HomeMy WebLinkAboutMITIGATION
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Hazardous Materials/Hazardous Waste Unified Permit
, CONDITIONS OF. ·PERMIT ON REVERSE SID~
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Permit 10 #:: 015-000-001573
.ALS RADIATOR SERVICE
LOCATION: 249 S UNION AVE
Issued by:
Bakersfield Fire Department
OFFICE OF ENVIRONMENTAL SERVICES·
1715 Chester Ave., 3rd Floor Approved by:
Bakersfield, CA 93301
Voice (661) 326-3979
FAX (661) 326-0576 Expiration Date:
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Issue Date
June 30, 2003
FIRE CHIEF
RON FRAZE
ADMINISTRATIVE SERVICES
2101 oW Street
Bakersfield. CA 93301
VOICE (661) 326-3941
FAX (661) 395-1349
SUPPRESSION SERVICES
2101 °Ho Street
Bakersfield. CA 93301
VOICE (661) 326-3941
FAX (661) 395-1349
PREVENTION SERVICES
1715 Chester Ave.
Bakersfield. CA 93301
VOICE (661) 326-3951
FAX (661) 326-D576
ENVIRONMENTAL SERVICES
1715 Chester Ave.
Bakersfield. CA 93301
VOICE (661) 326-3979
FAX (661) 326-D576
TRAINING DIVISION
5642 Victor Ave.
Bakersfield. CA 93308
VOICE (661) 399-4697
FAX (661) 399·5763
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July 5, 2000
Mr. Elmer Ezell
6201 Wright Ave
Bakersfield, Ca 93308-2031
RE: AI's Radiator, 249 South Union Ave
Dear Mr. Ezell:
This is to infonn you that this department has reviewed the result of the
Subsurface Investigation dated June 5, 2000 associated with the underground tank
removals which reportedly occurred in the early 1080's.
Based upon the infonnation provided, this department has detennined that
appropriate response actions have been completed, that acceptable remediation
practices were implemented, and that, at this time, no further investigation, remedial
or removal action or monitoring is required at the above stated address.
Nothing in this detennination shall constitute or be construed as a
satisfaction or release from liability for any conditions or claims arising as a result
of past, current, or future operations at this location. Nothing in this detennination
is intended or shall be construed to limit the rights of any parties with respect to
claims arising out of or relating to deposit or disposal at any other location of
substances removed from the site. Nothing in this detennination is intended or shall
be construed to limit or preclude the Regional Water Quality Control Board or any
other agency from taking any further enforcement actions.
This letter does not relieve the tank owner of any responsibilities mandated
under the California Health and Safety Code and California Water Code if existing,
additional, or previously unidentified contamination at the site causes or threatens to
cause pollution or nuisance or is found to pose a threat to public health or water
quality. Changes in land use may require further assessment and mitigation.
If you have any questions regarding this matter, please contact me at (661)
326-3979.
Sincerely,
~~~
Howard H. Wines, III
Hazardous Materials Technician
Office of Environmental Services
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PRELIMINARY LEVEL 2
SUBSURFACE INVESTIGATION
AT
AL'S RADIATOR
247 S. UNION AVENUE
BAKERSFIELD, CA
Prepared by:
CONSOLIDATED TESTING LABORATORIES, INC.
603 EAST WORTH AVENUE
PORTERVILLE, CA 93257
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June 5, 2000
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CONSOllDATfD TfSTING lABORATORlfS, INC.
Soils And Materials Testing
Geotechnical And Environmental Drilling
Field Inspection
June 5, 2000
File No. 4647-00
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Mr. Elmer Ezell
6201 Wright Avenue
Bakersfield, CA 93308-2031
PROJECT:
AI's Radiator, 247 S. Union Avenue, Bakersfield, CA
SUBJECT:
Preliminary Level 2 Subsurface Investigation to further evaluate the soil
conditions at various areas of the subject site previously identified in the Phase 1
prepared by Professional Service Industries, Inc.
Dear Mr. Ezell:
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In accordance with your request, we have completed the Preliminary Level 2 Subsurface
Investigation at the subject site. The areas investigated were previously identified in the Phase 1
Environmental Site assessment report prepared by Professional Service Industries, Inc. (PSI)
dated March 28, 2000.
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Our report presents analytical laboratory test results conducted on thirteen (13) selected soil
samples collected from thirteen (13) testhole borings drilled at the site. The testhole borings were
vertically drilled to various depths using a Mobile B-80 drill rig with 3 W' J.D. hollow stem augers
and hand auger with 2" J.D. drive tube sampler.
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Our field investigation and laboratory analyses were conducted in accordance with the California
LUFT Manual Guidelines, E.P.A. Regulations, A.S.T.M. test methods and County Health
Department requirements.
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Wayne F. Harris
R. C.E. 15342, Exp. 3/31/01
If you have any questions or need additional information, please contact this office.
603 East Worth Auenue · 559-781-0571 · Porteruille, CA 93257
FAX: 559-782-8389
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TABLE OF CONTENTS
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SCOPE OF WORK. ............ ...... ... ............. ........... ... .., ..................... .......... 1
SITE LOCATION................................. ................................................... 1
SITE DESCRIPTION ... ............ .................. ...... ................................. ........ 1
SITE HISTORy...... .................... ................ ............................................ 2
GEOLOGY ............................................................................................ 2
HYDROGEOLOGy......... ............ ............................................................. 3
SUBSURFACE SOIL CONDITIONS ......... .................. '" ...... .................. ...... 4
FIELD INVESTIGATION AND PREPARATION ............................................. 4
TESTHOLE BORING LOCATIONS. ..................................................... ...... 5
FIELI> INVESTIGATION ~THOI>S .......................................................... 7
TESTHOLE BORING CONTAINMENT ....................................................... 10
LABORATORY TESTS .................. .......................................................... 10
FINDINGS ................................................ ..................... ...... ............. ..... 11
CLOSING STATEMENT................................................... ....................... 13
FIGURES
VIClNITY MAP............................................................................ FIGURE 1
TESTHOLE BORING LOCATIO~ 1vIJ\J>.............................................. FIG~ 2
APPENDIX A
UNIFIED SOILS CLASSIFICATIO~ CHART
TEST BORING LOG LEGEND
TESTHOLE BORING LOGS
APPENDIX B
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SUMMARY OF LABORATORY ANALYSIS
CHAIN OF CUSTODY RECORD
REPORT OF ANALYTICAL RESULTS
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SCOPE OF WORK
The purpose of our preliminary Level 2 Subsurface Investigation was to further evaluate
the soil conditions at various areas of the subject property that were previously identified
in the March 28, 2000, Phase 1 Environmental Site Assessment Report prepared by
Professional Service Industries, Inc. (pSI). Based on the PSI investigation of the
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property, recommendations were made by PSI to evaluate impacts to the site ftom the
former gasoline and waste-oil underground storage tanks (USTs), radiator wash-rack
system, existing and former two (2) sumps, the vault at the southeast comer of the subject
site and the 20 foot by 20 foot radiator removal area.
SITE LOCATION
The subject property is located at 247 South Union Avenue, Kern County, Bakersfield,
CA. The subject site is located on the northwest comer of the intersection of South Union
Avenue and Terrace Way.
SITE DESCRIPTION
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The property consists of approximately 0.52 acres, is generally flat, and developed with
commercial structures. The metal sided former service station building was built in the
mid to late 1950's. The metal framed three-bay automotive repair shop was built in 1985.
This information is discussed in detail in the executive summary of the Phase 1 report
prepared by PSI.
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SITE HISTORY
The site was utilized as a gasoline service station ftom mid-to-Iate 1950's to the late
1970's. In 1980, two gasoline USTs were removed and in 1981 one waste-oil UST was
removed. According to the Kern County Environmental Health Department (KCEHD)
and the City of Bakersfield Fire Department (CBFD), no records concerning the removal
exist. According to Mr. Elmer Ezell, owner of the subject site, the two gasoline USTs
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were located to the south of the service station portion of the on-site structure and to the
east of the three bay-shop. The waste-oil UST was located to the east of the two service
bays of the former service station. At the time of removal, the CBFD instructed Mr. Ezell
he could fill the USTs with concrete and abandon them in place, however, Mr. Ezell
removed the USTs and gave the USTs to a nearby rancher. Mr. Ezell indicated that no
soil sampling was conducted at the time of the removal ofthe USTs. Based on the lack of
file information with the KCEHD and CBFD and due to lack of soil sampling at the time
of removal of the USTs, the former USTs represent a recognized environmental condition
in connection with the subject site.
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GEOLOGY
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The subject site is located in the Great Valley Geomorphic Province in the southern San
Joaquin Valley. This portion of the San Joaquin Valley is bounded by the Sierra Nevada
mountains to the east and the Coast Ranges to the west. The structure of the San Joaquin
Valley is a synclinal trough with its axis off center to the west (Norris and Webb, 1976).
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The bedrock forming the basement beneath the property consists of Jurassic and
Cretaceous-age igneous and metamorphic rock of the Franciscan Formation that dip east
beneath the San Joaquin Valley. Pliocne to recent-age marine and non-marine clastic
deposits overlie the bedrock and extend to depths between 5,000 and 15,000 feet below
ground surface. Shallow soil stratigraphy in the Kern County area is primarily sandy soils
and sand-silt combination soils.
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HYDROGEOLOGY
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The subject site is located in the San Joaquin Valley groundwater basin, which is part of
the San Joaquin Basin Hydrologic Study Area (SA). Twenty-six groundwater basins and
areas of potential groundwater storage have been identified in the San Joaquin Basin SA.
The SA is bounded by the Sacramento-San Joaquin Delta tot he north, the Sierra Nevada
to the east, the Tehachapi mountains to the south, and the Coast Ranges to the west.
Groundwater in the vicinity of the subject site is found within the San Joaquin regional
aquifer system, and unconfined to semi-confined aquifer system within the older alluvium
and deeper continental deposits. According to information obtained fÌ'om the Bakersfield
Water Service, groundwater beneath the site is presently at a depth of approximately 100
feet below ground surface and flows toward the southwest.
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SUBSURFACE SOIL CONDITIONS
According to the USDA Soil Survey of Kern County, 1971, native soil in the vicinity of the subject
site is Kirnberlina-Urban land-Cajon complex. KimberIina-Urban land-Cajon complex is a deep
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and well drained soil formed on recent alluvial fans and plains. It formed in alluvium derived
dominantly from granitic and sedimentary rock. Permeability is moderately slow and available
water holding capacity is very low to moderate.
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Subsurface soils encountered in our testhole borings generally consisted of Sandv Silt. and Silty
Sand (SM), Sand (SW) and Sandy Silt (ML). Soils encountered at sampling intervals ranged from
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loose to medium dense and dense, in accordance with the Standard Penetration Test Correlation
Chart.
FIELD INVESTIGATION AND PREPARATION
Underground utility locations were marked at the site by Underground Services Alert
(USA prior to drilling operations. The testhole borings were probed to a depth of four (4)
feet to reduce the possibility of damaging any underground utilities or obstructions.
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Boring B 13 was located in the field as close as allowable to the abandoned dry well to
pennit drill rig access safely due to overhead electrical power lines. The remainder of the
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borings were drilled in the Consolidated Testing Laboratories, Inc. proposed locations.
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TESTHOLE BORING LOCATIONS
(Previous UST Locations and Existing Abandoned Fuel Dispenser Islands)
Bl - was located at the west end of the previous two (2) approximately 8,000 gallon
gasoline UST locations.
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B2 - was located at the east end of the previous two (2) approximately 8,000 gallon
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gasoline UST locations.
B3 - was located at the west side of the existing western abandoned fuel dispenser island.
B4 - was located at the east side of the existing eastern abandoned fuel dispenser island.
B5 - was located at the approximate center of the previous one (1) approximately 500
gallon waste oil tank location.
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(Previous Abandoned Sumps and Former Hydraulic Lifts)
B6 - was located at the northeast corner of the former service station building within 12
inches of the northern edge of sumps.
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(Previous Abandoned Sumps and Former Hydraulic Lifts) - Continued
B7 - was located near the center of the former service station building within 12 inches of
the patched concrete from the removed hydraulic lift.
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B8 - was located at the northern section of thè three-bay automotive repair shops,
approximately 3 feet from the former hydraulic lift.
B9 - was located near the center section of the three-bay automotive repair shop,
approximately 8 inches from the previous abandoned sump and within 2 feet from the
existing operational hydraulic lift.
(Radiator Removal Area and Radiator Wash Rack)
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BIO - was located at the north end of radiator removal area near the vats between the
concrete slab and asphalt pavement.
Bll - was located near the center of the radiator removal area slab, approximately 3 feet
from the drainage inlet grate area.
B12 - was located near the radiator wash-rack area, approximately 2 feet 1Ì'om the racks.
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(Abandoned Drv Well)
B-13 - was located near the previously abandoned dry well at the southeast comer of the
property.
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FIELD INVESTIGATION METHODS
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Drillin2 Methods
Consolidated Testing Laboratories, Inc. used a truck mounted B-80 mobile drill rig with 7
inch outside diameter, 3.25 inside diameter hollow-stem augers, AASHTO Designation
T251-77 to drill the testhole borings. The augers were steam cleaned prior to and after
drilling the testhole borings.
Field SamDlin2 Procedures and Soil Classification
Personnel involved in collecting the soil samples and classifying the soils were under direct
supervision of the project engineer and full experienced in the field of environmental and
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geotechnical drilling. Soil samples and drill cuttings from borings Bl, B2, B3, B4, B5,
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and B13 were described in accordance with the Unified Soil Classification System.
Drilling and soil sampling was performed on May 15,2000. The investigation consisted of
drilling thirteen (13) testhole borings. Undisturbed soil samples were obtained by driving
a 2 inch I.D. California Modified Split Spoon Sampler at the selected depth intervals. The
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sampler was driven using a 140 lb. Hammer falling a distance of 30 inches and recording
blow counts for each 6 inch increment of drive on test boring logs.
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At selected depth intervals three (3) 2.0 x 6.0 inch brass sample tubes were inserted into
the sampler prior to use. The sample tubes and split spoon sampler were pre-cleaned with
Alconox detergent was and water prior to use and between each sampling interval.
Sterilized brass sample tubes were stored in clean plastic bags prior to use.
The boring locations within the existing buildings that were not accessible to the drill rig
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were hand sampled using a hand auger and hand drive tube sampler.
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Soil samples for laboratory analysis were collected at selected depth internals depending
on the boring locations. The testholes were drilled to a minimum depth of 5 feet and to a
maximum depth of 31.5 feet below surface grade.
After the soil samples were collected, the sample tube trom the bottom of the sampler was
immediately sealed in the field by placing teflon covers over the open ends of the tube and
placing plastic caps over the teflon covers. A cloth adhesive tape was placed around the
plastic caps to ensure that the caps were secured and an air-tight seal was maintained.
Field screening was performed using a portable photoionization detector (PID) by placing
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the split-sample in a plastic zip lock bag, breaking up the sample in the sealed bag, and
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then inserting the PID probe into the bag to measure the concentration ofvoIatile organic
compounds (VOCs) in the head space.
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All soil samples were labeled appropriately in the field. Labels included the following
infonnation; locatio~ depth, date, time, job number and field identification number.
Samples were placed immediately in an insulated storage container cooled with blue ice.
The temperature inside the storage container was maintained at 4 degrees Celsius/39.2
degrees Fahrenheit and monitored with a thermometer to ensure that the temperature
remained constant.
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A chain of custody record was maintained with the samples until delivered to the
laboratory. The chain of custody record included the following: Boring number, depth,
date, time, job number, temperature of sample container, field identification number,
analyses required, and personnel collecting samples. A field log book was maintained
containing essentially the same information as the chain of custody record with the
addition of any field observations about the sample.
Soil samples were delivered to Castle Laboratory, a state certified hazardous waste
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testing laboratory within 24 hours after the samples were collected. The temperature was
maintained at 4 degrees Celsius in the insulated storage container prior to delivering to the
laboratory.
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Once samples were delivered to the laboratory, the chain of custody was signed by the
laboratory indicating that possession of the samples had changed. The soil samples were
analyzed within the 14 day period following collection.
TESTHOLE BORING CONTAINMENT
The borings were backfilled with native soil cuttings following completion of drilling
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operations.
LABORATORY TESTS
Selected soil samples were transferred to Castle Analytical Laboratory, 2333 Shuttle
Drive, Atwater, Californi~ and were tested for the following constituents:
TEST METHODS FOR LABORATORY ANALYSIS
DESCRIPTION (SOIL)
MINIMUM DETECTION
(parts per million)
TPH (gas) 5030/8015
1.0 ppm
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BTX&E EP A Method
5030/8020 and MTBE
.005 ppm
Clycol Test
30 mglkg
Total Lead
3.0 mglkg
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FINDINGS
The findings that follow are the results of the May 15, 2000, field investigation and
laboratory analysis.
Field Investie:ation and Laboratory Analysis Findine:s
1.) Test boring Bl and B2 located within the approximate area of the previous two (2)
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gasoline fuel USTs were drilled to a maximúm depth of 31.5' below ground surface.
The approximate location of the borings were field located with the assistance of Mr.
Elmer Ezell based on his previous knowledge of the installation and removal of the
USTs. Soil samples collected at 5' depth intervals beginning at 15' were field
screened using an HNU P.I. detector and also visually observed. Field monitoring and
observation indicated no detection and no petroleum odor or staining. Laboratory
analysis conducted on samples Bl- 31.5' and B2 - 31.5' indicated N.D. for BTX&E,
MTBE and T.P.H. (gas). During drilling operations at Bl and B2, import fill material
with aggregate rock mixture and decayed construction lumber was encountered in the
upper 0' -10' indicating that the borings were within the tank excavation.
2.) Borings B3 and B410cated adjacent to the two (2) existing abandoned fuel dispenser
islands were drilled to a maximum depth of 10.5' below ground surface. Field
monitoring on soil cuttings indicated N.D. and no petroleum odor or staining.
Laboratory analysis conducted on samples B3-10.5' and B4- 10.5' indicated N.D. for
BTX&E, MTBE and T.P.H. (gas).
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3.) Boring B5 located near the center of the previous approximate 500 gallon waste oil
UST was drilled to a maximum depth of 15.5' below ground surface. Field monitoring
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on soil cuttings and samples indicated N.D. and no petroleum odor or staining.
Laboratory analysis conducted on sample Bl-15.5' indicated N. D. for BTX&E,
MTBE, T.P.H. (gas) and Total Recoverable Petroleum Hydrocarbons. The detection
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level for Total Lead was 5.1 ppm. The level recorded is consistent with normal
background levels in undisturbed subsoils.
4.) Boring B6-B9 were located near previous abandoned sumps and former hydraulic lift
locations, within the existing metal buildings at B6-5.5', B7-1O.5' B8-1O.5' and B9-
5.5', field monitoring on soil cuttings and samples indicated N. D. and no petroleum
odor or staining. Laboratory test results indicated all N.D. for Total Recoverable
Petroleum Hydrocarbons with the exception ofB6-5.5'. The detection level recorded
was 58 ppm and could be considered relatively low.
5.) Borings B10-B12 located within the existing radiator removal area and wash-rack area
were drilled to a maximum depth of 5.5' below ground surface. Field monitoring on
soil cuttings and samples indicated N.D. and no detectable odor or staining.
Laboratory analysis required for radiator coolant indicated all N.D. for Total Glycols.
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6.) Boring B 13 was located near the previously abandoned dry well at the southeast
comer of the property. The boring was drilled to a maximum depth of 21.5' below
ground surface. Soil samples were collected at 5' depth intervals beginning at 10.5'.
Field monitoring on soil cuttings and samples indicated all N.D. and no petroleum
odor or staining. Laboratory analysis indicated all N.D. for BTX&E, MTBE, T.P.H.
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(gas) and Total Recoverable Petroleum Hydrocarbons and Total Lead. The only fuel
constituent detected was Toluene 0.0056 ppm.
CLOSING STATEMENT
This report has been prepared for Ai's Radiator, 247 South Union Avenue, Bakersfield,
CA. The following findings rendered in this report are based on the field investigation and
laboratory testing of soil samples collected during this study; This report does not reflect
subsurface variations which may exist between sampling points. These variations cannot
be anticipated, nor could they be entirely accounted for, in spite of exhaustive additional
testing. Nor should this report be regarded as a guarantee that no further contamination,
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beyond that which could have been detected within the scope of the investigation, is
present beneath the said property. Under documented, unauthorized releases of hazardous
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materials, the remains of which are not readily identifiable by visual inspection and are of
different chemical' constituents, are difficult and often impossible to detect within the
scope of a chemical specific geotechnicaVenvironmental engineering, engineering geology,
and hydro-geology. No other warranty, either warranty, either expressed or implied is
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This opportunity to be of service is appreciated. Should you have any questions or
comments regarding this report, please contact this office at your convenience.
CONSOLIDATED TESTING LABORATORIES, INC.
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SCALF.
REFERENCE:
U.s.G.s. GOSFORD. CALIFORNIA 1978
PHOTOREVISED 1987
SITE LOCATION
AI.'S '~ADIATOR
247 SOUTH UNION AVE,
BAKERSFIELD. CALIFORNIA
PROJECT NUMBER: 575-0E047
DA TE: 11 24 99 CKD BY: FIGURE NO: 1
FILE NO: OE047 RA WN BY: P HUMPHREY
e
GALBRAITH VAN LINES
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DRUM STORAGE
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CANOPY
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LIFTS
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COMMERCIAL
OFFICES
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1- - - - fUEL-
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I 82 $ S 8f I
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PREYIOUS
UST LDCATlßN5
3 BAY SHOP
POSSIBLE
DRY WELL
B/3 5~
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TERRACE WAY
\ ..'
¡
COMMERCIAL
I OFFICES
J VACANT LAND I
~ I
I
&í /
(, !
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I; LEGEND
S Approximate location of testhole
I
I borings drilled on 5/15/00
~!
LEGEND
.-.-.-..-..-.
[ "
'~. .
I IfTIIIII ". "
111111\ 11 V 7 ENVIRONMENTAL
114111\1111
11111111111 AREAS OF STAINING IpS; CEOTECHNICAL
I 1111111111 CONSTRUCTION
¡ 11111111\ CONSUl. TING 'F:NGIN¡':F:RING' TESTINC
.J..1.L1.LJ·
---.--..
.. ----.- .- ---"'-.' . .-, N - -- - ..~.. - .-...-.-.......-.... ..
SITE LOCA nON
í" .... -1 AL'S RADIATOR
I I POSSIBLE FORMER USTs 247 SOUTH UNION AVENUE
BAKERSFIELD. CALIFORNIA 93307
- L .__ "_' .J PROJECT NUMBER: 575-9G076
03/24/~TCKD Bÿ~--"VIGURE -.---...
I DATE: NO.: 2
tiLE NO: OE047-2 DRAWN BY: G. ELIZONDO
UNIFIED SOIL CLASSIFICATleYSTEM
e
I :~
Major Divisions Group Typical names Laboratory classification criteria
Symbols
ç; GW Well graded gravels, graveH;and "'z"'~~~ - £22. greater than 4; C c (D.> )2
~Q mixtures, little or no fines Cu - -2..- between 1 and 3
~ ¡r", -Oa"'lC'9 D10X D60
_Ii¡ ~ ~ o ¡;¡ \II !I ª 010
I» " 5~ N~~~~'~'
.a ~
'" :r Ì~ Poorly graded gravels, gravel-sand a:"''''~oa:
... I» GP Not meeting all gradation requirements for GW
~'" mixtures, little or no fines ...._Vlwr.::J.,
im n"'a:!a:n
~ '" == å¡.., nå
~2.o : .., n m C'D ~
0 : n nt '" ::J \Q
¡;¡ . n ¡¡ ¡ ~rf.~~
;. .>g~ d !
~C) Atterburg limits below" A"
I» ii, $ ill" ~~ Silty gravels, gravel-sand-silt
'" GM* I--- III . il line or PJ. less than 4
~ ~ - "S! '" mixt ures
¡s.~ o ~ iñ U Above" A" line with P.I. between
g, .!!.õ ;;~! 4 and 7 are borderline cases
3 '" !.:- ~ ¡ ¡ i Ii
~g iii' ~3'" Atterburg limits above" A" requiring use of dual symbols
'" I» g ~ Clayey gravels, gravel-sand·day
¡¡¡. ¡¡¡ GC line with P.I. greater than 7
-" ¡;¡ mixtures
iiï ,¿, '"
~i
<.0'"
'" '" I
... 0. _ (030 )2 between 1 and 3
i~ '2 Well-graded sands, gravelly sands, ~ ~ k !: [ 060 greater than 6; C c
'" iñ =n SW little or no fines Cu-- I
z ~ '" ëi' g'.Z.::E ifn 0,0 o,OX 060 I
o I» i~C) N~ I
P ~ ~ ... '"
~ ¡¡ II! ""'0 8'"
I» ~ ¡f.~ ~ !!I.
0 = :r ::0 a.
'" I»
'" ... '" '" '" Poorly graded sands, gravelly sands, :;¡ ~(" ~
~. il ! SP little or no fines '" "'0 Not meeting all gradation requirements for SW
'" '" - IX ~.
¡:¡- zg,~ ii! {!..
~ Pnà. .c
~2U) 5. n I
¡~ d 5' 0 I
æ-$ I»
SM* - Silty sands, sand-silt mixtures <.0 $ Atterburg limits below "A"
~- ]à. 0. line or P.L less than 4 Limits plotting in hatched
!!I. ~ & <.0
N ~ g,~i u ¡¡¡ zone with P.l, between 4 ard
~g ::!IE~ ~ ~. 7 are borderline cases
"'..:r 3 0.
iñ ~0I3' g- requiring use of dual symbols
~~ Clayey sands, sand-clay mixtures iñ Atterburg fimits above" A"
r::: ~ SC : line with P.I. greater than 7
a
ML Inorganic silts and very fine sands,
rock flour, silty or clayey fine sands,
? or clayey silts with slight plasticity 60 V
E
6-
0.
-VI
3' ~ Inorganic clays of low to medium
~ ;:;-'"
-I» CL plasticity, gravelly clays, sandy clays, SO
0 to '"
õI b1 ~ silty clays, lean clays V
;. ~¡¡; CH
I» m,<
'" '" '"
~ VI /
,g 40
g, )( /
3 OL Organic silts and organic silty clays Q)
I» "T1 of low plasticity "0 /
íiíf .5
¡¡¡:,¿, »
Dr !1. .... 30 ;g¡
~ ii ? Inorganic silts, micaceous or dlato- 'ü If
1»0. E MH maceous fine sandy or silty soils, :¡:¡
1i'ts ;. en OH and MH
:ii 0. elastic silts n:I
i' ~~ c:: ~;.~
'" -. ~ 20
z .;¡ /
? ;
Q
~ ~n Inorganic clays of high plasticity, CL
0 :~ CH tat clays /
ill :r'"
1i" !: 10
! VI 1/
,g CL-ML 7
ML and OL
OH Organic clays of medium to high 1/
plasticity, organic silts 0
0 10 20 30 40 SO 60 70 80 90 100
t!li¡x Liquid limit
106 'Pt
i:f~~ Peat and other highly organic soils Plasticity Chart
P··.,
¡"
t"'··
'::\~
I"
. Division of GM and SM groups into subdivisions of d and u are tor roads and airfields only. Subdivision is based on Atterburg limits;
suffix d used when LL. is 28 or less and the P.I. is 6 or less; the suffix u used when L.L Is greater than 28.
-Sorder1ine classifications, used tor solis processing characteristics of two groups, are designated by combination of group symbols.
For example: GW-GC, well-graded grawl-sand mixture with clay binder.
CONSOLIDATED TESTING LABORATORIES INC"
PROJECT: Ai's Radiator
247 S. Union Avenue
Bakersfield, CA
e
~L CONSOLIDATED TESTING
l.; (, . LABORATORIES, INe
603 E. WORTH AVENUE
PORTERVILLE, CA 93257
(559)781-0571 *FAX(559)782-8389 BY:
BORING LOG NUMBER B 1 (Previous UST location)
JOB NO.:
DATE:
464 7-00
5/15/00
D.Harris
rm.1
,.
II.
~ BLOW SAMPLE ...;:¡ PERCENT DRY
DEPTH "0 SOIL DESCRIPTION
~ COUNTS NO. Ocz: MOISTURE DENSITY
~~
0'_ 0"-2" Asphalt concrete pavement
l- .
-l-
I- 2"-5" Base Material
-I- Gravelly sand: light yellowish brown, moist, very fine
I- to very coarse, with granules & pebbles 2mm to 12mm
-I- in size
I-
-I- 5"-10" Base Material
l-
s' _ I- Decomposed granite; light gray, moist, fine to
l- very coarse grain size with occasional sub-rounded
-I- rock 2mm to 16mm in size
I-
-l-
I- SM 10"-6' Import fill material
-I- Sandv silt: dark yellowish brown, very fine to
I- coarse grain size with occasional granules
-l-
I- 2mm to 4mm in size, sub-rounded, slightly
10';"1- cohesive, no petroleum odor or staining
I-
-I- 6'-8' Import fill material
I- Silty sand and agl!Tegate rock mixture,
-l-
I- no petroleum odor or staining
-~
~ SM 8'-15' Silty sand: dark yellowish brown, moist, very
-- fine to very coarse grain size, with occasional
-
15'_ granules 2mm to 4mm in size, sub-rounded, no
4 petroleum odor (note: very moist at 10'-12'
- 4 SPS HNU indicating bottom of previous UST excavation)
6 0
-- SM
- 15' -20 Sandy silt: yellowish brown, moist, very fine
-- to medium grain size, approximately 35% to
- 40% sand, no petroleum odor or staining,
--
- loose to medium dense
20'_ Sand: light yellowish brown, moist, very fine to
7 SPS ML 20'-25'
9 HNU fine grain size, occasional dark yellowish brown
-
10 0 mottling, no petroleum odor or staining, medium
-- dense
-
-l-
I- SW 25'·30' Sand; yellowish brown, damp, very fine to coarse
-I- grain size, sub-rounded, no petroleum odor or
- staining, mediùm dense
25'_
13
- II SPS HNU
_13 0 30'-30.5' Gravelly sand; light yellowish brown, damp,
-- medium to very coarse grain size, with granules
- and pebbles 2mm to 10mm in size, sub-rounded,
-- \ no petroleum odor or staining, dense
-
- Terminated drilling at 30.5' no fTee standing
HNU
3°'-19 '"I.D. 0 ground water encountered
22 split spoon
23 sampler
f"
r:
LOCA TION: B 1 (See location map)
EQUIPMENT: Mobile B-80 drill rig with 3 1/4" J.D. hollow stem augers
PROJECT: AI's Radiator
247 S. Union Avenue
Bakersfield, CA
e
a1([ CONSOLlDA TED TESTING
. ,.. LABORATORIES,INe JOB NO.:
603 E. WORTH AVENUE
PORTERVILLE. CA 93257 DATE:
(559)781-0571 *FAX(559)782-8389 BY:
BORING LOG NUMBER 82 (Previous UST location)
4647-00
Sit SIOO
D.Harris
r~'
..
""
þ; BLOW SAMPLE ...;¡;:¡ PERCENT DRY
DEPTH -0 SOIL DESCRIPTION
~ COUNTS NO. °Clli MOISTURE DENSITY
0 rI}~
0'__
- . 0"-2" Asphalt concrete pavement
-
-
--
-
--
-
-- SM 0'-4' Sandv silt: yellowish brown, moist. very fine to coarse
-
S' _ grain size, with occasional granules 2mm to 4mm in
size, sub-rounded (note: rotton construction lumber
-- debris encountered at 2' -4')
-
--
-
--
- 4'-8' Import fill material
-l-
I- Aggree:ate base material: fme to very coarse sand
10' _ I- and #4 to 3/4" sub-rounded rock, no petroleum
I- odor or staining
-l-
I-
-l-
I- Silty sand, dark yellowish brown, moist, very fme
-l- SM 8'-10'
I- to coarse grain size, sub-rounded, no petroleum
-I- odor or staining
I-
15'_
S
- 4 SPS HNU
5 0
-l-
I- SM 10'-14' Sandv silt: dark yellowish brown, moist to very
-I-
~ moist, very fine to coarse grain size, slightly
-- cohesive, no petroleum odor or staining
- (note: very moist at 10'-12' indication bottom
20'_
6 SPS of previous tank excavation)
- 9 HNU
9 0
--
- 30' -30.5' Sand: light yellowish brown, moist, fine to very
-- coarse grain size with occasional granules and
-- pebbles 2mm to 6mm in size sub-rounded, no
- petroleum odor or staining, loose to medium
25'_ 7 dense
- 9 SPS HNU
13 0
-l-
I-
-I- \ Terminated drilling at 30.5' no tree standing
I- ground water encountered
-I-
HNU
30' -I" '"ID. 0
10 split spoon
11 sampler
I..
~-#..:
LOCA TION: 82 (See location map)
EQUIPMENT: Mobile 8-80 drill rig with 3 1/4" I.D. hollow stem augers
PROJECT: At's Radiator
247 S. Union Avenue
Bakersfield, CA
e
ill l CONSOLIDATED TESTING
" i ¡, LABORATORIES, IN<4þ JOB NO.:
603 E. WORTH AVENUE
PORTERVILLE, CA 932S7 DATE:
(SS9)781-0S71 °FAX(SS9)782-8389 BY:
BORING LOG NUMBER ill. (West fuel island)
4647-00
5/15/00
D.Harris
i
I
, PERCENT DRY
iii BLOW SAMPLE ,.;;:¡
DEPTH "0 SOIL DESCRIPTION
~ COUNTS NO. 0= MOISTURE DENSITY
0 me
0'__
- .
--
-
-
0" -6" Concrete slab
--
-
--
-
5' __
-
--
-
-
-
--
- SM 6"-10.5' Silty sand: moist, very fine to coarse grain
- size sub-rounded, no petroleum odor
7
10' _ 8
9 HNU
-- 0
~
-I-
~
-l-
I-
-I-
'""
IS'_,""
'""
-l-
i-
-l-
I-
-,""
-
--
-
20'__
-
--
-
-
-
--
-
--
-
25'_ _
-
--
I- Terminated drilling at 10.5' no free standing
-I- ground water encountered
~
-,"" ,
-
30'_
R
r;'·~~
t";,',
~~;3
>::
¡ ",
I I
I
LOCA nON: ß3 (See location map)
EQUIPMENT: Mobile ß-80 drill rig with 3 1/4" J.D. hollow stem augers
PROJECT: AI's Radiator
247 S. Union Avenue
Bakersfield, CA
e
i('n:- CONSOLIDATED TESTING
\.,;. r L LABORATORIES, INcA JOB NO.:
603E.WORmAVENUE ..
PORTERVILLE, CA 93257 DATE:
(559)781-0571 ·FAX(559)782-8389 BY:
BORING LOG NUMBER B4 (East fuel island)
4647-00
S/1 S/OO
D.Harris
I'·
.'
r'
,~. '.'
" ~~~
ø.. PERCENT DRY
I~ BLOW SAMPLE .;¡:J
DEPTH -0 SOIL DESCRIPTION
I~ COUNTS NO. Oø¡: MOISTURE DENSITY
(fJt:)
o·_~
~ .
-...
...
-...
... 0"-5" Concrete slab
-
...
-~
~
S' _...
-
-
-
--
-
--
- SM 5"-10.5' Silty sand: moist, very fine to coarse grain
- size sub-rounded, no petroleum odor
6
10' _ 7
10 HNU
-- 0
-
--
-~
~
-~
~
lS'_~
~
-~
~
-~
~
-~
-
-
-
20'__
-
--
--
-
-
-
--
-
2S'_ _
~
-~
~ Terminated drilling at 10.5' no free standing
-~ ground wat~r encountered
~
-~ \
~
-l-
I-
30' _ i-
~"~
.;.~\
':'''1
r:
LOCATION: B4 (See location map)
EQUIPMENT: Mobile B-80 drill rig with 3 1/4" I.D. hollow stem augers
PROJECT: AI's Radiator
247 S. Union Avenue
Bakersfield, CA
e
~I CONSOLIDATEDTESTI~
\.,; ,. L LABORATORIES, IN.
603 E. WORTH AVENUE
PORTERVILLE. CA 93257
(559)781-0571 *FAX(SS9)782-8389 BY: D.Harris
BORING LOG NUMBER B5 (Previous UST waste oil tank location»
JOB NO.:
DATE:
4647-00
~/1 ~/OO
t·
=-
.~ BLOW SAMPLE ...;¡;;¡ PERCENT DRY
DEPTH "'0 SOIL DESCRIPTION
I~ COUNTS NO. 0a: MOISTURE DENSITY
me
0'__
- .
--
-
--
- 0"-4.5" Concrete slab
--
-
--
S' __ SM 4.5'-6' Silty sand: dark yellowish brown, moist, fine
- to coarse grain size, sub-rounded, occasional
- fractured aggregate rock fragments 6mm to
-
-- 18mm in size
-
--
- SW 6'-9' Sand; yellowish brown, moist, fine to very
-- coarse grain size, sub-rounded, no petroleum
-
10' _ odor
6
- 8 HNU
12 0 ML 9'-14.5' Sandy silt: yellowish brown, moist, very fine to fine
-- grain size, slightly cohesive, no petroleum odor
-
-- or staining, medium dense
-
-
5 2"ID.
15'_ 9 split
1 0 spoon HNU ML 14.5'-15.5' Silly clay: oJive, moist, strong brown mottling
-- sampler 0 throughout, moderately cohesive, no petroleum
~ odor or staining, medium dense
--
...
--
-
--
-
20'__
-
--
-
-
-
-
-
--
-
25'__
-
--
Terminated drilling at 15.5' no free standing
-~ ground water encountered
~
-~ \
...
--
-
30·....,...,
r·'"
.'~\
toO.
"-"-
.~;...
t"
I
I I
LOCA TION: B5 (See location map)
EQUIPMENT: Mobile B-80 drill rig with 3 1/4" J.D. hollow stem augers & 2" J.D. standard penetration
PROJECT: Ai's Radiator
247 S. Union Avenue
Bakersfield, CA
e
<TFL' ,. CONSOLIDATED TESTI~
\";f' ., LABORATORIES, IN. JOB NO.:
603 E. WORTH AVENUE
PORTERVILLE, CA 93257 DATE:
(559)781-0571 ·FAX(559)782·8389 BY: D.Harris
BORING LOG NUMBER B13 (Previous dry well Jocation»
4647-00
S/15/00
I.,
II. PERCENT
~ BLOW SAMPLE ..;;J DRY
DEPTH -0 SOIL DESCRIPTION
~ COUNTS NO. o=: MOISTURE DENSITY
0 (/)c
0'__
- .
--
-
--
0"-2" Asphalt concrete pavement
--
--
-
5'__ ML 2"-4' Sandy silt; yellowish brown, moist, very fine
- to medium grain size, slightly cohesive, no
-- petroleum odor or staining
-
--
-
--
- SM 4'-6' Silty sand: dark yellowish brown, moist, very
-- fine to coarse grain size, sub-rounded, no petroleum
-
10' _ odor or staining
6
- 8 HNU
10 0 SW 6'-21.5' Sand: yellowish brown, moist, fme to very coarse
-~ grain size with occasional granules 2mm to 4mm
~ in size, sub-rounded, no petroleum odor or staining,
-~
~ medium dense
-~
~
15'_
7 HNU
- 8 0
9
-""
""
-""
-
--
20'_
14 2" I.D. HNU
- 15 split 0
13 spoon
-- sample!
-
-
--
~
25'_~
~
-~
~ Terminated drilling at 21.5' no free standing
-~ ground water encountered
~
-~ \
~
-l-
I-
30'__
f]
l ':
~';
···./i~
:;;i~
r"'
LOCA nON: B 13 (See location map)
EQUIPMENT: Mobile 8-80 drill rig with 31/4" I.D. hollow stem augers
C,,'"
,;., .:.
.:-..--::.-
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PROJECT: Ai's Radiator
247 S. Union Avenue, Bakersfield, CA
FILE NO: 4647-00
SUMMARY OF SOIL SAMPLES COLLECTED DURING
FIELD INVESTIGATION ON MAY 15,2000
TOTAL
RECOVER -
ABLE e
PETROLEUM
ETHYL- TOTAL T.P.H. HYDROCAR- TOTAL TOTAL
SAMPLE # DEPfH MTBE BENZENE TOLUENE BENZENE XYLENES GAS nONS LEAD GLYCOLS
Bl-6 31 '-31.5' ND ND ND ND ND ND
B2-3 31'-31.5' ND ND ND ND ND ND
B3-2 10'-10.5' ND ND ND ND ND ND
B4-10 10'-10.5' ND ND ND ND ND
B5-13 15'-15.5' ND ND ND ND ND ND ND 5.1
B6-4 5'-5.5' 58 e
B7-5 10'-10.5' ND
B8-12 10'-10.5' ND
B9-11 5'-5.5' ND
BIO-8 5'-5.5' ND
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PROJECT: AI's Radiator
247 S. Union Avenue, Bakersfield, CA
FILE NO: 4647-00
I !
SUMMARY OF SOIL SAMPLES COLLECTED DURING
FIELD INVESTIGATION ON MAY 15,2000
TOTAL e
RECOVER -
ABLE
PETROLEUM
ETHYL- TOTAL T.P.H. HYDROCAR- TOTAL TOTAL
SAMPLE # DEPTH MTBE BENZENE TOLUENE BENZENE XYLENES GAS BONS LEAD GLYCOLS
Bl1-7 5'-5.5' ND
B12-9 5'-5.5' NO
B13-1 21 '-21.5' NO ND 0.0056 NO ND ND NO NO
SAMPLE PREP/ANALYSIS METHOD: EPA 5030/8015M, 8020
SAMPLE PREP/ANALYSIS METHOD: SM 5520 C & F
SAMPLE PREP/ANALYSIS METHOD: HACH Clycol Test (Aqueous extraction of soils. Test is only semi-quantitative)
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SAMPLES ANALYZED BY CASTLE ANALYTICAL LABORATORY, 2333 Shuttle Drive, Atwater, CA 95301
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TPH Diesel 3510 GC/FID
TPH Diesel 3.550 GC/FID
TPH as Jel Fuel
TClP: 0 Melals 0 YOA 0 Semi YOA
!~ TOTAL OIL AND GREASe::@i8~3.2J S03A
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CAM Metals: OSTlC 0 TIlC
EPTOX:O Metals CJ Pesticides 0 Herbicides
EPA Priority Pollulanl: D.Aelals CJHSL
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CASTLE ANALYTICAL LABORATORY
Envlronm.ntal Testln; Services 2333 Shuttl. Drive, Atwater. CA 95301
Certlftcate #2079
Phonlil: (209) 384-2930
Fax: (209) 384-1807
Conlloffdated Testing Laltoratorl\il$, Ino
e03 E. Worth Ave.
Portervllle, CA 93281
Attn: David He").
Client Project ID: 4647-00
Client Name: AI's Radiator
Lab Aeferenea Number: 300.
Semple Description: Soli
Sample Prep/Analysis Method: EPA 50JO/SOi5M. 8020
Lab Numbers: 3004-1S, 2S, 38. 65, 108
Sampled: 5-15-00
Received: 5-17-00
Extracted: 5-16-00
Analyzed: 5-18·00
Reported: 5·25-00
TOTAL PETROLI!UM HYDROCARBONS· GASOLINE
WITH BTEX DISTINCTION
[~. ANAL.>rÆ REPORTING LIMIT SAMPLE ID SAMPLE 10 SAMPLE 10 SAMPLE \0 SAMPLE 10
B 13·1 BS-2 B:Z-3 81-6 84-10
21'-21.4'1' , 0'-' 0.5' 31'-31.5' 31'·31.5' 10'·10.5'
(mglkg) (mglkg) (mglkg) (mgJkg) (mg/kg) (mgJkg)
MTSE 0.010 ND ND NO NO
BENZENE 0.001;10 NO ND ND NO NO
TOLUENE 0.0050 0.00515 NO NO NO NO
ETHYL BENZENE 0.0050 NO NO ND NO NO
TOTAL XVLISNES O.OOCiO NO NO NO NO NO
GASOLINE RANGE! 1.0 NO NO NO NO NO
HVC~OCÅRBONS
Report limIt Multiplication lador.
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Surrogate % Recovery;
fla:IT~/"~':ILn\ flD:tl.T1I/I'ID:n.I% flD:!01\t/PIO:IOI'll PICI:'U!\/P'lCI:".MI flCl:TU'tl/P;:¡:71'.O'll
In&trument 10:
VAR-GC1 VAR-GCi VAR-GlC1 VAR-GlC1 VAR-GC1
AnaJyt8$ reøorted all ND wlilre not dlltected ar belOw the Pr.ctiœl Q¡¡antltatlon Umlt
Practlcel Qu.ntlt.tlcn Limit· Reporting Umlt IC ~.port Limit Multiplication F.ctor
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CASTLE ANALYTICAL LABORATORY
Envlronmentel Testing Slrvlcea 2333 Shuttle Drive, Atwater, CA ~3ò1 Phon,: (209) 384-2930
Cart/Reale ~207~ FIx: (209) 384-1507
Consolidated Testing Laborlltorlr¡)s, Inc
603 e. Worth Ave.
Portervllle. CA 93257
Attn: DavId Harris
Client ProJeot 10: 4547·00
~Iltint Name: AI'. I'tadlator
LIb R.""nc. Number: 3004
Sample Deeorlptlon: Soli .
Sample Prep/Analysis Method: EPA 5030/8015M, 8020
Lab Numbers: 3004-138
Sampled: 5-15-00
Received: 5-17-00
Extracted: 5-18-00
Analyzed: 5-18-00
Reported: e-25-o0
TOTAL P!TROJ.eUM HYDROCARBONS· GASOLINE
WITH BTEX DISTINCTION
ANALYTE REPORTING LIMIT SAMPLE ID
B 5-13
15'-15.5'
(r'ngIkSl) (/TIll/kg)
MTBE 0.010 NO
BeNZENE 0.0050 ND
TOLUENE 0.0060 ND
ETHYL BENZENE 0.0090 NO
TOTAL. XYL.ENE8 0.0050 ND
GASOLINE RANGE 1.0 NO
HYDROCARBONS
Report Limit Multiplication Factor:
Surrogate % l\ecovary:
PIa, '2.1111 ~lo.ll.w
Instrument ID:
VAR-GC1
Analytes reported illS ND wltrlt not detected or below the Prac:t1cal Quantltatlon Limit
Practlça Quant/tatlon L.imlt · Reporting Limit x Report Limit Multipfçatlon Façtor
APPROVED !Y:
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CASTLE ANALYTICAL LABORATORY
EnvIronmental T.ltlng Slrvlc.. 2333 Shuttl. Orlv.. Atwater, CA 95301
CertltJc:atl No. :lOTS
Phon,,: (209) 384-2930
"ex: (ZOg) ~6'H '07
Consolldat.d THtlng Labor'~rles. Inc
603 E. Worth Ave.
Portervllle, CA 93:lðT
AU": O.vld Harris
Client Project 10: 4547·00
CII.nt Name; AI's Radiator
Lab F<e1erenco Number. 3004
Slmpl. D&Sorlptlon: Soli
Sample Prep/Analysis Method: SM !!f\20 C & F .
. Lab Numbers: 3004-18,45,58,118, 12S
Sampled: 6-16-00
Received: 5-17-00
Extracted: 5-18-00
Analyzed: 6.22-00
Rllportild: 5-25-00
TOTAlRECOVERABl!P!TROL~UMHYDROCARBONS
ANAL YTE
REPORTING L.IMIT
8AMPLE ]0 SAMPLE I!:) SAMPLE Ie SAMPLE ID SAMPLE ID
S 13·1 88-4 B7~ B ;'11 B a..12
21',21.5' 5'-8.5' 10'-10.15' "06,6' 10'·1Q.5'
(mg/kg) (mglkg) (mglkg) (mg/kg) (mglkg)
ND 58 NO NO ND
PETROLeUM
HYtlf(OCARBONS
(ms/k;)
15
Report ~mit Multiplication Fector:
Instrument ID:
IR-SPEC
IFl-SPEC
IR-SPEC
IR-$PEC
IR-SP!!C
Analytes reported as NO wire not clQtectad or below the PraetlcaJ QuantltatJon Limit
Prlctlcal Quantitation Limit. Reporting LImit x Report limit Multiplication Factot
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CASTLE ANALYTICAL LABORATORY
E:nvlrcmmental Teatlng SlIrvlctll 2333 Shuttl. Drive, Atwater, CA 95301
Cartlflc:.tt NO, 2079
Phone: (209) 384-2930
Fax: (209) 384·1 !50'7
Conlolld,ted Teðtlng Laboratories, IlIe
e03 E. Worth Ave.
Portervllle, CA 93257
Attn: D.vld HarrIs
Client prosc:t ID: 4647·00
Client Name: AI'fiI Radiator
l.ab Reference Number: 3004
Semple DescrIption: Soli
Sample Prep/Analysis Method: SM 151520 C & F
L.llb Numbers: 30040138
Sampled: 5·15·00
Received: 5·17.()0
Extraçled; 5·18-00
Analy¡ced: $-22-00
Reported: 15-215-00
TOTAL RECOVERABLE! P!TfltOL!UM HYDROCARBONS
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ANALYTE
REPORTING¡ LIMIT
PETROLEUM
HYDROCARBONS
(m~)
15
SAMPLE ID
85-13
15'·15.5'
(mglkg)
NO.
Report Limit MultiplicatIon Factor:
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I.,.~m"tlc' . ...sPEC
Allalyt$$ rvþort$d &II NO were n;t det.;ted or below the Practical QUlllnlltltlon Limit
Practical Quantltatlon Limit · Reportll'l" I.lmlt x RepOrt Limit MultiplicatIon Factor
ANALYST' C~AA~çr~
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CASTLE ANALYTICAL LABORATORY
environmental Tea,'ng Services 2333 Shuttle Drive, Atwater, CA 96301
C.rt/floate #2079
Phon.: (209) 384-2930
FÞ; (:l09) 384-1507
Con,;lIclated Teatlng laboratories, 11'10
60:5 E. Worth Ave.
Portarvlll., CA 93257
Attn: David HaITI,
Client Pr;jec! ID: 4647-00
CII,nl Name: Ar. Radllltor
Lab Ft.ference Number: 3004
Sample D..crfptJon; Soli
Sample Prep/Analyela Method: HACH Glycol Test-
Lab Numbers: 3004-7$. &S, 95
Sampled: 6-15-00
Rllcelved: e-17-00
Extracted: 5-24-00
Analyz&d: s..24-00
Report.,d: 5-24-00
ANALYTE
REPORTING LIMIT
SAMPLEID
B 11.7
5'.5.5'
<rT\gfkg)
NO
TOTAL GLYCOLS
(mglkg)
30
Report Limit Multiplication Factor:
- Aquaous extraction of soUs. Test III only IIl!Im\-cuantitatlve.
GLYCOL
SAMPLE ID
B1Q..8
5'-ð.5'
(mgtkg)
NO
SAMPLe 10
B 12-0
5'-5.6'
(mg~g)
ND
Analyt8$ reported liS ND ware no~ d.t.cted or below the Practical Quantltatlon Limit
Practical Quantltatlon Limit.. Reporting Limit x Report Limit Multiplication Factor
ANALVST, c&ù9~
Glori J. Cone
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...J 110 2nd Avc:nu~ South. #D1, Pacheco. CA 94S5J-$5fiO
8' Mç(~AMPBSLL ANALYTICAL me. TeIl!phonc: 925~798-1620 Fa.: 925.798.1622
.I11IP.:I!~.mccarMbcJ·cøm E-mail: maIn@m~4mpòe...com
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ClIent ProJeclLO: #300414647-00: AI',
RAdiator
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. Cudt: AJUI[yrtc:a1 LllboI1llory
2.333 Shl1tt1~ Dr.. Bldg 908/909
D$l1c SáïnPlè:d: OS/15/00
'·U
-
Da~ R~~i\'ed: OS/23/00
:
Atwater, C 95301
Client Contact Jim Phillip,
Client P.O:
Dltre Exttl¢r~ OS/23/00
Dote Am11yzed: 05123/00
I~j;
38411
38612
BJ3~111'-2tIl2'
s
Lead"
2xtractlan \I Lud'" % Recovery
SU'r'rUl!lillt.\:
Tn.C ND to?
TILC 5.1 tOO
I SPA _1V\ic¡ m.tbc>d6 6010120<>.1, 239.r
Lab JD Client ID Matrix
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fUl:lraction t1ul . DISTLC l'eIlUI1II1It" not applicable to S-1'1.C ...",1<atory 1l1IÙ1I.
Q P,"'A "1Itl"Kt; 11\ metbodt 131I(TCU"). 'O'O/]O:!Ð(w:w:r.~Ç). 3040<orpNC mII"'~·n\..q, J{I~(t(\I;ds..·I·I"CI~ STLr..~· CA 11t1e 12
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I) "quid sam Ie' Iba, cO,lIaill. plCfl than ~2 VI.t % Mdinwnl; Ihl~ _tdi\flllllt ÎII ./oirKt.d wlttllhe IJCùid. ill ø,:¡;c/IIJønce ....ith El'A.
INlb04oloAie amS _ ....I~".... G~-- 'ftICtal CCMlc:1tI\tnLU"IIt. .
DHS Cct ~flcation No. 1644 I '.1 ....}. I3dw~ HamlltoJI, Lab DwC'tor
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