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UST CLOSURE REPORT
DESCRIPTION: NC 42 AT NC 96 ROUNDABOUT
TIP NO: W-5704S
WBS: 44850.1.19
NCDOT PARCEL NO: 01
OWNER: RAYMOND E EARP JR. FAMILY TRUST
LOCATION: 7230 NC HWY 42 E, SELMA, JOHNSTON COUNTY, NC
NCPIN: 261900-14-7863
PREPARED FOR:
NORTH CAROLINA DEPARTMENT OF TRANSPORTATION
GEOTECHNICAL ENGINEERING UNIT
1020 BIRCH RIDGE DRIVE
RALEIGH, NC 27610
PREPARED BY:
FALCON ENGINEERING, INC.
1210 TRINITY ROAD, SUITE 110
CARY, NC 27513
PROJECT NUMBER: G23010.00
MARCH 23, 2023
FALCON ENGINEERING, INC. / 1210 TRINITY ROAD, SUITE 110 RALEIGH, NC 27607 / P: 919-871-0800 / F: 919-871-0803 / WWW.FALCONENGINEERS.COM
FALCON ENGINEERING, INC. / 1210 TRINITY ROAD, SUITE 110 CARY, NC 27513 / P: 919-871-0800 / WWW.FALCONENGINEERS.COM
March 23, 2023
Mr. Craig Haden
Geoenvironmental Project Manager
Geotechnical Engineering Unit
North Carolina Department of Transportation
1020 Birch Ridge Drive
Raleigh, NC 27610
Re: UST Closure Report
Description: NC 42 at NC 96 Roundabout
TIP No: W-5704S
WBS: 44850.1.19
NCDOT Parcel No: 01
Owner: Raymond E Earp Jr. Family Trust
Location: 7534 Nc Hwy 42, Selma, Johnston County, NC
NCPIN: 261900-14-7863
Craig:
Falcon is pleased to present the following Underground Storage Tank (UST) Closure Report in support of the above-
mentioned Project. This Report documents the closure by removal of two orphaned 4x8 foot (~750-gallon) USTs.
Laboratory analysis of gasoline and diesel range organics (GRO and DRO) identified GRO at 102 mg/kg and DRO at
182 mg/kg in Sample P1S4 which are above their respective action limits of 50 and 100 mg/kg. Risk-based analysis of
sample P1S4 did not identify constituents above Residential maximum soil contamination concentrations (MSCCs). Risk-
based analysis identified two aromatics (C11-C22 and C9-C10) at 113 and 48.3 mg/kg which is above their soil to
groundwater (SGW) MSCCs of 31 mg/kg for both but below the Residential MSCCs of 469 for both. Falcon recommends
this report be submitted to the State UST section.
Please review this report and advise us if you have any questions or concerns. We appreciate this opportunity to provide
services to you and look forward to partnering with you on future projects. If you have any questions, please give Falcon
a call at (919) 871-0800.
Sincerely,
FALCON ENGINEERING, INC.
Document not considered Final unless all signatures are completed.
Christopher J. Burkhardt Sophia Ross Jeremy R. Hamm, PE
Environmental Services Manager Geotechnical Staff Professional Geotechnical Services Manager PROJECT:REFERENCE:AT TIME OF INVESTIGATION
SEE SHEET 3 FOR PLAN SHEET LAYOUT
CHECKED BY
SUBMITTED BY
DATE
INVESTIGATED BY
DRAWN BY
PERSONNEL
EVANS, T. E.
EVANS, T. E.
EVANS, T. E.
FALCON ENG.
CAUTION NOTICE
THE SITE DIFFERING FROM THOSE INDICATED IN THE SUBSURFACE INFORMATION.
EXTENSION OF TIME FOR ANY REASON RESULTING FROM THE ACTUAL CONDITIONS ENCOUNTERED AT
PROJECT. THE CONTRACTOR SHALL HAVE NO CLAIM FOR ADDITIONAL COMPENSATION OR FOR AN
AS HE DEEMS NECESSARY TO SATISFY HIMSELF AS TO CONDITIONS TO BE ENCOUNTERED ON THE
THE BIDDER OR CONTRACTOR IS CAUTIONED TO MAKE SUCH INDEPENDENT SUBSURFACE INVESTIGATIONS
OPINION OF THE DEPARTMENT AS TO THE TYPE OF MATERIALS AND CONDITIONS TO BE ENCOUNTERED.
SUFFICIENCY OR ACCURACY OF THE INVESTIGATION MADE, NOR THE INTERPRETATIONS MADE, OR
DESIGN INFORMATION ON THIS PROJECT. THE DEPARTMENT DOES NOT WARRANT OR GUARANTEE THE
AND CONSTRUCTION PURPOSES, REFER TO THE CONSTRUCTION PLANS AND DOCUMENTS FOR FINAL
PRELIMINARY ONLY AND IN MANY CASES THE FINAL DESIGN DETAILS ARE DIFFERENT. FOR BIDDING
THE BIDDER OR CONTRACTOR IS CAUTIONED THAT DETAILS SHOWN ON THE SUBSURFACE PLANS ARE
INCLUDING TEMPERATURES, PRECIPITATION AND WIND, AS WELL AS OTHER NON-CLIMATIC FACTORS.
SOIL MOISTURE CONDITIONS MAY VARY CONSIDERABLY WITH TIME ACCORDING TO CLIMATIC CONDITIONS
INVESTIGATIONS ARE AS RECORDED AT THE TIME OF THE INVESTIGATION. THESE WATER LEVELS OR
THE OBSERVED WATER LEVELS OR SOIL MOISTURE CONDITIONS INDICATED IN THE SUBSURFACE
CAN BE RELIED ON ONLY TO THE DEGREE OF RELIABILITY INHERENT IN THE STANDARD TEST METHOD.
WITHIN THE BOREHOLE. THE LABORATORY SAMPLE DATA AND THE IN SITU (IN-PLACE) TEST DATA
REFLECT THE ACTUAL SUBSURFACE CONDITIONS BETWEEN BORINGS OR BETWEEN SAMPLED STRATA
GEOTECHNICAL INTERPRETATION OF ALL AVAILABLE SUBSURFACE DATA AND MAY NOT NECESSARILY
GENERAL SOIL AND ROCK STRATA DESCRIPTIONS AND INDICATED BOUNDARIES ARE BASED ON A
BORING LOGS, ROCK CORES AND SOIL TEST DATA ARE NOT PART OF THE CONTRACT.
GEOTECHNICAL ENGINEERING UNIT AT (919) 707-6850. THE SUBSURFACE PLANS AND REPORTS, FIELD
BE REVIEWED OR INSPECTED IN RALEIGH BY CONTACTING THE N. C. DEPARTMENT OF TRANSPORTATION,
PURPOSES. THE VARIOUS FIELD BORING LOGS, ROCK CORES AND SOIL TEST DATA AVAILABLE MAY
MADE FOR THE PURPOSE OF STUDY, PLANNING AND DESIGN, AND NOT FOR CONSTRUCTION OR PAY
THE SUBSURFACE INFORMATION AND THE SUBSURFACE INVESTIGATION ON WHICH IT IS BASED WERE
CONTENTS
COUNTY
PROJECT DESCRIPTION
STATE OF NORTH CAROLINA
DEPARTMENT OF TRANSPORTATION
DIVISION OF HIGHWAYS
GEOTECHNICAL ENGINEERING UNIT
SUBSURFACE INVESTIGATION
ROADWAY
LINESTATIONPLANPROFILE
CONDITIONS INDICATED HEREIN AND THE ACTUAL CONDITIONS AT THE PROJECT SITE.
FOR INCREASED COMPENSATION OR EXTENSION OF TIME BASED ON DIFFERENCES BETWEEN THE
BY HAVING REQUESTED THIS INFORMATION, THE CONTRACTOR SPECIFICALLY WAIVES ANY CLAIMS2.
OR CONTRACT FOR THE PROJECT.
OF TRANSPORTATION AS ACCURATE NOR IS IT CONSIDERED PART OF THE PLANS, SPECIFICATIONS
THE INFORMATION CONTAINED HEREIN IS NOT IMPLIED OR GUARANTEED BY THE N. C. DEPARTMENT1.
NOTES:
DATESIGNATURE
1STATE PROJECT REFERENCE NO.STATE NO.SHEET SHEETSTOTALN.C.B-5301
PITT
REPLACE BRIDGE NO. 87 OVER
NORFOLK SOUTHERN RAILROAD ON NC 33B-530146015
HAMM, J. R.
MID ATLANTIC DRILLING
-L-13+00 - 35+604-5
-DR1-
-DR2-
-DR3-
6
7
7
7
4
4
5
10+16.94 - 14+68.41
11+09.81 - 19+66.26
10+00 - 15+65
CROSS SECTIONS
LINESTATIONSHEETS
-L-
APPENDICES
APPENDIXTITLESHEETS
A
INVENTORY
23
14+00 - 32+505-14
-DR1-17+50 - 19+5015
CPT LOGS16-23
SEPTEMBER 2015
MMAH .R YME
REJ 039779PROFESSIONALE
NGINEER
N ORTH CARO
LINA
SEAL
03/23/2023
UST CLOSURE REPORT
NCDOT / W-5704S PARCEL NO. 01 / G23010.00 / MARCH 23, 2023 3
TABLE OF CONTENTS
SECTION 1: SITE INFORMATION ................................................................................. 4
1.1 SITE IDENTIFICATION .......................................................................................... 4
1.2 INFORMATION ABOUT CONTACTS ASSOCIATED WITH THE RELEASE ....... 4
1.3 INFORMATION ABOUT RELEASE ....................................................................... 4
SECTION 2: SITE HISTORY AND CHARACTERIZATION ............................................. 5
SECTION 3: CLOSURE PROCEDURE .......................................................................... 6
SECTION 4: SITE INVESTIGATION ............................................................................... 7
4.1 FIELD SCREENING .............................................................................................. 7
4.2 SAMPLE COLLECTION ........................................................................................ 7
4.3 METHODS ............................................................................................................. 7
4.4 ANALYTICAL RESULTS ....................................................................................... 7
SECTION 5: CONCLUSIONS AND RECOMMENDATIONS ........................................... 9
LIST OF ATTACHMENTS
TABLE B-3: SUMMARY OF SOIL SAMPLING RESULTS
VICINITY MAP
USGS TOPO MAP
AERIAL PHOTOGRAPH
PARCEL INFORMATION
SAMPLE LOCATION SKETCH
SAMPLE LOCATION MAP
SITE PHOTOGRAPHS
LABORATORY RESULTS
CONSTRUCTION PERMIT
MANIFESTS
RESUMES
UST CLOSURE REPORT
NCDOT / W-5704S PARCEL NO. 01 / G23010.00 / MARCH 23, 2023 4
SECTION 1: SITE INFORMATION
1.1 SITE IDENTIFICATION
Date of Report: March 23, 2023 Site Risk: TBD
Facility I.D.: 00-0-0000047607 UST Incident Number (if known): Unknown
Site Name: Raymond E Earp Jr. Family Trust Property
Street Address: 7534 NC Hwy 42
City/Town: Selma Zip Code: 27576 County: Johnston
Description of Geographical Data Point (e.g., diesel fill port): Former UST Pit
Location Method (GPS, topographical map, other): GPS
Latitude (decimal degrees): 35.662421 Longitude (decimal degrees): -78.280063
1.2 INFORMATION ABOUT CONTACTS ASSOCIATED WITH THE RELEASE
UST/AST Owner: Unknown Email: Unknown
Address: Unknown Tel: Unknown
UST/AST Operator: Unknown Email: Unknown
Address: Unknown Tel: Unknown
Property Owner: Unknown Email: Unknown
Address: Unknown Tel: Unknown
Property Occupant: Unknown Email: Unknown
Address: Unknown Tel: Unknown
Consultant/Contractor: Mr. Jeremy Hamm P.E. Email: jhamm@falconengineers.com
Address: 1210 Trinity Rd, Suite 110, Cary NC 27513 Tel: 919-302-9758
Analytical Laboratory: Waypoint Analytical State Certification No: 402
Address: 449 Springbrook Rd, P.O. Box 240543, Charlotte, NC 28224 Tel: (800) 529-6364
1.3 INFORMATION ABOUT RELEASE
Date Discovered: Unknown
Estimated Quantity of Release: Unknown
Cause of Release: Unknown
Source of Release (e.g., Dispenser/Piping/UST): UST/System
Sizes and Contents of Tanks or Other Containment
from which the Release Occurred: Unknown
UST CLOSURE REPORT
NCDOT / W-5704S PARCEL NO. 01 / G23010.00 / MARCH 23, 2023 5
SECTION 2: SITE HISTORY AND CHARACTERIZATION
The underground storage tank (UST) owners, operators, contact information, install dates, dates of use, and
last contents are unknown. NCDOT is proposing to construct a roundabout at this intersection. Falcon
Engineering, Inc. (Falcon) completed a Preliminary Site Assessment (PSA) of NCDOT TIP Project W-5704S
Parcel No. 01 dated September 27, 2021. Parcel 01 is Owned by the Raymond E Earp Jr. Trust and is addressed
as 7959 NC 42 in Selma, Johnston County, North Carolina. North Carolina Parcel Identification Number
(NCPIN) 261900-14-7863 corresponds to this parcel. Falcon spoke with the occupant of the north adjoining
residence and was informed this parcel has been vacant for at least the last 20 years to the best of their
knowledge.
As part of the previously prepared PSA, a geophysical investigation was performed on September 13, 2021 to
determine if unknown, metallic underground storage tanks (USTs) were present beneath the survey area. Two
probable USTs were identified. Both probable USTs were approximately 8 feet long and 4 feet wide
(approximately 750-gallons in capacity). Reconnaissance GPR also identified a suspected former product line
extending from the two probable USTs to the former pump island. Evidence of additional buried structures
such as USTs was not observed. Aboveground storage tanks were not observed on-site. Historic releases were
not associated with this site.
Falcon sampled soil around the two probable USTs, the suspect dispenser island, and in the vicinity of proposed
excavations for drainage features on this parcel during the September 2021 PSA. Soils requiring remediation or
special handling during construction were not identified at that time. However, some minor residual petroleum
hydrocarbons below action levels were identified at the tank pit.
UST CLOSURE REPORT
NCDOT / W-5704S PARCEL NO. 01 / G23010.00 / MARCH 23, 2023 6
SECTION 3: CLOSURE PROCEDURE
Prior to removing the USTs Falcon contacted CCI Environmental Services, Inc. (CCI) to subcontract the
excavation, removal, and disposal of the UST and contents. CCI contacted NC One Call to request public
utility locations be marked around the USTs. CCI obtained a UST removal Permit (No. 192852) from the
Johnston County Inspections Department.
Falcon and CCI arrived on site at approximately 9 am Monday February 27, 2023 to begin excavation. Clean
overburden was removed from above the USTs and stockpiled for back fill. The USTs were approximately 1-
foot below ground surface. After the clean overburden was removed, the USTs were vented by cutting a square
hole in the top to allow gasses to escape. The USTs were observed to be filled with stormwater. Petroleum
odors or a sheen on the water were not observed. Once the USTs were vented, the petroleum impacted water
was removed with a vacuum truck. The USTs were then cleaned with a pressure washer to remove residual
petroleum impacted water. The rinse water was also vacuumed out. In total, CCI hauled 1,387 gallons of non-
hazardous petroleum impacted water to their disposal facility in Thomasville, North Carolina.
CCI staff measured the lower explosive limit (LEL) inside both tanks (0.22, 0.28). The Johnston County Fire
Marshal confirmed the LEL was within acceptable range to safely remove the USTs. The USTs were removed
from the pit. The USTs appeared to be in fairly good condition with no obvious holes. Dispenser lines were
also removed. Concrete, bedrock, free product, or groundwater was not observed in the UST pit. Monitoring
wells were not required. The excavation pit was approximately 6 feet deep by 10 feet wide. The USTs were
hauled off-site by CCI to D.H. Griffin in Highpoint, North Carolina for disposal. After samples were collected
the clean overburden was used as back fill along with 18.88 tons of imported ABC stone to fill the void left by
the USTs. The ABC stone was nominally impacted with the excavator bucket. Compaction testing /verification
was not performed during backfilling. Subgrade preparation/stabilization for future construction will be the
responsibility of the contractor. Disposal manifests for the water and USTs are attached.
UST CLOSURE REPORT
NCDOT / W-5704S PARCEL NO. 01 / G23010.00 / MARCH 23, 2023 7
SECTION 4: SITE INVESTIGATION
4.1 FIELD SCREENING
After the USTs were removed from the ground, four selected soil samples (P1S1, P1S2, P1S3, and P1S4) were
collected from beneath the midline of the USTs (two samples per UST). These four samples were bagged and
scanned with a Minirae 3000 Photoionization Detector (PID) for petroleum hydrocarbons in an effort to
determine if over excavation would be required. The instrument was calibrated per manufacturer instructions
prior to use. Samples were placed in a sealed plastic bag for approximately 10 minutes to allow soil hydrocarbons
to reach equilibrium within the headspace prior to scanning with the PID.
The PID readings were below state action levels for GRO and DRO of 50 ppm and 100 ppm respectively. The
results are listed below in parts per million (PPM).
P1S1 0.0
P1S2 0.0
P1S3 2.4
P1S4 15.0
4.2 SAMPLE COLLECTION
After field screening, the four samples collected from beneath the former USTs were placed in laboratory
containers for analysis of gasoline and diesel range organics (GRO/DRO). Risk-based samples were also
collected to be analyzed if GRO or DRO laboratory analysis reported petroleum hydrocarbons above the action
levels. Please see the Attached Sample Location sketch and Map for a visual depiction of the sample locations.
4.3 METHODS
To avoid cross contamination, a new unused pair of non-powdered nitrile gloves was worn while extracting
each sample. Samples were placed in the appropriate laboratory provided containers. The labels on each
container were then completed so that each provided the date and time of sampling, method of analysis, sample
collector, preservative used and sampling location identification. Samples were placed in an ice filled cooler and
transported to the lab. Appropriate chain-of-custody procedures, including the completion of necessary forms,
were followed.
4.4 ANALYTICAL RESULTS
GRO and DRO was reported above their respective action limits of 50 and 100 mg/kg at 102 and 182 mg/kg.
(milligrams per kilogram) respectively in Sample P1S4. GRO was identified at 4.44 mg/kg in sample P1S3.
GRO was not reported above method detection limits in P1S1 or P1S2. DRO concentrations below the action
level were detected in the remaining samples as follows: P1S1: 42.4, P1S2: 13.8 and P1S3: at 15.6 mg/kg.
Sample P1S4 was selected for risk-based analysis using methods 8260, 8270, MADEP EPH, and MADEP
UST CLOSURE REPORT
NCDOT / W-5704S PARCEL NO. 01 / G23010.00 / MARCH 23, 2023 8
VPH. The additional analysis of P1S4 identified ten (10) constituents. Two aromatics (C11-C22 and C9-C10)
were identified at 113 and 48.3 mg/kg which is above their soil to groundwater (SGW) maximum soil
contamination concentrations (MSCCs) of 31 mg/kg for both but below their residential MSCCs. Six
contaminants (acetone, n-Butylbenzene, Carbon Disulfide, 1,2,4-Trimethylbenzene, 1,3,5-Trimethylbenzene,
and Aliphatic C19-C36) were “J” flagged indicating the result is an estimate. These constituents were below
their corresponding SGW MSCCs (aliphatic C19-C36 has a health based level of greater than 100%). Aliphatics
C9-C18 and C9-C12 were also identified above method detection limits but below their corresponding SGW
MSCCs. Detailed sampling results can be found in table B-3 Summary of Soil Sampling Results in Appendix B
Tables.
UST CLOSURE REPORT
NCDOT / W-5704S PARCEL NO. 01 / G23010.00 / MARCH 23, 2023 9
SECTION 5: CONCLUSIONS AND RECOMMENDATIONS
This Underground Storage Tank (UST) Closure Report documents the closure by removal of two orphaned
4x8 foot (~750-gallon) USTs. The findings are as follows:
PID scans of the soils beneath the USTs did not indicate petroleum hydrocarbons above action levels.
Laboratory analysis of GRO and DRO identified GRO at 102 mg/kg and DRO at 182 mg/kg in
Sample P1S4 which are above their respective action limits of 50 and 100 mg/kg.
Risk-based analysis of sample P1S4 did not identify constituents above Residential MSCCs.
Risk-based analysis identified two aromatics (C11-C22 and C9-C10) at 113 and 48.3 mg/kg which is
above their soil to groundwater (SGW) maximum soil contamination concentrations (MSCCs) of 31
mg/kg for both but below the Residential MSCCs of 469 for both.
Falcon recommends this report be submitted to the State UST section.
UST CLOSURE REPORT
NCDOT / W-5704S PARCEL NO. 01 / G23010.00 / MARCH 23, 2023 10
TABLE B-3: SUMMARY OF SOIL SAMPLING RESULTS (1 of 2)
Revision Date: Incident Number and Name: Facility ID#: 00-0-0000047607
Analytical Method (e.g., VOC by EPA 8260) -> GRO DRO 8260D 8260D 8260D 8260D 8260D
Contaminant of Concern -> Gasoline Range Organics Diesel Range Organics Acetone n-Butylbenzene Carbon Disulfide 1,2,4-Trimethylbenzene 1,3,5-Trimethylbenzene Sample ID Date Collected (mm/dd/yy)
Source Area (e.g., Tank Pit)
Sample Depth (ft BGS)
Incident Phase (IAA, LSA, etc.)
P1S1 02/27/23 Tank Pit 6 Closure < 42.4 - - - - -
P1S2 02/27/23 Tank Pit 6 Closure < 13.8 - - - - -
P1S3 02/27/23 Tank Pit 6 Closure 4.44J 15.6 - - - - -
P1S4 02/27/23 Tank Pit 6 Closure 102 182 0.008J 0.001J 0.001J 0.003J 0.001J
Minimum Reporting Limit (mg/kg) 2.60 5.53 0.003 0.0006 0.0008 0.0006 0.0007
Soil to Groundwater MSCC (mg/kg) - - 24 4.3 4.3 8.5 8.3
Residential MSCC (mg/kg) - - 14000 626 1564 782 782
Industrial/Commercial MSCC (mg/kg) - - 360000 16350 40880 20440 20440
Detection limits for contaminants not detected are indicated by a < symbol (e.g., < 1, 10, 42) MSCC = maximum soil contaminant concentration ft. BGS = feet below ground surface Results are reported in mg/kg. (milligrams per kilogram) J= estimated value Bold = concentration is above the Soil to Groundwater MSCC - Not analyzed
UST CLOSURE REPORT
NCDOT / W-5704S PARCEL NO. 01 / G23010.00 / MARCH 23, 2023 11
TABLE B-3: SUMMARY OF SOIL SAMPLING RESULTS (1 of 2)
Revision Date: Incident Number and Name: Facility ID#: 00-0-0000047607
Analytical Method (e.g., VOC by EPA 8260) -> EPH EPH EPH VPH VPH
Contaminant of Concern -> Aliphatic C9-C18 Aliphatic C19-C36 Aromatic C11-C22 Aliphatic C9-C12 Aromatic C9-C10 Sample ID Date Collected (mm/dd/yy)
Source Area (e.g., Tank Pit)
Sample Depth (ft BGS)
Incident Phase (IAA, LSA, etc.)
P1S1 02/27/23 Tank Pit 6 Closure - - - - -
P1S2 02/27/23 Tank Pit 6 Closure - - - - -
P1S3 02/27/23 Tank Pit 6 Closure - - - - -
P1S4 02/27/23 Tank Pit 6 Closure 365 61.9J 113 163 48.3
Minimum Reporting Limit (mg/kg) 11.6 15.4 17.9 5.72 0.782
Soil to Groundwater MSCC (mg/kg) 540 # 31 540 31
Residential MSCC (mg/kg) 1500 31000 469 1500 469
Industrial/Commercial MSCC (mg/kg) 40000 810000 12264 40000 12264
Detection limits for contaminants not detected are indicated by a < symbol (e.g., < 1, 10, 42) MSCC = maximum soil contaminant concentration ft. BGS = feet below ground surface Results are reported in mg/kg. (milligrams per kilogram) J= estimated value Bold = concentration is above the Soil to Groundwater MSCC # Health based level > 100% - Not analyzed
NC 42 AT NC 96 ROUNDABOUT
UST CLOSURE
TIP NO:W-5704S WBS:44850.1.19
SELMA, JOHNSTON COUNTY
VICINITY MAP
Project No.:G21044.00Date: March 2023Source:Google Maps
SITE
NC 42 AT NC 96 ROUNDABOUT
UST CLOSURE
TIP NO:W-5704S WBS:44850.1.19
USGS “FLOWERS, NC” 2019 TOPOGRAPHIC MAP
Project No.:G21044.00Date: March 2023Source: USGS Topoview website https://ngmdb.usgs.gov/topoview/
SITE
NC 42 AT NC 96 ROUNDABOUT
UST CLOSURE
TIP NO:W-5704S WBS:44850.1.19
2018 AERIAL PHOTOGRAPH
Project No.:G21044.00Date: March 2023Source:Google Earth
NC 42 AT NC 96 ROUNDABOUT
UST CLOSURE
TIP NO:W-5704S WBS:44850.1.19
Parcel Information
Project No.:G21044.00Date: March 2023Source:Johnston County GIS Websitehttps://mapclick6.johnstonnc.com/mapclick/MapClick4/
UST Location
NC 42 AT NC 96 ROUNDABOUT
UST CLOSURE
TIP NO:W-5704S WBS:44850.1.19
UST Sample Location sketch
Project No.:G21044.00Date: March 2023Source:Johnston County GIS Websitehttps://mapclick6.johnstonnc.com/mapclick/MapClick4/
NC 42 NC 96Not to Scale
P1S1
P1S2
P1S3
P1S4
BL-103
S S
GUY
GUY
GUY
S
GUY
GUY
GUYGUY
GUY
GUY
GUYGUY
GUY
GUYSS S S
SSSSSSS18" RCPINV=218.04'
INV=217.47'SHRINE
FOM
PT
N 09°06'31" E210.00'N 88°37'47" E
179.68'
WOODS
WOODS
WOODS
WOODS
DB 4576 PG 279MARY E MOORE WORLEY
RAYMOND E EARP JR FAMILY TRUST
TO R/WEPK .63'
TO R/WECM .37'
ECM
CONC
CONC
BST
BST
4'WWF TC
HH
C THHWCMWCM15
15-L- PC Sta. 13+58.97
-L- PRC Sta. 14+07.58
-L- PCC Sta. 17+09.81
-L- PRC Sta. 16+56.08
-Y- PT Sta. 17+22.38
-Y- PRC Sta. 16+62.39
-L- PRC Sta. 15+28.77
-RAB- PT Sta. 14+71.23-RAB- PC Sta. 10+00.00 =-L- POC Sta. 16+09.60 =
-RAB- POC Sta. 10+94.63-Y- POC Sta. 16+15.94 =
-RAB- POC Sta. 12+37.58-L- POC Sta. 14+59.04 =
R = 253.00'T = 62.22'L = 122.02'DPI Sta 14+76.15-Y- CURVE DATA
006
0
0
0 0100200260240200
1
0
0
0
0
005
000
025
025
025025025025020
020020020010
010010010
006 029029
1
65'+00 -L-
60'+25 -L-
45'+50 -Y-
EX. R/W+67.65 -L-
38'+25 -L-
45'+75 -L-
80'+50 -Y-EX. R/W+50 -Y-
EX. R/W+65.16 -L-
60'+00 -L-70'+75 -Y-
45'+25 -Y-
65'+75 -Y-
75'+50 -Y-
45'+00 -Y-
EX. R/W+75 -Y-
50'+50 -Y-
55'+50 -Y-
45'+50 -L-
P1S4
P1S3
P1S2
P1S1 NAD 83/ NSRS 2007NOTES:
0
FEET
SAMPLES WERE COLLECTED FROM 6 FEET BGS.
50 100
FALCON PROJECT NO. G23010.00
WBS: 44850.1.19 | TIP: W-5704S
JOHNSTON COUNTY, NC
NC42 AT NC96 ROUNDABOUT
SAMPLE LOCATION PLAN
CARY, NC 27513
1210 TRINITY ROAD, SUITE 110
FALCON ENGINEERING, INC.
www.falconengineers.com
PHONE: 919.871.0800
F
F
F
F
C
C
C
C
C
C
C
C
C C
C
Photograph No. 1: General view of the UST Pit and dispenser island.
Photograph No. 2: General view of the two removed USTs.
NC 42 AT NC 96 ROUNDABOUT
UST CLOSURE
TIP NO:W-5704S WBS:44850.1.19
Site Photographs
Photograph No. 3: General view of the removed dispenser Island and product lines.
Photograph No. 4: General view of the pit and dispenser Island after back filling.
NC 42 AT NC 96 ROUNDABOUT
UST CLOSURE
TIP NO:W-5704S WBS:44850.1.19
Site Photographs
Laboratory's liability in any claim relating to analyses performed shall be limited to, at laboratory's option, repeating the
analysis in question at laboratory's expense, or the refund of the charges paid for performance of said analysis.
3/15/2023
Falcon Engineering Christopher Burkhardt
1210 Trinity Road Suite 110
Cary, NC, 27513
Ref: Analytical Testing Lab Report Number: 23-059-0009
Client Project Description: W57045
Dear Christopher Burkhardt:
Waypoint Analytical, LLC (Charlotte) received sample(s) on 2/28/2023 for the analyses presented in the following report.
The above referenced project has been analyzed per your instructions. The analyses were performed in
accordance with the applicable analytical method.
The analytical data has been validated using standard quality control measures performed as required by the analytical method. Quality Assurance, method validations, instrumentation maintenance and calibration for all
parameters were performed in accordance with guidelines established by the USEPA (including 40 CFR 136 Method Update Rule May 2021) unless otherwise indicated. Certain parameters (chlorine, pH, dissolved oxygen, sulfite...) are required to be analyzed within 15 minutes of sampling. Usually, but not always, any field parameter analyzed at the laboratory is outside of this holding time. Refer to sample analysis time for confirmation of holding time compliance.
The results are shown on the attached Report of Analysis(s). Results for solid matrices are reported on an as-
received basis unless otherwise indicated. This report shall not be reproduced except in full and relates only to the samples included in this report. Please do not hesitate to contact me or client services if you have any questions or need additional information.
Sincerely,
Angela D Overcash Senior Project Manager
Page 1 of 43
Certification Summary
Laboratory ID: WP CNC: Waypoint Analytical Carolina, Inc. (C), Charlotte, NC
State Program Lab ID Expiration Date
07/31/202337735State ProgramNorth Carolina
12/31/2023402State ProgramNorth Carolina
07/31/202399012State ProgramSouth Carolina
12/31/202299012State ProgramSouth Carolina
Page 1 of 1 00016/23-059-0009
Page 2 of 43
Report Number:
Sample Summary Table
Client Project Description:
23-059-0009
W57045
Lab No Client Sample ID Matrix Date Collected Date Received
02/27/2023 12:00Solids 89929 P1S1 02/28/2023 12:00
02/27/2023 12:08Solids 89930 P1S2 02/28/2023 12:00
02/27/2023 12:23Solids 89931 P1S3 02/28/2023 12:00
02/27/2023 12:38Solids 89932 P1S4 02/28/2023 12:00
Page 3 of 43
Summary of Detected Analytes
QualifiersAnalyzedUnitsResult
Report Number:
Client Sample ID
Method Parameters
Lab Sample ID
23-059-0009
Report Limit
Project:W57045
V 89929P1S1
42.4 03/07/2023 11:008015C DRO Diesel Range Organics (C10-C28)mg/Kg - dry 5.71
18.6 03/02/2023 17:42SW-DRYWT Moisture %
V 89930P1S2
13.8 03/07/2023 11:228015C DRO Diesel Range Organics (C10-C28)mg/Kg - dry 5.53
15.9 03/02/2023 17:42SW-DRYWT Moisture %
V 89931P1S3
15.6 03/07/2023 11:438015C DRO Diesel Range Organics (C10-C28)mg/Kg - dry 5.96
J4.44 03/01/2023 15:568015C GRO Gasoline Range Organics (C6-C10)mg/Kg - dry 2.65
22.0 03/02/2023 17:42SW-DRYWT Moisture %
V 89932P1S4
182 03/07/2023 12:048015C DRO Diesel Range Organics (C10-C28)mg/Kg - dry 5.83
102 03/01/2023 16:248015C GRO Gasoline Range Organics (C6-C10)mg/Kg - dry 2.60
J0.008 03/08/2023 12:468260DAcetonemg/Kg - dry 0.003
J0.001 03/08/2023 12:468260Dn-Butylbenzene mg/Kg - dry 0.0006
J0.001 03/08/2023 12:468260DCarbon Disulfide mg/Kg - dry 0.0008
J0.003 03/08/2023 12:468260D1,2,4-Trimethylbenzene mg/Kg - dry 0.0006
J0.001 03/08/2023 12:468260D1,3,5-Trimethylbenzene mg/Kg - dry 0.0007
202 03/13/2023 16:09MADEP-EPH Aliphatic C9-C18 mg/Kg - dry 11.6
J61.9 03/13/2023 16:09MADEP-EPH Aliphatic C19-C36 mg/Kg - dry 15.4
113 03/13/2023 16:09MADEP-EPH Aromatic C11-C22 mg/Kg - dry 17.9
163 03/08/2023 14:51MADEP-VPH Aliphatic C9-C12 mg/Kg - dry 5.72
48.3 03/08/2023 14:51MADEP-VPH Aromatic C9-C10 mg/Kg - dry 0.782
20.3 03/02/2023 17:42SW-DRYWT Moisture %
Page 4 of 43
Client: Falcon Engineering CASE NARRATIVE
Project: W57045 Lab Report Number: 23-059-0009
Date: 3/15/2023
Semivolatile Organic Compounds - GC/MS Method 8270E Analyte: Aniline QC Batch No: V30753/V30730
Recovery for the LCS exceeded the upper acceptance limit. However, all sample results associated with the batch are below the MQL, so this high bias had no impact upon the client data. The results are considered to be
acceptable.
Sample 89932 (P1S4) Analyte: Bis(2-chloroethyl)ether
QC Batch No: V30753/V30730 Relative Percent Difference (RPD) for the duplicate analysis was outside of the allowable QC limits.
Page 5 of 43
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 27513
23-059-0009
00122
Suite 110
Falcon Engineering
1210 Trinity Road
Christopher Burkhardt
Cary
Received : 02/28/2023
W57045
Report Date : 03/15/2023
Sample ID :
Lab No :
Sampled:P1S1
89929 Matrix:
2/27/2023 12:00
Solids
Test Results Units MDL MQL By Analytical
Method
Date / Time
Analyzed
DF
18.6 %Moisture 1 03/02/23 17:42 SW-DRYWTAMB
Qualifiers/
Definitions
Estimated valueJDilution FactorDF
Method Quantitation LimitMQL
Page 6 of 43
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 27513
23-059-0009
00122
Suite 110
Falcon Engineering
1210 Trinity Road
Christopher Burkhardt
Cary
Received : 02/28/2023
W57045
Report Date : 03/15/2023
Sample ID :
Lab No :
Sampled:P1S1
89929 Matrix:
2/27/2023 12:00
Solids
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
3546
8015C DRO Prep Batch(es):V30498 03/06/23 10:30
42.4 mg/Kg - dry 5.71 12.3Diesel Range Organics (C10-C28)1 03/07/23 11:00 V30521AMP
8015C DROSurrogate: OTP Surrogate 88.7 Limits: 31-123%03/07/23 11:001 AMP
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
5035 MED
8015C GRO Prep Batch(es):V30320 03/01/23 08:00
<2.54 mg/Kg - dry 2.54 6.14Gasoline Range Organics (C6-C10)50 03/01/23 14:59 V30321TBL
8015C GROSurrogate: a,a,a-Trifluorotoluene 110 Limits: 50-137%03/01/23 14:5950 TBL
Qualifiers/
Definitions
Estimated valueJDilution FactorDF
Method Quantitation LimitMQL
Page 7 of 43
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 27513
23-059-0009
00122
Suite 110
Falcon Engineering
1210 Trinity Road
Christopher Burkhardt
Cary
Received : 02/28/2023
W57045
Report Date : 03/15/2023
Sample ID :
Lab No :
Sampled:P1S2
89930 Matrix:
2/27/2023 12:08
Solids
Test Results Units MDL MQL By Analytical
Method
Date / Time
Analyzed
DF
15.9 %Moisture 1 03/02/23 17:42 SW-DRYWTAMB
Qualifiers/
Definitions
Estimated valueJDilution FactorDF
Method Quantitation LimitMQL
Page 8 of 43
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 27513
23-059-0009
00122
Suite 110
Falcon Engineering
1210 Trinity Road
Christopher Burkhardt
Cary
Received : 02/28/2023
W57045
Report Date : 03/15/2023
Sample ID :
Lab No :
Sampled:P1S2
89930 Matrix:
2/27/2023 12:08
Solids
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
3546
8015C DRO Prep Batch(es):V30498 03/06/23 10:30
13.8 mg/Kg - dry 5.53 11.9Diesel Range Organics (C10-C28)1 03/07/23 11:22 V30521AMP
8015C DROSurrogate: OTP Surrogate 91.0 Limits: 31-123%03/07/23 11:221 AMP
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
5035 MED
8015C GRO Prep Batch(es):V30320 03/01/23 08:00
<2.46 mg/Kg - dry 2.46 5.95Gasoline Range Organics (C6-C10)50 03/01/23 15:28 V30321TBL
8015C GROSurrogate: a,a,a-Trifluorotoluene 111 Limits: 50-137%03/01/23 15:2850 TBL
Qualifiers/
Definitions
Estimated valueJDilution FactorDF
Method Quantitation LimitMQL
Page 9 of 43
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 27513
23-059-0009
00122
Suite 110
Falcon Engineering
1210 Trinity Road
Christopher Burkhardt
Cary
Received : 02/28/2023
W57045
Report Date : 03/15/2023
Sample ID :
Lab No :
Sampled:P1S3
89931 Matrix:
2/27/2023 12:23
Solids
Test Results Units MDL MQL By Analytical
Method
Date / Time
Analyzed
DF
22.0 %Moisture 1 03/02/23 17:42 SW-DRYWTAMB
Qualifiers/
Definitions
Estimated valueJDilution FactorDF
Method Quantitation LimitMQL
Page 10 of 43
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 27513
23-059-0009
00122
Suite 110
Falcon Engineering
1210 Trinity Road
Christopher Burkhardt
Cary
Received : 02/28/2023
W57045
Report Date : 03/15/2023
Sample ID :
Lab No :
Sampled:P1S3
89931 Matrix:
2/27/2023 12:23
Solids
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
3546
8015C DRO Prep Batch(es):V30498 03/06/23 10:30
15.6 mg/Kg - dry 5.96 12.8Diesel Range Organics (C10-C28)1 03/07/23 11:43 V30521AMP
8015C DROSurrogate: OTP Surrogate 86.5 Limits: 31-123%03/07/23 11:431 AMP
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
5035 MED
8015C GRO Prep Batch(es):V30320 03/01/23 08:00
4.44 J mg/Kg - dry 2.65 6.41Gasoline Range Organics (C6-C10)50 03/01/23 15:56 V30321TBL
8015C GROSurrogate: a,a,a-Trifluorotoluene 78.2 Limits: 50-137%03/01/23 15:5650 TBL
Qualifiers/
Definitions
Estimated valueJDilution FactorDF
Method Quantitation LimitMQL
Page 11 of 43
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 27513
23-059-0009
00122
Suite 110
Falcon Engineering
1210 Trinity Road
Christopher Burkhardt
Cary
Received : 02/28/2023
W57045
Report Date : 03/15/2023
Sample ID :
Lab No :
Sampled:P1S4
89932 Matrix:
2/27/2023 12:38
Solids
Test Results Units MDL MQL By Analytical
Method
Date / Time
Analyzed
DF
20.3 %Moisture 1 03/02/23 17:42 SW-DRYWTAMB
Qualifiers/
Definitions
Estimated valueJDilution FactorDF
Method Quantitation LimitMQL
Page 12 of 43
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 27513
23-059-0009
00122
Suite 110
Falcon Engineering
1210 Trinity Road
Christopher Burkhardt
Cary
Received : 02/28/2023
W57045
Report Date : 03/15/2023
Sample ID :
Lab No :
Sampled:P1S4
89932 Matrix:
2/27/2023 12:38
Solids
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
3546
8015C DRO Prep Batch(es):V30498 03/06/23 10:30
182 mg/Kg - dry 5.83 12.5Diesel Range Organics (C10-C28)1 03/07/23 12:04 V30521AMP
8015C DROSurrogate: OTP Surrogate 98.5 Limits: 31-123%03/07/23 12:041 AMP
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
5035 MED
8015C GRO Prep Batch(es):V30320 03/01/23 08:00
102 mg/Kg - dry 2.60 6.27Gasoline Range Organics (C6-C10)50 03/01/23 16:24 V30321TBL
8015C GROSurrogate: a,a,a-Trifluorotoluene 108 Limits: 50-137%03/01/23 16:2450 TBL
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
5035
8260D Prep Batch(es):V30593 03/08/23 08:00
0.008 J
mg/Kg - dry 0.003 0.025
Acetone 1 03/08/23 12:46 V30594TBL
<0.001 mg/Kg - dry 0.001 0.025Acrolein 1 03/08/23 12:46 V30594TBL
<0.0009 mg/Kg - dry 0.0009 0.025Acrylonitrile 1 03/08/23 12:46 V30594TBL
<0.0007 mg/Kg - dry 0.0007 0.006Benzene 1 03/08/23 12:46 V30594TBL
<0.0006 mg/Kg - dry 0.0006 0.006Bromobenzene 1 03/08/23 12:46 V30594TBL
<0.001 mg/Kg - dry 0.001 0.006Bromochloromethane 1 03/08/23 12:46 V30594TBL
<0.001 mg/Kg - dry 0.001 0.006Bromodichloromethane 1 03/08/23 12:46 V30594TBL
<0.001 mg/Kg - dry 0.001 0.006Bromoform 1 03/08/23 12:46 V30594TBL
<0.002 mg/Kg - dry 0.002 0.012Bromomethane 1 03/08/23 12:46 V30594TBL
Qualifiers/
Definitions
Estimated valueJDilution FactorDF
Method Quantitation LimitMQL
Page 13 of 43
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 27513
23-059-0009
00122
Suite 110
Falcon Engineering
1210 Trinity Road
Christopher Burkhardt
Cary
Received : 02/28/2023
W57045
Report Date : 03/15/2023
Sample ID :
Lab No :
Sampled:P1S4
89932 Matrix:
2/27/2023 12:38
Solids
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
5035
8260D Prep Batch(es):V30593 03/08/23 08:00
0.001 J mg/Kg - dry 0.0006 0.006n-Butylbenzene 1 03/08/23 12:46 V30594TBL
<0.0007 mg/Kg - dry 0.0007 0.006
sec-Butyl benzene 1 03/08/23 12:46 V30594TBL
<0.0006 mg/Kg - dry 0.0006 0.006tert-Butyl benzene 1 03/08/23 12:46 V30594TBL
0.001 J mg/Kg - dry 0.0008 0.006Carbon Disulfide 1 03/08/23 12:46 V30594TBL
<0.001 mg/Kg - dry 0.001 0.006Carbon Tetrachloride 1 03/08/23 12:46 V30594TBL
<0.0008 mg/Kg - dry 0.0008 0.006Chlorobenzene 1 03/08/23 12:46 V30594TBL
<0.001 mg/Kg - dry 0.001 0.006Chlorodibromomethane 1 03/08/23 12:46 V30594TBL
<0.001 mg/Kg - dry 0.001 0.012Chloroethane 1 03/08/23 12:46 V30594TBL
<0.001 mg/Kg - dry 0.001 0.006
Chloroform 1 03/08/23 12:46 V30594TBL
<0.0008 mg/Kg - dry 0.0008 0.012Chloromethane 1 03/08/23 12:46 V30594TBL
<0.0006 mg/Kg - dry 0.0006 0.0062-Chlorotoluene 1 03/08/23 12:46 V30594TBL
<0.0005 mg/Kg - dry 0.0005 0.0064-Chlorotoluene 1 03/08/23 12:46 V30594TBL
<0.0009 mg/Kg - dry 0.0009 0.006Di-Isopropyl Ether (DIPE)1 03/08/23 12:46 V30594TBL
<0.0006 mg/Kg - dry 0.0006 0.0121,2-Dibromo-3-Chloropropane 1 03/08/23 12:46 V30594TBL
<0.0007 mg/Kg - dry 0.0007 0.0061,2-Dibromoethane 1 03/08/23 12:46 V30594TBL
<0.0007 mg/Kg - dry 0.0007 0.006Dibromomethane 1 03/08/23 12:46 V30594TBL
<0.0004 mg/Kg - dry 0.0004 0.0061,2-Dichlorobenzene 1 03/08/23 12:46 V30594TBL
<0.0005 mg/Kg - dry 0.0005 0.0061,3-Dichlorobenzene 1 03/08/23 12:46 V30594TBL
<0.0008 mg/Kg - dry 0.0008 0.0061,4-Dichlorobenzene 1 03/08/23 12:46 V30594TBL
<0.001 mg/Kg - dry 0.001 0.012Dichlorodifluoromethane 1 03/08/23 12:46 V30594TBL
<0.001 mg/Kg - dry 0.001 0.0061,1-Dichloroethane 1 03/08/23 12:46 V30594TBL
<0.001 mg/Kg - dry 0.001 0.0061,2-Dichloroethane 1 03/08/23 12:46 V30594TBL
Qualifiers/
Definitions
Estimated valueJDilution FactorDF
Method Quantitation LimitMQL
Page 14 of 43
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 27513
23-059-0009
00122
Suite 110
Falcon Engineering
1210 Trinity Road
Christopher Burkhardt
Cary
Received : 02/28/2023
W57045
Report Date : 03/15/2023
Sample ID :
Lab No :
Sampled:P1S4
89932 Matrix:
2/27/2023 12:38
Solids
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
5035
8260D Prep Batch(es):V30593 03/08/23 08:00
<0.0009 mg/Kg - dry 0.0009 0.0061,1-Dichloroethene 1 03/08/23 12:46 V30594TBL
<0.0010 mg/Kg - dry 0.0010 0.006
cis-1,2-Dichloroethene 1 03/08/23 12:46 V30594TBL
<0.001 mg/Kg - dry 0.001 0.006trans-1,2-Dichloroethene 1 03/08/23 12:46 V30594TBL
<0.0006 mg/Kg - dry 0.0006 0.0061,2-Dichloropropane 1 03/08/23 12:46 V30594TBL
<0.0007 mg/Kg - dry 0.0007 0.0061,3-Dichloropropane 1 03/08/23 12:46 V30594TBL
<0.001 mg/Kg - dry 0.001 0.0062,2-Dichloropropane 1 03/08/23 12:46 V30594TBL
<0.0010 mg/Kg - dry 0.0010 0.0061,1-Dichloropropene 1 03/08/23 12:46 V30594TBL
<0.0007 mg/Kg - dry 0.0007 0.006cis-1,3-Dichloropropene 1 03/08/23 12:46 V30594TBL
<0.001 mg/Kg - dry 0.001 0.006
trans-1,3-Dichloropropene 1 03/08/23 12:46 V30594TBL
<0.0007 mg/Kg - dry 0.0007 0.006Ethylbenzene 1 03/08/23 12:46 V30594TBL
<0.001 mg/Kg - dry 0.001 0.062Ethyl Tertiary Butyl Ether (ETBE)1 03/08/23 12:46 V30594TBL
<0.0010 mg/Kg - dry 0.0010 0.012Hexachlorobutadiene 1 03/08/23 12:46 V30594TBL
<0.0008 mg/Kg - dry 0.0008 0.012n-Hexane 1 03/08/23 12:46 V30594TBL
<0.0008 mg/Kg - dry 0.0008 0.0252-Hexanone 1 03/08/23 12:46 V30594TBL
<0.0006 mg/Kg - dry 0.0006 0.006Isopropylbenzene 1 03/08/23 12:46 V30594TBL
<0.001 mg/Kg - dry 0.001 0.0064-Isopropyl toluene 1 03/08/23 12:46 V30594TBL
<0.0008 mg/Kg - dry 0.0008 0.025Methyl Ethyl Ketone (MEK)1 03/08/23 12:46 V30594TBL
<0.0008 mg/Kg - dry 0.0008 0.006Methyl tert-butyl ether (MTBE)1 03/08/23 12:46 V30594TBL
<0.018 mg/Kg - dry 0.018 0.0254-Methyl-2-Pentanone 1 03/08/23 12:46 V30594TBL
<0.001 mg/Kg - dry 0.001 0.012Methylene Chloride 1 03/08/23 12:46 V30594TBL
<0.001 mg/Kg - dry 0.001 0.012Naphthalene 1 03/08/23 12:46 V30594TBL
<0.0007 mg/Kg - dry 0.0007 0.006n-Propylbenzene 1 03/08/23 12:46 V30594TBL
Qualifiers/
Definitions
Estimated valueJDilution FactorDF
Method Quantitation LimitMQL
Page 15 of 43
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 27513
23-059-0009
00122
Suite 110
Falcon Engineering
1210 Trinity Road
Christopher Burkhardt
Cary
Received : 02/28/2023
W57045
Report Date : 03/15/2023
Sample ID :
Lab No :
Sampled:P1S4
89932 Matrix:
2/27/2023 12:38
Solids
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
5035
8260D Prep Batch(es):V30593 03/08/23 08:00
<0.001 mg/Kg - dry 0.001 0.006Styrene 1 03/08/23 12:46 V30594TBL
<0.001 mg/Kg - dry 0.001 0.006
1,1,1,2-Tetrachloroethane 1 03/08/23 12:46 V30594TBL
<0.0004 mg/Kg - dry 0.0004 0.0061,1,2,2-Tetrachloroethane 1 03/08/23 12:46 V30594TBL
<0.001 mg/Kg - dry 0.001 0.006Tetrachloroethene 1 03/08/23 12:46 V30594TBL
<0.0008 mg/Kg - dry 0.0008 0.006Toluene 1 03/08/23 12:46 V30594TBL
<0.0007 mg/Kg - dry 0.0007 0.0121,2,3-Trichlorobenzene 1 03/08/23 12:46 V30594TBL
<0.0008 mg/Kg - dry 0.0008 0.0121,2,4-Trichlorobenzene 1 03/08/23 12:46 V30594TBL
<0.001 mg/Kg - dry 0.001 0.0061,1,1-Trichloroethane 1 03/08/23 12:46 V30594TBL
<0.0006 mg/Kg - dry 0.0006 0.006
1,1,2-Trichloroethane 1 03/08/23 12:46 V30594TBL
<0.001 mg/Kg - dry 0.001 0.006Trichloroethene 1 03/08/23 12:46 V30594TBL
<0.002 mg/Kg - dry 0.002 0.012Trichlorofluoromethane 1 03/08/23 12:46 V30594TBL
<0.0009 mg/Kg - dry 0.0009 0.0061,2,3-Trichloropropane 1 03/08/23 12:46 V30594TBL
0.003 J mg/Kg - dry 0.0006 0.0061,2,4-Trimethylbenzene 1 03/08/23 12:46 V30594TBL
0.001 J mg/Kg - dry 0.0007 0.0061,3,5-Trimethylbenzene 1 03/08/23 12:46 V30594TBL
<0.0006 mg/Kg - dry 0.0006 0.012Vinyl Acetate 1 03/08/23 12:46 V30594TBL
<0.0006 mg/Kg - dry 0.0006 0.012Vinyl Chloride 1 03/08/23 12:46 V30594TBL
<0.0006 mg/Kg - dry 0.0006 0.006o-Xylene 1 03/08/23 12:46 V30594TBL
<0.001 mg/Kg - dry 0.001 0.012m,p-Xylene 1 03/08/23 12:46 V30594TBL
<0.0006 mg/Kg - dry 0.0006 0.006Xylene (Total)1 03/08/23 12:46 V30594
Surrogate: 4-Bromofluorobenzene 89.5 Limits: 70-130%03/08/23 12:461 TBL V30594
Surrogate: Dibromofluoromethane 105 Limits: 84-123%03/08/23 12:461 TBL V30594
Surrogate: Toluene-d8 103 Limits: 76-129%03/08/23 12:461 TBL V30594
Qualifiers/
Definitions
Estimated valueJDilution FactorDF
Method Quantitation LimitMQL
Page 16 of 43
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 27513
23-059-0009
00122
Suite 110
Falcon Engineering
1210 Trinity Road
Christopher Burkhardt
Cary
Received : 02/28/2023
W57045
Report Date : 03/15/2023
Sample ID :
Lab No :
Sampled:P1S4
89932 Matrix:
2/27/2023 12:38
Solids
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
3546
8270E Prep Batch(es):V30730 03/13/23 10:00
<0.145 mg/Kg - dry 0.145 0.828Acenaphthene 1 03/14/23 10:53 V30753JMV
<0.131 mg/Kg - dry 0.131 0.828
Acenaphthylene 1 03/14/23 10:53 V30753JMV
<0.190 mg/Kg - dry 0.190 0.828Aniline 1 03/14/23 10:53 V30753JMV
<0.179 mg/Kg - dry 0.179 0.828Anthracene 1 03/14/23 10:53 V30753JMV
<0.174 mg/Kg - dry 0.174 0.828Benzo(a)anthracene 1 03/14/23 10:53 V30753JMV
<0.184 mg/Kg - dry 0.184 0.828Benzo(a)pyrene 1 03/14/23 10:53 V30753JMV
<0.183 mg/Kg - dry 0.183 0.828Benzo(b)fluoranthene 1 03/14/23 10:53 V30753JMV
<0.170 mg/Kg - dry 0.170 0.828Benzo(g,h,i)perylene 1 03/14/23 10:53 V30753JMV
<0.171 mg/Kg - dry 0.171 0.828
Benzo(k)fluoranthene 1 03/14/23 10:53 V30753JMV
<0.727 mg/Kg - dry 0.727 2.51Benzoic Acid 1 03/14/23 10:53 V30753JMV
<0.131 mg/Kg - dry 0.131 0.828Benzyl alcohol 1 03/14/23 10:53 V30753JMV
<0.148 mg/Kg - dry 0.148 0.828Bis(2-Chloroethoxy)methane 1 03/14/23 10:53 V30753JMV
<0.134 mg/Kg - dry 0.134 0.828Bis(2-Chloroethyl)ether 1 03/14/23 10:53 V30753JMV
<0.170 mg/Kg - dry 0.170 0.414Bis(2-Chloroisopropyl)ether 1 03/14/23 10:53 V30753JMV
<0.150 mg/Kg - dry 0.150 0.828Bis(2-ethylhexyl)phthalate 1 03/14/23 10:53 V30753JMV
<0.136 mg/Kg - dry 0.136 0.8284-Bromophenyl phenyl ether 1 03/14/23 10:53 V30753JMV
<0.141 mg/Kg - dry 0.141 0.414Butyl benzyl phthalate 1 03/14/23 10:53 V30753JMV
<0.115 mg/Kg - dry 0.115 0.8284-Chloro-3-methylphenol 1 03/14/23 10:53 V30753JMV
<0.140 mg/Kg - dry 0.140 0.4144-Chloroaniline 1 03/14/23 10:53 V30753JMV
<0.145 mg/Kg - dry 0.145 0.8282-Chloronaphthalene 1 03/14/23 10:53 V30753JMV
<0.123 mg/Kg - dry 0.123 0.8282-Chlorophenol 1 03/14/23 10:53 V30753JMV
<0.158 mg/Kg - dry 0.158 1.254-Chlorophenyl phenyl ether 1 03/14/23 10:53 V30753JMV
Qualifiers/
Definitions
Estimated valueJDilution FactorDF
Method Quantitation LimitMQL
Page 17 of 43
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 27513
23-059-0009
00122
Suite 110
Falcon Engineering
1210 Trinity Road
Christopher Burkhardt
Cary
Received : 02/28/2023
W57045
Report Date : 03/15/2023
Sample ID :
Lab No :
Sampled:P1S4
89932 Matrix:
2/27/2023 12:38
Solids
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
3546
8270E Prep Batch(es):V30730 03/13/23 10:00
<0.178 mg/Kg - dry 0.178 0.828Chrysene 1 03/14/23 10:53 V30753JMV
<0.288 mg/Kg - dry 0.288 0.828
Dibenz(a,h)anthracene 1 03/14/23 10:53 V30753JMV
<0.149 mg/Kg - dry 0.149 0.828Dibenzofuran 1 03/14/23 10:53 V30753JMV
<0.118 mg/Kg - dry 0.118 0.8281,2-Dichlorobenzene 1 03/14/23 10:53 V30753JMV
<0.122 mg/Kg - dry 0.122 0.8281,3-Dichlorobenzene 1 03/14/23 10:53 V30753JMV
<0.122 mg/Kg - dry 0.122 0.4141,4-Dichlorobenzene 1 03/14/23 10:53 V30753JMV
<0.184 mg/Kg - dry 0.184 0.8283,3'-Dichlorobenzidine 1 03/14/23 10:53 V30753JMV
<0.120 mg/Kg - dry 0.120 0.8282,4-Dichlorophenol 1 03/14/23 10:53 V30753JMV
<0.225 mg/Kg - dry 0.225 0.828
Diethyl phthalate 1 03/14/23 10:53 V30753JMV
<0.218 mg/Kg - dry 0.218 0.828Dimethyl phthalate 1 03/14/23 10:53 V30753JMV
<0.135 mg/Kg - dry 0.135 0.4142,4-Dimethylphenol 1 03/14/23 10:53 V30753JMV
<0.134 mg/Kg - dry 0.134 0.828Di-n-butyl phthalate 1 03/14/23 10:53 V30753JMV
<0.301 mg/Kg - dry 0.301 1.884,6-Dinitro-2-methylphenol 1 03/14/23 10:53 V30753JMV
<0.652 mg/Kg - dry 0.652 1.882,4-Dinitrophenol 1 03/14/23 10:53 V30753JMV
<0.121 mg/Kg - dry 0.121 0.8282,4-Dinitrotoluene 1 03/14/23 10:53 V30753JMV
<0.135 mg/Kg - dry 0.135 0.8282,6-Dinitrotoluene 1 03/14/23 10:53 V30753JMV
<0.179 mg/Kg - dry 0.179 0.414Di-n-Octyl Phthalate 1 03/14/23 10:53 V30753JMV
<0.154 mg/Kg - dry 0.154 0.828Fluoranthene 1 03/14/23 10:53 V30753JMV
<0.160 mg/Kg - dry 0.160 0.828Fluorene 1 03/14/23 10:53 V30753JMV
<0.132 mg/Kg - dry 0.132 0.828Hexachlorobenzene 1 03/14/23 10:53 V30753JMV
<0.122 mg/Kg - dry 0.122 0.828Hexachlorobutadiene 1 03/14/23 10:53 V30753JMV
<0.196 mg/Kg - dry 0.196 0.828Hexachlorocyclopentadiene 1 03/14/23 10:53 V30753JMV
Qualifiers/
Definitions
Estimated valueJDilution FactorDF
Method Quantitation LimitMQL
Page 18 of 43
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 27513
23-059-0009
00122
Suite 110
Falcon Engineering
1210 Trinity Road
Christopher Burkhardt
Cary
Received : 02/28/2023
W57045
Report Date : 03/15/2023
Sample ID :
Lab No :
Sampled:P1S4
89932 Matrix:
2/27/2023 12:38
Solids
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
3546
8270E Prep Batch(es):V30730 03/13/23 10:00
<0.099 mg/Kg - dry 0.099 0.828Hexachloroethane 1 03/14/23 10:53 V30753JMV
<0.224 mg/Kg - dry 0.224 0.828
Indeno(1,2,3-cd)pyrene 1 03/14/23 10:53 V30753JMV
<0.239 mg/Kg - dry 0.239 0.828Isophorone 1 03/14/23 10:53 V30753JMV
<0.132 mg/Kg - dry 0.132 0.8281-Methylnaphthalene 1 03/14/23 10:53 V30753JMV
<0.125 mg/Kg - dry 0.125 0.8282-Methylnaphthalene 1 03/14/23 10:53 V30753JMV
<0.121 mg/Kg - dry 0.121 0.8282-Methylphenol 1 03/14/23 10:53 V30753JMV
<0.106 mg/Kg - dry 0.106 0.8283&4 Methylphenol 1 03/14/23 10:53 V30753JMV
<0.180 mg/Kg - dry 0.180 0.828Naphthalene 1 03/14/23 10:53 V30753JMV
<0.121 mg/Kg - dry 0.121 0.828
2-Nitroaniline 1 03/14/23 10:53 V30753JMV
<0.150 mg/Kg - dry 0.150 0.8283-Nitroaniline 1 03/14/23 10:53 V30753JMV
<0.117 mg/Kg - dry 0.117 0.4144-Nitroaniline 1 03/14/23 10:53 V30753JMV
<0.145 mg/Kg - dry 0.145 0.414Nitrobenzene 1 03/14/23 10:53 V30753JMV
<0.111 mg/Kg - dry 0.111 0.8282-Nitrophenol 1 03/14/23 10:53 V30753JMV
<0.146 mg/Kg - dry 0.146 0.8284-Nitrophenol 1 03/14/23 10:53 V30753JMV
<0.329 mg/Kg - dry 0.329 0.828N-Nitrosodimethylamine 1 03/14/23 10:53 V30753JMV
<0.227 mg/Kg - dry 0.227 0.828N-Nitrosodiphenylamine 1 03/14/23 10:53 V30753JMV
<0.148 mg/Kg - dry 0.148 0.828N-Nitroso-di-n-propylamine 1 03/14/23 10:53 V30753JMV
<0.435 mg/Kg - dry 0.435 1.25Pentachlorophenol 1 03/14/23 10:53 V30753JMV
<0.260 mg/Kg - dry 0.260 0.828Phenanthrene 1 03/14/23 10:53 V30753JMV
<0.140 mg/Kg - dry 0.140 0.828Phenol 1 03/14/23 10:53 V30753JMV
<0.168 mg/Kg - dry 0.168 0.828Pyrene 1 03/14/23 10:53 V30753JMV
<0.099 mg/Kg - dry 0.099 0.414Pyridine 1 03/14/23 10:53 V30753JMV
Qualifiers/
Definitions
Estimated valueJDilution FactorDF
Method Quantitation LimitMQL
Page 19 of 43
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 27513
23-059-0009
00122
Suite 110
Falcon Engineering
1210 Trinity Road
Christopher Burkhardt
Cary
Received : 02/28/2023
W57045
Report Date : 03/15/2023
Sample ID :
Lab No :
Sampled:P1S4
89932 Matrix:
2/27/2023 12:38
Solids
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
3546
8270E Prep Batch(es):V30730 03/13/23 10:00
<0.134 mg/Kg - dry 0.134 0.8281,2,4-Trichlorobenzene 1 03/14/23 10:53 V30753JMV
<0.120 mg/Kg - dry 0.120 0.828
2,4,5-Trichlorophenol 1 03/14/23 10:53 V30753JMV
<0.121 mg/Kg - dry 0.121 0.8282,4,6-Trichlorophenol 1 03/14/23 10:53 V30753JMV
8270ESurrogate: Phenol-d5 78.7 Limits: 34-121%03/14/23 10:531 JMV
Surrogate: 2-Fluorobiphenyl 84.4 Limits: 44-115%03/14/23 10:531 JMV V30753
Surrogate: 2-Fluorophenol 82.9 Limits: 35-115%03/14/23 10:531 JMV V30753
Surrogate: Nitrobenzene-d5 75.4 Limits: 37-122%03/14/23 10:531 JMV V30753
Surrogate: 4-Terphenyl-d14 89.8 Limits: 54-127%03/14/23 10:531 JMV V30753
Surrogate: 2,4,6-Tribromophenol 80.5 Limits: 39-132%03/14/23 10:531 JMV V30753
Qualifiers/
Definitions
Estimated valueJDilution FactorDF
Method Quantitation LimitMQL
Page 20 of 43
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 27513
23-059-0009
00122
Suite 110
Falcon Engineering
1210 Trinity Road
Christopher Burkhardt
Cary
Received : 02/28/2023
W57045
Report Date : 03/15/2023
Sample ID :
Lab No :
Sampled:P1S4
89932 Matrix:
2/27/2023 12:38
Solids
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
MAEPH (Prep)
MADEP-EPH Prep Batch(es):V30678 03/10/23 10:30
202 mg/Kg - dry 11.6 63.1Aliphatic C9-C18 1 03/13/23 16:09 V30725AMP
61.9 J
mg/Kg - dry 15.4 63.1
Aliphatic C19-C36 1 03/13/23 16:09 V30725AMP
113 mg/Kg - dry 17.9 63.1Aromatic C11-C22 1 03/13/23 16:09 V30725AMP
MADEP-EPHSurrogate: 2-Bromonaphthalene 87.8 Limits: 40-140%03/13/23 16:091 AMP
MADEP-EPHSurrogate: Chlorooctadecane 72.5 Limits: 40-140%03/13/23 16:091 AMP
MADEP-EPHSurrogate: OTP Surrogate 76.1 Limits: 40-140%03/13/23 16:091 AMP
Surrogate: 2-Fluorobiphenyl 96.5 Limits: 40-140%03/13/23 16:091 AMP V30725
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
MAVPH (Prep)
MADEP-VPH Prep Batch(es):V30604 03/08/23 08:00
<1.53 mg/Kg - dry 1.53 10.0
Aliphatic C5-C8 100 03/08/23 14:51 V30605TBL
163 mg/Kg - dry 5.72 10.0Aliphatic C9-C12 100 03/08/23 14:51 V30605TBL
48.3 mg/Kg - dry 0.782 10.0Aromatic C9-C10 100 03/08/23 14:51 V30605TBL
MADEP-VPHSurrogate: 2,5-Dibromotoluene (FID)93.8 Limits: 70-130%03/08/23 14:51100 TBL
MADEP-VPHSurrogate: 2,5-Dibromotoluene (PID)77.7 Limits: 70-130%03/08/23 14:51100 TBL
Qualifiers/
Definitions
Estimated valueJDilution FactorDF
Method Quantitation LimitMQL
Page 21 of 43
Quality Control Data
23-059-0009Report No:
Project Description:
Client ID:Falcon Engineering
W57045
QC Prep Batch Method:
Total Petroleum Hydrocarbons - Extractable
8015C DRO
V30521QC Analytical Batch(es):
Analysis Method:
Analysis Description:
3546
QC Prep:V30498
Associated Lab Samples: 89929, 89930, 89931, 89932
LRB-V30498 Matrix: SOLLab Reagent Blank
Parameter
AnalyzedMQLMDLBlank
ResultUnits
%
Recovery
% Rec
Limits
03/07/23 09:5710.04.65<4.65mg/KgDiesel Range Organics (C10-C28)
03/07/23 09:57OTP Surrogate (S)106 31-123
LCS-V30498 LCSD-V30498Laboratory Control Sample & LCSD
LCSD
ResultParameter Max
RPD
LCSD
% Rec
LCS
%Rec
LCS
Result
Spike
Conc.Units
% Rec
Limits RPD
75.9 11410771.766.7mg/KgDiesel Range Organics (C10-C28)46-126 5.6 20
114108OTP Surrogate (S)31-123
Page 1 of 20Date:03/15/2023 03:46 PM
Page 22 of 43
Quality Control Data
23-059-0009Report No:
Project Description:
Client ID:Falcon Engineering
W57045
QC Prep Batch Method:
Total Petroleum Hydrocarbons - Volatile
8015C GRO
V30321QC Analytical Batch(es):
Analysis Method:
Analysis Description:
5035 MED
QC Prep:V30320
Associated Lab Samples: 89929, 89930, 89931, 89932
LRB-V30320 Matrix: SOLLab Reagent Blank
Parameter
AnalyzedMQLMDLBlank
ResultUnits
%
Recovery
% Rec
Limits
03/01/23 14:035.002.07<2.07mg/KgGasoline Range Organics (C6-C10)
03/01/23 14:03a,a,a-Trifluorotoluene (S)93.4 50-137
LCS-V30320Laboratory Control Sample
Parameter
LCS %RecLCS
Result
Spike
Conc.Units
% Rec
Limits
10854.050.0mg/KgGasoline Range Organics (C6-C10)41-138
109a,a,a-Trifluorotoluene (S)50-137
V 89929-MS-V30320 V 89929-MSD-V30320Matrix Spike & Matrix Spike Duplicate
MS Result
Parameter
Max
RPD
MS
%Rec
MSD
Result
MSD
Spike
Conc.
MS Spike
Conc.ResultUnits
%Rec
Limits
MSD
%Rec RPD
50.4 10147.850.050.0<2.07mg/KgGasoline Range Organics (C6-C10)95.6 41-138 5.2 34
125a,a,a-Trifluorotoluene (S)104 50-137
Page 2 of 20Date:03/15/2023 03:46 PM
Page 23 of 43
Quality Control Data
23-059-0009Report No:
Project Description:
Client ID:Falcon Engineering
W57045
QC Prep Batch Method:
Volatile Organic Compounds - GC/MS
8260D
V30594QC Analytical Batch(es):
Analysis Method:
Analysis Description:
5035
QC Prep:V30593
Associated Lab Samples: 89932
LRB-V30593 Matrix: SOLLab Reagent Blank
Parameter
AnalyzedMQLMDLBlank
ResultUnits
%
Recovery
% Rec
Limits
03/08/23 11:400.0200.002<0.002mg/KgAcetone
03/08/23 11:400.0200.001<0.001mg/KgAcrolein
03/08/23 11:400.0200.0008<0.0008mg/KgAcrylonitrile
03/08/23 11:400.0050.0006<0.0006mg/KgBenzene
03/08/23 11:400.0050.0005<0.0005mg/KgBromobenzene
03/08/23 11:400.0050.0008<0.0008mg/KgBromochloromethane
03/08/23 11:400.0050.001<0.001mg/KgBromodichloromethane
03/08/23 11:400.0050.001<0.001mg/KgBromoform
03/08/23 11:400.0100.001<0.001mg/KgBromomethane
03/08/23 11:400.0050.0005<0.0005mg/Kgn-Butylbenzene
03/08/23 11:400.0050.0006<0.0006mg/Kgsec-Butyl benzene
03/08/23 11:400.0050.0005<0.0005mg/Kgtert-Butyl benzene
03/08/23 11:400.0050.0006<0.0006mg/KgCarbon Disulfide
03/08/23 11:400.0050.001<0.001mg/KgCarbon Tetrachloride
03/08/23 11:400.0050.0007<0.0007mg/KgChlorobenzene
03/08/23 11:400.0050.0009<0.0009mg/KgChlorodibromomethane
03/08/23 11:400.0100.0009<0.0009mg/KgChloroethane
03/08/23 11:400.0050.001<0.001mg/KgChloroform
03/08/23 11:400.0100.0006<0.0006mg/KgChloromethane
03/08/23 11:400.0050.0005<0.0005mg/Kg2-Chlorotoluene
03/08/23 11:400.0050.0004<0.0004mg/Kg4-Chlorotoluene
03/08/23 11:400.0050.0007<0.0007mg/KgDi-Isopropyl Ether (DIPE)
03/08/23 11:400.0100.0004<0.0004mg/Kg1,2-Dibromo-3-Chloropropane
03/08/23 11:400.0050.0006<0.0006mg/Kg1,2-Dibromoethane
03/08/23 11:400.0050.0006<0.0006mg/KgDibromomethane
03/08/23 11:400.0050.0003<0.0003mg/Kg1,2-Dichlorobenzene
03/08/23 11:400.0050.0004<0.0004mg/Kg1,3-Dichlorobenzene
Page 3 of 20Date:03/15/2023 03:46 PM
Page 24 of 43
Quality Control Data
23-059-0009Report No:
Project Description:
Client ID:Falcon Engineering
W57045
QC Prep Batch Method:
Volatile Organic Compounds - GC/MS
8260D
V30594QC Analytical Batch(es):
Analysis Method:
Analysis Description:
5035
QC Prep:V30593
Associated Lab Samples: 89932
LRB-V30593 Matrix: SOLLab Reagent Blank
Parameter
AnalyzedMQLMDLBlank
ResultUnits
%
Recovery
% Rec
Limits
03/08/23 11:400.0050.0006<0.0006mg/Kg1,4-Dichlorobenzene
03/08/23 11:400.0100.001<0.001mg/KgDichlorodifluoromethane
03/08/23 11:400.0050.0008<0.0008mg/Kg1,1-Dichloroethane
03/08/23 11:400.0050.001<0.001mg/Kg1,2-Dichloroethane
03/08/23 11:400.0050.0007<0.0007mg/Kg1,1-Dichloroethene
03/08/23 11:400.0050.0008<0.0008mg/Kgcis-1,2-Dichloroethene
03/08/23 11:400.0050.001<0.001mg/Kgtrans-1,2-Dichloroethene
03/08/23 11:400.0050.0004<0.0004mg/Kg1,2-Dichloropropane
03/08/23 11:400.0050.0006<0.0006mg/Kg1,3-Dichloropropane
03/08/23 11:400.0050.001<0.001mg/Kg2,2-Dichloropropane
03/08/23 11:400.0050.0008<0.0008mg/Kg1,1-Dichloropropene
03/08/23 11:400.0050.0005<0.0005mg/Kgcis-1,3-Dichloropropene
03/08/23 11:400.0050.0008<0.0008mg/Kgtrans-1,3-Dichloropropene
03/08/23 11:400.0050.0006<0.0006mg/KgEthylbenzene
03/08/23 11:400.0500.0008<0.0008mg/KgEthyl Tertiary Butyl Ether (ETBE)
03/08/23 11:400.0100.0008<0.0008mg/KgHexachlorobutadiene
03/08/23 11:400.0100.0007<0.0007mg/Kgn-Hexane
03/08/23 11:400.0200.0006<0.0006mg/Kg2-Hexanone
03/08/23 11:400.0050.0005<0.0005mg/KgIsopropylbenzene
03/08/23 11:400.0050.001<0.001mg/Kg4-Isopropyl toluene
03/08/23 11:400.0200.0007<0.0007mg/KgMethyl Ethyl Ketone (MEK)
03/08/23 11:400.0050.0006<0.0006mg/KgMethyl tert-butyl ether (MTBE)
03/08/23 11:400.0200.015<0.015mg/Kg4-Methyl-2-Pentanone
03/08/23 11:400.0100.001<0.001mg/KgMethylene Chloride
03/08/23 11:400.0100.0010<0.0010mg/KgNaphthalene
03/08/23 11:400.0050.0005<0.0005mg/Kgn-Propylbenzene
03/08/23 11:400.0050.001<0.001mg/KgStyrene
Page 4 of 20Date:03/15/2023 03:46 PM
Page 25 of 43
Quality Control Data
23-059-0009Report No:
Project Description:
Client ID:Falcon Engineering
W57045
QC Prep Batch Method:
Volatile Organic Compounds - GC/MS
8260D
V30594QC Analytical Batch(es):
Analysis Method:
Analysis Description:
5035
QC Prep:V30593
Associated Lab Samples: 89932
LRB-V30593 Matrix: SOLLab Reagent Blank
Parameter
AnalyzedMQLMDLBlank
ResultUnits
%
Recovery
% Rec
Limits
03/08/23 11:400.0050.001<0.001mg/Kg1,1,1,2-Tetrachloroethane
03/08/23 11:400.0050.0003<0.0003mg/Kg1,1,2,2-Tetrachloroethane
03/08/23 11:400.0050.0009<0.0009mg/KgTetrachloroethene
03/08/23 11:400.0050.0007<0.0007mg/KgToluene
03/08/23 11:400.0100.0005<0.0005mg/Kg1,2,3-Trichlorobenzene
03/08/23 11:400.0100.0006<0.0006mg/Kg1,2,4-Trichlorobenzene
03/08/23 11:400.0050.001<0.001mg/Kg1,1,1-Trichloroethane
03/08/23 11:400.0050.0005<0.0005mg/Kg1,1,2-Trichloroethane
03/08/23 11:400.0050.0009<0.0009mg/KgTrichloroethene
03/08/23 11:400.0100.002<0.002mg/KgTrichlorofluoromethane
03/08/23 11:400.0050.0007<0.0007mg/Kg1,2,3-Trichloropropane
03/08/23 11:400.0050.0005<0.0005mg/Kg1,2,4-Trimethylbenzene
03/08/23 11:400.0050.0005<0.0005mg/Kg1,3,5-Trimethylbenzene
03/08/23 11:400.0100.0005<0.0005mg/KgVinyl Acetate
03/08/23 11:400.0100.0005<0.0005mg/KgVinyl Chloride
03/08/23 11:400.0050.0005<0.0005mg/Kgo-Xylene
03/08/23 11:400.0100.001<0.001mg/Kgm,p-Xylene
03/08/23 11:404-Bromofluorobenzene (S)91.4 70-130
03/08/23 11:40Dibromofluoromethane (S)103 84-123
03/08/23 11:40Toluene-d8 (S)103 76-129
LCS-V30593 LCSD-V30593Laboratory Control Sample & LCSD
LCSD
ResultParameter Max
RPD
LCSD
% Rec
LCS
%Rec
LCS
Result
Spike
Conc.Units
% Rec
Limits RPD
0.078 78.284.80.0840.100mg/KgAcetone 29-198 8.0 20
0.082 82.787.40.0870.100mg/KgAcrolein 70-130 5.5 20
Page 5 of 20Date:03/15/2023 03:46 PM
Page 26 of 43
Quality Control Data
23-059-0009Report No:
Project Description:
Client ID:Falcon Engineering
W57045
QC Prep Batch Method:
Volatile Organic Compounds - GC/MS
8260D
V30594QC Analytical Batch(es):
Analysis Method:
Analysis Description:
5035
QC Prep:V30593
LCS-V30593 LCSD-V30593Laboratory Control Sample & LCSD
LCSD
ResultParameter Max
RPD
LCSD
% Rec
LCS
%Rec
LCS
Result
Spike
Conc.Units
% Rec
Limits RPD
0.099 99.699.30.0990.100mg/KgAcrylonitrile 65-134 0.3 20
0.051 1041040.0510.050mg/KgBenzene 74-127 0.0 20
0.054 1101070.0530.050mg/KgBromobenzene 73-125 2.5 20
0.051 10399.00.0490.050mg/KgBromochloromethane 72-134 4.3 20
0.058 1171150.0570.050mg/KgBromodichloromethane 75-122 1.0 20
0.043 86.689.40.0440.050mg/KgBromoform 66-135 3.1 20
0.050 1011150.0570.050mg/KgBromomethane 20-180 13.3 20
0.046 93.094.40.0470.050mg/Kgn-Butylbenzene 65-135 1.4 20
0.044 89.490.80.0450.050mg/Kgsec-Butyl benzene 66-131 1.5 20
0.046 93.494.80.0470.050mg/Kgtert-Butyl benzene 67-132 1.4 20
0.049 99.81050.0520.050mg/KgCarbon Disulfide 61-129 5.2 20
0.049 99.21010.0500.050mg/KgCarbon Tetrachloride 64-143 1.9 20
0.051 1031060.0520.050mg/KgChlorobenzene 74-118 2.1 20
0.055 1111110.0550.050mg/KgChlorodibromomethane 73-122 0.1 20
0.046 93.293.80.0460.050mg/KgChloroethane 33-149 0.6 20
0.056 1131150.0570.050mg/KgChloroform 73-127 2.2 20
0.040 81.084.80.0420.050mg/KgChloromethane 45-143 4.5 20
0.048 96.695.80.0470.050mg/Kg2-Chlorotoluene 67-124 0.8 20
0.048 96.695.80.0470.050mg/Kg4-Chlorotoluene 71-126 0.8 20
0.040 81.480.60.0400.050mg/KgDi-Isopropyl Ether (DIPE)59-159 0.9 20
0.041 83.083.00.0410.050mg/Kg1,2-Dibromo-3-Chloropropane 55-157 0.0 20
0.051 1031050.0520.050mg/Kg1,2-Dibromoethane 70-132 1.7 20
0.050 1011070.0530.050mg/KgDibromomethane 74-133 5.7 20
0.043 86.686.60.0430.050mg/Kg1,2-Dichlorobenzene 72-123 0.0 20
0.043 86.684.60.0420.050mg/Kg1,3-Dichlorobenzene 71-120 2.3 20
0.040 81.281.40.0400.050mg/Kg1,4-Dichlorobenzene 71-123 0.2 20
Page 6 of 20Date:03/15/2023 03:46 PM
Page 27 of 43
Quality Control Data
23-059-0009Report No:
Project Description:
Client ID:Falcon Engineering
W57045
QC Prep Batch Method:
Volatile Organic Compounds - GC/MS
8260D
V30594QC Analytical Batch(es):
Analysis Method:
Analysis Description:
5035
QC Prep:V30593
LCS-V30593 LCSD-V30593Laboratory Control Sample & LCSD
LCSD
ResultParameter Max
RPD
LCSD
% Rec
LCS
%Rec
LCS
Result
Spike
Conc.Units
% Rec
Limits RPD
0.052 1041060.0530.050mg/KgDichlorodifluoromethane 26-146 1.9 20
0.051 1031020.0510.050mg/Kg1,1-Dichloroethane 74-127 0.5 20
0.051 1031010.0500.050mg/Kg1,2-Dichloroethane 68-128 1.9 20
0.044 89.494.80.0470.050mg/Kg1,1-Dichloroethene 67-149 5.8 20
0.048 97.896.40.0480.050mg/Kgcis-1,2-Dichloroethene 76-134 1.4 20
0.049 98.497.40.0480.050mg/Kgtrans-1,2-Dichloroethene 73-132 1.0 20
0.049 99.41010.0500.050mg/Kg1,2-Dichloropropane 73-130 1.7 20
0.055 1111110.0550.050mg/Kg1,3-Dichloropropane 75-124 0.3 20
0.056 1131120.0560.050mg/Kg2,2-Dichloropropane 50-142 0.5 20
0.053 1071090.0540.050mg/Kg1,1-Dichloropropene 71-130 2.2 20
0.057 1151150.0570.050mg/Kgcis-1,3-Dichloropropene 71-125 0.3 20
0.059 1191200.0600.050mg/Kgtrans-1,3-Dichloropropene 68-123 1.5 20
0.048 96.61000.0500.050mg/KgEthylbenzene 74-128 3.4 20
0.099 99.497.70.0970.100mg/KgEthyl Tertiary Butyl Ether (ETBE)70-130 1.7 20
0.033 66.869.40.0340.050mg/KgHexachlorobutadiene 64-125 3.8 20
0.049 99.61100.0540.050mg/Kgn-Hexane 70-130 9.5 20
0.040 81.892.80.0460.050mg/Kg2-Hexanone 61-157 12.6 20
0.045 90.890.80.0450.050mg/KgIsopropylbenzene 68-126 0.0 20
0.047 94.093.40.0460.050mg/Kg4-Isopropyl toluene 68-129 0.6 20
0.042 85.492.40.0460.050mg/KgMethyl Ethyl Ketone (MEK)63-149 7.8 20
0.053 1071070.0530.050mg/KgMethyl tert-butyl ether (MTBE)70-130 0.5 20
0.046 93.490.20.0450.050mg/Kg4-Methyl-2-Pentanone 57-162 3.4 20
0.038 77.878.00.0390.050mg/KgMethylene Chloride 74-129 0.2 20
0.050 1011030.0510.050mg/KgNaphthalene 57-157 2.7 20
0.045 90.491.60.0450.050mg/Kgn-Propylbenzene 67-130 1.3 20
0.051 1041030.0510.050mg/KgStyrene 77-121 0.5 20
Page 7 of 20Date:03/15/2023 03:46 PM
Page 28 of 43
Quality Control Data
23-059-0009Report No:
Project Description:
Client ID:Falcon Engineering
W57045
QC Prep Batch Method:
Volatile Organic Compounds - GC/MS
8260D
V30594QC Analytical Batch(es):
Analysis Method:
Analysis Description:
5035
QC Prep:V30593
LCS-V30593 LCSD-V30593Laboratory Control Sample & LCSD
LCSD
ResultParameter Max
RPD
LCSD
% Rec
LCS
%Rec
LCS
Result
Spike
Conc.Units
% Rec
Limits RPD
0.047 95.81000.0500.050mg/Kg1,1,1,2-Tetrachloroethane 72-115 4.6 20
0.051 1041000.0500.050mg/Kg1,1,2,2-Tetrachloroethane 56-126 3.5 20
0.045 90.691.20.0450.050mg/KgTetrachloroethene 68-130 0.6 20
0.049 99.61020.0510.050mg/KgToluene 71-129 2.5 20
0.042 84.485.00.0420.050mg/Kg1,2,3-Trichlorobenzene 68-130 0.7 20
0.044 88.489.40.0440.050mg/Kg1,2,4-Trichlorobenzene 66-125 1.1 20
0.052 1051070.0530.050mg/Kg1,1,1-Trichloroethane 67-131 1.6 20
0.050 1011030.0510.050mg/Kg1,1,2-Trichloroethane 70-133 2.1 20
0.053 1071120.0560.050mg/KgTrichloroethene 75-133 5.1 20
0.047 95.297.60.0480.050mg/KgTrichlorofluoromethane 44-146 2.4 20
0.047 94.892.60.0460.050mg/Kg1,2,3-Trichloropropane 60-137 2.3 20
0.046 93.493.20.0460.050mg/Kg1,2,4-Trimethylbenzene 69-129 0.2 20
0.046 93.893.40.0460.050mg/Kg1,3,5-Trimethylbenzene 69-128 0.4 20
0.053 1061080.0530.050mg/KgVinyl Acetate 60-140 1.3 20
0.045 91.094.80.0470.050mg/KgVinyl Chloride 48-147 4.0 20
0.050 1011040.0510.050mg/Kgo-Xylene 74-126 2.7 20
0.102 1021040.1040.100mg/Kgm,p-Xylene 75-124 1.9 20
89.887.24-Bromofluorobenzene (S)70-130
102101Dibromofluoromethane (S)84-123
102101Toluene-d8 (S)76-129
Page 8 of 20Date:03/15/2023 03:46 PM
Page 29 of 43
Quality Control Data
23-059-0009Report No:
Project Description:
Client ID:Falcon Engineering
W57045
QC Prep Batch Method:
Semivolatile Organic Compounds - GC/MS
8270E
V30753QC Analytical Batch(es):
Analysis Method:
Analysis Description:
3546
QC Prep:V30730
Associated Lab Samples: 89932
LRB-V30730 Matrix: SOLLab Reagent Blank
Parameter
AnalyzedMQLMDLBlank
ResultUnits
%
Recovery
% Rec
Limits
03/13/23 22:000.6600.116<0.116mg/KgAcenaphthene
03/13/23 22:000.6600.105<0.105mg/KgAcenaphthylene
03/13/23 22:000.6600.152<0.152mg/KgAniline
03/13/23 22:000.6600.143<0.143mg/KgAnthracene
03/13/23 22:000.6600.139<0.139mg/KgBenzo(a)anthracene
03/13/23 22:000.6600.147<0.147mg/KgBenzo(a)pyrene
03/13/23 22:000.6600.146<0.146mg/KgBenzo(b)fluoranthene
03/13/23 22:000.6600.136<0.136mg/KgBenzo(g,h,i)perylene
03/13/23 22:000.6600.137<0.137mg/KgBenzo(k)fluoranthene
03/13/23 22:002.000.580<0.580mg/KgBenzoic Acid
03/13/23 22:000.6600.105<0.105mg/KgBenzyl alcohol
03/13/23 22:000.6600.118<0.118mg/KgBis(2-Chloroethoxy)methane
03/13/23 22:000.6600.107<0.107mg/KgBis(2-Chloroethyl)ether
03/13/23 22:000.3300.136<0.136mg/KgBis(2-Chloroisopropyl)ether
03/13/23 22:000.6600.120<0.120mg/KgBis(2-ethylhexyl)phthalate
03/13/23 22:000.6600.109<0.109mg/Kg4-Bromophenyl phenyl ether
03/13/23 22:000.3300.113<0.113mg/KgButyl benzyl phthalate
03/13/23 22:000.6600.092<0.092mg/Kg4-Chloro-3-methylphenol
03/13/23 22:000.3300.112<0.112mg/Kg4-Chloroaniline
03/13/23 22:000.6600.116<0.116mg/Kg2-Chloronaphthalene
03/13/23 22:000.6600.098<0.098mg/Kg2-Chlorophenol
03/13/23 22:001.000.126<0.126mg/Kg4-Chlorophenyl phenyl ether
03/13/23 22:000.6600.142<0.142mg/KgChrysene
03/13/23 22:000.6600.230<0.230mg/KgDibenz(a,h)anthracene
03/13/23 22:000.6600.119<0.119mg/KgDibenzofuran
03/13/23 22:000.6600.094<0.094mg/Kg1,2-Dichlorobenzene
03/13/23 22:000.6600.097<0.097mg/Kg1,3-Dichlorobenzene
Page 9 of 20Date:03/15/2023 03:46 PM
Page 30 of 43
Quality Control Data
23-059-0009Report No:
Project Description:
Client ID:Falcon Engineering
W57045
QC Prep Batch Method:
Semivolatile Organic Compounds - GC/MS
8270E
V30753QC Analytical Batch(es):
Analysis Method:
Analysis Description:
3546
QC Prep:V30730
Associated Lab Samples: 89932
LRB-V30730 Matrix: SOLLab Reagent Blank
Parameter
AnalyzedMQLMDLBlank
ResultUnits
%
Recovery
% Rec
Limits
03/13/23 22:000.3300.097<0.097mg/Kg1,4-Dichlorobenzene
03/13/23 22:000.6600.147<0.147mg/Kg3,3'-Dichlorobenzidine
03/13/23 22:000.6600.095<0.095mg/Kg2,4-Dichlorophenol
03/13/23 22:000.6600.180<0.180mg/KgDiethyl phthalate
03/13/23 22:000.6600.174<0.174mg/KgDimethyl phthalate
03/13/23 22:000.3300.108<0.108mg/Kg2,4-Dimethylphenol
03/13/23 22:000.6600.107<0.107mg/KgDi-n-butyl phthalate
03/13/23 22:001.500.240<0.240mg/Kg4,6-Dinitro-2-methylphenol
03/13/23 22:001.500.520<0.520mg/Kg2,4-Dinitrophenol
03/13/23 22:000.6600.096<0.096mg/Kg2,4-Dinitrotoluene
03/13/23 22:000.6600.108<0.108mg/Kg2,6-Dinitrotoluene
03/13/23 22:000.3300.143<0.143mg/KgDi-n-Octyl Phthalate
03/13/23 22:000.6600.123<0.123mg/KgFluoranthene
03/13/23 22:000.6600.128<0.128mg/KgFluorene
03/13/23 22:000.6600.106<0.106mg/KgHexachlorobenzene
03/13/23 22:000.6600.097<0.097mg/KgHexachlorobutadiene
03/13/23 22:000.6600.157<0.157mg/KgHexachlorocyclopentadiene
03/13/23 22:000.6600.079<0.079mg/KgHexachloroethane
03/13/23 22:000.6600.179<0.179mg/KgIndeno(1,2,3-cd)pyrene
03/13/23 22:000.6600.191<0.191mg/KgIsophorone
03/13/23 22:000.6600.106<0.106mg/Kg1-Methylnaphthalene
03/13/23 22:000.6600.100<0.100mg/Kg2-Methylnaphthalene
03/13/23 22:000.6600.097<0.097mg/Kg2-Methylphenol
03/13/23 22:000.6600.084<0.084mg/Kg3&4 Methylphenol
03/13/23 22:000.6600.144<0.144mg/KgNaphthalene
03/13/23 22:000.6600.096<0.096mg/Kg2-Nitroaniline
03/13/23 22:000.6600.120<0.120mg/Kg3-Nitroaniline
Page 10 of 20Date:03/15/2023 03:46 PM
Page 31 of 43
Quality Control Data
23-059-0009Report No:
Project Description:
Client ID:Falcon Engineering
W57045
QC Prep Batch Method:
Semivolatile Organic Compounds - GC/MS
8270E
V30753QC Analytical Batch(es):
Analysis Method:
Analysis Description:
3546
QC Prep:V30730
Associated Lab Samples: 89932
LRB-V30730 Matrix: SOLLab Reagent Blank
Parameter
AnalyzedMQLMDLBlank
ResultUnits
%
Recovery
% Rec
Limits
03/13/23 22:000.3300.093<0.093mg/Kg4-Nitroaniline
03/13/23 22:000.3300.116<0.116mg/KgNitrobenzene
03/13/23 22:000.6600.088<0.088mg/Kg2-Nitrophenol
03/13/23 22:000.6600.117<0.117mg/Kg4-Nitrophenol
03/13/23 22:000.6600.263<0.263mg/KgN-Nitrosodimethylamine
03/13/23 22:000.6600.181<0.181mg/KgN-Nitrosodiphenylamine
03/13/23 22:000.6600.118<0.118mg/KgN-Nitroso-di-n-propylamine
03/13/23 22:001.000.347<0.347mg/KgPentachlorophenol
03/13/23 22:000.6600.208<0.208mg/KgPhenanthrene
03/13/23 22:000.6600.112<0.112mg/KgPhenol
03/13/23 22:000.6600.134<0.134mg/KgPyrene
03/13/23 22:000.3300.079<0.079mg/KgPyridine
03/13/23 22:000.6600.107<0.107mg/Kg1,2,4-Trichlorobenzene
03/13/23 22:000.6600.096<0.096mg/Kg2,4,5-Trichlorophenol
03/13/23 22:000.6600.096<0.096mg/Kg2,4,6-Trichlorophenol
03/13/23 22:002-Fluorobiphenyl (S)93.4 44-115
03/13/23 22:002-Fluorophenol (S)91.5 35-115
03/13/23 22:00Nitrobenzene-d5 (S)85.0 37-122
03/13/23 22:004-Terphenyl-d14 (S)105 54-127
03/13/23 22:002,4,6-Tribromophenol (S)83.7 39-132
03/13/23 22:00Phenol-d5 (S)88.5 34-121
LCS-V30730Laboratory Control Sample
Parameter
LCS %RecLCS
Result
Spike
Conc.Units
% Rec
Limits
88.01.471.67mg/KgAcenaphthene 40-123
86.21.441.67mg/KgAcenaphthylene 32-132
Page 11 of 20Date:03/15/2023 03:46 PM
Page 32 of 43
Quality Control Data
23-059-0009Report No:
Project Description:
Client ID:Falcon Engineering
W57045
QC Prep Batch Method:
Semivolatile Organic Compounds - GC/MS
8270E
V30753QC Analytical Batch(es):
Analysis Method:
Analysis Description:
3546
QC Prep:V30730
LCS-V30730Laboratory Control Sample
Parameter
LCS %RecLCS
Result
Spike
Conc.Units
% Rec
Limits
222*3.711.67mg/KgAniline 12-197
97.61.631.67mg/KgAnthracene 47-123
99.41.661.67mg/KgBenzo(a)anthracene 49-126
1101.831.67mg/KgBenzo(a)pyrene 45-129
1011.681.67mg/KgBenzo(b)fluoranthene 45-132
95.81.601.67mg/KgBenzo(g,h,i)perylene 43-134
98.81.651.67mg/KgBenzo(k)fluoranthene 47-132
47.60.7961.67mg/KgBenzoic Acid 10-83
90.41.511.67mg/KgBenzyl alcohol 29-122
81.41.361.67mg/KgBis(2-Chloroethoxy)methane 36-121
74.21.241.67mg/KgBis(2-Chloroethyl)ether 31-120
85.61.431.67mg/KgBis(2-Chloroisopropyl)ether 33-131
1111.861.67mg/KgBis(2-ethylhexyl)phthalate 51-133
94.61.581.67mg/Kg4-Bromophenyl phenyl ether 46-124
1141.911.67mg/KgButyl benzyl phthalate 48-132
79.01.321.67mg/Kg4-Chloro-3-methylphenol 45-122
74.81.251.67mg/Kg4-Chloroaniline 17-106
88.61.481.67mg/Kg2-Chloronaphthalene 41-114
82.61.381.67mg/Kg2-Chlorophenol 34-121
86.81.451.67mg/Kg4-Chlorophenyl phenyl ether 45-121
1021.711.67mg/KgChrysene 50-124
85.61.431.67mg/KgDibenz(a,h)anthracene 45-134
88.61.481.67mg/KgDibenzofuran 44-120
75.41.261.67mg/Kg1,2-Dichlorobenzene 33-117
74.21.241.67mg/Kg1,3-Dichlorobenzene 30-115
74.21.241.67mg/Kg1,4-Dichlorobenzene 31-115
71.21.191.67mg/Kg3,3'-Dichlorobenzidine 22-121
Page 12 of 20* QC Fail Date:03/15/2023 03:46 PM
Page 33 of 43
Quality Control Data
23-059-0009Report No:
Project Description:
Client ID:Falcon Engineering
W57045
QC Prep Batch Method:
Semivolatile Organic Compounds - GC/MS
8270E
V30753QC Analytical Batch(es):
Analysis Method:
Analysis Description:
3546
QC Prep:V30730
LCS-V30730Laboratory Control Sample
Parameter
LCS %RecLCS
Result
Spike
Conc.Units
% Rec
Limits
80.81.351.67mg/Kg2,4-Dichlorophenol 40-122
95.21.591.67mg/KgDiethyl phthalate 50-124
90.41.511.67mg/KgDimethyl phthalate 48-124
81.41.361.67mg/Kg2,4-Dimethylphenol 30-127
1101.831.67mg/KgDi-n-butyl phthalate 51-128
88.01.471.67mg/Kg4,6-Dinitro-2-methylphenol 29-132
76.01.271.67mg/Kg2,4-Dinitrophenol 27-129
96.41.611.67mg/Kg2,4-Dinitrotoluene 48-126
94.01.571.67mg/Kg2,6-Dinitrotoluene 46-124
1081.801.67mg/KgDi-n-Octyl Phthalate 45-140
98.81.651.67mg/KgFluoranthene 50-127
91.01.521.67mg/KgFluorene 43-125
94.61.581.67mg/KgHexachlorobenzene 45-122
72.41.211.67mg/KgHexachlorobutadiene 32-123
71.21.191.67mg/KgHexachlorocyclopentadiene 32-117
73.01.221.67mg/KgHexachloroethane 28-117
94.61.581.67mg/KgIndeno(1,2,3-cd)pyrene 45-133
80.21.341.67mg/KgIsophorone 30-122
77.81.301.67mg/Kg1-Methylnaphthalene 40-119
73.61.231.67mg/Kg2-Methylnaphthalene 38-122
86.21.441.67mg/Kg2-Methylphenol 32-122
76.61.281.67mg/Kg3&4 Methylphenol 34-119
75.41.261.67mg/KgNaphthalene 35-123
89.21.491.67mg/Kg2-Nitroaniline 44-127
86.81.451.67mg/Kg3-Nitroaniline 33-119
89.81.501.67mg/Kg4-Nitroaniline 63-147
75.41.261.67mg/KgNitrobenzene 34-122
Page 13 of 20Date:03/15/2023 03:46 PM
Page 34 of 43
Quality Control Data
23-059-0009Report No:
Project Description:
Client ID:Falcon Engineering
W57045
QC Prep Batch Method:
Semivolatile Organic Compounds - GC/MS
8270E
V30753QC Analytical Batch(es):
Analysis Method:
Analysis Description:
3546
QC Prep:V30730
LCS-V30730Laboratory Control Sample
Parameter
LCS %RecLCS
Result
Spike
Conc.Units
% Rec
Limits
76.01.271.67mg/Kg2-Nitrophenol 36-123
1262.101.67mg/Kg4-Nitrophenol 30-132
57.30.9571.67mg/KgN-Nitrosodimethylamine 10-146
1191.981.67mg/KgN-Nitrosodiphenylamine 38-127
81.41.361.67mg/KgN-Nitroso-di-n-propylamine 36-120
97.01.621.67mg/KgPentachlorophenol 25-133
98.21.641.67mg/KgPhenanthrene 50-121
90.41.511.67mg/KgPhenol 34-121
1051.751.67mg/KgPyrene 47-127
40.20.6731.67mg/KgPyridine 10-80
73.01.221.67mg/Kg1,2,4-Trichlorobenzene 34-118
87.41.461.67mg/Kg2,4,5-Trichlorophenol 41-124
86.21.441.67mg/Kg2,4,6-Trichlorophenol 39-126
90.42-Fluorobiphenyl (S)44-115
90.32-Fluorophenol (S)35-115
74.8Nitrobenzene-d5 (S)37-122
1104-Terphenyl-d14 (S)54-127
91.82,4,6-Tribromophenol (S)39-132
88.2Phenol-d5 (S)34-121
V 89932-MS-V30730 V 89932-MSD-V30730Matrix Spike & Matrix Spike Duplicate
MS Result
Parameter
Max
RPD
MS
%Rec
MSD
Result
MSD
Spike
Conc.
MS Spike
Conc.ResultUnits
%Rec
Limits
MSD
%Rec RPD
1.43 85.61.281.671.67<0.116mg/KgAcenaphthene 76.6 40-123 11.0 20
1.42 85.01.271.671.67<0.105mg/KgAcenaphthylene 76.0 32-132 11.1 20
3.04 1822.921.671.67<0.152mg/KgAniline 175 12-197 4.0 20
Page 14 of 20Date:03/15/2023 03:46 PM
Page 35 of 43
Quality Control Data
23-059-0009Report No:
Project Description:
Client ID:Falcon Engineering
W57045
QC Prep Batch Method:
Semivolatile Organic Compounds - GC/MS
8270E
V30753QC Analytical Batch(es):
Analysis Method:
Analysis Description:
3546
QC Prep:V30730
V 89932-MS-V30730 V 89932-MSD-V30730Matrix Spike & Matrix Spike Duplicate
MS Result
Parameter
Max
RPD
MS
%Rec
MSD
Result
MSD
Spike
Conc.
MS Spike
Conc.ResultUnits
%Rec
Limits
MSD
%Rec RPD
1.54 92.21.411.671.67<0.143mg/KgAnthracene 84.4 47-123 8.8 20
1.47 88.01.391.671.67<0.139mg/KgBenzo(a)anthracene 83.2 49-126 5.5 20
1.62 97.01.501.671.67<0.147mg/KgBenzo(a)pyrene 89.8 45-129 7.6 20
1.52 91.01.381.671.67<0.146mg/KgBenzo(b)fluoranthene 82.6 45-132 9.6 20
1.41 84.41.331.671.67<0.136mg/KgBenzo(g,h,i)perylene 79.6 43-134 5.8 20
1.41 84.41.371.671.67<0.137mg/KgBenzo(k)fluoranthene 82.0 47-132 2.8 20
1.31 78.41.201.671.67<0.580mg/KgBenzoic Acid 71.8 10-83 8.7 20
1.43 85.61.271.671.67<0.105mg/KgBenzyl alcohol 76.0 29-122 11.8 20
1.29 77.21.151.671.67<0.118mg/KgBis(2-Chloroethoxy)methane 68.8 36-121 11.4 20
1.33 79.61.061.671.67<0.107mg/KgBis(2-Chloroethyl)ether 63.4 31-120 22.5*20
1.36 81.41.211.671.67<0.136mg/KgBis(2-Chloroisopropyl)ether 72.4 33-131 11.6 20
1.63 97.61.541.671.67<0.120mg/KgBis(2-ethylhexyl)phthalate 92.2 51-133 5.6 20
1.46 87.41.291.671.67<0.109mg/Kg4-Bromophenyl phenyl ether 77.2 46-124 12.3 20
1.65 98.81.571.671.67<0.113mg/KgButyl benzyl phthalate 94.0 48-132 4.9 20
1.23 73.61.131.671.67<0.092mg/Kg4-Chloro-3-methylphenol 67.6 45-122 8.4 20
1.15 68.81.031.671.67<0.112mg/Kg4-Chloroaniline 61.6 17-106 11.0 20
1.43 85.61.271.671.67<0.116mg/Kg2-Chloronaphthalene 76.0 41-114 11.8 20
1.35 80.81.191.671.67<0.098mg/Kg2-Chlorophenol 71.2 34-121 12.5 20
1.40 83.81.291.671.67<0.126mg/Kg4-Chlorophenyl phenyl ether 77.2 45-121 8.1 20
1.52 91.01.441.671.67<0.142mg/KgChrysene 86.2 50-124 5.4 20
1.27 76.01.191.671.67<0.230mg/KgDibenz(a,h)anthracene 71.2 45-134 6.5 20
1.43 85.61.351.671.67<0.119mg/KgDibenzofuran 80.8 44-120 5.7 20
1.24 74.21.081.671.67<0.094mg/Kg1,2-Dichlorobenzene 64.6 33-117 13.7 20
1.20 71.81.081.671.67<0.097mg/Kg1,3-Dichlorobenzene 64.6 30-115 10.5 20
1.19 71.21.071.671.67<0.097mg/Kg1,4-Dichlorobenzene 64.0 31-115 10.6 20
0.930 55.60.9041.671.67<0.147mg/Kg3,3'-Dichlorobenzidine 54.1 22-121 2.8 20
Page 15 of 20* QC Fail Date:03/15/2023 03:46 PM
Page 36 of 43
Quality Control Data
23-059-0009Report No:
Project Description:
Client ID:Falcon Engineering
W57045
QC Prep Batch Method:
Semivolatile Organic Compounds - GC/MS
8270E
V30753QC Analytical Batch(es):
Analysis Method:
Analysis Description:
3546
QC Prep:V30730
V 89932-MS-V30730 V 89932-MSD-V30730Matrix Spike & Matrix Spike Duplicate
MS Result
Parameter
Max
RPD
MS
%Rec
MSD
Result
MSD
Spike
Conc.
MS Spike
Conc.ResultUnits
%Rec
Limits
MSD
%Rec RPD
1.28 76.61.151.671.67<0.095mg/Kg2,4-Dichlorophenol 68.8 40-122 10.6 20
1.45 86.81.361.671.67<0.180mg/KgDiethyl phthalate 81.4 50-124 6.4 20
1.42 85.01.301.671.67<0.174mg/KgDimethyl phthalate 77.8 48-124 8.8 30
1.37 82.01.221.671.67<0.108mg/Kg2,4-Dimethylphenol 73.0 30-127 11.5 20
1.62 97.01.501.671.67<0.107mg/KgDi-n-butyl phthalate 89.8 51-128 7.6 20
1.46 87.41.371.671.67<0.240mg/Kg4,6-Dinitro-2-methylphenol 82.0 29-132 6.3 20
1.53 91.61.381.671.67<0.520mg/Kg2,4-Dinitrophenol 82.6 27-129 10.3 20
1.49 89.21.371.671.67<0.096mg/Kg2,4-Dinitrotoluene 82.0 48-126 8.3 20
1.47 88.01.341.671.67<0.108mg/Kg2,6-Dinitrotoluene 80.2 46-124 9.2 20
1.55 92.81.451.671.67<0.143mg/KgDi-n-Octyl Phthalate 86.8 45-140 6.6 20
1.50 89.81.371.671.67<0.123mg/KgFluoranthene 82.0 50-127 9.0 20
1.48 88.61.341.671.67<0.128mg/KgFluorene 80.2 43-125 9.9 20
1.47 88.01.321.671.67<0.106mg/KgHexachlorobenzene 79.0 45-122 10.7 20
1.20 71.81.071.671.67<0.097mg/KgHexachlorobutadiene 64.0 32-123 11.4 20
1.21 72.41.041.671.67<0.157mg/KgHexachlorocyclopentadiene 62.2 32-117 15.1 20
1.25 74.81.091.671.67<0.079mg/KgHexachloroethane 65.2 28-117 13.6 20
1.38 82.61.281.671.67<0.179mg/KgIndeno(1,2,3-cd)pyrene 76.6 45-133 7.5 20
1.26 75.41.121.671.67<0.191mg/KgIsophorone 67.0 30-122 11.7 20
1.28 76.61.151.671.67<0.106mg/Kg1-Methylnaphthalene 68.8 40-119 10.6 20
1.22 73.01.111.671.67<0.100mg/Kg2-Methylnaphthalene 66.4 38-122 9.4 20
1.37 82.01.201.671.67<0.097mg/Kg2-Methylphenol 71.8 32-122 13.2 20
1.23 73.61.081.671.67<0.084mg/Kg3&4 Methylphenol 64.6 34-119 12.9 20
1.23 73.61.091.671.67<0.144mg/KgNaphthalene 65.2 35-123 12.0 20
1.44 86.21.301.671.67<0.096mg/Kg2-Nitroaniline 77.8 44-127 10.2 20
1.28 76.61.181.671.67<0.120mg/Kg3-Nitroaniline 70.6 33-119 8.1 20
1.43 85.61.321.671.67<0.093mg/Kg4-Nitroaniline 79.0 63-147 8.0 20
Page 16 of 20Date:03/15/2023 03:46 PM
Page 37 of 43
Quality Control Data
23-059-0009Report No:
Project Description:
Client ID:Falcon Engineering
W57045
QC Prep Batch Method:
Semivolatile Organic Compounds - GC/MS
8270E
V30753QC Analytical Batch(es):
Analysis Method:
Analysis Description:
3546
QC Prep:V30730
V 89932-MS-V30730 V 89932-MSD-V30730Matrix Spike & Matrix Spike Duplicate
MS Result
Parameter
Max
RPD
MS
%Rec
MSD
Result
MSD
Spike
Conc.
MS Spike
Conc.ResultUnits
%Rec
Limits
MSD
%Rec RPD
1.21 72.41.111.671.67<0.116mg/KgNitrobenzene 66.4 34-122 8.6 20
1.17 70.01.091.671.67<0.088mg/Kg2-Nitrophenol 65.2 32-123 7.0 20
1.63 97.61.741.671.67<0.117mg/Kg4-Nitrophenol 104 30-132 6.5 20
0.799 47.80.7351.671.67<0.263mg/KgN-Nitrosodimethylamine 44.0 10-146 8.3 30
1.96 1171.761.671.67<0.181mg/KgN-Nitrosodiphenylamine 105 38-127 10.7 20
1.32 79.01.121.671.67<0.118mg/KgN-Nitroso-di-n-propylamine 67.0 36-120 16.3 20
1.57 94.01.451.671.67<0.347mg/KgPentachlorophenol 86.8 25-133 7.9 20
1.54 92.21.401.671.67<0.208mg/KgPhenanthrene 83.8 50-121 9.5 20
1.43 85.61.251.671.67<0.112mg/KgPhenol 74.8 34-121 13.4 20
1.55 92.81.451.671.67<0.134mg/KgPyrene 86.8 47-127 6.6 20
0.576 34.40.5241.671.67<0.079mg/KgPyridine 31.3 10-80 9.4 20
1.17 70.01.071.671.67<0.107mg/Kg1,2,4-Trichlorobenzene 64.0 34-118 8.9 20
1.38 82.61.281.671.67<0.096mg/Kg2,4,5-Trichlorophenol 76.6 41-124 7.5 20
1.41 84.41.251.671.67<0.096mg/Kg2,4,6-Trichlorophenol 74.8 39-126 12.0 20
87.42-Fluorobiphenyl (S)76.6 44-115
84.92-Fluorophenol (S)74.2 35-115
71.2Nitrobenzene-d5 (S)62.2 37-122
93.44-Terphenyl-d14 (S)87.4 54-127
86.12,4,6-Tribromophenol (S)78.4 39-132
81.0Phenol-d5 (S)70.9 34-121
Page 17 of 20Date:03/15/2023 03:46 PM
Page 38 of 43
Quality Control Data
23-059-0009Report No:
Project Description:
Client ID:Falcon Engineering
W57045
QC Prep Batch Method:
Massachusetts EPH
MADEP-EPH
V30725QC Analytical Batch(es):
Analysis Method:
Analysis Description:
MAEPH (Prep)
QC Prep:V30678
Associated Lab Samples: 89932
LRB-V30678 Matrix: SOLLab Reagent Blank
Parameter
AnalyzedMQLMDLBlank
ResultUnits
%
Recovery
% Rec
Limits
03/13/23 11:1850.09.20<9.20mg/KgAliphatic C9-C18
03/13/23 11:1850.012.2<12.2mg/KgAliphatic C19-C36
03/13/23 11:1850.014.2<14.2mg/KgAromatic C11-C22
03/13/23 11:182-Fluorobiphenyl (S)91.2 40-140
03/13/23 11:182-Bromonaphthalene (S)81.5 40-140
03/13/23 11:18Chlorooctadecane (S)91.1 40-140
03/13/23 11:18OTP Surrogate (S)79.6 40-140
LCS-V30678 LCSD-V30678Laboratory Control Sample & LCSD
LCSD
ResultParameter Max
RPD
LCSD
% Rec
LCS
%Rec
LCS
Result
Spike
Conc.Units
% Rec
Limits RPD
45.7 76.166.539.960.0mg/KgAliphatic C9-C18 40-140 13.5 50
79.2 99.097.177.780.0mg/KgAliphatic C19-C36 40-140 1.9 50
158 92.9122208170mg/KgAromatic C11-C22 40-140 27.3 50
87.01132-Fluorobiphenyl (S)40-140
75.01032-Bromonaphthalene (S)40-140
96.192.0Chlorooctadecane (S)40-140
76.894.1OTP Surrogate (S)40-140
Page 18 of 20Date:03/15/2023 03:46 PM
Page 39 of 43
Quality Control Data
23-059-0009Report No:
Project Description:
Client ID:Falcon Engineering
W57045
QC Prep Batch Method:
Massachusetts VPH
MADEP-VPH
V30605QC Analytical Batch(es):
Analysis Method:
Analysis Description:
MAVPH (Prep)
QC Prep:V30604
Associated Lab Samples: 89932
LRB-V30604 Matrix: SOLLab Reagent Blank
Parameter
AnalyzedMQLMDLBlank
ResultUnits
%
Recovery
% Rec
Limits
03/08/23 14:288.001.22<1.22mg/KgAliphatic C5-C8
03/08/23 14:288.004.56<4.56mg/KgAliphatic C9-C12
03/08/23 14:288.000.624<0.624mg/KgAromatic C9-C10
03/08/23 14:282,5-Dibromotoluene (FID) (S)121 70-130
03/08/23 14:282,5-Dibromotoluene (PID) (S)120 70-130
LCS-V30604 LCSD-V30604Laboratory Control Sample & LCSD
LCSD
ResultParameter Max
RPD
LCSD
% Rec
LCS
%Rec
LCS
Result
Spike
Conc.Units
% Rec
Limits RPD
31.5 98.492.529.632.0mg/KgAliphatic C5-C8 70-130 6.2 50
38.7 12111436.432.0mg/KgAliphatic C9-C12 70-130 6.1 50
12.7 11911212.010.7mg/KgAromatic C9-C10 70-130 5.6 50
94.393.22,5-Dibromotoluene (FID) (S)70-130
92.686.22,5-Dibromotoluene (PID) (S)70-130
Page 19 of 20Date:03/15/2023 03:46 PM
Page 40 of 43
Quality Control Data
23-059-0009Report No:
Project Description:
Client ID:Falcon Engineering
W57045
Dry Weight Determination
SW-DRYWT
V30380QC Analytical Batch:
Analysis Method:
Analysis Description:
V 90021-DUPDuplicate
Max RPD
Parameter
AnalyzedRPDDUP
Result
Result
Units
20.0 03/02/23 17:420.011.211.2%Moisture
V 90022-DUPDuplicate
Max RPD
Parameter
AnalyzedRPDDUP
Result
Result
Units
20.0 03/02/23 17:420.629.529.3%Moisture
Page 20 of 20Date:03/15/2023 03:46 PM
Page 41 of 43
Fed Ex
UPS
US Postal
Client
Lab
Courier
Other :
Shipment Receipt Form
Customer Number:
Customer Name:
Report Number:23-059-0009
Falcon Engineering
00122
Shipping Method
Shipping container/cooler uncompromised?
Thermometer ID:IRT15 3.2C
Chain of Custody (COC) present?Yes No
Yes No Not Present
Yes No Not Present
Yes No
COC agrees with sample label(s)?Yes No
COC properly completed
Samples in proper containers?
Sample containers intact?
Sufficient sample volume for indicated test(s)?
All samples received within holding time?
Cooler temperature in compliance?
Yes No
Yes No
Yes No
Yes No
Yes No
Yes NoCooler/Samples arrived at the laboratory on ice.
Samples were considered acceptable as cooling
process had begun.
Yes No
Yes No N/A
Yes No N/A
Yes No N/ASoil VOA method 5035 – compliance criteria met
Water - Sample containers properly preserved
Water - VOA vials free of headspace Yes No N/A
Trip Blanks received with VOAs
ü
Low concentration EnCore samplers (48 hr)
High concentration pre-weighed (methanol -14 d) Low conc pre-weighed vials (Sod Bis -14 d)ü
High concentration container (48 hr)
Custody seals intact on shipping container/cooler?
Custody seals intact on sample bottles?
Number of coolers/boxes received
Yes No
1
Signature:Angelo Norvell Date & Time:02/28/2023 13:45:09
Special precautions or instructions included?
Comments:
Page 42 of 43
Page 43 of 43
certifications
NC State University:
• S&EC/Storm Water
Workshop
• Advanced Problems in
Hydric Soils Evaluation
• Wetland Identification &
Delineation
• Intermittent & Perennial
Stream Identification for
Riparian Buffer Rules
NC & VA (NC DWQ)
professional affiliations
NCAEP- North Carolina
Association of Environmental
Professionals
ACEC- Environmental
Science and Planning
Subcommittee
SPWS- Society of Professional
Wetland Scientists
AIA- American Institute of
Architects
ULI- Urban Land Institute
SMPS- Society for Marketing
Professional Services
NCWRA- North Carolina
Water Resources
Association
education
B.S., Natural Resource
Management, North Carolina
State University, 2003
project experience
BB&T, Wells Fargo, TD Bank, SunTrust; Environmental Services
Approved Vendor
Mr. Burkhardt has managed hundreds of Phase I and II ESA’s, limited asbestos, lead-based
paint and mold surveys, Transaction Screens, UST Sampling and Closure Reports.
NCDOT; Various PSA’s
Provided Senior Project Management for the conductance of multiple PSA’s for road widen-
ing projects throughout North Carolina. The PSA’s included areas within the Right-of-Way
and PUE as well as entire parcels based on potential risk. Project tasks included the oversight
of Geophysical Survey activities, subcontractred Geoprobe Investigations, field sampling
activities, UST removal and final report writing.
City of Raleigh, Public Utilities Department, Proposed Devereux Meadows Park
and Sewer Improvements
Provided Phase I ESA services on the proposed 15 acre park and sewer improvements in
downtown Raleigh. The park was located on a former 1950s vehicle maintenance facility that
included a service building, fueling station, and car wash along with multiple USTs and oil
water separators. In addition, the site was surrounded by gas stations and dry cleaners with
known contamination. An appropriate soil and groundwater contamination investigation plan
was developed based on the findings.
Serving as Falcon’s Environmental Department Manager, Christopher Burkhardt’s duties
include project implementation and management; proposal preparation; review of
environmental reports (Phase I and II Environmental Site Assessments, Asbestos, Lead Based
Paint and Mold Inspections); coordinating and supervising environmental staff &
subcontractors; and providing technical expertise for routine to complex projects involving
compliance with Sections 401 & 404 of the Clean Water Act, NC Sedimentation Pollution
Control Act of 1973, Section 7 of the Endangered Species Act, Section 106 of the National
Historic Preservation Act, National and State Environmental Policy Acts (NEPA/SEPA).
Through Mr. Burkhardt’s professional experiences, he has worked with and developed
relationships with a network of regulators across the Mid-Atlantic States, including regulators
with the US Army Corps of Engineers, State Water Quality & Land Resources, US Fish
& Wildlife Service, and State Historic Preservation Office.
christopher burkhardt, pwsenvironmental department manager
Falcon engineering, inc.
Falcon engineering, inc - resume
1
PROFESSIONAL
REGISTRATIONS
Registered Professional
Engineer: NC #039779,
SC #32235, VA #56754
EDUCATION
B.S., Civil Engineering,
North Carolina State
University, 2008
FALCON ENGINEERING, INC.
PROJECT EXPERIENCE
Durham County, Brown Water Treatment Plant, Durham, NC
Falcon was retained to provide early geoenvironmental services as part of the plant expansion
at one of Durham County’s waste water treatment plants. During initial assessment, suspect
discolored groundwater was observed and Falcon was asked to investigate further for the
presence of potential contaminants. Two constituents, arsenic and barium, were identified.
However, Falcon was able to confirm the levels of these two constituents were consistent with
naturally occurring levels, were below the Protection of Groundwater Preliminary Soil
Remediation Goals, and were not likely to be of concern during construction of the
expansion project.
Andrews Bypass, US Highway 521, Williamsburg County, SC
Provided Senior Project Management for a geo-environmental assessment of 80 acres of
developed and undeveloped forested land in Andrews, South Carolina in support of a
proposed 3.7 mile, 200 foot wide proposed route to connect US Highway 521 and bypass the
municipality of Andrews. The assessments included areas within existing right-of-way as well
as entire parcels for proposed new construction. Project tasks included the oversight of envi-
ronmental Investigations locating USTs and ASTs managing staff and field sampling activities,
and final report writing.
City of Raleigh, Hillsborough Street Phase II Improvements, Raleigh, NC
Provided Senior Project Management for a UST Geo-Environmental Assessment within
the proposed Hillsborough Street Phase II Improvement Project Corridor from Henderson
Street to Gardner. The proposed project corridor included several former and current gas
stations and auto repair facilities. Project tasks included oversight of geo-physical services to
locate UST’s and utilities and management of geoprobe borings. Provided additional soil and
groundwater assessment where needed as well as contaminated soil monitoring, excavation,
and remediation during construction and installation of underground utilities.
Town of Chapel Hill, Police Department, Environmental Due Diligence,
Chapel Hill, NC
Falcon was originally asked to prepare an Environmental Due Diligence report for this prop-
erty prior to placing the parcel for sale. During the assessment, Falcon determined the site was
used as a borrow pit in the late 1950’s through early 1960’s then as a fill site from the mid-
1960’s to mid-1970’s. Falcon recommended additional assessment and confirmed the presence
of coal combustion products. Falcon utilized GPR services to confirm the absence of USTs
and avoid utilities, geoprobe technology to sample soil and groundwater, and rotary drill rigs
to install monitoring wells. Falcon sampled the soil and groundwater on-site in an effort to
further delineate environmental conditions present in regards to the former use as a landfill.
JEREMY HAMM, PEGEOTECHNICAL DEPARTMENT MANAGER
RESUME
Jeremy is currently in a design and project management role where he oversees projects from
their inception, including proposal and scope development, client relations, managing field
crews and activities, performing engineering design calculations, preparing and reviewing re-
ports, and project follow-up services. Jeremy is a professional engineer with great enthusiasm
and a keen interest in understanding complex geological and geotechnical concepts. He pos-
sesses meticulous attention to detail, mastery of technical writing skills, a commendable work
ethic, and a thirst for knowledge which ensure only the highest of quality in his work. He has
continually displayed his natural leadership abilities by independently seizing on opportuni-
ties to better both himself and Falcon through project, company, and client related needs, and
involvement in professional organizations and his community.