HomeMy WebLinkAbout09011 Arrow Laundry Cleaners Drum Removal Rpt 20170331
DRUM REMOVAL REPORT
SHADE VALLEY ROAD
CHARLOTTE, NORTH CAROLINA
ECS PROJECT NO. 49-3925
PREPARED FOR
OAKHURST TOWN HOME LOTS, LLC 136 MAIN STREET
PINEVILLE, NORTH CAROLINA 28134
MARCH 31, 2017
March 31, 2017
Ms. Susan Rosenblatt
Oakhurst Town Home Lots, LLC
136 Main Street
Pineville, North Carolina, 28134
Reference: Drum Removal Report
Oakhurst Site
Shade Valley Road
Charlotte, North Carolina
ECS Project No. 49-3925
Dear Ms. Rosenblatt:
ECS Southeast, LLP (ECS) is pleased to provide you with our Drum Removal Report that
documents the removal of impacted soil associated with a previous drum spill. Environmental
services were provided in general accordance with the ECS Work Authorization No. 49-4366
Rev2.
ECS appreciates the opportunity to provide our environmental consulting services to you on this
project. If you have any questions concerning this report or this project, please contact ECS.
Respectfully submitted,
ECS SOUTHEAST, LLP
Christopher D. Orrell John M. Stewart, P.G., CPG
Environmental Scientist Chief Geologist
Correll@ecslimited.com jstewart1@ecslimited.com
704-525-5152 336-856-7150
Drum Removal Report
Shade Valley Road
Charlotte, North Carolina
ECS Project No. 49-3925
March 31, 2017
TABLE OF CONTENTS
1.0 EXECUTIVE SUMMARY ................................................................................................. 1
2.0 SOIL SCREENING AND EXCAVATION PROCEDURES ............................................... 4
3.0 RESULTS ........................................................................................................................ 4
4.0 CONCLUSIONS .............................................................................................................. 5
5.0 RECOMMENDATIONS ................................................................................................... 5
6.0 QUALIFICATIONS ........................................................................................................... 5
FIGURES
Figure 1 Site Location Map
Figure 2 Sample Location Map
TABLES
Table 1 Summary of Soil Analytical Results
APPENDICES
Appendix A Laboratory Data Sheets and Chain of Custody Records
Appendix B Non-Hazardous Waste Disposal Manifests
Appendix C Photographic Log
Drum Removal Report
Shade Valley Road
Charlotte, North Carolina
ECS Project No. 49-3925
March 31, 2017
1
1.0 EXECUTIVE SUMMARY
The subject site is located off Shade Valley Road in Charlotte, Mecklenburg County, North
Carolina. According to the Mecklenburg County GIS website, the site consists of approximately
11.3 acres identified as Mecklenburg County Parcel Identification Number 16105208. During
site redevelopment activities, a damaged drum containing an oily liquid was uncovered amidst
buried building debris (i.e. tar roofing/shingles). A sample of the drum contents was collected
on February 6, 2017 for disposal purposes.
On March 2, 2017, ECS observed the excavation and removal of the damaged drum and
impacted soils/building debris to a depth of approximately two feet below the ground surface
(bgs). Approximately five tons of petroleum-impacted soils were removed from the excavation
and transported off-site for disposal. Due to the drum being surrounded by roofing tar and
shingles, ECS personnel collected a sample of the nearest available soil to the base of the
excavation. Laboratory analysis of the soil sample collected at the base of the excavation
detected various semi-volatile organic compounds (SVOCs) at levels above their respective
Industrial/Commercial Health Based Preliminary Soil Remediation Goals. The drum was located
within buried construction debris consisting of rolled tar roofing and shingles. ECS attributes the
elevated concentrations of the constituents detected (i.e. Benzo(a)anthracene, Benzo(a)pyrene,
Benzo(b)fluoranthene, Bezno(g,h,i)perylene, Benzo(k)fluoranthene, Chrysene,
Dibenzo(a,h)anthracene, Dibenzofuran, Ideno(1,2,3-cd)pyrene, and Naphtlane) to the presence of
roofing tar and asphalt shingles. The building debris is being removed and disposed of at a
construction debris landfill.
A. OWNERSHIP OF PROPERTY:
Oakhurst Town Home Lots, LLC
136 Main Street
Pineville, North Carolina 28134
B. FACILITY INFORMATION:
Shade Valley Road
Charlotte, Mecklenburg County, North Carolina
Latitude: 35° 11’ 40.19” N Longitude: 80° 46’ 47.95” W
(From Google Earth)
C. CONTACTS:
Primary Contact: Ms. Susan Rosenblatt
Oakhurst Town Home Lots, LLC
136 Main Street
Pineville, North Carolina 28134
Excavation Contractor: ADC Sitework
Marvin Garcia
General Superintendent
(980) 230-3725
Drum Removal Report
Shade Valley Road
Charlotte, North Carolina
ECS Project No. 49-3925
March 31, 2017
2
Soil Disposal Contractor Contaminant Control Inc. (CCI)
281 Lane Parkway
Salisbury, North Carolina 28146
Primary Consultant: ECS Southeast, LLP
1812 Center Park Drive, Suite D
Concord, North Carolina 28217
(704) 525-5152
Laboratory: Prism Laboratories, Inc.
48 Springbrook Road
Concord, North Carolina 28078
D. SITE CHARACTERISTICS:
The subject site is located off Shade Valley Road in Charlotte, Mecklenburg County, North
Carolina. According to the Mecklenburg County GIS website, the site consists of approximately
11.3 acres identified as Mecklenburg County Parcel Identification Number 16105208.
As determined from the USGS Topographic Map Charlotte East, North Carolina Quadrangle
(Figure 1), the site’s elevation is approximately 750 feet above mean sea level (msl). Surface
runoff on the site is generally to the east towards an unnamed tributary of Edwards Branch
According to the Geologic Map of North Carolina (1985), the subject property is situated in the
Charlotte Belt of the Piedmont Physiographic Province with the underlying bedrock composed of
granitic rock. The Piedmont Physiographic Province is characterized by gently rolling
topography, deeply weathered bedrock, and a relative paucity of solid outcrop. Rocks are
strongly weathered in the Piedmont's humid climate and bedrock is generally buried under a
thick (2-20 m) blanket of saprolite. Outcrops are commonly restricted to stream valleys where
saprolite has been removed by erosion.
The soils encountered in this area are the residual product of in-place chemical weathering of
rock presently underlying the site. In general, shallow unconfined groundwater movement within
the overlying soils is controlled largely by topographic gradients. However, as the groundwater
percolates downward to the bedrock, it becomes controlled by the orientation of the rock
fracture systems. Thus, the direction of groundwater movement may not be consistent with the
reflecting topography.
In the Piedmont Physiographic region, groundwater generally occurs under water table
conditions. Movement of groundwater under water table conditions is generally from higher to
lower elevations. Please note that fluctuations in the groundwater level can be expected
depending on variations in precipitation, run-off, and other factors not evident at the time of
subsurface exploration. Normally, the highest groundwater levels occur in late winter and spring
and the lowest levels occur in the late summer and fall. Groundwater was not encountered
during excavation.
Drum Removal Report
Shade Valley Road
Charlotte, North Carolina
ECS Project No. 49-3925
March 31, 2017
4
2.0 SOIL SCREENING, AND EXCAVATION PROCEDURES
ECS Southeast, LLP (ECS) was notified on February 6, 2017 that liquid, presumed to be oil,
was observed while removing buried construction debris consisting of roofing tar and shingles
during grading operations at the site. ECS personnel mobilized to the site on February 2, 2017
to observe the area and identify the source of the liquid. While onsite, ECS identified that the
source of the liquid was a damaged 55-gallon drum and collected a sample of the contents for
disposal purposes. The sampler, wearing new nitrile gloves placed the sludge into laboratory-
supplied sample containers which were shipped to Prism Laboratory under chain-of-custody
protocol. Because the source of drummed liquid was unknown, the sample was analyzed for
total petroleum hydrocarbons (TPH) diesel range and gasoline range organics (DRO/GRO)
using EPA Method 8015C, volatile and semi-volatile organic compounds (VOCs/SVOCs) using
EPA Methods 8260 and 8270, oil and grease using EPA Method 9017, and toxicity
characteristic leaching procedure (TCLP) VOCs, SVOCs, and RCRA metals. The subsequent
analysis determined the sludge was non-hazardous and petroleum based. Laboratory data
sheets and chain-of-custody records for the sample is provided in Appendix A. The drum was
covered with and placed on plastic to prevent cross contamination prior to disposal activities.
On March 2, 2017, ECS mobilized to the site to observe the removal of the damaged drum and
impacted soils surrounding the drum. ADC Sitework, the onsite contractor, excavated the drum
and impacted soil and direct loaded the contents onto a truck provided by Contaminant Control ,
Inc (CCI). The soil was screened with a photo-ionization detector (PID) for relative levels of
volatile organic vapors and checked for visual and olfactory evidence of contamination.
Evidence of soil contamination including odors and elevated PID readings were identified.
Impacted material was removed until the excavation reached a depth of approximately two feet
bgs. Approximately five tons of petroleum-impacted soil was removed from the area and
transported off-site for disposal. The soil was transported by CCI to Republic Services in
Charlotte, North Carolina. The Non-Hazardous Waste Disposal Manifests (Petroleum Impacted
Soil) are included in Appendix B.
Following removal of the impacted soil, ECS personnel collected a soil sample from the base (S-1)
of the excavation. The soil sample location is shown on Figure 2. The sampler, wearing new nitrile
gloves for each sample, placed the soil into laboratory-supplied sample containers which were
shipped to Prism Laboratory under chain-of-custody protocol. Laboratory data sheets and chain-of-
custody records for the sample is provided in Appendix A. The soil samples were analyzed for
VOCs and SVOCs using EPA Methods 8260 and 8270 respectively. Photographs of the area are
provided in Appendix C.
3.0 RESULTS
Laboratory analysis of the soil sample collected at the base of the excavation detected various
semi-volatile organic compounds (SVOCs) at levels above their respective Industrial/Commercial
Health Based Preliminary Soil Remediation Goals. The drum was located within buried
construction debris consisting of rolled tar roofing paper, roofing tar, and asphalt shingles. The
results are summarized in Table 1.
Drum Removal Report
Shade Valley Road
Charlotte, North Carolina
ECS Project No. 49-3925
March 31, 2017
5
4.0 CONCLUSIONS
A damaged drum containing an oil based liquid was discovered during redevelopment activities at
a site off of Shade Valley Road in Charlotte, North Carolina. ECS observed the removal of the
drum and the excavation of approximately five tons of impacted soil and roofing material from the
area for offsite disposal. Post excavation sample analysis detected various SVOCs at levels above
the Residential and Industrial/Commercial Health Based PSRGs. ECS attributes the elevated
concentrations of the constituents detected (i.e. Benzo(a)anthracene, Benzo(a)pyrene,
Benzo(b)fluoranthene, Bezno(g,h,i)perylene, Benzo(k)fluoranthene, Chrysene,
Dibenzo(a,h)anthracene, Dibenzofuran, Ideno(1,2,3-cd)pyrene, and Naphtlane) to the presence of
roofing tar and asphalt shingles.
5.0 RECOMMENDATIONS
ECS recommends that a copy of this report be submitted to the North Carolina Department of
Environmental Quality (NCDEQ) – Mooresville Regional Office (MRO), Brownfields Section for
their review. The remaining material, asphalt shingles, roofing paper and roofing tar, should be
properly disposed at an approved disposal facility.
6.0 QUALIFICATIONS
The activities and evaluative approaches used in this assessment are consistent with those
normally employed in assessments and remediation projects for surface discharges of petroleum
compounds. ECS’ evaluation of site conditions has been based on our understanding of the
project information and the data obtained during our field activities.
This report is provided for the use of Oakhurst Town Home Lofts, LLC and the NCDEQ. This
report is not intended to be used or relied upon in connection with other projects or by other
unidentified third parties. The use of this report by undesignated third party or parties will be at
such party’s sole risk and ECS disclaims liability for such third party use or reliance.
FIGURES
FIGURE 1
SITE LOCATION MAP
OAKHURST SITE
SHADE VALLEY ROAD
CHARLOTTE, MECKLENBURG COUNTY, NORTH CAROLINA
ECS PROJECT NO. 49-3925
SOURCE:
USGS TOPOGRAPHIC MAP:
CHARLOTTE EAST, DATED 2016
NORTH CAROLINA QUADRANGLE
SCALE: 1” = 2,000’
SITE
LEGEND
SOURCE:
GOOGLE EARTH
2015 AERIAL PHOTOGRAPH
(VIA THE INTERNET)
SCALE AS SHOWN
FIGURE 2
SAMPLE LOCATION MAP
OAKHURST SITE
SHADE VALLEY ROAD
CHARLOTTE, MECKLENBURG COUNTY, NORTH CAROLINA
ECS PROJECT NO. 49-3925
APPROXIMATE LOCATION OF SOIL SAMPLE
S-1
Drum
Location
TABLES
Parameter ANALYTICAL RESULTS
Sample ID S-1
Collection Date 3/2/17
Sample Depth 2ft
Semivolatile Organic Compounds by GC/MS
1-Methylnaphthalene 5.7 0.055 18 73
2-Methylnaphthalene 9.8 1.6 48 600
3/4-Methylphenol 0.66J --12.6 164
Acenapthene 23 8.4 720 9,000
Anthracene 37 660 3,6000 46,000
Benzo(a)anthracene 83 0.18 0.16 2.9
Benzo(a)pyrene 66 0.059 0.016 0.29
Benzo(b)fluoranthene 90 0.60 0.16 2.9
Benzo(g,h,i)perylene 32 7,800 -- --
Benzo(k)fluoranthene 26 5.9 1.6 29
Chrysene 76 18 16 290
Dibenzo(a,h)anthracene 9.3 0.19 0.016 0.29
Dibenzofuran 20 5.2 14.6 200
Fluoranthene 180 330 480 6,000
Fluorene 27 56 480 6,000
Ideno(1,2,3-cd)pyrene 37 2.0 0.16 2.9
Naphthalene 36 0.21 3.8 17
Phenanthrene 170 68 ----
Pyrene 140 220 360 4,600
Volatile Organic Compounds by GC/MS
1,2,4-Trimethylbenzene 0.0042J 6.7 11.6 48
1,3,5-Trimethlybenzene 0.0028J 6.7 156 182
Acetone 0.054J 24 12,200 100,000
Notes:
PSRG - Preliminary Soil Remediation Goal
Results presented in milligrams per kilogram (mg/kg), analogous to parts per million (ppm)
BRL = Compound not detected at a concentration above the method reporting limit
Bold denotes a concentration above the Protection of Groundwater PSRG
Underline denotes a concentration above the Unrestricted Use Health Based PSRG
Italics denotes a concentration above the Industrial/Commercial Health Based PSRG
Unrestricted
Use Health
Based PSRG
Industrial/
Commercial
Health Based
PSRG
TABLE 1: SUMMARY OF SOIL ANALYTICAL RESULTS
OAKHURST SITE
ECS PROJECT NO. 49-3925
CHARLOTTE, MECKLENBURG COUNTY, NORTH CAROLINA
Protection of
Groundwater
PSRG
COMPARISION CRITERIA
APPENDICES
Appendix A
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Appendix B
Appendix C
PHOTOGRAPH LOG
OAKHURST SITE
SHADE VALLEY ROAD
CHARLOTTE, MECKLENBURG COUNTY, NORTH CAROLINA
ECS PROJECT NO. 49-3925
Photo 1: View of the soil bank where the drum was located and surrounded by construction debris.
Photo 2 View of the damaged drum.