MO-7861_36478_CA_IAR_20080430

t
Excel Civil &
Environmental
Associates, PLLC
April 30, 2008
Mr. Ron Taraban
NCDENR / MRO / DWM
610 East Center Avenue
Mooresville, North Carolina 28115
RE: Initial Abatement Action Report
Overcash Family Property
5009 Kannapolis Parkway
Kannapolis, North Carolina
NCDENR No. N/A
EXCEL No. 28007
Dear Mr. Taraban:
625 Huntsman Court
Gastonia, NC 28054
Telephone [phone]
Facsimile 704.853.3949
RECEIVED
NCOVNIZ
MAY U 2 2008
Division of Waste Management
UST Section
Mooresville Regional Office
On behalf of Rauch Property Investments, Excel Civil & Environmental Associates,
PLLC, is pleased to submit the Initial Abatement Action Report for the above referenced
site.
If you have any questions, please contact me.
Sincerely yours,
EXCEL CIVIL & ENVIRONMENTAL ASSOCIATES, PLLC
�TStanVf,/P.E., �DEE
Project Engineer

INITIAL ABATEMENT ACTION REPORT
CEIVED
OVERCASH FAMILY PROPERTY l e'VENR
5009 KANNAPOLIS PARKWAY MAY 0 2 20M
' KANNAPOLIS, CABARRUS COUNTY, NORTH CAROLINA
NCDENR NO. NIA Division of Waste i%lanagement
EXCEL NO.28007 UST Section
' Mooresville Regional Office
April 30, 2008
Prepared for:
Rauch Property Investments, LLC
' 1309 Union Road
Gastonia, North Carolina 28054
Prepared by:
Excel Civil & Environmental Associates, PLLC
' 625 Huntsman Court
Gastonia, North Carolina 28054
' .T. Stanf , P.E., DEE
Principal Engineer

TABLE OF CONTENTS
DESCRIPTION
I. General Information
II. Closure Procedures
III. Site Investigation
IV. Conclusions and Recommendations
V. Limitations
VI. References
VII. Signature of Professional Engineer
TABLES
Table 1 - Project Contacts
Table 2 - UST Information
Table 3 - TPH Soil Analytical Data
Table 4 - Compound Specific Soil Analytical Data
FIGURES
Figure 1 - Site Vicinity Map
Figure 2 - Site Plan
Figure 3 - Sampling Locations Map
Figure 4 - TPH Concentration Map
APPENDICES
Appendix A - UST/2 Form
Appendix B - Laboratory Reports and Chain -of -Custody Forms
Appendix C - Site Photographs
Appendix D - Soils Disposal Manifests
PAGE
1
3
5
8
9
9
9

Initial Abatement Action Report Page No. 1
Overcash Family Property
Kannapolis, North Carolina Excel No. 28007
UNDERGROUND STORAGE TANK CLOSURE REPORT
The closure report should contain, at a minimum, the following information. Any other
information that is pertinent to the site should be included.
I. General Information
A. Ownership of USTs
1. Name of UST owner;
Ms. Edna Crines Overcash
2. Owner address and telephone number;
5009 Boy Scout Camp Road (renamed Kannapolis Parkway)
Kannapolis, North Carolina 28081
Contact Person: Edna Crines Overcash
Telephone: [phone]
B. Facility Information
1. Facility name;
Overcash Family Property
2. Facility ID #;
Not Applicable
3. Facility address, telephone number and county;
5009 Kannapolis Parkway
Kannapolis, Cabarrus County, North Carolina
Telephone: Not pplicable
C. Contacts
1. Name, address, telephone number and job title of primary contact
person;
5009 Boy Scout Camp Road
Kannapolis, NC 28081
Contact Person: Edna Crines Overcash
Telephone: [phone]
Excel Civil & Environmental Associates, PLLC

' Initial Abatement Action Report Page No. 2
Overcash Family Property
Kannapolis, North Carolina Excel No. 28007
2. Name, address, and telephone number of closure contractor;
DeBruhl Environmental Excavating
4921 Hoover Drive
' Charlotte, NC 28269
Telephone: [phone]
' 3. Name, address, and telephone number of primary consultant;
Excel Civil & Environmental Associates, PLLC (Excel)
' 625 Huntsman Court
Gastonia, North Carolina 28054
Telephone: [phone]
Attn: Mike Stanforth
4. Name, address, telephone number, and State certification number of
laboratory;
Shealy Environmental Services, Inc.
' Pace Analytical Services, Incorporated
9800 Kincey Avenue, Suite 100
Huntersville, North Carolina 28078
Telephone: [phone]
NC State Certification No. DW37706, WW12, FS5342
' D. UST Information
Tank No.
Size (gal)
Dimensions (ft)
Last Contents
-NIA
500
40" x 96"
Heating Oil
E. Site Characteristics
1. Describe any past releases at this site;
1 �
None
2. Is the facility active or inactive at this time? If the facility is inactive
' note the last time the USTs were in operation;
Currently, the site is inactive and is under plans for redevelopment as a
' commercial property. The approximate 500-gallon UST was formerly
used to fuel the farm house onsite heating system.
' Excel Civil & Environmental Associates, PLLC

' Initial Abatement Action Report Page No. 3
Overcash Family Property
Kannapolis, North Carolina Excel No. 28007
3. Describe surrounding property use (for example, residential,
commercial, farming, etc.);
Surrounding properties consist of primarily residential establishments.
4. Describe site geology/hydrogeology;
The subject site is located in the Charlotte Belt of the Piedmont geologic
' province of North Carolina. The 1985 Geologic Map of North Carolina
indicates this area as being underlain by metavolcanic rock. Partially
weathered subsurface materials are generally referred to as saprolite.
' Saprolite thickness may vary in depth from a few feet near bedrock
outcrops to over 100 feet.
Groundwater was not encountered during closure activities. Based on
previous assessment reports completed for sites within the area,
groundwater is located at approximately 30-fbgl across the site and flows
' in a western direction.
'Ill. Closure Procedures
A. Describe preparations for closure including the steps taken to notify
' authorities, permits obtained and the steps taken to cleanup and purge the
tanks;
' A Notice of Intent: UST Permanent Closure or Change -In -Service form
(GW/UST-3) was not required for removal of this UST.
' B. Note the amount of residual material pumped from the tank(s);
The initial UST removal was completed by the UST owners and no residual fuel
' was reported as removed from the UST.
C. Describe the storage, sampling and disposal of the residual material;
None reported.
�
1 D. Excavation;
' Note: Refer to the "Groundwater Section Guidelines for the Investigation
and Remediation of Soils and Groundwater" on limiting excavations. The
Trust Fund will not pay for excessive excavation unless it is justified and
I
verified by laboratory results.
IExcel Civil & Environmental Associates, PLLC

' Initial Abatement Action Report Page No. 4
Overcash Family Property
Kannapolis, North Carolina Excel No. 28007
1. Describe excavation procedures noting the conditions of the soils
and the dimensions of the excavation in relation to the tanks, piping,
' and/or pumps;
UST closure activities were conducted at the site on March 31, 2008. The
'
side dimensions of the excavation following the removal of the UST was
measured to be approximately 6-feet x 10-feet with a total depth of
approximately 10-fbgl (see Figure 2). The soils stockpiled during
'
excavation activities were removed as necessary for removal of the UST,
initially no soils beyond five feet of the tanks were removed for disposal as
detailed in the NCDENR's Underground Storage Tank Section Guidelines
1
for Site Checks, Tank Closure and Initial Response and Abatement, dated
March 1, 2007 and any subsequent revisions.
2. Note the depth of tank burial(s) (from land surface to top of tank);
'
The UST was located approximately 5-fbgl.
3, Quantity of soil removed;
Q ty ,
'
Approximately 8-tons of soil was removed during the excavation activities
of the UST, stockpiled on -site and disposed of at an offsite facility.
Following collection of the samples from beneath the UST, elevated levels
'
of organic vapors were observed during field screening activities. Excel
proceeded with over -excavation activities until screening results
suggested impacted soils had been removed. Approximately 49.2 total
tons of contaminated soils were removed and disposed of by
Environmental Soils Incorporated located in Lattimore, North Carolina.
4. Describe soil type(s);
' Native or residual soils encountered during closure activities (materials
sampled) were observed to be brown to reddish brown in color consisting
of a silt -clay mixture (CL).
' 5. Type and source of backfill used;
Backfill soils were brought to the site in order td return the site back to
' grade.
E. CONTAMINATED SOIL
1. Describe how it was determined to what extent to excavate the soil;
Excel Civil & Environmental Associates, PLLC

' Initial Abatement Action Report Page No. 5
Overcash Family Property
Kannapolis, North Carolina Excel No. 28007
' An OVA meter was used to screen the soil samples removed from the
excavation pit. The over -excavation activities reached a total depth of
approximately 12-fbgl within the area of the former UST.
2. Describe method of temporary storage, sampling and
' treatment/disposal of soil;
Soils were stockpiled on -site prior to excavation activities, at which time
' both stockpile soils and suspected contaminated soils were loaded
directly into a dump -truck for offsite disposal. No stockpile soil samples
were collected due to the direct disposal of all excavated materials.
III. Site Investigation
A. Provide information on field screening and observations, include methods
used to calibrate field -screening instrument(s);
' Initial soil samples were collected from beneath the UST and following over -
excavation activities soil samples were collected from the sidewalls and base of
the excavation. All soil samples were screened during assessment activities as
part of Excel standard operating procedures for UST Closures. OVA meter
readings from these soils ranged from < 1 to 300 parts per million (ppm).
The OVA meter is calibrated at the beginning of any field activities in which the
equipment will be used by Excel Personnel.
' B. Describe soil sampling points and sampling procedures used;
' Two (2) initial soil samples were collected from beneath the UST based on the
overall length of the tank. Additional soil samples were collected from the
sidewalls and base of the excavation in accordance with the NCDENR UST
' Closure Policy Guidelines (refer to Figure 3).
Soil samples for laboratory analysis were preserved and packed into approved
' sample containers, st ed in a chilled cooler, and submitted to a North Carolina
certified laboratory. he samples collected from the sidewalls and base of the
excavation were analyzed for volatile organics by EPA Method 8260, semi -
volatile organics by EPA Method 8270, MADEP VPH and MADEP EPH. Soil
samples collected from directly beneath the UST were analyzed for Total
' Petroleum Hydrocarbons, Gasoline and Diesel Range Organics by EPA Method
TPH-5030 and TPH-3550, respectively.
' C. Describe ground water or surface water sampling procedures used,
including:
Excel Civil & Environmental Associates, PLLC

1
Initial Abatement Action Report
Overcash Family Property
Kannapolis, North Carolina
I D.
1
Page No. 6
Excel No. 28007
Note: Refer to the "Groundwater Section Guidelines for the Investigation
and Remediation of Soils and Groundwater" for information about
sampling requirements.
No groundwater was encountered during the excavation.
Quality Control Measures
Describe sample -handling procedures including sample preservation and
transportation;
After collection, samples were placed in laboratory -supplied containers and
labeled. The samples were then placed in an ice filled cooler for preservation
and transported to the laboratory for analysis.
Describe decontamination procedures used;
The decontamination procedures outlined below are used for field equipment
(e.g., hand augers, split spoon sampling device, trowels) that come into direct
contact with the material being sampled and that is used more than once at a
particular site.
' The decontamination procedures outlined below are used for field equipment
(e.g., hand augers, split spoon sampling device, trowels) that come into direct
contact with the material being sampled and that is used more than once at a
' particular site.
No equipment was utilized during the UST closure sampling activities. To reduce
' the risk of cross contamination, new disposable latex gloves were worn during
each sample collection.
Describe time and date samples were collected and date submitted to lab;
Soil samples were collected at the site at 1603 and 1605 on March 25, 2008 and
between 920 and 941 on April 14, 2008. The soil samples were logged into the
laboratory on March 25 and 14, 2008 (see Appendix B).
Describe samples collected for quality control purl6oses (e.g. duplicates,
' field blanks, trip blanks, etc.). Include methods used to obtain these
samples and analytical parameters;
' No trip blanks were utilized for this assessment
' Describe how results of quality control samples may have affected your
interpretation of soil, groundwater or surface water sample results;
' Excel Civil & Environmental Associates, PLLC

' Initial Abatement Action Report Page No. 7
Overcash Family Property
Kannapolis, North Carolina Excel No. 28007
' Describe how results of quality control samples may have affected your
interpretation of soil, groundwater or surface water sample results;
No trip blanks were utilized for this assessment
E. Investigation Results
Describe results of Site Sensitivity Evaluation (SSE), (if SSE was not
' conducted, explain why not)
The subject property appears to be primarily served by private well service. On
' April 14, 2008, Excel personnel conducted a reconnaissance for potable wells
within 1,500 feet of the site; five were identified during the vehicle
reconnaissance. The nearest surface water body is Afton Run which forms the
' western subject property line...
In addition, any underground utilities such as storm sewer, sanitary sewer, water
lines, etc., are typically considered potential vapor collection points and conduits
for vapor/contamination travel.
Describe methods of analyses used (include U.S. EPA method number);
Two (2) soil samples were collected from beneath the UST, one from beneath
' the associated product piping and analyzed for TPH-5030 and 3550.
' Four (4) soil samples were collected from the sidewalls and one (1) from the
base of the excavation and analyzed for volatile organics by EPA Method 8260,
semi -volatile organics by EPA Method 8270, MADEP VPH and MADEP EPH.
' Describe analytical results for samples; discuss in relation to site -specific
cleanup level or action level, as appropriate;
' The soil samples (S-1 and S-2) collected from beneath the 500-gallon UST (SS-
1) were found to be above NCDENR action levels of 10 ppm for both TPH-GRO
& DRO analysis. The soilsample (S-3) collected from beneath the product piping
was found to be below the ion levels.
Analytical results for soil §amples collected from the sidewalls and base of the
' excavation were found to be below the applicable Soil -to -Water Maximum Soil
Contaminant Concentrations (MSCCs) for all constituents. Laboratory analytical
results for the soil samples are presented in Table 3 and Table 4, respectively,
with the analytical laboratory report presented in Appendix B. A completed
GW/UST-2 form is also included in Appendix A.
IExcel Civil & Environmental Associates, PLLC
1

Initial Abatement Action Report Page No. 8
Overcash Family Property
Kannapolis, North Carolina Excel No. 28007
IV. Conclusions and Recommendations
Include probable sources of contamination, further investigation or
remediation tasks, or whether no further action is required;
Based upon the information in this report, it appears that the soils at the
Overcash Family Property facility located at 5009 Kannapolis Parkway,
Kannapolis, North Carolina, do not contain levels of petroleum hydrocarbons
which exceed the applicable Soil -to -Water MSCCs. Therefore at this time based
on the information in this report we recommend No Future Assessment be
conducted at the subject site.
Excel Civil & Environmental Associates, PLLC

' Initial Abatement Action Report Page No. 9
Overcash Family Property
Kannapolis, North Carolina Excel No. 28007
V. Limitations
' This report is based on a limited number of soil samples and chemical analyses. The
conclusions presented in this report are based only on the observation made during this
investigation and on data provided by others. The report presents a description of the
' subsurface conditions observed at each excavation location during this investigation.
Subsurface conditions may vary significantly with time, particularly with respect to
groundwater elevations and quality. Conclusions and recommendations set forth herein
are applicable only to the facts and conditions described at the time of this report.
In performing its professional services, Excel uses that degree of care and skill
exercised under similar circumstances by members of the environmental profession
practicing at the same or similar locality under similar conditions. The standard of care
shall be judged exclusively as of the time these services are rendered and not
according to later standards. Excel makes no express or implied warranty beyond its
conformance to this standard. Excel shall not be responsible for conditions or
consequences arising from the relevant facts that were concealed, withheld or not fully
' disclosed for this report. Excel believes that all information contained in this report is
factual, but no guarantee is made or implied.
' VI. References
EPA Region III, 1997. Risk -based Concentration Tables (RBC Tables). Office of RCRA,
Technical and Program Branch,(httr)://www.epa.gov/reg3hwmd/index.html).
' North Carolina Department of Environment, Health and Natural Resources, March 1997
and amendments. "Groundwater Section Guidelines for the Investigation and
Remediation of Soil and Groundwater."
North Carolina Department of Environment and Natural Resources, January 1998 and
amendments. "Groundwater Section Guidelines for the Investigation and Remediation
of Soil and Groundwater."
North Carolina Department of Environment and Natural Resources, March 2007.
"Underground Storage Tank Section Guidelines for Site Checks, T nk Closure and
Initial Response and Abatement."
VII. Signature of Professional Engineer
ichael T. gtdnforth, P.E., DEE
Principal Engineer
' Excel Civil & Environmental Associates, PLLC

TABLES
Table 1 - Project Contacts
Table 2 - UST Information
Table 3 - TPH Soil Analytical Data
Table 4 - Compound Specific Soil Analytical Data

Table 1 - Project Contacts
(Overcash Family Property
5009 Kannapolis Parkway
Kannapolis, North Carolina
Owner Name:
Edna Crines Overcash
Address:
5009 Boy Scout Camp Road, Kannapolis, NC 28081
Telephone Number:
704-659-6599
Name:
Karl Kirk
Job Title:
Property Owner/Representative
Telephone Number:
704) 351-4200
Name:
DeBruhl Environmental Excavating
Address:
4921 Hoover Drive, Charlotte, NC 28269
Telephone Number:
704) 598-2681
Name:
Excel Civil & Environmental Associates, PLLC
Address:
625 Huntsman Court, Suite B, Gastonia NC 28056
Telephone Number:
[phone]
Name: Shealy Environmental Services, Inc.
Name: Pace Analytical Services, Inc.
Address: 106 Vantage Point Drive, West Columbia, SC 29172
Telephone Number: 803) 791-9700
Certification Number: DW37706, WW12, FS5342

Table 2 - UST Information
Overcash Property
5009 Kannapolis Parkway
Kannapolis, North Carolina
I
11
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FIGURES
' Figure 1 - Site Vicinity Map
' Figure 2 - Site Plan
Figure 3 - Sampling Locations Map
Figure 4 - TPH Concentration Map

EXCEL CIVIL & ENVIRONMENTAL
ASSOCIATES, PLLC
625 HUNTSMAN COURT
GASTONIA, NC 28054
(704) 853-08000
FIGURE 1 - Topographical
Map
Excel Project Number 28007
Source: U.S.G.S. 7.5 Minute Topographic Map
Kannapolis-NC, Quadrangle, 1983
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APPENDICES
Appendix A — UST/2 Form
Appendix B — Laboratory Reports and Chain -of -Custody Forms
' Appendix C — Site Photographs
Appendix D — Soils Disposal Manifests

�I
p
1
APPENDIX A
UST/2 Form
I
1
1

UST-2 Rev 11/2006

F
APPENDIX B
Laboratory Reports and Chain -of -Custody Forms
n

ENVIRONMENTAL
SCIENCE CORP.
Mr. Mike Stanforth
Excel Civil & Environmental Associates
PO Box 6172
Gastonia, NC 28056-6000
12065 Lebanon Rd.
Mt. Juliet, TN 37122
[phone]
1-800-767-5859
Fax [phone]
Tax I.D. 62-0814289
Est. 1970
The analytical results in this report are based upon information supplied
by you, the client, and are for your exclusive use. If you have any
I
questions regarding this data package, please do not hes ate to 11
Entire Report Reviewed By:
Laboratory Cerd£cadon Numbers Jimmy un epresen a l ve
A2LA - 1461-01, AIHA - 09227, 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
NJ - TN002, SC - 84004, TN - 2006, VA - 00109, WV - 233
AZ - 0612, MN - 047-999-395, NY - 11742, WI - 998093910
This report may not be reproduced, except in full, without written approval from Environmental Science Corp.
3 Samples Reported: 04/01/08 13:23 Printed: 04/01/08 13:23
Page 1 of 8

12065 Lebanon Rd.
Mt. Juliet, TN 37122
ENVIRONMENTAL
1-800-767-5859
SCIENCE CORP.
Fax [phone]
Tax I.D. 62-0814289
Est. 1970
REPORT
OF ANALYSIS
Mr. Mike Stanforth
April 01,2008
Excel Civil & Environmental Associa
PO Box 6172
Gastonia, NC 28056-6000
ESC Sample # L337897-01
Date Received March 26, 2008
Description Ranch UST Closure
Site ID
Sample ID S-1
Project # 28009
Collected By M. Stanforth
Collection Date 03/25/08 16:01
Parameter Dry
Result
Det. Limit
Units Method Date
Dil.
Total Solids
67.2
% 254OG 03/29/08
1
TPH (GC/FID) Low Fraction
95.
15.
mg/kg 5035/GRO 03/29/08
100
Surrogate Recovery (10-130)
a,a,a-Trifluorotoluene(FID)
89.4
% Rec. 5035/GRO 03/29/08
100
TPH (GC/FID) High Fraction
11000
300
mg/kg DRO 03/29/08
50
Surrogate Recovery (50-150)
o-Terphenyl
0.00
% Rec. DRO 03/29/08
50
Results listed are dry weight basis.
BDL - Below Detection Limit
Det. Limit - Practical Quantitation Limit(PQL)
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
Reported: 04/01/08 13:23 Printed: 04/01/08 13:23
Page 2 of 8

ENVIRONMENTAL
SCIENCE CORP.
REPORT OF ANALYSIS
Mr. Mike Stanforth
Excel Civil & Environmental Associa
PO Box 6172
Gastonia, NC 28056-6000
12065 Lebanon Rd.
Mt. Juliet, TN 37122
[phone]
1-800-767-5859
Fax [phone]
Tax I.D. 62-0814289
Est. 1970
April 01,2008
ESC Sample # : L337897-02
Date Received
March 26, 2008
Description
Ranch UST Closure
Site
ID
Sample ID
S-2
Project #
28009
Collected By
M. Stanforth
Collection Date
03/25/08 16:03
Parameter
Dry
Result
Det. Limit Units
Method
Date
Dil.
Total Solids
84.2
%
2540G
03/29/08
1
TPH (GC/FID) Low
Fraction
39.
12. mg/kg
5035/GRO
03/31/08
100
Surrogate Recovery
(70-130)
a,a,a-Trifluorotoluene(FID)
94.1
% Rec.
5035/GRO
03/31/08
100
TPH (GC/FID) High
Fraction
16000
480 mg/kg
DRO
03/29/08
100
Surrogate Recovery
(50-150)
o-Terphenyl
0.00
% Rec.
DRO
03/29/08
100
Results listed are dry weight basis.
BDL - Below Detection Limit
Det. Limit - Practical Quantitation Limit(PQL)
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
Reported: 04/01/08 13:23 Printed: 04/01/08 13:23
Page 3 of 8

12065 Lebanon Rd.
0
Mt. JulietTN 37122
,-5859
ENVIRONMENTAL
858
1-800-767
SCIENCE CORP.
Fax [phone]
Tax. I.D. 62-0814289
Est. 1970
REPORT
OF ANALYSIS
Mr. Mike Stanforth
April 01,2008
Excel Civil & Environmental Associa
PO Box 6172
Gastonia, NC 28056-6000
ESC Sample # L337893-03
Date Received March 26, 2008
Description Ranch UST Closure
Site ID
Sample ID S-3
Project # 28009
Collected By M. Stanforth
Collection Date : 03/25/08 16:05
Parameter Dry
Result
Det. Limit
Units Method Date
Dil.
Total Solids
78.5
% 2540G 03/29/08
1
TPH (GC/FID) Low Fraction
BDL
0.64
mg/kg 5035/GRO 03/30/08
5
Surrogate Recovery (70-130)
a,a,a-Trifluorotoluene(FID)
93.6
Rec. 5035/GRO 03/30/08
5
TPH (GC/FID) High Fraction
BDL
5.1
mg/kg DRO 03/28/08
1
Surrogate Recovery (50-150)
o-Terphenyl
81.7
% Rec. DRO 03/28/08
1
Results listed are dry weight basis.
BDL - Below Detection Limit
Det. Limit - Practical Quantitation Limit(PQL)
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
Reported: 04/01/08 13:23 Printed: 04/01/08 13:23
Page 4 of 8

Attachment A
List of Analytes with QC Qualifiers
Sample # Analyte Qualifier
L337897-01 o-Terphenyl J7
L337897-02 o-Terphenyl J7
Page 5 of 8

Attachment B
Explanation of QC Qualifier Codes
Qualifier Meaning
J7 Surrogate recovery limits cannot be evaluated; surrogates were diluted out I
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, I
or surrogates.
Page 6 of 8
7
L
1

J
F—
L
1
ENVIRONMENTAL
SCIENCE CORP.
Excel Civil & Environmental Associates
Mr. Mike Stanforth
PO Box 6172
Gastonia, NC 28056-6000
Quality Assurance Report
Level II
L337897
12065 Lebanon Rd.
Mt. Juliet, TN 37122
[phone]
1-800-767-5859
Fax [phone]
Tax I.D. 62-0814289
Est. 1970
April 01, 2008
Analyte Result Units Date Analyzed Batch
OU a -,VGA
Total Solids < .1 03/29/08 15:22 WG352521
NPOM
TPH'(GCD} Low ....Faction < .1 mg/kg 03/29%08 15:47 WG352729
;M�c ttkj
Analyte Units Result Duplicate RPD Limit Ref Samp Batch
l' �� 21
Analyte Units Known Val. Result Rec Limit Batch
Total Solids
50
50.0
100. 85-115 WG352521
,hb 6'l F'
TPH GC FID} Low Fraction
mg kg 5.5
5.07
92.1 67 135 WG352729
TPW1y
Analyte
Units LCSD Res Ref Res RPD Limit %Rec Batch
TPH (GC/FID) Low Fraction
m /k� 5.01 5.07 1.12
20 91
WG352729
1�..,,..>,..
FID
TPH (GC/'Low Fraction
mgcg 4.76 4 59 3.67
20 87
WG352863
NMIV
Analyte
Units MS Res Re Res TV 96
Rec Limit
Ref Samp Batch
TPH (GC/FID) Low Fraction
mg/kg
16.9 1.80
5.5
55.0 55-109
L337744 11 WG352729
TPHr(GC%FID) Low Fraction
mg kg
21.8 0.00
5.5
79.2 55-109
L337897-03 WG352863
Analyte
Units MSD Res Ref Res
RPD
Limit %Rec
Ref Samp Batch
,481
TPH (GC/FID) Low Fraction
mg/kg
17.3 16.9
2.08
20 56.3
L337744 it WG352729
M2.13
y
T H (GC FID) Low Fraction
mg/kg
22.3 21.8
20 80.9
L337897-03 WG352863
Batch number /Run number / Sample number cross reference
WG352481: R359728: L337897-01 02 03
WG352521: R359804: L337897-01 02 03
WG352863: R359918: L337897-02 03
WG352729: R359919: L337897-01
* * Calculations are performed prior to rounding of reported values
Page 7 of 8

ENVIRONMENTAL
SCIENCE CORP.
Excel Civil & Environmental Associates
Mr. Mike Stanforth
PO Box 6172
Quality Assurance Report
Level II
12065 Lebanon Rd.
Mt. Juliet, TN 37122
[phone]
1-900-767-5859
Fax [phone]
Tax I.D. 62-0814289
Est. 1970
Gastonia, NC 28056-6000 April 01, 2008
L337897
The data package includes a summary of the analytic results of the quality
control samples required by the SW-846 or CWA methods. The quality control
samples include a method blank, a laboratory control sample, and the matrix
spike/matrix spike duplicate analysis. If a target parameter is outside
the method limits, every sample that is effected is flagged with the
appropriate qualifier in Appendix B of the analytic report.
Method Blank - an aliquot of reagent water carried through the
entire analytic process. The method blank results indicate if
any possible contamination exposure during the sample handling,
digestion or extraction process, and analysis. Concentrations of
target analytes above the reporting limit in the method blank are
qualified with the "B" qualifier.
Laboratory Control Sample - is a sample of known concentration
that is carried through the digestion/extraction and analysis
process. The percent recovery, expressed as a percentage of the
theoretical concentration, has statistical control limits
indicating that the analytic process is "in control". If a
target analyte is outside the control limits for the laboratory
control sample or any other control sample, the parameter is
flagged with a 11J4" qualifier for all effected samples.
Matrix Spike and Matrix Spike Duplicate - is two aliquots of an
environmental sample that is spiked with known concentrations of
target analytes. The percent recovery of the target analytes
also has statistical control limits. If any recoveries that are
outside the method control limits, the sample that was selected
for matrix spike/matrix spike duplicate analysis is flagged with
either a 11J5" or a 11J611. The relative percent difference (%RPD)
between the matrix spike and the matrix spike duplicate
recoveries is all calculated. If the RPD is above the method
limit, the effected samples are flagged with a "J3" qualifier.
Page 8 of 8
u
1
1
1

SHEALY ENVIRONMENTAL SERVICES, INC.
' Report of Analysis
Excel Civil & Environmental Associates, PLLC
' PO Box 6172
Gastonia, NC 28056-6000
Attention: Michael Stanforth
' Project Name: Rauch UST Closure
Project Number:28007
' Lot Number:JD15051
Date Completed:04/23/2008
R. Brooke Montgomery
Project Manager
' This report shall not be reproduced, except in its entirety, without the written approval of Shealy Environmental Services, Inc.
The following non -paginated documents are considered part of this report: Chain of Custody Record and Sample Receipt Checklist.
Shealy Environmental Services, Inc. Page: 1 of 24
106 Vantage Point Drive West Columbia, SC 29172 [phone] Fax [phone] www.shealylab.com Level 1 Reportv2.1

SHEALY ENVIRONMENTAL SERVICES, INC.
SC DHEC No: 32010 NELAC No: E87653 NC DEHNR No: 329
Case Narrative
Excel Civil & Environmental Associates, PLLC
Lot Number: JD15051
This Report of Analysis contains the analytical result(s) for the sample(s) listed on the Sample Summary following this Case Narrative. The sample
receiving date is documented in the header information associated with each sample.
Sample receipt, sample analysis, and data review have been performed in accordance with the most current approved NELAC standards, the
Shealy Environmental Services, Inc. ("Shealy") Quality Assurance Management Plan (QAMP), standard operating procedures (SOPS), and Shealy
policies. Any exceptions to the NELAC standards, the QAMP, SOPs or policies are qualified on the results page or discussed below.
If you have any questions regarding this report please contact the Shealy Project Manager listed on the cover page.
Shealy Environmental Services, Inc. Page: 2 of 24
106 Vantage Point Drive West Columbia, SC 29172 [phone] Fax [phone] www.shealylab.com Level 1 Report v2.1

I SHEALY ENVIRONMENTAL SERVICES, INC.
Sample Summary
Excel Civil & Environmental Associates, PLLC
Lot Number: JD15051
'
Sample Number
Sample ID
Matrix
Date Sampled
Date Received
001
N Sidewall
Solid
04/14/2008 0941
04/15/2008
002
003
E Sidewall
W Sidewall
Solid
Solid
04/14/2008 0920
04/14/2008 0923
04/15/2008
04/15/2008
004
S Sidewall
Solid
04/14/2008 0925
04/15/2008
005
Base
Solid
04/14/2008 0935
04/15/2008
'
(5 samples)
1
I�
' Shealy Environmental Services, Inc. Page: 3 of 24
106 Vantage Point Drive West Columbia, SC 29172 [phone] Fax [phone] www.shealylab.com Level 1 Report v2.1
I�

SHEALY ENVIRONMENTAL SERVICES, INC.
Executive Summary
Excel Civil & Environmental Associates, PLLC
Lot Number: JD15051 ,
Sample Sample ID Matrix Parameter Method Result Q Units Page
(0 detections)
1
11
1
u
1
1
P
Shealy Environmental Services, Inc. Page: 4 of 24
106 Vantage Point Drive West Columbia, SC 29172 [phone] Fax [phone] www.shealylab.com Level 1 Reportv2.1

1
1
1
f'
I
Client: Excel Civil & Environmental Associates, PLLC Laboratory ID: JD15051-001
Description: N Sidewall Matrix: Solid
Date Sampied:04/14/2008 0941 % Solids: 68.2 04/15/2008 2244
Date Received: 0411612008
Volatile Organic Compounds by GC/MS
Run Prep Method Analytical Method Dilution Analysis Date Analyst
Prep Date
Batch
Sample Wt.(g)
1 5035
8260B 1 04/17120081324 LH
77160
4.20
CAS
Analytical
Parameter
Number
Method
Result 0
PQL
Units
Run
Acetone
67-64-1
8260B
ND
35
ug/kg
1
Benzene
71-43-2
8260B
ND
8.7
ug/kg
1
Bromobenzene
108-86-1
8260E
ND
8.7
ug/kg
1.
Bromochloromethane
74-97-5
8260B
ND
8.7
ug/kg
1
Bromodichioromethane
75-27-4
82606
ND
8.7
ug/kg
1
Bromoform
75-25-2
8260B
ND
8.7
ug/kg
1
Bromomethane (Methyl bromide)
74-83-9
8260B
ND
8.7
ug/kg
1
2-Butanone (MEK)
78-93-3
8260B
ND
17
ug/kg
1
n-Butylbenzene
104-51-8
8260E
ND
8.7
ug/kg
1
sec-Butylbenzene
135-98-8
8260B
ND
8.7
ug/kg
1
tert-Butylbenzene
98-06-6
8260B
ND
8.7
ug/kg
1
Carbon tetrachloride
56-23-5
8260B
ND
8.7
ug/kg
1
Chlorobenzene
108-90-7
8260E
ND
8.7
ug/kg
1
Chloroethane
75-00-3
8260B
ND
8.7
ug/kg
1
Chloroform
67-66-3
8260B
ND
8.7
ug/kg
1
Chloromethane (Methyl chloride)
74-87-3
8260B
ND
8.7
ug/kg
1
2-Chlorotoluene
95-49-8
8260E
ND
8.7
ug/kg
1
4-Chlorotoluene
106-43-4
8260B
ND
8.7
ug/kg
1
Dibromochloromethane
124-48-1
8260E
ND
8.7
ug/kg
1
1,2-Dibromoethane (EDB)
106-93-4
8260E
ND
8.7
ug/kg
1
1,2-Dichlorobenzene
95-50-1
8260B
ND
8.7
ug/kg
1
1,3-Dichlorobenzene
541-73-1
8260E
ND
8.7
ug/kg
1
1,4-Dichlorobenzene
106-46-7
8260E
ND
8.7
ug/kg
1
Dichlorodifluoromethane
75-71-8
8260B
ND
8.7
ug/kg
1
1,1-Dichloroethane
75-34-3
8260B
ND
8.7
ug/kg
1
1,2-Dichloroethane
107-06-2
8260B
ND
8.7
ug/kg
1
1,1-Dichloroethene
75-35-4
8260B
ND
8.7
ug/kg
1
cis-1,2-Dichloroethene
156-59-2
8260E
ND
8.7
ug/kg
1
trans-1,2-Dichloroethene
156-60-5
8260E
ND
8.7
ug/kg
1
1,2-Dichloropropane
78-87-5
8260B
ND
8.7
ug/kg
1
1,3-Dichloropropane
142-28-9
8260E
ND
8.7
ug/kg
1
2,2-Dichloropropane
594-20-7
8260B
ND
8.7
ug/kg
1
1,1-Dichloropropene
563-58-6
8260E
ND
8.7
ug/kg
1
cis-1,3-Dichloropropene
10061-01-5
8260E
ND
8.7
ug/kg
1
trans-1,3-Dichloropropene
10061-02-6
8260B
ND
8.7
ug/kg
1
Diisopropyl ether (IPE)
108-20-3
8260E
ND
8.7
ug/kg
1
Ethylbenzene
100-41-4
8260E
ND
8.7
ug/kg
1
2-Hexanone
591-78-6
8260E
ND
17
ug/kg
1
Isopropylbenzene
98-82-8
8260B
ND
8.7
ug/kg
1
p-Isopropyltoluene
99-87-6
8260E
ND
8.7
ug/kg
1
PQL = Practical quantitation limit B = Detected in the method blank E = Quentitation of compound exceeded the calibration range
ND = Not detected at or above the PQL J = Estimated result < PQL and _> MDL P = The RPD between two GC columns exceeds 40%
Where applicable, all soil sample analysis are reported on a dry weight basis unless flagged with a "W' N = Recovery is out of criteria
Shealy Environmental Services, Inc. Page: 5 of 24
106 Vantage Point Drive West Columbia, SC 29172 [phone] Fax [phone] www.shealylab.com Level 1 Report v2.1

Client: Excel Civil & Environmental Associates, PLLC Laboratory ID: JD16051-001
Description: N Sidewall Matrix: Solid
Date Sampled:04/14/2008 0941 % Solids: 68.2 04/16/2008 2244
Date Received:04/1512008
Volatile Organic Compounds by GC/MS
Run Prep Method Analytical Method Dilution Analysis Date Analyst Prep Date Batch Sample Wt.(g)
1 5035 8260B 1 04/17/20081324 LH 77160 4.20
CAS
Analytical
Parameter
Number
Method
Result Q
PQL
Units
Run
Methyl tertiary butyl ether (MTBE)
1634-04-4
8260E
ND
8.7
ug/kg
1
4-Methyl-2-pentanone
108-10-1
8260E
ND
17
ug/kg
1
Methylene chloride
75-09-2
8260B
ND
8.7
ug/kg
1
Naphthalene
91-20-3
8260B
ND
8.7
ug/kg
1
n-Propylbenzene
103-65-1
8260E
ND
8.7
ug/kg
1
Styrene
100-42-5
8260E
ND
8.7
ug/kg
1
1,1,2,2-Tetrachloroethane
79-34-5
8260B
ND
8.7
ug/kg
1
Tetrachloroethene
127-18-4
8260E
ND
8.7
ug/kg
1
Toluene
108-88-3
8260B
ND
8.7
ug/kg
1
1,2,3-Trichlorobenzene
87-61-6
8260B
ND
8.7
ug/kg
1
1,2,4-Trichlorobenzene
120-82-1
8260B
ND
8.7
ug/kg
1
1,1,1-Trichloroethane
71-55-6
8260B
ND
8.7
ug/kg
1
1,1,2-Trichloroethane
79-00-5
8260B
ND
8.7
ug/kg
1
Trichloroethene
79-01-6
8260B
ND
8.7
ug/kg
1
Trichlorofluoromethane
75-69-4
8260B
ND
8.7
ug/kg
1
1,2,3-Trichloropropane
96-18-4
8260B
ND
8.7
ug/kg
1
1,2,4-Trimethylbenzene
95-63-6
8260B
ND
8.7
ug/kg
1
1,3,5-Trimethylbenzene
108-67-8
8260E
ND
8.7
ug/kg
1
Vinyl acetate
108-05-4
8260E
ND
8.7
ug/kg
1
Vinyl chloride
75-01-4
8260B
ND
8.7
ug/kg
1
Xylenes (total)
1330-20-7
8260B
ND
8.7
ug/kg
1
Run 1
Acceptance
Surrogate
Q % Recovery
Limits
1,2-Dichloroethane-d4
74
53-142
Bromofluorobenzene
109
47-138
Toluene-d8
81
68-124
Semivolatile Organic Compounds by GC/MS
Run Prep Method Analytical Method Dilution Analysis Date Analyst Prep Date Batch
1 3550B 8270C 1 04/17/20081159 GLR 04/16/20081315 76991
CAS
Analytical
Parameter
Number
Method
Result Q
PQL
Units
Run
Acenaphthene
83-32-9
8270C
ND
480
ug/kg
1
Acenaphthylene
208-96-8
8270C
ND
480
ug/kg
1
Acetophenone
98-86-2
8270C
ND
480
ug/kg
1
Anthracene
120-12-7
8270C
ND
480
ug/kg
1
Atrazine
1912-24-9
8270C
ND
480
ug/kg
1
Benzaldehyde
100-52-7
8270C
ND
1200
ug/kg
1
Benzo(a)anthracene
56-55-3
8270C
ND
480
ug/kg
1
PQL = Practical quantitation limit B = Detected in the method blank E = Quantitation of compound exceeded the calibration range
ND = Not detected at or above the PQL J = Estimated result < PQL and > MDL P = The RPD between two GC columns exceeds 40%
Where applicable, all soil sample analysis are reported on a dry weight basis unless flagged with a' W' N = Recovery is out of criteria
Shealy Environmental Services, Inc. Page: 6 of 24
106 Vantage Point Drive West Columbia, SC 29172 [phone] Fax [phone] www.shealylab.com Level 1 Report v2.1
1
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1
1
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1
Client: Excel Civil & Environmental Associates, PLLC Laboratory ID: JD15051-001
Description: N Sidewall Matrix: Solid
Date Sampled:04/14/2008 0941 % Solids: 68.2 04/15/2008 22"
Date Received:0411512008
Semivolatile Organic Compounds by GC/MS
Run Prep Method
Analytical Method Dilution Analysis Date
Analyst
Prep Date
Batch
1 3550B
8270C 1 04/17/20081159
GLR
04/16/20081315
76991
CAS Analytical
Parameter
Number Method
Result Q
PQL
Units
Run
Benzo(a)pyrene
50-32-8
8270C
ND
480
ug/kg
1
Benzo(b)fluoranthene
205-99-2
8270C
ND
480
ug/kg
1
Benzo(g,h,i)perylene
191-24-2
8270C
ND
480
ug/kg
1
Benzo(k)fluoranthene
207-08-9
8270C
ND
480
ug/kg
1
1,1'-Biphenyl
92-52-4
8270C
ND
480
ug/kg
1
4-Bromophenyl phenyl ether
101-55-3
8270C
ND
480
ug/kg
1
Butyl benzyl phthalate
85-68-7
8270C
ND
480
ug/kg
1
Caprolactam
105-60-2
8270C
ND
1200
ug/kg
1
Carbazole
86-74-8
8270C
ND
480
ug/kg
1
4-Chloro-3-methyl phenol
59-50-7
8270C
ND
480
ug/kg
1
4-Chloroaniline
106-47-8
8270C
ND
480
ug/kg
1
bis(2-Chloroethoxy)methane
111-91-1
8270C
ND
480
ug/kg
1
bis(2-Chloroethyl)ether
111-44-4
8270C
ND
480
ug/kg
1
bis(2-Chloroisopropyl)ether
108-60-1
8270C
ND
480
ug/kg
1
2-Chloronaphthalene
91-58-7
8270C
ND
480
ug/kg
1
2-Chlorophenol
95-57-8
8270C
ND
480
ug/kg
1
4-Chlorophenyl phenyl ether
7005-72-3
8270C
ND
480
ug/kg
1
Chrysene
218-01-9
8270C
ND
480
ug/kg
1
Di-n-butyl phthalate
84-74-2
8270C
ND
480
ug/kg
1
Di-n-octylphthalate
117-84-0
8270C
ND
480
ug/kg
1
Dibenzo(a,h)anthracene
53-70-3
8270C
ND
480
ug/kg
1
Dibenzofuran
132-64-9
8270C
ND
480
ug/kg
1
3,3'-Dichlorobenzidine
91-94-1
8270C
ND
1200
ug/kg
1
2,4-Dichlorophenol
120-83-2
8270C
ND
480
ug/kg
1
Diethylphthalate
84-66-2
8270C
ND
480
ug/kg
1
Dimethyl phthalate
131-11-3
8270C
ND
480
ug/kg
1
2,4-Dimethylphenol
105-67-9
8270C
ND
480
ug/kg
1
4,6-Dinitro-2-methylphenol
534-52-1
8270C
ND
1200
ug/kg
1
2,4-Dinitrophenol
51-28-5
8270C
ND
1200
ug/kg
1
2,4-Dinitrotoluene
121-14-2
8270C
ND
480
ug/kg
1
2,6-Dinitrotoluene
606-20-2
8270C
ND
480
ug/kg
1
bis(2-Ethylhexyl)phthalate
117-81-7
8270C
ND
480
ug/kg
1
Fluoranthene
206-44-0
8270C
ND
480
ug/kg
1
Fluorene
86-73-7
8270C
ND
480
ug/kg
1
Hexachlorobenzene
118-74-1
8270C
ND
480
ug/kg
1
Hexachlorobutadiene
87-68-3
8270C
ND
480
ug/kg
1
Hexachlorocyclopentadiene
77-47-4
8270C
ND
1200
ug/kg
1
Hexachloroethane
67-72-1
8270C
ND
480
ug/kg
1
Indeno(1,2,3-c,d)pyrene
193-39-5
8270C
ND
480
ug/kg
1
Isophorone
78-59-1
8270C
ND
480
ug/kg
1
PQL = Practical quantitation limit B = Detected in the method blank E = Quantitation of compound exceeded the calibration range
ND = Not detected at or above the PQL J = Estimated result < PQL and > MDL P = The RPD between two GC columns exceeds 40 %
Where applicable, all soil sample analysis are reported on a dry weight basis unless flagged with a "W' N = Recovery is out of criteria
Shealy Environmental Services, Inc. Page: 7 of 24
106 Vantage Point Drive West Columbia, SC 29172 [phone] Fax [phone] www.shealylab.com Level 1 Report v2.1
u

Client: Excel Civil & Environmental Associates, PLLC Laboratory ID: JD15051-001
Description: N Sidewall Matrix: Solid
Date Sampled:04/14/2008 0941 % Solids: 68.2 04/15/2008 2244
Date Received:0411512008
Semivolatile Organic Compounds by GC/MS
Run Prep Method Analytical Method Dilution Analysis Date Analyst Prep Date Batch
1 3550B 8270C 1 04/17/20081159 GLR 04/16/20081315 76991
CAS
Analytical
Parameter
Number
Method
Result Q
PQL
Units
Run
2-Methylnaphthalene
91-57-6
8270C
ND
480
ug/kg
1
2-Methylphenol
95-48-7
8270C
ND
480
ug/kg
1
3 & 4-Methylphenol
106-44-5
8270C
ND
980
ug/kg
1
N-Nitrosodi-n-propylamine
621-64-7
8270C
ND
480
ug/kg
1
N-Nitrosodiphenylamine (Diphenylamine)
86-30-6
8270C
ND
480
ug/kg
1
Naphthalene
91-20-3
8270C
ND
480
ug/kg
1
2-Nitroaniline
88-74-4
8270C
ND
480
ug/kg
1
3-Nitroaniline
99-09-2
8270C
ND
480
ug/kg
1
4-Nitroaniline
100-01-6
8270C
ND
480
ug/kg
1
Nitrobenzene
98-95-3
8270C
ND
480
ug/kg
1
2-Nitrophenol
88-75-5
8270C
ND
480
ug/kg
1
4-Nitrophenol
100-02-7
8270C
ND
1200
ug/kg
1
Pentachlorophenol
87-86-5
8270C
ND
1200
ug/kg
1
Phenanthrene
85-01-8
8270C
ND
480
ug/kg
1
Phenol
108-95-2
8270C
ND
480
ug/kg
1
Pyrene
129-00-0
8270C
ND
480
ug/kg
1
2,4,5-Trichlorophenol
95-95-4
8270C
ND
480
ug/kg
1
2,4,6-Trichlorophenol
88-06-2
8270C
ND
480
ug/kg
1
Run 1
Acceptance
Surrogate
Q % Recovery
Limits
2,4,6-Tribromophenol
55
30-117
2-Fluorobiphenyl
65
33-102
2-Fluorophenol
60
28-104
Nitrobenzene-d5
63
22-109
Phenol-d5
63
27-103
Terphenyl-d14
78
41-120
PQL = Practical quantitation limit B = Detected in the method blank E = Quantitation of compound exceeded the calibration range
ND = Not detected at or above the PQL J = Estimated result < PQL and _> MDL P = The RPD between two GC columns exceeds 40 %
Where applicable, all soil sample analysis are reported on a dry weight basis unless flagged with a "W' N = Recovery is out of criteria
Shealy Environmental Services, Inc. Page: 8 of 24
106 Vantage Point Drive West Columbia, SC 29172 [phone] Fax [phone] www.shealylab.com Level 1 Report v2.1

1
C
1
1
Client: Excel Civil & Environmental Associates, PLLC Laboratory ID: JD15051-002
Description: E Sidewall Matrix: Solid
Date Sampled:04/14/2008 0920 % Solids: 66.7 04/15/2008 2244
Date Received:0411612008
Volatile Organic Compounds by GC/MS
Run Prep Method Analytical Method Dilution Analysis Date Analyst Prep Date Batch Sample Wt.(g)
1 5035 8260B 1 04/17/20081347 LH 77160 4.25
CAS
Analytical
Parameter
Number
Method
Result Q
PQL
units
Run
Acetone
67-64-1
8260B
ND
35
ug/kg
1
Benzene
71-43-2
8260B
ND
8.8
ug/kg
1
Bromobenzene
108-86-1
8260B
ND
8.8
ug/kg
1
Bromochloromethane
74-97-5
8260B
ND
8.8
ug/kg
1
Bromodichloromethane
75-27-4
8260B
ND
8.8
ug/kg
1
Bromoform
75-25-2
8260B
ND
8.8
ug/kg
1
Bromomethane (Methyl bromide)
74-83-9
8260B
ND
8.8
ug/kg
1
2-Butanone (MEK)
78-93-3
8260B
ND
18
ug/kg
1
n-Butylbenzene
104-51-8
8260B
ND
8.8
ug/kg
1
sec-Butylbenzene
135-98-8
8260E
ND
8.8
ug/kg
1
tert-Butylbenzene
98-06-6
8260B
ND
8.8
ug/kg
1
Carbon tetrachloride
56-23-5
8260B
ND
8.8
ug/kg
1
Chlorobenzene
108-90-7
8260E
ND
8.8
ug/kg
1
Chioroethane
75-00-3
8260E
ND
8.8
ug/kg
1
Chloroform
67-66-3
8260B
ND
8.8
ug/kg
1
Chloromethane (Methyl chloride)
74-87-3
8260B
ND
8.8
ug/kg
1
2-Chlorotoluene
95-49-8
8260B
ND
8.8
ug/kg
1
4-Chlorotoluene
106-43-4
8260B
ND
8.8
ug/kg
1
Dibromochloromethane
124-48-1
8260B
ND
8.8
ug/kg
1
1,2-Dibromoethane (EDB)
106-93-4
8260E
ND
8.8
ug/kg
1
1,2-Dichlorobenzene
95-50-1
8260B
ND
8.8
ug/kg
1
1,3-Dichlorobenzene
541-73-1
8260E
ND
8.8
ug/kg
1
1,4-Dichlorobenzene
106-46-7
8260E
ND
8.8
ug/kg
1
Dichlorodifluoromethane
75-71-8
8260B
ND
8.8
ug/kg
1
1,1-Dichloroethane
75-34-3
8260B
ND
8.8
ug/kg
1
1,2-Dichloroethane
107-06-2
8260B
ND
8.8
ug/kg
1
1,1-Dichloroethene
75-35-4
8260B
ND
8.8
ug/kg
1
cis-1,2-Dichloroethene
156-59-2
8260E
ND
8.8
ug/kg
1
trans-1,2-Dichloroethene
156-60-5
8260E
ND
8.8
ug/kg
1
1,2-Dichloropropane
78-87-5
8260B
ND
8.8
ug/kg
1
1,3-Dichloropropane
142-28-9
8260B
ND
8.8
ug/kg
1
2,2-Dichloropropane
594-20-7
8260E
ND
8.8
ug/kg
1
1,1-Dichloropropene
563-58-6
8260E
ND
8.8
ug/kg
1
cis-1,3-Dichloropropene
10061-01-5
8260E
ND
8.8
ug/kg
1
trans-1,3-Dichloropropene
10061-02-6
8260E
ND
8.8
ug/kg
1
Diisopropyt ether (IPE)
108-20-3
8260E
ND
8.8
ug/kg
1
Ethylbenzene
100-41-4
8260B
ND
8.8
ug/kg
1
2-Hexanone
591-78-6
8260E
ND
18
ug/kg
1
isopropylbenzene
98-82-8
8260B
ND
8.8
ug/kg
1
p4sopropyltoluene
99-87-6
8260B
ND
8.8
ug/kg
1
PQL = Practical quantitation limit B = Detected in the method blank E = Quantitation of compound exceeded the calibration range
ND = Not detected at or above the PQL J = Estimated result < PQL and > MDL P = The RPD between two GC columns exceeds 40%
Where applicable, all soil sample analysis are reported on a dry weight basis unless flagged with a' W' N = Recovery is out of criteria
Shealy Environmental Services, Inc. Page: 9 of 24
106 Vantage Point Drive West Columbia, SC 29172 [phone] Fax [phone] www.shealylab.com Level 1 Report v2.1

Client: Excel Civil & Environmental Associates, PLLC Laboratory ID: JD15061-002
Description: E Sidewall Matrix: Solid
Date Sampled:04/14/2008 0920 % Solids: 66.7 04/15/2008 22"
Date Received:0411512008
Volatile Organic Compounds by GC/MS
Run Prep Method Analytical Method Dilution Analysis Date Analyst Prep Date Batch Sample Wt.(g)
1 5035 8260E 1 04/17/20081347 LH 77160 4.25
CAS
Analytical
Parameter
Number
Method
Result Q
PQL
Units
Run
Methyl tertiary butyl ether (MTBE)
1634-04-4
8260E
ND
8.8
ug/kg
1
4-Methyl-2-pentanone
108-10-1
8260B
ND
18
ug/kg
1
Methylene chloride
75-09-2
8260B
ND
8.8
ug/kg
1
Naphthalene
91-20-3
8260B
ND
8.8
ug/kg
1
n-Propylbenzene
103-65-1
8260B
ND
8.8
ug/kg
1
Styrene
100-42-5
8260E
ND
8.8
ug/kg
1
1,1,2,2-Tetrachloroethane
79-34-5
8260B
ND
8.8
ug/kg
1
Tetrachloroethene
127-18-4
8260E
ND
8.8
ug/kg
1
Toluene
108-88-3
8260E
ND
8.8
ug/kg
1
12,3-Trichlorobenzene
87-61-6
8260B
ND
8.8
ug/kg
1
1,2,4-Trichlorobenzene
120-82-1
8260E
ND
8.8
ug/kg
1
1,1,1-Trichloroethane
71-55-6
8260B
ND
8.8
ug/kg
1
1,1,2-Trichloroethane
79-00-5
8260B
ND
8.8
ug/kg
1
Trichloroethene
79-01-6
8260B
ND
8.8
ug/kg
1
Trichlorofluoromethane
75-69-4
8260B
ND
8.8
ug/kg
1
1,2,3-Trichloropropane
96-18-4
8260E
ND
8.8
ug/kg
1
1,2,4-Trimethylbenzene
95-63-6
8260B
ND
8.8
ug/kg
1
1,3,5-Trimethylbenzene
108-67-8
8260E
ND
8.8
ug/kg
1
Vinyl acetate
108-05-4
8260B
ND
8.8
ug/kg
1
Vinyl chloride
75-01-4
8260E
ND
8.8
ug/kg
1
Xylenes (total)
1330-20-7
8260E
ND
8.8
ug/kg
1
Run 1
Acceptance
Surrogate
Q % Recovery
Limits
1,2-Dichloroethane-d4
72
53-142
Bromofluorobenzene
108
47-138
Toluene-d8
82
68-124
Semivolatile Organic Compounds by GC/MS
Run Prep Method Analytical Method Dilution Analysis Date Analyst Prep Date Batch
1 35508 8270C 1 04/17/20081217 GLR 04/16/20081315 76991
CAS
Analytical
Parameter
Number
Method
Result Q
PQL
Units
Run
Acenaphthene
83-32-9
8270C
ND
480
ug/kg
1
Acenaphthylene
208-96-8
8270C
ND
480
ug/kg
1
Acetophenone
98-86-2
8270C
ND
480
ug/kg
1
Anthracene
120-12-7
8270C
ND
480
ug/kg
1
Atrazine
1912-24-9
8270C
ND
480
ug/kg
1
Benzaldehyde
100-52-7
8270C
ND
1200
ug/kg
1
Benzo(a)anthracene
56-55-3
8270C
ND
480
ug/kg
1
PQL = Practical quantitation limit B = Detected in the method blank E = Quantitation of compound exceeded the calibration range
ND = Not detected at or above the PQL J = Estimated result < PQL and > MDL P = The RPD between two GC columns exceeds 40 %
Where applicable, all soil sample analysis are reported on a dry weight basis unless flagged with a' W' N = Recovery is out of criteria
Shealy Environmental Services, Inc. Page: 10 Of 24
106 Vantage Point Drive West Columbia, SC 29172 [phone] Fax [phone] www.shealylab.com Level 1 Report v2.1
1
1
11
1
_l
11

1
1
1
Client: Excel Civil & Environmental Associates, PLLC Laboratory ID: JD15051-002
Description: E Sidewall Matrix: Solid
Date Sampled:04/14/2008 0920 % Solids: 66.7 04/15/2008 2244
Date Received:04115/2008
Semivolatile Organic Compounds by GC/MS
Run Prep Method Analytical Method Dilution Analysis Date Analyst Prep Date Batch
1 3550B 8270C 1 04/17/20081217 GLR 04/16/20081315 76991
CAS
Analytical
Parameter
Number
Method
Result Q
PQL
Units
Run
Benzo(a)pyrene
50-32-8
8270C
NO
480
ug/kg
1
Benzo(b)fluoranthene
205-99-2
8270C
NO
480
ug/kg
1
Benzo(g,h,i)perylene
191-24-2
8270C
NO
480
ug/kg
1
Benzo(k)fluoranthene
207-08-9
8270C
NO
480
ug/kg
1
1,1'-Biphenyl
92-52-4
8270C
ND
480
ug/kg
1
4-Bromophenyl phenyl ether
101-55-3
8270C
NO
480
ug/kg
1
Butyl benzyi phthalate
85-68-7
8270C
ND
480
ug/kg
1
Caprolactam
105-60-2
8270C
NO
1200
ug/kg
1
Carbazole
86-74-8
8270C
ND
480
ug/kg
1
4-Chloro-3-methyl phenol
59-50-7
8270C
NO
480
ug/kg
1
4-Chloroaniline
106-47-8
8270C
NO
480
ug/kg
1
bis(2-Chloroethoxy)methane
111-91-1
8270C
NO
480
ug/kg
1
bis(2-Chloroethyl)ether
111-44-4
8270C
NO
480
ug/kg
1
bis(2-Chloroisopropyl)ether
108-60-1
8270C
ND
480
ug/kg
1
2-Chloronaphthalene
91-58-7
8270C
NO
480
ug/kg
1
2-Chlorophenol
95-57-8
8270C
ND
480
ug/kg
1
4-Chlorophenyl phenyl ether
7005-72-3
8270C
ND
480
ug/kg
1
Chrysene
218-01-9
8270C
NO
480
ug/kg
1
Di-n-butyl phthalate
84-74-2
8270C
ND
480
ug/kg
1
Di-n-octylphthalate
117-84-0
8270C
NO
480
ug/kg
1
Dibenzo(a,h)anthracene
53-70-3
8270C
ND
480
ug/kg
1
Dibenzofuran
132-64-9
8270C
ND
480
ug/kg
1
3,3'-Dichlorobenzidine
91-94-1
8270C
NO
1200
ug/kg
1
2,4-Dichlorophenol
120-83-2
8270C
ND
480
ug/kg
1
Diethylphthalate
84-66-2
8270C
NO
480
ug/kg
1
Dimethyl phthalate
131-11-3
8270C
NO
480
ug/kg
1
2,4-Dimethylphenol
105-67-9
8270C
NO
480
ug/kg
1
4,6-Dinitro-2-methylphenol
534-52-1
8270C
NO
1200
ug/kg
1
2,4-Dinitrophenol
51-28-5
8270C
ND
1200
ug/kg
1
2,4-Dinitrotoluene
121-14-2
8270C
NO
480
ug/kg
1
2,6-Dinitrotoluene
606-20-2
8270C
ND
480
ug/kg
1
bis(2-Ethylhexyl)phthalate
117-81-7
8270C
ND
480
ug/kg
1
206-44-0
8270C
NO
480
ug/kg
1
Zoranthene
orene
86-73-7
8270C
ND
480
ug/kg
1
Hexachlorobenzene
118-74-1
8270C
NO
480
ug/kg
1
Hexachlorobutadiene
87-68-3
8270C
ND
480
ug/kg
1
Hexachlorocyclopentadiene
77-47-4
8270C
NO
1200
ug/kg
1
Hexachloroethane
67-72-1
8270C
NO
480
ug/kg
1
Indeno(1,2,3-c,d)pyrene
193-39-5
8270C
ND
480
ug/kg
1
Isophorone
78-59-1
8270C
NO
480
ug/kg
1
PQL = Practical quantitation limit B = Detected in the method blank E = Quantitation of compound exceeded the calibration range
ND = Not detected at or above the PQL J = Estimated result < PQL and > MDL P = The RPD between two GC columns exceeds 40%
Where applicable, all soil sample analysis are reported on a dry weight basis unless flagged with a "W" N = Recovery is out of criteria
Shealy Environmental Services, Inc. Page: 11 of 24
106 Vantage Point Drive West Columbia, SC 29172 [phone] Fax [phone] www.shealylab.com Level 1 Report v2.1
L

Client: Excel Civil & Environmental Associates, PLLC Laboratory ID: JD15061-002
Description: E Sidewall Matrix: Solid
Date Sampled:04/14/2008 0920 % Solids: 66.7 04/15/2008 2244
Date Received:0411512008
Semivolatile Organic Compounds by GC/MS
Run Prep Method Analytical Method Dilution Analysis Date Analyst Prep Date Batch
1 3550B 8270C 1 04/17/20081217 GLR 04/16/20081315 76991
CAS
Analytical
Parameter
Number
Method
Result Q
PQL
Units
Run
2-Methylnaphthalene
91-57-6
8270C
ND
480
ug/kg
1
2-Methylphenol
95-48-7
8270C
ND
480
ug/kg
1
3 & 4-Methylphenol
106-44-5
8270C
ND
980
ug/kg
1
N-Nitrosodi-n-propylamine
621-64-7
8270C
ND
480
ug/kg
1
N-Nitrosodiphenylamine (Diphenylamine)
86-30-6
8270C
ND
480
ug/kg
1
Naphthalene
91-20-3
8270C
ND
480
ug/kg
1
2-Nitroaniline
88-74-4
8270C
ND
480
ug/kg
1
3-Nitroaniline
99-09-2
8270C
ND
480
ug/kg
1
4-Nitroaniline
100-01-6
8270C
ND
480
ug/kg
1
Nitrobenzene
98-95-3
8270C
ND
480
ug/kg
1
2-Nitrophenol
88-75-5
8270C
ND
480
ug/kg
1
4-Nitrophenol
100-02-7
8270C
ND
1200
ug/kg
1
Pentachlorophenol
87-86-5
8270C
ND
1200
ug1kg
1
Phenanthrene
85-01-8
8270C
ND
480
ug/kg
1
Phenol
108-95-2
8270C
ND
480
ug/kg
1
Pyrene
129-00-0
8270C
ND
480
ug/kg
1
2,4,5-Trichlorophenol
95-95-4
8270C
ND
480
ug/kg
1
2,4,6-Trichlorophenol
88-06-2
8270C
ND
480
ug/kg
1
Run 1
Acceptance
Surrogate
Q %, Recovery
Limits
2,4,6-Tribromophenol
62
30-117
2-Fluorobiphenyl
60
33-102
2-Fluorophenol
69
28-104
Nitrobenzene-d5
60
22-109
Phenol-d5
61
27-103
Terphenyl-d14
73
41-120
1
1
1
1
�7
PQL = Practical quantitation limit B = Detected in the method blank E = Quanitation of compound exceeded the calibration range
ND = Not detected at or above the PQL J = Estimated result < PQL and > MDL P = The RPD between two GC columns exceeds 401%
Where applicable, all soil sample analysis are reported on a dry weight basis unless flagged with a "W' N = Recovery is out of criteria ,
Shealy Environmental Services, Inc. Page: 12 of 24
106 Vantage Point Drive West Columbia, SC 29172 [phone] Fax [phone] www.shealylab.com Level 1 Report v2.1

1
P
u
Client: Excel Civil & Environmental Associates, PLLC Laboratory ID: JD15061-003
Description: W Sidewall Matrix: Solid
Date Sampled:04/14/2008 0923 % Solids: 73.9 04/15/2008 22"
Date Received: 04/15/2008
Volatile Organic Compounds by GC/MS
Run Prep Method Analytical Method Dilution Analysis Date Analyst Prep Date Batch Sample Wt.(g)
1 5035 8260E 1 04/17/20081411 LH 77160 4.33
CAS
Analytical
Parameter
Number
Method
Result Q
PQL
Units
Run
Acetone
67-64-1
8260B
ND
31
ug/kg
1
Benzene
71-43-2
8260B
ND
7.8
ug/kg
1
Bromobenzene
108-86-1
8260B
ND
7.8
ug/kg
1
Bromochioromethane
74-97-5
8260E
ND
7.8
ug/kg
1
Bromodichloromethane
75-27-4
8260B
ND
7.8
ug/kg
1
Bromoform
75-25-2
8260B
ND
7.8
ug/k9
1
Bromomethane (Methyl bromide)
74-83-9
8260B
ND
7.8
ug/kg
1
2-Butanone (MEK)
78-93-3
8260B
ND
16
ug/kg
1
n-Butylbenzene
104-51-8
8260E
ND
7.8
ug/kg
1
sec-Butylbenzene
135-98-8
8260E
ND
7.8
ug/kg
1
tert-Butylbenzene
98-06-6
8260B
ND
7.8
ug/kg
1
Carbon tetrachloride
56-23-5
8260B
ND
7.8
ug/kg
1
Chlorobenzene
108-90-7
8260B
ND
7.8
ug/kg
1
Chloroethane
75-00-3
8260B
ND
7.8
ug/kg
1
Chloroform
67-66-3
8260B
ND
7.8
ug/kg
1
Chloromethane (Methyl chloride)
74-87-3
8260B
ND
7.8
ug/kg
1
2-Chlorotoluene
95-49-8
8260B
ND
7.8
ug/kg
1
4-Chlorotoluene
106-43-4
8260B
ND
7.8
ug/kg
1
Dibromochloromethane
124-48-1
8260E
ND
7.8
ug/kg
1
1,2-Dibromoethane (EDB)
106-93-4
8260B
ND
7.8
ug/kg
1
1,2-Dichlorobenzene
95-50-1
8260B
ND
7.8
ug/kg
1
1,3-Dichlorobenzene
541-73-1
8260B
ND
7.8
ug/kg
1
1,4-Dichlorobenzene
106-46-7
8260B
ND
7.8
ug/kg
1
Dichlorodifluoromethane
75-71-8
8260E
ND
7.8
ug/kg
1
1,1-Dichloroethane
75-34-3
8260B
ND
7.8
ug/kg
1
1,2-Dichloroethane
107-06-2
8260E
ND
7.8
ug/kg
1
1,1-Dichloroethene
75-35-4
8260B
ND
7.8
ug/kg
1
cis- 1,2-Dichloroethene
156-59-2
8260E
ND
7.8
ug/kg
1
trans-1,2-Dichloroethene
156-60-5
8260E
ND
7.8
ug/kg
1
1,2-Dichloropropane
78-87-5
8260B
ND
7.8
ug/kg
1
1,3-Dichioropropane
142-28-9
8260E
ND
7.8
ug/kg
1
2,2-Dichloropropane
594-20-7
8260B
ND
7.8
ug/kg
1
1,1-Dichloropropene
563-58-6
8260E
ND
7.8
ug/kg
1
cis-1,3-Dichloropropene
10061-01-5
8260B
ND
7.8
ug/kg
1
trans-1,3-Dichloropropene
10061-02-6
8260B
ND
7.8
ug/kg
1
Diisopropyl ether (IPE)
108-20-3
8260E
ND
7.8
ug/kg
1
Ethylbenzene
100-41-4
8260E
ND
7.8
ug/kg
1
2-Hexanone
591-78-6
8260E
ND
16
ug/kg
1
Isopropylbenzene
98-82-8
8260B
ND
7.8
ug/kg
1
p-Isopropyltoluene
99-87-6
8260B
ND
7.8
ug/kg
1
PQL = Practical quantitation limit B = Detected in the method blank E = Quantitation of compound exceeded the calibration range
ND = Not detected at or above the PQL J = Estimated result < PQL and > MDL P = The RPD between two GC columns exceeds 40%
Where applicable, all soil sample analysis are reported on a dry weight basis unless flagged with a "W' N = Recovery is out of criteria
Shealy Environmental Services, Inc. Page: 13 of 24
106 Vantage Point Drive West Columbia, SC 29172 [phone] Fax [phone] www.shealylab.com Level 1 Report v2.1

Client: Excel Civil & Environmental Associates, PLLC Laboratory ID: JD15051-003
Description: W Sidewall Matrix: Solid
Date Sampled:04/14/2008 0923 % Solids: 73.9 04/15/2008 2244
Date Received:04115/2008
Volatile Organic Compounds by GC/MS
Run Prep Method Analytical Method Dilution Analysis Date Analyst Prep Date Batch Sample Wt.(g)
1 5035 8260B 1 04/17/20081411 LH 77160 4.33
Parameter
CAS
Number
Analytical
Method
Result Q
PQL
Units
Run
Methyl tertiary butyl ether (MTBE)
1634-04-4
8260E
ND
7.8
ug/kg
1
4-Methyl-2-pentanone
108-10-1
8260B
ND
16
ug/kg
1
Methylene chloride
75-09-2
8260B
ND
7.8
ug/kg
1
Naphthalene
91-20-3
8260B
ND
7.8
ug/kg
1
n-Propylbenzene
103-65-1
8260B
ND
7.8
ug/kg
1
Styrene
100-42-5
8260B
ND
7.8
ug/kg
1
1,1,2,2-Tetrachloroethane
79-34-5
8260B
ND
7.8
ug/kg
1
Tetrachloroethene
127-18-4
8260B
ND
7.8
ug/kg
1
Toluene
108-88-3
8260E
ND
7.8
ug/kg
1
1,2,3-Trichlorobenzene
87-61-6
8260B
ND
7.8
ug/kg
1
1,2,4-Trichlorobenzene
120-82-1
8260E
ND
7.8
ug/kg
1
1,1,1-Trichloroethane
71-55-6
8260B
ND
7.8
ug/kg
1
1,1,2-Trichloroethane
79-00-5
8260B
ND
7.8
ug/kg
1
Trichloroethene
79-01-6
8260B
ND
7.8
ug/kg
1
Trichlorofluoromethane
75-69-4
8260E
ND
7.8
ug/kg
1
1,2,3-Trichloropropane
96-18-4
8260B
ND
7.8
ug/kg
1
1,2,4-Trimethylbenzene
95-63-6
8260B
ND
7.8
ug/kg
1
1,3,5-Trimethylbenzene
108-67-8
8260B
ND
7.8
ug/kg
1
Vinyl acetate
108-05-4
8260E
ND
7.8
ug/kg
1
Vinyl chloride
75-01-4
8260E
ND
7.8
ug/kg
1
Xylenes (total)
1330-20-7
8260E
ND
7.8
ug/kg
1
Run 1 Acceptance
Surrogate Q % Recovery Limits
1,2-Dichloroethane-d4 71 53-142
Bromofluorobenzene 108 47-138
Toluene-d8 81 68-124
Semivolatile Organic Compounds by GC/MS
Run Prep Method Analytical Method Dilution Analysis Date Analyst Prep Date Batch
1 3550B 8270C 1 04/17/20081235 GLR 04/16/20081315 76991
Parameter
CAS
Number
Analytical
Method
Result Q
PQL
Units
Run
Acenaphthene
83-32-9
8270C
ND
440
ug/kg
1
Acenaphthylene
208-96-8
8270C
ND
440
ug/kg
1
Acetophenone
98-86-2
8270C
ND
440
ug/kg
1
Anthracene
120-12-7
8270C
ND
440
ug/kg
1
Atrazine
1912-24-9
8270C
ND
440
ug/kg
1
Benzaldehyde
100-52-7
8270C
ND
1100
ug/kg
1
Benzo(a)anthracene
56-55-3
8270C
ND
440
ug/kg
1
PQL = Practical quantitation limit B = Detected in the method blank E = Quanitation of compound exceeded the calibration range
ND = Not detected at or above the PQL J = Estimated result < PQL and > MDL P = The RPD between two GC columns exceeds 40%
Where applicable, all soil sample analysis are reported on a dry weight basis unless flagged with a' W' N = Recovery is out of criteria
Shealy Environmental Services, Inc.
106 Vantage Point Drive West Columbia, SC 29172 [phone] Fax [phone] www.shealylab.com
Page: 14 of 24
Level 1 Report v2.1
1
11
1
d
11

1
fJ
Client: Excel Civil & Environmental Associates, PLLC Laboratory ID: JD16051-003
Description: W Sidewall Matrix: Solid
Date Sampled:04/14/2008 0923 % Solids: 73.9 04/15/2008 2244
Date Received:04/1512008
Semivolatile Organic Compounds by GC/MS
Run Prep Method
Analytical Method Dilution Analysis Date Analyst
Prep Date
Batch
1 3550B
8270C 1 04/17120081235 GLR
04/16120081315
76991
CAS
Analytical
Parameter
Number
Method
Result Q
PQL
Units
Run
Benzo(a)pyrene
50-32-8
8270C
NO
440
ug/kg
1
Benzo(b)fluoranthene
205-99-2
8270C
NO
440
ug/kg
1
Benzo(g,h,i)perylene
191-24-2
8270C
NO
440
ug/kg
1
Benzo(k)fluoranthene
207-08-9
8270C
NO
440
ug/kg
1
1,1'-Biphenyl
92-52-4
8270C
NO
440
ug/kg
1
4-Bromophenyl phenyl ether
101-55-3
8270C
NO
440
ug/kg
1
Butyl benzyl phthalate
85-68-7
8270C
NO
440
ug/kg
1
Caprolactam
105-60-2
8270C
NO
1100
ug/kg
1
Carbazole
86-74-8
8270C
NO
440
ug/kg
1
4-Chloro-3-methyl phenol
59-50-7
8270C
NO
440
ug/kg
1
4-Chloroaniline
106-47-8
8270C
NO
440
ug/kg
1
bis(2-Chloroethoxy)methane
111-91-1
8270C
NO
440
ug/kg
1
bis(2-Chloroethyl)ether
111-44-4
8270C
NO
440
ug/kg
1
bis(2-Chloroisopropyl)ether
108-60-1
8270C
NO
440
ug/kg
1
2-Chloronaphthalene
91-58-7
8270C
NO
440
ug/kg
1
2-Chlorophenol
95-57-8
8270C
NO
440
ug/kg
1
4-Chlorophenyl phenyl ether
7005-72-3
8270C
NO
440
ug/kg
1
Chrysene
218-01-9
8270C
NO
440
ug/kg
1
Di-n-butyl phthalate
84-74-2
8270C
NO
440
ug/kg
1
Di-n-octylphthalate
117-84-0
8270C
NO
440
ug/kg
1
Dibenzo(a,h)anthracene
53-70-3
8270C
NO
440
ug/kg
1
Dibenzofuran
132-64-9
8270C
NO
440
ug/kg
1
3,3'-Dichlorobenzidine
91-94-1
8270C
NO
1100
ug/kg
1
2,4-Dichlorophenol
120-83-2
8270C
NO
440
ug/kg
1
Diethyl phthalate
84-66-2
8270C
NO
440
ug/kg
1
Dimethyl phthalate
131-11-3
8270C
NO
440
ug/kg
1
2,4-Dimethylphenol
105-67-9
8270C
NO
440
ug/kg
1
4,6-Dinitro-2-methyl phenol
534-52-1
8270C
NO
1100
ug/kg
1
2,4-Dinitrophenol
51-28-5
8270C
NO
1100
ug/kg
1
2,4-Dinitrotoluene
121-14-2
8270C
NO
440
ug/kg
1
2,6-Dinitrotoluene
606-20-2
8270C
NO
440
ug/kg
1
bis(2-Ethylhexyl)phthalate
117-81-7
8270C
NO
440
ug/kg
1
Fluoranthene
206-44-0
8270C
NO
440
ug/kg
1
Fluorene
86-73-7
8270C
NO
440
ug/kg
1
Hexachlorobenzene
118-74-1
8270C
NO
440
ug/kg
1
Hexachlorobutadiene
87-68-3
8270C
NO
440
ug/kg
1
Hexachlorocyclopentadiene
77-47-4
8270C
NO
1100
ug/kg
1
Hexachloroethane
67-72-1
8270C
NO
440
ug/kg
1
Indeno(1,2,3-c,d)pyrene
193-39-5
8270C
NO
440
ug/kg
1
Isophorone
78-59-1
8270C
NO
440
ug/kg
1
PQL = Practical quantitation limit B = Detected in the method blank E = Quantitation of compound exceeded the calibration range
ND = Not detected at or above the PQL J = Estimated result < PQL and > MDL P = The RPD between two GC columns exceeds 40%
Where applicable, all soil sample analysis are reported on a dry weight basis unless flagged with a' W' N = Recovery is out of criteria
Shealy Environmental Services, Inc. Page: 15 of 24
106 Vantage Point Drive West Columbia, SC 29172 [phone] Fax [phone] www.shealylab.com Level 1 Reportv2.1
H

Client: Excel Civil & Environmental Associates, PLLC Laboratory ID: JD15051-003
Description: W Sidewall Matrix: Solid
Date Sampled:04/14/2008 0923 % Solids: 73.9 04/15/2008 2244
Date Received:04/15/2008
Semivolatile Organic Compounds by GC/MS
Run Prep Method Analytical Method Dilution Analysis Date Analyst Prep Date Batch
1 3550E 8270C 1 04/17/20081235 GLR 04/16/20081315 76991
CAS
Analytical
Parameter
Number
Method
Result Q
PQL
Units
Run
2-Methylnaphthalene
91-57-6
8270C
ND
440
ug/kg
1
2-Methylphenol
95-48-7
8270C
ND
440
ug/kg
1
3 & 4-Methylphenol
106-44-5
8270C
ND
900
ug/kg
1
N-Nitrosodi-n-propylamine
621-64-7
8270C
ND
440
ug/kg
1
N-Nitrosodiphenylamine (Diphenylamine)
86-30-6
8270C
ND
440
ug/kg
1
Naphthalene
91-20-3
8270C
ND
440
ug/kg
1
2-Nitroaniline
88-74-4
8270C
ND
440
ug/kg
1
3-Nitroaniline
99-09-2
8270C
ND
440
ug/kg
1
4-Nitroaniline
100-01-6
8270C
ND
440
ug/kg
1
Nitrobenzene
98-95-3
8270C
ND
440
ug/kg
1
2-Nitrophenol
88-75-5
8270C
ND
440
ug/kg
1
4-Nitrophenol
100-02-7
8270C
ND
1100
ug/kg
1
Pentachlorophenol
87-86-5
8270C
ND
1100
ug/kg
1
Phenanthrene
85-01-8
8270C
ND
440
ug/kg
1
Phenol
108-95-2
8270C
ND
440
ug/kg
1
Pyrene
129-00-0
8270C
ND
440
ug/kg
1
2,4,5-Trichlorophenol
95-95-4
8270C
ND
440
ug/kg
1
2,4,6-Trichlorophenol
88-06-2
8270C
ND
440
ug/kg
1
Run 1
Acceptance
Surrogate
Q % Recovery
Limits
2,4,6-Tribromophenol
52
30-117
2-Fluorobiphenyl
58
33-102
2-Fluorophenol
43
28-104
Nitrobenzene-d5
57
22-109
Phenol-d5
58
27-103
Terphenyl-dl4
75
41-120
PQL = Practical quantilation limit B = Detected in the method blank E = Quantitation of compound exceeded the calibration range
ND = Not detected at or above the PQL J = Estimated result < PQL and > MDL P = The RPD between two GC columns exceeds 40%
Where applicable, all soil sample analysis are reported on a dry weight basis unless flagged with a' W' N = Recovery is out of criteria
Shealy Environmental Services, Inc. Page: 16 of 24
106 Vantage Point Drive West Columbia, SC 29172 [phone] Fax [phone] www.shealylab.com Level 1 Report v2.1
u
1
,7
�l

LJI
1
F
1
u
Client: Excel Civil & Environmental Associates, PLLC Laboratory ID: JD15051-004
Description: S Sidewall Matrix: Solid
Date Sampled:04/14/2008 0925 % Solids: 69.9 04/15/2008 2244
Date Received: 04/1512008
Volatile Organic Compounds by GC/MS
Run Prep Method Analytical Method Dilution Analysis Date Analyst Prep Date Batch Sample Wt.(g)
1 5035 8260E 1 04/17/20081435 LH 77160 4.74
CAS
Analytical
Parameter
Number
Method
Result Q
PQL
Units
Run
Acetone
67-64-1
8260B
ND
30
ug/kg
1
Benzene
71-43-2
8260B
ND
7.5
ug/kg
1
Bromobenzene
108-86-1
8260B
ND
7.5
ug/kg
1
Bromochloromethane
74-97-5
8260B
ND
7.5
ug/kg
1
Bromodichloromethane
75-27-4
8260B
ND
7.5
ug/kg
1
Bromoform
75-25-2
8260B
ND
7.5
ug/kg
1
Bromomethane (Methyl bromide)
74-83-9
8260E
ND
7.5
ug/kg
1
2-Butanone (MEK)
78-93-3
8260B
ND
15
ug/kg
1
n-Butylbenzene
104-51-8
8260E
ND
7.5
ug/kg
1
sec-Butylbenzene
135-98-8
82608
ND
7.5
ug/kg
1
tert-Butylbenzene
98-06-6
8260B
ND
7.5
ug/kg
1
Carbon tetrachloride
56-23-5
8260B
ND
7.5
ug/kg
1
Chlorobenzene
108-90-7
8260B
ND
7.5
ug/kg
1
Chloroethane
75-00-3
8260B
ND
7.5
ug/kg
1
Chloroform
67-66-3
8260B
ND
7.5
ug/kg
1
Chloromethane (Methyl chloride)
74-87-3
8260B
ND
7.5
ug/kg
1
2-Chlorotoluene
95-49-8
8260B
ND
7.5
ug/kg
1
4-Chlorotoluene
106-43-4
8260B
ND
7.5
ug/kg
1
Dibromochloromethane
124-48-1
8260E
ND
7.5
ug/kg
1
1,2-Dibromoethane (EDB)
106-93-4
8260E
ND
7.5
ug/kg
1
1,2-Dichlorobenzene
95-50-1
8260B
ND
7.5
ug/kg
1
1,3-Dichlorobenzene
541-73-1
8260E
ND
7.5
ug/kg
1
1,4-Dichlorobenzene
106-46-7
8260B
ND
7.5
ug/kg
1
Dichlorodifluoromethane
75-71-8
8260B
ND
7.5
ug/kg
1
1,1-Dichloroethane
75-34-3
8260B
ND
7.5
ug/kg
1
1,2-Dichloroethane
107-06-2
8260B
ND
7.5
ug/kg
1
11-Dichloroethene
75-35-4
8260E
ND
7.5
ug/kg
1
cis-1,2-Dichloroethene
156-59-2
8260E
ND
7.5
ug/kg
1
trans-1,2-Dichloroethene
156-60-5
8260B
ND
7.5
ug/kg
1
1,2-Dichloropropane
78-87-5
8260B
ND
7.5
ug/kg
1
1,3-Dichloropropane
142-28-9
8260E
ND
7.5
ug/kg
1
2,2-Dichloropropane
594-20-7
8260B
ND
7.5
ug/kg
1
1,1-Dichloropropene
563-58-6
8260B
ND
7.5
ug/kg
1
cis-1,3-Dichloropropene
10061-01-5
8260E
ND
7.5
ug/kg
1
trans-1,3-Dichloropropene
10061-02-6
8260E
ND
7.5
ug/kg
1
Diisopropyl ether (IPE)
108-20-3
8260E
ND
7.5
ug/kg
1
Ethyibenzene
100-41-4
8260E
ND
7.5
ug/kg
1
2-Hexanone
591-78-6
8260E
ND
15
ug/kg
1
Isopropylbenzene
98-82-8
8260B
ND
7.5
ug/kg
1
p-Isopropyltoluene
99-87-6
8260B
ND
7.5
ug/kg
1
PQL = Practical quantitation limit B = Detected in the method blank E = Quantitation of compound exceeded the calibration range
ND = Not detected at or above the PQL J = Estimated result < PQL and _> MDL P = The RPD between two GC columns exceeds 40%
Where applicable, all soil sample analysis are reported on a dry weight basis unless flagged with a "W' N = Recovery is out of criteria
Shealy Environmental Services, Inc. Page: 17 of 24
106 Vantage Point Drive West Columbia, SC 29172 [phone] Fax [phone] www.shealylab.com Level 1 Reportv2.1
11

Client: Excel Civil & Environmental Associates, PLLC Laboratory ID: JD75051-004
Description: S Sidewall Matrix: Solid
Date Sampled:04/14/2008 0925 % Solids: 69.9 04/15/2008 2244
Date Received:0411612008
Volatile Organic Compounds by GC/MS
Run Prep Method Analytical Method Dilution Analysis Date Analyst Prep Date Batch Sample Wt.(g)
1 5035 8260E 1 04/17/20081435 LH 77160 4.74
CAS
Analytical
Parameter
Number
Method
Result Q
PQL
Units
Run
Methyl tertiary butyl ether (MTBE)
1634-04-4
8260B
ND
7.5
ug/kg
1
4-Methyl-2-pentanone
108-10-1
8260E
ND
15
ug/kg
1
Methylene chloride
75-09-2
8260B
ND
7.5
ug/kg
1
Naphthalene
91-20-3
8260B
ND
7.5
ug/kg
1
n-Propylbenzene
103-65-1
8260E
ND
7.5
ug/kg
1
Styrene
100-42-5
8260E
ND
7.5
ug/kg
1
1,1,2,2-Tetrachloroethane
79-34-5
8260B
ND
7.5
ug/kg
1
Tetrachloroethene
127-18-4
8260E
ND
7.5
ug/kg
1
Toluene
108-88-3
8260E
ND
7.5
ug/kg
1
1,2,3-Trichlorobenzene
87-61-6
8260B
ND
7.5
ug/kg
1
1,2,4-Trichlorobenzene
120-82-1
8260E
ND
7.5
ug/kg
1
1,1,1-Trichloroethane
71-55-6
8260B
ND
7.5
ug/kg
1
1,1,2-Trichloroethane
79-00-5
8260B
ND
7.5
ug/kg
1
Trichloroethene
79-01-6
8260B
ND
7.5
ug/kg
1
Trichlorofluoromethane
75-69-4
8260B
ND
7.5
ug/kg
1
1,2,3-Trichloropropane
96-18-4
8260B
ND
7.5
ug/kg
1
1,2,4-Trimethylbenzene
95-63-6
8260B
ND
7.5
uglkg
1
1,3,5-Trimethylbenzene
108-67-8
8260E
ND
7.5
ug/kg
1
Vinyl acetate
108-05-4
8260B
ND
7.5
ug/kg
1
Vinyl chloride
75-01-4
8260B
ND
7.5
ug/kg
1
Xylenes (total)
1330-20-7
8260E
ND
7.5
ug/kg
1
Run 1
Acceptance
Surrogate
Q % Recovery
Limits
1,2-Dichloroethane-d4
73
53-142
Bromofluorobenzene
110
47-138
Toluene-d8
82
68-124
Semivolatile Organic Compounds by GC/MS
Run Prep Method Analytical Method Dilution Analysis Date Analyst Prep Date Batch
2 3550B 8270C 1 04/21/20081729 DC 04/18/20081924 77198
CAS
Analytical
Parameter
Number
Method
Result Q
PQL
Units
Run
Acenaphthene
83-32-9
8270C
ND
470
ug/kg
2
Acenaphthylene
208-96-8
8270C
ND
470
ug/kg
2
Acetophenone
98-86-2
8270C
ND
470
ug/kg
2
Anthracene
120-12-7
8270C
ND
470
ug/kg
2
Atrazine
1912-24-9
8270C
ND
470
ug/kg
2
Benzaldehyde
100-52-7
8270C
ND
1200
ug/kg
2
Benzo(a)anthracene
56-55-3
8270C
ND
470
ug/kg
2
PQL = Practical quantitation limit 8 = Detected in the method blank E = Quantitation of compound exceeded the calibration range
ND = Not detected at or above the PQL J = Estimated result < PQL and > MDL P = The RPD between two GC columns exceeds 40 %
Where applicable, all soil sample analysis are reported on a dry weight basis unless flagged with a' W' N = Recovery is out of criteria
Shealy Environmental Services, Inc.
106 Vantage Point Drive West Columbia, SC 29172 [phone] Fax [phone] www.shealylab.com
1
Page: 18 of 24 '
Level 1 Report v2.1

u
0
u
11
Client: Excel Civil & Environmental Associates, PLLC Laboratory ID: JD15061-004
Description: S Sidewall Matrix: Solid
Date Sampled:04/14/2008 0925 % Solids: 69.9 04/16/2008 2244
Date Received:04115/2008
Semivolatile Organic Compounds by GC/MS
Run Prep Method Analytical Method Dilution Analysis Date Analyst Prep Date Batch
2 3550B 8270C 1 04/21/20081729 DC 04/18/20081924 77198
CAS
Analytical
Parameter
Number
Method
Result Q
PQL
Units
Run
Benzo(a)pyrene
50-32-8
8270C
ND
470
ug/kg
2
Benzo(b)fluoranthene
205-99-2
8270C
ND
470
ug/kg
2
Benzo(g,h,i)perylene
191-24-2
8270C
ND
470
ug/kg
2
Benzo(k)fluoranthene
207-08-9
8270C
ND
470
ug/kg
2
1,1'-Biphenyl
92-52-4
8270C
ND
470
ug/kg
2
4-Bromophenyl phenyl ether
101-55-3
8270C
ND
470
ug/kg
2
Butyl benzyl phthalate
85-68-7
8270C
ND
470
ug/kg
2
Caprolactam
105-60-2
8270C
ND
1200
ug/kg
2
Carbazole
86-74-8
8270C
ND
470
ug/kg
2
4-Chloro-3-methyl phenol
59-50-7
8270C
ND
470
ug/kg
2
4-Chloroaniline
106-47-8
8270C
ND
470
ug/kg
2
bis(2-Chloroethoxy)methane
111-91-1
8270C
ND
470
ug/kg
2
bis(2-Chloroethyl)ether
111-44-4
8270C
ND
470
ug/kg
2
bis(2-Chloroisopropyl)ether
108-60-1
8270C
ND
470
ug/kg
2
2-Chloronaphthalene
91-58-7
8270C
ND
470
ug/kg
2
2-Chlorophenol
95-57-8
8270C
ND
470
ug/kg
2
4-Chlorophenyl phenyl ether
7005-72-3
8270C
ND
470
ug/kg
2
Chrysene
218-01-9
8270C
ND
470
ug/kg
2
Di-n-butyl phthalate
84-74-2
8270C
ND
470
ug/kg
2
Di-n-octylphthalate
117-84-0
8270C
ND
470
ug/kg
2
Dibenzo(a,h)anthracene
53-70-3
8270C
ND
470
ug/kg
2
Dibenzofuran
132-64-9
8270C
ND
470
ug/kg
2
3,3'-Dichiorobenzidine
91-94-1
8270C
ND
1200
ug/kg
2
2,4-Dichlorophenol
120-83-2
8270C
ND
470
ug/kg
2
Diethylphthalate
84-66-2
8270C
ND
470
ug/kg
2
Dimethyl phthalate
131-11-3
8270C
ND
470
ug/kg
2
2,4-Dimethylphenol
105-67-9
8270C
ND
470
ug/kg
2
4,6-Dinitro-2-methylphenol
534-52-1
8270C
ND
1200
ug/kg
2
2,4-Dinitrophenol
51-28-5
8270C
ND
1200
ug/kg
2
2,4-Dinitrotoluene
121-14-2
8270C
ND
470
ug/kg
2
2,6-Dinitrotoluene
606-20-2
8270C
ND
470
ug/kg
2
bis(2-Ethylhexyl)phthalate
117-81-7
8270C
ND
470
ug/kg
2
Fluoranthene
206-44-0
8270C
ND
470
ug/kg
2
Fluorene
86-73-7
8270C
ND
470
ug/kg
2
Hexachlorobenzene
118-74-1
8270C
ND
470
ug/kg
2
Hexachlorobutadiene
87-68-3
8270C
ND
470
ug/kg
2
Hexachlorocyclopentadiene
77-47-4
8270C
ND
1200
ug/kg
2
Hexachloroethane
67-72-1
8270C
ND
470
ug/kg
2
Indeno(1,2,3-c,d)pyrene
193-39-5
8270C
ND
470
ug/kg
2
Isophorone
78-59-1
8270C
ND
470
ug/kg
2
PQL = Practical quantitation limit B = Detected in the method blank E = Quantitation of compound exceeded the calibration range
ND = Not detected at or above the PQL J = Estimated result < PQL and > MDL P = The RPD between two GC columns exceeds 40%
Where applicable, all soil sample analysis are reported on a dry weight basis unless Ragged with a "W' N = Recovery is out of criteria
Shealy Environmental Services, Inc. Page: 19 of 24
106 Vantage Point Drive West Columbia, SC 29172 [phone] Fax [phone] www.shealylab.com Level 1 Reportv2.1

Client: Excel Civil & Environmental Associates, PLLC Laboratory ID: JD15051-004
Description: S Sidewall Matrix: Solid
Date Sampled:04/14/2008 0925 % Solids: 69.9 04/16/2008 2244
Date Received:04/1512008
Semivolatile Organic Compounds by GC/MS
Run Prep Method Analytical Method Dilution Analysis Date Analyst Prep Date Batch
2 3550B 8270C 1 04/21/20081729 DC 04/18/20081924 77198
CAS
Analytical
Parameter
Number
Method
Result Q
PQL
Units
Run
2-Methyinaphthalene
91-57-6
8270C
ND
470
ug/kg
2
2-Methylphenol
95-48-7
8270C
ND
470
ug/kg
2
3 & 4-Methylphenol
106-44-5
8270C
ND
950
ug/kg
2
N-Nitrosodi-n-propylamine
621-64-7
8270C
ND
470
ug/kg
2
N-Nitrosodiphenylamine (Diphenylamine)
86-30-6
8270C
ND
470
ug/kg
2
Naphthalene
91-20-3
8270C
ND
470
ug/kg
2
2-Nitroaniline
88-74-4
8270C
ND
470
ug/kg
2
3-Nitroaniline
99-09-2
8270C
ND
470
ug/kg
2
4-Nitroaniline
100-01-6
8270C
ND
470
ug/kg
2
Nitrobenzene
98-95-3
8270C
ND
470
ug/kg
2
2-Nitrophenol
88-75-5
8270C
ND
470
ug/kg
2
4-Nitrophenol
100-02-7
8270C
ND
1200
ug/kg
2
Pentachlorophenol
87-86-5
8270C
ND
1200
ug/kg
2
Phenanthrene
85-01-8
8270C
ND
470
ug/kg
2
Phenol
108-95-2
8270C
ND
470
ug/kg
2
Pyrene
129-00-0
8270C
ND
470
ug/kg
2
2,4,5-Trichlorophenol
95-95-4
8270C
ND
470
ug/kg
2
2,4,6-Trichlorophenol
88-06-2
8270C
ND
470
ug/kg
2
Run 2
Acceptance
Surrogate
Q % Recovery
Limits
2,4,6-Tribromophenol
61
30-117
2-Fluorobiphenyl
66
33-102
2-Fluorophenol
73
28-104
Nitrobenzene-d5
65
22-109
Phenol-d5
68
27-103
Terphenyl-d14
81
41-120
PQL = Practical quantitation limit B = Detected in the method blank E = Quantitation of compound exceeded the calibration range
ND = Not detected at or above the PQL J = Estimated result < PQL and > MDL P = The RPD between two GC columns exceeds 40%
Where applicable, all soil sample analysis are reported on a dry weight basis unless flagged with a' W' N = Recovery is out of criteria
Shealy Environmental Services, Inc.
106 Vantage Point Drive West Columbia, SC 29172 [phone] Fax [phone] www.shealylab.com
Page: 20 of 24
Level 1 Report v2.1
Ll
7
1
1

P
E
P
.1
J
H
j
Client: Excel Civil & Environmental Associates, PLLC Laboratory ID: JD15051-005
Description: Base Matrix: Solid
Date Sampled:04/14/2008 0935 % Solids: 78.0 04/15/2008 22"
Date Received:04/1612008
Volatile Organic Compounds by GC/MS
Run Prep Method Analytical Method Dilution Analysis Date Analyst Prep Date Batch Sample Wt.(g)
1 5035 8260E 1 04/17/20081459 LH 77160 4.15
CAS
Analytical
Parameter
Number
Method
Result Q
PQL
Units
Run
Acetone
67-64-1
8260B
ND
31
ug/kg
1
Benzene
7143-2
8260B
ND
7.7
ug/kg
1
Bromobenzene
108-86-1
8260E
ND
7.7
ug/kg
1
Bromochioromethane
74-97-5
8260B
ND
7.7
ug/kg
1
Bromodichloromethane
75-27-4
8260B
ND
7.7
ug/kg
1
Bromoform
75-25-2
8260E
ND
7.7
ug/kg
1
Bromomethane (Methyl bromide)
74-83-9
8260E
ND
7.7
ug/kg
1
2-Butanone (MEK)
78-93-3
8260B
ND
15
ug/kg
1
n-Butylbenzene
104-51-8
8260E
ND
7.7
ug/kg
1
sec-Butylbenzene
135-98-8
8260E
ND
7.7
ug/kg
1
tert-Butylbenzene
98-06-6
8260B
ND
7.7
ug/kg
1
Carbon tetrachloride
56-23-5
8260B
ND
7.7
ug/kg
1
Chlorobenzene
108-90-7
8260E
ND
7.7
ug/kg
1
Chloroethane
75-00-3
8260B
ND
7.7
ug/kg
1
Chloroform
67-66-3
8260B
ND
7.7
ug/kg
1
Chloromethane (Methyl chloride)
74-87-3
8260B
ND
7.7
ug/kg
1
2-Chlorotoluene
95-49-8
8260B
ND
7.7
ug/kg
1
4-Chlorotoluene
106-43-4
8260B
ND
7.7
ug/kg
1
Dibromochloromethane
124-48-1
8260B
ND
7.7
ug/kg
1
1,2-Dibromoethane (EDB)
106-93-4
8260B
ND
7.7
ug/kg
1
1,2-Dichlorobenzene
95-50-1
8260B
ND
7.7
ug/kg
1
1,3-Dichlorobenzene
541-73-1
8260B
ND
7.7
ug/kg
1
1,4-Dichlorobenzene
106-46-7
8260B
ND
7.7
ug/kg
1
Dichlorodifluoromethane
75-71-8
8260B
ND
7.7
ug/kg
1
1,1-Dichloroethane
75-34-3
8260B
ND
7.7
ug/kg
1
1,2-Dichloroethane
107-06-2
8260E
ND
7.7
ug/kg
1
1,1-Dichloroethene
75-35-4
8260B
ND
7.7
ug/kg
1
cis-1,2-Dichloroethene
156-59-2
8260E
ND
7.7
ug/kg
1
trans-1,2-Dichloroethene
156-60-5
8260B
ND
7.7
ug/kg
1
1,2-Dichloropropane
78-87-5
8260B
ND
7.7
ug/kg
1
1,3-Dichloropropane
142-28-9
8260B
ND
7.7
ug/kg
1
2,2-Dichloropropane
594-20-7
8260E
ND
7.7
ug/kg
1
1,1-Dichioropropene
563-58-6
8260B
ND
7.7
ug/kg
1
cis-1,3-Dichioropropene
10061-01-5
8260B
ND
7.7
ug/kg
1
trans-1,3-Dichloropropene
10061-02-6
8260B
ND
7.7
ug/kg
1
Diisopropyl ether (IPE)
108-20-3
8260B
ND
7.7
ug/kg
1
Ethylbenzene
100-41-4
8260E
ND
7.7
ug/kg
1
2-Hexanone
591-78-6
8260B
ND
15
ug/kg
1
Isopropylbenzene
98-82-8
8260B
ND
7.7
ug/kg
1
p-Isopropyltoluene
99-87-6
8260B
ND
7.7
ug/kg
1
PQL = Practical quantitation limit B = Detected in the method blank E = Quantitation of compound exceeded the calibration range
ND = Not detected at or above the PQL J = Estimated result < PQL and > MDL P = The RPD between two GC columns exceeds 40%
Where applicable, all soil sample analysis are reported on a dry weight basis unless flagged with a' W' N = Recovery is out of criteria
Shealy Environmental Services, Inc. Page: 21 of 24
106 Vantage Point Drive West Columbia, SC 29172 [phone] Fax [phone] www.shealylab.com Level 1 Reportv2.1

Client: Excel Civil & Environmental Associates, PLLC Laboratory ID: JD75051-005
Description: Base Matrix: Solid
Date Sampled:04114/2008 0935 % Solids: 78.0 04/15/2008 2244
Date Received:04/15/2008
Volatile Organic Compounds by GC/MS
Run Prep Method Analytical Method Dilution Analysis Date Analyst Prep Date Batch Sample Wt.(g)
1 5035 8260E 1 04/17/20081459 LH 77160 4.15
CAS
Analytical
Parameter
Number
Method
Result Q
PQL
Units
Run
Methyl tertiary butyl ether (MTBE)
1634-04-4
8260E
ND
7.7
ug/kg
1
4-Methyl-2-pentanone
108-10-1
8260E
ND
15
ug/kg
1
Methylene chloride
75-09-2
8260B
ND
7.7
ug/kg
1
Naphthalene
91-20-3
8260B
ND
7.7
ug/kg
1
n-Propylbenzene
103-65-1
8260B
ND
7.7
ug/kg
1
Styrene
100-42-5
8260B
ND
7.7
ug/kg
1
1,1,2,2-Tetrachloroethane
79-34-5
8260B
ND
7.7
ug/kg
1
Tetrachloroethene
127-18-4
8260E
ND
7.7
ug/kg
1
Toluene
108-88-3
8260B
ND
7.7
ug/kg
1
1,2,3-Trichlorobenzene
87-61-6
8260B
ND
7.7
ug/kg
1
1,2,4-Trichlorobenzene
120-82-1
8260E
ND
7.7
ug/kg
1
1,1,1-Trichioroethane
71-55-6
8260B
ND
7.7
ug/kg
1
1,1,2-Trichloroethane
79-00-5
8260B
ND
7.7
ug/kg
1
Trichloroethene
79-01-6
8260B
ND
7.7
ug/kg
1
Trichlorofluoromethane
75-69-4
8260B
ND
7.7
ug/kg
1
1,2,3-Trichloropropane
96-18-4
8260B
ND
7.7
ug/kg
1
1,2,4-Trimethylbenzene
95-63-6
8260B
ND
7.7
ug/kg
1
1,3,5-Trimethylbenzene
108-67-8
8260E
ND
7.7
ug/kg
1
Vinyl acetate
108-05-4
8260E
ND
7.7
ug/kg
1
Vinyl chloride
75-01-4
8260B
ND
7.7
ug/kg
1
Xylenes (total)
1330-20-7
8260E
ND
7.7
ug/kg
1
Run 1
Acceptance
Surrogate
Q % Recovery
Limits
1,2-Dichloroethane-d4
72
53-142
Bromofluorobenzene
105
47-138
Toluene-d8
80
68-124
Semivolatile Oraanic Compounds by GC/MS
Run Prep Method
Analytical Method Dilution Analysis Date
Analyst
Prep Date
Batch
1 3550B
8270C 1 04/17/20081312
GLR
04/16/20081315
76991
CAS Analytical
Parameter
Number Method
Result Q
PQL
Units
Run
Acenaphthene
83-32-9
8270C
ND
410
ug/kg
1
Acenaphthylene
208-96-8
8270C
ND
410
ug/kg
1
Acetophenone
98-86-2
8270C
ND
410
ug/kg
1
Anthracene
120-12-7
8270C
ND
410
ug/kg
1
Atrazine
1912-24-9
8270C
ND
410
ug/kg
1
Benzaldehyde
100-52-7
8270C
ND
1000
ug/kg
1
Benzo(a)anthracene
56-55-3
8270C
ND
410
ug/kg
1
PQL = Practical quantitation limit 8 = Detected in the method blank E = Quantitation of compound exceeded the calibration range
NO = Not detected at or above the PQL J = Estimated result < PQL and > MDL P = The RPD between two GC columns exceeds 40%
Where applicable, all soil sample analysis are reported on a dry weight basis unless flagged with a' W' N = Recovery is out of criteria
Shealy Environmental Services, Inc. Page: 22 of 24
106 Vantage Point Drive West Columbia, SC 29172 [phone] Fax [phone] www.shealylab.com Level 1 Report v2.1
1
1
1�
L
11
1
E
u
0

11
5
1
n
1
Client: Excel Civil & Environmental Associates, PLLC Laboratory ID: JD15051-005
Description: Base Matrix: Solid
Date Sampied:04114/2008 0935 % Solids: 78.0 04/15/2008 2244
Date Received:0411512008
Semivolatile Organic Compounds by GC/MS
Run Prep Method Analytical Method Dilution Analysis Date Analyst Prep Date Batch
1 3550B 8270C 1 04/17/20081312 GLR 04/16/20081315 76991
CAS
Analytical
Parameter
Number
Method
Result Q
PQL
Units
Run
Benzo(a)pyrene
50-32-8
8270C
ND
410
ug/kg
1
Benzo(b)fluoranthene
205-99-2
8270C
ND
410
ug/kg
1
Benzo(g,h,i)perylene
191-24-2
8270C
ND
410
ug/kg
1
Benzo(k)fluoranthene
207-08-9
8270C
ND
410
ug/kg
1
1,1'-Biphenyl
92-52-4
8270C
ND
410
ug/kg
1
4-Bromophenyl phenyl ether
101-55-3
8270C
ND
410
ug/kg
1
Butyl benzyl phthalate
85-68-7
8270C
ND
410
ug/kg
1
Caprolactam
105-60-2
8270C
ND
1000
ug/kg
1
Carbazo►e
86-74-8
8270C
ND
410
ug/kg
1
4-Chloro-3-methyl phenol
59-50-7
8270C
ND
410
ug/kg
1
4-Chloroaniline
106-47-8
8270C
ND
410
ug/kg
1
bis(2-Chloroethoxy)methane
111-91-1
8270C
ND
410
ug/kg
1
bis(2-Chloroethyl)ether
111-44-4
8270C
ND
410
ug/kg
1
bis(2-Chloroisopropyl)ether
108-60-1
8270C
ND
410
ug/kg
1
2-Chloronaphthalene
91-58-7
8270C
ND
410
ug/kg
1
2-Chlorophenol
95-57-8
8270C
ND
410
ug/kg
1
4-Chlorophenyl phenyl ether
7005-72-3
8270C
ND
410
ug/kg
1
Chrysene
218-01-9
8270C
ND
410
ug/kg
1
Di-n-butyl phthalate
84-74-2
8270C
ND
410
ug/kg
1
Di-n-octylphthalate
117-84-0
8270C
ND
410
ug/kg
1
Dibenzo(a,h)anthracene
53-70-3
8270C
ND
410
ug/kg
1
Dibenzofuran
132-64-9
8270C
ND
410
ug/kg
1
3,3'-Dichlorobenzidine
91-94-1
8270C
ND
1000
ug/kg
1
2,4-Dichlorophenol
120-83-2
8270C
ND
410
ug/kg
1
Diethylphthalate
84-66-2
8270C
ND
410
ug/kg
1
Dimethyl phthalate
131-11-3
8270C
ND
410
ug/kg
1
2,4-Dimethylphenol
105-67-9
8270C
ND
410
ug/kg
1
4,6-Dinitro-2-methylphenol
534-52-1
8270C
ND
1000
ug/kg
1
2,4-Dinitrophenol
51-28-5
8270C
ND
1000
ug/kg
1
2,4-Dinitrotoluene
121-14-2
8270C
ND
410
ug/kg
1
2,6-Dinitrotoluene
606-20-2
8270C
ND
410
ug/kg
1
bis(2-Ethylhexyl)phthalate
117-81-7
8270C
ND
410
ug/kg
1
206-44-0
8270C
ND
410
ug/kg
1
Zoranthene
orene
86-73-7
8270C
ND
410
ug/kg
1
Hexachlorobenzene
118-74-1
8270C
ND
410
ug/kg
1
Hexachlorobutadiene
87-68-3
8270C
ND
410
ug/kg
1
Hexachlorocyclopentadiene
77-47-4
8270C
ND
1000
ug/kg
1
Hexachioroethane
67-72-1
8270C
ND
410
ug/kg
1
Indeno(1,2,3-c,d)pyrene
193-39-5
8270C
ND
410
ug/kg
1
Isophorone
78-59-1
8270C
ND
410
ug/kg
1
PQL = Practical quantitation limit 8 = Detected in the method blank E = Quantitation of compound exceeded the calibration range
ND = Not detected at or above the PQL J = Estimated result < POL and > MDL P = The RPD between two GC columns exceeds 40%
'Where applicable, all soil sample analysis are reported on a dry weight basis unless flagged with a' W' N = Recovery is out of criteria
Shealy Environmental Services, Inc. Page: 23 of 24
106 Vantage Point Drive West Columbia, SC 29172 [phone] Fax [phone] www.shealylab.com Level 1 Report v2.1

Client: Excel Civil & Environmental Associates, PLLC Laboratory ID: JD16051-005
Description: Base Matrix: Solid
Date Sampled:04/14/2008 0935 % Solids: 78.0 04/15/2008 2244
Date Received:0411512008
Semivolatile Organic Compounds by GC/MS
Run Prep Method Analytical Method Dilution Analysis Date Analyst Prep Date Batch
1 3550B 8270C 1 04/17/20081312 GLR 04/16/20081315 76991
CAS
Analytical
Parameter
Number
Method
Result Q
PQL
Units
Run
2-Methylnaphthalene
91-57-6
8270C
ND
410
ug/kg
1
2-Methylphenol
95-48-7
8270C
ND
410
ug/kg
1
3 & 4-Methylphenol
106-44-5
8270C
ND
830
ug/kg
1
N-Nitrosodi-n-propylamine
621-64-7
8270C
ND
410
ug/kg
1
N-Nitrosodiphenylamine (Diphenylamine)
86-30-6
8270C
ND
410
ug/kg
1
Naphthalene
91-20-3
8270C
ND
410
ug/kg
1
2-Nitroaniline
88-74-4
8270C
ND
410
ug/kg
1
3-Nitroaniline
99-09-2
8270C
ND
410
ug/kg
1
4-Nitroaniline
100-01-6
8270C
ND
410
ug/kg
1
Nitrobenzene
98-95-3
8270C
ND
410
ug/kg
1
2-Nitrophenol
88-75-5
8270C
ND
410
ug/kg
1
4-Nitrophenol
100-02-7
8270C
ND
1000
ug/kg
1
Pentachlorophenol
87-86-5
8270C
ND
1000
ug/kg
1
Phenanthrene
85-01-8
8270C
ND
410
ug/kg
1
Phenol
108-95-2
8270C
ND
410
ug/kg
1
Pyrene
129-00-0
8270C
ND
410
ug/kg
1
2,4,5-Tdchlorophenol
95-95-4
8270C
ND
410
ug/kg
1
2,4,6-Trichlorophenol
88-06-2
8270C
ND
410
ug/kg
1
I
AcceptanceRun
Surrogate
Q % Recovery
Limits
2,4,6-Tribromophenol
51
30-117
2-Fluorobiphenyl
56
33-102
2-Fluorophenol
60
28-104
Nitrobenzene-d5
56
22-109
Phenol-d5
56
27-103
Terphenyl-04
67
41-120
PQL = Practical quantitation limit B = Detected in the method blank E = Quantitation of compound exceeded the calibration range
ND = Not detected at or above the PQL J = Estimated result < PQL and > MDL P = The RPD between two GC columns exceeds 40%
Where applicable, all soil sample analysis are reported on a dry weight basis unless flagged with a "W" N = Recovery is out of criteria
Shealy Environmental Services, Inc.
106 Vantage Point Drive West Columbia, SC 29172 [phone] Fax [phone] www.shealylab.com
R
1
F,
I�I
7
IL
l�
Page: 24 of 24 '
Level 1 Report v2.1
1

SHEALY ENVIRONMENTAL SERVICES, INC.
t .Nw* r,�16 RqAam Dar, s
Roviikm Kuoftr- 6 P-m4we Dtft: a5 c#7
Sample Rece Cbec�l��i/s/9t� (S # t# r y
Client-ri U' ti� +�'lcrlilspocted aclste.��� �
Means of r=cipt S SI Clicnt [UPS [] FedEx: ❑ Ai-limeExp 0 Other
Yes
No
NA
- W`em cttstodv Seals plesent on the paler?
`pi ;Lj
I No
Lj
I NA
2. If cugu4 seals *qr: en were tha int t and unbroliwoll
C0oler I 71perature upon receipt -C t — °C 6C ' °+
aC i C I 0C oic
Mediod,k �emperattre_Blank Apikist £#ot i
Me hod of coolant. 'ei Ice Blue Ice D1-IcY ❑ Non
Tf response is'No for Yes for 14, 1 S. 6), an , lanationdttsolution must, he mwided.
Yes (l
No 0
3. If temperature of any° Choler exceeded 6_M, was Proa,u,.t Manager nee.?
NA t72 Phi notified by SRC, phone, nce (circle one), rather: (For
1 ; wlars received via commercial couriers P is arc to be 001i fled immediately..,
Y
o
NA
t 4. is the. commercial touria's packingrli auaahed to this farm?
Yes
No
NA
( 5. Werepropercustod procedures mlin tsitednecettvcl followed? -
Yes
No
NA
f. W= se ' le TT)s Ii"wd?
Yes
No
NA
t 7, Was M elon date & timtt.li�sd?
Yes
Yes
Na
N
NA
i $, Were t to be es^fortned listed' tnt the C C or was quote �' ovided?
NA
9. Did all samples arrive. in the r anntainers for ra Lh test?
Y
l�o
NA
I i 0. Did all containc r Ivbel infortnotion D. date, time a with COC?
Yes
No
Nit
11 . Did all t o iiainets arrive m od condition funbrokpq lids ore, eitc_- ?
Y�
No
NA
U 12, Was adequate same le volume available?
Yes
No
13. Were all swriplus received within Vi the, holdingtime or 49 hours, whichever
� NA 1 comas ftrat7
Ye"
?� o
NA [' 14. W samples ionise missing?
Yes
No
:'
NA I 1'� there $nn eau ess mmples not listed on cm?
Yes
N6,E]
VA LT 16. Iffurc bubbles present 6mm in d ametterl in any VOA
vials?
*:s
i t
7r' 4 i 17. St' all meta &1U&t<,v44E nutrient ssm les r.�.eive i at a �I of �2,'?
No
NA P71 : 18. Were all qwudt and -or sulfide SSm lvx ri: =iVtdl at 8 H>12?
Yes E:,
No ❑
NA ` "-Were all applicable ?'H3,TK?vayauidepbeoot B- A/pesc!PC,& erb
i c 4.2mw'I..l and toxicity (-0.Im '`I,) satin les free of residual chlorine?
)*es
No
NA 120. llection tem ;ratures documented on the CCC for NC sain les?
Sample Pr+ emst
on (Must lae completed or ati�t surplerrss) incorrectly preserved or svitlt he�iacc )
Samples) __.._..- were:rceeiNvd inoorm tly, preyed and vc ,=, 4djusted
acwrdfrigly in sample receiving with I2$0JN%,11Cl,N i-T) )Wth tht SR 0 (number)
Sample(s) 1<vere receive with bubbles >6 mm to d1
sample(s) Avre received with TRC .2 tail for Nl31
TXX,'c ranid M -es ?CBr'IAEx .
Toxicity sam rle(a)mere received w th 'I°P.0 X1.1 m L and Crete
aitatI ttte�d ��C1.f;
Cc►rractiectiaata Laken. if n ssarr:
Was client rtr►t fief Ycs No Did client respond; ices [I No
SESI employee. Date ofrespon
Comments.,
Shealy Environmental Services, Inc
106 Vantage Point Drive West Columbia, SC 29172 [phone] Fax [phone] www.shealylab.com Level 1 Report v2.1

Ice
Analyticalm
' www.po*obs.com
April 22, 2008
Pace Analytical Services, Inc.
2225 Riverside Dr.
Asheville, NC 28804
[phone]
Pace Analytical Services, Inc.
9800 Kincey Ave. Suite 100
Huntersville, NC 28078
[phone]
' Ms. Brooke Montgomery
Shealy Environmental Services
106 Vantage Point Dr.
' Cayce, SC 29033
' RE: Project: ROUSCH
Pace Project No.: 9217453
' Dear Ms. Montgomery:
Enclosed are the analytical results for sample(s) received by the laboratory on April 16, 2008. The
' results relate only to the samples included in this report. Results reported herein conform to the
most current NELAC standards, where applicable, unless otherwise narrated in the body of the
report.
' Inorganic Wet Chemistry and Metals analyses were performed at our Pace Asheville laboratory and
Organic testing was performed at our Pace Huntersville laboratory unless otherwise footnoted. All
Microbiological analyses were performed at the laboratory where the samples were received.
' If you have any questions concerning this report, please feel free to contact me.
Sincerely,
Brenda Pathammavong
[e-mail]
Project Manager
Enclosures
REPORT OF LABORATORY ANALYSIS
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, Inc..
Coq�'
21
Page 1 of 10

a0
6Analytical
www.pacelaQs. Wm
)
i
Project. ROUSCH
Pace Project No.: 9217453
Charlotte Certification IDs
Florida/NELAP Certification Number: E87627
Kansas Certification Number: E-10364
Louisiana/LELAP Certification Number: 04034
North Carolina Drinking Water Certification Number: 37706
North Carolina Wastewater Certification Number: 12
Asheville Certification IDS
Florida/NELAP Certification Number: E87648
Louisiana/LELAP Certification Number: 03095
New Jersey Certification Number: NC011
North Carolina Drinking Water Certification Number: 37712
North Carolina Wastewater Certification Number: 40
North Carolina Bioassay Certification Number: 9
Eden Certification IDS
North Carolina Drinking Water Certification Number: 37738
Virginia Drinking Water Certification Number: 00424
Pace Analytical Services, Inc.
2225 Riverside Dr.
Asheville, NC 28804
[phone]
CERTIFICATIONS
Pace Analytical Services, Inc.
9800 Kincey Ave. Sufte 100
Huntersville, NC 28078
[phone]
North Carolina Field Services Certification Number: 5342
South Carolina Certification Number: 990060001
South Carolina Bioassay Certification Number: 990060003
Tennessee Certification Number: 04010
Virginia Certification Number: 00213
Pennsylvania Certification Number: 68-03578
South Carolina Certification Number: 99030001
South Carolina Bioassay Certification Number: 99030002
Tennessee Certification Number: 2980
Virginia Certification Number: 00072
North Carolina Wastewater Certification Number: 633
REPORT OF LABORATORY ANALYSIS Page 2 of 10
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, Inc..
ri Jaffe=
[J

Anal iC aee ,� al
Wmpacelaucom
Project: ROUSCH
' Pace Project No.: 9217453
Lab ID
' 9217453001 N
9217453002 E
' 9217453003 W
' 9217453004 S
' 9217453005 BASE
i
1
Pace Analytical Services, Inc.
2225 Riverside Dr.
Asheville, NC 28804
[phone]
SAMPLE ANALYTE COUNT
Pace Analytical Services, Inc.
9800 Kincey Ave. Suite 100
Huntersville, NC 28078
[phone]
Sample ID Method
Analysts
Analytes
Reported
Laboratory
ASTM D2974-87
TNM
1
PASI-C
MADEP EPH
JAD
7
PASI-C
MADEP VPH
DHW
5
PASI-C
ASTM D2974-87
TNM
1
PASI-C
MADEP EPH
JAD
7
PASI-C
MADEP VPH
DHW
5
PASI-C
ASTM D2974-87
TNM
1
PASI-C
MADEP EPH
JAD
7
PASI-C
MADEP VPH
DHW
5
PASI-C
ASTM D2974-87
TNM
1
PASI-C
MADEP EPH
JAD
7
PASI-C
MADEP VPH
DHW
5
PASI-C
ASTM D2974-87
TNM
1
PASI-C
MADEP EPH
JAD
7
PASI-C
MADEP VPH
DHW
5
PASI-C
REPORT OF LABORATORY ANALYSIS
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, Inc..
C pqC'
e6
Page 3 of 10

aceAnalyl cal to
wwwpacetabs.mm
Pace Analytical Services, Inc.
2225 Riverside Dr.
Asheville, NC 28804
[phone]
ANALYTICAL RESULTS
Pace Analytical Services, Inc.
9800 Kincey Ave. Suite 100
Huntersville, NC 28078
[phone]
Project: ROUSCH
Pace Project No.: 9217453
Sample: N Lab ID: 9217453001 Collected: 04/14/08 09:41 Received: 04/16/08 11:15 Matrix: Solid
Results reported on a "dry -weight" basis
Parameters Results Units Report Limit DF Prepared Analyzed CAS No. Qual
MADEP EPH NC Soil
Aliphatic (C09-C18)
Aliphatic (C19-C36)
Aromatic (Cl 1-C22)
Nonatriacontane (S)
o-Terphenyl(S)
2-Fluorobiphenyl (S)
2-Bromonaphthalene (S)
MADEP VPH NC Soil
Aliphatic (C05-CO8)
Aliphatic (C09-C12)
Aromatic (C09-C10)
2,5-Dibromotoluene (PID)(S)
2,5-Dibromotoluene (FID)(S)
Percent Moisture
Percent Moisture
Analytical Method: MADEP EPH Preparation Method: MADEP EPH
ND mg/kg
14.7
1
04/21/08 00:00 04/22/08 05:30
ND mg/kg
14.7
1
04/21/08 00:00 04/22/08 05:30
ND mg/kg
14.7
1
04/21/08 00:00 04/22/08 05:30
102 %
40-140
1
04/21/08 00:00 04/22/08 05:30 7194-86-7
76 %
40-140
1
04/21/08 00:00 04/22/08 05:30 84-15-1
93 %
40-140
1
04/21/08 00:00 04/22/08 05:30 321-60-8
95 %
40-140
1
04/21/08 00:00 04/22/08 05:30 580-13-2
Analytical Method: MADEP VPH Preparation
Method:
MADEP VPH
ND mg/kg
14.9
1
04/16/08 15:38 04/17/08 00:06
ND mg/kg
14.9
1
04/16/08 15:38 04/17/08 00:06
ND mg/kg
14.9
1
04/16/08 15:38 04/17/08 00:06
106 %
70-130
1
04/16/08 15:38 04/17/08 00:06
108 %
70-130
1
04/16/08 15:38 04/17/08 00:06
Analytical Method: ASTM D2974-87
32.0 %
0.10
1
04/17/08 08:35
Sample: E Lab ID: 9217453002 Collected: 04/14/08 09:20 Received: 04/16/08 11:15 Matrix: Solid
Results reported on a "dry -weight" basis
Parameters Results Units Report Limit DF Prepared Analyzed CAS No. Qual
MADEP EPH NC Soil
Aliphatic (C09-C18)
Aliphatic (C19-C36)
Aromatic (Cl 1-C22)
Nonatriacontane (S)
o-Terphenyl(S)
2-Fluorobiphenyl (S)
2-Bromonaphthalene (S)
MADEP VPH NC Soil
Aliphatic (C05-CO8)
Aliphatic (C09-C12)
Aromatic (C09-C10)
2,5-Dibromotoluene (PID)(S)
2,5-Dibromotoluene (FID)(S)
Percent Moisture
Percent Moisture
Analytical Method: MADEP EPH Preparation Method: MADEP EPH
ND mg/kg
13.2
1
04/21/08 00:00 04/22/08 06:06
ND mg/kg
13.2
1
04/21/08 00:00 04/22/08 06:06
ND mg/kg
13.2
1
04/21/08 00:00 04/22/08 06:06
100 %
40-140
1
04/21/08 00:00 04/22/08 06:06 7194-86-7
83 %
40-140
1
04/21/08 00:00 04/22/08 06:06 84-15-1
95 %
40-140
1
04/21/08 00:00 04/22/08 06:06 321-60-8
94 %
40-140
1
04/21/08 00:00 04/22/08 06:06 580-13-2
Analytical Method: MADEP VPH Preparation Method:
MADEP VPH
ND mg/kg
16.1
1
04/16/08 15:38 04/17/08 00:36
ND mg/kg
16.1
1
04/16/08 15:38 04/17/08 00:36
ND mg/kg
16.1
1
04/16/08 15:38 04/17/08 00:36
110 %
70-130
1
04/16/08 15:38 04/17/08 00:36
113 %
70-130
1
04116/0815:38 04/17/08 00:36
Analytical Method: ASTM D2974-87
24.5 %
0.10
1
04/17/08 08:36
Date: 04/22/2008 02:48 PM REPORT OF LABORATORY ANALYSIS Page 4 of 10
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, Inc..

lace
AnalXical
www.peoeaD&can
i
Project: ROUSCH
Pace Project No.: 9217453
Pace Analytical Services, Inc. Pace Analytical Services, Inc.
2225 Riverside Dr. 9800 Kincey Ave. Suite 100
Asheville, NC 28804 Huntersville, NC 28078
[phone] [phone]
ANALYTICAL RESULTS
Sample: W Lab ID: 9217453003
Results reported on a "dry -weight" basis
Parameters Results Units
Collected: 04/14/08 09:23
Report Limit OF
Received: 04/16/08 11:15 Matrix: Solid
Prepared Analyzed CAS No. Qual
MADEP EPH NC Soil
Analytical Method: MADEP EPH Preparation Method: MADEP EPH
Aliphatic (C09-C18)
NO mg/kg
15.1
1
04/21/08 00:00 04/22/08 06:42
Aliphatic (C19-C36)
NO mg/kg
15.1
1
04/21/08 00:00 04/22/08 06:42
Aromatic (Cl 1-C22)
NO mg/kg
15.1
1
04/21/08 00:00 04/22/08 06:42
Nonatriacontane (S)
101 %
40-140
1
04/21/08 00:00 04/22/08 06:42
7194-86-7
o-Terphenyl (S)
80 %
40-140
1
04/21/08 00:00 04/22/08 06:42
84-15-1
2-Fluorobiphenyl (S)
98 %
40-140
1
04/21/08 00:00 04/22/08 06:42
321-60-8
2-Bromonaphthalene (S)
100 %
40-140
1
04/21/08 00:00 04/22/08 06:42
580-13-2
MADEP VPH NC Soil
Analytical Method: MADEP VPH Preparation Method: MADEP VPH
Aliphatic (C05-008)
NO mg/kg
15.7
1
04/16/08 15:38 04/17/08 01:06
Aliphatic (C09-C12)
NO mg/kg
15.7
1
04/16/08 15:38 04/17/08 01:06
Aromatic (C09-C10)
NO mg/kg
15.7
1
04/16/08 15:38 04/17/08 01:06
2,5-Dibromotoluene (PID)(S)
108 %
70-130
1
04/16/08 15:38 04/17/08 01:06
2,5-Dibromotoluene (FID)(S)
111 %
70-130
1
04/16/08 15:38 04/17/08 01:06
Percent Moisture
Analytical Method: ASTM D2974-87
Percent Moisture
33.8 %
0.10
1
04/17/08 08:36
Sample: S Lab ID: 9217453004 Collected: 04/14/08 09:25 Received: 04/16/08 11:15 Matrix: Solid
Results reported on a "dry -weight" basis
Parameters Results Units Report Limit OF Prepared Analyzed CAS No. Qual
MADEP EPH NC Soil
Aliphatic (C09-C18)
Aliphatic (C19-C36)
Aromatic (C11-C22)
Nonatriacontane (S)
o-Terphenyl(S)
2-Fluorobiphenyl (S)
2-Bromonaphthalene (S)
MADEP VPH NC Soil
Aliphatic (C05-008)
Aliphatic (C09-C12)
Aromatic (C09-C10)
2,5-Dibromotoluene (PID)(S)
2,5-Dibromotoluene (FID)(S)
Percent Moisture
Percent Moisture
Date: 04/22/2008 02:48 PM
Analytical Method: MADEP EPH Preparation Method: MADEP EPH
NO mg/kg
15.2
1
04/21/08 00:00 04/22/08 07:18
NO mg/kg
15.2
1
04/21/08 00:00 04/22/08 07:18
NO mg/kg
15.2
1
04/21/08 00:00 04/22/08 07:18
191 %
40-140
1
04/21/08 00:00 04/22/08 07:18 7194-86-7 S3
138 %
40-140
1
04/21/08 00:00 04/22/08 07:18 84-15-1
90 %
40-140
1
04/21/08 00:00 04/22/08 07:18 321-60-8
93 %
40-140
1
04/21/08 00:00 04/22/08 07:18 580-13-2
Analytical Method: MADEP VPH Preparation Method: MADEP VPH
NO mg/kg
15.4
1
04/16/08 15:38 04/17/08 01:37
NO mg/kg
15.4
1
04/16/08 15:38 04/17/08 01:37
NO mg/kg
15.4
1
04/16/08 15:38 04/17/08 01:37
106 %
70-130
1
04/16/08 15:38 04/17/08 01:37
108 %
70-130
1
04/16/08 15:38 04/17/08 01:37
Analytical Method: ASTM D2974-87
34.4 %
0.10
1
04/17/08 08:36
REPORT OF LABORATORY ANALYSIS
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, Inc..
:WIy 16t-
Page 5 of 10

aceAnaIXical
www.peceteMWM
{
i
Pace Analytical Services, Inc.
2225 Riverside Dr.
Asheville, NC 28804
[phone]
ANALYTICAL RESULTS
Pace Analytical Services, Inc.
9800 Kincey Ave. Suite100
Huntersville, NC 28078
[phone]
Project: ROUSCH
Pace Project No.: 9217453
Sample: BASE Lab ID: 9217453005 Collected: 04/14/08 09:35 Received: 04/16/08 11:15 Matrix: Solid
Results reported on a "dry -weight" basis
Parameters Results Units Report Limit DF Prepared Analyzed CAS No. Qual
MADEP EPH NC Soil
Aliphatic (C09-C18)
Aliphatic (C19-C36)
Aromatic (Cl 1-C22)
Nonatriacontane (S)
o-Terphenyl(S)
2-Fluorobiphenyl (S)
2-Bromonaphthalene (S)
MADEP VPH NC Soil
Aliphatic (C05-008)
Aliphatic (C09-C12)
Aromatic (C09-C10)
2,5-Dibromotoluene (PID)(S)
2,5-Dibromotoluene (FID)(S)
Percent Moisture
Percent Moisture
Analytical Method: MADEP EPH Preparation Method: MADEP EPH
ND mg/kg
14.5
1
04/21/08 00:00 04/22/08 07:54
ND mg/kg
14.5
1
04/21/08 00:00 04/22/08 07:54
ND mg/kg
14.5
1
04/21/08 00:00 04/22/08 07:54
192 %
40-140
1
04/21/08 00:00 04/22/08 07:54 7194-86-7 S3
133 %
40-140
1
04/21/08 00:00 04/22/08 07:54 84-15-1
78 %
40-140
1
04/21/08 00:00 04/22/08 07:54 321-60-8
81 %
40-140
1
04/21/08 00:00 04/22/08 07:54 580-13-2
Analytical Method: MADEP VPH Preparation Method:
MADEP VPH
ND mg/kg
14.5
1
04/16/08 15:38 04/17/08 02:07
ND mg/kg
14.5
1
04/16/08 15:38 04/17/08 02:07
ND mg/kg
14.5
1
04/16/08 15:38 04/17/08 02:07
106 %
70-130
1
04116/0815:38 04/17/08 02:07
108 %
70-130
1
04/16/08 15:38 04/17/08 02:07
Analytical Method: ASTM D2974-87
30.9 %
0,10
1
04/17/08 08:36
Date: 04/22/2008 02:48 PM REPORT OF LABORATORY ANALYSIS Page 6 of 10
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, Inc..

aceAnalidical
'www.pa siabs:corn
i
Pace Analytical Services, Inc.
2225 Riverside Dr.
Asheville, NC 28804
[phone]
QUALITY CONTROL DATA
Pace Analytical Services, Inc.
9800 Kincey Ave. Suite 100
Huntersville, NC 28078
[phone]
Project: ROUSCH
Pace Project No.: 9217453
'
QC Batch: GCV/1947
Analysis Method: MADEP VPH
QC Batch Method: MADEP VPH
Analysis Description: MADEP VPH NC Soil
Associated Lab Samples: 9217453001, 9217453002, 9217453003, 9217453004, 9217453005
METHOD BLANK: 102066
Associated Lab Samples: 9217453001, 9217453002, 9217453003, 9217453004, 9217453005
Blank Reporting
'
Parameter
Units
Result Limit Qualifiers
Aliphatic (C05-008)
mg/kg
ND 10.0
'
Aliphatic (C09-C12)
Aromatic (C09-C10)
mg/kg
mg/kg
NO 10.0
ND 10.0
2,5-Dibromotoluene (FID)(S)
%
105 70-130
2,5-Dibromotoluene (PID)(S)
%
105 70-130
LABORATORY CONTROL SAMPLE & LCSD: 102067
102068
Spike LCS LCSD LCS LCSD
% Rec Max
Parameter
Units
Conc. Result Result % Rec % Rec
Limits RPD RPD
'
Aliphatic (C05-008)
mg/kg
20 18.1 18.6 90 93
70-130 3 25
Aliphatic (C09-C12)
mg/kg
5 NO ND 93 94
30-130 .3 25
Aromatic (C09-C10)
mg/kg
5 ND ND 92 92
70-130 .5 25
2,5-Dibromotoluene (FID)(S)
%
105 109
70-130
'
2,5-Dibromotoluene (PID)(S)
%
106 110
70-130
1
Date: 04/22/2008 02:48 PM
1
REPORT OF LABORATORY ANALYSIS
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, Inc..
�ORp,
Qualifiers
Page 7 of 10

Pace Analytical Services, Inc.
Analytical*
2225 Riverside Dr.
wwwpobscm
Asheville, NC 28804
I
[phone]
QUALITY CONTROL DATA
Project: ROUSCH
Pace Project No.: 9217453
QC Batch: PMST/1594 Analysis Method: ASTM D2974-87
QC Batch Method: ASTM D2974-87 Analysis Description: Dry Weight/Percent Moisture
Associated Lab Samples: 9217453001, 9217453002, 9217453003, 9217453004, 9217453005
SAMPLE DUPLICATE: 102373
9217449009 Dup
Parameter Units Result Result RPD Qualifiers
Percent Moisture % 18.1 19.3 7
Date: 04/22/2008 02:48 PM
REPORT OF LABORATORY ANALYSIS
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, Inc..
Pace Analytical Services, Inc.
9800 Kincey Ave. Suite 100
Huntersville, NC 28078
[phone]
Page 8 of 10

eeAnalytical
wwwpacemlcom
Project: ROUSCH
'
Pace Project No.: 9217453
Pace Analytical Services, Inc.
2225 Riverside Dr.
Asheville, NC 28804
[phone]
QUALITY CONTROL DATA
QC Batch: OEXT/2967
Analysis Method: MADEP EPH
QC Batch Method: MADEP EPH
Analysis Description: MADEP EPH NC Soil
'
Associated Lab Samples:
9217453001, 9217453002, 9217453003, 9217453004, 9217453005
METHOD BLANK: 103750
Associated Lab Samples:
9217453001, 9217453002, 9217453003, 9217453004, 9217453005
Blank Reporting
'
Parameter
Units
Result Limit Qualifiers
Aliphatic (C09-C18)
mg/kg
ND 10.0
Aliphatic (C19-C36)
mg/kg
ND 10.0
Aromatic (C11-C22)
mg/kg
ND 10.0
2-Bromonaphthalene (S)
%
102 40-140
2-Fluorobiphenyl (S)
%
99 40-140
'
Nonatriacontane (S)
o-Terphenyl(S)
%
%
108 40-140
93 40-140
LABORATORY CONTROL SAMPLE 8, LCSD: 103751
Parameter
Units
Aliphatic (C09-C18)
mg/kg
Aliphatic (C19-C36)
mg/kg
'
Aromatic (C11-C22)
mg/kg
2-Bromonaphthalene (S)
%
2-Fluorobiphenyl (S)
%
Nonatriacontane (S)
%
'
o-Terphenyl(S)
%
Date: 04/22/2008 02:48 PM
Pace Analytical Services, Inc.
9800 Kincey Ave. Suite 100
Huntersville, NC 28078
[phone]
103752
Spike
LCS LCSD
LCS
LCSD
% Rec Max
Cone.
Result Result
% Rec
% Rec
Limits RPD RPD
10
ND ND
60
61
40-140 2 50
13.3
11.3 12.8
85
96
40-140 12 50
28.3
28.0 24.6
99
87
40-140 13 50
108
95
40-140
109
97
40-140
103
111
40-140
103
77
40-140
REPORT OF LABORATORY ANALYSIS
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, Inc..
Qualifiers
Page 9 of 10

ac6Analytical
t wwwpacelabs.com
QUALIFIERS
Project: ROUSCH
Pace Project No.: 9217453
Pace Analytical Services, Inc.
2225 Riverside Dr.
Asheville, NC 28804
[phone]
Pace Analytical Services, Inc.
9800 Kincey Ave. Suite 100
Huntersville, NC 28078
[phone]
DEFINITIONS
DF - Dilution Factor, if reported, represents the factor applied to the reported data due to changes in sample preparation, dilution of
the sample aliquot, or moisture content.
ND - Not Detected at or above adjusted reporting limit.
J - Estimated concentration above the adjusted method detection limit and below the adjusted reporting limit.
MDL -Adjusted Method Detection Limit.
S - Surrogate
1,2-Diphenyihydrazine (8270 listed analyte) decomposes to Azobenzene.
Consistent with EPA guidelines, unrounded data are displayed and have been used to calculate % recovery and RPD values.
LCS(D) - Laboratory Control Sample (Duplicate)
MS(D) - Matrix Spike (Duplicate)
DUP - Sample Duplicate
RPD - Relative Percent Difference
NC - Not Calculable.
Pace Analytical is NELAP accredited. Contact your Pace PM for the current list of accredited analytes.
LABORATORIES
PASI-C Pace Analytical Services - Charlotte
ANALYTE QUALIFIERS
S3 Surrogate recovery exceeded laboratory control limits. Analyte presence below reporting limits in associated samples.
Results unaffected by high bias.
Date: 04/22/2008 02:48 PM REPORT OF LABORATORY ANALYSIS Page 10 of 10
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, Inc..
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Client Name: Project # 5, 1 3
Courier: ❑Fed Ex [I UPS ❑ USPS� Client ❑ Commerci j'ace Other Opttoria[ h h
Custody Seal on Cooler/Box Present: El �no Seals int ct. ❑ yes no Prof Due Date N/A '
P.ror Na:rne � N/A ��
Packing Material: ❑ Bubble Wrap Oubble Bags ❑ None ❑Other
Thermometer Used T060 e of Ice
� Type Blue None IrilSamoles on ice cnnlinn nrnr•Pcc hac hcnnn
Cooler Temperature L
Temp should be above freezing to 6°C
Biological Tissue is Frozen: Yes No N/A
Comments:
Date and I •tia of pe s n examining
content
Chain of Custody Present:
.{'ies ONO
❑N/A
1.
Chain of Custody Filled Out:
D09s ONo
❑N/A
2_
Chain of Custody Relinquished:
OYes .O'No
ON/A
3
Sampler Name & Signature on COC:
Oyes P<o
ON/A
4•
Samples Arrived within Hold Time:
.EJYes ONO
ON/A
5.
Short Hold Time Analysis (<72hr):
OYes ,PMo
❑NIA
6,
Rush Turn Around Time Requested:
OYes la'Fio
❑N/A
7.
Sufficient Volume:
OYes �Ao
ON/A
g.
b YLACt is
Correct Containers Used:
-Pace Containers Used:
.Nees ONO
OYes .12'No
ON/A
❑N/A
g. 'W —kk bph
zSl@9'1t L_s
Containers Intact:
Dyes ONO
❑N/A
10•
Filtered volume received for Dissolved tests
OYes ONO
JR1 /A
11 •
Sample Labels match COC:
-Includes date/time/ID/Analysis Matrix:
!ems- n❑No
So ¢�
❑N/A
12.
All containers needing preservation have been checked.
All containers needing preservation are found to be in
compliance with EPA recommendation.
exceptions: VOA, coliform, TOC, O&G, Wf-0130 (water)
_ Yes ONO
,,,,{
UYes ONO
OYes ONO
❑NIA
ON/A
13.
Initial when completed
Samples checked for dechlorination:
OYes ONO
CIA
14.
Headspace in VOA Vials ( >6mm):
OYes ONO
UWA
15.
Trip Blank Present:
Trip Blank Custody Seals Present
Pace Trip Blank Lot # (if purchased): NIA
OYes ONO .
OYes ONO
UWA
C?NM
16.
Client Notification/ Resolution: Field Data Required? Y / N / N/A
Person Contacted: Date/Time:
Comments/ Resolution:
Project Manager Review: zt�, i Date:
I
1
Note: Whenever there is a discrepancy affecting North Carolina compliance samples, a copy of this form will be sent to the North Carolina DEHNR I
Certification Office ( i.e out of hold, incorrect preservative. out of temn Pre o incorrect rnnfniy

11
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APPENDIX C
Site Photographs

EXCEL CIVIL & ENVIRONMENTAL ASSOCIATES, PLLC
1
1
fl
H
n
PHOTOGRAPH LOG
PHOTOGRAPH
NUMBER
PHOTOGRAPH REVIEW AND COMMENTS
1
View of location of heating -oil UST after removal.
2
View of location of heating -oil UST after removal.
3
View of basin following removal of UST.
4
View of UST prior to disposal.
5
View of basin during over -excavation activities.
6
View of basin during over -excavation activities.
7
View of basin during over -excavation activities.
8
View of area of excavation during excavation activities.
Excel Project No. 28007
17�

ax
1
'Photograph Number 2
Excel Project No. 28007
1
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s
1
1 � a
v,
Photograph Number 3
1
1
' r d
1
'Photograph Number 4
Excel Project No. 28007

' Excel Project No. 28007
1

Excel Project No. 28007
1

1
1
APPENDIX D
Soils Disposal Manifests

Rpr 16 2009 1:35PM ENVIROMMENTRL SOILS
7044349533
p.I
P.0.13OX 2.95
ENVIRONMENTAL SOILS, INC. LAT nMORE. N.C. 28089
704434.0075
NON -HAZARDOUS PETROLEUM CONTAMINATED SOIL
AppROVAL it MANIFEST #
LOCATION OF SOIL:
'
TRANSPORTER:
l
AAf
Q.' 7¢ l+h
TIME: � � — —
TRUCK # �4
GROSS WT. 7 9(40 LBS.
_�___ii
TARE WT. � t88.
DATE:
SIGNATURE
LICENS
-
DRIVER
TRUCK #�
f3R©S.S WT. LBS.
TIME:D
I.
LICENSE N
TARE WT. -Las.
DATE: -
DR_ IVER SIGNATURE
TIME:
TIME:
TRUCK
GROSS Wr. Las-
LICENSE
TARE WT. LBS,
DRIVER SIGNATURE
f
TIME: TRUCK #
DATE: LICENSE #
DRIVER SIGNATURE
INSPECTED & ACCEPTED BY EWAR(, M MEN'T'AL
SUPERVISOR'S SIGNATURE
I
1 ,.,a, ti , li1,
GRb S WT. LBS.

1 Apr 16 2008 1:36PM ENVIRONMENTAL SOILS
7044348533 p.4
' ENVIRONMENTAL SOILS, INC.
P.d. BOX as
LATTIMOM N.C. 2808li�t�4A9
1 (M) 434M= FAX
Jae Hams: _ Dy ru, f,,1
1
1
4iross Wgt.:
'WM 7WOlb
TWO Wyt: 02: 3" 04I14
Not WQL: 102; 3M 04/14/M
"ORT" cmotita
Tons: LIC an
RAY T0r1t T
WdOW br. IWAi.
ENVMGNgbffAL SMS, INC.
,.,... P.O. BOX 295
LAMMORE, N.C. 2SOOS-0489
704M34.OWS
(704) 4344M FAX
Job I h=&' DrA*tL,.l
Grocs WOW:
z F00
T. Wyt: Y9179
10:3M 04114nM
Nat lAlyl..
NORTH CgRptMA
Tans: LKVGE E jtnw sa'o
- ......�,W 317ft
wakond br.
ENVIRONMENTAL SOLS,1NC.
1
P.O. BOX 295
7"431
M) 43+ FAX
l
e-t r"(wTmcW
1
Nana. '"
Job Na
1
Gross wa-: )Fvn P
1
rAKO lb
Two We:
cm
1
TOM - .
{iVelOhsd by: .
1 .uu ollmml4•1oil

npr lb euua 1135PM ENVIRONMENTAL SOILS 7044349533
,. p.3
1
1
1
L�
I�
DEBRUHL ENVIRONMENTAL EXCAVATING, INC.
4921 HOOVER DRIVE
CHARLOTTE, NC 28269
704/598-2681- OFFICE
704/S98-2988 - FAX
NON E AZARDOUS WASTE MANIFEST
DATE 4 NUMBER I
ENVIRONMENTAL CONSULTANT: Excel Civil & Environmental Associates
Contact: Mike Stanforth Phone: [phone]
GENERATOR: Overcash Family
Address:5009 Kanmapolis Parkway, Kannapolis, NC 28081
Contact: Phone:
TRANSPORTER: Trexler Tracking
Contact. Randy DeBruhl Phone: [phone]
DESTINATION: Environmental Soils, Inc., Dedicated Land Application Site
CLASS & TYPE OF CONTAMINATE IN SOIL: Class R - heating o0
WASTE ORIGINATION POINT: 5009 Kannapolis Hwy., Kannapolis, NC 28081
COUNTY: Cabarrtus SOURCE OF CONTAMINATION: UST
TRUCK#• t T ,.., _ VOLUME: segz 7A, 0? t0, J05k
DRIVER SIGNA
M
GENERATORS CECATION OF WASTE CONSTPT[IENTS:
In lien of submitting anidytical data (methods 9240 and $270) verifying that the waft in
question does not contain organic constmxna other than those which would noaaatly
appear in analysis of virgin petroleum product residue, I am submitting'this Certificate of
Wasto Constituents. I certify that I am familiar with the source of contamination of the
soil and fwther certify the source, to the best of my knowledg+ey, contains no eontaminaM
other than that listed above.
Signature_; •Orate 31Ida
Company. Name Title /ice-' (ate- L' were" !
V y �
r
G
4ne 1141111Th.r tlai

APr 16 2008 1:35PM EMVIROMMENTHL SOILS 7044349533
1
DEBRUHL ENVIRONMENTAL EXCAVATING, INC.
4921 HOOVER DRIVE
CB A►RLOM NC 28269
' 704/598-2681- OFFICE
7(WS98-290 -- FAX
' NON -HAZARDOUS WASTE MANIFEST
P.2
DATE q /� O� LOAD NUMBER �
'
ENVIRONMENTAL CONSULTANT: Excel Civil & Environmental Associates
Contact: Mike Stanforth Phone: 704l853-0900
GENERATOR: Ovcrcash Family
Address:5009 Karmapolis Parkway, Kmmmgvhs, NC 29081
'
Contact` Phone:
TRANSPORTER: Trmder Tricking
'
Contact: Randy DcBnuhi Phone: [phone]
DESTINATION: Envhumm atal Soils, Inc., Dedicated Land Application Site
CLASS & TYPE OF CONTAMINATE IN SOIL: Class R -- heating oil
WASTE ORIGINATION POINT: 5009 Kannapolis Hwy., Knanapol* NC 25081
'
UST
COUNTY: Cabm Tus SOURCE OF CONTAMINATION-
TRUCK#: — 17 VOLUME:
t/�1 ! DATE
lr t�00aV
DRIVER SIGNATURE.
'
7 J60
CZ AT1lUN OF WASTE CONSTITUENTS: A Q
GENERATORS
In lieu of submitting analytical data (methods 8240 and 8270) verifying that the 4
question does not contain organic constituents other thew those which would normally
'
appear m analysis of virgin petroleum product residue, I am s►ubmid ing this Certificate of
•
Wiisto Constituents. I certify *zat I un famBiar with fln source of contamination of the .�
soil and fiirther certify the sowce, to the best of ray knovdedge, contains no contaminants
'
other than that listed above.
rr
Signature Date % /y �Ji
c
Company Name'/''" Title
i,ru uaoil I ) k81-