HomeMy WebLinkAboutElkin Chrysler Redev_2002.11.08_Phase I Limited Site Assessment-OCRI
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TABLE OF CONTENTS
I p~
1.0 INTRODUCTION ... ) ...................................................................................................... 1
1.1 Site Location and Description ...................................................................................... 1
1.2 Purpose of Limited Site Assessment ............................................................................ 1
2.0 SITE HISTORY .............................................................................................................. I
3.0 RISK CHARACTERIZATION ...................................................................................... 2
3 .1 Receptor Information ................................................................................................... 5
3.2 Source Control ............................................................................................................. 5
4.0 SITE GEOLOGY AND HYDROGEOLOGY. ............................................................... 6
4.1 Regional Geology ........................................................................................................ 6
4.2 Site Geology ................................................................................................................. 6
4.3 Regional Hydrogeology ............................................................................................... 7
4.4 Site Hydrogeology ........................................................................... ,,. ........................... 7
5.0 SAMPLING RESULTS ........................................................... ; .. ~·····················r:,., ......... 7
6.0 CONCLUSIONS AND RECOMMENDATIONS ................. , ... r.r: ••..... ~ •.•.. :~·.,.:\ ....•• 8
\\',' ~ "-. \~i?''\ cP ·~~\
TABLES v~\ ~ ~\.
\<!/ .,. " " \~~ ',;;.' Table 1
Table 2
Table 3
Table 4
Table 5
Figure 1:
Figure 2:
Figure 3:
Figure 4
Figure 5:
Summary of Ownership History
Soil Analytical Data from June 10, 2002
Summary of Surrounding Property Owners
Soil Analytical Data from October 10, 2002
Groundwater Analytical Data from October 15, 2002
FIGURES
·". ( \~/(~/' ~~~
Portion of U.S.G.S. Southwest Durham, North Carolina topographic map
illustrating the location and topography of the site.
Site vicinity map illustrating properties in the surrounding area within a
1500 ft. radius of the site.
Site map illustrating locations of Elkins Chrysler Plymouth, existing
structures, utilities, former underground storage tank, and monitoring well.
Site map illustrating soil analytical test results from soil sample MW-1;
samples SS-1 through SS-6. Data collected on October 10, 2002
Site map illustrating groundwater analytical test results from monitoring
well MW-1. Data collected on October 15, 2002.
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ATTACHMENT A:
ATTACHMENT B:
ATTACHMENT C:
ATTACHlVtENTS
Field Boring Log
Soil Analytical Data from October 10, 2002
Groundwater Analytical Data from October 15, 2001
LIMITATIONS
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PHASE I LIMITED SITE ASSESSMENT
Elkins Chrysler Plymouth
125 East-West Expressway
925 Jackie Robinson Drive
Durham (Durham County), North Carolina
1.0 INTRODUCTION
1.1 Site Location and Description
The site is located at 125 East-West Expressway, now known as 925 Jackie Robinson
Drive, in Durham, North Carolina. The site is bound by Dillard Street to the north, Jackie
Robinson Drive to the south, South Roxboro Road to the east, and South Mangum Street
to the west in Durham, Durham County, North Carolina (Figures 1-3). The site, presently
owned by E & L Realty, LLC, consists of a retail automobile dealership with an
automotive service facility and is located in downtown Durham adjacent to the Durham
Bulls baseball stadium. The site property encompasses approximately 6.2 acres, which
presently includes two main buildings.
1.2 Purpose of Limited Site Assessment
On June 10, 2002, Elkins Chrysler Plymouth contracted IMS to perform the excavation
and removal of a 1,500 gallon waste oil underground storage tank (UST). IMS prepared
an UST Closure Report along with soil analytical data and submitted the report on July
10, 2002 to the North Carolina Department of Environment and Natural Resources -
Division of Waste Management -UST Section (DWM-UST Section). The DWM-UST
Section issued a Notice of Regulatory Requirement (NORR) dated July 12, 2002
directing that a Phase I Limited Site Assessment (LSA) be prepared in accordance with
risk based corrective action regulations outlined by North Carolina Administrative Code
(NCAC) Title 15A, Subchapter 2L, .0115. The purpose of this Phase I LSA is to
determine the appropriate risk classification of the site with respect to NCAC 15A,
Subchapter 2L, .0115.
2.0 SITE HISTORY
Elkins Chrysler Plymouth has occupied the property since 1969 and has operated as a
retail automobile dealership since that date (Table 1 ). The 1,500 gallon waste oil UST
was installed on May 11, 1987. On June 4, 2002, IMS submitted Notice of intent form
GW/UST-3 to the DWM-UST Section. On June 6, 2002, Durham County issued the
required permit for the removal of the UST. On June 10, 2002, IMS removed the UST
and the associated piping. Surrounding soil in the UST excavation did not reflect
indications of a release. However, hydrocarbon odors and photoionization detector (PID)
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monitoring reflected the presence of hydrocarbon constituents in the soils. A soil sample
was collected from beneath the former UST piping (sample SS-1) and each end of the
UST (SS-2 and SS-3). Soil analytical data and sample depths from the UST Closure
Report are summarized on Table 2.
In response to the NORR dated July 12, 2002, the property owners contracted IMS to
conduct and complete a Phase I Limited Site Assessment (LSA). IMS installed one
monitoring well (MW-1) in the source area to a depth of 30 ft below land surface. The
monitoring well was installed on October 10, 2002. As directed by DWM-UST Section
soil samples were collected every 5 ft and submitted to a North Carolina Division of
Water Quality (NC DWQ) certified laboratory for analysis. Groundwater samples were
collected from monitoring well MW-1 on October 15, 2002 and submitted to a NC DWQ
certified laboratory for analysis. The analytical results are further discussed in Section 5.
The boring log for monitoring well MW-1 is included as Attachment A.
3.0 RISK CHARACTERIZATION
As part of the risk characterization, IMS conducted a Site Reconnaissance Survey (SRS)
of the Elkins Property and the surrounding area on October 22, 2002. The information
gathered during the SRS along with information obtained from other sources was used in
completing the Limited Site Assessment Risk Classification and Land Use Form, which
follows:
Limited Site Assessment Risk Classification and Land Use Form
Part I -Groundwater/Surface waterN apor Impacts
High Risk
1. Has the discharge or release contaminated any water supply well including any
used for non-drinking purposes? NO
If yes, explain.
2. Ls· a water supply well used for drinking water located within 1000 feet of the
source area of the discharge or release? NO
3. Is a water supply well used for any purpose (e.g., irrigation, washing cars,
industrial cooling water, filling swimming pools) located within 250 feet of the
source area of the release or discharge? NO
4. Does groundwater within 500 feet of the source area of the discharge or release
have the potential for future use in that there is no other source of water supply
other than the groundwater? NO
Explain. Surrounding area supplied by City of Durham water.
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5. Do vapors from the discharge or release pose a threat of explosion because of
accumulation of the vapors in a confined space or pose any other serious threat to
public health, public sqfety or the environment? NO
If yes, explain. ________________________ _
6. Are there any other factors that would cause the discharge or release to pose an
imminent danger to public health, public safety, or the environment? NO
If yes, explain. ________________________ _
Intermediate Risk
7. Is a surface water body located within 5 00 feet of the source area of the discharge
or release? NO
Jf yes, does the maximum groundwater contaminant concentration exceed the
surface water quality standards and criteria found in J 5A NCAC 2B . 0200 by a
factor of 10? NIA
8. Is the source area of the discharge or release located within a designated wellhead
protection area as defined in 42 USC 300h-7(e)? NO
If yes, explain. ________________________ _
9. Is the discharge or release located in the Coastal Plain physiographic region as
designated on a map entitled "Geology of North Carolina" published by the
Department in 1985? NO
Jf yes, is the source area of the discharge or release located in an area in which
there is recharge to an unconfined or semi-confined deeper aquifer that is being
used or may be used as a source of drinking water? NIA
10. Do the levels of groundwater contamination for any contaminant exceed the gross
contamination levels established (see Table 7) by the Department? NO
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Part II -Land Use
Property Containing Soµrce Area of Discharge or Release
The questions below pert~in to the property containing the source area of the release.
I. Does the property contain one or more primary or secondary residences
(permanent or temporary)? NO
Explain. ___________________________ _
2. Does the property contain a school, daycare center, hospital, playground, park,
recreation area, church, nursing home, or other place of public assembly? NO
Explain. ___________________________ _
3. Does the property· contain a commercial (e.g. retail, warehouse, office/business
space, etc.) or industrial (e.g. manufacturing, utilities, industrial research and
development, chemical/petroleum bulk storage, etc.) enterprise, an inactive
commercial or industrial enterprise, or is the land undeveloped? YES
Explain. The property is a retail automobile dealership and service facility
that has been in operation since 1969.
4. Do children visit the property? YES
Explain. As part of the retail automobile dealership children may visit the
property on a limited basis. The former UST area is off limits to unauthorized
personnel and is surrounded by a chain link fence.
5. Is access to the property reliably restricted consistent with its use (e.g., by fences,
security personnel or both)? YES
Explain. The former UST area is surrounded by a chain link fence and
security patrols the area after normal business hours.
6. Do pavement, buildings, or other structures cap the contaminated soil? YES
Explain. The former UST area is capped by the existing asphalt parking pad.
If yes, what mechanisms are in place or can be put into place to ensure that the
contaminated soil will remain capped in the foreseeable future?
Site development plans can be addressed.
7. What is the zoning status of the property? Industrial zoning status
Obtained from Durham City/County Planning Department.
8. Is the use of the property likely to change in the next 20 years? NO
Explain. The site is currently part of the downtown business district and is
an established car dealership.
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Property Surrounding Source Area of Discharge or Release
The questions below pertain to the area within 1500 feet of the source area of the
discharge or release (excludes property containing source area of the release):
11. What is the distance from the source area of the release to the nearest primary or
secondary residence (permanent or temporary)? The distance from the source
area of release to the nearest residence is approximately 1200 ft to the south west
(Figure 2. refer to Section 3.1 for details).
12. What is the distance from the source area of the release to the nearest school,
daycare center, hospital, playground, park, recreation area, church, nursing
home or other place of public assembly? Durham Bull Baseball field 1s
located 400 ft west of the location of the former UST (Figure 2).
13. What is the zoning status of properties in the surrounding area? Mixed use
industrial, commercial and residential. Durham Freeway 147 separates the site
from the residential areas.
14. Briefly characterize the use and activities of the land in the surrounding area.
The surrounding area consists of mixed industrial and commercial. Uses include
retail automobile dealerships, the Durham Bulls Baseball Field and various
commercial and retail buisness.
3.1 Receptor Information
As previously stated, IMS conducted a SRS of the surrounding area. The SRS was
accomplished by physically surveying the area and interviewing property occupants
within a 1,500 ft radius of the source area ofrelease. The SRS did not identify any water
supply wells within a 1,500 ft radius of the site.
Public water is supplied to the area from the City of Durham. There are no planned or
approved wellhead protection areas within 1,500 ft of the source area. Subsurface
structures present on the site include underground utilities (Figure 3). Details of the
surrounding properties are presented on Table 3. Surrounding land use is primarily
industrial and commercial. The Durham Bulls Baseball Field is located 400 ft west of the
site and is the closest location of public assembly (Figure 2). Forest Hill Heights
Community is approximately 1200 ft to the southeast and is the location of the closest
residence. The only surface water observed within 1,500 ft of the former UST is an
unnamed creek approximately 1,500 feet south west of the site (Figure 1).
3.2 Source Control
Currently free product has. not been detected during any of the subsurface investigations
conducted at the site. As mentioned above, the UST at the site has been removed.
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4.0 SITE GEOLOGY AND HYDROGEOLOGY
4.1 Regional Geology
The City of Durham is located in the middle of Durham County. North Carolina
occupies three major physiographic provinces: the Coastal Plain; the Piedmont; and the
Blue Ridge. Durham County is located within the Piedmont physiographic province.
The Piedmont province is bordered to the east by the Fall Line and on the west by the
Blue Ridge scarp. The Piedmont occupies approximately 45 percent of the area of the
state. Within the Piedmont, topographic elevations range from 300 to 600 feet above sea
level along the eastern border and gradually rise to the west to approximately 1,500 feet
above sea level at the base of the Blue Ridge scarp (Wilson, et al, 1980). The Piedmont
is divisible into parallel geologic belts oriented in a northeast to southwest direction.
These geologic belts are the Eastern slate belt, the Raleigh belt, the Triassic Basin, the
Carolina slate belt, the Charlotte belt, the Kings Mountain belt, and the Inner Piedmont
belt. Durham County is located within the Triassic Basin and a portion of the Eastern
slate belt of the Piedmont province.
In general, the underlying geology of Durham County is composed of a thick sequence of
red to gray sedimentary rocks of Late Triassic age, known as the Triassic Basin. The
Triassic Basin within Durham County consists of three general belts. These belts are,
from east to west, a fanglomerate belt, a sandstone-mudstone belt, and a limestone-chert
belt (Parker, 1979). The northern portion of Durham County is characterized as zones of
gray-greenish gray to black felsic metavolcanic rock, intermediate metavolcanic rock and
mafic metavolcanic rock (Brown et al, 1985).
4.2 Site Geology
According to the Southwest Durham 7.5 minute topographic quadrangle map, the site lies
at an approximate elevation of 350 ft above mean sea level (Figure 1). Relief in the
immediate vicinity is gently rolling to flat.
The Geologic Map of North Carolina by Brown et al, 1985 depicts the site within the
Undivided Chatham Group of the Triassic Basin's sandstone-mudstone belt. The
Undivided Chatham Group consists of sedimentary rocks comprised predominantly of
red, buff, and dark gray micaceous sandstones, siltstones, mudstones, and claystones
(Brown et al, 1985; Parker, 1979). A boring log from the site indicates that a
structureless soil consisting of poorly sorted, brown to dark brown clayey sand to clay,
and extends down to an approximate depth of 30 ft. This structureless soil maybe
residium or fill material used in developing the site. The field boring log can be found as
Attachment A.
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4.3 Regional Hydrogeology
The triassic and meta-argillitic bedrock serves as the primary aquifer systems in the
region. Flat areas underlain with metavolcanics and argillite generally yield the greatest
regional gallon per minute (gpm) quantity of water. Wells that utilize the bedrock aquifer
tend to average in depth of 100 ft. Deeper wells in the region, with depths greater than
200 ft, generally have a poorer yield than shallower wells. The thickness of overlain
weathered material plays a significant role in gpm yield. Yield from wells in argillitic-
graywacke and metavolcanic units appear directly proportional to depth of weathering
(Bain, 1966).
4.4 Site Hydrogeology
During the monitoring well installation wet soil was encountered at a depth of
approximately 15 ft below grade. Based on gauging data collected on October 15, 2001,
static water levels were measured to approximately 13.68 ft below grade.
5.0 SAMPLING RESULTS
Soil samples were analyzed following the July 2001 Guidelines for Assessment and
Corrective Action. As described in Section 2.0, and directed by DWM-UST Section,
IMS collected soil samples during the installation of monitoring well MW-1 every five
feet (MW-1; SS-I through SS-6, Table 4, Figure 4 ). Soil samples collected for the LSA
were analyzed by EPA 5035 sample preparation and 8260 with IPE & MTBE, MADEP
VPH, EPA 8270, MADEP EPH, and EPA 3050 preparation (Chromium and Lead). The
analytical data for the soil samples collected above the water table during the monitoring
well installation reported no concentrations above the maximum soil contaminate
concentrations for Soil to Groundwater or Residential levels, whichever are lower, as
defined in Guidelines for Assessment and Corrective Action. The soil analytical report is
attached as Attachment B.
The analytical data for soil samples collected during the UST Closure Report showed SS-
1 concentrations of 83 mg/kg for VPH C9-C 10 Aromatics, 940 mg/kg for EPH C 11-C22
Aromatics, 1.2 mg/kg for Ethylbenzene, 5.1 mg/kg for Napthalene, 12 mg/kg for 1,2,4
Trimethylbenzene, and 8.3 mg/kg for total Xylenes, which exceed the Soil to
Groundwater Concentrations. SS-2 showed concentrations of 78 mg/kg for VPH C9-C 10
Aromatics, 1,000 mg/kg for EPH Cl l-C22 Aromatics, 1.6 mg/kg for Ethylbenzene, 7.6
mg/kg for Napthalene, 14 mg/kg for 1,2,4 Trimethylbenzene, and 11 mg/kg for total
Xylenes which exceed the Soil to Groundwater concentrations. The Soil to Groundwater
Concentrations are: 34 mg/kg for VPH C9-C10 Aromatics, 206 mg/kg for EPH Cl 1-C22
Aromatics 0.24 mg/kg for Ethylbenzene, 0.58 mg/kg for Napthalene, 8 mg/kg for 1,2,4
Trimethylbenzene, and 5 mg/kg for total Xylenes. A summary the soil analytical data
collected for the UST Closure Report is on Table 2.
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The groundwater sample collected from monitoring well MW-1 on October 15, 2002 was
analyzed by Standard Method 621 OD, MADEP VPH, 625 with 10 largest peaks, MADEP
EPH, and Metals 3030c (Chromium and Lead) and reported all concentrations below the
gross contamination levels (GCLs) established by 15A NCAC 2L .0115 (Table 5).
However, the concentration of lead was reported at 37 µg/l, above the groundwater
standard of 15 µg/l established by NCAC 2L .0202. All other constituent concentrations
were reported below NCAC 2L .0202 standards. Groundwater analytical data is
presented in Table 5 and illustrated in Figure 5. The groundwater analytical report is
attached as Attachment C.
6.0 CONCLUSIONS AND RECOMMENDATIONS
Based on the information gathered during the preparation of this Phase I LSA and in
accordance with the July 2001 Guidelines for Assessment and Corrective Action, IMS
concludes that the risk classification of the site is 'Low Risk,' as defined by NCAC ISA
Subchapter 2L .0115. Public water is supplied to all properties within a 1,500 ft radius of
the source area. There are no active water supply wells used for drinking within a 1,500
ft of the source area. There are no surface water bodies within 1,000 feet of the source
area. This site is not in a "Coastal Plain" setting with recharge to a deeper aquifer. There
are no planned or approved well head protection areas within 1,500 ft of the site.
According to the laboratory data collected during the LSA, the soil and groundwater were
below established concentration levels, with the exception of lead reported at 37 µg/l,
above the NCAC 2L .0202 groundwater concentration of 15 µg/1. The level of lead may
be attributed to the natural occurrence of metals in the area. Based on the data obtained
IMS requests that "No Further Action" be issued for this incident.
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REFERENCES CITED
Bain, G.L, I 966. Geology and Groundwater in the Durham Area, North Carolina. North
Carolina Department of Water Resources, Division of Groundwater.
Brown, P.M., et al., 198S. Geologic Map of North Carolina. Scale 1 :S00,000. North
Carolina Department of Natural Resources and Community Development -North
Carolina Geological Survey, Geologic Map of North Carolina. North Carolina
Geological Survey.
North Carolina Department of Environment and Natural Resources -Division of Waste
Management, Underground Storage Tank Section, April 2001. Guidelines for
Assessment and Corrective Action.
North Carolina Environmental Management Commission, November 1993. North
Carolina Administrative Code, Title I SA, Subchapter 2L: Classifications and
Water Quality Standards Applicable to the Groundwaters of North Carolina.
North Carolina Environmental Management Commission, November 1993. North
Carolina Administrative Code, Title ISA, Subchapter 2N: Criteria and Standards
Applicable to Underground Storage Tanks.
Parker, J.M., 1979. Geology and Mineral Resources of Wake County. North Carolina
Department of Environmental, Health and Natural Resources, Division of Land
Resources, Geological Survey Section, reprint I99S.
Wilson, W F., et al., 1980. North Carolina Geology and Mineral Resources: A
Foundation for Progress, North Carolina Geological Survey Section Educational
Series No. 4 North Carolina Department of Natural Resources and Community
Development.
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I TABLES
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I FIGURES
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--
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- - - - --- - - -- -
COMMERCIAL
I DILLARD STREET / ,-----------------------------------------+--.. I --------------w---------------------------w-------------T-I
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PARKING LOT
PARKING LOT
Ul ~ CD
w u ~ ~ .,
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w u ~ w Ul
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ELKINS
CHRYSLER
PLYMOUTH
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--s----! ------I
JACKIE ROBINSON DRIVE
HIGHWAY 147
llS
ENVIRONMENTAL SERVICES
~ u a:: w ::;: ::;: 0 u
-- - -
Legend: I 551 .0216
-0 Monitoring Well
u~ Underground
Storage Tank
---w---Water Line
--E-Electric Line
--s--Storm Sewer
--T-Telephone Line
-Fo-Fiber Optic
Line
Site Locotion:
Elkins Chrysler Plymouth
1 25 East West Expressway
Durham, North Carolina
<&J ~ ').-
IMS ENVIRONMENTAL SERVICES
3901-B Commerce Park Drive
Raleigh, North Carolina 27610 Figure 3: Site map illustrating locations of Elkins Chrysler
Plymouth, existing structures, utilities, former
underground storage tank, and monitoring well. Project No: 551 .0216
Prepored By: CJS
Approximote Scole:
0 25 50 75 100
Date: November 4, 2002 1" = 100'
-
- - - -- - - --- - -
COMMERCIAL
~ DILLARD STREET
PARKING LOT
PARKING LOT
(/) ~ CD (Q]~ MW-1 w (/)
(.) FORMER
(/)
~ ~
Cl 0
USED OIL
c c
CD
w
;o -l
(/) UST
I I )> ;;:: ;;::
~ CD c G'l r c [;i ;;::
(/) :'.\ :;;! ;o rTJ Cl ':::i c ;;::
ELKINS
CHRYSLER
PLYMOUTH ~ PARKING LOT
PARKING LOT
MW-1 MW-1 MW-1 I MW-1 tW-1 MW-1
COMPOUND SS-1 SS-2 SS-3 i;;i;; 1 S-5 SS-6
(ALL UNITS mg/Kg) (D-2 FT) (5-7 FT) (10-12 FT) (15-17 FT) (20-22 FT) (25-27 FT)
CHROMIUM 16 14 4.8 23 32 13
LEAD 28 7.4 11 18 28 52
1, 1 DICHLOROETHANE <0.0011 <0.0012 0.0055 <0.0011 <0.0012 <0.0013
MTBE <0.0011 <0.0012 0.0018 <0.0011 <0.0012 <0.0013 EPH C9-C18 ALIPHATICS <6.3 <6.5 <6.6 <6.3 <6.6 <7.2
EPH C19-C36 ALIPHATICS 52 11 8.5 6.9 <6.6 <7.2
\ EPH C11-C22 AROMATICS 52 12 9.4 <6.3 <6.6 <7.2
JACKIE ROBINSON DRIVE
HIGHWAY 147
Figure 4: Site map illustrating soil analytical test results
from soil sample MW-1; samples SS-1 through
SS-6. Data collected on October 10, 2002.
- -
' )
a <§ a::
I/ iE ::i 0 (/)
llS
ENVIRONMENTAL SERVICES
-' <(
(} a:: w :::;: :::;: 0 (.)
-- - -
Legend: I 0216LSA
0
UST
Monitoring Well
Underground
Storage Tank
Site Location:
Elkins Chrysler Plymouth
125 East West Expressway
Durham, North Carolina
~ ~ '>-
IMS ENVIRONMENTAL. SERVICES
3901-B Commerce Park Drive
Raleigh, North Carolina 27610
Project No: 0216LSA
Prepared By: CJS
Approximate Scale:
0 25 50 75 100
Date: November 6, 2002 1" = 100'
-
-- - -- -
PARKING LOT
Cl Vl en 0 ~ c ~ :;a CD I I l> :;:: :;:::
ID l> z c G"'l .--c .--:;::: en
en ~ :;;! :;a
Cl [Tl c '::'.1 :;::
PARKING LOT
\..
--
COMMERCIAL
DILLARD STREET
-
1
en ~ CD
w u ~ w en
r
ELKINS
CHRYSLER
PLYMOUTH
JACKIE ROBINSON DRIVE
HIGHWAY 147
-- -
COMPOUND
(ALL RESULTS ug/L)
VPH C5-C8-ALIPHATICS
VPH C9-C12 ALPIPHATICS
VPH C9-C10 AROMATICS
BENZENE
ETHYLBENZENE
MTBE
TOLUENE
TOTAL XYLENES
1, 2 DIBROMOETHANE (EDB)
DHSOPROPYL ETHER (IPE)
CHROMIUM
LEAD
[QJ-0 MW-1
FORMER
USED OIL
UST
PARKING LOT
Figure 5: Site map illustrating groundwater analytical test
results from monitoring well MW-1. Data
collected on October 15, 2002.
- - - - - -
MW-1
<100
<100
<100
<1.0
<1.0
<1.D
<5.0
<2.0
<1.0
<1.0
15
37
~ a::
0 a:: 0 CD x 0 a::
~ 0 en
llS
ENVIRONMENTAL SERVICES
~ (.) a:: w :::;; :::;; 0 u
I Legend: I 0216LSA
~ Monitoring Well
UST Underground
Storage Tank
Site Location:
Elkins Chrysler Plymouth
1 25 East West Expressway
Durham, North Carolina
@ ~ ~
IMS ENVIRONMENTAL SERVICES
3901-B Commerce Park Drive
Raleigh, North Carolina 27610
Project No: 0216LSA Approximate Scale:
Prepared By: CJS 0 25 50 75 100
Dote: November 6, 2002 1" = 100'
-
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Field Boring Log
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ATTACHMENT B:
Soil Analytical Data from October 10, 2002
I.
I ENVIRONMENTAL
SCIENCE CORP.
12065 Lebanon Rd.
Mt. Juliet, TN 37122
(615) 758-5858
1-800-767-5859
Fax (615) 758-5859
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REPORT OF ANALYSIS
Bobby Veit
IMS Environmental Services
3901 B Commerce Park Drive
Raleigh, NC 27610
Date Received
Description
Sample ID
Collected By
Collection Date
October 11, 2002
Elkins Chrysler
MW-1 SS-1 0-2 FT
Matt Renfrow
10/10/02 08:15
Parameter Dry Result
Total Solids
Chromium
Lead
Volatile Petroleum Hydrocarbons
CS-CB Aliphatics
C9-Cl2 Aliphatics
C9-Cl0 Aromatics
Surrogate Recovery
2,5-Dibromotoluene(FID)
2,5-Dibromotoluene(PID)
Volatile Organics
Acetone
Acrolein
Acrylonitrile
Benzene
Bromobenzene
Bromodichloromethane
Bromoform
Bromomethane
n-Butylbenzene
sec-Butylbenzene
tert-Butylbenzene
Carbon tetrachloride
Chlorobenzene
Chlorodibromomethane
Chloroethane
2-Chloroethyl vinyl ether
Chloroform
Chloromethane
2-Chlorotoluene
4-Chlorotoluene
1,2-Dibromo-3-Chloropropane
1,2-Dibromoethane
Dibromomethane
1,2-Dichlorobenzene
1,3-Dichlorobenzene
1,4-Dichlorobenzene
Results listed are dry weight basis.
BDL -Below Detection Limit
87.3
16.
28.
BDL
BDL
BDL
BDL
102.
87.0
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
Det. Limit -Estimated Quantitation Limit(EQL)
Det. Limit
0.57
0.29
5.7
5.7
5.7
5.7
0.057
0.057
0.057
0. 0011
0.0011
0. 0011
0. 0011
0. 0011
0.0011
0.0011
0. 0011
0.0011
0.0011
0.0011
0.0011
0.057
0.0057
0.0011
0. 0011
0.0011
0.0023
0. 0011
0. 0011
0. 0011
0. 0011
0. 0011
Tax I.D. 62-0814289
Est. 1970
October 17,2002
Units
%
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
ESC Sample #
Site ID
Project # :
Method
2540G
6010B
6010B
MADEPV
MADEPV
MADEPV
MADEPV
% Rec.
% Rec.
MADEPV
MADEPV
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
L92355-01
551.0216
Date Dil.
10/12/02 1
10/16/02 1
10/16/02 1
10/16/02 50
10/16/02 50
10/16/02 50
10/16/02 50
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
Laboratory Certification Numbers:
A2LA -1461-01, AIHA -100789, AL -40660, CA -I-2327, CT-PH-0197, FL -E87487, GA -923, IN -C-TN-01
KY -90010, KYUST -0016, NC -ENV375,DW21704, ND -R-140, SC -84004, TN -2006, VA -00109, WV -233
Note:
This report shall not be reproduced, except in full, without the written approval from ESC.
The reported analytical results relate only to the sample submitted
Page 1 of 26
•• I ENVIRONMENTAL
SCIENCE CORP.
12065 Lebanon Rd.
Mt. Juliet, TN 37122
(615) 758-5858
1-800-767-5859
Fax (615) 758-5859
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REPORT OF ANALYSIS
Bobby Veit
IMS Environmental Services
3901 B Commerce Park Drive
Raleigh, NC 27610
Date Received
Description
Sample ID
Collected By
Collection Date
October 11, 2002
Elkins Chrysler
MW-1 SS-1 0-2 FT
Matt Renfrow
10/10/02 08:15
Parameter Dry Result
Dichlorodifluoromethane
1,1-Dichloroethane
1,2-Dichloroethane
1,1-Dichloroethene
cis-1,2-Dichloroethene
trans-1,2-Dichloroethene
1,2-Dichloropropane
1,1-Dichloropropene
1,3-Dichloropropane
cis-1,3-Dichloropropene
trans-1,3-Dichloropropene
2,2-Dichloropropane
Di-isopropyl ether
Ethylbenzene
Hexachlorobutadiene
Isopropylbenzene
p-Isopropyltoluene
2-Butanone (MEK)
Methylene Chloride
4-Methyl-2-pentanone (MIBK)
Methyl tert-butyl ether
Naphthalene
n-Propylbenzene
Styrene
1,1,1,2-Tetrachloroethane
1,1,2,2-Tetrachloroethane
Tetrachloroethene
Toluene
1,2,3-Trichlorobenzene
1,2,4-Trichlorobenzene
1,1,1-Trichloroethane
1,1,2-Trichloroethane
Trichloroethene
Trichlorofluoromethane
1,2,3-Trichloropropane
1,2,4-Trimethylbenzene
1,3,5-Trimethylbenzene
Vinyl chloride
Xylenes, Total
Surrogate Recovery
Results listed are dry weight basis.
BDL -Below Detection Limit
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
Det. Limit -Estimated Quantitation Limit(EQL)
Det. Limit
0. 0011
0. 0011
0. 0011
0.0011
0. 0011
0.0011
0.0011
0.0011
0.0011
0.0011
0.0011
0. 0011
0. 0011
0. 0011
0. 0011
0. 0011
0. 0011
0.057
0.0057
0.057
0. 0011
0.0057
0. 0011
0. 0011
0. 0011
0. 0011
0. 0011
0.0057
0. 0011
0. 0011
0. 0011
0. 0011
0. 0011
0. 0011
0. 0011
0. 0011
0. 0011
0. 0011
0.0034
Tax I.D. 62-0814289
Est. 1970
October 17,2002
Units
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
ESC Sample #
Site ID
Project # :
Method
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
L92355-01
551. 0216
Date Dil.
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
Laboratory Certification Numbers:
A2LA -1461-01, AIHA -100789, AL -40660, CA -I-2327, CT-PH-0197, FL -E87487, GA -923, IN -C-TN-01
KY -90010, KYUST -0016, NC -ENV375,DW21704, ND -R-140, SC -84004, TN -2006, VA -00109, WV -233
Note:
This report shall not be reproduced, except in full, without the written approval from ESC.
The reported analytical results relate only to the sample submitted
Page 2 of 26
I.
I ENVIRONMENTAL
SCIENCE CORP.
12065 Lebanon Rd.
Mt. Juliet, TN 37122
(615) 758-5858
1-800-767-5859
Fax (615) 758-5859
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Bobby Veit
IMS Environmental Services
3901 B Commerce Park Drive
Raleigh, NC 27610
Date Received
Description
October 11, 2002
Elkins Chrysler
Sample ID
Collected By
Collection Date
MW-1 SS-1 0-2 FT
Parameter
Matt Renfrow
10/10/02 08:15
Toluene-dB
Dibromofluoromethane
4-Bromofluorobenzene
Extractable Petroleum Hydrocarb
C9-C18 Aliphatics
C19-C36 Aliphatics
Cll-C22 Aromatics
Surrogate Recovery
o-Terphenyl
1-Chloro-octadecane
2-Fluorobiphenyl
2-Bromonaphthanene
Base/Neutral Extractables
Acenaphthene
Acenaphthylene
Anthracene
Benzi dine
Benzo(a)anthracene
Benzo(b)fluoranthene
Benzo(k)fluoranthene
Benzo(g,h,i)perylene
Benzo(a)pyrene
Bis(2-chlorethoxy)methane
Bis(2-chloroethyl)ether
Bis(2-chloroisopropyl)ether
4-Bromophenyl-phenylether
2-Chloronaphthalene
4-Chlorophenyl-phenylether
Chrysene
Dibenz(a,h)anthracene
3,3-Dichlorobenzidine
2,4-Dinitrotoluene
2,6-Dinitrotoluene
Fluoranthene
Fluorene
Hexachlorobenzene
Hexachloro-1,3-butadiene
Hexachlorocyclopentadiene
Results listed are dry weight basis.
BDL -Below Detection Limit
Dry
REPORT OF ANALYSIS
Result
99.
110
89.
100
BDL
52.
52.
80.0
72.0
74.0
99.0
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
Det. Limit
6.3
6.3
6.3
6.3
0.38
0.38
0.38
0.38
0.38
0.38
0.38
0.38
0.38
0.38
0.38
0.38
0.38
0.38
0.38
0.38
0.38
0.38
0.38
0.38
0.38
0.38
0.38
0.38
0.38
Det. Limit -Estimated Quantitation Limit(EQL)
Tax I.D. 62-0814289
Est. 1970
October 17,2002
ESC Sample # L92355-01
Site ID
Project # : 551.0216
Units Method Date
% Rec. 8260B 10/16/02
% Rec. 8260B 10/16/02
% Rec. 8260B 10/16/02
mg/kg MADE PE 10/16/02
mg/kg MADE PE 10/16/02
mg/kg MADE PE 10/16/02
mg/kg MADE PE 10/16/02
% Rec. MADE PE 10/16/02
% Rec. MADE PE 10/16/02
% Rec. MADE PE 10/16/02
% Rec. MADE PE 10/16/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
Laboratory Certification Numbers:
Dil.
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
A2LA -1461-01, AIHA -100789, AL -40660, CA -I-2327, CT-PH-0197, FL -E87487, GA -923, IN -C-TN-01
KY -90010, KYUST -0016, NC -ENV375,DW21704, ND -R-140, SC -84004, TN -2006, VA -00109, WV -233
Note:
This report shall not be reproduced, except in full, without the written approval from ESC.
The reported analytical results relate only to the sample submitted
Page 3 of 26
•• I ENVIRONMENTAL
SCIENCE CORP.
12065 Lebanon Rd.
Mt. Juliet, TN 37122
(615) 758-5858
1-800-767-5859
Fax (615) 758-5859
I
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REPORT OF ANALYSIS
Bobby Veit
IMS Environmental Services
3901 B Commerce Park Drive
Raleigh, NC 27610
Date Received
Description
Sample ID
Collected By
Collection Date
October 11, 2002
Elkins Chrysler
MW-1 SS-2 5-7 FT
Matt Renfrow
10/10/02 08:40
Parameter Dry Result
Total Solids
Chromium
Lead
Volatile Petroleum Hydrocarbons
CS-CB Aliphatics
C9-C12 Aliphatics
C9-C10 Aromatics
Surrogate Recovery
2,5-Dibromotoluene(FID)
2,5-Dibromotoluene(PID)
Volatile Organics
Acetone
Acrolein
Acrylonitrile
Benzene
Bromobenzene
Bromodichloromethane
Bromoform
Bromomethane
n-Butylbenzene
sec-Butylbenzene
tert-Butylbenzene
Carbon tetrachloride
Chlorobenzene
Chlorodibromomethane
Chloroethane
2-Chloroethyl vinyl ether
Chloroform
Chloromethane
2-Chlorotoluene
4-Chlorotoluene
1,2-Dibromo-3-Chloropropane
1,2-Dibromoethane
Dibromomethane
1,2-Dichlorobenzene
1,3-Dichlorobenzene
1,4-Dichlorobenzene
Results listed are dry weight basis.
BDL -Below Detection Limit
84.0
14.
7.4
BDL
BDL
BDL
BDL
98.0
83.0
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
Det. Limit -Estimated Quantitation Limit(EQL)
Det. Limit
0.60
0.30
6.0
6.0
6.0
6.0
0.060
0.060
0.060
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.060
0.0060
0.0012
0.0012
0.0012
0.0024
0.0012
0.0012
0.0012
0.0012
0.0012
Tax I.D. 62-0814289
Est. 1970
October 17,2002
ESC Sample # L92355-02
Site ID
Project # : 551.0216
Units Method Date
% 2540G 10/12/02
mg/kg 6010B 10/16/02
mg/kg 6010B 10/16/02
mg/kg MADEPV 10/16/02
mg/kg MADEPV 10/16/02
mg/kg MADEPV 10/16/02
mg/kg MADEPV 10/16/02
% Rec. MADEPV 10/16/02
% Rec. MADEPV 10/16/02
mg/kg B260B 10/16/02
mg/kg B260B 10/16/02
mg/kg B260B 10/16/02
mg/kg B260B 10/16/02
mg/kg B260B 10/16/02
mg/kg B260B 10/16/02
mg/kg B260B 10/16/02
mg/kg B260B 10/16/02
mg/kg B260B 10/16/02
mg/kg B260B 10/16/02
mg/kg B260B 10/16/02
mg/kg B260B 10/16/02
mg/kg B260B 10/16/02
mg/kg B260B 10/16/02
mg/kg B260B 10/16/02
mg/kg B260B 10/16/02
mg/kg B260B 10/16/02
mg/kg B260B 10/16/02
mg/kg B260B 10/16/02
mg/kg 8260B 10/16/02
mg/kg 8260B 10/16/02
mg/kg 8260B 10/16/02
mg/kg B260B 10/16/02
mg/kg B260B 10/16/02
mg/kg 8260B 10/16/02
mg/kg B260B 10/16/02
Laboratory Certification Numbers:
Dil.
1
1
1
50
50
50
50
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
A2LA -1461-01, AIHA -100789, AL -40660, CA -I-2327, CT-PH-0197, FL -EB7487, GA -923, IN -C-TN-01
KY -90010, KYUST -0016, NC -ENV375,DW21704, ND -R-140, SC -84004, TN -2006, VA -00109, WV -233
Note:
This report shall not be reproduced, except in full, without the written approval from ESC.
The reported analytical results relate only to the sample submitted
Page 5 of 26
•• I ENVIRONMENTAL
SCIENCE CORP.
12065 Lebanon Rd.
Mt. Juliet, TN 37122
(615) 758-5858
1-800-767-5859
Fax (615) 758-5859
I
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I
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REPORT OF ANALYSIS
Bobby Veit
IMS Environmental Services
3901 B Commerce Park Drive
Raleigh, NC 27610
Date Received
Description
Sample ID
Collected By
Collection Date
October 11, 2002
Elkins Chrysler
MW-1 SS-2 5-7 FT
Matt Renfrow
10/10/02 08:40
Parameter Dry Result
Dichlorodifluoromethane
1,1-Dichloroethane
1,2-Dichloroethane
1,1-Dichloroethene
cis-1,2-Dichloroethene
trans-1,2-Dichloroethene
1,2-Dichloropropane
1,1-Dichloropropene
1,3-Dichloropropane
cis-1,3-Dichloropropene
trans-1,3-Dichloropropene
2,2-Dichloropropane
Di-isopropyl ether
Ethylbenzene
Hexachlorobutadiene
Isopropylbenzene
p-Isopropyltoluene
2-Butanone (MEK)
Methylene Chloride
4-Methyl-2-pentanone (MIBK)
Methyl tert-butyl ether
Naphthalene
n-Propylbenzene
Styrene
1,1,1,2-Tetrachloroethane
1,1,2,2-Tetrachloroethane
Tetrachloroethene
Toluene
1,2,3-Trichlorobenzene
1,2,4-Trichlorobenzene
1,1,1-Trichloroethane
1,1,2-Trichloroethane
Trichloroethene
Trichlorofluoromethane
1,2,3-Trichloropropane
1,2,4-Trimethylbenzene
1,3,5-Trimethylbenzene
Vinyl chloride
Xylenes, Total
Surrogate Recovery
Results listed are dry weight basis.
BDL -Below Detection Limit
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
Det. Limit -Estimated Quantitation Limit(EQL)
Det. Limit
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.060
0.0060
0.060
0.0012
0.0060
0.0012
0.0012
0.0012
0.0012
0.0012
0.0060
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.0036
Tax I.D. 62-0814289
Est. 1970
October 17,2002
ESC Sample #
Units
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
Site ID
Project # :
Method
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
L92355-02
551. 0216
Date Dil.
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
Laboratory Certification Numbers:
A2LA -1461-01, AIHA -100789, AL -40660, CA -I-2327, CT-PH-0197, FL -E87487, GA -923, IN -C-TN-01
KY -90010, KYUST -0016, NC -ENV375,DW21704, ND -R-140, SC -84004, TN -2006, VA -00109, WV -233
Note:
This report shall not be reproduced, except in full, without the written approval from ESC.
The reported analytical results relate only to the sample submitted
Page 6 of 26
•• I ENVIRONMENTAL
SCIENCE CORP.
12065 Lebanon Rd.
Mt. Juliet, TN 37122
(615) 758-5858
1-800-767-5859
Fax (615) 758-5859
I
I
I
I
I
I
I
I
I
I
I
I
I
I
I
I
I
REPORT OF ANALYSIS
Bobby Veit
IMS Environmental Services
3901 B Commerce Park Drive
Raleigh, NC 27610
Date Received
Description
Sample ID
Collected By
Collection Date
October 11, 2002
Elkins Chrysler
MW-1 SS-2 5-7 FT
Matt Renfrow
10/10/02 08:40
Parameter Dry Result
Toluene-dB
Dibromofluoromethane
4-Bromofluorobenzene
Extractable Petroleum Hydrocarb
C9-Cl8 Aliphatics
Cl9-C36 Aliphatics
Cll-C22 Aromatics
Surrogate Recovery
o-Terphenyl
1-Chloro-octadecane
2-Fluorobiphenyl
2-Bromonaphthanene
Base/Neutral Extractables
Acenaphthene
Acenaphthylene
Anthracene
Benzidine
Benzo(a)anthracene
Benzo(b)fluoranthene
Benzo(k)fluoranthene
Benzo(g,h,i)perylene
Benzo(a)pyrene
Bis(2-chlorethoxy)methane
Bis(2-chloroethyl)ether
Bis(2-chloroisopropyl)ether
4-Bromophenyl-phenylether
2-Chloronaphthalene
4-Chlorophenyl-phenylether
Chrysene
Dibenz(a,h)anthracene
3,3-Dichlorobenzidine
2,4-Dinitrotoluene
2,6-Dinitrotoluene
Fluoranthene
Fluorene
Hexachlorobenzene
Hexachloro-1,3-butadiene
Hexachlorocyclopentadiene
Results listed are dry weight basis.
BDL -Below Detection Limit
100
llO
llO
23.
BDL
ll.
12.
77.0
70.0
74.0
96.0
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
Det. Limit -Estimated Quantitation Limit(EQL)
Det. Limit
6.5
6.5
6.5
6.5
0.39
0.39
0.39
0.39
0.39
0.39
0.39
0.39
0.39
0.39
0.39
0.39
0.39
0.39
0.39
0.39
0.39
0.39
0.39
0.39
0.39
0.39
0.39
0.39
0.39
Tax I.D. 62-0814289
Est. 1970
October 17,2002
ESC Sample # L92355-02
Site ID
Project # : 551.0216
Units Method Date
% Rec. 8260B 10/16/02
% Rec. 8260B 10/16/02
% Rec. 8260B 10/16/02
mg/kg MADE PE 10/16/02
mg/kg MADE PE 10/16/02
mg/kg MADE PE 10/16/02
mg/kg MADE PE 10/16/02
% Rec. MADE PE 10/16/02
% Rec. MADE PE 10/16/02
% Rec. MADE PE 10/16/02
% Rec. MADE PE 10/16/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
Laboratory Certification Numbers:
Dil.
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
A2LA -1461-01, AIHA -100789, AL -40660, CA -I-2327, CT-PH-0197, FL -E87487, GA -923, IN -C-TN-01
KY -90010, KYUST -0016, NC -ENV375,DW21704, ND -R-140, SC -84004, TN -2006, VA -00109, WV -233
Note:
This report shall not be reproduced, except in full, without the written approval from ESC.
The reported analytical results relate only to the sample submitted
Page 7 of 26
•• I ENVIRONMENTAL
SCIENCE CORP.
12065 Lebanon Rd.
Mt. Juliet, TN 37122
(615) 758-5858
1-800-767-5859
Fax (615) 758-5859
I
I
I
I
I
I
I
I
I
I
I
I
I
I
I
I
I
REPORT OF ANALYSIS
Bobby Veit
IMS Environmental Services
3901 B Commerce Park Drive
Raleigh, NC 27610
Date Received
Description
Sample ID
Collected By
Collection bate
October 11, 2002
Elkins Chrysler
MW-1 SS-3 10-12 FT
Matt Renfrow
10/10/02 09:10
Parameter Dry Result
Total Solids
Chromium
Lead
Volatile Petroleum Hydrocarbons
CS-CB Aliphatics
C9-Cl2 Aliphatics
C9-Cl0 Aromatics
Surrogate Recovery
2,5-Dibromotoluene(FID)
2,5-Dibromotoluene(PID)
Volatile Organics
Acetone
Acrolein
Acrylonitrile
Benzene
Bromobenzene
Bromodichloromethane
Bromoform
Bromomethane
n-Butylbenzene
sec-Butylbenzene
tert-Butylbenzene
Carbon tetrachloride
Chlorobenzene
Chlorodibromomethane
Chloroethane
2-Chloroethyl vinyl ether
Chloroform
Chloromethane
2-Chlorotoluene
4-Chlorotoluene
1,2-Dibromo-3-Chloropropane
1,2-Dibromoethane
Dibromomethane
1,2-Dichlorobenzene
1,3-Dichlorobenzene
1,4-Dichlorobenzene
Results listed are dry weight basis.
BDL -Below Detection Limit
83.4
4.B
11.
BDL
BDL
BDL
BDL
98.0
84.0
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
Det. Limit -Estimated Quantitation Limit(EQL)
Det. Limit
0.60
0.30
6.0
6.0
6.0
6.0
0.060
0.060
0.060
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.060
0.0060
0.0012
0.0012
0.0012
0.0024
0.0012
0.0012
0.0012
0.0012
0.0012
Tax I.D. 62-0814289
Est. 1970
October 17,2002
ESC Sample # L92355-03
Site ID
Project # : 551.0216
Units Method Date
% 2540G 10/12/02
mg/kg 6010B 10/16/02
mg/kg 6010B 10/16/02
mg/kg MADEPV 10/16/02
mg/kg MADEPV 10/16/02
mg/kg MADEPV 10/16/02
mg/kg MADEPV 10/16/02
% Rec. MADEPV 10/16/02
% Rec. MADEPV 10/16/02
mg/kg B260B 10/16/02
mg/kg B260B 10/16/02
mg/kg B260B 10/16/02
mg/kg B260B 10/16/02
mg/kg B260B 10/16/02
mg/kg B260B 10/16/02
mg/kg B260B 10/16/02
mg/kg B260B 10/16/02
mg/kg B260B 10/16/02
mg/kg B260B 10/16/02
mg/kg B260B 10/16/02
mg/kg B260B 10/16/02
mg/kg B260B 10/16/02
mg/kg B260B 10/16/02
mg/kg B260B 10/16/02
mg/kg B260B 10/16/02
mg/kg B260B 10/16/02
mg/kg B260B 10/16/02
mg/kg B260B 10/16/02
mg/kg B260B 10/16/02
mg/kg B260B 10/16/02
mg/kg B260B 10/16/02
mg/kg B260B 10/16/02
mg/kg B260B 10/16/02
mg/kg B260B 10/16/02
mg/kg B260B 10/16/02
Laboratory Certification Numbers:
Dil.
1
1
1
50
50
50
50
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1.
1.
A2LA -1461.-01., AIHA -100789, AL -40660, CA -I-2327, CT-PH-01.97, FL -EB74B7, GA -923, IN -C-TN-01
KY -90010, KYUST -0016, NC -ENV375,DW21704, ND -R-1.40, SC -84004, TN -2006, VA -001.09, WV -233
Note:
This report shall not be reproduced, except in full, without the written approval from ESC.
The reported analytical results relate only to the sample submitted
Page 9 of 26
•• I ENVIRONMENTAL
SCIENCE CORP.
12065 Lebanon Rd.
Mt. Juliet, TN 37122
(615) 758-5858
1-800-767-5859
Fax (615) 758-5859
I
I
I
I
I
I
I
I
I
I
I
I
I
I
I
I
I
REPORT OF ANALYSIS
Bobby Veit
IMS Environmental Services
3901 B Commerce Park Drive
Raleigh, NC 27610
Date Received
Description
October 11, 2002
Elkins Chrysler
Sample ID
Collected By
Collection Date
MW-1 SS-3 10-12 FT
Parameter
Matt Renfrow
10/10/02 09:10
Dichlorodifluoromethane
1,1-Dichloroethane
1,2-Dichloroethane
1,1-Dichloroethene
cis-1,2-Dichloroethene
trans-1,2-Dichloroethene
1,2-Dichloropropane
1,1-Dichloropropene
1,3-Dichloropropane
cis-1,3-Dichloropropene
trans-1,3-Dichloropropene
2,2-Dichloropropane
Di-isopropyl ether
Ethylbenzene
Hexachlorobutadiene
Isopropylbenzene
p-Isopropyltoluene
2-Butanone (MEK)
Methylene Chloride
4-Methyl-2-pentanone (MIBK)
Methyl tert-butyl ether
Naphthalene
n-Propylbenzene
Styrene
1,1,1,2-Tetrachloroethane
1,1,2,2-Tetrachloroethane
Tetrachloroethene
Toluene
1,2,3-Trichlorobenzene
1,2,4-Trichlorobenzene
1,1,1-Trichloroethane
1,1,2-Trichloroethane
Trichloroethene
Trichlorofluoromethane
1,2,3-Trichloropropane
1,2,4-Trimethylbenzene
1,3,5-Trimethylbenzene
Vinyl chloride
Xylenes, Total
Surrogate Recovery
Results listed are dry weight basis.
BDL -Below Detection Limit
Dry Result
BDL
0.0055
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
0.0018
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
Det. Limit -Estimated Quantitation Limit(EQL)
Det. Limit
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.060
0.0060
0.060
0.0012
0.0060
0.0012
0.0012
0.0012
0.0012
0.0012
0.0060
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.0036
Tax I.D. 62-0814289
Est. 1970
October 17,2002
ESC Sample #
Site ID
Project # :
Units
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
Method
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
L92355-03
551.0216
Date Dil.
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
Laboratory Certification Numbers:
A2LA -1461-01, AIHA -100789, AL -40660, CA -I-2327, CT-PH-0197, FL -E87487, GA -923, IN -C-TN-01
KY -90010, KYUST -0016, NC -ENV375,DW21704, ND -R-140, SC -84004, TN -2006, VA -00109, WV -233
Note:
This report shall not be reproduced, except in full, without the written approval from ESC.
The reported analytical results relate only to the sample submitted
Page 10 of 26
•• I ENVIRONMENTAL
SCIENCE CORP.
12065 Lebanon Rd.
Mt. Juliet, TN 37122
(615) 758-5858
1-800-767-5859
Fax (615) 758-5859
I
I
I
I
I
I
I
I
I
I
I
I
I
I
I
I
I
REPORT OF ANALYSIS
Bobby Veit
IMS Environmental Services
3901 B Commerce Park Drive
Raleigh, NC 27610
Date Received
Description
Sample ID
Collected By
Collection Date
October 11, 2002
Elkins Chrysler
MW-1 SS-3 10-12 FT
Matt Renfrow
10/10/02 09:10
Parameter Dry Result
Toluene-dB
Dibromofluoromethane
4-Bromofluorobenzene
Extractable Petroleum Hydrocarb
C9-C18 Aliphatics
C19-C36 Aliphatics
Cll-C22 Aromatics
Surrogate Recovery
o-Terphenyl
1-Chloro-octadecane
2-Fluorobiphenyl
2-Bromonaphthanene
Base/Neutral Extractables
Acenaphthene
Acenaphthylene
Anthracene
Benzi dine
Benzo(a)anthracene
Benzo(b)fluoranthene
Benzo(k)fluoranthene
Benzo(g,h,i)perylene
Benzo(a)pyrene
Bis(2-chlorethoxy)methane
Bis(2-chloroethyl)ether
Bis(2-chloroisopropyl)ether
4-Bromophenyl-phenylether
2-Chloronaphthalene
4-Chlorophenyl-phenylether
Chrysene
Dibenz(a,h)anthracene
3,3-Dichlorobenzidine
2,4-Dinitrotoluene
2,6-Dinitrotoluene
Fluoranthene
Fluorene
Hexachlorobenzene
Hexachloro-1,3-butadiene
Hexachlorocyclopentadiene
Results listed are dry weight basis.
BDL -Below Detection Limit
100
110
100
18.
BDL
8.5
9.4
72 .o
64.0
69.0
90.0
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
Det. Limit -Estimated Quantitation Limit(EQL}
Det. Limit
6.6
6.6
6.6
6.6
0 .40
0 .40
0.40
0.40
0.40
0 .40
0 .40
0.40
0.40
0 .40
0 .40
0.40
0.40
0.40
0 .40
0.40
0.40
0.40
0 .40
0 .40
0.40
0.40
0.40
0 .40
0 .40
Tax I.D. 62-0814289
Est. 1970
October 17,2002
ESC Sample # L92355-03
Site ID
Project # : 551. 0216
Units Method Date
% Rec. 8260B 10/16/02
% Rec. 8260B 10/16/02
% Rec. 8260B 10/16/02
mg/kg MADE PE 10/16/02
mg/kg MADE PE 10/16/02
mg/kg MADE PE 10/16/02
mg/kg MADE PE 10/16/02
% Rec. MADE PE 10/16/02
% Rec. MADE PE 10/16/02
% Rec. MADE PE 10/16/02
% Rec. MADE PE 10/16/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
Laboratory Certification Numbers:
Dil.
1
1
1
1
1
1
1
1
1
1
l
1
1
1
1
1
l
1
1
1
1
l
1
1
1
1
l
1
1
l
1
1
1
l
1
l
A2LA -1461-01, AIHA -100789, AL -40660, CA -I-2327, CT-PH-0197, FL -E87487, GA -923, IN -C-TN-01
KY -90010, KYUST -0016, NC -ENV375,DW21704, ND -R-140, SC -84004, TN -2006, VA -00109, WV -233
Note:
This report shall not be reproduced, except in full, without the written approval from ESC.
The reported analytical results relate only to the sample submitted
Page 11 of 26
•• I ENVIRONMENTAL
SCIENCE CORP.
12065 Lebanon Rd.
Mt. Juliet, TN 37122
(615) 758-5858
1-800-767-5859
Fax (615) 758-5859
I
I
I
I
I
I
I
I
I
I
I
I
I
I
I
I
I
REPORT OF ANALYSIS
Bobby Veit
IMS Environmental Services
3901 B Commerce Park Drive
Raleigh, NC 27610
Date Received
Description
Sample ID
Collected By
Collection Date
October 11, 2002
Elkins Chrysler
MW-1 SS-4 15-17 FT
Matt Renfrow
10/10/02 09:50
Parameter Dry Result
Total Solids
Chromium
Lead
Volatile Petroleum Hydrocarbons
cs-ca Aliphatics
C9-Cl2 Aliphatics
C9-Cl0 Aromatics
Surrogate Recovery
2,5-Dibromotoluene(FID)
2,5-Dibromotoluene(PID)
Volatile Organics
Acetone
Acrolein
Acrylonitrile
Benzene
Bromobenzene
Bromodichloromethane
Bromoform
Bromomethane
n-Butylbenzene
sec-Butylbenzene
tert-Butylbenzene
Carbon tetrachloride
Chlorobenzene
Chlorodibromomethane
Chloroethane
2-Chloroethyl vinyl ether
Chloroform
Chloromethane
2-Chlorotoluene
4-Chlorotoluene
l,2-Dibromo-3-Chloropropane
1,2-Dibromoethane
Dibromomethane
1,2-Dichlorobenzene
1,3-Dichlorobenzene
1,4-Dichlorobenzene
Results listed are dry weight basis.
8DL -Below Detection Limit
87.3
23.
18.
BDL
BDL
BDL
BDL
102.
87.0
BDL
8DL
8DL
8DL
BDL
BDL
BDL
8DL
8DL
8DL
BDL
8DL
8DL
BDL
8DL
8DL
BDL
8DL
BDL
8DL
8DL
BDL
8DL
8DL
8DL
8DL
Det. Limit -Estimated Quantitation Limit(EQL)
Det. Limit
0.57
0.29
5.7
5.7
5.7
5.7
0.057
0.057
0.057
0.0011
0. 0011
0. 0011
0.0011
0. 0011
0. 0011
0.0011
0.0011
0. 0011
0. 0011
0. 0011
0.0011
0.057
0.0057
0. 0011
0.0011
0. 0011
0.0023
0. 0011
0. 0011
0. 0011
0. 0011
0. 0011
Tax I.D. 62-0814289
Est. 1970
October 17,2002
ESC Sample #
Site ID
Project # :
Units
%
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
% Rec.
% Rec.
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
Method
2540G
60108
60108
MADEPV
MADEPV
MADEPV
MADEPV
MADEPV
MADEPV
82608
82608
8260B
82608
8260B
82608
82608
8260B
8260B
8260B
8260B
8260B
8260B
82608
8260B
8260B
8260B
82608
82608
82608
82608
82608
8260B
8260B
82608
8260B
L92355-04
551.0216
Date Dil.
10/12/02 1
10/16/02 1
10/16/02 1
10/16/02 50
10/16/02 50
10/16/02 50
10/16/02 50
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
Laboratory Certification Numbers:
A2LA -1461-01, AIHA -100789, AL -40660, CA -I-2327, CT-PH-0197, FL -E87487, GA -923, IN -C-TN-01
KY -90010, KYUST -0016, NC -ENV375,DW21704, ND -R-140, SC -84004, TN -2006, VA -00109, WV -233
Note:
This report shall not be reproduced, except in full, without the written approval from ESC.
The reported analytical results relate only to the sample submitted
Page 13 of 26
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• ENVIRONMENTAL
SCIENCE CORP.
REPORT OF ANALYSIS
Bobby Veit
IMS Environmental Services
3901 B Commerce Park Drive
Raleigh, NC 27610
Date Received
Description
Sample ID
Collected By
Collection Date
October 11, 2002
Elkins Chrysler
MW-1 SS-4 15-17 FT
Matt Renfrow
10/10/02 09:50
Parameter Dry Result
Dichlorodifluoromethane
1,1-Dichloroethane
1,2-Dichloroethane
1,1-Dichloroethene
cis-1,2-Dichloroethene
trans-1,2-Dichloroethene
1,2-Dichloropropane
1,1-Dichloropropene
1,3-Dichloropropane
cis-1,3-Dichloropropene
trans-1,3-Dichloropropene
2,2-Dichloropropane
Di-isopropyl ether
Ethylbenzene
Hexachlorobutadiene
Isopropylbenzene
p-Isopropyltoluene
2-Butanone (MEK)
Methylene Chloride
4-Methyl-2-pentanone (MIBK)
Methyl tert-butyl ether
Naphthalene
n-Propylbenzene
Styrene
1,1,1,2-Tetrachloroethane
1,1,2,2-Tetrachloroethane
Tetrachloroethene
Toluene
1,2,3-Trichlorobenzene
1,2,4-Trichlorobenzene
1,1,1-Trichloroethane
1,1,2-Trichloroethane
Trichloroethene
Trichlorofluoromethane
1,2,3-Trichloropropane
1,2,4-Trimethylbenzene
1,3,5-Trimethylbenzene
Vinyl chloride
Xylenes, Total
Surrogate Recovery
Results listed are dry weight basis.
BDL -Below Detection Limit
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
Det. Limit -Estimated Quantitation Limit(EQL)
Det. Limit
0. 0011
0. 0011
0. 0011
0. 0011
0. 0011
0.0011
0.0011
0. 0011
0. 0011
0. 0011
0. 0011
0.0011
0.0011
0. 0011
0. 0011
0. 0011
0. 0011
0.057
0.0057
0.057
0. 0011
0.0057
0. 0011
0.0011
0.0011
0. 0011
0. 0011
0.0057
0.0011
0.0011
0. 0011
0. 0011
0. 0011
0. 0011
0.0011
0.0011
0. 0011
0. 0011
0.0034
12065 Lebanon Rd.
Mt. Juliet, TN 37122
(615) 758-5858
1-800-767-5859
Fax (615) 758-5859
Tax I.D. 62-0814289
Est. 1970
October 17,2002
ESC Sample #
Site ID
Project # :
Units
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
Method
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
L92355-04
551.0216
Date Dil.
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
Laboratory Certification Numbers:
A2LA -1461-01, AIHA -100789, AL -40660, CA -I-2327, CT-PH-0197, FL -E87487, GA -923, IN -C-TN-01
KY -90010, KYUST -0016, NC -ENV375,DW21704, ND -R-140, SC -84004, TN -2006, VA -00109, WV -233
Note:
This report shall not be reproduced, except in full, without the written approval from ESC.
The reported analytical results relate only to the sample submitted
Page 14 of 26
I.
I ENVIRONMENTAL
SCIENCE CORP.
12065 Lebanon Rd.
Mt. Juliet, TN 37122
(615) 758-5858
1-800-767-5859
Fax (615) 758-5859
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REPORT OF ANALYSIS
Bobby Veit
IMS Environmental Services
3901 B Commerce Park Drive
Raleigh, NC 27610
Date Received
Description
Sample ID
Collected By
Collection Date
October 11, 2002
Elkins Chrysler
MW-1 SS-4 15-17 FT
Matt Renfrow
10/10/02 09:50
Parameter Dry Result
Toluene-dB
Dibromofluoromethane
4-Bromofluorobenzene
Extractable Petroleum Hydrocarb
C9-Cl8 Aliphatics
Cl9-C36 Aliphatics
Cll-C22 Aromatics
Surrogate Recovery
o-Terphenyl
1-Chloro-octadecane
2-Fluorobiphenyl
2-Bromonaphthanene
Base/Neutral Extractables
Acenaphthene
Acenaphthylene
Anthracene
Benzi dine
Benzo(a)anthracene
Benzo(b)fluoranthene
Benzo(k)fluoranthene
Benzo(g,h,i)perylene
Benzo(a)pyrene
Bis(2-chlorethoxy)methane
Bis(2-chloroethyl)ether
Bis(2-chloroisopropyl)ether
4-Bromophenyl-phenylether
2-Chloronaphthalene
4-Chlorophenyl-phenylether
Chrysene
Dibenz(a,h)anthracene
3,3-Dichlorobenzidine
2,4-Dinitrotoluene
2,6-Dinitrotoluene
Fluoranthene
Fluorene
Hexachlorobenzene
Hexachloro-1,3-butadiene
Hexachlorocyclopentadiene
Results listed are dry weight basis.
BDL -Below Detection Limit
100
110
100
6.9
BDL
6.9
BDL
85.0
66.0
83.0
107.
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
Det. Limit -Estimated Quantitation Limit(EQL)
Det. Limit
6.3
6.3
6.3
6.3
0.38
0.38
0.38
0.38
0.38
0.38
0.38
0.38
0.38
0.38
0.38
0.38
0.38
0.38
0.38
0.38
0.38
0.38
0.38
0.38
0.38
0.38
0.38
0.38
0.38
Tax I.D. 62-0814289
Est. 1970
October 17,2002
ESC Sample # L92355-04
Site ID
Project # : 551. 0216
Units Method Date
% Rec. 8260B 10/16/02
% Rec. 8260B 10/16/02
% Rec. 8260B 10/16/02
mg/kg MADE PE 10/16/02
mg/kg MADE PE 10/16/02
mg/kg MADE PE 10/16/02
mg/kg MADE PE 10/16/02
% Rec. MADE PE 10/16/02
% Rec. MADE PE 10/16/02
% Rec. MADE PE 10/16/02
% Rec. MADE PE 10/16/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
Laboratory Certification Numbers:
Dil.
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
A2LA -1461-01, AIHA -100789, AL -40660, CA -I-2327, CT-PH-0197, FL -E87487, GA -923, IN -C-TN-01
KY -90010, KYUST -0016, NC -ENV375,DW21704, ND -R-140, SC -84004, TN -2006, VA -00109, WV -233
Note:
This report shall not be reproduced, except in full, without the written approval from ESC.
The reported analytical results relate only to the sample submitted
Page 15 of 26
I.
I ENVIRONMENTAL
SCIENCE CORP.
12065 Lebanon Rd.
Mt. Juliet, TN 37122
(615) 758-5858
1-800-767-5859
Fax (615) 758-5859
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REPORT OF ANALYSIS
Bobby Veit
IMS Environmental Services
3901 B Commerce Park Drive
Raleigh, NC 27610
Date Received
Description
Sample ID
Collected By
Collection Date
October 11, 2002
Elkins Chrysler
MW-1 SS-5 20-22 FT
Matt Renfrow
10/10/02 10:15
Parameter Dry Result
Total Solids
Chromium
Lead
Volatile Petroleum Hydrocarbons cs-ca Aliphatics
C9-Cl2 Aliphatics
C9-Cl0 Aromatics
Surrogate Recovery
2,5-Dibromotoluene(FID)
2,5-Dibromotoluene(PID)
Volatile Organics
Acetone
Acrolein
Acrylonitrile
Benzene
Bromobenzene
Bromodichloromethane
Bromoforrn
Bromomethane
n-Butylbenzene
sec-Butylbenzene
tert-Butylbenzene
Carbon tetrachloride
Chlorobenzene
Chlorodibromomethane
Chlo roe thane
2-Chloroethyl vinyl ether
Chloroform
Chloromethane
2-Chlorotoluene
4-Chlorotoluene
l,2-Dibromo-3-Chloropropane
1,2-Dibromoethane
Dibromomethane
1,2-Dichlorobenzene
1,3-Dichlorobenzene
1,4-Dichlorobenzene
Results listed are dry weight basis.
BDL -Below Detection Limit
83.1
32.
28.
BDL
BDL
BDL
BDL
105.
89.0
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
Det. Limit -Estimated Quantitation Limit(EQL)
Det. Limit
0.60
0.30
6.0
6.0
6.0
6.0
0.060
0.060
0.060
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.060
0.0060
0.0012
0.0012
0.0012
0.0024
0.0012
0.0012
0.0012
0.0012
0.0012
Tax I.D. 62-0814289
Est. 1970
October 17,2002
ESC Sample # L92355-05
Site ID
Project # : 551.0216
Units Method Date
% 2540G 10/12/02
mg/kg 6010B 10/16/02
mg/kg 6010B 10/16/02
mg/kg MADEPV 10/16/02
mg/kg MADEPV 10/16/02
mg/kg MADEPV 10/16/02
mg/kg MADEPV 10/16/02
% Rec. MADEPV 10/16/02
% Rec. MADEPV 10/16/02
mg/kg 8260B 10/16/02
mg/kg 8260B 10/16/02
mg/kg 8260B 10/16/02
mg/kg 8260B 10/16/02
mg/kg 8260B 10/16/02
mg/kg 8260B 10/16/02
mg/kg 8260B 10/16/02
mg/kg 8260B 10/16/02
mg/kg 8260B 10/16/02
mg/kg 8260B 10/16/02
mg/kg 8260B 10/16/02
mg/kg 8260B 10/16/02
mg/kg 8260B 10/16/02
mg/kg 8260B 10/16/02
mg/kg 8260B 10/16/02
mg/kg 8260B 10/16/02
mg/kg 8260B 10/16/02
mg/kg 8260B 10/16/02
mg/kg 8260B 10/16/02
mg/kg 8260B 10/16/02
mg/kg 8260B 10/16/02
mg/kg 8260B 10/16/02
mg/kg 8260B 10/16/02
mg/kg 8260B 10/16/02
mg/kg 8260B 10/16/02
mg/kg 8260B 10/16/02
Laboratory Certification Numbers:
Oil.
1
1
1
50
50
50
50
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
A2LA -1461-01, AIHA -100789, AL -40660, CA -I-2327, CT-PH-0197, FL -E87487, GA -923, IN -C-TN-01
KY -90010, KYUST -0016, NC -ENV375,DW21704, ND -R-140, SC -84004, TN -2006, VA -00109, WV -233
Note:
This report shall not be reproduced, except in full, without the written approval from ESC.
The reported analytical results relate only to the sample submitted
Page 17 of 26
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• ENVIRONMENTAL
SCIENCE CORP.
REPORT OF ANALYSIS
Bobby Veit
IMS Environmental Services
3901 B Commerce Park Drive
Raleigh, NC 27610
Date Received
Description
Sample ID
Collected By
Collection Date
October 11, 2002
Elkins Chrysler
MW-1 SS-5 20-22 FT
Matt Renfrow
10/10/02 10:15
Parameter Dry Result
Dichlorodifluoromethane
1,1-Dichloroethane
1,2-Dichloroethane
1,1-Dichloroethene
cis-1,2-Dichloroethene
trans-1,2-Dichloroethene
1,2-Dichloropropane
1,1-Dichloropropene
1,3-Dichloropropane
cis-1,3-Dichloropropene
trans-1,3-Dichloropropene
2,2-Dichloropropane
Di-isopropyl ether
Ethylbenzene
Hexachlorobutadiene
Isopropylbenzene
p-Isopropyltoluene
2-Butanone (MEK)
Methylene Chloride
4-Methyl-2-pentanone (MIBK)
Methyl tert-butyl ether
Naphthalene
n-Propylbenzene
Styrene
1,1,1,2-Tetrachloroethane
1,1,2,2-Tetrachloroethane
Tetrachloroethene
Toluene
1,2,3-Trichlorobenzene
1,2,4-Trichlorobenzene
1,1,1-Trichloroethane
1,1,2-Trichloroethane
Trichloroethene
Trichlorofluoromethane
1,2,3-Trichloropropane
1,2,4-Trimethylbenzene
1,3,5-Trimethylbenzene
Vinyl chloride
Xylenes, Total
Surrogate Recovery
Results listed are dry weight basis.
BDL -Below Detection Limit
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
Det. Limit -Estimated Quantitation Limit(EQL)
Det. Limit
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.060
0.0060
0.060
0.0012
0.0060
0.0012
0.0012
0.0012
0.0012
0.0012
0.0060
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.0012
0.0036
12065 Lebanon Rd.
Mt. Juliet, TN 37122
(615) 758-5858
1-800-767-5859
Fax (615) 758-5859
Tax I.D. 62-0814289
Est. 1970
October 17,2002
ESC Sample #
Site ID
Project # :
Units
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
Method
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
8260B
L92355-05
551. 0216
Date Dil.
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
10/16/02 1
Laboratory Certification Numbers:
A2LA -1461-01, AIHA -100789, AL -40660, CA -I-2327, CT-PH-0197, FL -E87487, GA -923, IN -C-TN-01
KY -90010, KYlJST -0016, NC -ENV375,DW21704, ND -R-140, SC -84004, TN -2006, VA -00109, WV -233
Note:
This report shall not be reproduced, except in full, without the written approval from ESC.
The reported analytical results relate only to the sample submitted
Page 18 of 26
•• I ENVIRONMENTAL
SCIENCE CORP.
12065 Lebanon Rd.
Mt. Juliet, TN 37122
(615) 758-5858
1-800-767-5859
Fax (615) 758-5859
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Bobby Veit
IMS Environmental Services
3901 B Commerce Park Drive
Raleigh, NC 27610
Date Received
Description
October 11, 2002
Elkins Chrysler
Sample ID MW-1 SS-5 20-22 FT
Collected By
Collection Date
Parameter
Matt Renfrow
10/10/02 10:15
Toluene-dB
Dibromofluoromethane
4-Bromofluorobenzene
Extractable Petroleum Hydrocarb
C9-Cl8 Aliphatics
Cl9-C36 Aliphatics
Cll-C22 Aromatics
Surrogate Recovery
o-Terphenyl
1-Chloro-octadecane
2-Fluorobiphenyl
2-Bromonaphthanene
Base/Neutral Extractables
Acenaphthene
Acenaphthylene
Anthracene
Benzi dine
Benzo(a)anthracene
Benzo(b)fluoranthene
Benzo(k)fluoranthene
Benzo(g,h,i)perylene
Benzo(a)pyrene
Bis(2-chlorethoxy)methane
Bis(2-chloroethyl)ether
Bis(2-chloroisopropyl)ether
4-Bromophenyl-phenylether
2-Chloronaphthalene
4-Chlorophenyl-phenylether
Chrysene
Dibenz(a,h)anthracene
3,3-Dichlorobenzidine
2,4-Dinitrotoluene
2,6-Dinitrotoluene
Fluoranthene
Fluorene
Hexachlorobenzene
Hexachloro-1,3-butadiene
Hexachlorocyclopentadiene
Results listed are dry weight basis.
BDL -Below Detection Limit
Dry
REPORT OF ANALYSIS
Result
100
llO
llO
BDL
BDL
BDL
BDL
74.0
64.0
74.0
97.0
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
Det. Limit
6.6
6.6
6.6
6.6
0 .40
0.40
0.40
0.40
0.40
0 .40
0 .40
0 .40
0 .40
0 .40
0 .40
0.40
0.40
0.40
0 .40
0 .40
0 .40
0 .40
0 .40
0.40
0.40
0 .40
0.40
0 .40
0 .40
Det. Limit -Estimated Quantitation Limit{EQL)
Tax I.D. 62-0814289
Est. 1970
October 17,2002
ESC Sample # L92355-05
Site ID
Project # : 551.0216
Units Method Date
% Rec. 8260B 10/16/02
% Rec. 8260B 10/16/02
% Rec. 8260B 10/16/02
mg/kg MADE PE 10/16/02
mg/kg MADE PE 10/16/02
mg/kg MADE PE 10/16/02
mg/kg MADE PE 10/16/02
% Rec. MADE PE 10/16/02
% Rec. MADE PE 10/16/02
% Rec. MADE PE 10/16/02
% Rec. MADE PE 10/16/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
Laboratory Certification Numbers:
Dil.
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
A2LA -1461-01, AIHA -100789, AL -40660, CA -I-2327, CT-PH-0197, FL -E87487, GA -923, IN -C-TN-01
KY -90010, KYUST -0016, NC -ENV375,DW21704, ND -R-140, SC -84004, TN -2006, VA -00109, WV -233
Note:
This report shall not be reproduced, except in full, without the written approval from ESC.
The reported analytical results relate only to the sample submitted
Page 19 of 26
•• I ENVIRONMENTAL
SCIENCE CORP.
12065 Lebanon Rd.
Mt. Juliet, TN 37122
(615) 758-5858
1-800-767-5859
Fax (615) 758-5859
I
I
I
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REPORT OF ANALYSIS
Bobby Veit
IMS Environmental Services
3901 B Commerce Park Drive
Raleigh, NC 27610
Date Received
Description
Sample ID
Collected By
Collection Date
October 11, 2002
Elkins Chrysler
MW-1 SS-6 25-27 FT
Matt Renfrow
10/10/02 10:30
Parameter Dry Result
Total Solids
Chromium
Lead
Volatile Petroleum Hydrocarbons cs-ca Aliphatics
C9-C12 Aliphatics
C9-C10 Aromatics
Surrogate Recovery
2,5-Dibromotoluene(FID)
2,5-Dibromotoluene(PID)
Volatile Organics
Acetone
Acrolein
Acrylonitrile
Benzene
Bromobenzene
Bromodichloromethane
Bromoform
Bromomethane
n-Butylbenzene
sec-Butylbenzene
tert-Butylbenzene
Carbon tetrachloride
Chlorobenzene
Chlorodibromomethane
Chloroethane
2-Chloroethyl vinyl ether
Chloroform
Chloromethane
2-Chlorotoluene
4-Chlorotoluene
1,2-Dibromo-3-Chloropropane
1,2-Dibromoethane
Dibromomethane
1,2-Dichlorobenzene
1,3-Dichlorobenzene
1,4-Dichlorobenzene
Results listed are dry weight basis.
BDL -Below Detection Limit
75.8
13.
52.
BDL
BDL
BDL
BDL
104.
88.0
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
Det. Limit -Estimated Quantitation Limit(EQL)
Det. Limit
0.66
0.33
7.8
7.8
7.8
7.8
0.066
0.066
0.066
0. 0013
0.0013
0. 0013
0. 0013
0. 0013
0.0013
0.0013
0. 0013
0. 0013
0. 0013
0. 0013
0.0013
0.066
0.0066
0.0013
0. 0013
0. 0013
0.0026
0. 0013
0. 0013
0. 0013
0.0013
0. 0013
Tax I.D. 62-0814289
Est. 1970
October 17,2002
ESC Sample # L92355-06
Site ID
Project # : 551. 0216
Units Method Date
% 2540G 10/12/02
mg/kg 6010B 10/16/02
mg/kg 6010B 10/16/02
mg/kg MADEPV 10/16/02
mg/kg MADEPV 10/16/02
mg/kg MADEPV 10/16/02
mg/kg MADEPV 10/16/02
% Rec. MADEPV 10/16/02
% Rec. MADEPV 10/16/02
mg/kg 8260B 10/16/02
mg/kg 8260B 10/16/02
mg/kg 8260B 10/16/02
mg/kg 8260B 10/16/02
mg/kg 8260B 10/16/02
mg/kg 8260B 10/16/02
mg/kg 8260B 10/16/02
mg/kg 8260B 10/16/02
mg/kg 8260B 10/16/02
mg/kg 8260B 10/16/02
mg/kg 8260B 10/16/02
mg/kg 8260B 10/16/02
mg/kg 8260B 10/16/02
mg/kg 8260B 10/16/02
mg/kg 8260B 10/16/02
mg/kg 8260B 10/16/02
mg/kg 8260B 10/16/02
mg/kg 8260B 10/16/02
mg/kg 8260B 10/16/02
mg/kg 8260B 10/16/02
mg/kg 8260B 10/16/02
mg/kg 8260B 10/16/02
mg/kg 8260B 10/16/02
mg/kg 8260B 10/16/02
mg/kg 8260B 10/16/02
mg/kg 8260B 10/16/02
Laboratory Certification Numbers:
Dil.
1
1
1
59
59
59
59
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
A2LA -1461-01, AIHA -100789, AL -40660, CA -I-2327, CT-PH-0197, FL -E87487, GA -923, IN -C-TN-01
KY -90010, KYUST -0016, NC -ENV375,DW21704, ND -R-140, SC -84004, TN -2006, VA -00109, WV -233
Note:
This report shall not be reproduced, except in full, without the written approval from ESC.
The reported analytical results relate only to the sample submitted
Page 21 of 26
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• ENVIRONMENTAL
SCIENCE CORP.
Bobby Veit
IMS Environmental Services
3901 B Commerce Park Drive
Raleigh, NC 27610
Date Received
Description
October 11, 2002
Elkins Chrysler
Sample ID
Collected By
Collection Date
MW-1 SS-6 25-27 FT
Matt Renfrow
10/10/02 10:30
Parameter
Dichlorodifluoromethane
1,1-Dichloroethane
1,2-Dichloroethane
1,1-Dichloroethene
cis-1,2-Dichloroethene
trans-1,2-Dichloroethene
1,2-Dichloropropane
1,1-Dichloropropene
1,3-Dichloropropane
cis-1,3-Dichloropropene
trans-1,3-Dichloropropene
2,2-Dichloropropane
Di-isopropyl ether
Ethylbenzene
Hexachlorobutadiene
Isopropylbenzene
p-Isopropyltoluene
2-Butanone (MEK)
Methylene Chloride
4-Methyl-2-pentanone (MIBK)
Methyl tert-butyl ether
Naphthalene
n-Propylbenzene
Styrene
1,1,1,2-Tetrachloroethane
1,1,2,2-Tetrachloroethane
Tetrachloroethene
Toluene
1,2,3-Trichlorobenzene
1,2,4-Trichlorobenzene
1,1,1-Trichloroethane
1,1,2-Trichloroethane
Trichloroethene
Trichlorofluoromethane
1,2,3-Trichloropropane
1,2,4-Trimethylbenzene
1,3,5-Trimethylbenzene
Vinyl chloride
Xylenes, Total
Surrogate Recovery
Results listed are dry weight basis.
BDL -Below Detection Limit
Dry
REPORT OF ANALYSIS
Result Det. Limit
BDL 0. 0013
BDL 0. 0013
BDL 0. 0013
BDL 0.0013
BDL 0. 0013
BDL 0. 0013
BDL 0. 0013
BDL 0. 0013
BDL 0. 0013
BDL 0.0013
BDL 0. 0013
BDL 0. 0013
BDL 0.0013
BDL 0.0013
BDL 0. 0013
BDL 0.0013
BDL 0. 0013
BDL 0.066
BDL 0.0066
BDL 0.066
BDL 0. 0013
BDL 0.0066
BDL 0. 0013
BDL 0.0013
BDL 0.0013
BDL 0. 0013
BDL 0.0013
BDL 0.0066
BDL 0.0013
BDL 0. 0013
BDL 0. 0013
BDL 0. 0013
BDL 0. 0013
BDL 0.0013
BDL 0. 0013
BDL 0. 0013
BDL 0.0013
BDL 0.0013
BDL 0.0040
Det. Limit -Estimated Quantitation Limit(EQL)
12065 Lebanon Rd.
Mt. Juliet, TN 37122
(615) 758-5858
1-800-767-5859
Fax (615) 758-5859
Tax I.D. 62-0814289
Est. 1970
October 17,2002
ESC Sample # L92355-06
Site ID
Project # : 551.0216
Units Method Date Dil.
mg/kg 8260B 10/16/02 1
mg/kg 8260B 10/16/02 1
mg/kg 8260B 10/16/02 1
mg/kg 8260B 10/16/02 1
mg/kg 8260B 10/16/02 1
mg/kg 8260B 10/16/02 1
mg/kg 8260B 10/16/02 1
mg/kg 8260B 10/16/02 1
mg/kg 8260B 10/16/02 1
mg/kg 8260B 10/16/02 1
mg/kg 8260B 10/16/02 1
mg/kg 8260B 10/16/02 1
mg/kg 8260B 10/16/02 1
mg/kg 8260B 10/16/02 1
mg/kg 8260B 10/16/02 1
mg/kg 8260B 10/16/02 1
mg/kg 8260B 10/16/02 1
mg/kg 8260B 10/16/02 1
mg/kg 8260B 10/16/02 1
mg/kg 8260B 10/16/02 1
mg/kg 8260B 10/16/02 1
mg/kg 8260B 10/16/02 1
mg/kg 8260B 10/16/02 1
mg/kg 8260B 10/16/02 1
mg/kg 8260B 10/16/02 1
mg/kg 8260B 10/16/02 1
mg/kg 8260B 10/16/02 1
mg/kg 8260B 10/16/02 1
mg/kg 8260B 10/16/02 1
mg/kg 8260B 10/16/02 1
mg/kg 8260B 10/16/02 1
mg/kg 8260B 10/16/02 1
mg/kg 8260B 10/16/02 1
mg/kg 8260B 10/16/02 1
mg/kg 8260B 10/16/02 1
mg/kg 8260B 10/16/02 1
mg/kg 8260B 10/16/02 1
mg/kg 8260B 10/16/02 1
mg/kg 8260B 10/16/02 1
Laboratory Certification Numbers:
A2LA -1461-01, AIHA -100789, AL -40660, CA -I-2327, CT-PH-0197, FL -E87487, GA -923, IN -C-TN-01
KY -90010, KYUST -0016, NC -ENV375,DW21704, ND -R-140, SC -84004, TN -2006, VA -00109, WV -233
Note:
This report shall not be reproduced, except in full, without the written approval from ESC.
The reported analytical results relate only to the sample submitted
Page 22 of 26
I ..
I ENVIRONMENTAL
SCIENCE CORP.
12065 Lebanon Rd.
Mt. Juliet, TN 37122
(615) 758-5858
1-800-767-5859
Fax (615) 758-5859
I
I
I
I
I
I
I
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I
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I
I
REPORT OF ANALYSIS
Bobby Veit
IMS Environmental Services
3901 B Commerce Park Drive
Raleigh, NC 27610
Date Received
Description
Sample ID
Collected By
Collection Date
October 11, 2002
Elkins Chrysler
MW-1 SS-6 25-27 FT
Matt Renfrow
10/10/02 10:30
Parameter Dry Result
Toluene-dB
Dibromofluoromethane
4-Bromofluorobenzene
Extractable Petroleum Hydrocarb
C9-Cl8 Aliphatics
Cl9-C36 Aliphatics
Cll-C22 Aromatics
Surrogate Recovery
o-Terphenyl
1-Chloro-octadecane
2-Fluorobiphenyl
2-Bromonaphthanene
Base/Neutral Extractables
Acenaphthene
Acenaphthylene
Anthracene
Benzidine
Benzo(a)anthracene
Benzo(b)fluoranthene
Benzo(k)fluoranthene
Benzo(g,h,i)perylene
Benzo(a)pyrene
Bis(2-chlorethoxy)methane
Bis(2-chloroethyl)ether
Bis(2-chloroisopropyl)ether
4-Bromophenyl-phenylether
2-Chloronaphthalene
4-Chlorophenyl-phenylether
Chrysene
Dibenz(a,h)anthracene
3,3-Dichlorobenzidine
2,4-Dinitrotoluene
2,6-Dinitrotoluene
Fluoranthene
Fluorene
Hexachlorobenzene
Hexachloro-1,3-butadiene
Hexachlorocyclopentadiene
Results listed are dry weight basis.
BDL -Below Detection Limit
100
110
110
BDL
BDL
BDL
BDL
88.0
80.0
81.0
104.
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
Det. Limit -Estimated Quantitation Limit(EQL)
Det. Limit
7.2
7.2
7.2
7.2
0.44
0.44
0.44
0.44
0.44
0.44
0.44
0.44
0.44
0.44
0.44
0.44
0.44
0.44
0.44
0.44
0.44
0.44
0.44
0.44
0.44
0.44
0.44
0.44
0.44
Tax I.D. 62-0814289
Est. 1970
October 17,2002
ESC Sample # L92355-06
Site ID
Project # : 551.0216
Units Method Date
% Rec. 8260B 10/16/02
% Rec. 8260B 10/16/02
% Rec. 8260B 10/16/02
mg/kg MADE PE 10/16/02
mg/kg MADE PE 10/16/02
mg/kg MADE PE 10/16/02
mg/kg MADE PE 10/16/02
% Rec. MADE PE 10/16/02
% Rec. MADE PE 10/16/02
% Rec. MADE PE 10/16/02
% Rec. MADE PE 10/16/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
mg/kg 8270C 10/15/02
Laboratory Certification Numbers:
Oil.
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
A2LA -1461-01, AIHA -100789, AL -40660, CA -I-2327, CT-PH-0197, FL -E87487, GA -923, IN -C-TN-01
KY -90010, KYUST -0016, NC -ENV375,DW21704, ND -R-140, SC -84004, TN -2006, VA -00109, WV -233
Note:
This report shall not be reproduced, except in full, without the written approval from ESC.
The reported analytical results relate only to the sample submitted
Page 23 of 26
I
I Sample #
I L923SS-01
I
I L923SS-02
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I L923SS-03
I
I L923SS-04
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L923SS-OS
I
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I L923SS-06
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Attachment A
List of Analytes with QC Qualifiers
Analyte
Volatile Petroleum Hydrocarbons
CS-CB Aliphatics
C9-C12 Aliphatics
C9-C10 Aromatics
Acrolein
2-Chloroethyl vinyl ether
Benzidine
3,3-Dichlorobenzidine
4-Nitrophenol
Volatile Petroleum Hydrocarbons
CS-CB Aliphatics
C9-C12 Aliphatics
C9-C10 Aromatics
Acrolein
2-Chloroethyl vinyl ether
Methyl tert-butyl ether
Naphthalene
Benzi dine
3,3-Dichlorobenzidine
4-Nitrophenol
Volatile Petroleum Hydrocarbons
CS-CB Aliphatics
C9-C12 Aliphatics
C9-C10 Aromatics
Acrolein
2-Chloroethyl vinyl ether
Methyl tert-butyl ether
Xylenes, Total
Benzi dine
3,3-Dichlorobenzidine
4-Nitrophenol
Volatile Petroleum Hydrocarbons
CS-CB Aliphatics
C9-C12 Aliphatics
C9-C10 Aromatics
Acrolein
2-Chloroethyl vinyl ether
Methyl tert-butyl ether
Xylenes, Total
Benzi dine
3,3-Dichlorobenzidine
4-Nitrophenol
Volatile Petroleum Hydrocarbons
CS-CB Aliphatics
C9-C12 Aliphatics
C9-C10 Aromatics
Acrolein
2-Chloroethyl vinyl ether
Methyl tert-butyl ether
Xylenes, Total
Benzidine
3,3-Dichlorobenzidine
4-Nitrophenol
Volatile Petroleum Hydrocarbons
CS-CB Aliphatics
C9-C12 Aliphatics
C9-C10 Aromatics
Acrolein
2-Chloroethyl vinyl ether
Methyl tert-butyl ether
Xylenes, Total
Benzi dine
3,3-Dichlorobenzidine
4-Nitrophenol
Nitrobenzene-dS
Qualifier
0
0
0
0
J4
J4
J3
J3
J4
0
0
0
0
J4J6
J4J6
J4JS
J6
J3
J3
J4
0
0
0
0
J4
J4
J4
J3
J3
J3
J4
0
0
0
0
J4
J4
J4
J3
J3
J3
J4
0
0
0
0
J4
J4
J4
J3
J3
J3
J4
0
0
0
0
J4
J4
J4
J3
J3
J3
J4
J2
Page 2S of 26
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Qualifier
J2
J3
J4
JS
J6
0
Attachment B
Explanation of QC Qualifier Codes
Meaning
Surrogate recovery limits have been exceeded; values are outside lower
control limits
The associated batch QC did not successfully meet the established quality
control criteria for precision.
The associated batch QC did not successfully meet the established quality
control criteria for accuracy.
The sample matrix interfered with the ability to make any accurate
determination; spike value is unacceptably high
The sample matrix interfered with the ability to make any accurate
determination; spike value is unacceptably low
(ESC) Sample diluted due to matrix interferences that impaired the ability
to make an accurate analytical determination. The detection limit is
elevated in order to reflect the necessary dilution.
Qualifier Report Information
ESC utilizes sample and result qualifiers as set forth by the EPA Contract Laboratory Program and
as required by most certifying bodies including NELAC. In addition to the EPA qualifiers adopted
by ESC, we have implemented ESC qualifiers to provide more information pertaining to our analytical
results. Each qualifier is designated in the qualifier explanation as either EPA or ESC.
Data qualifiers are intended to provide the ESC client with more detailed information concerning
the potential bias of reported data. Because of the wide range of constituents and variety of
matrices incorporated by most EPA methods, it is common for some compounds to fall outside of
established ranges. These exceptions are evaluated and all reported data is valid and useable
unless qualified as 'R' (Rejected).
Definitions
Accuracy -The relationship of the observed value of a known sample to the
true value of a known sample. Represented by percent recovery and
relevant to samples such as: control samples, matrix spike recoveries,
surrogate recoveries, etc.
Precision -The agreement between a set of samples or between duplicate samples.
Relates to how close together the results are and is represented by
Relative Percent Differrence.
Surrogate -Organic compounds that are similar in chemical composition, extraction,
and chromotography to analytes of interest. The surrogates are used to
determine the probable response of the group of analytes that are chem-
ically related to the surrogate compound. Surrogates are added to the
sample and carried through all stages of preparation and analyses.
TIC -Tentatively Identified Compound: Compounds detected in samples that are
not target compounds, internal standards, system monitoring compounds,
or surrogates.
I Page 26 of 26
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ATTACHMENT C:
Groundwater Analytical Data from October 15, 2001
I ..
I ENVIRONMENTAL
SCIENCE CORP.
12065 Lebanon Rd.
Mt. Juliet, TN 37122
(615) 758-5858
1-800-767-5859
Fax (615) 758-5859
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Mr. Bobby Veit
IMS Environmental Services
3901 B Commerce Park Drive
Raleigh, NC 27610
Date Received
Description
Sample ID
Collected By
Collection Date
Parameter
pH (On Site)
Chromium
Lead
October 16, 2002
Elkins Chrysler
MW-1 30FT
Matt Renfrow
10/15/02 13:30
Volatile Petroleum Hydrocarbons
cs-ca Aliphatics
C9-Cl2 Aliphatics
C9-Cl0 Aromatics
Surrogate Recovery
2,5-Dibromotoluene(FID)
2,5-Dibromotoluene(PID)
Volatile Organics
Acetone
Acrolein
Acrylonitrile
Benzene
Bromobenzene
Bromodichloromethane
Bromoform
Bromomethane
n-Butylbenzene
sec-Butylbenzene
tert-Butylbenzene
Carbon tetrachloride
Chlorobenzene
Chlorodibromomethane
Chloroethane
Chloroform
Chloromethane
2-Chlorotoluene
4-Chlorotoluene
l,2-Dibromo-3-Chloropropane
1,2-Dibromoethane
Dibromomethane
1,2-Dichlorobenzene
1,3-Dichlorobenzene
1,4-Dichlorobenzene
Dichlorodifluoromethane
BDL -Below Detection Limit
REPORT OF ANALYSIS
Result
6.6
15.
37.
BDL
BDL
BDL
BDL
94.0
92.0
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
Det. Limit
10.
5.0
100
100
100
100
50.
50.
50.
1. 0
1. 0
1. 0
1. 0
1. 0
1.0
1.0
1. 0
1. 0
1. 0
1. 0
1. 0
5.0
1. 0
1.0
1. 0
2.0
1. 0
1. 0
1. 0
1. 0
1.0
1. 0
Det. Limit -Estimated Quantitation Limit(EQL)
Tax I.D. 62-0814289
Est. 1970
October 22, 2002
ESC Sample # L92747-01
Site ID
Project # 551.0216
Units Method Date
SU 10/15/02
ug/l 6010B 10/17/02
ug/l 6010B 10/17/02
ug/l MADEPV 10/18/02
ug/l MADEPV 10/18/02
ug/l MADEPV 10/18/02
ug/l MADEPV 10/18/02
% Rec. MADEPV 10/18/02
% Rec. MADEPV 10/18/02
ug/l 6210D 10/19/02
ug/l 6210D 10/19/02
ug/l 6210D 10/19/02
ug/l 6210D 10/19/02
ug/l 6210D 10/19/02
ug/l 6210D 10/19/02
ug/l 6210D 10/19/02
ug/l 6210D 10/19/02
ug/l 6210D 10/19/02
ug/l 6210D 10/19/02
ug/l 6210D 10/19/02
ug/l 6210D 10/19/02
ug/l 6210D 10/19/02
ug/l 6210D 10/19/02
ug/l 6210D 10/19/02
ug/l 6210D 10/19/02
ug/l 6210D 10/19/02
ug/l 6210D 10/19/02
ug/l 6210D 10/19/02
ug/l 6210D 10/19/02
ug/l 6210D 10/19/02
ug/l 6210D 10/19/02
ug/l 6210D 10/19/02
ug/l 6210D 10/19/02
ug/l 6210D 10/19/02
ug/l 6210D 10/19/02
Laboratory Certification Numbers:
Dil.
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
A2LA -1461-01, AIHA -100789, AL -40660, CA -I-2327, CT-PH-0197, FL -E87487, GA -923, IN -C-TN-01
KY -90010, KYUST -0016, NC -ENV375,DW21704, ND -R-140, SC -84004, TN -2006, VA -00109, WV -233
Page 1 of 8
I.
I ENVIRONMENTAL
SCIENCE CORP.
12065 Lebanon Rd.
Mt. Juliet, TN 37122
(615) 758-5858
1-800-767-5859
Fax (615) 758-58~9
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Mr. Bobby Veit
IMS Environmental Services
3901 B Commerce Park Drive
Raleigh, NC 27610
Date Received
Description
Sample ID
Collected By
Collection Date
Parameter
October 16, 2002
Elkins Chrysler
MW-1 30FT
Matt Renfrow
10/15/02 13:30
1,1-Dichloroethane
1,2-Dichloroethane
1,1-Dichloroethene
cis-1,2-Dichloroethene
trans-1,2-Dichloroethene
1,2-Dichloropropane
1,1-Dichloropropene
1,3-Dichloropropane
2,2-Dichloropropane
Di-isopropyl ether
Ethylbenzene
Hexachlorobutadiene
Isopropylbenzene
p-Isopropyltoluene
2-Butanone (MEK)
Methylene Chloride
4-Methyl-2-pentanone (MIBK)
Methyl tert-butyl ether
Naphthalene
n-Propylbenzene
Styrene
1,1,1,2-Tetrachloroethane
1,1,2,2-Tetrachloroethane
Tetrachloroethene
Toluene
1,2,3-Trichlorobenzene
1,2,4-Trichlorobenzene
1,1,1-Trichloroethane
1,1,2-Trichloroethane
Trichloroethene
Trichlorof luoromethane
1,2,3-Trichloropropane
1,2,4-Trimethylbenzene
1,3,5-Trimethylbenzene
Vinyl chloride
a-Xylene
m&p-Xylenes
Surrogate Recovery
Toluene-dB
Dibromof luoromethane
BDL -Below Detection Limit
REPORT OF ANALYSIS
Result
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
100
120
Det. Limit
1. 0
1. 0
1. 0
1. 0
1. 0
1. 0
1. 0
1. 0
1. 0
1.0
1. 0
1. 0
1.0
1.0
50.
5.0
50.
1. 0
5.0
1. 0
1. 0
1. 0
1. 0
1. 0
5.0
1. 0
1. 0
1. 0
1. 0
1. 0
1. 0
1. 0
1. 0
1. 0
1. 0
1. 0
2.0
Det. Limit -Estimated Quantitation Limit(EQL)
Tax I.D. 62-0814289
Est. 1970
October 22, 2002
ESC Sample # L92747-01
Site ID
Project # 551.0216
Units Method Date
ug/l 6210D 10/19/02
ug/l 6210D 10/19/02
ug/l 6210D 10/19/02
ug/l 6210D 10/19/02
ug/l 6210D 10/19/02
ug/l 6210D 10/19/02
ug/l 6210D 10/19/02
ug/l 6210D 10/19/02
ug/l 6210D 10/19/02
ug/l 6210D 10/19/02
ug/l 6210D 10/19/02
ug/l 6210D 10/19/02
ug/l 6210D 10/19/02
ug/l 6210D 10/19/02
ug/l 6210D 10/19/02
ug/l 6210D 10/19/02
ug/l 6210D 10/19/02
ug/l 6210D 10/19/02
ug/l 6210D 10/19/02
ug/l 6210D 10/19/02
ug/l 6210D 10/19/02
ug/l 6210D 10/19/02
ug/l 6210D 10/19/02
ug/l 6210D 10/19/02
ug/l 6210D 10/19/02
ug/l 6210D 10/19/02
ug/l 6210D 10/19/02
ug/l 6210D 10/19/02
ug/l 6210D 10/19/02
ug/l 6210D 10/19/02
ug/l 6210D 10/19/02
ug/l 6210D 10/19/02
ug/l 6210D 10/19/02
ug/l 6210D 10/19/02
ug/l 6210D 10/19/02
ug/l 6210D 10/19/02
ug/l 6210D 10/19/02
% Rec. 6210D 10/19/02
% Rec. 6210D 10/19/02
Laboratory Certification Numbers:
Dil.
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
A2LA -1461-01, AIHA -100789, AL -40660, CA -I-2327, CT-PH-0197, FL -E87487, GA -923, IN -C-TN-01
KY -90010, KYUST -0016, NC -ENV375,DW21704, ND -R-140, SC -84004, TN -2006, VA -00109, WV -233
Page 2 of 8
I.
I ENVIRONMENTAL
SCIENCE CORP.
12065 Lebanon Rd.
Mt. Juliet, TN 37122
(615) 758-5858
1-800-767-5859
Fax (615) 758-5859
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Mr. Bobby Veit
IMS Environmental Services
3901 B Commerce Park Drive
Raleigh, NC 27610
Date Received
Description
Sample ID
Collected By
Collection Date
Parameter
October 16, 2002
Elkins Chrysler
MW-1 30FT
Matt Renfrow
10/15/02 13:30
4-Bromofluorobenzene
Extractable Petroleum Hydrocarb
C9-C18 Aliphatics
C19-C36 Aliphatics
Cll-C22 Aromatics
Surrogate Recovery
o-Terphenyl
1-Chloro-octadecane
2-Fluorobiphenyl
2-Bromonaphthanene
625 Base/Neutrals w/ TIC
Acenaphthene
Acenaphthylene
Anthracene
Benzi dine
Benzo(a)anthracene
Benzo(b)fluoranthene
Benzo(k)fluoranthene
Benzo(g,h,i)perylene
Benzo(a)pyrene
Bis(2-chlorethoxy)methane
Bis(2-chloroethyl)ether
Bis(2-chloroisopropyl)ether
4-Bromophenyl-phenylether
2-Chloronaphthalene
4-Chlorophenyl-phenylether
Chrysene
Dibenz(a,h)anthracene
3,3-Dichlorobenzidine
2,4-Dinitrotoluene
2,6-Dinitrotoluene
Fluoranthene
Fluorene
Hexachlorobenzene
Hexachloro-1,3-butadiene
Hexachlorocyclopentadiene
Hexachloroethane
Indeno(l,2,3-cd)pyrene
BDL -Below Detection Limit
REPORT OF ANALYSIS
Result
110
BDL
BDL
BDL
BDL
63.0
59.0
63.0
66.0
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
Det. Limit
100
100
100
100
10.
10.
10.
50.
10.
10.
10.
10.
10.
10.
10.
10.
10.
10.
10.
10.
10.
10.
10.
10.
10.
10.
10.
10.
10.
10.
10.
Det. Limit -Estimated Quantitation Limit(EQL}
Tax I.D. 62-0814289
Est. 1970
October 22, 2002
ESC Sample # L92747-01
Site ID
Project # 551.0216
Units Method Date
% Rec. 6210D 10/19/02
ug/l MADE PE 10/21/02
ug/l MADE PE 10/21/02
ug/l MADE PE 10/21/02
ug/l MADE PE 10/21/02
% Rec. MADE PE 10/21/02
% Rec. MADE PE 10/21/02
% Rec. MADE PE 10/21/02
% Rec. MADE PE 10/21/02
ug/l 625 10/19/02
ug/l 625 10/19/02
ug/l 625 10/19/02
ug/l 625 10/19/02
ug/l 625 10/19/02
ug/l 625 10/19/02
ug/l 625 10/19/02
ug/l 625 10/19/02
ug/l 625 10/19/02
ug/l 625 10/19/02
ug/l 625 10/19/02
ug/l 625 10/19/02
ug/l 625 10/19/02
ug/l 625 10/19/02
ug/l 625 10/19/02
ug/l 625 10/19/02
ug/l 625 10/19/02
ug/l 625 10/19/02
ug/l 625 10/19/02
ug/l 625 10/19/02
ug/l 625 10/19/02
ug/l 625 10/19/02
ug/l 625 10/19/02
ug/l 625 10/19/02
ug/l 625 10/19/02
ug/l 625 10/19/02
ug/l 625 10/19/02
Laboratory Certification Numbers:
Dil.
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
A2LA -1461-01, AIHA -100789, AL -40660, CA -I-2327, CT-PH-0197, FL -E87487, GA -923, IN -C-TN-01
KY -90010, KYUST -0016, NC -ENV375,DW21704, ND -R-140, SC -84004, TN -2006, VA -00109, WV -233
Page 3 of 8
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SCIENCE CORP.
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Mr. Bobby Veit
IMS Environmental Services
3901 B Commerce Park Drive
Raleigh, NC 27610
Date Received
Description
Sample ID
Collected By
Collection Date
Parameter
Volatile Organics
Acetone
Acrolein
Acrylonitrile
Benzene
October 16, 2002
Elkins Chrysler
TRIP BLANK
Matt Renfrow
10/15/02 00:00
Bromobenzene
Bromodichloromethane
Bromoform
Bromomethane
n-Butylbenzene
sec-Butylbenzene
tert-Butylbenzene
Carbon tetrachloride
Chlorobenzene
Chlorodibromomethane
Chloroethane
Chloroform
Chloromethane
2-Chlorotoluene
4-Chlorotoluene
1,2-Dibromo-3-Chloropropane
1,2-Dibromoethane
Dibromomethane
1,2-Dichlorobenzene
1,3-Dichlorobenzene
1,4-Dichlorobenzene
Dichlorodifluoromethane
1,1-Dichloroethane
1,2-Dichloroethane
1,1-Dichloroethene
cis-1,2-Dichloroethene
trans-1,2-Dichloroethene
1,2-Dichloropropane
1,1-Dichloropropene
1,3-Dichloropropane
2,2-Dichloropropane
Di-isopropyl ether
Ethylbenzene
Hexachlorobutadiene
Isopropylbenzene
BDL -Below Detection Limit
REPORT OF ANALYSIS
Result
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
Det. Limit
0.050
0.050
0.050
0.0010
0.0010
0.0010
0.0010
0. 0010
0.0010
0.0010
0.0010
0.0010
0.0010
0.0010
0.0010
0.0050
0.0010
0.0010
0.0010
0.0020
0.0010
0.0010
0.0010
0.0010
0.0010
0.0010
0.0010
0.0010
0.0010
0.0010
0.0010
0.0010
0.0010
0.0010
0.0010
0.0010
0.0010
0.0010
0.0010
Det. Limit -Estimated Quantitation Limit(EQL)
Units
mg/l
mg/l
mg/l
mg/l
mg/l
mg/l
mg/l
mg/l
mg/l
mg/l
mg/l
mg/l
mg/l
mg/l
mg/l
mg/l
mg/l
mg/l
mg/l
mg/l
mg/l
mg/l
mg/l
mg/l
mg/l
mg/l
mg/l
mg/l
mg/l
mg/l
mg/l
mg/l
mg/l
mg/l
mg/l
mg/l
mg/l
mg/l
mg/l
Laboratory Certification Numbers:
12065 Lebanon Rd.
Mt. Juliet, TN 37122
(615) 758-5858
1-800-767-5859
Fax (615) 758-5859
Tax I.D. 62-0814289
Est. 1970
October 22, 2002
ESC Sample # L92747-02
Site ID
Project # : 551.0216
Method Date Dil.
6210D 10/19/02 1
6210D 10/19/02 1
6210D 10/19/02 1
6210D 10/19/02 1
6210D 10/19/02 1
6210D 10/19/02 1
6210D 10/19/02 1
6210D 10/19/02 1
6210D 10/19/02 1
6210D 10/19/02 1
6210D 10/19/02 1
6210D 10/19/02 1
6210D 10/19/02 1
6210D 10/19/02 1
6210D 10/19/02 1
6210D 10/19/02 1
6210D 10/19/02 1
6210D 10/19/02 1
6210D 10/19/02 1
6210D 10/19/02 1
6210D 10/19/02 1
6210D 10/19/02 1
6210D 10/19/02 1
6210D 10/19/02 1
6210D 10/19/02 1
6210D 10/19/02 1
6210D 10/19/02 1
6210D 10/19/02 1
6210D 10/19/02 1
6210D 10/19/02 1
6210D 10/19/02 1
6210D 10/19/02 1
6210D 10/19/02 1
6210D 10/19/02 1
6210D 10/19/02 1
6210D 10/19/02 1
6210D 10/19/02 1
6210D 10/19/02 1
6210D 10/19/02 1
I A2LA -1461-01, AIHA -100789, AL -40660, CA -I-2327, CT-PH-0197, FL -E87487, GA -923, IN -C-TN-01
KY -90010, KYUST -0016, NC -ENV375,DW21704, ND -R-140, SC -84004, TN -2006, VA -00109, WV -233
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L92747-02 I
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Attachment A
List of Analytes with QC Qualifiers
Analyte
Acrolein
Benzene
Methyl tert-butyl ether
Naphthalene
4,6-Dinitro-2-methylphenol
Nitrobenzene-d5
Phenol-d5
2-Fluorophenol
2,4,6-Tribromophenol
Acrolein
Benzene
Methyl tert-butyl ether
Naphthalene
Qualifier
J4
J4
J4
J4
J4
J2
J2
J2
J2
J4
J4
J4
J4
Page 7 of 8
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Qualifier Meaning
Attachment B
Explanation of QC Qualifier Codes
J2 Surrogate recovery limits have been exceeded; values are outside lower
control limits
J4 The associated batch QC did not successfully meet the established quality
control criteria for accuracy.
Qualifier Report Information
ESC utilizes sample and result qualifiers as set forth by the EPA Contract Laboratory Program and
as required by most certifying bodies including NELAC. In addition to the EPA qualifiers adopted
by ESC, we have implemented ESC qualifiers to provide more information pertaining to our analytical
results. Each qualifier is designated in the qualifier explanation as either EPA or ESC.
Data qualifiers are intended to provide the ESC client with more detailed information concerning
the potential bias of reported data. Because of the wide range of constituents and variety of
matrices incorporated by most EPA methods, it is common for some compounds to fall outside of
established ranges. These exceptions are evaluated and all reported data is valid and useable
unless qualified as 'R' (Rejected).
Definitions
Accuracy -The relationship of the observed value of a known sample to the
true value of a known sample. Represented by percent recovery and
relevant to samples such as: control samples, matrix spike recoveries,
surrogate recoveries, etc.
Precision -The agreement between a set of samples or between duplicate samples.
Relates to how close together the results are and is represented by
Relative Percent Differrence.
Surrogate -Organic compounds that are similar in chemical composition, extraction,
and chromotography to analytes of interest. The surrogates are used to
determine the probable response of the group of analytes that are chem-
ically related to the surrogate compound. Surrogates are added to the
sample and carried through all stages of preparation and analyses.
TIC -Tentatively Identified Compound: Compounds detected in samples that are
not target compounds, internal standards, system monitoring compounds,
or surrogates.
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LIMITATIONS
It is important to note that the soil and groundwater samples analyzed in this investigation
are considered as isolated data points that may not be representative of the subsurface
conditions across the entire site; therefore, the conclusions of this investigation may not
be completely representative of all subsurface conditions. The conclusions are based on
existing analytical data and supplementary site information gathered by IMS as applied,
in accordance with the NCAC Title 15A, Subchapter 2L, Section .0115 and Subchapter
2L, Section .0202. No other warranty is expressed or implied, and IMS will accept no
responsibility for damages or claims resulting from a past or future release or subsequent
remediation.