, the. ................
potential for cross-contamination.
3. A G.R.I. geologist observes the work, visually logs the soils, and collects
samples at appropriate intervals.
4. The Unified Soils Classification System is utilized to classify soils
encountered. Additional geological observations are noted as appropriate."
5. Soil samples destined for laboratory .analysis are collected by a modified
California Split Spoon. This sampler uses three, six inch long, by two and
one-half inch diameter (o.d.) tubes.
Various tubes can be utilized to accommodate the type of analysis necessary:
Brass All organics and general analyses (not to be used for
copper or zinc analysis)
Stainless Steel All organics and metals analyses for Steel copper and
zinc (not to be used for chrome or nickel analyses)
Plastic All metals analyses (not to be used for organics)
6. The tubes axe cleaned and prepared in the G.R.I. laboratory. Tubes axe
scrubbed, inside and outside, with a brush and TSP, rinsed, dryed, and
packed in clean containers with seals. Tubes axe delivered to the drilling site
in these closed containers to preserve the state of cleanliness.
7. After the sample(s) have been removed from the sampler, the sampler is
completely disassembled and scrubbed in TSP and tap water. It is then
rinsed in clean tapwater and reassembled with three clean tubes.
8. Dirty tubes axe field washed in TSP solution, rinsed with water, and reused. ·
9. The sampler is driven by a 140 pound hammer with a 30 inch free fall. Blow
counts are recorded as number of blows per inch of drive.
...... .... ' ............... · ............._10 ....... The sampler~is_driven 18 inches-at each sampling interval. The f'trst (or .......
lowest) tube is generally retained as the sample for analysis. The other two
tubes axe retained for back-up or split samples.
PAGE 1 GROUNDWATER RESOURCES, INC.
SAMPLING PROTOCOL
TEST BORING PROCEDURES
(continue~)
11. A sand catcher is used in the sampler where loose soils are anticipated. This
will prevent the soil from falling out of the sampler.
12. After retrieval, the sample is visually logged and immediately sealed with
aluminum foil lined caps, labeled, and chilled. Clean ice chests and
chemical ice ("blue ice") are used to keep the samples cold until delivered
to the chemical laboratory. Teflon seals axe also available for field samples.
13. Samples are delivered to the laboratory the same day they are taken, if
physically possible. If the samples must be held until the next day, they are
14. Sample control is maintained by a Chain of Custody form which accompanies
the sample. The form documents the time, date, and .responsible person
during each step in the transportation process.
MONITORING WELL SAMPLING PROTOCOL
II. Groundwater Sampling
A. All equipment that is used in a monitoring well for purging, sampling, or depth
measurement is decontaminated by steam cleaning or a TSP wash and rinse procedure
prior to use and before re-using when more than one sample is collected.
B. Purge Volume Determination
The following procedure is followed to determine the appropriate purging volume prior
to well sampling.
1. The depth-to-water is measured by a clean, electric level indicator.
Measurement datum is the top of well protector.
2. Depth to the bottom of the well is measured by a clean tape and plumb bob.
If possible, this is compared to thc well construction .log to determine
inconsistencies, i.e. damaged casing, sediment in casing, etc.
3. Water volume is calculated by using the total water depth and the inside
diameter of the casing.
C. Well Purging and 'Sampling "
1. Prior to sampling, a minimum of three to five well volumes are purged from
each well to ensure that water sampled is representative of the groundwater
within the formation.
.................... 2~ . Measurements of.-H, conductivity and temperature are taken at frequent.
,. intervals during the purge. Stabilization of these values indicates that
representative formation fluids are being removed from the well.
PAGE 2 GROUNDWATER RESOURCES, INC.
SAMPLING PROTOCOL
MONITORING WELL sAMPLING PROTOCOL
(continued)
3. In the event that the well is pumped dry, and alternate procedure will be
followed. Once a well is pumped dry, the water that enters the well during
........ · _.._.recovery is, .by. definition, representative formation ,water..The ~wellwill,=~.
" ---'-' -:'-' --.~-- -: ......therefore, be pumped dry and allowed to recover to 80%:or-'"mo~ 6f
original water level.
4. Purge water is pumped directly into barrels on site until the proper method
of disposal is determined.
5. Samples are pumped or poured from a bailer into sampling bottles prepared
· .by a state certified laboratory contracted for the particular job_ _.an~.pl .~_. ~ed.....'in. ...........
· ' ' - ...................... refrigerated COOlers for'transport to the labOratOry.'
6. Samples are delivered by courier, directly to the lab on the same day of
sampling, whenever practical. If next day delivery is necessary, the samples
are kept refrigerated at 4 degrees C overnight and delivered to the
laboratory the following morning.
7. Samples are accompanied by a Chain of Custody form which dOCuments the
time, date and responsible person during each step of the transportation
process.
8. The G.R.I. coded sample numbering system allows identification of sample
and client to G.R.I., while not revealing the client to anyone else.
PAGE 3 GROUNDWATER RESOURCES, INC.