NCD000813592_20000808_GA-Pacific Corp Hdwd Saw_FRBCERCLA RI_Draft Remedial Investigation Report-OCR

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Response Action Contract
For Remedial, Enforcement Oversight, and Non-time
Critical Removal Activities at Sites of Release or
Threatened Release of Hazardous Substances
In EPA Region VIII
U.S. EPA Contract No. 68-W5-0022
Draft
Remedial Investigation Report
Georgia-Pacific Hardwood Site
Plymouth, North Carolina
. Work Assignment No.: 027-RICO-04RF
Document Control No.: 3280-027-RT-RIRT-08101
August 8, 2000
Prepared for:
U.S. Environmental Protection Agency
Region IV
Atlanta, Georgia
Prepared by:
CDM Federal Programs Corporation
2030 Powers Ferry Road, Suite 490
Atlanta, Georgia 30339
RECEIVED
SEP O 12000
SUPERFUND SECTION
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Prepared by:
Response Action Contract
For Remedial, Enforcement Oversight, and Non-time
Critical Removal Activities at Sites of Release or
Threatened Release of Hazardous Substances
In EPA Region VIII
U.S. EPA Contract No. 68-WS-0022
Draft
Remedial Investigation Report
Georgia-Pacific Hardwood Site
Plymouth, North Carolina
Work Assignment No.: 027-RICO-04RF
Date:
Terence Chu~
a ger
Date:
Mike rofit
Te9'111cal Rz5iew~f?' -, ,.,,---
[?,,,t,•1 r, Cvctl,l:Yf-.,1/ Approved by: _____________ _ Date:
Gary P. Clemons, Ph.D.
Region 4 Program Manager
CDM Federal Progroms Corporation
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Executive Summary
The Georgia-Pacific Hardwood Sawmill Site (hereinafter referred to as the "Georgia-
Pacific Site" or "the site"), is defined as the 24-acre area located on Plywood Drive
· .,__ within the city limits of Plymouth, North Carolina. Contaminants consisting primarily
\, ·4,. \r-'I o\" of dioxins/ furans, polynuclear aromatic hydrocarbons, pentachlorophenol, pesticides,
~" _ yl} p~hlorinated..b.iJ2henyls, and a few heavy metals were released into the
'if'-. · v~ environment during past sawmill wood treating operations. Having been placed on
f"t;(J ~ I the National Priorities List in 1999, a remedial investigation and feasibility study of 1/ the Georgia-Pacific Site is thus required as promulgated by the Comprehensive
Environmental Response, Compensation, and Liability Act and the National
Contingency Plan. This document is the draft Remedial Investigation Report and was
prepared by CDM Federal Programs Corporation in cooperation with U.S.
Environmental Protection Agency Region IV Science and Ecosystem Support Division.
Soil, surface water, sediment, al}1 ~oundwater samples, both onsite and offsite, were
collected by Science and EcosiMem Support Division personnel and sample analyses
were performed by the EPA' s Contract Laboratory Program. Dioxins and Furans
were analyzed by an EPA Special Purchase Agreement laboratory because of the
special requirement for dioxins and furan analyses. Analytical results, were validated ~-\/ l:JQ _'jf. J,y the Science and Ecosystem Support Division Quality Assurance personnel.
{f'\\~~ ~ /following is a summary of the analytical results:
The
~ ~ -:\ . f t
Analyses of soil sam Jes collected indicate extensive contamination by ij~:r ~~ i
\j'
~\)
d1oxms urans, polynuclear aromatic hydrocarbons, polychlorinated
biph_enyls, and inorganics. This contamination seemed to be focused in an area
centrally located on the site property where most past operations were located.
~ was indication of offsite contamination from site related constituents,
~ever the concentrations were lower than onsite concentration.
• Surface waters at the site discharge into the Roanoke River. Analyses of <...( surface water and sediment samples collected from the intermittent drainage J '--ditches located onsite indicate contamination by arsenic and manganese in
VJ ~' ~ surface water, and by dioxins/ furans, acetone, methyl ethyl ketone,
~ /'poly;uclear aromatic hydrocarbons, arsenic, lead, and zinc in sediments.
+¥
c_l,o-''t, ~-"' ;;-{-. ) d1' .:_1,V.. -f-
CDM Federal Pmi:r:mu CorporJ1i,t: ~
SPIN 28/EXSUM.WPD •~ ~;'lo '1."' ii
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Executive Summary
The site is underlain by a shallow surficial unconfined aquifer. Groundwater
flow at the site is likely toward the Roanoke River, where it discharges.
Analyses of groundwater samples at the site indicate contamination by arsenic
and manganese. Concentrations of some other contaminants such as
aluminum, iron, and manganese are above other criteria such as Secondary
Drinking Water Maximum Contaminant Levels (MCLs).
Following a initial review of the RI data, EPA prepared site specific removal action
levels of nine constituents of concerns and performed a removal action at the site. The
removal action consisted of excavation of soil from contaminated grids and ultimately
shipping soil, debris, buildings, and tanks offsite. Following the removal action, EPA
Science and Ecosystem Support Division personnel sampled the bottom and sides of
the excavations to confirm compliance to site specific removal action levels and then
the site was backfilled with clean soil.
Based on the results of the RI and considering the removal action data, the following
actions are recommended:
V.
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CDM Federal Proi,:rJm.1 Corporation
SPIN 28/EXSUM.WPO
Remedial action objectives for soil and groundwater contamination at
the site should be established based on human health exposure risks, as
well as the potential for future contaminant migration from one
medium to another (e.g., soils to groundwater).
Alternatives for reducing soil and groundwater contamination at the
site to achieve the established remedial action objectives should be
evaluated, and the most cost-effective alternative for each
implemented.
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List of Acronyms
ASTs
bis
Above ground storage tanks
below land surface
BBLES Blasland, Bouck & Lee, Engineers and Scientists, Inc
BRA Baseline Risk Assessment
CDM Federal CDM Federal Programs Corporation
CERCLA Comprehensive Environmental Response, Compensation, and Liability
Act
CFR Code Federal Regulations
CLP
coc
COPC
cPAH
cy
EPA
FS
HSWA
MCL
MCLG
ms!
MW
NCP
ND
NPL
Contract Laboratory Program
Contaminant of Concern
Contaminant of Potential Concern
Carcinogenic Polynuclear Aromatic Hydrocarbon
cubic yard
Environmental Protection Agency
Feasibility Study
Hazardous and Solid Waste Amendments
Maximum Contaminant Level
Maximum Contaminant Level Goal
mean sea level
Monitor Well
National Contingency Plan
not detectable
National Priorities List
OCDD Octachlorodibenzodioxin
PAH
PCB
PCP
PRP
QA
QC
RCRA
RI
CDM Federal Prn1:rnn1s Corpomtion
SPIN 2B/EXSUM.WPD
polynuclear aromatic hydrocarbon
polychlorinated biphenyl
Pentachlorophenol
Potentially Responsible Party
Quality Assurance
Quality Control
Resource Conservation and Recovery Act
Remedial Investigation
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List of Acronyms (continued)
ROD
RPM
SAP
SESD
SIP
SSI
SSRAL
svoc
TAL
TCDD
TCE
TCL
TEF
TEQ
voe
Record of Decision
Remedial Project Manager
Sampling and Analysis Plan
Science and Ecosystem Support Division
Site Inspection Prioritization
Screening Site Inspection
Site specific removal action level
Semi-volatile organic compound or Extractables
Target Analyte List
2,3,7,8-Tetrachlorinated dibenzodioxin
Trichloroethene
Target Compound List
toxicity equivalent factor
toxicity equivalent value
Volatile organic analyte
2378TCDD TEQ 2,3,7,8 tetrachlorodibenzodioxin toxicity equivalent concentration
CDM Federal Pmi:rnm• Cmporntion
SPIN 28/EXSUM.WPO V
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CONTENTS
EXECUTIVE SUMMARY ................................................... .
LIST OF ACRONYMS ...................................................... .
1.0 INTRODUCTION ................................................... .
1.1 Purpose of Report ............................................ ..
1.2 Site Description ............................................... .
1.3 Environmental Setting ......................................... .
1.4 Site Operations History ........................................ .
1.5 Previous Sampling Investigation Results ......................... .
1.6 Nature of Problem ............................................. .
1.7 RI Field Investigation Summary ................................. .
1.8 Removal Action ............................................... .
1.9 Overview of Report ............................................ .
2.0 SOIL SAMPLING INVESTIGATION ................................... .
3.0
4.0
5.0
6.0
2.1 Purpose and Scope ............................................ .
2.2 Methods ..................................................... .
2.3 Summary .................................................... .
SURFACE WATER/SEDIMENT SAMPLING INVESTIGATION .......... .
3.1 Purpose and Scope ............................................ .
3.2 Methods ..................................................... .
3.3 Summary .................................................... .
GROUNDWATER SAMPLING INVESTIGATION ....................... .
4.1
4.2
4.3
Purpose and Scope ............................................ .
Methods ..................................................... .
Summary .................................................... .
CONTAMINANT FATE AND TRANSPORT ANALYSIS ................. .
5.1 Contaminant Migration ........................................ .
5.2 Contaminant Persistence ....................................... .
QUALITY ASSURANCE REPORT ..................................... .
6.1 Controlling Documents ........................................ .
6.2 Field Investigation ............................................. .
6.3 Field Quality Control Procedures ................................ .
6.4 Data Validation ............................................... .
CDM Federal Programs Corporation
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1-1
1-1
1-2
1-8
1-11
1-12
1-13
1-14
1-15
1-16
2-1
2-1
2-1
2-3
3-1
3-1
3-1
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4-1
4-1
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5-1
5-7
6-1
6-1
6-1
6-1
6-1
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6.5 Data Evaluation ............................................... .
6.6 Precision, Accuracy, Representativesness, Comparability, Completeness
6.7 Audits ...................................................... .
7.0 RI SUMMARY AND CONCLUSIONS ................................. .
8.0 REFERENCES ....................................................... .
APPENDIX A
APPENDIXB
CDM Federal Programs Corporation
SPINB2/SECT4
RI Analytical Data and Quality Assurance Data
Removal Action Remaining Soil Analytical Data
6-1
6-1
6-1
7-1
8-1
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Tables
2-1
2-2
2-3
2-4
2-5
3-1
3-2
3-3
3-4
4-1
4-2
5-1
5-2
Soil Sampling Summary -Volatile and Extractable Organics ........... .
Soil Sampling Summary -Pesticides and PCBs ...................... .
Soil Sampling Summary -Dioxins and Furans ....................... .
Soil Sampling Summary-Inorganics ............................... .
Removal Action.Confirmation Analysis ............................ .
Surface Water Sampling Summary ................................. .
Sediment Sampling Summary -Dioxins/Furans ..................... .
Sediment Sampling Summary -Organics ........................... .
Sediment Sampling Summary -lnorganics .......................... .
2-5
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2-41
2-59
2-89
3-3
3-4
3-5
3-6
Groundwater Sampling Field Measurements . . . . . . . . . . . . . . . . . . . . . . . . . 4-3
Groundwater Sampling Summary . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 4-4
Estimated Physical and Chemical Properties of the Contaminants of Concern 5-2
Estimated Degradation Potential of the Contaminants of Concern. . . . . . . 5-9
CDM Federal Programs Corporation
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Figures
1-1 Site and Surrounding Properties Map
1-2 Former Site Usage and Features .................................... .
2-1 Onsite and Off site Soil Sampling Locations ........................... .
2-2 P AHs and cPAHs Detected in Onsite Soil ............................ .
2-3 PAHs and cP AHs Detected in Offsite Surface Soil ..................... .
2-4 PCBs Detected in Onsite Soil ....................................... .
2-5 Dioxins and Furans (TEQ) Detected in Onsite Soil ..................... .
2-6 Dioxins and Furans (TEQ) Detected in Onsite Subsurface Soil ........... .
2-7 Metals Detected in Onsite Soil ...................................... .
3-1 Surface Water/Sediment Sampling Locations ........................ .
3-2 Inorganic Contaminant Distribution in Surface Water ................. .
3-3 Dioxin/Furan Contaminant Distribution in Sediment ................. .
3-4 VOC Contaminant Distribution in Sediment ......................... .
3-5 P AH Contaminant Distribution in Sediment ......................... .
3-6 Inorganic Contaminant Distribution in Sediment ..................... .
4-1 Groundwater Sampling Locations .................................. .
4-2 Inorganic Contaminant Distribution in Groundwater .................. .
CDM Federal Programs Corporation
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1.0 Introduction
1.1 Purpose of Report
The Georgia-Pacific Hardwood Sawmill Site (hereinafter referred to as the "Georgia-
Pacific Site" or "the site"), is defined as the 24-acre area located on Plywood Drive
within the city limits of Plymouth, North Carolina. Contaminants consisting primarily
of dioxins/ furans, polynuclear aromatic hydrocarbons (PAHs), pentachlorophenol
(PCP), pesticides, polychlorinated biphenyls (PCBs), and a few heavy metals were
released into the environment during past sawmill wood treating operations. The site
was placed on the National Priorities List (NPL) in October of 1999. Having been
placed on the NPL, a remedial investigation and feasibility study (RI/FS) of the
Georgia-Pacific Site is thus required as promulgated by the Comprehensive
Environmental Response, Compensation, and Liability Act (CERCLA) and the
National Contingency Plan (NCP).
The purpose of the RI/FS process is to gather, as quickly and cost-effectively as
possible, enough information about the site to support an informed risk management
decision regarding which remedy appears to be most appropriate for the site. The RI
serves as the mechanism for collecting data to characterize site conditions, determine
the nature and extent of the waste, assess risk to human health and the environment,
and conduct treatability testing as necessary to evaluate the potential performance
and cost of the treatment technologies being considered. The FS serves as the
mechanism for development, screening, and detailed evaluation of alternative
remedial actions. The various steps, or phases, of the RI/FS process are briefly
described below:
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COM FeJcrnl Programs Corporation
SPINBVSEC1.WPD
Scoping: -the initial planning phase of the RI/FS, including the
preliminary assessment and site investigation
Site Characterization -definition of the nature and extent of contamina-
tion, identification of applicable or relevant and appropriate require-
ments (ARARs), and development of the baseline risk assessment
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Section 1
Introduction
Development and Screening of Alternatives -identification of potential
treatment technologies, screening of these technologies, assembly of the
technologies into alternatives, and screening of the alternatives
Treatabilit;y Investigations -bench-or pilot-scale testing to assess the
feasibility of a technology
Detailed Analysis of Alternatives -further refinement of the
alternatives, analysis of the alternatives with respect to nine evaluation
criteria, and comparison of the alternatives against each other.
The RI and FS are conducted concurrently so that data collected in the RI influence the
development of remedial alternatives in the FS, which in turn affects the data needs
and scope of the treatability studies and any additional field investigations.
The purpose of this report is to document the results of the RI field investigation
performed by EPA for the Georgia-Pacific Site, and provide the information needed to
perform a human health and ecological risk assessment assessing the impacts of
contamination at the site, and a feasibility study evaluating potential remediation
alternatives, if necessary. This document is submitted to EPA in accordance with
Work Assignment No. 027-RICO-0401 under Contract No. 68-WS-0022.
1.2 Site Description
1.2.1 Location
The Georgia-Pacific Site is located on Plywood Drive within the city limits of
Plymouth, Washington County, North Carolina, approximately 0.5 miles east of the
downtown district. The geographic coordinates of the site are 35'52' 27" North
latitude and 76°44' 27.5" West longitude.
1.2.2 Physical Features
The site is approximately 24 acres in size, and is bounded to the north by the Roanoke
River, to the west by Atlantic Coast Railroad property, to the east by residential
properties, and to the south by the Plymouth High School and the Boy Scouts of
America property. A map of the site and surrounding properties is provided in
Figure 1-1. The site terrain is flat, low-lying with elevation increasing south of the
CDM Federal Prui:nims Corporarion
SPINB2/SEC1.WPD 1-2
0 250' - -
Roanoke
River
500' - --'
Georgia-Pacific Hardwoods
a Pl outh, North Carolina
GEORGIA
PACIFIC
Sl1E
Scouts
0 Hut
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... :\
~
Footbol~ Field ✓
LEGEND:
... ... ...
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Site Map
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PROPERlY BOUNDARY
INTERMITTENT DRAINAGE
DITCH
MARSHY AREA
RIVER
TREE LINE
RAILROAD
Figure No.
1-1 ~ CDM Federal ~IUDII CorporaUon
~.__·-__ .,_ .... _-_· __ .. ____ __,_ ________________________ ..J.._..:.7!.:./0::.:0:..___J
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Section 1
Introduction
site. Portions of the site are exposed hard packed dirt, gravel, asphalt, or concrete,
while other areas are overgrown with grass, trees, and heavy vegetation. The site is
presently unoccupied, and some of the former structures used in the past have been
demolished. Recently, the removal action activities further demolished and removed
other structures and materials from the site and all that remains is one smoke stack.
Figure 1-2 depicts the site layout including all the former structures.
As indicated in Figure 1-2, the site has been subdivided into five separate areas to
allow for a better description and understanding of former activities at the site. These
five areas are described below.
1.2.2.1 Former Finished Wood Products Storage Area/Outerbanks
Contractors Asphalt Mixing Plant
This is the area that starts at the entrance to tl1e site and continues to the south of the
former railroad spur bed where finished wood products were stored. This area was
also subsequently used by Outerbanks Contractors for its asphalt mixing plant
operations (see Section 1.4). It is bordered to the south by the perimeter drainage
ditch; to the north by the former railroad bed spur; and abuts the property boundaries
to the east and west.
Most of the surface cover in this area is vegetated with a variety of grasses. Significant
features in this area include a pre-fabricated metal storage shed erected by
Outerbanks Contractors and the access gate to the site from Plywood Road (installed
recently by EPA). The area in and around the metal storage shed is the location of
several containers (drums, cans, canisters, bags, etc.). Prior to a removal action
conducted by the PRPs (see Section 1.8), approximately 200 cubic yards of asphalt
stockpiled in numerous piles were located in the center of this area. The asphalt
stockpile area was roughly rectangular in shape with dimensions of approximately
260 feet by 230 feet (approximately 1.4 acres). During the removal action, the property
owner eliminated approximately 50% of the asphalt piles by recycling the asphalt, and
moved the remaining asphalt to the front of the storage shed.
CDM Fedeml Pm!:ra1m Corporation
SPINB2/SEC1.v'IPD 1-4
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0 -300' -600'
Georgia-Pacific Hardwoods j __ P_l.._m_o_u_t_h_,_N_o_r_th_-_c_a_ro_l_i_n_a---t
•
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LEGENQ;
-···-RIVER EDGE
r--v-y-TREE LINE
----PROPERTY BOUNDARY
--- -INTERMITTENT DRAINAGE DITCH
• • . MARSHY AREA
~ RAILROAD
Figure No.
Former Site Usage & Features 1-2
~ CDM Federal Pr,:1,rame Corporation
~ ,_,, __ • .... 6/00 ~---------------------------
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Section 1
Introduction
Prior to the removal action, two 400-gallon aboveground storage tanks (ASTs), one
800-gallon AST, and one 2,500-gallon tanker trailer were also located in this area.
During the removal action, the two 400-gallon ASTs were removed from the site. The
remaining two tanks were left onsite, by request of the property owner, to be recycled
later. A septic tank located in the south-central part of this area was also discovered
during the removal action and left in place with a piece of concrete placed over the
entrance.
1.2.2.2 Former Finished Wood Products Storage/Employee Parking
Area
This is the area extending from the Roanoke River south to the bed of the former
railroad spur where finished wood products were stored and employee vehicles were
parked. A portion of this area was also used by Outerbanks Contractors for their
asphalt mixing operations. It is bordered to the south by the former railroad spur bed;
to the north by the Roanoke River; to the west by the property boundary; and to the
east by the Raw Timber Process Area.
Most of the surface cover in this area is vegetated with a variety of grasses, shrubs,
and saplings. Significant features include the office house located inside the entrance
gate from Plywood Road and the pier on the Roanoke River (in the western comer of
the site) that was constructed after 1984. Approximately 200 cubic yards of soil
stockpiled in two piles are also located at the western margin of this area. The source
of the soil is unknown.
1.2.2.3 Former Raw Timber Process Area
The Former Raw Timber Process Area is located in the north-central section of the site,
extending from the Roanoke River to the former locations of several finished wood
product storage sheds and a dry kiln. This area supported the timber process
buildings where raw timber logs were debarked, sawed, planed, and (in some
instances) surface treated with a liquid anti-stain formulation (dilute
pentachlorophenate to prevent staining from mold and mildew growth) and allowed
to dry. It was also used by Outerbanks Contractors for its asphalt mixing plant
COM Federal Programs Cnrpnrntion
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Section 1
Introduction
operations. The area is bordered to the south by the former railroad bed spur; to the
north by the Roanoke River; to the east by an intermittent drainage ditch; and to the
west by the Former Finished Wood Products Storage/Employee Parking Area.
Most of the surface cover in this area is a mix of remnant buildings, foundations, and
concrete pads with a dense cover of grasses, shrubs, and trees. Significant features
prior to the removal action included a machine shop building, log deck ramp, boiler
house and stack, and concrete foundations and storage pads. During the removal
action, the boiler house and machine shop were demolished, and most of the
demolition debris was transported offsite. Only the machine shop brick was left
onsite in this area, at the request of the property owner.
Prior to the removal action, one 20,000-gallon AST, and one 7,500-gallon tanker trailer
were also located in this area. These two tanks were thought to contain petroleum
products. During the removal action, the tanker trailer was removed from the site.
The remaining 20,000 AST was left onsite, by request of the property owner, to be
recycled later.
1.2.2.4 Former Raw Timber Receiving Area
The Former Raw Timber Receiving Area is located in the easternmost portion of the
site where raw timber logs were received and stored prior to processing. This area is
bordered to the south by the Former Finished Wood Products Storage
Area/Outerbanks Contractors Asphalt Mixing Plant; to the north by the Roanoke
River; to the west by the Former Raw Timber Process Area; and abuts the property
boundary and perimeter intermittent drainage ditch to the east. Most of this area's
surface cover is densely vegetated with a variety of shrubs and trees.
1.2.2.5 Intermittent Drainage Ditches
This area is comprised of the following two intermittent drainage ditches:
•
COM Fcdernl Pru1:rnms C.irpnratinn
SPINB2/SEC1.WPD
Perimeter Intermittent Drainage Ditch -this ditch borders the property
boundary from the site access gate on Plywood Road to its confluence
with the Roanoke River at the northern corners of the property.
1-7
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Section 1
Introduction
• Raw Timber Process Area Intermittent Drainage Ditch -this ditch
extends from the former railroad spur bed to its confluence with the
Roanoke River, separating the Raw Timber Process Area from the Raw
Timber Receiving Area.
1.2.3 Demography
The estimated population within a 4-mile radius of the site is approximately 7,000.
The nearest residence is located approximately 700 feet east of the site. The Plymouth
High School is located 0.27 miles south of the site. A Boy Scouts of America facility is
located adjacent to the Plymouth High School. The land to the north of the site, and
immediately north of the Roanoke River, is classified as wetlands.
Access to the site is restricted by a gate; however, there are no fences around the
property. A zone of dense woods separates the site from the Plymouth High School,
the Boy Scouts of America facility, and residential properties. There has been visual
evidence that people trespass onsite and use the docks for recreational fishing in the
Roanoke River.
1.2.4 Surrounding Land/Water Use
The principal land use in the immediate vicinity of the site is residential and
institutional. The citizens of Plymouth have water supplied from one of three sources:
the city of Plymouth Public Works Water System, the Washington County system, or
private wells. The city and county water supplies are obtained from 4 municipal
wells located within 1-2 miles southwest of the site. It is not known how many private
or community wells are currently being used within a four-mile radius of the site.
There are no surface water intakes located within a fifteen-mile surface water pathway
downstream from the site.
1.3 Environmental Setting
1.3.1 Physiography /Topography
Washington County, North Carolina lies in the Atlantic Coastal Plain Physiographic
Province. This portion of the Atlantic Coastal Plain is primarily characterized by
CDM Fe<lcral ProJ.:r.tms Cmporatiun
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Section 1
Introduction
extensive, flat coastal swamps and marshes. Approximately half of the land mass
within a four-mile radius of the site is wooded marsh or wetland. The elevation of the
site is approximately 5 feet above mean sea level (ms!), and is slightly below 5 feet ms!
in the nearby wetland areas. Elevations increase to 15 feet ms! to the south of the site.
1.3.2 Climate/Meteorology
The climatological data for Washington County, North Carolina is representative of
the climate in the Plymouth area. Northwestern Washington County has a mean
annual precipitation of approximately 50 inches and a mean annual lake evaporation
of 41 inches. Therefore, the net annual precipitation is 9 inches. The 2-year, 24-hour
rainfall is approximately 4 inches.
1.3.3 Geology
The regional geology of Washington County is characterized by complexly
interbedded sediments. The sediments are unconsolidated and consist primarily of
sand, silt, and clay transported by streams from the adjacent uplands of the Piedmont
and Blue Ridge Provinces. The surficial sediments at the site are approximately 25
feet thick, and are underlain by a confining layer which is 25 feet thick. The primary
geologic units in the Plymouth area are the Yorktown and Duplin Formations. The
Yorktown is generally characterized by fine-grained sands interspersed with varying
amounts of silt, clay, and shell beds, and sandy and silty limestones, while the Duplin
Formation contains fossiliferous sand, sandy limestone, silty limestone, and calcareous
silty sand.
The majority of the onsite soil is described as Tarboro sand, while the soil in the
adjacent wetlands and the small stream surrounding the property is described as
Muckalee loams. Tarboro sand is an excessively drained soil normally found on low
broad ridges commonly adjacent to the Roanoke River. The surface layer of this soil is
low in organic matter content. Permeability is rapid and the available water capacity
is low. The soil is well suited to most urban uses and provides a good support for
most structures. The Muckalee loam is a nearly level, poorly drained hydric soil. It is
subject to frequent flooding.
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Section 1
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1.3.4 Hydrogeology
The surficial aquifer in the area of the site is comprised of approximately 25 feet of
surficial deposits, underlain by a 25-foot confining layer. Depth to the water table in
the surficial aquifer at the site typically varies from 3.5 to 5 feet below land surface
(bis). Although no water level measurements have been collected at the site, typical
hydrogeology for such a site dictates that groundwater in the surficial aquifer most
likely flows toward and discharges into the Roanoke River during normal baseflow
conditions in the Roanoke River.
The surficial aquifer and the 25-foot confining layer are underlain by 40 feet of sand
and marl of the Yorktown Formation. The Yorktown Aquifer is a confined aquifer
which serves as a major source of water for portions of Washington County. The
Yorktown Aquifer is underlain by the confined Pungo Aquifer, which can be reached
90 feet below the land surface. The Yorktown Aquifer is underlain by a 25-foot
confining layer. Below this confining layer, the Castle Hayne Aquifer can be reached
at a depth of approximately 115 feet bis.
The extent of water withdrawal from the aquifers overlying the Castle Hayne in the
vicinity of the site is unknown; no groundwater targets have been identified for
aquifers in the area other than the Castle Hayne. The Castle Hayne Aquifer serves as
the principal source of groundwater in the Plymouth area, and consists of porous and
permeable limestone, sandy limestone, and sand. Hydraulic conductivity values in
the Castle Hayne Aquifer range from 15 ft/ day to 200 ft/ day. The Castle Hayne
Aquifer in the Plymouth area can be reached from 150 to 180 feet bis.
Recharge to the surficial aquifer is directly from precipitation. Recharge to the
underlying groundwater system occurs primarily in the upland interstream areas
where the sand layers crop out. Discharge from the system occurs by seepage to
streams, estuaries and the ocean. Movement of water from the recharge areas to
discharge is controlled primarily by the hydraulic gradients of the dipping beds.
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1.3.5 Surface Water Hydrology
Section 1
Introduction
The site is located immediately to the south of the Roanoke River. The Roanoke River
receives surface water from the site through direct runoff, and from several onsite
intermittent drainage ditches. The surface water pathway flows in an northeasterly
direction along the Roanoke River for approximately 6 miles, where it flows into the
Albemarle Sound. Surface waters in the Albemarle Sound flow eastward towards the
Atlantic Ocean for the remainder of the 15-rnile surface water pathway.
1.3.6 Wildlife and Natural Resources
The Roanoke River is classified as a "Class C" river with an "Sw" supplemental
designation. Class C waters are protected for aquatic life propagation and survival,
fishing, wildlife, secondary recreation, and agriculture. A fish consumption advisory
has been in effect for a period of years along the lower Roanoke River due to elevated
levels of dioxin in fish tissue. There are extensive wetlands around the site; however,
there are no known critical habitats of Federally-listed endangered species within the
vicinity of the site. There are several endangered and threatened species in
Washington County, North Carolina, including the bald eagle as a state and federally-
designated endangered species, and the golden eagle and the Waccamaw killifish as
state-designated endangered and threatened species.
1.4 Site Operations History
The site was originally owned and operated by the Atlas Plywood Company. There is
no information regarding Atlas's operations and waste management practices.
Georgia-Pacific reportedly bought the facility in 1950, and operated the facility until
1980 employing approximately 400 workers. Site operations involved debarking,
sawing, and planing rough hardwood timber from logs. Surface treatment of some
finished lumber took place using a conveyor belt and dip vat. The sawmill facility
was permanently closed after a 1983 fire destroyed the sawmill. Georgia-Pacific sold
the property to Decatur Partnerships, and the site was leased to Outerbanks
Contractors who used a portion of the site as an asphalt mixing plant, employing
approximately 10 workers. Allegedly, during the time of the asphalt mixing plant
operations, a spill of trichloroethene (TCE) caused by the North Carolina Department
CDM Fe<leml Prn):rntns Corporation
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Section 1
Introduction
of Transportation occurred in the Former Finished Wood Products Storage
Area/Outerbanks Contractors Asphalt Mixing Plant area of the site. The amount of
the spill was not determined for this report. The entire site is currently unoccupied
and inactive.
The wood treating process at the site involved passing wood through a dip vat located
on a conveyor system, where the wood was surface coated with preservatives and/ or
insecticides. After treatment, the wood was reportedly allowed to drip dry directly onto
the ground or onto concrete pads before being placed in the lumber storage areas. The
dip vat solutions contained pentachlorophenate, sodium meta borate, lindane, and other
chlorophenol compounds. Georgia-Pacific's Resource Conservation and Recovery Act
(RCRA) Part A Permit Application identified process wastes associated with the facility
included spent oil containing metals (D001-ignitable/D007-chrornium, D008-lead), spent
halogenated degreasing solvents (F001), spent non-halogenated degreasing solvents
(F003/F005), and bottom sediment sludge from the treatment of wastewater from the
wood treating process (K001). The amount of waste generated on a yearly basis by
Georgia-Pacific was estimated to be 20,000 pounds of D001/D007 /D008 waste, 375
pounds of F001/F003/F005 wastes, and 16,300 pounds of K001 waste. Wastes were
either incinerated onsite or transported to the county landfill.
1.5 Previous Sampling Investigation Results
Prior investigations at the site include the Preliminary Assessment conducted by the
North Carolina Division of Health Services on December 6, 1985, the Phase I Screening
Site Inspection (SSI) conducted by the NUS Corp. on October 11, 1989, the Phase II SSI
conducted by Greenhorne & O'Mara Inc. in September 1991, the Site Inspection
Prioritization (SIP) conducted by the Dynamac Corp. on April 15, 1994, and the
Expanded Site Inspection conducted by the North Carolina Department of
Environment, Health, and Natural Resources in June 1995. Sampling was performed
only during the Phase II SSI and the Expanded Site Inspection. During the Phase II SSI,
4 surface soil samples, 2 drainage ditch soil samples, and 3 temporary well point
groundwater samples were collected. During the Expanded Site Inspection, 5 surface
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Section 1
Introduction
soil samples, 1 drainage ditch soil sample, and 3 surface water/ sediment samples from
the Roanoke River were collected.
The analytical results from these investigations indicated that onsite soils have been
contaminated as a result of past operations. ·Elevated levels of dioxin/furan isomers,
metals, pesticides/PCB's, as well as purgeable and extractable organic compounds were
identified in the soils in the dip vat area during both sampling investigations. Elevated
levels of many of these compounds were also detected in the sediment samples from the
drainage ditches which carry site runoff to the Roanoke River. In addition, the Phase II
551 results indicate that onsite groundwater may have been contaminated with VOCs,
pesticides, and metals. However, no groundwater samples were collected during the
1995 ES! to confirm these results.
Surface water runoff from the site has resulted in site-related contamination in the
Roanoke River. Sediment samples collected during the 1995 ES! indicated the presence
of elevated levels of aluminum, arsenic, iron, lead, pentachlorophenol, (3 and/ or 4)
methyl phenol, benzo(b/k) fluoranthene, the dioxin/furans congeners 2,3,7,8-
tetrachlorodibenzodioxin (TCDD), 1,2,3,7,8-pentachlorodibenzodioxin, 1,2,3,4,7,8-
hexachlorodibenzodioxin, octachlorodibenzodioxin, and 2,3,7,8-tetrachlordibenzofuran.
1.6 Nature of Problem
As indicated above, many chemicals have been identified as having contaminated
various media at the site. Dioxin and pentachlorophenol are two of the principal
contaminants found in the onsite surface soil and river sediments. General physical,
chemical, and toxicity characteristics of these contaminants are presented below:
•
CDM Federal Prn,:rnms Corporacion
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Dioxin -Chlorinated dibenzo-p-dioxins are a class of compounds
referred to as dioxins. One form of dioxin, TCDD, is the most toxic form
of dioxin in humans. It is a colorless solid with no known odor. TCDD
does not occur in nature. Exposures to high levels of TCDD can cause
chloracne, a severe skin lesion that usually occurs on the head and upper
body. There is suggestive evidence that TCDD may cause liver damage,
and is suspected of causing cancer.
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Section 1
Introduction
Animal studies also suggest that exposure to high levels of dioxin may
cause liver damage in certain species. Exposure can also cause loss of
appetite, weight loss, digestive disorders, and death. Dioxin exposure
may also result in abnormal reproduction of offspring. Exposure to
TCDD has been proven to cause cancer in certain animals.
Pentachlorophenol -Pure pentachlorophenol exists as colorless crystals
with a very sharp odor when hot, but little odor at room temperature. ·
Pentachlorophenol in impure form can appear dark gray to brown dust,
beads, or flakes. Pentachlorophenol does not occur naturally. It is
widely used as a wood preservative for power poles, fence posts, lumber,
etc. Short-term exposures to pentachlorophenol can reportedly cause
harmful effects on the human liver, kidneys, skin, blood, lungs, nervous
system, and intestinal tract, and can cause death. The inhalation of the
sodium salt of pentachlorophenol by animals has proven to be extremely
toxic.
Thus, the results of the previous investigations indicate a threat to human health and
the environment may exist at the site. However, because the previous investigations
did not fully define the nature and extent of the contamination, further site
characterization was required to identify and assess the health and environmental
concerns related to the exposure routes substantiated through the previous
investigations.
1.7 RI Field Investigation Summary
The primary objective of this RI was to provide the additional data needed to
adequately support a baseline human health and ecological risk assessment, and to
provide a basis on which to recommend a subsequent cost-effective remedial action
plan, if necessary. Note that this RI focused on all aspects of the Georgia-Pacific Site
south of the Roanoke River. Because, the Roanoke River is a large and complex surface
water body that may have been affected by many other sites or sources of
contamination upstream of the Georgia-Pacific Site, the sampling and analysis of
Roanoke River samples was not included in this RI. Instead, a separate RI is currently
being conducted for the Roanoke River which can better address the potential multi-site
releases of contamination to this surface water body.
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The first step in the remedial investigation, after the project plans were developed, was
a field investigation. The field investigation included the following tasks:
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Soil Sampling -A total of 70 surface soil and 67 subsurface soil samples
(not including duplicates) were collected from various locations on-and
offsite. The number of soil samples collected from the various areas are
as follows:
Area
Sawmill Plant Area
School and Boy Scout Area
Residential Areas
Surface Soil
Samples
55
7
8
Subsurface Soil
Samples
67
0
0
. All of the surface and subsurface soil samples were sent to a CLP
laboratory for complete TCL/TAL analyses, except one. One of the
surface soil samples was not analyzed for VOCs. In addition, 60 of the
surface soil samples and 19 of the subsurface soil samples were analyzed
for dioxins/ furans by a CLP laboratory.
Surface Water/Sediment Sampling-A total of 3 surface water and 7
sediment samples (not including duplicates) were collected from the
intermittent drainage ditches onsite. All the surface water/ sediment
samples were sent to a CLP laboratory for complete TCL/T AL analyses.
In addition, all the sediment samples were sent to a CLP laboratory for
analysis of dioxins/ furans.
Temporary Well Installation and Groundwater Sampling-A total of 5
temporary shallow monitor wells were installed. Groundwater samples
were then collected from these 5 temporary monitor wells, as well as 9
existing shallow monitor wells installed previously at the site. All
groundwater samples were sent to a CLP laboratory for complete
TCL/T AL analyses.
1.8 Removal Action
In August 1999, after the RI field investigation was completed and the analytical results
were received from the CLP laboratories, the PRPs conducted a removal action at the
site under order by EPA to "abate the imminent and substantial endangerment of the
public health, welfare, or the environment that may be presented by the actual or
threatened release of hazardous substances at or from the site." All the activities
conducted during the removal action are described in detail in the Removal Action
Summary Report(BBL Environmental Services, 1999, later referred to as BBLES).
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Section 1
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As indicated in the above sections, two buildings were demolished and three storage
tanks were removed from the site during this removal action. The main activity of the
removal action, however, was the removal of soil with concentrations of contaminants
(as determined from the RI sampling investigation data and data collected during the
removal action) exceeding the following site-specific removal action levels (SSRALs):
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2,3,7,8-TCDD; 1 ug/kg
Dioxin expressed as 2,3,7,8-TCDD toxic equivalent quotient; 1 ug/ kg
Pentachlorophenol ; 25 mg/ kg
Total PAHs; 100,000 ug/kg
Total cPAHs; 50,000 ug/kg
Arsenic ; 30 mg/kg
Chromium (total) ; 200 mg/kg
Chromium VI ; 90 mg/kg
Lead; 400 mg/kg
Soils exceeding these criteria were excavated and transported offsite to a secure landfill.
The excavated areas were then backfilled and compacted to pre-existing grade with
clean soil.
Prior to conducting the soil removal activities, several additional soil samples were
collected from specific site areas to better characterize the soil concentrations. In
addition, after conducting the soil removal activities and prior to backfilling, several
confirmation samples of soils were collected to ensure that all the soil exceeding the
removal action levels was removed. The original RI soil sampling data and the
subsequent excavated grid confirmation sample data are presented and discussed in
Section 2.
1. 9 Overview of Report
The remainder of this report contains descriptions and results of the sampling activities
performed during the RI and the Removal Action. Brief summaries of the remaining
sections are presented below:
•
COM Federal Program~ Corporation
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Sections 2, 3, and 4, discuss the results of the soil, surface
water/ sediment, and groundwater sampling investigations, respectively.
Each of these sections describes the purpose of the investigation, outlines
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Section 1
Introduction
the methodology for sampling, and summarizes the results of the
investigation.
Section 5 presents the results of the contaminant fate and transport
analysis.
Section 6 presents the Quality Assurance Report which summarizes and
quantifies the RI analytical data and especially the quality control data.
Section 7 summarizes the results of the remedial investigation and
presents the conclusions reached based on these results.
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2.0 Soil Sampling Investigation
2.1 Purpose and Scope
The amount of pre-remedial investigation data and information accumulated on the
GP Site was insufficient to complete a baseline risk assessment to adequately develop
a practical and effective remediation plan for the site. In August 1998, the USEP A
Region IV SESD prepared a Remedial Investigation (RI) Work Plan to obtain the
additional data needed. The Work Plan described the field investigation methods
and procedures for collection of onsite and offsite soil for determining the nature of,
and the areal and vertical extent of contamination in soils at the site. Upon receipt and
review of the analytical results of the RI, EPA determined that a removal action was
necessary at the site to address the potential of impact on human health and the
environment. Prior to the mobilization of removal action contractor, EPA established
site-specific action levels for nine constituents of concern (COCs) detected in soil and
intermittent drainage ditch sediment at the site. These site specific action levels
(SSRALs) are provided in Section 1.8 of this report. The RI analytical data were
compared to the SSRALs and grids were identitied where the action levels were
exceeded. Once a grid was excavated, soil samples were collected to confirm that the
remaining soils were below SSRALs. The RI and removal action confirmation
analytical data will be discussed in the subsequent sections.
2.2 Methods
2.2.1 Remedial Investigation Soil Sampling
For the RI field investigation, a grid system was established throughout the GP site
property as shown in Figure 2-1. Figure 2-1 also shows the general offsite sampling
locations at various residential, school, and Boy Scout properties. Fifty-five grids were
used for the onsite sampling. For the surface soil sample collection, one composite
sample was prepared by collecting five aliquots within each grid. As stated in the
Work Plan, one aliquot was collected from the center of each grid. The four other
aliquots were located approximately 35 feet, 60 feet or 85 feet from the center of the
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0 250' -

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--

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Roanoke
River
500'
-I
Georgia-Pacific Hardwoods I Plymouth, North Carolina
Scouts
0 Hut
c:2201-SLA
■ GP-202-SI..A • <:>
■ GP-203-SLA
Football
Field
LEGEND:
OP-205-SU. •
211c O
Onsite and 0ffsite
Soil Sampling Locations
N
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0
0
D
SURFACE SOIL
SAMPLE LOCATION
0
0
0
0
0
0
COMPOSITE SURFACE SOIL
SAMPLE LOCATION
GRID
RIVER
TREE LINE
RAILROAD
Figure No.
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Section 2
Soil Sampling Investigation
grid, based on the grid sizes of 100 by 100 feet, 150 by 150 feet and 200 by 200 feet,
respectively, at angles 0°, 90°, 180°, and 270° from north. Some deviations to this
sampling procedure were necessary due to conditions encountered at the site. In
some grids only the grab sample from the center could be collected and in other grids
some of the aliquot locations were not collected or were collected at different locations
within a grid other than the distance or angles described above. The surface soil
samples were collected from Oto 6 inches below land surface (bis). The samples were
analyzed for volatile (VOA) and extractable organic compounds (SVOAs), pesticides,
polychlorinated biphenyls, metals, dioxins, and dibenzofurans. The VOA soil sample
was collected as a grab sample from the center of the grid.
For the subsurface soil, a grab sample was collected from the center of each grid at a
depth of 18 to 24 inches bis. In addition, subsurface soil samples were collected from
grids 25 through 55 at a depth interval of 35 to 42 inches bis. As above, a few of these
subsurface soils could not be collected due to subsurface obstructions preventing use
of hand augering.
Surface soils were also collected at fourteen locations on residential properties
adjacent to the site. These samples were collected as a composite of five aliquots
and were analyzed for the same constituents as onsite soils.
Analysis of RI samples was performed by EPA' s contracted laboratories. Data
validation of the RI analytical data was performed by Region IV SESD Office of
Quality Assurance and Data Integration.
2.2.2 Removal Action Soil Sampling
In general, five point aliquot composite samples were collected and the samples were
analyzed for the same constituents as the RI data by a laboratory subcontracted by
BBLES, Savannah Laboratories and Environmental Services, Inc. in Savannah Georgia.
The RI data were compared to SSRALs and the following grids were planned for
excavation at the depths given:
• Grid 39 - 1 foot;
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Grid 40 - 1 foot;
Grid 41 -2.5 feet;
Grid 44 -2.5 feet;
Grid 46 - 4 feet;
Grid 47 -1 foot; and
Grid 49 -2.5 feet
Section 2
Soil Sampling Investigation
Following the excavation of the grids, one five-point composite sample was collected
from the surface of each of the seven excavated grids and these samples were
analyzed for the constituents of concern that originally exceeded the SSRAL. The
USEP A also collected and analyzed split samples of these confirmation samples
collected by BBLES. The BBLES results are presented below following the RI
sampling results.
2.3 Summary
The analytical results for surface and subsurface soil samples collected onsite and
offsite in the residential neighborhood are summarized in Tables 2-1 through 2-4.
Table 2-1 presents the volatile and extractable organic constituents detected. Table 2-
2 presents the pesticide and PCBs constituents detected. Table 2-3 presents the
dioxins and furans detected. Table 2-4 presents the inorganic constituents detected.
Note that for the purpose of summarizing, only chemicals detected at least once in
each medium and their measured concentrations are presented in the summary tables.
The complete data set of analytical results for the CLP laboratory analyses performed
are provided in Appendix A.
In the tables the following sample identifiers were used:
•
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The SLA on the sample designation was a soil sample collected from 0 - 6
inches below land surface (bis);
The SLB represents a soil sample collected from 18 -24 inches bis;
The SLC represents a soil sample collected from 36 -42 inches bis;
The numbers 00X in GP004SLA corresponds to the Grid number.
The residential soil samples are represented by the 200 series designation, for
example, GP204SLA
COM Federnl Pn~nuns Corp,1rnti<1n
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CHEMICAL
VOLATILE ORGANICS
EXTRACTABLE ORGANICS
-- - - - - - --
TABLE 2-1
SOIL SAMPLING SUMMARY -VOLATILE AND EXTRACTABLE ORGANICS
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
-
GP001SLA GP001SLB
(Duplicate)
GP002$LA GP002$LB GP003SLA GP003SLB GP004SLA
Pat.a OualifJers·
U = Material was analyzed but not detected. The number is the minimum quantitatlon limit
NA= Not analyzed.
J = Estimated value
Concentrations presented in ug/kg
Section 2
Soll Sampling Investigation
GP004SLB
1 of 18
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CHEMICAL
VOLATILE ORGANICS
-- - - - - ---
TABLE 2-1
SOIL SAMPLING SUMMARY -VOLATILE AND EXTRACTABLE ORGANICS
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
GP005SLA GPOOSSLB GP006SLA GP006SLB GP007SLA GP007SLA
(Duplicate)
GP007SLB
Section 2
Soll Sampf/ng Investigation
GP007SLB
(Dupllcate)
1,1-qlCHLOROETJ-{ENE (1, 1-QICH_LORQ_ETH~~~-NE), :·1 : :-i.l2 -. 1]'.:!J,·:··•,,2\ ~-.>~Ji-=_Q{~,?::?JJ~U:Qii~;~~ :.-~~;;i:f{f((!..'.t_~~~{~[Jt1P:~;;\;:?:~ :i:.f1Ji',\ ~-~t!;~f.;-~·j'i_ LJ:· -~,-. ~:-11 u
1,2-DICHLOROETHENE (TOTAL) 11 U 11 U 11 U 11 U 11 U 11 U 11 U 11 U
CARBON DISULFIDE-~ . ·-·::-, ~'.:_ ;-~~ ~:;~,_1-.-.-:•;;_,.:. D .u :.,:::<.-:'?~•--' Jii9.~i?;~sr;·~~f ~t!.'~t:~~~ ·0iJ:JJl!::-lf.f!!Xf.,1}1Q/_>,:-={J~·\\tJj~-~.;.,::_::;r!::t:::;.:J1(Q:'"-J: _:-:._-;,.;:,~:-"\1: ·u
METHYLETHYLKETONE 11 U 11 U 11 U 11 U 11 U 11 U 11 U 11 U
TETRACHLoRoETHENE ctETRACl:i~oR0EtHv11t.f~i. ,.,: :' ·: 1 \:~~d.::;i, :\ '':'!'.'lfQJ;:i;"':::~:, I 11r.:;-: ;;;~;'3TI"1'"'i-i'~J.ZJ"-~'iF9 ,tr:,-.,? -:'1 fy· ??'·::-·.Ji p-__ : _':\ .. _1 r~ .
TOLUENE 11UJ 11UJ 11U 11U 11U 11U 11U 11U
TRICHLOROETHENE (TRIC.H~QRO~THYi..E!'Jg) ··(1• ~: ~_ .• 1: 1,:· r·:~ ::.:;,~~~::v=·{:-,.t· ·:~;Jj£Jt:;:~~~~-::_'"fFQ/:t;L<f#fifi}~k~"~1IJf_l){;f~bi~?•~:1~. 0'-~·:.,\?,·;~---._11 q•~ · ·. · y . ·. 11 Ll·
EXTRACTABLE ORGANICS
2 of 18
----- -
CHEMICAL
VOLATILE ORGANICS
---- - - ---
TABLE 2-1
SOIL SAMPLING SUMMARY -VOLATILE AND EXTRACTABLE ORGANICS
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
GP008SLA GPOOSSLB GP009SLA GP009SLB GP010$LA GP010SLB GP011SLA
Section 2
Soll Sampling Investigation
GP012SLA
1, 1-0/CHLOROETHENE (1:1-DICHLOROETHYbE_NE); ;,:,, ._,·:(:'; '11 u . . ;•_;· .1fli'''.'. ;: ", . _j_)'QC;L •''•~t."':~fQI'f -i"l.1/':if\i'?-";:·-•:;::11 '[.r ,.,. 11· u. 11 u
1,2-DICHLOROETHENE (TOTAL) 11 U 12 U 11 U 59 UJ 11 U 11 U 11 U 11 U
CARBON DISULFIDE .. ' ;-;:-, ·. ··,ifi.i,; .. ,'. ,· ~~ci'Q•.~••c?. Tiu.::-' ';'.-".'sT~1·:tJ<:;?}'iVO:S:•,··:;_,;:'JJ:_uc :,-Jiu.>· . 11 u
METHYL ETHYL KETONE 11 U 12 U 11 U 59 UJ 11 U 11 U 11 U 11 U
T~TRACljLOROETHEN~. (TET_RA_CH~Q89~t8Y}l~!'{E)'~~.~.;::;;_·.::: r·. 1-i. Q:":,:;:·•.-i,~ ·f ~1r1u:-'4:,:-t;:<j.f~.O~'lsf'~-? .?9. Q'"J~-:~~~-;~f~ffQ·. ~-i':-~;-f~~_:J} p .•' -,~.~-:_:·_::~·;:,j_Llf'_~· .' ~:~ : 11 u
TOLUENE 11U 12U 11U 59UJ 11U 11U 11U 11U
TRICHLOROETHENE (TRICHLORO$THYLEN_E) ,);;.:!,> --. ,, . ';_ fr u}:'_5 . :-rnc: :i:.: :: -.-. 'ii'1'1:E' . .''' ··;_'~t~J?~';;/ff\f'::,'.:.:.t( i (U, '. '.' . h U 11 U -
EXTRACTABLE ORGANICS
3 of 18
--- -- --- - - -- -
TABLE 2-1
---Section 2
Soll Sampling Investigation
SOIL SAMPLING SUMMARY -VOLATILE AND EXTRACTABLE ORGANICS
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
GP013SLA GP013SLB GP015SLA GP015SLB GP016SLA GP016SLB GP017SLA GP017SLA
(Dupllcate) CHEMICAL
VOLATILE ORGANICS
1, 1-DICHLOROEJHENE (1_, 1-DICHLORO~THYL~NE) . --· .. i -11 0
1,2-DICHLOROETHENE (TOT AL) 11 U
CARBON DISULFIDE ., -- · ·. ·.-,;so 1J :,
METHYL ETHYL KETONE 11 U
TETRACHLOROETHENE(TETRAGHLOR()ETHYLEJ'!Ec) . .:":.... -·_. _,ff_((,:.: -
TOLUENE 7 J
TRICHLOROETHENE (TRICHLOROETHYLENE). . . ,· 1_1 jj'. _ _,;"
EXTRACTABLE ORGANICS
1j Q?~. ·:~ ··:(!j',l_!-.:-~·.-r~~\>.;~·f~:;!i~:{",'-Sr°:·::-:t:\:1f~ji.-::(:';. ·,·~1 \I_. . 1_Q lt
11U 11U 12U 11U 11U 10U
. 1,j .9·.~-::.,'. /i,(:. il Q.{~·rf~-::.: :·· J~1JJjf-;'.~c\•.;,,··, ''.,'.t::69,Q!';, ~};.:,. /?Ti !-!-. : :-. ,·,.•,;:_ ~-,:JO µ~ \·,
11U 11U 12U 11U 11U 10U
. n--~:i. ~ ffQf:o,i,'.:._:,:·ir~u~trtr~~~.,rrP: -~:<r .... ,:: ";Ti-~-. --1Q ~ .. ~-. ·
11U 11U 12U 11U 11U 10U ·~ 1.f!J.•~---_ ... : ·_,-._ 1r\r· ~:/~--?-·· jf~T ;~·t~r~~~/ d"f-D.--~--:···~ ~-·~-11 ·u -.10 Y~;:~ _
.. 10 U
10 U
10 U
10 U
10 U
10 U
10 U
4 of 18
---- --- -- - ----
TABLE 2-1
SOIL SAMPLING SUMMARY -VOLATILE AND EXTRACTABLE ORGANICS
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
111!!1
Section 2
Soll Sampling Investigation
GP017SLB GP017SLB
(Duplicate)
GP018SLA GP018SLA
(Duplicate)
GP019SLA GP019SLB GP020SLA GP020SLB
CHEMICAL
VOLATILE ORGANICS
1, 1-DICHLOROETHENE (1,1,DICHLOROETHYL~Nl~f .r. . .. '''1 j LJ . ·:, : 1j Uf) ·.·'· .. · S:c11' iJ. ,·./'.' :''. f1:[:·:'.\J;C:: 1,(i,i,:',l'\{· ':r.11 .U:'>''·
1,2-DICHLOROETHENE (TOTAL) 11 U 11 U 11 U 11 U 11 U 11 U
CARBON DISU.LFIQE ~ ·:,<;: ·~f1.·P-£ • · ·1f:Qr}:;'_•:;_!.~::·J1;_~0,:t~~,~(_",,JjJ{J\;_..:.\;f:, _ _.~ .If.Q~;/_/:;, ·.1j,._Qt'_:;•~.
METHYL ETHYL KETONE 11 U 11 U 11 U 11 U 11 U 11 U
TETRACHLoRoETHENE (TETRACHLORoErHff~f!~Y >,,,. :. , ::~H:i;i. ·: .. \' · 1 LQ,:t:'.:,,,,:\ffu· ";"'J~~t11r0_;.,,:·tr,':c-1-r1:i:.•· ""· c,ff il
TOLUENE 11 U 11 U 11 U 11 U 11 U 11 U
TRICHLOROETHENE (TRICHLQROETHYLENE)' '¥ '/: ': ·, , 1,f'.I],?/ '., ';•, ,ffjJ_;?,}".?}: ';f.ft,J,'',')',;::;:,'.: 11'lJj,:J,f2f;:)!'!,Ji ',1, ••, i' ;_ ii,itf;• c .
EXTRACTABLE ORGANICS
.,_ '!.~ LJ,'. '
12 U
:•12 Li_, ,i
12 U
'12 IJ. >
12 U · '12u:>
5 of 18
12 U
12 U
12 U.
12 U
12 U
12 U
12 U
==
-------- --- ---- --Section 2
Soil Sampling lnvestJgaUon
CHEMICAL
VOLATILE ORGANICS
TABLE 2-1
SOIL SAMPLING SUMMARY -VOLATILE AND EXTRACTABLE ORGANICS
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
GP021SLA GP021SLB GP022SLA GP022SLB GP023$LA GP023SLB GP024SLA
1, 1-DICHLOROETHENE (1,1-CllCHLOROETHYLENE) ... >.• ·:,c-. ._, 12 LI ;l' ' _1 Hh, ::.:_ ::. Jiy:; :~ ..• i)i1,.u: 2,.'.;>· .1?:Ll : '\:-~. _:1i 1:r -)1.UJ
1,2-DICHLOROETHENE(TOTAL) 12U 11U 12U 11U 12U 13U 11UJ
CARBON DISULflDE . . . . .: :~·•. ~ ·., f~ ~/; · ,' fj._q,; :.:i·.:~:\ <itQi;_:·,_. f~i-!:tJ.1 -~·'•,~::,.\:,:.;-: .·:_,, g;y;;;;f.::t/,.tftQ i:-:: ~. :. '~~i:·~; .
METHYL ETHYL KETONE 12 U 11 U 12 U 11 U 12 U 13 U 11 UJ
TETRACHLoRoETHENt /TET~<;HLoR9EfHYLE:~ei ', ,:',>·: :c12Ji• ;.,_, ·,· .. ·· 11:yc;-,:-,.,.,.,_,:-inf'.,', ,,-.,-;/H V.''''': ~· , : WJ!.'i\r::;;-·:1) _u_,.\,; .-... ... 11 _uJ_
TOLUENE 12 U 11 U 12 U 11 U 12 U 13 U 11 UJ
GP024SLB
rn1cHLOROETHENE crR1c;HLORoetHYLENE> -. , ,. · 12 u . ,. . ; .. 1 i'l.1 :~: :,,.:: w.:Q ·,-·::;;1;;: :::u:.Ji.-::.J1.·:";_ 1tQ:::.:L,·,_;:,i3 u.;.::,,-. _11 uJ .••
12 U,
12 U
12 U
12 U
12_U
12 U
12 U
EXTRACTABLE ORGANICS
(3-ANo,oR 4-JMETHYLPHENQL'. . . , 3Jg li ,· : ·. 31q·i/· . ,:·>,, :i]!9.,u_.;,,,:; :_;:,tfo·I,!;:\ ... ;; -'@cf•Qd,~•\ ... ,.~49 u:;_·,·:: 1400 u . : .~oo u
2,4-DINITROTOLUENE 370 U 340 U 380 U 370 U 400 U 440 U 1400 U , 2500 J
2-METHYLNAPHTHALENE · 37.Q u , . :iiQ._l/' -. :•.:::.:,__3~_ci Q· " , ':ito u•· -~ '::·: :\iliiLO:; : · .. .'~Q u: ·:, • 1400 y. · , s6oo u
ACENAPHTHENE 370 U 340 U 380 U 370 U 400 U 440 U 1400 U 5600 U
ACENAPHTHYLENE ·. ~t□i.i-, . :½o.u ·,: ')ii.11:t:i:::. 3t,qg',;.~;;"''''1@_u_,,'.1.1;:¥QT1 -·· ._Hq_qu ~6o_ou
ANTHRACENE 370 U 340 U 380 U 370 U 400 U 440 U 1400 U 5600 U
BENZO(A)ANTHRACENE_ . . ··''.·~-":~tQ _Q,; :_ . ·:, 340 U "'' .. ·• '~:0 u._,.c[:"::7':·:,_:i]Q ld'·'.0~n••:_;~11_i:i:9._ ·-~·:J?,::..'¥.~.\J.-, ; , : . ;j~oil _l,i.-. , ,5600 U ,
BENZO(B AND/OR K)FLUORANTHENE 370 U 340 U 380 U 370 U 400 U 440 U 1400 U . · 1400 J
BENZO(GHl)PERYLENE ' . . . . ;_ ' : . f ,· ,' . .-:~?,(i l,i ,. ·. ':: 34o;u >'. :-~SQ (p,;;;,',j'::·~10 :q;:~1;.'c·_ ~ ~()Q__l]'/•4·'' ,AfO 1.1,:,•, ~;i~OQ LL' >.:. ?600 u
BENZO-A-PYRENE 370 U 340 U 380 U 370 U 400 U 440 U 1400 U 5600 U
GA~BAZOLE ' · · ~~-•. :;,:."~ · r,-·: ,:·c ~J.::)Iii?Q. ~r.·.··-·:; ,:.'. ~~:f!.i:f.Q· ;·:· '::--~ ~~lQ Y).:~~~·lliiI?Jt1I~~;f,.:;t/~QiL~~:-·.}/J~¥JfJt,~.-.t -~·-1400 u: : -~6qo I..!
CHRYSENE 370 U 340 U 380 U 370 U 400 U 440 U 1400 U 5600 U
DIBENZO(A,H)ANTHRAl::l(NE . • • " ·,. . . ,· <, •\;0:;.-\~ZQ. u,.:: :': <,.3-19.LW' , . .,_,;:T:;' .~Q:)J iti::il::~·w!L\:J[£t~.'ili.q]F:')'l''-".i;i~~ Q;:/',:,.:~' 14o_Q W ·c:. :, !}60,0 lJ,
DIBENZOFURAN 370 U 340 U 380 U 370 U. 400 U 440 U 1400 U 5600 U
FLUORANTHENE : :··; · ,, ~<?~~;;::f11~~?.Q•Q~~:·,:~ .. --~; .. ;.J1.cF"Q ·::-:~~i}l:~:~I~EQ.7.=:J;:C1~?R J&1 :;:;~i! ]f&;Q:!~~~sf.J.;J~if.:Y)-~~:t X· 140Q_4:.'. /: ·! ::.~~Q.]; _
FLUORENE. 370 U 340 U 380 U 370 U 400 U 440 U 1400 U 5600 U
IND~NO (1,2,3-CD) .PYRENf_ •. '· :· ;.; .· ·. "'·. : ?ii jf.fi,ifO: U':' ': '.l4_Q'Q' ; _ t';';~fil[,jl;:/: ~~illQ. uli::}"-;ci''.':4o\FQ ;;1'·:c:J':t,¥]:_Q\, : ·;:,_1{<)Q u ~--·::· ~60,0 !,J,
N-NITROSODIPHENYLAMINE/DIPHENYLAMINE 370 U 340 U 380 U 370 U 400 U 440 U 1400 U 5600 U
~APHTHALENE --, ·· .. · . ;, .... -_~::.···:··:f.'~· .. -_. {}370:_~ · _..:;~~i';:<M!f[ :; .. ~:\-:., )~lY]~f/~.~:-~~~711o'"Qff~t;\~~-~Q~i!J'-I/~-\:Dt~~44~iJ .. ;/:j:. _:·: '14Q.Qj.J_:-;.;• ,'-·.~··s~90 y_
PENTACHLOROPHENOL 920 U 860 U 970 U 930 U 1000 U 1100 U 3400 U 14000 U
PHE~ANTHRENE .• · .• ·~ ,;• . .J-' .. '· •• X .. :/::~:,t-.~ ,3701!,lfti~-?}f. 34f\f.-_1~~w •:3s{);_UJ:f::~;;1:3·i9,y::;r~·41~:f!Q['·P;~?fi~[/~{:H.Q·1t-:s-Jt~Y/i~QQ:jl i;: .. < -~§0Q..Y.:
PYRENE 370 U 340 U 380 U 370 U 400 U 440 U 1400 U 580 J
6 of 18
------------
TABLE: 2-1
SOIL SAMPLING SUMMARY· VOLATILE: AND EXTRACTABLE: ORGANICS
GEORGIA-PACIFIC SITE:
PLYMOUTH, NORTH CAROLINA
---Section 2
Soll Sampling Investigation
GP025SLA GP025SLB GP025SLC GP026SLA GP026SLB GP026SLC GP027SLA GP027SLB
CHEMICAL
VOLATILE ORGANICS
1,1-DICHLORQEJ"HENE {1_, ~-DICHLORQf[HY~~N~):,'. · -~'-.:.: .. ,. '-
1,2-DICHLOROETHENE (TOTAL)
CARBON DISULFIDE
METHYL ETHYL KETONE
TETRACH_LOROETH~NE (TETRAC:HLORQ~TtJ'(l~NE)
TOLUENE
TRICHLOROETHENE (TRICHhOROETrlYL~N!c) .'· ' ·
EXTRACTABLE ORGANICS
uli :::.:-r._.:11 l!: 1tu <.:/;~; 11.:i:iLJ'.:'.·,11-I/,, ·> 11 u• ·11 u, • 11 U
11 U
11 U
11 U
11 U
3 J
11 U
11U 11U 12U 12U 11U 11U 11U , ... :-. .u ~ .: .. .-:••-' · -~ u -~•_.,:;._:. --i~:::~Jf!-f ~-,-~f:J:?Jt~~:5k:::.z:Ji-Cf::-Z_-:.,< ~1-~ , ?.9 u,-
11 u 11U 12U 12U 11U 11U 11U
11 u_ ., .. :._:W• .,11.fi ';}:: ,, 7'12:u; ,;··.,<\ .fi'Q:,.;:4\,·.,, ffQ::·::c. ·. •. ·11 iY''·'·• .--11 u ·. · ·
11U 11U 12U 12U 11U 11U 11U 11 ~ · -:'·: .: .. ~/~:Jf U---~-:.: :~ .L?_,ii_. ~-:._-;:;~ JfQIJ;Ti-.. ~-~,A i lJ -~• .... ~ ~ ~ -: 11_ ~-··• , __ :_.t :. _ f 1-!J,
350 U
350 U
350 U
350 U
3~0 lJ
350 U c4 J
,190 J
•42 J··
1'78 J
· 3~\!_U
. 73 J
, :.350 U.
350 U
J.E.ri J
350 U
:~6§. ./
350 U
_ _350 U
870 U
_58 J
130 J
7 of 18
-
---
CHEMICAL
VOLATILE ORGANICS
--·---... _ -
TABLE 2-1
SOIL SAMPLING SUMMARY -VOLATILE AND EXTRACTABLE ORGANICS
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
GP027SLC GP028SLA GP028SLB GP028SLC GP029SLA GP029SL8 GP029SLC
--Section 2
Soll Sampling Investigation
GP030SLA
1,1-DICHLOROETHENE (1,1'DL~HLQROETHYL~g)_: .· •• ,-.:-~.:'...:'t1'.Y.1l',it'.;i.{f_LI:/'.', ~:~1,:.1g_-[;1~::i:gf;}It,ff{1L'SE tl½!tQ .. :,;·,,._:1I.\JJc11:1C :.:<' JL\J: ·_ ··. 11 u
1,2-DICHLOROETHENE (TOTAL) 11 U 11 U 12 U 11 U 10 U 12 U 11 U 11 U
CARBON DISULFIDE : ~ . .,. . -."-. :~'· ~\~::<, >, -~•::'.,:;,. -: .-.. /~_:::;~•:.:}' .u-:JI~~;;:,;dt~?:~tQ""•P-;?i./-;\;,~/_:;~q_-.iu;-;lBi]2!TitQ;;~Jd'lflfo:iQ:Q;, .. r. ;:;:/-~1J~QE~~~~t? ·L·fi:._i.J_-)'.I~:. 20 u
METHYL ETHYL KETONE 11 U 11 U 12 U 11 U 10 U 12 U 11 U 11 U
TETRACHLORO!=T~E~.t (~T~GH~Q~OET!"iXh[N]) ~ .. :.-:.'!:t:l·; _ 11·~~fi£·~~di-Q)t~lrT~~:-:rr-!J}Jf1lt~\fU\1.i:f:~~:t~';_~~TQ:!J._:--_, ,:.:;r. •?._1f"Qil!i::-~~-( :·~ 'j 1 J1 .. ~<-1, u
TOLUENE 11U 6J ,3J 11U -1J 12U 11U 2J
TRICHLOROETHEN~ (TRl~ti(Q.R9ETHY~~_r-.r~>\•:-:_,i/~·0, -.-.::";.,t · __ -·-:n.~1L~::::.-:-:_-~_:·:.11·:1J1:.-·:.::·: --~:::1_r.~:-i~ it:J:fJ2JIJ!i·::,~l:.:;~,:~:1Q!_~.::-. // •::·-~::_::il-~T.--~;. ! .• -. '.) 1.-~:: _,,; ... ·[ -11 u
EXTRACTABLE ORGANICS
8 of 18
-
----
CHEMICAL
VOLATILE ORGANICS
------
TABLE 2-1
SOIL SAMPLING SUMMARY· VOLATILE AND EXTRACTABLE ORGANICS
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
GP030SLB GP030SLC GP031SLA GP031SLB GP032SLA GP033SLA GP034SLA
Section 2
Soil Sampling Investigation
GP034SLB
1, 1-DICHLOROETHENE (1, 1,DICHLOR.QETHYh~NE) · ;·... 1}.L(:·/,;·. '. ,; 11 l,l : \~ :. :_.1.(1,J :~,;,,;;it"J.fJ'.fci~t,~,·,,;l.g,jJ'''. f'_. _ · ·11 Y,.,;! · . 10 li ·_' 11 U
1,2-DICHLOROETHENE(TOTAL) 11 U 11 U 11 U 11 U 12 U 11 U 10 U 11 U
CARBON rnsuLFIDE -..... JI~~--~·,-'; ·'.:~~10 J! \ .. -·~ :.-·. :.1_1 .. Q-._ ., t:tf{~/f1•.I2;:;r;:::~~E.,1~tr: .:.:~~\ ._ .-JJ~_Q:,j~.1(t.~°!.-~ . ..1.~f~r.~:.~;~t_-: 11 u
METHYL ETHYL KETONE 11 U 11 U 11 U 11 U 12 U 11 U 10 U 11 U
TETRACHLOROETHENE (TET~CH~QR()_E'rHy~_r;je;/ fi i,: : ·/ '.'.:J j -l,i\:;,~, > ... 'fi. !JC ti;: , ' fr i} < :;i:,;~;ij 'jJ ':cfi.J.[:,;:Cq 2v~ ?\ -'{ '. '1ij)1'. r?: . ·: . i O Li :~; r, . . . i 1 Li
TOLUENE 2J 2J 11U 11U 12U 11U 10U 11U
TRICHLOROETHENE (TRICHLOROETHYLENE) '. /'.:·. JfQ,;:L ·< , ii.Q '•' · i}U\: 1;'.iC~if; Li,': ~;j,:;-j;?,Q :· ,:.•"· ;0,•.·11jL:'1\ /· ._ jO ·u. ,,.: ;:: : 11 U.
EXTRACTABLE ORGANICS
9 of 18
-
--
CHEMICAL
VOLATILE ORGANICS
--·-_, __ 1111,· --
TABLE 2-1
SOIL SAMPLING SUMMARY· VOLATILE AND EXTRACTABLE ORGANICS
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
GP034$LC GP035SLA GP035SLB GP035SLC GP036SLA GP036SLB GP036SLC
--Section 2
Soll Sampflng Investigation
GP037SLA
1, 1-DICHLOROETHEN~ (1, 1,QiCHLOR.Qi;"ff-i_y4~NE): ·: ·~~": -. :':i i.EQ"t,.,,: . 1 : }J lJ-:i;::,:0 ,:1.?' g_:;_;;,i?;~j''fi ;ff· ;,i"J,f/'J j(lJ L'. ":.":S fUh'.{:;;,;/,';j;[ _LI· \ '.' .· . _ 1_20 U
1,2-DICHLOROETHENE (TOTAL) 11 U 11 UJ 12 U 11 U 11 U 11 U 11 U 120 U
cARsoN D1suLF1DE · · ·· ;,, •. :. • · ·. , ,. · ·J1J£>_,::,~:; ' :n uI/I•:'.i; ~-~fs~·:::~ ,; 'i-~f;g,..:J:.i:.'?:j.f J:i.,. :;;:, , .20 J.F;tlf '..-1 i 1.1 -.~ -: ·1,. 120 u
METHYL ETHYL KETONE 11 U 11 UJ 12 U 11 U 11 U 11 U 11 U 120 U
TETRACHl-OROETHEf\!E_ tf~:r~~~·f!-.Q.R9~tH.Y~~N~>;~:; .. ✓:--,-:::·: ~':jfU~t-Ac:;:,,{ 3l 1lJ_ fl.?h: -~·jJ·Q~.r~~l\~;JJ.~f1:·t.i~\~iJ{Q~i:·f:,r~r:,_:~1f'PJt1~;i,.;.': 1 i ~ ~ ·? · ·:>:· 1:fo Li
TOLUENE 11U 11UJ 12U 11UJ 11U 11U 11U 120U
rnIcHLOROETHENE (TfllCHLOR<;l_ETHYLENE) _ .+ :/t . ~ 1.r;iJ.1t,":::· · _, · fi-P:EJ?~:,:··.ItlJr::,]sI,ffi1-L:'.t:.iJ:;-,,;JfJL',,;.:./ ::,.: 1iy,;E;;,-:,· 11 u ·_ .• ,·•~.: .120 u
EXTRACTABLE ORGANICS
(3-AND/OR 4-)METHYLPH~NQL ..
2.4-DINITROTOLUENE
2-METHYLNAPHTHALENE. ·
ACENAPHTHENE
ACENAPHTHYLENE
ANTHRACENE
BENZO(A)ANTHRACENE.
BENZO(B AND/OR K)FLUORANTH_ENE
BENZO(GHl)P~f3YLENE.
BENZO-A-PYRENE
PYRENE
. ··" .) '.•:..·.
10 of 18
-
------ -.. -
TABLE 2-1
SOIL SAMPLING SUMMARY -VOLATILE AND EXTRACTABLE ORGANICS
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
GP037SLB GP037SLC GPD38SLA GP038SLA
(Duplicate)
GP038SLB GP038SLC GP039SLA
CHEMICAL
VOLATILE ORGANICS
1, 1-DICHLOROETHENE (1, 1-DICHLQROETHYIJ'NE) · :-
1,2-DICHLOROETHENE (TOTAL)
CARBON DISULFIDE
METHYL ETHYL KETONE
TETRACHLOROETHENE (TETRACHl,,9RQETJ-iXbtN~)('J :·: ·. • ,
TOLUENE
TRICHLOROETHENE (TRICHLORO_ETl-jY~EN~) '.
EXTRACTABLE ORGANICS
Section 2
Soll Sampling Investigation
GP040SLA
11 U
• • .. 11 u
(3-AND/OR 4-)METHYLPHE_NOL .. 780\J ,;•·; ~-6.~ \,I · -~: .,,,. ~fo·u ...... ,:,,j.j"ffu :;:-~.~' . _:35() \J ' • ,. ': jso;iL' .:1200 U 370 U .
2,4-DINITROTOLUENE 780 U 360 U 370 U 370 U 350 U 360 U 2200 U 370 U
2-METHYLNAPHTHALENE 78..Q Li: i .. ,: -~60 U · ._;. 0 ':iio_ 0J''',c\J31·o~ij,_ .. ·::., ,.: 3.~Q Q;.. :jii_Q lj,,,. ::' i~OO \J .... _370 U
ACENAPHTHENE 780 U 360 U 370 U 370 U 350 U 360 U 2200 U 370 U
ACENAPHTHYLENE -t~o·Q. ·c.'•. :j§Q Q :, ,., .: ~~Qi{;•,A]:~~)fii].:VC:.:c.,::; ,:i_5jj i:J_ :_.-·, ~&Q y_.;<,.:,·.· 2:?oii lJ 370 u
ANTHRACENE 780 U 360 U . 100 J 370 U 350 U ( 41 J 2200 U 370 U
B~NZO(A)ANTHRACENE • -. ' : :~iiii:,_: :::; ,/'j]~ u .=:: __ ; : ; 11§. J/,:,;;./';_i.90•.fi:-':'':·2-i, ":iS:cXR ;· '_; •.;~~E:i''::: :b??QO Li 370 u
BENZO(B AND/OR K)FLUORANTHENE 1200 J 360 U 270 J : 320 J 350 U :830 2200 U 370 U
BENZO(GHl)PERYLENE . . . . · ., •,; ,: 430· J:' '°' ·•· · .'":foo Li• ' • ..:'·' ,~'43 J · . ·;; ':)·140'\j; ic,,,•:,o •;: 350-U ..---:·,,,.',370'.fc' · . <' 2200 iJ _ ;, .37Q U
BENZO-A-PYRENE '540 J"' ... 360 u -.. '140 J ... ~--1:;go-:i·· -" Jso'u. ,., . ';'550' . . ·2200 u 370 u
CARBAZOLE . ;~:.~.~~/ '<•. I~~Q ~._;:;_:~ .. ;: ~SQ_U~ _~_t?-t~t:Q,Q ~.:;~~112:3101.rrr:~::;.--:,'"IS<f,_ij.~:-_t, ·:~j_s_Q:.Q:2~2.~;~JipQ. µ .L: .,,. ,379 U·
CHRYSENE . 710 J 360 U 180 J -230 J 350 U f540 . 2200 U 370 U
rnsENzo(A,H)ANrnRAcENE • sc • -z~g'iJ.;:,:.:-,Y~:~ll_Ji· :.,,"3j.9..Jf:..-t:,.'l.T?Q.iJli'.,t!:f;:jJq.\J-:,':~',,.s,_:i.® 1t:.i~~:;_:z-zoii J.J _ ~_70 u
DIBENZOFURAN 780 U 360 U 370 U 370 U 350 U 360 U 2200 U 370 U
F~UOJ3ANTHEN~ , . :.: .... ::.~. ·.· ·'/~70 .~J:·}f..'£7;:_~§J-!>~•.:-•~2:~:iff~:fafF~'.:[!~OO~t}1tI-\~35DJL~~~= S': .. fifC~~~~-.;~-~t2_~\:[9 i/. 379 u
FLUORENE 780 U 360 U ·41 J . 370 U 350 U 360 U 2200 U 370 U
iNoE:N_o (1,2,3_:CD} pvR~N~. : · __ ,_. •: .•-.. ::......:·_. >:;::~: :_); !/ · :~4@:~l:~;:,,::1~~P;_:~[Q_._Q;:-§$.-'-:•.~~~--~~~75 __ -Qe,.~~_{-~,:;:.~13o~~l]~I~E~tl§g_~!J :5 :~-i--:·@O·,j~i_~.-~~;~:'-T~Qq !X·· -·, ·. ~~-~??O L!
N-NITROSODIPHENYLAMINE/DIPHENYLAMINE 780 U 360 U 370 U 370 U 350 U 360 U 2200 U 370 U
NAPHTHALENE --,.. ,·f --~ _:· !;•· .. :·. ;~ __ '.? ... _~, ;:'.· ... _:z1sa~:u--::::y~!':L~F~36ofl[:;~~:~J/{ :~370~•□-<;?~·;.;~CT7oijff§~)·:;\~~:JS()';Q:r. ~' ~:·.~-360 u:.~b,1:T··::;;2200 lr.f' :·= . ·--~~7!) u
PENTACHLOROPHENOL 2000 U 910 U 930 U 930 U 890 U 910 U 5600 U 12000'
PHEt:4ANTHRE!'-J~ _.·:· :·::"· ✓-?/:f:'1,:·:;;;-:;~~;i~ ~; ~-._.,:~.:;~7i§lJI :t.'.~·; .. ·~~:iftEtf'-;J_~ :,:1&1s0:l1~{11:,!:Z35C5[~:.~-:-:.~:i.:it!!it1Jt?;~.::~£QQ (,~-~~~--:.// · 3?(> U
PYRENE 850 360 U 270 J · 350 J' 350 U · 1000 2200 U 370 U
11 of18
-
-.. ----- ---
TABLE 2-1
SOIL SAMPLING SUMMARY -VOLATILE AND EXTRACTABLE ORGANICS
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
---Section 2
Soll Sampling lnve.stigation
GP040SLB GP041SLA GP041SLB GP041SLC GP042SLA GP042SLB GP042SLC GP043$LA
CHEMICAL
VOLATILE ORGANICS
1, 1-DICHLOROETHENE (1 ;i-DICHL,(JROEJHY,~NE)·.• "-,·. ·, _.
1,2-DICHLOROETHENE (TOTAL)
CARBON DISULFIDE ..
METHYL ETHYL KETONE
'f.-
TETRACHLOROETHENE (TETRAGHlQROETHY\.ENE) .::~. '.;:".:
TOLUENE
TRICHLOROETHENE (TRICHLOflO_l;T_HYLENE) .
EXTRACTABLE ORGANICS
(3-AND/OR 4-)METHYLPHENOL
2,4-DINITROTOLUENE
2-METHYLNAPHTHALENE
ACENAPHTHENE
ACENAPHTHYLENE
ANTHRACENE
BENZO(A)ANTHRAC~NE .
BENZO(B AND/OR K)FLUORANTHENE
BENZO(GHl)PERYLENE
BENZO-A-PYRENE
11 U
11 U
11 U
11 U
11 U
11 U
11 U
370 U
370 U
_370 U
370 U
370 U
370 U
. ... _370 U
370 U
370 U
370 U
370 U
370 U
. 370 U
370 U
12 of 18
-
------· ---· ---
TABLE 2-1
SOIL SAMPLING SUMMARY. VOLATILE AND EXTRACTABLE ORGANICS
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
--Section 2
Soll Sampllng Investigation
GP044SLA GP044SLB GP045SLA GP045SLB GP045SLC GP046SLA GP046SLB GP046SLC
CHEMICAL
VOLATILE ORGANICS
1, 1-DICHLOROETHENE (1, 1-DICHLOROETHY~E:NE) ;'·: :\ ,
1,2-DICHLOROETHENE (TOTAL)
CARBON DIS!JLFIDE
METHYL ETHYL KETONE
TETRACHLOROETHENE (TETRACHLQRCl!=THY\,ENE).', r, :,,.
TOLUENE
TRICHLOROETHENE (TRJCHLORQETHY~St-JE) \·~.::-.-.-::.~
EXTRACTABLE ORGANICS
"1.7 JJ
17 U ~Qy··-.,
17 U .j1Q_;·
17 U 11u:·--
:. 1_1 U
11 U
11 U
11 U
11 U
11 U
1i lJ
(3-AND/OR 4-)METHYLPHENOL ·; -~90 Q 86_0:o LJ: •i,' , ''.' :i_ii:ii jJ ·: ".'\);'~§9 LJ,:,.c '><:i_SQ;ij 35[ !J:. '· . •~4 j _ 370 U
2,4-DINITROTOLUENE 390 U 8600 U 390 U 360 U 360 U 350 U 400 U 370 U
2-METHYLNAPHTHALENE Jfilj-Q'. '. 8690 jj, .. · -. ·~: ,l~.,/_c,j'.,E((J~§Q'.U_.: "_'.-;~ ':iti§jJ· ': '< ,· __ 35Q Q.:'? iio· J -_..,., · _37_0 U -'---··
ACENAPHTHENE 390 U 1300 J 390 U 360 U 360 U 350 U 310 J 370 U
ACENAPHTHYLENE 3_9Q )d, , · . 860Q JJ s:->:jjj9 !J. ,_,,-;,;:j}6Q U_ ,,_:1'< . ;3~Q l]_,.}iJ.~ ·-~~O ti_'. ; ·. c; 20Qi/ : '_370. U
ANTHRACENE 390 U 3200 J ,43 J 360 U 360 U 350 U ,2800 370 U
BENZO(A)ANTHRACENE ,,. 4-'!.-! ." -jg_i/ijg' -. . ::, ;J~Q J --:~JJ:ij;o_ij '-i :t:,c'0:~gQf:.z:· · 3S_o'_ii-\. '_']@ii Y-' _ 370 u
BENZO(B AND/OR K)FLUORANTHENE 48 J 14000 J 520 J 47 J _ 360 U 350 U _ _400 U . 55 J,
BENZO(GHl)PERYLENE ,'<.i'·C• ._._. 390 lJ ---4~Qo·:t-.,f/F.!J4Q,l. <-:·.,;~Q'{J:\:i::t ... ~s_It);:_"(;": --~5_0_!J·.':-'. 100 u . .c'_.c-_)70 u
BENZO-A-PYRENE 390 U 8000 J .180 J 360 U 360 U 350 U 400 U 370 U
CARBAZOLE : . . :·;. • ~-3g'Q_ ~· . . . -~~Qk ./.:·.f;;}::½.iiQ.c.Q.·::;.:·::~~~;l§Q~1I.·~;,s~,~~(·Q"";!=~{·~•::~J$Q_~,:;} ~·,. i.l_s~~, ,,:_·, .::.;:_:.3?9 u_
CHRYSENE . 56 J 10000 .-260 J 37 J / 360 U 350 U 7300 J 370 U
DIBENZO(A,H)ANTHRACENE _. ,' ::·:·::'-t'c.-''.~;_~:~q '.QJ,< :_8~_Q_Q·uc_,:.-_ i{r;)~!d; ··:'!.tL~i'Jl1Q: LJ,::';'.;'.t;:,!,\3_6__Q'll •?~:.'.·' : 3~Q:\J';;':':~·., --~40Q. u_'_,, .) 370 lJ _
DIBENZOFURAN 390 U 1200 J 390 U 360 U 360 U 350 U 560 370 U
FLUORA_t--!T!-ll;NE . ~-,· -.'~: .... ;,;,:~:·~--:: · ..... ,_., ~tL~.,:!J~:· ':<·~tzifQ~~~i:i.~t' {~-~~~-.;~~ ... 11-~.:~;;ti·:-4t_;:µr.~:jJ;;fI~66l'Q i'.~,/~~;t~1~9_y}..il~:i·a.s_iJQ_Q;·.·-.:~l':>,j;;'CJi{li.✓ .
FLUORENE 390 U 1700 J 390 U 360 U 360 U 350 U ,1100 370 U
INDE_NO (1,2,3-CD)PYRENE ·---.· ,_::· ;,.;;c :;:;-, ,, c•.: -, :i9o·Q?:< ~~l-;c1::c.\:f1~:~~' ,¼'iJ,t:i_~fi'p,i;J:?'[,]'.?]§Q'.l.CV,;:•r'.~9:Yi:t','~ }~-9 i: .. JY. ;_370 u .
N-NITROSODIPHENYLAMINE/DIPHENYLAMINE 390 U 8600 U 390 U 360 U 360 U 350 U 400 U 370 U
NAPHTHALENE · · ··""°• ""' .• :: .-.::::J{ ~±;;<-~:. :-~~:. ~Q-.~::Ji.: -_~;:.J.iO<;~-1~-~ . ~~~½:i!£dt :. i~~J.!-}.§QJ~~~Cfif~~r~~~.2Q.:~0J~::~;z-2:.~j§~~Q} ~~:7;·1~· i'! 6~:J., _ .. _ .. ~-:--. ~_)?Q· u
PENTACHLOROPHENOL 980 U 22000 U 990 U 900 U 890 U 890 U 1000 U 940 U
PHENANTHRENE. . :·. :,.~?~~-!~~ ~-'.\ ~ _.5:t~~Q·TI -~-~-. ·~· :~~ f5~.Q_ ?~;.·.'tif*.,.}_3i["'l ± :~·;,~r~]:6Jj~:Ji~or~J60lQ~-I£;.;~;'\:: 35ft~V.::.t~t·;~faoo'q_~;: ~:1.;._-~'° ... ·. ~}70 ~ ,·
PYRENE 70 J 18000 350 J '46 J 360 U 350 U 1400 U 63 J,
13 of 18
-
----
CHEMICAL
VOLATILE ORGANICS
1, 1-DICHLOROETHENE (1, 1-QICHLOROETHYL(N~) '.
1,2-DICHLOROETHENE (TOTAL)
CARBON DISULFIDE
METHYL ETHYL KETONE
TETRACHLOROETHENE (TETRACHLOROETHYL~NE)
TOLUENE
TRICHLOROETHENE (TRICHLOROETHYLENE) _
EXTRACTABLE ORGANICS
- -- - --·-
TABLE 2-1
SOIL SAMPLING SUMMARY -VOLATILE AND EXTRACTABLE ORGANICS
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
-- -
Section 2
Soll Sampling Investigation
GP047SLA GP047SLB GP048SLA GP048SLB GP048SLC GP049SLA GP049SLB GP049SLC
<\ 1_? U
12 U
70 u,
12 U
... 12_U
2 J
. . 12 U
(3-AND/OR 4-)METHYLPHENOl '\.OQ U . ·,37.Q iJ . . :~~9(! LJ_:f_, ;,'.~~7.Q ·y. ,':;;j~'i::, ')§0,Q -,;)$9:lJ: ;✓• : 610 LI. 830 U
2,4-DINITROTOLUENE 400 U 370 U 1700 J 370 U 380 U 350 U 810 U 830 U
2-METl:lYLNAPHTHALENE ..... ·. ~69 U }· 37Q lJ . ','':i_gop\J. ,:,-:';' )ifo_iJ '"'':}1.--;~li_o·iJ., ; ','.")soy·::-:-8jO iJ_ -_·faoj
ACENAPHTHENE 400 U 370 U 3900 U 370 U 380 U 350 U 810 U , .180 J
ACENAPHTHYLENE :.4.oou :~t\1Q·. ,.-~'ifoQ:"~.::i:.::"i?P!J:''~J.i:'.'.'.3~01i • .'-: ":')sq __ u'::-c _li16iJ.·i;_:' --~30lJ
ANTHRACENE 400 U 370 U 3900 U 370 U 380 U 350 U 810 U · 640 J
BENZO(A)ANTHRACENI; . ; . ~ .. -4~(!tj ~ __ . 370)J. ~-,-.j@.Q Q .'-~~:-~\-;-jfQ_ 11_ • ;.i,~~~f~~~ }]. ;,:r{,~,.".:~~:J t: -:;;.: _ ·<J.~.Q /-.:·_.r '. , L 1_~~(! ,
BENZO(B AND/OR K)FLUORANTHENE 400 U 370 U 3900 U 370 U 380 U 110 J 310 J ,2200
BENZO(GHl)PERYLENE ·.;40_0 if'., -~ ·., ~19 i;!,, ... /)9_b_cjj.f :-'~: ))'.'°:ijti L)' ':};_\,}/;_:i~:o _i;i_: ;'·; '?13§i!]E,:/ · ·. · 160:J_ -·, /9!0,
BENZO-A-PYRENE 400 U 370 U 3900 U 370 U 380 U 55 J -170 J 1300
CARBAZQLE ,.· .. :-~ ':¥ .:l:~fi.Q.Q.!L:.i:._:_·.~---.~jj~{Y_;J.~ ·'"~>~sQ91(:fa211~~~:[?lf P-=-~i~lt~-fQ:~~~:;~L~~Q11lit-tJ · L~10~u ~1~o-~
g~~~~~!.HJANTHRAcsNE ·, . , :if; _ :,,-·, ,J~t~~f -' · _: {t~:.ti-:_ ~-:~'-1~~flh~:cfitd~~t:;;:~221&,d!ttl;,;-;\:":'.:jfo_c_Q:;:',~.:: J~i:~-:~ .. _ !~~~ _u
DIBENZOFURAN 400 U 370 U 3900 U 370 U 380 U 350 U 810 U -190 J
FLU013ANTHENE -:./ ,;~~ .~~:, ,. ~·-~·:_.~;~~ .·-~~'./{,?f-:ifa:~i~·• -:·~~.~7.Q;__Q_~~I, ~~,-~i_;i.l~~~~~~:~~?_Q.i~: .. ;;~~![;}ij~-:Y,7:'~i~~i::7 ~t~5-:·::.ti~~--;!~ ·: .:;;. ··: ... '~:~~O~ ~~ _
FLUORENE 400 U 370 U _ 3900 U _370 U 380 U 350 U 81.0 U ;260 J
INDE~O (1,2,3-C_D) ~y~~-~E •.. . -''---L .'':;;:,(-;. -~/~:;,. ·:12;::4@,:_uj :.j ·. 370.'l.1,.~:,:'., ·1-,;3900.o.'.r~ITT)~~~,.310":i.f f}}~~;'..f38o'U_~;;~~i~::!~~?350flf:-:~;·-:: . (14o'i~ :·:_ .· .. ,~qo ·.
N-NITROSODIPHENYLAMINE/DIPHENYLAMINE 400 U 370 U 3900 U 370 U 380 U 350 U 810 U 830 U
NAPHTHALENE · ... · · -_}-_;.·_,--__ -,,:.·-: .;.,~;~·-··.?.~_; ·;~'1,4.Q~fQ'.~.;''..· ·: .:~ _ .. :._~?.[.l:l_: :,::i:~:~~ItFJ1\~r::·:~t"}fffQJL-JI;1{.filfcf_p;/;{~i~/G!lf~IO-_Q~i:I:.;_~ .. _ ~f Q.Y~ _:~ .. : :·;~o,f.1-
PENTACHLOROPHENOL 1000 U 940 U 9900 U 930 U 950 U 880 U 2000 U 2100 U
PHENAl';HHR.EN~ . ~-~--': -~'.~r:;\~;;~43 ~i:~1: ~; i.\i;,3,;:9_::--~•~;.:2:~.~(~~~~~~;L£~TI1, ~~Mr~'.3~Q~JJ1}::;;~t: 350~ u~~~l:::., J}[<f ~ _} _~·:: .. 01<!9
PYRENE ,52 J 370 U 3900 U 370 U 380 U 53 J 380 J .3000
14 of 18
-
----- ---- ---_,_ --Section 2
Soll Sampling Investigation
CHEMICAL
VOLATILE ORGANICS
TABLE 2-1
SOIL SAMPLING SUMMARY -VOLATILE AND EXTRACTABLE ORGANICS
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
GP050SLA GP050SLB GP051SLA GP051SLB GP051SLC GP052SLA GP052SLB GP053SLA
1, 1-DICHLOROETl:IENE (1, 1-DICf-l~(JR(lgTHYLEN~i.,, """:i<. ·. j,1 I.! '< )._: , 1~ u.):·•:•;,;C;,J:{_1,J ·: '.:': };,..§ti:u:i;;:~:,;-;~;j_2_jJ~~;;.:c, _ ·.JflJ; :::,~ -~.17 UJ .. 13 UJ
13 UJ
13 UJ
13 UJ
1,2-DICHLOROETHENE (TOTAL) 11 U 14 U 14 U 11 UJ 12 U 12 U 17 UJ
CARBON DISULFID!= '\~·, :.:\:~·t;_:·_-_ __{1 ~_ \J; -,f ."' 1_4 if_).:-·_ '~!l' J~fQ\: -y_;~~i~;'.J1Jff[f:_;~;; ·~:Yl-tf~.f~-.-_\":.t~j;!'(i~~::2:, ~ 1? U~
METHYL ETHYL KETONE 11 U 14 U 14 U 11 UJ 12 U 12 U 17 UJ
TETRACHLORO_ETH~NE <t$rRACH~Q8Q~THY_L§Ng)?/t?:~·; .· ·.1;1:iJ. \:.-:.\:)· ·jif_Q~~:-,·:c\~")'f'.~T~~µ~~::·~;:.~.r".?:.ff-.Y.~Tt1'i,'.: s t~"\:I~t!ffJ~~ ;_ :-121r :~.1::-_r:~.:' iz.~·~: : , 1,3 UJ
13 UJ
13 UJ
TOLUENE 11 U 14 U 14 UJ , 2 J 3 J 12 U 5 J
TRICHLOROETHENE (TRl<::HLORO~TtiY!,ENE) i.1~.' .-_ij ~--. \4 '(i'_•·· .. '· '.;:_;J~,U< ~~:(,:.,Jfl,i,f,:i_'::;'.'f: 12 Tit;]:~'~-~~;'·'. i~!J-'.\:-~ ·.:.:. l°i iJ ·
EXTRACTABLE ORGANICS
15 of 18
-
- - -... ------ ----
TABLE 2-1
SOIL SAMPLING SUMMARY -VOLATILE AND EXTRACTABLE ORGANICS
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
-
GP053SLB GP053$LC GP054SLA GP054SLB GP054SLC GP055SLA GP055SLB
CHEMICAL
VOLATILE ORGANICS
1, 1-DICHLOROETHENE (1,!:0.ICHLOROETHYLlcc_f'i~j_:·:,.J.';::\,., .. 14:)J,. , .
1,2-0ICHLOROETHENE (TOTAL) 14 U
CARBON OISULf=:IDE .... -.:, _; .~;_,.;~-~:t•~. j~ l/:" , ~
METHYL ETHYL KETONE 14 U
TETRACHLOROETHENE(TETRACJ-\LORQETHYLENE). ~:~.:•'/ .. j4 i.J:·
TOLUENE 14 U
TRICHLOROETHENE (T~ICHLOROE_THYLENE) · {,.;;:~•; ... : :j4 U -
EXTRACTABLE ORGANICS
- -
Section 2
Soll Sampling Investigation
GP056SLA
. : NA
NA
N'i,:
NA
.: NA
NA
NA
(3-ANDIOR 4-)METHYLPHENOL _;: < . 9500,lJ. ]?O_ lJ :,;''.: : -~ ;~s_Q,J!:~: ;..'.';~)§q::i:[~;: .. /t::jfo~_Li,, ,'._',!,: ;4.QQ u· • : ~ :i~Q U · 340 lJ
2,4-DINITROTOLUENE 9500 U 370 U 350 U 390 U 370 U 400 U 350 U 340 U
2-METHYLNAPHTHALENE. '.-i ., -; ;,9§,QO u ,: . -~-," ~?Q ~';,' :-.:':7-'ISQ\Li':: '. '.'i:~10JJ2\E'.'::·:rrJi,.U: ~~t:r·. ::;.-:c. 359 lJ i. ·,: . -:i<io LI
ACENAPHTHENE 9500 U 370 U 350 U 390 U 370 U 400 U 350 U 340 U
ACENAPHTHY~ENE ,,_ -. • ·,_.-, ,,." •· ·.9§o§Q :.~ . · .Eii J.! : :..;'(:· ~si&O;,:·: 1cf-.cJ!iii1!,,:,c-·:):J'?.!i .... i,ii.;.:\f-', ·;;o:i1J;·fifi~.=fs_o u· -...• , : ~o u
ANTHRACENE 9500 U 370 U 350 U 390 U 370 U 400 U 350 U 340 U
BENZO(A)ANTHRACE_N~ -_ . -~ ~ ·~ . r :--, . _.: · • ,~·.:--:<~~it,~:;_ .t~ '.9_~QP _y_ :· ·,/'.: f \: I?1f9:,.,· -'.-):'.: ;.:~s[~f t\'t:t~J)90 i!J\f';:rr::_~fcLQ.~¾~-/·. ~~Q. .-!.:.' ~J? .. :· ;·~~ti ·y _ _,, ·. :~ ::. ~46 1-:!
BENZO(B AND/OR K)FLUORANTHENE 9500 U 370 U 350 U 390 U 370 U 480 J 350 U 340 U
sENzocGH1JPERYLE.NE :,c· · · · ,, · :_:,::,' ;) ,~§QQ \i :,;.::;; ~ZQJi ,_., :::,:@fili.,Q',. ·.,::•"X@cFu:ff;i-djffQ .:;ti,;.,:.':'.1.§i_~_, ~-Si; .)s91.! .• ___ 340 u
BENZO-A-PYRENE 9500 U 370 U 350 U 390 U 370 U 220 J 350 U 340 U
GARBAZOLE -1.-,_ . ._ _ .• •::,: : -~· :t) .. ·:~J9_DjJ.-:.:/ht::~f!;EU/ :·:.,:j_:',~~~sci\f\ ... 1~•~::~~__9..Q1J%.t.;~.:;i.]icf·1F·· ;?;J -~::jb9Jt~_r:: • -:)~P:~· · :.~ ~, :-~Q !-J ·
CHRYSENE 9500 U 370 U 350 U 390 U 370 U 210 J 350 U 340 U
Dli?ENZQ{A,H)f,N,:-H~Q!;~_E . . ;::•·~1 .. r-.::'•.~'.Li;::{:, ~::-9506~ u' :.:~.~·-:;-~ 0
'.• 370~u;;~-:·, ·:: c·1~J:35o"'TJ.J~..,,'.~}t1.396TP~;t:.~-:g;37·ou·.}i-''.:.:F::_:.~ ~oo·u-'~·_ . .-_·;:;,_ . :359. l!·• ~ "•\_ ;·_:·: ,. 349 l!
DIBENZOFURAN 9500 U 370 U 350 U 390 U 370 U 400 U 350 U 340 U
FL_U9~NTHEN~. ~-; :.:.~: :;-\·-~ :.,.\!-.fd~-~•:.:0'..:...:,:i, (;.iI~9.Q~i.L:· •. :~~¥,.f{37Q,'._~~j~\~:i!:{~,1.§Q~QlI~!-\~§39i:iitYJ1~a1.iJ.1t@ZQJ1:t.;w;t.t.0J90 J6_.-_::j:z;t::;.. i~ef=U: ::· ~~ ,:1·:...~D,. ~
FLUORENE 9500 U 370 U 350 U 390 U 370 U 400 U 350 U 340 U
1NoENo 0,2,~-¢~) PYR~J'~!;. , __ ., ::_~;~:_·. ~-~-di:.-:i,.'}t .. ~~:.;_-~ t:~:;950Q-1_Q·:.:· ::~:~~?~qy;~·f5[U;hl2.[Q~-;.-'J~~~39Q&~:~~~37Qff~~~:'lI_Z,.~fso ,~ .~{~S..: 3~~tf p ~, .. ~.: .~}4_0 .. u~-
N-NITROSODIPHENYLAMINEIDIPHENYLAMINE 9500 U 370 U 350 U 390 U 370 U 400 U 350 U 340 U
NAPHTHAL~~{E -·•-• , . • ~ ·i ~ __ •1• :· : • :;,?.;. ~;/~ :~:.: .1-f>...'.'~-~~t~J:th.t~§.9Q;j.L?"'~t:;:;t:_3j§_'!-!:: ._•;1·:f!11IsJ~1Tc::;>:J}:d:~_go·1o~~tf.'f~:f~Z9:~~}.'Jil':~~@Q I[C::_·Jrt'l.t~ -~~9.· IJ: ~ .. :-'\~-~-_ ~Q -~ -·
PENTACHLOROPHENOL 24000 U 940 U 890 U 980 U 930 U 1000 U 870 U 860 U
PHENANTHRENE --~~:~/ .. · .. :; .. ~:.. .;-•-:.:: . _.;-.·;~~~;:_~<< :·:_{ ~;J7ig5QO'LJY:.,:1 ... ":~-·}3iQ.Mr,;-;.\.~-~T350'.Ut°r"jp~39otUi~;,::_:;,~37jfU~~::-,.,;.G,,:a4~J.:FCr~i~r350:U · '. -"-:·-;340-·u PYRENE -. ·-... ·-... _._950ctu ___ ,,., 370 U -. -"3sou -· --390 IJ , --370 U , • .,."fro]--· ---•350U. ·--"34i5\j
16 of 18
-
-- - ---- ---- -- -
TABLE 2-1
SOIL SAMPLING SUMMARY· VOLATILE AND EXTRACTABLE ORGANICS
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
---Section 2
Soll Sampling Investigation
GP201SLA GP201SLA
(Duplicate)
GP202$LA GP202SLA
(Resample)
GP203SLA GP204SLA GP205SLA GP206SLA
CHEMICAL
VOLATILE ORGANICS
1, 1-DICHLOROETHENE (1, 1-DICHLOROETHYLENE) , .. ;,, t. .1.D l,J·•'.
1,2-DICHLOROETHENE (TOTA.L) 10 U
CARBON DISULFIDE _ ·;.:°PL ·_,:;i['c:, ·
METHYL ETHYL KETONE 10 U
TETRACHLOROETHEN.E (TETRACHLOROETHYLENEj' ·,.,; ".'l; •,,•.. 10 iJ.
TOLUENE 10 U
TRICHLOROETHENE (TRICHLOROETfj'Y_~ENE) :-.:·-.:•;· . 19 ~ ;,
EXTRACTABLE ORGANICS
·11 UJ.
11 UJ
11 UJ ;.~,:
11 UJ
11..y~-~: .
11 UJ
•'' ·" 11 uJ , ·/_.
·. 11 UJ
11 UJ
11 UJ
11 UJ
11 UJ
11 UJ
11 UJ
17 of 18
-
------
CHEMICAL
VOLATILE ORGANICS
- ---- -- -
TABLE 2-1
SOIL SAMPLING SUMMARY -VOLATILE AND EXTRACTABLE ORGANICS
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
- - -
Section 2
Soll Sampling Investigation
GP207SLA GP208SLA GP209SLA GP210SLA GP211SLA GP212SLA GP213SLA GP214SLA
1, 1-DICHLOROETH!cf-:JE (1, 1-DICHLOROET_HY!,E_NE)_ ., . ",:::{,, ·: 1Q u. <: ,•.·.'11 y . ,: '.:;: ,;fr'Q\ .. L.,:f..C:j]jJ,f-2:,,:::::ii.9 ,-i/.:L:J.-:1 i.Y·, ,, (.: . '10 u 11. Li
1,2-DICHLOROETHENE(TOTAL) 10 U 11 U 11 U 10 UJ 11 U 11 U 10 U 11 U
cARsoN rn~uLFI0E · ._ --.. '; -/:,j;;~:-~i::.}.~;:;..sS.7: : --. ; . • . :.:·~.i 1. -~ _._--:: _;~ ~· .~t2:1~~~~:::6~~.'!':IQ;_iik~*f~r~t~fi5.iJ~:,. ·:~tifNt:~~£:-;':;_, . .; ... ~~-".1Q -~ ~ l· ~--~· ... ~. 1 LU
METHYL ETHYL KETONE 10 U 11 U 11 U 10 UJ 11 U 11 U 10 U 11 U
TETRACHLoRoETHENE (TETRACflL□RQETHY~gi.lEi {· ';·~·:'" 1:irw-:· • · · n.JJ/: .. t , 1'1.1 iJ.i'I:,i~\r!, 10.Plrr:f'trfff[it :,I:-Fi:c{'fiJ.[-,: ·>:-' 10 u 11 uJ
TOLUENE '7 J 11 U 11 U 10 UJ 11 U 11 U 2 J 11 UJ
TRICHLOROETHENE (TRIC_HLOROETHYl!cN\c) ,~; '' :/ • :.( . .' io Q _:., •:,': ;. 11 ·u::.; ·>HftJ:'.:t;?/l/flfiJ_Jj,:l('',,.::.:n]i:,,'.,j}t~-;;,h,Q,'_:•·'i'': :. iQ Li .. ~ .. , 11 U
EXTRACTABLE ORGANICS
(3-ANDIOR 4-)METHY~P~ENOL ."·,.-~-. .:.•i.<:iS;~JtcfQ:.W: .. ·'--. _3JO•.!i-·Jt·:;~ .. \-~~~9 -~U ~~~j;}i\~~tfJl{!\t:~:~j:·,~~~tu_'..~/.:Jti.1.Ycio .. ~:: -.'.:·.,~;;·J... 3_4_0 u ·_. :-' :·.:· . 340 ~-
2,4-DINITROTOLUENE . 1700 U 350 U 350 U 340 U 390 U 1700 U 340 U 340 U
2-METHYLNAPHTHALENE ., '":: :, XtQQ~ [so u'',:: ~: t~§p Qt';} ;';:\:½9 jJ/;:i:i}/' :i~ctQ::,·' ~-:'.·;f.'i_iili:O:,·.\ .::J{o iJ :, ·=· '• . '340 U
ACENAPHTHENE 1700 U 350 U 350 U 340 U 390 U 1700 U 340 U 340 U
ACENAPHTHYLENE '; ;:. , :· fiqg u., ' •; ':i~IQ , · ~;;:,•:; ~§Q!I :::; ·~•;,}1Q iJii'c:T:t. j~cfQ<D?'i:jfiJq jJ .. . .:'.)10 Li ; -::, • _<,77, :i .,
ANTHRACENE 1700 U 350 U 350 U 340 U 390 U 1700 U 340 U 150 J
BENZO(A)ANTHRf'.CE~I; ~. ,. . __ r:.;:) -'··) :5-1iQO, V.. ~.: .. _~ .,:'i',~jf~---! .· ·:: ·_~\Z~rr:::::,~fit~]Xftr·:I,~'tir~M-:~c~: ~:t'./15~i?__;J_\ •;~:.;: \·~--:.:.~9,0. ~.~i.B~p_: .
BENZO(B AND/OR K)FLUORANTHENE 1700 U 350 U '160 J 340 U 210 J 1200 J 340 U 14700.
sENzocGH1>PERYLENE -. · · · • . .: , ::'.f flji> :\L ~ . ·:' )s_o' u .. .-:::;:,,,,,:~_'!J.;>;.:'<f~'. .. !::Ho..112.iZ.I t;.~i:J ;-,;_.'i/:~· ;,~ii,J : , '~ -· .. :::i4o iJ _ .··.i ,!~o_
BENzo-A-PYRENE 1700 UJ_ 350 UJ 78 J .. 340 UJ 100 J . ." 580 J 340 UJ ,1100 J
cARsAZoLE ~ -.j.~i :i"-:-~ ... ·erAqjr .. . .. )~_cu.r-,.: ·_ :r-~~!1.?: .. ~r;;_;~~~o-t1i'l~T1f;~3s9 -~'-:f:~;2.110QJ1,~:·:. ,:•;:1 --~-;HQ y · ~!-~ : _:_33(! _J ·
CHRYSENE 1700 U 350 U 120 J 340 U 130 J 620 J 340 U ,3900
DiBENZO(A,H)ANTHRAC,ENE ' • • : ,-~~ "'.<:°', ·::/.1?00 "Q. ' :~.' .:!§.ii:1.1. :. '.,:: :,,35Q'Q'.ia·,,.t1{:ftQJ/;i~t3i,'.: 390 Li :'.'(;:~,;1700 Qt.: :· '}i.Q lj '<' .:. :Ro u
DIBENZOFURAN 1700 U 350 U 350 U 340 U 390 U 1700 U 340 U 340 U
FL~oRAN~HENE -~":<{ ~~ -~j;,f,13{...-;i •.-<lZQQ·p ,::· .. ·./.·:~~-3so~~~~ "·:~:~~~?3o 1L{~f-~;;:_~ __ I1\i!lMPD'"l.,;tr:v~oo··:r.-. :_ -: ... --~MQ !.f :,. . :t. i91oo_~..:-
FLuoRENE 1700 U 350 U 350 U 340 U 390 U 1700 U 340 U . 34 J
INDEr,JO (1,2,3--Gl?) P)'.RE~E __ . :_•·~ .. ', ·:J.~:,.·;,~ l'.-,(:t.(:; ·-;'. ·-:~-~:ffim.!i.T t•: i:,~-'i~Q_!)·~ -~:,:;_/~2,:.~---;1 ... f-sl-'fiL:g_fjJ\:1~~fil~~iJ_~i~1~;1f£'O r;;;--._-:/..:, -~-.::.}~O ~ ,. ·., .. ··-.. 790 .. -. '
N-NITROSODIPHENYLAMINE/DIPHENYLAMINE 1700 U 350 U 350 U 340 U 390 U 1700 U 340 U .. ·-340 °LJ
NAPHTHALENE . ·. ·. "· ~-:·"-::;,;-::-;; ::._-..... ~~,;-;;-_:\J: :-;-; 1700 ir:-_:.:.· 7 : 350.iJ;. -.'-·~/ '._35i5·0~-,:·:;.•!~-r34o-iJ;@ff'?.~39Q1U~ .. ~i.Si\~Tf70Q1F·: ~;_; . '.,-34Q (J -~ :.,-:)40-U
PENTACHLOROPH,ENOL ' .... ""··· ., ··-'"4300·u -· ··amu ,,,_87ou·•----sso~u -'99ou·· .,,,_4300U" _,,_840U 850U
PHENANTHRENE _; -• . :: ~~:,<·--~·,:-:~'. _,: r{:;~; ~ -~:_;: ;~;;f :fl§Jl·.JJ.:"·:~ :::-'.'.: ·';~~•i!i i::~~,:i.;@0\J.~~;~t·~~.l:!;34o{ji1$~:: .. [J§~;'.; .. :~~;;;_}1-·46f~-:;~~~-~::..-':lr~p Q ~-:~ : -£1~!'9 , -.;.."
PYRENE 1700 U 350 U 190 J 340 U 180 J 980 J 340 U '1300
18of18
-
-------------------
CHEMICAL
PESTICIPESIPCBS
TABLE 2-2
Section 2
Soll Sampling Investigation
SOIL SAMPLING SUMMARY -PESTICIDES AND PCBs
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
GP001SLA GP001SLB
(Duplicate)
@~itivl·
3.5 U 1.5 J
GP002SLA
H :S\0cJJ nwrn M%/l q: ihl
1.8U 1.9U
GP002SLB GP00JSLA
f,1),IJJ:l'T/ Vi2:fl1?i
4 UR 21 U
:;::j!JJq;;J:q:q:.§Q}\)J:,:r
2.1 U 11 U
GP00JSLB GP004SLA GP004SLB
/Hurn .·.·.· .. · ; ~!]RE
4 U 4 UR 3.7 UR
•.•. lJ!Hiii I rnnrnrn}!f!j)j i@HP:H'silt Q .
2.1 U 2.1 U 1.9 U
BETA-BHC 1.8 U 1.9 U 1.8 U 2.1 U 11 U 2.1 U 2.1 U 1.9 U
OEt[,%~1'\!;1$)ll@i%jili;irnmrnrn11rn iifflfffl n @ff It Mi~ .Ql /l&i!HMlllQ ; lfffl ffJ~J;/ E'.5%;1 1;ili[@btfaI1M'J;;!l; I}:g/~ q i;rn ;;g;xµ;;Gn ; ;}1'.g'.t/}
DIELDRIN 3.5 U 3.7 U 3.6 U 4 U 21 U 4 U 4 U 3.7 U
t!;&od~!iJtl\'AN,irlAtief.lA)l n;r@fa i t II ii Iliil!M;/Ji!i!I li wt@M!Ml!i!i.iitl!Hilli ~HliRBilil 1@1it!YRIH\ifoi: iJ~IW/HH@/ii@11I!!ilH IIII iLi De~ niiti:li YR
ENDOSULFAN II (BETA) 3.5 U 3.7 U 3.6 UR 4 UR 6.7 U 4 U 4 UR 3.7 UR
gfi!QRll\lF. mqg;;;n;;fl) H !iil!la;§lP!Hilli!}i(?'faiJ!Ji!I!t!!}l!~!!!lll illlI\tll!il!Jt!l!lg1i!J!lilHlill'lifjiiH ;4]':[ ' ;;;;$,%,Q,:
ENDRIN ALDHYDE c.1 J 3.7 U 3.6 U 4 U 21 U 4 U 4 U 3.7 U
§NQR!ti!ffi'C!iPt:!ElI T ll l!Jl§!aY'i ii!:l:1ii!~i~!il!i!'l r d\etua #!llW!!:llllrn::31:!!!.iilI il!IIli!~iiYlill :;;:4oa;:: ll~l!:!lJ
GAMMA-BHC (LINDANE) 1.8 U 1.9 U 1.8 U 11 U 2.1 U 2.1 U 1.9 U
~M!&tWfiildROANEliiW 1!8 UH Fi1 'l\ijf§luH r. %1Wi!JY 'f ::Im~: @rn:l : H 2.·, ··u·.·· .•.. ······.2.1 ··4 ' . I / 1!9iU/
HEPTACHLOR 1.8 U 1.9 U 1.8 U 2.1 U 11 U 2.1 U 2.1 U 1.9 U
!l!li4eltei@Bli9Bi§RQX]R§li!li'i 1l~ !ii !:::Hi: i:ll11~LWI!ll I fl~];! I i ! ii11 :wi li K 1(11\ki . l ~11 ;~ ;;; i ; ; ra;~ µ; ;;;; . t 1.'9.: l/ fa
METHOXYCHLOR 18 U 19 U 18 U 21 U 110 U 21 U 21 U 19 U
flQ§~~g§~l~~99§WQfil[ic%§rtX t T eaHl!inl!ll li !B.A!!JHfflHII Pi:\!f!Ii H~\!iHSE!Jff,~71.!;j;iili i!iiil~inl: lll' ; 1gl!;l;J!I!m1l!ll1~%!!;l
PCB-1260 (AROCHLOR 1260) 35 U 37 u 36 U 40 U 210 U 40 U 40 U 37 U
Data Qualifiers:
U = Material was analyzed but not detected. The number is the minimum quantitation limit
R = QC indicates that data is unusable.
J = Estimated value. N = Presumptive evidence of presence of material
Concentrations reported in ug/kg. 1 of 18
-------------------
TABLE 2-2
Section 2
Soll Sampling Investigation
SOIL SAMPLING SUMMARY -PESTICIDES AND PCBs
GEORGIA-PACIFIC SITE
GP005SLA GP005SLB
CHEMICAL
PESTICIDESIPCBS
3.7
§NQBIN !S§XTQff§ t m I i ~i't 9. IH
GAMMA-BHC (LINDANE) 1.9 U 1.8 U
G5MM..%GHPORPi\\!\!!i:l!l! r nn @;$ Q I 1!~ ill
HEPTACHLOR 1.9 U 1.8 U
e@iflg~/ifiR9§ttM@R1?$il'IIE
PCB-1260 (AROCHLOR 1260) 37 U 34 U
PLYMOUTH, NORTH CAROLINA
GP006SLA GP006SLB
2U 2U
38 U 38 U
GP007SLA GP007SLA
(Duplicate)
GP007SLB GP007SLB
(Duplicate)
1.9 U 1.9 U 2.1 U 2 U
i1!@!J> 'I#l$tl i\ g;ig S~tU/
1.9 U 1.9 U 2.1 U 2 U
37 U 37 U 41 U 38 U
2 of 18
---- --- ---- --------Sec:t/on 2
Son Sampling Investigation
TABLE 2-2
SOIL SAMPLING SUMMARY -PESTICIDES AND PCBs
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
GP00BSLA GP00BSLB GP009SLA GP009SLB GP010SLA GP010SLB GP011SLA GP012SLA
CHEMICAL
PESIICIDES/PCBS
4ll!l@RQ((RlRitRRRl li ,. l!itliiffi/ ' m ; l%Ri§ !i!BiffHH\liJJ41\:1BN rn na&MR} n;@H§i§tQa H}liS@§j wrnn rnl ;zj§f.!WFM ii!!Rl1 9.RHHtlIJ@;glQ "
4,4'-DDE (P,P'-DDE) 3.6 UR 4.4 UR 3.6 UR 6.3 UR ( 0.67 J 3.6 U 3.4 UR 3.5 UR
4ili8P9I(?i!filtRR®L r nrnrnwr ; ; nuafe;qrnrnrnh\!kl!lPlPll i llleI!i!? l ; {@$;\$\U@H' !!?~!$-P nrnlPl 'qillB!i@/lM ; ;~(4 Q ff iFH3l$. ow
ALDRIN 2.3 U 1.6 U 3.2 U 1.6 U 1.6 U 1.6 U
DIELDRIN 3.6 U 4.4 U 3.6 U 6.3 U 3.5 U 3.6 U 3.5 U
§@RR§hl~#l!§i;t~lm!l!&il;ii!:ff •••< 1.a:qiii,, T!M?l~ll!R : ;;i~pg;; !1iI@1gil:!B11!lll1! 11~w. ::;n 1,g:14::n;t ataI:ua
ENDOSULFAN II (BETA) 3.6 UR 4.4 UR 3.6 UR 6.3 UR 3.5 U 3.6 U 3.4 UR 3.5 UR
§NPSlNl) !:i ' ; ;....... .. r;:;;;:;Uli:itn:Hrnit;:g Hi !l! ~'.!:lit.Jfi, ;;; W4l!ilj!jff ;;,;;; i~ley;µ ;rrn;@Jey;(J)iO\jj1!1}1Hls;l!ili) !Hi i ;::;@;fiof(f\lljh!FlH@iJ!i g HJ l~:$-QW
ENDRIN ALDHYDE 3.6 U 4.4 U 3.6 U 6.3 U 3.5 U 3.6 U 3.4 U 3.5 U
!;fjp}AfNIKl;'@lg&(';l!l!!i:@l!t!ii\!MH!@fa; " " --1;zy\gi!,,!iHWNlHL4i1!UUHMifa!l9J!f:!C!!PMWHFvi%W!tiHH #gl9,tQM!;lHMHt%\§JM;iMMhiH@i!lVµ1urmm;@igQJt
GAMMA-BHC (LINDANE) 1.9 U 2.3 U 1.6 U 3.2 U 1.6 U 1.6 U 1.6 U 1.6 U
%!%MM&llf!i!£9!tP~§ff.!lMilli! l!MHi: I$i~tiif1;J;ii~!~tl l Itf1HIUiHlll:}lsi2@<:, 1.s u,,, ,: , , 1.~p,':'.;'>: -, 1.~ u Hiliff1!~!Jff
HEPTACHLOR 1.9 U 2.3 U 1.6 U 1.6 U 1.6 U 1.6 U 1.6 U
Ht!Pjif>f!§fiµoR Ef!.9.X\95 gm M~ MT.! !! Fi2is UH j;JfQ'. t M~ V i ; nm:Ml!lU:t,rnrrn lMWP t k ("ta u
METHOXYCHLOR 19 U 23 U 16 U 16 U 16 U 16 U 16 U
e£l!¾Jl!~lt~B2§1\\W@®jg§fil'.li:!fl •·•••·•••·•-• •!K;P H@§Il!il H!lll:lil?$)'!l!Wl!l1·J :e.4rg L••••••• @§JJ;
PCB-1260 (AROCHLOR 1260) 36 U 44 U 36 U 35 U 36 U 34 U 35 U
3 of 16
_____________ , _____ _
TABLE 2-2
SOIL SAMPLING SUMMARY -PESTICIDES AND PCBs
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
Section 2
Soll Samp/fng Investigation
GP013SLA GP013SLB GP015SLA GP015SLB GP016SLA GP016SLB GP017SLA GP017SLA
(Duplicate) CHEMICAL
PESTICIDES/PCB$
DIELDRIN 3.6 U 3.6 U 3.7 U 3.8 U 3.6 U 3.5 U 3.4 U 3.4 U
1.a(!H
3.4 U
$!\!P2i1:!!filr&!\/Jif.t;!ifi!i!i'i!t 11~ua wauRw fad;$oo<···•·• Hl!Iii!B Mi§!!i!Hi l1l~!JR1 n t1a1J1 r
ENDOSULFAN II (BETA) 3.6 UR 3.6 UR 3. 7 UR 3.8 UR 3.6 UR 3.5 UR 3.4 U
siiibliiiii n tiJl\li I ij(e;UH 1$/tI!il t i;~l!!H@ I iiiIQ H l@;t!M l Iil'.#v IH i.i!fW
ENDRIN ALDHYDE 3.6 U 3.6 U 3.7 U 3.8 U 3.6 U 3.4 U 3.4 U
ltNPRIN KltYXQNi; .............. ........ ; ~',S 94 I i~il'l urn ll;t l!J 1i r t I at~ lil;f lfiifij a 4 u
GAMMA-BHC (LINDANE) 1.9 U 1.8 U 1.9 U 2 U 1.8 U 1.8 U ·1.8 U 1.8 U
GAtWvil!JoBl!otlJ>.w.llgt? ········•••·•·•·•·•·•·•·••··•·•·•·•••·•·•·• r$•t1 .. ·•·•·•·•·•·•·•···t·•·•·•·•·••1;ap .. •••·•·•·•·••··•·•···•••·•·•·••··1;~gJ gµ Lttn 11~:9 M!M!i I HI ll~M ii 1i8!Ji
HEPTACHLOR 1.9 U 1.8 U 1.9 U 2U 1.8 U 1.8 U 1.8 U 1.2 JN
METHOXYCHLOR
i@l&!@~itill@Pft§@R1g§!!I ....... -.. :,
PCB-1260 (AROCHLOR 1260) 36 U 36 U 37 U 38 U 36 U 34 U
4 of 18
-------------------
GP017SLB
CHEMICAL
PESTICIDES/PCBS
TABLE 2-2
SOIL SAMPLING SUMMARY -PESTICIDES AND PCBs
GEORGIA-PACIFIC SITE
GP017SLB
(Duplicate)
PLYMOUTH, NORTH CAROLINA
GP018SLA GP018SLA
(Duplicate)
GP019SLA GP019SLB GP020SLA
Section 2
Soll Sampling Investigation
GP020SLB
!!i!!'f@Rtlte1e;:@12@r1@ + !W i Imm ti rn:t :rni@iBW!!! , i1;;1g !11!:ts I~/$. ll!R 1 i~l~ !i!Rt ;: w rnu§1µ11iw ;;;; #tt9 1rm1~ww~:§?P" : M w ~;7,µ
4,4'-DDE (P,P'-DDE) 3.7 U 19 U 3.5 UR 3.5 UR 18 U 3.7 U 3.6 UR 3.7 UR
#t#HRPIBlIBlfiliP:Rflilff1l!lliil >> c :; ;,,,, £ >·vtvN,,v+:wu :l!!itU ·······1n;:g1prnj ?fF6gilJ)?rnMi1)R?iiii!h:}!l¢§f\:!RWP?e?i9
ALDRIN 9.2 U 1.9 U 1.9 U 1.9 U
DIELDRIN 3.7U 19U 3.5U 3.5U 18U 3.7U 3.6U 3.7U
§WR@§Wirf'.ittlii[e!lwii!:1 77'.T/ff{'.; Tir:90 ;2:; :neu; LAJ'VQ!lt··· ··mmHOR LZ f~@q trnrnrnJ{QJ!ilfd@i# ihliillR!@HMHiiFOR
ENDOSULFAN II (BETA)
1¥N@R!NF
ENDRIN ALDHYDE
itNR!'!l!'l Kiiirn@!'i§l rn
GAMMA-BHC (LINDANE)
GAMMAfG!i!!\QRQ/:s;!)lpt2? ·• ··········· ··
METHOXYCHLOR
RGaiiff~$4I!f,R,עBlioRti~54H fi
PCB-1260 (AROCHLOR 1260)
3.7 U 40 U 3.5 UR 3.5 UR 18 U 3.7 U 3.6 UR 3.7 UR
><><>< GTE ~r:11>>> '.'.'.iffi!it :z dsp ~;§u Jllc!'!n:;: ,at7Iui +•irai\lut ii@;1K1w
3.7 U 3.5 U 3.5 U 18 U 0.76 J 3.6 U 3.7 U
,: '.~;'tlii B;§Q4 ~l§!!JlL .t~V":'1:i!IE!~\1'.!lm;:;;;;::;:!&l!Q~': :;:g;z!ll4
1.9U 9.6U 1.8U 1.8U 9.2U 1.9U 1.9U 1.9U ·!lJiaW • i9i6•U ; :J~Q a;irm;;; ~i:?9.,FLTMfrs"U'.'ttn :J;Jl\g 1rntidF
1.9 U 9.6 U 9.2 U 1.9 U 1.9 U 1.9 U t't:r~v+ ::+i!4u rn~:z;o::; t:l!;g~;u;r1:;::x1:sru+rn;;;;1;~u:
19 U 96 U 18 U 18 U 92 U 19 U 19 U 19 U
>··'i!F!'. ;9,;~z:tr ;;tt~gqe 351] @§;µ;; l1i\Ottl.@%}HF3'r\.UK:l:: 36UWIH 370T
37 U 190 U 35 U 35 U 180 U 37 U 36 U 37 U
5 of 18
-- -- -- - ----- - - - -- -
Section 2
Soll Sampllng Investigation
TABLE 2-2
SOIL SAMPLING SUMMARY· PESTICIDES AND PCBs
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
GP021SLA GP021SLB GP022SLA GP022SLB GP023SLA GP023SLB GP024SLA GP024SLB
CHEMICAL
PESTICIPESIPCBS
if;~*RPR(fl1fft!?ia!?lI @ey;§@BL. B!1LVRY a.au· · .. ·•i;'.'a·:z:u l ll ~!!!ll1lll~I4Ml llil1 ~l~YBlll IWlAH1I
4,4'-DDE (P,P'-DDE) 3.6UR 3.4UR 3.8U 3.7U 4U '...2J 6.8UR 3.2J
1\lf'.tRRTilfl\!ll)f!:IgT}!!Hl ..... , i ;;i~jeyg &;~;g fff@1!liU i;;;p;gs;) III 4iQff@iG lM(4!J; lNliffW;;JjQ rnrnr ill!t!!il
ALDRIN 1.9 U 1.8 U 2U 1.9 U 2 U 2.3 U 3.5 U 2.9 U
DIELDRIN 3.8 U 3.7 U 4 U 4.4 U 6.8 U 5.6 U
§t'!@@i1W£Eeif!!l!&!&~&i t@IWi 'dliji!iffl ;; : g;urnr; 2aW.t ··.·.·.·.·a;s gR . @l~WR
ENDOSULFAN II (BETA) 3.6 UR 3.4 UR 3.8 U 3.7 U 4 U 6.8 UR 5.6 UR
ENDRii\:f ·.-;-:-.-:•,:·:·::;:❖:•;.·-·.;,·.·.·. fojg;§Y; }'. !ti#Q:li;::'.; I~l~lliil ;;ta)ttL I ft;Q;; Willi' §it!M: rn {Il$llMQHl
ENDRIN ALDHYDE 3.6 U 3.4 U 3.8 U 3.7 U 4 U 4.4 U 6.8 U 5.6 U
!:t:IRRIN !Slf'Nl1f@!i!,$Hil@i\ifl :&ifri I l ililtMF@:l,s uJ i ,3;4, o;fi,f@ i¾ itU i ?;{Hl~l!!Ml,W '\, ~;q:;72;;; ,¥¥9 ' illff F?ia;wnI;1rni!§l§l!!!U
GAMMA-BHC (LINDANE) 1.8 U 2 U 1.9 U 2 U 2.3 U 3.5 U 2.9 U
dAMMA.~C8tpfIDANEizdi ... . •·•·•·•·t llf]/1:/ \ [f g ; ;;;;;;;1%4'. <> JFU•D;E '.;@%H....... L.~.6 U· >A fgJ8t©I
HEPTACHLOR 1.9 U 1.8 U 2 U 1.9 U 2 U 0.82 JN 3.5 U 2.9 U
METHOXYCHLOR
R@!Ri3§il~l2@HYRB@tl°ll li!l l
PCB-1260 (AROCHLOR 1260)
19 U
YL>•i•~eµ;
36 U
18 U
•:; iJi! !Jrc;
34 U
20 U 23 U 35 U 29 U
*9;g;r;;;;:;71;4;q;;c; Rl§!Jil!l!I@IIU ®UL
38 U ~u ~u 68U ~u
6 of 18
-
-- ---
CHEMICAL
PESTICIPESIPCBS
1;1~Bi{e!ffll!l!RRlill tJ CS
4,4'-DDE (P,P'-DDE)
li)!!iiR.BI {R;filfQRiiI@!lli!! rnr
ALDRIN
AtPi1l~aR& HI :-:-:,:-:-:«❖:❖:❖:❖:❖:❖:•:·:·:•:•:•:•:·:❖:•:❖:❖·--,.
BETA-BHC
-- --- - ------ -
Section 2
Soll Sampl/ng Investigation
TABLE 2-2
SOIL SAMPLING SUMMARY -PESTICIDES AND PCBs
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
GP025SLA GP025SLB GP025SLC GP026SLA GP026SLB GP026SLC GP027SLA GP027SLB
f@•l➔l!?!l!B f;il l~\#°MB! il W~!~!i!ft il!J;!J~l§\0$\l i§:t .VR!fftl:l!~l~;litBnffa l:~;s(iJ@H tiiif~i~P. :
3.6 UR 3.4 UR 3.9 UR 3.5 UR 5.1 UR 3.6 UR 3.5 UR 3.4 UR
Hiil~l!!fli!Iil ll§l~Q ij:i!iu th d#@J@;i; %4,Mi.Uiii;i@$;ittUfriiil @l1l@1 · aAU
1.8 U 1.8 U 2 U 1.8 U 2.6 U 1.8 U 1.8 U 1.8 U
n na&ll?IVll; lll !lIJl§lQ#li Eilt;;g·yl!];i;,;r;;:;1i*tYMiiil[i:i Iq\~Q~;/;~;I@iewi!ii I 1:tl§l!fig ;; rt ~Qg
4.6N 1.8U 2U 1.8U 2.6U 1.8U 1.8U 1.8U
DIELDRIN 3.6 U 3.4 U 3.9 U 3.5 U 5.1 U 3.6 U 3.5 U 3.4 U
gfilpfl§QµfiANllf~RRffl~! r f•~\!lWRl 1\~Q/31 :;: '.,?!JR/ 1i~YRi I] ~iR!i!Biirnrn1i§QfllE fH~iaIORM !HJlil~QB
ENDOSULFAN II (BETA) 3.6 UR 3.4 UR 3.9 UR 3.5 UR 5.1 UR 3.6 UR 3.5 UR 3.4 UR i;NbRIN ;rrrnww I;rnrnt nnnnrnrn;;;rnR£1rumrw;raA1pn;rn 1;,,,3;sumff J?i!'Wt:1;n;;;;;91~t;1+rn;w1r3:et1I ;qquu; 1 ·rna:!ttli
ENDRIN ALDHYDE 2.8 J 3.4 U 3.9 U 3.5 U 6.4 3.6 U 3.5 U 3.4 U
§J'iRfl!Ni~§Ym§N§lI!l H I n ;;;n; m;; ;g w~t \;/ilJ@tliill %l41\;pjj lHh~i!li!il.iJ! M!idI ~;§ l:14/I ; l i!lf@g li wrnrn~i§!!il!!i%frt@I§!&•\:MF n Hl@4!W
GAMMA-BHC (LINDANE) 1.8 U 1.8 U 2 U 1.8 U 2.6 U 1.8 U 1.8 U 1.8 U
QAMMt#GFiii'dROANEiz H rnE1!!!t! Imii!l m§l\:IHH wm;gg;11im1i1;~;i(l,t!l I@i~l!i(l!Iililfil!!i!l!!!!li H\tH!l8</l!IIMli1i!~!JW
HEPTACHLOR 1.8 U 1.8 U 2 U 1.8 U 2.6 U 1.8 U 1.8 U 1.8 U
fflsRIA§filgQf§§RQX!PsWII rnrn;.; x 'S i;tiili*P .. ,;.I 1i~IH; I );;;;g;Ji)) .w\ ... J.,!i;,\\l,,i ,;.; ..... g,§,.Q ... ; ... , .. ; .. \1.,§.!)!;,",········J,§;Q .... ;;. Mih~R;;
METHOXYCHLOR 18 U 20 U 18 U 26 U 18 U 18 U 18 U
B@!¾!@§#!AB8P)ib9B1g§jfj W:m!i!! ~gJi! fili~EiJll!l!;'is1u iNi@§il!: ll i~~p t ii~iiu
PCB-1260 (AROCHLOR 1260) 36 U 34 U 39 U 35 U 51 U 36 U 35 U 34 U
7 of 18
-
--- - --- - - - ------- --Section 2
SoD Sampling Investigation
TABLE 2-2
SOIL SAMPLING SUMMARY -PESTICIDES AND PCBs
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
GP027SLC GP028SLA GP028SLB GP028SLC GP029SLA GP029SLB GP029SLC GP030SLA
CHEMICAL
PESTICIPES/PCBS
1;\!\4ppl)i(l?1Ri\PPPil &Fl% l M; lH @Ml!hd l it$ ORH@t!: J3i$ PB M;rn ?i~ Q.&n l t;I@ll!iP..RIIliH)/$;!!t!l¥!H\1i;' ~Jl ;IJ! Ib Mil~iZ U 1 ! ;rnihi ~;$ U.R
4,4'-DDE (P,P'-DDE) 3.5 UR 3.5 UR 3.9 UR 3.5 UR 3.4 U 3.8 U 1.7 J 3.5 UR
l4li\'tl?l?rnl!elfltt!?B'9 n •·•·•·•·•·•·•·•·•·•·•·•·•·•·•·•·•···········•·•······ @!§!l!!i•g1w?:srui_ ppi9••-□ naisrnnmrnrn ~i~)g,IF. ~11l'P .. >e:, mrrn:nn@isrun
ALDRIN 1.8U 1.8U 2U 1.8U 1.7U 2U 1.9U 1.8U
e,µffRA!!lB.◊Mff ; ; '.jjJ@;il!l! lk+ !1;& !l/JlM!dli !;l!l!JJI Vi:il:';Z;iJJ I; ;!JJ})Ji!lii i i it\liW!JfNTlMI ;rn l\z Q ffff rn Il!llllim!l•ltl!JhJ!}I!li&
BETA-BHC 1.8 U 1.8 U 2 U 1.8 U 1.7 U 2 U 1.9 U 1.8 U
ENDOSULFAN II (BETA) 3.5 UR 3.5 UR 3.9 UR 3.5 UR 3.4 U 3.8 U 3.7 U 3.5 UR
qi[lg13ii[I i rnrr ., .... ,. . ... CE' 1;.r~l!tti@ll!Wf~)$U n l:l~liJllMlJ l\~;gl;b l!~ilHf!HE ,; ;Hliy rn•:!f}jtl#l?)Ql: • ffl'.}~l~QH
ENDRIN ALDHYDE 3.5 U 3.5 U 3.9 U 3.5 U 3.4 U 3.8 U 3.7 U 3.5 U
~M?fB!IHtlosti*NS!~;: !MfflH M/eyJ~H l!(\,jj~!tlil@I Ii!liiliFli( :2q z•i. 1lq~--?ii:~11••••·
HEPTACHLOR 1.8 U 1.8 U 2 U 1.8 U 1.7 U 2 U 1.9 U 1.8 U
§§J;'[ACH@::!BsRi219H§Hhl nw I!!!Wii ; ~glNffW!Hwll1)~I!i! n l IMIFMlgll!'! ::::d;.ey;rj}} 1/i!·/UY ii ; ;; ~ ~X;Y} %~•¥! ii '. a !;'8 g
METHOXYCHLOR 18 U 18 U 20 U 18 U 17 U 20 U 19 U 18 U
!il%§1%)@.p~\~~lt!i!!i9Bi1&~~m; H l!lW lliM?!!Jl !li!Wif@llp If! i H ;n l~~lO ' j;'35'U' " ;~ J!!;rnrnm ?~;q ;:: ;;; ;};JIU ;;;; ; ; 3!i U
PCB-1260 (AROCHLOR 1260) 35 U 35 U 39 U 35 U 34 U 38 U 37 U 35 U
8 of 18
---- ----- -- - ---- - -
Section 2
Soll Sampling Investigation
TABLE 2-2
SOIL SAMPLING SUMMARY -PESTICIDES AND PCBs
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
GP0305LB GP030SLC GP031SLA GP031SLB GP032SLA GP033SL.A GP034SL.A GP034SLB
CHEMICAL
PESTICIDES/PCB$
~l~liPRQfRiB'.fQR9ll!l[\i!'I rn#t L iftjj It\ ;; H~:$ g§ :: :;:&;y: gj§ ZFL l\l;glQRK W$i,t 01"{ rn k$\ffiQl'fiH@lll~;?!!MRW l!il ;}i§it/~ l !lI;lll)l~ l:L
4,4'-DDE (P,P'-DDE) 3.6 UR 3.7 UR 3.6 UR 3.7 UR 3.8 UR 3.5 UR 3.6 UR 3.7 UR
!liii!ii!RBT(B!B!tRRIBl i I l tg/§I!! ! ; Jl}t;U : ais u I~lz !I! I !!I t!i@1l!I!l/I ::n ! l llg!§ !it ll i ! §]ll!QiiIII iiil~;f!!'!I!
ALDRIN 1.9 U 1.9 U 1.9 U 1.9 U 2 U 1.8 U 1.8 U 1.9 U
&\\BMet!:lfil§)iJ!H ;;!;:1;t;;; rnmil!WQl!!irn@ti\fJ:mrn@t Wl!lP.AH '. :){ij(lj • F\.i!JJF:i; jj\\Jjfr ?h;Ji l/4 ,4,;d(sqq,
BETA-BHC 1.9 U 1.9 U 1.9 U 1.9 U 2 U 1.8 U 1.8 U 1.9 U
DIELDRIN 3.6 U 3.7 U 3.6 U 3.7 U 3.8 U 3.5 U 3.6 U 3.7 U
i::NDQSQLl1AN ji)l;(pflA·) It ilfll ltlli w tlfaiaiUR wrnHH#ii! IJs l rn l 'l:91QR1 {; i @tWluR ili faWHtz i:u,i;i;;H t#ii!t/RP.n }iiil!iUR ; Fil[) 1fa WR ......... ..: ..... :.: .......... c ... .:,. .. ,., .. dJJ, .•• , .•... ; ..• ,.,, .•.•••. :.n . .. . . .... .. . . ,.. .......... . . .. ............. . ......... . ... . .... .. . . .. .. ... .. . .. ..
ENDOSULFAN II (BETA) 3.6 UR 7 UR 3.6 UR 3.7 UR 3.8 UR 3.5 UR 3.6 UR 3.7 UR
E,N\tlRlf:llllEH ! nie l ~;!l;G li ! §;z;g ! !4i!!ill!\;; li~1?;lU ;n d@1l!,!l/ll ;•;; ;~;1mn ;;a;i\U if ;;~~?ti£
ENDRIN ALDHYDE 3.6 U 20 U 3.6 U 3.7 U :4.7 3.5 U 3.6 U 5 U
€Nf?ffi!)!!S§MlllQ!l!§..IHI:m· ?t)il$/6i!llil fr; $llYQ! pa•s·••ulid I 3;7•pli···.•··••;:•::··s;s··uu· .: , .. :)PU!Jif';; j i~)!E!t~ii! i~i?!lW••
GAMMA-BHC (LINDANE)
GAMMffi§.fillil'RRRAf:!J?i2i t
HEPTACHLOR
HElPTACRLOREP6Xi6!%H
1.9U 1.9U 1.9U 1.9U 2U 1.8U 1.8U 1.9U
:; ;;; lii~I@llI!ii!Ii1ill'Mil!Mli@J!!I!Jll q1,gu; ;r:~Q 0:2 Ji§\Wii ::rn1:J!,U i!;iJ:lE!l/
1.9 U 1.9 U 1.9 U 1.9 U 2 U · 1.8 U 1.8 U 1.9 U
11;~g IIifli1\~9['ii F1!llI!!!IlI fi:hllV ;;;·: @\f;;';;;; rr~r;e;: ;.; .. ,J,.~.\J : n;!!Qi
METHOXYCHLOR 19 U 19 U 19 U 19 U 20 U 18 U 18 U 19 U
PG§it9?&XARQ$.1il!'iPB1f?fr}Jl@WM!• ....... ·.fo iC••· ··•·•·•·•·um§IQL .... · '!'i~?P .. ····•;;+; -~§;Mnn .. Ei:~zq; .... p;$31VH;y ' asur. '.?,'.(},6!} jpi/y:f31tJf
PCB-1260 (AROCHLOR 1260) 36 U . 210 36 U 37 U 38 U 35 U 36 U 100 U
9 of 18
-
- ---
CHEMICAL
PESTICIDES/PCBS
!i~:!Pfl'fi:IR1Rtf@R!?l
4.4'-DDE (P,P'-DDE)
iflm!RPlliRBiiJJqg;QI;
ALDRIN
:4freiiUiU!illc
BETA-BHC
- --- - -- - - --- --Section 2
Soil Sampling lnvesUgation
TABLE 2-2
SOIL SAMPLING SUMMARY -PESTICIDES AND PCBs
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
GP034SLC GP035SLA GP035SLB GP035SLC GP036SLA GP036SLB GP036SLC GP037SLA
411¥/B % q;;};ttj~J... IH~;~•••WB ·rn:I@;~gg t•ta1gg. nt WWURT F~isUt,HF tii§lWW•···
4.1 UR 4 UR 5 UR 3.7 UR 3.4 UR 3.7 UR 3.5 UR 3.7 UR
rnrnrn+ntil IIIHM@ifl)Qt:rnnnrn@wtlti!MVi!H@.l~lP:tUW!Ii!@.iZQIEMIH•~>!l!JiltlffHl;fiz:l!i.! ;19;gll\! ' ; ~YI:\!)
2.1 U 2 U 2 U 1.9 U 1.8 U 1.9 U 1.8 U 1.9 U
·g,!i:1a ·. ::,. 2 u:1 IR!l@liltI!l~il!Jirnll!l11§;t!!iiliF:t@t~Ii¥i!i.lrnI1i112, rn~wm
2.1 U 2 U 2 U 1.9 U 1.8 U 1.9 U 1.8 U 1.9 U
DIELDRIN 4.1 U 4 U 3.8 U 3.7 U 3.4 U 3.7 U 3.5 U 3.7 U
gNQQB\!1@;6!\iit(~!!RB&1III!ii!illiIHl : 1 M [Ji!llltl ,fi1i!i.tRH! ll I @!!flllirn! 1g;!!!f{ lllill!ii1i~li!!!Rilllil!WJ1.i.§1!i/BJliliilll1illi litR li jf;J!!ti~l!i.tfli · :1 ifDa
ENDOSULFAN II (BETA) 4.1 UR 4 UR 3.8 UR 4 UR 3.4 UR 3.7 UR 3.5 UR 3.7 UR
Eilibi'ii& r• ••········· •: ••-t•••••, •+&Au ••t•• • A•ti •· ··rn~;~•!iNI:rnn;•i?i@!l!•!HMMM•~;1:.u••••·· t\Wtr•iw•·••••••••••••••~;ey;u• ··••••·•·•·a·t·u•
ENDRIN ALDHYDE 4.1 U 4 U 5 U 3.7 U 3.4 U 3.7 U 3.5 U 3.7 U
!if!RR!rl !S@f@;Qfi/.§ t • m lffHW+rn l litnt;;;;4@\!!!!fri!foil /Ml#'.Wi!Mlt!Iiii~ ~ !lii!li)iljjl,~)J'iI!ll~Iifr•li)i[~\1ill!Afll; ; ;G&)zm!; ; : ;;~;:§ QJ . Eiali j)j
GAMMA-BHC (LINDANE) 2.1 U 2 U 2 U 1.9 U 1.8 U 1.9 U 1.8 U 1.9 U
GAMMA!OBL'oR@.fil;j'!;g ··················•·••··•·· m H W@l ?{iJQl•!il•! ;; %12 uw· Z o:. ·.·.·.· .... · '. ; 2 Yf!l'R t;J•··!! U : 'lJFU ·•··•·X·•·•·•·•·•·<1>QJ;f•.·•
HEPTACHLOR 2.1 U 2 U 2 U 1.9 U 1.8 U 1.9 U 1.8 U 1.9 U
Hi?BW6¢t!MRB!ifR9~!R§; !illll igi1@Hlili!il!1i&MH1 . ?WI. ,fabii1i~b\ ::!Yd,e,•••u iiii1!9Ui k iJ!~iUt: • 1:9un
METHOXYCHLOR 21 U 20 U 20 U 19 U 18 U 19 U 18 U 19 U
R¢!'!111??4(A~®fil@tB14~41.. iM!lHllillFt!M I 1lMl!HftQ1Iil w;;;g~s%l mm;g;Q mmilHMWH nrnt;n@?P.. lll!lM@l~,$;Ql@; '.'. :3f~YC
PCB-1260 (AROCHLOR 1260) 41 U 40 U 110 · 87 34 U 37 U 35 U 37 U
10 of 18
-
-------------------
CHEMICAL
PEST!C!PES/PCBS
HEPTACHLOR
ffieerr@PHU&® ®'i!fi?{!Pii
METHOXYCHLOR
e@i¾1!§1!&R~W9RI1g§4J
PCB-1260 (AROCHLOR 1260)
TABLE 2-2
Sect/on 2
Soll Sampling Investigation
SOIL SAMPLING SUMMARY -PESTICIDES AND PCBs
GEORGIA-PACIFIC SITE
GP037SLB GP037SLC
2 U 1.8 U
7?t?r !CQ ··••fn??1@P
20 U 18 U
PLYMOUTH, NORTH CAROLINA
GPOJBSLA GP038SLA
(Duplicate)
GPOJBSLB
1.9U 1.9U 1.8U ····•··· rn:!!!J I Irn1;gg r a;au
19 U 19 U 18 U n~~Q r ;mmc @zw nnnazvn ssu
39 U 36 U 37 U 37 U 35 U
GPOJBSLC
1.9 U
pj;$lll!t
GP039SLA GP040SLA
19U 23U 96U
l:~il!J •••• ;ai,itld I HHfigqpn
36 U .570 190 U
11 of 18
---- -- - ---- - - --- ---Section 2
Soil Sampling Investigation
TABLE 2-2
SOIL SAMPLING SUMMARY· PESTICIDES AND PCBs
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
GP040SLB GP041SLA GP041SLB GP041SLC GP042SLA GP0425LB GP042SLC GP043SLA
CHEMICAL
PESTICIPES/PCBS
~l~WQ!?RlfillR\i:@PP1n11 I ;; r······ l@J[ijqi@§ IIlm l lt2\~::!!RH! @iI~\~I!J§. H ljjj~($Mf§l@ li!H:?lQR e.'.§:!\l!3d@@ia)pRIR .
4,4'-DDE (P,P'-DDE) .· 0.98 JN 6.2 J 3.6 UR 3.5 UR 4.2 UR 3.6 UR 3.6 UR
~l~]RRIBlRlRl@!'iiPlli •·•·•·•·•·•·•·•·•·•·•························································H!i!@?HP... t@iiI:9{'.•.•.'.~·.·, if&tl OH . '\iRi?'!l!i:iMrnl·m1fa?Hi!I •. t~)6UM\ }i·•~··ll·•·o•·•·•···•·c ALDRIN 1.8 U 2.2 U 1.8 U
DIELDRIN 3.5 U 3.6 U 3.6 U 3.5 U 4.2 U 5 U 3.6 U 3.7 U
1;~o~sp1.JFAN/ilA¼PiilA!l Iil lt trn Iilli:l;Mf il fofaia)µ I Ii !%ll!;gqgtW/11!!Mfll' WFJ lil rnwa1ii1BH!@iil:H2t\!iJ{l)I ii~: ORt}n!@!i'JllilLIR ll fi;s;ua
ENDOSULFAN II (BETA) 3.5 U 3.6 UR 3.6 UR . 3.5 UR 4.2 UR 3.6 UR 3.6 UR 3.7 UR
€i!l!RB!NH ilMrnlHllL....... iIIMMitmrnmit~Ji!l@PM!ll~l§.@ff,MiMIH$\lKP l l llRi?!i!i!lli1llll!l6il\! lil H gg\QWMIHlllgJ§!i! H HH$!'1'Qf
ENDRIN ALDHYDE 3.5 U 3.6 U 3.6 U 3.5 U 4.2 U 3.6 U 3.6 U 3.7 U
§NfilB!NK§XffiQN§\il\ 'EH1l~lilr ll'l ll:~;;gq ll!l:::ll@l~Wf ii l~l§l!\!~J;;@rn::r4@:µ.g;;; I %\?)Q;JH lliiI~l~ ua i@;Z\!'W
GAMMA-BHC (LINDANE) 1.8 U 40 U 1.8 U · 1.8 U 2.2 U 1.9 U 1.8 U 1.9 U
§~f¢ffi!il'2BPAN$f?H Hiil!ti i?!~i\l,'.tHHJi?P 1i~!,lll')Tlill?1?lHilli I1!%!ii\ :;•MtP M!IP
HEPTACHLOR 1.8 U 1.9 U 1.8 U 1.8 U 2.2 U 1.9 U 1.8 U 1.9 U
ReefAi:;fli!i;iR!l;g,q~r&E!I n i;n@1:1mr~1;r: IH i1l§IPlFHJ 41~!!1! n mnurMrnnn;i~@n rnm;wo1nrni@wa;l}!Pn I:ii;g!JI
METHOXYCHLOR 18 U . 28 18 U 18 U 22 U 19 U 18 U 19 U
fiR!;l@4!'i!fXA89PH4!?BiJ?filffl l Il!JllHMitill@Ai!!ti ;;ug;~g(g;;rnf~IWE\!· 1 '. 3§U ;;wrn;ah!\ll )2'.tf$;pt:rn:t; ; '.allµ ;;ff~y::o:
PCB-1260 (AROCHLOR 1260) 35 U 36 U 36 U 35 U 42 U 110 36 U 37 U
12 of 18
---- - --- - - - - ----- - -
Section 2
Soll Sampling Investigation
TABLE 2-2
SOIL SAMPLING SUMMARY -PESTICIDES AND PCBs
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
GP044SLA GP044SLB GP045SLA GP045SLB GP045SLC GP046SLA GP046SLB GP046SLC
CHEMICAL
PESTICIDES/PCB$
it#tJ©QPJRiRHPPPJUr
4,4'-DDE (P,P'-DDE)
1t4'.1!lllThm!e1RttPRT1
t:';•t?······ 1i@~l~;0a lii\l,!li§i!l!Biltlll ey;~jQ?;HiilNii@l§llMBHW:ill)@l@WBliiri l ~l$JVtl!illn @20/u;ti ll'@glii
3.9 UR 4.3 UR 3.9 UR 3.6 UR 3.6 UR 3.5 U 19 U
Hl/!lQ aoun amun ~!!~vi @fJ!l!Hli t~:~llJl:I HlH1!!il'!
ALDRIN 2U 2.2U 2U 1.8U 1.8U 1.8U 10U 9.7U
DIELDRIN 3.9 U 4.3 U 3.9 U 3.6 U 3.6 U 3.5 U 20 U 19 U
§N!llQ§!i!\\f.1£NlH(i%~B\M)J!l llW ;;}; il!MM!&!!!!B ': Ji?'tiUB :a!·t iti.B/i;b;:d:~ URI'Dfa'AiaDR#J{;ffi:a;ti: :'! ; \nl Otfa'; >;%wi@n
ENDOSULFAN II (BETA) 3.9 UR 4.3 UR 2.9 J 3.6 UR 3.6 UR 3.5 U 31 U 160 U
ENPWN H l ll~'-~l!l! Hil l#l~i!! :: ~l~D)i! l' ll~l§!ll 1·1.:rnrn@\l}pl ,I;;lH @!{(!Jlffl@l ll\?llQ • l!?W
ENDRIN ALDHYDE 60 U 140 U 31 3.6 U 3.6 U 3.5 U 20 U 190 U
€li!Rifilli!!S§Yffi9!l!§]l :: i!'.~im@! ;;;rn:~@IRJlill;: a;gµJ !HLl~l§@i i;%i~\§LQg;JlH::il~l%'YPf ;;; gii;r;r;:n; ; Higo
GAMMA-BHC (LINDANE) 2 U 2.2 U 2 U 1.8 U 1.8 U 1.8 U 10 U 1.5 J
§4MM!¥9HilPRt!A!llgg ii• H mmr· @:ti P i i::11~ ,Ni ll I l t g !iM l l!Hll~l~IQ i@tifi%11~ liWI ;li H !!~ Ui:tlll\ i19 !llii{{;' !N?}Yi
HEPTACHLOR 2 U 2.2 U 2 U 1.8 U 1.8 U 1.8 U 10 U 9.7 U
H~f1f4Qf!WRR gggx!R~ii! rn nrntML I :i:11 g1u I n :g;z o ;;: ;;;; ~ u ; urn: ;;1m:!ll: ;; ;n;Jrn;;p;;:rn:rnx ~ts v:;; ;; ;; l@'!iU: ; ; ; Jag,nn
20 U 60 U 20 U 18 U 18 U 18 U 170 97 U METHOXYCHLOR
{;L:w 11 ll~,3l9 iH!l~gW-! lll Mi~!l!l!!'1 lll g~.\ii il iI~tl,!llM fllll~~!Mr!l l![i1~00~HlH
2800 160 U 49 36 U 35 U 200 U 190 U B9§11i~JiB!ll~filij@Bli@iil!I
PCB-1260 (AROCHLOR 1260) 1100
13 of 18
------
CHEMICAL
PESJICIPES/PCBS
:#M!.!fR!?RfB;R!Ii?PP~I
4,4'-DDE (P,P'-DDE)
li'lli'fi!if@J\(B!BlfR!aNl: F
ALDRIN
DIELDRIN
§!'!.P@§\;/gg.,«N.\!If\\$t111>1rnmirn
ENDOSULFAN II (BETA)
ENdRiN '.
ENDRIN ALDHYDE
€t'!RB1til!S€Ym2tl§ iii!! 1!!1 !itilI n ;;;u,r
GAMMA-BHC (LINDANE)
@AMM6f,9!;lijQBR&N§Igi rnm
HEPTACHLOR
!:J§iII6§t!ggg:§R~~\9§ i!miWH
- - ---- -- - - --Seer/on 2
Soll Sampling InvestigaUon
TABLE 2-2
SOIL SAMPLING SUMMARY -PESTICIDES AND PCBs
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
GP047SLA GP047SLB GP048SLA GP048SLB GP048SLC GP049SLA GP049SLB GP049SLC
1111~1gI!llsf1l ;11~1z:2a: H :m~;~qg ,t,\$yt4aymif!a;1.uR.n , ,(!;s<µR iiiua;;
3.9 UR 3.7 UR 3.9 UR 3.7 UR 3.7 UR 3.5 UR 6 UR 4.2
:uiu $!irl9Wt unmtli!!P: 7?3at0:· .> ;~~§,Yi , "i't!i!;;; >>•·•;12
3.9 U
ifo;I;lll!gfl!~iih
3.9 UR
'\'\3-i9?ti:ffNJ
2.1 U
3.9 U 3.7 U 3.7 U 3.5 U 4 U 4.2 U ,· ;2,ua;,,, w,disua,niii;1,a.0Rii, 1,atiR,, ,, "'2ittlR ,,n,tzilu
3.9 UR 3.7 UR 3.7 UR 3.5 UR 5 UR 4.2 UR
; ~;g!!; ·+:i·3i1Q '. '. '. $;z q > ~l§t\Jl , WU '. gqp:
3.9 U 3.7 U 3.9 U 3.7 U 3.7 U 3.5 U 20 U 4.2 U
%WM%igili/f!tEtliti ?lZMi!lil Wa\$£!®! EI:llE~iZIQ~l!iidlitII~;WI!Jilliiff lfrl~/§JQl!I < ; ii IJj ;; ; ; ii z .uti
2 U 1.9 U 2 U 1.9 U 1.9 U 1.8 U 2.1 U 2.1 U
71iil'.il!:'l'k11lll0'' 'illl ElHll~;~Q ':iHl ti!!i!:/'!l'Bttt:l!~W!F' I@mu ~MP.I
2 U 1.9 U 1.9 U 1.9 U 1.8 U 2.1 U 2.1 U
I llHHli§ili Hii@JTI!l!IUWllJHl ,,,,._,·>-,&·su ·i;V,•,·•A e,oi--··-• ,:ws11-·-·,·····, ···9,:1··•·•u · ,··,;,, "2:19"
METHOXYCHLOR 20 U 19 U 20U 19U 19U 18U 21U 21U
i~glll .. EtR •fr'.397 ip,::: ;i,9fa;g:;;;; :i1PYi, 4:~!Ei
37 U 37 U 35 U . 320 42 U
gg~jjg~('5R2QflH@Rig§4ili "" liHfjllJJ i,WiP-w-····
PCB-1260 (AROCHLOR 1260) 39 U 37 U 39 U
14 of 18
-
----- ----- ---- - --- -
Section 2
Soll Sampling Investigation
TABLE 2-2
SOIL SAMPLING SUMMARY -PESTICIDES AND PCBs
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
GP0S0SLA GP0S0SLB GP051SLA GP051$LB GP051SLC GP052SLA GP052SLB GP053SLA
CHEMICAL
PEST!CIDES/PCBS
!fi!fl!Rl?!?Rffli@l!RWRJ !3-!5\l! iii iii ~1;~:Qlli ii; hi)g!JR! ~;$iJRil'.t!!1& URlTft~;e:o tr:v;,S;\iU; kiksua
4,4'-DDE (P ,P'-DDE) 3.5 U 4.8 U 4.2 UR 3.9 UR 4.5 UR 3.9 U c:__ 10
frifr(fP.ilfti!'!lR:IRmlJf ··· •.· ...
ALDRIN
.• £:.; .. , tJ~ieyjµ ill )h&UWdM•Hi<Hgrurn nnrn@;g;µ};t@4;SjVAiW@ ~;Y,\QWW11ii~if[Q%
2.5 U 2.1 U (4.1 2.3 U 2 U 2.9 U
DIELDRIN 4.2 U 3.9 U 4.5 U 3.9 U 5.7 U 4.5 U 1#1mg§l2£E~!1!&Heffi6IlrnHi1 i j d ,fg~(lli> nn3;g~uR,. c:2:~uR t " '2'0' u· ~su:r , :t3't/R
ENDOSULFAN II (BETA) 3.5 U 4.8 U 4.2 UR 3.9 UR 4.5 UR '--0.86 J 5.7 U 4.5 UR
!tM9Rlf!HiHt ......... ;;::: %~;5'!@H nt!~f!\,fil:E ;;;;ft;t&!n:;/\~~;t!i;:i;;id§Q ;;; ~;~!ii i;;ti!Zl!!;n • <ih'5•··u
ENDRIN ALDHYDE 3.5 U 4.8 U 7 U 3.9 U 4.5 U 3.9 U 5.7 U 4.5 U §NPR!MBQN§l ;'. ;:~;$!)., ;:4,ab ;.4,z!JJ ';;$9¥;%:•:4/§j)j ... ;.a;~Jlc .:.Lii~i!tfL'.; H!!l&!!i.1¥
GAMMA-BHC (LINDANE) 1.8 U 2.5 U 2.1 U 2 U 2.3 U 0.48 J 2.9 U 2.3 U
~MA%li@m9BPANEmlI!h .·····) tlP•·.··.·.·.~.·.··.··.··•·-2su•·•wr•·I ;b1ti,·; •. ··.··c .z tf .;j ..... f!@!i! .. ( L/@.U,ft.. C2&ft , , g~·!.1.)•
HEPTACHLOR 1.8 U 2.5 U 2.1 U 2 U 2.3 U 2 U 2.9 U 2.3 U H€BTeISfil£9B€BfilX!!¥§':;;;f!:;J ,c'., 0::x:.,1.a-:v:'',:\2;s;u :: :Lill \.'./'':2Qr\:;>2faui• , :2u< 1:z:g:::< ;,, ;vrv:
METHOXYCHLOR 18 U 25 U 21 U 20 U 23 U 20 U 29 U 23 U
R£§t~R§~feig99ftM9ff!1M§1i!ifi >,;+ hd?~!JWlH Kii!!lilti iMKlM~¥.IHL i@ggrn; ." 145:U! n }}l!t!!rnn ...... > !l't!Jf%i i45U
PCB-1260 (AROCHLOR 1260) 35 U 48 U . 78 39 U 45 U 39 U 57 U 45 U
15 of 18
-------------------
GP053SLB
CHEMICAL
PESTICIDES/PC BS
./!11!~i?IP1Rlf@i?@l iii
4,4'-DDE
TABLE 2-2
SOIL SAMPLING SUMMARY -PESTICIDES AND PCBs
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
GP053SLC GP054SLA GP054SLB GP054SLC GP055SLA GP055SLB
Section 2
Soll Sampling Investigation
GP056SLA
DIELDRIN 18 U 3.9 U 4 U 3.4 U 3.4 U
1Bili@@§\1!Rll~!flil{6~Jll61ll rnrn;;;:1 ............ w.1w. :;::.•: <?J:L••·•• ••.•··.··············•··1 ivgny +lHWP.R,rn11:Iw11~1p .. .
ENDOSULFAN II (BETA) 4.8 UR 3.7 UR 18 U 3.9 U 3.7 U 4 UR 3.4 UR
ENDRINH ' '.ViP"''''t·w;;v,; t# . l~H&Y ;; !@:7:!J'.f:'. 11: 'J'~!y:1; :;;1111!\W;~; ?it§ ;,; 14Y.tI1iii:liil:@.\l!liiilWiHN :mm!W
ENDRIN ALDHYDE 4.8 U 3.7 U 18 U 3.9 U 3.7 U 4 U 3.4 U 3.4 U
eNPBlN KE;'QlQNSllldjbj;;j@WHU :rnm nn ! ;,; !!ie\1#. i $}7'1.l1J y ;es; tS .(!F' ;? l''-;3i9JJ '.7', I@J:ti!l! Il it!MM/!i!i!l! Mll@JilA$ij!;\!l4iitrnrn;rn?l4lPPl
GAMMA-BHC (LINDANE) 2.5 U 1.9 U 9.1 U 2 U 1.9 U 2 U 1.8 U 1.8 U
l?4MMAft;ljitOROAf/$J2;j;))/jJL ; ; ; ;g;J$;p ~ i Ftii.HtJi@i@Ht2'-ffi!'P p)W42!t.HW ;;t;sru I ; i!lbQJ/)Wi;~11ilt:iiNf@fff1!a}l;1f
HEPTACHLOR 2.5 U 1.9 U 4.8 J 2 U 1.9 U 2 U 1.8 U 1.8 U
BFgT~J1!1Li@fll§Pl:>*'9.§! !:11rr11t i 1nrn i 11 r ?cl§ µ w 1 1 ~1~1p1;;;1r1n~ ;Mm&;; 1 w 1fr111%H' M11 m~ \i/ g 1!!:: trnirn;a;§r!;fmmnrn 11~ µ
METHOXYCHLOR 25 U 19 U -91 U 20 U 19 U 20 U 18 U 18 U
RP!¾Jtqff(1/8Qeflll!iiB1~eift: ···•·•·•·•·•·•·•<i·· P!&EUN I ;; ~7-;!)gq;;;;;;!§!l;l;{!;;n ;;;;;~9,;g;; ;; 2tQ·· ··············•\40 u Ijff Ufa;m !)H);/;I ;$4!·t
PCB-1260 (AROCHLOR 1260) 48 U 37 U 180 U 39 U 37 U 40 U 34 U 34 U
16 of 18
-------------------
CHEMICAL
PESTICIDES/PCB$
\11lis!lH!?filffl1Rtt!?'l1Pl
4,4'-DDE (P,P'-DDE)
lH!i(lPQI{fi;Rl@i@nim
ALDRIN
GP201SLA
TABLE 2-2
SOIL SAMPLING SUMMARY -PESTICIDES AND PCBs
GEORGIA-PACIFIC SITE
GP201SLA
(Duplicate)
PLYMOUTH, NORTH CAROLINA
GP202SLA GP202SLA
(Resample)
GP203SLA GP204SLA GP205SLA
Section 2
Soll Sampllng Investigation
GP206SLA
3_6 u ·:'.m~;:~ ~~~ ~1~:~N ',!;~~ i !;;~;~~ .E~;,g ii:i:~1~121
If?{?:iiil Mi llii~ddl IW MH@lritirnm@~#iKI ff§PIJIQ/j ffWltl\jW) l}l)j§lt;;M lUH)il4;9W!;
1.9U 1.8U 1.8U 1.9U 1.9U 1.8U 1.9U 2U
ENDRIN ALDHYDE 3.6 U 3.6 U 3.4 U 3.7 U 3.7 U 3.5 U 3.7 U 3.8 U
i;Nci!3.lf,j(l5§YlliQN_§lW i .ES i ;faifri ·································•· / , jiff(§ !i!il nifol@l§ \Mtrn M Iil~llt QIIi@lrn:~;zmg 1 i fa, ;~n;;.Q 1F/1!!$J§IJJt WI1 ;$if\!:.!; f H ·3:a u·. GAMMA-BHC (LINDANE) 1.9 U 1.8 U 1.8 U • 15 J 1.9 U 1.8 U 1.9 U 2 U
@AMMM@Hk9EQAN§/ii ;});; Jl!! UH E1% tti{:l] !!!H IJtrnrt!!lliMI ; 'H!-~Rf!lff 'EM~P ! i )'i;it8tHi :mmw; ;
HEPTACHLOR 1.9 U 1.8 U 1.8 U 1.9 U 1.9 U 1.8 U 1.9 U 2 U
METHOXYCHLOR
eqiil:1i@~JARRGH~Q!:}hlg§~lJWWIW
PCB-1260 (AROCHLOR 1260)
19 UJ 18 UJ
?~i!iiff lHMilil®JP.WIW
36 U 36 U
18 UJ 19 U 19 UJ 18 UJ 19 UJ 20 UJ
naM!ll IiWHHg't 4rn@rnrn ;!$:p m Mtrnm J)~!i!!i/rntn i@@BlLY l I lli[E~ Pi
37 U 37 U 35 U 37 U 38 U 34 U
17 of 18
-------------------
GP207SLA
CHEMICAL
PESTICIPES/PCBS
METHOXYCHLOR
!:l@!'¾Jg~ l\'¥R@@li!W@R@?§if1
PCB-1260 (AROCHLOR 1260) 34 U
TABLE 2-2
SOIL SAMPLING SUMMARY -PESTICIDES AND PCBs
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
GP20BSLA GP209SLA GP210SLA GP211SLA GP212SLA
18 UJ 17 UJ 20 UJ 18 UJ
:'II\35:':IJ/:':':' {ttt/gj!HJ: t::':':':':'t':t\39iUt,:II'''''''''W·C··· 3!%U .-:-:-:❖:❖:-:,:-:-:-:-:-:-:-:❖:❖·-;-:,:-:-:-:-:-:.:-:-:-:-:-:-:-:-.•.·.·.·-·-·:"
35 U 35 U 34 U 39 U 34 U
GP213SLA
Section 2
Soll Sampling Investigation
GP214SLA
18 UJ 17 UJ
M.U•••Fi @EV
34 U 34 U
18 of 18
-------- ----S"'1on 2
son Sampling ttwfftigatJon
CHEMICAL
PIOXINS/EIJRANS
1di~i~M@&i!l!!Wfff,,QljJ;Q~@i~~lQX!EF; L ; .
1,2,3,4,6, 7,8-HEPTACHLORODIBENZOFURAN i~!~ii;i!i!i€Al!rif !q'.jtggjjj!!§~!lli/#.ij
1,2,3,4, 7 ,8-HEXACHLORODIBENZODIOXIN
iwi,l!ltl~ii@&A%\t@l¢!\lij/oo.;;ilifm m
GP001SLA
TABLE 2-3
SOIL SAMPLING SUMMARY· DIOXINS AND FURANS
GEORGIA-PACIFIC SITE
GP001SLB
(Duplicate)
PLYMOUTH, NORTH CAROLINA
GP002SLA GP002SLB GP003SLA GP003SLB GP004SLA GP004SLB
::}:~:;:::t2trtMt ··--.·-·-·-·--,.~r::::/:::~A ------:,,,,,L~,,,,,,,:::::,,,htfa. ----❖-·' ----~,=~d~r ;;;;;;:\:\:;:;;;_;:::::/:Nl(t::::.,:{,:LffEY?NAr:z::•:•~:r:=:=•Et::::m>:?t:?•<<= :::::;;;;<5}~
NA : j·· :dlii
NA ,14 NA ?)iii¥ ••t•·,·, ··M,s@r:::w· WE!'!/\ NA NA 27 !:/,NI tiniil .·.·.·········;···:·m;;arnm ............. .
NA NA 4.8 U NA NA NA 4.2 J NA w r··: trw;,: wa&+ .,. ; MA :rnmr.. t<< NA > '.~:•: 1¥x< r ;;gi;
1,2,3,6,7,8-HEXACHLORODIBENZODIOXIN NA NA 3.6 J NA NA NA· 12 NA
:i@?l~iil®~PBt9l!!li\iijiiii~&iimm1nrn·nirnm ·.: :.• ::;:; .; . .zwc;;: ·•;:;; :1 :wii vi WihN@nnw:n#.if · • • >·m· +:++6w·m:"'A :··· ,·•·#u " ~'"''+-<+,/!<A
1,2,3,7,8,9-HEXACHLORODIBENZODIOXIN NA NA 4.8 U NA NA NA 6.8 NA :~q;~~!.A~~H.~D~9P!§~#:)~~1IiliMJVi@1IIF:l :::::;:::;:::0:;: :ijA}-:•:=ct+:::~=::z,::Nk=r=:::::,:;:=:::=:':':::::=:::,:=:::=:,:;fff'Oti('.=f=:w::~=•=~:=wnA:,:=:,:0:g:=:,=,,=,:::::;:::7:ffiAfF'F}H?tWI&g~:r:=:=:}'?\:X:~':-;,~~:j)'.~?F:':::97:(Nt?:t::.:
1,2,3,7,8-PENTACHLORODIBENZODIOXIN NA NA 4.8 U NA NA NA 4.8 U NA !i;~!ti;;~ffl;,i;q'.j(QRQp(il§ijjggm i!!i:i HMlt;!WJ!llMIV NA ii:.~ µ ' I itt1 11/,i;Yn·;p llji l!f4 '' '" '1E!!li~ll/:lI!H!1\iliji
2,3,4,6,7,8-HEXACHLORODIBENZOFURAN NA NA 4.8 U NA. NA NA· 4.8 U NA
2,3,7,8-TETRACHLORODIBENZODIOXIN NA NA 1.9 U NA NA NA 1.9 U NA
ifat%w,1eff~cfilU:\fiooiiliifgo/i-'gE@WfolMI .;.·.·.·c·····.•:; ":i:!iii Hfrdi~fo·#A ·•·•··•·•·••·•·•·•·••·••;•)ttA'il:;; ·>:.iik .···.··;;, .. ··:.);1.t;ZF:E;;;m> ............. -:o,:i)i·,1:,1 ......... NAi;)
HEPTACHLORODIBENZODIOXIN (TOTAL) NA NA 240 J NA NA NA 510 J NA
B$t\i19ilto/%&pi[~Nii:i~i)AAii#i:\f&;H!iliMIFMlH ; fl 'f"/{ '.'." ; :nxmt : ; < efii;t;, ;;~; m > ., ff A >ts:; Rli4t Yi ;E;Jt~itt!d;; ; [i,i/(f/
HEXACHLORODIBENZODIOXIN (TOTAL) NA NA . 31 J NA NA NA 110 J NA /li~gi!i@i&i&i~/wz§iffit.li!rr&f!(i\t )<.;;:;/ ;)ff . · : i'lfi ~ o "'~~., : ,Ii,,;; '.: .... '..: ·.:••;TJlM!. > ; /·. W5 i frifr1W'isin!mi:nlrn/'!5W TtffV~;;wng; n ii#
OCTACHLORODIBENZODIOXIN 2200 J NA NA 2600 NA
PENTACHLORODIBENZODIOXIN (TOTAL) NA NA 4UJ NA NA NA 28J· NA
' ' .... ~.. .•.•.•.•.•.•.•.•.•.•.;, ............... . il!Wf4¢@@llfilQi!'igig§@!¾&1!9;t~Ht , · ••··•·• :pt .. ·qg ;. •··•·1!1(···. ' ;NA]; l#iilii!:@ : ';w,\ :•: ~ ·J!A/k :\ /MA ....... . ioWJ:Tt;'·:w;;:
TEO (TOXIC EQUIV. VALUE, FROM I-TEF/89) NA NA 3.9 J NA NA NA 7,7 NA
r!tiM\@ji@Rqpiiji:f~6Jo\ilRrro'.t.M)M!iMl!)(ffH 3?%% l%l1iM;M#EMWUNffA ii!ifatiJi\h@il'iAd ··•?;p·•··•·;u;.:·c;7 :ti Wi Wbl/ii;i:lefc\t.)i#dffhiifA#,
TETRACHLORODIBENZOFURAN (TOTAL) NA NA 0.16 J NA NA NA 0.3 J . NA
Pata Qualifiers;
U = Material was analyzed but not detected. The number is the minimum quantltatlon limit
R = QC Indicates that data is unusable.
J = Estimated value. N = Presumptive evidence of presence of material
Concentrations reported in ng/kg. 1 of 18
-
_, -_, ---
CHEMICAL
PIOXINS/EURANS
.................... , .......................................... . ~l?A/f;~mw®etA9llt◊RQQl!l!;~!Ql\!J'l
-_, --; --
GPOOSSLA
TABLE 2-3
SOIL SAMPLING SUMMARY -DIOXINS AND FURANS
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
GPOOSSLB GP006SLA GP006SLB GP007SLA GP007SLA
(Oupllcate)
GP007SLB
-· -Section 2
Soll Samplfns, Investigation
GP007SLB
(Duplicate)
~f~=NN=iinM=rn:nnJi~:n:ttii,:ti:::::123i~~t,~,}=~= =:::=::::/::x:=rJX ,;,;;;:;t;;::);;;;At;taji;§,; :rrnn:nw;::1:11t.:;~::~~:~::r::n~~~:n~~•;::Jtx: iH@iH:@@itNAtnn
1,2,3,4,6,7,8-HEPTACHLORODIBENZOFURAN NA NA , 12 NA 10 ·9.5 NA NA
1~:~1~!Vi~i~lHg!ff¥!i1l!iqtii!i!l~W%l:il%\UI w >> .. •·•· .. •·><·•·•·•·•· .. •••·•·•·•·•··· .. NA · ..• · •••• ; N!l········•.·· · ,. ··········rn;¥Hiu··············· < f;~·••iii ::t'••·~ ··········•· ,.,NA •·
1,2,3,4, 7,8-HEXACHLORODIBENZODIOXIN
%ifaiMi:@ii€x4bflilooooiiilmzoe&i#til t ;
1,2,3,6, 7,8-HEXACHLORODIBENZODIOXIN
.·.•.·.·.·.·.·.-.·.·.-❖:•·······❖:~;-:-·-·.·.-.·.·.·-·.-.·.·.·.·.·.·.·.·.·-·.·-:❖:❖:<❖:c❖:-:❖:❖: .......... ·-·· ••• ···············•:~
t~@!i'i?m±!EXAPl#~QRQP!~lilllQfQ!lf.\!'f:FKt• '
1,2,3, 7 ,8.9-HEXACHLORODIBENZODIOXIN
i~l?;tlaloiB~Ei#IQ'&/g&lt6#flwJ'l; filI
1,2,3, 7 ,8-PENT ACHLORODIBENZODIOXIN
.,:-:=:-::::,:_::::: •. ,.; ••• :., •• ,;,,:w,,;;;.,.;::;,:,:_:;::=:=:=:::·:.=:=.=::;.=.--.·:>.=::<;_:_:_:_:_:_:,:_:_;::.:_;_:_: ... : .. :=·'·=······-•·w•• !)g\@Zi!W/§t·!J)'iQH\\QRQQ!@IM?QfQRA!f!
2,3,4,6, 7,8-HEXACHLORODIBENZOFURAN
?1~111@;iwi~m\@ffiiifill2i\lmiitl1!!mm
NA 3 J NA 4. 7 U 4.8 U NA NA
, u;;;; ••••••• ;; <•¥iu ···•'E ?tl«t 1il@i[JJlfit•rntnm~m;; Ml INAf ·······, ffAAPf NA NA .'6.7 . NA '-~6 :.'_7_2 NA NA ..• ::z;·w;;"· :;g;m; lilt\4\li:/\••··••D:•LNA'. :nrntiMWO :k\#!iftiPiH•MWi:i·'••··· ,fr)% I
NA NA 8.8 NA 18 21 NA NA ;.. ,,·.·.·. , :w,vr .t:-)A; /i!W!f HiMNAHMM Wli:'iiIDTIWHi:!MliiiJ :tli:li®X ''' 'SM¥
NA NA 4.7 U NA 4.7 U 4.8 U NA NA
.-.•-•.•-·-·.·-·-·f'@tN.At:~~~~:~:~._-:·:~::'.:~::::?:':~1~~3\uu:r:~fdt~:iNi:W:~::~U:!~:~:}\#~:411;:tl!:t~MH~::W~@}fi.ftfr:!fffitH!:t~Af::ttt:dt~::~:::}JA\trt'
NA 4. 7 U NA 4. 7 U 4.8 U NA NA
, HHHN&I·· : :'.litJil.. ..NN ,rn,:iu grnrnno············•um; •·::::Lll¼'t
2,3,7,8-TETRACHLORODIBENZODIOXIN NA NA 1.9 U NA 1.9 U 1.9 U NA NA
2;&iiMtli'lW@B®moifiiiejlgjjKljjwf,:HE(k.•···••.····· ····~····~•"<••··· t·AA+•tH ),{•····•·w1·•· ···•·.x··•xfriii~Xi.••· ,t,:dr)¼t:; ... -,,., .. HtJM~fo~tHJrnfH1#fa&l:#@ftfH%MH@&@WHMTN)@Mi&Wt@
NA NA 650 J 120 J NA NA
HEXACHLORODIBENZODIOXIN (TOTAL) NA NA 98 J NA 140 J NA NA
ii™i!iB®ifi66M@t{;jtj)\Wllrr¢1#,tfriii;i n;fa@in •·•·•·•·• i\L,i;,;> •·•·•·•·•·•·•·•·•·•Nk·•·•·•·•·•·•·····•·•· i{§!H4Jtfai i:!h(~i; lHWiih~w j/iJiil;th1A YJH@NifaA ii ll tliJWlil
OCTACHLORODIBENZODIOXIN 6000 NA 9600 1100 NA NA
PENTACHLORODIBENZODIOXIN (TOTAL) NA NA 12 UJ NA . 20 J . 19 J NA NA
iliii'#@iNii;oRoPiilWU&iillRXiii\lffi'f,ffafWlH ;;.sw ....... ,,,...... t!AH? l}FAfAMW ;;;zii¥i:iiii , .. Jwl tL@Wllii\%MM{tffFK~W@iMV•Mii¾ tl i•Aiw'ii
TEQ (TOXIC EQUIV. VALUE, FROM I-TEF/89) NA NA .10 NA 15 13 NA NA fgl@§flilooi!i~gq§@~Jiiiffqjggj l H l l l!\¼li :,Nil)D kks12 tD /j>';/t#iiL t :;t:J;;W ;; i t tM DJ'. ,M@~ /An t NA!%
TETRACHLORODIBENZOFURAN (TOTAL) NA NA p.16 J NA p,26 J 0.21 J NA NA
2 of 18
-
- - --
CHEMICAL
QIOXINSIFLJRANS
-· -·--· -_,_ -
GP008SLA
TABLE 2-3
SOIL SAMPLING SUMMARY -DIOXINS AND FURANS
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
GPOOBSLB GP009SLA GP009SLB GP010SLA GP010SLB
---
GP011SLA
-· -Section 2
Soll Samp/11111 Investigation
GP012SLA
••rm ·;;; ;;,if.IA'· i;jiim •ttt iiiiAN•·•······•·•·•·•·•· i N4l ~ h
1,2,3,4,6,7,8-HEPTACHLORODIBENZOFURAN 36 NA NA . ... NA ....•... ,, ........ ~.8 U... ..~.'.",..... NA 4.7 U
¥WlJ•~q~ !l!HilflIAcfltoROOi!le/;lroiiuAAN t .. •.•·.•·.•·.•·.·••·4·•·.:.ll.····.•·.u .• ·.··. , .• ??+ i,wf •.•·•.•·.•··•.•··.•.•.·.·•.•·····•.•·•.•····••.•·.::.· .. ••.•··"'··.• .. :.:: ... ·• .. NA .. ·.·.· .. · .. ·· .. ·.•.·. · .. •·.•.•.•.•.•.·.•.·.•.·.• ... '.•.-.·•.•.·.·.· .. ·.··.·.•."'.·.·.·.•,'.· .. A ... \~ ... ··.•.·.· .. u.·.· .. · .. ··.·.·.·•.• .. ·• .. ·•.·.·.•. ;.:.;£NA:..... •·.l.••.•·················':'·•····•·., .•. •.•.····m· •. • .. •. ·.•:.t.··.•· ...... ····· ... AliWli:l j ··•"''-···•···"·"·•·i•.·• ....... ·.···•········•······'-············•·············-'·································•·············•····..:::•· ... . .. .... .... . . . . --.. ... ... . . . . .. .
1,2,3,4,7,8-HEXACHLORODIBENZODIOXIN . 4.8 J NA NA 4.8 U NA NA 4.7 U
'i4i~iiil%iii8iili'\¢l@liiRllPi~@:ii\l!&ii&llh@ Y -F ; :i;J;;;;;;;;;;; ; wii+ ··-· ·; im'i Hilll•lW-ii~iiiilff E l!iifli\HNW l Wl:IA@H ilfii ifriiu+
1,2,3,6,7,8-HEXACHLORODIBENZODIOXIN 12 NA NA '6.6 J NA NA 4.7 U MiWi~#iii+l~il¼l.;Hif$R9p1iifill~g~!j n ti :: ' )L #&lt:n;: t!mi •·•·<•·•·•·r••·· i·•·•·Nili ......... ❖•❖.• ••• ❖ ••a~W;vB .. H&/H( .. I rnw;n ; ; ;;/foil
1,2,3,7,8,9-HEXACHLORODIBENZODIOXIN 1D NA NA NA (12 NA NA 4.7 U
l@?i?!iil~B§El\9ilgiliiifill?Qfmrn; ....... ; ..... ;;.;. ;;;; wr ~ra1rn1rnm NA?·· ,, Nii•••••••• "•;;: ~ ;;;; ;; iiiiia uii: rn •·•· ;NA'r ;.. •Gf;IAmw ;: r 11~wu1;
1,2,3,7,8-PENTACHLORODIBENZODIOXIN 4.8 U NA NA NA 4.8 U NA NA 4.7 U i=:=:ia=:z:a=¥ENTAGHtOROD\8£#ZOF.URtJi~=:{,:,:,~ t~t:?t::n:::::;1r:Gt:;;:?{:::r;:n~~intt:t4mrrn:r:&f;:~r~:~;::~}~:~::z:;::;:: ;::NA:;;:;::;;:;~~;~::;:;::~::~:~::~:~::::a@{;;::::::::~::;;rtf:r:::;:ti~faLUR:;:;::;: :/:/):NA:?/<-~ntn:rn:NArwfnw·~dhifadrti:i· : .. .i ... i •... i ...... , ..•••..•.... :. ···•·······'······~• .. ·. • ..... · .. · .. ·.·.·.·.·.·.·•. : .......... ·.·.·•·················•;::•:::: .. . . . . . . . . . . . . . . . . . . • •. . . . . ,. ' .• .• - -• . . .. . . • . . . . . . . .
2,3,4,6,7,8-HEXACHLORODIBENZOFURAN 4.8 U NA NA NA 4.8 U NA NA 4.7 U
2,3,7,8-TETRACHLORODIBENZODIOXIN 1.9 U NA NA NA 1.9 U NA NA 1.9 U
ii~/itilU'iff/¼¢A[bifodiBE.NZPBlIBMIHWM rm l•m· w·vt ... i .. )isJui•iiifaL •·IJAw ;. <,C• t"Mi ·••j)c)ijl,{ ·"' v>·.y)¥·1t·>:X"'·'•N!\t }'.. ·••; • Ni'/faU mntkilillBH
HEPTACHLORODIBENZODIOXIN (TOTAL) 72D J NA NA NA . 810 J NA NA '91 J figgf~9@iggl;ii'\@!j/;g95p84~l!QI-/wl! }Y :n: !AA' ·····•·fW ; '. : ; NA;C •rnw;w;~qJ .... ................ : :)fjl/7
HEXACHLORODIBENZODIOXIN , 76 J
OCTACHLORODIBENZODIOXIN NA 17D0D J NA ¢§t.l\£B\i2@jj!iE@¢f~ Ji: + @t;E;;;;r· ..................... ,_. ••• iiA ')!§&A ii MW@#iii ii iN5fa%
PENTACHLORODIBENZODIOXIN (TOTAL) 12 UJ NA NA NA 6.2 UJ NA NA 4.7 UJ ei!~r.?i.?iilffi.9gqgjijgjg§fil)fMHlmif.@lM!ff! •••••• •:iisiiiJLi••:·. :NA ..... , iiiA ·.·.·.·····'·pp(NK +,Hi•••w •• 3 JiA/3•3·' ·f:iAyF •. , ••Abililtil
TEO (TOXIC EQUIV. VALUE, FROM I-TEF/89) 13 NA NA NA ,23 J NA NA ·1.6
rlifill\¢Rlioowi.1g2!li@Ni!'tt§i'AMl!lil c;;;x ;4foJ:P,nt NAFl • AfA YTIFW.:•· rninm;m~IW ; Jwrnni ••·••·•i!# ....... ,2n;n\ur
TETRACHLORODIBENZOFURAN (TOTAL) 9.1 UJ NA NA NA 3 UJ NA NA 1.9 UJ
3 of 18
-
----
CHEMICAL
PIOXINS/EURANS
_, ---· ---
GP013SLA
TABLE 2-3
SOIL SAMPLING SUMMARY -DIOXINS AND FURANS
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
GP013SLB GP015SLA GP015SLB GP016SLA GP016SLB
--
GP017SLA
-· -Sactlon 2
Soil Sampllng lnve$tlgatlon
GP017SLA
(Duplicate)
l,~:~;{@fiilifffi@'f;g!jg§R§pj~g~iRll!Nl ....••••.• NA•······. •< I!Mliii iiio~;j .·.·>•NAU<L,.·.·.•.·.·.·············•59b·••·····•·· ./·•······· !Mi ti ii it?ffeff ;j\ !@It
1,2,3,4,6,7,8-HEPTACHLORODIBENZOFURAN NA NA 230 NA <91 NA 310 J 280 J ~Jifa/,\jiiti'%~etXoJJtB.®Pi~f:iiqjjoAA# M!WiWli x xs~ fr w fNNini •·•·•·• ,15 :···........ .. <,NNw k'· r 1,;2 p:;n ;NArnfrmm t·····•····11U <t·····•· 2l! :::
1,2,3,4,7,8-HEXACHLORODIBENZODIOXIN NA NA 12 NA 4.5 U NA ·14 J 16 J
j;ji)~i~W)~!B~¢tilioi@ip!~lffiz9ifµ/½NH ··········;:; iNA \Ii¼' c+••·•·•·•·•·• iefi-i•+ Ni\hh ···•.··· ,K~'.\JEYWttNA) ··•·+ 1~Z'.Z;; T~li
1,2,3,6,7,8-HEXACHLORODIBENZODIOXIN NA NA •50 NA '31 J NA 52 J 62 J
1fa:~l~Hl~~&4l%t&ili;ilJ!i\eyjzqj~~& .................. , .. ,.,; 'l!IK2 illf:t\tL i~i;;;; Ni ;;; ... ; 1,JiJ:;;;; ,NA"v·v + , fa y·; '·' iii ~
1,2,3,7,8,9-HEXACHLORODIBENZODIOXIN NA NA . 24 NA ,7.7 J NA •·30 40
i@!ili@illB~xA4!M9ilPP!i'lfillt§)Hifil;/HMi .. <:· ·;;+, ·,•.•, iid,w{ ;; ; ; &A:r;;;; w )faHDlF' 'NA'.'7? 2 ;mu;;,·.•·-;; H@ffH!!!!!HiflH\llil!B!Iiitl: ;~;~;iiiR
1,2,3,7,8-PENTACHLORODIBENZODIOXIN NA NA 4.9 NA . 4.5 U NA 9.7 '13
i:~i~ff·~ie~lliii/,:iw@iiglli~Rll~ :: l !ff x•·•·•·•·•·• ················ mu we; ;; •·•·•·?••····•·•·•·~ ilµfr < 1'4''. @li µ '. '. nM ;:;:::::;mmw;iiun w ; @iA!iin
2,3,4,6,7,8-HEXACHLORODIBENZOFURAN NA NA _ 7.5 NA 4.5 U NA 120 J 19 J
z~i4W$!PWW#&l@lil'9Piiiiffiio#tii{Nili •-.~·,;····· iH!/M/%j'@ • ii\ifa.)iff;i HiNifa;iiUHii!iiis'IJ@''HifaNNU@%Y ·••)tt;f/'.> << /£¥VF
2,3,7,8-TETRACHLORODIBENZODIOXIN NA NA 1.8 U NA 1.8 U NA 3.5 U '1.1 J
!!4ltl4\i:l@!m¢.B~RRQQ!\i§'!t§R~!diWH ... '. ... ,'.> • :wvc . ]JikbW!t T/4,B~J/B•;aNAq;;;• ; 4:4t£::•:n. ;•&A•;•,;:;; :.::.:~¥ir.:.7.:-.::)i9:
HEPTACHLORODIBENZODIOXIN (TOTAL) NA NA '2100 J NA J300 J NA :2700 J 2500 J
ili!lil1A2i®lliii§&liig~ill½filr\$/i'Mllrn. tNA·+ i. i iFiAAiFi .:.·.:paJ x ; 1% ;;;;;; ;,f,1/i,Vii •~11v11wtl@!Wt•rnu tfoo:i+
HEXACHLORODIBENZODIOXIN (TOTAL) NA NA '.320 J NA '100 J NA ·410 J ·520 J
f!gli&\;l(!Mj~gg\~W,#i~!T!?I.®!li ·•·•·· ::C:7i7n -... i,c;i'jA.;· ........... iiliiH!Kil l l!'#WiJWil i!Af'#.\1;:···'; !1imt~i!f:\i·•<·• •i:!.i#CJ;T; Bali;;@;>: sww;
OCTACHLORODIBENZODIOXIN NA NA , 14000 NA (4400 NA ,17000 J 12000
§¢fe,gjggjjlw.\l!i:1!g§/@~l ·················•········· /NA ri +NA:,, HH~ii11 ; i Nfi ··························• ~mn id ~f@i¥ i¥41n ,; tml:t
PENTACHLORODIBENZODIOXIN (TOTAL) NA NA 37 J NA 23 J NA '87 J 'B1 J
WiffKcAfikiiioNBelUoJ®iiiifiirofAi¥ .·•····•·•·· ;: :;:.;••· ,,_ ;;rnJ#Arnrnr ii ;NA';; ;;;· HisiiiiiM+ :nNA,±+:J ,<32,oJ;w;s :riMir;22c;:;t¥M:X;; ~titJA
TEQ (TOXIC EQUIV. VALUE, FROM 1-TEF/89) NA NA 41 J NA ·15 J NA 59 J :f50 J
rirr/½¢figgsgp!~~QR\9XWITQT6MH @··•· iim·· M.il'Jf Nkil"_ ii1i~Li!iiiiiiii !f¾:3 ;,'.'. i~iiiiiiiiiifiN1iiM
TETRACHLORODIBENZOFURAN (TOTAL) NA NA 49 J NA 0.47 J NA 260 J ?BO J
4 of 18
-
---------- -
Section 2
Soll Sampling /nve$Ugation
CHEMICAL
PIOXINS/EURANS
1,2,3,4,6,7,8-HEPTACHLORODIBENZOFURAN
i@iiitii:ll;l!liitit~!lil?@iiiigg~llR4&1iH
1,2,3,4,7,8-HEXACHLORODIBENZODl_oX.I.N.
it@Miill±itM¢!:MW@itliillmt$l%ll½Nl
GP017SLB
TABLE 2-3
SOIL SAMPLING SUMMARY -DIOXINS AND FURANS
GEORGIA-PACIFIC SITE
GP017SLB
(Duplicate}
PLYMOUTH, NORTH CAROLINA
GP01BSLA GP018SLA
(Duplicate)
GP019SLA GP019SLB GP020SLA GP020SLB
NA NA 15 15 72 J NA 11 4.7 U
t•l4t;••·• ...... , ..... ~rn; 4WP;:L, )li5D •·•·•·•·•·•·•·•·•·•···•·•·•···•·•·M!Uc;;/'.i Nl\;(i;J;•d. 4't•••U<FVi ii~\i@i
NA ~ 4.7U 4.5U 5.6U NA 4.8U 43U
k !AA E'' ff\&g{: i!iiiQifai' AKO ~Ji\/;;; ?Ne/ #,~w.e: •w !ftVt
1,2,3,6,7,8-HEXACHLORODIBENZODIOXIN NA NA 6.9 ·7.3 ··30 J NA 15.4 4.7 U i!ill?l~M~ti~~@mqil//iil$J~9~ji@tH ····•%%{;mm; ·••wn >·•·•·•·•·•·• NAY/hr trn!iliM@fHjiH jiiifo .·.·.•.·.·.·.·.·.;·. ·&2iµJ;;;;;;;;;NP£;··· cF ;iiiiJL:;;: \4EciF
1,2,3,7,8,9-HEXACHLORODIBENZODIOXIN NA NA 4.7 U 4.5 U •.13 NA 4.8 J 4.7 U 1:~:~liili)~iti~~(;QflQJ;ii!l§j?Qf~i1llii ll!Mii@:;; i% /;iA; A,tQ;. . .. ;.u:+5:. i2itiiif NA ; ;;;i;au; ?Pti?
1,2,3,7,8-PENTACHLORODIBENZODIOXIN NA NA 4.7 U 4.5 U 5.2 U NA 4.8 U 4.7 U ti2iiiiiiaii?€1:rrf:cagQ!lop1~Nio1iiiJiNI ; ;;;j,/4;{; Hi%!>••;;;; HiAAt•tnn A;;lUWAM 4)5!0\kM/rn &;!UR nifr;NA ;;: 7 :uraux:• ·•·ii 4)fllirn
2,3,4,6,7,8-HEXACHLORODIBENZOFURAN NA NA 4.7 U 4.5 U '.3.2 J NA 4.8 U 4.7 U
?i~i1lt;~;e~Hti\1™@m22,~~fi~§!!~Irn •·•···•••·••·••••tM n llti ;wrn ;;; rn;i liiiiiii 1;~ !JIH!idi ~gffilii ~r i//·)M••·o ···•·•·•·•·•·,!t)t, \.
2,3,7,8-TETRACHLORODIBENZODIOXIN NA NA 1.9 U 1.8 U 0.54 J NA 1.9 U 1.9 U ~@rl~if!rri!A!:\ti!l@@li:iillimiifi!f:gn • trnrnnn ff:@ ················•·NA U>•itilWJ l/fliAWii••H •ti iiiij!J}l \.•.••+•·•·JAA......... • '%FD @MJ:
HEPTACHLORODIBENZODIOXIN [TOTAL)
HgJifA§fliI5fil56m!&toli!Ji!Amn@f,m\E• •·•·•·•. •.· ..
NA NA -J =J ~J NA :=J =J.
i<iA F!WMH1 l®td!i@!t HY@hdb\ l# Jit;/Mi ii;!ii.;y •1\ fhli "¼)iljj;jhil l#i# cwn• i tli OJ
HEXACHLORODIBENZODIOXIN NA 51 J '.240 J NA '59 J
OCTACHLORODIBENZODIOXIN '.1600 1600 J 15300 NA • 11000 19000
§QfAciilloirooiii€!lib!l0@:iil¥ • ••+ifr n Jtii:ihii:i ii)® f/Ah••···· ;;;;p;c; ·: •• ;>; •2~{• <:Jc. ;: ~4. i,(
PENTACHLORODIBENZODIOXIN [TOTAL) NA NA 7.6 UJ 7.5 UJ 18 UJ NA li:3 UJ 4.7 UJ
Rfill.tA¢&1@i@Rm~Nt.§@~llilt9tA!ilMI@W•I , ,t+,nr•Wl•lMfl!I m;• w,, ,. +10J• J , H;it1r, '21u · ::z ww• :: •t~.u;i ·rnw•wwww
TEO [TOXIC EQUIV. VALUE, FROM I-TEF/89) NA NA '.3.6 '3.8 J :17 J NA , 14 •20 !~!MMi®.#.~~g§.Q!PX!fitiAIAhl :::::::::,:,::.,:,::<??? r:f.m. ... :::::~:::::;d:tY=;~:;:_ f#\IDftlHf?ifii~j!j@tf ::i:rr:~:ifaJ@}{i\Ifa!i:;Ji~Af:~::~:qqg~~tfE@KiPfiJiHt\Ei ;~j~:;:fiii= :ntt@M@H
TETRACHLORODIBENZOFURAN [TOTAL) NA NA 0.61 J ,_0.14 J .48 J NA 1.9 UJ 1.9 UJ
5 of 18
-
------ - ---·------·-Section 2
Soll Sampllng Investigation
GP021SLA
CHEMICAL
QIOXINS/ElJRANS
TABLE 2-3
SOIL SAMPLING SUMMARY -DIOXINS AND FURANS
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
GP021SLB GP022SLA GP022SLB GP023SLA GP023SLB GP024SLA GP024SLB
1,2,3,4,6,7,8-HEPTACHLORODIBENZOFURAN NA NA 10 U NA 160 J NA NA NA
1,2,3,4, 7,8-HEXACHLORODIBENZODIOXIN
1@1i:ifrriih8~!;8~9®ili#~ziiii~r < A
1,2,3,6, 7,8-HEXACHLORODIBENZODIOXIN
iiJi:1ttHiwffi™filltPBSRi~fqi(l)wJiH
1,2,3, 7,8,9-HEXACHLORODIBENZODIOXIN ·::::::::c,::::::::::::::::::,,,,,.,,,,,,,,-,.::,·:::::::::,r,:,,,=,r:::.:::::: ._.,... ... .,_,~,;_:::,;_:,:,;_ .......... . 1,J;3Y!Wi ~f!!"l½l';Hl@!:!QQt~l;9f!J!lAf!Ml ff
1,2,3, 7 ,8-PENT ACHLORODIBENZODIOXIN
t@i~fr;~fe$Nfi!,JW®B9!llai:if~lrn
NA NA 10 U NA 10 J NA NA NA ,tiA> ; ,l#:tm· II i1ii@rn wrn:;;;; \\Iinrn i iwi••••·····;!'.Min•• H!%H
NA 8.9J NA jiJ NA NA NA
:• •HMNkiiiiit I•••!fo(i•r :H•·Ml@trnrn: .•. 'iii'•+•<·.·.·.,·.·•········NAi·'><0••·•; .• •.••riAT;7 •·'·•···· IiAA ..•
NA NA U NA ~ NA NA NA
•mtili#;M;i •N&Iffi+ .:)o•.•ur§;•;; ?YN&ffl "•x:e.:uR:;;.x•hN?,\idiF•rTii;w; ;;;c;,iwv
NA NA 10 U NA ·s.6 NA NA NA
•tJA n ··u;;;:;;;'.' @Icil!if ·•·iNA fr;/ 1;~Ji;j;;i; ••i·•·•·••NM,•·•••:··••·•• ilAitl . ''liiA/'
PENTACHLORODIBENZODIOXIN (TOTAL) NA NA 16 UJ NA '39 J NA NA NA
w,;;;c; i t1irwsii tiAA:::::: ::,;:;,;::;;:;:;;: <riw' ;;:;;; w.tt•;t i\,IAAtt g€ITT4Gm%Rl:iPl~~~9fj)l~ltrrSr.Aiir!1 E t :ht i itk,'iM
i~i;i11~i$Wttii~£iiili:l , ))'Vi +··•····;···~·:
NA ro NA ~J NA NA NA
)N,\' ;;··· >i!Hivw; ; •••·•rr:i,,.iii ;;,;•·•·•·• iii L ; HA A ;; ; ; iiA •••••·•••·r:.••·• :NA···
TETRACHLORODIBENZOFURAN (TOTAL) NA NA UW NA nJ NA NA NA
6 of 18
--· ---- -·-- ----.. --Sectlonz
Soll Sampling Investigation
CHEMICAL
PIOXINS/EIJRANS
1,2,3,4,6,7,8-HEPTACHLORODIBENZOFURAN lf?(il:;w;ilitl~i!f!@!tf1R9fliw.im9RiMfiH
1,2,3,4, 7 ,8-HEXACHLORODIBENZODIOXIN
i!i)~illHimti™§i!lMii'«\Piiji@!~llii!ffiHM
1,2,3,6,7,8-HEXACHLORODIBENZODIOXIN
ii~iiiJ11i@il$i/A\:JAfaii.loRiij§§i§i!ffiH M BUI
1,2,3, 7 ,8,9-HEXACHLORODIBENZODIOXIN
1]iii'fililiilfl™1ltl~!l!li~f9flffil
1,2,3, 7,8-PENTACHLORODIBENZODIOXIN
1iii:ilii.il,1?emi\ci,Jrol:loBifumzo#i[iRAl,i
2,3,4,6,7,8-HEXACHLORODIBENZOFURAN
t~1tmliitiirlll:;tiiii:IR9i;lii!g1liP\i~
2,3, 7,8-TETRACHLORODIBENZODIOXIN ?.li~?f.ik~I:MGHµmQQ/~iQEffilffH :::,::::>-·:·:·
TABLE 2-3
SOIL SAMPLING SUMMARY • DIOXINS AND FURANS
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
GP025SL.A GP025SLB GP025SLC GP026SLA GP026SLB GP026SLC GP027SLA GP027SLB
590 NA NA 36
'C @ 11( · '· u:i!%lit ---,.,··-,·x-:ItNAtatttrntmn~:tmrtn@
63 NA NA 15 U NA NA 6.7 NA
;;~~ ; ......... JMikW>,, &ii HilllfaGBtMl Mllimllrnrn ti:-¼i .... Ji li1)Kt\!1li ;;'!WSL
370 NA NA ~ NA NA ft NA ::zwr:•:•:· :e~t :>: ::.::;Nii> nui :n:::Mt1m::v1@1:ms:t·:nn:::rn:,rNAJn : ·+· ·••::•NP(:·••:•:•:•:•:•••: :.:u,:iHt:Q
130 NA NA 27 NA NA 13 NA
:: l{I}lllljdiiiTill b/44 HM# H Nii iliW F~iliil@rnrnt ; &AL . . L.,,Ni'(\>:.:." ~.7)J'•· :_ Nii )
'. 96 NA NA . 8.6 NA NA 4.7 U NA
n1~1· .. ) ...... ;!w.: ······'N&nii @)i)ijJuPm1rrni¼,t NM ............ Jtid? li/@:t ?
23 NA NA 4.8 U NA 4.7 U NA
@HiiiiJk tNAH•: n• un·;;iA ii,J!Wi@ti iii&:: '%4',Ebh ·· , 9Mit:•
6.7 NA NA 1.9 U NA NA 1.9 U NA :rnmnrn @m1rn :> NA'1' ' ;NA { ::i Ni:s§ iiHfr i'i ?!W ·•·•·•·•·•·<·•·· •·:}ik : < :m Mii~i;;t&W .. .;.Ni ;;
HEPTACHLORODIBENZODIOXIN (TOTAL) •8900 J NA NA '2600 J NA NA fagirrAfiw;gJl@wij~lggiw/¼~rr&r6lil '' l!!!!I\HMmiwHl ttiiw;i:fomn Twv:: ..... · :Y¥4 ;!M,'.; ; ; i'Yir:···· •· ··· NA
ii:NAifo~
R~BAt6k66i~;i&WJW®ff$t4tiIMM%IMM i;; rn;rntttii;/Jjfi : :);)/ {;~:Ui n ;i:; ·•·•·•·•:•:•;'. H/4HJH\H mf;;;J;rn" IIrn;;n
OCTACHLORODIBENZODIOXIN
!$qf@l¥i.4PR®i$!!if##it!fu¾:JH
PENTACHLORODIBENZODIOXIN (TOTAL)
i#l'm'11GfitQRQraijijiJi®JW#Aif Hl#WiJJl
TETRACHLORODIBENZOFURAN (TOTAL)
· 63000 NA NA 15000 NA NA '130000 NA
IfWW rnt"'@.!%K HHT&/H >i(@ffliff····· Ht.I-IA' W#ff ff Eif.i~!i n //iitK
290 J 43 J NA NA 13 UJ NA
Hi&iUI f@;j irojwi ·iii LNA / i,·.•.·. Hw O iil~:~t~i iHW! t
. 41 NA NA ', 140
·· '.fti4i;,;:;;, ,NAf\::>.••i>>t•·•:NA.:f<•<r•:••••:•·A:iiiS n
NA
:tiro1n:::-:·:"
·.75 J NA NA 0.58 J NA NA 0.25 J NA
7 of 18
-
--·--------- - ----Section 2
Soil Sampling Investigation
GP027SLC
CHEMICAL
PIOXINS/EURANS
TABLE 2-3
SOIL SAMPLING SUMMARY· DIOXINS AND FURANS
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
GP0285LA GP028SLB GP028SLC GP029SLA GP029SLB GP029SLC GP030SLA
1t?;~:~rn;rt~i~!itllilim!1,i&i~!!lg9!ll9~l~liii!Ml\\!rn "' . c;w-:v i ;+ wm+>c:<r····r·*K:•·•·•·•·•·•·••>••·•·•·•·•iiiik······; <>•···•·•·•'.100••··+> >>c?!lAt ; ••. ·.•.·.•.···········• :Rik , : : · ::Jwrr>·
1,2,3,4,6,7,8-HEPTACHLORODIBENZOFURAN NA 13 NA NA 4.9 U NA NA 4.9 U
1i~;~;~fa;~:~;~~IA¢ft~QRQP/~§~gg/W,ttf!II k!llll F ; !:IA:'! $;j{p• ... •.•·>i·•····••NAX .•. ·.·.·.•··························•· #K·•··········.·~ i·.············\f111•i;; .. ·•·······•·i·.·.·.·.·.iJ.ii .•. · /.·.·.···········•·i.·.·.JilA·. ·•·•·>·········•'·• )ttU•
1,2,3,4, 7 ,8-HEXACHLORODIBENZODIOXIN NA ~3U NA NA ~9U NA NA 4~U
l~~J~'.~Wl&H.i~~Bt~:ilil#@;~~t.OE:mt ···········:····, •:>d••!<IA'l'•• •>1ni;v.• jiiA •••r1;c'•·•·J••w~rn•••?·NK 7 @:•:f!K't•:t'.Dl:f'tlt
1,2,3,6,7,8-HEXACHLORODIBENZODIOXIN NA 5.3 U NA NA 4.9 U NA NA 4.7 U
)iiifa~lil1;if!i~tiiil~~gi~zoilmllMHll l )ii('. n•rn1!ifaloithffilff\:l)( lN w;;! WHHHi'.eULiliwilfoiid iiiAi hi £ifotui
1,2,3, 7 ,8,9-HEXACHLORODIBENZODIOXIN 1;g;J:1;~;1iiB~timD1l1li~i!,i!i&ii Jllil rn
NA UU NA NA UU NA NA ~7U ....... :-: ···•···c'WW/iVWK''.fF!ic~'i.k·· •</pk/; /}NATT ·········•·:::;nitil'i ,.· .. ·•···· #A•L•kXIb!'!i!{ii•••L:1;n1t
NA 5.3 U NA
!ifi\1:liii Iil'6TI I!IlEWt~ivHi!Mli W.4!!
1.2,3, 7,8-PENT ACHLORODIBENZODIOXIN
1~;@;'1;j;#!!Nf6q/~ggp/~?@R!m@lff P'
NA iffi'{-' .. 4.9 U NA NA 4. 7 U
ii~:9uf1'···· · i!-fii / •·>>•••·•·•·:JiiX>>•>·>·•·•••·"rri•••·:
2,3,4,6,7,8-HEXACHLORODIBENZOFURAN
#M!m!!rn/lMM,liBt!®Q$i!ll/flu:l!Ml¼NM !HM!Jff
NA 5~U NA NA 4SU NA NA 4~U
.... NA .... , · .. :~.:!JI +NA /#A ;;; fr@~cii .;:#A :5 // #A ; ifrifr
2,3, 7,8-TETRACHLORODIBENZODIOXIN ?l~lfiijtftfl@,tiiilµm/.\Biij~fotmn
NA 2.1 U NA NA 1.9 U NA NA 1.9 U •++ w;l\ i!itr4li •••••••••••i iiliiE N/4:i :;;:Vitte ff!!'lilA E!t7tw>i;31'.;AY Aiiiiii
HEPTACHLORODIBENZODIOXIN (TOTAL) NA
i'!ghlf,i,ct!tilgd/li~~Nib!iPRAiilrri#AtJ1n ········· # )NJ% ;Jw;irnu
530 J NA NA '230 J NA NA 170 J
• ••••••••••• •'••,.•••H• ~ :-,. ' •
•HJikm•,· v••···~·V·•·, ,·~··· :A!&ii•i•· A·•,;@gJ1t;•···••?s••t!l\.hfrii•ih•·•·ffA••·k•{· ·•·E•·••d~••;c;.
HEXACHLORODIBENZODIOXIN (TOTAL) NA 63 J NA NA 24 J NA NA '. 23 J f.i~§il!K@!l9!'il~/lli?Qffi&WIIT9f#}!IW I ti / +• • • t:!&.; .... T> ··s~ w F> '. ;'NA)/ J;•;• ; NA iy; ... >r;; 8;$MJ; ;!}> /#A; \;/ ;•} <NA:ji>• +•>·• ~,;i:u.
OCTACHLORODIBENZODIOXIN NA 22000 NA NA J NA NA 7200
PENTACHLORODIBENZODIOXIN (TOTAL)
iitflfiGtfil.qs.!J~~N?f/.\iitfr4ijngf;;tirn
NA UW NA NA ~9W NA NA ~7W :;rnp;;n ;; .:)t11c r ·•·•·••• ;'ii:ii:iL/: 5,;,r ;: nirn;w,;;;rn;rnrn;m;,;1;;mrn1mwi •·>•·•···•·····•···•••i<m<••·• :: .... ," ~imN
NA ·24 NA NA •·7.8 J NA 8
l!M)MHH l'i.MMMf@@SfiJlli!;IIH #!!'.• ·•·<•·•:JUA .. ;,;; :; lf,em: ... q ... SMi H1M@J
NA .0.17 J NA NA NA NA 1.9 UJ
8 of 18
-
----------- -----SO<t/on2
Soil Sampling lnvntlgation
GP030SLB
CHEMICAL
PIOXINSIFURANS
TABLE 2-3
SOIL SAMPLING SUMMARY -DIOXINS ANO FURANS
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
GP030SLC GP031SLA GP031SLB GP032SLA GP033SLA GP034SLA GP034SLB
•••••••••••••••••••••••••••••••••••••••••y.••• • ••• • •••••••••••••••,•••••"·•••••••••••••••••••••••• ••• ••••••••••••••• ,•,•,•,•,•,•• •••••••• S V , U -' , _.. ,
1•••••ihi1i•tll.ii'tEi1tActltoRbbiBENZOOitiXiN%%••;••••M• •·•·•·•·•·•·•·• Nii•• :.:.:.:.:.:.211J..• .. •.:•:•:.: . .:.:.:.:cc::• . .:.:.:. .. •.NA.•.•.·.·.•.·.•• .. t.• .••.••.••.•.•.•.•·•.•.i.'.•.1.·.i!o.••.··•· .. a.·.••.••.••.••.•·;·•··•.•.••.••.••• ••\ •2100.·.·.\•L<h .. ••·•·•·t.:1.··.·.w.•.·•.••·.• .. wt.••••.t.\.••.J.t.t.•• .... Hs.oo.·•·.•.·.•.o.·•.'..••·.••.•• .. t.••.••.•· .&• ' '· ' . ... . . . .•. . .• . ....... ·.. ··• . . . . ....................... .,... ...... ,... . ..... " . . . . . • . . .. . . .. . ..
NA NA ' 29 NA 250 '······ +NkII•it!:% .. t MiO·--·r•cNii•·· .. \ iii 1,2,3,4,6,7,8-HEPTACHLORODIBENZOFURAN 1m1tl~t1ra:iliifffei~gi@iwJim&Jmw;ij
1,2,3,4, 7 ,8-HEXACHLORODIBENZODIOXIN NA NA 4.7 U NA 31 36 . 3.1 J 46
1#im;;fii!1Hm!A½B@i&@J'liij\wfa:\€l!!wl@H }iii; .·.·•••••NA /X;; $!£# ·• ::NA ;· j\::µ:XL ··•·~·•······ .•11..•.•••.·• •h Hli•l!iti!#iiffMlt•~•H
1,2,3,6, 7 ,8-HEXACHLORODIBENZODIOXIN NA NA 12 U NA 82 120 13 ' 300
i!iijltifl!f:Hili'AB8@i&ociiij~z pf;µw!!;l!ff n::N!t tt:::·::=• j~if#Hiiit··· -··=;J)f:NA!f''?Tff :::~fft)-f:\: ..................... , .. · •. ·,, ...................................... , ,. ~ ·e·•·•n·•·?·•·•·•·w1ax::·•·•·•··•·• ... •.•n•:'.?\11r:•+<•
1,2,3,7,8,9-HEXACHLORODIBENZODIOXIN NA 4.8 NA 49 68 . 11 120
1:1ii~l1i~i!i\B~XAB8~1'.1PlQ~;i9f'µw f }rn >>i t iii\@@ < :;~:iii ~,:,,~f ?i4fi:'.: -:-·.-.·.~-: ::~~;;;~:;;~:~~~;;~:&;~~L:;:;;:;i iii,i:i·: ;; :;mu•;J X:411@
1,2,3,7,8-PENTACHLORODIBENZODIOXIN
1!i#&i~re~Wi<.BiliiiPR6Bi•BiiAT
2,3,4,6, 7,8-HEXACHLORODIBENZOFURAN
%1l\iifiiret&f#iw\!&i&1R'l\i!i@Wr&Ml
2,3,7,8-TETRACHLORODIBENZODIOXIN
zfa\fiifiiW:,Bt9ffoPi~zl$gµw
NA NA 4.7 U NA 13 18 4.7 U 30 :~;:NA6Ite-~ 101 ;:j,b¥;:\:;;:;:;:; ~:::ii ~rt~@~11v. it;~;i{%:NP./;;~;:;;;:it;i;:;; :):/~•~:il::fr:::;::::::::·: Ui&Mii••nrn;fi•tlnr · i'.Ft ;:::::::::::;:
NA
•'••'"•NAY••••••••
NA
····•·•·•··•••••••Nk,::.:
4.7 U NA :i;,9 '11 4.7U 0 24
•~•·••::ftQ • •frlli!!li \i~!Jii W#i/;Mu•; .i ":k.¥6%! IHHml@i
NA NA 1.9U NA 1.9U 2.2 U 1.9 U 3.5
: :•i%L ::: iii;•> di #idiR6 y; TNA) < ,. %iN#P IIIFZ:HitH fI1ttOSHfHJ@#VilliHH%%
8@kfX&iW6lib@~~;;;;~ff&fxt1ff•HW;F t;;.; . .;.;;;;.;.: : rn ;r; . ;:. .,. 560 J
i~~Mff
NA
iAA'F
• 3900 J
;;iiii~DB
4300 J · 650 J 11000 J n~arn WA@ ;; !f{iiiilf
~~2~ .. ~8~881~';~38918;;:~\I(?I:H ·•.·•.·•·'.NA.·•.·.•• .. •.·•.·.·.·.•.••••.••.·•••.·• .. •.· •. • •. •.. . NA ?~ J ·················~·· •. 580 .. J ····· ·.· ... · .. IIBJ ......... , ...... 120J... • 16.oo. J H.~9%9R9Pl1\!ic'l~Qfl.l~IT9TAAf•· ·~ }NA • •1'~!!:•• ... ••••·•··•W>i•• . •• \S;(t1e:c2 •·•/·•·• 1.11.~•4HNi 1• •MtiW VW@1iiilW?
OCTACHLORODIBENZODIOXIN NA NA 3000 J NA 22000 23000 17000 •11000
6bf¥cl!lto~OOla\'!i'd6ii~I@,.,. iik;;;;L;i•••iiiA ;;: /{j ·.·•···•·••h• , \}di'JJ,H, g;;;+:ia)KK,LGJY@,ji)T, ··•.•qwzr rnt~ii#H
PENTACHLORODIBENZODIOXIN (TOTAL)
ea!iiiitltl$i/l$~~Ni9!!u11Ai;iugf&&Hn
~~s . .rr.s~1s.~2H1~,x~~H::t.~?.~ .. 1.:T~ti~~1 J'!:IM1WliPBOQ.l!l!;i:gpp1.QX!!!fl'QTA!'clfff
TETRACHLORODIBENZOFURAN (TOTAL)
NA NA 9.5 UJ NA 58 J , 91 J 18 UJ '230 J
•·•·•·· .; !fflimfi •;; ::;;;;;ii@i Hid •.•.• :111 •. w .•.•.•• t,!%,.t••·············••!iJ•A•L·•·· d tf\l•t•• ;. •·iitiiJ.!#nt WM~#t
NA NA ~6J .... ,. .. .. . ......... , ...... ,..... "· k i®L . ;·• M iNii• •+•n ;za:•:uJ NA 70 .... · ..... : ··-~·~······❖•• HlK.,. , .............. ···•'t·}l:HiiXK········••i••·····"'••·······••flMil;;..
23 200
•gSiuii+tt rtsli'Rnr
NA NA .. 0.19 J NA 1.2 J 2 J 0.3 J ~160 J
9 of 18
-
-... ---
CHEMICAL
PIOXINS/EURANS
1,2,3,4,6, 7,8-HEPTACHLORODIBENZOFURAN ll?l~:;;iiilli1/iiiti:A'9l@filRQQ!~~WJggµfiAij
1,2,3,4, 7,8-HEXACHLORODIBENZODIOXIN
i@~l,friiifB~i:itiiliii&itiii:il'aji¢~li \lid
1,2,3,6,7,8-HEXACHLORODIBENZODIOXIN
1fafa,~;'tii\tl™9fiiii:IB@Mij€fiiP.i!miH
1,2,3, 7 ,8,9-HEXACHLORODIBENZODIOXIN
1;g1~;2;i;itB™1:\fiiii:IB991i\'€fiz9rm:r"·
1,2,3, 7 ,8-PENTACHLORODIBENZODIOXIN i~#iiiiiWgN'fJAfil&l'i.99!~ij[4!lm· .....
2,3,4,6,7,8-HEXACHLORODIBENZOFURAN
ti!iiili\i@i!#.4l$lfi;ii!iimiijgm/KiW!@I
2,3,7,8-TETRACHLORODIBENZODIOXIN
tii\ritf~'tw(i:iiiiiQ\¾l:il?i~zi:?t~it
HEPTACHLORODIB ENZODIOXI.N .(TOTAL)
H!iilf&liffi§Ri:i@llf@ill!Wi!rr§.ff¥1
HEXA.CHLORODIBE.NZOrnO.XIN (TOT AL) i;ig%\.\:itllb'i16Mal~#Biiuru®rr&¥4lli
OCTACHLORODIBENZODIOXIN
&BfJicl'ltiiik6bl?MJiioiiiliWJ!i
PENTACHLORODIBENZODIOXIN (TOTAL)
.,.,.,.,.,.,.,.,.,.,-:-=-=c·=·=·=·=·=·=•:-:•·:::·.,❖,-:-:-:·:·:·=<•✓.:-:•=·=·=·=·····=·=•:-:-:-:-:-=-~=-=:=·:-:-:-.·->-··-·-·-·=···-·.,.,,,.,_,_,_, fil;NIAi;;tl\i.QRQP!El!;~Qf\:!fY\!'!flOIM}
TEO (TOXIC.EQUIV .. VALUE,. FROM. t,.TEF/89).
f~'ti¾P!'li;i@@pi~tPP!P&li!fi!i'.M,!W t '
TETRACHLORODIBENZOFURAN (TOTAL)
---- --- ---· --SO<tlon 2
Soll Sampling Investigation
GP034SLC
TABLE 2-3
SOIL SAMPLING SUMMARY • DIOXINS AND FURANS
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
GP035SLA GP035SLB
11
M\I~i;i ••••••••ix••••••
GP035SLC
NA
:,::·::,•::;:,:,,l\iASI
GP036SLA .
11 ;;;;;ij;;
GP036SLB
4.8 U 4.6 U NA NA 4.5 U NA
•; l@llllif 1MMM'Jfol(ff ·• r:,·, 1'iA L /i ii!&; l@,@B, ;mm ]1,4 :X
4.8 U 7 NA NA 4.5 U NA
ii llt~:1\P'i MMW¼foiiJHfiH ~iiti ' ' f&NIW hk~;\itii i llwifo;
GP036SLC GP037SLA
NA 830
iNK >•<WT'.?
NA 210
,,,,,,,,,,ii,,;.•/•'•'•:• •ttt::}•·••••·:«•'•'••nn
NA -1300
itikirn :;;;:wi,ri•i
4.8 U 8.4 NA NA 4.5 U NA NA 790 .. i ifa!ii!fri:b iilil&lMlHiHlfiAffH\ htt!'ieirn \i;~~,F• ,,;/:' NA,,,.· .. Ni'.; i ::iiu
4.8 U 4.6 U NA NA 4.5 U NA NA 110
:;.:.·+'I%Mb1F I41\BlbfflfiffNA)f •••!lA'+m;· ··'@Ks&; )fol!"¼% ' NA ;,,¥)ii#
4.8 U 4.6 U NA NA 4.5 U NA NA 20 A¥o;i ;n,; ;iwomnw;n;wMrn , ii& :; \f)ij!J rnwmminrnrnrn NA • :i tii:
1.9 U 1.9 U NA NA 1.8 U NA NA 14 HP?tfiG?W mt1ii£;····· Nl\h. !Wfow t ;1;iiA w iwit _, ,. i&N ;7 3: ~ii i>
130 J 720 J NA NA '.260 J NA ,,,,,,,,,,.,,,,,,.,., ,,w,,,, ••... ".' .. '.••.'·'~.·.'.'',·.,.'·,'·y''.' .. '·· ... ' .. ' .. '·.·.-.·.·,,.·.,. ··. ··,v····· •.•.· ............. · .. ·.... ,. .·.··•······· "·"·' ....... •.• .. •,-.· .• .. •.· ... • ... ..· ... · .... · ...... . ,,, ,.,,; n ,.~ , •~.t\U,tt, :%:l'IAE??F '' ttNA ::::t:,.,<:<~.t'.l!XT!TTN>'(
47 J 82 J NA NA (34 J NA 6700 J
lliEti;nTii!]tiJ rnrnn¥libi;l N¥U J i iNJ.•)i i \iifi: '/}NA';c ?F~AAVD
730 J 27000 NA NA , 4400 NA NA ,-170000
.; +wu·wtrn+#WH ti¾' ¥I !JlNkf!H ilMHluhHH)Tiffii<WHil! 7'Lfil,;F /F/l)mf 7
7.7 UJ 11 UJ NA NA 4.5 UJ NA NA 1400 J
i~@Wl W!iff~IiWi lMFHi¾'H • H tt1'iA ••.•.•...... r:¥s•417+WN'A t; ;%:fiA'I ii7Jgrnlfr
' 640
;taa@f
1.9 UJ 3.4 UJ NA NA 1.8 UJ NA NA <140 J ,_
10 of 18
-
------ -- - ------- - -
Section 2
Soll Sampling Investigation
GP037SLB
CHEMICAL
DIOXINSIFURANS
TABLE 2-3
SOIL SAMPLING SUMMARY -DIOXINS AND FURANS
GEORGIA-PACIFIC SITE
GP037SLC
PLYMOUTH, NORTH CAROLINA
GP038SLA GP038SLA
(Duplicate)
GP038SLB GP038SLC GP039SLA GP040SLA
••••• ::::::-:::•:-:.;.:.:-:-:❖:❖:-:-:•:-:•:❖:-:-:❖»::.:,:-...... :;;-:cc:·.;:-:•:❖:❖:•:-:.;.:-:❖:❖:;•:❖:•:•:.;-;.•·· ::::·:· •• ::::::.: ·······•: · • ❖.•.❖ •• • •··•.,·.·.;· : •• :::'"·::::::. ::::: •• ,.;,.;;... • ·•.•·.•. .,, •••• w , :,:.:,:...,. ❖ ,.w , , , f..' , , -:° -:° '"':-,' ,', :-:.,-❖ ._., , . iiMHJiit,~i!l!!;r!A9Ht\:l!'©Plli1;@;qp\gi!!fi frfrt :nv@W'. ;>>51~• :k@i!~ 1?!/il;i;; · ·•~!! ..... ·o ~ • ••• soog.-·-,J:t@!t!WII
1,2,3,4,6, 7,8-HEPT ACHLORODIBENZOFURAN
ifa;~:~\t;~;~l~ffi'.A~fiijqpjij$@&fµ~# H
64 4.7 U ·280 . 260 4.7 U 4.8 U 1700 110000 J •••••••· , ,;.,au t¥lfi!!M T~l!:··· ••••:: t,$.i;······ •• •• •,;;;7,;;p•• IiEJ~J;u @Wi ; •#t!;hi.1iiilifo
1,2,3,4, 7,8-HEXACHLORODIBENZODIOXIN
lliliMitiiB!l:m,¢Bl@li$Mijgfl@¢twwi ff
28 4.7 U 22 25 4.7 U 4.8 U 28 4000 J rn !fi;lµ# IffiK#!i!!HFF@ ··············•· di'. iiti!J.ri t'!IAiR ••t~~ MililWJH
1,2,3,6,7,8-HEXACHLORODIBENZODIOXIN 160 8.2 110 ! 100 4.7 U 4.8 U 280 · 47000 J ll~i~Wliiiffig:@,jjfl(gijqq(jjj§,ijit\iiirei®I h : • ·•·•· <: s:+·. :inrn Q. ?••·· rn,;M O r: rntFJii:f PH . i '.C•it.;L HJ} • 4/i#Hi i :: •%~ o . .;;,. ++w ••.•. : .•.•.•.•...•.• ( 160iir•·•·:••·
1,2,3, 7,8,9-HEXACHLORODIBENZODIOXIN
i;ii~if;i@m~iiAPM!PBQQta£2if~!!M
85 4.7 U 48
d;teiVHPW ,;diQMI i (MJFW 54
)ii§@.
4.7 U 4.8 U 98 12000
l iJ ~friuii i!lP!\!IJJNiUMl@l~ll WlMilME@mlJi!B
1,2,3,7,8-PENTACHLORODIBENZODIOXIN 13 4.7 U 14 , 13 4.7 U 4.8 U 24 1800 1MfaiiW!FimA\::liitooSBiii!iil£8i1&iwfm nrn IiI ;n; ;,;e.-uz;;; M\ilPiH w+ t,~li! fa; /¼$IL a;a ifiiui ::: iiii);t:;;i i11x+ir u,e1.wa
2,3,4,6,7,8-HEXACHLORODIBENZOFURAN 4.6 U 4.7 U : 8.9 -10 4.7 U 4.8 U . 35 1500
il~!li)i;~\Ril'iir4-mi~&BQPll/fj!iiliil~ll,rn TEWMUMHHlilWiiil,IIU ·•HJ¥lli L ;~iiiui trn !lM70JMMHW\ili/illH% ;iii :'i iffHQ#i
2,3,7,8-TETRACHLORODIBENZODIOXIN 1.9 U 1.9 U -1.7 J 1.7 J 1.9 U 1.9 U '3.9 \110 J
tfai&i@ii\Aci!itdi'W6laaiiBR~ % :· ......... :.:.:.•-.:::.: .• :••··· Hff:fa:i,•nli>--···•·•--1 ll u --H,l!, ilWJllf Ifr l!}J;J,j 1nam~ru;rn1;;rnnm~Ml m rnrrnu"t,m fl!IH1W&l$E ·. n > ., ··.... . .·.· •· ... :••·•·•·•·•·• -....... .. .. . .. . .... . ..... ············ .. ... ..... ... ······· ................... .
m~iiliaWB@igw!~Wh~~;ifdf ~~;;m; 1 me ;+ , n Th~ ii iii if ;;~~l~J x , ~~; ~ ;; ;~~; Jg ;;: f !¥t\Pff)l; ii#~~i,Jt; m ;,;: ~;;;;H;a~& &IE
ffi;~i~@i@&l$iz&;m;i~t~ilrnmt;;;irrnh••·••%) +!::,~;.s,.;;J;;..;~i,0,fr. ,.rnZ:;ii wi ,::r~i ... ,.,i.;.. ~ij,iiifi,l;+•i••A;:,! ciJ•i•+tn!J: ii+ ,i;::.~:n
OCTACHLORODIBENZODIOXIN .14000 750 .27000 22000 1600 700 · 51000 10000000
9.¢.f#¢BUgij§!;jj~ig@!Qlmi! j .,;;.+npqv: @ijj~,j •:MltHWrnl!Ji!W gy;pa;; .. :,.. ·.m:fx;;)bq,;trnn ;:;;:, ld\O /('.)700, ;, .. #SOil®{ "
PENTACHLORODIBENZODIOXIN (TOTAL) -140 J 9.3 UJ J4 J 73 J 4.7 UJ 4.8 UJ 220 J .13000 J
ggf#~¢Hiii¢fiqpj~~liii&ii\ii#ii&a&fk¥Wf··•· !HlW&wI ll i%mwl !Hff~## nu dtSObkiI W?lmF}fliNW@ilii e '.LW.if!P! mi~ii
TEQ (TOXIC EQUIV. VALUE, FROM I-TEF/89) fgf&4Q1!!Q!#gpi§~oP.iti!@)fi'i\r¥t1f ···J Msili
:2.3 ', 99
Niilii&WA rfitiit
· 77 , ·2 · 1.3 200 · 27000 J
:iii ii H Jt1\~®!ff t HEQ 22 tiiiJ ii Wiiiii6JH
TETRACHLORODIBENZOFURAN (TOTAL) 1.1 J 1.9 UJ 41 J ,-53 J 16 UJ 1.9 UJ ·380 J 3300 J
11 of 18
-
------------ -- --Section 2
Soll Sampling lnve:;tigation
CHEMICAL
PIOXlNSIFURANS
1:i;:faiA:t:~rn1ei¾1;;~1;li!R9!!1iic§@@12½1fd.
1,2,3,4,6,7,8-HEPTACHLORODIBENZOFURAN
GP040SLB
TABLE 2-3
SOIL SAMPLING SUMMARY -DIOXINS AND FURANS
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
GP041SLA GP041SLB GP041SLC GPD42SLA GP042SLB GP042SLC GP043SLA
L·•·· @!Mi!½nnt UifoliWMWH1il11illi\'blf:C inH:ziiliiiltn ii;i40Qiii +x;;y•w;;;;;;; HA;;x ;zSii&i'.n
NA 110000 23000 570 130 NA NA '49
@i f!AEW HM£14~iHl1 i!i~Il:li WM•M'M <<>Hilt lli\'$.'t l! n ~! \.·.·.•m· ~,i.ibF IJg;~t~\tl~i~\iigl#:$,gii;gfi9!)!~!#'9!l!:iijNjil\H
1,2,3,4,7,8-HEXACHLORODIBENZODIOXIN NA 1300 1700 , 23 11 NA NA . 4
:i@ii)M1ifu8ij&iil';BU§llQQ!ijW'lf&!lmr Mi diUWffl ••?hliffn·tt XU} ;Li H~iii:@ NA .·.·.·.,, .... l@il : ifavQH
1,2,3,6,7,8-HEXACHLORODIBENZODIOXIN NA 50000 •4900 .150 '.53 NA NA •. 36 ·
ii:;i#;~Mi!ifill~&@ll!iwil@R!~~Q[Qi'wli Ml rn;w•;;nwrnnmrnnt,!iiHWU%UiW:l#iiU ! iFIMtlt NMMli®Mrnn .;;w;; 0•#(Jff
1,2,3,7,8,9-HEXACHLORODIBENZODIOXIN NA 4600 ,1400 27 '. 26 NA NA 13 iJJ~l\ilri~(gffii§½Plii!PRRQl~gpf'Vfl.Aflff iM • n@ifohl;;l;\ i Nkrtrnrn ;n;~ nnnrn;; NI~ µ•\HI i!J\ Qi iii rn~.~· ti ii !ll lii@ffl t ' ;; ; Ntii i jji~\!!Nit
1,2,3,7,8-PENTACHLORODIBENZODIOXIN NA 1300 J ' 520 14 .4.8 NA NA 4.9 U
i~!iilifieiJfi\lii'iil3lfoB/liENt8iilJiwlF ....... ············•·.•••.•·.NA.·.·.:.1.••.•·····;:•n.••·······•··•··•·.~ .•.. ,.P:I.••· .. ···•·1·•········ t ;1 ... i :., •············ JW~itt.••··········'········•············ .. ··········k·:'·,·•·ii iii.r.t .• · .• ·.c: ·.·······:.•ilA .•...•..•. ·.·.f.i.\.I.i.i. NA ···• .. • M,~ u • .. ../ .. i •. •,.t .•.... ·.·•················•·············•··········•·······.·.·.·•······•·······•·•····················· .. . . . . .. . .
2,3,4,6,7,8-HEXACHLORODIBENZOFURAN
%~:Mt(liin!foifii'.l%\(9/'ii:lQ!!Jgl'!l@!iQll4fF
NA 3300 85 , 5.7 4.6 U NA NA 4.9 U
.... , ........... , Mi+ M #mi Ifr T1! fa +@i::¥ •vu i;i}ii\iiili U fa E)@ti·+uE Jii;igh i ii ii:iirii
2,3,7,8-TETRACHLORODIBENZODIOXIN NA 140 180 \ 4.2 1.9 U NA NA 1.9 U
ifa'i@fofWI\BilE&a6Biii!miliil!ifil®k ·.•··•·•··•·•· •.··.·•.•·•.··., .......... ·••.••·•t•.••·•·••F•••·;••··•.•·•.•····•·•·•· INA Wm .•. 4JiflWM Hi£ ij# i#iS:Ji@rn Iii~iiiiikb tNi>i\i ;•rnw.ifab• '.iij;'t,;;; ...... , ................................... , .•..............................•...•. , ... . . ... ······ .... .. . . . .. . .... ........ ...... ..... ······ ..... .
. HEPTACHLORODIBENZODIOXIN (TOTAL) NA 1600000 J 200000 J 5600 J '2900 J NA NA ( 1200 J.
iiliiiff&ilil ··•·•·•·•&seNioifu/£Wfi¥6'fAil1······•·•• ............ ··••·Md••··••n•··••i••h Ir.·• .. t.fft&A d• l~.9.·o··· .. ·PD.·· .. ••.••· .. :.~•··%•.Il.• .. ·• e.,.'..10.·•·•·.ii/i# .. U)i., .••. _ .•..•. ME.F.il.J/!.\.·.l.I i.fi .. I ........... t.:::.••.··~.·• .. •.••.·••.i.i\.ffN.::. ..... f.•/ NA,.. : ::,:.;•::+•.••Nk. :+.·•· ............... 1.:••·t·••··ii·•·.~.1!.·.·.·· ........ J.•·.··.:.t.% ................... ·QBQ ...... , ....... ,., .. , ..•.... ,., •...... ,.:.· ,....... . . .. .. . .. . . . .
~.~S:.~fr?.~?.8!.~.~.~:?P.1?.*!~ \I?!tH... NA >.••.·.•~. •.: .• o.o .. •JJ••· .• ::;.; ••• •.•.;;.•.;t:{~.9.~~.o~.>.:.·:.::-.•.•·••••••>X••••.!~~ •. :.•·.;.; ... ;.:.; .. ;.,c;.•.•·<•;•.:!.o~. :,, ,+:.,:.-. ··• :••.•·:•••••••••••••••·i·:x;.;;.,;.;.•••7, .. A .•.. ,;; .• :::. ..................... •.••·.'.'•·•·•••:·2., .• !~ .. /ii,·.••••··· t!gX/\,§!ilP.QRRR!.@.!i!'!IQ.eJ~•.crQT@Y:m ·~-. . C ~-" •=, UM ~· '"'· •=· . .. ,n ..
8100000 J ;840000 34000 ··28000 NA NA I 6300
#6PiiWU••Wt~mHMl.UUW@ffHMH#ffeiPWMiP@R·MtiHiMW NkiL '.)if~tst OCTACHLORODIBENZODIOXIN
oct!l&ik&a&Biffi€&26'#&¥ rn ;wrrn ; rn
NA noo J'' i860 J 250 J 48 J NA NA ·21 J
i ilfilim!EiM lFil@lt:H@Eii:iii@W! MlffMJli#ilWl!i '.X~~~?Jti. '.,NA:~ ; ; !IA, ; ,nAi PENTACHLORODIBENZODIOXIN (TOTAL)
Wlitliii¢ii©Afiiii!ij~fg&f\J#AK/fi&f&U
NA 28000 J :3400 . 100 >, 56 NA NA 19
·•·•·•·•····· ,,,11rn @niii,\lJnrn+ • ioiihi ... 3\niio'il7 .. :r'.f;id;r iJ mwr,l'wrnw nM.1N;; •••••·••r ;:vil@&r:;;;: •tzJFiit ~~i;~i;;i~iti.iriii~±l[ii~1 ··
TETRACHLORODIBENZOFURAN (TOTAL) NA 2400 J ;200 J · 46 J p.52 J NA NA • 0.9 J
12 of 18
-
---------- - ----- --Section 2
So,1 Sampling Investigation
GP044SLA
CHEMICAL
OIOXINS/EURANS
TABLE 2-3
SOIL SAMPLING SUMMARY -DIOXINS AND FURANS
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
GP044SLB GP045SLA GP045SLB GP045SLC GP046SLA GP046SLB GP046SLC
J;g;~i+;~iii\\1/iiif!li~Pilhii~ill~§~!l?xi~ijij <fr· .. ?Ff•., .. ,. •W1q~k':".c: TiiiiAii;; iiiiiiiiioiiii iitnN.ii #iii ;·ii½i > t !i~ tt it~i!ml! ; ;; !M~@H
1,2,3,4,6,7,8-HEPTACHLORODIBENZOFURAN 210 NA 340 NA NA 35 J . '300 J 3300 J
lJJW11!\¼llelH,W!Ail6ii.BilfBEi4ZBi1l:\l!i./&f .• •.:.••.••.·••·l·••·••.••·••.'.•·.•·.••.••·••·•••··1·••.i.I.S.}.••·•••·;·;·•••·••·•••·•·•••.••··••.•••·ir.·.:..•.•••·•,•••·;·t·••·••· H • •NA .. . 'Hdf~t . ' l l lN,it• .. ' iiNiii ·•••·••.•··••·•··••·•··•·••·;·i·••·•··••••·••·•~·\·~·•·••·••·ll·'.···.•··••··•.•••·••·I·••··••·•··•·•••·••••••·••·••·••·••·M·•·•·•··•···••·••·i··••· iMW n ·.· .. / ... ,.J.J ..... L•···•·•·······•••····'····•·····•··•·· ...... ·.'··········•·····•·•···•••··•··•······· . .. . . .. . . . . . . . .. ..
1,2,3,4,7,8·HEXACHLORODIBENZODIOXIN .12 NA 42 NA NA 4.6 U 25 J 290 U
fi:i;i•.i'i .. lililliix)(oo(biidoial!NZOiiOW,i\i· .nlt••···· HHX••·••NA•'' .•.••.•. : ....................................... • •. J ... , .•. ·.•·.•··· ••+NA ,.... NA. . •.•.• >4~ 0 ·:."• ::/•i,;Jf •.·•.·••.•···•.·•.·•.•···•····.·•2 ..... ~ ... ·· ...••.••. 'il.·• •. •.·•.•·····• ••.·• . .< ..••. x.L •.•........... ••·····•·••····••··•···•·•············•·· ... ············•·•• . . ... . . .. . . .. ...... . ... .
1,2,3,6,7,8·HEXACHLORODIBENZODIOXIN 89 NA 190 NA NA . '21 J '140 J '2500 J ,&i~:~;f:J@)l~&i!M@9ii8i:iiEifflzqiiiffl½N ······'·'···•·····;;x;;;; DE ii fr•·•· • NA ·x t·c ;;13 . ; i-iA ••• w\ ;; '.i(4:efoifrij :2:iltl? , :tt®:::
1,2,3,7,8,9·HEXACHLORODIBENZODIOXIN 35 NA 110 NA NA 7.7 U .48 630
'1\~@i/\i9Jl&V~BHE6!i8BMl!Nz8/i/litiJ;f.· ... ·.·.·.·.·.·.·.·.·.·.· ······· .. . ..... ·•• .. nt.I.~.··.1s.··.··.·.·.ib.JH.!.·•·m·r·+· H,i.•·.·A·.·.·.··.••·I·I·n·I·f·••··•·!·i ······•·.A.·•.···.:a.·.· ... · ... •.••·u··.•.·.··.•·•. '.i./.••.•·.••·;·••.·•••'· NA.·.······. F.H+ll@H /iikfr rnmmrnntiifrlR. TV ·•1. %5111.. @fi.WifH.•• rn•1JW% .-i:f,~v;·,,w, .:m~·--: :._· ___ -·. .·.-·:.·•-_. ___ .:;:;:,:;~:,:,m:::::::,~:,:,~:::::::/:fa:fa:~•~=•-------...... --... -.. -'''"'··-·-·•v, , ....... -.-~ ,._
1,2,3,7,8-PENTACHLORODIBENZODIOXIN 9.8 NA .34 NA NA 4.6 U , 13 · 130.
l2i'i•\JigJWJ.15l[6!l8oiBEht8l1&J'iJ@"· ., : :~. :·.~ za J ..•• , • •' -'wt ' ... • '. :· '.: # .. it; . ''T.I.••·'™·''•"·•·'Y• .. ····'·'··· •.••.••.•••. r.·•.e.·•····NA···.··.'.··.,.·•·1·•···•.I.f.i.t.••.I.H.•.•·'.i.l.I.f.i.u.···.··.r.'.JJ.'.· ... •··'·········•·i·••.1.r ..... l.t.••··•·I.:.·•·.· ... '.l.t.··.1.••·~········,..·'·••.l.!.·•.1.1.••.: .••.••.••..••.•. •.•·., .•. ,. 4. $t ,u ,.;., .. L .... ·•··•••·<·•· • ................... ...,.,..,. . ... . . . . ... . . . .. . .. . . . . . . . . . . .
2,3,4,6,7,8·HEXACHLORODIBENZOFURAN ·• 8.8 NA ff NA NA 4.6 U ·. 12 J '; 180 J
:smiit#\&!;fl/JI\9.WQR9Plii~ff?Pf\!WiliMl! k M\~P i rn !iw T' ·•·····•~AW••·•·····•·· Ni\'. ,.··············••tmt ii ;l *!~id . iijit#lil. 'it••·······•fiiLv••·····
2,3,7,8-TETRACHLORODIBENZODIOXIN . f.4 J NA 20 NA NA 1.8 U • 3.6 . 16
!ii~@*\m§:@Q:!liQRQQ!l!§li;Q[~Kfa t•t ·················• ................................ ¥,i::: , .. :·:. '.. ··~ ··• •·•·•·•·•·•·• t.t • •·•·· ·•:·: .. : &,4;J·rr + '.HNA .................. +tit\·.·. .... faiViiiL • + ; • ·}t~••b
HEPTACHLORODIBENZODIOXIN (TOTAL) 2200 J NA 5100 J NA NA 780 J ·4500 J .65000 J
@#if~i:;ihlp~§Diijl/fi?PliiJJpifoiifii\r,iii;JMH@WlHHfl!I FFi~i!fPIW JI'® I if•X#B!PWH Wl/$ •·••••.•; •illl >s·•·>'\i!ioCJ\·<•·•·•·•·•·>ilgjipJ l!itf~lli
HEXACHLORODIBENZODIOXIN (TOTAL) 450 J NA ·1200 J NA NA 140 J 740 J 10000 J iii~l:llii©lm~@:lcl~§filliwiR't§t#li!llll TS>••· : ; ; %1 ltf~@ii lWM •WM! iWIK\!W.WiilfH ll!HfNMi •·•· ;•·•···•·•·•·•· iw!fr@fr,@itP.!int; r ;n~l!ii!f i '-&~/&@
OCTACHLORODIBENZODIOXIN .9400 NA ,f6000 NA NA 3900 J -21000 400000 J
Qi;t,i\qB¢6W:joi~~QfUfW';IKWM:nn·• •)ti L . 'Y :&@ihMM JMW;/.V/ ;HtP•il·••wFA••M• t• /N,\; •• •: •m:•;•.NA!• ••top•; )'i;b H Wt•iil9lHii ;; •• •Jim\/F
PENTACHLORODIBENZODIOXIN (TOTAL) 58 J NA · 260 J NA NA 15 UJ 90 J 't300 J
~A¢M\PRQP@\;1@'§l¾Ji'§ftoof.4@i! t tt~ii! • Hill~ ii Wi4~ ii:•H Tiffi Ni¥ wk' i£ ;; ;w J; @ Diffeiiii + Xitiiii Jff
TEO (TOXIC EQUIV. VALUE, FROM I-TEF/89) NA , 130 NA NA ff J :97 J 1300 J
illrAA\';l@$iii$,9l!lgfgg.!ii§8!~aqf.~!1JW •; :NA FY' "*JHI .;; f,ieJ.;.•s;.t• .. W.J .uzm•~l\\WXI; '.@il • \t&if@t
TETRACHLORODIBENZOFURAN (TOTAL) 59 J NA ;f30 J NA NA ,· 36 J .-300 J 1600 J
13 of 18
-
------- -- - - - ------Section 2
Soil Sampling Investigation
GP047SLA
CHEMICAL
PIOXINS/E\JRANS
TABLE 2-3
SOIL SAMPLING SUMMARY -DIOXINS AND FURANS
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
GP047SLB GP048SLA GP048SLB GP048SLC GP049SLA GP049SLB GP049SLC
i@~@i!ir:~lti§!lf£gjl;q/ippj§§jggp\§x{~ rnn~~HMldliii!l~l h W&Wli ''311' <?/i><f6•.;.: ., . !AA F rl~F
1,2,3,4,6,7,8-HEPTACHLORODIBENZOFURAN 3000 NA 66
1i?)~;~!ii~lWE@!lI£gjl;fi~PPl!t~~Pfl!Ri!Rt:li!Jlfi '.> tn htmlililllli ffNA{IH rn; rnswwr
4.6 U 4.6 U 12
n~;!lut ·•·•·•·•·•·•·; fij:iii\iii ii; HK%DJJ 42 6
li:i0; L; ii!ii~iiii
1,2,3,4,7,8-HEXACHLORODIBENZODIOXIN 170 NA 12 4.6 U 4.6 U 4.5 U 3.1 J 4.6 U
li~fai4ii!ali1!¼¼<\i'it61:fol6iel!Ni6il'~@fr.·.·.·.·.·.•.c: ·Li n ¥Wit lrnMilX ••·•,• ¥ill ES? !OJDH•·•••••~••••••·••tkGiJtt:'T4:K\JX?§ iiiciiQi•••••;; N'¥Q@
1,2,3,6,7,8-HEXACHLORODIBENZODIOXIN 1700 NA 37 4.6 U 4.6 U ' 8.8 14
j;gfa:~i?i&B™¢BMiBiiii;ii~~iPi!ww!i ;;;;·•,•;q;; 1t1nrn ;;; NX iinnn li\ill'i ·;+· it~PA ;;;; ~w;vt " wtmli:;· Ttn@WPt
1,2,3,7,8,9-HEXACHLORODIBENZODIOXIN 460 NA 24 4.6 U 4.6 U 4.5 U , 9.1 4.6 U
i@~it;*lw8~§lll¼'IB¢Pilliifl~ilf'mW H!@Mii : 'NM ,, ;;;; AI?Q; Fl'l li;ailliU MiiiiilliDift!MiW¥ilUH@lNi%%iJ ;)iH.lll'.WU
4.6 U
1,2,3,7,8-PENTACHLORODIBENZODIOXIN 130 NA 4.7 U 4.6 U 4.6 U 4.5 U 4.7 U 4.6 U
1daiafi~iWAB'it:oRaoiilliiNzi:Mi!irwr·'· ·"•····· itdlf )F)fui;•t •••Ni'i ,i:iuut• •··••·'·""·'·'·'···••·u·1•.~.·.a ... ·•.••.v.· .. ·••n.• ·.,.i.t.• ,.·••·••·•'·•·•·•••·••.w .. · .. ,e .... ·••·:t·.·••1 ... ••·!·•·!·••·•·••··&·'•·'·••·••.•'·•··"·"·••·'··;5·······•·••·v·····•·•••·!··•·····•···;••••·•q;1·dt'. ti~fo;0i •···•···'-i•.i•.·•'··••! ..........•.. •.·•···•···•··• ·••···•·•···••········• ·••·•··•'········•··'· ....... ~ ..... . . . .. ·~ -· ·· · · -· , ., ·
2,3,4,6,7,8-HEXACHLORODIBENZOFURAN 150 NA 4,7 U 4.6 U 4.6 U 4.5 U 4.7 U ~~;4;f;~;#!l&l!~g:jgq#.!l\!illw~wl!iiiw! lH ; • • i+ ;:;U~WK rn ELNA+ £ ii •ifitiO f + We Uh ; ;; '. ;;;;~ ;s;;; ;: 4lci,) ;; @ffiii.it
4.6 U
@:@lij@fi
2,3,7,8-TETRACHLORODIBENZODIOXIN 13 NA 1.9 U 1.8 U 1.9 U 1.8 U %~ifiwr~fi'¼¢l!i~RRi~§l~l:Ji!ww!i@i,iWJI: W Mg ff@l;@It·"'·····•• n~··••.<;••·•·•••· MfoM@ < fr~µ/\ j;~lcn.•• · · ·11.:u ;;; • ~;~ lHiiffii;if#~i•ii 1.9 U 1.9 U
HEPTACHLORODIBENZODIOXIN (TOTAL) 54000 J. NA ' 2500 J 150 J 79 J 310 J 630 J 1 120 J •··•• •• •• •• •••• ,. • ••• . • ••• •••••• "•""<"" •¾•••-w.•,•••• ❖Y ., .. •· .... •· -•• ••••· -•• •••• ... • ·•· .-:❖:-::<>. •• :: ... :;,!;.'.;::::,<-:!:-;.:'.;::.., .• ,:..: •,•,•:•• .. ,, ..... , •· H~erMit!ii§JNP!!@\gR@!Mtltt9!MlI :,@ii&lib • HNAHR ·····:~@f:•: AAf!J~··· H•M/40~ ··.·.········Mvili,·· mrw r i,,@r.\JJi
HEXACHLORODIBENZODIOXI.N (TOTAL) 6500 J NA -290 J 12 UJ 41 J ·51 J . 90 J 16 UJ i;/l\l!Ao\K~oilotiisfuiioil~lfi:i'fAtii tit1 :1d> UJNA+#lUt+ tl/4Jlirn %%\4& w.+ @ ]iiiji iiu....... •• tiiV>'. T• '.s1; J· @till.;
OCTACHLORODIBENZODIOXIN 160000 NA '16000 460 650 '1500 · 4300 J 900
oiifr#cBtBiiooiat&za~• rnntm rnn m lL ,2rnmn1rnw.w ~rn;mm; wNww nn 1sitt< > MM' ; • a;,ru:~ ;; :; >n, :;; ;,;; 100; ;;; , ; @~~iww
PENTACHLORODIBENZODIOXIN (TOTAL) 960 J NA 23 J 4.6 UJ 5.9 UJ 4.5 UJ 16 UJ 4.6 UJ l!gm'¼,qtJtpWli@l!\~/:giffeiPilA~rr~i'f&\rrnrn;n ·;;;;: iii rnm~wirnrnrn ;wirnw;rnw n~~Wl t ;i;.uiaJ}r i,;;;fkiiJ£ ; ; ziui xv;;pJ·;•· ii#@~
860 NA 35 J 0.76 0.81 4.2 .11 J · 1.6.
281!lin • ,NA ,v, ;h wl!iJJ,' .;,r11cLc:t ilf!foivJfriAt#~iiiJi· r· Hbilt··· ;/iif!WM T~? IT?~'8I?~'Y.•Y~b~L~~8~};I:f(~?l., " , "' , JJ;:;IMm1.UOROR!.~9.P.!.O.xm.JtQJi!il1/f :,:,:,::::::
TETRACHLORODIBENZOFURAN (TOTAL) 860-!_, NA 2.2 UJ 1.8 UJ 1.9 UJ ·0.22 J ·38 J ~.95 J
14 of 18
-
---- -- ------- --- --Soction 2
Soll Sampling Investigation
TABLE 2-3
SOIL SAMPLING SUMMARY -DIOXINS AND FURANS
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
GPOSOSLA GP050SLB GP051SLA GP051SLB GP051SLC GP052SLA GP052SLB GP053SLA
CHEMICAL
PlOXINSIFURANS
1@~Al!iizi41t@er¾9l~QR9/;i\m;il?,®i2~@. v 1i 11iisot \ 11tni N% ; w tv~~mw :w+ 1~i/#Wlii itil:iiBt> >' >i~iiii;ii\> x : NAT >; , m\,.x
1:i:~:~;;:*tmi~1 x2AEB~i1i;l@.wiuwiw , , , , •j~i•ci > .~~ •• ;•. • • • • ::~ •• ; ••• ; •• ,. :.::.;,. ,+·< .:;i~n,.,v,,.:~: ~. . ........... :.;; .... ·+····· .;:;: ... / .
1,2,3,4,7,8-HEXACHLORODIBENZODIOXIN 4.4 U NA 48 11 4.7 U ·11 J NA 26
1!i#t¥Hl£1l~l/,@@tgl@ifii~i&i!&lMM +wittill•l t•t#lWi .>c:D.\ .•. ~~.,>, .. ·. ;,; .... ;,.,·fa~h, .. ;.·;. .. ,. , •. ,1,1;1.ir,, ;. .. ,.· !ti·v ......•.. : .. :;•f:¼ • • : : :.;M •
1,2,3,6,7,8-HEXACHLORODIBENZODIOXIN • 45 J NA 350 75 3.5 J 89 J NA 84
~'ii\#t\kMiii'J~tfilCqilqp/i@i/)QffflI@F ( &~v.h ; jffe·,.·.· ... ·.·.·.·.·.·.yh ii;• %%st ;; J;i;i:i;i····· 'iiaiiJ[.·\V friii\ L··Ji;ij>
1,2,3,7,8,9-HEXACHLORODIBENZODIOXIN 10 NA 100 29 4.7 U 32 NA 21
j@s/tia;ii}BEU,c/:lilOl@iOIE!i;Ntol\)l:Wi!'li:il:Ei.•iW•• •: B:,.K::• ¥F%!4:4JlJ!l..#• nd•NA : rn::•.t:.:t: :1s:ui::•••Hkl••%nu:)h#:t:b:.il7i:JJ#:K.:?F :•;S!i>•Ull •hlW: ::•:fflfffff:% •••:l:ti!iiF.\IM
1,2,3,7,8·PENTACHLORODIBENZODIOXIN 4.4 U NA ·31 7.9 4.7 U ·6.7 J NA '5.6
i;g;&,,~\R!!NTAcat&lci6ial!!'lzo1,m;i tr ,•.•·· ···· ..... ·.·. di\iii.i Aililin;ibJ+ ~N ·:r ;:~?··:za:,; fr;; ii!~fa:ui,, lil !i~Im a; wi;ifoiin; :i;~i$11
2,3,4,6,7,8-HEXACHLORODIBENZOFURAN 3.8 J NA 17 '6.1 4.7 U 5.3 J NA -8
:b;;m:MM!mA®toRooiMNtoitiliRAfl rnu, n •7 •mrn1u11:rn ,•;ii'le; :;;;z :;;; ; #fiii : ;;¥tM<:.:;2;.:;ta;rn;::~:;;::::w;;;::;;;;: IIM¥Irn
2,3,7,8-TETRACHLORODIBENZODIOXIN 1.8 U NA '8.4 '2.1 1.9 U 11 U NA 4 U zi;}\)!lif~f/ll@iB~miJM~!®iPfffl)il!iH El : L ; g; l!l@iil :' ;'; HiiJi(l I PY if!•'.} ;;; :;;;s;;;;; 7 ; ;oiis;J ; ;; ii: ;;;; ;7;'.,NA : '. T '.,;;;;;s;
HEPTACHLORODIBENZODIOXIN (TOTAL) '980 J NA 61000 J 1300 J 140 J 3800 J NA · 1900 J .•.•.•.,.;.:.;.:.,.;.•.;.:•:C❖:❖:-:-:❖):❖:-:-:-:-:❖:~❖C-:•:❖X•!•:•:❖:•!•:•!•!•:•:•:❖:•:•:-:❖:-:-:-:-:-:❖:❖>:❖:❖:❖:•:•:•:•:•:::,;-;.;.;.;.;.;.. .-...•.•,,,;-:;:❖!•'''•'•''•"~•' •'•'•!❖ ••••• _,. ••• .·.·.·.·.·.••.•.•.·.·.·.•.·.•.·.•.·.•.·.•.·.•.i, .. 9 ...• 0 ... ;.• .. •.=ti .. :: •. •.•.'.•.·.··.•.=:.::: '•'•"''•'❖"•>"·' ••• •··•• '❖'·"❖',,,-,.-;:;!;:;:;:;;:;:,:;:;:;:;!X!::::;: ,•,••:;~~;.;.• :;:;:;;:;:;:;:;:;:;:;:;:;:;:;:;:;:;: @er@fliiQ!'\QP.!!1!;!¢;Qfili!!i\i'!ITR!Af)l:t: ff#@iklt•i•••M:1!H•:Wt•?#i\. · v .,-· ·+fl!6@\h ::·14\°i:,e·::·:::::;:?~!Ut:; ·······NA. :·s6f/4•
7,~S~h.2~2P1.~~.~:2.Bisi.2.I~.rr. 2.r!~.1.,.. . ......................... 2.10J .... , NA H~~cHtoRol'Ji~ai?o8/8Af!ITQTAftt ........... ;.,. ;1ww w mm rnwv nm itHflAiH
1500 J r380 J 25 J 530 J NA 410 J rH1t~a11;1: i;H#d4 >·••:·:·>r1w>w:>·.·.···>.1i~·JF: Xiii\ :1 ~xm
OCTACHLORODIBENZODIOXIN 3700 J NA :24000 6400 1100 55000 J NA 11000
◊¢t@51i\$f:i.lmi~wQl(µiMft :-... , 1w r" : :wrnm' nniturn1n ;rn;mnn H:b1sl1!).n::;•••m.+t,Uiid ,:.-·••A2!i.L;•t:•:-:n2@\IP.:.::·:<·: i-lA·r:L .• '" ··:t~~At
PENTACHLORODIBENZODIOXIN (TOTAL) 17 UJ NA '200 J ,62 J 4.8 U 60 J NA :30 J
~i'itl'i¢1it¾BPPm~N¥&!\i://¾ijrrg'fX\iltif"'·'·''":''"•······· :rn~WT:i@:t:mifoi@ :· ,iisoiiJ;· ·iiti"i<> :in.wwtiJ/dd:#J)ijk t• \l:lli#k .;;;~$;ii;
I~?Q821S~9.~1YY!\#~:rn9M 1;I~E{I~I ......... w .w: ... !.1 .. / ................... ~.. . 160 . ·43 . ,·.2·2 . 95 J .NA. .. . .... 42J .. .
I!;IRAG!:!~9BQPl~;':91'JIQ~!!mmwn Si ;;:;.: :,;;;.; d!!'~i!+w+ •• \NA; ;t;.·.»;;,;.:;··:.:L··:; •58 :r.·,:·;;;. :;+.4,~;(JJ;;:;;:;:;;.;;;tiCJZi•+:rx·•NAt:p ·•;;.;;: :;rnmfH#
TETRACHLORODIBENZOFURAN (TOTAL) . 23 J NA 150 J ' 76 J 0.35 J .50 J NA
15 of 18
-
-- ----- - - - - ---- --Section2
SoU Sampling Investigation
CHEMICAL
PIOXINS/FURANS
1,2,3,4,6, 7 ,8-HEPTACHLORODIBENZOFURAN
1fa;&~11;Wi#1f1€iir/4mit&RQ51sll~oiit.1~n / ;
1,2,3,4, 7,8-HEXACHLORODIBENZODIOXIN
{;i@\tz;m!ll~xbitiilii®Pl$lmfli!mIHH
1,2,3,6, 7 ,8-HEXACHLORODIBENZODIOXIN
iii~)~;~;i;fili!i~pjijgqijqqj~§'li&tm . • n
GP053SLB
TABLE 2-3
SOIL SAMPLING SUMMARY -DIOXINS AND FURANS
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
GP053SLC GP054SLA GP054SLB GP054SLC GP055SLA GP055SLB GP056SLA
55 4.6 U 80 J NA NA NA NA 4.8 U
ffii{;@omtrntlks'.Wi \,c •~A:ur;rn:;;i%: \'.; £:Nkt N/4E o ;~; fifaip;;
4.9 U 4.6 U 11 J NA NA NA NA 4.8 U
it~Ii!TF m~l~ilf··· Eii~;~;i;i ;,··•·••iiii&\i ;s JAAH i!H ; f.¼'Hi •·.·.·.,·.·.·.·.·.·.·.·•·••!'IA··•··•··•··•··•·•• ti!i@!P
7.1 4.6 U 63 J NA NA NA NA 7.9
:r··•·•·:••· I!iJillI i#iiiv········· IPK~fi! ?;HNXF?? T .·.··•NA·;·······.·· .•. · .•.• ~··;&k.••:r;;:;;M;;... Alim
1,2,3,7,8,9-HEXACHLORODIBENZODIOXIN 5,3 4.6 U 28 NA NA NA NA 4.8 U 1,1;~;1;~;!lwgl\e.l;8~@R!~~2ii&illl!!ilm!I }r· i , ;1rnu. rrn@WI'l!\ll@mrn ;· · .... :•:·i;·ukiH, MHfJA-W : I FY¥@? ;Iqq; i½ '.?'.{E '.;WC ..... <: nrnror
1,2,3,7,8-PENTACHLORODIBENZODIOXIN 4.9 U 4.6 U ' 6.2 J NA NA NA NA 4.8 U
jig:3(',j(~iREITTACH~OOli\!$HzoliililwiiMi)t ;:+ PP@'I)@iJHllM \iilJ;Unrnr;;c;;¥¥4 ·················••i&A)<<.i/ 'AA + ' wC; , vw;< 'a L -<c1l.JJ
2,3,4,6,7,8-HEXACHLORODIBENZOFURAN 4.9 U 4.6 U ,4,7 J NA NA NA NA 4.8 U
ihlliiiiiiM!l/#4?i@$Rq¢\miiiPF~Vii!fii!\l@!I ,L ; t;M;Wrni'l il!ll@Mi rnni~&!Jtt· It@@ ·.·.·.•.· .. , JiKL: ··••N1L••··························•·········••Nk•• ,.......... UMDH
2 U 1.9 U • 0.65 J NA NA NA NA 1.9 U
;r:-0AiJ: +••nntFHi:M,XHi#trM;1wi,@:H,UHRWEV • ™'·••••::< •·NA••••7••• ....... NA.,••• •• •"•·•11ite1.•Jr•
2,3,7,8-TETRACHLORODIBENZODIOXIN
%1:iit1i~ii!Ai:iBQ9!%i:ltiiij§'lt&ifQMN f "
HEPTACHLORODIBENZODIOXIN (TOTAL) 640 J • 39 J 2100 J NA NA NA NA ·140 J
ffi§!l[AQ®QRQQj~g/!g9B!!'½~ffQ!A!MMrn W:fft i@iliit@i'tiiiJ:iir ji,iiµii'.iii .. ~~MP ..•. ·.·.·•············•w,;•·•···>·· ii'.H@<i+· '\Jl,{ Y•·•··••':n•:Jlmi;;;';; J:MJi4
HH·.·.·.· .. ··.~.'.'.•.·.·.·.·.·.,.·.·.·.•.··.E.·.•.·.·.·.HH •..•. •.•.'.·.: ....... ·.·oo· .. ···•·.·.·aR.·.·.·.•.·.oo.· .. '.·.•.·.Do·.·.·.·.· .. 11 ••. BB •..•..•. ·.L.·.·.· .. N .... •.·.• .. zz··.•.·.oo·.·.·.•.·.·.·.E.•.·.••.·ul.·.o.·.·.".·.·.x·.·•.,·.•.·.: ..• ·.N·· .... •.••.• .... • .... ·.£.• •. ·.• .. ·.·.2 ...... •.· ... •.r .... ·.' .. •.t.•.· .. ···.L ... ·.·•.!.• •. ·,•.•.·.. . • .. • ..... ~1···J··········. 16 UJ ..... , ...... ,i:io.J .... .,., ........... , . ., ... NJ\ ..... ,.... NA ······~· .... ········'··········· ,t-11\ ........ ···•· ·····•·•···'Jt./ ... . =~ ~ = ~. ~• ,,u-~, :MH:tli!.lt· •'.H".$iJ®k :#:::tlmt:tfrKA•::fJ\liiiMW, ./\NA<. ••••N/\••:;x>:c•· \NA ,..,. ••••;JVtt/J
OCTACHLORODIBENZODIOXIN 3900 340 J , 14000 NA NA
PENTACHLORODIBENZODIOXIN (TOTAL)
i!il"i'fiJZmmslilimlt&iai\01¥Aij&gfsiliM
6.4 UJ 4.6 UJ 30 J NA
.·.·.·.·•·•••••••;>'.'..• i!.iiun iMi\li\xrn: , diiiiii " .•.... NN ..•.. ,.;
11 UJ
%~~Ji
NA NA NA
fJfw; •;a•• :;);NA>•• •••·•·••••·•••••NAY
i~ilt~ii1&~iiii~i!cii11% 7.9' •. ,.. tH:~;~:~tt~!:~;~~t~HMI 0.34 J
iii;~§
.39 J it"i?' NA NA NA NA .2.1 Ht NA: :; ····· /!¾fr ;; W1ii,; t,N&, • ; @~atJJ
TETRACHLORODIBENZOFURAN (TOTAL) 0.42 J 1.9 UJ 39 J NA NA NA NA '.0.16 J
16 of 18
-
-.. - -- - -- - --·--- -- --Section 2
Soil Sampling lnvestlgatlon
GP201SLA
CHEMICAL
PIOXINS/FURANS
TABLE 2-3
SOIL SAMPLING SUMMARY -DIOXINS AND FURANS
GEORGIA-PACIFIC SITE
GP201SLA
(Dupllcate)
PLYMOUTH, NORTH CAROLINA
GP202SLA GP202SLA
(Resample)
GP203SLA GP204SL.A GP205SLA GP206SL.A
1~:?l~Ji:z:i1ii.iii/2i1iPRQQ!?§tg@!Q*(llt !0 nmr IM!lflHi!il t;i/JGJ!!!ff 39!4iUl;; .. ,r ;;NR;7;;;;;;::1hf /\. lFIJiiiriltiti1!/fr51i@idHNfaiM)
1,2,3,4,6,7,8-HEPTACHLORODIBENZOFURAN 11 J 4.6 U 6.4 U NA 8.9 U 9.9 U 17 J 4.6 U ti~i~:\i:1;~:~iii~ifri\iligf:iQQ\~gtggfgR,f\!:/ji ;;;)£ . : : Ilill jg)/! ili Ui!fi~ili ;/\! lfaj\~ !J • ' < &ii@ t lJ~ !'! ~\~'.µ ji , , %\i'H ;, 24'.KQ
12 U 4.8 U 4.9 U NA 4.6 U 4.9 U 6.2 U 4.8 U
t l'HHiqn •,#iiiBn t:JMMH ihlHA /t:· !flf!)\ XA,lliiL : ... :.;;a.:.a.:. ii,Ml!ii
1,2,3.4, 7 ,8-HEXACHLORODIBENZODIOXIN
1fi)t#Wl/½Hii&itiBUQi\0RlilwMlt\U&W
6.6 J 4.8 U 4.9 U NA 4.8 U 4.9 U 13 J 6.3 U
•• ff)~µ Hi\\®IU !Hi¼'·•· iiwki:!lditff,(@u:rn •n+~lliod '.<'§Tf/3 rn@!ilUid 1,2,3,6, 7 ,8-HEXACHLORODIBENZODIOXIN
1l~M;;fl&illi~Pti4®!6Riijaifi:iiiiJ@JlH
7.8 4.8 U 4.9 U NA 4.6 U 4.9 U 11 6.9 ••,•H,•o••«n••••••••••••••• ••••••-•.-.-,•.•.-••••••••••-••••• •, ... NNN,•,•••••':❖••• "❖'"'"" ••,v,••• •,••••••••• ••••••OoH••• •••• ••••• • •• • •••• •• • • W
U#J2'UR• , ff!Wl•PRiT•t• Plf\illlk .......... •\NA+pib; •f;llJ\iR}F MT'iltii'.UR'F Hll,i!flJkf •rn~!!UJg
1,2,3, 7 ,8,9-HEXACHLORODIBENZODIOXIN
i&:&¥.i~!!iiliiiBiABilliIB!lBB:ig~z&ii~ \tkk rnn f
1,2,3,7,8-PENTACHLORODIBENZODIOXIN 12 U 4.8 U 4.9 U NA 10 4.9 U 4.7 U 4.8 U 'i##fiWi#Ei$-)(a:l/iBRaol~oifvlw! Lt ,frw,n; 7li%lllk@P,faifo(u!t l IV+:~llik NAii/ ;;;; AiiiPii; rntm~i#tii#&mfo~HHJiib;· Z;'Awelli~
2,3,4,6,7,8-HEXACHLORODIBENZOFURAN 12 U 4.8 U 4.9 U NA 4.6 U 4.9 U 4.7 U 4.8 U
g~~l~li\~\i:iiil0.%BRiw9Ql!Wfgpfm ········•··· ;;}•·•·····•·•· j;/Qff l#Ji)ll m wM@liMDi NA ;.; 'k~D F Hi!rn!JJl falilfoil#WllliHl, ll\ #;~µt
4.9 U 1.9 U 1.9 U NA 0.21 J . 0.21 J '0.58 J 1.9 U
• 111,iwt t•I:/%4• • rn• H#;J/!Q •mm: : • Ni l ff •ttt)(~q;'. • •ji\!£ :'·fainw.tii!H ff :: · u.u
B~xi@i§;~~~~~;;&i§t.il:1 nt~~+ ················'.tjj;t;Jt ~~~~ti •H ~t :::.~:~g;, t:~.;; ••ii(i;,;~;i.~ i i··i•~j••ili••:
~.~S~.\:8~8.9.1.~.7~.if.2819*:~ .. IT.8.I.tbL.. .. . . ....... ..... ..~t.r...... }H,_f p J . NA.......... 4.0 J . . • 53 J . .. 88 J He~§BLOROPIJlElolZQF\/RANIT◊TAtft nr ········ ··•····· HiltUJM. f\]i!HJJ +•rn•@l'm ::;; :nAAn:;:· :r::-::;atpJ\ .g1s:wx:; •trn tti$lQW
2,3,7,8-TETRACHLORODIBENZODIOXIN
iii:iifiirriiA\:iill;®li:iiiii~iiii~n
OCTACHLORODIBENZODIOXIN (3500 J ·4100 J 1400 NA 2000 J , 7600 J 27000 . 26000
6¢fA&lL&ll65ll!€/,iid/i/J@Jl nn@nn ff i-iiiii ;rn; l'I~$!0WWJrnnnrn~Rlfi NA ;; Zibi;i£DF iff!H!&HMH : @•: • ;; L ?.$9}
PENTACHLORODIBENZODIOXIN (TOTAL) 12 UJ 5 UJ 4.9 UJ NA 87 J 4.9 UJ 19 UJ 8 UJ pgfgg~81(qfigpj~~&£®iiliri½NrrRT.M} H MtHlhiilF ·••.•·; Hjjg wmrrn HH~lli lim j@ i@jjQJ1 ;;;,'; ;&,, nm i!il~ wHlI ill li\i\l®iilMEIMI~J~;J kill ; ''··,1.11· W
6.8 J 5.2 J . 2.3 NA .. 8.3 J 12 J 36 30 ifk~Iwi .. ,, sicitiili ................ @J?I!® ·.,, .• ,•;m .... ,,khgf21!dii/ iiliii 7'\if?!I ' ,izii'iii~ TEQ (TOXIC EQUIV. VALUE, FROM I-TEF/89)
fijfi¾mN6'ilPOil@g§p/§!wi/ff.&ii\M n:···
TETRACHLORODIBENZOFURAN (TOTAL) 9.2 J •9 J NA 5.9 J :·10 J 17 J 3.9 J
17 of 18
-
--- - - -- - - --------Section 2
Soll Sampling Investigation
GP207SLA
CHEMICAL
PIOXINS/FllRANS
TABLE 2-3
SOIL SAMPLING SUMMARY • DIOXINS AND FURANS
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
GP208SLA GP209SLA GP210SLA GP211SLA GP212SLA GP213SLA GP214SLA
iF•a\fijiii iiEiii'iicll!MlROOiseNiooloxiN ·.······.··.··.".····.· ·······••m••·······•·"'·• l.·••.t.@:.·• .. t.400.··.··.·.··.··.\m.... ti. @~E.·• .· .. · .. · .. ·••·.·········· tfa.2.a.··.·· .. ••··;·rn .. •• .. t.t.i.l.• ii.ii.·. ;ii•··•·• >·•·••iao ....... . • .. 6 .... d, . .; .. ; .. ;, .......... i ............. .; .. , ..•............. ,.-.•···•···.;· ... .'. ..... .-. . . .. . .. . . . . . . . . . . • ... . . . .
1,2.3,4,6,7,8·HEPTACHLORODIBENZOFURAN 14 J :11 J 47 J 6.3 U 5.9 U '18 J 4.8 U 5.1 U !!~l%~\%~l%~m~&PR99!li.ig!iifQw/lH •· .. .. :iifa4 i;i .... =' ili0flr Rll II U\l& wnrn;rn; l:4\?Ii;JJ[I! lti :l~ll! w Hi >':4:1 •u ;. .. .. ; .. ; ... ;)q i;i;;. :'.t&¼h
5~U UU 4•U UU UU ~9U
&@J!J .... "'· ;t:tQ ~ 1; Wi\.l >> ; AdY ; ;:;,¥\ii ..... · ;i;iiQH 1,2,3,4,7,8-HEXACHLORODIBENZODIOXIN ......................... •.•.·.·.·. 3.2 U 4.7 U il~l~~#ltlmBglih¢Bi@!i§Qlijl\Ht!@lmirnm .... . ....... ,.,, Ii•I~l@XE % ki/5Q!MHU
1.2,3,6,7,8-HEXACHLORODIBENZODIOXIN t;t~:~@tB~tBtooootll~i:difmm ..................... '······· ........... . 7.1 J 5.7 U 10 J
1 @All• ·.·,·mi [e-mail] ·· Wil!t
UU UU ~1U UU
~;1n;1 ibbit;1ii!Plhi.. iHWWffti Wi@\'.I.. .
4.9 U
•ia¥Mi
1,2,3, 7 ,8,9-HEXACHLORODIBENZODIOXIN
i'.[iillzli:i@~fltl@ilfilfill~ftl€ii'ilill!ll!i
12 7.6 9.4 4.7 U 4.9 U
flit H@iI/1'§++ MMltlffi/EIH tiiWDfiTF iiidhih iiii iigiJifo
5.6 U 4.8 U 4.9 U @diufii i!P,+;~;iiR/... f/4(\jQ~ ..
1.2,3, 7,8-PENT ACHLORODIBENZODIOXIN
i#lill?ill\R§ITTA½i'l!@B.99!&2€m;;rn
2AU UU 4~U UU ~9U UU 4~U
t?:¾PRMill liiii':!18.H ..... @f'.!li!.iRlf foiwuiifrfrdlil~!Qf;JI niiifrtii;ii#Hii!i,uuR•
4.9 U ·•@iifoi
2,3,4,6,7,8-HEXACHLORODIBENZOFURAN 2A U 4.7 U 4.8 U 4.7 U 4.9 U 4.7 U 4.8 U 4.9 U tt~@l~\tlgiif~iwt&Rs:iillli\l,\1/¾jf\i/;Mifall! ·arn .... lHW ltiWBtMrnmmwwonm @%ti@; i iiijj(;'. :\ ti@4dii ,nw:vo .... ·.·} ... · '·•·'4,/l .. ·•U········• ... ·.·.:•······ <ii{yj\jff
2,3,7,8-TETRACHLORODIBENZODIOXIN 1 U 1.9 U 8.1 0.11 J •'0.13 J 0.69 J 1.9 U 1.9 U
iiYMi~iiit@iilit61l6Bia€Ni6i!UiwF' ·.•••.• ... •····•·1·• ... i.h.• .......... !fu ................ , .••.••. l.l.l .••.••. ,.· ... •·•·'· .. ·•·t·••.\ ...... l.\i ........... b ............ l.l.•·.I.l.I.·•·'·'··•·;·•·· ... , .••. l.\ ... ·.• .• ~.·· .......... u.·· ........................................ ,.l.1 ..... \.!!.· ... •···•·u·•··· ........ ' · ·•.••.•••.•·.i.t.-... il.'.'.u.· ... :.··•·••.r .•. l ................ ; .• •.•······•·;··•·1.·.:.~.·.•··'·b·••.·. -:!ill u : ', • •.••.••.•. l.•.•·········;· ... · •. ·\i· .... · .. •·.f.b.'.".l .••..••.• ,.,.,. .................... · .. ··•·· .................................................... .,.... . .. " . ' ..
HEPTACHLORODIBENZODIOXIN (TOTAL) 400 J 740 J 650 J :310 J 450 J 1200 J ( 89 J . 530 J lil~Ri:~i!fi@filrifilml\~fgqmR!i1lrrgf/4lil ;;;; ;;;; ...... +.. i;+~@i '''iii.ii$'. ii;/11Wiii t ii:lilwH rn~@m~ .. vt·t;r~;;; :?wflu· !@0ii
HEXACHLORODiBENZODIOXIN(TOTAL) 87 J 83 J 99 J '32 J 53 J 88 J 14 UJ 59 J
/:l~2illt6ii66l!HffizBtuAAllwBfMl" u •lmrn~@i.ilH.ll WH1¾l:@H.li +M9"Jt > <i'1·w• ............. ;w11umt I ;; ;i;0;;; Xdii,a;;;:;•;; ... • ... •.•• .... ·••.1.••.·•.r.·••.1•.•·.ll .... ·•··l·u·•·· .. · .. J.· ... ·••·••·· ..... . ' • . .. . .................... ..-,, .......... ,+ . . .. . . ....... .. . . . . ... .. ....... .,... ... ~ ......... ' ...................................... +.... .... .. . . . . . . . . .-..... . . . .. .
OCTACHLORODIBENZODIOXIN , 11000 J C 15000 J ·9000 J ·12000 J . 13000 '.8200 (820 \11000 J se..t4®ii6JlBiile€fi&i\GlwHml ", .. , .. ,? •• •++n rn+®rcii•iWW ;r:aii1r: n .. t•SffiL.b• xz.... 1il)J;;.. ;,;;;nniu;x .... : .. 71wx .. , .. <,.,116·:tL ... t+i•••d~lfur
PENTACHLORODIBENZODIOXIN (TOTAL) 11 UJ 14 UJ 19 UJ 4.7 UJ 6.9 UJ 9 UJ 4.8 UJ 4.9 UJ li#Hi~$i'it¾il'i~~igi%1Jw/Mrr&f&&m1m•• nm • Mffi&iH•m • •• sWJJ •@s~ iJii) • irn• (4\tUJ••rn w;wswmnm:i&fa\11\liadl g .. ifitiil~ Wl • l,ni!l)J
·11 J :19 J \23 J '{5 J ·. 15 .12 ,1.2 13 J
fi1;@iii'fahfr@liiifrb:L l M@tmnrn ~ii#itfa mlP43iift #JJ;~l!fa;. '";{,iiq;i, • ti1iiiuµ••·
~14 J 8.5 J '
.5 J 1.9 UJ · 6.1 .J · 4.8 J 3.1 UJ _8 J
18 of 18
-
---
CHEMICAL
ALUMINUM
ANTIMONY
ARSENIC
BARIUM
BERYLLIUM
CADMIUM
CALCIUM
CHROMIUM
COBALT
COPPER
IRON
LEAD
MAGNESIUM
MANGANESE
NICKEL
POTASSIUM
SELENIUM
SILVER
-
SODIUM _
TOTAL MERCURY
VANADIUM , 0"
ZINC
---- - - ----
GP001SLA
Data Qualifiers·
GP001SLB
(Duplicate)
TABLE 2-4
SOIL SAMPLING SUMMARY -INORGANICS
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
GP002SLA GP002SLB GP003SLA GP003SLB
U = Material was analyzed but not detected. The number is the minimum quantitation limit
NA = Not analyzed.
J = Estimated value
Concentrations presented in mg/kg
----
GP004SLA
Section 2
Soll Sampling Investigation
GP004SLB
1 of 18
-
---- --- ---- --- ---- -
Section 2
CHEMICAL
ALUMINUM
ANTIMONY
ARSENIC ·
BARIUM
BERYLLIUM
CADMIUM
CALCIUM
CHROMIUM
COBALT
COPPER
IRON
LEAD
MAGNESIUrvl
MANGANESE
NICKEL
POTASSIUM
SELENIUM
SILVER
SODIUM
TOTAL MERCURY
VANADIUM
ZINC
GP00SSLA GP00SSLB
TABLE 2-4
SOIL SAMPLING SUMMARY -INORGANICS
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
GP00BSLA GP00BSLB GP007SLA GP007SLA
(Duplicate)
GP007SLB
Soil Sampling Investigation
GP007SLB
(Duplicate)
~!QQ:.~~--~tY::L:: {~?99.· }-.'.~ ~-:..~:-;: ~~q,r0:~:f::::~h:t1§Q§QS?:,J~;:;~~-~Q(>}?J~i~·??V:~so~.~·-~~~Y~'. :i1:[~:·11Q :: ;~:· ; '.". j~~ :,;)iOJ) :,, .. :
0.76 UR 1.1 U 1.1 U 1.1 U 1.1 U 1.1 U 1.2 U 1.2 U
. ~:.! ~J~J~l.:.; __ :_, ·. ___ q~~9 q: -~-.-•,.':·. '.~.:-.. ~-JJ~~~~~~-=~ti:t:.-f~•i:-".!&t:·t/:-.. ~::1~~~~~'.; ~:L?.it/t_;t--..t? :,~•i<f -~-!1 ... ~t. ~ -7i_~-:.: ,:!l]4_ .W _: w u ~ n n ~ a2 14
· o,M .. :I. ::i:f ':: °Q.Ii u ::i , , · .□:'?.·t·!d.'9?t\ ::· :r,::Q<'f!:-t~', QifQc':·i:t ;Jf22;· o: t :::-: -~□--~4 IJ> . :'.:' J~ :u
0.18 U 0.21 U 0.22 U 0.22 U 0.22 U 0.22 U 0.24 U 0.23 U
---.;~pQ ~ . ·:; .. _·;::-~ f?:¢.O~.-~,; __ ~ ____ : . fiJPQ.< --~::-::~~i{~i{tQ9/it;.f;.;-iJ::-~'.1.~q-~~Ai1~:~:1~~~~~(~i?iQ.··'..t~~;::~.f:_.;j4~ _; .. :-;:~~:::.-. iBq .·f. ·
2.6 7 3.4 8.5 5.1 4.5 1.5 J 1.8 J oJt_\:J ,_: : \ : 2 ·J.' -,:f,~;i::c~~' '/:'1_.J[.,{'{jJ/,:,:•JlfiJ.i:\tt?'.fd l · 3 Ji:.Q,4a D •; .. < .o.fii j
6.1 J 9.4 3.9 J 5.2 J 4.2 J 4.5 J 2.2 J 2.7 J
. 36Q.O :f ". ·.' 4!JOQ : .; .: .. ' ifp.o.~1; i,:02 .. i§Q9; ':i ;~1;;iieJ'.J§91! j}S:l:!"?ZQQ ."::~'./·,;;;,';!.PO .. ~ :: .i'. /.tijp. :, •.
7 J 5.2 J 7 J 15 J 17 J 19 J 1.4 J 1.4 J
's"oo __ , , ._ tii@. :·:,: · .. 27-q .. ·';:·-~·;{ ')111 > \V;.;;;!;~}q~f:~"?i i:~l!;.•,.-:':'"_;,.'.if-',.:· · .. ":.· ·_-131_
67 120 81 78 87 79 3.1 J 4.8
C!:~~--J-.-:-.~--~-, ·.:~ ~-:-.~./-.,._.~•::~;_?·/~ ·\)t~·,-·.:ij~--~-•:1t~'.t-~~/j~_F1/\!?:.!:~>:~;0'~ ~~~:.T)"~··'':"'·:•-; ·-,(_.t1.U .1 ~,
760 800 J 200 J 190 J 200 J 170 J 25 J 37 J o:t§ 11. ·: . ·· ·f.J Q <,~., . . · .. 1 jj,( :":·:;.•:.,,'-;:3 ;1;jf1:L1i:::'i;1J:.P11.t·/:, ,~J_) :~ .: , "-.~, C::1.t!! .. _ , · t:.1,2 fJ ;
0.31 U 0.43 U 0.45 U 0.45 U 0.43 U 0.44 U 0.48 U 0.47 U ::'BO ~.:· · ··. · 1QQ Y. . : ,fQ .l:!. >::\,XJ.§g g-., :7;t;}7J!l''.['r ,·;;_ :~·)]: q,;· , , .'.'?Cl lJ. : ·: '·. '"i;o u .
0.1 U 0.1 U 0.1 U 0.11 U 0.1 U 0.11 U 0.12 U 0.11 U ... ·. ~-l·i-LJ-~-~·;\=··: :,_ ~~,>.~)./I::, j ::;~~7 ~ -~r::0<~/f,Jf ::?~:t,tj!f/2.·;~-:i:-Q;~<iif•j.~•f.t~i~<-·~r ;~1:·,~::·1!·/:· .. J •• :: •• •• / -~~t .. J:_·
18 J 19 17 J 19 J 19 J 18 J 4.6 J 4.3 J
2 of 18
--- -
CHEMICAL
ALUMINUM.
ANTIMONY
ARSENIC
BARIUM
BERYLLIUM
CADMIUM
CALCIUM
CHROMIUM
COBALT
COPPER
IRON
LEAD
MAGNESIUM
MANGANESE
NICKEL
POTASSIUM
SlcLENIUM
SILVER
SODIUM
TOTAL MERCURY
VANADIUl\1
ZINC
-- - - - - - - - - -
TABLE 2-4
SOIL SAMPLING SUMMARY -INORGANICS
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
~ - - -
Section 2
Soll Sampling Investigation
GP00BSLA GP00BSLB GP009SLA GP009SLB GP010SLA GP010SLB GP011SLA GP012SLA
_;_.~~p_q/. ?J:it:~ ~ : ~§.QQ. ;.;-~-: .. ~.:}-i·.~:•l~'l9-~li~E.,]~:i 1.l!tff ~.j!' ~1: ·;:; ::~fl>~2r2I~3I! ~fQQiJll&J~iii7~1QQ;:f'f~.~~;{~ 3.~gq ~ · · .
1.1 U 1.3 U 1 U 1.6 U 0.67 UR 0.67 UR 1.1 U 1.1 U
. :t::<·s!§•; ±/\.; .... -: / ···.: 'l!i :-~·.--: --~(-: t~I}J~; .. f:· :::<~f~{J/:f\t·1t~~:~]/;l~}~!.:.};/~, _,: ¾\:~:~~\\-. '-{~/\ -~t§1:JT: ~.:.r-~<-_ o:§? u u ~ a2 ~ a a 21 21
;Jli21J.!d: ,,\ , : ii]~ ~ ,, . · . -sr_~1 Qi ,:. \._-,:,~~;Q:,.:·,};;c ;;"[If"}J;~,j-<-;;:·/~:If/Jf/(.' :. 021' 1.F,:,' / ~ 9..:H \,J •
0.22 U 0.26 U 0.21 U 0.33 U 0.16 U 0.16 U 0.21 U 0.21 U · 'ao_iio_;: . . : :{stiq ·· . Jig,j,.,,.,:a:; .: 34.0.!Jhi,,~= : · --·~}'ifgj:~tc,~,1,,,,,.--,.iioo , Jt2t;>1sgq•,,1 :\::::-: 1600 , .
5.4 3,3 2,3 2.4 J 13 3,6 3.4 4,2 · .f.f··J._ ~-·:-~ _ !:§ ~(;:.r::~ _cr2~ __ ;[:2 ~·•:· .•?J:~~;~('.~-;-::r· ·,~1g.s?~.tftl~~~J.:i'7i_.:-g}~--YJi<_~r-~ ~::J:~ ·ii-r1.·.-?:·· 2.? J.
6.7 8.2 2.8 J 5.6 J 5 J 2 UJ 7.5 5.3
. ~~!iil .: : J~tlo.. :: ' :'·. ~ i@Q: \,~ ·.:: .2p§g;.;k. ;t·t,:<-:@QIE;f'.t:.:::::f:2.1tlti. L~~:;, "j4go_ ~::: '.'.,_jigo
17 J 14 J 2.9 J 5,6 J 42 J 5.5 J 6.4 J 6,5 J
_fisii __ ·: .19-f,:."· _ , ;;[q::-.: ·-·:.stq;::. ;:;:-__ -;M1P1;>;:::.:..-.1~6-,;_:-'ci 11.00 ::.:-' ,., 1<100
100 100 59 64 52 32 210 180
_:-3 ~-.· _.:.;~tft -~ ·~_-:,..· ~-....... ,~--J/:;;;":·:·•.'(~t[il~/;~?;:~:-~,---Q.t~ 4•/·~t~?:-:..:~~-4-fl:·_;~-/-~-. ___ 4 u
390 J 160 J 370 J 270 J 410 120 1600 J 1300 J
~_-ij l,h' . Jfj j.i{,; ; \' _::· ;J Q~: ;'),: ::Jf]J.;.,,,,fj,,,:::Y!i?:t1F~1:°.\; .Q,'.[4 Pi,;.;:_ -JiJ.it~ ,_;, -•-~ 1 _1_ u
Q«U o.~u o~u o~u QVU QVU o~u o~u
k. ·12Q:~·-·. ,'.·_. : -~_-jQQ _Q>:_·; ·_;. :7:-. : __ (§1FQ~:,:·::i::i:;~_.:__))Q.J.f:,fi~ -~~~~:fR£Q::2-;r;;.1:;j~i~tQ]:t_f:~?.;J;I?Q.J:( ~:::~ __ :·:· .:!19 .!d
0.11 U 0.13 U 0.1 U 0.17 U 0.1 U 0.05 U 0.11 U 0.1 U -----~:~-ft-) . ;-:-:'~,: :~i :~-sf3\q:::~~::i:r:~·-,:tt~5D¼E%~}.··:: -~_tf:i~:Erlf-'~~r;~~11IIrt;~1-\.:~r t1:Jr-Jjt,;:_:::~-,.~r~-~."ii.-\!f:~}: :{;~~ ::~ ,11 :·_
23 J 20 J 10 J 26 J 26 J 9,1 J 27 28
3 of 18
----
CHEMICAL
ALUMINUM
ANTIMONY
ARSENIC
BARIUM
BERY~LIUM
CADMIUM
CALCIUM
CHROMIUM
COBALT
COPPER
IRON
LEAD
MAGNESIUM
MANGANESE
NICKEL
POTASSIUM
SELENIUM
SILVER
SODIUM
TOTAL MERCURY
VANADIUM
ZINC
-- - -- - - - - - -
TABLE 2-4
SOIL SAMPLING SUMMARY -INORGANICS
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
-- -
Section 2
Soll Sampling Investigation
GP013SLA GP013SLB GP015SLA GP015SLB GP016SLA GP016SLB GP017SLA GP017SLA
(Duplicate)
·::t;;gq_g /r:\?, ~.~ -.. , _ .. ~P<iq · _ : · ·;; · -~ ljQQ:~iii·, __ -<t-~i:1 ~JqQ±~. j£~{ ·:-:·;g~9pr~WJi~Ir:~9q: -·~?~; ;,"~\\. 49fJ...irJ~ t~;~---s:~~ ~o."<!. ;, i
1.1 U 1.1 U 1.1 U 1.2 U 1.1 U 1.1 U 0.66 UR 0.57 UR \ tt '!: , __ · , .'.:-:1_.§_ · · : _-: -!.~.:: '.,~~;::,_: :'{Q~~~ )~--· .. /<~.:.~:\:1 t~1fJ~:~~rf.~·>.~-~~-:V-~\.:·_~ ,:~: : 11' .1•; -~-:: r _·,i:-· 21 . ·
31 27 69 23 54 26 46 83 -Ht·,':. __ ;ju . _ -~1·\J>. : '·"1i~~)i.:. : ·•:TfUi;U:•· ''1'.iii :· ''0,1.1_:J ·::·"', _.:0.1:i J
0.23 U 0.22 U 0.23 0.23 U 0.22 U 0.21 U 0.16 U 0.14 U 1?.99 . )12_6. 110.QQ:.,<-:• ': .i~.-,,'c;. ''. Jt!io.it.it/ ) -~~Ii:{,; ~: _c3290 _::::i:.:-,::5_200
7.5 5.7 5.1 3.6 4.4 2.8 5.6 7.8
.1.1.J. -·1.tJ-)ii,·:_;_· ttd,· ,,,.:J:B:.Ji,;;<l,'1J::0)·8_/,"•.;·~.4•cJ:,·_·:-.-· _·3:1,1_
4.8 J 3.5 J 15 6.9 16 -5.2 J 11 J 19 J
6962 _ _ ~I/Qi:~ .-A~"kii.'.. . ·5s{!~-: ~'. ./'..f1g,g}~1:1~ c. ~5!1¢ .·.; ·,/. 61gij l 1oqq J
18 J 12 J 28 J 13 J 26 J 3.2 J 39 J 90 J jfQ. '!QQ .. . • ){OQ :, : -~~Q ''.. ~ ., ;_'j~Qf~·:t;~ __ ;-. 1!!0 ,.:-: (.; ; 9J2 ',, " '. !l~O .
100 56 220 50 150 79 170 250
· :\ tL ,. _:Ju. · '.' ?-,Q-):.; ;., -; ? Q _,'\ }'.f.:,1~l•ld:i,?~:t: ; C:) u :. \ :.f 1 J ·.: · -~ , sf J -
540 J 240 J 620 J 180 J 350 J 120 J 1100 910 'fJ \J· ,:·.:, '.: 1,1 l! . :,1.J Id l : ·:, i ·-ftQc2'.,,;:;;; ·~ditJT~•:_~:., ".' .f.1 _Q • '. ,_,,·_:· _q_§°il__l:f '·' ' 0.59 u
0,45 U 0.43 U 0.45 U 0.46 U 0.43 U 0.42 U 0.27 U 0.23 U . '99 9. ,,·, '_: -~ @:'t,[:;·: . :~§Q'Y.(: ,d ''90:.-u -'-'::,,;,§:;wow;'1,'.f'.\: , . .,:10 u·.,';•::·~~ ·70 u :":,.:.:.::·~O _u
0.1 U 0.11 U 0.11 U 0.12 U 0.1 U 0.11 U 0.05 U 0.05 U :,•_.1i",~:;_, .:::12-f• ··.,;: .f',-'/i.J,·-•';;,/,:· '"5:f:_J.5,.G:;-:,;:~--7'J'i'J\-i.'J1ik~-,-;fij'j.:,,. ,.-.·,•i/j.i Jl;c·· ,.--: 78 J -.-----'-•·----··.,"". -.. _, '•---=-----····~•-,~ ·::..-:, .. ...:...£.., _ _,.',,_-,.:-..,C'.? :~..::_._ __ ._,.,: .::...: ·:!.-~. ·---~'-.~---... :~~ __._. ___ . ., .. __ ,.; -... _ .
24 20 34 U 18 54 8.6 37 J 69 J
4 of 18
-
----- ------ - - - -- - - -
CHEMICAL
ALUMINUM
ANTIMONY
ARSENIC
BARIUM
BERYLLIUM
CADMIUM
CALCIUM
CHROMIUM
COBALT
COPPER
IRON
LEAD
MAGNESIUM
MANGANESE
NICKEL
POTASSIUM
SELENIUM
SILVER
SODIUM
TOTAL MERCURY
VANADIUM
ZINC
GP017SLB
.·-8400.J. ., .. ····~-~--.
0.61 UR
, ~5~_;'• _.·
72 .. Q.i;i J
GP017SLB
(Duplicate)
TABLE 2-4
SOIL SAMPLING SUMMARY -INORGANICS
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
GP018SLA GP018SLA
(Duplicate)
GP019SLA
Sectlon 2
Soll Sampling Investigation
GP019SLB GP020SLA GP020SLB
.:1000)• :,:.: . : ~§.~!1.0:{;\,i''7X~YQ"!i!,L;; <~ '4]Jg_qf;tt" ;,(,.:'J1§iJ.•'!f-::;•_ ,:; -; ,:i3oo ·_·!!: "5300 .
1 UJ 1.1 U 1 U 0.74 UR 0.72 UR 1.1 U 1.2 U
?,3 _, . 'C ,j,U;,_. _ _-.. ;,, 1j l 0:'';i,::·.tf~1;\'tk:;,.:,:c,;:9~~LJ;, .:;·.:?:Li\\·: ' ,3 u
62 26 22 40 16 16 31
.o,.gi' • .(: :)iJ1\J __ '. .0·:._q,i1 Uc: .. : ·.;,:·o.:ffZ,(f: _. .'. ·o.ff.fC<-,_D.?}L!.:: \0_.~4·u
0.2 U 0.21 U 0.21 U 0.18 U 0.18 U 0.22 U 0.24 U 0.15 U
2500·-·
8.7
": i'23_00 ··· 'fi]fii.Q · · · "f.~go/'_: /,.:'.,ikii!h;!:,,;:~: ~-: i.2.0.-,,,,· , _.410(!;;:','·.:.,·., 890_·
. 2.7 .I
6.4 J
715()0 J
19 J
579,
170
~-5-,J
410 ,. __ ci.\l~ JJ. .
0.25 U
~ §9, 4 -
0.05 U .. -13 ''-·
18 J
7.9 7.1 4.6 5.9 2.7 4.8 9
. ~,3 l ' · · · ·_ 6 . .1. -·fr.1 ., ,;, ,JfflfJ:':<:,, q_:~11._.1_, :-': !J.f2_ {'.:,, 0.41 u
5 UJ 20 6.9 7.5 J 0.47 UJ 8.3 3.2 J
'iJ'-iQQ .I '12000 , ~8-Ql1'. · ,.. Jiq_i/.-.J·•·-'i . 20/jq.J . i.410/J. '.:': 100!)0
17 J 5.3 J 5.1 J 15 J 1.9 J 8.3 J 11 J
43_0 _5'foo,_ :-1600; : c: .;. :.··: 1200:?. : i, '. '. 1fir.". :·,:_: . '.:~ _36_Q JJ:·, < 190
190 450 170 130 16 42 8.1
_3_,7J.__ .·. 'fi!1,, -·•.<1!.,i:'<'.;;:{•·.,:i°jJ.'.;[·:,;~. ·. ji.JJ.•_,·,;~·J·?'l{· ,;,,,,, 2U
330 990 J 1100 J 940 80 U 250 J 170 J
•. Q.~3u_ •. , :.::ttu.., . _ ... -.-Jl:!:--~:~.:_,EQ;f&JP-i/),.cfz1_Q~ .. :;_-/c:,::r1:i:rtL·· .-?· 1.2 u
0.33 U 0.42 U 0.42 U 0.3 U 0.29 U 0.44 U 0.47 U
·_ :'iig Li.,~-:· _:~.§Q:_(: -'.f1.q 9./f.J{f 'i~:ao Q:)i'.:, .\~Q _Q ~ ,; ·:;;:-;,;;tQ.Q~~ : ••.. _j10 iJ
0.2 U 0.1 U 0.11 U 0.05 U 0.06 U 0.11 U 0.11 U ~> >1!· ·;i-·' ·. -? t.1.iilJ.::.~. ·_,:· --·:} ~ ·\::~ 1i3? :·;[s!i&f Jf{ !t-_::-_:;;~~ ~-;Jl ·:-~:~;:.;.~-:.t~: (q-.1/.?J.Y ';~ :.: L ~ ... t I! .
13 J 28 27 32 J 2.7 J 13 13 7.7
5 of 18
- - - -
CHEMICAL
ALUMINUM.
ANTIMONY
ARSENIC
BARIUM
BERYLLIUM
CAOMIUM
CALCIUM
CHROMIUM
COBALT
COPPER
IRON
LEAD
MAGNESII.JM
MANGANESE
NICKEL
POTASSIUM
SELENIUM
SILVER
SODIUM
TOTAL MERCURY
VANADIUM
ZINC
- - - - ---- - - -
GP021SLA GP021SLB
TABLE 2-4
SOIL SAMPLING SUMMARY· INORGANICS
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
GP022SLA GP022SLB GP023SLA GP023SLB GP024SLA
--- -
Section 2
Soll Sampling Investigation
GP024SLB
5400, . 2~0~ , ijog l : ·;r t~·~901fiH1f '{ 1Hi111l,h7,,_: '11f. :26q/i Jf/ : , . '47.00,.-. · · ·. ·. 3000 .
1.2 U 2 U 0.76 UR 0.65 UR 0.75 UR 0.77 UR 2 U 1.3 U
17. t1 •· · ~.Y :,',' •~rr-:r.1~2·.~:{{,,"J:~ji/.,·:~·.:;~A•::,:,:-/:' '. 7,2 ', '·.· .:1.2
57 33 31 38 200 130 230 39
., ! y g.~1\!. ·o.s J ....... q.-iJ,1:'i:fJ:1:~:Q,Q§iiJ'~L'.L:c., . .9J>_a u<·.,~\:::Lsu .· .... Q.~6 u
0.23 U 0.21 U 0.18 U 0,16 U 0.18 U 0.19 U 0.27 U 0.26 U
2000 12{)g_ , . 2ioq J.'.,,:, ,. /3!Jth,-t';J,f:??OtJQ)"'''~:~'.:;Mo.P.ib:/;' ·,:j3000 ·< ·. •· 44000 .•· .·
&3 11 S6 14 8 S6 6 ~6
1.6 J. (!,IJ J ·:· 1f,i_ _, '·',1!~J.f./'•J~i/: ·2.~ ,! :.·:/'J/1...:i_·:::~:,.-·,.2.9 J. ·'· .. 1.6 J
6.4 2.7 J 1 UJ 4 UJ 7.7 J 5.9 J 20 12
8200 .. f 2690. 52g9 J• ··Ei1oq,:T::':.:. 4ti9.o,).;/ '·'4?7JQ_J: ~.. ·:4909 . 5500
23 J 3.3 J 14 J 17 J 11 J 9 J 28 J 21 J 4Q. 1~0.-' 3~1) '.:,·, ·,37g_._',,,,-~;{•~~ft;,: ., •. :_1:j[ii'>c;'-·,:-" !fro· 880
92 39 21 21 410 250 370 96
3 u •. , 2 u • o.~'f ,1_ : .• •·, .• 1r~. ~' '''.·£::.~,;~~:_:.; -!. : 1·J,' ;,g)·,,,i, ·,'L: ~ u ' · · 3 u .
230 J 55 J 80 U 150 340 550 1300 J 250 J
1-'.~ .~·Jf? --,.~:) -µ :. ; •'.)· .-' .:Q;t§·:R. _,. :;,;~J-~~3f.£IT, ~::st~t~t-r~·.QJ7.~_(J}j\:I•t;~~Q:Z~·.1l.-::/~-.~::\._{J.~1.~ ~q: ... -~-:.-. ___ 1_} u
0.46 U 0.41 U 0.31 U 0.26 U 0.3 U 0.31 U 0.54 U 0.53 U · 1~fi.u -?>.: ; s.Q .1.1 • ~, .• • :~ !!Cl V;, .:;;;{,:,·::Ezl.\ P.ilt'.:,c,.i:i,;,: §Ql}o:,I 2fI1iQIQi,\:. : . ';:,~s_o 2;;< c': ·J!!9 y .
0.12 U 0.1 U 0.06 U 0.06 U 0.06 U 0.07 U 0.14 U 0.13 U -'if.::~_-.:;:: .-.,:}s."i:.~\:: -/:-:;-_.~::.-.tt)t:_~~~£.:~~;:f!I~:~;~2Jlt·r:·~~:-J)~;;:J/:~it?~r~:~~-t?\l:t~r~d 1~-)_ .-.:~ :.~; i:i ~
u ~9 a2J 12J aJ UJ ~J 47J
6 of 18
--- - --- - -----
TABLE 2-4
SOIL SAMPLING SUMMARY -INORGANICS
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
--- - - -
Section 2
Soil Sampling Investigation
GP025SLA GP025SLB GP025SLC GP026SLA GP026SLB GP026SLC GP027SLA GP027SLB
CHEMICAL
ALUMINUM
ANTIMONY
ARSENIC
BARIUM
BERYLLIUM
CADMIUM
CALCIUM
CHROMIUM
COBALT
COPPER
IRON
LEAD
MAGNESIUM.
MANGANESE
NICKEL
POTASSIUM
SELENIUM .
SILVER
SODIUM
TOTAL MERCURY
VANADIU.M-.
ZINC
310§ •,
1.1 U
1J· .
66
1 \L
0.21 U
65(!0.-
6.1
'•1,8 J
·.~,--,~3°toQ;~:-~~.;,·-\··~)4Q<? ); t·~~i-: :·~9.Q~f~}i'~~i{?l§fi~~:.;~:r~\::}?Ji[ii __ 1?'.i•}:,':~--~~'I~"@ti•-\~~ : , T--_ -"2s6o
1.1U 1.2U 1.1U 3U 1U 1.1U 1U ·_ ~ u· ~-~\ ;<·,.~-:t.:~. -~'."tlr.·;f.f~~~tt:;f<tit·~~::i~'.-·1··-:t~r:q_:~t-u·.,~:-:\:?~::·.~;_:~ -t.Q -.. , 1.6 J:
60 34 45 1500 44 33 36
•' -. ,j g_:_-;:c • --~-I-Q.• ·· ",/LrLJ.':8TI\~'iJiC:,;,':,X/:/qJfy:·>;:0-'\:~~-.'.:1:\L · · · 1 u·
0.21 U 0.23 U 0.22 U 0.3 U 0.21 U 0.22 U 0.2 U
i'ipo, ,,, ; , · . !150.·.i, .· -.-~1§9.::d"f,,.-;.\11tigg'Q ·" ;,_, .. 21gq_,f(-:Ijt,·:f2_oq ::;:·, 1000 ; ·
3.3 9.1 4.7 8.8 3.7 5.1 2.3
."-··-; j .:· ... ~<-, .',~}_·~,,_'. ::-_ < · ~ ~\~1(:i_;;~.:.:i-~:;.;= ::~~"1:"i-1~{/J ·.-.·o;~t~, ·~::{;~·::l·;_ :~'..f~ .l· .,;:· <~);-_ · 0.6~ J
16 3.3 J 3.2 J 8.3 64 3.3 J 7.1 2.3 J
520.§. -~ii_iio -; :·:.: 1_2qoo. , ,_ • s2-qo. >i;'};_, i~q·L-~J:., .. :: ~61/<f:'. · /::,r·~:iqq ;:_ . c . _26oq
22 J 8.8 J 5 J 18 J 43 J 3 J · 15 J 6.1 J
6q_q /: ·-'410 : .-·_.471J,(-;.;.i·, :'?~.f':tt·'.?,~.fiii_ii_ ,:::{iii~::. ~~!i,;•~•'··':et· ,t~iig :: , •/ jqo •·.
170 59 84 170 3400 100 150 120 .-;~2-u · : · . _;~-~-2-.tt '.-\··. ':i_; :··~:t·~iQ~~,:.::t .. -'! .···-C.t~-!~1;::~~~Jtt i§.l: .. ~~¥.:4~Fr:~--·:::7 Lfj/~f:TJ(~::~: __ )-·Q_·.: t:·-"'·-::< :!.~·-2 u·
350 J 350 J 360 J 610 J 3900 J 130 J 970 J 210 J
' ~:1·:-:1. !d;;: ~:-: :-_~-1·.j Q".1 ~~,, :: '-~·:i::1-~?. :Q:{·::~~;:_:::: ~----.. ~1j,a[l1!~~Jtfi).{F~:LJ"7::,i}!L;:(·f :?I:Q .. =E'fi['_L_:~./~t1·-~); .. '._~-~ \ -~~ •, .1 .l:1_
0.43 U 0.43 U 1 U 1 U 0.61 U 2 U 0.43 U 0.41 U
· ·'_1{fQ Jt: · -:-:.-.:~ 1119.-Q;\\\ <_-:\~Q--kr·::~f>/:·-~jf~q··~11~tEf.,.~;\]~ .. ~~t~~t:1~~~.-;-~J?T!:,t~·-;;~.::;·~)4"P: 9_~::_ ~-t/·:·~~o u _
0.11 U 0.11 U 0.12 U 0.11 U 0.15 U 0.11 U 0.11 U 0.1 U
-"-6.:~?~~~, ~~-:·,i·: -:t_ :]I~~} .. :1ti:f~::·:~.,'. .. ~•ti -JfJ:l~::i-'.~ ·/~~!1~: Jfi£;S1:B0;r~114~~~f!•!!f~:-~~~f.f"i&~;:-_f1&!?·i :~>-::1-:~;~-1 ~ ': • __ -~ J~--n 14 13 ~ n ~2 n u
7 of 18
---
CHEMICAL
ALUMINUM
ANTIMONY
ARSENIC
BARIUM
BERYLLIUM
CADMIUM
CALCIUM
CHROMIUM
COBALT
COPPER
IRON
LEAD
MAGNESIUM -
MANGANESE
NICKEL
POTASSIUM
SELENIUM
SILVER
-
SODIUM _ __
TOTAL MERCURY
VANADIUM . : ''•
ZINC
- - --- - - -- - - - ---Section 2
Soil Sampling Investigation
TABLE 2-4
SOIL SAMPLING SUMMARY -INORGANICS
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
GP027SLC GP026SLA GP026SLB GP026SLC GP029SLA GP029SLB GP029SLC GP030SLA
. "1JP.tr~:. _· ~-~ . . .;1100.1,,~t Q.,:' . :~f§i'&.i:-~~JEfL·~( . .:;: ~lb: -)~:4€i ~/.t1·qq_]f ;t~tJ.ll[i ~ftQ j{f )Jjl{ijg"q_Q ~r;:· . tj~'. ·fi~~ ... : .
3.8 5.5 11 2.7 4.5 8.7 14 6.2 .. t: :f:.. :,-1i~J:J:_,,· · '1 J;~-':' -, -·-o'.'"1fs' lii?~1f'· ·:·6:66':LV;:''.f1t.;:·o:ifa Uc;;'}"-J:§;;:cis3 u· ,' <'-· 2.6 j.
1.8 J 4 J 3 J 1 J 2 UJ 4 UJ 47 J 6.8
. 3~fJij,i~ _: i,siJo< ;":' _10000 ;~;'..{'<'.'24iJ(f':,~--;~;_;-;i'ififb1,:.;:;,:.,:r3:fiiliJJ;-:r'"'~-;;2:iiooJ:: :,}:"-s100_,
4.2 J 22 J 12 J 2.9 J 6.6 J -17 J 92 J 5.7 J
28()_· -..... ,: __ .: .... _5j9_.:):~:,' :~ ... · -~-6j2_1 ·: :.; ?~/ ?f~~Y~.:~Y~1t:.\;_§.9o[f{i?~~t;r{J-.,.~_o,i~-!\·_.-:>i_)7qq_;_:::~~ r;,·~,, '~f2..Q9. \ .
56 67 36 18 91 17 57 130
'~.cl!-;•;;":''' ' ),~: ,,,, ~-<~.J ti]:~: -f.>,>it~,~:\JJ7~~1lflQ~65~~!~~~t-tt::qJ(-f:-Y.J(f;~;:i~)t~1:)J~.;~;-~)~.:-~~~--. 9 :u
160 J 400 J 370 J 54 J 850 120 200 1000 J
_-:tJ1l;-:-.~1i•.) .. ·, '_ -1. tiJ, :_\~. .·. t?~~1L;~\-~~~1h_.;~!~,t:.~-·-Q ~JL2-~i~-9.-~:uJX1;l4~;:-:L<?.-~1:~~;~~~;;:::.~;·<L~-9.-~1!f !J·;/> ~:.-;~~-1~1-~:
0.43 U 0.42 U 0.46 U 1 U 0.25 U 0.29 U 0.22 U 0.44 U
··: · ·146~1} ?·::A}: .. ~:'' ___ ',9[);'8' .::, / · -_,,-~J10~1J,:~~:t~~~~;l~~;;·70-:Q1:~t;Jf ~:;_~;L&Q jJ~·:1ifi~b:F.Q Qi~ ~:r~:. :.~~QJU,.,0
~ f. Q ·::s'i ~-q _ld
0.11 U 0.11 U 0.12 U 0.11 U 0.05 U 0.1 U 0.1 U 0.11 U
8 of 18
--- -
CHEMICAL
ALUMINUM
ANTIMONY
ARSENIC
BARIUM
BERYLLIUM
CADMIUM
CALCIUM
CHROMIUM
COBALT
COPPER
IRON
LEAD
!'v1AGNESIUM.
MANGANESE
NICKEL.
POTASSIUM
SEL.ENIUM
SILVER
SODIUM
TOTAL MERCURY
VANADIUM
ZINC
...,, --
GP030SLB GP030SLC
- - ----
TABLE2-4
SOIL SAMPLING SUMMARY -INORGANICS
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
-
GP031SLA GP031SLB GP032SLA GP033SLA
-- - - -
Section 2
Soll Sampling Investigation
GP034SLA GP034SLB
9 of 18
--..
CHEMICAL
ALUMINUM.
ANTIMONY
ARSENIC
BARIUM
BERYLLIUM
CADMIUM
CALCIUM
CHROMIUM
COBALT
COPPER
IRON
LEAD
MAGNESIUM
MANGANESE
NICKEL
POTASSIUM
SELENIUM
SILVER
SODIUM
-
TOTAL MERCURY
VANADIUM
ZINC
--, ~ --- ---) - - --- -
Section 2
Soil Sampling Investigation
TABLE 2-4
SOIL SAMPLING SUMMARY -INORGANICS
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
GP034SLC GP035SLA GP035SLB GP035SLC GP036SLA GP036SLB GP036SLC GP037SLA
· 3~qq· ::: .)_:·-~, : ~3!'9~::~r£ ·::~ :;~ -~ .s4.qq ,,. ~ :~~i~~z_:~~:-~·1]~~;i.~<i!i~i6oq:3~~; ;r:::-·:~J~Q.-'/~~~;:2r·E~~~3-~~!2.~ ... rs:-~! ~ ,,_:. :-.~~if9-...
L2 U 1.2 U 12 U 12 U 1 U U U 1.1 U 2 U
a·. 94 LJ \ · ; ~ : ·<\~. ~t ·. __ ";_ ~j ,/:--~~~:J .. ,(:•3. ·:.~! ~:~:i~~f!J:{iJ'f :·_:: ~ §:·~·t:F~-;-t~; .f.f ·:• -_.'i i .1\-l,~-f-t.; t:\~~ /~;:· :~' l.f \:(.:_: -· ~: ·}: ~ J .
260 35 150 340 17 34 32 40
_ ·::1_ ~ <1:~~ ~?;:::-::, .-Q:~fY \~r ~:t:1_·cr~~---:tf::~~:x:-.~~~tfPE!)t-:~~{:}:::~:·:_-flt-:/':~~;~?t ::_) 1.r~:. '..-~ ;_ . __ 1 u ~
0.23 U 0.23 U 0.23 U 0.23 U 0.21 U 0.23 U 0.22 U 0.34 J
51Q '.. . · · : 2590 <:~ '. < 13:~CJQ . ; :{ · .,iBQ!)Q. • ,::S.ii.'.-~~-~§9'?;(ic!'.i ;?;::2}J10. ,:. )i.•i'.~•1!12Q-·•0 •; : : • .:3700
5.3 8.5 7.6 8.7 3.6 7.4 3.8 7.4
·'!-~ J,_ t,s J? · ·• t{;:J > Ii) .. :,-;_::,.71.,'d/,1,.;{{/,:. ··1.j ,,1,:: -.~(ii._T§~-h:> · 3.3 J
2.5 J 4.8 J 17 20 3.3 J 5 J 3.2 J 42
3QQ°i1.'.,: ___ , .fio];. •:· :' _ fiofi,. :,-.\ ifai/ik. •·<i:.~::~@o'".:~:i'I.s.8!JQ.•?'.':::):·;~2_9.fi_•:'.,,,r:. ·_~1qo __ _
11 J 16 J 33 J 34 J 8.3 J 10 J 5.6 J 50 J
2~g : __ ·;._-• !i6f ;·--~-_· :i~po: ... -.2!00 ?>:>':.'/?:t~q-·-~c, :,c: 4~"!V:-i:•:t,,.2;3e·-; ,, faoo c -
44 63 380 760 87 73 93 230
_? V ,_;!LJ ··.\' ~.&i/--_ ::•-,:,::a.Jt\ ;ti,;,(/~;(t;-.::\_~:' ., 3 !i-'.:0-,t;c(· 2·u • .. >._/ 7.H
130 J 1700 J 2100 J 3500 J 510 J 340 J 130 J 1100 J .-~f? bb~·::~: .· ( f~-.. Pt:-<,· !' :r~ ;,_j:J·~-)i}•~-:_;._:·:I~t-~~1~~~:rt\:~~-J~:Q,.}E:~ .. ,:l~-:i::i lJ..~:~~~·-.l." ... ~-;~j;::1_ Q;t .! . ~_:__.:;J .1 u•
0.47 U 250 270 250 0.42 U 0.46 U 0.44 U 0.44 U
.jQ9 !J·-:~ /~. _·._·c~-1 QQ.> ~ !Sit~: ·.\ .. :~.~Q-!:.f)l-~,,.· :· -:_:· 110 ;/r{~{Jf-Jflf~QJj\f ::~1:-1\ .. ,:\~Q .U:: :_··/.t~.>iQ6}~.;,.: .: __ ·_:·_1~0 u -
0.12 U 0.11 U 0.11 U 0.11 U 0.11 U 0.11 U 0.1 U 0.11 U
::-:·~-:-.. :"-~ !··: ·~;§. ·y_ · ~ '.. ·:-~ fil·'_J_ ·-_;-~-;:.-t~/-·iYt:··:. --~:Jj :~~? ;:,2~L1a;t;f·~~hI~t!;-f tit!:·:t':1t .. i.~'.1~:J.i:_;~/~:_?:..:: ·.•:_" -,. t;:.11.
100 25 170 73 15 24 11 150
10 of 18
-
_,_ -! -
CHEMICAL
ALUMINUM
ANTIMONY
ARSENIC
BARIUM
BERYLLIUM
CADMIUM
CALCIUM
CHROMIUM
COBALT
COPPER
IRON
LEAD
MAGNESIUM
MANGANESE
NICKEL
POTASSIUM
SELENIUM
SILVER
SODIUM
TOTAL MERCURY
VANADIUM '.
ZINC
-
GP037SLB GP037SLC
---
TABLE 2-4
SOIL SAMPLING SUMMARY -INORGANICS
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
GP038SLA GP038SLA
(Duplicate)
GP038SLB GP038SLC
-- - -
Sectlon 2
Soll Sampllng Investigation
GP039SLA GP040SLA
: 43fJQ . --.. < : _:4Bgef.i ½~~!{·,,,·: .:-~ ,.-~!tfQ '}!'\~_-,:~I: ~ ··:)~QQ;,·f~RiltPiQQt:~~~;~~rf ;~:~~q-~Jt:,~~·I:;;~::~ti~i(~·: -i-=. ·. ·• :t~Too J
1.1U 1.1U 2U 1.1U 1.1U 1.1U 4U 2UJ Q.?_g·:u~~,,:;:.: :-·.: ~ ·1:.tJfi{~<.··,~ ·: .. ::_f~ :~::1i;~~\:\,-t-~)!.t:}~;:~~f~!l~)'1:~~2,LJ2.t·'.·-.~-:o~~~-~!d{;.~ .. ;/lit.~ ~Qi-~~-\t; -~-~~-_: . -~~2 · ·
83 35 76 82 33 23 290 110
''.:1._lr~--~--:_,_. cL:r.t:g-_f(::•·. : ·j ·q,~,,:.u:_:·:;'_1 _N:\ .. IJL:.~£I~i!-~:i:~~~;L!,J_:;~!~:~'.(~; ~--~-~t.lJ.~·{.~~~~--::~;;•~~ (\!:.~-~-_.:_:·.~_-Q..11 ;,·
0.22 U 0.21 U 0.23 U 0.23 U 0.22 U 0.22 U 1.2 J 0.16 U
-· ~~gq. \',,~_~ .. _ ·,t'" --i,~(}Q~~:-~;}f.r.·· -j_-?(}qQ. ·:;J; ---~-\-~; '?t'qf-:>>}~~!~{It"~g",Q:. ~:;~ •i-~-.i~~~~ :: J~Q(~~//: .,$".{~~~?gq_·:·~;'.:;. t~i-_.-.. ~~Q{JO :
4.5 4.4 6.2 7 4.2 3.3 270 6.1
t~J.: ,,,.:: ' 1:J '.J.,) ;,:·, :A,f ~_i::~~i/ :;e_3-,3;J.i?.{iti;Jf::f ':c:;'1<1(~ {;~:·,,,: fji'J;;:l :~· tl-l. 2.5 'J
13 4.3 J 33 28 4.5 J 4.3 J 260 32 J js()g, . · . , :gf()q_:,;.,,_ ,· ,i",~ifQ(! <· · ·s,jQQ ;_,0,,J'f:ti2oiiiiJ~'.~'-'J,::-.1i(io •L'1?'':'::f 2gif.1ri, '.i ·_ · ~~_/ioQo J ·
39 J 5.6 J 85 J 72 J 32 J 10 J 130 J 28 J !12 ,_; ·, .. : :.. )!Q-· :~-".'.-·{ :., ."i~Q ':· '" "· ffg_,_i;:;~!J,1;~' i;ff§f-:i{ '.-~tr-. -1~9.'-'£7'-:·,ic"s;;§!Q ,,~ ' /. ·1200 ; '.
130 62 180 190 42 54 280 190
; · __ --:·if~ = -. ---<?'~_iQ _ ·/." :·. ~ ·:>,-.~-::i1 Q~::~-:. j.: ··:r1 f-Q~£::): •·f~~--~~i f_Q_~t¥Y/<_ ·;~i-~·:·q~~0~?.cil: / 1!P:. __ ;_. \'. ;:~< ~s.g·'J
340 J 240 J 430 J 530 J 180 J 100 J 500 J 290 JJ IJ.~ c -,, '.:..ff Y.:.:;;,.,; ->::}\ Q";,-'f: ,~ . · if 1-JI~;i':f"·ti, ;r,:r.Q,c;'-?:"::. E(iil.f;,.:;~-:,:,;;:t:~f 1 q:, _, -'.L:.-. o,6s u
0.45 U 0.43 U 0.46 U 1 U 1 U 0.44 U 1 U 0.26 U
,_:._ . J221:i ;, ·,_.::\: ';1~Q q·~~.\!.'. ~,"'126:JJ..'i'.}:.;:,'. ;,i1~Q°1Q;J1}r,£,~f.::;.[6J4:r,-::if'."i:,£•f9 Qi: ·:JL\i:;'.fs"gj/ ,.•:·:,·,r.,• 120 v ..
0.11 U 0.1 U 0.1 U 0.11 U 0.11 U 0.11 U 0.13 U 0.06 U ]:;·: -->t?/J:I_ · .. : ..... ~ -~ .;Ji:1f.jtA::~:?~~-::;if.9i/Ji11~t{~.?,:.:·, ~;~t11/.2~,0tfI;Eff[!BiflJf?:\f~'."if.i~.f:1~t~tt/!~.1j{~ -~-._: :?.'1-~i~B_ j
64 11 58 55 14 21 740 210 J
11 of 18
-
--
CHEMICAL
ALUMINUM
ANTIMONY
ARSENIC
BARIUM
BERYLLIUM
CADMIUM
CALCIUM
CHROMIUM
COBALT
COPPER
IRON
LEAD
MAGNESIUM
MANGANESE
NICKEL
POTASSIUM
SELENIUM
SILVER
SODIUM , ...
TOTAL MERCURY
VANADIUM
ZINC
-·--
GP040SLB GP041SLA
--_,_
TABLE 2-4
SOIL SAMPLING SUMMARY • INORGANIC$
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
GP041SLB GP041SLC GP042SLA GP042SLB
---·-Section 2
Soil Sampling Investigation
GP042SLC GP043SLA
~~i!P.:'\J·:c:;;_ :; ~.': :/t4~Q JI?jtf::; e ~ \•::~fQQ,:;f;.:: f :~r.~ t;i~P{(~;;£~fl~~'!{~~[tf '.C~f~tii¾;~t~]~?f l!iift{:.:~~:!i§.OO;~: t~• • :~> •~B1JiO ~-. ·: •
0. 71 UR 1.1 U 1.1 U 1 U 1.3 U 2 U 1.1 U 1.1 U .,_ r ..... ::i-· ~-:,~:-\ ).;~:·~JfC~·· · .. ·_: r:~:__~~f~ }ff~.}. ~;o_j~::tJ.f~Yltt:J.i:?~t.it~t:?:J/: ... :'J!~;_.~;_1~Jfi~l: f.1.:~f:J_ ·>.: t· ::•~ ~-1.· :·
32 180 160 19 65 120 19 360
o:'1_~ d · ·: · ~_\Q.li.ht:·/:. ··::-:·-. 'l ~ ,:-,..: 5·. ·,"Qif'!.fft![J_;~Q:]?.:yJfil{:.}':?~J;,:uJ7_JiC~i ~iJ..!t-~ ~-·/; _-· _ 1 .u
0.17 U 0.22 U 0.22 U 0.21 U 0.27 U 0.22 U 0.21 U 0.23 U
· . 811.Q!J'. '.'° ·• '. ,·. popq : . ,7 fli{lf :,,' , ; •,• ~4~(!, )'.0,\,;\'-i~.QQQlt,\'.',J,~.:~oo ,; {.~'-~·:tr f4Q :,!< · . -~-460QO .·
6.8 5.8 6.1 2 J 9 4.3 2.5 10
4.5 .J. 1.1} j; ~-. . : • 4JJ_ j ·.:: : ,q:,ifi,'"j:ft'.·= / ';ff).,~;{{},,,; ·, 1#. .✓ ·:c:t: .. >t~ ·j :,-;; .· '.' • 12
12 J 9.9 24 2.8 J 7.1 9.5 1.4 J 25
94i:J§J•. · : Jigq .,,, '._ · ,~9@,'l ,./}. f~ii!i. :?ILl,)~,ioQ•/~i,?:c' J~oof·.:,::: :'.i:::111.9~ :, </11.oqo .. ·
7.2 J 29 J 55 J 2.6 J 35 J 18 J 2.1 J 32 J
2l.Qi1 . · 3~_ :.::,:-t~Q.q . ·<•: :•_{1/1. ;.:;;~::;_ ~ ,t~§. l'.\s:,-,;{ :.~Q/1 '.;_:.':'C..,-: ·t10 -·'.: r--3900 .·
~ ~ = 15 120 1M ~ ~
6.9 J: -;.,. ~:" (J. > , ,::·fy ·.:,. , ',,i U:t ·'.:;::.::.'::•.3:1)Jf;ifc:.~i-;:~~1-L~ ;,,.})' · ? u. : : .• ' :., 11.
1900 200 J 730 J 47 J 280 J 320 J 86 J 3500 J . ~.:tt lA ·. · :· ~ ;:-_ .:::r1-~ ;:·~~<)t.j:Ji.,~/:t,,/::: .,.;.:J:.:.~:}~_q_tti~t~1I:J:.}:Uut~:~·~~-· ,:::TT:.Q::-_}j\~:?:::".I .. f U .: '··:: ·; ·1.-~ ~ -
0.29 U 0.45 U 0.44 U 0.41 U 0.53 U 0.45 U 0.43 U 0.45 U
_:§~'"Q '; .. :\: j ~@_Cl_<(:::'1
# •• •• ..1.?.Q~Q.~~:· --_ .. -.§Q Q~:i~~i66Ji~i-f:.::•~-~li~-.Q B..L@~~:~~6J.J __ . ..__ 'J~ ·:J~O
0.05 U 0.11 U 0.11 U 0.1 U 0.12 U 0.11 U 0.11 U 0.12 U • _·· ; -'-lt:Yt _;· ·::~~ :.--~ )'.f:;~)1--'~~.>•~;;:: :: :~f !I. ~:}·f:~:: t~Z:.f§~imt~~!.11r!tt{i:l}5t.t~~~ (~J'ti!:~,:~~·._t·t-:(.~ :~ /:~· ~. :·: rr. · -
40 J 47 J 110 J 6.1 J 37 23 7.7 79
12 of 18
-
-.. -!
CHEMICAL
ALUMINUM
ANTIMONY
ARSENIC
BARIUM
BERYLLIUM
CADMIUM
CALCIUM
CHROMIUM
COBALT
COPPER
IRON
LEAD
MAGNESIUM
MANGANESE
NICKEL
POTASSIUM
SELENIUM
SILVER
SODIUM
-
TOTAL MERCURY
VANADIUM.
ZINC
_,, --- ---_, ---: ----Section 2
Soil Sampling Investigation
TABLE 2-4
SOIL SAMPLING SUMMARY -INORGANICS
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
GP044SLA GP044SLB GP045SLA GP045SLB GP045SLC GP046SLA GP046SLB GP046SLC
_:·6qq~r ·~:-:··: ->/~} .. G~qrt·~ · .. ;; :·~. ~?::?.~'ef.?.ifQ?:·?;_::'.';.~--:~~.12Q~:i~~!~~:,~ ~):~;~11~:~\~t~i~Q<L7·Jj~: .. ~~ .. 9~t?~i<-l~:~:-~-:::. ~ «~q J.:.
1.2 U 9 U 1.2 U 1.1 U 1.1 U 1 UJ 5 UJ 600 J ·_tft. :',i = .:_· ,.,-. , ~-·?:~ ~.:{~ 1~i)t/-:~}~ ~-~i~i. _·f_Q-~ltlt:-;tQ.Mi&tt::~ii :::,_:_:Q;§.~~u :•:.-; -·;·J,._~-":~;f:-~/}r.· ii·\~----~:6· -_ ·
260 320 110 79 26 22 1200 130 ·_ , . ·-. .1 ·g-{>··•\:_ · .-.' -~ Q .. -,_.: :: -~--~?~'\f<)\ .. :-•/·'.:_~£J: __ Qt~:·;:::·({'~~i1f!ta}\~-~-•;••QlfvJ_t· ~---~-:_~-~q.'Qf~:g)'~_ .. ·\:> ~-o~QB -~
0.24 U 0.59 J 0.24 U 0.21 U 0.21 U 0.15 U 0.17 U 0.21 J
i6oqo_. · ... isooo , : • . -gioo • .-?lOQ:,~:. .... ,:,::-:,<:c!@.iftitj .. ~;JL ~?!'i,\:? ;•100000/;•;-·q~,;.3iooo -13 ·· is -·s:2 s.1 4 2.9 · ····21 ·-· 23·
7.'1 •J. 1,T-1) · · .,'"i2 ·Jl,'': ·-:,' iJ:J ::;;1,.'.'o,~{:<J.,'Jif:.. 'i!f ~,[ _'.. ;_. ~ts~ .i,i · · . ·;;,_s J
25 67 18 12 2.4 J 2 UJ 130 J 150 J · v~qq 71oq.' / : f1QQQ : . · '40QO.,; :: ·;_-; ~~§2.?;t>; _· -·2sgo_ :/ \ <)~so"o_q .[° :s' :_ 19oq_o J
53 J 240 J 11 J 29 J 4.4 J 6.3 J 150 J 3300 J
· 2soo ... f~q_o ,_ .. _, ... : 4°q@.,":,. : .· .. ~38-~--:, ,,:;;.J:-;'~i~G:iL::,.--:,:1~f:;'''-.,:Jt2.i?o ,,-.:;:,··:/:}100 ,
680 700 480 85 38 22 2600 360
, ·10·.u, , · ;_,_~ 9 u_ ·1 _:_ ·• >:?::?}:,:~<:">' .... :< :\:::~·-~·'·~·~}3~:~-~(21i~_F/:/>:,~;:~:f)ii,··Y :,-:\:~~;:ijg_,_';/;_,.i-,J .. · :·~~-~iq _J
2500 J 2000 J 2700 J 210 J 140 J 80 4700 510 ::ti Q. :. ·. 1':~ \cf,<\ ·--~•\t:il,,:'.I'-.,<';!f'i Q.'1'\:ft'tzf:i;l!E'.L/::· R,&i,1) :,c,./S:cii}_IIJ:~ :: :·q.1e \!.
0.48 U 1 U 0.47 U 0.43 U 0.42 U 0.25 U 0.28 U 1 U
2~.ii 4;_ · ,£' ,: 249 Y. ;, ··,. -::~tl!o.i1F: ;_ :.:,: ;;1_:i§ 1F:L~litZ-::sO::u¥:s,: ;.;;~:_ ,.Yfo..Jt,:· ~:t .. :~4i:i.-i \. __ ;-'.-250 u
0.12 U 0.13 U 0.12 U 0.1 U 0.11 U 0.05 U 0.1 U 0.13
, : :;; ·, ~:~f;;F;~··:\.-'/~/i.:~;2-1~ .. .: :1i,_. -{ .?~~-i~f:?-:A!-~<~,y,.~~X.~ 21~<if1f~Iii1'9ffQif~:i~t:I tk:[ Y~~ ~:t:: IJ:.·:1.tt·~;; 1¼i!i:.:_•_:.:·.~-~:-~ .j_ ,_
92 200 51 45 13 9.5 J 300 J 1000 J
13 of 18
- ---
CHEMICAL
ALUMINUM
ANTIMONY
ARSENIC
BARIUM
BERYLLIUM
CADMIUM
CALCIUM
CHROMIUM
COBALT
COPPER
IRON
LEAD
MAGNESIUM
MANGANESE
NICKEL
POTASSIUM
SELENIUM
SILVER
SODIUM
TOTAL MERCURY
VANADIU~ ·
ZINC
-----: - - -------
GP047SLA GP047SLB
TABLE 2-4
SOIL SAMPLING SUMMARY -INORGANICS
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
GP048SLA GP048SLB GP048SLC GP049SLA GP049SLB
-_,_ -Section 2
Soil Sampling Investigation
GP049SLC
2~oq:._ .~\-.:~-.-~ :-~~?!: /~~--. :~·-:~{iI!.9.·~-:-t?~--:-(;r~~~~:~(~V.~\h~S~1fif-l;_ ~~(~.{f#!.Q}f;J,s;:.~.-~\LBO_Og~~~-~--)~909 -~ :·
1.1 U 1.1 U 1.3 U 1.1 U 1.1 U 2 U 1.3 U 2 U
3r · · .. ~ -~--· -. ~-\'--\1
• __ •• ::.:. ~ • ._-;_.,/.,.-1. ~:~~:JJ::ftr,~r·;_~iJAJ•:l,~} .. _:~§~Q1 :-:r;;--~~}·:r<jf ·)-:~ -_:::: . 10 .
160 80 47 69 21 440 330 2200
-~--~ ~-,· · .·:···-.. 1~1t~:,.. !t~§-If~ ··::•;?\--2:~rQ·!},!1:!\~Q-~~~--U:?~(t·i_.~---r~~:~.1)1.~~ .r{ ~-1 ·u,· · ~:_ __ ~ u
0.23 U 0.22 U 0.25 U 0.22 U 0.23 U 3.2 3.3 0.24 U
65000. ~ .. : _.)iii_ji[§. • .-1300~Q; . · .:, .• /2@Q(i;0 ;,: ,,1 :._._;,:4jf,~•:i,: ·,:;:~ii~Q!)' ,,.>;,,, c~tiiqq,< . , · 75(!_0 -. •
53 6 4.8 3.5 2.8 18 13 17
:l_,9.-.J':,,, 1,~:( > -{~:J ,/:,.,,!_lcJf~/'J\·:-:11{.~'.(~~;. :t~./.\ ,:_,ij .; . 6.7.J
U ~ U U YJ W U 37
10000, .. .-; • 31/i.!i ,. ;, 211011, :; \;:,ftqf.,;';, ':Eii}_/lflQ fl<:; ?Q!IQ["-'. :: ·iii/Joo._.-· .10000· .
17 J 7.3 J 5.3 J 13 J 2.6 J 260 J 78 J 140 J
1.1(!(J''' . ·. ?,9Q: ' ':/ ... )~q§ ·•;; ,,.:: j '.;i:is._iJ· '. :,::'.Y~':;1~ii-, D?,\. \: 19QQ:::-. ·. : -. ·,}!@ ·-\· 10(!0 ; ..
450 150 110 88 23 900 940 260
8 lJ .·~. .[r~•i.J:::;•_;;-•, .·~~_:·u ··\~ .. : _ _f~~~_':]:.1.J~·-.~~:J/1'.:~~-:_~J:Q·~t-·.~0 ·~-;_~f~)~:._t~i;,'<;;_-:~:'.i:}✓~-U. _,./~ /.:12.
490 J 310 J 630 J 290 J 190 J 5400 J 2600 J 1100 J u.u. ·L-':-,,FLt-L. ,•,: .. ::1.-~11-.--.,;;·c:t.JILQ:_i:,//: ,f:1:...Q;t,,,:.,;'...:,ilLiJ.',i~;i,•;'';~JjO_-.,,c:'t2U.
0.45 U 0.45 U 0.51 U 0.45 U 0.45 U 0.42 U 0.5 U 0.48 U ~!P./:-:•:~: i--~-;.)1-tQ-U. · ~~:.;_;.<· ~)Q:-i_.·:~~:::. ?~~J® U\J;:.t-.[;:-ti<r-. .u~;t~:__:.<~ti ~,t44_tt:3~·: :,·\_,::: ~_24q ·Li.:-:-;_· J: --~::2_4q --~ :
0.86 4.4 0.13 U 0.11 U 0.11 U 0.1 U 0.13 U 0.12 U
_--;. l;~~,~-:1•:=~~~:; \-.. ~~1.::/~~:-:~ .. ~:;_i:~{~~z:::-~~:~,:;:tf s-··s~4~;~~l!If1~fE~?:~~f-J:~~~~1q,:_;~1;,----~;{~~1:~. f(.:#.~.-: ~ -~ _:._ ~~: ~
140 23 16 14 15 900 840 900
14 of 18
-_, -----
GP050SLA GP050SLB
CHEMICAL
-· --· -
TABLE 2-4
SOIL SAMPLING SUMMARY • INORGANICS
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
GP051SLA GP051SLB GP051SLC GP052SLA
~----Section 2
Soll Sampling Investigation
GP052SLB GP053SLA
15 of 18
--· -
CHEMICAL
ALUMINUM
ANTIMONY
ARSENIC
BARIUM
BERYLLIUM
CADMIUM
CALCIUM
CHROMIUM
COBALT
COPPER
IRON
LEAD
MAGNESIUM.
MANGANESE
NICKEL
POTASSIUM
SELENIUM
SILVER
-
SODIUM : , ,
TOTAL MERCURY
VANAD)U¥ · '"
ZINC
---
GP053SLB GP053SLC
- - ---- -- - ---Section 2
Soll Sampling Investigation
TABLE 2-4
SOIL SAMPLING SUMMARY -INORGANICS
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
GP054$LA GP054SLB GP054SLC GP055SLA GP055SLB GP056SLA
16 of 18
--
CHEMICAL
ALUMINUM
ANTIMONY
ARSENIC.
BARIUM
BERYLLIUM
CADMIUM
CALCIUM ·'.
CHROMIUM
COBALT
COPPER
IRON
LEAD
MAGNESIUM
MANGANESE
NICKEL
POTASSIUM
SELEN.1~~
SILVER
-
SODIUM~ .....
TOTAL MERCURY
VANADIUM
ZINC
- -
GP201SLA GP201SLA
(Duplicate)
- -- - -
TABLE 2-4
SOIL SAMPLING SUMMARY -INORGANICS
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
GP202SLA GP202SLA
(Resample)
GP203SLA GP204SLA
-- - - -
Section 2
Soil Sampling Investigation
GP205SLA GP206SLA
17 of 18
---
CHEMICAL
ALUMINUM
ANTIMONY
ARSENIC
BARIUM
BERYLLIUM.
CADMIUM
CALCIUM
CHROMIUM
COBALT
COPPER
IRON
LEAD
MAGNESIUM
MANGANESE
NICKEL
POTASSIUM
SELENIUM
SILVER
-
SODIUM .·
TOTAL MERCURY
VANADIUM
ZINC
----- -- ---
TABLE 2-4
SOIL SAMPLING SUMMARY -INORGANIC$
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
- - - -
Section 2
Soll Sampling Investigation
GP207SLA GP208SLA GP209SLA GP210SLA GP211SLA GP212SLA GP213SLA GP214SLA
· 8§9.ifrtt~~-~~ ~:::':: .)·f Qir: ·: l t1~ \:.~ p1·oq~;;;~}~;.--fl%_J~f101!£l~lt~?10½'J~t;1:~./~{Zo.gQ:£ltit'lt:;J~pq_<··; :~-: -~ {·;.: .. 4.~~q ~· .' :.
2 UR 2 UR 2.1 UR 1.8 UR 2.3 UJ 2 UJ 1.9 UJ 1.9 UJ
. ~.-J~:-i ~---~: f·: :: :~,)~> .:-b; :· ··f1 .. ;i_,:;~~~ -:?t?_~.,r1{~;(J~,t~ri1{:t:1·;QiiI•~t,~ :t·-~f2f~f J-t~r~:;,,i:/tt ~> ,'. -~-::_: ; .. 1.2 u-•
37 34 31 30 37 31 38 25
_. _.f ~(\~-•-•-~•.:_: ... ; ·J __ ~·:_.J~:> · <, J. g:./:.t~1{~.:;_._:d:1lt~sr:.:tf:1~~(·.1Ji.~{£H:2·:·~~~~;r~tf:!f·-\::.·ri:·~1 t.f'"_.;l ·::::·::-:_ -~.1 ~
0.14 U 0.14 U 0.15 U 0.13 U 0.2 U 0.18 U 0.17 U 0.17 U
41oo·j T'·:Hbo_o_·_.·:1.· 1,ioa:i ... '"":fioo'J.·., .. :,:·~~·ssoa;i:;,;:,;,,,;·7soo·,'.:r:'",:·420 . .-'.·socio· -,-•-• "~ -~ -.-•. '1\,. "' •••~~•••.,,l, ' -••• .,. ~' "'••-" •-•• •-
12 13 15 7.1 26 14 4.6 6.8
· 1 i.i" .-{-·.:'. ·, .:_:··. ~-'1 .u ..... , .· . o:~t~Q ~-.i~~-/i ::~;~;Q:.ff.[tJ/(~:"~~Q;~li-.!-.L~[[~~l t9.?tf Jti:lJ::·:·9:1~ µ _-_'.-:~ o:1s -~
5.7 7.1 6.2 5 U 5 U 4 U 3 U 2 U
1200g " , : .· : 1oqpg ,.\)) 1,~q!i: >.t: :.:: :.s1qt:.'~/~;;j:sj9.q,:_i:J,'.: :·:,:}·{l°Q.o,; .r::<_;:: ~'¥bi?' .. 2.100 :; 12 J 12 J 14 J 8.6 J 16 J 19 J 12 J 7.3 J
1!60 .,,;c ~-,. . 11~1? · • · :Gg_q_; f_: · /·~.:~~!!~ •~ ':;:}-_;:-j_iiJ .. ,; t6/~-' ;:~iQ:.''{:. . . .. '~gQ ·. ; .·., : 4~0 · .. ·.
100 85 58 69 81 79 97 54
1,ii / ,;.< \ 1,;; ,! , •. _,< !-.l_J;_ '· :·.:)t~I1/1I01E:{.'.fi ,:tf;ii': i.,ti~·d:-~\.'.:;-/;;jj _J. ,,j 2.1 J.
600 U 570 U 460 U 380 U 330 U 320 U 120 U 210 U a,~§ _95_,;;:· / ci:'7~. Q ,.-:\ 0~79 u, ,,:·1·:·:Yod;iJ,'-:.•::,i1;6's61J .·.· ·: :!7.'®5---;u,,;; ;., :;.:.0.12 u ~/ --\Q.7~.u. .
0.46 U 0.45 U 0.48 U 0.42 U 0.52 U 0.45 U 0.44 U 0.45 U
· 1~lj il:;:·•~::.:·, )~9-lJ' : •:•: .· ·196 t:f; :,,."(t•<-,{fi:o:iJ:·J''.';l•1,~::2'fo u1:c: ,;:~,:,c•~w;tY'. :· .. )§~ lJ_ .Jso u
0.05 U 0.05 U 0.05 U 0.05 U 0.06 U 0.05 U 0.05 U 0.05 U
... :.2~; :h.~ ~ _ _.~\;ii~~;~'-·~~'.==:··· .l.if :~;;~~~t?1:·~~~1J~:rr.f;~ri~tlt:1:c~f~~~it1~~-ft1:_-:~~),.tt~::~ _LL .. · ·;·~~·--.-··-~ !~ /_.
~J UJ nJ 19J U ~ 12 18
18 of 18
-
i i
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I
I
Volatile Organic Contamination
Section 2
Soil Sampling Investigation
The RI investigation soil sampling results did not reveal significant contamination of
volatile organic constituents in surface soils or to the sampled depth of 52 inches bis
for both onsite and offsite soil samples. Seven volatile organic constituents were
detected with toluene and carbon disulfide being the most prevalent. Toluene was
detected only as an estimated value below the detection limit of the analytical method.
Carbon disulfide detections ranged from estimated values of 2 to 810 µg/kg. The
estimated concentration of 810 µg/kg was detected in GP009SLB. Other carbon
disulfide concentrations were significantly lower. Chlorinated volatile organics were
detected but were only an estimated concentration below the method detection limit.
No areas of significant volatile organic contamination were identified either onsite or
offsite based on this data.
Extractable Organic Contamination
The extractable organic compounds, predominantly the polynuclear aromatic
hydrocarbons (PAHs), were extensively detected in surface and subsurface soils
throughout onsite and off site soil. However, most of the detections highlighted in the
tables were below the method detection limits and reported as estimated
concentrations. Some of the soils contained concentrations of the carcinogenic PAHs
( cP AHs) near or an order of magnitude above the detection limits. The highest
constituent detected was pyrene at 18,000 µg/kg in the soil sample collected from
GP044SLB. Samples from GP044SLB, GP046SLB, and GP049SLC all contained PAHs.
Offsite locations GP201SLA, GP202SLA, and GP214SLB contained P AHs just below
the method detection limit. However, locations GP202SLA (resample) and GP214SLA
both contained a signficant level of PAHs with the highest concentration of fluorene at
9100 µg/kg in GP214SLA. Figure 2-2 shows the depth intervals and concentrations of
P AHs and cPAHs detected above the method detection limits for onsite soils. Figure
2-3 shows the concentrations of PAHs and cPAHs detected above the method
detection limits for offsite surface soils.
Figure 2-2 shows the areas of the site as potential areas of significant P AH
contamination. These areas were typically located in former process areas centrally
COM ·Federal Pmi:nuns Corpor.iclon
SPIINB2/SEC2.WPD 2-77
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A
A
B
C \ o
B 14
B ,--;-:ra,-, .I 49
A
A
0 300' -----
C
600'
Georgia-Pacific Hardwoods
i Pl mouth, North Carolina t:i---,;-==~----------1
N
c:::::J
C 0
[
LEGEND:
AEl&E PAH & cPAH's IN ug/kg
DEPTH INTERVAL
A <, \ \ )
V GRID
-···-RIVER
~ TREE LINE
~ RAILROAD
PAH and cPAH
Detected in 0nsite Soils
Figure No.
2-2 ~ CDM Federal Pro2rams Corporation .__,., ____ .._ 7/00
~L----------ii,,,.._ __________ _
-____ !ml, ___ _ I
111111 .. -
0
.1·
I
1·
.. /··
250'
Roanoke
River
.. /·
./·
500' ------• I
i Georgia-Pacific Hardwoods
~ Pl outh, North Carolina
~ COM Federal ProJll'Olllll Corporation I A.....,..,Qiipa--~ .....
QP-21D-SI.A 210. BE/\ ■ ,~
~210d
.,,. .,,.
OP-212
~\.~:::::-,
I LEGEND:
. I . . . ~-T .•
2110 □
Em3
I
PAH & cPk
Detected in Off~ite Soils
I
.. -- ---
N
D
D
D
D
D
D
SURFACE SOIL
SAMPLE LOCATION
GRAB SURFACE SOIL
SAMPLE LOCATION
D
D
D
D
PAH & cPAH's IN ug/kg
RIVER
TREE LINE
RAILROAD
Figure No.
2-3
7/00
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Section 2
Soil Sampling Investigation
located on the Georgia-Pacific property. The lateral extent of the PAH contamination
was not significant beyond the site property. However, as Figure 2-3 shows, there
were areas offsite which had low PAH contamination. These offsite areas were
located adjacent to the site where airborne or surface runoff could have impacted the
soils causing these areas of contamination.
Downward migration of P AHs into the shallow groundwater could have occurred
since some of the subsurface samples collected showed P AH contamination. See
section 4 for the discussion of PAHs in groundwater.
Prior to initiating the removal action, the P AH analytical data were compared to the
SSRALs established for the site. Only Grid 44 exceeded the SSRALs for Total PAH.
The SSRALs for cPAHs was also nearly exceeded in Grid 44.
Pesticides and Polychlorinated biphenyls
Trace levels of chlorinated pesticides were detected in the onsite and offsite soil. The
most frequently detected pesticide was 4,4'-DDT with the highest concentration
reported as 69 µg/kg in GP019SLA. However, PCBs mixtures were detected at
significant levels in several samples collected onsite. None of the offsite soil contained
PCBs. Aroclors 1254 and 1260 were the only PCBs detected with the highest
concentration being 13,000 µg/kg of Aroclor 1254 in GP046SLC. Also noteworthy was
that the level of Aroclor 1254 at this location increased as sample depth increased.
(GP046SLA -410 µg/kg, GP046SLB -3300 µg/kg, and GP046SLC -13,000 µg/kg.
Groundwater is just below the SLC sample depth. The next highest concentration of
Aroclor 1254 was detected in GP017SLB. However the 3200 µg/kg of Aroclor 1254
was not detected in the duplicate from the same sample location and depth. The
highest concentration of Aroclor 1260 was detected in GP044SLB at 2,800 µg/kg.
Figure 2-4 shows the depths and concentrations of PCBs detected above the method
detection limits for onsite soils.
Contaminant levels of pesticides and/ or PCBs did not reveal any significant source
areas on or off the site. However, Grid 46 PCB concentration did increase with depth
COM Federal Proi;:mms Corporation
SPIINB2tSEC2.WPD 2-80
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')er 0\ \JRoonoke
\) River
A
B
B
B N
0 300' 600'
Georgia-Pacific Hardwoods
t Pl mouth, North Carolina ~1-,.;,,;;~;.;... ........... _____ __,
N
I
[
A 1~::~~ ~i~ PCB's IN ug/kg
DEPTH INTERVAL
ND NON DETECT
A < 1 \ \ > GRID
V
--···--RIVER
~ TREE LINE
~ RAILROAD
PCBs
Detected in Onsite Soils
Figure No.
2-4 ~ CDM Federal Pro£rams Corporation ,_., ____ .._ 7/00 ~a__ ______ ___,1,, _________ ,______,
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Section 2
Soil Sampling Investigation
which would indicate a downward migration into the shallow groundwater. See
section 4 for discussion of groundwater sample analysis in or near Grid 46.
Dioxin/Furan Chemical Contamination
Varying concentrations of dioxins and furans were detected in all the samples
collected both at the surface and in the subsurface soil. This was for both onsite and
offsite sample locations. Octachlorodibenzodioxin (OCDD) was the most frequently
detected dioxin and had the highest concentrations. The highest OCDD was detected
in the sample collected from GP040SLA and reported as 10,000,000 ng/kg (equivalent
to 10,000 µg/kg). Other dioxins and furans were also reported in the sample from
GP040SLA and the toxic equivalent value (TEQ) was estimated at 27,000 ng/kg. The
TEQ is calculated to normalize the toxicity of the detected dioxin-like compounds to
the toxicity of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), the most widely studied
and most toxic of the dioxins. Each dioxin-like compound is assigned a toxic
equivalence factor (TEF) as defined in Interim Procedures for Estimating Risks
Associated with Exposures to Mixtures of Chlorinated Dibenzo-p-dioxins and
Dibenzofurans (CDDs and CDFs) and 1989 Update (EPA, 1989). The TEQ is the sum
of the concentrations of the dioxin-like compounds multiplied by their respective
TEFs. The TEQ reported in GP041SLA was estimated as 28,000 ng/kg with OCDD
detected at an estimated concentration of 8,100,000 ng/kg. The other grids which
contained notable concentrations of dioxins and furans included: GP037, GP039,
GP041, GP046, GP047, and GP051. Samples collected from GP046 showed TEQ
increasing as samples were collected deeper from 11 ng/ kg in the GP046SLA, 97
ng/kg in the GP046SLB, and to 1300 ng/kg in the GP046SLC. These concentrations
were estimated. However, the TEQ concentrations decreased with increasing depth in
the three sample intervals from GP041, GP051, and GP053. Figure 2-5 shows the TEQ
values for the surface soil locations where the TEQ was greater than 100 ng/kg.
Figure 2-6 shows the TEQ values for the subsurface soil locations where the TEQ was
greater than 10 ng/kg.
The samples collected in the neighborhood contained dioxins and furans. The TEQ
concentrations in the neighborhood ranged from non-detected (quantitation limit of
CDM Federnl Pmi:rnms Corporation
SPIINB2/SEC2.vVPD 2-82
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0 - -
Roanoke
River
300' - - -
600'
Georgia-Pacific Hardwoods
Pl outh, North Carolina
I c:::::i N
LEGEND•
SURFACE SOIL TEQ IN ng/kg ~-::-g 100-1,000 .. -~ JI_IJI:, 1,001-10,000
(NOT DETECTED IN THIS RANGE)
10,001-100,000
GRID
RIVER
TREE LINE
RAILROAD
Dioxins and Furans TEQs
Detected in 0nsite Surface Soils
Figure No.
2-5
~ COM Federal Prol!l'IIDUI Corporation ._ ... .,_,_~--7/00 IL-______ ...L.. ________ ........__
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'B
Roanoke
River
C~I=□~
e5J□i-~r-----..._
300' - --- -
600'
Georgia-Pacific Hardwoods I 1-.:P.:l.:;;;;O;.;u;;;t.h=•-N;.;.;;o .. rt.h,;;;;;;..,;C;.;ar;;.;o;;;li;;;;"n;;;;a ... -l
N
c:::::i
/
[
,~BfiB DIOXINS & FURANS IN ng/kg
DEPTH INTERVAl.S
NA NOT ANAL YlED
GRID
-----RIVER
TREE LINE
RAILROAD
Dioxins and Furans TEQs Detected
in Subsurface 0nsite Soils
e No.
2-6
~ COM Federal Pron-ams Corporation ,_.,.,._.......... '7/00 ~L.-_______ ..__ _____________ _
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Section 2
Soil Sampling Investigation ·
1.9 ng/kg) to 36 ng/kg. The sample from GP205SLA contained the highest TEQ of
36 ng/kg and the highest concentration of OCDD of 27,000 ng/kg.
The analytical data and Figures 2-5 and 2-6 show the general areas of dioxin and furan
contamination potentially occurring from source areas on the site. Other dioxin and
furan concentrations were below the site source area levels. In addition no significant
downward migration is evident in the data collected.
Grids 40 and 41 were selected for excavation during the removal action due to
exceedance of the TEQ of 1 µg/kg (1,000 ng/kg) SSRAL. See the Post Removal Data
discussion below for further discussion of the selection of grids requiring excavation.
Inorganic Chemical Contamination
The following table summarizes the ranges of concentrations in mg/ kg of metals
detected in the surface and subsurface soils collected onsite and offsite.
ONSITE OFFSITE
Metal Minimum Maximum Minimum Maximum
Aluminum 520 16,000 2,900 11,000
Antimony 0.55 600 1.6 260
Arsenic 0.82 83 1.1 18
Barium 2.6 2,200 25 120
Beryllium 0.07 2.5 0.22 1
Cadmium 0.13 3.3 0.13 0.22
Calcium 210 130,000 420 21,000
Chromium 1.3 270 2.8 26
Cobalt 0.44 24 0.72 2
Copper 0.43 260 2 17
Iron 300 48,000 2,400 13,000
Lead 1.4 3,300 7.3 2,300
Magnesium 54 9,500 200 890
Manganese 2.5 3,400 54 260
Nickel 0.65 310 0.77 4.3
Potassium 18 17,000 120 600
Selenium 0.59 1.6 0.7 1.1
Silver 0.22 270 0.34 0.55
Sodium 50 4,500 130 220
CDM FederJl Proi;n11ns Corporation
SPIINB2/SEC2.WPO 2-85
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Section 2
Soil Sampling Investigation
ONSITE OFFSITE
Metal Minimum Maximum Minimum Maximum
Total Mercury 0.05 4.4 0.05 0.11
Vanadium 1 110 4 25
Zinc 1.8 1.000 12 72
In general, the onsite soils showed higher concentrations of the nutrient metals;
calcium, iron, potassium, and sodium, than offsite soils. Aluminum was the other
metal detected at a significant concentration however was similar to offsite
concentrations.
Other metals were detected at higher concentrations at individual grid locations
compared to the site average concentrations. Arsenic was detected in grid sample
GP049SLA at a concentration of 59 mg/kg and at a concentration of 83 mg/kg in
GP049SLB. The highest concentration of arsenic detected in an offsite location was an
estimated concentration of 18 mg/kg at GP202SLA. Barium was detected in
GP049SLC at a concentration of 2,200 mg/kg, whereas the highest concentration of
barium detected off site was 120 mg/kg in GP206SLA. Chromium was detected at 270
mg/kg in GP039SLA whereas the average concentration of chromium including
offsite was less than 15 mg/kg. The highest concentration of copper was also detected
in GP039SLA at 260mg/kg. Lead was detected in GP046SLC at an estimated
concentration of 3,300mg/kg and in GP202SLA (offsite) at an estimated concentration
of 2,300 mg/kg. The lead concentration increased with depth for the samples
collected in grid GP046. The majority of soil samples collected onsite and offsite
contained lead concentrations less than about 50 mg/kg. The highest magnesium
concentration was detected onsite in GP056SLA at 9,500 mg/kg. Another metal with
a significant high concentration was zinc, which was detected in GP046SLC at an
estimated concentration of 1,000 mg/kg. At this sample location the zinc
concentration increased as the depth increased which is similar to the lead
concentration also at this location. In addition, zinc was detected in GP049SLA,
GP049SLB, and GP049SLC at concentrations of 900,840, and 900 mg/kg, respectively.
Most of the other soil samples both onsite and off site contained zinc concentrations
CDM Federal Pmi:rams Corporation
SPIINB2/SEC2.W'PD 2-86
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Section 2
Soil Sampling Investigation
less than 100 mg/kg. Figure 2-7 shows the onsite sampling grids with the highest
detections of metals other than the nutrient metals.
Post Removal Data
Table 2-5 presents the detected contaminants of concern from the removal action
confirmation samples collected by BBLES. EPA reviewed the RI data ·and selected
grids for excavation. The method of selecting grids for excavation was based on
elevated contaminant levels of various constituents as well as physical evidence of
former site activities. Elevated concentrations of dioxins, furans, (expressed as TEQ),
metals, or PAHs were compared to the SSRALs established by the EPA. Metals,
dioxins, furans, or PAHs were evident as the primary contaminants in grids 39, 40, 41,
44, 46, 47, and 49. These grids were selected for excavation along with an area along -the southern portion of the site which was formerly the asphalt mixing plant.
However, later focused sampling of the areas of the former asphalt mixing plant did
not reveal any contamination exceeding the site specific removal action levels. A more
detailed discussion of the reasoning and methods for resampling these grids was
provided in the Removal Action Summary Report. Following the excavation and
off site disposal of the soil, samples were collected from the bottom of the excavations
to confirm the adequate removal of the contaminants. For grids 1, 2, and 3, only the
arsenic concentration from the RI data slightly exceeded the SSRALs. Upon
recommendation by Georgia-Pacific and concurrence by EPA these grids were
resampled prior to the removal action. Table 2-5 above provides a confirmation that
the targeted constituents were removed.
COM Ftdernl Pnl):nnns Cnrpurmion
SPIJNB2/SEC2.WPO 2-87
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A B C
0
As
B
N
Roanoke
River
,Pb Zn
A ~~6>.:t(::+:~i;Jl,"JP
BC tf1 ~O!QJill!.QO!Q!O!bJ d_ 00J 1000J
A
Cr
Ba
N
N
Cu
Zn
300' ---600'
Georgia-Pacific Hardwoods J ._...;,P.;l.,,;,;m;,;,o,,;,u=t;;,;h,:,., _N;,,;,,;;o,,;,r,,;,th ___ c_a_r_o_I_in_a_,
I
LEGEND:
Cr
A I 27□ I
NA
A <, \ \ )
V
0
0
[
METALS
DEPTH INTERVAL
NOT ANALYZED
GRID
RIVER
TREE LINE
RAILROAD
N
Metals Detected in
Onsite Soils
Figure No.
2-7
CDM Federal Proarams Corporation
,,_.,_,,_ .... "... 7/00 ~L.,_ _______ _.___ ___________ __,
e 1/ - - --
CHEMICAL
Pab'.1:bl2[illated Uilu:niodiolinsl'.Dibenio[ucaos (ne&e)
HeptaCDD
HeptaCDF
OctaCDD
OctaCDF
2,3, 7,8-TCDD TEQ (SSRAL = l µglkg)
Polrnuclear A[orn~tk lil:'.dtos:atb:ons (uelke)
Fluoranthene
Pyrene
Benzo(b)fluoranthene (cPAH)
Total PAHs (SSRAL=l00,000 µglkg)
Total cPAHs (SSRAL=50,000 µglkg)
Pentachloroohenol (ne/kel
Pentachlorophenol (SSRAL=25,000 µglkg)
Jnoreanits (mg/kg)
Arsenic (SSRAL=30 mg/kg)
Chromium (SSRAL=200 mg/kg)
Lead (SSRAL=400 mg/kg)
Notes:
cPAH = Carcinogenic polynuclear aromatic hydrocarbons
PAH = Polynuclear aromatic hydrocarbons
NA .. Not analyzed
ND =-Not detected
SSRAL • Site-specific removal action level
---- - -
TABLE 2-5
REMOVAL ACTION CONFIRMATION ANALYSES
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
!irill..ll !irilUlt !iri.!!..il !irill.M
--
~
----Section 2
Soil Sampling Investigation
!iriU1 !i.rilU2
CONF-39-COMP CONF-40-COMP CONF-41-COMP CONF-44-COMP CONF-46-COMP CONF-47-COMP CONF-49-COMP
NA I.I 1.2 u NA 1.3 U NA NA
NA 0.55 1.2 u NA 1.3 U NA NA
NA 0.7 J 1.6 UJ NA 1.7 UJ NA NA
NA 1.6 UJ 1.7 UJ NA 1.8 UJ NA NA
NA 0.017 ND NA ND NA NA
NA NA NA 200 J NA NA NA
NA NA NA 220 J NA NA NA
NA NA NA 180 J NA NA NA
NA NA NA 600 J NA NA NA
NA NA NA 180 J NA NA NA
NA 3040 UJ NA NA NA NA NA
16 NA NA NA NA 1.4 10
33 J NA NA NA NA NA NA
NA NA NA NA 7.8 NA NA
-
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3.0 Surface Water/Sediment Sampling
Investigation
3.1 Purpose and Scope
Surface water and sediment sampling were conducted in the intermittent drainage
ditches located onsite to determine the nature and extent of contamination in these
areas. Three surface water and seven sediment samples were collected from the
drainage ditches. The locations of all the sur ace-water and sediment samples are
shown on Figure 3-1. Note that it was intended for both a surface water and a
sediment sample to be collected from each sampling location. In four locations,
however, there was insufficient surface water to collect samples.
3.2 Methods
All surface water and sediment samples collected were grab samples and were
collected according to the procedures established in the Remedial Investigation Work
Plan (EPA, 1998) for the Georgia Pacific Site, and Section 4 of EPA's Environmental
Investigations Standard Operating Procedures and Quality Assurance Manual
(EPA, 1996). The surface water samples were collected from several inches below the
air-water interface and sent to a CLP laboratory for analysis of all TCL/TAL
constituents. Sediment samples were collected from the zero-to three-inch interval
below the water-sediment interface and sent to a CLP laboratory for analysis of all
TCL/TAL constituents as well as for dioxin/furan analysis.
3.3 Summary
The analytical results for the surface water and sediment samples collected at the site
are summarized in Tables 3-1 (surface water), and Tables 3-2 through3-4 (sediment).
Note that for the purpose of summarizing, only chemicals detected at least once in
each medium and their measured concentrations are presented in the summary tables.
The complete data set of analytical results for the CLP laboratory analyses performed
are provided in Appendix A.
CDM Federal Programs Corporation
3-1
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0 - ---
Roanoke
River
300' 600'
Georgia-Pacific Hardwoods ~ Pl mouth, North Carolina E ~"'----------.......... -----1
~ COM Federal ProKrams Corporation ~ A subsidbry al ~ ,i,_. • Mi:i"N h:.
LEGEND:
SW-01.
,--..,....,,
N
SURFACE WATER SEDIMENT
SAMPLE LOCATION 3 ~
SEDIMENT SAMPLE
LOCATION
RIVER EDGE
TREE LINE
----PROPERlY BOUNDARY
INTERMITTENT DRAINAGE
DITCH
MARSHY AREA
Surface Water/Sediment
Sampling Locations
Figure No.
3-1
6/00
- -----------------
°P
CHEMICAL
VOLATILE ORGANICS
INORGANICS
Pata Qualifiers
TABLE 3-1
SURFACE WATER SAMPLING SUMMARY
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
SW-3 SW-3
(Dup.)
SW-4
U-Material was analyzed for but not detected. The number is the minimum quantitation limit.
----
SW-7
Section 3
Surface Water/Sediment Investigation
Concentrations presented in ug/L. Concentrations printed in bold italicized text are considered to reflect a valid detection of unnatural contamination.
I
-
-- ---
CHEMICAL
----- ---
TABLE 3-2
SEDIMENT SAMPLING SUMMARY -DIOXINS/FU RANS
GEORGIA-PACIFIC SITE
SD-1
PLYMOUTH, NORTH CAROLINA
SD-2 SD-3 SD-3
(Dup.)
SD-4
--
SD-5
- - - -
Sectlon 3
Surface Water/Sediment Investigation
SD-6 SD-7
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1,2,3,4,6,7,8-HEPTACHLORODIBENZOFURAN 2400 J 970 J 730 J 580 J 2400 J 9.4 U 9.3 U 470 J
1@@,l!i1Vkl!!Bgl'lfAWB@lRQi?i1}~¢lWM!\lT!I'H :?1-10; tlti! ••·<·•·:54; ·•·•·•·•·•;·•••·••·< Wr<•·••••; t•Mfi's/il ••·••··•······················· •4:itu ...•.... ·.·•·•·•·•·•·····•·• Dl7rn \~iii#
1,2,3,4,7,8-HEXACHLORODIBENZODIOXIN 94 J 40 J 63 J 44 J 290 J 4.8 U 4.7 U 34 J
w~~A!r;jli!i/~BJ\9899i~l(j,jg,q/;Q!l§f:1El[;.ttJ#: •• iii';! ; ;;; ;;3o;tc;• ::;;:n;v;;r: Leng; '. ·;•;t4)KU ' 4'.'/FlJ.'.'.• >• ••11'/Y
1,2,3,6,7,8-HEXACHLORODIBENZODIOXIN 380 J 150 J 210 J 160 J 1000 J 6.9 J 4.7 U 160 J
ti~ti&itili!B§iA¢Hli9RQ@l~.~j,jgtjj\QB#f:i is§)W t\C·•··•3a J' ····················•rn•i~tr::L············· :·~~!H•W •)Tr;ifE••·•w C Ai!F\l :: ;: i!?!l'.'.ZTL : ~§i!!A1
1,2,3,7,8,9-HEXACHLORODIBENZODIOXIN 200 94 120 82 460 8 4.7 U 92 J
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1,2,3,7,8-PENTACHLORODIBENZODIOXIN 48 19 J 34 J 21 J 160 4.8 U 4.7 U 23 J
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2,3,4,6,7,8-HEXACHLORODIBENZOFURAN 61 J 27 J 34 J 17 J 79 J 4.8 U 4.7 U 16 J ~1$)#;1i!¾efillIAQB~QRQQ!fl~NZ9iH!!!!§i.i . .,; ;: ;; :; 2'/J/ j I%¥HW1ff Wi G•&/Pil •· ... •' • a Ji ; . ;• : Jq:'J;;;; • . ;4;a;u, • ;; ;<• A%U•;•• •.;. . : 6;1;;(
2,3,7,8-TETRACHLORODIBENZODIOXIN 8.7 3 J 4.3 J 1.5 J 16 J 0.21 J 0.21 J 12 J
kl~izilifm@&j@QA¢Rl@N?.RRllflAN1ffi,fff1 ,!!@::;m :r:n::•:::n~i,tl!tn:•:n •.• s,1; u · ·, ••• • ·••• •• ,,.,3u• • •·· • •r·;12Mz••· .-, •••• .;.,uuJ::··· •>•· • LVJ• •••.•• / •100.t c:
HEPTACHLOROrnBENZODIOXIN (TOTAL) 15000 J 3300 J 8600 J 7700 J 23000 J 490 J 350 J 12000 J
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HEXACHLORODIBENZODIOXIN (TOTAL) 2400 J 1000 J 1500 J 1200 J 7400 J 81 J 49 J 1400 J
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OCTACHLORODIBENZODIOXIN 52000 58000 67000 56000 270000 6200 J 4400 J 82000
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PENTACHLORODIBENZODIOXIN (TOTAL) 350 J 150 J 200 J 140 J 1100 J 10 UJ 5 UJ 180 J
Pl;J\IJACtlkOROP!l31lNZOfURAN,ftdt/\li}•·•···········•····· .... ,> .. •,·•·•·•···•f·•·<·n••·••!150 .. M••••o;••I•.•····;·•····••i;1~:;;;r.> •.•... ; •....•••• -;;•···A~o .••• µ; ••••••••••• .., ••••.•.• \ ....... 11Qt!)fr;?y'••n·•·•i:<~1//•Ai•··••'••······•···· .. .;:;·.Ai&.µJ ....... ,,y••···············""'·l/J ....... ;·.••···"·•.Jhniihl•C••,·
TEO (TOXIC. EQUIV. VALUE, FROM I-TEF/89) 280 J 160 J 140 J 150 J 850 J 9.9 J 5.7 J 210 J
Tl:STI:~,N;;H!iQRPQ!$!ilitPPi~!NlIQT$lil ; l; •;t l @;: ~@WI •l! ;;J ##it ilrnrn i?9itiii !WF~ifii/H Hillfai.11.i/J\li#fiiltQl~t;m rn;rnrnl!4fi1!@1MUUM1J{({t
TETRACHLORODIBENZOFURAN (TOTAL) 470 J 150 J 180 J 140 J 450 J 3.3 UJ 2.9 UJ 250 J
Data Qualifiers
J-Estimated value.
U-Material was analyzed for but not detected. The number is the minimum quantitation limit.
R-QC indicates that data unusable. Compound may or may not be present. Resampling and analysis necessary for verification.
Concentrations presented in ng/kg. Concentrations printed in bold italicized text are considered to reflect a valid detection of unnatural contamination.
------
CHEMICAL
VOLATILE ORGANICS
\' _ ... fJ }
EXTRACTABLE ORGANICS
... - -----
SD-1
TABLE 3-3
SEDIMENT SAMPLING SUMMARY -ORGANICS
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
SD-2 SD-3 SD-3
(Dup.)
SD-4
- -
SD-5
- - - -
SecUon 3
Surface Water/Sediment Investigation
SD-6 SD-7
~~
~i~~~~i;RENE rrnr ; ~:;@J;,· •t 1~&iinm;vm11w;M1n Fffji§ij~jd p]g;~~+wrn:~;~~j rn t\~@Mwi prn; a~~rqt:;i;;qi~ij@Q!F
1.N······:.r ..•. : .... ~ ... E'.:.¢.".'.: ... ~.' •..•. :.· •. :.·~ .••.. ~.-.. FU.1
·~·,··.'.H.R.···.·~.;.••·.-.: ... c ... N .. ·.:.o.·· .. · .. · .. :.) .•. ·.· .. · .. :,i=~; ~.· .. :.·.,.· •. t.••.J·;····~.:.•····· .. !.· •. • ..•. :.i ... ··.,.::,.:.:.~.· .. 1.· •.. :.: ... : .•. •.··.:.!.·•·····;·:···:·:·:·:.·.:.·•·······.:.·.:.·.•·.·.l ... ·.! ... · ..... ;.: ... ;..! ... ·.•········;·· ···········.·.·:.:.·.•.· .. :. ·.· ... · •. :.:.·.· .. ·.:.· •. :.'.i.: .•. · .. ·.1 ...• ~.c .•.... 0
.:.·.•.•······.·.! ... :.; .•. '.;.· •. t.: .•. ·.··.~.: .•.... :.• .. ·.~o~.
0
.·.·.•.·.:.:.: .•...•. :.· •. :.:.· •. ·.•··•.:.·.: .•. • •. ~.: .•. -.i.:.· •.. go.~ .. : ... · •..•. ·.•······.! ....•... ·.:.;.:;.· .. :.· •. t.· ... · .. i.· .. •.:.:.······:.· •. • .. ~.·· .... =.·.:.· •. ·.:.·.:.· •. • .. • .. ··.:.:.:.• •. :.l.·•~.~.···o·o·
0
·.··•.··•····.!.·•····.·•.:.·.· .. •.·.·
~YR;;-;E '' ~ .....• •~@~)!i~!_\iUj 4700. 1400 U . .. . 3;~ ~ . .. ;00 J ;;;O ~ •c •;~~ ~ iii'. ~; ~ •;;;;; ~·
PESTICIPES/PCBS
l'Mi'.iPA!il!!i!!fi;\QWJ i
1,1':[) I) E.(f',f'.';[)(:l,lc) • •• 4¥H?PJE!!li!l'.tPPnk
ENDOSULFAN II (BETA)
Pata Qualifiers
J•Estimated value.
@w,fWM Mtff::iHiff%Jffs,&Ot11iMMMl!!Ulff H4iJltllrn #ii!li! );;51lfD;
150 12U 3.SU 14U 4U 4.9U 18U Y~t I&1gy;··· UP§@\l· .. •,··pq; MAl!JUMHt t~li/k!iMM#l!!!-H frMiiFAlKVit
14U 12U 3.SU 14U 4U 4.9U 18U
LI-Material was analyzed for but not detected. The number is the minimum quantitation limit.
Concentrations presented in ug/kg. Concentrations printed in bold italicized text are considered to reflect a valid detection of unnatural contamination.
------
CHEMICAL
Pata Qualifiers
J-Estimated value.
N-Presumptive evidence of presence of material.
---- - --
SD-1
TABLE 3-4
SEDIMENT SAMPLING SUMMARY -INORGANICS
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
SD-2 SD-3 SD-3
(Dup.}
SD-4
LI-Material was analyzed for but not detected. The number is the minimum quantitation limit.
- --- -
SD-5
Section 3
Surface Water/Sediment Investigation
SD-6 SD-7
Concentrations presented in mg/kg. Concentrations printed in bold italicized text are considered to reflect a valid detection of unnatural contamination.
-
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Section 3
Surface Water/Sediment Sampllng Investigation
In the summary tables, those concentrations considered to reflect a valid detection of
unnatural contamination are printed in bold italicized text to distinguish them from
the other measurements. Since organic chemicals are not believed to be naturally
occurring in surface water, any detection of an organic chemical in surface water is
considered to be unnatural contamination. The same is true for sediments. For the
inorganics in both surface water and sediments, since no background surface water or
sediment samples were collected at the site, the concentrations were compared to
typical background concentrations at other North Carolina sites in an attempt to
distinguish unnatural contamination from natural chemical concentrations.
3.3.1 Surface Water
As indicated in Table 3-1, the number of chemicals detected in the surface water
samples collected at the site was relatively small. The spectrum of chemicals detected
in at least one surface water sample from this area included only one volatile organic
and 11 inorganics.
Volatile Organic Contamination
Volatile organic chemical contamination in surface water appears to be relatively
insignificant. The only VOC detected in surface water was acetone and it was
detected in only one surface water sample (SW-7) at a concentration of 1§!l ug/1 SW 7
is located in the northeastern part of the perimeter drainage ditch near the Roanoke
River.
Inorganic Chemical Contamination
As indicated in Table 3-1, of the 11 inorganic chemicals detected in surface water at
the site, only two appear to be at concentrations which are clearly indicative of
unnatural contamination. These two chemicals, arsenic and manganese, were
detected at concentrations significantly above typical background concentrations in at
least two of the three surface water samples collected. The areal distribution of the
arsenic and manganese contamination found in surface water in this remedial ~
U I' ,.(\ rr-' U\, investigation is shown in Figure 3-2.
i4'5~
CDM Federal Programs Corporation
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Roanoke
River
0 300' I _ _,_ 600'
Georgia-Pacific Hardwoods ~ Pl mouth, North Carolina !~~;;..;.;_.....,_ __ _,
~ CDM Federal Pr011rams Corporation ~ A SUO:sidi:l'y o/ eo. D'ISw I: llcii. he.
LEGEND:
sw-01 e
00
-···-
~ ----
- - - -
• • •
SURFACE WATER SAMPLE
LOCATION
N
ARSENIC CONCENTRATION (ug/L)
MANGANESE CONCENTRATION (ug/L)
RIVER EDGE
TREE LINE
PROPERTY BOUNDARY
INTERMITTENT DRAINAGE DITCH
MARSHY AREA
Inorganic Contaminant
Distribution in Surface Water
Figure No.
3-2
6/00
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3.3.2 Sediment
Section 3
Surface Water/Sediment Sampling Investigation
As indicated in Tables 3-2 through 3-4, a wide variety of chemicals were detected in
the sediment samples collected at the site. The spectrum of chemicals detected in at
least one sediment sample from this area included 17 dioxins/furans, 2 volatile
organics, 14 extractable organics, 4 pesticides, and 14 inorganics.
Dioxin/Furan Chemical Contamination
As indicated in Table 3-2, numerous dioxins/ furans were found at concentrations
which appear to be significantly above typical background concentrations in all the
sediment samples except SD-5 and SD-6. The TEQ for the dioxins/ furans measured
in the sediments ranged from 9.9 ng/kg to 850 ng/kg. (See section 2.3 Dioxin/Furan
Chemical Contamination for an explanation of TEQ.) The areal distribution of the
dioxin/ furan contamination (as indicated by TEQ calculations) found in sediments in
this remedial investigation is shown inFigure 3-3.
Volatile Organic Chemical Contamination
As indicated in Table 3-3, only two VOCs were detected in any of the sediment
samples: acetone and methyl ethyl ketone. Acetone was found in 4 of the 7 sediment
samples at concentrations ranging from 350 ug/kg to 2800 ug/kg. Methyl ethyl
ketone was found in 3 of the 7 sediment samples at concentrations ranging from 84
ug/kg to 440 ug/kg. The areal distribution of the VOC contamination found in
sediments in this remedial investigation is shown inFigure 3-4.
Extractable Organic Chemical Contamination
The extractable organic contt!· µon found in.the sediments appears to be
significant at only one locati ~f the extractable organics detected in
sediments are PAHs, and at S >~1~ PAHs were detected with concentrations
ranging from 240 to 5600 ug/kg. The carcinogenic PAH concentrations in the SD-1
sediment sample range from 540 ug/kg to 4400 ug/kg. The total PAH concentration
measured in sediment sample SD-1 is 31,500 ug/kg while the total carcinogenic PAH
concentration measured is 13,840 ug/kg. A few PAHs were also detected in sediment
CDM Federal Programs Corporation
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Roanoke
River
.300' ---600'
Georgia-Pacific Hardwoods
Pl mouth, North Carolina
_/
/
/
LEGEND:
N
SO-I 18) SEDIMENT SAMPLE LOCATION
DIOXIN/FURAN TEO
CONCENTRATION (ng/kg)
RIVER EDGE
~ TREE LINE
----PROPERTY BOUNDARY
----INTERMITTENT DRAINAGE DITCH
MARSHY AREA
Dioxin/Furan Contaminant
Distribution in Sediment
Figure No.
3-3 CDM Federal Prol!rams Corporation ,..._.,_,._........ 6/00 ~.___ _______ ......... _________ _,,,&,,. ___ _____.
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Roonoke
River
300' 600'
Georgia-Pacific Hardwoods ! Pl mouth, North Carolina
~ CDM Federal Pro11rams Corporation ~ AJ&llld:fo,y,IC..,,ths...tlti.k
LEGEND:
ND
-···-
,....._ ,....,,....
----
- - - -
• • •
N
SEDIMENT SAMPLE LOCATION
ACETONE CONCENTRATION {ug/kg)
METHYL ETHYL KETONE
CONCENTRATION {ug/kg)
NON DETECT
RIVER EDGE
TREE LINE
PROPERTY BOUNDARY
INTERMITTENT DRAINAGE DITCH
MARSHY AREA
VOC Contaminant
Distribution in Sediment
Figure No.
3-4
6/00
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Section 3
Surface Water/Sediment Sampling Investigation
samples SD-3, SD-6, and SD-7, but at relatively low concentrations (ranging from 71
ug/kg to 350 ug/kg), and none of the PAHs detected in these samples are
carcinogenic. The areal distribution of the extractable organic chemical contamination
(as indicated by total PAH and total cPAH calculations) found in sediments in this
remedial investigation is shown in Figure 3-5.
Pesticide Chemical Contamination
Pesticide chemical contamination in sediments at the site appears to be relatively
insignificant. Three of the four pesticides detected are 4,4-DDX chemicals (4,4-DDD,
4,4-DDE, and 4,4-DDT), and they were found in only one sediment sample (SD-2) at
concentrations ranging from 190 ug/kg to 540 ug/kg. Likewise, the fourth pesticide
detected (Endosulfan II) was found in only one sediment sample (SD-1) at a·
concentration of 6.1 ug/kg. SD-2 is located in the southwestern part of the perimeter
drainage ditch near the entrance gate, while SD-1 is located in the northwestern part
of the perimeter drainage ditch near the Roanoke River.
Inorganic Chemical Contamination
As indicated in Table 3-4, of the 14 inorganic chemicals detected in sediments at the
site, only five appear to be at concentrations which are·clearly indicative of unnatural
contamination. Three of these five chemicals (arsenic, lead, and zinc) were detected at
concentrations significantly above typical background concentrations in several of the
sediment samples. The other two chemicals (barium and iron) were detected at
concentrations significantly above typical background concentrations in only one
sediment sample (SD-2). The areal distribution of the arsenic, lead, and zinc
contamination found in sediments in this remedial investigation is shown in Figure 3-
6. The arsenic and zinc contamination in sediments appears to be spread throughout
most of the length of the intermittent drainage ditches, having been detected at
elevated concentrations in SD-1, SD-2, SD-3, SD-4, and SD-7. The detected
concentrations of arsenic ranged from 3.7 mg/kg to 300 mg/kg, while the detected
concentrations of zinc ranged from 12 mg/kg to 340 mg/kg. The drainage ditch areas
considered to be contaminated with arsenic and zinc include the western,
southwestern, and northeastern segments of the perimeter drainage ditch. The lead
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Roanoke
River
300' 600'
Georgia-Pacific Hardwoods J Pl mouth, North Carolina
~ COM Federal Pro11rams Corporation ~ A subifaiy o/ ~ a,_. • »;Ka tc.
s0-1 ®
ND
-···-
~ ----
- - --
• • •
N
SEDIMENT SAMPLE LOCATION
PAH CONCENTRATION (ug/kg)
cPAH CONC£NTRATION (ug/kg)
NONDETECT
RIVER EDGE
TREE LINE
PROPERTY BOUNDARY
INTERMITTENT DRAINAGE DITCH
MARSHY AREA
PAH Contaminant
Distribution in Sediment
Figure No.
3-5
6/00
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Roanoke
River
300' --600'
Georgia-Pacific Hardwoods
f1-..;P:,.;l:...,::m=ou=th;:,,:...:,N,;.;o;.:r~t,;.;h;...;;C.;;a;:,r,;;,ol;.:i,;.;n.;;a~
~ COM Federal Proirrams Corporation ~ A rumi6oty ol ea.. a,-~ Ati"• tic.
50-1 @
Eiffl
ND
-···-
~ ----
- - ---• -
N
SEDIMENT SAMPLE LOCATION
ARSENIC CONCENTRATION (mg/kg)
LEAD CONCENTRATION (mg/kg)-
ZINC CONCENTRATION (mg/kg)'----'-
NON DETECT
RIVER EDGE
TREE LINE
PROPERTY BOUNDARY
INTERMITTENT DRAINAGE DITCH
MARSHY AREA
Inorganic Contaminant
Distribution in Sediment
Figure No.
3-6
6/00
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Section 3
Surface Water/Sediment Sampling Investigation
contamination also appears to be spread throughout much of the length of the
intermittent drainage ditches, having been detected at elevated concentrations in SD-
1, SD-2, SD-3, and SD-4. The detected concentrations of lead ranged from 5.7 mg/kg
to 140 mg/kg. The drainage ditch areas considered to be contaminated with lead
include the western and southwestern segments of the perimeter drainage ditch.
COM Federal Programs Corporation
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4.0 Groundwater Sampling Investigation
4.1 Purpose and Scope
Groundwater sampling was conducted at the site in both new temporary well points
and existing shallow monitor wells to fully assess the types and concentrations of
contaminants present in the underlying shallow aquifer, and to determine the extent
and magnitude of groundwater contamination in the shallow aquifer at the site. A
total of five temporary well points were installed at the approximate locations shown
in Figure 4-1 to supplement the nine existing monitor wells installed previously at the
site (also shown in Figure 4-1) prior to this remedial investigation. Note that the nine
existing monitor wells were all constructed with 2-inch diameter PVC.
4.2 Methods
One groundwater sample was collected from each of the. five temporary well points
and the nine existing monitor wells identified above. These samples were sent to a
CLP laboratory for complete TCL/TAL analyses. Just prior to sampling of each
monitor well, field measurements of the well depth, depth to water, groundwater
temperature, pH, conductivity, and turbidity were taken, and the results are provided
in Table 4-1. All groundwater samples collected were grab samples and were
collected according to the procedures established in the Remedial Investigation Work
Plan (EPA, 1998) for the Georgia Pacific Site, and Section 4 of EPA's Environmental
Investigations Standard Operating Procedures and Quality Assurance Manual
(EPA, 1996).
4.3 Summary
The concentrations of chemicals detected in the groundwater samples collected at the
site are summarized in Table 4-2. Note that for the purpose of summarizing, only
chemicals detected at least once in groundwater and their measured concentrations
are presented in the summary table. Complete analytical results for the CLP
laboratory analyses performed are provided in Appendix A. In Table 4-2, those
concentrations considered to reflect a valid detection of unnatural contamination are
printed in bold italicized text to distinguish them from the other measurements.
CDM Federal Programs Corporation
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Roanoke
River
300' - --600'
Georgia-Pacific Hardwoods
ii--P-l ..,m_o_u_t_h_,_N_o_r_t_h_C_a_r_o_li_n_a __ -1
~ CDM Federal Pro11rams Corporation
/
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LEGEND:
MW-I.
TMW-1®
,..._,_.._..,
N
EXISTING MONITORING
WELL LOCATION
TEMPORARY MONITORING
WELL LOCATION
RIVER
TREE LINE
PROPERTY BOUNDARY
INTERMITTENT DRAINAGE
Well Location Map
Figure No.
4-1
A a.midio,y ol ~ ~ • M:i'• .he. ~------------------------__,ji....s..;./_o_o__,
---------------- ---Section 4
Groundwater Investigation
TABLE 4-1
GROUNDWATER SAMPLING FIELD MEASUREMENTS
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
Well Total Depth Depth to Water Temperature Conductivity Turbidity
Number (ft) (ft) (°C) pH (umhos) (NTUs)
MW-1 19.3 7.6 18.9 6.5 717 5.3
MW-2 15.3 7.8 21.1 6.6 447 6.7
MW-3 17.4 8.4 18.4 6.2 1491 53.4
MW-4 18.2 5.9 20.0 6.5 1196 2.5
MW-5 42.3 8.6 17.5 6.8 488 3.0
MW-6 17.1 6.0 19.6 6.5 434 5.9
MW-7 17.3 5.8 20.6 6.3 807 5.5
MW-8 16.2 5.3 20.7 6.3 601 27.6
MW-9 15 8.1 19.7 6.7 1183 4.4
TW-24 9 19.2 7.5 1892 132
TW-29 9 22.0 6.2 736 12.3
TW-49 10 18.9 5.1 1169 394
TW-51 12.3 5.4 1085 408
TW-54 7.5 6.5
--.. ----- --- - ----- --Section 4
Groundwater Investigation
TABLE 4-2
GROUNDWATER SAMPLING SUMMARY
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
MW-1 MW-2 MW-3 MW-4 MW-5 MW-6 MW-6 MW-7
CHEMICAL (□up.)
VQLATILE QBGl\t,!IQS G;,v-,STO~IL.
EXTAAQTABLE QRGANIQS
INQBGI\NIQS
--·-c:, u 140 SJ 140 990 4 U 4U 4U •••
IA
!CALCIUM osnnn 58000 1snnnn 130000 .450()0 51000 45000 92000
COBALT 2U 2U 2 U 2U 2U 2 U 2 U 2 U
, IRON :,,aO
·-
13000 1800 ssnnn 35000 1400 1snnn ,snnn ssnnn
osnn 7~0(1 ?onnn 21non . 43()0 4700 4fo() 7Jg~H!I
UM 22000 J 4700 J 24000 J -~~-000 J 2700 J S?MJ sonn J 12000 J
...... :.: 2U 2U 2 U 2U 2 U ? II ? II 2 II
Pata Qualifiers
J-Estimated value.
U-Material was analyzed for but not detected. The number is the minimum quantitation limit.
Concentrations presented in ug/L. Concentrations printed in bold italicized text are considered to reflect a valid detection of unnatural contamination.
-.. ---- -
MW-8
CHEMICAL
VQLAIILE QBG/lt,IICS
E~IB/ICT/l!;!LE QBQMICS
-111_ .. '.-'L..l'IL.. tjr:~; 10 U
IFLL,~ ,_ 10 U
INQBG/ltllCS
ijA~@M1 22
CALCIUM 67000
!COBALT 2U
IIRON 30000
;'.;,;~,~~~ 9200
'"Ju1 •11 ••• asnn J
" .. sJ
Pata Qualifiers
J-Estimated value.
- ----
TABLE 4-2 (cont.)
GROUNDWATER SAMPLING SUMMARY
GEORGIA-PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
MW-9 TW-24 TW-29
10 U 10 U 10 lJ
10 U 10 U 10 U
28 26 an
110000 220000 7400()
2 U 5 J 8 J
8900 67000 ssnnn
33000 •snnn 1snnn
72000 J 30000 J 18000 J
2U 3 J 2 U
U-Material was analyzed for but not detected. The number is the minimum quantitation limit.
- - -
TW-49 TW-51
10 U 10 II
10 U 10 U
~ 4 II
unnnn J 1 rnnnn
4J 2 U
tii! 1onnn
i•nnn
49000 J sannn J
"J 2U
Concentrations presented in ug/L Concentrations printed in bold italicized text are considered to reflect a valid detection of unnatural contamination.
-- -
TW-54
,j
2 J
1sn~ii
•• J
46000 .
1snnn
30000 J
S?
Section 4
Groundwater Investigation -
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Section 4
Groundwater Sampling Investigation
Since organic chemicals are not believed to be naturally occurring in groundwater in
this area, any detection of an organic chemical was considered to be unnatural
contamination. For the inorganics, since no background groundwater samples were
collected at the site, the concentrations were compared to typical background
concentrations at other North Carolina sites in an attempt to distinguish unnatural
contamination from natural chemical concentrations.
As indicated in Table 4-2, a wide variety of chemicals were detected in the
groundwater samples collected at the site. The spectrum of chemicals detected in at
least one groundwater sample from this area included one volatile organic, five
extractable organics, and 15 inorganics.
Volatile Organic Chemical Contamination
Volatile organic chemical contamination in groundwater at the site is relatively
insignificant. The only VOC detected in groundwater was toluene and it was detected
in only one monitor well (MW-1) at an estimated concentration of 1 ug/1. MW-1 is
located in the Former Raw Timber Processing Area. Note that no VOCs were detected
in any of the monitor wells located in or near the alleged TCE spill area.
Extractable Organic Chemical Contamination
Extractable organic chemical contamination in groundwater at the site is also
relatively insignificant. The five extractable organics detected are all PAHs, and they
were detected in only one well (TW-54) at concentrations ranging from only 1 ug/1 to
3 ug/1. TW-54 is located near the Roanoke River in the Former Raw Timber Receiving
Area. It should be noted that when well point ~s installed, the drillers
experienced an extremely strong creosote odor emanating from the hole and soils after
drilling to a depth of 5 feet.
Inorganic Chemical Contamination
As indicated in Table 4-2, of the 15 inorganic chemicals detected in groundwater at the
site, only two appear to be at concentrations which are clearly indicative of unnatural
contamination. These two chemicals, arsenic and manganese, were detected at
concentrations significantly above typical background concenh·ations in several wells.
CDM Federal Programs Corporation
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Section 4
Groundwater Sampling Investigation
The areal distribution of the arsenic and manganese contamination found in
groundwater in this remedial investigation is shown in Figure 4-2. Some of the other
inorganics detected (i.e., aluminum, chromium, cobalt, copper, lead, vanadium, and
zinc) were found at slightly elevated concentrations in well points TW-49 and TW-54
when compared to the other wells onsite, but the concentrations measured in these
samples are within the realm of possible background concentrations, particularly
when considering the high turbidity of the TW-49 sample and the potential high
turbidity of the TW-54 sample. The turbidity of the sample from TW-54 was not
measured, but well point samples typically are very turbid due to the inability to
develop a well point.
The arsenic contamination in groundwater appears to be spread throughout much of
the site, having been detected at elevated concentrations in MW-1, MW-3, MW-4,
MW-7, MW-8, MW-9, TW-24, TW-29, TW-49, and TW-54. The detected concentrations
of arsenic ranged from an estimated 5 ug/1 to 990 ug/1. The highest concentration of
arsenic was found in the area of the alleged TCE spill, but other high concentrations of
arsenic (above its 50 ug/1 MCL) were also found in the Former Raw Timber
Processing Area (MW-1) and the eastern part of the Former Finished Wood Products
Storage Area/Outerbanks Contractors Asphalt Mixing Plant Area (MW-3 and TW-29).
The manganese contamination appears to be concentrated in the Former Finished
Wood Products Storage Area/Outerbanks Contractors Asphalt Mixing Plant Area,
having been detected at elevated concentrations in MW-3, MW-4, MW-7, and TW-29.
The detected concentrations of manganese ranged from 62 ug/1 to 4700 ug/1. Note
that no well had a concentration of manganese below its 50 ug/1 SMCL indicating that
background concentrations of manganese in the surficial aquifer are likely above the
SMCL.
CDM Federal Prol!rnms Corporation
SPINB2/SEC4.v\lPO 4-7
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0
Roonoke
River
300' 600'
Georgia-Pacific Hardwoods
fi-_P_l..._m __ o_u_t_h_, __ N_o_r_th ....... C .. a_r_o_li_n_a.....,.
/
LEGEND: .,._,.
ND
-···-
~ ----
- - --
• • •
N
/
EXISTING MONITORING WELL LOCATION
TEMPORARY MONITORING WELL LOCATION
ARSENIC CONCENTRATION (ug/L)
MANGANESE CONCENTRATION (ug/L)
NONDETECT
RIVER EDGE
TREE LINE
PROPERTY BOUNDARY
INTERMITTENT DRAINAGE DITCH
MARSHY AREA
Figure No.
Inorganic Contaminant
Distribution in Groundwater 4-2
~ COM Federal Programs Corporation
~ • ._.,_,,,_......... 6/00 ~---------------------------
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5.0 Contaminant Fate and Transport Analysis
An evaluation of the environmental fate and transport of site-related contaminants is
important in determining the potential for exposure to the contaminants. There are
several mechanisms by which contaminants may migrate at the Georgia Pacific Site.
Migration into the air can occur via volatilization or dust generation. Migration into
groundwater can occur by percolation of infiltrating rainwater or groundwater flow
through waste materials or contaminated soils. Transport to surface waters can occur
via surface water runoff, and/ or through groundwater discharge. The mechanisms of
migration for the contaminants of concern detected at the site (see Section 6) are
discussed in more detail below. Estimates of the physical and chemical properties of
the contaminants of concern which may affect contaminant migration are presented in
Table 5-1. Note that the properties for the dioxins/furans are represented by the
properties of 2,3,7,8-TCDD (one particular dioxin) in Table 5-1. Some variation in
properties is expected between each of the individual dioxins and furans, but the
variations are not expected to be significant. The general persistence of the
contaminants of concern is also discussed below.
5.1 Contaminant Migration
5.1.1 Air Migration
Generally, volatilization from soil and/ or water into air may be an important
transport mechanism for the organic chemicals with Henry's Law Constants greater
than 10-5 atrn-m3 / mole and molecular weights less than 200 g/ mole. None of the
organic contaminants of concern found at the site meet these criteria, and thus,
volatilization of the contaminants of concern is not considered an important release
mechanism at this site.
Fugitive dust emissions from wind or mechanical disturbances may occur from
unpaved or unvegetated areas of the site. The environmental factors that influence
wind erosion are wind speed, moisture content, vegetative cover, and soil
composition. Because the environmental factors at the Georgia Pacific Site are at times
COM Fcd~ral Programs Corporation
SPIN2B/SECT5 5-1
---------· --- --- - - - -
TABLES-I
Section 5
Contaminant Fate and Transport
ESTIMATED PHYSICAL AND CHEMICAL PROPERTIES OF THE CONTAMINANTS OF CONCERN
GEORGIA-PACIFIC SITE
Contaminant
of
Concern
In organics
Aluminum
Arsenic
Barium
Chromium
Iron
Lead
Manganese
Vanadium
Molecular
Weight
(g/mol)
NA
NA
NA
NA
NA
NA
NA
NA
Extractable Organics
Benzo(a)anthracene 2281
Benzo(b &/ or k)fluoranthene2521
Benzo-a-pyrene 2521
Dibenzo(a,h)anthracene 2781
Indeno(l,2,3-cd)pyrene 2761
Other Organics
PCB-1254
PCB-1260
2,3,7,8-TCDD (Dioxin)
3271
3701
3221
PLYMOUTH, NORTH CAROLINA
Solubility
at25°C
(mg/~
NA
NA
NA
NA
NA
NA
NA
NA
0.0142
0.000552
0.00382
0.00052
0.622
0.0122
0.00272
0.21
Henry's
Constant
(atm-m3 /mo! x 10·5 )
I<.,.,
(ml/g)
NA
NA
NA
NA
NA
NA
NA
NA
0.0661
1.21
0.241
0.000731
3.0 X 10-15 1
2301
7101
5.4 X 10"18 1
NA
NA
NA
NA
NA
NA
NA
NA
1,400,0001
550,0001
400,0001
1,700,0001
31,000,0001
400,0001
2,600,0001
4,600,0001
Kow
(ml/g)
NA
NA
NA
NA
NA
NA
NA
NA
140,0002
3,700,0002
1,100,0002
930,0002
46,000,0002
1,100,0002
14,000,0002
2,000,0001
2004
o.s•
304
800•
16,000•
7504
5303
14,0003
42003
35003
170,0003
42003
53,0003
76003
-------------------
TABLE 5-1 (cont.)
Section 5
Contaminant Fate and Transport
ESTIMATED PHYSICAL AND CHEMICAL PROPERTIES OF THE CONT AMIN ANTS OF CONCERN
GEORGIA PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
Notes:
Koc -Organic carbon partition coefficient
K,w -Octanol/ water partition coefficient
Kd -Soil/ water partition coefficient
NA -Not Applicable
-No Data Available
Sources:
1) Montgomery and Welkom (1989)
2) Walton (1984)
3) Based on a typical fraction of organic carbon in soil
and the following equation (Walton, 1984):
foe = fraction of organic carbon in soil (0.006)
4) Based on data presented in Thibault, et al. (1990)
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Section 5
Contaminant Fate and Transport
and places conducive to wind erosion, each of the contaminants of concern detected in
surface soil is susceptible to migration via fugitive dust generation.
5.1.2 Surface Water Migration
Contaminant migration into the Roanoke River, a major surface water body at the
Georgia Pacific Site, may occur through surface water runoff, and/ or through
groundwater discharge. Upon reaching this surface water pathway, contaminants
may remain in the water column, volatilize, or sorb to bottom or suspended
sediments. Volatile organic contaminants tend to quickly volatilize into the
atmosphere upon reaching surface waters and for this reason are rarely observed at
detectable concentrations in surface water samples. Nevertheless, even though there
are no volatile organic contaminants of concern at the site, it should be noted that
during this RI, one volatile organic chemical (acetone) was detected in both surface
water and sediment samples collected from the intermittent drainage ditches which
lead to the Roanoke River.
The dioxins/ furans and other organics with low water solubilities and high I<;., values
such as PAHs, pesticides, and PCBs will tend to associate with sediments as opposed
to volatile organics and extractable organics with high water solubilities and low Koc
values, which tend to stay in the water column. All the organic contaminants of
concern at this site have low water solubilities and high I<;,, values and based on the
surface water and sediment sample results obtained in this remedial investigation, it
appears that these contaminants are mostly sorbing to sediment particles, as expected.
This does not preclude the migration of these contaminants to the Roanoke River,
however, as the contaminated sediments may be conveyed to and within the Roanoke
River via sediment transport mechanisms during storm events.
The behavior of the inorganic contaminants of concern in surface water is affected by
pH, temperature, and hardness. Inorganic compounds can occur in aquatic systems
as dissolved ions, dissolved complexes with organic and inorganic chemicals, colloids,
or particulates. The solubility and mobility of the metal inorganic contaminants is
enhanced by their ability to form complexes with humic and fulvic acids, carbonates,
CDM Federal Pmi:rnms Corporation
SP!N2B/SECT5 5-4
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Section 5
Contaminant Fate and Transport
hydroxides, and phosphates. Based on the surface water and sediment sample results
obtained in this remedial investigation, it appears that several inorganic chemicals are
migrating to surface waters at the site, and that the geochemical processes in the
surface waters allow for some of these contaminants to both remain in the water
column and sorb to sediments, while others are mostly sorbed to sediment particles.
Again, however, the sorbing of contaminants to sediment particles does not preclude
the migration of these contaminants to the Roanoke River, as the contaminated
sediments may be still be conveyed to and within the Roanoke River via sediment
transport mechanisms during storm events.
5.1.3 Soil Migration
Contaminants present in surface and subsurface soils may leach to the underlying
aquifer. Many factors influence the rate of contaminant movement through soils.
These include the physical/ chemical properties of the contaminants (e.g., solubility,
density, viscosity, K.,.,, ~w), and the physical/ chemical properties of the environment
(e.g., rainfall percolation rate, soil permeability, porosity, particle size distribution,
organic carbon content). Because all these factors can affect the rate of contaminant
movement through soils, it is very difficult to predict such movement. However,
based on the data collected in this remedial investigation some gross generalizations
of this movement can be made.
Sorption of a chemical to soil particles is the only significant hinderance of
contaminant migration in soils at the Georgia Pacific Site. If it were not for sorption,
rainfall recharge and soil permeability at this site are high enough such that all the
contaminants of concern would readily move through the soils. Sorption of
contaminants is generally described by their distribution coefficients (~). The
distribution coefficient can be expressed as:
mass of contaminant on the solid phase per mass of solid phase
=
concentration of solute in solution
As indicated in Table 5-1, all the organic contaminants of concern at this site have very
high Ki values and even though they have been observed in the soils and sediments at
CDM Fe<lc:ral Pmi;:rams Corporation
SPIN28/SECT5 5-5
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Section 5
Contaminant Fate and Transport
significant concentrations, they have not been observed in groundwater. Sorption of
these contaminants of concern to the soils at the site has apparently prevented
significant migration into groundwater.
Except for barium (and possibly aluminum and vanadium), the inorganic.
contaminants of concern also have high l<;i values, and thus, these contaminants will
also readily sorb to soil particles at the site. However, the observance of some of these
inorganic contaminants (i.e., arsenic and manganese) in groundwater at significant
concentrations indicates that the abundance of these contaminants in soil may be too
high for complete sorption to occur. The concentrations of the inorganics in the soils is
apparently high enough such that a significant amount of this inorganic
contamination can still leach into groundwater. Nevertheless, except for barium (and
possibly aluminum and vanadium), movement of the inorganic contaminants of
concern in the soils at this site is expected to be very slow due to their high propensity
for sorption.
5.1.4 Groundwater Migration
Many factors influence the rate of contaminant movement in an aquifer system. These
include the physical/ chemical properties of the contaminants (e.g., solubility, density,
viscosity, etc.), and the physical/ chemical properties of the environment (e.g., soil
permeability, porosity, bulk density, particle size distribution, extent and connectivity
of fractures, etc.). Because all these factors can affect the rate of contaminant
movement through aquifers, it is very difficult to predict such movement. However,
based on the data collected in this RI, some gross approximations of this movement
can be made.
Once the contaminants of concern reach groundwater, they will generally move as
groundwater moves, through the process of advection. However, the process of
dispersion will also cause the contaminants to spread both horizontally and vertically.
Dispersion generally causes contaminants to migrate (spread) 10 to 20 percent farther
than migration created by advection alone. Counteractive to the advection and
CDM Federal Programs Corporncion
SPIN2B1SECT5 5-6
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Section 5
Contaminant Fate and Transport
dispersion processes, however, is the process of sorption which will retard the
movement of the contaminants.
Estimates of the distribution coefficients for the contaminants of concern at the site are
presented in Table 5-1. As indicated in this table, the majority of the inorganic
contaminants of concern and all of the organic contaminants of concern have_relatively
high I<., values, and thus, these contaminants will readily sorb to soil particles at the
site and are essentially immobile. Barium and possibly a few other inorganic
contaminants of concern, however, generally have lower ~ values, and thus will not
sorb to soil particles as readily as the other contaminants of concern. These
contaminants are therefore considered to be mobile, and will generally move as
groundwater moves, only at reduced velocities. Furthermore, since groundwater
most likely moves toward the Roanoke River, these mobile contaminants will also
migrate toward the Roanoke River where, eventually, they will be discharged.
5.2 Contaminant Persistence
Persistence is the measure of how long a chemical will exist in the environment before
it degrades or transforms, either chemically or biologically, into some other chemical.
Some of the factors which affect the persistence of a chemical include the state of the
chemical, the availability of the chemical, exposure to sunlight, oxygen availability, the
types and quantities of microorganisms present, availability of nutrients, temperature,
pH, as well as the presence of other chemicals which may inhibit or enhance
degradation. Usually, persistence is expressed in terms of a chemical half-life and can
be on the order of days, weeks, or years.
Because of the many complex factors which may affect persistence, the actual rate of
chemical degradation is very difficult to predict for a given chemical at a given site,
especially without the benefit of any degradation data collected from site-specific field
studies. However, a qualitative evaluation of the potential for degradation of a
chemical can be made based on the results of laboratory and/ or field studies
conducted previously at other locations. Such a qualitative evaluation was conducted
for the contaminants of concern detected at the Georgia Pacific Site, and the results are
CDM Federal Pro1:r:uns Corporation
SPIN2B/SECT5 5-7
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Section 5
Contaminant Fate and Transport
summarized in Table 5-2. Again, note that the degradation potential for the
dioxins/furans are represented by the degradation potential for 2,3,7,8-TCDD in Table
5-2. Some variation in the degradation potential is expected between each of the
individual dioxins and furans, but the variations are not expected to be significant. In
this table, the degradation potential for each of the contaminants of concern is
indicated for the following three environmental media categories:
•
•
•
Atmospheric Degradation -A chemical released to the atmosphere may
degrade by such processes as photolysis and/ or reactions with the
hydroxyl radical, ozone, or other chemicals present.
Aquatic Degradation -A chemical released to fresh, marine, or
estuarine surface waters may degrade by such processes as photolysis,
hydrolysis, oxidation, and/ or biodegradation. · •
Terrestrial Degradation -A chemical released to soil or groundwater
may degrade by such processes as hydrolysis, oxidation, and/ or
biodegradation.
As indicated in Table 5-2, of all the contaminants of concern at the Georgia Pacific Site,
the metals have the least potential to degrade in all media and therefore will likely
persist the longest at the site. In fact, these contaminants, under ordinary conditions,
will likely persist indefinitely (for all practicable purposes). Other chemicals which
also have low degradation potential include the PCBs. All the other contaminants of
concern (i.e., the dioxins/ furans and the PAHs) generally have low to moderate
potentials for degradation, unless released to the atmosphere, in which case all the
P AHs generally have a high potential for degradation.
CDM Fedem! Progrnms Curpnmtion
SP!N2B!SECTS 5-8
-------------------
TABLES-2
Section 5
Contaminant Fate and Transport
ESTIMATED DEGRADATION POTENTIAL OF THE CONTAMINANTS OF CONCERN'
GEORGIA-PACIFIC SITE
Contaminant
of
Concern
Jnorganics
Aluminum
Arsenic
Barium
Chromium
Iron
Lead
Manganese
Vanadium
Extractable Organics
Benzo( a)anthracene
Benzo(b &/ or k)fluoranthene
Benzo-a-pyrene
Dibenzo(a,h)anthracene
Indeno(l,2,3-cd)pyrene
Other Organics
PCB-1254
PCB-1260
2,3,7,8-TCDD (Dioxin)
PLYMOUTH NORTH CAROLINA
Atmospheric
Degradation
Potential
Low
Low
Low
Low
Low
Low
Low
Low
High
High
High
High
High
Low/Moderate
Low /Moderate
Moderate
Aquatic
Degradation
Potential
Low
Low
Low
Low
Low
Low
Low
Low
Low /Moderate
Low /Moderate
Low/Moderate
Low/Moderate
Low /Moderate
Low
Low
Low/Moderate
Terrestrial
Degradation
Potential
Low
Low
Low
Low
Low
Low
Low
Low
Low/Moderate
Low/Moderate
Low/Moderate
Low/Moderate
Low/Moderate
Low
Low
Low/Moderate
-------------------
TABLE 5-2 (cont.)
Section 5
Contaminant Fate and Transport
ESTIMATED DEGRADATION POTENTIAL OF THE CONTAMINANTS OF CONCERN'
GEORGIA PACIFIC SITE
PLYMOUTH, NORTH CAROLINA
10ualitative Evaluations Made Based on Information Obtained from the Following Sources:
1) U.S. Department of Health and Human Services Toxicological Profiles
2) Fate and Exposure Data For Organic Chemicals, (Howard, 1989)
3) Handbook of Environmental Degradation Rates, (Howard, 1991)
4) Hazardous Substance Data Bank maintained by the National Library of Medicine in Bethesda, Maryland
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6.0 Quality Assurance Report
6.1 Controlling Documents
The primary objective in instituting quality control procedures is to ensure that staff
collect and record data in a uniform manner and that data are of consistently high
quality. Data are thus more likely to be accurate and can be interpreted with a high
degree of confidence. In order to collect and record data in a uniform manner,
controlling documents that described and specified quality assurance/ quality control
(QA/QC) procedures for the field investigation were prepared and/ or used. The
documents used to guide and direct procedures throughout the investigation
included:
Environmental Investigations Standard Operating Procedures and
Quality Assurance Manual, U.S. EPA Region IV, Science and
Ecosystem Support Division, May 1996 and 1997 revisions
U.S. EPA Region4 Remedial Investigation Work Plan Georgia-Pacific
Hardwood Sawmill Plymouth. North Carolina, Science and Ecosystem
Support Division, August 1998
Final Work Plan for Remedial Investigation Georgia-Pacific Hardwood
Sawmill Site Plymouth. North Carolina, CDM Federal Programs
Corporation, January, 1999
Guidance for the Data Quality Objectives process. EPA 600/R-96/055,
September 1994
The U.S. EPA Work Plan specified and described all QA, QC, analytical, data
management, auditing and reporting procedures for this investigation. In addition,
the U.S. EPA Work Plan established the DQO levels for field and analytical data
using the DQO levels defined in EPA 600 / R-96 / 055 September 1994. For this
investigation, field measurements such as pH, temperature, NTUs, conductivity,
water level, and ground survey measurements were considered DQO Level I data.
The contaminant analysis data of surface water, sediment, soil, and groundwater
provided by Contract Laboratory Program (CLP) laboratories and validated by
Environmental Protection Agency (EPA) Science and Ecosystem Support Division
(SESD) were considered DQO Level IV data.
CDM Federnl Pmgraffill Corp:1r.uiun
SPINB2/SEC1.I/JPO 6-1
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Section 6
Quality Assurance Report
By providing a framework for sample collection, decontamination, field quality
control, sample identification, chain-of-custody and sample handling procedures, the
controlling documents help ensure that high quality data is collected and data
comparability is enhanced.
6.2 Field Investigation
6.2.1 Groundwater Sampling
The work plan had called for the installation of ten temporary monitoring wells and
then collection of groundwater from the temporary well points and from five existing
monitor wells. Temporary monitoring well installation and sampling was performed
in accordance with the specifications in the Work Plan except that only five temporary
monitor wells were completed due to conditions encountered at the site and actually
nine of the permanent wells were sampled.
As specified in the Work Plan, the samples were collected with a peristaltic pump. All
groundwater samples collected were sent to CLP laboratories and analyzed according
to DQO Level IV requirements.
6.2.1.1 Water Level Measurements
Water level measurements followed the procedures specified in the work plan. Field
measurements associated with this activity were conducted in accordance with DQO
Level I requirements.
6.2.1.2 Field Parameter Measurements
Field parameters (pH, specific conductivity, temperature, and turbidity) were
measured on groundwater during well purging. Daily calibration of the monitoring
instruments was performed and recorded in the field logbooks. In addition, post
calibration checks were performed on the instruments following the days' activities.
Instrument calibration and measurements performed appeared accurate and
acceptable and no instrument malfunctions were reported.
CDM Federal Pmi;r.uns Corpor.11ion
SPINB2/SEC1.WPO 6-2
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6.2.2 Surface Water/Sediment Sampling
Section 6
Quality Assurance Report
Surface water and sediment samples were collected according to procedures specified
in the work plan. However instead of the six surface water and six sediment samples
planned there were actually three surface waters and seven sediments samples
collected. Surface water was not adequate enough to collect samples. All samples
were sent to CLP laboratories and analyzed according to DQO Level IV requirements.
6.2.5 Soil Sampling
USEP A divided the site into 54 grids and collected one five-aliquot composite surface
sample from each grid. Samples were analyzed for volatile organic compounds
(VOCs), semivolatile organic compounds(SVOCs), pesticides, polychlorinated
biphenyls (PCBs), metals, and dioxin/ dibenzofuran (approximately 80% of the
samples were analyzed for dioxin/ dibenzofuran). In addition, grab subsurface
samples were collected at the center of each grid at a depth of 18" -24" bgs, and from
grids 25 through 54 at a depth of 36" to 54" bgs. The grab samples were analyzed for
VOCs, SVOCs, pesticides, PCBs, metals, and dioxin/ dibenzofuran (approximately
80% of the samples were analyzed for dioxin/ dibenzofuran). Two additional soil
samples were collected onsite that were not associated with the 54 intially established
grids. One sample was collected in an area just west of Grid 17, designated as sample
GP055SLA, and another was collected of ash near the boiler house, designated as
sample GP056SLA. Other minor sampling deviations occurred due to conditions
encountered at the site. For example, some of the five point aliquots could not be
collected due to buried obstructions.
Twenty offsite locations were proposed for surface soil sample collection and some of
these for subsurface soil sample collection. However, only 14 locations were identified
and samples were collected for volatiles and extractable organics, metals, pesticides,
PCBs, dioxins, and furans.
6.3 Field Quality Control Procedures
All data was collected as specified in the work plan. Field measurements were
performed in accordance with procedures specified in the work plan. All monitoring
CDM F.,Jen1l Pm1:r.um Corpmation
SPINB2/SEC1.WPO 6-3
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Section 6
Quality Assurance Report
instruments were calibrated either before each use, at the beginning of each field day,
or at the frequency specified for each instrument. All sampling equipment that came
in contact with sample media was decontaminated as specified in the work plan
before each sample was collected.
All sample collection, chain-of-custody, and sample shipping procedures were carried
out as specified in the work plan. As part of the sample collection and analysis effort,
field quality control samples were prepared to monitor the performance of the CLP
laboratories and the offsite laboratories, and to check the field sampling procedures.
A description of each QC sample type and QC sample results are discussed in Section
6.5.
6.4 Data Validation
6.4.1 CLP Laboratory Analysis
All DQO Level IV data collected under the Georgia-Pacific remedial investigation
were validated by EPA Region IV SESD using EPA CLP data validation procedures.
The validation process involves review for compliance with holding times, instrument
calibration, method and laboratory blanks, instrument tuning and performance data,
and constituent quantification. Results of duplicate, matrix spike and other QC
samples are used to assess precision and accuracy of the analytical data and potential
matrix effects. The following qualifier flags are typically used by SESD to qualify
data.
COM Fedeml Progr.ims Corpum1ion
SPINB2/SEC1.\o\'PD
A-Average Value
NA-Not Analyzed
NAI-Interferences
J-Estimated Value
N-Presumptive Evidence of Presence of Material
K-Actual Value Is Known To Be Less Than Value Given
L-Actual Value Is Known To Be Greater Than Value Given
U-Material Was Analyzed For, But Not Detected, The Number Is The
Minimum Quantitation Limit
R-QC Indicates That Data Is Unusable, Compound May or May Not Be
Present; Resampling and Reanalysis is Necessary For Verification
6-4
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Section 6 -
Quality Assurance Report
The purpose of validating the data is to allow the data user to interpret and use the
data with varying degrees of confidence depending on how the data are qualified (e.g.
unqualified, estimated, or rejected).
For this investigation the data validation for both organic and inorganic analyses
revealed that the overall data package can be accepted with confidence. However
some data had to be rejected. Some results were rejected due to detection of analytes
or compounds in blanks insufficient recovery of spiked samples. For organics in each
media sampled, the "U" qualifier was applied on most data due to the contaminant
being analyzed for but not detected at the minimum quantitation limit. The "J"
qualifier was generally applied due to the sample containing those compounds less
than the quantitation limits. Some extractable PAHs in samples were flagged with "J"
due to low performance evaluation sample recovery for those P AHs.
For the inorganics, the soils and sediment samples analyses resulted in actual levels of
metals in most samples so no qualifiers were applied. For the aqueous samples
analyzed much of the data was qualified "U" due to the those metals not detected at
the minimum quantitation limit. For nonaqueous samples, the "U" was applied when
the percent relative standard deviation %RSD greater than 20% for Inductively
Coupled Plasma Emission Spectoscopy (ICP) multiple exposures and reported results
were greater than instrument detection limit (IDL), but less than contract required
detection limit (CRDL) or there was some baseline instability. The "J" qualifier was
applied to some of the metals analyzed for a multitude of reasons which include
matrix spike recovery and matrix duplicate out of control limits, and the Contract
Laboratory Program Statement of Work (CLP SOW) requires analysis of two times
CRDL standard for ICP analysis.
6.5 Data Evaluation
As part of the overall data review, the results of field QC samples were examined so
that effects of field procedures on data quality could be evaluated. Field QC samples
included EPA blanks and spikes, duplicate samples, trip blanks, equipment rinsates,
material blanks, and water blanks. In addition, sampling personnel collected
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-Section 6
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sufficient volume for the CLP laboratories to analyze matrix spike and matrix spike
duplicate samples.
6.5.1 EPA Spikes
Spike sample ampules were shipped from SESD to the CLP laboratories. The
laboratory provided full CLP documentation for spike sample analyses. Spike
samples were submitted for liquid environmental matrices during the subject week of
sample collection. The spike samples submitted to the CLP laboratories were
analyzed for TAL and TCL parameters. The sample results were used by EPA to
check adherence to procedures by the CLP laboratories.
These samples were submitted to the respective CLP laboratories on a blind basis.
Fictitious station numbers were used on the traffic report forms; the CLP laboratories
did not know which samples were blanks and spikes. These samples were identified
as such only on the copy of the traffic report forms that were returned to SESD and
Sample Management Office (SMO).
6.5.1 EPA Inorganic Blank
In addition to the EPA Spike, SESD also prepared a blind inorganic blank which is
sent to the field personnel to be shipped along with the field collected samples to the
CLP inorganic laboratories. It is given a ficticious sample location and is reported by
the CLP with the field sample data. SESD evaluated the CLP analytical results and
did not report any false positives.
6.5.2 Trip Blanks
Trip blanks (for VOCs only) accompanied the shipments of samples to the CLP
laboratory whenever coolers contained samples for VOA analyses. Trip blanks were
prepared for both aqueous and soil/ sediment type samples. Trip blanks are used to
show contamination potentially having occurred during sample handling or storage.
The trip blank was prepared by the field team prior to the sampling event and kept
with the investigative samples throughout the sampling event. It was then packaged
for shipment with the other samples and sent for analysis. Trip blank results are
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presented in the Appendix A Quality Assurance Data. Only a few detections were
noted in the trip blanks analytical results. All detections were qualified "U" or as a low
"J" value. These detected constituents were generally corrunon laboratory
contaminants or metal salts are not considered site contaminants of concern. ·
6.5.3 Equipment Rinsates
Rinsate blanks were obtained by running organic-free water over sampling equipment
after it had been decontaminated. These samples were used to determine if cleaning
procedures were adequate. Equipment rinsate samples were collected from
decontaminated soil/ sediment sampling, groundwater sampling, and surface water
sampling equipment. Rinsate blank results are presented in the Appendix A Quality
Assurance Data. No constituents of organic or inorganic nature were detected in the
equipment rinsates which would indicate inadequate decontamination of sampling
equipment.
6.5.4 Field Blanks (Water Blanks)
Field blanks are generally collected of the organic free water purification system
which is connected to an onsite public water or well water supply. Water samples
were sent for analysis of metals, volatile and extractable organics, pesticides and
PCBs. No constituents of any significance were detected.
6.5.5 Duplicate Samples
Field duplicates were collected as a means of quality control from the point of sample
collection through all analytical processes. Duplicates were collected for all media
sampled except sediment. The Relative Percent Difference (RPD) values calculated for
field samples and their duplicates are calculated on positive results only. The RPD
values calculated for inorganic analyses of the groundwater, surface water, sediment,
and soil, sample/ duplicate pairs were: 15.3%, 2.3%, 10%, and 26%, respectively. This
indicates that sample/ duplicate pairs for those media showed similar results and that
the objectives of analyzing duplicate samples were achieved. The organic analytical
results showed all non-detects for the sample/ duplicate pairs except for dioxins and
furans in the sediments and soil which had RPDs of 34% and 22% respectively.
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A soil extractable organic analysis RPD was calculated as 26% and was based on
detections in three sample/ duplicate pairs.
6.6 Precision, Accuracy, Representativeness,
Comparability, Completeness
6.6.1 Precision
Precision is the evaluation of the reproducibility of a measurement. Precision is
estimated by the analysis of duplicate samples and the calculation of RPD or RSD.
This project involved both the collection of field duplicates and the creation of
laboratory duplicates. Field duplicate samples serve as an indicator of overall
precision from sample collection through laboratory analysis. Laboratory duplicates
focus on precision of the analytical method.
Based on the %RPD results on the duplicate analyses provided above and the goals
for soil duplicates of 20% and for aqueous duplicates of 35%, the data has met the
criteria.
6.6.2 Accuracy
Accuracy is a measure of the bias in a system. It is the degree of agreement of a
measurement with an accepted reference or true value. Accuracy for this project was
estimated from the analysis of QC samples whose true values are known (surrogate or
matrix spikes) and was expressed as percent recovery. EPA provided performance
evaluation samples to the CLP laboratories including spike samples. These were
analyzed by the CLP along with the site samples and reported. EPA SESD evaluated
and validated the data according to the results reported by the CLP. The reported
analytical qualitative and quantitative results of the spike samples were within
acceptable limits for accuracy in CLP contract.
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6.6.3 Representativeness, Comparability
Section 6
Quality Assurance Report
Representativeness expresses the degree to which data accurately and precisely
represent a characteristic of a population at a sampling point, process condition or
environmental condition. Comparability expresses the confidence with which one
data set can be compared to another. Representativeness and comparability are
qualitative objectives which were met by following standard operating procedures for
sample collection and analysis.
6.6.4 Completeness
Completeness is the measure of the amount of valid data obtained from a
measurement system compared to the amount that was expected to be obtained under
current normal conditions.
The completeness of the data set for this investigation is based on the number of valid
data points. Data validation and evaluation effects completeness of the data. Some
data was rejected. Table 2 presents the completeness data.
Table 1
Soils Data Completeness
Analytical Fraction Total Data Valid Data Rejected Data Set
Points Points Data Points Completeness
Metals 3,151 3,120 31 99.1%
Volatile OrR;anics 4,422 4,409 13 99.7%
Semivolatile OrR;anics 8,694 8,602 92 99.0%
Pesticides/PCBs 4,030 3,680 350 91.3%
Totals 20,297 19,811 486 97.3%
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Analytical Fraction
Metals
Volatile Orf{anics
Semivolatile Orf{anics
Pesticides/PCBs
Dioxins/Furans
Totals
Analytical Fraction
Metals
Volatile Orf{anics
Semivolatile Orf{anics
Pesticides/PCBs
Totals
Analytical Fraction
Metals
Volatile Orf{anics
Semivolatile Or~anics
Pesticides/PCBs
Totals
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Table2
Sediment Data Completeness
Total Data Valid Data Rejected
Points Points Data Points
299 292 7
231 224 7
819 819 0
364 364 0
286 274 12
1,999 1,973 26
Table 3
Surface Water Data Completeness
Total Data Valid Data Rejected
Points Points Data Points
69 69 0
99 96 3
189 189 0
84 84 0
441 438 3
Table 4
Groundwater Data Completeness
Total Data Valid Data Rejected
Points Points Data Points
322 322 0
462 462 0
882 868 14
392 336 56
2,058 1,988 70
Data Set
Comoleteness
97.6%
97.0%
100.0%
100.0%
95.8%
98.1%
Data Set
Completeness
100.0%
97.0%
100.0%
100.0%
99.2%
Data Set
Completeness
100.0%
100.0%
98.4%
85.7
96.0%
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The EPA SESD Work Plan had established a completeness goal of 99% for this project
for DQO level IV analytical results. This goal was not met except for the surface
water samples. However, the remaining media and data set completeness was better
than 96% which is generally acceptable for this type of sampling and analysis.
6.7 Audits
6.7 Audit Findings
As part of CDM Federal' s Quality Assurance Program, various projects are selected
quarterly for auditing. Auditing can be either system or performance audits.
Performance audits are quantitative checks on different segments of project activity;
they are most appropriate for field measurements and for laboratory analysis
activities. System audits are qualitive reviews of project activity to check that the
overall CDM Federal QA program is functioning and any project-specific QA and QC
requirements are being met. System audits are generaIJy performed on a selected
number of projects per calendar quarter. This project was not selected for audit of the
field activities by CDM Federal Quality Assurance management since EPA performed
the field work. However, an office audit will likely be performed to check office files.
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7.0 RI Summary and Conclusions
The Georgia Pacific Site was placed on the National Priorities List under the
Comprehensive Environmental Response, Compensation, and Liability Act in October
1999, and therefore was designated for an RI/FS. In 1998, EPA initiated the RI/FS to
address all contamination at the site. The primary objective of the RI was to provide
the additional data needed to support a baseline risk assessment and provide a basis
on which to recommend a subsequent remedial action for the site. The RI was divided
into five parts:
•
•
•
•
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A soil sampling investigation (Section 2.0)
A surface water/ sediment sampling investigation (Section 3.0)
A groundwater sampling investigation (Section 4.0)
A contaminant transport and fate evaluation (Section 5.0)
A baseline risk assessment (submitted separately)
The details of each of these investigations are presented in their appropriate sections
and should be consulted for a full understanding of the results of the RI. The major
conclusions reached as a result of the RI include the following:
• Analyses of soil samples collected indicate extensive contamination by
dioxins/ furans, P AHs, PCBs, and inorganics. This contamination
seemed to be focused in an area centrally located on the site property
where most past operations were located. However, following the
removal action, selected contaminated grids and other waste materials
located onsite were removed from the site. There was indication of
•
off site contamination from site related constituents, however the
concentrations were lower than onsite concentration. The results of the
baseline risk assessment indicate that while the current human health
risks associated with the levels of contamination found in the soils at
the site are within EPA's acceptable target range, the potential future
human health risks are slightly above EP A's acceptable target range,
primarily due to the presence of dioxins/furans, carcinogenic PAHs,
and arsenic.
Surface waters at the site discharge into the Roanoke River. Analyses
of surface water and sediment samples collected from the intermittent
drainage ditches located onsite indicate significant contamination by
arsenic and manganese in surface water, and by dioxins/ furans,
acetone, methyl ethyl ketone, PAHs, arsenic, lead, and zinc in
sediments.
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Section 7
RI Summary and Conclusions
The results of the baseline human health risk assessment indicate that
both the current and potential future human health risks associated
with the levels of contamination found in the intermittent drainage
ditches are within EPA's acceptable target range.
The site is underlain by a surficial unconfined aquifer. Groundwater
flow at the site is likely toward the Roanoke River, where it discharges.
Analyses of groundwater samples at the site indicate significant
contamination by arsenic and manganese. The results of the baseline
risk assessment indicate that the potential future human health risks
associated with the levels of contamination found in the groundwater
are significantly above EPA's acceptable target range, primarily due to
the presence of arsenic. In addition, the concentrations of some of the
contaminants found are above MCLs.
Based on the results of the RI, the following actions are recommended:
•
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Remedial action objectives for soil and groundwater contamination at
the site should be established based on human health exposure.risks, as
well as the potential for future contaminant migration from one
medium to another (e.g., soils to groundwater).
Alternatives for reducing soil and groundwater contamination at the
site to achieve the established remedial action objectives should be
evaluated, and the most cost-effective alternative for each
implemented.
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