WI0400035_Monitoring (Report)_20100706

Quarterly HRC Monitoring Report
Fairchild Industrial Products Company
Winston-Salem, North Carolina
Kleinfelder Project No. 97626
RECEIVED I QENR I CJWQ
Aquifef Protection Section
Copyright 2010 Kleinfelder
JUL 06 2010
All Rights Reserved
ONLY THE CLIENT OR ITS DESIGNATED REPRESENTATIVES MAY USE THIS DOCUMENT AND ONLY FOR THE SPECIFIC
PROJECT FOR WHICH THIS REPORT WAS PREPARED.

KL EINFEL DER
\ Bright People. Right Solutions.
May 6, 2010
File No. 97626 1 GS01OR084
Mr. Qu Qi
UIC Program
North Carolina DENR - DWQ
1636 Mail Service Center
Raleigh, North Carolina 27699-1636
Reference: Quarterly HRC Monitoring Report
Fairchild Industrial Products Company
Winston-Salem, North Carolina
Site ID No. NONCD 0001700
Dear Mr. Qi:
Kleinfelder is pleased to provide our quarterly monitoring report for the Underground
Injection Control (UIC) Permit for treatment of groundwater with Hydrogen Release
Compound (HRC) at the referenced site. Enclosed is a copy of the report for your
review. Should you have any questions regarding this information, please do not
hesitate to contact our office.
Very truly yours,
KLEINFELDER SOUTHEAST, INC.
04
Christopher W. ay, E.I., RSM
Environmental Group Manager
Annamarie Blauser
Staff Professional I
CW H/AB:cas
Enclosure
RECEIVED i DENR t DM
Aquifer Protection Section
JUL 06 2010
313 Gallimore Dairy Road, Greensboro, NC 27409 p 1336.668.0093 f 1336.668.3868

North Carolina Depenineot of Finvironment
and Natural Resources
Division of Waste Management
Superhmd Section
Inactive Hazardous Sites Branch
REMEDIATI NG PARTY DOCUMENT CERTIFICATION STATEMENT (.0306(b)(2)):
"I certify under penalty of law that I have personally examined and am familiar with the
information contained in this submittal, including any and all documents accompanying this
certification, and that, based on my inquiry of those individuals immediately responsible for
obtaining the information, the material and information contained herein is, to the best of my
knowledge and belief, true, accurate and complete. I am aware that there are significant
penalties for willfully submitting false, inaccurate or incomplete information."
(Nam f me 'atin arty fficial)
(Sioa04oflivQiatingrParty Official)
C0Ia4.b,, ' (Enter State)
COUNTY
11:341
10
Date
I,--��Ik�evl e /��}R�S , a Notary Public of said County and State, do
hereby certify that ,C.njaj .SchaAb did personally appear and sign
before me this day, produced proper identification in the form of✓t�.Lve ergs t? ,
was duly sworn or affirmed, and declared that, to the best of his or her knowledge and belief,
after thorough investigation, the information contained in the above certification is
true and accurate, and he or she then signed this Certification in my presence.
WITNESS my hand and official seal this e2— day of ';zD/y
Notary Public (signature)
My commission expires: S /y a2Ul
Darlene Harris
Notify Public, DiSWd Of COIUMW
My Cmwdssw Exphes 5/1412011
Document Certification Form No. DC -1
(OFFICIAL SEAL)
RECEIVED I DENR 1 Dim
quifPr Protection Secuan
JUL 0 6 2010

North Carolina Department of Environment
and Natural Resources
Division of Waste Management
Superfund Section
Inactive Hazardous Sites Branch
REGISTERED SITE MANAGER DOCUMENT CERTIFICATION STATEMENT (.0306(b)(1)):
"I certify under penalty of law that I am personally familiar with the information contained in
this submittal, including any and all supporting documents accompanying this certification, and
that the material and information contained herein is, to the best of my knowledge and belief,
true, accurate and complete and complies with the Inactive Hazardous Sites Response Act G.S.
130A-310, et seq, and the remedial action program Rules 15A NCAC 13C .0300. I am aware
that there are significant penalties for willfully submitting false, inaccurate or incomplete
information."
� k\G
C�,r 1�j
(Name of Regist� ed SiteManager)
(Signature of Register6k Site Manager)
N U RT K 0A ZOL(NA (Enter State)
U l LFORD
COUNTY
-7 z I t c
Date
I, e,NQ.RI-OTTE HA2RELL , a Notary Public of said County and State, do
hereby certify that 0,"Tzts HA`f did personally appear and sign
before me this day, produced proper identification in the form of N C *V1Z1VER'S LICENSE ,
was duly sworn or affirmed, and declared that, he or she is the duly authorized
environmental consultant of the remediating party of the property referenced above and
that, to the best of his or her knowledge and belief, after thorough investigation, the
information contained in the above certification is true and accurate, and he or she then
signed this Certification in my presence.
•� T E /�
WITNESS my hand and official seal this 2ND day of J UAr
L �.� • • " � `
C.):
OTAl�y;��
Notary Public (signature) Fri'
My commission expires: 02 to3 20IZ Cow
RECEIVED 1 DENR 1 D1NQ
Aquife, D—toc:tinn SPGtion
Document Certification Form No. DC - H JUL 06 2010

TABLE OF CONTENTS
1.0 SITE BACKGROUND................................................................................................1
2.0 RECEPTOR SURVEY...............................................................................................2
3.0 HRC INJECTION.......................................................................................................3
4.0 HRC MONITORING ACTIVITIES..............................................................................5
5.0 GROUNDWATER ANALYTICAL RESULTS.............................................................6
6.0 CONCLUSIONS AND RECOMMENDATIONS.........................................................7
7.0 LIMITATIONS............................................................................................................8
TABLES
1 Monitoring Well Construction Details
2 Field Analysis Summary
3 Historical Groundwater Analytical Summary (Volatile Organic Compounds)
FIGURES
1 Site Location Map
2 Site Survey
3 Surrounding Property Owners Map
4 HRC Injection Locations
5 Historical Average Groundwater Elevations
6 Shallow Groundwater Map
7 Tetrachloroethene Isoconcentration Map
APPENDICES
A Tetrachloroethene versus Time Graphs
B Laboratory Report and Chain -of -Custody Document
97626 1 GS01OR084 Page i May 7, 2010
Copyright 2010 Kleinfelder

1.0 SITE BACKGROUND
The street address of the site is 3920 Westpoint Boulevard in the Westpoint Business
Park, Winston-Salem, Forsyth County, North Carolina. The site is located on the south
side of Westpoint Boulevard and east of Viceroy Drive (Figure 1). Fairchild Industrial
Products Company occupies the building.
Kleinfelder (previously Trigon Engineering Consultants, Inc.) conducted a
Comprehensive Site Assessment (CSA), dated December 11, 1998, which concluded
that the volatile organic compounds (VOCs) tetrachloroethene or perchloroethene
(PCE), trichloroethene (TCE), cis-1,2-dichloroethene (cis-1,2-DCE), and toluene were
detected in soils near the source area. VOCs were detected above North Carolina Title
15A NCAC 2L groundwater standards (NCGWS) in monitoring wells MW-1, MW-2,
MW-3, MWA and MW-6. A Corrective Action Plan (CAP) proposing the application of
Hydrogen Release Compound (HRC) was prepared to address these constituents. No
free product was encountered at the site during the CSA.
Both Forsyth County Tax Maps and the 1950 USGS 7.5-Minute Topographic Map,
Winston-Salem West Quadrangle indicate a tributary of Salem Creek formerly crossed
the western and southern portions of the site flowing to the southeast. No surface
water is currently located within 500 feet of the source area. Buried water, power, and
natural gas utilities are located along the eastern side of Viceroy Drive running north to
south. However, none of these utilities are suspected conduits of contaminant
migration or vapor accumulation.
The North Carolina Department of Environment and Natural Resources (NCDENR)
Groundwater Section approved the CAP in May 2001. The goal of the CAP was to
provide details for the remediation of PCE by assuring that known and foreseeable
pathways are monitored while natural degradation occurs. The preferred remedial
alternative to address soil contamination in the source area was soil vapor extraction
(SVE). A SVE system was installed and operated at the site from July 2000 through
June 2001. The preferred remedial alternative to address groundwater contamination
was the application of HRC.
An Administrative Agreement for the REC Program was executed March 3, 2009. A
survey of the property was conducted in June 2009. A copy of the survey is included as
Figure 2.
97626 1 GS01 OR084 Page 1 of 9 May 7, 2010
Copyright 2010 Kleinfelder

2.0 RECEPTOR SURVEY
On September 29, 1998, Kleinfelder completed a limited well survey of the site area.
The limited well survey reconnaissance consisted of viewing the properties within 1,500
feet of the subject site and talking to available property owners. Water meters were
identified at properties having public water service. Two water supply wells were
identified within 1,500 feet of the source area. One of the water supply wells is actively
used. The other water supply well is not actively used since the home was connected
to municipal water.
In November 2005, Kleinfelder updated the well survey by conducting a field
reconnaissance of properties and by mailing letters to the property owners within 500
feet downgradient of the site. Letters were sent to five property owners by registered
mail. No water supply wells were identified within 500 feet of the site and no water
wells were identified within 1,500 feet downgradient (southeast) of the site. However,
two water supply wells were identified approximately south-southwest (crossgradient) of
the site. Based on the locations of the wells identified, they are not anticipated to be
impacted by contaminants at the site.
Land use in Westpoint Business Park is primarily commercial and industrial. The
majority of the properties in the business park are zoned GI. Zone GI is defined as
general industrial. The site is bound to the north by Westpoint Boulevard, to the east by
Annapolis Drive, to the south by Sides Mobile Home Court, and to the west by Viceroy
Drive.
On October 14, 2009, a survey was completed to include areas within '/2 mile of the
release. The areas within '/2 mile north and east of the site generally include industrial
properties. Fire hydrants and water meters were observed in these areas. No water
supply wells were observed. The areas within'/2 mile south and west of the site include
residential and industrial properties. This area is on the southern edge of the City of
Winston-Salem limits. The properties on the north side of West Clemmonsville Road
were annexed by the City of Winston-Salem in September of 2006. According to the
Forsyth County GIS, many of the residences consist of homes built more than 30 years
ago. Fire hydrants and water meters were observed in the area as well as several
water supply wells. Due to the age of the residences and being on the outskirts of the
city limits, the properties are likely to have water supply wells. Figure 3 shows the
location of the wells observed during the surveys. Several small ponds were also
97626 1 GS01 OR084 Page 2 of 9 May 7, 2010
Copyright 2010 Kleinfelder

observed in the area and can be seen in the aerial photograph (Figure 3). Water wells
identified during the receptor survey are not anticipated to be impacted by the release
at the site.
3.0 HRC INJECTION
Kleinfelder requested a permit from the Underground Injection Control (UIC) Program of
the Division of Water Quality to inject HRC for remediation of groundwater
contamination identified during the CSA. The original UIC Program permit expired
September 30, 2003. The HRC application plan included collecting groundwater
samples prior to application of HRC to provide baseline contaminant levels, drilling
injection wells, injecting seven to eleven pounds of HRC per vertical foot in each well,
and conducting remedial monitoring.
In August 2001, Kleinfelder initiated the first round of HRC injection. HRC injection
locations included twenty-nine injection points (IP-1 through IP-29) and six injection
wells (IW-1 through IW-6) shown on Figure 4. Four injection points (IP-1 through IP-4)
and six injection wells (IW-1 through IW-6) were drilled inside the facility to depths
ranging between 24.5 and 35.0 feet below the ground surface. Seven pounds of HRC
per vertical foot were placed in each borehole and injection well inside the facility. Ten
injection points (IP-5 through IP-14) were drilled in the parking area downgradient of
MW-6 and upgradient of MW-7 to depths of approximately 30 feet below the ground
surface. Seven pounds of HRC per vertical foot was placed in each borehole. Fifteen
injection points (IP-15 through IP-29) were drilled upgradient of the source area to
depths ranging between 23 and 35 feet below the ground surface. Eleven pounds of
HRC per vertical foot were placed in injection points IP-15 through IP-29.
Five quarters of groundwater sampling and corrective action monitoring were completed
following the injection of HRC into groundwater at the site. Following the November
2002 sampling event, Kleinfelder recommended additional HRC application in the
vicinity of MW-7, MW-9, MW-10, and MW-13. Kleinfelder requested a second permit
from the Underground Injection Control (UIC) Program of the Division of Water Quality
to inject additional HRC. The second UIC Program permit was effective through
November 30, 2006. This HRC application plan included converting monitoring wells
MW-6, MW-14, and MW-15 into injection wells, drilling additional injection wells,
97626 1 GS01 OR084 Page 3 of 9 May 7, 2010
Copyright 2010 Kleinfelder

injecting seven pounds of HRC per vertical foot in each well, and conducting remedial
monitoring.
On March 11, 2004, Kleinfelder mobilized to the site to begin the installation of the
additional injection wells and points. HRC injection locations included twenty-one
injection points (IP-30 through IP-50), three new injection wells (IW-7, IW-8, and IW-9),
and the conversion of three existing monitoring wells (MW-6, MW-14, and MW-15) to
injection wells (IW-10, IW-11, #W-12). Fifteen injection points (IP-30 through IP-44) and
six injection wells (IW-7 through IW-12) were drilled inside the facility to depths ranging
between 25 and 35 feet below the ground surface. Seven pounds of HRC per vertical
foot was placed in each borehole with the exception of IW-10 and IW-11 in which four
pounds of HRC per vertical foot were placed. Six injection points (IP-45 through IP-50)
were drilled in the parking area downgradient of MW-6 and upgradient of MW-7 to
depths of 40.0 feet below the ground surface. Seven pounds of HRC per vertical foot
were placed in each borehole. The injection locations are shown on Figure 4. HRC
injection was completed in March of 2004.
Kleinfelder submitted a request to modify and renew the UIC Program permit. The
request included augmenting the injection well system in the vicinity of MW-9 and
MW-11, injecting additional HRC, and conducting remedial monitoring. A permit was
issued by the UIC Program on May 2, 2007 and is effective until May 30, 2010.
On May 30, 2007, Kleinfelder mobilized to the site to begin the installation of the
additional injection wells, IW-13 and IW-14. Injection well IW-13 was drilled northwest
of monitoring well MW-11 and injection well IW-14 was drilled northwest of monitoring
well MW-9. The injection well locations are shown on Figure 4. Monitoring wells
DW-17 and DW-18 were also converted to injection wells IW-15 and IW-16,
respectively. Between May 17, 2007 and June 26, 2007, approximately thirty pounds of
HRC was placed in each of the injection wells with the exception of injection wells IW-1,
IW-2, and IW-3. Three hundred pounds of HRC, approximately twenty-five pounds per
injection well, was placed in the injection wells on December 18, 2007; March 4, 2008;
September 3, 2008; and March 4, 2009.
97626 1 GS01 OR084 Page 4 of 9 May 7, 2010
Copyright 2010 Kleinfelder

4.0 HRC MONITORING ACTIVITIES
Static water levels were recorded in all of the monitoring wells on -site on March 31,
2010. Groundwater samples were collected from twelve monitoring wells (MW-1,
DW-2, MW-5, MW-6R, MW-7, MW-8, MW-9, MW-10, MW-11, MW-13, DW-16, and
DW-19) and analyzed for VOCs by EPA Method 6210. Additionally, monitoring wells
DW-2, MW-6R, MW-9, MW-10, MW-11, MW-13, DW-16, and DW-19 were sampled for
metabolic acids. Field parameters including oxidation-reduction potential (ORP), pH,
conductivity, dissolved oxygen, and temperature of representative groundwater samples
were also recorded from each monitoring well sampled. Groundwater elevations in the
existing monitoring wells were used to determine the groundwater flow direction,
average hydraulic gradient, vertical hydraulic gradient, and plume orientation. Table 1
provides a summary of monitoring well construction details and the groundwater
elevations measured on March 31, 2010. Historical average groundwater elevation
measurements are summarized on Figure 5.
The static water levels measured on March 31, 2010 between monitoring wells MW-1
and MW-7 indicate a horizontal groundwater flow gradient of 0.03 feet per foot to the
southeast. A groundwater flow map of the shallow aquifer based on the March 31,
2010 groundwater elevations is shown on Figure 6. Static water levels measured in
monitoring wells MW-1 and DW-2 indicate a vertical groundwater gradient of 0.01 feet
per foot downward. Static water levels measured in monitoring wells MW-10 and
DW-16 indicate a vertical groundwater gradient of 0.04 feet per foot downward. Static
water levels measured in monitoring wells MW-6R and DW-19 indicate a vertical
groundwater gradient of 0.04 feet per foot downward.
In -situ aquifer tests performed on shallow monitoring wells at the site during the CSA
indicated that the surficial aquifer has an average hydraulic conductivity of 1.2 feet per
day. The average groundwater velocity is estimated to be 0.12 feet per day (40 feet per
year), based on the average groundwater gradient from the March 31, 2010 water level
measurements and an estimated effective porosity of thirty percent.
Groundwater samples were collected using low flow sampling procedures from the
monitoring wells. The wells were first purged of one to two well volumes of water, until
field parameters stabilized, at a low flow rate with a peristaltic pump. Groundwater
samples were collected and placed in laboratory prepared containers. The
groundwater samples were maintained on ice until delivered to Pace Analytical in
97626 1 GS01OR084 Page 5 of 9 May 7, 2010
Copyright 2010 Kleinfelder

Huntersville, North Carolina. The samples were analyzed for VOCs by Method 6200
and metabolic acids to monitor contaminant levels at the site and metabolism of HRC.
5.0 GROUNDWATER ANALYTICAL RESULTS
The groundwater field analysis generally indicates that the subsurface environment is
within acceptable limits for biodegradation to occur. The field measurements recorded
on March 31, 2010 are summarized in Table 2, which includes the preferred conditions
for natural biodegradation of chlorinated compounds within the groundwater plume.
Conductivity is recorded for quality control and sampling consistency.
The lab was unable to process the volatile organic acid samples within the hold time.
Therefore, the volatile organic acid sample results are not reported for the March 31,
2010 sampling event.
Groundwater sample analytical results indicate that several VOCs were detected in the
monitoring wells sampled. PCE was detected at levels exceeding the NCGWS in each
of the monitoring wells sampled. PCE concentrations in monitoring wells MW-1, MW-9,
MW-10, MW-11, MW-13, MW-16 and DW-19 decreased since the previous sampling
event and the concentration in monitoring well DW-2, MW-5, MW-7, and MW-8
remained consistent compared to the previous events. The concentration in monitoring
well MW-6R increased. Graphs of the PCE concentrations versus time are included in
Appendix A. Based on a review of the graphs, PCE concentrations in the monitoring
wells generally have decreasing trends, with the exception of monitoring wells DW-16
and DW-19. PCE concentrations in DW-16 generally have an increasing trend that are
stabilizing, and are stable in DW-19.
A graph of the average PCE concentrations versus time is also included in Appendix A.
This graph shows the overall average of the twelve wells sampled, an average of the
shallow wells, and an average of the deep wells. Note that prior to January 2006, ten or
less wells were sampled so the averages are based on fewer data points. The trend in
the deep wells tends to mirror the slight decrease in monitoring well DW-16 which also
shows in a slight decrease in the overall average of the wells in the most recent
sampling event. The shallow wells also showed a decrease in the most recent
sampling event. A PCE isoconcentration map is shown on Figure 7.
97626 1 GS01 OR084 Page 6 of 9 May 7, 2010
Copyright 2010 Kleinfelder

TCE was detected at levels exceeding the NCGWS in monitoring wells MW-1, MW-6R,
MW-9, MW-10, MW-11, MW-13, DW-16, and DW-19. Cis-1,2-DCE was detected at
levels exceeding the NCGWS in monitoring wells MW-1, MW-9, MW-10, MW-13, and
DW-16. Vinyl chloride was detected at levels exceeding the NCGWS in monitoring
wells MW-1, MW-9, MW-10, MW-11, MW-13, and DW-16. A summary of historical
VOC analytical results is provided in Table3. A copy of the analytical results including
the chain -of -custody form is included in Appendix B.
6.0 CONCLUSIONS AND RECOMMENDATIONS
In general, the most definitive evidence of biodegradation of contaminants in
groundwater is the reduction in contaminant concentrations and the presence of the
constituents into which the contaminants degrade. The average PCE concentration
versus time graph in Appendix A indicates the average PCE concentration has
decreased ninety percent (92%) from its peak (approximately 750 pg/L) to the current
average PCE concentration (approximately 63 pg/L). PCE concentrations have shown
generally decreasing trends in each of the monitoring wells, except DW-16 and DW-19.
The presence of daughter products of dechlorination of PCE in monitoring wells MW-1,
DW-2, MW-5, MW-6R, MW-7, MW-8, MW-9, MW-10, MW-11, MW-13, DW-16, and
DW-19 also indicates degradation is occurring. The trend of rising PCE concentrations
in monitoring well DW-16 is of concern; however, the PCE concentrations had
decreased since the last sampling event.
In order to further accelerate the process of natural attenuation, we have prepared and
submitted an application to modify and renew the existing injection permit to allow for
injection of an additional hydrogen generating compound. The Regenesis product 3-D
MicroEmulsion (3DMe) incorporates Hydrogen Release Compound (HRC) Advanced
and is designed to time release highly efficient electron donors. The 3DMe product is
designed to have a greater longevity. Application of the 3DMe as an emulsified
suspension in water will allow for a greater radius of influence during injection. The
radius of influence will increase over time as the soluble components of 3DMe are
distributed within the aquifer by advection and diffusion.
Bio-Dechlor INOCULUM Plus will also be injected, if necessary, to accelerate the
degradation of cis-1,2-dichloroethene and vinyl chloride at the site following application
of 3DMe and evidence of appropriate aquifer conditions.
97626 1 GS01 OR084 Page 7 of 9 May 7, 2010
Copyright 2010 Kleinfelder

The recommended injection plan is intended to further reduce contaminant
concentrations (PCE), address the rising concentrations in DW-16 and the stable
contaminant concentrations in DW-19, and reduce the recalcitrant daughter products of
dechlorination of PCE (primarily cis-1,2-dichloroethene and vinyl chloride). The
injection plan will be implemented following approval by the NCDENR UIC Program.
Based on the results of the monitoring event, we recommend the continuation of
corrective action monitoring on a quarterly schedule. The next monitoring event should
be scheduled for June 2010.
7.0 LIMITATIONS
Kleinfelder offers various levels of investigative and engineering services to suit the
varying needs of different clients. It should be recognized that definition and evaluation
of geologic and environmental conditions are a difficult and inexact science.
Judgments leading to conclusions and recommendations are generally made with
incomplete knowledge of the subsurface conditions present due to the limitations of
data from field studies. Although risk can never be eliminated, more -detailed and
extensive studies yield more information, which may help understand and manage the
level of risk. Since detailed study and analysis involves greater expense, our clients
participate in determining levels of service that provide adequate information for their
purposes at acceptable levels of risk.
During the course of the performance of Kleinfelder's services, hazardous materials
may have been discovered. Kleinfelder assumes no responsibility or liability
whatsoever for any claim, loss of property value, damage, or injury that results from
pre-existing hazardous materials being encountered or present on the project site, or
from the discovery of such hazardous materials. Nothing contained in this report should
be construed or interpreted as requiring Kleinfelder to assume the status of an owner,
operator, or generator, or person who arranges for disposal, transport, storage or
treatment of hazardous materials within the meaning of any governmental statute,
regulation or order. Fairchild Industrial Products Company is solely responsible for
directing notification of all governmental agencies, and the public at large, of the
existence, release, treatment or disposal of any hazardous materials observed at the
property, either before or during performance of Kleinfelder's services. Fairchild
97626 1 GS01 OR084 Page 8 of 9 May 7, 2010
Copyright 2010 Kleinfelder

Industrial Products Company is responsible for directing all arrangements to lawfully
store, treat, recycle, dispose, or otherwise handle hazardous materials, including
cuttings and samples resulting from Kleinfelder's services.
The information included on graphic representations in the Quarterly HRC Monitoring
Report has been compiled from a variety of sources and is subject to change without
notice. Kleinfelder makes no representations or warranties, express or implied, as to
accuracy, completeness, timeliness, or rights to the use of such information. These
documents are not intended for use as a land survey product, nor are they designed or
intended as a construction design document. The use or misuse of the information
contained on these graphic representations is at the sole risk of the party using or
misusing the information.
97626 1 GSO10R084 Page 9 of 9 May 7, 2010
Copyright 2010 Kleinfelder

TABLES

TABLE 1: MONITORING WELL CONSTRUCTION DETAILS
Monitoring
Well
Date
Constructed=feetb
Total
Screened
Interval
feet b s
Depth to
Groundwater
feet TOC
Top of Casing
Elevation
100' Datum
Groundwater
Elevation
100' Datum
MW-1
September-98
27.37
12.37 - 27.37
16.10
94.42
78.32
DW-2
October-98
43.34
38.34 - 43.34
15.97
94.09
78.12
MW-3
September-98
22.32
12.32 - 22.32
14.86
98.17
83.31
MW-4
September-98
18.65
8.65 - 18.65
16.29
91.38
75.09
MW-5
September-98
25.11
15.11 - 25.11
17.21
87.07
69.86
MW-6R
March-04
34.40
14.40 - 34.40
21.39
91.55
70.16
MW-7
November-98
26.56
11.56 - 26.56
21.32
86.81
65.49
MW-8
November-98
26.70
16.70 - 26.70
20.92
89.25
68.33
MW-9
March-99
24A1
9.41 - 24.41
16.34
94.24
77.90
MW-10
March-99
29.52
14.52 - 29.52
18.55
94.09
75.54
MW-11
Ma -99
24.12
9.12 - 24.12
17.54
94.31
76.77
MW-12
May-99
25.70
5.70 - 25.70
16.94
94.28
77.34
MW-13
June-99
33.46
8.46 - 33.46
20.12
94.22
74.10
DW-16
October-05
35.00
30.00 - 35.00
18.41
93.89
75.48
DW-19
December-05
54.80
49.80 - 54.80
18.26
87.46
69.20
feet bgs = Feet below ground surface
feet TOC = Feet below top of well casing
100' Datum = Well casings were surveyed to an arbitrary 100 foot Datum. The benchmark is the center of the
manhole cover at the south end of Viceroy Street.
Notes: Static Water Levels were measured March 31, 2010.
MW-6, MW-14, MW-15, DW-17, and DW-18 were converted to injection wells IW-12, IW-14, IW-
11, IW-15, and IW-16 respectively.
97626 1 GS01 OR084 Page 1 of 1 May 6, 2010
Copyright 2009 Kleinfelder

TABLE 2: FIELD ANALYSIS SUMMARY
Monitoring
Well
Sample Date
Temperature
(°C)
Conductivity
(MS/cm)
pH
Dissolved
oxygen
ORP
(mV)
Preferred
Conditions
> 200C
---
5<pH<9
<0.5 mg/L
<50 mV
MW-1
03/31/10
17.37
0.255
7.34
0.19
-173
DW-2
03/31/10
17.95
2.218
7.5
0.3
-147.1
MW-5
03/31/10
12.33
0.123
8.2
0.37
-141
MW-6R
03/31/10
17.08
0.426
7.31
0.22
-118.2
MW-7
03/31/10
17.29
0.147
7.64
0.30
-132.9
MW-8
03/31/10
19.58
0.328
6.35
1.55
-122.9
MW-9
03/31/10
19.86
0.638
7.37
0.45
-106.6
MW-10
03/31/10
20.35
0.493
6.17
0.28
-143.8
MW-11
03/31/10
19.31
0.521
7.81
0.32
-142.9
MW-13
03/31/10
20.22
0.816
6.38
0.28
-146.2
DW-16
03/31/10
20.16
0.195
6.96
0.50
-157.5
DW-19
03/31/10
18.17
0.183
7.16
1 2.21
-112.9
ORP = oxidation-reduction potential
mS/cm = millisiemens per centimeter
mg/L = milligrams per liter, analogous to parts per million
mV = millivolts
Note: Conductivity is measured for consistency in groundwater sample collection.
97626 1 GS01 OR084 Page 1 of 1 May 6, 2010
Copyright 2009 Kleinfelder

TABLE 3: HISTORICAL GROUNDWATER ANALYTICAL SUMMARY (VOLATILE ORGANIC COMPOUNDS)
Sampling Location
EPA Method 6200 A alytical Results /L)
Sampling Date
PCE
TCE
Trans-1,2-DCE
cis-1,2-DCE
1,1-DCE
Chloroform
Chloro-
methane
Bromochloro-
methane
Acetone
Vinyl nyl Chloride
Toluene
MTBE
methane
Ethylbenzene
1,2,4-Trimethyl
benzene
Xylenes
Benzene
Methylene
Chloride
1,2-DCA
Chloro-
ethane
NCGWS
0.7
3
100
70
7
70
3
0.6
6,000
0.03
600
20
NE
600
400
500
1
5
0.4
3.000
MW-1
10/07/98
15.6
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
06/25/99
1.5
BDL
BDL
BDL
BDL
BDL
BDL
4.5
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
08/24/00
23
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
06/14/01
9.9
BDL
BDL
BOL
BDL
5.4
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
11/27/01
0.52
BDL
BDL
BDL
BDL
BDL
BDL
26
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
02/26/02
0.63
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
05/01/02
BDL
BDL
BDL
BDL
BDL
BDL
BDL
9.6
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
08/13/02
4.7
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
I BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
11/21/02
2.6
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
0.62
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
06/09/04
1.7
2.5
BDL
16
BDL
BDL
BDL
BDL
NA
1.5
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
09/09/04
BDL
1.4
0.67
14
BDL
BDL
BDL
BDL
NA
1.1
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
12/09/04
BDL
1.2
BDL
17
BDL
BDL
BDL
BDL
NA
0.67
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
03/22/05
1.2
6.5
0.55
37
BDL
BDL
BDL
BDL
BDL
1.6
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
09/28/05
BDL
BDL
1.3
60
BDL
BDL
BDL
BDL
BDL
4.2
0.51
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
01/06/06
0.63
BDL
BDL
2.4
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
03/15/06
BDL
1.6
BDL
11
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
06/21/06
BDL
BDL
0.85
50
BDL
BDL
BDL
BDL
BDL
4.4
BDL
BDL
BDL
BOL
BDL
BDL
BDL
BDL
BDL
BDL
09/28/06
BDL
0.59
BDL
7.6
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
12/06/06
BDL
BDL
BDL
3.8
BDL
BDL
52
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
03/08/07
BDL
1.5
2.1
54
BDL
BDL
BDL
BDL
BDL
8.7
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
06/26/07
BDL
15
4.6
170
0.76
BDL
BDL
BDL
BDL
23
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
09/18/07
BDL
BDL
BDL
6.1
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
12/18/07
0.93
BDL
BDL
0.87
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
03/04/08
1.1
BDL
BDL
1.9
BDL
B-DL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
06/04/08
5.4
8.9
1.4
196
0.96
BDL
BDL
BDL
NA
7.8
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
09/03/08
4.1
13.4
2.2
280
0.76
BDL
BDL
BDL
NA
5
BDL
BDL
BDL
BDL
BDL
BDL-
BDL
BDL
BDL
BDL
01/13/09
3.3
2.7
BDL
4.5
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BOL
BDL
BDL
BDL
03/04/09
4.3
1.0
BDL
6.9
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
07/08/09
3.4
2.5
5.5
278
1.2
BDL
BDL
BDL
NA
21.9
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
09/03/09
2.4
4
6.6
356
BDL
BDL
BDL
BDL
NA
19.9
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
12/09/09
6.5
4.6
3.6
159
0.74
BDL
BDL
BDL
NA
26.3
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
03/31/10
4.9
83.6
29
854
3.7
BDL
BDL
BDL
NA
155
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
DW-2
10/16/98
2.4
BDL
BDL
BDL
BDL
12.9
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
06/25/99
45
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
08/24/00
5.3
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
11/01/00
2.5
BDL
BDL
BDL
BDL
NA
BDL
NA
NA
NA
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
12101/00
4.8
BDL
BDL
BDL
BDL
NA
BDL
NA
NA
NA
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
01/03/01
BDL
BDL
BDL
BDL
BDL
NA
BDL
NA
NA
NA
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
06/14/01
BDL
BDL
BDL
BDL
BDL
1.3
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
11/27/01
0.92
BDL
BDL
BDL
BDL
BDL
BDL
0.59
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
02/26/02
0.50
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
05/01/02
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
08/13/02
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
11/21/02
2.6
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
06/09/04
2.2
BDL
BDL
BDL
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
09/09/04
17
7.2
BDL
BDL
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
12/09/04
1.2
1.4
BDL
BDL
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
2.2
BDL
BDL
BDL
BDL
BDL
BDL
03/22/05
BDL
1.2
BDL
1.5
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
8.1
0.8
BDL
BDL
BDL
BDL
09/28/05
BDL
BDL
BDL
3.6
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
01/06/06
11
0.61
BDL
3.3
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
03/15/06
4
0.54
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
0.58
BDL
BDL
BDL
BDL
BDL
06/21/06
7.7
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
09/28/06
13
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
12/06/06
16
BDL
BDL
BDL
BDL
BDL
7.1
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
03/08/07
12
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
06/26/07
12
BDL
BDL
0.86
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
NCGWS = North Carolina Groundwater Standards
PCE = Tetrachloroethene
pg/L = micrograms per liter, analogous to parts per billion
TCE = Trichloroethene
BDL = Below Laboratory Detection Limits
Trans-1,2-DCE = trans-1,2-Dichloroethene
NA = Not Analyzed
cis-1,2-DCE = cis-1,2-Dichloroethene
NE = Not Established
1.1-DCE = 1,1-Dichloroethene
Bold = Concentration exceeds NCGWS
1,2-DCA = 1,2-Dichloroethane
976261 GS01OR084
Copyright 2009 Kleinfelder Page 1 of 7 May 6, 2010

TABLE 3: HISTORICAL GROUNDWATER ANALYTICAL SUMMARY (VOLATILE ORGANIC COMPOUNDS)
Sampling Location
EPA Method 6200 A alytical Results /L
Sampling Date
PCE
TCE
Trans-1,2-DCE
cis-1,2-DCE
1,1-DCE
Chloroform
Chloro-
methane
Bromochloro-
methane
Acetone
Vinyl Chloride
Toluene
MTBE
Bromo-
methane
Ethylbenzene
1,2,4-Trimethyl
benzene
Xylenes
Benzene
Methylene
Chloride
1,2-DCA
Chloro-
ethane
NCGWS
0.7
3
100
70
7
70
3
0.6
6,000
0.03
600
20
NE
600
400
500
1
5
0.4
3,000
DW-2 Continued
09/18/07
4.1
BDL
BDL
39.1
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
12/18/07
2.5
BDL
BDL
9.7
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
03/04/08
2.7
0.55
BDL
7.4
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
06/04/08
2.7
BDL
BDL
2.0
BDL
BDL
BDL
PDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
09/03/08
2.3
BDL
BDL
1.4
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
01/13/09
4.1
2.2
BDL
3.2
BDL
BDL
BDL
BDL
NA
BDL
0.53
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
03/04/09
2.6
0.61
BDL
8.6
BDL
BDL
BDL
BDL
NA
BDL
I BDL
BDL
I BDL
I BDL
I BDL
BDL
BDL
I BDL
I BDL
BDL
07/08/09
2.2
BDL
BDL
1.7
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
1.1
09/03/09
3.1
0.69
BDL
1.8
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
12/09/09
5.3
2.4
BDL
5.8
BDL
BDL
BDL
BDL
NA
BDL
BDL
I BDL
I BDL
BDL
BDL
BDL
BDL
I BDL
I BDL
BDL
03/31/10
5.2
2.6
BDL
5.5
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
I BDL
I BDL
BDL
M W-3
10/07/98
BDL
BDL
BDL
BDL
BDL
1.3
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
06/25/99
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
08/24/00
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
11/28/01
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
06/09/04
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
09/09/04
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
12/09/04
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
MW-4
10/07/98
3.3 BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
06/25/99
2.2 BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
08/24/00
Well was dry on the sampling date
06/14/01
Well was dry on the sampling date
02/26/02
Well was dry on the sampling date
05/01/02
Well was dry on the sampling date
08/13/02
Well was dry on the sampling date
MW-5
10/07/98
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
06/25/99
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
08/24/00
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
02/26/02
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
05/01/02
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
08/13/02
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
11/21/02
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
08/22/03
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL I
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
09/09/04
5.0
4.6
BDL
1.1
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
12/09/04
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
03/22/05
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
06/09/05
0.66
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
09/28/05
0.78
0.53
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
01/05/06
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
03/15/06
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
0.52
BDL
BDL
BDL
BDL
BDL
06/21/06
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL I
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
09/28/06
BDL
BDL
BDL
2.3
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
12/06/06
BDL
BDL
BDL
2.6
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
03/08/07
BDL
BDL
BDL
2.1
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
06/26/07
BDL
BDL
BDL
3.2
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
09/18/07
BDL
BDL
BDL
2.4
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
12/18/07
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
03/04/08
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
06/04/08
BDL
BDL
BDL
1.2
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
09/03/08
0.53
BDL
BDL
0.84
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
01/13/09
0.67
0.62
BDL
0.59
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
03/04/09
1.5
BDL
BDL
BDL
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
NCGWS = North Carolina Groundwater Standards
pg/L = micrograms per liter, analogous to parts per billion
BDL = Below Laboratory Detection Limits
NA = Not Analyzed
NE = Not Established
Bold = Concentration exceeds NCGWS
PCE = Tetrachloroethene
TCE = Tichooroethene
Trans-1,2-DCE = trans-1,2-Dichloroethene
cis-1,2-DCE = cis-1,2-Dichloroethene
1.1-DCE = 1, 1 -Dichloroethene
1,1-DCA = 1, 1 -Dichloroethane
976261 GS01OR084
Copyright 2009 Kleinfelder Page 2 of 7 May 6, 2010

TABLE 3: HISTORICAL GROUNDWATER ANALYTICAL SUMMARY (VOLATILE ORGANIC COMPOUNDS)
Sampling Location
EPA Method 6200 A alytical Results /L)
Sampling Date
PCE
TCE
Trans-1,2-DCE
cis-1,2-DCE
1,1-DCE
Chloroform
Chloro-
methane
Bromochloro-
methane
Acetone
Vinyl Chloride
Toluene
MTBE
Bromo-
methane
Emylbenzene
1,2,4-Trimethyl
benzene
Xylenes
Benzene
Methylene
Chloride
1,2-DCA
Chloro-
ethane
NCGWS
0.7
3
100
70
7
70
3
0.6
6,000
10.03
600
20
NE
600
400
500
1
1 5
0.4
3,000
M W-5
07/08/09
BDL
BDL
BDL
0.51
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
09/03/09
BDL
BDL
BDL
0.51
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
12/09/09
1.1
0.75
BDL
1.2
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
03/31/10
1.1
0.78
BDL
3.3
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
MW-6
10/07/98
10.4
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
06/25/99
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
08/24/00
1.3
BDL
BDL
BDL
BDL
BDL
BDL
BDL
130
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
O6/14/01
Well was dry on the sampling date
11/27/01
Well was dry on the sampling date
02/26/02
Well was dry on the sampling date
05/01/02
Well was dry on the sampling date
08/13/02
Well was d on the sampling date
11/21/02
Well was d on the sampling date
MW-6R
06/09/04
55
8.2
BDL
22
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
09/09/04
58
10
BDL
12
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
12/09/04
94
8.1
BDL
BDL
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
03/22/05
80
9
BDL
1.5
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
O6/09/05
100
9.5
BDL
2.2
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
09/28/05
100
5.6
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
O1/05/06
65
6.1
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
03/15/06
58
9.8
BDL
1.6
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
0.83
BDL
BDL
BDL
BDL
BDL
O6/21/06
53
13
BDL
3.6
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
09/28/06
49
11
BDL
1.8
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
12/06/06
58
12
BDL
3
BDL
BDL
8
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
03/08/07
54
13
BDL
3.9
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
06/26/07
58
13
BDL
5.6
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
09/18/07
17.8
7.5
BDL
6.1
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
12/18/07
42.9
9.7
BDL
4.9
BDL
BDL
BDL
BDL
BDL
I BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
03/04/08
64.5
12.0
BDL
5.5
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
06/04/08
44.9
11.1
BDL
5.0
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
09/03/08
10.9
3.6
BDL
1.7
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
01/13/09
61.4
18.8
BDL
8.4
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
03/04/09
20.4
5.9
BDL
2.4
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
07/08/09
32.7
18.5
BDL
10.4
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
09/03/09
15.9
14.9
BDL
12.7
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
12/09/09
2.6
2.4
BDL
1.8
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
03/31/10
19.1
9.8
BDL
6.9
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
MW-7
11/16/98
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
06/25/99
1.1
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
08/24/00
4
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
06/14/01
7.5
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
11/27/01
5
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
02/26/02
3.6
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
05/01/02
2.3
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
08/13/02
Well was dry on the sampling date
11/21/02
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
O8/22/03
15
2.4
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
O6/09/04
19
6.9
BDL
BDL
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
09/09/04
15
5.5
BDL
0.76
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
12/09/04
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
03/22/05
4.3
8.6
BDL
1.2
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
06/09/05
2.1
9.1
BDL
1
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL I
BDL
BDL
BDL
BDL
BDL
09/28/OS
1.4
8.7
BDL
1
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
01/05/O6
0.98
15
BOL
2.7
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
0.64
BDL
BDL
BDL
BDL
BDL
03/15/06 1
BDL
14
BDL
3
BDL
BDL
BDL
BDL
BDL
BDL I
BDL I
BDL
BDL
BDL
0.74
BDL
BDL
BDL
BDL
BDL
NCGWS = Norm Carolina Groundwater Standards
pg/L = micrograms per liter, analogous to parts per billion
BDL = Below Laboratory Detection Limits
NA = Not Analyzed
NE = Not Established
Bold = Concentration exceeds NCGWS
PCE = Tetrachloroemene
TCE = Trichloroemene
Trans-1,2-DCE = trans-1,2-Dichloroethene
cis-1,2-DCE = cis-1.2-Dichloroethene
1,1 -DC E = 1,1-Dichloroemene
1,1-DCA = 1,1-Dichloroethane
97626 1 GS01OR084
Copyright 2009 Kleinfelder Page 3 of 7 May 6, 2010

TABLE 3: HISTORICAL GROUNDWATER ANALYTICAL SUMMARY (VOLATILE ORGANIC COMPOUNDS)
Sampling Location
EPA Method 6200 A alytical Results /L
Sampling Date
PCE
TCE
Trans-1,2-DCE
cis-1,2-DCE
1,1-DCE
Chloroform
Chloro-
methane
Bromochloro-
methane
Acetone
Vinyl Chloride
Toluene
MTBE
Bromo-
methane
Ethylbenzene
1,2,4-Trim: rn•,4
benzene
Xylenes
Benzene
Methylene
Chloride
1,2-DCABeane
NCGWS
0.7
3
100
70
7
70
3
0.6
6,000
0.03
600
20
NE
600
400
500
1
5
0.4
3,000
MW-7 Continued
06/21/06
BDL
13
BDL
2.8
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
09/28/06
BDL
8
BDL
9.1
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
12/06/06
BDL
4
BDL
8.2
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
03/08/07
BDL
9
BDL
15
BDL
BDL
BDL
BDL
BDL
BDL
0.65
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
06/26/07
BDL
0.67
0.57
19
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
09/18/07
BDL
BDL
1.2
23.9
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
1.5
BDL
12/18/07
BDL
6.2
0.88
29.4
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
03/04/08
0.54
14.4
1.1
17.8
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
O6/04/08
BDL
5.1
0.58
9.1
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
09/03/08
BDL
4.4
0.95
16.1
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
01/13/09
0.85
1.7
BDL
2.2
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
03/04/09
2.0
0.87
BDL
BDL
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
07/08/09
BDL
2
1.4
26.9
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
09/03/09
BDL
BDL
BDL
4
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
12/09/09
1.1
0.65
BDL
BDL
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
03/31/10
1.2
0.92
BDL
6.8
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
MW-8
11/16/98
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
06/25/99
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
O8/24/00
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
08/22/03
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
03/22/05
1.3
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
06/09/05
0.67
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
09/28/05
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
01/05/06
1.2
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
0.64
BDL
BDL
BDL
BDL
BDL
03/15/06
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
O6/21/06
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
09/28/06
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
12/06/06
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
03/08/07
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
0.69
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
06/26/07
BDL
BDL
BDL
BDL
BDL
0.50
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
09/18/07
BDL
BDL
BDL
BDL
BDL
0.60
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
12/18/07
0.55
BDL
BDL
BDL
BDL
0.58
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
03/04/08
1.3
BDL
BDL
0.78
BDL
0.70
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
06/04/08
1.5
BDL
BDL
0.75
BDL
0.51
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
09/03/08
0.7
BDL
BDL
0.57
BDL
0.63
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
01/13/09
1.3
0.63
BDL
1.1
BDL
0.54
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
03/04/09
2.1
0.55
BDL
0.88
BDL
0.54
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
07/08/09
0.5
BDL
BDL
0.79
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
09/03/09
BDL
BDL
B
BDL
BDLL
BD
BDL
NA
D
B
B
L
B
L
DL
BDL
BDL
BDL
BDL
1.5
0.76
BDL
BD
DL
B
BDL
NA
BD
BD
BD
B12/09/09 DLL
BDL
BELL
BDL
BDL
BDL
BDL
03/31/10
1.2
0.59
BDL
2.0
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
M W-9
04/12/99
144
159
2.4
49
1.3
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
O6/25/99
177
187
BDL
60
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
08/24/00
1,300
920
15
140
3.3
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
10/31/00
1,700
710
13
190
3.5
NA
BDL
NA
NA
NA
NA
NA
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
12/01/00
1,000
570
8.7
170
2.9
NA
BDL
NA
NA
NA
NA
NA
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
01/03/01
1,100
770
11
330
5
NA
BDL
NA
NA
NA
NA
NA
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
06/14/01
420
220
24
510
6.8
11
BDL
BDL
BDL
2
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
11/27/01
2,800
1,600
BDL
710
BDL
BDL
BDL
BDL
BDL I
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
02/26/02
5,000
1,800
BDL
1,000
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
05/01/02
5,000
1,900
25
1,200
6.2
BDL
BDL
34
BDL
1.5
0.92
2.7
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
08/13/02
3,600
1,200
31
1,200
5.4
BDL
BDL
BDL
BDL
2.5
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
11/21/02
4,000
1,500
BDL
2,200
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
06/09/04
1,400
730
70
2,300
7.5
BDL
BDL
BDL
NA
35
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
09/09/04
820
590
60
2,300
BDL
BDL
BDL
BDL
NA
15
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
12/09/04 1
540
800
BDL 1
1,200
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
NCGWS = North Carolina Groundwater Standards PCE = Tetrachloroethene
pg/L = micrograms per liter, analogous to parts per billion TCE = Tichooroethene
BDL = Below Laboratory Detection Limits Trans-1,2-13CE = trans-1,2-Dichloroethene
NA = Not Analyzed cis-1,2-DCE = cis-1,2-Dichloroethene
NE = Not Established 1,1-DCE = 1,1-Dichloroethene
Bold = Concentration exceeds NCGWS 1,1-DCA = 1, 1 -Dichloroethane
97626 1 GSO10R084
Copyright 2009 Kleinfelder Page 4 of 7 May 6, 2010

TABLE 3: HISTORICAL GROUNDWATER ANALYTICAL SUMMARY (VOLATILE ORGANIC COMPOUNDS)
Sampling Location
EPA Method 6200 A alytical Results /L
Sampling Date
PCE
TCE
Trans-1,2-DCE
-]
cis-1,2-DCE
1,1-DCE
Chloroform
Chloro-
methane
Bromochloro-
methane
Acetone
Vinyl Chloride
Toluene
MTBE
Bromo-
methane
1,2,4-Trimethy
Ethylbenzehe benzene
Xylenes
Benzene
Methylene
Chloride
12-DCA
,
Chloro-
ethane
NCGWS
0.7
3
100
70
7
70
3
0,6
1 6,000
0.03
600
20
NE
600 400
500
1
5
0.4
3.000
MW-9 Continued
03/22/05
900
1,100
BDL
990
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
06/09/05
250
830
48
850
3.2
BDL
BDL
BDL
BDL
23
BDL
BDL
BDL
BDL
BDL
BDL
0.58
0.58
BDL
BDL
09/28/05
80
520
47
960
BDL
BDL
BDL
BDL
BDL
34
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
01/05/06
200
760
54
740
BDL
BDL
BDL
BDL
BDL
49
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
03/15/06
270
660
44
700
BDL
BDL
BDL
BDL
BDL
40
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
06/21/06
89
240
42
1,100
BDL
BDL
BDL
BDL
BDL
200
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
09/28/06
190
570
32
760
BDL
BDL
BDL
BDL
BDL
110
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
12/06/06
300
620
41
600
BDL
BDL
BDL
BDL
BDL
110
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
03/08/07
280
580
73
950
3.6
BDL
BDL
BDL
BDL
280
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
06/26/07
38
110
70
1,300
BDL
BDL
BDL
BDL
BDL
500
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
09/18/07
133
397
71A
721
BDL
BDL
BDL
BDL
BDL
208
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
12/18/07
42.7
187
32.9
520
BDL
BDL
BDL
BDL
BDL
320
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
03/04/08
27.7
146
42.8
536
BDL
BDL
BDL
BDL
NA
277
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
06/04/08
18.6
76.5
31.1
893
BDL
BDL
BDL
BDL
NA
466
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
09/03/08
54.5
198
70.9
903
3.6
BDL
BDL
BDL
NA
905
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
01/13/09
24.0
93.7
45.7
466
BDL
BDL
BDL
BDL
NA
822
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
03/04/09
30.1
133
48.1
498
BDL
BDL
BDL
BDL
NA
824
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
07/08/09
51
161
25.7
482
BDL
BDL
BDL
BDL
NA
711
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
09/03/09
30.7
142
27.7
601
BDL
BDL
BDL
BDL
NA
1,140
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
12/09/09
115
224
63
638
2.4
BDL
BDL
BDL
NA
2,170
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
03/31/10
73.0
160
18.5
404
BDL
BDL
BDL
BDL
NA
828
BDL
BDL
BDL
BDL
BDL
BDL
BDL
I BDL
BDL
BDL
MW-110
04/12/99
7.5
1.3
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
06/25/99
106
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
O8/24/00
240
68
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
06/14/01
440
21
BDL
5.7
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
11/27/01
270
60
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
02/26/02
31
BDL
BDL
440
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
05/01/02
65
9.1
0.97
190
BDL
BDL
BDL
8.1
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
08/13/02
150
15
BDL
90
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
11/21/02
170
35
BDL
39
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
06/09/04
150
63
BDL
46
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
09/09/04
150
57
BDL
48
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
12/09/04
150
40
BDL
20
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
03/22/05
160
28
BDL
18
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
06/09/05
140
27
BDL
16
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
09/28/05
150
12
BDL
13
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
01/05/06
180
15
BDL
29
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
03/15/06
170
11
BDL
25
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
06/21/06
160
13
BDL
25
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
09/28/06
160
13
BDL
38
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
12/06/06
130
8.6
BDL
26
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
16
BDL
BDL
03/08/07
140
14
BDL
38
BDL
BDL
BDL
BDL
BDL
BDL
0.61
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
06/26/07
130
14
BDL
51
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
09/18/07
104
42.1
BDL
77.9
BDL
BDL
BDL
BDL
BDL
5
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
12/18/07
79.0
18.8
BDL
64.3
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
03/04/08
149
17.0
BDL
68.9
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
O6/04/08
46.4
13.6
0.73
120
BDL
BDL
BDL
BDL
NA
1.7
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
09/03/08
86.6
16.5
0.57
111
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
01/13/09
87.1
28.7
1.2
84.0
BDL
BDL
BDL
BDL
NA
62
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
03/04/09
58.0
23.0
1.4
88.8
BDL
BDL
BDL
BDL
NA
7.0
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
07/08/09
29.1
4
0.58
115
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
09/03/09
40.8
10.3
0.98
132
BDL
BDL
BDL
BDL
NA
1.3
0,85
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
12/09/09
25
18.3
2.6
102
BDL
BDL
BDL
BDL
NA
51.3
0.79
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
03/31/10
9.5
14.0
2.4
106
BDL
BDL
BDL
BDL
NA
82.8
0.61
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
NCGWS = North Carolina Groundwater Standards
pg/L = micrograms per liter, analogous to parts per billion
BDL = Below Laboratory Detection Limits
NA = Not Analyzed
NE = Not Established
Bold = Concentration exceeds NCGWS
PCE = Tetrachloroethene
TCE = Trichloroethene
Trans-1,2-DCE = trans-1,2-Dichloroethane
cis-1,2-DCE = cis-1,2-Dichloroethene
1,1-DCE = 1,1-Dichloroethane
1,1-DCA = 1. 1 -Dichloroethane
97626 1 GSO1OR084 May 6, 2010
Copyright 2009 Kleinfelder Page 5 01 7 Y

TABLE 3: HISTORICAL GROUNDWATER ANALYTICAL SUMMARY (VOLATILE ORGANIC COMPOUNDS)
Sampling Location
EPA Method 6200 A alytical Results /L)
Sampling Date
PCE
TCE
Trans-1,2-DCE
cis-1,2-DCE
1,1-DCE
Chloroform
Chloro-
methane
Bromochloro-
methane
Acetone
Vinyl Chloride
Toluene
MTBE
Bromo-
methane
Etl'ylbe �ene
1,2,4-Trimethyt
benzene
xylenes
Benzene
Methylene
Chloride
1,2 DCA
Chloro-
ethane
NCGWS
0.7
3
100
70
7
70
3
0.6
6,000
0.03
600
20
NE
600
400
500
1
5
0.4
3,000
M W-11
06/04/99
415
23
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
08/24/00
200
34
BDL
4.9
BDL
BDL
BDL
BDL
76
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
06/14/01
200
74
BDL
21
BDL
BDL
BDL
34
BDL
BDL
0.85
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
11/28/01
210
23
BDL
19
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
02/26/02
600
46
BDL
80
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
05/01/02
370
30
0.62
31
BDL
1.2
BDL
0.96
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
08/13/02
Well was dry on the sampling date
11/21/02
Insufficient water to sample
06/09/04
380
52
BDL
35
BDL
1.1
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
09/09/04
360
45
BDL
30
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
12/09/04
480
59
BDL
43
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
03/22/05
430
54
BDL
45
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
06/09/05
290
39
BDL
43
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
09/28/05
320
36
BDL
33
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
01/05/06
360
63
BDL
63
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
03/15/06
190
31
BDL
40
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
06/21/06
230
43
BDL
38
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
09/28/06
230
53
BDL
41
BDL
BDL
BDL
RDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
12/06/06
100
36
BDL
32
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
03/08/07
250
41
0.51
36
BDL
0.58
BDL
BDL
BDL
BDL
0.62
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
06/26/07
130
29
BDL
41
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
09/18/07
95.1
31.3
BDL
35.1
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
12/18/07
75.8
30.6
BDL
53.4
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
03/04/08
60.4
28.6
0.80
51.6
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
06/04/08
37.5
18.1
1.1
45.9
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
09/03/08
50.3
29.3
2.4
63.8
BDL
BDL
BDL
BDL
NA
13
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
01/13/09
34.9
20.4
0.69
33.4
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
03/04/09
26.7
18.9
0.67
30.1
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
07/08/09
40.1
29.8
1.4
81
BDL
BDL
BDL
BDL
NA
12A
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
09/03/09
37.7
37.3
2.9
131
BDL
BDL
BDL
BDL
NA
48.4
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
12/09/09
34.2
32.6
2.5
1 98.1
BDL
BDL
BDL
BDL
NA
5.2
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
03/31/10
7.7
4.6
2.6
43.7
BDL
BDL
BDL
BDL
NA
89.9
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
M W-12
06/04/99
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
08/24/00
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
MW-13
06/04/99
112
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
08/24/00
190
2.3
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
06/14/01
260
6
BDL
1.2
BDL
BDL
BDL
BDL
BDL
BDL
0.6
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
11/27/01
170
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
02/26/02
390
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
05/01/02
270
11
BDL
2.2
BDL
0.59
BDL
7.7
BDL
BDL
BDL
BDL
1.2
BDL
BDL
BDL
BDL
BDL
BDL
BDL
08/13/02
320
16
BDL
5.3
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
11/21/02
210
11 1
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
08/22/03
270
34
0.56
35
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
06/09/04
37
24
2.9
220
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
09/09/04
BDL
BDL
BDL
210
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
12/09/04
BDL
BDL
BDL
250
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
03/22/05
BDL
BDL
BDL
130
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
06/09/05
BDL
BDL
BDL
270
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
09/28/05
BDL
BDL
BDL
270
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
01/05/06
BDL
BDL
BDL
220
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
03/15/06
BDL
BDL
BDL
220
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
06/21/06
BDL
BDL
BDL
270
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
09/28/06
BDL
BDL
BDL
280
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
12/06/06
BDL
BDL
5.6
220
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
03/08/07
2.1
1.2
6.0
320
BDL
BDL
BDL
BDL
BDL
BDL
1.3
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
NCGWS = North Carolina Groundwater Standards
PCE = Tetrachloroethene
pg/L = micrograms per liter, analogous to parts per billion
TCE = Trichloroethene
BDL = Below Laboratory Detection Lirnft
Trans-1,2-DCE = trans-1,2-Dichloroethene
NA = Not Analyzed
cis-1,2-DCE = cis-1.2-Dichloroethene
NE = Not Established
1,1-DCE = 1,1-Dichloroethene
Bold = Concentration exceeds NCGWS
1,1-DCA = 1, 1 -Dichloroethane
Note: Laboratory analysis of the groundwater samples collected from monitoring wells MW-13 and DW-16 were run outside the hold time for the September 3, 2008 sampling event.
976261 GS01 OR084 May 6, 2010
Copyright 2009 Kleinfelder Page 6 of 7 Y

TABLE 3: HISTORICAL GROUNDWATER ANALYTICAL SUMMARY (VOLATILE ORGANIC COMPOUNDS)
Sampling Location
EPA Method 6200 A alytical Results ( L
Sampling Date
PCE
TCE
Trans-1,2-DCE
cis-1,2-DCE
1,1-DCE
Chloroform
Chloro-
methane
Bromochloro-
methane
Acetone
Vinyl Chloride
Toluene
MTBE
Bromo- methane
Ethylbenzene
1,benzene 2,4-Trimethyl
Xylenes
Benzene
Chloride Methylene
1,2-DCA
Chloro-
ethane
NCGWS
0.7
3
100
70
7
70
3
0.6
6,000
0.03
600
20
NE
600
400
500
1
5
0.4
3,000
MW-13 Continued
06/26/07
BDL
BDL
BDL
240
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
09/18/07
12.3
12.3
11.2
269
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
12/18/07
BDL
BDL
BDL
220
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
03/04/08
1.9
1.2
9.0
249
BDL
BDL
BDL
BDL
NA
2.1
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
06/04/08
3.6
4.3
11.1
271
BDL
BDL
BDL
BDL
NA
22
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
09/03/08
BDL
BDL
14.3
321
BDL
BDL
BDL
BDL
NA
2.1
BDL
2.4
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
O1/13/09
5.4
6.4
14.2
281
BDL
BDL
BDL
BDL
NA
2.9
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
03/04/09
9.1
7.0
1 12.5
251
BDL
I BDL
BDL
BDL
NA
2.4
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
L BDL
07/08/09
0.65
BDL
9.6
168
0.57
BDL
BDL
BDL
NA
1.8
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
09/03/09
BDL
BDL
9.3
201
BDL
BDL
BDL
BDL
NA
16.5
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
12/09/09
7.2
5.0
11.8
124
BDL
BDL
BDL
BDL
NA
101
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
03/31/10
6.3
4.2
9.0
86.7
BDL
BDL
BDL
BDL
NA
86.1
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
DW-16
10/24/05
490
34
BDL
29
BDL
BDL
3.1
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
01/05/06
3.5
4.7
1.4
470
BDL
BDL
BDL
BDL
BDL
1.8
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
03/15/06
BDL BDL
BDL
480
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
O6/21/06
BDL
I BDL
BDL
530
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
09/28/06
BDL
BDL
BDL
550
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
12/06/06
BDL
5.2
5.9
420
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
22
BDL
BDL
03/08/07
15
23
8.4
620
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
06/26/07
200
130
7.6
460
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
09/18/07
38.7
216
25.9
436
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
12/18/07
12.3
71.7
11.9
451
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
03/04/08
24.3
107
15.5
463
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
06/04/08
278
285
1 53.8
287
BDL
BDL
BDL
BDL
NA
7.9
1.8
BDL
BDL
BDL
1.4
BDL
BDL
BDL
BDL
BDL
09/03/08
592
375
14.7
214
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
01/13/09
597
355
16.9
182
BDL
BDL
BDL
BDL
NA
3.6
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
03/04/09
561
200
8.2
101
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
I BDL
BDL
07/08/09
680
205
7.7
109
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
09/03/09
644
181
5.6
95.3
BDL
BDL
BDL
BDL
NA
6.8
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
12/09/09
711
234
6.2
101
BDL
BDL
BDL
BDL
NA
6.4
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
03/31/10 1
542
162
4.3
85.0
BDL
BDL
BDL
BDL
NA
11.3
BDL
BDL
BDL
I BDL
BDL
BDL
BDL
BDL
BDL
BDL
DW-17
10/24/O5 1
18
17
25
750
0.83
0.65
BDL
BDL
BDL
6.3
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
01/05/06
5.7
43
14
400
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
DW-18
01/05/06 110 16 BDL 2.7 BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL 0.59 BDL BDL BDL BDL BDL
DW-19
01/05/06
100
3.1
BDL
1.2
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
0.65
BDL
BDL
BDL
BDL
BDL
03/15/06
46
1.8
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
0.69
BDL
BDL
BDL
BDL
BDL
06/21/06
56
2.1
BDL
BDL
BDL
0.56
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
09/28/06
56
2.6
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
12/06/06
62
2.2
BDL
0.73
BDL
0.58
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
03/08/07
120
3.4
BDL
0.83
BDL
0.71
BDL
BDL
BDL
BDL
0.60
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
06/26/07
100
3.3
BDL
0.78
BDL
0.59
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
09/18/07
39.9
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
12/18/07
64.2
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
03/04/08
94.8
3.1
BDL
0.90
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
06/04/08
90.9
2.8
BDL
0.78
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
09/03/08
113
3.2
BDL
0.81
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
O1/13/09
112
3.5
BDL
0.93
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
03/04/09
112
3.8
BDL
1.5
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
07/08/09
102
3.2
BDL
0.95
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
09/03/09
100
3.2
BDL
1
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
12/09/09
99.2
3.3
BDL
BDL
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
03/31/10
88.7
3.1
BDL
1.2
BDL
BDL
BDL
BDL
NA
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
BDL
NCGWS = North Carolina Groundwater Standards
PCE = Tetrachloroethene
pg/L = micrograms per liter, analogous to parts per billion
TCE = Trichloroethene
BDL = Below Laboratory Detection Limits
Trans-1,2-DCE = trans-1,2-Dichloroethene
NA = Not Analyzed
cis-1,2-DCE = cis-1,2-Dichloroethene
NE = Not Established
1.1-DCE = 1, 1 -Dichloroethene
Bold = Concentration exceeds NCGWS
1.1-DCA = 1 A-Dichloroethane
Note: Laboratory analysis of the groundwater samples collected from monitoring wells MW-13 and DW-16 were run outside the hold time for the September 3, 2008 sampling event.
97626 1 GS01 OR084
Copyright 2009 Kleinfelder Page 7 of 7 May 6, 2010

FIGURES

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3. W—.tw fhown n raon N a can iatllM of data RIII.(wl Ma bcalian. cW.e. �-----__------_---
Aay 20 and OIS nlwmedw PreMEM ey —.yl. Com wnly. M. I. nol I. b. ten.MnM 1
I bo,a.—, —., GRAPHIC SCALE
.. U..wryw male. no .—t. IA.I I.e alpilie. Wloun camp,M PM wen e1NINe ti 6W}ID-p,3p1
IM ww, .II.w F .w1se w abwdwM, lhs .wryer NIL— dew net —1 1.e1 III BELLE
ACQUISTIOIIS, LLC
wdergp.ld dliitW &~ are ti Un ..ael —6a e1d1e91M W—gh .. dwe ewtlly 00 2797 PC e312Sim
Itrl tb.y w. Iede1M e. aeeMelWy W1 PseWe 'I-1.Iwmelbrl er6mte. The wryer
11ae net OPMe 6y Ieealed I" wMpand .Ii6Me. ( in PERT
SOUTHFORK TOWNSHIP
FORSYPH COUNTY
WINSTON-SALKAI. NORTH CAROL/NA
Regional Land S,,,,yo., Im.
5562 WEST MARKET STREET, SUITE 100
CREENSBORO, NORTH CAROLINA 27409
TELEPHONE [phone]
1 LK E/NF"ELOER FIGURE 2
Bright People. Right solar SITE SURVEY

® = WATER WELL LOCATION
rlooKLEINF-ELDER
Bright People. Right Solutions.
FIGURE 3
SURROUNDING PROPERTY OWNERS MAP
Fairchild Industrial Products Company I
I 3920 Westpoint Boulevard
Winston-Salem, North Carolina
57
...R.,�,,..,r..:,.�....,,.....,r APPPiQ51E45
LATF MAv 5, &i)
SOURCE: FORSYTH C�UMTY CdS
NO W62G

VICEROY DRIVE
MW-
IP-7 pDW-19
%s• 2p I -as SIP as LEGEND
IP B
I 11 / APPROXIMATE PROPERTY BOUNDARY
IP- 0 13 IVA2 �^
IP t2 Y 1e MW-1 MONITORING WELL LOCATION
DW-2 DEEP MONITORING WELL LOCATION
♦ IP-1 HRC INJECTION POINT
IP'd 0 IW-1 HRC INJECTION WELL
IP-49*
IP-50
i
MW.7
GRAPHIC SCALE
NOT TO SCALE
ANNAPOLIS DRIVE

65.00 ' 1 00
ANNAPOLIS DRIVE
MATE PROPERTY BOUNDARY
ING WELL LOCATION WITH
NATER ELEVATION
NITORING WELL LOCATION WITH
NATER ELEVATION
WATER CONTOUR LINE 3/31/10
60 30 0 30 60 120
GRAPHIC SCALE

FIGURE 5: HISTORICAL AVERAGE GROUNDWATER ELEVATIONS
Jan-98 Jan-99 Jan-00 Jan-01 Jan-02 Jan-03 Jan-04 Jan-05 Jan-06 Jan-07 Jan-08 Jan-09
Date
76.00
75.00
74.00
73.00
0
c
a
o�
72.00
c m
3
d
0
71.00
70.00
68.00
Jan-10

r
ANNAPOLIS DRIVE
vs
60 30 0 30 60 120
GRAPHIC SCALE
MATE PROPERTY BOUNDARY
ING WELL LOCATION WITH
ILOROETHENE CONCENTRATIONS (ug/L)
NITORING WELL LOCATION WITH
ILOROETHENE CONCENTRATION (ug/L)
4LOROETHENE
:ENTRATION LINE
ETECTION LIMITS

APPENDIX A

Average PCE Concentration vs. Time
1,200
1,000
800
n
600 m
400
200
0
Jan-99 Jan-00 Jan-01 Jan-02 Jan-03 Jan-04 Jan,08 Jan-06 Jan-07 Jan-08 Jan-09 Jan-10
c
7
Time

Jan-98 Jan-99 Jan-00 Jan-01 Jan-02 Jan-03
MW-1
nnr — T:__
Jan-04 Jan-05 Jan-06 Jan-07 Jan-08 Jan-09 Jan-10
Time
700
600
500
v
n
m
400 n
0
c�
m
w
0
300
200
ittill
0

t
Jan-98 Jan-99 Jan-00 Jan-01 Jan-02 Jan-03
DW-2
PCE vs. Time
Jan-04 Jan-05
Time
Jan-06 Jan-07 Jan-08 Jan-09 Jan-10
700
611I11
m
400 n
0
0
0
m
0
v
o'
0
300
Will
100
0

MW-5
PCE vs. Time
Jan-98 Jan-99 Jan-00 Jan-01 Jan-02a Jan-03 Jan-04
Time
Jan-05 Jan-06
Jan-07 Jan-08 Jan-09
700
600
500
v
0
400 n
0
m
0
300
to
P,
200
100
0
Jan-10

Jan-98 Jan-99 Jan-00 Jan-01 Jan-02 Jan-03
MW-6/6R
Jan-04 Jan-05 Jan-06 Jan-07 Jan-08 Jan-09 Jan-10
Time
j( X
M.
611101
(7
m
400 n
0
o�
o'
300
OIN
100

Jan-98 Jan-99
MW-7
PCE vs. Time
Jan-00 Jan-01 Jan-02 Jan-03 Jan-04
Time
700
M
Jan-05 Jan-06 Jan-07 Jan-08 Jan-09 Jan-10
500
n
m
400 n
0
CD
m
m
0
300 c
200
100
0

MW-8
PCE vs. Time
j I ♦ 4--- I-
Jan-98 Jan-99 Jan-00 Jan-01 Jan-02 Jan-03 Jan-04
Time
KIIII
M
500
n
m
400 n
0
M
0
m
M
200
100
0
Jan-05 Jan-06 Jan-07 Jan-08 Jan-09 Jan-10

MW-9
Jan-98 Jan-99 Jan-00 Jan-01 Jan-02 Jan-03 Jan-04 Jan-05
Time
6,000
5,000
4,000
n
m
n
0
m
3,000
2,000
1,000
0
Jan-06 Jan-07 Jan-08 Jan-09 Jan-10
0
3
C

MW-10
PCE vs. Time 700
600
+ 500
v
m
400 n
0
1
300
`e
r
v
200
100
— _ 0
Jan-98 Jan-99 Jan-00 Jan-01 Jan-02 Jan-03 Jan-04 Jan-05 Jan-06 Jan-07 Jan-08 Jan-09 Jan-10
Time

Jan-98 Jan-99
MW-11
Jan-00 Jan-01 Jan-02 Jan-03 Jan-04 Jan-05 Jan-06 Jan-07 Jan-08 Jan-09 Jan-10
Time
600
500
0
m
400 C)
0
m
y
1
0
300
1'1'
100
0

MW-13
nt-r .._ T:__
Jan-98 Jan-99 Jan-00 Jan-01 Jan-02 Jan-03 Jan-04 Jan-05
Time
700
600
500
0
400 n
0
300
200
100
0
Jan-06 Jan-07 Jan-08 Jan-09 Jan-10
0

DW-16
PCE vs. Time
Jan-98 Jan-99 Jan-00 Jan-01 Jan-02 Jan-03 Jan-04 Jan-05
Time
Jan-06 Jan-07 Jan-08 Jan-09 Jan-10
5,000
4,000
3,000
d
2,000
1,000
0
0

DW-19
nor .._ T:__
Jan-98 Jan-99 Jan-00 Jan-01 Jan-02 Jan-03 Jan-04 Jan-05
Time
`j X
500
m
400 n
0
0
0
co
M
m
0
300
200
100
0
Jan-06 Jan-07 Jan-08 Jan-09 Jan-10

r/ ® Pace Analytical Services, Inc. Pace Analytical Services, Inc.
PaceAnalytical 2225 Riverside Dr. 9800 KinceyAve. Suite 100
www.pacelabscorn Asheville, NC 28804 Huntersville, NC 28078
[phone] [phone]
April 28, 2010
Mr. Chris Hay
Kleinfelder, Inc.
313 Gallimore Dairy Rd
Greensboro, NC 27409
RE: Project: Fairchild 26805
Pace Project No.: 9266545
Dear Mr. Hay:
Enclosed are the analytical results for sample(s) received by the laboratory on April 01, 2010. 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,
Bonnie McKee
[e-mail]
Project Manager
Enclosures
REPORT OF LABORATORY ANALYSIS
This report shall not be reproduced, except in full,
withcut the written consent of Pace Analytical Services, Inc..
Page 1 of 34

® Pace Analytical Services, Inc. Pace Analytical Services, Inc.
FaceAnalytical 2225 Riverside Dr. 9800 Kincey Ave. Suite 100
wwwpacelabs corn Asheville, NC 28804 Huntersville, NC 28078
[phone] [phone]
Project: Fairchild 26805
Pace Project No.: 9266545
Charlotte Certification Ms
9800 Kincey Ave. - Ste 100 Huntersville, NC 28078
Connecticut Certification #: PH-0104
Virginia Certification M 00213
Tennessee Certification #: 04010
South Carolina Drinking Water Cert. #: 990060003
South Carolina Certification #: 990060001
Pennsylvania Certification #: 68-00784
North Carolina Wastewater Certification #: 12
CERTIFICATIONS
North Carolina Field Services Certification #: 5342
North Carolina Drinking Water Certification #: 37706
New Jersey Certification M NCO12
Louisiala/LELAP Certification #: 04034
Kentucky UST Certification #: 84
Flodda/NELAP Certification M E87627
West Virginia Certification #: 357
REPORT OF LABORATORY ANALYSIS
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, Inc..
Page 2 of 34

® Pace Analytical Services, Inc. Pace Analytical Services, Inc.
or �accAnalytical 2225 Riverside Dr. 9800 Kincey Ave. Suite 100
wwwpaceiabs tom Asheville, NC 28804 Huntersville, NC 28078
[phone] [phone]
Project:
Fairchild 26805
Pace Project No.:
9266545
Lab ID
Sample ID
9266545001
MW-1
9266545002
MW-5
9266545003
MW-7
9266545004
MW-8
9266545005
DW-2
9266545006
MW-6R
9266545007
MW-9
9266545008
MW-10
9266545009
MW-11
9266545010
MW-13
9266545011
DW-16
9266545012
DW-19
SAMPLE SUMMARY
Matrix
Date Collected
Date Received
Water
03/31/1012:05
04/01/10 15:05
Water
03/31/1013:21
04/01/10 15:05
Water
03/31/1013:36
04/01/10 15:05
Water
03/31/1014:34
04/01/10 15:05
Water
03/31/1011:46
04/01/10 15:05
Water
03/31/1014:04
04/01/10 15:05
Water
03/31/10 09:36
04/01/10 15:05
Water
03/31/10 09:54
04/01/10 15:05
Water
03/31/10 09:16
04/01/10 15:05
Water
03/31/1010:47
04/01/10 15:05
Water
03/31/1010:18
04/01/10 15:05
Water
03/31/1015:50
04/01/10 15:05
REPORT OF LABORATORY ANALYSIS
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, Inc..
Page 3 of 34

Pace Analytical Services, Inc. Pace Analytical Services, Inc.
PaceAnalytical 2225 Riverside Dr. 9800 Kincey Ave. Suite 100
www.pacelebs � Asheville, NC 28804 Huntersville, NC 28078
[phone] [phone]
SAMPLE ANALYTE COUNT
Project: Fairchild 26805
Pace Project No.: 9266545
Lab ID Sample ID
9266545001
MW-1
9266545002
MW-5
9266545003
MW-7
9266545004
MW-8
9266545005
DW-2
9266545006
MW-6R
9266545007
MW-9
9266545008
MW-10
9266545009
MW-11
9266545010
MW-13
9266545011
DW-16
9266545012
DW-19
Method
SM 6200B
SM 6200B
SM 6200B
SM 6200B
SM 6200B
SM 6200B
SM 6200B
SM 6200B
SM 6200B
SM 6200B
SM 6200B
SM 6200B
REPORT OF LABORATORY ANALYSIS
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, Inc..
,x CCOAO
Analysts
BLC
BLC
BLC
BLC
BLC
BLC
AW
BLC
BLC
BLC
BLC
BLC
Analytes
Reported
64
64
64
64
64
64
64
64
64
64
64
64
Page 4 of 34

r® Pace Analytical Services, Inc. Pace Analytical Services, Inc.
�aloAnalytical 2225 Riverside Dr. 9800 KinceyAve. Suite 100
wwwpacelabs c= Asheville, NC 28804 Huntersville, NC 28078
[phone] [phone]
ANALYTICAL RESULTS
Project: Fairchild 26805
Pace Project No.: 9266545
Sample: MW-1
Parameters
Lab ID: 9266545001
Results Units
Collected:
Report
Limit
03/31/10 12:05
MDL DF
Received: 04/01/10 15:05 Matrix: Water
Prepared Analyzed CAS No. Qual
6200E MSV
Analytical Method: SM 6200B
Benzene
ND ug/L
0.50
0.50
1
04/07/10 19:44
71-43-2
Bromobenzene
ND ug/L
0.50
0.50
1
04/07/10 19:44
108-86-1
Bromochloromethane
ND ug/L
0.50
0.50
1
04/07/10 19:44
74-97-5
Bromodichloromethane
ND ug/L
0.50
0.50
1
04/07/10 19:44
75-27-4
Bromoform
ND ug/L
0.50
0.50
1
04/07/10 19:44
75-25-2
Bromomethane
ND ug/L
5.0
1.0
1
04/07/10 19:44
74-83-9
n-Butylbenzene
ND ug/L
0.50
0.50
1
04/07/10 19:44
104-51-8
sec-Butylbenzene
ND ug/L
0.50
0.50
1
04/07/10 19:44
135-98-8
tert-Butylbenzene
ND ug/L
0.50
0.50
1
04/07/10 19:44
98-06-6
Carbon tetrachloride
ND ug/L
0.50
0.50
1
04/07/10 19:44
56-23-5
Chlorobenzene
ND ug/L
0.50
0.50
1
04/07/10 19:44
108-90-7
Chloroethane
ND ug/L
1.0
1.0
1
04/07/10 19:44
75-00-3
Chloroform
ND ug/L
0.50
0.50
1
04/07/10 19:44
67-66-3
Chloromethane
ND ug/L
1.0
1.0
1
04/07/10 19:44
74-87-3
2-Chlorotoluene
ND ug/L
0.50
0.50
1
04/07/10 19:44
95-49-8
4-Chlorotoluene
ND ug/L
0.50
0.50
1
04/07/10 19:44
106-43-4
1,2-Dibromo-3-chloropropane
ND ug/L
1.0
1.0
1
04/07/10 19:44
96-12-8
Dibromochloromethane
ND ug/L
0.50
0.50
1
04/07/10 19:44
124-48-1
1,2-Dibromoethane (EDB)
ND ug/L
0.50
0.50
1
04/07/10 19:44
106-93-4
Dibromomethane
ND ug/L
0.50
0.50
1
04/07/10 19:44
74-95-3
1,2-Dichlorobenzene
ND ug/L
0.50
0.50
1
04/07/10 19:44
95-50-1
1,3-Dichlorobenzene
ND ug/L
0.50
0.50
1
04/07/10 19:44
541-73-1
1,4-Dichlorobenzene
ND ug/L
0.50
0.50
1
04/07/10 19:44
106-46-7
Dichlorodifluoromethane
ND ug/L
0.50
0.50
1
04/07/10 19:44
75-71-8
1,1-Dichloroethane
ND ug/L
0.50
0.50
1
04/07/10 19:44
75-34-3
1,2-Dichloroethane
ND ug/L
0.50
0.50
1
04/07/10 19:44
107-06-2
1,1-Dichloroethene
3.7 ug/L
0.50
0.50
1
04/07/10 19:44
75-35-4
cis- 1,2-Dichloroethene
854 ug/L
10.0
10.0
20
04/09/1022:24
156-59-2
trans-1,2-Dichloroethene
29.0 ug/L
0.50
0.50
1
04/07/10 19:44
156-60-5
1,2-Dichloropropane
ND ug/L
0.50
0.50
1
04/07/10 19:44
78-87-5
1,3-Dichloropropane
ND ug/L
0.50
0.50
1
04/07/10 19:44
142-28-9
2,2-Dichloropropane
ND ug/L
0.50
0.50
1
04/07/10 19:44
594-20-7
1,1-Dichloropropene
ND ug/L
0.50
0.50
1
04/07/10 19:44
563-58-6
cis-1,3-Dichloropropene
ND ug/L
0.50
0.50
1
04/07/10 19:44
10061-01-5
trans- 1,3-Dichloropropene
ND ug/L
0.50
0.50
1
04/07/10 19:44
10061-02-6
Diisopropyl ether
ND ug/L
0.50
0.50
1
04/07/10 19:44
108-20-3
Ethylbenzene
ND ug/L
0.50
0.50
1
04/07/10 19:44
100-41-4
Hexachloro-1,3-butadiene
ND ug/L
2.0
2.0
1
04/07/10 19:44
87-68-3
Isopropylbenzene (Cumene)
ND ug/L
0.50
0.50
1
04/07/10 19:44
98-82-8
Methylene Chloride
ND ug/L
2.0
2.0
1
04/07/10 19:44
75-09-2
Methyl-tert-butyl ether
ND ug/L
0.50
0.50
1
04/07/10 19:44
1634-04-4
Naphthalene
ND ug/L
2.0
2.0
1
04/07/10 19:44
91-20-3
n-Propylbenzene
ND ug/L
0.50
0.50
1
04/07/10 19:44
103-65-1
Styrene
ND ug/L
0.50
0.50
1
04/07/10 19:44
100-42-5
1,1,1,2-Tetrachloroethane
ND ug/L
0.50
0.50
1
04/07/10 19:44
630-20-6
1,1,2,2-Tetrachloroethane
ND ug/L
0.50
0.50
1
04/07/10 19:44
79-34-5
Date: 04/28/2010 02:17 PM REPORT OF LABORATORY ANALYSIS Page 5 of 34
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, Inc..
\`�CC090�C
C,
f
u!�I z

A Pace Analytical Services, Inc. Pace Analytical Services, Inc.
PiceAnalytical 2225 Riverside Dr. 9800 Kincey Ave. Suite 100
www.pecolabs.com Asheville, NC 28804 Huntersville, NC 28078
[phone] [phone]
ANALYTICAL RESULTS
Project: Fairchild 26805
Pace Project No.: 9266545
Sample: MW-1 Lab ID: 9266545001 Collected: 03/31/10 12:05 Received: 04/01/10 15:05 Matrix: Water
Report
Parameters Results Units Limit MDL DF Prepared Analyzed CAS No. Qual
6200B MSV Analytical Method: SM 6200B
Tetrachloroethene
4.9 ug/L
0.50
0.50
1
04/07/10 19:44
127-18-4
Toluene
ND ug/L
0.50
0.50
1
04/07/10 19:44
108-88-3
1,2,3-Thchlorobenzene
ND ug/L
2.0
2.0
1
04/07/10 19:44
87-61-6
1,2,4-Trichlorobenzene
ND ug/L
2.0
2.0
1
04/07/10 19:44
120-82-1
1,1,1-Trichloroethane
ND ug/L
0.50
0.50
1
04/07/10 19:44
71-55-6
1,1,2-Trichloroethane
ND ug/L
0.50
0.50
1
04/07/10 19:44
79-00-5
Trichloroethene
83.6 ug/L
0.50
0.50
1
04/07/10 19:44
79-01-6
Trichlorofluoromethane
ND ug/L
1.0
1.0
1
04/07/10 19:44
75-69-4
1,2,3-Trichioropropane
ND ug/L
0.50
0.50
1
04/07/10 19:44
96-18-4
1,2,4-Trimethylbenzene
ND ug/L
0.50
0.50
1
04/07/10 19:44
95-63-6
1,3,5-Trimethylbenzene
ND ug/L
0.50
0.50
1
04/07/10 19:44
108-67-8
Vinyl chloride
155 ug/L
20.0
20.0
20
04/09/10 22:24
75-01-4
m&p-Xylene
ND ug/L
1.0
1.0
1
04/07/10 19:44
1330-20-7
o-Xylene
ND ug/L
0.50
0.50
1
04/07/10 19:44
95-47-6
1,2-Dichloroethane-d4(S)
102 %
70-130
1
04/07/10 19:44
17060-07-0
Dibromofluoromethane (S)
98 %
70-130
1
04/07/10 19:44
1868-53-7
4-Bromofluorobenzene (S)
99 %
70-130
1
04/07/10 19:44
460-00-4
Toluene -dB (S)
98 %
70-130
1
04/07/10 19:44
2037-26-5
Date: 04/28/2010 02:17 PM
REPORT OF LABORATORY ANALYSIS
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, Inc..
/.CCOgO'
C:
Page 6 of 34

® Pace Analytical Services, Inc. Pace Analytical Services, Inc.
NceAnalyfical 2225 Riverside Dr. 9800 Kincey Ave. Suite 100
NWW.PWWabscom Asheville, NC 28804 Huntersville, NC 28078
[phone] [phone]
ANALYTICAL RESULTS
Project: Fairchild 26805
Pace Project No.: 9266545
Sample: MW-5 Lab ID: 9266545002 Collected: 03/31/10 13:21 Received: 04/01/10 15:05 Matrix: Water
Report
Parameters Results Units Limit MDL DF Prepared Analyzed CAS No. Qual
6200B MSV
Benzene
Bromobenzene
Bromochloromethane
Bromodich loromethane
Bromoform
Bromomethane
n-Butylbenzene
sec-Butylbenzene
tert-Butyl benzene
Carbon tetrachloride
Chlorobenzene
Chloroethane
Chloroform
Chloromethane
2-Chlorotoluene
4-Chlorotoluene
1,2-Dibromo-3-chloropropane
D i bromoch lorom eth an e
1,2-Dibromoethane (EDB)
Dibromomethane
1,2-Dichlorobenzene
1,3-Dichlorobenzene
1,4-Dichlorobenzene
Dich lorodifluoromethane
1,1-Dichloroethane
1,2-Dichloroethane
1,1-Dichloroethene
cis-1,2-Dichloroethene
trans-1,2-Dichloroethene
1,2-Dichloropropane
1,3-Dichloropropane
2,2-Dichloropropane
1,1-Dichloropropene
cis-1,3-Dichloropropene
trans- 1,3-Dichloropropene
Diisopropyi ether
Ethylbenzene
Hexachloro-1,3-butadiene
Isopropylbenzene (Cumene)
Methylene Chloride
Methyl-tert-butyl ether
Naphthalene
n-Propylbenzene
Styrene
1,1,1,2-Tetrachloroethane
1,1,2,2-Tetrachloroethane
Date: 04/28/2010 02:17 PM
Analytical Method: SM 6200B
ND ug/L
0.50
0.50
1
04/09/10 21:39
71-43-2
ND ug/L
0.50
0.50
1
04/09/10 21:39
108-86-1
ND ug/L
0.50
0.50
1
04/09/10 21:39
74-97-5
ND ug/L
0.50
0.50
1
04/09/10 21:39
75-27-4
ND ug/L
0.50
0.50
1
04/09/10 21:39
75-25-2
ND ug/L
5.0
1.0
1
04/09/10 21:39
74-83-9
ND ug/L
0.50
0.50
1
04/09/10 21:39
104-51-8
ND ug/L
0.50
0.50
1
04/09/10 21:39
135-98-8
ND ug/L
0.50
0.50
1
04/09/10 21:39
98-06-6
ND ug/L
0.50
0.50
1
04/09/10 21:39
56-23-5
ND ug/L
0.50
0.50
1
04/09/10 21:39
108-90-7
ND ug/L
1.0
1.0
1
04/09/10 21:39
75-00-3
ND ug/L
0.50
0.50
1
04/09/10 21:39
67-66-3
ND ug/L
1.0
1.0
1
04/09/10 21:39
74-87-3
ND ug/L
0.50
0.50
1
04/09/10 21:39
95-49-8
ND ug/L
0.50
0.50
1
04/09/10 21:39
106-43-4
ND ug/L
1.0
1.0
1
04/09/10 21:39
96-12-8
ND ug/L
0.50
0.50
1
04/09/10 21:39
124-48-1
ND ug/L
0.50
0.50
1
04/09/10 21:39
106-93-4
ND ug/L
0.50
0.50
1
04/09/10 21:39
74-95-3
ND ug/L
0.50
0.50
1
04/09/10 21:39
95-50-1
ND ug/L
0.50
0.50
1
04/09/10 21:39
541-73-1
ND ug/L
0.50
0.50
1
04/09/10 21:39
106-46-7
ND ug/L
0.50
0.50
1
04/09/10 21:39
75-71-8
ND ug/L
0.50
0.50
1
04/09/10 21:39
75-34-3
ND ug/L
0.50
0.50
1
04/09/10 21:39
107-06-2
ND ug/L
0.50
0.50
1
04/09/10 21:39
75-35-4
3.3 ug/L
0.50
0.50
1
04/09/10 21:39
156-59-2
ND ug/L
0.50
0.50
1
04/09/10 21:39
156-60-5
ND ug/L
0.50
0.50
1
04/09/10 21:39
78-87-5
ND ug/L
0.50
0.50
1
04/09/10 21:39
142-28-9
ND ug/L
0.50
0.50
1
04/09/10 21:39
594-20-7
ND ug/L
0.50
0.50
1
04/09/10 21:39
563-58-6
ND ug/L
0.50
0.50
1
04/09/10 21:39
10061-01-5
ND ug/L
0.50
0.50
1
04/09/10 21:39
10061-02-6
ND ug/L
0.50
0.50
1
04/09/10 21:39
108-20-3
ND ug/L
0.50
0.50
1
04/09/10 21:39
100-41-4
ND ug/L
2.0
2.0
1
04/09/10 21:39
87-68-3
ND ug/L
0.50
0.50
1
04/09/10 21:39
98-82-8
ND ug/L
2.0
2.0
1
04/09/10 21:39
75-09-2
ND ug/L
0.50
0.50
1
04/09/10 21:39
1634-04-4
ND ug/L
2.0
2.0
1
04/09/10 21:39
91-20-3
ND ug/L
0.50
0.50
1
04/09/10 21:39
103-65-1
ND ug/L
0.50
0.50
1
04/09/10 21:39
100-42-5
ND ug/L
0.50
0.50
1
04/09/10 21:39
630-20-6
ND ug/L
0.50
0.50
1
04/09/10 21:39
79-34-5
REPORT OF LABORATORY ANALYSIS Page 7 of 34
This report shall not be reproduced, except in full,
without the written conse�`ntt �of PaceoerAnalytical Services, Inc..

® Pace Analytical Services, Inc. Pace Analytical Services, Inc.
�aceAnalytical 2225 Riverside Dr. 9800 Kincey Ave. Suite 100
www.pwWabacom Asheville, NC 28804 Huntersville, NC 28078
[phone] [phone]
ANALYTICAL RESULTS
Project: Fairchild 26805
Pace Project No.: 9266545
Sample: MW-5 Lab ID: 9266545002 Collected: 03/31/10 13:21 Received: 04/01/10 15:05 Matrix: Water
Report
Parameters Results Units Limit MDL DF Prepared Analyzed CAS No. Qual
6200E MSV Analytical Method: SM 6200B
Tetrachloroethene
1.1 ug/L
0.50
0.50
1
04/09/10 21:39
127-18-4
Toluene
ND ug/L
0.50
0.50
1
04/09/10 21:39
108-88-3
1,2,3-Trichlorobenzene
ND ug/L
2.0
2.0
1
04/09/10 21:39
87-61-6
1,2,4-Trichlorobenzene
ND ug/L
2.0
2.0
1
04/09/10 21:39
120-82-1
1,1,1-Trichloroethane
ND ug/L
0.50
0.50
1
04/09/10 21:39
71-55-6
1,1,2-Trichloroethane
ND ug/L
0.50
0.50
1
04/09/10 21:39
79-00-5
Trichloroethene
0.78 ug/L
0.50
0.50
1
04/09/10 21:39
79-01-6
Trichlorofluoromethane
ND ug/L
1.0
1.0
1
04/09/10 21:39
75-69-4
1,2,3-Trichloropropane
ND ug/L
0.50
0.50
1
04/09/10 21:39
96-18-4
1,2,4-Tri methyl benzene
ND ug/L
0.50
0.50
1
04/09/10 21:39
95-63-6
1,3,5-Tri methyl benzene
ND ug/L
0.50
0.50
1
04/09/10 21:39
108-67-8
Vinyl chloride
ND ug/L
1.0
1.0
1
04/09/10 21:39
75-01-4
m&p-Xylene
ND ug/L
1.0
1.0
1
04/09/10 21:39
1330-20-7
o-Xylene
ND ug/L
0.50
0.50
1
04/09/10 21:39
95-47-6
1,2-Dichloroethane-d4 (S)
99 %
70-130
1
04/09/10 21:39
17060-07-0
Dibromofluoromethane (S)
97 %
70-130
1
04/09/10 21:39
1868-53-7
4-Bromofluorobenzene (S)
104 %
70-130
1
04/09/10 21:39
460-00-4
Toluene-d8 (S)
99 %
70-130
1
04/09/10 21:39
2037-26-5
Date: 04/28/2010 02:17 PM
REPORT OF LABORATORY ANALYSIS
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, Inc..
,M .CCOAO�
Page 8 of 34

Pace Analytical Services, Inc. Pace Analytical Services, Inc.
PaceAnalytical 2225 Riverside Dr. 9800 Kincey Ave. Suite 100
www.pacelabs.com Asheville, NC 28804 Huntersville, NC 28078
[phone]
[phone]
ANALYTICAL RESULTS
Project: Fairchild 26805
Pace Project No.: 9266545
Sample: MW-7 Lab ID: 9266545003 Collected: 03/31/10 13:36 Received: 04/01/10 15:05 Matrix: Water
Report
Parameters Results Units Limit MDL DF Prepared Analyzed CAS No. Qual
6200B MSV Analytical Method: SM 6200B
Benzene
ND ug/L
0.50
0.50
1
04/07/10 20:28
71-43-2
Bromobenzene
ND ug/L
0.50
0.50
1
04/07/10 20:28
108-86-1
Bromochloromethane
ND ug/L
0.50
0.50
1
04/07/10 20:28
74-97-5
Bromodichloromethane
ND ug/L
0.50
0.50
1
04/07/10 20:28
75-27-4
Bromoform
ND ug/L
0.50
0.50
1
04/07/10 20:28
75-25-2
Bromomethane
ND ug/L
5.0
1.0
1
04/07/10 20:28
74-83-9
n-Butylbenzene
ND ug/L
0.50
0.50
1
04/07/10 20:28
104-51-8
sec-Butylbenzene
ND ug/L
0.50
0.50
1
04/07/10 20:28
135-98-8
tert-Butyl benzene
ND ug/L
0.50
0.50
1
04/07/10 20:28
98-06-6
Carbon tetrachloride
ND ug/L
0.50
0.50
1
04/07/10 20:28
56-23-5
Chlorobenzene
ND ug/L
0.50
0.50
1
04/07/10 20:28
108-90-7
Chloroethane
ND ug/L
1.0
1.0
1
04/07/10 20:28
75-00-3
Chloroform
ND ug/L
0.50
0.50
1
04/07/10 20:28
67-66-3
Chloromethane
ND ug/L
1.0
1.0
1
04/07/10 20:28
74-87-3
2-Chlorotoluene
ND ug/L
0.50
0.50
1
04/07/10 20:28
95-49-8
4-Chlorotoluene
ND ug/L
0.50
0.50
1
04/07/10 20:28
106-43-4
1,2-Dibromo-3-chloropropane
ND ug/L
1.0
1.0
1
04/07/10 20:28
96-12-8
Dibromochloromethane
ND ug/L
0.50
0.50
1
04/07/10 20:28
124-48-1
1,2-Dibromoethane (EDB)
ND ug/L
0.50
0.50
1
04/07/10 20:28
106-93-4
Dibromomethane
ND ug/L
0.50
0.50
1
04/07/10 20:28
74-95-3
1,2-Dichlorobenzene
ND ug/L
0.50
0.50
1
04/07/10 20:28
95-50-1
1,3-Dichlorobenzene
ND ug/L
0.50
0.50
1
04/07/10 20:28
541-73-1
1,4-Dichlorobenzene
ND ug/L
0.50
0.50
1
04/07/10 20:28
106-46-7
Dichlorodifluoromethane
ND ug/L
0.50
0.50
1
04/07/10 20:28
75-71-8
1,1-Dichloroethane
ND ug/L
0.50
0.50
1
04/07/10 20:28
75-34-3
1,2-Dichloroethane
ND ug/L
0.50
0.50
1
04/07/10 20:28
107-06-2
1,1-Dichloroethene
ND ug/L
0.50
0.50
1
04/07/10 20:28
75-35-4
cis-1,2-Dichloroethene
6.8 ug/L
0.50
0.50
1
04/07/10 20:28
156-59-2
trans- 1,2-Dichloroethene
ND ug/L
0.50
0.50
1
04/07/10 20:28
156-60-5
1,2-Dichloropropane
ND ug/L
0.50
0.50
1
04/07/10 20:28
78-87-5
1,3-Dichloropropane
ND ug/L
0.50
0.50
1
04/07/10 20:28
142-28-9
2,2-Dichloropropane
ND ug/L
0.50
0.50
1
04/07/10 20:28
594-20-7
1,1-Dichloropropene
ND ug/L
0.50
0.50
1
04/07/10 20:28
563-58-6
cis-1,3-Dichloropropene
ND ug/L
0.50
0.50
1
04/07/10 20:28
10061-01-5
trans-1,3-Dichloropropene
ND ug/L
0.50
0.50
1
04/07/10 20:28
10061-02-6
Diisopropyi ether
ND ug/L
0.50
0.50
1
04/07/10 20:28
108-20-3
Ethylbenzene
ND ug/L
0.50
0.50
1
04/07/10 20:28
100-41-4
Hexachloro-1,3-butadiene
ND ug/L
2.0
2.0
1
04/07/10 20:28
87-68-3
Isopropylbenzene (Cumene)
ND ug/L
0.50
0.50
1
04/07/10 20:28
98-82-8
Methylene Chloride
ND ug/L
2.0
2.0
1
04/07/10 20:28
75-09-2
Methyl-tert-butyl ether
ND ug/L
0.50
0.50
1
04/07/10 20:28
1634-04-4
Naphthalene
ND ug/L
2.0
2.0
1
04/07/10 20:28
91-20-3
n-Propylbenzene
ND ug/L
0.50
0.50
1
04/07/10 20:28
103-65-1
Styrene
ND ug/L
0.50
0.50
1
04/07/10 20:28
100-42-5
1,1,1,2-Tetrachloroethane
ND ug/L
0.50
0.50
1
04/07/10 20:28
630-20-6
1,1,2,2-Tetrachloroethane
ND ug/L
0.50
0.50
1
04/07/10 20:28
79-34-5
Date: 04/28/2010 02:17 PM REPORT OF LABORATORY ANALYSIS Page 9 of 34
This report shall not be reproduced, except in full,
without '.he written consent of Pace Analytical Services, Inc..

® Pace Analytical Services, Inc. Pace Analytical Services, Inc.
1)7�accAnalytical 2225 Riverside Dr. 9800 Kincey Ave. Suite 100
www.pacelabs can Asheville, NC 28804 Huntersville, NC 28078
[phone] [phone]
ANALYTICAL RESULTS
Project: Fairchild 26805
Pace Project No.: 9266545
Sample: MW-7 Lab ID: 9266545003 Collected: 03/31/10 13:36 Received: 04/01/10 15:05 Matrix: Water
Report
Parameters Results Units Limit MDL DF Prepared Analyzed CAS No. Qua]
6200B MSV Analytical Method: SM 6200B
Tetrachloroethene
1.2 ug/L
0.50
0.50
1
04/07/10 20:28
127-18-4
Toluene
ND ug/L
0.50
0.50
1
04/07/10 20:28
108-88-3
1,2,3-Trichlorobenzene
ND ug/L
2.0
2.0
1
04/07/10 20:28
87-61-6
1,2,4-Trichlorobenzene
ND ug/L
2.0
2.0
1
04/07/10 20:28
120-82-1
1,1,1-Trichloroethane
ND ug/L
0.50
0.50
1
04/07/10 20:28
71-55-6
1,1,2-Trichloroethane
ND ug/L
0.50
0.50
1
04/07/10 20:28
79-00-5
Trichloroethene
0.92 ug/L
0.50
0.50
1
04/07/10 20:28
79-01-6
Trichlorofluoromethane
ND ug/L
1.0
1.0
1
04/07/10 20:28
75-69-4
1,2,3-Tdchloropropane
ND ug/L
0.50
0.50
1
04/07/10 20:28
96-18-4
1,2,4-Trimethylbenzene
ND ug/L
0.50
0.50
1
04/07/10 20:28
95-63-6
1,3,5-Trimethylbenzene
ND ug/L
0.50
0.50
1
04/07/10 20:28
108-67-8
Vinyl chloride
ND ug/L
1.0
1.0
1
04/07/10 20:28
75-01-4
m&p-Xylene
ND ug/L
1.0
1.0
1
04/07/10 20:28
1330-20-7
o-Xylene
ND ug/L
0.50
0.50
1
04/07/10 20:28
95-47-6
1,2-Dichloroethane-d4 (S)
103 %
70-130
1
04/07/10 20:28
17060-07-0
Dibromofluoromethane (S)
100 %
70-130
1
04/07/10 20:28
1868-53-7
4-Bromofluorobenzene(S)
99 %
70-130
1
04/07/10 20:28
460-00-4
Toluene-d8(S)
98 %
70-130
1
04/07/10 20:28
2037-26-5
Date: 04/28/2010 02:17 PM REPORT OF LABORATORY ANALYSIS Page 10 of 34
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, Inc..
"h(kc,_

Pace Analytical Services, Inc. Pace Analytical Services, Inc.
PaeeAnalytical 2225 Riverside Dr. 9800 Kincey Ave. Suite 100
www.pacelabs.com Asheville, NC 28804 Huntersville, NC 28078
.[phone] [phone]
ANALYTICAL RESULTS
Project: Fairchild 26805
Pace Project No.: 9266545
Sample: MW-8 Lab ID: 9266545004 Collected: 03/31/10 14:34 Received: 04/01/10 15:05 Matrix: Water
Report
Parameters Results Units Limit MDL DF Prepared Analyzed CAS No. Qual
6200B MSV Analytical MethDd: SM 6200B
Benzene
ND ug/L
0.50
0.50
1
04/07/10 20:51
71-43-2
Bromobenzene
ND ug/L
0.50
0.50
1
04/07/10 20:51
108-86-1
Bromochloromethane
ND ug/L
0.50
0.50
1
04/07/10 20:51
74-97-5
Bromodichloromethane
ND ug/L
0.50
0.50
1
04/07/10 20:51
75-27-4
Bromoform
ND ug/L
0.50
0.50
1
04/07/10 20:51
75-25-2
Bromomethane
ND ug/L
5.0
1.0
1
04/07/10 20:51
74-83-9
n-Butylbenzene
ND ug/L
0.50
0.50
1
04/07/10 20:51
104-51-8
sec-Butylbenzene
ND ug/L
0.50
0.50
1
04/07/10 20:51
135-98-8
tert-Butylbenzene
ND ug/L
0.50
0.50
1
04/07/10 20:51
98-06-6
Carbon tetrachloride
ND ug/L
0.50
0.50
1
04/07/10 20:51
56-23-5
Chlorobenzene
ND ug/L
0.50
0.50
1
04/07/10 20:51
108-90-7
Chloroethane
ND ug/L
1.0
1.0
1
04/07/10 20:51
75-00-3
Chloroform
ND ug/L
0.50
0.50
1
04/07/10 20:51
67-66-3
Chloromethane
ND ug/L
1.0
1.0
1
04/07/10 20:51
74-87-3
2-Chlorotoluene
ND ug/L
0.50
0.50
1
04/07/10 20:51
95-49-8
4-Chlorotoluene
ND ug/L
0.50
0.50
1
04/07/10 20:51
106-43-4
1,2-Dibromo-3-chloropropane
ND ug/L
1.0
1.0
1
04/07/10 20:51
96-12-8
Dibromochloromethane
ND ug/L
0.50
0.50
1
04/07/10 20:51
124-48-1
1,2-Dibromoethane (EDB)
ND ug/L
0.50
0.50
1
04/07/10 20:51
106-93-4
Dibromomethane
ND ug/L
0.50
0.50
1
04/07/10 20:51
74-95-3
1,2-Dichlorobenzene
ND ug/L
0.50
0.50
1
04/07/10 20:51
95-50-1
1,3-Dichlorobenzene
ND ug/L
0.50
0.50
1
04/07/10 20:51
541-73-1
1,4-Dichlorobenzene
ND ug/L
0.50
0.50
1
04/07/10 20:51
106-46-7
Dichlorodifluoromethane
ND ug/L
0.50
0.50
1
04/07/10 20:51
75-71-8
1,1-Dichloroethane
ND ug/L
0.50
0.50
1
04/07/10 20:51
75-34-3
1,2-Dichloroethane
ND ug/L
0.50
0.50
1
04/07/10 20:51
107-06-2
1,1-Dichloroethene
ND ug/L
0.50
0.50
1
04/07/10 20:51
75-35-4
cis-1,2-Dichloroethene
2.0 ug/L
0.50
0.50
1
04/07/10 20:51
156-59-2
trans-1,2-Dichloroethene
ND ug/L
0.50
0.50
1
04/07/10 20:51
156-60-5
1,2-Dichloropropane
ND ug/L
0.50
0.50
1
04/07/10 20:51
78-87-5
1,3-Dichloropropane
ND ug/L
0.50
0.50
1
04/07/10 20:51
142-28-9
2,2-Dichloropropane
ND ug/L
0.50
0.50
1
04/07/10 20:51
594-20-7
1,1-Dichloropropene
ND ug/L
0.50
0.50
1
04/07/10 20:51
563-58-6
cis- 1,3-Dichloropropene
ND ug/L
0.50
0.50
1
04/07/10 20:51
10061-01-5
trans- 1,3-Dichloropropene
ND ug/L
0.50
0.50
1
04/07/10 20:51
10061-02-6
Diisopropyl ether
ND ug/L
0.50
0.50
1
04/07/10 20:51
108-20-3
Ethylbenzene
ND ug/L
0.50
0.50
1
04/07/10 20:51
100-41-4
Hexachloro-1,3-butadiene
ND ug/L
2.0
2.0
1
04/07/10 20:51
87-68-3
Isopropylbenzene (Cumene)
ND ug/L
0.50
0.50
1
04/07/10 20:51
98-82-8
Methylene Chloride
ND ug/L
2.0
2.0
1
04/07/10 20:51
75-09-2
Methyl4ert-butyl ether
ND ug/L
0.50
0.50
1
04/07/10 20:51
1634-04-4
Naphthalene
ND ug/L
2.0
2.0
1
04/07/10 20:51
91-20-3
n-Propylbenzene
ND ug/L
0.50
0.50
1
04/07/10 20:51
103-65-1
Styrene
ND ug/L
0.50
0.50
1
04/07/10 20:51
100-42-5
1,1,1,2-Tetrachloroethane
ND ug/L
0.50
0.50
1
04/07/10 20:51
630-20-6
1,1,2,2-Tetrachloroethane
ND ug/L
0.50
0.50
1
04/07/10 20:51
79-34-5
Date: 04/28/2010 02:17 PM REPORT OF LABORATORY ANALYSIS Page 11 of 34
This report shall not be reproduced, except in full,
withL•ut .he written consent of Pace Analytical Services, Inc..

y ® Pace Analytical Services, Inc. Pace Analytical Services, Inc.
��G`�a'i '�' 2225 Riverside Dr. 9800 Kincey Ave. Suite 100
w,N,N,�e� com Asheville, NC 28804 Huntersville, NC 28078
[phone] [phone]
ANALYTICAL RESULTS
Project: Fairchild 26805
Pace Project No.: 9266545
Sample: MW-8
Lab ID: 9266545004
Collected:
03/31/10 14:34
Received: 04/01/10 15:05 Matrix: Water
Report
Parameters
Results Units
Limit
MDL
DF
Prepared Analyzed
CAS No. Qual
6200E MSV
Analytical Method: SM 6200B
Tetrachloroethene
1.2 ug/L
0.50
0.50
1
04/07/10 20:51
127-18-4
Toluene
ND ug/L
0.50
0.50
1
04/07/10 20:51
108-88-3
1,2,3-Trichlorobenzene
ND ug/L
2.0
2.0
1
04/07/10 20:51
87-61-6
1,2,4-Trichlorobenzene
ND ug/L
2.0
2.0
1
04/07/10 20:51
120-82-1
1,1,1-Trichloroethane
ND ug/L
0.50
0.50
1
04/07/10 20:51
71-55-6
1,1,2-Trichloroethane
ND ug/L
0.50
0.50
1
04/07/10 20:51
79-00-5
Trichloroethene
0.59 ug/L
0.50
0.50
1
04/07/10 20:51
79-01-6
Trichlorofluoromethane
ND ug/L
1.0
1.0
1
04/07/10 20:51
75-69-4
1,2,3-Trichloropropane
ND ug/L
0.50
0.50
1
04/07/10 20:51
96-18-4
1,2,4-Trimethylbenzene
ND ug/L
0.50
0.50
1
04/07/10 20:51
95-63-6
1,3,5-Trimethylbenzene
ND ug/L
0.50
0.50
1
04/07/10 20:51
108-67-8
Vinyl chloride
ND ug/L
1.0
1.0
1
04/07/10 20:51
75-01-4
m&p-Xylene
ND ug/L
1.0
1.0
1
04/07/10 20:51
1330-20-7
o-Xylene
ND ug/L
0.50
0.50
1
04/07/10 20:51
95-47-6
1,2-Dichloroethane-d4 (S)
102 %
70-130
1
04/07/10 20:51
17060-07-0
Dibromofluoromethane (S)
101 %
70-130
1
04/07/10 20:51
1868-53-7
4-Bromofluorobenzene(S)
98 %
70-130
1
04/07/10 20:51
460-00-4
Toluene-d8 (S)
99 %
70-130
1
04/07/10 20:51
2037-26-5
Date: 04/28/2010 02:17 PM
REPORT OF LABORATORY ANALYSIS
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, Inc..
Page 12 of 34

�� Pace Analytical Services, Inc. Pace Analytical Services, Inc.
yaceAnalytical 2225 Riverside Dr. 9800 Kincey Ave. Suite 100
wxw.pacelabs.com
Asheville, NC 28804 Huntersville, NC 28078
[phone]
ANALYTICAL RESULTS
Project: Fairchild 26805
Pace Project No.: 9266545
Sample: DW-2 Lab ID: 9266545005 Collected: 03/31/10 11:46 Received: 04/01/10 15:05 Matrix: Water
[phone]
Report
Parameters Results Units Limit MDL DF Prepared Analyzed CAS No. Qual
6200E MSV Analytical Method: SM 6200B
Benzene
ND ug/L
0.50
0.50
1
04/07/10 21:13
71-43-2
Bromobenzene
ND ug/L
0.50
0.50
1
04/07/10 21:13
108-86-1
Bromochloromethane
ND ug/L
0.50
0.50
1
04/07/10 21:13
74-97-5
Bromodichloromethane
ND ug/L
0.50
0.50
1
04/07/10 21:13
75-27-4
Bromoform
ND ug/L
0.50
0.50
1
04/07/10 21:13
75-25-2
Bromomethane
ND ug/L
5.0
1.0
1
04/07/10 21:13
74-83-9
n-Butylbenzene
ND ug/L
0.50
0.50
1
04/07/10 21:13
104-51-8
sec-Butylbenzene
ND ug/L
0.50
0.50
1
04/07/10 21:13
135-98-8
tert-Butyl benzene
ND ug/L
0.50
0.50
1
04/07/10 21:13
98-06-6
Carbon tetrachloride
ND ug/L
0.50
0.50
1
04/07/10 21:13
56-23-5
Chlorobenzene
ND ug/L
0.50
0.50
1
04/07/10 21:13
108-90-7
Chloroethane
ND ug/L
1.0
1.0
1
04/07/10 21:13
75-00-3
Chloroform
ND ug/L
0.50
0.50
1
04/07/10 21:13
67-66-3
Chloromethane
ND ug/L
1.0
1.0
1
04/07/10 21:13
74-87-3
2-Chlorotoluene
ND ug/L
0.50
0.50
1
04/07/10 21:13
95-49-8
4-Chlorotoluene
ND ug/L
0.50
0.50
1
04/07/10 21:13
106-43-4
1,2-Dibromo-3-chloropropane
ND ug/L
1.0
1.0
1
04/07/10 21:13
96-12-8
Dibromochloromethane
ND ug/L
0.50
0.50
1
04/07/10 21:13
124-48-1
1,2-Dibromoethane (EDB)
ND ug/L
0.50
0.50
1
04/07/10 21:13
106-93-4
Dibromomethane
ND ug/L
0.50
0.50
1
04/07/10 21:13
74-95-3
1,2-Dichlorobenzene
ND ug/L
0.50
0.50
1
04/07/10 21:13
95-50-1
1,3-Dichlorobenzene
ND ug/L
0.50
0.50
1
04/07/10 21:13
541-73-1
1,4-Dichlorobenzene
ND ug/L
0.50
0.50
1
04/07/10 21:13
106-46-7
Dichlorodifluoromethane
ND ug/L
0.50
0.50
1
04/07/10 21:13
75-71-8
1,1-Dichloroethane
ND ug/L
0.50
0.50
1
04/07/10 21:13
75-34-3
1,2-Dichloroethane
ND ug/L
0.50
0.50
1
04/07/10 21:13
107-06-2
1,1-Dichloroethene
ND ug/L
0.50
0.50
1
04/07/10 21:13
75-35-4
cis-1,2-Dichloroethene
5.5 ug/L
0.50
0.50
1
04/07/10 21:13
156-59-2
trans-1,2-Dichloroethene
ND ug/L
0.50
0.50
1
04/07/10 21:13
156-60-5
1,2-Dichloropropane
ND ug/L
0.50
0.50
1
04/07/10 21:13
78-87-5
1,3-Dichloropropane
ND ug/L
0.50
0.50
1
04/07/10 21:13
142-28-9
2,2-Dichloropropane
ND ug/L
0.50
0.50
1
04/07/10 21:13
594-20-7
1,1-Dichloropropene
ND ug/L
0.50
0.50
1
04/07/10 21:13
563-58-6
cis-1,3-Dichloropropene
ND ug/L
0.50
0.50
1
04/07/10 21:13
10061-01-5
trans- 1,3-Dichloropropene
ND ug/L
0.50
0.50
1
04/07/10 21:13
10061-02-6
Diisopropyl ether
ND ug/L
0.50
0.50
1
04/07/10 21:13
108-20-3
Ethylbenzene
ND ug/L
0.50
0.50
1
04/07/10 21:13
100-41-4
Hexachloro-1,3-butadiene
ND ug/L
2.0
2.0
1
04/07/10 21:13
87-68-3
Isopropylbenzene (Cumene)
ND ug/L
0.50
0.50
1
04/07/10 21:13
98-82-8
Methylene Chloride
ND ug/L
2.0
2.0
1
04/07/10 21:13
75-09-2
Methyl-tert-butyl ether
ND ug/L
0.50
0.50
1
04/07/10 21:13
1634-04-4
Naphthalene
ND ug/L
2.0
2.0
1
04/07/10 21:13
91-20-3
n-Propylbenzene
ND ug/L
0.50
0.50
1
04/07/10 21:13
103-65-1
Styrene
ND ug/L
0.50
0.50
1
04/07/10 21:13
100-42-5
1,1,1,2-Tetrachloroethane
ND ug/L
0.50
0.50
1
04/07/10 21:13
630-20-6
1,1,2,2-Tetrachloroethane
ND ug/L
0.50
0.50
1
04/07/10 21:13
79-34-5
Date: 04/28/2010 02:17 PM REPORT OF LABORATORY ANALYSIS Page 13 of 34
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, Inc..
,M •CCOAO'
u ``t/ z

® Pace Analytical Services, Inc. Pace Analytical Services, Inc.
PaceAnal yfl 'aI 2225 Riverside Dr. 9800 Kincey Ave. Suite 100
wwwpeoelabswn Asheville, NC 28804 Huntersville, NC 28078
[phone] [phone]
ANALYTICAL RESULTS
Project: Fairchild 26805
Pace Project No.: 9266545
Sample: DW-2 Lab ID: 9266545005 Collected: 03/31/10 11:46 Received: 04/01/10 15:05 Matrix: Water
Report
Parameters Results Units Limit MDL DF Prepared Analyzed CAS No. Qual
6200B MSV Analytical Method: SM 6200B
Tetrachloroethene
5.2 ug/L
0.50
0.50
1
04/07/10 21:13
127-18-4
Toluene
ND ug/L
0.50
0.50
1
04/07/10 21:13
108-88-3
1,2,3-Trichlorobenzene
ND ug/L
2.0
2.0
1
04/07/10 21:13
87-61-6
1,2,4-Trichlorobenzene
ND ug/L
2.0
2.0
1
04/07/10 21:13
120-82-1
1,1,1-Trichloroethane
ND ug/L
0.50
0.50
1
04/07/10 21:13
71-55-6
1,1,2-Trichloroethane
ND ug/L
0.50
0.50
1
04/07/10 21:13
79-00-5
Trichloroethene
2.6 ug/L
0.50
0.50
1
04/07/10 21:13
79-01-6
Trichlorofluoromethane
ND ug/L
1.0
1.0
1
04/07/10 21:13
75-69-4
1,2,3-Trichloropropane
ND ug/L
0.50
0.50
1
04/07/10 21:13
96-18-4
1,2,4-Trimethylbenzene
ND ug/L
0.50
0.50
1
04/07/10 21:13
95-63-6
1,3,5-Trimethylbenzene
ND ug/L
0.50
0.50
1
04/07/10 21:13
108-67-8
Vinyl chloride
ND ug/L
1.0
1.0
1
04/07/10 21:13
75-01-4
m&p-Xylene
ND ug/L
1.0
1.0
1
04/07/10 21:13
1330-20-7
o-Xylene
ND ug/L
0.50
0.50
1
04/07/10 21:13
95-47-6
1,2-Dichloroethane-d4 (S)
103 %
70-130
1
04/07/10 21:13
17060-07-0
Dibromofluoromethane (S)
101 %
70-130
1
04/07/10 21:13
1868-53-7
4-Bromofluorobenzene(S)
97 %
70-130
1
04/07/10 21:13
460-00-4
Toluene-d8 (S)
98 %
70-130
1
04/07/10 21:13
2037-26-5
Date: 04/28/2010 02:17 PM
REPORT OF LABORATORY ANALYSIS
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, Inc..
,. •_\•_\oa�r`
:iJ_IL�CLS.�;
Page 14 of 34

® Pace Analytical Services, Inc. Pace Analytical Services, Inc.
, acaAnalytical 2225 Riverside Dr. 9800 Kincey Ave. Suite 100
www.pacelabs.com Asheville, NC 28804 Huntersville, NC 28078
[phone]
ANALYTICAL RESULTS
Project: Fairchild 26805
Pace Project No.: 9266545
Sample: MW-6R Lab ID: 9266545006 Collected: 03/31/10 14:04 Received: 04/01/10 15:05 Matrix: Water
[phone]
Report
Parameters Results Units Limit MDL DF Prepared Analyzed CAS No. Qual
6200B MSV Analytical Method: SM 6200B
Benzene
ND ug/L
0.50
0.50
1
04/07/10 21:35
71-43-2
Bromobenzene
ND ug/L
0.50
0.50
1
04/07/10 21:35
108-86-1
Bromochloromethane
ND ug/L
0.50
0.50
1
04/07/10 21:35
74-97-5
Bromodichloromethane
ND ug/L
0.50
0.50
1
04/07/10 21:35
75-27-4
Bromoform
ND ug/L
0.50
0.50
1
04/07/10 21:35
75-25-2
Bromomethane
ND ug/L
5.0
1.0
1
04/07/10 21:35
74-83-9
n-Butylbenzene
ND ug/L
0.50
0.50
1
04/07/10 21:35
104-51-8
sec-Butylbenzene
ND ug/L
0.50
0.50
1
04/07/10 21:35
135-98-8
tert-Butyibenzene
ND ug/L
0.50
0.50
1
04/07/10 21:35
98-06-6
Carbon tetrachloride
ND ug/L
0.50
0.50
1
04/07/10 21:35
56-23-5
Chlorobenzene
ND ug/L
0.50
0.50
1
04/07/10 21:35
108-90-7
Chloroethane
ND ug/L
1.0
1.0
1
04/07/10 21:35
75-00-3
Chloroform
ND ug/L
0.50
0.50
1
04/07/10 21:35
67-66-3
Chloromethane
ND ug/L
1.0
1.0
1
04/07/10 21:35
74-87-3
2-Chlorotoluene
ND ug/L
0.50
0.50
1
04/07/10 21:35
95-49-8
4-Chlorotoluene
ND ug/L
0.50
0.50
1
04/07/10 21:35
106-43-4
1,2-Dibromo-3-chloropropane
ND ug/L
1.0
1.0
1
04/07/10 21:35
96-12-8
Dibromochloromethane
ND ug/L
0.50
0.50
1
04/07/10 21:35
124-48-1
1,2-Dibromoethane (EDB)
ND ug/L
0.50
0.50
1
04/07/10 21:35
106-93-4
Dibromomethane
ND ug/L
0.50
0.50
1
04/07/10 21:35
74-95-3
1,2-Dichlorobenzene
ND ug/L
0.50
0.50
1
04/07/10 21:35
95-50-1
1,3-Dichlorobenzene
ND ug/L
0.50
0.50
1
04/07/10 21:35
541-73-1
1,4-Dichlorobenzene
ND ug/L
0.50
0.50
1
04/07/10 21:35
106-46-7
Dichlorodifluoromethane
ND ug/L
0.50
0.50
1
04/07/10 21:35
75-71-8
1,1-Dichloroethane
ND ug/L
0.50
0.50
1
04/07/10 21:35
75-34-3
1,2-Dichloroethane
ND ug/L
0.50
0.50
1
04/07/10 21:35
107-06-2
1,1-Dichloroethene
ND ug/L
0.50
0.50
1
04/07/10 21:35
75-35-4
cis-1,2-Dichloroethene
6.9 ug/L
0.50
0.50
1
04/07/10 21:35
156-59-2
trans-1,2-Dichloroethene
ND ug/L
0.50
0.50
1
04/07/10 21:35
156-60-5
1,2-Dichloropropane
ND ug/L
0.50
0.50
1
04/07/10 21:35
78-87-5
1,3-Dichloropropane
ND ug/L
0.50
0.50
1
04/07/10 21:35
142-28-9
2,2-Dichloropropane
ND ug/L
0.50
0.50
1
04/07/10 21:35
594-20-7
1,1-Dichloropropene
ND ug/L
0.50
0.50
1
04/07/10 21:35
563-58-6
cis-1,3-Dichloropropene
ND ug/L
0.50
0.50
1
04/07/10 21:35
10061-01-5
Vans-1,3-Dichloropropene
ND ug/L
0.50
0.50
1
04/07/10 21:35
10061-02-6
Diisopropyl ether
ND ug/L
0.50
0.50
1
04/07/10 21:35
108-20-3
Ethylbenzene
ND ug/L
0.50
0.50
1
04/07/10 21:35
100-41-4
Hexachloro-1,3-butadiene
ND ug/L
2.0
2.0
1
04/07/10 21:35
87-68-3
Isopropylbenzene (Cumene)
ND ug/L
0.50
0.50
1
04/07/10 21:35
98-82-8
Methylene Chloride
ND ug/L
2.0
2.0
1
04/07/10 21:35
75-09-2
Methyl-tert-butyl ether
ND ug/L
0.50
0.50
1
04/07/10 21:35
1634-04-4
Naphthalene
ND ug/L
2.0
2.0
1
04/07/10 21:35
91-20-3
n-Propylbenzene
ND ug/L
0.50
0.50
1
04/07/10 21:35
103-65-1
Styrene
ND ug/L
0.50
0.50
1
04/07/10 21:35
100-42-5
1,1,1,2-Tetrachloroethane
ND ug/L
0.50
0.50
1
04/07/10 21:35
630-20-6
1,1,2,2-Tetrachloroethane
ND ug/L
0.50
0.50
1
04/07/10 21:35
79-34-5
Date: 04/28/2010 02:17 PM REPORT OF LABORATORY ANALYSIS Page 15 of 34
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, Inc..
h Je

0❑ /�, / �+'/ ® Pace Analytical Services, Inc. Pace Analytical Services, Inc.
1 aG'e/`'l/ lal)/l'ica 2225 Riverside Dr. 9800 Kincey Ave. Suite 100
� pJ e`er corn Asheville, NC 28804 Huntersville, NC 28078
[phone] [phone]
ANALYTICAL RESULTS
Project: Fairchild 26805
Pace Project No.: 9266545
Sample: MW-6R
Lab ID: 9266545006
Collected:
03/31/10 14:04
Received: 04/01/10 15:05 Matrix: Water
Report
Parameters
Results Units
Limit
MDL
DF
Prepared Analyzed
CAS No. Qual
6200B MSV
Analytical Method: SM 6200B
Tetrachloroethene
19.1 ug/L
0.50
0.50
1
04/07/10 21:35
127-18-4
Toluene
ND ug/L
0.50
0.50
1
04/07/10 21:35
108-88-3
1,2,3-Trichlorobenzene
ND ug/L
2.0
2.0
1
04/07/10 21:35
87-61-6
1,2,4-Tdchlorobenzene
ND ug/L
2.0
2.0
1
04/07/10 21:35
120-82-1
1,1,1-Tdchloroethane
ND ug/L
0.50
0.50
1
04/07/10 21:35
71-55-6
1,1,2-Tdchloroethane
ND ug/L
0.50
0.50
1
04/07/10 21:35
79-00-5
Trichloroethene
9.8 ug/L
0.50
0.50
1
04/07/10 21:35
79-01-6
Trichlorofluoromethane
ND ug/L
1.0
1.0
1
04/07/10 21:35
75-69-4
1,2,3-Trichloropropane
ND ug/L
0.50
0.50
1
04/07/10 21:35
96-18-4
1,2,4-Tri meth ylbenzene
ND ug/L
0.50
0.50
1
04/07/10 21:35
95-63-6
1,3,5-Trimethyl benzene
ND ug/L
0.50
0.50
1
04/07/10 21:35
108-67-8
Vinyl chloride
ND ug/L
1.0
1.0
1
04/07/10 21:35
75-01-4
m&p-Xylene
ND ug/L
1.0
1.0
1
04/07/10 21:35
1330-20-7
o-Xylene
ND ug/L
0.50
0.50
1
04/07/10 21:35
95-47-6
1,2-Dichloroethane-d4(S)
102 %
70-130
1
04/07/10 21:35
17060-07-0
Dibromofluoromethane (S)
99 %
70-130
1
04/07/10 21:35
1868-53-7
4-Bromofluorobenzene(S)
97 %
70-130
1
04/07/10 21:35
460-00-4
Toluene-d8(S)
98 %
70-130
1
04/07/10 21:35
2037-26-5
Date: 04/28/2010 02:17 PM
REPORT OF LABORATORY ANALYSIS
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, Inc..
Page 16 of 34

7 a/+� ® Pace Analytical Services, Inc. Pace Analytical Services, Inc.
eAnal ical 2225 Riverside Dr. 9800 Kincey Ave. Suite 100
www.pacelabs.com
Asheville, NC 28804 Huntersville, NC 28078
[phone] [phone]
ANALYTICAL RESULTS
Project: Fairchild 26805
Pace Project No.: 9266545
Sample: MW-9 Lab ID: 9266545007 Collected: 03/31/10 09:36 Received: 04/01/10 15:05 Matrix: Water
Report
Parameters Results Units Limit MDL DF Prepared Analyzed CAS No. Qual
6200E MSV Analytical Method: SM 6200B
Benzene
ND ug/L
5.0
5.0
10
04/12/10 20:25
71-43-2
Bromobenzene
ND ug/L
5.0
5.0
10
04/12/10 20:25
108-86-1
Bromochloromethane
ND ug/L
5.0
5.0
10
04/12/10 20:25
74-97-5
Bromodichloromethane
ND ug/L
5.0
5.0
10
04/12/10 20:25
75-27-4
Bromoform
ND ug/L
5.0
5.0
10
04/12/10 20:25
75-25-2
Bromomethane
ND ug/L
50.0
10.0
10
04/12/10 20:25
74-83-9
n-Butylbenzene
ND ug/L
5.0
5.0
10
04/12/10 20:25
104-51-8
sec-Butylbenzene
ND ug/L
5.0
5.0
10
04/12/10 20:25
135-98-8
tert-Butylbenzene
ND ug/L
5.0
5.0
10
04/12/10 20:25
98-06-6
Carbon tetrachloride
ND ug/L
5.0
5.0
10
04/12/10 20:25
56-23-5
Chlorobenzene
ND ug/L
5.0
5.0
10
04/12/10 20:25
108-90-7
Chloroethane
ND ug/L
10.0
10.0
10
04/12/10 20:25
75-00-3
Chloroform
ND ug/L
5.0
5.0
10
04/12/10 20:25
67-66-3
Chloromethane
ND ug/L
10.0
10.0
10
04/12/10 20:25
74-87-3
2-Chlorotoluene
ND ug/L
5.0
5.0
10
04/12/10 20:25
95-49-8
4-Chlorotoluene
ND ug/L
5.0
5.0
10
04/12/10 20:25
106-43-4
1,2-Dibromo-3-chloropropane
ND ug/L
10.0
10.0
10
04/12/10 20:25
96-12-8
Dibromochloromethane
ND ug/L
5.0
5.0.
10
04/12/10 20:25
124-48-1
1,2-Dibromoethane (EDB)
ND ug/L
5.0
5.0
10
04/12/10 20:25
106-93-4
Dibromomethane
ND ug/L
5.0
5.0
10
04/12/10 20:25
74-95-3
1,2-Dichlorobenzene
ND ug/L
5.0
5.0
10
04/12/10 20:25
95-50-1
1,3-Dichlorobenzene
ND ug/L
5.0
5.0
10
04/12/10 20:25
541-73-1
1,4-Dichlorobenzene
ND ug/L
5.0
5.0
10
04/12/10 20:25
106-46-7
Dichlorodifluoromethane
ND ug/L
5.0
5.0
10
04/12/10 20:25
75-71-8
1,1-Dichloroethane
ND ug/L
5.0
5.0
10
04/12/10 20:25
75-34-3
1,2-Dichloroethane
ND ug/L
5.0
5.0
10
04/12/10 20:25
107-06-2
1,1-Dichloroethene
ND ug/L
5.0
5.0
10
04/12/10 20:25
75-35-4
cis- 1,2-Dichloroethene
404 ug/L
5.0
5.0
10
04/12/10 20:25
156-59-2
trans- 1,2-Dichloroethene
18.5 ug/L
5.0
5.0
10
04/12/10 20:25
156-60-5
1,2-Dichloropropane
ND ug/L
5.0
5.0
10
04/12/10 20:25
78-87-5
1,3-Dichloropropane
ND ug/L
5.0
5.0
10
04/12/10 20:25
142-28-9
2,2-Dichloropropane
ND ug/L
5.0
5.0
10
04/12/10 20:25
594-20-7
1,1-Dichloropropene
ND ug/L
5.0
5.0
10
04/12/10 20:25
563-58-6
cis- 1,3-Dic hloropropene
ND ug/L
5.0
5.0
10
04/12/10 20:25
10061-01-5
trans- 1,3-Dichloropropene
ND ug/L
5.0
5.0
10
04/12/10 20:25
10061-02-6
Diisopropyl ether
ND ug/L
5.0
5.0
10
04/12/10 20:25
108-20-3
Ethlbenzene
ND ug/L
5.0
5.0
10
04/12/10 20:25
100-41-4
Hexachloro-1,3-butadiene
ND ug/L
20.0
20.0
10
04/12/10 20:25
87-68-3
Isopropylbenzene (Cumene)
ND ug/L
5.0
5.0
10
04/12/10 20:25
98-82-8
Methylene Chloride
ND ug/L
20.0
20.0
10
04/12/10 20:25
75-09-2
Methyl-tert-butyl ether
ND ug/L
5.0
5.0
10
04/12/10 20:25
1634-04-4
Naphthalene
ND ug/L
20.0
20.0
10
04/12/10 20:25
91-20-3
n-Propylbenzene
ND ug/L
5.0
5.0
10
04/12/10 20:25
103-65-1
Styrene
ND ug/L
5.0
5.0
10
04/12/10 20:25
100-42-5
1,1,1,2-Tetrachloroethane
ND ug/L
5.0
5.0
10
04/12/10 20:25
630-20-6
1,1,2,2-Tetrachloroethane
ND ug/L
5.0
5.0
10
04/12/10 20:25
79-34-5
Date: 04/28/2010 02:17 PM REPORT OF LABORATORY ANALYSIS Page 17 of 34
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, Inc..
�n •CCp,pe'
i'�z

Pace Analytical Services, Inc. Pace Analytical Services, Inc.
all!/pA a//ca/®
2225 Riverside Dr. 9800 Kincey Ave. Suite 100
wwwp"abscorn Asheville, NC 28804 Huntersville, NC 28078
[phone] [phone]
ANALYTICAL RESULTS
Project: Fairchild 26805
Pace Project No.: 9266545
Sample: MW-9 Lab ID: 9266545007 Collected: 03/31/10 09:36 Received: 04/01/10 15:05 Matrix: Water
Report
Parameters Results Units Limit MDL DF Prepared Analyzed CAS No. Qual
6200B MSV Analytical Method: SM 6200B
Tetrachloroethene
73.0 ug/L
5.0
5.0
10
04/12/10 20:25
127-18-4
Toluene
ND ug/L
5.0
5.0
10
04/12/10 20:25
108-88-3
1,2,3-Trichlorobenzene
ND ug/L
20.0
20.0
10
04/12/10 20:25
87-61-6
1,2,4-Trichlorobenzene
ND ug/L
20.0
20.0
10
04/12/10 20:25
120-82-1
1,1,1-Trichloroethane
ND ug/L
5.0
5.0
10
04/12/10 20:25
71-55-6
1,1,2-Trichloroethane
ND ug/L
5.0
5.0
10
04/12/10 20:25
79-00-5
Trichloroethene
160 ug/L
5.0
5.0
10
04/12/10 20:25
79-01-6
Trichlorofluoromethane
ND ug/L
10.0
10.0
10
04/12/10 20:25
75-69-4
1,2,3-Tdchloropropane
ND ug/L
5.0
5.0
10
04/12/10 20:25
96-18-4
1,2,4-Trimethylbenzene
ND ug/L
5.0
5.0
10
04/12/10 20:25
95-63-6
1,3,5-Trimethylbenzene
ND ug/L
5.0
5.0
10
04/12/10 20:25
108-67-8
Vinyl chloride
828 ug/L
10.0
10.0
10
04/12/10 20:25
75-01-4
m&p-Xylene
ND ug/L
10.0
10.0
10
04/12/10 20:25
1330-20-7
o-Xylene
ND ug/L
5.0
5.0
10
04/12/10 20:25
95-47-6
1,2-Dichloroethane-d4 (S)
89 %
70-130
10
04/12/10 20:25
17060-07-0
Dibromofluoromethane (S)
89 %
70-130
10
04/12/10 20:25
1868-53-7
4-Bromofluorobenzene (S)
116 %
70-130
10
04/12/10 20:25
460-00-4
Toluene-d8 (S)
96 %
70-130
10
04/12/10 20:25
2037-26-5
Date: 04/28/2010 02:17 PM REPORT OF LABORATORY ANALYSIS Page 18 of 34
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, Inc..
A
rt C's

® Pace Analytical Services, Inc. Pace Analytical Services, Inc.
PaceAnalytical 2225 Riverside Dr. 9800 Kincey Ave. Suite 100
www.pecolabs.com Asheville, NC 28804 Huntersville, NC 28078
[phone] [phone]
Project: Fairchild 26805
Pace Project No.: 9266545
Sample: MW-10
Parameters
6200B MSV
Benzene
Bromobenzene
Bromochloromethane
Bromodichloromethane
Bromoform
Bromomethane
n-Butylbenzene
sec -Butyl benzene
tert-Butylbenzene
Carbon tetrachloride
Chlorobenzene
Chloroethane
Chloroform
Chloromethane
2-Chlorotoluene
4-Chlorotoluene
1,2-Dibromo-3-chloropropane
Dibromochloromethane
1,2-Dibromoethane (EDB)
Dibromomethane
1,2-Dichlorobenzene
1,3-Dichlorobenzene
1,4-Dichlorobenzene
Dichlorodifluoromethane
1, 1 -Dichloroethane
1,2-Dichloroethane
1,1-Dichloroethene
cis- 1,2-Dichloroethene
trans- 1,2-Dichloroethene
1,2-Dichloropropane
1, 3-Dichloropropane
2,2-Dichloropropane
1,1-Dichloropropene
cis-1, 3-Dichloropropene
trans-1, 3-Dichloropropene
Diisopropyl ether
Ethylbenzene
Hexachloro-1,3-butadiene
Isopropylbenzene (Cumene)
Methylene Chloride
Methyl-tert-butyl ether
Naphthalene
n-Propylbenzene
Styrene
1,1,1,2-Tetrachloroethane
1,1,2,2-Tetrachloroethane
Date: 04/28/2010 02:17 PM
ANALYTICAL RESULTS
Lab ID: 9266545008 Collected: 03/31/10 09:54
Report
Results Units Limit MDL DF
Analytical Method: SM 6200B
Received: 04/01/10 15:05 Matrix: Water
Prepared Analyzed CAS No. Qual
ND ug/L
0.50
0.50
1
04/07/10 22:20
71-43-2
ND ug/L
0.50
0.50
1
04/07/10 22:20
108-86-1
ND ug/L
0.50
0.50
1
04/07/10 22:20
74-97-5
ND ug/L
0.50
0.50
1
04/07/10 22:20
75-27-4
ND ug/L
0.50
0.50
1
04/07/10 22:20
75-25-2
ND ug/L
5.0
1.0
1
04/07/10 22:20
74-83-9
ND ug/L
0.50
0.50
1
04/07/10 22:20
104-51-8
ND ug/L
0.50
0.50
1
04/07/10 22:20
135-98-8
ND ug/L
0.50
0.50
1
04/07/10 22:20
98-06-6
ND ug/L
0.50
0.50
1
04/07/10 22:20
56-23-5
ND ug/L
0.50
0.50
1
04/07/10 22:20
108-90-7
ND ug/L
1.0
1.0
1
04/07/10 22:20
75-00-3
ND ug/L
0.50
0.50
1
04/07/10 22:20
67-66-3
ND ug/L
1.0
1.0
1
04/07/10 22:20
74-87-3
ND ug/L
0.50
0.50
1
04/07/10 22:20
95-49-8
ND ug/L
0.50
0.50
1
04/07/10 22:20
106-43-4
ND ug/L
1.0
1.0
1
04/07/10 22:20
96-12-8
ND ug/L
0.50
0.50
1
04/07/10 22:20
124-48-1
ND ug/L
0.50
0.50
1
04/07/10 22:20
106-93-4
ND ug/L
0.50
0.50
1
04/07/10 22:20
74-95-3
ND ug/L
0.50
0.50
1
04/07/10 22:20
95-50-1
ND ug/L
0.50
0.50
1
04/07/10 22:20
541-73-1
ND ug/L
0.50
0.50
1
04/07/10 22:20
106-46-7
ND ug/L
0.50
0.50
1
04/07/10 22:20
75-71-8
ND ug/L
0.50
0.50
1
04/07/10 22:20
75-34-3
ND ug/L
0.50
0.50
1
04/07/10 22:20
107-06-2
ND ug/L
0.50
0.50
1
04/07/10 22:20
75-35-4
106 ug/L
0.50
0.50
1
04/07/10 22:20
156-59-2
2.4 ug/L
0.50
0.50
1
04/07/10 22:20
156-60-5
ND ug/L
0.50
0.50
1
04/07/10 22:20
78-87-5
ND ug/L
0.50
0.50
1
04/07/10 22:20
142-28-9
ND ug/L
0.50
0.50
1
04/07/10 22:20
594-20-7
ND ug/L
0.50
0.50
1
04/07/10 22:20
563-58-6
ND ug/L
0.50
0.50
1
04/07/10 22:20
10061-01-5
ND ug/L
0.50
0.50
1
04/07/10 22:20
10061-02-6
ND ug/L
0.50
0.50
1
04/07/10 22:20
108-20-3
ND ug/L
0.50
0.50
1
04/07/10 22:20
100-41-4
ND ug/L
2.0
2.0
1
04/07/10 22:20
87-68-3
ND ug/L
0.50
0.50
1
04/07/10 22:20
98-82-8
ND ug/L
2.0
2.0
1
04/07/10 22:20
75-09-2
ND ug/L
0.50
0.50
1
04/07/10 22:20
1634-04-4
ND ug/L
2.0
2.0
1
04/07/10 22:20
91-20-3
ND ug/L
0.50
0.50
1
04/07/10 22:20
103-65-1
ND ug/L
0.50
0.50
1
04/07/10 22:20
100-42-5
ND ug/L
0.50
0.50
1
04/07/10 22:20
630-20-6
ND ug/L
0.50
0.50
1
04/07/10 22:20
79-34-5
REPORT OF LABORATORY ANALYSIS Page 19 of 34
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, Inc..
ble '

f Pace Analytical Services, Inc. Pace Analytical Services, Inc.
PaceA alyti al 2225 Riverside Dr. 9800 Kincey Ave. Suite 100
www.pacglabs.com Asheville, NC 28804 Huntersville, NC 28078
[phone] [phone]
ANALYTICAL RESULTS
Project: Fairchild 26805
Pace Project No.: 9266545
Sample: MW-10
Lab ID: 9266545008
Collected:
03/31/10 09:54
Received: 04/01/10 15:05 Matrix: Water
Report
Parameters
Results Units
Limit
MDL
DF
Prepared Analyzed
CAS No. Qual
6200E MSV
Analytical Method: SM 6200B
Tetrachloroethene
9.5 ug/L
0.50
0.50
1
04/07/10 22:20
127-18-4
Toluene
0.61 ug/L
0.50
0.50
1
04/07/10 22:20
108-88-3
1,2,3-Trichlorobenzene
ND ug/L
2.0
2.0
1
04/07/10 22:20
87-61-6
1,2,4-Trichlorobenzene
ND ug/L
2.0
2.0
1
04/07/10 22:20
120-82-1
1,1,1-Trichloroethane
ND ug/L
0.50
0.50
1
04/07/10 22:20
71-55-6
1,1,2-Trichloroethane
ND ug/L
0.50
0.50
1
04/07/10 22:20
79-00-5
Trichloroethene
14.0 ug/L
0.50
0.50
1
04/07/10 22:20
79-01-6
Trichlorofluoromethane
ND ug/L
1.0
1.0
1
04/07/10 22:20
75-69-4
1,2,3-Trichloropropane
ND ug/L
0.50
0.50
1
04/07/10 22:20
96-18-4
1,2,4-Trimethylbenzene
ND ug/L
0.50
0.50
1
04/07/10 22:20
95-63-6
1,3,5-Trimethylbenzene
ND ug/L
0.50
0.50
1
04/07/10 22:20
108-67-8
Vinyl chloride
82.8 ug/L
1.0
1.0
1
04/07/10 22:20
75-01-4
m&p-Xylene
ND ug/L
1.0
1.0
1
04/07/10 22:20
1330-20-7
o-Xylene
ND ug/L
0.50
0.50
1
04/07/10 22:20
95-47-6
1,2-Dichloroethane-d4 (S)
102 %
70-130
1
04/07/10 22:20
17060-07-0
Dibromofluoromethane (S)
100 %
70-130
1
04/07/10 22:20
1868-53-7
4-Bromofluorobenzene(S)
97 %
70-130
1
04/07/10 22:20
460-00-4
Toluene -dB (S)
99 %
70-130
1
04/07/10 22:20
2037-26-5
Date: 04/28/2010 02:17 PM
REPORT OF LABORATORY ANALYSIS
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, Inc..
i o`.t�V�Ybll z
Page 20 of 34

Pace Analytical Services, Inc. Pace Analytical Services, Inc.
-± a eAnal"tkal ' 2225 Riverside Dr. 9800 Kincey Ave. Suite 100
w, wwpelabs.com Asheville, NC 28804 Huntersville, NC 28078
[phone] [phone]
ANALYTICAL RESULTS
Project: Fairchild 26805
Pace Project No.: 9266545
Sample: MW-11 Lab ID: 9265545009 Collected: 03/31/10 09:16 Received: 04/01/10 15:05 Matrix: Water
Report
Parameters Results Units Limit MDL DF Prepared Analyzed CAS No. Qual
6200E MSV
Benzene
Bromobenzene
Bromochloromethane
Bromod ich loromethane
Bromoform
Bromomethane
n-Butylbenzene
sec-Butylbenzene
tert-Butyl benzene
Carbon tetrachloride
Chlorobenzene
Chloroethane
Chloroform
Chloromethane
2-Chlorotoluene
4-Chlorotoluene
1,2-Dibromo-3-chloropropane
Dibromochlorometha ne
1,2-Dibromoethane (EDB)
Dibromomethane
1,2-Dichlorobenzene
1,3-Dichlorobenzene
1,4-Dichlorobenzene
Dichlorodifluoromethane
1,1-Dichloroethane
1,2-Dichloroethane
1,1-Dichloroethene
cis-1,2-Dichloroethene
Vans-1,2-Dichloroethene
1,2-Dichloropropane
1,3-Dichloropropane
2,2-Dichloropropane
1,1-Dichloropropene
cis-1,3-Dichloropropene
trans-1, 3-Dichloropropene
Diisopropyl ether
Ethylbenzene
Hexachloro-1,3-butadiene
Isopropylbenzene (Cumene)
Methylene Chloride
Methyl-tert-butyl ether
Naphthalene
n-Propylbenzene
Styrene
1,1,1,2-Tetrachloroethane
1,1,2,2-Tetrachloroethane
Date: 04/28/2010 02:17 PM
Analytical Method: SM 6200B
ND ug/L
0.50
0.50
1
04/07/10 22:42
71-43-2
ND ug/L
0.50
0.50
1
04/07/10 22:42
108-86-1
ND ug/L
0.50
0.50
1
04/07/10 22:42
74-97-5
ND ug/L
0.50
0.50
1
04/07/10 22:42
75-27-4
ND ug/L
0.50
0.50
1
04/07/10 22:42
75-25-2
ND ug/L
5.0
1.0
1
04/07/10 22:42
74-83-9
ND ug/L
0.50
0.50
1
04/07/10 22:42
104-51-8
ND ug/L
0.50
0.50
1
04/07/10 22:42
135-98-8
ND ug/L
0.50
0.50
1
04/07/10 22:42
98-06-6
ND ug/L
0.50
0.50
1
04/07/10 22:42
56-23-5
ND ug/L
0.50
0.50
1
04/07/10 22:42
108-90-7
ND ug/L
1.0
1.0
1
04/07/10 22:42
75-00-3
ND ug/L
0.50
0.50
1
04/07/10 22:42
67-66-3
ND ug/L
1.0
1.0
1
04/07/10 22:42
74-87-3
ND ug/L
0.50
0.50
1
04/07/10 22:42
95-49-8
ND ug/L
0.50
0.50
1
04/07/10 22:42
106-43-4
ND ug/L
1.0
1.0
1
04/07/10 22:42
96-12-8
ND ug/L
0.50
0.50
1
04/07/10 22:42
124-48-1
ND ug/L
0.50
0.50
1
04/07/10 22:42
106-93-4
ND ug/L
0.50
0.50
1
04/07/10 22:42
74-95-3
ND ug/L
0.50
0.50
1
04/07/10 22:42
95-50-1
ND ug/L
0.50
0.50
1
04/07/10 22:42
541-73-1
ND ug/L
0.50
0.50
1
04/07/10 22:42
106-46-7
ND ug/L
0.50
0.50
1
04/07/10 22:42
75-71-8
ND ug/L
0.50
0.50
1
04/07/10 22:42
75-34-3
ND ug/L
0.50
0.50
1
04/07/10 22:42
107-06-2
ND ug/L
0.50
0.50
1
04/07/10 22:42
75-35-4
43.7 ug/L
0.50
0.50
1
04/07/10 22:42
156-59-2
2.6 ug/L
0.50
0.50
1
04/07/10 22:42
156-60-5
ND ug/L
0.50
0.50
1
04/07/10 22:42
78-87-5
ND ug/L
0.50
0.50
1
04/07/10 22:42
142-28-9
ND ug/L
0.50
0.50
1
04/07/10 22:42
594-20-7
ND ug/L
0.50
0.50
1
04/07/10 22:42
563-58-6
ND ug/L
0.50
0.50
1
04/07/10 22:42
10061-01-5
ND ug/L
0.50
0.50
1
04/07/10 22:42
10061-02-6
ND ug/L
0.50
0.50
1
04/07/10 22:42
108-20-3
ND ug/L
0.50
0.50
1
04/07/10 22:42
100-41-4
ND ug/L
2.0
2.0
1
04/07/10 22:42
87-68-3
ND ug/L
0.50
0.50
1
04/07/10 22:42
98-82-8
ND ug/L
2.0
2.0
1
04/07/10 22:42
75-09-2
ND ug/L
0.50
0.50
1
04/07/10 22:42
1634-04-4
ND ug/L
2.0
2.0
1
04/07/10 22:42
91-20-3
ND ug/L
0.50
0.50
1
04/07/10 22:42
103-65-1
ND ug/L
0.50
0.50
1
04/07/10 22:42
100-42-5
ND ug/L
0.50
0.50
1
04/07/10 22:42
630-20-6
ND ug/L
0.50
0.50
1
04/07/10 22:42
79-34-5
REPORT OF LABORATORY ANALYSIS Page 21 of 34
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, Inc..
,M I.cCcgo.
, /i `~'z

r
� Pace Analytical Services, Inc. Pace Analytical Services, Inc.
PaceAnalytical ® 2225 Riverside Dr. 9800 KinceyAve. Suite 100
www.pacelabs.com Asheville, NC 28804 Huntersville, NC 28078
[phone] [phone]
ANALYTICAL RESULTS
Project: Fairchild 26805
Pace Project No.: 9266545
Sample: MW-11
Lab ID: 9266545009
Collected:
03/31/10 09:16
Received: 04/01/10 15:05 Matrix: Water
Report
Parameters
Results Units
Limit
MDL
DF
Prepared Analyzed
CAS No. Qual
6200E MSV
Analytical Method: SM 6200B
Tetrachloroethene
7.7 ug/L
0.50
0.50
1
04/07/10 22:42
127-18-4
Toluene
ND ug/L
0.50
0.50
1
04/07/10 22:42
108-88-3
1,2,3-Trichlorobenzene
ND ug/L
2.0
2.0
1
04/07/10 22:42
87-61-6
1,2,4-Trichlorobenzene
ND ug/L
2.0
2.0
1
04/07/10 22:42
120-82-1
1,1,1-Trich►oroethane
ND ug/L
0.50
0.50
1
04/07/10 22:42
71-55-6
1,1,2-Trichloroethane
ND ug/L
0.50
0.50
1
04/07/10 22:42
79-00-5
Trichloroethene
4.6 ug/L
0.50
0.50
1
04/07/10 22:42
79-01-6
Trichlorofluoromethane
ND ug/L
1.0
1.0
1
04/07/10 22:42
75-69-4
1,2,3-Tdchloropropane
ND ug/L
0.50
0.50
1
04/07/10 22:42
96-18-4
1,2,4-Trimethylbenzene
ND ug/L
0.50
0.50
1
04/07/10 22:42
95-63-6
1,3,5-Trimethylbenzene
ND ug/L
0.50
0.50
1
04/07/10 22:42
108-67-8
Vinyl chloride
89.9 ug/L
1.0
1.0
1
04/07/10 22:42
75-01-4
m&p-Xylene
ND ug/L
1.0
1.0
1
04/07/10 22:42
1330-20-7
o-Xylene
ND ug/L
0.50
0.50
1
04/07/10 22:42
95-47-6
1,2-Dichloroethane-d4(S)
102 %
70-130
1
04/07/10 22:42
17060-07-0
Dibromofluoromethane (S)
99 %
70-130
1
04/07/10 22:42
1868-53-7
4-Bromofluorobenzene(S)
98 %
70-130
1
04/07/10 22:42
460-00-4
Toluene-d8(S)
98 %
70-130
1
04/07/10 22:42
2037-26-5
Date: 04/28/2010 02:17 PM
REPORT OF LABORATORY ANALYSIS
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, Inc..
Page 22 of 34

® Pace Analytical Services, Inc. Pace Analytical Services, Inc.
�alceAnalytical 2225 Riverside Dr. 9800 Kincey Ave. Suite 100
www.pacelabs.com Asheville, NC 28804 Huntersville, NC 28078
[phone] [phone]
Project: Fairchild 26805
Pace Project No.: 9266545
Sample: MW-13
Parameters
6200B MSV
Benzene
Bromobenzene
Bromochloromethane
Bromodichloromethane
Bromoform
Bromomethane
n-Butylbenzene
sec -Butyl benzene
tert-Butylbenzene
Carbon tetrachloride
Chlorobenzene
Chloroethane
Chloroform
Chloromethane
2-Chlorotoluene
4-Chlorotoluene
1,2-Dibromo-3-chloropropane
Dibromochloromethane
1,2-Dibromoethane (EDB)
Dibromomethane
1,2-Dichlorobenzene
1, 3-Dichlorobenzene
1,4-Dichlorobenzene
Dich lorod ifluorometha ne
1,1-Dichloroethane
1,2-Dichloroethane
1,1-Dichloroethene
cis-1,2-Dichloroethene
trans-1,2-Dichloroethene
1,2-Dichloropropane
1,3-Dichloropropane
2,2-Dichloropropane
1,1-Dichloropropene
cis-1,3-Dichloropropene
trans-1, 3-Dichloropropene
Diisopropyl ether
Ethylbenzene
Hexachloro-1,3-butadiene
Isopropylbenzene (Cumene)
Methylene Chloride
Methyl-tert-butyl ether
Naphthalene
n-Propylbenzene
Styrene
1,1,1,2-Tetrachloroethane
1,1,2,2-Tetrachloroethane
Date: 04/28/2010 02:17 PM
ANALYTICAL RESULTS
Lab ID: 9266545010 Collected: 03/31/10 10:47
Report
Results Units Limit MDL DF
Analytical Method: SM 6200B
Received: 04/01/10 15:05 Matrix: Water
Prepared Analyzed CAS No. Qual
ND ug/L
0.50
0.50
1
04/07/10 23:05
71-43-2
ND ug/L
0.50
0.50
1
04/07/10 23:05
108-86-1
ND ug/L
0.50
0.50
1
04/07/10 23:05
74-97-5
ND ug/L
0.50
0.50
1
04/07/10 23:05
75-27-4
ND ug/L
0.50
0.50
1
04/07/10 23:05
75-25-2
ND ug/L
5.0
1.0
1
04/07/10 23:05
74-83-9
ND ug/L
0.50
0.50
1
04/07/10 23:05
104-51-8
ND ug/L
0.50
0.50
1
04/07/10 23:05
135-98-8
ND ug/L
0.50
0.50
1
04/07/10 23:05
98-06-6
ND ug/L
0.50
0.50
1
04/07/10 23:05
56-23-5
ND ug/L
0.50
0.50
1
04/07/10 23:05
108-90-7
ND ug/L
1.0
1.0
1
04/07/10 23:05
75-00-3
ND ug/L
0.50
0.50
1
04/07/10 23:05
67-66-3
ND ug/L
1.0
1.0
1
04/07/10 23:05
74-87-3
ND ug/L
0.50
0.50
1
04/07/10 23:05
95-49-8
ND ug/L
0.50
0.50
1
04/07/10 23:05
106-43-4
ND ug/L
1.0
1.0
1
04/07/10 23:05
96-12-8
ND ug/L
0.50
0.50
1
04/07/10 23:05
124-48-1
ND ug/L
0.50
0.50
1
04/07/10 23:05
106-93-4
ND ug/L
0.50
0.50
1
04/07/10 23:05
74-95-3
ND ug/L
0.50
0.50
1
04/07/10 23:05
95-50-1
ND ug/L
0.50
0.50
1
04/07/10 23:05
541-73-1
ND ug/L
0.50
0.50
1
04/07/10 23:05
106-46-7
ND ug/L
0.50
0.50
1
04/07/10 23:05
75-71-8
ND ug/L
0.50
0.50
1
04/07/10 23:05
75-34-3
ND ug/L
0.50
0.50
1
04/07/10 23:05
107-06-2
ND ug/L
0.50
0.50
1
04/07/10 23:05
75-35-4
86.7 ug/L
0.50
0.50
1
04/07/10 23:05
156-59-2
9.0 ug/L
0.50
0.50
1
04/07/10 23:05
156-60-5
ND ug/L
0.50
0.50
1
04/07/10 23:05
78-87-5
ND ug/L
0.50
0.50
1
04/07/10 23:05
142-28-9
ND ug/L
0.50
0.50
1
04/07/10 23:05
594-20-7
ND ug/L
0.50
0.50
1
04/07/10 23:05
563-58-6
ND ug/L
0.50
0.50
1
04/07/10 23:05
10061-01-5
ND ug/L
0.50
0.50
1
04/07/10 23:05
10061-02-6
ND ug/L
0.50
0.50
1
04/07/10 23:05
108-20-3
ND ug/L
0.50
0.50
1
04/07/10 23:05
100-41-4
ND ug/L
2.0
2.0
1
04/07/10 23:05
87-68-3
ND ug/L
0.50
0.50
1
04/07/10 23:05
98-82-8
ND ug/L
2.0
2.0
1
04/07/10 23:05
75-09-2
ND ug/L
0.50
0.50
1
04/07/10 23:05
1634-04-4
ND ug/L
2.0
2.0
1
04/07/10 23:05
91-20-3
ND ug/L
0.50
0.50
1
04/07/10 23:05
103-65-1
ND ug/L
0.50
0.50
1
04/07/10 23:05
100-42-5
ND ug/L
0.50
0.50
1
04/07/10 23:05
630-20-6
ND ug/L
0.50
0.50
1
04/07/10 23:05
79-34-5
REPORT OF LABORATORY ANALYSIS Page 23 of 34
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, Inc..
"._c

Pace Analytical ivoPace
Analytical Services,
5 Riverside Dr. 9800 Kicey Ave. Suite 100
Nwwpacelabscom Asheville, NC 28804 Huntersville, NC 28078
[phone] [phone]
ANALYTICAL RESULTS
Project: Fairchild 26805
Pace Project No.: 9266545
Sample: MW-13 Lab ID: 9266545010 Collected: 03/31/10 10:47 Received: 04/01/10 15:05 Matrix: Water
Report
Parameters Results Units Limit MDL DF Prepared Analyzed CAS No. Qual
6200B MSV Analytical Method: SM 6200B
Tetrachloroethene
6.3 ug/L
0.50
0.50
1
04/07/10 23:05
127-18-4
Toluene
ND ug/L
0.50
0.50
1
04/07/10 23:05
108-88-3
1,2,3-Trichlorobenzene
ND ug/L
2.0
2.0
1
04/07/10 23:05
87-61-6
1,2,4-Trichlorobenzene
ND ug/L
2.0
2.0
1
04/07/10 23:05
120-82-1
1,1,1-Trichloroethane
ND ug/L
0.50
0.50
1
04/07/10 23:05
71-55-6
1,1,2-Trichloroethane
ND ug/L
0.50
0.50
1
04/07/10 23:05
79-00-5
Trichloroethene
4.2 ug/L
0.50
0.50
1
04/07/10 23:05
79-01-6
Trichlorofluoromethane
ND ug/L
1.0
1.0
1
04/07/10 23:05
75-69-4
1,2,3-Trichloropropane
ND ug/L
0.50
0.50
1
04/07/10 23:05
96-18-4
1,2,4-Trimethylbenzene
ND ug/L
0.50
0.50
1
04/07/10 23:05
95-63-6
1,3,5-Trimethylbenzene
ND ug/L
0.50
0.50
1
04/07/10 23:05
108-67-8
Vinyl chloride
86.1 ug/L
1.0
1.0
1
04/07/10 23:05
75-01-4
m&p-Xylene
ND ug/L
1.0
1.0
1
04/07/10 23:05
1330-20-7
o-Xylene
ND ug/L
0.50
0.50
1
04/07/10 23:05
95-47-6
1,2-Dichloroethane-d4 (S)
104 %
70-130
1
04/07/10 23:05
17060-07-0
Dibromofluoromethane (S)
100 %
70-130
1
04/07/10 23:05
1868-53-7
4-Bromofluorobenzene(S)
97 %
70-130
1
04/07/10 23:05
460-00-4
Toluene-d8 (S)
98 %
70-130
1
04/07/10 23:05
2037-26-5
Date: 04/28/2010 02:17 PM
REPORT OF LABORATORY ANALYSIS
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, Inc..
�CCogo.
Q/ _ e
bct
Page 24 of 34

�r Pace Analytical Services, Inc. Pace Analytical Services, Inc.
l laceAnayrl ili//++ a/ 2225 Riverside Dr. 9800 Kincey Ave. Suite 100
.
www.pacelabs.com Asheville, NC 28804 Huntersville, NC 28078
[phone] [phone]
ANALYTICAL RESULTS
Project: Fairchild 26805
Pace Project No.: 9266545
Sample: DW-16 Lab ID: 9266545011 Collected: 03/31/10 10:18 Received: 04/01/10 15:05 Matrix: Water
Report
Parameters Results Units Limit MDL DF Prepared Analyzed CAS No. Qual
6200B MSV Analytical Method: SM 6200B
Benzene
ND ug/L
2.5
2.5
5
04/07/10 23:27
71-43-2
Bromobenzene
ND ug/L
2.5
2.5
5
04/07/10 23:27
108-86-1
Bromochloromethane
ND ug/L
2.5
2.5
5
04/07/10 23:27
74-97-5
Bromodichloromethane
ND ug/L
2.5
2.5
5
04/07/10 23:27
75-27-4
Bromoform
ND ug/L
2.5
2.5
5
04/07/10 23:27
75-25-2
Bromomethane
ND ug/L
25.0
5.0
5
04/07/10 23:27
74-83-9
n-Butylbenzene
ND ug/L
2.5
2.5
5
04/07/10 23:27
104-51-8
sec-Butylbenzene
ND ug/L
2.5
2.5
5
04/07/10 23:27
135-98-8
tert-Butyl benzene
ND ug/L
2.5
2.5
5
04/07/10 23:27
98-06-6
Carbon tetrachloride
ND ug/L
2.5
2.5
5
04/07/10 23:27
56-23-5
Chlorobenzene
ND ug/L
2.5
2.5
5
04/07/10 23:27
108-90-7
Chloroethane
ND ug/L
5.0
5.0
5
04/07/10 23:27
75-00-3
Chloroform
ND ug/L
2.5
2.5
5
04/07/10 23:27
67-66-3
Chloromethane
ND ug/L
5.0
5.0
5
04/07/10 23:27
74-87-3
2-Chlorotoluene
ND ug/L
2.5
2.5
5
04/07/10 23:27
95-49-8
4-Chlorotoluene
ND ug/L
2.5
2.5
5
04/07/10 23:27
106-43-4
1,2-Dibromo-3-chloropropane
ND ug/L
5.0
5.0
5
04/07/10 23:27
96-12-8
Dibromochloromethane
ND ug/L
2.5
2.5
5
04/07/10 23:27
124-48-1
1,2-Dibromoethane (EDB)
ND ug/L
2.5
2.5
5
04/07/10 23:27
106-93-4
Dibromomethane
ND ug/L
2.5
2.5
5
04/07/10 23:27
74-95-3
1,2-Dichlorobenzene
ND ug/L
2.5
2.5
5
04/07/10 23:27
95-50-1
1,3-Dichlorobenzene
ND ug/L
2.5
2.5
5
04/07/10 23:27
541-73-1
1,4-Dichlorobenzene
ND ug/L
2.5
2.5
5
04/07/10 23:27
106-46-7
Dichlorodifluoromethane
ND ug/L
2.5
2.5
5
04/07/10 23:27
75-71-8
1,1-Dichioroethane
ND ug/L
2.5
2.5
5
04/07/10 23:27
75-34-3
1,2-Dichioroethane
ND ug/L
2.5
2.5
5
04/07/10 23:27
107-06-2
1,1-Dichloroethene
ND ug/L
2.5
2.5
5
04/07/10 23:27
75-35-4
cis-1,2-Dichloroethene
85.0 ug/L
2.5
2.5
5
04/07/10 23:27
156-59-2
Vans-1,2-Dichloroethene
4.3 ug/L
2.5
2.5
5
04/07/10 23:27
156-60-5
1,2-Dichloropropane
ND ug/L
2.5
2.5
5
04/07/10 23:27
78-87-5
1,3-Dichloropropane
ND ug/L
2.5
2.5
5
04/07/10 23:27
142-28-9
2,2-Dichloropropane
ND ug/L
2.5
2.5
5
04/07/10 23:27
594-20-7
1,1-Dichloropropene
ND ug/L
2.5
2.5
5
04/07/10 23:27
563-58-6
cis-1,3-Dichloropropene
ND ug/L
2.5
2.5
5
04/07/10 23:27
10061-01-5
trans- 1,3-Dichloropropene
ND ug/L
2.5
2.5
5
04/07/10 23:27
10061-02-6
Diisopropyl ether
ND ug/L
2.5
2.5
5
04/07/10 23:27
108-20-3
Ethylbenzene
ND ug/L
2.5
2.5
5
04/07/10 23:27
100-41-4
Hexachloro-1,3-butadiene
ND ug/L
10.0
10.0
5
04/07/10 23:27
87-68-3
Isopropylbenzene (Cumene)
ND ug/L
2.5
2.5
5
04/07/10 23:27
98-82-8
Methylene Chloride
ND ug/L
10.0
10.0
5
04/07/10 23:27
75-09-2
Methyl-tert-butyl ether
ND ug/L
2.5
2.5
5
04/07/10 23:27
1634-04-4
Naphthalene
ND ug/L
10.0
10.0
5
04/07/10 23:27
91-20-3
n-Propyibenzene
ND ug/L
2.5
2.5
5
04/07/10 23:27
103-65-1
Styrene
ND ug/L
2.5
2.5
5
04/07/10 23:27
100-42-5
1,1,1,2-Tetrachloroethane
ND ug/L
2.5
2.5
5
04/07/10 23:27
630-20-6
1,1,2,2-Tetrachloroethane
ND ug/L
2.5
2.5
5
04/07/10 23:27
79-34-5
Date: 04/28/2010 02:17 PM REPORT OF LABORATORY ANALYSIS Page 25 of 34
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, Inc..

PakeAnalytical
"mpacelabs.wn
Pace Analytical Services, Inc.
2225 Riverside Dr.
Asheville, NC 28804
[phone]
Pace Analytical Services, Inc.
9800 Kincey Ave. Suite 100
Huntersv�ite, NC 28078
[phone]
Project: Fairchild 26805
Pace Project No.: 9266545
ANALYTICAL RESULTS
Sample: DW-16
Lab ID: 9266545011
Collected:
03/31/10 10:18
Received: 04/01/10 15:05 Matrix: Water
Report
Parameters
Results Units
Limit
MDL
DF
Prepared Analyzed
CAS No. Qual
6200B MSV
Analytical Method: SM 6200B
Tetrachloroethene
542 ug/L
2.5
2.5
5
04/07/10 23:27
127-18-4
Toluene
ND ug/L
2.5
2.5
5
04/07/10 23:27
108-88-3
1,2,3-Trichlorobenzene
ND ug/L
10.0
10.0
5
04/07/10 23:27
87-61-6
1,2,4-Trichlorobenzene
ND ug/L
10.0
10.0
5
04/07/10 23:27
120-82-1
1,1,1-Trichloroethane
ND ug/L
2.5
2.5
5
04/07/10 23:27
71-55-6
1,1,2-Trichloroethane
ND ug/L
2.5
2.5
5
04/07/10 23:27
79-00-5
Trichloroethene
162 ug/L
2.5
2.5
5
04/07/10 23:27
79-01-6
Trichlorofluoromethane
ND ug/L
5.0
5.0
5
04/07/10 23:27
75-69-4
1,2,3-Trichloropropane
ND ug/L
2.5
2.5
5
04/07/10 23:27
96-18-4
1,2,4-Trimethylbenzene
ND ug/L
2.5
2.5
5
04/07/10 23:27
95-63-6
1,3,5-Trimethylbenzene
ND ug/L
2.5
2.5
5
04/07/10 23:27
108-67-8
Vinyl chloride
11.3 ug/L
5.0
5.0
5
04/07/10 23:27
75-01-4
m&p-Xylene
ND ug/L
5.0
5.0
5
04/07/10 23:27
1330-20-7
o-Xylene
ND ug/L
2.5
2.5
5
04/07/10 23:27
95-47-6
1,2-Dichloroethane-d4 (S)
102 %
70-130
5
04/07/10 23:27
17060-07-0
Dibromofluoromethane (S)
100 %
70-130
5
04/07/10 23:27
1868-53-7
4-Bromofluorobenzene(S)
96 %
70-130
5
04/07/10 23:27
460-00-4
Toluene-d8 (S)
99 %
70-130
5
04/07/10 23:27
2037-26-5
Date: 04/28/2010 02:17 PM
REPORT OF LABORATORY ANALYSIS
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, Inc..
w nCCpgnCCpg(e/'�
U'y lrR,i1�z
Page 26 of 34

0 Pace Analytical Services, Inc. Pace Analytical Services, Inc.
PaceAnalytical 2225 Riverside Dr. 9800 Kincey Ave. Suite 100
WWWpacelebscom Asheville, NC 28804 Huntersville, NC 28078
[phone] [phone]
ANALYTICAL RESULTS
Project: Fairchild 26805
Pace Project No.: 9266545
Sample: DW-19 Lab ID: 9266545012 Collected: 03/31/10 15:50 Received: 04/01/10 15:05 Matrix: Water
Report
Parameters Results Units Limit MDL DF Prepared Analyzed CAS No. Qual
6200E MSV Analytical Method: SM 6200B
Benzene
ND ug/L
0.50
0.50
1
04/07/10 23:49
71-43-2
Bromobenzene
ND ug/L
0.50
0.50
1
04/07/10 23:49
108-86-1
Bromochloromethane
ND ug/L
0.50
0.50
1
04/07/10 23:49
74-97-5
Bromodichloromethane
ND ug/L
0.50
0.50
1
04/07/10 23:49
75-27-4
Bromoform
ND ug/L
0.50
0.50
1
04/07/10 23:49
75-25-2
Bromomethane
ND ug/L
5.0
1.0
1
04/07/10 23:49
74-83-9
n-Butylbenzene
ND ug/L
0.50
0.50
1
04/07/10 23:49
104-51-8
sec-Butylbenzene
ND ug/L
0.50
0.50
1
04/07/10 23:49
135-98-8
tert-Butylbenzene
ND ug/L
0.50
0.50
1
04/07/10 23:49
98-06-6
Carbon tetrachloride
ND ug/L
0.50
0.50
1
04/07/10 23:49
56-23-5
Chlorobenzene
ND ug/L
0.50
0.50
1
04/07/10 23:49
108-90-7
Chloroethane
ND ug/L
1.0
1.0
1
04/07/10 23:49
75-00-3
Chloroform
ND ug/L
0.50
0.50
1
04/07/10 23:49
67-66-3
Chloromethane
ND ug/L
1.0
1.0
1
04/07/10 23:49
74-87-3
2-Chlorotoluene
ND ug/L
0.50
0.50
1
04/07/10 23:49
95-49-8
4-Chlorotoluene
ND ug/L
0.50
0.50
1
04/07/10 23:49
106-43-4
1,2-Dibromo-3-chloropropane
ND ug/L
1.0
1.0
1
04/07/10 23:49
96-12-8
Dibromochloromethane
ND ug/L
0.50
0.50
1
04/07/10 23:49
124-48-1
1,2-Dibromoethane (EDB)
ND ug/L
0.50
0.50
1
04/07/10 23:49
106-93-4
Dibromomethane
ND ug/L
0.50
0.50
1
04/07/10 23:49
74-95-3
1,2-Dichlorobenzene
ND ug/L
0.50
0.50
1
04/07/10 23:49
95-50-1
1,3-Dichlorobenzene
ND ug/L
0.50
0.50
1
04/07/10 23:49
541-73-1
1,4-Dichlorobenzene
ND ug/L
0.50
0.50
1
04/07/10 23:49
106-46-7
Dichlorodifluoromethane
ND ug/L
0.50
0.50
1
04/07/10 23:49
75-71-8
1,1-Dichloroethane
ND ug/L
0.50
0.50
1
04/07/10 23:49
75-34-3
1,2-Dichloroethane
ND ug/L
0.50
0.50
1
04/07/10 23:49
107-06-2
1,1-Dichloroethene
ND ug/L
0.50
0.50
1
04/07/10 23:49
75-35-4
cis-1,2-Dichloroethene
1.2 ug/L
0.50
0.50
1
04/07/10 23:49
156-59-2
trans- 1,2-Dichloroethene
ND ug/L
0.50
0.50
1
04/07/10 23:49
156-60-5
1,2-Dichloropropane
ND ug/L
0.50
0.50
1
04/07/10 23:49
78-87-5
1,3-Dichloropropane
ND ug/L
0.50
0.50
1
04/07/10 23:49
142-28-9
2,2-Dichloropropane
ND ug/L
0.50
0.50
1
04/07/10 23:49
594-20-7
1,1-Dichloropropene
ND ug/L
0.50
0.50
1
04/07/10 23:49
563-58-6
cis-1,3-Dichloropropene
ND ug/L
0.50
0.50
1
04/07/10 23:49
10061-01-5
trans-1,3-Dichloropropene
ND ug/L
0.50
0.50
1
04/07/10 23:49
10061-02-6
Diisopropyl ether
ND ug/L
0.50
0.50
1
04/07/10 23:49
108-20-3
Ethylbenzene
ND ug/L
0.50
0.50
1
04/07/10 23:49
100-41-4
Hexachloro-1,3-butadiene
ND ug/L
2.0
2.0
1
04107/1023:49
87-68-3
Isopropylbenzene (Cumene)
ND ug/L
0.50
0.50
1
04/07/10 23:49
98-82-8
Methylene Chloride
ND ug/L
2.0
2.0
1
04/07/10 23:49
75-09-2
Methyl-tert-butyl ether
ND ug/L
0.50
0.50
1
04/07/10 23:49
1634-04-4
Naphthalene
ND ug/L
2.0
2.0
1
04/07/10 23:49
91-20-3
n-Propylbenzene
ND ug/L
0.50
0.50
1
04/07/10 23:49
103-65-1
Styrene
ND ug/L
0.50
0.50
1
04/07/10 23:49
100-42-5
1,1,1,2-Tetrachloroethane
ND ug/L
0.50
0.50
1
04/07/10 23:49
630-20-6
1,1,2,2-Tetrachloroethane
ND ug/L
0.50
0.50
1
04/07/10 23:49
79-34-5
Date: 04/28/2010 02:17 PM REPORT OF LABORATORY ANALYSIS Page 27 of 34
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, Inc..

PaceAnalyfical
*" pacelabs.=n
Pace Analytical Services, Inc.
2225 Riverside Dr.
Asheville, NC 28804
[phone]
Pace Analytical Services, Inc.
9800 KinceyAve. Suite 100
Huntersville, NC 28078
[phone]
Project: Fairchild 26805
Pace Project No.: 9266545
ANALYTICAL RESULTS
Sample: DW-19
Lab ID: 9266545012
Collected:
03/31/10 15:50
Received: 04/01/10 15:05 Matrix: Water
Report
Parameters
Results Units
Limit
MDL
DF
Prepared Analyzed
CAS No. Qual
6200E MSV
Analytical Method: SM 6200B
Tetrachloroethene
88.7 ug/L
0.50
0.50
1
04/07/10 23:49
127-18-4
Toluene
ND ug/L
0.50
0.50
1
04/07/10 23:49
108-88-3
1,2,3-Trichlorobenzene
ND ug/L
2.0
2.0
1
04/07/10 23:49
87-61-6
1,2,4-Trichlorobenzene
ND ug/L
2.0
2.0
1
04/07/10 23:49
120-82-1
1,1,1-Trichloroethane
ND ug/L
0.50
0.50
1
04/07/10 23:49
71-55-6
1,1,2-Trichloroethane
ND ug/L
0.50
0.50
1
04/07/10 23:49
79-00-5
Trichloroethene
3.1 ug/L
0.50
0.50
1
04/07/10 23:49
79-01-6
Trichlorofluoromethane
ND ug/L
1.0
1.0
1
04/07/10 23:49
75-69-4
1,2,3-Tdchloropropane
ND ug/L
0.50
0.50
1
04/07/10 23:49
96-18-4
1,2,4-Trimethylbenzene
ND ug/L
0.50
0.50
1
04/07/10 23:49
95-63-6
1,3,5-Trimethylbenzene
ND ug/L
0.50
0.50
1
04/07/10 23:49
108-67-8
Vinyl chloride
ND ug/L
1.0
1.0
1
04/07/10 23:49
75-01-4
m&p-Xylene
ND ug/L
1.0
1.0
1
04/07/10 23:49
1330-20-7
o-Xylene
ND ug/L
0.50
0.50
1
04/07/10 23:49
95-47-6
1,2-Dichloroethane-d4(S)
102 %
70-130
1
04/07/10 23:49
17060-07-0
Dibromofluoromethane (S)
99 %
70-130
1
04/07/10 23:49
1868-53-7
4-Bromofluorobenzene (S)
95 %
70-130
1
04/07/10 23:49
460-00-4
Toluene-d8(S)
97 %
70-130
1
04/07/10 23:49
2037-26-5
Date: 04/28/2010 02:17 PM
REPORT OF LABORATORY ANALYSIS
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, Inc..
Page 28 of 34

llwlaceAnal ical
www.pacelab&=n
Pace Analytical Services, Inc.
2225 Riverside Dr.
Asheville, NC 28804
[phone]
Project: Fairchild 26805
Pace Project No.: 9266545
QUALITY CONTROL DATA
Pace Analytical Services, Inc.
9800 Kincey Ave. Suite 100
Huntersville, NC 28078
[phone]
QC Batch: MSV/10522 Analysis Method: SM 6200B
QC Batch Method: SM 6200B Analysis Description: 6200E MSV
Associated Lab Samples: 9266545001, 9266545002, 9266545003, 9266545004, 9266545005, 9266545006, 9266545007, 9266545008,
9266545009,9266545010,9266545011,9266545012
METHOD BLANK: 424834 Matrix: Water
Associated Lab Samples: 9266545001, 9266545002, 9266545003, 9266545004, 9266545005, 9266545006, 9266545007, 9266545008,
9266545009,9266545010,9266545011,9266545012
Blank Reporting
Parameter Units Result Limit Analyzed Qualifiers
1,1,1,2-Tetrachloroethane
ug/L
ND
0.50
0410711015:38
1,1,1-Trichloroethane
ug/L
ND
0.50
04107/1015:38
1,1,2,2-Tetrachloroethane
ug/L
ND
0.50
04/07/10 15:38
1,1,2-Trichloroethane
ug/L
ND
0.50
04/07/10 15:38
1,1-Dichloroethane
ug/L
ND
0.50
04/07/10 15:38
1,1-Dichloroethene
ug/L
ND
0.50
04/07/10 15:38
1,1-Dichloropropene
ug/L
ND
0.50
04/07/10 15:38
1,2,3-Trichlorobenzene
ug/L
ND
2.0
04/07/10 15:38
1,2,3-Trichloropropane
ug/L
ND
0.50
04/07/10 15:38
1,2,4-Trichlorobenzene
ug/L
ND
2.0
04/07/10 15:38
1,2,4-Trimethylbenzene
ug/L
ND
0.50
04/07/10 15:38
1,2-Dibromo-3-chloropropane
ug/L
ND
1.0
04/07/10 15:38
1,2-Dibromoethane (EDB)
ug/L
ND
0.50
04/07/10 15:38
1,2-Dichlorobenzene
ug/L
ND
0.50
04/07/10 15:38
1,2-Dichloroethane
ug/L
ND
0.50
04/07/10 15:38
1,2-Dichloropropane
ug/L
ND
0.50
04/07/10 15:38
1,3,5-Trimethylbenzene
ug/L
ND
0.50
04/07/10 15:38
1,3-Dichlorobenzene
ug/L
ND
0.50
04/07/10 15:38
1,3-Dichloropropane
ug/L
ND
0.50
04/07/10 15:38
1,4-Dichlorobenzene
ug/L
ND
0.50
04/07/10 15:38
2,2-Dichloropropane
ug/L
ND
0.50
04/07/10 15:38
2-Chlorotoluene
ug/L
ND
0.50
04/07/10 15:38
4-Chlorotoluene
ug/L
ND
0.50
04/07/10 15:38
Benzene
ug/L
ND
0.50
04/07/10 15:38
Bromobenzene
ug/L
ND
0.50
04/07/10 15:38
Bromochloromethane
ug/L
ND
0.50
04/07/10 15:38
Bromodichioromethane
ug/L
ND
0.50
04/07/10 15:38
Bromoform
ug/L
ND
0.50
04/07/10 15:38
Bromomethane
ug/L
ND
5.0
04/07/10 15:38
Carbon tetrachloride
ug/L
ND
0.50
04/07/10 15:38
Chlorobenzene
ug/L
ND
0.50
04/07/10 15:38
Chloroethane
ug/L
ND
1.0
04/07/10 15:38
Chloroform
ug/L
ND
0.50
04/07/10 15:38
Chloromethane
ug/L
ND
1.0
04/07/10 15:38
cis- 1,2-Dichloroethene
ug/L
ND
0.50
04/07/10 15:38
cis-1,3-Dichloropropene
ug/L
ND
0.50
04/07/10 15:38
Dibromochloromethane
ug/L
ND
0.50
04/07/10 15:38
Dibromomethane
ug/L
ND
0.50
04/07/10 15:38
Dichlorodifluoromethane
ug/L
ND
0.50
04/07/10 15:38
Diisopropyl ether
ug/L
ND
0.50
04/07/10 15:38
Ethylbenzene
ug/L
ND
0.50
04/07/10 15:38
Date: 04/28/2010 02:17 PM REPORT OF LABORATORY ANALYSIS
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, Inc..
!:1__IfIGLL.�
Page 29 of 34

� r
/ . PaceAnalytical
www.pacelabs.crom
Pace Analytical Services, Inc.
2225 Riverside Dr.
Asheville, NC 28804
[phone]
Pace Analytical Services, Inc.
9800 Kincey Ave. Suite 100
Huntersville, NC 28078
[phone]
Project: Fairchild 26805
Pace Project No.: 9266545
QUALITY CONTROL DATA
METHOD BLANK: 424834 Matrix: Water
Associated Lab Samples: 9266545001, 9266545002, 9266545003, 9266545004, 9266545005, 9266545006, 9266545007, 9266545008,
9266545009, 9266545010, 9266545011, 9266545012
Blank Reporting
Parameter Units Result Limit Analyzed Qualifiers
Hexachloro-1,3-butadiene
ug/L
ND
2.0
04/07/10 15:38
Isopropylbenzene (Cumene)
ug/L
ND
0.50
04/07/10 15:38
m&p-Xylene
ug/L
ND
1.0
04/07/10 15:38
Methyl-tert-butyl ether
ug/L
ND
0.50
04/07/10 15:38
Methylene Chloride
ug/L
ND
2.0
04/07/10 15:38
n-Butylbenzene
ug/L
ND
0.50
04/07/10 15:38
n-Propylbenzene
ug/L
ND
0.50
04/07/10 15:38
Naphthalene
ug/L
ND
2.0
04/07/10 15:38
o-Xylene
ug/L
ND
0.50
04/07/10 15:38
sec-Butylbenzene
ug/L
ND
0.50
04/07/10 15:38
Styrene
ug/L
ND
0.50
04/07/10 15:38
tert-Butylbenzene
ug/L
ND
0.50
04/07/10 15:38
Tetrachloroethene
ug/L
ND
0.50
04/07/10 15:38
Toluene
ug/L
ND
0.50
04/07/10 15:38
trans-1,2-Dichloroethene
ug/L
ND
0.50
04/07/10 15:38
trans- 1,3-Dichloropropene
ug/L
ND
0.50
04/07/10 15:38
Trichloroethene
ug/L
ND
0.50
04/07/10 15:38
Trichlorofluoromethane
ug/L
ND
1.0
04/07/10 15:38
Vinyl chloride
ug/L
ND
1.0
04/07/10 15:38
1,2-Dichloroethane-d4 (S)
%
101
70-130
04/07/10 15:38
4-Bromofluorobenzene (S)
%
99
70-130
04/07/10 15:38
Dibromofluoromethane (S)
%
100
70-130
04/07/10 15:38
Toluene-d8 (S)
%
100
70-130
04/07/10 15:38
LABORATORY CONTROL SAMPLE:
Parameter
424835
Units
Spike
Conc.
LCS
Result
LCS
% Rec
% Rec
Limits Qualifiers
1,1,1,2-Tetrachloroethane
ug/L
50
46.1
92
60-140
1,1,1-Trichloroethane
ug/L
50
46.8
94
60-140
1,1,2,2-Tetrachloroethane
ug/L
50
44.1
88
60-140
1,1,2-Trichloroethane
ug/L
50
46.2
92
60-140
1,1-Dichloroethane
ug/L
50
47.0
94
60-140
1,1-Dichloroethene
ug/L
50
46.5
93
60-140
1,1-Dichloropropene
ug/L
50
43.5
87
60-140
1,2,3-Trichlorobenzene
ug/L
50
51.0
102
60-140
1,2,3-Tdchloropropane
ug/L
50
44.8
90
60-140
1,2,4-Trichlorobenzene
ug/L
50
47.8
96
60-140
1,2,4-Trimethylbenzene
ug/L
50
45.3
91
60-140
1,2-Dibromo-3-chloropropane
ug/L
50
47.1
94
60-140
1,2-Dibromoethane (EDB)
ug/L
50
46.7
93
60-140
1,2-Dichlorobenzene
ug/L
50
45.7
91
60-140
1,2-Dichloroethane
ug/L
50
44.7
89
60-140
1,2-Dichloropropane
ug/L
50
45.4
91
60-140
1,3,5-Trimethylbenzene
ug/L
50
45.6
91
60-140
Date: 04/28/2010 02:17 PM REPORT OF LABORATORY ANALYSIS Page 30 of 34
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, Inc..

® Pace Analytical Services, Inc.
! aceAnalytical 2225 Riverside Dr.
www.paceiabs.com
Asheville, NC 28804
[phone]
Pace Analytical Services, Inc.
9800 Kincey Ave. Suite 100
Huntersville, NC 28078
[phone]
QUALITY CONTROL DATA
Project: Fairchild 26805
Pace Project No.: 9266545
LABORATORY CONTROL SAMPLE:
Parameter
424835
Units
Spike
Conc.
LCS
Result
LCS
% Rec
% Rec
Limits
1,3-Dichlorobenzene
ug/L
50
44.9
90
60-140
1,3-Dichloropropane
ug/L
50
45.4
91
60-140
1,4-Dichlorobenzene
ug/L
50
44.4
89
60-140
2,2-Dichloropropane
ug/L
50
48.3
97
60-140
2-Chlorotoluene
ug/L
50
44.7
89
60-140
4-Chlorotoluene
ug/L
50
46.1
92
60-140
Benzene
ug/L
50
44.1
88
60-140
Bromobenzene
ug/L
50
45.0
90
60-140
Bromochloromethane
ug/L
50
41.7
83
60-140
Bromodichloromethane
ug/L
50
42.8
86
60-140
Bromoform
ug/L
50
47.5
95
60-140
Bromomethane
ug/L
50
52.2
104
60-140
Carbon tetrachloride
ug/L
50
39.8
80
60-140
Chlorobenzene
ug/L
50
46.1
92
60-140
Chloroethane
ug/L
50
44.6
89
60-140
Chloroform
ug/L
50
43.0
86
60-140
Chloromethane
ug/L
50
46.7
93
60-140
cis- 1,2-Dichloroethene
ug/L
50
44.2
88
60-140
cis-1,3-Dichloropropene
ug/L
50
47.7
95
60-140
Dibromochloromethane
ug/L
50
45.3
91
60-140
Dibromomethane
ug/L
50
47.3
95
60-140
Dichlorodifluoromethane
ug/L
50
38.6
77
60-140
Diisopropyl ether
ug/L
50
47.0
94
60-140
Ethylbenzene
ug/L
50
45.4
91
60-140
Hexachloro-1,3-butadiene
ug/L
50
47.4
95
60-140
Isopropylbenzene (Cumene)
ug/L
50
47.8
96
60-140
m&p-Xylene
ug/L
100
92.7
93
60-140
Methyl-tert-butyl ether
ug/L
50
53.3
107
60-140
Methylene Chloride
ug/L
50
40.1
80
60-140
n-Butylbenzene
ug/L
50
46.5
93
60-140
n-Propylbenzene
ug/L
50
46.5
93
60-140
Naphthalene
ug/L
50
50.4
101
60-140
o-Xylene
ug/L
50
46.9
94
60-140
sec-Butylbenzene
ug/L
50
46.8
94
60-140
Styrene
ug/L
50
48.8
98
60-140
tert-Butylbenzene
ug/L
50
46.5
93
60-140
Tetrachloroethene
ug/L
50
45.8
92
60-140
Toluene
ug/L
50
44.9
90
60-140
trans- 1,2-Dichloroethene
ug/L
50
43.4
87
60-140
trans-1,3-Dichloropropene
ug/L
50
48.5
97
60-140
Trichloroethene
ug/L
50
45.0
90
60-140
Trichlorofluoromethane
ug/L
50
41.4
83
60-140
Vinyl chloride
ug/L
50
42.4
85
60-140
1,2-Dichloroethane-d4 (S)
%
99
70-130
4-Bromofluorobenzene (S)
%
103
70-130
Dibromocuoromethane (S)
%
101
70-130
Toluene-d8 (S)
%
100
70-130
Date: 04/28/2010 02:17 PM REPORT OF LABORATORY ANALYSIS
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, Inc..
,• ncc0A0,
C:
U' 1 i
Qualifiers
Page 31 of 34

rI ® Pace Analytical Services, Inc. Pace Analytical Services, Inc.
Rake Analytical 2225 Riverside Dr. 9800 Kincey Ave. Suite 100
wwwpwwabscom Asheville, NC 28804 Huntersville, NC 28078
[phone] [phone]
QUALITY CONTROL DATA
Project: Fairchild 26805
Pace Project No.: 9266545
MATRIX SPIKE & MATRIX SPIKE DUPLICATE: 424836
9266545003
Parameter Units Result
MS
Spike
Conc.
MSD
Spike
Conc.
424837
MS
Result
MSD
Result
MS
% Rec
MSD
% Rec
% Rec
Limits
Max
RPD RPD Qual
1, 1, 1,2-Tetrachloroethane
ug/L
ND
20
20
21.3
21.8
106
109
60-140
3
30
1, 1, 1 -Trichloroethane
ug/L
ND
20
20
23.3
23.2
117
116
60-140
1
30
1,1,2,2-Tetrachloroethane
ug/L
ND
20
20
19.5
21.6
98
108
60-140
10
30
1,1,2-Trichloroethane
ug/L
ND
20
20
21.1
22.5
105
113
60-140
7
30
1,1-Dichloroethane
ug/L
ND
20
20
22.5
22.8
113
114
60-140
1
30
1,1-Dichloroethene
ug/L
ND
20
20
23.0
22.8
115
114
60-140
1
30
1,1-Dichloropropene
ug/L
ND
20
20
21.4
20.8
107
104
60-140
3
30
1,2,3-Trichlorobenzene
ug/L
ND
20
20
21.0
23.8
105
119
60-140
13
30
1,2,3-Tdchloropropane
ug/L
ND
20
20
20.6
22.7
103
114
60-140
10
30
1,2,4-Trichlorobenzene
ug/L
ND
20
20
19.9
22.5
99
112
60-140
12
30
1,2,4-Trimethylbenzene
ug/L
ND
20
20
21.2
22.5
106
113
60-140
6
30
1,2-Dibromo-3-chloropropane
ug/L
ND
20
20
20.4
22.9
102
114
60-140
11
30
1,2-Dibromoethane (EDB)
ug/L
ND
20
20
20.4
21.6
102
108
60-140
5
30
1,2-Dichlorobenzene
ug/L
ND
20
20
21.0
22.2
105
111
60-140
6
30
1,2-Dichloroethane
ug/L
ND
20
20
21.4
22.3
107
112
60-140
4
30
1,2-Dichloropropane
ug/L
ND
20
20
21.8
22.0
109
110
60-140
1
30
1,3,5-Trimethylbenzene
ug/L
ND
20
20
22.1
23.1
111
116
60-140
4
30
1,3-Dichlorobenzene
ug/L
ND
20
20
21.3
22.0
106
110
60-140
3
30
1,3-Dichloropropane
ug/L
ND
20
20
20.5
21.6
103
108
60-140
5
30
1,4-Dichlorobenzene
ug/L
ND
20
20
21.0
21.9
105
110
60-140
4
30
2,2-Dichloropropane
ug/L
ND
20
20
16.2
16.6
81
83
60-140
3
30
2-Chlorotoluene
ug/L
ND
20
20
22.0
22.5
110
113
60-140
2
30
4-Chlorotoluene
ug/L
ND
20
20
21.7
22.8
108
114
60-140
5
30
Benzene
ug/L
ND
20
20
21.8
21.9
109
109
60-140
0
30
Bromobenzene
ug/L
ND
20
20
21.6
22.5
108
112
60-140
4
30
Bromochloromethane
ug/L
ND
20
20
22.2
22.2
111
111
60-140
0
30
Bromodichloromethane
ug/L
ND
20
20
20.5
20.9
103
105
60-140
2
30
Bromoform
ug/L
ND
20
20
18.8
20.6
94
103
60-140
9
30
Bromomethane
ug/L
ND
20
20
23.7
24.1
119
121
60-140
2
30
Carbon tetrachloride
ug/L
ND
20
20
25.1
24.9
126
124
60-140
1
30
Chlorobenzene
ug/L
ND
20
20
22.1
22.9
111
114
60-140
3
30
Chloroethane
ug/L
ND
20
20
23.6
22.7
118
114
60-140
4
30
Chloroform
ug/L
ND
20
20
20.6
20.8
103
104
60-140
1
30
Chloromethane
ug/L
ND
20
20
18.4
18.0
92
90
60-140
2
30
cis-1,2-Dichloroethene
ug/L
6.8
20
20
27.7
27.1
105
101
60-140
2
30
cis-1,3-Dichloropropene
ug/L
ND
20
20
18.3
19.2
92
96
60-140
5
30
Dibromochloromethane
ug/L
ND
20
20
19.4
20.9
97
104
60-140
7
30
Dibromomethane
ug/L
ND
20
20
21.7
23.0
109
115
60-140
6
30
Dichlorodifluoromethane
ug/L
ND
20
20
21.2
20.4
106
102
60-140
4
30
Diisopropyl ether
ug/L
ND
20
20
21.3
22.0
107
110
60-140
3
30
Ethylbenzene
ug/L
ND
20
20
22.0
22.7
110
114
60-140
3
30
Hexachloro-1,3-butadiene
ug/L
ND
20
20
20.1
19.7
100
99
60-140
2
30
Isopropylbenzene (Cumene)
ug/L
ND
20
20
23.1
24.0
115
120
60-140
4
30
m&p-Xylene
ug/L
ND
40
40
46.7
47.3
117
118
60-140
1
30
Methyl-tert-butyl ether
ug/L
ND
20
20
24.2
25.7
121
128
60-140
6
30
Methylene Chloride
ug/L
ND
20
20
19.4
19.2
96
95
60-140
1
30
n-Butylbenzene
ug/L
ND
20
20
21.5
23.7
108
118
60-140
9
30
Date: 04/28/2010 02:17 PM REPORT OF LABORATORY ANALYSIS Page 32 of 34
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, Inc..

® Pace Analytical Services, Inc. Pace Analytical Services, Inc.
Pa'ceAnalytical 2225 Riverside Dr. 9800 Kincey Ave. Suite 100
www.pwwabscom Asheville, NC 28804 Huntersville, NC 28078
[phone] [phone]
QUALITY CONTROL DATA
Project: Fairchild 26805
Pace Project No.: 9266545
MATRIX SPIKE & MATRIX SPIKE DUPLICATE: 424836
9266545003
Parameter Units Result
MS
Spike
Conc.
MSD
Spike
Conc.
424837
MS
Result
MSD
Result
MS
% Rec
MSD
% Rec
% Rec
Limits
Max
RPD RPD Qual
n-Propylbenzene
ug/L
ND
20
20
23.1
23.8
115
119
60-140
3
30
Naphthalene
ug/L
ND
20
20
20.8
23.5
102
115
60-140
12
30
o-Xylene
ug/L
ND
20
20
22.3
22.9
112
115
60-140
3
30
sec -Butyl benzene
ug/L
ND
20
20
23.0
25.0
115
125
60-140
8
30
Styrene
ug/L
ND
20
20
21.6
22.3
108
112
60-140
3
30
tert-Butyl benzene
ug/L
ND
20
20
22.9
24.8
114
124
60-140
8
30
Tetrachloroethene
ug/L
1.2
20
20
23.0
23.2
109
110
60-140
1
30
Toluene
ug/L
ND
20
20
21.9
22.1
109
111
60-140
1
30
trans-1,2-Dichloroethene
ug/L
ND
20
20
21.8
21.2
108
104
60-140
3
30
trans-1,3-Dichloropropene
ug/L
ND
20
20
18.0
19.2
90
96
60-140
6
30
Trichloroethene
ug/L
0.92
20
20
23.2
22.7
111
109
60-140
2
30
Trichlorofluoromethane
ug/L
ND
20
20
23.0
22.6
115
113
60-140
2
30
Vinyl chloride
ug/L
ND
20
20
22.1
21.4
109
105
60-140
3
30
1,2-Dichloroethane-d4(S)
%
100
100
70-130
4-Bromofluorobenzene(S)
%
99
101
70-130
Dibromofluoromethane (S)
%
101
100
70-130
Toluene-d8 (S)
%
100
100
70-130
Date: 04/28/2010 02:17 PM
REPORT OF LABORATORY ANALYSIS
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, Inc..
Page 33 of 34

® Pace Analytical Services, Inc. Pace Analytical Services, Inc.
' ���'a'��y��L}}''' 2225 Riverside Dr. 9800 Kincey Ave. Suite 100
w,w. ebs Asheville, NC 28804 Huntersville, NC 28078
[phone] [phone]
QUALIFIERS
Project: Fairchild 26805
Pace Project No.: 9266545
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-Diphenylhydrazine (8270 listed analyte) decomposes toAzobenzene.
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.
U - Indicates the compound was analyzed for, but not detected.
Date: 04/28/2010 02:17 PM REPORT OF LABORATORY ANALYSIS Page 34 of 34
This report shall not be reproduced, except in full,
without the written consent of PaceAnalytical Services, Inc..
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CHAIN -OF -CUSTODY J Analytical Request Document
The Chain -of -Custody is a LEGAL DOCUMENT. All relevant fields must be completed accurately.
In A Section B Section C
red Client Information: Required Project kdormatlon: Invoice Information: Page 1 Of 1
any: Meinfelder, Inc. sport To. Chris Hay Attention: Chris Ha
Sac 313 Gallimore Dairy Rd copy To: y Name: Kleinfelder, Inc.
rtsboro, NC 27409
Address: 313 Gallimore Dairy Rd, Greensboro, N
To: cha @ kleinfelder.com
rchase Order No.
Pace Quote Reference:
1: 336 668-OM Fax:
lent Project ID: Fairchild
Pace Project Manager: Helton, Brandon
Wed Due Date/TAT: 10 De Defauk
ainer Order Number. 805
Pace Profile t:17412 — /
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Client Name- k rn �tAr, Project #
Courier: Fed Ex UPS ❑ USPS ❑Client ❑ �O ❑ ❑ '^Q/ mmercial Pace Other Eit[oFlr�
Custody Seal on Cooler/Box Present: ❑ yes no Seals vact: ❑ yes 12rono r-
Pto a[ - / r
Packing Material: ❑ Bubble Wrap Bubble Bags El None Cllther
Thermometer Used T060 Type of Ice: A Blue None Samples on ice, cooling process has begun
Cooler Temperature 15.01
Biological Tissue is Frozen: Yes No N/A
Date and tniti of e o fining
contents: i
Temp should be above freezing to 6'C
Comments:
Chain of Custody Present:
Yes ONo
ON/A
1.
Chain of Custody Filled Out:
Ye
ONo
❑N/A
2.
Chain of Custody Relinquished:
es
No
ON/A
3,
Sampler Name & Signature on COC:
Ye
No
❑N/A
4.
Samples Arrived within Hold Time:-
Yes
ONo
ON/A
5.
Short Hold Time Analysis (<72hr).
Oyes
VN.
❑N/A
6.
Rush Turn Around Time Requested:
Ores
o
❑N/A
7.
Sufficient Volume:
zlyle
ONO
ON/A
8.
'.orrect Containers Used:.
Ye - No
❑N/A
g- a -
-Pace Containers Used:
Yes
ONo
ON/A
OM21nerS Intact:
Yes
ONO
ON/
10. .
ltered volume received for Dissolved tests
❑Yes
ONo
N/A
11.
ample Labels match COC:
es
ONo
ON/A
12. -
wt
-Includes date/time/ID/Analysis Matrix:
containers needing preservation have been checked.
Yes
ONo
❑N/A
13.
containers needing preservation are found to be in
2es
ONO
ON/A
ipliance with EPA recommendation.
plions: VOA, coliform, TOC, O&G, Wt-DRO (water)
❑Yes
ONo
Initial when completed
nples checked for dechlorination:'
❑Yes
ONo
ol
N/A
14-
dspace in VOA Vials ( >6mm):
❑Yes
4K
❑N/A
15.
Blank Present:
❑Yes
ONO
/A
16.
Blank Custody Seats Present
OYes
ONo
/A
Trip Blank Lot # (if purchased): N/A
t Notification/ Resolution: Field Data Required? Y / N / N/A
Person Contacted:
Iments/ Resolution:
Date/Time:
+ct Manager Review: E)m t4 Date: