HomeMy WebLinkAboutUNDERGROUND TANK-C-02/01/94
CONTRACT OPTIONS FOR r,~A.T'f. II~
Site Specific Time Accounting Sheet
Permit # ~ ~-~5(~ Site Specific Status Changes:
Employee #
~loyee Signature
Site Name or Address
Fur~ing (~1, State, of Federal)
Category Activity Hours
Date Code Code Description ( 10the )
Note~:
Data Entered By: Date:
!
KERN COUNTY ENVIRONMENTAL HEALTH DEPARTMENT
INVESTIC~ATION RECORD
ASSeSSOr' PARent # ..... CT ~P-~~m~,.9~.
CHRONOLOGICAL. RECORD OF INVESTIGATION
,~-~,~ ~ ~ . Kennedy/Jenks C~)nsultants
ODIS DYKES, INC.
BAKERSFIELD, CALIFORNIA
SITE CHARACTERIZATION REPORT FOR
THE FORMER FUEL DISPENSING AREA
DANIELS LANE FACILITY
BAKERSFIELD, CALIFORNIA
6 JANUARY 1992
(K/J 912319.00)
Prepared for: Odis Dykes, Inc.
313 Daniels Lane
Bakersfield, California 93307
(805) 327-3039
Prepared by: Kennedy/Jenks Consultants
200 New Stine Road, Suite 11
Bakersfield, California 93309
(805) 835-9785 .
Kennedy/Jenks Consultants
.Engineers and Scientists
200 New Stine Road, Suite 115
Bakersfield, California 93309
805-835-9785
8 January 1992 FAX 805-831-5196
Mr. Michael Driggs
Hazardous Materials Specialist
Department of Environmental Health Services
County of Kern, Resource Management 'Agency
2700 M Street, Suite 300
Bakersfield, California 93301
Subject: Odis Dykes, Inc.
Site Characterization Report for the Former Fuel Dispensing Area
Daniels Lane Facility
Bakersfield, California
K/J 912319.00
Dear Mr. Driggs:
Enclosed herewith, as authorized and directed by Odis Dykes, Inc., are two copies of the
Site Characterization Report for the Former Fuel Dispensing Area (Report) dated 6 January
1992.
The Report summarizes the results of Kennedy/Jenks Consultants field investigation
associated with a former fuel dispensing area at the Daniels Lane Facility. The
investigation was conducted to fulfill requirements set forth by the Kern County Resource
Management Agency, Department of Environmental Health Services in its Site
Characterization and Site Remediation Handbook #UT-35. Kennedy/Jenks Consultants
interpretation of the results of the investigation and recommendations for remedial action
are presented in the Report.
Please call me or Mr. Jon Cooper if you have any questions or would like to discuss the
Report in more detail.
Very truly yours,
KENNEDY/JENKS.CONSULTANTS
Project Manager
MJP:rw
cc: Ms. Vickie Breaw, Odis Dykes, Inc.
Kennedy/Jenks Consultants
ODIS DYKES, INC.
SITE CHARACTERIZATION REPORT FOR
THE FORMER FUEL DISPENSING AREA
DANIELS LANE FACILITY
BAKERSFIELD, CALIFORNIA
K/J 912319.00
6 January 1992
TABLE OF CONTENTS
INTRODUCTION .................................................. 1
Site Description .... ' .......................................... 1
Site Background ............................................. 2
SITE CHARACTERIZATION ........................................... 2
Installation of Soil Borings ....................................... 2
LABORATORY ANALYSIS ........................................... 3
Analytical Methods .................................... ~ ....... 3
Analytical Results ............................................ 4
SUMMARY OF FINDINGS ............................................ 6
Litholog¥ ................................................... 6
Distribution of Petroleum Hydrocarbons ............................. 6
EVALUATION OF REMEDIAL ACTION ALTERNATIVES ....................... 7
No Further Action ............................................ 7
Installation of an Asphalt Cap .................................... 7
Excavation and Aeration of Affected Soils ........................... 8
In-Situ Vapor Extraction ........................................ 9
CONCLUSIONS AND RECOMMENDATIONS ............................... 9
TABLES
FIGURES '
ATTACHMENT A - Work Plan Approval Letter from Kern County Department of
Environmental Health Services
ATTACHMENT B - Soil Boring Logs
ATTACHMENT C - Field Sample Chain-of-Custody Records
ATTACHMENT D - Laboratory Analysis Reports
Kennedy/Jenks Consultants
ODIS DYKES, INC.
SITE 'CHARACTERIZATION REPORT FOR
THE FORMER FUEL DISPENSING AREA
DANIELS LANE FACILITY
BAKERSFIELD, CALIFORNIA
K/J 912319.00
6 January 1992
INTRODUCTION
This report is based on site characterization activities conducted by Kennedy/Jenks
Consultants at Odis Dykes, Inc.'s Daniels Lane facility on 6 November 1 991.
Site work was conducted as proposed in Kennedy/Jenks Consultants' 9 October
1991 Revised Site Characterization Work Plan. The Work Plan was approved by
the Kern County Department of Environmental Health Services (KCDEHS) in a letter
to Odis Dykes, Inc., dated 1 5 October 1991. The report is intended to satisfy the
KCDEHS requirement for submittal of a Site Characterization Report and a Remedial
Action Plan as specified in KCDEHS Handbook UT-35.
Site Description
The site is located at 31 3 Daniels Lane in Bakersfield, California (Figure 1 ),.in a
construction equipment storage yard. The site is located approximately 140 feet
east of the Odis Dykes, Inc. office and approximately 100 feet south of Daniels
Lane and includes the area adjacent to a concrete pad which is the former
foundation of a fuel dispensing island (Figure 2). The east branch of the Kern Island
Canal is located approximately 200 feet south of the site, and a Water supply well
operated by California Water Service Co. is located approximately 400 feet south of
the site.
The site is relatively flat, with surface drainage directed southward toward the
canal. The 1959 Kern County Water Agency Report on Water Conditions,
Improvement District No.4, indicates a depth to groundwater of approximately 190
feet at the site.
Regional geology is described as unconsolidated sand and gravel of dissected
uplands and Sierra Nevada Provenance. The Sierra Nevada derived material
consists of basal gravel deposits overlain by medium grained sands. Dissected
upland derived material consists of heterogeneous deposits of sand and gravel.
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Kennedy/Jenks Consultants
Site Background
Odis Dykes,. Inc. formerly operated a fuel dispensing facility at the site. The fuel
dispensing facility consisted of one 8,000-gallon aboveground diesel fuel tank and
one 4,000-gallon aboveground gasoline tank that .were connected to separate
dispensers onthe fuel dispensing island. There was also one 2,500-gallon
underground diesel fuel storage tank that reportedly had not been used since 1988.
On 14 June 1991, Odis Dykes, Inc. removed the 2,500-gallon underground diesel
fuel storage tank and associated piping. During the underground tank removal, soil
samples were collected by B.C. Laboratories, Inc. beneath the former underground
tank and the dispensers. Soil samples were reportedly collected at depths of two
feet and four feet below each end of the former underground storage tank and at
depths of two feet and six feet below each of the dispensers. Petroleum
hydrocarbons were not detected in any of the soil samples collected below the
former underground storage tank, however, elevated concentrations of petroleum
hydrocarbons were detected in soil samples collected below each of the two
dispensers at depths of two feet and six feet.
KCDEHS, in a letter dated 23 July 1991, notified Odis Dykes, Inc. that an
unauthorized release of hazardous materials had occurred at the site. Odis Dykes,
Inc. was identified as the responsible party in,the KCDEHS letter and was therefore
required to develop a Site Characterization, Feasibility Study and Remedial Action
Plan for the site. Odis Dykes, Inc. subsequently selected the County of Kern Local
Agreement Option for oversight cost recovery and deposited $1,000.00 in the
County of Kern Local Option Trust Account. Odis Dykes, Inc. subsequently
retained Kennedy/Jenks Consultants to conduct additional site characterization
activities.
SITE CHARACTERIZATION
Installation of Soil Borings
Three soil borings (OD1, OD2, and OD3) were installed by Kennedy/Jenks
Consultants on 6 November 1991. at the locations shown on Figure 3. The borings
were installed to attempt to characterize the horizontal and vertical extent of
elevated concentrations of petroleum hydrocarbons in the soil near the location of
the former fuel dispensers. Borings were installed in accordance with the 9 October
1991 Revised Site Characterization Work Plan approved by KCDEHS in a letter
dated 15 October 1991. A cOpy of the letter of approval is included as Attachment
A to this report.
Soil borings were advanced to total vertical depths of approximately 21.5 feet
(OD1), 36.5 feet (OD2), and 71.5 feet (OD3) using hollow stem auger techniques.
Soil samples were collected at five-foot intervals with a driven California modified
split'spoon sampler containing pre-cleaned brass liners. Work was done under the
supervision of a Kennedy/Jenks Consultants geologist. Boring logs describing soil
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Kennedy/J enks Consultants
sample recovery, lithology, field organic vapor readings and other general comments
are included as Attachment B to this report.
A Model 580B portable organic vapor meter (OVM).manufactured by Thermo
Environmental, Inc. was used to conduct field headspace measurements. The
instrument is a photo ionization detector with an operating range of 0-2000 parts
per million (ppm) with a minimum detection limit of 0.1 ppm using a 10.0 eV lamp.
The OVM was calibrated in the field using isobutylene at a concentration of 100
ppm.
Field headspace measurements of selected soil samples for organic vapors were
conducted after the contents of the sample liners were placed in plastic bags,
disaggregated and placed in a warm location for approximately ten minutes. The
OVM was used to measure the organic vapor content in the headspace of the
selected samples by carefully opening the bags and sampling the headspace. The
magnitude and distribution (relative concentration) of these organic vapor readings
were used to aid in the selection of soil samples for laboratory analyses. A
summary of field headspace analysis results is presented in Table 1.
Sample liners containing soil samples to be analyzed by the laboratory were sealed
on both ends with Teflon sheets and plastic caps. Samples were labelled and kept
chilled during transport to B.C. Laboratories, Inc. for analysis. Copies of the field
sample chain-of-custody records which accompanied the soil samples to the
laboratory are included as Attachment C to this report.
Drill cuttings were placed in DOT approved drums and stored onsite in a secure area
for appropriate disposal by Odis Dykes, Inc. pending receipt and review of
laboratory analysis results. Completed soil borings OD1 and OD2 were backfilled
with clean drill cuttings from their respective borings after approval by the KCDEHS
inspector. Completed soil boring OD3 was filled with Bentonite chips and hydrated
with clean water to seal the boring. Soil borings were sealed, beginning at total
depths and ending at surface grade.
LABORATORY ANALYSIS
Analytical Methods
Based on the results of field screening using headspace analysis, soil samples were
specifically selected for analysis of Total Petroleum Hydrocarbons (TPH, both
gasoline and diesel) by Modified EPA Method 8015 utilizing gas chromatography
with flame ionization detection. Benzene, toluene, xylene and ethyIbenzene (BTXE)
in soil samples were analyzed by EPA Method 8020 for aromatic volatile organics
utilizing gas chromatography.
A total of fourteen soil samples collected from the soil borings were transported to
B.C. Laboratories, Inc. for analysis. Copies of the field sample chain-of-custody
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Kennedy/Jenks Consultants
records which accompanied the soil samples to the laboratory are included as
Attachment C to this report.
Analytical Results
Table 2 presents a summarY of detected analytes for soil samples collected during
the site characterization. Copies of individual laboratory analysis reports are
included as Attachment D to this report. Analysis results for soil samples collected
from each boring are described below and are also presented in a conceptual cross
section (Figure 4).
Estimated action level criteria used for comparison in the following discussions are
established in Table 2-1, Leaching Potential Analysis for Gasoline and Diesel,
Leaking Underground Fuel Tank (LUFT) Manual, State of California Leaking
Underground Fuel Tank Task Force, May 1988. The intent of the table was to
permit estimation of the concentrations of TPH and BTXE that may be left in place
without potentially threatening ground water quality.
Soil Boring OD1
Based on field screening techniques, two (2) soil samples from soil boring OD1
were selected for laboratory analysis. Soil samples analyzed from soil boring OD1
contained no detectable concentrations of TPH (gasoline or diesel) or BTXE.
Soil Boring OD2
Based on field screening techniques, three (3) soil samples from soil boring OD2
were selected for laboratory analysis. Soil samples analyzed from soil boring OD2
contained detectable concentrations of TPH (gasoline and diesel) and BTXE. A
summary of the depths of detection and concentrations detected in soil samples
analyzed from soil boring OD2 follows:
TPH (as diesel) was detected at concentrations ranging from a maximum of
20 mg/Kg in soil sample OD2A3 collected at a depth of approximately 11.0 to
11.5 feet, to a minimum of less than 5.0 rog/Kg in soil samples OD2A7 and
OD2A8 collected at depths of approximately 31.0 to 31.5 feet and 36.0 to
36.5 feet respectively. The TPH concentration detected was below the
estimated action level of 10,000 mg/K,g for TPH (as diesel) in soil.
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Kennedy/Jenks .Consultants
Soil Boring OD3
Based on field screening techniques, six (6) soil samples from soil boring OD3 were
selected for laboratory analysis. Soil samples analyzed from soil boring OD3
contained detectable concentrations of TPH (gasoline and diesel) and BTXE. A
summary of the depths of detection and concentrations detected in soil samples
analyzed from soil boring OD3 follows:
· TPH (as diesel) was detected at concentrations ranging from a
maximum of 4,000 mg/Kg in soil sample OD3A3 collected at a depth of
approximately 11.0 to 11.5 feet, to a minimum of less than 5.0 mg/Kg
in s°il samples OD3A15 and OD3A16 collected at depths of
approximately 66.0 to 66.5 feet and 71.0 to 71.5 feet respectively.
The TPH concentrations detected, except those detected in the 11.0 to
11.5 feet and 46.0 to 46.5 feet samples, were below the estimated
action level of 10,000 rog/Kg for TPH (as diesel) ~';'n-~0il.
· TPH (as gasoline) was detected at concentrations ranging from a
maximum of 6800 mg/Kg in soil sample OD3A3 collected at a depth of
approximately 11.0 to 11.5 feet, to a minimum of less than 1.0 mg/Kg
in soil samples OD3A15 and OD3A16 collected at depths of
approximately 66.0 to 66.5 feet and 71.0 to 71.5 respectively. The
TPH concentrations detected, except those detected in the 11.0 to 11.5
feet and 46.0 to 46.5 feet samples, were below the estimated action
level of 1,000 rog/Kg for TPH (as gasoline) in soil.
· Benzene was detected at concentrations ranging from a maximum of
14.0 mg/Kg in soil sample OD3A11 collected at a depth of
approximately 46.0 to 46.5 feet, to a minimum of less than 0.005
rog/Kg in soil samples OD3A15 and OD3A16 collected at a depth of
approximately 66.0 to 66.5 feet and 71.0 to 71.5 feet. The benzene
concentrations detected, except those detected in the 11.0 to 11.5 feet
and 46.0 to 46.5 feet samples, were bel___o_w the estimated action level
of 1 mg/Kg for benzene in soil.
· Toluene was detected at concentrations ranging from a maximum of
270 rog/Kg in soil sample OD3A11 collected at a depth of
approximately 46.0 to 46.5 feet, to a minimum of less than 0.005
mg/Kg in soil samples OD3A15 and OD3A16 collected at a depth of
approximately 66.0 to 66.5 feet and 71.0 to 71.5 feet respectively.
The toluene concentrations detected, except those detected in the 11.0
to I 1.5 feet and 46.0 to 46.5 feet samples, were below the estimated
action level of 100 mg/Kg for toluene in soil.
· Xylenes were detected at concentrations ranging from a maximum of
840 mg/Kg in soil sample OD3A3 collected at a depth of approximately
11.0 to 11.5 feet, to a minimum of less than 0.005 rog/Kg in soil
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Kennedy/Jenks Consultants
samples OD3A15 and OD3A16 collected at depths of approximately
66.0 to 66.5 feet and 71.0 to 71.5 feet respectively. The xylenes
concentrations detected, except those detected in the' 11.0 to 11.5 feet
and 46.0 to 46.5 feet samples, were below the estimated action level
of 50 mg/Kg for xylenes in soil. -------
· Ethylbenzene was detected at concentrations ranging from a maximum
of 120.0 mg/Kg in soil sample OD3A11 collected at a depth of
approximately 46.0 to 46.5 feet, to a minimum of less than 0.005
mg/Kg in soil samples OD3A15 and OD3A16 collected at depths of
approximately 66.0 to 66.5 feet and 71.0 to 71.5 feet respectively.
The ethylbenzene concentrations detected, except that detected in the
46.0 to 46.5 feet sample, were below the estimated action level of 50
mg/Kg for ethylbenzene in soil. ~
SUMMARY OF FINDINGS
Lithology
The uppermost 10 feet of the site appears to consist of gravels, sands and silty
sands (Figure 4). Fine to medium-grained sands were noted in all three borings
from 10 to 20 feet in depth, and from 20 to 35 feet in depth in borings OD2 and
OD3. At 35 feet in depth, samples from borings OD2 and OD3 are described as
fine in grain size. From 40 to 65 feet in depth, samples are mostly described as
fine-grained sand containing varying amounts of silt and clay. A clay content of
40% is estimated for the 60-foot sample. This clayey deposit appears to be
underlain by sand in the vicinity of boring OD3.
Distribution of Petroleum Hydrocarbons
Petroleum hydrocarbons were not detected in soil samples analyzed from soil
borings OD1 and OD2.
Elevated concentrations of petroleum hydrocarbons were detected to'a depth of
approximately 50 feet below ground surface in soil samples collected from soil
boring OD3. The concentrations of petroleum hydrocarbons detected were above
their respective estimated action levels based on criteria established in the LUFT
manual.
Based on the relatively homogeneous soil types encountered, field screening of soil
samples, and a review of laboratory analytical results, it appears that petroleum
hydrocarbons migrated vertically beneath the former fuel dispensing island with
minimal, if any, lateral dispersion. Assuming a symmetrical plume, approximately
twelve feet in diameter and fifty feet deep, it can be estimated that approximately
20~_0__cLJhic yards of soil may have been affected by petroleum hydrocarbons.
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Kennedy/J enks Consultants
EVALUATION OF REMEDIAL ACTION ALTERNATIVES
Remedial action alternatives were developed to address the concentrations of
petroleum hydrocarbons in soils detected above the estimated action level criteria
established in the LUFT Manual.
Kennedy/Jenks Consultants considered four options for remediation of affected soils
in accordance with KCDEHS Handbook UT-35. The options considered include: no
further action; installation of an asphalt cap; excavation and aeration of affected
soils; and in-situ vapor extraction. An evaluation of each option follows.
No Further Action
Description: No further action refers to a scenario of conducting no activities to
reduce the potential exposure to the chemicals of concern and no activities to
reduce the level of concentration of those chemicals in the affected soils.
Feasibility: Given an undetermined amount of time, and soil moisture distribution
from pre-existing conditions and future rainfall, remediation by naturally-occurring
biological degradation may reduce the concentrations of the chemicals of concern
to levels that no longer pose a potential threat to the environment (APl, 1 980).
Cost: No additional expenditure.
Necessary Data Acquisition: None anticipated.
Risk Appraisal: No further action would extend the existing potential for exposure
of workers, and others onsite to the chemicals of concern, some of which may be
carcinogenic. Exposure paths are through dermal contact and inhalation through
possible future excavation and by ingestion if percolating rainwater transports the
chemicals into aquifers serving domestic supplies.
EXpected Range of Concentrations of Chemicals of Concern after Remediation.' No
immediate reduction; assume a five to ten year period is required to allow natural
biological degradation to reduce the concentrations of the chemicals of concern
below the estimated action levels.
Installation of an Asphalt Cap
Description: Pavement of an area of ground surface at the site sufficient in extent
to prevent surface water infiltration and subsequent leaching of the chemicals of
concern into groundwater.
Feasibility: If properly maintained, caps can be considered as adequate barriers
against future dermal exposure or inhalation of subsurface chemicals. In addition,
caps can protect against surface water infiltration and subsequent leaching of the
chemicals of concern into groundwater. Biological degradation processes may
7 912319.00
Kennedy/Jenks Consultants
gradually decrease the concentration of petroleum hydrocarbons in the soil (APl,
1980).
Cost: Low
Necessary Data Acouisition: Cap should be monitored for integrity, subsurface soils
should be analyzed sufficiently over time to establish that chemicals of concern
have been immobilized or degraded.
Risk ADoraisal: Capping would immediately protect against infiltration, dermal
contact and inhalation; however, resultant decreased moisture levels may retard
biodegradatiOn.
Expected Ranae of ConcentratiQn8 of Chemicals of Concern efter Remediation:
Relatively Iow concentrations after five years,
Excavation and Aeration of Affected Soils
Description: Excavation of Shallow soils (surface to 20 feet deep) containing the
highest concentrations of petroleum hydrocarbons, and subsequent on-site aeration
of soils. Backfilling excavation with clean Iow permeability fill material.
Feasibility: Aeration is a common method for remediating soils containing volatile
petroleum hydrocarbons. The sandy soil types encountered at the site should
enhance the effectiveness of this method. However; Rule 463.5, recently proposed
for adoption by the San Joaquin Valley Unified Air Pollution Control District, may
render this alternative unacceptable.
Cost: Moderate
Necessary Data Acquisition: Aerated soil should be sampled regularly and analyzed
to evaluate remediation progress.
Exoected Ranqe of Concentrations of Chemicals of Concern after Remediation:
Relatively~concentrations after 6 to 1 2 months.
In-Situ Vapor Extraction
Description: Installation of perforated wells into affected sediments in the vadose
(unsaturated) zone. Connection of a blower to an extraction well to create a
negative pressure gradient which extracts soil vapor and volatiles from the soil.
Volatiles are then treated and disposed at the surface.
Feasibility: Vapor extraction can be an efficient method for removing volatile
organic compounds (i.e., gasoline) from the soil, and has shown efficiency rates
ranging from 65 to 99 percent (Clark et.al., 1990; EPA 1989c.). The sandy soil
types encountered at the site should enhance the effectiveness of this method.
8 912319.00
Kennedy/Jenks Consultants
However, vapor extraction is not expected to significantly reduce concentrations of
diesel fuel in the soil.
Necessary Data Acouisiti0n: Extracted vapors should be sampled regularly and
analyzed to evaluate progress of remedial activities.
Cost: High
Expected Ranoe of Concentrations of Chemicals of Concern ~fl;er Remediation:
Concentrations below action levels after 6 to 1 2 months of operation.
CONCLUSIONS AND RECOMMENDATIONS
Based on an evaluation of the findings presented in this report, the following
conclusions are presented below:
· Analytical results from soil boring OD1 and OD2 indicate that elevated
concentrations of petroleum hydrocarbons were not detected in soil
samples analyzed.
· Analytical results from soil boring OD3 indicate that elevated
concentrations of petroleum hydrocarbons were detected from ground
surface to approximately 50 feet below ground surface.
· The approximate.lateral and vertical extent of soils affected by
petroleum hydrocarbons appears to have been defined. The lateral
extent appears to be limited to the immediate area surrounding OD3.
The vertical limit of affected soils appears to extend from ground
surface to approximately 50 feet below ground surface
· A relatively Iow permeability (clayey sand) zone was encountered in soil
boring OD3 at a depth of approximately 60 feet below ground surface.
The Iow permeability zone appears to have reduced the vertical
migration of the petroleum hydrocarbons in the vicinity of boring OD3.
· Regional depth to gro~u~__ndwa~ter in the site area is reported to be
approximately 190~f_eet below ground surface.
· On the basis of a review of concentrations and depths of detection for
petroleum hydrocarbons, the soil types encountered, the regional depth
to groundwater, and LUFT Manual guidelines, it appears that no
significant threat to the groundwater exists in the area.
· The concentrations of petroleum hydrocarbons detected in the soil
samples analyzed appears to indicate that a limited quantity of soil, if
any, may require remedial action.
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Kennedy/J enks Consultants
On the basis of the findings presented in this report it appears that no further action
should be required at thiS site. However, in order to take a more conservative
approach in protecting the environment, Kennedy/Jenks Consultants recommends/i~,<k~'--
that the former fuel dispensing area at the Odis Dykes, Inc. site _b~ capped with~ ~ ' ~'- .....
asphalt and sloped accordingly to allow for run-on and run-off of water. Placement
and maintenance of the asphalt cap should reduce infiltration of surface water into
the underlying soils and the subsequent potential for leaching of petroleUm
hydrocarbons into the groundwater. Inspection of the cap should be conducted
periodically with prompt repair of cracks or other damage as identified. The cap
should be designed to accommodate heavy equipment traffic. We propose that a
brief W_._ork Plan ~e submitted under separate cover to describe the work proposed
to compile remediation of this site.
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Kennedy/Jenks Consultants
References Cited
American Petroleum Institute, 1980, Undemround SPill Cleanup Menuel, publication
No. 1628.
Clark,.A.N., Mutch, R.D., Mutch, P.D., and Wilson, D.J., In Situ StrioDines Results
of a Year-Lone Pilot; St;udy, Hazardous Materials Control, 1990.
U.S. Environmental Protection Agency, 1989, Soil Vapor Extraction VOC Control
Technoloav Assessment;, U.S.E.P.A. Report 450/4-89/017.
'1
Kennedy/Jenks Consultants
TABLE 1
ODIS DYKES, INC,
SITE CHARACTERIZATION REPORT
FOR THE FORMER FUEL DISPENSING AREA
DANIELS LANE FACILITY
BAKERSRELD, CALIFORNIA
K/J 912319.00
JANUARY 1992
:::::::::::::::::::::::: :: '! :i :.~:.:::.:~:.~::::::~:~ ~:.:h~m ~,~i~:~-rs:::~: :' :.i:;:..
ODlCl 0.0-0.6 2 ~
OD1 C2' 6.0.6.6 2 ppm
ODIC3 10.O-10.6 2 ppm
0DIC4' 16.0-16.E 4 ~
OD1C6 20.O-20.6 1 ~
OD2C 1 0.o-0.6 1626 ppm
OD2C2 6.0-6.6 1345 prim
OD2C3° 10.0-10.6 1862 I~orn
OD2C4 16.0-15.5 186 ppm
OD2C6 20.0-20.6 62 ppm
OD2C6 26.0-26.6 g ~
0D2C7' 30.0-30.6 11 ~
OD2C8' 36.0-36.6 19 m>m
OD3C1 0.0.0.6 819 porn
OD3C2 6.0-6.6 812 ppm
OD3C3' 10.0.10.6 1833 ppm
OD3C4 15.0-15.5 NS
OD3C5 20.O-20.15 1148 ppm
OD3C6 25.O-26.6 1480 ppm
OD3C7 30.0-30.6 1423 ppm
OD3C8 36.O-35.6 1368 ppm
OD3C9 40.0-40.6 712 ~
OD3C11 * 46.0-46,5 723
OD3C 12 60.0-50.6 607
OD3C 13' 65.0-66,6 270
OD3C14' 60.0.60.6 138 ~
OD3Cll5' 66.0-66.6 83 ~
OD3C 16 ° 70.0-70.6 17 ppm
(1) Refer to Fig~xe 3 fro' eoil b¢xing
(2} Depth below grm.~d
(3) Bamed on field screening uling Photo IO~zltio~ Detector {PtD}. Concel3trltionl indiClted I~'e p~l ~ millio¢l (ppi-n) by vcdume, m ilob~tyierle
equivalent.
· Sample interval selected fo~ leborltory enalylis based on o~genic vapor.
NS Not ICreel3~d in field with PID.
Tlble 2
ODIS DYKES. INC.
SITE CHARACTERIZATION REPORT
FOR THE FORMER FUEL DISPENSING AREA
DANIELS LANE FACILITY
BAKERSFIELD, CAJ. IFORNIA
K/J 012319.00
JANUARY 1992
: · . : ~:: .: :.:. i~ed Co,ce,~itiom imasa) ~'.:::::::::::::::::::::::: :i::i:??:?:::
::,'.:' :::::::::::::::::::::::::::: t :: :.. I: :.il ............ ::.:
OD1A2 6.0-6.6 < 1.0 < 6.0 < 0.006 < O.O05 < 0.006 < 0.006
OD1A4 16.O-16.6 < 1.0 < 6.0 < O.006 < 0.OO6 < 0.006 < O.OOS
OD2A3 11.0-11.6 < 1.0 20.0 < 0.006 < 0.01 < O.006 < 0.006
OD2A7 31.0-31.6 < 1.0 < 6.0 < O.006 < 0.005 < O.O~6 < O.OO$
OD2A8 38.0-38.6 < 1.0 < 6.0 < 0.006 < 0.006 < 0.006 < 0.006
OD3A3 11.0-11.6 8800.0 4000.0 < 6.0 6g.O 32.0 840.0
OD3A11 46.O-48.6 6000.0 1200.0 14.0 270.0 120.0 720.0
OD3A13 66.O-6B.6 1.0 < 6.0 < 0,005 < 0.01 < 0.006 < 0.006
OD3A14 61.0-61.6 3.0 20.0 0.6 1.2 0.083 0.400
OD3A16 66.0-66.6 < 1.0 < 6.0 < 0.006 < 0.006 < O.OO6 < O.006
OD3A16 71.O-71,6 < 1.0 < 6.0 < 0.006 < 0.006 < 0.006 < 0.006
Notes:
(1) Refe~ to Figure 3 for loll boring Iocitlonl
(2) Depth ~ow grour~l lUff ICe
< Comp<xJnd w~ not detected it c°nCentritio~ ebove vllue indicated.
.~. ~'.~,¢~----'~ ~-~..-~ I .11
I
l,o,~ /'.'l~J ..I i~1 c~', 'g),o ~t~* ~[~'"--~C~'~ --_~ ~ ~ ~--j s,
,--- ~.."' ~.~ L.= I ~
7"~ · J ' ., . ~) ., ' ~ v ¢ ' --~
Kennedy/Jenks Consultants
Odis Dykes, Inc.
Bakersfield, California
Location Map
K/J 912319.00
January 1992
Figure I
Denle s Lene
Main gate____/ N
Fuel dispensing island-~ Former Gasoline
.
.dispenser
Former undergound -- ~,~ -- 1 ~ Property
diesel fuelpiping' ' ~// \Former Diesel I line
/ I
..~r.~ fuel dispenser
Former 2,500 gallon~
underground diesel
fuel storoge tank Former Underground
gasoline piping
Former Undergound-__l
diesel fuel piping
× 8,000 gallon obove-
Aboveground 4,000 gallon ob v
waste oil tank ground gasoline tank
Kennedy/Jenks Consultants
Odis Dykes, inc.
Bakersfield, California
Site Plan
0 40 80 120
1 "= 40' K/J 912519.00
Approximate scale January 1992
Figure 2
Former underground
Former gasoline dispenser ~Lr-"""'~ ~ ~ gasoline piping
N OD1 OD2
Fuel dispensing island ~~ /
Former diesel fuel dispenser Former underground
diesel
/ pipin'g
/,Jx~ Former underground
// diesel fuel piping
/
' I
Former 2,500 gallon
underground diesel Kennedy/denks Consultants
I fuel st°rage tank I
Odis Dykes, Inc.
I , Bakersfield, California
Soil Boring Locatlona
-~-Soil Location 9.12319.00
Boring
K/J
, January 1992
0 5 '~ 10 15 Figure 3
~'--~~--~ Environmental Health Sew~ces Department
RANDALL L. ABBOTT ~ ST~'VE mcca~ ~ ~v, rE~S. DIm~ctor
DIRECTOR ~r Pollution Control I~strict
DAVID PRICE !ii V~LUA~ J. RODDY. APCO
ASSISTANT DIRECTOR
Planning & Development Senates Depa~tznent
TED JAMES, AlCP, DIRECTOR
ENVIRONHENTAL HEALTH SERVICES DEP'6~~;~F-NK$1CHIL'i-ON
~AKER$'r:~£LD. CA
October 15, 1991 FI E C £ j I.~ E D
OCT 17 1991
Job #._~.~ .~ ,/.~. ~)f__.~
Vickie Breaw ~
Odis Dykes, Inc.
313 Daniels Lane ~
Bakersfield, CA 93307
SUBJECT: Location : 313 Daniels Lane, Bakersfield, CA
Known As : Odis Dykes, Inc.
Permit # : 250024
Dear Ms. Breaw:
Our Department has reviewed the site characterization workplan submitted by
Kennedy/Jenks Consultants. The workplan addressing soil sampling constituents to be
analyzed is acceptable, and health and safety considerations are also acceptable, for
investigation of extent of contamination present at this former underground tank site.
Please notif3, this office 48 hours prior to retrieving soil samples. Within thirty (30)
days after sampling and laboratory analyses are completed, a comprehensive 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, extension 566.
' . Sincerely.
~Michael Drigg~ ~'
Hazardous Materials Specialist
Hazardous Materials Management Program
MD:ch
cc: -Kennedy/Jenks Consultants - Mark Pishinsky
driggs\breaw.m 14
2700 "M" STREET, SUITE 300 BAKERSFIELD, CALIFORNIA 93301 (805) 861-3636
FAX: (805) 861-3429
Boring &. Well Construct/ Log _ Kennedy/Jenks
BORING LOCATION ODIS D YKES~ INC.~ BAKERSFIELD CA Boring/Well Name OD 1
DRILUNG COMPANY D~IU,.ER
Me/ton Drilling Randy Project Name Odis Dykes
DRIUJNG METHOD(6) DRILL BIT(S) 6IZE
Hollow Stem Auger 8 inch Project Number 912319.00
ISOLATION CASING FROM TO FT.
N/A ELEVATION AND DATUM TOTAL DEFTH
m~NK c~m mOM TO FT. N/A 20 FEET
N/A t)ATE STARTED DATE COMPLETED
I~RFORATED C~G mOM TO FT. I 1/6/91 I I/6/91 '
N/A . STAT~ WATER ~VAT~N
raZE AND TY~ OF ~LT~ PAC~ mOM TO FT. None Encountered
N/A LO~ SY ~ST~.
SEAL FROM TO FT. J. Cooper N/A
BENTONI7'E CHIPS 0 20 s~M~L~. M~rHODS W~LL COM~'rio.
~ROU? FROM TO FT. California Modified D S~FAC~ .OUS~.
N/A ~olit ~ooon m aTANO ~.~ N/A FT.
SAMPt.~S WELL CONSTRUCTION
TW,,~ ~ ~ (r~ Log ~ Colin. &LE DESCRIPTION amd DRB.UNG REMARKS
Cl 1.2 26 ::::::'::::::::: GC GRAVE[: SURFACE PAVING WITH SOME
9 .....-.........- 2 PARTS PER MILUON (ppm)
.-.:.:..-.:.:.:.:.:
4 5- !iiiiiiiiiiiiiiii = SW IOYR SAND: DARK YELLOWISH BROWN, MEDIUM
c2 1.4. 6 _ :i:!:i:!:!:i:i:i: . ...***... 4/2 GRAINED, POORLY SORTED, MAXIMUM CLASTS
7 10- !ii~ii!i!i!iii!i! ' IOYR SAND: MODERATE YELLOWISH BROWN, FINE TO
7 15- '~'~'['~',5YR ' SAND: LIGHT BROWN, FINE TO MEDIUM
C4 1.4 ~1 - i':'['~': .... 516 GRAINED. SLIGHTLY MOIST.
[~ 2.~.2.2.:
o :..-.2.?,
~- - :':':':'"' IOYR '"
' 12 20- .'.'.'.'. 6/2
~,T .'.'.'.','
TD 20.0 FEET SPLIT-SPOON DRIVEN TO 21.5
FEET.
1 ppm OV.
NOTE: SAMPLES DESCRIBED ARE THE "C"
(UPPER) PORTION OF THE CORE RECOVERED AT
EACH INTERVAL SAMPLED.
? SACKS OF BENTONITE CHIPS TREMIED
THROUGH AUGER AND HYDRATED TO GROUT
BORING
?-40. ~
(6-87) ($-88) (8-90) SHEET I OF I
Boring & Well constructia~z Log Kennedy/Jenks
BORING LOCATION
ODIS DYKES~ INC.~ BAKERSFIELD CA ~oringAtVel/Nerne OD2
DRIt. UNG COMPANY DRILLER
Me/ton Dr#ling Randy Project Neme Odis Dykes
DRILLING METHOD(S) DRill B/T(S)
Ho#ow Stem Auger 8 inch Project Number 912319.00
iSOLATION CASING FROM TO FT.
N/A EL~'VATION ANO ;)ATUM TO~A~
,LA, K C'~,~, FROM TO FT. N/A 35 FEET
N/A ;)ATE ST~.qT;;) OATE
~O~ATE;) CAS~. FROM TO ~T. I 1/6/91
N/A STA~C WATER F.~EVA?IO, ,ORTH,~e
S=£ AN;) TY~ OF F~T~ ~'ACK FRC~M TO FT. None Encountered
N/A LO,e~ ,Y ~ASTINe
S~L FROM TO ~. ~. Cooper
B£NTON/T£ CH/PS 0 $5 ~u,, ~rrHoos WLL COM~_~TIO,
DROU~ FROM TO FT. California Mod/f/ed D SURFACE .OUSINe
N/A Sprit Spoon "" STAND ~ N/A FT.
~.ES WELL CONSTRUCTION
SAMPLE D~IFTION end DRILUNG REMARKS
SILTY SAND: DUSKY YELLOWISH BROWN, 40%
SILT, FINE GRAINED, CLASTS SIZE <3 cra,
HYDROCARBON ODOR.
1526 PARTS PER MILLION (ppm)
ORGANIC VAPORS (OV)
1345 ppm OV.
SAND: DARK YELLOWISH BROWN, 5% SILT,
WELL GRADED, FINE TO MEDIUM GRAINED,
SLIGHT HYDROCARBON ODOR, SLIGHTLY
BENTONITE MOIST.
1862 ppm OV.
SAND: MODERATE YELLOWISH BROWN, WELL
GRADED, FINE TO MEDIUM GRAINED, SLIGHT
HYDROCARBON ODOR, MOIST.
185 ppm OV.
SAND: PALE YELLOWISH BROWN, WELL
GRADED, FINE TO MEDIUM GRAINED, NO ODOR.
62 ppm 0V.
SAND: PALE YELLOWISH BROWN, WELL
GRADED, MEDIUM TO COARSE GRAINED, NO
ODOR, MOIST.
9 ppm OV.
F-40. l
(t~-$?) ($-8~) (8-~0) SHEET I OF 2
Borin~ & Well Constructi~ ,' og -- Kenne#~/Jenk$
Project Neme Odis Dykes Project Number. 912319.00 8orlng/VVell Neme OD2
~M Pr. ES V~r. LL ~NS~UCTmN
~ ~ U~
9 :~:~:~:~:~:~:~:~:~ '-:.:.;. IOYR ~D: P~ YELLOWISH BROWN, WE~
CS 1.4 1~ :::::::::::::::::: , .~.~.?. 6/2 G~ED, MEDIUM TO CO~SE G~NED, NO
~ - ~:~:~:~:~:~:~:~:~: : :*:.:.:. ODOR. MmST.
¥:::::¥::::::: '. ','.'.
:5::::::::::::::: X.2-2.
10 30- [~[~ ':':'[': IOYR ' ~D: D~K YE~OWISH BROWN. WE~ ' '
c7 1.4 14 :::::::::::::::::: ~';'~'~' 4/2 GRADED, FINE TO MEDIUM GRAINED, NO ODOR,
o ~t~o~t -- ~[:~:~:~: ':':':':
:.:.:.:.:.:.:.:.:
- -:.:.:.:
l~ - '.'.'-'-'-'.'.'.', '" ' 0~0~,
,.:.:.:.:.:.:.:.:, .-.';:'..~
ID 35.0 FE~
S~IT ,S~ON DRIVEN TO 36.5 FE~.
NO~: S~ES DESCRIBED ARE THE 'C'
(UP.R) ~RTION OF THE CORE RECOVERED AT
EACH INTERV~ S~ED.
17 SACKS OF BENTONITE CHIPS TREMIED
THROUGH AUGER AND HYDRATED ~O
BORING.
F-40.1 '
(6-87) ($-88) (8-90) SHEET 2 OF 2
· Boring & Well Construct/ Log -- Kennedy/,,c.~
BORING LOCATION OO/S DYKESt INC. t BAKERSFIELD CA BoringAtVellNam~ OD3
DRILLING COMPANY DRILLER
Me/ton Drilling Randy Pro/act Name Odis Dykes
DR..uNe M~rHOmm DR.J. mr~m ~ZE
Ho/Iow Stem Auger 8 inch Project Number 912319.00
LSO LATION CASING FROM TO FT.
N/A ELEVATION AND OATUM TOTAL
STANK CAaNG FROM TO r~. N/A 70 FEET
N/A STATIC WATER ELEVATION NORTHING
I SEE AND TYI~ OF FILTER PACK FROM TO FT. None Encountered N/A
N/A LOGGEO ey r. ASTem
SEAL FROM TO FT. d. Cooper N/A
BENTONITE CH/PS· 0 70 ~AMPLIR~ METHOD~ WELL COMPLETION
GROUT FROM TO FT. , Celifomi~ MoEit~
~AMPLE$ WELL CONSTRUCTION
I~ USCS
Tv~ ~ ""'~'"~ lr-,~ L~g ue.~ Colo~ &AMFLE DESCRIFTION and DRILLING REMARKS
16 ':'-":'-":':'-":' GP ~m~ IOYR SANDY GRAVEL: DARK YELLOWISH BROWN, 60
'-'-'-'-"'-'.'.' ~' ORGANIC VAPORS (OV)
4 5- SP ~ IOYR SAND: DUSKY YELLOWISH BROWN, 30% SILT,
c2 1.4 4 '." .' · 2/2 POORLY GR.~ED. FINE TO COARSE OR. NED,
6 - ":'::':- ' STRONG HYDROCARBON ODOR, DRY.
6 10- SW ~ IOYR SAND: DARK YELLOWISH BROWN, 5% SILT,
c3 ~.4 6 ......,.. 4/2 WELL GRADED, FINE TO MEDIUM GRAINED,
8 - .:-:-:.:, ' MODERATE HYDROCARBON ODOR, DRY.
- -~ :.:.:.:.:
~o - ::::::::::::::::: - .:.:..:i
- ::::::::::::::::: - :.:.:.:.
o ::::::::::::::::: .:. :.:.:
- ::::::::::::::::: - ........
::::::::::::::::: .:.:.:.:
F-40,1
(6-87) ($-88) (8-~0) SHEET ? OF 3 ·
t ..~?~,~..(~ Location_ .. of Cro Section
A ' A' " Depth (feet)
OD, OD2 0A~--
o 1 0~v~.o~,~ A'
~ ~ 0 10 20
"'~' !: ~' ~' ._ U~"% 1" 10'
-.. ..['. ~2~~', ~~~' ..~ =
...
' ~_ :~'. · Legend:
~,-. ~ '/
:" " ' '. ' ' .... ' .)~t~ I
'" ' ' " .... '~ Aoproximote location of Contact
-~~~ ~ ~6'': o/ -o.o -- Gravel, Sandy
.~~ ~~'~~' ':' ~ p,~ , between Lithologic Units
..~ · · ~ ~'~"'~,' 40 ~ -t"- q- S~nd, C~e~
~ - , . ~ . . ~ Approximate Extent of Elevated
" Sand, Silty or Fine Grained ~ Petroleum Hydroccrbons
. -- ...... : ~,_,o ~.~-~' Sand ~ _ Concentration of TPH - Diesel
. -
·.<< ' ~ ~/. o~/~ / ,~ -- Soil Boring. (mg/kg)
. . .. · -'~ ~' ~ ,D
:~. ~
Unknown L~ter~l Extent
60
C))' 10 20 30
~ 1"=10'
70
' ~ Kennedy/Jenks Consultants
Odis Dykes, lncl
Bakersfield, California
61eneralized Geologic
................................... Cr_ose Sect_Ion
i K/J 912519.00
I ~.. ~'~0~ ~ danuar~ 1992
~ Figure 4
Boring & Well Constructfi Log Kennedy/Jenk$
Project Name Odis Dykes Project Number. 912319.00 Boring/We# Name OD3
~AMI~E$ WElL CONSTRUCTION
Lm] ~ Color SAMPI,E DESCRIPTION end DRILLJNG AEMA~I~
TyiN
lO J:::::::::::::::'. :-:.:.:.'.iIOYR SAND: PALE YELLOWISH BROWN, 6% SILT,
c6 1.4 '14 ::::::::::::::::: ~, 612 WELL GR,~ED, F'INE TO MEDIUM GR~INED,
'18 - ::::::::::::::::: MODERATE HYDROCARBON ODOR, DRY.
::::::::::::::::: 1480 ppm OV.
-
':!:i:i:!:!:!:!:i:
0
-
':!:i:!:i:i:!:i:i:
13 30- i:i:i:i:i:::i-*!:i ........ "1423 ppm OV.
C7 1.4 17
29 -
- .:.:..*.;.:.;...:.
:.'.:._'.:.:.'_.:.:
- .?.:.:.:.:.;.:.
0
-
10 35- :i:i:i:!:i:i:!:!: SP IOYR SAND: PALE YELLOWISH BROWN, POORLY
c~ 1.4 17 ::::::::::::::::: ~ 6/2 GRADED, FINE GRAINED, MICACEOUS,
22 - '"**'"**'*'**" MODERATE HYDROCARBON ODOR.
'-~-:'.*':':'.";'i
· ':':'***:':*:*:':' 1368 ppm OV.
o
- i:i:i:i:i:i:i:i:
'-:-;-:-:':-:-:'i
:.:.'..*.:.:.:.:,
19 40-'.v.v.v.v:::::::::::::::: SM i:'[:.~',~ IOYR ~ILTY SAND: DARK YELLOWISH BROWN,
C9 1.4 27..v.v.-.-.v':::::::::::::::: l~!~ 4/2 I POORLY GRADED, FINE GR/MNED, 40% SILT,
35 - *.'.v.'.*.**'.* MODERATE HYDROCARBON ODOR.
~:.;.:.:.:.:-:.:.'.
:!;!:!:!:!:!:!:!: ~. 712 ppm OV.
- :':':':':':':':'; i
::::::::::::::::: :'. ::'::
- [.:-:.:.:.:.:.:-:. .' -:'i '-!
~::::::::::::::::: :. ::: -:!
:.:.:.:.:.:.:.:.: · .. ~ .
'.:.:.:.:.:.:.:.:.
12 45- :-:-:':':':-:*:': SP ) SAND: DARK YELLOWISH BROWN, POORLY
C1'1 1.4 18 :::::::i::::::::: i G~D, FINE TO MEDIUM GRAINED, 5% SILT,
20 - ::::::::::::::::: MODERATE HYDROCARBON ODOR.
,::!:!:!:::!:!:!:! 723 ppm OV.
-
0 - BENTONITE
- ,:::::::::::::::::
::::::::::::::::::
'.:.:.:.:.:.:.:.:.
12 50 - .:::;:::::::::;::: SM ~iLTY SAND: DARK YELLOWISH BROWN, 30%
C12 1.4 28 ::::::::::::::::: SILT, POORLY GRADED, FINE GRAINED,
' 30 - ::::':::::::::::: CLAY, MODERATE HYDROCARBON ODOR.
.:::::::::::;::;:: 607 ppm OV.
- ::::::::::::::::::
- ,.:.:.:.:.:.:.:.:.
0
- ::::::::::::::::::
10 55 - ::::?:::::::::::: ML SANDY SILT: DARK YELLOWISH BROWN, 40%
C13 1.4 28 :i:i:!:!:!:i:!:i:! FINE GRAINED SAND, MODERATE
30 - ::::::::::::::::*: HYDROCARBON ODOR.
:::::::::::::::::: 270 ppm OV.
:.:.:.:.:.:.:.:.:.
F-40.1
(6-87) 0-88) (8-90) SHEET 2 OF 3
Borin=, & Well Construct/ ( og Kennedr/Jenks
Project Name Odis Dykes Project Number. 912319.00 Boring~I/Veil Name OD3
SAMPLES WELL CONSTRUCTION
~ ~ USC$
T~. ~ ~ ~ Log Color SAMPLE DESCRIPTION .nd DRB.UNG REMARI~
:::::::::::::::::: .
9 60- iiiiiiiiiiiii~iiii SC 5Y CLAYEY SAND: UGHT OUVE GRAY, 40% CLAY,
C14 1.4 11 :::::5::::::::::: 5/2 LOW PLASTICITY, SUGHT HYDROCARBON
~ 3 - !:!:!:i:i:!:i:i:i: ODOR.
i:i:!:i:i:!"i:i:i 138 ppm OV.
- ,,.:::..::;:::-::::..
0 ::::':::'::::::::..
-
'.:.:.:.:.:.:.:.:~
16 65- .:-:.:.:.:-:-:.:.: SW IOYR SAND: MODERATE YELLOWISH BROWN, WELL
c16 1.4 30 ::i:i:i:i:i:i:i:i: 5/4 GRADED, FINE TO MEDIUM GRAINED, 1096 SILT,
46 - .::::::::::::::::: SLIGHT HYDROCARBON ODOR.
'iiiii!iiiiiiiiiii .3 ppm OV.
:.:.:.:.:.:.:.:.:
- .:.:.:.:.:.:.:.:,
0 :.:.:.:.:.:.:.:.:
I':':':':':':':':'
18 70- BENTONITE -- ~::::::::: SP IOYR SAND: PALE YELLOWISH BROWN, POORLY
C16 1.4 24 :::::::::'.':::::: 6/2 GRADED, MEDIUM GRAINED, SLIGHT
6o - ,::::::::::::::::: HYDROCARBON ODOR. CLASTS <2 cm, IRON
OXIDE STAINING.
17 ppm OV.
TD 70.O FEET; SPLIT SPOON DRIVEN TO 71.5
FEET
23 SACKS OF BENTONITE CHIPS TREMIED
THOUGH AUGER AND HYDRATED TO GROUT
BORING.
NOTE: SAMPLES DESCRIBED ARE THE 'C'
(UPPER) PORTION OF THE CORE RECOVERED AT
EACH INTERVAL SAMPLED.
F-40.1
(6-87) (3-88) (8-90) SHEET 3 OF 3
F;eld Sample Chain of Cust0 Record Kennedy/Jenks/Chilton
Laboratory Division
Source of Sample (s) (~4'~; PT~ .5' K/J/C Job No.
Address Affiliation
Sample Information (1)
Lab No. Field No. Date Time Type Depth Remarks (Suspected Contaminants, Con-
(Lab Use Only) (2) ruiners, Preservatives, Field Conditions, etc.)
Chain of Possession
Relinquished by Date Time Received by (3) Date Time
(Signature and affiliation) (Signature and affilia.tion)
2.
Logged in at K/J/C by
(1) A separate Laboratory Analysis Request Form is to be filled out by the collector and given to the laboratory when samples are delivered.
(2) e.g. water, sludge, soil, etc.
(3) If any samples are not intact at time of transfer, please describe on the back of this form.
Each batch of 10 or fewer samples of each matrix type (soil, water, etc.) must include enough of one sample for triplicate analysis.
WARNING These samples contain unknown chemicals which, upon analysis, may be determined to be "known to the State to cause cancer or reproductive toxicity;'
under the California Safe Drinking Water and Toxics Enforcement Act of 1986 (Proposition 65). Lab-6 ~LAB~
'~eld Sample Chain of Cust~ Record . KennedY/Jenks/Chilton
Laboratory Division~ '
Source of Sample (s) ~ ~'~ ~) Y/'e--J" K/J/C Job No.
/
Collector
Address Affiliation
Address~ 0~---~ .)V'~ ~ 5'~ ,~'-~- //~"" .
Phone ~:~/~:'P~ ~'
Repo,,o ~/< ~ ~/,~$/~ Phone d~)'~ ~- ~ ~ .'
/
Sample Information (1)
Lab No. Field No. Date Time Type Dept~ Remar~ (Sus~cted Contaminants. ~n-
(~b Use Only) (2) (~W) tainers. Preser~tives. Field Conditions. etc.)
Chain of Possession
Relinquished by Date Time Received by (3) Date Time
2.
Logged in at K/J/C by _
(1) A separate Laboratory Analysis Request Form is to be filled out by the collector and ~iYen to the laboratory when samples am delivered.
(2) eg. water, sludOe, soil, etc.
(3) If any samples are not intact at time of transfer, ~lease ~escriBe on the Back of this form.
ffach Batch o~ 10 or fewer samples of oath matrix ~y~e (soil, water, otc.) must include enough o~ one sam~l~ ~or triplicate anal~is.
WA~NING lhese sam¢les contain unknown chemicals which, upon analysis, mag ge de,ermined to be "known to the State to cause cancer or m~roductive to×icit¥:'
undo[ the California Safe Drinkm~ ~ater and lo×ics Enforcement Act el ~86 IProposition 65). ~b-~ {I_~B)
Labor .atory ~.~alysis Request Form Kennedy/Jenks/Chilton
Page _/__.of LaboratOry Division
Date of Request/~f~/h,/ K/J/C Job No. ~ / ~ .% / ~, O ~.-). Analysis Authorized by ~ ~ O ~'/~---
Client 0 ~/5 ~/~'~ AffiliationlAddress ~/~/~- ~-~ ~ ~'~ _~
Source of Samples ~.~-~ ~ ~/ ~~ Phon~~ ~
Shipper Arrival Date ~/ ~/~ / Repod Results Phone
Condition Rec'd. Specific Analyses Requested Results Desired
· ~ Identi~ing Information at Laboratory ?) Date of (e.g. Volatiles [601,602], other organics, metals, inorganicHow Soon? (3)
Lab Number ~ .-
(Lab to fill in) ~ ~ (e.g. site taken, field I.D. ~ ~. . Collec- anions, coliform, pH, physical prope~ies, etc.) (3) One Two One Two
~ number, etc.) ~ ~ ~ tion Please cite specific methods and individual anal~es. Day Days Wk W~
002 4
2 ,_
Remark:
(1) Specify as water 0/V). soil (S), or other (describe on back if;need be).
(2) Questions are to be answered (Y) or no (N) if possible. Special concerns (re. condition of sample, detection limits desired, important information re. sample history, etc.) should be noted under remarks..
(3)tt is not possible to indicate alt possibilities in this space. Please discuss with appropriate lab personnel if you are uncertain.
(4) Normal turnaround time is 2 weeks; there will usually be a surcharge for short turnaround times.
Note: Top copy to laboratory with ,~ample~ Lab-7 (LAB)
Rev, 12/88
Laboratory Analysis Request Form Kennedy/Jenks/Chilton
· Page _~ of 7_,- Laboratory Division
Date of Request K/J/C Job No. q t/ ~ ~/'7' O 0 Analysis Authorized by \]"'""~ ~ (~/)/~ %
Client OQ/'~,, Pt//~-..-~..~ Afliliation/Address/--"/(7/C20~ ~[/ot,~,5~ ~'"f'-~ '//~"
Source of Samples
Arrival Date {/// 9' Report Results t $ ~, ,,z $ . Phone
o,,,l~p~, .......... / / / ~
~' Condition Rec'd. Specific Analyses Requested Results Desired
e ~- Identifying Information at Laboratory (2) Date of e.g. Volatiles [601,602], other organics, metals, inorganicHOW Soon? (3)
Lab Number ~.'-' Collec- '"
(Lab to fill in) E, ne (e.g. site taken, field I.D.~'~ ~,<.- ~-. anions, coliform, pH, physical properties, etc.) (3)One Two One Two
o ~ ~ ~ tion Please cite specific methods and individual analytes. Day Days Wk Wks '-'
r~ '~ number, etc.) ~ ~.~. O -
t'
Remarks:
(1) Specify as water (VV), soil (S), or other (describe on back if need be).
' (2) Questions are to be answered (Y) or no (N) if possible. Special concerns (re. condition of sample, detection limits desired, important inlormation re. sample history, etc.) should be noted under remarks.
' (3) It is not possible to indicate all possibilities in this space. Please discuss with appropriate lab personnel il you are uncertain.
~,~ ~.t,-,.~, ,rmrm md time is 2 weeks: there will usually be a surchar.cje for short turnaround limes. Lab-7 (LAB)
' Rev. 12/88
ENVIRONMENTAL
LABORATORIES, INC.
PETROLEUM J' J' EGLIN, REG. CHEM. ENGR.
4100 ATLAS CT., BAKERSFIELD, CALIFORNIA 93308 PHONE (805) 327-4911 FAX (805) 327-1918
Petroleum Hydrocarbons
KENNEDY/JENKS/CHILTON Date of
LABORATORY DIVISION Report: 11/14/91
200 NEW STINE ROAD, SUITE 115 Lab ~: 12071-1
Bakersfield, CA 93309
Attn.: MARK PISHINSKY. 805-835-9785~
Sample Description: JOB ~912319.00/ ODIS DYKES: OD3A13 ® 56.5' (SOIL), SAMPLED 11-6-91
® 14:50 PM BY J. COOPER
TEST METHOD: TPH by D.O.H.S. / L.U.F.T. M~nual Method - Modified EPA 8015
Individual constituents by EPA Method 5030/8020.
Sample Matrix: Soil
Date Sample Date Sample Date Analysis
Collected: Received @ Lab: Completed:
11/06/91 11/07/91 11/20/91
Minimum
Analysis Reporting Reporting
Constituents Results Units Level
Benzene None Detected mg/kg 0. 005
Toluene None Detected mg/kg 0.01
Ethyl Benzene None Detected mg/kg 0. 005
o-Xylene None Detected mg/kg 0. 005
m-Xylene None Detected mg/kg 0. 005
p-Xylene None Detected mg/kg 0. 005
Total Petroleum
Hydrocarbons (gas) 1. mg/kg 1.
Total Petroleum
Hydrocarbons (diesel) None Detected mg/kg 5.
Comments:
California D.O.H.S. Cert. ~1186
Department Supervisor
ENVIRONMENTAL
LABO RATO RI FS, INC.
PETROLEUM J* J' EGLIN, REG. CHEM. ENGR.
4100 ATLAS CT., BAKERSFIELD, CALIFORNIA 93308 PHONE (805) 327-4911 FAX (805) 327-1918
Petroleum Hydrocarbons
KENNEDY/JENKS/CHILTON Date of
LABORATORY DIVISION Report: 11/14/91
200 NEW STINE ROAD, SUITE 115 Lab ~: 12071-2
Bakersfield, CA 93309
Attn.: MARK PISHINSKY 805-835-9785.
Sample Description: JOB %912319.00/ ODIS DYKES: OD3A14 @ 61.5' (SOIL), SAMPLED 11-6-91
@ 14:58 PM BY J. COOPER
TEST METHOD: TPH by D.O.H.S. / L.U.F.T. M~ual Method - Modified EPA 8015
Individual constituents by EPA Method 5030/8020.
Sample Matrix: Soil
Date Sample Date Sample Date Analysis
Collected: Received @ Lab: Completed:
11/06/91 11/07/91 11/20/91
Minimum
Analys i s Report ing Report lng
Constituents Results Units Level
Benzene 0 46 mg/kg 0.005
Toluene 1 2 mg/kg 0.005
Ethyl Benzene 0 083 mg/kg 0.005
o-Xylene 0 15 mg/kg 0.005
m-Xylene 0 21 mg/kg 0.005
p-Xylene 0 088 mg/kg 0.005
Total Petroleum
Hydrocarbons (gas) 3. mg/kg 1.
Total Petroleum
Hydrocarbons (diesel) 20. mg/kg 5.
Comments:
California D.O.H.S. Cert. #1186
Department Supervisor
ENVIRONMENTAL
LABORATORIES, INC.
PETROLEUM J' J' EGLIN, REG. CHEM. ENGR.
4100 ATLAS CT., BAKERSFIELD, CALIFORNIA 93308 PHONE (805) 327~1911 FAX (805) 327-1918
Petroleum Hydrocarbons
KENNEDY/JENKS/CHILTON Date of
LABORATORY DIVISION Report: 11/15/91
200 NEW STINE ROAD, SUITE 115 Lab ~: 12071-13
Bakersfield, CA 93309
Attn.: M3%RK PISHINSKY 805-835-9785
Sample Description: JOB #912319.00/ ODIS DYKES: OD3A3 ® 11.5' (SOIL), SAMPLED 11-6-91
BY J. COOPER
TEST METHOD: TPH by D.O.H.S. / L.U.F.T. MAnual Method - Modified EPA 8015
Individual constituents by EPA Method 5030/8020.
Sample Matrix: Soil
Date Sample Date Sample Date Analysis
Collected: Received @ Lab: Completed:
11/06/91 11/07/91 11/20/91
Minimum
Analysis Reporting Reporting
Constituents Results Units Level
BenZene None Detected mg/kg 5.
Toluene 59. mg/kg 5.
Ethyl Benzene 32. mg/kg 5.
o ~ Xyl ene 360. mg/kg 5.
m- Xyl ene 340. mg/kg 5.
p -Xylene 140. mg/kg. 5.
Total Petroleum
Hydrocarbons (gas) 6800. mg/k9 500.
Total Petroleum
Hydrocarbons (diesel) 4000. mg/kg 500.
Comments:
California D.O.H.S. Cert. #1186
Department Supervisor
ENVIRONMENTAL
LABORATORIES, INO.
PETROLEUM J' J' EGLIN, REG. CHEM. ENGR.
4100 ATLAS CT., BAKERSFIELD, CALIFORNIA 93308 PHONE (805) 3274911 FAX (805) 327-1918
Petroleum Hydrocarbons
KENNEDY/JENKS/CHILTON Date of
LABORATORY DIVISION Report: 11/15/91
200 NEW STINE ROAD, SUITE 115 Lab #: 12071-14
Bakersfield, CA 93309
Attn.: MOkRK PISHINSKY 805-835-9785
Sample Description: JOB #912319.00/ ODIS DYKES: OD3A11 @ 46.5' (SOIL), SAMPLED 11-6-91
® 14:16 PM BY J. COOPER
TEST METHOD: TPH by D.O.H.S. / L~U.F.T. Fh%nual Method - Modified EPA 8015
Individual constituents by EPA Method 5030/8020.
Sample Matrix: Soil
Date Sample Date Sample Date Analysis
Collected: Received @ Lab: Completed:
11/06/91 11/07/91 11/20/91
Minimum
Analysis Reporting Reporting
Constituents Results Units Level
Benzene 14 mg/kg 5.
Toluene 270 mg/kg 5.
Ethyl Benzene 120 mg/kg 5.
o- Xylene 250 mg/kg 5.
m - Xylene 360 mg/kg 5.
p-Xylene 130 mg/kg 5.
Total Petroleum
Hydrocarbons (gas) 5000. mg/kg 1000.
Total Petroleum
Hydrocarbons (diesel) 1200. mg/kg 100.
Comments:
California D.O.H.S. Cert. #1186
Department Supervisor
ENVIRONMENTAL
LABORATORIES, INO.
P£TROLEU¥ J' J' EGLIN, REG. CHEM. ENGR.
4100 ATLAS CT., BAKERSFIELD, CALIFORNIA 93308 PHONE (805) 327-4911 FAX (805) 327-1918
Petroleum Hydrocarbons
KEN-NEDY/JENKS/CHILTON Date of
LABORATORY DIVISION Report: 11/15/91
200 NEW STINE ROAD, SUITE 115 Lab %: 12071-9
Bakersfield, CA 93309
Attn.: F~%RK PISHINSKY 805-835-9785 .
Sample Description: JOB %912319.00/ ODIS DYKES: OD1A2 ~ 6.5' (SOIL), SD/~PLED 11-6-91 BY
J. COOPER
TEST METHOD: TPH by D.O.H.S. / L.U.F.T. MAnual Method - Modified EPA 8015
Individual constituents by EPA Method 5030/8020.
Sample Matrix: Soil
Date Sample Date Sample Date Analysis
Collected: Received @ Lab: Completed:
11/06/91 11/07/91 11/20/91
Minimum
Analysis Reporting Reporting
Constituents Results Units Level
Benzene None Detected mg/kg 0. 005
Toluene None Detected mg/kg 0. 005
Ethyl Benzene None Detected mg/kg 0.005
o-Xylene None Detected mg/kg 0. 005
m-Xylene None Detected mg/kg 0. 005
p-Xylene None Detected mg/kg · 0. 005
Total Petroleum
Hydrocarbons (gas) None Detected mg/kg 1.
Total Petroleum
Hydrocarbons (diesel) None Detected mg/kg 5.
Comments:
California D.O.H.S. cert2 ~1186
Department Super~zisor
ENVIRONI~ENTAL
LABO RATO RI F.?,, INO.
PETROLEU¥ J' J' EGLIN. REG. CHEM. ENGR.
41~ AT~S CT., BAKERSFIELD, CALIFORNIA 9~ PHONE (~) ~911 F~ (~5) 327-1918
Petroleum Hydrocarbons
KENNEDY/JENKS/CHILTON Date of
LABORATORY DIVISION Report: 11/15/91
200 NEW STINE ROAD, SUITE 115 Lab ~: 12071-10
Bakersfield, CA 93309
Attn.: PU~RK PISHINSKY 805-835-9785
Sample Description: JOB ~912319.00/ ODIS DYKES: OD1A3 ~ 11.5' (SOIL), SAMPLED 11-6-91
BY J. COOPER
TEST METHOD: TPH by D.O.H.S. / L.U.F.T. Manual Method - Modified EPA 8015
Individual constituents by EPA Method 5030/8020.
Sample Matrix: Soil
Date Sample Date Sample Date Analysis
Collected: Received ® Lab: Completed:
11/06/91 11/07/91 11/20/91
Minimum
Analysis Reporting Reporting
Constituents Results Units Level
Benzene None Detected mg/kg 0. 005
Toluene None Detected mg/kg 0. 005
Ethyl Benzene None Detected mg/kg 0.005
o-Xylene None Detected mg/kg 0. 005
m-Xylene None Detected mg/kg 0. 005
p-Xylene None Detected mg/kg 0. 005
Total Petroleum
Hydrocarbons (gas) None Detected mg/kg 1.
Total Petroleum
Hydrocarbons (diesel) None Detected mg/kg 5.
Comments:
California D.O.H.S. Cert. %1186
Department Supervisor
ENVIRONMENTAL
LABORATORIES, INO.
J. J. EGLIN, REG. CHEM. ENGR.
PETROLEUM
4100 ATLAS CT., BAKERSFIELO, CALIFORNIA 93308 PHONE (805) 327.4911 FAX (805) 327-1918
Petroleum Hydrocarbons
KENNEDY/JENKS/CHILTON Date of
LABORATORY DIVISION Report: 11/15/91
200 NEW STINE ROAD, SUITE 115 Lab ~: 12071'-11
Bakersfield, CA 93309
Attn,: MARK PISHINSKY 805-835-9785
Sample Description: JOB %912319.00/ ODIS DYKES: OD1A4 @ 16.5' (SOIL), SAMPLED 11-6-91
BY J. COOPER
TEST METHOD: TPH by D.O.H.S. /L.U.F.T. Man~al Method - Modified EPA 8015
individual constituents by EPA Method 5030/8020.
Sample Matrix: Soil
Date Sample Date Sample Date Analysis
Collected: Received ® Lab: Completed:
11/06/91 11/07/91 11/20/91
Minimum
Analysis Reporting Reporting
Constituents Results Units Level
Benzene None Detected mg/k~ 0. 005
Toluene None Detected mg/kg 0. 005
Ethyl Benzene None Detected mg/kg 0.005
o-Xylene None Detected mg/kg 0. 005
m-Xylene None Detected mg/kg 0. 005
p-Xylene None Detected mg/kg 0. 005
Total Petroleum
Hydrocarbons (gas) None Detected mg/kg 1.
Total Petroleum
Hydrocarbons (diesel) None Detected mg/kg 5.
Comments:
California D.O.H.S. Cert. ~1186
Department Supervisor ·
ENVIRONMENTAL
LABORATORIES, INC.
PETROLEUM J' J' EGLIN, REG. CHEM. ENGR.
4100 ATLAS CT., BAKERSFIELD, CALIFORNIA 93308 PHONE (805) 327-4911 FAX (805) 327-1918
Petroleum Hydrocarbons
KENNEDY/JENKS/CHILTON Date of
LABORATORY DIVISION Report: 11/22/91
200 NEW STINE ROAD, SUITE 115 Lab #: 12071-3
Bakersfield, CA 93309
Attn.: MARK PISHINSKY 805-835-9785.
Sample Description: JOB ~912319.00/0DIS DYKES: OD3A15 ® 66.5' (SOIL), SAMPLED 11-6-91
15:15 PM BY J. COOPER
TEST METHOD: TPH by D.O.H.S. / L.U.F.T. M~nual Method - Modified EPA 8015
Individual constituents by EPA Method 5030/8020.
Sample Matrix: Soil
Date sample Date Sample Date Analysis
Collected: Received @ Lab: Completed:
11/06/91 11/07/91 11/20/91
Minimum
Analys i s Report lng Reporting
Constituents Results Units Level
Benzene None Detected mg/kg 0. 005
Toluene None Detected mg/kg 0. 005
Ethyl Benzene None Detected mg/kg 0.005
o-Xylene None Detected mg/kg 0. 005
m-Xylene None Detected mg/kg 0. 005
p-Xylene None Detected mg/kg 0. 005
Total Petroleum
Hydrocarbons (gas) None Detected rag/kg 1.
Total Petroleum
Hydrocarbons (diesel) None Detected mg/kg 5.
Comments:
California D.O.H.S. Cert. #1186
Department Supervisor
ENVIR~,¥BENTAL
LABORATORIES, INC.
J. J. EGLIN, REG. CHEM. ENGR.
P£TROL£U¥
4100 ATLAS CT., BAKERSFIELD, CALIFORNIA 93308 PHONE (800') 327'-4911 FAX (805) 327'.1918
Petroleum Hydrocarbons
KENNEDY/JENKS/CHILTON Date of
LABORATORY DIVISION Report: 11/22/91
200 NEW STINE ROAD, SUITE 115 Lab #: 12071-4
Bakersfield, CA 93309
Attn.: MARK PISHINSKY 805-835-9785'
Sample Description: JOB ~912319.00/ ODIS DYKES: OD3A16 % 71.5' (SOIL), SAMPLED 11-6-91
BY J. COOPER
TEST METHOD: TPH by D.O.H.S. / L.U.F.T. M~ual Method - Modified EPA 8015
Individual constituents by EPA Method 5030/8020.
Sample Matrix: Soil
Date Sample Date Sample Date Analysis
Collected: Received ® Lab: Completed:
· 11/06/91 11/07/91 11/20/91
Minimum
Analysis Reporting Reporting
Constituents Results Units Level
Benzene None Detected mg/kg 0.005
Toluene None Detected mg/kg 0.005
Ethyl Benzene None Detected mg/kg 0.005
o-Xylene None Detected mg/kg 0.005
m-Xylene None Detected mg/kg 0.005
p-Xylene None Detected mg/kg 0.005
Total Petroleum
Hydrocarbons (gas) None Detected m~/k~ 1.
Total Petroleum
Hydrocarbons (diesel) None Detected mg/kg 5.
Comments:
California D.O.H.S. Cert. $1186
Department Supervisor
ENVIRONMENTAL
LABORATORIES, INO.
J. J. EGLIN, REG. CHEM. ENGR.
PETROLEUM
4100 ATLAS CT., BAKERSFIELD, CALIFORNIA 93308 PHONE (805) 327-4911 FAX (805) 327-1918
Petroleum Hydrocarbons
KENNEDY/JENKS/CHILTON Date of
LABORATORY DIVISION Report: 11/22/91
200 NEW STINE ROAD, SUITE 115 Lab ~: 12071-5
Bakersfield, CA 93309
Attn.: MARK PISHINSKY 805-835-9785
Sample Description: JOB ~912319.00/ ODIS DYKES: OD2A3 ~ 11.5' (SOIL), SAMPLED 11-6-91
BY J. COOPER
TEST METHOD: TPH by D.O.H.S. / L.U.F.T. Manual Method - Modified EPA 8015
Individual constituents by EPA Method 5030/8020.
Sample Matrix: Soil
Date Sample Date Sample Date Analysis
Collected: Received @ Lab: Completed:
11/06/91 11/07/91 11/20/91
Minimum
Analysis Reporting Reporting
Constituents Results Units Level
Benzene None Detected mg/kg 0. 005
Toluene None Detected mg/kg 0.01
Ethyl Benzene None Detected mg/kg 0. 005
o-Xylene None Detected mg/kg 0. 005
m-Xylene None Detected mg/kg 0. 005
p-Xylene None Detected mg/kg 0. 005
Total Petroleum
Hydrocarbons (gas) None Detected mg/kg 1.
Total Petroleum
Hydrocarbons (diesel) 20. mg/kg 5.
Comments:
California D.O.H.S. Cert. ~1186
Department Supervisor
ENVIRONMENTAL
LABORATORIES, INC.
PETROLEUM J- J- EGLIN, REG. CHEM. ENGR.
4100 ATLAS CT., BAKERSFIELD, CALIFORNIA 93308 PHONE (805) 3274911 FAX (805) 327.1918
Petroleum Hydrocarbons
KENNEDY/JENKS/CHILTON Date of
LABORATORY DIVISION Report: 11/22/91
200 NEW STINE ROAD, SUITE 115 Lab %: 12071-6
Bakersfield, CA 93309
Attn.: MARK PISHINSKY 805-835-9785
San%01e Description: JOB ~912319.00/ ODIS DYKES: OD2A5 ~ 21.5 (SOIL), SAMPLED 11-6-91 BY
J. COOPER
TEST METHOD: TPH by D.O.H.S. / L.U.F.T. M~nual Method - Modified EPA 8015
Individual constituents by EPA Method 5030/8020.
Sample Matrix: Soil
Date Sample Date Sample Date Analysis
Collected: Received ® Lab: Completed:
11/06/91 11/07/91 11/20/91
Minimum
Analysis Reporting Reporting
Constituents Results Units Level
Benzene None Detected mg/kg 0. 005
Toluene None Detected mg/kg 0. 005
Ethyl Benzene None Detected mg/kg 0. 005
o-Xylene None Detected mg/kg · 0.005
m-Xylene None Detected mg/kg 0. 005
p-Xylene None Detected mg/kg 0. 005
Total Petroleum
Hydrocarbons (gas) None Detected mg/kg 1.
Total Petroleum
Hydrocarbons (diesel) None Detected mg/kg 5.
Comments:
California D.O.H.S. Cert. #1186
Department Supervisor
ENVIRON~IENT,4L ~ ~
LABORATORIES, INO.
PETROLEUM J' J' EGLIN, REG. CHEM. ENGR.
4100 ATLAS CT., BAKERSFIELD, CALIFORNIA 93308 PHONE (805) 327-4911 FAX (805) 327-1918
Petroleum Hydrocarbons
KENNEDY/JENKS/CHILTON Date of
LABORATORY DIVISION Report: 11/22/91
200 NEW STINE ROAD, SUITE 115 Lab ~: 12071-7
Bakersfield, CA 93309
Attn.: MARK PISHINSKY 805-835-9785
Sample Description: .JOB ~912319.00/ ODIS DYKES: OD2A7 ® 31.5 (SOIL), SAMPLED 11-6-91 BY
J. COOPER
TEST METHOD: TPH by D.O.H.S. / L.U.F.T. Manual Method - Modified EPA 8015
Individual constituents by EPA Method 5030/8020.
Sample Matrix: Soil
Date Sample Date Sample Date Analysis
Collected: Received ® Lab: Completed:
11/06/91 11/07/91 11/20/91
Minimum
Analysis Reporting Reporting
Constituents Results Units Level
Benzene None Detected mg/kg 0. 005
Toluene None Detected mg/kg 0. 005
Ethyl Benzene None Detected mg/kg 0.005
o-Xylene None Detected mg/kg 0. 005
m-Xylene None Detected mg/kg 0. 005
p-Xylene None Detected mg/kg 0. 005
Total Petroleum
Hydrocarbons (gas) None Detected mg/kg 1.
Total Petroleum
Hydrocarbons (diesel) None Detected mg/kg 5.
Comments:
California D.O.H.S. Cert. #1186
Department Supervisor
ENVIRONMENTAL
LABORATORIES, INC.
PETROLEUM J' J' EGLIN, REG. CHEM. ENGR.
4100 ATLAS CT., BAKERSFIELD, CALIFORNIA 93308 PHONE (805) 327.4911 FAX (805) 327-1918
Petroleum Hydrocarbons
KENNEDY/JENKS/CHILTON Date of
LABORATORY DIVISION Report: 11/22/91
200 NEW STINE ROAD, SUITE 115 Lab %: 12071-8
Bakersfield, CA 93309
Attn.: MARK PISHINSKY 805-835-9785
Sample DescriPtion: JOB %912319.00/ ODIS DYKES: OD2A8 @ 36.5' (SOIL), SAMPLED 11-6-91
BY J. COOPER
TEST METHOD: TPH by D.O.H.S. / L.U.F.T. Manual Method - Modified EPA 8015
Individual constituents by EPA Method 5030/8020.
Sample Matrix: Soil
Date Sample Date Sample Date Analysis
Collected: Received @ Lab: Completed:
11/06/91 11/07/91 11/20/91
Minimum
Analys i s Report ing Report ing
Constituents Results Units Level
Benzene None Detected mg/kg 0. 005
Toluene None Detected mg/kg 0. 005
Ethyl Benzene None Detected mg/kg 0.005
o-Xylene None Detected mg/kg 0. 005
m-Xylene None Detected mg/kg 0. 005
p-Xylene None Detected mg/kg 0. 005
Total Petroleum
Hydrocarbons (gas) None Detected mg/kg 1.
Total Petroleum
Hydrocarbons (diesel) None Detected mg/kg 5.
Comments:
California D.O.H.S. Cert. ~1186
Department Supervisor
FILE' CONTE.~ITS SUMMARY
Activity Date # Of Tanks Comments
ESTIMATED SOLUTE DOWNWARD HIGRATION IN SOIL
ENTER DATA ~ DEFAULT/OPTIONAL = AUTOCALC
BENZENE REF
+++++++++++++++++++++++++++++++++++++++++++++++++++++++++++++
.... [ _" ?, .....NT
ON F ~,.~1 ± ?:~, INFORMATION
Cone. chemical (Co) ppm ~ 14
Chemical biodegradation (b ppm/day ~ ' 0.0003 !
:-~ h.:-~:,IETED. S /
Depth of ~nsatuz'a'tecf zone cm ~ 4389
%o~ ~ ' ' + ~' dist. coef t Kd) mi/g · ()
.... u/ ~,~,_,~ . , · ~ r .
.Amt. ~ercoiarine' soil water cm/yr' · "~
.... ,' ' " :~ 0 ! 0
Sc)ii moisture c:on,_.er.% (Ow) ml/mi .
~Eetardatioa facnor (R~ = 128!
.'-,- ... () 98'~
. emica[ veiocitE- ~n ~oii cra/vt = ..1 a83
Tr-av~J *-ime in unsat'O zone yr = 29135
Corec. <'hem.i.c::~.[ l_eft aftec 7, ppm : -3, i TE+04
+++~+++++++++++++++++++++++++++++++++++e+++++++++++++++++~+++
fed = f(oc :~ foe o]:' may Oe ac~:ua.J, ly der:er'mined.
DISTIBUTION OF BULK HYDROCARBON
GASOLIi~E
~.ensitv of petroleum H ml
Aver'age TPH conc. mg/kg 3000
Bmlk density of soil g/cm"3 160
Soi~ porosity -- 0.3
Est[mated plume radius ft 10
Depth of plume ft 30
~:istimated plume volume it'"3 9424.8
~ d" 3 349
~,/eie'ht impacted soil
Volume HC discharged gal 4.23E+04
Depth unimpacted so.il ft !40
Volume unimpacted soil vd"3 439S2.4--
i 1'
Lo ..... me soil_ fo'r ~es. S yd"3 6410 ~ ~,F~ ~,~m,~ -~
WATER RESOURES CONTROL BOARD
DIVISION OF WATER QUALITY
UST .CLEANUP PROGRAM
SITE SPECIFIC QUARTERLY REPORT
CONTRACTOR NO: 15000 SOURCE OF FUNDS: SUBSTANCE: 12034
SITE NO: 250024 FEDERAL EXEMPT: N PETROLEUM: Y
SITE NAME: ODIS DYKES INC. DATE REPORTED: 06/20/91
ADDRESS: 313 DANIELS LANE DATE CONFIRMED: 06/20/91
CITY/ZIP: BAKERSFIELD, CA 93307 MULTIPLE R.P's: N
SITE STATUS
CASE TYPE: S CONTRACT STATUS: 4 EMERGENCY RESPONSE:
RP SEARCH: S DATE UNDERWAY: 06/20/91 DATE COMPLETED: 06/20/91
PRELIMINARY DATE UNDERWAY: 06/14/91 DATE COMPLETED: 07/19/91
ASSESSMENT: C
REMEDIAL DATE UNDERWAY: / / DATE COMPLETED: / /
INVESTIGATION:
REMEDIAL ACTION: DATE UNDERWAY: / / DATE COMPLETED: / /
POST REMEDIAL DATE UNDERWAY: / / DATE COMPLETED:
ACTION MONITORING:
ENFORCEMENT ACTION TYPE: DATE TAKEN:
TAKEN:
LUFT FIELD MANUAL CONSIDERATION 2, S, C, A.
(CATEGORY 1, 2, 3, PLUS H, S, C, A, R, W, G, OR O AS APPLICABLE)
CASE CLOSED: DATE CLOSED: / /
DATE EXCAVATION STARTED: / / REMEDIAL ACTIONS TAKEN:
RESPONSIBLE PARTY
CONTACT NAME: VICKIE SPECIALIST:
COMPANY NAME: ODIS DYKES INC. SENSITIVITY: NES
ADDRESS.: 313 DANIELS LANE ABANDONMENT i: A1456-25
CITY/STATE: BAKERSFIELD, CA 93307 DATE OF REPORT: 07/19/91
PHONE ~: (805) 322-3039 LEAK REPORT: Y
L ~ Environmental Health Senfices Department
RANDALL . ABBOTT STEVE McC.al ~ ~'y, REHS, DIRECTOR
DIRECTOR
DAVID PRICE 111 wn ~,]~M J. RODDY, APCO
ASSISTANT DIRECTOR Ptanning & Development Services Department
TED JAMES, AICP, DIRECTOR
ENVIRONMENTAL HEALTH SERVICES DEPARTMENT
July 3, 1991
John Noonan
Regional Water QualitY Control Board
3614 E. Ashland
Fresno, CA 93726
Dear Mr. Noonan:
On June 14, 1991, one underground storage tank used for the
storage of diesel was abandoned under County Permit #A1456-25. The
facility, Odis Dykes, Inc. located at 313 Daniels Lane in Kern
County has aboveground tanks dispensing product from the same
dispenser island as the underground tank did. After the removal of
the underground tank 'as per permit requirements soil samples were
retrieved at two and six feet beneath the tank and dispenser
island.
High levels of hydrocarbons were detected in the samples
retrieved from beneath the gasoline and diesel dispensers. The
remediation will be overseen by the Underground Storage Tank
Enforcement and Mitigation Section of the Kern County Environmental
Health Services Department. Any repairs to the dispensers or
piping associated with the aboveground tanks will be' overseen by
John Hodes of the Bakersfield Fire Department.
If you have any questions concerning the aboveground tanks
please contact John Hodes at (805) 326-3951. If you have any
questions regarding the remediation of the contamination under the
dispenser island contact Chris Burger at (805) 861-3636.
Sincerely~
Hazardous Materials Specialist
Hazardous Materials Management Program
CG:jg
cc: Chris Burger
Odis Dykes, Inc.
John Hodes
2700 "M" STREET, SUITE 300 BAKERSFIELD, CALIFORNIA 93301 (805) 861-3636
FAX: (805) 861-3429
PRINTED ON RECYCLED PAPER
ENVIRONMENTAL HEALTH SERVICES' DEPARTMENT
STEVE McCALLEY, R.E.H.S. ~ 2700 "M" Street, Suite 300
DIRECTOR V/~ Bakersfield, CA 93301
(805) 861-3636
(805) 861-3429 FAX
November 29, 1993
Odis Dykes
Odis Dykes, Inc.
P. O. Box 10088
Bakersfield, CA 93389-0088
SUBJECT: Location: 313 Daniels Lane
Bakersfield, CA
Known As: Odis Dykes, Inc.
Permit #: 250024
Dear Mr. Dykes:
This letter is to reaffirm our meeting on November 18, 1993, 'regarding the above-referenced
facility.
Discussions were conducted on options for remediating the gasoline hydrocarbon
contamination that exists beneath the site of a former underground storage tank.
It was agreed upon that the following activities would be conducted before a closure letter
could be issued for this site.
1. All visible contaminated soil will be excavated by Odis Dykes, Inc., within a
minimum area of ten (10) feet radius of the center of the dispenser pad and
approximately twenty (20) feet in depth, resulting in the removal of the
majority of the high levels of contamination.
2. The excavated soil will be placed on visquine and spread out to a depth of 8-
12 inches. Periodic turning of the soil will be conducted to facilitate the
aeration process.
3. Clean material will be brought to the site and the excavation will be backfilled
and compacted to the natural grade of the existing facility yard.
After implementation of the above, a review of all file data and inspection of the site will
be conducted by this Department. It is expected at that time a closure letter for this facility
will be issued.
Odis Dykes
Subject: Former Underground Storage Tank - 313 Daniels Ln., Bakersfield, CA
November 29, 1993
Page 2
If there are any further questions, please do not' hesitate to call me at (805) 861-3636,
Extension 566.
Sincerely,
Steve McCalley, Director
Driggs, R.E.A.
By Y~Iichael R.EX~.S~.,
Hazardous Materials Specialist II
Hazardous Materials Program
MD:cas
cc'. File
\driggs~.,50024
ENVIRONiV,, )TAL HEALTH SERVI¢ DEPARTMENT
STEVE McCALLEY, R.E.H.S.
i 2700 "M" Street, Suite 300
DIRECTOR Bakersfield, CA 93301
. u ~j~l~.~:;~Wl,~ (805) 861-3636
'~,~~L~,~?' (805) 861-3429 FAX
February 1, 1994
REMEDIAL ACTION COMPLETION CERTIFICATION
Odis Dykes
Odis.Dykes, Inc.
P. O. Box 10088
Bakersfield, CA 93389-0088
SUBJECT: Location: 313 Daniels Lane, Bakersfield, CA
Known As: Odis Dykes, Inc.
Site No.: 250024
Dear Mx. Dykes: .
This letter confirms the completion of site investigation and remedial action for the
underground storage tank(s) at the above site. Thank you for your cooperation throughout
this investigation. With the provision that the information provided to this agency was
accurate and representative of site conditions, no further action related to the underground
tank release is required based on the available information as set forth in California Code
of Regulations, Title 23, Division 3, Chapter 16, Article 11, Section 2721(e) (Underground
Storage Tank Corrective Action Regulations).
If you have any questions regarding this matter, please contact Michael Driggs at (805)
861-3636, Extension 566.
Sincerely,./~ ~k]~~
Steve McCalley, Director D~entPa~a
-Environmental Health Services
SMc:ch
SENDER:
.* Complete items 1 and/or 2 for additional servicea.,~., ~ also wish to receive the
Complete items 3. and 4e & b. t * following services (for an extra
· PHnt your name and address on the reverse of this~ ~ that we can
ream this car~ to you. f~):
d~s ~ A~aChnot ~erm~.this fo~ to the front of the mail~iece, or on the back if s~ace 1. ~ Address~'s Address
· W~e "R~m Receipt R~st~" on t~ mail~ ~w t~ a~cle numar
2. ~ Reetricted Delivew
· The Re~rn Receipt will s~w to w~m.t~ a~ was ~elive~ a~ ~ date
deliver~.
3. A~icle Addressed to: ~ ~ ' Con. It ~s~a~er for fee.
OD~S ~YKES, ~NC.
~' ~ 4b. Sewi~ T~
~'~' ~ ] ~ J ~ R~i~e~ ~ Insur~
~ERSFIELD., CA 93389-0088 I~l~Ce~fi~"~ ~ COD
Merchandise
5.~tur. (AOdresse~ O. ASr._,. Addre. (Only if ,.que~,
(Agent)
Signature ~- '~~ '~'
~ Form 3811, Decem~r 1991 ~ u.s.G~.o.:i~;.~ DOMES~C R~URN RECEI~
POSTAL SERVICE IL
UNITED
STATES
II
Official Business PENALTY FOR PRIVATE'
USE TO AVOID PAYMENT
OF POSTAGE. $300
Print your name, address and ZIP. Code here
£.~Vi:-~ONMENTAL HEALTH DEPARTMENT
2700 "M" STREET, SUITE 300
BAKERSFIELD, CA 93301
STEVE McCALLEY, R.E.H.S. ~ 270o 'M' Street, Suite 300
DIRECTOR tV Bakersfield, CA 93301
(805) 861-3636
(805) 861~3429 FAX
October 19, 1993
Odis Dykes, Inc.
P. O. Box 10088
Bakersfield, CA 93389-0088
SUBJECT: Location: 313 Daniels Lane
Bakersfield, CA
Known As: Odis Dykes, Inc.
Permit #: 250024
Gentlemen:
A recent review of the above-~referenced file revealed that no action had been conducted in
regard to this Department's letter of April 14, 1992. Attempts to speak with someone at the
facility have been unsuccessful.
An option to excavate the contaminated soil and aerate at the site was requested by Odis
Dykes, Inc., on April 7, 1992, and was approved by this Department. It is necessary that
mitigation of the gasoline hydrocarbon contamination at this site be conducted without
further delay.
If a meeting to discuss this option or other concerns would be helpful, please contact this
office. The Department is willing to work with you in arriving at an acceptable solution of
this matter. It is essential that you contact this Department and advise of your intentions.
Sincerely,
Steve McCalley, Director
By: Michael Driggs, R~..,/I~I.S., R.E.A.
Hazardous Materials Specialist II
Hazardous Materials Program
MD:cas
~driggs~250024.1tr
.,
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I,, !" 1.0886 VINEIO_-II'IVO O'IE]I..-ISEI:~NVE]
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~,. "' J.N:ll/tlJ.~lyd~lO $=IOlAEIEI$ HJ.-IWlH 'IV/N~IWNOtlIAN~I
'ENVIRONMENTAL HEALTH SERVlCE II DEPARTMENT'
STEVE McCALLEY, R,E.H.S. , 2700 "M" Street, SuiTe 300
~,~~ (805) 861-3429 FAX
May 17, 1993
Vickie Breaw
Odis Dykes, Inc.
P. O. Box 6157
Bakersfield, CA 93386
SUBJECT: Location: 313 Daniels Lane
Bakersfield, CA 93307
Known As: Odis Dykes, Inc.
PERMIT #: 250024
Dear Ms. Breaw:
This letter is an official notice to inform you that, as the responsible party for the property
described above, your agreement with the Kern County Environmental Health Services
Department is about to expire, in accordance with Section d.2. of that agreement, which
states:
"Fourteen (14) hours of billable time has been reached. This will give notice
that the available funds will be exhausted after six (6) additional hours of
billable time at which time the agreement will expire. A statement estimating
the amount time necessary to complete any remaining oversight work will be
sent. The responsible party will then have another opportunity to renew their
agreement with the County.
"Failure to enter into another agreement shall require Kern County
Environmental Health to utilize the State Water Resources Control Board
Pilot Project for which the responsible party may be billed by the State
directly for the cost of County services as well as State costs."
You are hereby notified that your trust account is overdrawn by $ 38.00. Remaining
oversight will require an estimated 12 hours to complete. We are, therefore, extending this
opportunity to renew your agreement with Kern County Environmental Health Services
Department or to utilize the State Water Resources Control Board Pilot Project for
completion of the required oversight activities.
Vickie Breaw
Subject: Odis Dykes, Inc.
May 17, 1993
Page 2
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 cost incurred by Kern County Environmental Health Services Department for the
oversight of the work for the site characterization, feasibility study, remediation action plan,
site remediation, and ongoing monitoring is not covered by any fees or permits.
These costs are recovered by Kern County Environmental Health Services Department in
one of the two methods described below. It is your responsibility to select the method of
overSight cost recovery under the terms of (A) State contract or (B) County of Kern Local
Agreement Option. These options pertain only to costs associated with oversight.
(A) STATE CONTRACT
The State Leaking Underground Storage Tank Local Oversight Program provides a
mechanism for the State to reimburse the .County for County oversight. The County will
conduct the necessary oversight and bill the State Water Resources Control Board under this
State contract. The State will then charge you, a responsible party, for the costs incurred
by both the County and the State, pertaining to your site, under the State terms explained
below:
Whereas the federal Petroleum Leaking Underground Storage Tank Trust Fund provides
~ funding to pay the local and state agency administrative and oversight costs associated with
the cleanup of releases from underground storage tanks; and Whereas the Legislature has
authorized funds to pay the local and state agency administrative and oversight costs
associated with the cleanup of releases from underground storage tanks; and Whereas the
direct and indirect costs of site investigation or remedial action at the above site are funded,
in whole or in part, from the federal Trust Fund; and Whereas the above individual(s) or
entity(ies) have been identified as the party or parties responsible for investigation and
cleanup of the above site; YOU ARE HEREBY NOTIFIED that pursuant to Title 42 of the
United States Code, Section 699Ih(h)(6) and Section 25360 of the Health and Safety Code,
the above Responsible Party or Parties shall reimburse the State Water Resources Control
Board not more than 150 percent of the total amount of site-specific oversight costs actually
incurred while overseeing the cleanup of the above 'underground storage tank site, and the
above Responsible Party or Parties shall make full payment of such costs within 30 days of
receipt of a detailed invoice from the State Water Resources Control Board.
(B) COUNTY OF KERN LOCAL AGREEMENT OPTION
Kern County Environmental Health Services Department is providing this option for those
who prefer to pay the County directly and avoid the addition of State costs. Prior to the
County's performance of services, this option requires your deposit of $1,000.00 (one
thousand dollars) with the County to be held in the Local Option Trust Account. Charges
Vickie Breaw
Subject: Odis Dykes, Inc.
May 17, 1993
Page 3
for County oversight are made against this account. In this option, a responsible party must
enter into a County agreement, Attachment "B".
The environmental sensitivity (Attachment "C") of this site has been reviewed by
Environmental Health Services Department to determine the potential threat for
groundwater contamination. Only sites determined to be non-environmentally Sensitive may
enroll in the Local Option Agreement. The site described above is not in an
environmentally sensitive area and may be enrolled in the Local Agreement Option;
however, the County of Kern reserves the right to cancel any Local Agreement Option,
should it be discovered that groundwater contamination or a unique, complex
hydrogeological condition exists. In such cases, Environmental Health Services Department
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 Services Department of your choice:
either the State contract or the County's Local Agreement Option. If you select the
County's Local Agreement, please complete and sign the Local Agreement (Attachment B)
and return it with your check for $1,000.00 (one thousand dollars) made payable to the
County of Kern, addressed to Kern County Environmental Health Services Department,
2700 M Street, Suite 300, Bakersfield, CA 93301, Attention: AccoUnting - Local Agreement
Option. If you select the State contract, please indicate, in writing, that you have made this
selection and that you have read the above official notification.
Failure to respond within ten (10) calendar days to this notice will automatically result in
oversight cost recovery for your site(s) to be placed under the terms of the State contract
for Leaking Underground Storage Tanks.
If you should have any questions regarding this matter, please contact Susan Gonzales at
(805) 861-3636, Extension 510.
'~ '~vl h~cCalley, Direc_tor :
Environmental Health Serv/ces D~par~ment
SMc:BS:cas
Attachments
\c01t~50024
Attachment
KERN COUNTY LOCAL AGREEMENT OPTION
BETWEEN
KERN COUNTY ENVIRONMENTAL HEALTH SERVICES DEPARTMENT
(Kern County Underground Storage Tank Permitting Authority)
AND
VICKIE BREAW
Responsible Party for Underground Storage Tank
for: ODIS DYKES, INC.
Permit #250024
This facility has experienced an unauthorized release of hazardous substances from an underground storage
tank. Action is necessary to protect the public health and the environment of the County, pursuant to Chapter
6.7 of the California Health and Safety Code and Chapter 8.48 of the Kern County Ordinance Code.
THE WITNESS FOR THE COUNTY AND SIGNATURE(S) FORA RESPONSIBLE PARTY OF THE
SUBJECT FACILITY DESCRIBED ABOVE DO HEREBY AGREE THAT:
Kern County Environmental Health Services Department shall act as the lead agency for regulatory oversight
for the:
a) Site characterization: the study of a site, including sampling of subsurface soil and water
where contamination is found in order to fully assess its extent and threat to the environment.
It shall include a discussion of the relative risk to biological receptors and possible pathways
of exposure. It may include removal or in-place closure of the tank, disposal or on-site
treatment of contaminated backfill or adjacent soil, removal of hazardous substances floating
on groundwater, and the drilling of groundwater monitor wells.
b) Feasibility study: the identification and evaluation of feasible alternatives for cleaning up the
site and remedying threats to public health and safety.
c) Remedial action plan: the most cost-effective, appropriate plan to lessen, alleviate, abate,
correct or clean-up the effects that a release of hazardous substances may have on the
environment, based on the feasibility study.
d) Remediation: the action chosen by the responsible party and approved by Kern County
Environmental Health Services Department for the mitigation and clean-up of contamination
resulting from an unauthorized release of hazardous materials and any ongoing monitoring
of the site.
The responsible party shall do the following:
a. Conduct all work as directed by Kern County Environmental Health Services Department
pursuant to State and local law and in conformance with appropriate regulations to assess
and remediate the contaminated site.
b. Deposit with the Kern County Environmental Health Leaking Underground Storage Tank
Local Option Trust Fund the'sum of $1,000.00. The Department's oversight activities will
be charged against this account at the rate prescribed by Kern County Ordinance Code
Chapter 8.04 ($80.00 per hour). Monthly statements will be prepared detailing the activities
and services provided and the remaining credit balance.
Kern County Environmental Health Services Department shall provide the following services:
a. Oversight of all activities to characterize the site's threat to the environment and/or the
groundwater, and coordination with the appropriate State, County and local regulatory
agencies.
b. Serve as the single contact point for the responsible party's representatives and other
regulatory agencies for the activities described in "a" above. If during the Department's
review of the site characterization/remedial action plan, it is determined that a permit may
be required by another agency, the responsible party shall be referred to that permitting
agency.
c. Review reports, conduct inspections, and oversee monitoring until the site poses no further
environmental or public health threat. An official certification letter shall be given to the
responsible party when the site is determined to no longer pose a significant threat to the
environment.
d. The responsible party will be officially notified by Kern County Environmental Health
Services Department when:
1. Necessary oversight is completed. A final statement will be provided to the
responsible party. If there remains an unexpended balance of the deposit made by
the responsible party in the Leaking Underground Storage Tank Trust Fund, a
refund for the unexpended balance will be issued;
- or -
2. Fourteen (14) hours of billable time has been reached. This will give notice that the
available funds will be exhausted after six (6) additional hours of billable time, at
which time the agreement will expire. A statement estimating the amount of time
necessary to complete any remaining oversight work will be sent. The responsible
party will then have another opportunity to renew his agreement with the County.
3. Failure to enter into another agreement shall require Kern County Environmental
Health Services Department to utilize the State Water Resources Control Board
· Local Oversight Program for which the responsible party may be billed by the State
directly for the cost of County services as well as State costs.
Kern County Environmental Health Services Department reserves the right to cancel this agreement at any
time for any reasons, including groundwater contamination or a uniquely complex hydrogeological condition.
If an unexpended balance remains on deposit from the responsible party under the terms of this agreement,
a refund for the unexpended balance will be issued and the agreement terminated. Once the agreement is
cancelled, you, as a responsible party, will be enrolled in the State Leaking Underground Storage Tank Local
Oversight Program.
This agreement may be cancelled any time by either party by certified registered return receipt letter to the
other party within five days of said notification.
I, (responsible party), have read and agree to the conditions of this
agreement for the contaminated site described as:
Site Name
Site Address
City Zip
Owner
Owner's Address
Citv Zip
Telephone
Operator
Telephone
Billing Address Attn:
Permit #
In order for this agreement to be executed, it must be signed and accompanied by the deposit of one-thousand
dollars ($1000.00).
Responsible Party:
Date:
For the County of Kern:
Date:
Attachment "C",
KERN COUNTY ENVIRONMENTAL ~ALTH
EXPLANATION OF ENVIRONMENTAL SENSITIVITY
I. Extremely Environmentally Sensitive - Highest historic groundwater is within 50 feet
of ground surface.
II. Environmentally Sensitive - (any of the following)
A. Highest historic groundwater is within 50-100 feet of ground surface, or
B. Nearest surface water in unlined conveyance is within 75 feet of tanks(s), or
C. Nearest agricultural or domestic water well is within 75 feet of tank(s), or
D. Facility is located in a designated aquifer recharge area, or
E. Permitting Authority determines possible adverse environmental impact due to
facility proximity to unique wildlife habitat areas.
III. Non-Environmentally Sensitive - Highest historic groundwater is greater than 100 feet
from ground surface.
items I sndlor 2 for~dd~'onal ~ewices. ' , a,so w~s,, to receive the
BAKERSF~LD, CA 93~6 ~ [ ~ ~press Mail ~ Return Receipt for
............ ~ I Merchandise
Signa~re ~dd~e~ee ,
~e8} / ~ ~ 8. Addre~ee s Addreas (Only if requested
. ' ." [ and f~ is paid)
~1 1, Decem~r 1991 , u~.~.P.O.: ~;~ DOMESTIC R~URN RECEI~
q3O E35 7&O Receipt for
nco Coverage provided
No_ I.n.s.u~a;e for international Mai~
VICKIE BREAN
ODIS DYKES, ING.
~AKERSFIELD, CA 93386
EnvironmentaJ Health Set, v~ces Department
~DA~ L. ABBO~ ST~ McC~ ~ .Y, R~, D~CTOR
DIRECTOR ~i~ Po~t~n Con~ D~
DASD PRICE !!! ~ J. RODDY, ~O
A~T~ DI~CTOR ~i~ & ~e~p~t ~ ~
~ J~, ~CP, D~OR
ENVIRONMENTAL HEALTH SERVICES DEPARTMENT
April 14, 1992
Vickie Breaw
Odis Dykes, Inc.
P.O. Box 6157 ·
Bakersfield, CA 93386
RE: Site Remediation
313 Daniels Lane, Bakersfield, CA
Permit #: 250024
Dear Ms. Breaw:
Your request to perform the removal of petroleum hydrocarbon soil utilizing Odis
Dykes" equipment at the above-referenced facility is acceptable to this Department. A
workplan and Health and Safety plan must be submitted for review. The workplan must
discuss, but is not limited to, questions such as: What will be used for the backfill; clean soil,
or will the contaminated soil be reused after aeration? If the aerated soil is to be later used,
what safety measures will be followed around the excavation while the contaminated soil is
aerating? ·
Enclosed is a copy of Kern County Environmental Health Services Department's
policy on aeration of petroleum contaminated soil as requested in your letter of
April 7, 1992. Marked in yellow are important items that need to be closely followed.
It is recommended that you obtain an environmental contractor to submit a workplan
and be available to witness the excavation. They would also take samples from sides and
floor of excavation, and sample and monitor the aeration process. This would assure the
proper removal of most of the contaminated soil and necessary sampling of the stockpile for
aeration. The contractor would also be expected to submit a final report for this site with
a request to'this office for a closure letter.
If there are any further questions, please do not hesitate to call me at (805) 861-3636,
Extension. 566.
I ~.incerely, fl~ .
1Wi'chael Driggs, R?Eg.A.
Hazardous Materials Specialist II
Hazardous Materials Management Program
MD:ch
cc: File
driggs\breaw3.1et
2700 "M" STREET, SUITE 300 BAKERSFIELD, CALIFORNIA 93301 (805) 861-3636
FAX: (805) 861-3429
. P.O. Box 6157
· Bakersfield, CA 93386
Phone (805) 322-3039
FAX (805) 322-5132
~ Contractors Lic. #528384
· !~ ,. ,,. FEIN 95-2999667
Earthmoving · Grading · Trucking .
April 7, 1992
Environmental Health Services Department
2700 M St Suite 300
Bakersfield, Ca. 93301
Attn: Mr. Michael Driggs
Dear Mr. Driggs,
I received your letter da'ted April 2, 1992. After discussing our
· I options with my father, we have decided to go with #2, excavation
O~-~nd on-site aeration of the contaminated material.
We would l±ke t:o perform the excavat±on ourselves w±th your perm±ss±on.
Could I obta±n a copy of t:he Kern Gounty Env±ronment:al Health Serv±ces
Depart:ment's Aerat:±on Pol±cy on aerat±on? Is t:h±s someth±ng that: should
be superv±sed by your department~ Do we get the so±is tes~:s? Hopefully
your Pol±cy w±ll outl±ne these q~st±ons for me.
R±ght: now, all of our equ±pment ±s work±ng, but we are look±ng at a
break at: t:he end of t:h±s month. We should be able to proceed at that
time.
Sincerely,
/ Vickie Breaw
· Complete itemsCl and/or 2 for additional services. I also wish to receive the
· Complete items 3. and 4a & b. following services (for an extra
· Print your name and address on the reverse of this form so that we can
return this card to you. fee):
· Attach this form to the front of the msilpiece, or on the beck if space 1. [] Addressee's Address
does not permit.
· Wdte "Return Receipt Requested" on the meilpiece below the article numbe~ 2. [] Restricted Delivery
· The Return Receipt Fee will provide you the signature of the person delivere¢
tO and the date of delivery. Consult postmaster for fee.
3. Article Addressed to: 4a. Article Number
· Vickie Breaw 4b. Service Type
Odis Dykes, Inc. [] Registered [] Insured
P.O. BOX 6157 '~ Certified [] COD
' Bakersfield, CA. [] Express Mail [] Return Receipt for
Merchandise
-_ 9338
7
5. SLq~re..(Addressee}_ 8. Addressee's Address (Only if requested
///~ ..~/~,~--- and fee ia paid)
6. Signature (Agent)
PS Form 381 1, November 1990 ,u.s. G,O.' ~,--2S?~ DOMES"rIO RETURN RECEIP?
:..' .': 'PEI~LTYFOR PRIVATE
· ' ~' .,'.'" '.**USE.'$300
Print your name, address and ZIP COde here
i~IRO~ITAL HEALTH DEP~ "
2700 '~" STR~.~.T, SUITE 300
BAZERS~e CA. 93301
· RESt..~CE MANAGEMENT A~
Environmental Health Setvice~ Department
RANDALL L. ABBOTT STL~E McCA~ i I=y, REHS, DIRECTOR
DIRECTOR ~r Pollution Control District
DAVID PRICE Iii VaU.LO! J. RODDY, APCO
ASSISTANT DIRECTOR Planning & Devek~nent ,Setv~c~ Department
TEO J~d~ES, ~UCP, O~CTOR
ENVIRONMENTAL HEALTH SERVICES DEPARTMENT
APril 2, 1992
Vickie Breaw
Odis Dykes, Inc.
P.O. Box 6157
Bakersfield, CA 93386
SUBJECT: Location : 313 Daniels Lane, Bakersfield, CA
Known As: Odis Dykes, Inc.
Permit # : 250024
Dear Ms. Breaw:
This letter is to confirm our meeting on March 31, 1992, concerning the above-referenced
facility. During the meeting we 'discussed the following options to remediate the
hydrocarbon contamination that exists at this former underground tank site:
1. Evaluate the possibility of leaving significant levels of contamination in place by
performing a risk assessment.
2. Excavation of soils to a depth determined by equipment capabilities, and
subsequent on-site aeration of the material. Soil samples would need to be taken
fi.om the sides and floor of excavation, and analyzed to determine the levels of
petroleum hydrocarbons which remain. It would then be necessary to backfill
with clean, Iow-permeable fill material. The excavated soils would need to be
properly contained on site, and aerated as outlined in Kern County
Environmental Health Services Department's Aeration Policy on aeration.
As we discussed, it would be advisable to obtain multiple bids for either of the options
before selecting a qualified contractor, it is necessary that you select a remediation option
and advise this Department within 30 days of receipt of this letter as to your course of
action.
We will work with you in any way we can in arriving at an acceptable solution to this matter.
It is essential that you keep us informed of your intentions.
2700 "M" STREET, SUITE 300 BAKERSFIELD, CALIFORNIA 93301 (805) 861.3636
FAX: (805) 861-3429
Vickie Breaw
April 2, 1992
Page 2
If you have any further questions, please do not hesitate to call me at (805) 861-3636,
Extension 566.
Sincerely,
Michael Driggs, R.E.A.
Hazardous Materials Specialist II
Hazardous Materials Management Program
MD:ch
cc: File
driggs\breaw2.1et
Bakersfield, CA 93386
Phone (805) 322-3039
FAX (805)' 322-5132
Contractors Lic. //528384
FEIN 95-2999667
Earthrnoving · Grading · Trucking
March 25 1992'
iH \I
Environmental Health Services Department iU ~J'
2700 M St. ~
Bakersfield, Ca. 93301 ~ .~
Attn: Michael Driggs
Dear Mr. Driggs,
I have received your letter dated March 23, 1992, and apologize for any
delay in response. I have looked over my entire file on this project, and
cannot locate a letter dated January 16, 1992. However, our mailbox was stolen
in January causing a great deal of confusion for that month. I would like
to request you change your mailing address to: PO Box 6157 Bakersfield 93386,
to insure that we receive future correspondence.
In the Site Characterization Report from Kennedy/Jenks dated January 6, 1992,
on page 7 under Evaluation of Remedial Action Alternatives, we have opted
to install an Asphalt Cap on our yard. As you know, this is going to cost
a considerable sum of money. I have applied for the Petroleum Undergroun~
Storage Tank Clean Up Fund, but to date have not had a reply.
To date the cost is in excess of $14,000.00. Our company has not worked in
three months. We have recently signed contracts and are beginning new projects
starting March 23. I am anticipating an increase in my cash flow within the
next 45 to 60 days. We will be getting bids for the Asphalting within the
next 15 days.
If this letter is not sufficient response, please advise.
Sincerely,
Vickie Breaw
Office Manager
· Complete items 1 ana 'h' I also wish to receive the
· Comnlete items 3, an( ~' follov~:c'q services (for an extra
· Print your name and I~e~S:fO~L~he.'l~ *s ~lcan fee):
return this caro to you.
does not oermit.' A~acn this ,erin to t~ ~m~°f t~lp~,~ba,~~ [~e ~ 1. ~ Addressee's Address
· Wrffe"Return Receim d" he ~ 2. ~ Restricted Delivery
· The Return Receiot Fe~
to and the Sate of deliv~ ~stmaster for fee,
3.~ A~icle Addres~ ~t~
" j~:.. C ~ ~ ~ ' ~ Regi~er~ ~ Insured
~ Express Mail ~ Return Receipt for
Merchandise
5. Sig~ ~AOOressee)
8. ~ddre~'s Addres~ (Only if requested
~~~ and .fee is paid)
6. ~gnature (Agent~
PS Form 3811, November 1990 ~U.S. GPO:~--~S~ DOMESTIC RETURN RECEIPT
UNITED STATES POSTAL SE ~~
Official Business
PENALTY FOR PRIVATE
USE, $30O e
· '-'-'-:' Print your name, address and ZIP Code here
'"/ ~' · ·
q:::..
' O:'- .,-. :: ]~'~'i~OI~I~ITAL HEAL~ DEPARTI~I~
x,. U.,:~..T-- .:, ;.: v
.,~..-- :2700 '~tr' E,~RF.J~'[', SU['['~ :300
]~[.ER,.SFT~.n, CA. 9330].
RANDALL L. ABBOTT STEVE McCA~ ~ ~"Y, REHS, DIRECTOR
DIRECTOR ~r ~o~t~ co~u~ D~
DAVID PRICE I11 W~LLiAM ,l. RODDY, APCO
A$SISTANT DIRECTOR
Ptarmmg & I:)~elo~a~t ~ ~ .
TED JAMES, AJCP, DllI~"TOR
ENviFIONMENT^L HEALTH SERVICES DEPARTMENT
March 23, 1992
Vickie Breaw
Odis Dykes, Inc.
313 Daniels Lane
Bakersfield, CA 93307
SUBJECT: Location : 313 Daniels Lane, Bakersfield, CA
Known As: Odis Dykes, Inc.
Permit # : 250024
Dear Ms. Breaw:
Review of the above-referenced file reveals you have taken no action to select a
remediation option for the known contamination at your facility.
'The Department's letter of January 16, 1992, expressed the willingness to work with
you in arriving at an acceptable solution. It has been two months now and there has been
no indication' of your intentions.
It is our Department's position that enough time has been allowed for you to proceed
with action to resolve this matter. Therefore, a remediation workplan, prepared by a
qual/fied registered, geologist or civil engineer, must reach this office within ten (10) days of
receipt of this letter. Failure to comply with this order may initiate legal proceedings being
brought against you.
Sincerely,
Michael Driggs, R.E.A.
Hazardous Materials Specialist II
Hazardous Materials Management Program
MD:ch
cc: Mark J. Pishinsky, Kennedy/Jenks Consultants -
File
driggs\breaw.let
2700 "M" STREET, SUITE 300 BAKERSFIELD, CALIFORNIA 93301 (805) 861-36.36
FAX: (8OS) 861-3429
RESOURCE MANAGEMENT A ENCY
Environmental HeaJth Services Department
RANDALL L. ABBOTT STEVE McCALLEY, REH$, DIRECTOR
DIRECTOR Ai, Pollution Control District
DAVID PRICE Iii VaLLIAM J. RODD¥, APCO
ASSISTANT DIRECTOR Planning & Devetovment Services Department
TED JAMES, AiCP, DIRECTOR
ENVIRONMENTAL HEALTH SERVICES DEPARTMENT
January 16, 1992
Vickie Breaw
ODIS DYKES, INC.
313 Daniels Lane
Bakersfield, CA 93307
SUBJECT: Location: 313 Daniels Lane, Bakersfield
Known As: Odis Dykes, Inc.
Permit #: 250024
Dear M~.. Breaw:
The Department has reviewed the site characterization report
submitted by Kennedy/Jenks Consultants on behalf of the above-
mentioned facility. The options for excavation/aeration of
affected soils and in-situ extraction are both workable and
acceptable to this Department. The "No Action" option is not
workable based upon the State Water Resources Control Board's LUFT
(Leaking Underground Fuel Tank) Field Manual and is denied.
One of the exercises in the Manual was designed to estimate
the concentrations of Total Petroleum Hydrocarbons (TPH) and
Volatile Aromatic Hydrocarbons (BTXE) that can be left in-place
without threat to groundwater. Although groundwater may not
potentially be threatened, the TPH and BTXE concentrations
demonstrated at this site greatly exceed the levels which may cause
a threat to human health and other bioreceptors which may live
and/or work in the .area.
It must also be pointed out that allowing the known
contamination to remain in-place creates a hazardous condition
which must be disclosed prior to any possible sale or lease of the
property.
This office requests that one of the other available options
'be selected and submitted for review. A short addendum to the site
characterization report would be satisfactory. We will work with
you in any way we can at arriving at an acceptable solution to this
matter.
2700 "M" STREET, SUITE 300 BAKERSFIELD, CALIFORNIA 93301 (805) 861-3636
FAX: (805) 861.3429
PRINTED ON RECYCLED PAPER
Vickie Brean
Page Two
January 16, 1992
If you have any further questions or you feel a meeting would
be beneficial, please do not hesitate to call me at (805) 861-3636,
ext. 566.
~~~~~incere~' . ,
Hazardous Materials Specialist
Hazardous Materials Management Program
MD:jg
cc: Mark Pishinsky, Kennedy/Jenks Consultants
File
Environmental Health Ser,~ce~ Department
RANDALL L. ABBOTT STEVE McCAI ! Fy, REHS, DIRECTOR
DIRECTOR
Air Pollution Control District
DAVID PRICE 111 WILLIAM J. ROODY, APCO
ASSISTANT DIRECTOR
P~anning & Development Services Department
TED ,lAMES, AICP, DIRECTOR
ENVIRONMENTAL HEALTH SERVICES DEPARTMENT
October 15, 1991
Vickie Breaw
Odis Dykes, Inc.
313 Daniels Lane
Bakersfield, CA 93307
SUBJECT: Location : 313 Daniels Lane, Bakersfield, CA
Known As : Odis Dykes, Inc.
Permit # : 250024
Dear Ms. Breaw:
Our Department has reviewed the site characterization workplan submitted by
Kennedy/Jenks Consultants. The workplan addressing soil sampling constituents to be
'analyzed is acceptable, and health and safety considerations are also acceptable, for
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 comprehensive 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, extension 566.
. Sincerely.
Hazardous Materials Specialist
Hazardous Materials Management Program
MD:ch
cc: Kennedy/Jenks Consultants - Mark Pishinsky
driggs\breaw, ml4
2700 "M" STREET, SUITE 300 BAKERSFIELD, CALIFORNIA 93301 (805) 861-3636
Kennedy/Jenks Consultants
Engineers and Scientists
200 New Stine Road, Suite 115
Bakersfield, California 93309
805-835-9785
FAX 805-831-5196
9 October 1991
Mr. Michael Driggs
Hazardous Materials Specialists
Department of Environmental Health Services
County of Kern, Resource Management Agency
2700 M Street, Suite 300
Bakersfield, California 93301
Subject: Odis Dykes, Inc.
Daniels Lane Facility
Revised Site Characterization Work Plan
K/J 912319.00
Dear Mr. Burger:
Enclosed herewith as Attachment A, are two copies of the revised Site Characterization
Work Plan for the Odis Dykes, Inc~, DanielS Lane Facility in Bakersfield, California. This
revised Work Plan has been prepared in response to additional information requested by
the Kern County Resource Management Agency, Department of Environmental Health
Services in its letter dated 2 October 1991. This revised Work Plan has been prepared in
accordance with guidelines set forth by the County in its Site Characterization and Site
Remediation Handbook #UT-35.
Please review the enclosed revised Work Plan. We are ready to proceed with the field
work upon receipt of your approval. Please call Mr. Richard Casias or me if you have any
questions.
Very truly yours,
KENNEDY/JENKS CONSULTANTS
Mark J. Pishinsky, R.E.A.
Project Manager
cc: Ms. Vickie Breaw
Kennedy/Jenks Consultants
ATTACHMENT A
ODIS DYKES, INCORPORATED
REVISED SITE CHARACTERIZATION WORK PLAN
FOR THE DANIELS LANE FACILITY
K/J 912319.00
INTRODUCTION
Odis Dykes, Inc. formerly operated a fuel dispensing facility at its 313 Daniels Lane
location in Bakersfield, California. The fuel dispensing facility consisted of one
8,000 gallon aboveground diesel fuel tank and one 4,000 gallon aboveground
gasoline tank that were connected to separate dispensers on a common fuel
dispensing island. (See Figure 1). There was also one 2,500 gallon underground
~!~!i!.i~ii storage tank that reportedly had not been used since 1988.
On .......... 14 June 1991, Odis Dykes, Inc. removed the 2,500 gallon underground
~!i storage tank and associated piping.
FINDINGS OF PREVIOUS INVESTIGATION
During the underground tank removal by Odis Dykes, Inc., soil samples were
collected by B.C. Laboratories, Inc. beneath the former underground tank and the
dispensers. Soil samples were reportedly collected at depths of two feet and four
below each end of the former underground storage tank and at depths of two feet
and six feet below each of the dispensers. Petroleum hydrocarbons were not
detected in any of the soil samples collected below the former underground storage
tank, however, elevated concentrations of petroleum hydrocarbons were detected
in soil samPles collected below each of the two dispensers at depths of two feet
(#1148AK) 1 912319.00
Kennedy/Jenks Consultants
The .County, in its letter dated 23 July 1991, notified Odis Dykes, Inc. that the
County had determined that an unauthorized release of hazardous materials had
occurred at the site. Odis Dykes, Inc. was identified as the responsible party in the
County's letter and therefore was required to develop a Site Characterization,
Feasibility Study and Remedial Action Plan for the site. Odis Dykes, Inc.
subsequently chose the County of Kern Local Agreement Option for oversight cost
recovery and deposited $1,000.00 in the County of Kern Local Option Trust
Account.
PROPOSED SCOPE OF WORK
A phased approach to the site characterization and subsequent remediation of the
site is proposed. The site characterization phase will assess the vertical and lateral
extent of the chemicals of interest in the soils in the area of the former fuel
'dispensers and associated piping. On the basis of the results of the site
characterization, alternative site remediation measures will be identified and
evaluated, and a recommended remediation alternative selected. Upon approval of
a plan for implementation of the selected remedial alternative by the County, the
recommended site remediation will be performed by Odis Dykes, Inc.
Task 1 - Work Plan Development
This Work Plan has been prepared in accordance with guidelines set forth by the
County in its Site Characterization and Site Remediation Handbook #UT-35. The
Work Plan is based on the information provided to Kennedy/Jenks Consultants by
Odis Dykes, Inc. and review of the findings of the previous site investigation
described above.
Task 2 - Pre-field Investigation
Prior to initiating the field investigation, a review of potential underground utilities
and structures in the investigation area will be conducted by Odis Dykes, Inc.'s
designated facility manager. The drilling contractor will coordinate site access with
the designated facility manager to minimize potential impacts to current operations.
Required drilling permits will be secured by Odis Dykes, Inc. during coordination
drilling Finally, a Health and Safety Plan for the protection
with
the
subcontractor.
and safe conduct of Kennedy/Jenks Consultants' personnel while they are working
at the site will be developed. The Drilling Contractor shall have all necessary
licenses and training prior to performing the field investigation.
Task 3 - Field Investiqation
On the basis of the findings from the preliminary site assessment, a minimum of
three soil borings are proposed for the site characterization. Borings are in the fuel
dispensing island area as shown on Figure 2. Proposed boring locations may be
relocated in the field based on conditions encountered during drilling operations. All
borings will be drilled using an eight inch outside diameter hollow stem auger.
(~114BAK) 2 912319.00
Kennedy/Jenks Consultants
Undisturbed soil samples will be obtained at five-foot intervals beginning at the
surface and continuing to a depth of approximately 20 feet or first-encountered free
water, whichever is shallower.
All borings will be drilled to the proposed depths unless organic vapors significantly
above "background" values are detected by headspace analysis from the bottom
sample of the boring. If this occurs, drilling will continue until organic vapor
concentrations-attenuate sufficiently to indicate that the vertical extent of
contamination has most likely been evaluated.
Field headspace analyses of soil samples for organic vaporswill be conducted by
placing soil from selected sample liners in re-closeable plastic bags and sealing them
alosed. The selected soil samples will be desegregated and placed in a warm
location for approximately ten minutes following sample collection. An organic
vapor analyzer will be used to measure the organic vapor content in the headspace
of selected samples by carefully inserting the organic vapor analyzer probe into the
bag. The magnitude and distribution of these organic vapor readings will be used to
help select soil samples for laboratory analyses. All monitoring data will be recorded
and included on drilling logs.
Additional boring may be installed if the lateral and vertical extent of elevated
concentrations of gasoline constituents are not adequately defined by analysis of
soil samples from borings B1, B2, and B3.
In addition to headspace analyses of soil samples collected, field personnel will
perform air monitoring twice daily with a direct reading organic vapor analyzer
(OVA, OVM or HNU) in the breathing zone at each work location. All readings will
be recorded in field logs. All direct reading instruments will be calibrated according
to the manufacturer's specifications.
If OVA readings obtained during air monitoring for a particular work area
consistently exceed 5 parts per million (ppm) above background, then sampling will
cease and personnel will withdraw from the work area. If concentrations persist
above 5 ppm, Level C protection will be required if work is to continue. If OVA
readings exceed 10 ppm in the breathing zone while workers are in Level C
protection, then work will cease and the source of the emission will be identified
and controlled before work continues.
(//114BAK) 3 912319.00
Kennedy/Jenks Consultants
Field personnel will wear equipment to protect against potential physical and
chemical hazards. Level D protection will be required at a minimum for field
activities at the site. Level D personal protective equipment to be used will include:
· ANSI approved hard hat
· Chemical resistant gloves
· Work' clothes or Tyvek
· ANSI approved safety glasses (for drilling activities)
All borings will be logged and sampled by a Kennedy/Jenks Consultants geologist.
The soil samples will be collected in pre-cleaned brass liners using a clean split-
spoon drive sampler. Upon collection, each sample liner will be sealed on both ends
with Teflon sheeting and plastic caps. The samples will be labeled and kept chilled
during transport by Odis Dykes, Inc. to a laboratory certified by the state of
California for analysis. A chain-of-custody form will be completed and will
accompany the soil samples. The soil sampler, soil sample liners and. augers will be
steam cleaned prior to their initial use and between borings. The sampler will also
be washed between each subsequent use to reduce the likelihood of cross
contamination of samples.
analyzed for Total Petroleum Hydrocarbons by Modified EPA Method 8015 utilizing
gas chromatography with flame ionization detection. Benzene, toluene and xylene
will be analyzed by EPA Method 8020 for aromatic volatile organics utilizing gas
chromatography.
Completed soil borings will be abandoned in accordance with local regulatory
guidance. Auger flights will be progressively removed and cement/bentonite grout
will be tremied or poured through the augers. Each boring will be sealed from total
depth and finished to surface grade.
Drill cuttings will be collected and placed in labeled drums and left onsite until
laboratory analyses are completed and a proper disposal method can be evaluated.
Kennedy/Jenks Consultants will be available to assist Odis Dykes, Inc. to aid in
evaluating the appropriate disposal methods for the drill cuttings.
Task 4 - Site Characterization Report/Feasibility Study/Remedial Action Plan
Upon completion of Tasks 1 through 3, a Site Characterization Report will be
prepared summarizing the results of the field and laboratory investigations. The
report will include a site map showing the location of soil borings, a description of
soil lithologies and approximate distribution of any hydrocarbons detected in the soil
(//114BAK) 4 912319.00
Kennedy/Jenks Consultants
samples analyzed. The report will also indicate sample collection procedures,
analytical results and the analytical methodology used.
include soil vapor extraction and treatment, excavation and bioremediation, or
capping and post-closure monitoring.
The Feasibility Study will consider the technical feasibility, cost effectiveness, and
short and long term effects to public health and the environment, including potential
contaminant migration routes for each alternative.
A Remedial Action Plan, if warranted, will be developed based on the findings of the
Feasibility Study. A detailed scope of work for site'remediation will be prepared as
part of the Remedial Action Plan.
PROJECT SCHEDULE
Selected elements of the Pre-field Investigation Task have already been initiated.
Site characterization field activities will be initiated within two weeks of written
approval of the Work Plan by the County, subject to contractor availability. The
Site Characterization Report/Feasibility Study/Remedial Action Plan will be prepared
and submitted to the County within three weeks of receipt of analytical results.
(#1148AK) 5 912319.00
LEGEND
,/~,,,~ Fre~w~
Kennedy/Jenks Consultonts
Odis Dykes, Inc.
Bakersfield, Colifornio
Location Map
K/J 912319.00
September, 1991
Figure I
Danie s Lane
× 'lV Ix × ~
Main gate
N
Fuel dispensing island Gasoline dispenser
~--~~~ :~ lI -- Property
Former undergound 'line
fuel piping ""~/'
diesel
e
r-'f dispenser
Former 2,500 gallon
underground diesel
fuel storage tank Underground ---4-,
gasoline piping
Undergound
diesel fuel piping
8,000 above-
gallon
~ gr°und diesel fuelT-
~ tank
Aboveground 4,000 lion ab v
waste oil tank ground gasoline tank
Kennedy/Jenks Consultants
Odis Dykes, Inc.
Bakersfield, California
Site .Plan
0 40 80 120
1"=40' '~ K/J 912519.00.
Approximate scale September, 1991
Figure 2
Underground
gosoline dispenser ~ ~ Gosoline piping
Fuel dispensing island
Diesel fuel dispenser / Underground
////z' Diesel piping
/ X Former underground
./,// diesel fuel piping
/
/
I Former 2,500 gallon I
underground diesel Kennedy/Jenks Consultants
I fuel storage tank I
Odis Dykes, Inc.
I , Bakersfield, California
Proposed Soil
_~ Boring Locations
-Proposed Soil Boring Location K/J 912519.00
September, 1991
0 5 10 15
t"=5' Figure 3
Emdronmemal Health Setvk:e~ Department
RANDALL L. ABBO~ s~ ~cC,~
DIRECTOR Air Pollut~n Con~l
OA~O PRICE iil ~
A~T~ DI~CTOR
~ a~, ~CP, D~CTOR
ENVIRONMENT~ H~L~ SER~CES D~~ENT
October 2, 1991
Mark J. Pishinsky
Kennedy/Jenks Consultants
200 New Stine Road, Suite 115
Bakersfield, CA 93309
SUBJECT: Location: 313'Daniels Lane, Bakersfield, CA
Known As: Odis Dykes, Inc.
Permit #: 250024
Dear Mr. Pishinsky:
The Site-Characterization Work Plan dated September 27, 1991, and submitted on behalf
of the above-referenced facility has been reviewed.
Our Department would like to comment on the tbllowing items:
1. The work plan per Handbook #UT-35 lacks the following:
Information on local topography, geology, nearby waterways, and depth to
groundwater.
Area map showing site location relative to highways, urban or industrial areas,
etc.
Analytical results of the preliminary site assessment. The statement, "elevated
concentrations of petroleum hydrocarbons were detected..." (work plan - page
1) does not satisfy this requirement.
2. All borings will be advanced to a depth of 10 feet beyond the last contamination as
indicated by field methods.
3. All samples taken from the vertical boring (nearest center of plume) will be analyzed.
2700 "M" STREET, SUITE 300 BAKERSFIELD, CALIFORNIA 93301 (805) 861-3636
FAX: (805) 861-3429
Mr. Mark J. Pishinsky
October 2, 1991
Page 2
4. A discussion on procedures that will be followed if groundwater is encountered needs
to be iiicluded with the work plan. Should a water monitoring well become
necessary, it will be installed in accordance with Kern County Handbook UT-50.
Operations will be suspended and permits obtained from the Kern County
Department of Environmental Health Services before construction of the well begins.
5. Per Kern County Handbook UT-35, the Site Characterization Work Plan will contain
three (3)' remedial options, which will include a no-action option.
6. All Kern County file data refers to the removed underground storage tank as a diesel
tank. The Site Characterization Work Plan refers to the tank as containing gasoline.
If this is an error of the Department, please so advise otherwise this needs to be
corrected within the text and on figure 2.
Please submit a revised work plan or addendum addressing all of the above-mentioned
concerns. Once this has been received by this Department the review can be completed.
If there are any additional questions, please feel free to call me at (805) 861-3636,
extension 566.
Si.ncerely, ~ .
Hazardous Materials Specialist
Hazardous Materials Management Program
MD:cas
\250024.1tr
Kennedy/Jenks Consultants
Engineers and Scientists
200 New Stine Road, Suite 115
Bakersfield, California 93309
805-835-9785
27 'September 1991 FAX 805-831-5196
Mr. Chris Burger
Program Manager, Hazardous Materials
Department of Environmental Health Services
County of Kern, Resource Management Agency
2700 M Street, Suite 300
Bakersfield, California 93301
Subject: Odis Dykes, Inc.
Daniels Lane Facility
Site Characterization Work Plan
K/J 912319.00
Dear Mr. BUrger:
Enclosed herewith as Attachment A, are two copies of the Site Characterization Work Plan
for the Odis Dykes, Inc., Daniels Lane Facility in Bakersfield, California. This Work Plan
has been prepared in response to requirements set forth by the Kern County Resource
Management Agency, Department of Environmental Health Services in its letters dated 23
July and 29 August 1991. This Work Plan has been prepared in accordance with
guidelines set forth by the CoUnty in its Site Characterization and Site Remediation
Handbook #UT-35.
Please review the enclosed Work Plan. We are ready to proceed with the field work upon
receipt of your approval. Please call Mr. Richard Casias or me if you have any questions.
Very truly yours,
KENNEDY/JENKS CONSULTANTS
Mark J. Pishinsky, R.E.A.
Project Manager
MJ P/r w(#~ r.~,^,~
CC: MS. Vickie Breaw
Kennedy/Jenks Consultants
ATTACHMENT A
ODIS DYKES, INCORPORATED
SITE CHARACTERIZATION WORK PLAN
FOR THE DANIELS LANE FACILITY
K/J 912319.00
INTRODUCTION
Odis Dykes, Inc. formerly operated a fuel dispensing facility at its 313 Daniels Lane
location in Bakersfield, California. The fuel dispensing facility consisted of one
8,000 gallon aboveground diesel fuel tank and one 4,000 gallon aboveground
gasoline tank that were connected to separate dispensers on a common fuel
di__s.oen_siP, g island. (See Figure 1). There was also one 2,500 gallon underground
"~---~('gasoline.,~torage tank that reportedly had not been used since 1988.
On 14 June 1991, Odis Dykes, Inc. removed the 2,500 gallon underground gasoline
storage tank and associated piping.
FINDINGS OF PREVIOUS INVESTIGATION
During the underground tank removal by Odis Dykes, Inc., soil samples were
collected by B.C. Laboratories, Inc. beneath the former underground tank and the
dispensers. Soil samples were reportedly collected at depths of two feet and four/
below each end of the former underground storage tank and at depths of two feet
and six feet below each of the dispensers. Petroleum hydrocarbons ~p~:~t
de~tected in any of the soil samples collected baJ~ the former underground-storage
ta_.n.~nk, however, ele_v, ated concentrations of petroleum hydrocarbons were ~d
in soil samples collected below each of the two dispensers at depths of two feet
and six feet.
The County, in its letter dated 23 July 1991, notified Odis Dykes, Inc. that the
County had determined that an unauthorized release of hazardous materials had
occurred at the site. Odis Dykes, Inc. was identified as the responsible party in the
County's letter and therefore was required to develop a Site Characterization,
Feasibility Study and Remedial Action Plan for the site. Odis Dykes, Inc.
subsequently chose the County. of Kern Local Agreement Option for oversight cost
recovery and deposited $1,000.00 in the County of Kern Local Option Trust
Account.
PROPOSED SCOPE OF WORK
A phased approach to the site characterization and subsequent remediation of the
site is proposed. The site characterization phase will assess the vertical and lateral
(#114BAK) 1 912319.00
Kennedy/Jenks Consultants
extent of the chemicals of interest in the soils in the area of the former fuel
dispensers and associated piping. On the basis of the results of the site
characterization, alternative site remediation measures will be identified and
evaluated, and a recommended remediation alternative selected. Upon approval of
a plan for implementation of the selected remedial alternative by the County, the
recommended site remediation will be performed by Odis Dykes, Inc.
Task I -Work Plan Development
This Work Plan has been prepared in accordance with guidelines set forth by the
County in its Site Characterization and Site Remediation Handbook #UT-35. The
Work Plan is based on the information provided to Kennedy/Jenks Consultants by
Odis Dykes, Inc. and review of the findings of the previous site investigation
described above.
Task 2 - Pre-field Investi,qation
Prior to initiating the field investigation, a review of potential underground utilities
and structures in the investigation area will be conducted by Odis Dykes, Inc.'s
designated facility manager. The drilling contractor will coordinate site access with
the designated facility manager to minimize potential impacts to current operations.
Re~_q_¥ired drilling~ermits will be secured by Odis Dykes, Inc. during coordination
with the drilling subcontractor. Finally, a Health and Safety Plan for the protection
and safe conduct of Kennedy/Jenks Consultants' personnel while they are working
at the site will be developed. The Drilling Contractor shall have all necessary
licenses and training prior to performing the field investigation.
Task 3 - Field Investiqation
On the basis of the findings from the preliminary site assessment, a minimum of
three soil borings are proposed for the site characterization. Borings are in the fuel
dispensing island area as shown on Figure 2. Proposed boring locations may be
relocated in the field based On conditions encountered during drilling operations. All
borings will be drilled using an eight inch outside diameter hollow stem auger.
Undisturbed soil samples will be obtained at five-foot intervals beginning at the
surface and continuing to a depth of approximately 20 feet or first-encountered free
water, whichever is shallower.
All borings will be drilled to the proposed depths unless organic vapors significantly
above "background" values are detected by headspace analysis from the bottom
sample of .the boring. If this occurs, drilling will continue until organic vapor
concentrations attenuate sufficiently to indicate that the vertical extent of
contamination has most likely been evaluated. ,,- ,/. -' ,'\//'~
Field headspace analyses of soil Samples for organic vapors will be conducted by
placing soil from selected sample liners in re-closeable plastic bags and sealing them
closed. The selected soil samples will be disaggregated and placed in a warm
(# 114BAK) 2 912319.00
Kennedy/Jenks Consultants
location for approximately ten minutes following sample collection. An organic
vapor analyzer will ~be used to measure the organic vapor content in the headspace
of selected samples by carefully inserting the organic vapor analyzer probe into the
bag, The magnitude and distribution of these organic vapor readings will be used to
help select soil samples for laboratory analyses. All monitoring data will be recorded
and included on drilling logs,
Additional boring may be installed if the lateral and vertical extent of elevated
concentrations of gasoline constituents are not adequately defined by analysis of
soil samples from borings B1, B2, and B3.
In addition to headspace analyses of sOil samples collected, field personnel will
perform air monitoring twice daily with a direct reading organic vapor analyzer
(OVA, OVM or HNU) in the breathing zone at each work location. All readings will
be recorded in field logs. All direct reading instruments will be calibrated according
to the manufacturer's specifications.
If OVA readings obtained during air monitoring for a particular work area
consistently exceed 5 parts per million (ppm) above background, then sampling will
cease and personnel will withdraw from the work area. If concentrations persist
above 5 ppm, Level C protection will be required if work is to continue. If OVA
readings exceed 10 ppm in the breathing zone while workers are in Level C
protection, then work will cease and the source of the emission will be identified
and controlled before work continues.
Field personnel will wear equipment to protect against potential physical and
chemical hazards. Level D protection will be required at a minimum for field
activities at the site. Level D personal protective equipment to be used will include:
· ANSI approved hard hat
· Chemical resistant gloves
· Work clothes or Tyvek
· ANSI approved safety glasses (for drilling activities)
All borings will be logged and sampled by a Kennedy/Jenks Consultants geologist.
The soil samples will be collected in pre-cleaned brass liners using a clean split-
spoon drive sampler. Upon collection, each sample liner will be sealed on both ends
with Teflon sheeting and plastic caps. The samples will be labeled and kept chilled
during transport by Odis Dykes, Inc. to a laboratory certified by the state of
California for analysis. A chain-of-custody form will be completed and will
accompany the soil samples. The soil sampler, soil sample liners and augers will be
steam cleaned prior to their initial use and between borings. The sampler will also
be washed between each subsequent use to reduce the likelihood of cross
contamination of samples.
(#114BAK) 3 912319.00
.. ~.~';*~ ' Kennedy/Jenks ConsultantS
Soil sampleS selected for laboratory analyses will be identified by headspace
analysis and visual techniques. Soil samples will be analyzed for Total Petroleum
Hydrocarbons by Modified EPA Method 8015 utilizing gas chromatography with
flame ionization detection. Benzene, toluene and xylene will be analyzed by EPA
Method 8020 for aromatic volatile organics utilizing gas chromatography.
Completed soil borings will be abandoned in accordance with local regulatory
guidance. Auger flights will be progressively removed and cement/bentonite grout
will be tremied or poured through the augers. Each boring will be sealed from total
depth and finished to surface grade. *
Drill cuttings will be collected and plaCed in labeled drums and left onsite until
laboratory analyses are completed and a proper disposal method can be evaluated.
Kennedy/Jenks Consultants will be available to assist Odis Dykes, Inc. to aid in
evaluating the appropriate disposal methods for the drill cuttings.
Task 4 - Site Characterization Report/Feasibility Study/Remedial Action Plan
Upon completion of Tasks 1 through 3, a Site Characterization Report will be
prepared summarizing the results of the field and laboratory investigations. The
report will include a site map showing the location of soil borings, a description of
soil lithologies and approximate distribution of any hydrocarbons detected in the soil
samples analyzed. The report will also indicate sample collection procedures,
analytical results a~nd the analytical methodology used.
If warranted, '~--~' report will also include a brief Feasibility Study which will identify
and evaluate at least three remedial alternatives including a "no further action"
alternative. Possible alternative remedial actions which could be evaluated include
soil vapor extraction and treatment, excavation and bioremediation, or capping and
post-closure monitoring.
The Feasibility Study will consider the technical feasibility, cost effectiveness, and
short and long term effects to public health and the environment, including potential
contaminant migration routes for each alternative.
A Remedial Action Plan, if warranted, will be developed based on the findings of the
Feasibility Study. A detailed scope of work for site remediation will be prepared as
part of the Remedial Action Plan.
PROJECT SCHEDULE
Selected elements of the Pre-field Investigation Task have already been initiated.
Site characterization field activities will be initiated within two weeks of written
approval of the Work Plan by the County, subject to contractor availability. The
Site Characterization Report/Feasibility Study/Remedial Action Plan will be prepared
and s~.bmitted to the County within three weeks of receipt of analytical results.
(#114BAK) 4 912319.00 -
Danie s Lane
× I ,, IX
Main ga.te _~
.... Fuel dispensing island----~ Gasoline dispenser
> . ~ Property
Former undergound line
/ gasoline piping
e
r--f dispenser
Former 2,500 gallon
underground storage "
tank Underground
gasoline piping
Undergound --...
diesel piping
8,000 above-
gallon
~ gr°und diesel f~el-fzl
~ tank
Aboveground ,, // ~,000 lion
waste oil tank 9round gasoline tank
Kennedy/Jenks Consultants
Odis Dykes, Inc.
Bakersfield, California
Site Plan
0 40 8O 120
1"=40' K/J 912319.00
Approximate scale September, 1991
Figure I
Underground
Gasoline dispenser ~ ~ Gasoline piping
Fuel dispensing island
Diesel fuel dispenser ~ Underground
/z/. Diesel piping
? -- Former underground
,//' Gasoline piping
/'
/.
__ /
I Former 2,.500 gallon
underground storage rx/i/ennedyXJenks
I tank I Odis Dykes, Inc.C°nsultants
I , Bakersfield, Californiq
Proposed $oil
.~ Boring Locations
--Proposed Soil Boring Location K/J 912319.00
September, 1991
0 5 1'0 15
1"=5' Figure 2
Kennedy/Jenks Consultants
ATTACHMENT A
ODIS DYKES, INCORPORATED
SITE CHARACTERIZATION WORK PLAN
FOR THE DANIELS LANE FACILITY
K/J 912319.00
INTRODUCTION
Odis Dykes, Inc. formerly operated a fuel dispensing facility at its 313 Daniels Lane
location in Bakersfield, California. The fuel dispensing facility consisted of one
8,000 gallon aboveground diesel fuel tank and one 4,000 gallon aboveground
gasoline tank that were connected to separate dispensers on a common fuel
dispensing island. (See Figure 1). There was also one 2,500 gallon underground
gasoline storage tank that reportedly had not been used since 1988.
On 14 June 1991, Odis Dykes, Inc. removed the 2,500 gallon underground gasoline
storage tank and associated piping.
FINDINGS OF PREVIOUS INVESTIGATION
During the underground tank removal by Odis Dykes, Inc., soil samples were
collected by B.C. Laboratories, Inc. beneath the former underground tank and the
dispensers. Soil samples were reportedly collected at depths of two feet and four
below each end of the former underground storage tank and at depths of two feet
and six feet below each of the dispensers. Petroleum hydrocarbons were not
detected in any of the soil samples collected below the former underground storage
tank, however, elevated concentrations of petroleum hydrocarbons were detected
in soil samples collected below each of the two dispensers at depths of two feet
and six feet.
The County, in its letter dated 23 July 1991, notified Odis Dykes, Inc. that the
County had determined that an unauthorized release of hazardous materials had
occurred at the site. Odis Dykes, Inc. was identified as the responsible party in the
County's letter and therefore was required to develop a Site Characterization,
Feasibility Study and Remedial Action Plan for the site. Odis Dykes, Inc.
subsequently chose the County of Kern Local Agreement Option for oversight cost
recovery and deposited $1 ,OO0.00 in the County of Kern Local Option Trust
Account.
PROPOSED SCOPE OF WORK
A phased approach to the site characterization and subsequent remediation of the
site is proposed. The site characterization phase will assess the vertical and lateral
(#114BAK) 1 912319.00
Kennedy/Jenks Consultants
extent of the chemicals of interest in the soils in the area of the former fuel
dispensers and associated piping. On the basis of the results of the site
characterization, alternative site remediation measures will be identified and
evaluated, and a recommended remediation alternative selected. Upon approval of
a plan for implementation of the selected remedial alternative by the County, the
recommended site remediation will be performed by Odis Dykes, Inc.
Task 1 - Work Plan Development
This Work Plan has been prepared in accordance with guidelines set forth by the
· County in its Site Characterization and Site Remediation Handbook #UT-35. The
Work Plan is based on the information provided to Kennedy/Jenks Consultants by
Odis Dykes, Inc. and review of the findings of the previous site investigation
described above.~
Task 2 - Pre-field Investi.qation
Prior to initiating the field inVestigation, a review of potential underground utilities
and structures in the investigation area will be conducted by Odis Dykes/Inc.'s
designated facility manager. The drilling contractor will coordinate site access with
the designated facility manager to minimize potential impacts to current operations.
Required drilling permits will be secured by Odis Dykes, Inc. during coordination
with the drilling subcontractor. Finally, a Health and Safety Plan for the protection
and safe conduct of Kennedy/Jenks Consultants' personnel while they are working
at the site will be developed. The Drilling Contractor shall have all necessary
licenses and training prior to performing the field investigation.
Task 3 - Field Investi.qation
On the basis of the findings from the preliminary site assessment, a minimum of
three soil borings are proposed for the site characterization. Borings are in the fuel
dispensing island area as shown on Figure 2. Proposed boring locations may be
relocated in the field based on conditions encountered during drilling operations. All
borings will be drilled using an eight inch outside diameter hollow stem auger.
Undisturbed soil samples will be obtained at five-foot intervals beginning at the
surface and continuing to a depth of approximately 20 feet or first-encountered free
water, whichever is shallower.
All borings will be drilled to the proposed depths unless organic vapors significantly
above "background" values are detected by headspace analysis from the bottom
sample of the boring. If this occurs, drilling will continue until organic vapor
concentrations attenuate sufficiently to indicate that the vertical extent of
contamination has most likely been evaluated.
Field headspace analyses of soil samples for organic vapors will be conducted by
placing soil from selected sample liners in re-closeable plastic bags and sealing them
closed.' The selected soil samples will be disaggregated and placed in a warm
(#114BAK) 2 912319.00
Kennedy/Jenks Consultants
location for.approximately ten minutes, following sample collection.. An. organic
vapor analyzer will be used to measure the organic vapor content in the headspace
of selected samples by carefully inserting the organic vapor analyzer probe into the
bag. The magnitude and distribution of these organic vapor readings will be used to
help select soil samples for laboratory analyses. All monitoring data will be recorded
and included on drilling logs.
Additional boring may be installed if the lateral and vertical extent of elevated
concentrations of gasoline constituents are not adequately defined by analysis of
soil samples from borings B1, B2, and B3.
In addition to headspace analyses of soil samples collected, field personnel will
perform air monitoring twice daily with a direct reading organic vapor analyzer
(OVA, OVM or HNU) in the breathing zone at each work location. All readings will
be recorded in field logs. All direct reading instruments will be calibrated according
to the manufacturer's specifications.
If OVA readings obtained during air monitoring for a particular work area
consistently exceed 5 parts per million (ppm) above background, then sampling will
cease and personnel will withdraw from the work area. If concentrations persist
above 5 ppm, Level C protection will be required if work is to continue. If OVA
readings exceed 10 ppm in the breathing zone while workers are in Level C
protection, then work will cease and the source of the emission will be identified
and controlled before work continues.
Field personnel will wear equipment to protect against potential physical and
chemical hazards. Level D protection will be required at a minimum for field
activities at the site. Level D personal protective equipment to be used will include:
· ANSI approved hard hat
· Chemical resistant gloves
· Work clothes or Tyvek
· ANSI approved safety glasses (for drilling activities)
All borings will be logged and sampled by a Kennedy/Jenks Consultants geologist.
The soil samples will be collected in pre-cleaned brass liners using a clean split-
spoon drive Sampler. Upon collection, each sample liner will be sealed on both ends
with Teflon sheeting and plastic caps. The samples will be labeled and kept chilled
during transport by Odis Dykes, Inc. to a laboratory certified by the state of
California for analysis. A chain-of-custody form will be completed and will
accompany the soil samples. The soil sampler, soil sample liners and augers will be
steam cleaned prior to their initial use and between borings. The sampler will also
be washed between each subsequent use to reduce the likelihood of cross
contamination of samples.
(~114BAK 3 912319.00
Kennedy/Jenks Consultants
Soil samples selected for laboratory analyses will be identified by headspace
analysis and visual techniques. Soil samples will be analyzed for Total Petroleum
Hydrocarbons by Modified EPA Method 8015 utilizing gas chromatography with
flame ionization detection. Benzene, toluene and xylene will be analyzed by EPA
Method 8020 for aromatic volatile organics utilizing gas chromatography.
Completed soil borings will be abandoned in accordance with local regulatory
guidance. Auger flights will be progressively removed and cement/bentonite grout
will be tremied or poured through the augers. Each boring will be sealed from total
depth and finished to surface grade.
Drill cuttings will be collected and placed in labeled drums and left onsite until
laboratory analyses are completed and a proper disposal 'method can be evaluated.
Kennedy/Jenks Consultants will be available to assist Odis Dykes, Inc. to aid in
evaluating the appropriate disposal methods for the drill cuttings.
Task 4 - Site Characterization Report/Feasibility Study/Remedial Action Plan
Upon completion of Tasks 1 through 3, a Site Characterization Report will be
prepared summarizing the results of the field and laboratory investigations. The
report will include a site map showing the location of soil borings, a description of
soil lithologies and approximate distribution of any hydrocarbons detected in the soil
samples analyzed. The report will also indicate sample collection procedures,
analytical results and the analytiCal methodology used.
If warranted, the report will also include a brief Feasibility Study which will identify
and evaluate at least three remedial alternatives including a "no further action"
alternative. Possible alternative remedial actions which could be evaluated include
soil vapor eXtraction and treatment, excavation and bioremediation, or capping and
post-closure monitoring.
The Feasibility Study will consider the technical feasibility, cost effectiveness, and
short and long term effects to public health and the environment, including potential
contaminant migration routes for each alternative.
A Remedial Action Plan, if warranted, will be developed based on the findings of the
Feasibility Study. A detailed scope of work for site remediation will be prepared as
part of the Remedial Action Plan.
PROJECT SCHEDULE
Selected elements of the Pre-field Investigation Task have already been initiated.
Site characterization field activities will be initiated within two weeks of written
approval of the Work Plan by the County, subject to contractor availability. The
Site Characterization Report/Feasibility Study/Remedial Action Plan will be prepared
and submitted to the County within three weeks of receipt of analytical results.
(#114BAK) ~' 912319.00
Daniels Lane
x × x × "V ' ~
Main gate~
Fuel ..... dispensing island~_Gosoline dispenser
..... Property
Former undergound _ //~. .. line
gasolinep~p~ng' ' ~// Diesel fuel
dispenser
underground storage
tank Underground --
gasoline piping
Undergound --__
diesel piping
8,000 above-
gallon
~~tank gr°und diesel fuel/~T
X X X X X / X X NNI
/
Aboveground 4,000 gallon above-.--~
waste oil tank ground gasoline tank
Kennedy/Jenks Consultants
Odis Dykes, Inc.
Bakersfield, California
Site Plan
0 40 80 .120
1"=40' K/J 912319.00
Approximate scale September, 1991
Figure I
Underground
Gasoline dispenser ~ ~ Gasoline piping
Diesel fuel dispenser Underground
Diesel
piping
J~-- Former underground
Gasoline piping
r ~ ~
I[o~m~ ~,~00 ~o"on I
underground storage Kennedy/denks Consultants
I tank I
Odis Dykes, Inc.
I , Bakersfield, California
Propoeed 8oll
Boring Locatlone
-~-Proposed Soil Boring Location
K/J
912319.00
September, 1991
0 5 10 15
1,,=5~ Figure 2
.A CE MANA6EMENT
~ronment~ H~th ~ D~nment
~NDALL L. ABBO~ s~ McCA![EY, R~S, DIRECT°R
DIRECTOR a~, Pol~t~n Control D~tdm
DAVID PRICE !I! ~ J. RODDY, ~CO
A~T~T DI~CTOR ~nni~ & D~t ~es ~ent
~ J~, ~CP, DI~CTOR
ENVIRONMENTAL HEALTH SERVICES DEPARTMENT
August 29, 1991
Vickie Breaw
Odis Dykes, Inc.
313 Daniels Lane
Bakersfield, CA 93307
SUBJECT: Location: 313 Daniels Lan®, Bakersfield, .CA
Known As: Odis Dykes, Inc.
PERMIT #: 250024
Dear Ms. Breaw:
The intent of this letter is to inform you of the necessary deadlines for work required at
the property described above. As a responsible party for a leaking underground storage tank,
you have previously received a letter from this Department notifying you of the required work
necessary to identify the extent of the contamination. We are now requesting that this work,
outlined in UT-35, be done in a timely manner.'
In accordance with California Health and Safety. Code, Chapter 6.7, and Kern County
Ordinance Code, Chapter 8.48, the Kern County Environmental Health Services Department
requires a determination'of the threat to the environment. Accordingly, you must select an
environmental contractor and submit a site characterization workplan proposal to this office by
September 27, 1991. The workplan must be approved by this Department before any work is
started.
If you should have any questions regarding this matter, please contact me immediately
at (805) 861-3636, Ext. 566.
Sincerely,
· \ '
Hazardous Materials Specialist
Hazardous Materials Management Program
MD:cas
\250O24.121
2700 "M" STREET, SUITE 300 BAKERSFIELD, CALIFORNIA 93301 (805) 861-3636
FAX: (805) 86].-3429
SENDER:
· Complete itema 1 and/or 2 for
· Complete itama 3, and 4a & b. ! (for an ex~a
,, Print your nmmeend acldre~ on
return ~ card to you.
· Attach tttia fm'm to the front of the maitl~,
doea not permit,~
· Wr~a
· The Return ~ecei~ Fee wi# I
to and the date of
3., A~cle Ad4resaed to:
313 Daniei$ Lane
Bakersfield, CA 93307
5. Signature (Addressee)
6. Si
November 1990 RECEIPT
Official Business ~:~?._~'
PENALTY FOR PRIVATE
USE, $300
Print your name, address and ZIP Code here
[(e~-_q ~'~ount7 Environmental.
270o "H" S1:~e~:, S'n.i't:e 300
Baker:~ fieid. CA 93301
RE$~I~URCE MANAGEMENT A~'NCY
Environmental Health Sen~ces Department
RANDALL L. ABBOTT STEVE .McCA! ! ~'Y, REHS, DIRECTOR
DIRECTOR ~r PoU.t~ Co.~ t~st~ct
DAVID PRICE I!! VdLUAM J. RODDY, APCO
ASSISTANT DIRECTOR Planning & Development Setvice~ Department
'IT.D JAMES, AICP, DIRECTOR
ENVIRONMENTAL HEALTH SERVICES DEPARTMENT
JUly 23, 1991
Vickie
Odis Dykes, Inc.
313 Daniels Lane
Bakersfield, CA 93307
SUBJECT: Location: 313 Daniels Lane, Bakersfield, CA 93307
Known as: Odis Dykes, Inc.
PERMIT #: 250024
Dear Vickie:
This letter is an official notice to inform you that the property described above has been
de~ermined by Kern County Environmental Health Services Department to be the site of
an unauthorized release of hazardous materials from an underground storage tank. This
no:ice 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 actMties. California. Health and
Safety Code, Chapter 6.7, and Kern County Ordinance Code, ChaPter 8.48, require a
determination of the threat to the environment as a result of this release. THE
RESPONSIBLE PARTY SHALL, ON A TIMELY BASIS, DEVELOP A SITE
CHARACTERIZATION, FEASIBILITY STUDY AND REMEDIAL ACTION PLAN
FOR KERN COUNTY ENVIRONMENTAL HEALTH SERVICES DEPARTMENT'S
REVIEW AND APPROVAL BEFORE THE WORK IS INITIATED. 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 Services Department for the
oversight of the work for the site characterization, feasibility study, remediation action plan,
site remediation, and ongoing monitoring is not covered by any fees or permits. These costs
2700 "M" STREET, SUITE 300 BAKERSFIELD, CALIFORNIA 93301 (805) 861-3636
Vickie - Odis Dykes, Inc.
July 23, 1991
Page 2
are recovered by Kern County Environmental Health Services Department in one of the tWo
methods described below. It is your responsibility to select the method of oversight cost
recovery under the terms of (A) State contract or (B) County of Kern Local Agreement
Option. These options pertain only to costs associated with oversight.
(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 the costs incurred by both the County and
the State, pertaining to your site, under the State terms explained below:
Whereas the federal Petroleum Leaking Underground Storage Tank Trust Fund provides
funding to pay the local and state agency administrative and oversight costs associated with
the cleanup of releases from underground storage tanks; and Whereas the Legislature has
authorized funds to pay the local and state agency administrative and oversight costs
associated with the cleanup of releases from underground storage tanks; and Whereas the
direct and indirect costs of overseeing removal or remedial action at the above site are
funded, in whole or in part, from the federal Trust Fund; and Whereas the above
individual(s) or entity(ies) have been identified as the party or parties responsible for
investigation and cleanup of the above site; YOU ARE HEREBY NOTIFIED that pursuant
to Title 42 of the United States Code, Section 699lb(h)(6) and Section 25360 of the Health
and Safety Code, the above Responsible Party or Parties shall reimburse the State Water
Resources Control Board not more than 150 percent of the total amount of site-specific
oversight costs actually incurred while overseeing the cleanup of the above underground
storage tank site, and the above Responsible Party or Parties shall make full payment of such
costs within 30 days of receipt of a detailed invoice from the State Water Resources Control
Board.
(B) COUNTY OF KERN LOCAL AGREEMENT OPTION
Kern County Environmental Health Services Department is providing this option for those
who prefer to pay the County directly and avoid the addition of State costs. Prior to the
County's performance of services, this option requires your deposit of $1,000.00 (one
thousand dollars) with the County to be held in the Local Option Trust Account. Charges
for County oversight are made against this account. In this option, a responsible party must
enter into a County agreement, Attachment "B".
The environmental sensitivity (Attachment "C") of this site has been reviewed by
Environmental Health Services Department to determine the potential threat for
groundwater contamination. Only sites determined to be non-environmentally sensitive may
enroll in the Local Option Agreement. The site described above is not in an
environmentally sensitive area and may be enrolled in the Local Agreement Option;
however, the County of Kern reserves the right to cancel any Local Agreement Option
Viclde - Odis Dykes, Inc.
July 23, 1991
Page 3
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 Services Department of your choice:
either the State contract or the County's Local Agreement Option. If you select the
County's Local Agreement, please complete and sign the Local Agreement (Attachment B),
and return it with your check for $1,000.00 (one thousand dollars) made payable to the
County of Kern, addressed to Kern County Environmental Health Services Department,
2700 M Street, Suite 300, Bakersfield, CA 93301, Attention: Accounting - Local Agreement
Option. If you select the State contract, please indicate, in writing, that you have made this
selection and that you have read the above official notification.
Failure to respond within ten (10) calendar days to this notice will automatically result in
oversight cost recovery for your site(s) to be placed under the terms of the State contract
for Leaking Underground Storage Tanks.
If you should have any questions regarding this matter, please contact Susan Gonzales at
(805) 861-3636, Extension 510.
S' ~erely, , ,-x/f~ f",
Environmental Health Services D~,,~ment
JS:jrw
Attachments
(colt~250024.a)
Attachment ~B~
KERN COUNTY LOCAL AGREEMENT OPTION
BETWEEN
KERN COUNTY ENVIRONMENTAL HEALTH SERVICES DEPARTMENT
(Kern County Underground Storage Tank Permitting Authority)
AND
VICKIE
Responsible Party for Underground Storage Tank
for: ODIS DYKES, INC.
Permit #250024
This facilitY has experienced an unauthorized release of hazardous substances from an underground
storage tank. Action is necessary to protect the public health and the environment of the County, pursuant
to Chapter 6.7 of the California Health and SafetY Code and Chapter 8.48 of the Kern County Ordinance
Code.
THE WITNESS FOR THE COUNTY AND SIGNATURE(S) FOR A RESPONSIBLE PARTY OF
THE SUBJECT FACILITY DESCRIBED ABOVE DO HEREBY AGREE THAT:
Kern County Environmental Health Services Department shall act as the lead agency for regulatory
oversight for the:
a) Site characterization: the study of a site, including sampling of subsurface soil and water
where contamination is found in order to fully assess its extent and threat to the environment.
It shall include a discussion of the relative risk to biological receptors and possible pathways
of exposure. It may include removal or in-place closure of the tank, disposal or on-site
treatment of contaminated backfill or adjacent soil, removal of hazardous substances floating
on groundwater, and the drilling of groundwater monitor wells.
b) FeasibilitY study: the identification and evaluation of feasible alternatives for cleaning up the
site and remedying threats to public health and safetY.
c) Remedial action plan: the most cost-effective, appropriate plan to lessen, alleviate, abate,
correct or clean-up the effects that a release of lla?ardous substances may have on the
environment, based on the feasibilitY study.
d) Remediation: the action chosen by the responsible party and approved by Kern County
Environmental Health Services Department for the mitigation and clean-up of contamination
resulting from an unauthorized release of hazardous materials and any ongoing monitoring
of the site.
The responsible party shall do the following:
a. Conduct all work as directed by Kern County Environmental Health Services Department
pursuant to State and local law and in conformance with appropriate regulations to assess
and remediate the contaminated site.
b. Deposit with the Kern County Environmental Health Leaking Underground Storage Tank
Local Option Trust Fund the sum of $1,000.00. The Department's oversight activities will
be charged against this account at the rate prescribed by Kern County Ordinance Code
Chapter 8.04 (currently $65.00 per hour). Monthly .statements will be prepared detailing the
activities and services provided and the remaining credit balance.
Kern County Environmental Health Services Department shall provide the following services:
a. Oversight of ail activities to characterize the site's threat to the environment and/or the
groundwater, and coordination with the appropriate State, County and local regulatory
agencies.
b. Serve as the single contact point for the responsible party's representatives and other
regulatory agencies for the activities described in 'a' above. If during the Department's
review of the site characterization/remedial action plan, it is determined that a permit may
be required by another agency, the responsible party shall be referred to that permitting
agency.
c. Review reports, conduct inspections, and oversee monitoring until the site poses no further
environmental or public health threat. An official certification letter shall be given to the
responsible party when the site is determined to no longer pose a si~tmificant threat to the
environment.
d. The responsl'ole party will be officially notified by Kern County Environmental Health
Services Department when:
1. Necessary oversight is completed. A final statement will be provided to the
responsible party. If there remains an unexpended balance of the deposit made by
the responsible party in the Leaking Underground Storage Tank Trust Fund, a
refund for the unexpended balance will be issued;
- or -
2. Fourteen (14) hours of billable time has been reached. This will give notice that the
available funds will be exhausted after six (6) additional hours of billable time, at
which time the agreement will expire. A statement estimating the amount of time
necessary to complete any remaining oversight work will be sent. The responsible
party will then have another opportunity to renew his agreement with the County.
3. Failure to enter into another agreement shall require Kern County Environmental
Health Services Department to utilize the State Water Resources Control Board
Pilot Project for which the responsible party may be billed by the State directly for
the cost of County services as well as State costs.
2
Kern County Environmental Health Services Department reserves the fight to cancel this a
at any time for any reasons, including groundwater contamination or a uniquely complex hydrogeological
condition. If an unexpended balance remains on deposit from the responsible party under the' terms of this
agreement, a refund for the uneXpended balance will be issued and the agreement terminated. Once the
agreement is cancelled, you, as a responsible party, will be enrolled ia the State Leaking Underground Storage
Tank Pilot Program; see Attachment "D".
This agreement may be cancelled any time by either party by certified registered return receipt letter
to the other party within five days of said notification.
I, Vick±~ ) (responsible party), have read and agree to the conditions of this
·
agreement for the coa~tamatated site described as:
Site Name Oais~,DYkeg~i Inc.
Site Address 31 3 Daniels Lane
Ci~ Bakersfield, Ca. 93307 Zip
OWller Odis F Dykes
Owner's Address 31 3 Daniels Lane
City Bakersfield, Ca. 9~Q7 Zip
Telephone 805- 322- 3039
Operator
Telephone
Billing Address Atm: Vickie
PO Box 61 57
Bakersfield. C.a 9~
Permit # 250024
In order for this agreement to be executed, it must be signed and accompanied by the deposit of one.thousand
dollars ($1000.00). //O/~/~ _ _
Responsible Party: //~/~J
Date: July 26, 1991
For the County of Kern:
Date:
UNDERGROUND STORAGE TANK UNAUTHORIZED RELEASE (LEAK) / CONTAMINATION SITE REPORT
EMERGENCY HAS STATE OFFICE OF EMERGENCY SERVICES
[] YES ~ NO REPORT SEEN FILED? [] YES [].NO
FIEPORT DATE . CASE, :::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::
NAMJ~ OF INDIVIDUA~L FILING REPORT - PHONE
REPRE~.~..G [] OW~",OPE~TOR [] E
'~' ADORESS
~_ .A,~E CONT~CTPEaSO...
S~E~ ~ATE I ~p
;~[Ll~ N~E (iF APPMC~L~ OPE~TOR P~NE
~ ~088 8T~E~
~ ~EGION~ ~AR~ ' .. ~. ' P~N~
m (1) t ~ NAME / ~ QU~T~ LOST (G~LONS)
~ ~o,~.~o~ ~ 0ol (ol ~ /, ~WDI~VE~D~ TANK mST ~ TA~REMOVALIN~mORY~mROL ~ O~ERSU~URF~EMONITORING ~ ' NUISA~E~NDIT~NS
~ ~TE DI~HARGE BE~N M~OD U~D ~ STOP DIe. ROE (CHECK [L ~T ~PL~
~ .I ,I ol ol ~1 ~1 ~u.~ow. ~
~MOVE~N~N~ ~ R~P~ET~K ~ CL~ET~K
~ ·
~ ~SOI~.ARGEB~NSTOPPED? ~ ~PAIRT~K ~ REPAIR PIPING ~ CH~GEPR~EDURE
~ ~ ~ T~K~ ~ UN~O~
~ ,
~ ~ ~ PIPING LE~ ~ O. ER ~ ~R~SION ~ UNK~WN ~ O~R
~ ~ ~E~ONEONLY
~ ~UNDE~RMINED ~ ~,LONLY ~ GROUNDWA~R ~ DRINKINGWA~R-(CHECKONLYIFWA~R~LLSHAVEACm~LYBEENAFFEC~D)
CHE~ ONE ONLY
~ ~ ~ NOACTION TArN ~ PRELIMINA~SI~E~ME~RKP~N SUBM~D ~ ~LLUTIONCHA~C~R~T~N
~ REUEDIATION P~ ~ CASE ~OSED (C~UP COUPleD OR UNNECE~AR~ ~ ~NUP UNDERWAY
~ EXCAVATE & DISPOSE (ED) ~ RE~O~ F~E P~CT (F~ ~ ENH~ED g~ ~GR~ATION (1~
CHECK
~PROPRIA~
ACTION(S)
-~ ~ C~SIm(CD) ~ EXCAVA~&TREAT(E~ -~ F,UMP&TREATGmUNDWAmRIG3 ~ REP~ SUPPLY (RS)
~ ~ CONTAINMENT BARRIER (CB) ~ ~T~NREQUIRED(NA) ~ T~ATMENTAT~O~P(HU) ~ ~NT~IL~
PROVIDE DRAWING OI CAL LAYOUT OF FACILIT'I ,G SPACE PROVIDED BELOW.
ALL OF THE FOLLOWING INFORMATION MUST BE INCLUDED IN ORDER FOR THE
APPLICATION TO BE PROCESSED:
TANK(S), PIPING & DISPENSER(S), INCLUDING LENGTHS &
DIMENSIONS.
PROPOSED SAMPLING LOCATIONS DESIGNATED BY THIS SYMBOL
NEAREST STREET OR INTERSECTION
ANY WATER WELLS OF SURFACE WATERS WITHIN 100' RADIUS OF
FACILITY
NORTH ARROW
JR. HIGH
~CHOOL
Plant '.;I
~ t' 'I,i : .
,m . ( ' .. :: ':: ~'
...... .¢ 'F':':"'"'":"":"":'~':':
;. W,~e w,k-, · '" ':"'*":: :'1
I.; ~ :
Brook 1:: ' 1- I COUNTY
l: ~ . ' I OF KERN
v l 1:: ' SEWER FARM
..... ': :.='"' I*: ..... ~1~ ,..
:-] t: .:,
~ I': ~ r'~-"~-I I "~
I ~.~;. I I'. .....
~ST PANAMA
Underground
GQsoline dispenser ~ I-'----I ~ Gasoline piping
-I---I
~,~ :'~C6..,~..- Fuel dispensing island ~ ~ y
Diesel fuel dispenser ~ Un'derground
--~'- x~ Diesel piping
, /// '~'
· ~ [ormer ~der~round
~ // G~soline pipin~
'- ~ .... -~--
~nder~round storage
[ t~nk~~~~/ I Kennedy/Jenks Consultonts
--~:~, Odis Dykes, Inc.
I ~~ "' " Bakersfield, California
Proposed 8~il
Boring
. -Proposed Soil
September,
0 5 10 15
Kennedy/Jenks Consultants
ATTACHMENT A
ODIS DYKES, INCORPORATED
REVISED SITE CHARACTERIZATION WORK PLAN
FOR THE DANIELS LANE FACILITY.
K/J 91231
INTRODUCTION
Odis Dykes, Inc. formerly operated a fuel dispensing facility at its 313 Daniels Lane
location in Bakersfield, California. The fuel dispensing facility consisted of one
8,000 gallon aboveground diesel fuel tank and one 4,000 gallon aboveground
gasoline tank that were connected to separate dispensers on a common fuel
dispensing island. (See Figure 1). There was also one 2,500 gallon underground
~i~!i~i[~i! storage tank that reportedly had not been used since 1988.
On ....... 14 June 1991, Odis Dykes, Inc. removed the 2,500 gallon underground
~i! storage tank and associated piping.
~RE~iiGEO~OG'~
FINDINGS OF PREVIOUS INVESTIGATION
During the underground tank removal by Odis Dykes, Inc., soil samples were
collected by B.C. Laboratories, Inc. beneath the former underground tank and the
dispensers. Soil samples were reportedly collected at depths of two feet and four
below each end of the former underground storage tank and at depths of two feet
and six feet below each of the dispensers. Petroleum hydrocarbons were not
detected in any of the soil samples collected below the former underground storage
tank, however, elevated concentrations of petroleum hydrocarbons· were detected
in soil samples collected below each of the two dispensers at depths of two feet
(1114BAK) I 012310.00
The County, in its letter dated 23 July 1991, notified Odis Dykes, Inc. that the
· .. County had determined that an unauthorized release of hazardous materials had
occurred at the site'. Odis Dykes, Inc. was identified as the responsible party in the-
County's letter and therefore was required to develop a Site Characterization,
Feasibility Study and Remedial Action Plan for the site, Odis Dykes, Inc.
subsequently chose the County of Kern Local Agreement Ol~tion for oversight cost
recovery and deposited $1,000.00 in the County of Kern Loc'al Option Trust
Account.
PROPOSED SCOPE OF WORK
A phased approach to the site characterization and subsequent remediation of the
site is proposed. The site characterization phase will assess the vertical and lateral
extent of the chemicals of interest in the soils in the area of the former fuel
dispensers and associated piping. On the basis of the results of the site
characterization, alternative site remediation measures will be identified and
evaluated, and a recommended remediation alternative selected. Upon approval of
a plan for implementation of the selected remedial alternative by the County, the
recommended site remediation will be performed by Odis Dykes, Inc.
Tesk 1 - Work Plan Development
This Work Plan has been prepared in accordance with guidelines set forth by the
County in its Site Characterization and Site Remediation Handbook #UT-35. The
Work Plan is based on the information provided to Kennedy/Jenks Consultants by
Odis Dykes, Inc. and review of the findings of the previous site investigation
described above.
Task 2 - Pre-field Investi.qation
Prior to initiating the field investigation, a review of potential underground utilities
and structures in the investigation area will be conducted by Odis Dykes, Inc.'s
designated facility manager. The drilling contractor will coordinate site access with
the designated facility manager to minimize potential impacts to current operations.
Required drilling permits will be secured by Odis Dykes, Inc. during coordination
with the drilling subcontractor. Finally, a Health and Safety Plan for the protection
and safe conduct of Kennedy/Jenks Consultants' personnel while they are working
at the site will be developed. The Drilling Contractor shall have all necessary
licenses and training prior to performing the field investigation.
Tpsk :~ - Field Investigation
On the basis of the findings from the preliminary site assessment, a minimum of
three soil borings are proposed for the site characterization. Borings are in the fuel
dispensing island area as shown on Figure 2. Proposed boring locations may be
relocated in the field based on conditions encountered during drilling operations. All
borings will be drilled using an eight inch outside diameter hollow stem auger.
(/114BAK.) 2 ~1231~.(X)
Kennedy/Jenks Consultants
Undisturbed soil samples will be obtained at five-foot .intervals beginning at the
surface and continuing to a depth of approximately 20 feet or first-encountered free
water, whichever is shallower.
~i~B~ i~i~!:i!:~!~iiii~i!i~i!i~i~i ....................................................................................................................................................................................................... . .........................
All borings will be drilled to the proposed depths unless organic vapors s~gnificantly
above "background" values are detected by headspace analysis from the bottom
sample of the boring. If this occurs, drilling will continue until organic vapor
concentrations attenuate sufficiently to indicate that the vertical extent of
contamination has most likely b~,en evaluated.
Field headspace analyses of soil samples for organic vapors will be conducted by
placing soil from selected sample liners in re-closeable plastic bags and sealing them
closed. The selected soil samples will be desegregated and placed in a warm
location for approximately ten minutes following sample collection. An organic
vapor analyzer will be used to measure the organic vapor content in the headspace
of selected samples by carefully inserting the organic vapor analyzer probe into the
bag. The magnitude and distribution of these organic vapor readings will be used to
help select soil samples for laboratory analyses. All monitoring data will be recorded
and included on drilling logs.
Additional boring may be installed if the lateral and vertical extent of elevated
concentrations of gasoline constituents are not adequately defined by analysis of
soil samples from borings B1, B2, and B3.
In addition to headspace analyses of soil samples collected, field personnel will
perform air monitoring twice daily with a direct reading organic vapor analyzer
(OVA, OVM or HNU) in the breathing zone at each work location. All readings will
be recorded in field logs. All direct reading instruments will be calibrated according
to the manufacturer's specifications..
If OVA readings obtained during air monitoring for a particular work area
consistently exceed 5 parts per million (ppm) above background, then sampling will
cease and personnel will withdraw from the work area. If concentrations persist
above 5 ppm, Level C protection will be required if work is to continue. If OVA
readings exceed 10 ppm in the breathing zone while workers are in Level C
protection, then work will cease and the source of the emission will be identified
and controlled before work continues.
(~114BAXI 3 612316.00
Field personnel will Wear equipment to protect against potential physical and
chemical hazards. Level D protection will be required at a minimum for field
activities at the site. Level D personal protective equipment to be used will include:'
· ANSI approved hard hat
· Chemical resistant gloves '
· Work clothes or Tyvek
· ANSI approved safety glasses (for drilling .activities)
All borings will be logged and sampled by a Kennedy/Jenks Consultants geologist.
The soil samples will be collected in pre-cleaned brass liners using a clean split-
spoon drive sampler. Upon collection, each sample liner will be sealed on both ends
with Teflon sheeting and plastic caps. The samples will be labeled and kept chilled
during transport by Odis Dykes, Inc. to a laboratory certified by the state of
California for analysis. A chain-of-custody form will be completed and will
accompany the soil samples. The soil sampler, soil sample liners and augers will be
steam cleaned prior to their initial use and between borings. The sampler will also
be washed between each subsequent use to reduce the likelihood of cross
contamination of samples.
analyzed for Total Petroleum Hydrocarbons by Modified EPA Method 8015 utilizing
gas chromatography with flame ionization detection. Benzene, toluene and xylene
will be analyzed by EPA Method 8020 for aromatic volatile organics utilizing gas
chromatography.
Completed soil borings will be abandoned in accordance with local regulatory
guidance. Auger flights will be progressively removed and cement/bentonite grout
will be tremied or poured through the augers. Each boring will be sealed from total
depth and finished to surface grade.
Drill cuttings will be collected and placed in labeled drums and left onsite until
laboratory analyses are completed and a proper disposal method can be evaluated.
Kennedy/Jenks Consultants will be available to assist Odis Dykes, Inc. to aid in
evaluating the appropriate disposal methods for the drill cuttings.
Task 4 - Site Characterization Report/Feasibility Study/Remedial Action Plan
Upon completion of Tasks 1 through 3, a Site Characterization Report will be
prepared summarizing the results of the field and laboratory investigations. The
report will include a site map showing the location of soil borings, a description of
soil lithologies and approximate distribution of any hydrocarbons detected in the soil
W114BAK) 4 012310.00
Kennedy/Jerks Consultants
samples analyzed. The report will also indicate sample collection procedures,
analytical results and the analytical methodology used.
include soil vapor extraction and treatment, excavation and bioremediation, or
capping and post-closure monitoring.
The Feasibility Study will consider the technical feasibility, cost effectiveness', and
short and long term effects to public health and the environment, including potential
contaminant migration routes for each alternative.
A Remedial Action Plan, if warranted, will be developed based on the findings of the'
Feasibility Study. A detailed scope of work for site remediation will be prepared as
part of the Remedial Action Plan.
PROJECT SCHEDULE
Selected elements of the Pre-field Investigation Task have already been initiated.
Site characterization field activities will be initiated within two weeks of written
approval of the Work Plan by the County, subject to contractor availability. The
Site Characterization Report/Feasibility Study/Remedial Action Plan will be prepared
and submitted to the County within three weeks of receipt of analytical results.
(~114BAK) 5 I123~11.0~
LEGEND
~, i,~'~ Fr~wO~~
Kennedy/Jenks Consultants
Odis Dykes, Inc.
Bakersfield, California
Location Map
K/J 912519.00
September, 1991
Figure 1
Daniels Laoe
Main gate_ N
Fuel dispensing island Gasoline dispenser
---~ -- Property
Former undergound line
diesel fuel piping ~/ Diesel fuel
___/
Former 2,500 gollon.~
dispenser
underground diesel
fuel storage tank Underground ---
gasoline piping
Undergound -_.
diesel fuel piping
8,000 above-
gallon
tank
Aboveground 4.000 gallon ahoy
waste oil tank ground gasoline tank
Kennedy/Jenks Consultants
Odis Dykes, Inc.
Bakersfield, California
Site Plan
0 4O 8O 120
1"=40' K/J 912319.00
Approximate scale September, 1991
Figure 2
Underground
Gasoline
piping
N Gasoline dispenser
F'uel dispensing island ~~-
Diesel fuel dispenser Underground
Diesel
piping
'' J~ F.ormer unde.rg, rou nd
/~ diesel fuel p~p~ng
/ .
I ~,~oo~o,,o~ I
underground diesel Kennedy/Jenks Consultants
I fuel storage tank I
Odis Dykes, Inc.
I ...... Bakersfield, California
Proposed 8oll
Boring L. ocatlone
-~ -- Proposed Soil Boring Location
K/J
912319.00
September, 1991
0 5 10 15 Figure
1"=5'
f · ·
,~,~, LABORATORIES, INC..
~ ~ t0u,, Ille, Olnl, IIM,
zytonl.
~yd~or~ano (4&l~J) Pg/g 13000. ~.
TEST )Lr, THO~t TPH kY I),O,II,I, / L.U,r,T~ Nanull t(ethod - IfodifLod l~A 1015
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:'..:-..-.: ~Y
LABORATORIES, INC,
TIIST ICE?14oPl ??Jr bY I),O,l,t, / T,,U,IP,T.. lle,.~,Ol Method · #odLftod l~A BOss
lp4~vtd~sJ O9~ltt~vtntl Iq Bt~ ~hod Iso3o/oo2o.
· . '. ~t)eoted, bcetved I Phi ~letedj
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,,,~,~,, I~J'~~~BORATORIES. INO.
~ 4. 4. [m. ud, Ma. ~tItL INM.
NTlqlt~.rJ 41aQ ATLILS ~Tt JAKEI~IIfl), GALJFORIqUt M3C4 PHONI Jl~ 104811 FAX (~ 1~.1ltl
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~/g ~ono ~toet~ O.OOS
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m-Zy~one ~g pone Deleted O.~S
AB ~ecoLvod libel
Oopp,,I m?. !,
J/~4/O~ J ~Ol~ ~.N. BY P, ~I~NHOUSB.
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~tel ~trelo~ '
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lenmene
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.. (f. ~/l~,tft~ ........
TEST I~?HO~f Tffl ~¥ ~,O,B,i, / L.U,F,T, Hanuei lie~hod - ISodLfLod SPA 00%s-
%ndLySd~o~ ~tuen~g'~¥ gth Kathod SO30180~0.
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LABORATORIES. INC.
ll~ 6~ GT,~ IAI(~.MIqlt,4t, IWJFQP, NI4 133O1 PHONI llmOl} 117,4~I~ Fq M t21.1111
fetrgtgum #~i~'l~nl
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l~hV; ~n;tnm rvv~ ?~o. 6.
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Cmnt; ~
~t$ ~IL ~ L~b ~t 7~08-8
ac.
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810. 4.
~n ~6co~vo¢ lost!
D&te Sldnp~e Date Simp. lo _ Date Ana~yltl
o~XylOne uO/9 ~one Petec~ed 0.~5
~-X~One . ~g/g Mono Deteoted O.~S
~rocor~n~ (d~ts~) gg/g ?.8 3.
~n~tv&du8$ eOnl~L~gn~! ~¥ ~thH~hod IO)O/lO~O.
LABORATORIES. INC.
tlO0 P, TI~ t~1',~ IWEI~tlLD, ~UFO~NU~ e~t0t fHONI
¢otXewted, ltacetved I ~Ibl cc~%lkedl
B,n,ene ~/g ~one Oete~ed O.OOl
r%l ~o~e hero.ed
~flsont pg/g ~oflo Do, coted O.OOS
~tuene pg/g ~one Oeteeked o.ool
o-xy~eflo pglg ~ono g~e~te~ o.ool
m*xyxen, pg~g Hone ~.teotet o.oOs
~x~on, Pr/9 ~o,, Deteoled o.oos
4100 ATLAS GI'~ W~ELI~. ~ALIFOI~N~ W PHC)HE II~ 12?4~tt FAX ~
fO1~FO~un
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ENVIRONMENTAL
LABORATORIES, INC.
J. J. EGLIN, REG. CHEM. ENGR.
PETROLEUM
4100 ATLAS CT., BAKERSFIELD, CALIFORNIA 93308 PHONE (805) 327-4911 FAX (805) 327-1918
Petroleum Hydrocarbons
ODIS-DYKES Date of
313 DANIEL LANE Report: 06/20/91
Bakersfield, CA 93307 Lab #: 7108-1
Attn.: EDDY 000-0000
Sample Description: ODIS DYKES TANK REMOVAL PROJECT: DIESEL TANK 2' EAST END, COLLECTED
6/14/91 @ 10:00 A.M. BY D. RITTENHOUSE.
Date Sample Date Sample Date Analysis
Collected: Received @ Lab:. Completed:
06/14/91 06/14/91 06-18-91
Minimum
Reporting Analysis Reporting
Constituents Units Results Level
Benzene ug/g None Detected 0.005
Toluene ug/g None Detected 0.005
Ethyl Benzene ug/g None Detected 0.005
o-Xylene ug/g None Detected 0.005
m-Xylene ug/g None Detected 0.005
p-Xylene ug/g None Detected 0.005
Total Petroleum
Hydrocarbons (diesel) ug/g 7.8 3.
TEST METHOD: TPH by D.O.H.S. / L.U.F.T. Manual Method - Modified EPA 8015
Individual constituents by EPA Method 5030/8020.
As Received Basis
Comments:
California D.O.H.S. Cert. #1186
~ ~nalyst
ENVIRONMENTAL
LABO RATO RI ES, INC.
J. J. EGLIN, REG. CHEM. ENGR.
PETROLEUM
4100 ATLAS 'CT., BAKERSFIELD, CALIFORNIA 93308 PHONE (805) 327-4911 FAX (805) 327-1918
Petroleum Hydrocarbons-
ODIS-DYKES Date of
313 DANIEL LANE Report: 06/20/91
Bakersfield, CA 93307 Lab #: 7108-2
Attn.: EDDY 000-0000
Sample Description: ODIS DYKES TANK REMOVAL PROJECT: DIESEL TANK 4' EAST END, COLLECTED
6/14/91 @ 10:00 A.M. BY D. RITTENHOUSE.
Date Sample Date Sample Date Analysis
Collected: Received @ Lab: Completed:
06/14/91 06/14/91 06-19-91
Minimum
Reporting Analysis Reporting
Constituents Units Results Level
Benzene Bg/g None Detected 0.005
Toluene Bg/g None Detected 0.005
Ethyl Benzene ug/g None Detected 0.005
o-Xylene Pg/g None Detected 0.005
m-Xylene ug/g None Detected 0.005
p-Xylene pg/g None Detected 0.005
Total Petroleum
Hydrocarbons (diesel) Bg/g 8.7 3.
TEST METHOD: TPH by D.O.H.S. / L.U.F.T. Manual Method - Modified EPA 8015
Individual constituents by EPA Method 5030/8020.
As Received Basis
Comments:
California D.O.H.S. Cert. #1186
ENVIRONMENTAL
LABORATORIES, INC.
PETROLEUB J' J' EGLIN, REG. CHEM. ENGR.
4100 ATLAS CT., BAKERSFIELD, CALIFORNIA 93308 PHONE (805) 327~1911 FAX (805) 327-1918
Petroleum Hydrocarbons
ODIS-DYKES Date of
313 DANIEL LANE Report: 06/20/91
Bakersfield, CA 93307 Lab #: 7108-3
Attn.: EDDY 000-0000
Sample Description: ODIS DYKES TANK REMOVAL PROJECT: DIESEL TANK 2' WEST END, COLLECTED
6/14/91 @ 10:00 A.M. BY D. RITTENHOUSE.
Date Sample Date Sample Date Analysis
Collected: Received @ Lab: Completed:
06/14/91 06/14/91 06-18-91
Minimum
Reporting Analysis Reporting
Constituents Units Results Level
Benzene Hg/g None Detected 0.005
Toluene ug/g None Detected 0.005
Ethyl Benzene ug/g None Detected 0.005
o-Xylene ug/g None Detected 0..005
m-Xylene ug/g None Detected 0.005
p-Xylene ug/g None Detected 0.005
Total Petroleum
Hydrocarbons (diesel) ug/g None Detected 3.
TEST METHOD: TPH by D.O.H.S. / L.U.F.T. Manual Method - Modified EPA 8015
Individual constituents by EPA Method 5030/8020.
As Received Basis
Comments:
California D.O.H.S. Cert. #1186
ENVIRONMENTAL
LABORATORIES, INC.
PETROLEUM J' J' EGLIN, REG. CHEM. ENGR.
4100 ATLAS CT., BAKERSFIELD, CALIFORNIA 93308 PHONE (805) 327-4911 FAX (805) 327-1918
Petroleum Hydrocarbons
ODIS-DYKES Date of
313 DANIEL LANE Report: 06/20/91
Bakersfield, CA 93307 Lab #: 7108-4
Attn.: EDDY 000-0000
Sample Description: ODIS DYKES TANK REMOVAL PROJECT: DIESEL TANK 4' WEST END, COLLECTED
6/14/91 @ 10:00 A.M. BY D. RITTENHOUSE.
Date Sample Date Sample Date Analysis
Collected: Received @ Lab: Completed:
06/14/91 06/14/91 06-18-91.
Minimum
Reporting Analysis Reporting
Constituents Units Results Level
Benzene Hg/g None Detected 0.005
Toluene Hg/g None Detected 0.005
Ethyl Benzene ug/g None Detected 0.005
o-Xylene ug/g None Detected 0.005
m-Xylene ug/g None Detected 0.005
p-Xylene ug/g None Detected 0.005
Total Petroleum
Hydrocarbons (diesel) Hg/g None Detected 3.
TEST METHOD: TPH by D.O.H.S. / L.U.F.T. Manual Method - Modified EPA 8015
Individual constituents by EPA Method 5030/8020.
As Received Basis
Comments:
California D.O.H.S. Cert. #1186
/~ Hnalyst
ENVIRONMENTAL
LABO RATO RI F.?,. INO.
J. J. EGLIN, REG. CHEM. ENGR.
PETROLEUM
4100 ATLAS CT., BAKERSFIELD, CALIFORNIA 93308 PHONE (805) 327-4911 FAX (805) 327-1918
Petroleum Hydrocarbons
ODIS-DYKES Date'of
313 DANIEL LANE Report: 06/20/91
Bakersfield, CA 93307 Lab #: 7108-5
Attn.= EDDY 000-0000
Sample Description: ODIS DYKES TANK REMOVAL PROJECT: DIESEL DISPENSER 2' , COLLECTED
6/14/91 @ 11:00 A.M. BY D. RITTENHOUSE.
Date Sample Date Sample Date Analysis
Collected: Received @ Lab: Completed:
06/14/91 06/14/91 06-19-91
Minimum
Reporting Analysis Reporting
Constituents Units Results Level
Benzene ug/g 2.3 1.
Toluene ug/g 5.3 1.
Ethyl Benzene Pg/g 4.8 1.
o-Xylene pg/g 6.3 1.
m-Xylene ug/g 20. 1.
.p-Xylene ug/g 7.2 1.
Total Petroleum
Hydrocarbons (diesel) Pg/g 22000. 1000.
TEST METHOD: TPH by D.O.H.S. / L.U.F.T. Manual Method - Modified EPA 8015
Individual constituents by EPA Method 5030/8020.
As Received Basis
Comments:
California D.O.H.S. Cert. #1186
BY~ ~_~ A~nalySt~L~
ENVIRONMENTAL
PETROLEUM J' J' EGLIN, REG. CHEM. ENGR.
4100 ATLAS CT., BAKERSFIELD, CALIFORNIA 93308 PHONE (805) 327~1911 FAX (805) 327-1918
Petroleum Hydrocarbons
ODIS-DYKES Date of
313 DANIEL LANE Report: 06/20/91
Bakersfield, CA 93307 Lab #: 7108-6
Attn.: EDDY 000-0000
Sample Description: ODIS DYKES TANK REMOVAL PROJECT: DIESEL DISPENSER 6' , COLLECTED
6/14/91 @ 11:00 A.M. BY D. RITTENHOUSE.
Date Sample Date Sample Date Analysis
Collected: Received @ Lab: Completed:
06/14/91 06/14/91 06-19-91
Minimum
Reporting Analysis Reporting
Constituents Units Results Level
Benzene Hg/g 1.8 1.
Toluene Hg/g 18. 1.
Ethyl Benzene ug/g 6.2 1.
o-Xylene Bg/g 29. 1.
m-Xylene Bg/g 62. 1.
p-Xylene Bg/g 21. 1.
Total Petroleum
Hydrocarbons (diesel) ug/g 14000. 900.
TEST METHOD: TPH by D.O.H.S. / L.U.F.T. Manual Method - Modified EPA 8015
Individual constituents by EPA Method 5030/8020.
As Received Basis
Comments:
California D.O.H.S. Cert. #1186
ENVIRONMENTAL
LABO RATO RI F.?,, INO.
J. J. EGLIN, REG. CHEM. ENGR.
PETROLEUM
4100 ATLAS CT., BAKERSFIELD, CALIFORNIA 93308 PHONE (805) 327-4911 FAX (805) 327-1918
Petroleum Hydrocarbons
ODIS-DYKES Date of
313 DANIEL LANE Report: 06/20/91
Bakersfield, CA 93307 Lab #: 7108-7
· Attn.: EDDY 000-0000
Sample Description: ODIS DYKES TANK REMOVAL PROJECT: GASOLINE DISPENSER 2' , COLLECTED
6/14/91 @ 11:00 A.M. BY D. RITTENHOUSE.
Date Sample Date Sample Date Analysis
Collected: Received @ Lab: Completed:
06/14/91 06/14/91 06-19-91
Minimum
Reporting Analysis Reporting
Constituents Units Results Level
Benzene pg/g 170. 5.
Toluene pg/g 2300. 5.
Ethyl Benzene Bg/g 710. 5.
o-Xylene ug/g 1400. 5.
m-Xylene ug/g 2700. 5.
p-Xylene pg/g 930. 5.
Total Petroleum
Hydrocarbons (gas) Bg/g 41000. 900.
TEST METHOD: TPH by D.O.H.S. / L.U.F.T. Manual Method - Modified EPA 8015
Individual constituents by EPA Method 5030/8020.
As Received Basis
Comments:
California D.O.H.$. Cert. #1186
Eglin /~/- /Analyst
ENVIRONMENTAL
LABO RATO RI F.?,, '1 NC.
J. J. EGLIN, REG. CHEM. ENGR.
PETROLEUM
4100 ATLAS CT., BAKERSFIELD, CALIFORNIA 93308 PHONE (805) 327.4911 FAX (805) 327-1918
Petroleum Hydrocarbons
ODIS-DYKES Date of
313 DANIEL LANE Report: 06/20/91
Bakersfield, CA 93307 Lab #: 7108-8
Attn.: EDDY 000-0000
Sample Description: ODIS DYKES TANK REMOVAL PROJECT: GASOLINE DISPENSER 6' , COLLECTED
6/14/91 @ 11:00 A.M. BY D. RITTENHOUSE.
Date Sample Date Sample Date Analysis
Collected: Received @ Lab: Completed:
06/14/91 06/14/91 06-19-91
Minimum
Reporting Analysis Reporting
Constituents Units Results Level
Benzene . ~g/g 28. 4.
Toluene ug/g 590. 4.
Ethyl Benzene Bg/g 220. 4.
o-Xylene ug/g 500. 4.
m-Xylene ~g/g 870. 4.
p-Xylene ug/g 270. 4.
Total Petroleum
Hydrocarbons (gas) ug/g 12000. 900.
TEST METHOD: TPH by D.O.H.S. / L.U.F.T. Manual Method - Modified EPA 8015
Individual constituents by EPA Method 5030/8020.
As Received Basis
Comments:
California D.O.H.S. Cert. #1186
/ a6alyst
~. Report To: ~ ,. '~ Analysis Requested
-- ~ m r,.) rr
"r Lab# Sample Description Date & Time Sampled
.j
Comment: Billing Info: i Recleived by: (Signature) Date: Time:
Name: ~'fl~ ~ _.~ (I ~'~.,~ Relinquished by: (Signature) eivod by: (Sign~aiure) ~-~ Date: TJm~
· Address
City State ' Relinquished by: (Signature) Received by: (Signature) Date: Time:
Attention:
~_ ~,~.~. Relinquished by: (Signature) Received by: (Signature) Date: Time:
,I Miles: ---. --_, ~ \r,) ~_ Relinquished by: (Signature) Received by: (Signature) Date: Time:
Sample Disposal P.O.#
~ ~c-Disposal @ 5.00 ea. -- Relinquished by: (Signature) Received by: (Signature) Date:' Time:
El Return to client
· :THE- N U ~B ~R~O Fh~,~ANKS~,U SPEC T E D~YT 0% BE
: 2 · '' · '.'-" '~,.'~,~":F ;~i'~ '"':~ f~'~g~:~-'::'-'~'~" ~" ,.b:.: - ~i~ .~:/': .~ ~.~. ~ ,'L-,-
D ' ~ .-.
ATE' PER~ I'TT ING.-POL I.C~.,':LEI. TER LHAS:- ~A I LED
DATE RETURN:,;CORRESPONDENCE/OR PHONE CA NAS~:.RECEI:~ ..
~OTEg ON CORREgPONDENCE/PHONE CALL '.,.,~
MBER OF TANKS ON PERMIT PLICATION:
TANKS WILL BE REMOVED
TANKS WILL BE OPERATED
RESOURCE MANAGEMENT AGENCY
Environmental Health ~ Departmem
RANDALL L. ABBOTT ~ M~C_~ ~ ~V, ~-~S, DW. ECTOR
DIRECTOR A~r Pollution Control Di~U~ct '
DAVID PRICE [] ~ J' RODDY, AI~O
ASSISTANT DIRECTOR Planning & Development ~m~ De~ent
TED JAMES, AICP, DiI~CTOR
ENVIRONMENTAL HEALTH SERVICES DEPARTMENT
January 28, 1991
Odis Dykes, Inc.
313 Daniels Lane
Bakersfield, CA 93307
Re: 1,000-gallon diesel tank
Ladies and Gentlemen:
It has come to the attention of the Kern County Environmental
Health Services Department that you own at least one underground
storage tank which is currently not permitted through this
department.
Current law requires that all owners .of existing underground
storage tanks apply for a permit to operate their facilities,
unless they meet exemptions provided in Chapter 6.7 of California's
Health and Safety Code. The exemptions provided in law are listed
below:
1. A tank with a capacity of 1,100 gallons or less which is located
on a farm and which stores motor vehicle fuel used primarily for
agricultural purposes and not for resale.
2. A tank which is located on a farm or at the residence of a
person which has a capacity of 1,100 gallons or less and which
stores home heating oil for consumptive use on the premises
where stored.
3. Structures such as sumps, separators, storm drains, catch
basins, oil field gathering lines, refinery pipelines, lagoons,
evaporation ponds, well cellars, separation sumps, lined and
unlined pits, sumps, and lagoons.
4. Tanks not substantially underground.
5. Tanks storing substances not designated as "hazardous"} the
following liquid and solid substances are considered "hazardous
substances":
o~cv~ ,,x,v, c~ccw ~rlrTl: ~r~ RAI, C1:RRI:T1:T n ~AI IFF~RNIA q3.'qrH (805) 861-3&q6
-Odis Dykes, Inc.
January 28, 1991
Page 2
-- those defined as such in Section 25316 of the Health and
Safety Code of the State of California
-- substances on the list prepared by the Director of Industrial
Relations pursuant to Section 6382 of the Labor Code of the
State of California
-- any substance or material classified by the National Fire
Protection Association as a flammable liquid, a Class II
combustible liquid, or a Class III-A combustible liquid
-- any regulated substance, as defined in Subsection (2) of
Section 6991 of Title 42 of the United States Code, as that
section reads on January 1, 1989, or as it may subsequently
be amended or supplemented.
QWNERS OF THE FACILITIES NOT DESCRIBED AS EXEMPT ARE CURRENTLY
VIOLATING THE LAW AND MUST OBTAIN ONE OF THE FOLLOWING PERMITS IN
QRDER TO BRING THE FACILITY INTO COMPLIANCE:
-- A permit for operation
..-- A permit for tank removal
The owner must'submit a completed application to the Kern County
Environmental Health Services Department before the permit will be
issued. To assist you with compliance, the Department has included
applications and instructions for the proper completion of each
application within this packet. Comnleted forms must be returned
within 14 days.
The application for the permit for permanent closure of your tanks
is' to be submitted IN LIEU OF the application for the permit to
operate. Failure to obtain a permit may result in fines of five
hundred dollars ($500) to five thousand dollars ($5,000) per day
per Division 8, Section 8.48.480, of the Kern County Ordinance
Code.
If you have any questions, please feel free to call Jane Warren or
Amy E. Green at (805) 861-3636.
....... ·
Hazardo slMateri 4. _Sv.3ialist IV ·
Hazardof~JMaterials~-a'hagement Program
AEG:JW:jrw
Enclosures
GIBSON OIL & REFINING CO., INC.
RE: Load Acceptance MANIFEST# ~ ~--;-/'~' ,~ z7~-,~ '~,~
Dear Customer:
This Letter is to inform you that Gibson OII & Refining has the appropriate permits for and has
accepted your material for recycling. The amount we received was ~zy~,.~ ,~. gallons.
If this does not agree with your data please notify us within 10 days so that we can resolve
any discrepancies. Phone (805) 327-0413
Very truly yo'urs, ~ ' ~
Gibson Oil & Refining Co., Inc.
Customer Service
3300 Truxtun Avenue, Suite 200
Bakersfield, CA 93301
A Subsidiary of V.L.S., Inc.
~.11 East Ocean Blvd., Suite 231 2101 Webster St., Suite 1500 3300 Truxtun Avenue, Suite 200
ong Beach, CA 90802 Oakland, CA 94612 Bakersfield, CA 93301
13 / 499-4996 Telex: 664-611 415 / 446-7777 Telex: 338-139 805 / 327-0413 / 800-582-3935
~.X 213 / 499-4980 FAX 415 / 836-4503 FAX 805 1861-0229
~'~ Recycled Paper
State of California--Health and Welfare Agency ,'~- Department of HealtH-Services
rorm,~vIo~uv=u OMB NO. 2050--0039 ~^pires 9-30-91~ Toxic Substances Control Division
'~' P(ea~e"~rint or type. (Form designed for use on elite I .... Ypewriter). ] ~~ Sacramento, California
~~ ~~ ID No. I Manifest~ Info~ation in the'shaded areas
ORM HAZARDOUS enerator's US EPA Document No.
WASTE MANIFEST~ ~ I I I. I I I I I I~ I I I I
~is Dykes, Inc. .. ,
B;~ate ~rato~f~;2':~?~-~??:::~': . ::(-:: , .
~ Box 615~ B~e~$~eld~ Ca. 93386
4. Generator's Phone ( B05 ) 3 2 2--30 39 ~: .~:~,.,,t;: ::, ?/v'J~?-', ~ :~,l~{:$~?F-~:~t~:?l:,~-~:,t;I
5. Transpolar 1 Company. Name ~. US EPA ID Number C: ,,St~ff~n~ ~'~:~'a~?~ :'
7. Transpolar 2 Company Name 8. US EPA ID Number.' E ;S~o T~P~'~:T~?~~{~{'?~ .~:: .-
' I I I I I I I I I I I I ~"~-'-
?.,~ >.~ '9:,De~md~F~ty:~meand S~e'Addre~..:,.:: :,~:.>-;'-::: -.-:~O.:~,: ;~>EPA d~r~g~' -'~' .T,~-- ~., ~,~ ~--~',~,~,~,~,,-~,~, ~ ~ ~ :~,~,~
12. Containers 13. Total. 147 i~13;e~,~,?~l~,~,;,:,;~.-
', Quanti~' ' Unit- ?~=~Wa~e~No:;:~?~'~5
11. US DOT Description (Including P~oper Shipping Name. Hazard Class. and ID Number) No. Type Wt/Vol ;~?~;~%~<~;~5~;~::~:;%,:
E NON RC~ ~0US WASTE LIQUID 0 i0 il T iT ~lC/l::'[C~l ~b~
A ' EPAI ~er~::*:',
I I .I I I I I ':.';~%:~:~":~
State:: :¥;',~'
J. Additional Descriptions for Materials Listed A~ve * K. Handli~,C~s f~ Wastes L~ ~ve -; ' :, '
A) DIESEL/GASOLINE RINSATE .: ' :[:::::' '~
OILY WATER - · '. . .,' :.. '" '~'~' c~.":-:.~,':~? q~' ~" ~.~.~,~:~'~,~-~:~::%:,:~
15. Special Handling Instructions and Additional Information
GLOVZS, ~,0G~LES, :~ ~' ~T ~
...... · R0, ~.~V~; 0UTEP~ GA~iENTS~ ~LEASEt/ 1163-1
16.
GENErATOr'5 CErTIfiCaTION: I hereby declare t~at tbs contents of this consignment are fully and accurately described above by proper s~ipping name
and are classified, packed, marked, and labele~, and ate in all respects in proper condition for transpo~ by highway according to applicable international and
national government regulations. ·
~' If I am a large quantity generator, I ce~i~ tbs[ I have a program in place to reduce the volume and toxicity of waste generated to the degree I have datelined
/ to be economically practicable and that I have selected the practicable method of treatment, storage, or disposal currently available lo me which minimizes the
present and future threat to human health and the environment; OR, if I am a small quantiW generator, I have made a good faith effo~ to minimize my waste
generation and select the best waste management method that is available to me and.that I,can afford.
Month Day Year
Printed/Typed Name Signature ~ '/:.::...' .
T 17. Transpo~er'l Acknowledgement of Receipt of Materials /
A Printed/Typed Name ~ Signature ]~ ~ " ~ Month Day Year
I
N
s Vickie Breaw /':/~c'"zP~~ Io 16 I
g 18. Transpomer 2 Acknowledgement of Receip~ of ~aterial~
~ Printed/Typed Name I Signature Month Day Year
19. Discrepancy Indication Space
<~-~ · =-.' . *. -.r ....--~: ~ ~. ~ ~ ~ r ''~- '. ~ ~''- "'~.* :-~''~/'*<'~"'~' ,~"~:~:--~'~ *'~::~'T*~','' '~:~''" "--'"'~' ''"~ --:~'"' :~'''*'~' '' ............ "' "~ ........... '
C
L
I 20. Fac~ty Ownff~ or Operator CeHificafio~ of receip~f~azardoua materials covered by,this manifeS~xcept as noted~m 19.
:HS ~022 A (1 z~) Do Not Write ~low This line
{PA 870~22
Rev. 9-88) Previous editions are obsolete.
' "' Yellow~ TSDF SENDS THIS COPY TO GENERATOR WITHIN 30 DAYS
....: , . ~ groundwater~ )urces inc. ,' .--' ,~SF!EED
'. : ;_::: ..' : . ,- ...
· : .... .: . .. :': : ':" . :. :"'-'.'i.:':-.:' -.:'Cla~
:?" ":':~:: ".' ; ~':... : :.',.':.
~':" -.'April..'26, 1989~-h,: ".' ?'
' .-.': ' 'P,'o ;. B~x '615.7.' · ."?.:: ": .:: :'. :':.:.:, ~'~=~TAL'HEALTH':%:~f. '.' . "-~ '.':~
· :.:':::.::.-: '. ',' . .", - ":':'"' ':.......,: ' Re: ' Prec's'on ~'an'-:..~es~":'::,:'
'":'" Enclosed a~e ~wo. coPie~ of the. ~est results for th°
::tank . ~es~ perf0rmed"on.April 20,. 1989 at. 7our facili~7;?~:':
-...'... Tank ~1' R,500' ~all°n~ PASSED ' -.042 G.:P.'.H...::.".
CONCLUSIONS: . .
The. a~ove referenced t~nk failed pe'~NFP~ ~29 tolerance. .... ""~:~'}:?
· .,, ."i~::::: :.~ .:
P~ease keep one.. cop7 o~ the results for 7our records and
one ~op7 LO the: Kern Coun~ Health Depa~Lmen~ ~i'~hi~ ~h~7"(
If' 7ou have a~7 q~es~ions re~ardin~ ~his Lan~ Zest, please
our main o~fice a~ (805) 8~5-7700, ~::: '"~';':':
~R: d j i .
~'~'.', :.:
MAILING ADDRE~: P.O. BO~-9383, B~KERSFIELD, CA 93389 (805} 835-77~ . .'::,:..:.
OTHER L~ATIONS: LOS ANGELES {213} 724-3147 PLACENTIA (714) 528~2415
...... . - ,-.~. ~. ,m..T~? - ................ ................................. ................... ~ ............................................ . ....................................... : .,~.~ ................... ?..
~ -~ 2 ...- ?:...'
Name of Supplier. Owner or ~aler Address No.'~nd StreeHs) C~ty Slale Date of ,~
I
15. TANK T0 TEST 15a. BRIEF DIAGRAM 0F TANK FIELD 16. CAPACITY
1~8' ~ ~ / ~ ~ Nomina, Capacily . ~ ~ ~ Tank Manufaclure,'s Cha,,
6 ~ Company Engineering ~ata
Brand and Grade ~-~ ~ ~ By meal accurate ~ Charls supplied wilh
17. FILL~UP FOR TEST ~'~
/
/
IO W' Oa,lo.. Ta.k Oiameler in. , .... ,Dry ~:
18. SPE iAL' CONDITIONS AND PROCEDURES T0 TEST THIS TANK ~ w.,~, ,. ,.., ~ ~,.~,,~ ~,.g,~,,~ w,,, ~v~. ~ .~ ~
~e manual a~hOnSl applicable. Ch~k ~low and r~ord proc~ure in log (27). High water table in tank e~cavation ..
Fou, poun~ ,ule do ..... pp y fo doublewalled tanks. 19. TANK MEASUREMENTS FOR z,...~., ,o~.~ ~o ,.~ =~
Complef .... ion~.,~: TSTT ASSEMBLY 21. VAPOR RECOVERY SYSTEM ~
~flom of tank lo gra~' . ........................... ~ ~/ in.
~"~o~"~',,o~,~ 30 ,,. 24b. COEFFICIENT 0F EXPANSION
1 Islou, po, ld,ule,,uired~ Yes ~ No ~ Total tubing to ass~b~ -- appmximal, ......... /~/ ~,. RECIPROCAL METHOD
2. H~g,~,o ~2"~,,k~,om~,~O,~..k . //~._~,. 20. EXTENSION HOSE SE~ING Type of Producl ' ...... ............
Tank lop lo grade' ...' ............ _ in. E~drometer Employed ..................................
Extend h~e on lucllon lu~ 6" o~ more Temperalure in Tank
AFter Circulation .....................................
b~wtank lop ...................................... in. . .. ~
4. ~essu;e ~t top el tank P.S.L '11 Fill pipe exlends a~e 9rede. u~e top of lill. Temporalure el Sample .................................
22.Thermal-~nsor reading alte~ circulation / ~ ~ ' Oiflmence (*/-) ............
/ Bet~en .................................
Tankdi.. &~ ,. 23. Digits per 'F in range of exp~ted chang, ~'~ ,~lproca, ~0~ Page,
. digits '
COEF~ICIEN; 0F EXPANSION (Complete after circulation) ~. ~ ~ ~ ~
~4a. Cozrected AP.I. Gravi~ Total quantity in Reciprocal V~ume
er ts . In. full tank (16 o; 17)
b~TES: ....... -- Ttansfer,~tO
~sewed
Gritty
~dr~te; employ~ ....................................
~..~.d ~. T.~,~.~ ..... ~ 24C. FOR TESTIN6 WITH WATER ..
~rrected A.P.L Gr~i~
~ ~F, Fzom Table A ........ Waler Tempe;ature after Circulation
........................ Table C ..................................................
The ~bove calcu 8IIORS Rt~ lo ~ ~Sed fOr dw soil conditions lo for Involv~ P;odu~ Coeflicio~t ol Water
eslablish a ~
area. Transfer CeE to Line 2~. Added Surfac ante ~ Yes ~ NO Transfer CeE to Line
Refer Io N.I '
p.A. 30, ~,o., 2-3.2.4 ..~ ~.~ ..~ ~ ~..~ 25. (a) ~ ~) =
manufacturel regarding allowable Syslem I~t pressures.
Total ~uanlity In
full tank (16 or 17) Involved pr~u~ per ~F
26. (a~l,l~4~?/~ ' ~ = ,
27. Sensor Calibrnliun/~,~,~"-~ ./_;~,/_&..~ 30. HYDROSTATIC 31. 34.
I 38... voLuM~
PRESSURE VOLUME MEASUREMENIS (VI 1EMPERATURE COMPEHSAflON CHANGING i ACCUIMULATED
~ LeG OF 1ESI PflOCEDUnES - CONTROL . RECORo TO .mi GAL. US[ FACTOR {al EACH REAOING , CHANGE
28. '""--'~ '"'"-- ~ ~ _...,__.___ ._____..._______._ ...__..___. ------,-------
DATE Record de. tails of selling up 29. Slandpipa Level 32, Ftoducl In 33. Product 35. 36. 37, lempefalme
and running lesl. (Use hdl Reading In Inches Graduale Replaced (-) Adju$1menl
lenglh of line II needed.) No. Chanoa Computation ..
B%i~aing Level to Thermal Higher · {cl, ia), Volume Minus
TIME of which Before Afler Sensor Lower -
{24 hr.) Producl Expansion · EJq)an$ion I.I or Al ow Level compule
C~anoe per Hour
,mmmmm,~m ~ m Reading Reslored Reading Beadino Recovered {°l Reading lc) Conhaclion - Coflifaclion I-) ~iNFF'A (:rilerial
I
,--') . ~ ,. ',,-' ~ ' ,
II II tl 11 ~ ~ ~Z.~ ,1~ ,?fO ~lib~
I~ 1~ 12.3 ./~ ,I75~ ~,o~ c/o ~ ~.o~m ~,oom -,~e~
i I~' 1~ /~'~ ,17~ ,/~ ~o~a oI~ ~ ~~ --.oo~ -- :~
,i~
P-T Ta ,k Tell Dala Charl z Statement: ~ ~ ~ ~
II is Ihe responsibility of the owner 8nd/or operator of Ibis
Additional hi fo ~Tank and product' handling system has ~en resin lighl system to immediately advise slate and local 8uthmi(ies of
according to lhe Pr~Ision Test Criteria 8s established by
' - N.F.P.A.. publication 329. This ts not Intended I0 indicate Implied hazard and the possibility ol any reportable ppIlutton to
, permission of a leak. the environment as a resull of lfle indicated fail,re of Ibis
I. ~l Volume Change Conclusion of Precision Tell ,-P~,h syslem. Heath Consullants Iflcor~rated does not assume 8ny
,Signature of Tester: ~ [8flk:b~d prodOcIhand ngsyslemhasfelledthelanktlghlnees
, o ment. /
~ test according to the ~ecislon Test Criteria as established by
. RES ? CE MANAGEMENT AC x CY ·
**UNDERGROUND TANK DISPOSITION TRACKING RECORD** .':
This fom is to be returned to.the Kern County Environmental' Health Services
Department within .14 days of acceptance of the tank(s) by an approved disp°sal
or recycling facility. The holder of the pemit with the number noted above:, is
resuonsible for insuring that this; rom is completed and returned-. '.
Section I To be filled out by tank removal contractor:
Tank Removal Contractor: od~s Dyk~, ~nc_ "
Address: Pozeox 6157 Phone. ~:
Bakersfield, Ca. 93386
Date Tank(s) Removed: 6/14/91 No. of Tank(s): 1
Section ~ To be fi]led out by contractor "decontaminating" tank(s):
Tank "Decont~ination" Contractor: odis Dykes~ Inc.
Address: PO Box 6157 Phone ~: 805-322-3039
Bakersfield, C.a 93386 Z~:
Tank Size L.E.L. Tank Size L.E.L.
p~nn
Authorized representative of the contractor certifies by signing below that the
tank(s) have been decontaminated in accordance with Kern County Environmental
Health Services Department requirements.
Signature- Title ......
Section 3 To. be filled out and signed by an authorized representative of the approved disposal or recycling facility accepting the tank(s):
Facility Name: Valley Tree & Construction
Address: 4233 uinn Road Phone #: 399-1783
!rsfield, CA. Zi~: 93308
.Date June 14, 1991 No. of Tank(s): 1
Si Title: Bookkeeper
Author1 zed Representer ive)
· * * MAILIN8 INSTRUCTIONS: Fold and ~ap.~o'. F~: (~5)
KERN COUNTY ENVZRON~ENTAL HEALTH ~~ DEP~[~
2700 "~" STREET, SU[TE. 300.
BAKERSFIELD, CALIFORNIA .... 93301
ATTN= UN~E~ROUN~ ~N~ 8EOTZO~
ODI 'DYKES, INC.
BO. BOX 6157, ~KERSFIELD, '~LIFORNIA
PhOne (805) 322~039 F~ (805) 322.6132
9'91
.Tank ~emoval Procedure
2. ~o~t Permit
3. Notify necessary agen~-ies prior to commeacing work
5. Plush lines from t~k
5. R~ove lines fr~ t~
7. D~ ice ~ank to inert
8. Triple rinse with ste~ clever
(Ch~ck LEL level after each rinse ~o below ~%' after ~hird rinse)
9. Dispose with vacu~ truck and haul to apprOVed disposal site
7 0. R~cve .tank and inspect but=om upon aDD-oval by inspector
7~. Load and haul tank to disposal site
7 2. Backfill
RES( RCE MANAGEMENT AG qCY
Environmental Health Sen~ces Department.
RANDALL L. ABBOTT STEVE McCA! I Fy, REHS, DIRECTOR
DIRECTOR ^i, Pollution Control District
DAVID PRICE !!i V~LLU~ J. RODDY, APCO
ASSISTANT DIRECTOR Planning & Development Se~ices Department
TED dAMES, AICP, DIRECTOR
ENVIRONMENTAL HEALTH SERVICES DEPARTMENT
PERMIT FOR PERMANENT CLOSURE PERMIT NUMBER A 145625
OF UNDERGROUND HAZARDOUS
SUBSTANCES STORAOE FACILITY
FACILITY NAME/ADDRESS: OWNER(S) NAME/ADDRESS: CONTRACTOR:
Odis Dykes, Inc. Odis Dykes, Inc. Odis Dykes, Inc.
313 Daniels Lane 313 Daniels Lane 313 Daniels Lane
Bakersfield, CA 93307 Bakersfield, CA 93307 Bakersfield, CA 93307
License #528384
Phone: 805-322-3039 Phone: 805-322-3039
PERMIT FOR CLOSURE OF PERMIT EXPIRES June 12, 1991
1 TANK(S) AT ABOVE APPROVAL DATE March 12, 1991
LOCATION APPROVED BY ~-~--,~ ~'
Carrie Oeorgi ' '
Hazardous Materials' Specialist
............................................................................................... POST ON PREMISES ................................................................................................
CONDITIONS AS FOLLOWS:
1. It is the responsibility of the Permittee to obtain permits which may be required by other regulatory agencies prior to beginning work (i.e., City Fire and Building
Departments).
2. Permittee must notify the Hazardous Materials Management Program at (805) 861-3636 two working days prior to tank removal or abandonment in place to
arrange for required inspections(s).
3. Tank closure activities must be per Kern County Environmental Health and Fire Department approved methods as described in Handbook UT-30.
4. It is the contractor's responsibility to 'know and adhere to all applicable laws regarding the handling, transportation or treatment of hazardous materials.
5. The tank removal contractor must have a qualified company employee on site supervising the tank removal. The employee must have tank removal experience
prior to working unsupervised.
6. If any contractors other than those listed on permit and permit application are to be utilized, prior approval must be granted by the specialist listed on the
permit. Deviation from the submitted application is not allowed.
7. Soil Sampling:
a. Tank size less than or equal to 1,000 gallons - a minimum of two samples must be retrieved from beneath the center of the tank at depths of
approximately two feet and six feet.
b. Tank size greater than 1,000 to 10,000 gallons - a minimum of four samples must be retrieved one-third of the way in from the ends of each tank
at depths of approximately two feet and six feet.
c. Tank size greater than 10,000 gallons - a minimum of six samples must be retrieved one-fourth of the way in from the ends of each tank and beneath
the center of each tank at depths of approximately two feet and six feet.
8. Soil Sampling (piping area):
A minimum of two samples must be retrieved at depths of approximately two feet and six feet for every 15 linear feet of pipe run and under the dispenser area.
2700 "M" STREET, SUITE 300 BAKERSFIELD, CALIFORNIA 93301 (805) 861-3636
FAX: (805) 861-3429
PERMIT FOR PERMANENT CLOSURE PERMIT NUMBER A 1456-2~
OF UNDERGROUND HAZARDOUS ADDENDUM
SUBSTANCES STORAOE FACILITY
9. Soil Sample analysis!
a. Ail soil samples retrieved from beneath gasoline (leaded/unleaded) tanks and appurtenances must be analyzed for benzene, toluene, XYlene, and total
petroleum hydrocarbons (for gasoline).
b. All soil samples retrieved from beneath diesel tanks and appurtenances must be analyzed for total petroleum hydrocarbons (for diesel) and benzene.
c. Ali soil samples retrieved from beneath waste oil tanks and appurtenances must be analyzed for total organic halides, lead, oil and grease.
d. All soil samples retrieved from beneath crude oil tanks and appurtenances must be analyzed for oil and grease.
e. All soil samples retrieved from beneath tanks and appurtenances that contain unknown substances must be analyzed for a full range of substances
that may have been stored within the tank.
f. All soil samples retrieved from beneath tanks and appurtenances that contained furfuryl alcohol resin must be analyzed for phenols, formaldehyde
and furfuryi alcohol.
10. The following timetable lists pre- and post-tank removal requirements:
Complete permit application submitted At least two weeks prior to closure
to Hazardous Materials Management Program
Notification to inspector listed on permit of date Two working days
and time of closure and soil sampling
Transportation and tracking forms sent to Hazardous No later than 5 working days for transportation and 14 working
Materials Management Program. All hazardous waste days for the tracking form after tank removal
manifests must be signed by the receiver of the
hazardous waste
Sample analysis to Hazardous Materials Management No later than 3 working days after completion of analysis
Program
11. Purging/Inerting Conditions:
a. Liquid shall be pumped from tank prior to purging such that less than 8 gallons of liquid remain in tank. (CSH&SC 41700)
b. Tank shall be purged through vent pipe discharging at least 10 feet above ground level. (CSH&SC 41700)
c. No emission shall result in odors detectable at or beyond property line. (Rule 419)
d. No emission shall endanger the health, safety, comfort or repose of any person. (CSH&SC 41700)
e. Vent lines shall remain attached to tank until the inspector arrives to authorize removal.
RECOMMENDATIONS/GUIDELINES FOR REMOVAL OF UNDERGROUND STORAGE TANKS
This department is responsible for enforcing the Kern County Ordinance Code, Division 8 and state regulations pertaining to underground storage tanks.
Representatives from this department respond to job sites during tank removals to ensure that the tanks are safe to remove/close and that the overall job performance
is consistent with permit requirements, applicable laws and safety standards. The following guidelines are offered lo clarify the interests and expeclalions for Ibis
department.
1. Job site safety is one of our primary concerns. Excavations are inherently dangerous. It is the contractor's responsibility to know and abide by CAL-OSHA
regulations. The job foreman is responsible for the crew and any subcontractors on the job. As a general rule, workers are not permitted in improperly sloped
excavations or when unsafe conditions exist in the hole. Tools and equipment are to be used only for their designed function. For er. ample, backhoe buckets
are never substituted for ladders.
2. Properly licensed contractors are assumed to understand the requirements of the permit issued. The job foreman is responsible for knowing and abiding by
thc conditions of the permit. Deviation from thc permit conditions may result in a stop-work order.
3. Individual contractors will be held responsible for their post-removal paperwork. Tracking forms, hazardous waste manifests and analyses documentation are
necessary for each site in order to close a case file or move it into mitigation. When contractors do not follow through on necessary paperwork, an
unmanageable backlog of incomplete cases results. If this continues, processing time for completing new closures will increase.
Accepted By:. ~f'{~O~e~~R ORAGENT "~1.~.-- q iDATE
CG:ch
georgi\1456-25.pta
ODIS DYKES, INC.
GRADING - PAVING - TRUCKING - DEMOLITION
P.O. BOX 6157, BAKERSFIELD, CALIFORNIA 93386
Phone (805) 322-3039 Fax (805) 322-5132
Contractors License #528384
March ~2, 1991
Tank removal pEDcedure
1. Obtain removal permit from the Health Department.
2. Post permit
3. Notify necessary agencies prior to commencing work
4. Expose tank and piping with backhoe
5. Flush lines from tank
6. Remove lines from tank
7. Dry iceetank to inert ~FO0~O
8. Triple rinse with steam cleaner and dispose with vacuum truck ~L 74 Oj%Po~4t ~
9. Remove tank~and inspect bottom upon approval by inspector
10. Load and haul tank to disposal site
Backfill
KEI~I COUNTY RESOURCE MANAGEMENT ACENCY INTERNAL USE ONLY= ....
(8o5)a61-36:~6
(FILL OUT CNE APPLICATICN PER FACILITY)
APPLICATION.FOE PERMIT FOR PERMANENT
c, REX AN .ENT OF
HAZAROOJ$ S~.JBSTANCE STORAGE FACILITY
THIS APPLICATION I$ FOR: [v~ REMOVAL, O~ [] ABANDONMENT IN PLACE
A: FACILITY IIf:CI~TI~
(laul.
I
STiiEL'T: Union '& Hwy
'Pt'll~ I: (805) 322-3O39 CITY: i3akersfie].d ZIP: 9330'7 -
(]iliEil: Od±s Dykes [Al:~I~8: Same as above I STATE: CA.
i
I
PtlC~ I: (805) 322-3039 CITY: ~3aJ~ersfie].d [ ZiP: 9330'7
~1: (805) 322-3039 [CITY: Bakersfield IZIP: 9330'7
~$T~11~TE: A.$.A.P. C~LIFC~IALICDiSEI'YPE&I: A 528384
90-488861-01
~ I: B.C. Laboratoz~ 327-49tl CITY: 4100 Pierce Rd Bak IZIP: CA 933
~ I: B.C. Laborato~ 327-491t CITY: 4100 ?ierce R~ BaAh ZIP: ~a 9330
C:HEMICAL COMPOSTION OF MATERIALS STORED:
TANK # VOLUME CHEMICAL STORED DATES STORED CHEMICAL FORMERLY STORE£'
~1 2]_5_00 qal. diesel '76 TO 88
I0'
! I~TER TO F~CIL~TY P~OVIDED BY: CaLifornia water service I IS I~IJIOIATER NI~IN 50 FEET? Y OR N
no
NEAI~T NATER I~LLq;~VE DISTANCE IF iIIl~l1500 FEET: none ! SOIL TY~ AT FACILITY: sa~ loam
8~$ F~R ~OIL TI~ A~D GRDLI~TER OI~IH OLql~I~TI~: ~ern ~ountv Agency Zmprovement District #
TOTALNLI~I~EROFSAI~:~J~TO~ANALYZEO:,'? ~ ~,~ I,~!~10~""~: T.P.H. (oil_ grease & Benzen~
DBXI~q'~I~TI~ I:~(/[I~: Rinse with high pressure water
~1: (805) 322-3039 Gibson Oil & Refining
9ISK~ ~27~0 ~ IA~($): Recycling ~I~ ~I~ ~ ~($): Valley Tree
~PtEAS~ COMPt~T£ IH~ REVF3~ $IO~ O~ THIS AP~tICATION 8~=0~ SUSMIT~IN~
T~U5 AND
PROVIDE DRAWING O1! r,~ CAL LAYOUT OF FAC ~G SPACE PROVIDED BELOW.
ALL OF THE FOLLOWING INFORMATION MUST BE INCLUDED IN ORDER FOR THE
APPLICATION TO BE PROCESSED:
TANK(S), PIPING & DISPENSER(S), INCLUDING LENGTHS'&
.DIMENSIONS.
PROPOSED SAMPLING LOCATIONS DESIGNATED BY THIS SYMBOL
NEAREST STREET OR INTERSECTION
ANY WATER WELLS OF SURFACE WATERS WITHIN 100' RADIUS OF
FACILITY
NORTH ARROW
R E C E I P T PAGE 1
03/08/91 Invoice Nbr. 1 46586
9:25 am KERN COUNTY PLANNING & DEVELOPMENT
2700 'M' Street
8akensfie]d, CA 93301 Type of Order N
(805) 861-2615
CASH REGISTER ODIS DYKES INC
Customer P.O.~ Nth By Order Oa~e Ship Date Via Terms
H0308911 YKN 03/08/91 0S/08/91 DD NT
L~ne Oescr~pC~on Quantity Pr~ce Unfit O~sc Tota]
~ OERMIT TO CLOSE/ABANDON i 250.00 E 250.00
170G
Order Total 250.00
Amoun~ Due 250.00
Payment Made By Check 250.00
THANK YOU !
i 03/08/91 Invoice Nbr~ 1' 46586'
9:25 am KERN COUNTY PLANNING & DEVELOPMENT
2700 'M' Street
Bakersfield, CA 93301 Type of Order N
(805) 861-2615' ' ,~. :: .~ ".:':-'
C'~H REGISTER ODZS DYKES INC
,Customer P.O.~ I N'tn 8y IOrder...Da~e Shffp Date Via I Terms
H0308911 i YKN i 03/08/91 03/08/91 DD I NT
:_ine,..De$crip~fion Quen%ffty price Unit Disc Totaq
~ PERMZT TO CLOSE/A8AHDON i 250.00 E 250.00
... 170G' ...
Order Tot'at 250°00
Amoun~ Due 250'00
Paymen~ Made By Check ' 250.00' '
"~IHANK TCU!