NCD000813592_19920201_GA-Pacific Corp Hdwd Saw_SERB PA SI_Phase II Screening Site Inspection Volume I-OCR

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Sl'ATE Of'
NORTH CljtROLINA -
Depa,·t,nent of Environment, 1-Iealth,
and Natural Resources
Division of Solid Waste ltlra11agen1ent
Superfund Section
Georgua Pacific Corporation Hardwood Sawmill
NCD 000813592
Phase II
Screening Site Inspection
Volun1e I
Septemberl 991
By:
Greenhorne & O'l\tara, Inc.
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PHASE II
SCREENING SITE INVESTIGATION
FOR THE
GEORGIA PACIFIC CORPORATION HARDWOOD SAWMILL
PLYMOUTH, NORTH CAROLINA
NCD 000813592
Submitted to:
State of North Carolina
Department of Environment, Health,
and Natural Resources
Division of Solid Waste Management
Superfund Section
Raleigh, North Carolina
Prepared By:
Greenhorne & O'Mara, Inc.
9001 Edmonston Road
Greenbelt, Maryland 20770
September 1991
Revised February 1992
CERCLA
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TABLE Of CONTENTS
EXECUTIVE SUMMARY ••••••••••••••••••••••••••••••••••••••••••••••••••••• 1
1. 0 INTRODUCTION ••••••••••••••••••••• '. •••••••••••••••••••••••••••••••• 2
1. 1 OBJECTIVES •••••••••••••••••••••••••••••••••••••••••••••••••••• 2
1. 2 SCOPE OF WORK ••••••••••••••••••••••••••••••••••••••••••••••••• 2
2. 0 SITE CHARACTERIZATION ••••.••••••••••••••••••••••••••••••••••••••••• 4
2 .1 SITE BACKGROUND AND HISTORY ••••••••••••••••••••••••••••••••••• 4
2. 2 SITE DESCRIPTION ••••••••••••••••••••••••••••.••••••••••••••••• 4
2.2.1 Site Location ........•.•.••..••..•........•...•...••••. 4
2.2.2 Site Features .•.....•...•..•......•.......••..•••.•.••• 4
2.2.3 Waste Characteristics ••••••••••.•.•......•••...•..••••• 5
3 • 0 ENVIRONMENTAL SETTING •••••••••••••••••••••••••••••.••••••••••••••• 7
3 .1 TOPOGRAPHY •••••••••••••••••••••••••••••••••••••••••••••••••••• 7
3. 2 SURFACE WATER ••••••••••••••••••••••••••••••••••••••••••••••••• 7
3.2.1 Overland Drainage and Affected Water Bodies .........•... 7
3.2.2 Climatology ......•..............•...•..........•....•... 7
3 .3 GROUNDWATER ••••••••••••••••••••••••••••••••••••••••••••••••••• 7
3. 3 .1 Hydrogeology ...•.•..••...•.• , ......•.......•....•.•..•.. 7
3.3.2 Aquifer Use .......•..•...•..•......•.......•...••....•.. 8
3. 3 . 3 Soils ......•.....•...•...•..•..............•.........••. 8
3. 4 POPULATION DISTRIBUTION ••••••••••••••••••••••••••••••••••••••• 9
3.5 WATER SUPPLY •••••••••••••••••••••••••••••••••••••••••••••••••• 9
3.6 LAND USE ••••••••••••••••••••••••••••••••••••••••••••••••••••• 10
3. 7 SENSITIVE ENVIRONMENTS ••••••••••••••••••••••••••••••••••••••• 10
4. 0 FIELD INVESTIGATION •••••••••••••••••••••••••••••••••••••••••••••• 11
4.1 DESCRIPTION OF SAMPLES AND SAMPLE LOCATIONS •••••••••••••••••• 11
4. 2 FIELD MEASUREMENTS ••••••••••••••••••••••••••••••••••••••••••• 11
4. 3 ANALYTICAL RE SUL TS ••••••••••••••••••••••••••••••••••••••••••• 11
5. 0 CONCLUSIONS AND RECOMMENDATIONS •••••••••••••••••••••••••••••••••• 14
REFERENCES
APPENDIX A
APPENDIX B
APPENDIX C
MAPS, PHOTOGRAPHS AND TABLES
SITE INSPECTION FORM
ANALYTICAL DATA
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EXECUTIVE SUMMARY
The Georgia Pacific Corporation Hardwood Sawmill site is a 25-acre site
located off of Plywood Drive within Plymouth city limits, in \lashing ton
County. It was previously owned by Atlas Plywood and operated as a plywood
plant. In 1950, the Georgia-Pacific Corporation purchased the site,
demolished the existing structures, and developed a planer-sawmill-office
facility. The facility was primarily engaged in sawing and planing rough
hardwood lumber and timber from logs. After a fire in 1983, the plant
permanently closed and operations ceased. The site was later used by Outer
Banks Contractors for an asphalt operation. It is currently unoccupied and
inactive.
Process wastes associated with operations at the Georgia Pacific
facility consisted primarily of spent oil, spent halogenated degreasing
agents, spent nonhalogenated solvents, bottom sediment sludge from wood
preserving processes, and an insecticide formulation. The wood
preservative used contained pentachloropheneate, sodium metaborate, and
other chlorophenols; the insecticide formulation contained lindane. During_
the wood treatment process, lumber was passed through a dip vat on a
conveyor system and allowed to drip dry onto the ground.
The Georgia Pacific Hardwood Sawmill is located withil) the Atlantic
Coastal Plain Physiographic Province. It is located adjacent to the
Roanoke River in a region characterized by extensive, flat coastal swamps
and marshes. The primary geologic units identified in the Plymouth area
are Tertiary rocks of the Coastal Plain referred to as the Yorktown
Formation and the Duplin Formation. The Yorktown Formation is a confined
aquifer which serves as the chief source of water supply for the eastern
part of \lashington County.
On December 6, 1985, NCDHR/DHS completed a Preliminary Assessment on
the Georgia Pacific plant and recommended that the site be inspected on a
low priority basis. NUS Corporation conducted an off-site reconnaissance
and a Phase I Screening Site Inspection (SSI) on _October 11, 1989, and'
recommended that no further action be planned for the site. On July 11,
1991, Greenhome & O'Hara Inc., under contract with NCDEHNR, conducted a
Phase II SSI.
A total of nine (9) environmental samples were taken at the site.
Results of the sampling event indicate that releases of contaminants have
occurred around the facility. Due to the presence of wetlands, fisheries,
and recreational activities downstream in the Roanoke River and Albemarle
Sound, G&O is recommending that the site move onto the next stage of the
pre-remedial process.
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1.0 INTRODUCTION
1. 1 OBJECTIVES
Greenhorne and O'Hara, Inc. (G&O) conducted a Phase II Screening Site
Inspection (SSI) at the Georgia Pacific Corporation Hardwood Sawmill site
located in Plymouth, Washington County, North Carolina. The overall
objective of the Phase II SSI is to provide information to determine
whether a site should move onto the next stage of the pre-remedial process
or be designated as "no further remedial action planned (NFRAP)" under the
Federal Superfund program. Additional objectives of the Phase II SSI are
the following:
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Identify the types of contaminants present.
Assess whether a release of hazardous substances has occurred;
Search for evidence of actual human and environmental exposure to
contaminants.
Determine the likelihood of the site scoring high enough on the
HRS to be recommended for further pre-remedial action under the
Federal Superfund program.
The SSI builds upon data obtained during the preliminary assessment
(PA) and Phase ISSI stages to further characterize problems at or near the
site and to support a management recommendation.
1.2 SCOPE OF VORK
The scope of work for the Phase II 551 includes the following tasks:
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Reviewing both EPA and state file material.
Preparing an abbreviated site-specific sampling plan and Health
and Safety Plan. This task included developing · a site map to
illustrate proposed sampling locations, the approximate number of
samples, and the type of samples to be collected.
Conducting a site reconnaissance with the NCDEHNR to determine and
flag actual sampling locations based on the sampling plan and
existing field conditions, and the professional judgement of the
NCDEHNR and the G&O sampling team. During the site
reconnaissance, G&O also developed a site layout map to illustrate
all of the important site features including location of
buildings, access roads, and waste source areas, as well as site
drainage.
Performing field sampling activities by collecting up to five (5)
environmental media samples and three (3) QA/QC samples. The five
environmental samples usually included two (2) groundwater samples
(with a maximum well depth of 15 feet) and three (3) surface soil
samples. The three (3) QA/QC samples included one (1) water
duplicate, one (1) surface soil duplicate, and one (1) trip blank.
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Analyzing laboratory data and presenting the data in four summary
tables: volatile organic compounds, semi-volatile organic
compounds, inorganic compounds, and pesticides/PCBs. Any releases
that were observed were highlighted on the tables and discussed in
the Phase II SSI report.
Preparing a Phase II SSI report that presents information gathered
during the site visit, field observations, and laboratory data
with respect to observed releases. Any existing data gaps will be
discussed in the text. Greenhorne and O'Mara was not contracted
to collect additional background information.
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2.0 SITE CHARACTERIZATION
2.1 SITE BACKGROUND AND HISTORY
The Georgia Pacific Corporation Hardwood Sawmill site is a 25-acre
parcel of land previously owned by Atlas Plywood. In 1950, the Georgia
Pacific Corporation purchased the site, demolished the existing structures,
and developed a planer-sawmill-office facility (Ref. 2) The facility was
primarily engaged in sawing and planing rough hardwood lumber and timber
from logs (Ref. 3). After a fire in 1983, the plant pe'rmanently closed and
operations ceased (Ref. 2). In 1989, the site was owned by Decatur
Part_nerships of Naggshead, North Carolina and was leased to Outer Banks
Contractors, Inc. Plant Number 4, an asphalt operation (Ref. 4). The site
is currently owned by Outer Banks Contractors (Ref. 9).
The Georgia Pacific facility submitted a RCRA Part A application for a
hazardous waste permit on November 12, 1980 (Ref. 3). In August of 1982,
the facility's status was changed from a treatment/storage/disposal (TSO)
and generator facility to a small-quantity generator. According to NCDHR
representatives, the Georgia Pacific facility is currently listed as a
conditionally exempt, small-quantity generator (less than 250 pounds per
month) due to its inactive status. No remedial activities have been
performed at this facility (Ref. 1, 6).
On December 6, 1985, the North Carolina Department of Human
Resources/Division of Health Services (NCDHR/DHS) completed a preliminary
assessment report on the Georgia Pacific Hardwood Sawmill plant. The
report concluded that because it had been in operation for at least 35
years and since past waste handling practices were unclear, the site should
be inspected on a low priority basis (Ref. 2).
NUS Corporation conducted an off-site reconnaissance on October 11,
1989, and subu1itted a Phase I Screening Site Inspection (SSI) to EPA on
August 20, 1990 (Ref. 1, 7). Based on the low probability that drinking
water would be impacted by prior waste handling practices, the NUS report
recommended that no further remedial action be planned for the site (Ref.
1) .
2.2 SITE DESCRIPTION
2.2.1 Site Location
The Georgia Pacific site is located off of Plywood Drive within
Plymouth city limits, in Washington County (Appendix A, Figure 1). The
site can be found on the Plymouth East and Westover, N.C. USGS 7.5'
Quadrangle Maps at latitude 35° 52' 30'N and longitude 76° 44' 30"W (Ref.
8) •
2.2.2 Site Features
The property consists of approximately 25 acres. NUS Corporation
conducted an off-site reconnaissance on October 11, 1989 and noted that the
facility was accessible by way of wooded areas surrounding the site. They
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noted that the main entrance was off of Plywood Drive and was blocked by a
metal gate during non-operational hours. NUS prepared a site sketch, which
included an office building, other unidentified buildings, air emissions
stacks, two storage tanks, a sand mound, a weigh house, tanks, and Georgia
Pacific planer and sawmill buildings (Ref. 7).
On July 11, 1991, Greenhorne & O'Mara staff conducted an on-site
reconnaissance and carried out a sampling plan on the Plymouth site. The
site was presently unoccupied, but many of the buildings and structures
used by the former occupants were still present, including the sawmill, the
boiler house, the machine shop, and smoke stacks (Photograph 8). Few
remains of the green chain system were visible. The green chain system was
deScribed by a site representative to be the conveyor system that carried
the cut lumber from the sawmill, through a dip tank process, and finally
into the holding area. Wood from the former green chain structure
(Photograph 5) and the some of the old belts from the conveyor system
(Photograph 6) were identified on the site, as well as the concrete pads
which were used as temporary stacking areas (Photograph 2, 7). No signs of
contamination were noted in this area (Ref. 9).
A site representative also indicated that the former plywood plant,
employing approximately 400 workers, was located adjacent to the sawmill.
He also indicated that approximately 10 employees worked on the site during
the time of the asphalt operation. An alleged spill of TCE occurred during
the time of the asphalt operation; the vegetation in this area appeared to
be stressed and blotchy (Ref. 9).
2.2.3 Waste Characteristics
Operations at the Georgia Pacific facility included the production of
treated and nontreated hardwood lumber (Ref. 3, 10). Process wastes
associated with the plant consisted primarily of spent oil (DOOO-
ignitable/D007-chromium, D008-lead), spent halogenated degreasing agents
(FOOl), spent nonhalogenated solvents (F003, FOOS), bottom sediment sludge
from the treatment of wastewaters from the wood preserving processes, and
an insecticide formulation (Ref. 1). The preservative used, Noxtane (trade
name); was manufactured by the Koppers Company of St. Louis and contained
pentachloropheneate, sodium metaborate, and other chlorophenols. The
insecticide formulation contained lindane (Refs. 1, 3, 10, 11, 12). During
the process of wood preserving, lumber was passed through a dip vat on a
conveyor system. After removal from the preservative or insecticide
formulation, the wet wood was allowed to drip dry onto the ground, thus
contaminating the soil (Ref. 1, 10). Annual waste production at the
facility included 20,000 pounds of DOOO, D007, and D008 waste, 16,300
pounds of KOOl waste (bottom sediment sludge from the treatment of
wastewaters from wood preserving processes that use pentachlorophenol) with
lindane, and 375 pounds of FOOl, F003, FOOS waste (Ref. 1, 3).
A RCRA Part A application indicated that the wastes were stored in
drums (Ref. 1, 3). During a RCRA Inspection· conducted on October 1981,
representatives from the North Carolina Department of Human Resources
(NCDHR) discovered that the wastes were being burned in the facility
boilers and/or sent to the county landfill (Ref. 1, 10). It was also noted
during the inspection that the wood treatment process involved spilling
waste directly on the ground (Ref. 1, 10). A tank used in the wood
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treatment process was also found to be leaking (Ref. 10, 13). Remedial
action plans were initiated by NCDHR in November 1981, but no remedial
activities have been performed at the facility (Ref. 6, 14).
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3.0 ENVIRONMENTAL SETTING
3.1 TOPOGRAPHY
The Georgia Pacific Hardwood Sawmill site is on a relatively flat
parcel of land surrounded by the Roanoke River on the northwest and
wetlands around the remainder of the property. It is located in a region
characterized by extensive, flat coastal swamps and marshes. According to
USGS Quadrangle maps, elevations in the vicinity of the site are slightly
above 5 feet National Geodetic Vertical Datum (NGVD) around the facility
and slightly below 5 feet NGVD in the nearby wetland areas (Figure 3 and
Ref. 8).
3.2 SURFACE WATER
3.2.1 Overland Drainage and Potentially Affected Water Bodies
The green chain conveyor system and dip tank were formerly located
approximately 250 feet south of the banks of the Roanoke River. Generally,
runoff from the site drains to adjacent wetlands and ditches as well as to
the Roanoke River. The Roanoke River flows northeast for approximately 5.7
miles and empties into Albemarle Sound, which flows east for the remainder
of the 15-mile migratory pathway (Ref. 8).
The Roanoke River is classified as a nclass en river with an "Sw" or
Swamp Water supplemental classification (Ref. 35). Class C waters are
protected for aquatic life propagation and survival, fishing, wildlife,
secondary recreation, and agriculture. Swamp waters have low velocities
and other characteristics which are different from adjacent streams.
Albemarle Sound, in the vicinity of Bachelor Bay ( see Figure 1), is
classified as a 'Class B Sw' water body, denoting primary recreation and
any other usages specified by the C classification (Ref. 35). Common fish
caught in the area are the spot clocker, the catfish, the American and
hickory shed, the white perch, the strip bass, and the blue back (Ref. 15).
There are no surface water intakes for municipal drinking water supplies
within 15 miles downstream of the site (Ref. 1, 8). '
3.2.2 Climatology
Northwestern Washington County has
approximately 50 inches and a mean annual
41 inches (Ref. 16). Therefore, the net
The 2-year, 24-hour rainfall in this area
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3.3 GROUNDWATER
3.3.1 Hydrogeology
a mean annual precipitation of
lake evaporation of approximately
annual precipitation is 9 inches.
is approximately 4.0 inches (Ref.
The site is located within the Atlantic Coastal Plain Physiographic
Province, which is characterized by complexly interbedded sediments. The
sediments are unconsolidated and consist primarily of sand, silt, and clay
transported by streams from the adjoining uplands of the Piedmont and Blue
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Ridge Provinces. The geologic formations dip towards the coast (Ref. 18).
The primary geologic units identified in the Plymouth area are Tertiary
rocks of the Coastal plain referred to as Yorktown Formation and the Duplin
Formation (Ref. 19). The Yorktown Formation in North Carolina includes
three members: the Sunken Meadow Member, the Rushmere Member, and the
Morgarts Beach Member. The Sunken Meadow Member consists of a fine,
moderately to well-sorted sand containing 5 to 15 percent silt and 1
percent clay. Large mollusks are common in this member. The Rushmere
Member overlies the Sunken Meadow Member and is typically moderately well
sorted fine-grained sand. Phosphate and glauconite are common in the
Rushmere Member in amounts less than 10 percent. Shell-rich beds are also
common. The uppermost part of the three Yorktown members is the Morgarts
Beach Member which is described as very fine-grained, with silt and clay
content up to 60 percent. The Duplin Formation is a sandy, calcareous,
fossiliferous unit. It includes fossiliferous sand, sandy limestone, silty
limestone, and calcareous silty sand (Ref. 19).
3.3.2 Aquifer Use
East of Plymouth, in the Town of Roper, a typical cross section of the
underlying strata includes 15 feet of surficial deposits, 200 feet of sand
and marl of the Yorktown Formation, and then the limestones of the Castle
Hayne Formation. The surficial deposits aquifer is usually unconfined and
is rarely used for potable water supplies. The Yorktown Formation is a
confined aquifer, which serves as the chief source of water supply for the
eastern part of Washington County. Although the section thins from east to
west, the Yorktown Formation is present under Plymouth (Ref. 19).
The Castle Hayne aquifer is generally a confined formation and it is
the most productive aquifer in North Carolina (Ref. 20). It is the
principal source of water supply in the western part of the county. The
aquifer consists of porous and permeable limestone and lies at a depth
ranging from about 120 feet in the western part of the county to 400 feet
in the eastern part of the county (Ref. 19). The Castle Hayne aquifer is
used in the Plymouth area and it can be reached between 150 feet to 180
feet below land surface (bls). Due to large withdrawals in recent years,
the artesian effects have been eliminated (Ref. 23). Depth to groundwater
is generally 28 feet bls. However, the site is located adjacent to the
Roanoke River and the water level measured during the July, 1991 sampling
event was between 3.5 and 5 feet bls (Ref. 9).
The layer of marl and sand found in Plymouth represents the layer of
lowest hydraulic conductivity between the aquifer and the surface. Marl
and sand of this type have been shown to have 1 x 10-5 to 1 x 10-7 cm/sec
(Ref. 24).
3.3.3 Soils
The soils on the Georgia Pacific site are primarily Tarboro sands with
a slope of Oto 3 percent. The soils in the wetlands adjacent to the site
are Muckalee loams (Ref. 25). Tarboro sand is an excessively drained soil
normally found on low broad ridges commonly adjacent to Albemarle Sound and
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.
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The soil is well suited to most urban uses and provides a good support for
most structures. Muckalee loams, found in the small stream surrounding the
property, is a nearly level, poorly-drained hydric soil found on
floodplains and small streams in this region. It is subject to frequent
flooding (Ref. 25).
3.4 POPULATION DISTRIBUTION
The City of Plymouth currently has a population density of 1,138.9
persons per square mile (Ref. 27). To determine the population within
unincorporated areas of Washington County, a house count was conducted from
the USGS quadrangle maps. The number of houses was then multiplied by
2. 72, which is the 1990 average number of residents per household in
Washington County (Ref. 27). The number of residents within each radius
ring was then calculated and the values were added to provide a cumulative
population. Since the site is currently unoccupied and inactive, there was
no on-site population. The table below summarizes the calculated total
population (Ref. 28):
Radius Population/Radii Cumulative Population
1/4-mile 421 421
1/2-mile 524 945
1-mile 1,295 2,240
2-mile 2,242 4,482
3-mile 2,091 6,573
4-mile 1,599 8,172
3.5 WATER SUPPLY
Groundwater is the only source of potable water in Washington County.
Only the Towns of Roper and Plymouth have public water supplies (Ref. 25).
Residents within a 4-mile radius of the site obtain their water supply from
one of three sources: the City of Plymouth Public Works Water System, the
Washington County system (which obtains water from the City of Plymouth),
and private well use (Ref. 1, 7). The City of Plymouth Public Works Water
System uses four wells having an average depth of approximately 175 feet;
three of the wells are located inside the city limits and the fourth is
located within one mile of the city limits. All the wells are located
between 1 to 2 miles south of the site and the total population served is
approximately 5,000 residents (Ref. 1, 8, 29). The water system also has
two tanks: a 250,000 gallon capacity tank at the Fork of Hobkins,
Roosevelt, and a 500,000 gallon tank on Eastman Street (Ref. 7).
The Washington County system connects to the Plymouth system and serves
unincorporated areas as shown in Figure 3 (Ref. 7, 30). The county system
serves 3,900 residents· (Ref. 29). The remainder of the residents living
within a 4-mile radius of the site rely on private wells for their water
supply. Private wells within the study area are generally 200 feet deep.
The closest private well is located on Route 1 approximately 2.7 miles from
the facility (Ref. 1, 7). The total population using groundwater is
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estimated below (Ref. 28):
Population relying on groundwater for potable water
Radius Population/Radii Cumulative Population
On-site 0 0
1/4-mile 0 0
1/2-mile 0 0
1-mile 0 0
2-mile 8,919 8,919
3-mile 316 9,235
4-mile 628 9,863
3.6 LAND USE
Access to the site is limited by fencing and a gate ·guardhouse (Ref. 1,
7). The nearest residence is located approximately 700 feet east of the
facility. Plymouth High School is located on the property approximately
700 feet south of the facility, Also, a baseball park and a residential
area are adjacent to the facility (Ref. 1, 7). Land northeast of Plymouth
and north of the Roanoke River is primarily uninhabited wetlands (Ref. 1,
8) •
3.7 SENSITIVE ENVIRONMENTS
There are no known critical habitats of Federally-listed endangered
species in the vicinity of the site (Ref. 31). There are, however, several
endangered and threatened species identified in the county. The bald eagle
is a federally and state-designated endangered species; and the Waccamaw
killifish and golden eagle are state-designated endangered and threatened
species, respectively (Ref. 1, 32). There are also extensive wetland areas
in the vicinity.of the site. Approximately half of the 4-mile radius study
area is covered by wooded marsh or swamp (Ref. 8). The river and sound may
also be spawning areas, migratory pathways or feeding areas for fish
species.
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4.0 FIELD INVESTIGATION
4.1 DESCRIPTION OF SAMPLES AND SAMPLE LOCATIONS
A total of nine (9) environmental samples were collected to
characterize the site. To determine whether a release of contaminants has
occurred, limited subsurface and surficial investigation was recommended to
obtain soil, groundwater, and sediment samples for laboratory analysis.
The locations of the sampling points were originally proposed in an
abbreviated sampling plan prepared by G&O; however, the NCDEHNR made the
final recommendations during the sampling event conducted on July 11, 1991.
Therefore, the final sampling locations as shown in Appendix A, Figure 2
reflect the decision of the NCDEHNR staff.
To determine whether contaminants were released into the environment,
two ( 2) surface soil samples ( SSOl and SS02) and three ( 3) groundwater
samples (G\,101, G\,102, and G\,103) were obtained by G&O personnel. Surface
soil sample SS02 was a composite of three locations. A representative of
the NCDEHNR collected two (2) surface soil samples and two (2) sedi.ment
samples from the locations shown on the site layout and sampling map
(Appendix A, Figure 2 and Photographs 1 through 10). All the samples
collected on the site were contained, preserved, and held in accordance
with the Standard Operating Procedures (SOP) (Ref. 33).
4.2 FIELD MEASUREMENTS
Field measurements collected for groundwater samples include
temperature and conductivity. These values are listed in Table 1.
SAMPLE CODE
GWGWOl
GWGW03
TABLE 1
FIELD MEASUREMENTS FOR GROUNDWATER SAMPLES
GEORGIA PACIFIC HARDVOOD SAVKILL
PLYMOUTH, VASHINGTON COUNTY, NORTH CAROLINA
p.11
5.5
7.0
TEMPERATURE Cllcl
26.6-29.0
23.7-24.9
CONDUCTIVITY lnmhos/cml
0.80-0.81
2.03-2.24
4.3 ANALYTICAL RESULTS
Upon completion of the sampling event, the G&O samples were taken for
analysis to Industrial and Environmental Analysts, Inc. ( IEA) in Research
Triangle Park, North Carolina (see Volume II). Level IV Routine Analytical
Service (RAS) Contract Laboratory Program (CLP) data packages and
associated narratives were assembled for this project by IEA. The IEA
analytical data was validated by NUS Corporation. The NCDEHNR samples were
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were taken to the State Laboratory of Public Health in Raleigh for
analysis. The results of the sample analysis are summarized in
Tables 2A and 2B (Appendix B) and discussed below.
I.
DOWNGRADIENT GROUNDWATER (GWGW02) A groundwater sample was
collected from a hand-augured temporary.well located in the green
chain area. No Volatile organic Compounds (VOCs) or Semi-Volatile
Organic Compounds (BNAs) were detected above CRDL in this sample.
Alpha BHC (0.12 ppb), beta BHC (0.045J ppb), delta BHC (0.13 ppb)
and gamma BHC (lindane) (0.32 ppb) were the only PCBs and/or
Pesticides reported significantly higher than background in this
sample. Several inorganics were identified and reported in the
groundwater sample; however only beryllium and manganese were
detected in significant concentrations (greater than 3x above the
background concentration). The beryllium exceeded the Federal
Maximum Contaminant Level (MCL) of 1 ppb and manganese exceeded the
NCMCL (50 ppb).
DOWNGRADIENT GROUNDWATER (GWGW03) A groundwater sample was
collected from a hand-augured temporary well located in the TCE
area. Chloroethane ( 990 ppb) was the only Volatile Organic
Compound (VOC) reported significantly higher than background in
this sample. No Semi-Volatile Organic Compounds (BNAs) were
detected above CRDL in this sample. No PCBs and/or Pesticides were
reported in this sample. Several inorganics were identified and
reported in the groundwater sample; however only arsenic, manganese
and sodium were detected in significant concentrations (greater
than 3x above the background concentration).
GREEN CHAIN AREA COMPOSITE (GWSS02) -A composite soil sample was
collected in the green chain area at the site. No voes or BNAs
were reported in this sample. Alpha BHC (470 ppb), delta BHC (480
ppb), gamma BHC (lindane) (980 ppb) and 4,4'-DDD (170C ppb) were
the only PCBs and/or Pesticides reported significantly above
background in this sample. Barium (320 ppm), calcium (79000 ppm),
cobalt (5.3 ppm), copper (23 ppm), lead (33 ppm), magnesium (3600
ppm), manganese (850 ppm) and potassium (1800 ppm) were the only
inorganics reported in significant concentrations in this sample.
Note: The following four samples were collected by NCDEHNR
personnel and analyzed by the State Laboratory of Public Health.
TRANSFORMER STATION AREA COMPOSITE (GWSS03) A composite soil
sample was collected in the transformer station area at the site.
No voes or BNAs were reported in this sample. Aroclor 1254
(1.08 ppb) was the only PCBs and/or Pesticides reported
significantly above background in this sample. Arsenic (32 ppm),
barium (220 ppm) and lead (110 ppm) were the only inorganics
reported in significant concentrations in this sample.
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TCE AREA COMPOSITE (GWSS04) A composite soil sample was
collected in the TCE area at the site. No voes, BNAs or PCBs
and/or Pesticides were reported in this sample. Arsenic (10 ppm)
and lead (20 ppm) were the only inorganics reported in significant
concentrations in this sample.
LUMBER STACK SEDIMENT SAMPLE (GWSED0l) A sediment sample was
collected adjacent the lumber stack area. No voes or BNAs were
reported in this sample. Aroclor 1254 (0.30 ppb) was the only PCB
and/or Pesticide reported above detection limit in this sample.
Barium (27 ppm) and lead (27 ppm) were the only inorganics reported
above detection limit in this sample.
TCE SEDIMENT SAMPLE (GWSED02) A sediment sample was collected
adjacent the TCE area. No voes, BNAs or PCBs and/or Pesticides
were reported in this sample. Arsenic (9.8 ppm), barium (45 ppm),
cadmium (160 ppm) and lead (20 ppm) were the only inorganics
reported above detection limit in this sample.
In conclusion, releases of hazardous contaminants have occurred to
groundwater and soils on the site. Groundwater has releases of
alpha BHC, delta BHC, gamma BHC (lindane), chloroethane, 1,2-
dichloroethene (total), arsenic, beryllium, manganese and sodium.
Soils on the site are contaminated with alpha BHC, delta BHC, gamma
BHC (lindane), 4,4'-DDD, Aroclor 1254, arsenic, barium, calcium,
chromium, cobalt, copper, iron, lead, magnesium, manganese and
potassium. Sediments at the site appear to be contaminated with
Aroclor 1254 and possibly arsenic, cadmium and lead.
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5.0 RECOMMENDATIONS AND CONCLUSIONS
Based on the analytical results of the sampling event at the Georgia
Pacific Hardwood Sawmill site, the following areas have had environmental
releases of hazardous contaminants that may be associated with the site:
0
0
0
0
0
0
0
groundwater in the green chain dip area is contaminated with alpha
BHC, delta BHC, gamma BHC (Lindane), beryllium, and manganese.
surface soils in the
4, 4-DDD, alpha BHC,
barium, copper. lead,
groundwater in the
chloroethane, arsenic,
green chain dip area are contaminated with
beta BHC, delta BHC, gamma BHC (Lindane),
magnesium, and manganese.
TCE spill area
and manganese.
is contaminated with
surface soils in the transformer station are contaminated with
Aroclor 1254, arsenic, barium, chromium, and lead.
surface soils in the TCE spill area are contaminated with arsenic,
and lead.
sediment in the ditch east of the sawmill complex is contaminated
with Aroclor 1254 and lead.
sediment in the ditch south of the TCE spill area is contaminated
with arsenic, cadmium, and lead.
Due to the fact that there is quantitative evidence of groundwater,
soil, and sediment contamination around the facility and that several of
the contaminants can be associated with the site activities, G&O is
recommending that the Georgia-Pacific Hardwood Sawmill site move onto the
next stage of the pre-remedial process. The Roanoke River, which supports
recreation and fishing activities, is located immediately downstream from
the site and Albemarle Sound is located less than 6 miles downstream from
the probable point of entry. Also, wetlands are located around the
perimeter of the facility as well as downstream along the river. No
surface water samples were collected to characterize surface water in the
area; however, samples were taken at two locations along drainage ditches
surrounding the site. Since the ditches outfall to the river,
contamination detected in the ditches indicates that migration of
contaminants may be occurring. Further investigation is recommended in
order to determine whether the site poses a threat to the environment or
the public.
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LIST OF REFERENCES FOR GEORGIA PACIFIC CORP. HARDWOOD SAi/MILL
EPA I.D. NUMBER 000813592
1. Louis T. McAdams. (NUS). 1990. Letter to Mr. A.R. Hanke (EPA)
regarding Screening Site Inspection, Phase I of the Georgia Pacific
Corporation Hardwood Sawmill Site, August 20.
2. Potential Hazardous Waste Site Preliminary Assessment (EPA Form 2070-
12) for Georgia Pacific Corporation Hardwood Sawmill, Plymouth, North
Carolina. Filed by Grover Nicholson, North Carolina Department of
Human Resources, Solid and Hazardous Waste Management Branch, December
6, 1985.
3. EPA Hazardous Waste Permit Application (EPA Forms 3510-1 and 3510-3)
for Georgia Pacific Corporation Hardwood Sawmill, Plymouth, North
Carolina. Filed by H.S. Merscream, Senior Vice President, November 12,
1980.
4. Tim Beachum, Decatur Partnerships, telephone conversation with Louis
McAdams, NUS Corporation, July 17, 1990. Subject: Facility ownership.
5. 0. W, Strickland, Head, Solid and Hazardous Waste Management Branch,
Environmental Health Section, North Carolina Department Human
Resources, Division of Health Services, letter to Gerald W. Tice,
Senior Environmental Engineer for the South Division, Georgia Pacific
Corporation, Augusta, Georgia, August 11, 1982. Subject: Change in
RCRA status.
6. Jim Edwards, North Carolina Department of Human Resources, Hazardous
Waste Branch, telephone conversation with Louis McAdams, NUS
Corporation, June 20, 1990. Subject: Current facility status.
7. NUS Corporation Logbook No. F4-1719 for Georgia Pacific Corporation
of facility Hardwood Sawmill, TDD No. F4-8909-89. Documentation
reconnaissance, October 11 1989.
8. U.S. Geological Survey, 7.5-minute series Topographic Quadrangle Maps
of North Carolina: Plymouth East 1954 (Photorevised 1974), Plymouth
West 1979, Westover 1954, Woodard 1979, scale 1:24,000.
9. Greenhorne & O'Mara, Inc. 1991. Field notebooks for Georgia Pacific
Hardwood Sawmill for documentation of facility reconnaissance. July
11.
10. RCRA Inspection Report for Georgia Pacific
Sawmill, Plymouth, North Carolina, October 22,
state file.
Corporation Hardwood
1981; obtained from
11. National Archives and Records Administration Code of Federal
Regulations Protection of Environment 40: Parts
July 1, 1988 (Washington, D.C.: GPO, 1988).
120 to zgg. Revised
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12. Robert L. Metcalf, "Insect Control Technology," Kjrk-Othmer
Encyclopedia of Chemical Technology. 3rd Edition, Volume 13 (New York:
John Wiley & Sons, 1983).
13. Gerald W. Tice, Senior Environmental Engineer for the South Division-
Georgia Pacific Corporation, Augusta, Georgia, letter to O. W.
Strickland, Head, Solid and Hazardous Waste Management Branch,
Environmental Health Section, North Carolina Department of Human
Resources, Division of Health Services, November 30, 1981. Subject:
Treatment process leak and leaking tank.
14. 0. W. Strickland, Head, Solid and Hazardous Waste Management Branch,
Environmental Health Section, North Carolina Department of Human
Resources, Division of Health Services, letter to Gerald W. Tice.
Senior Environmental Engineer, South Division, Georgia Pacific
Corporation, Plymouth, North Carolina, November 13, 1981. Subject:
Remedial action for treatment process leakage planned.
15. Samuel Melver, NUS Corporation, telephone conversation with Sarah
Winslow, Biologist for N.C. Division of Marine Fisheries, Subject:
Fish caught in vicinity, January 25, 1990.
16. U.S. Department of Commerce, CJ imatic Atlas of the United States
(Washington, D.C.: GPO, June 1968) Reprint: 1983, National Oceanic and
Atmospheric Administration, pp. 43, 63 .
17. U.S. Department of Commerce, Rainfaj) Frequency At las pf the United
States, Technical Paper No. 40 (Washington, D.C.: GPO. 1961), p.93.
18. Linda Aller, et al., DRASTIC: A Standardized System for Evaluating
Ground Water Pollution Potential Using Hydrogeo]ogic Settings, EPA-
600/2-87-035 (Ada, Oklahoma: EPA, April 1987), pp. 270, 271.
19. Philip M. Brown, Chief Geologist, North Carolina Geologic Survey, North
Carolina Geologic map, Department of Natural Resources, 1985.
20. U.S. Geological Survey, National Water S11mmary 1984; Hydrologic
21.
Events, Selected Water Quality Trends and Ground-Water Resources,
Water Supply Paper 2275 (1984), pp. 329-334.
Richard Powers, Groundwater Section Division,
telephone conversation with Brant Mccanless,
and 20, 1990. Subject: Geology and
Williamston, Martin County, North Carolina.
Environmental Management,
NUS Corporation, July 19
aquifer information for
22. Perry F. Nelson, Geology and Ground-Water Resources of the swanquarter
Area North Carolina, Ground-Water Bulletin Number 4 (Raleigh, North
Carolina, 1964), pp. 54, 55, 76, 77.
23. Allen Spencer, Bell Grey Well Drilling, telephone
Brant Mccanless, NUS Corporation, February 22, 1990.
and water levels in Plymouth, North Carolina.
conversation with
Subject: Geology
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24. R. Allan Freeze and John A. Cherry, Groundwater (Englewood Cliffs,
N.J.: Prentice-Hall, Inc., 1979), p.29.
25. Soil Conservation Service. Soi 1 Survey of Washington County North
Carol jna, United States Department of Agriculture, Soil Conservation
Service, December 1981.
26. North Carolina Department of Transportation, llashington County, North
Carolina, Revised, January 1, 1990.
27. Department of Commerce, 1990 Census Information: Table 6. Household,
Family and Group Quarters Characteristics.
28. Mendoza, Irene (G&O) 1991. Population and \later Supply Computations,
December 5.
29. North Carolina Department of Human Resources, Environmental Health
Section, \later Supply Branch, Alphabetic Listing of Public \/ell Systems
within \lashington County, Report No. 110415-ALPHA IIANG July 10, 1990.
30. Mr. Long, Director, \lashington System,
Louis McAdams, NUS Corporation, July 19,
water service in the Plymouth area.
telephone conversation with
1990. Subject: Extent of
31. DeRosa, Pat (NC Superfund Branch). 1989. Memo (and attachments) to
File concerning Habitats of Federally Listed Endangered Species in
North Carolina, Division of Health Services, Raleigh, NC, May 18.
32. North Carolina Natural Heritage Program Element List of \lashing ton
County, North Carolina, November 22, 1989.
33. U.S. Environmental Protection Agency, Environmental Services Division,
Environmental Compliance Branch Standard Operating Procedures and
Quality Assurance Manual. Athens, Georgia, February 1, 1991.
34. U.S. Environmental Protection Agency, Office of Drinking \later
Regulations and Health Advisories. November 1990.
35. Division of Environmental Management, Raleigh, North Carolina, NCDEHNR,
Classification and Water Quality Standards Assigned to the Waters of
the Roanoke River Basin November 1, 1990.
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APPENDIX A
MAPS ' PI-IOTOGRAPIIS, AND rrAB 1
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WASHINGTON COUNTY, N.C.
N
t
,._
B"SO'
s
'
\l
c, c.,~., ill!
c. '•,
' , I ~ ' ~ -
GEORGIA PACIFIC CORPORATION HARDWOOD SAWMILL PLYMOUTH, NC
FIGURE 1 ,r;a (1161/lllRS • UCIIIIICIS • l'IIUtAS • SCll-llSIS • SUl'l'ITOIIS • l'><0I0CIIU.i .. 1111,sa
GREENHORNE & O'MARA, INC.
9001 EDMONSTON ROAD. GREENBB..T. MARYLAND 20no
! 3011 982-2BOO
,.,.,,P•••~ .,.., .• ,. • .,,.,., •• ,, .. ,,..,co,.,_.,,,..._ '"'l•~""'"'" ,,.,,,_,,,., ,.,
'., .. ~,, ~,., ... ,,, ......... ~~•~ ..... ,,o;,, ............. , ,...,,,. .... ,"
SITE LOCATION
NCD 000813592
I SOURCE: North Carolina Department of Transportation, County Road i,taps, 1990.
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SOURCE : USGS Topographic Map, Westover & Plymouth East, N.C.
GEORGIA PACIFIC CORPORATION HARDWOOD SAWMILL PLYMOUTH, NC
SCALE 1· = 2000' CONTOUR INTERVAL 5 FEET
GREENHORNE & O'MARA. INC.
9001 E~STON ROAD. GREENBELT, MARYlAND 2DTT0
( 3111 982. 2800
FIGURE 2a
SITE LOCATION MAP
NCD 000813592
--------
flow •
--
ROANOKE ,-----------------
1
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Burner
I GWOl
® ( background I
liiil
RI VER
Temporary
Stacking
Area
-
flow .. --
.
\
\
\
\
\
\
Green Chain I
I Conveyor System I I
/sso,
-r
, a ~~ i ,
Former location otHr--------i g ~
old asphalt plant -I TCE Spill I Shed ---.,.. Area
GW-03 ___ '-I 1 ---------
I I SS~4<1> ) 'i------------I L '... ____ J I, ----------, ___ ----.....:,-c_c_ __ -l __ Di_\_e_h _
SED02
GEORGIA PACIFIC CORPORATION HARDWOOD SAWMILL NCO 000813592 PLYMOUTH, NC
[MGM((~S • IRCfllHCIS • l'\UO<(RS • SCll'fllS!S • S~V!TCA~.° ""'010(;U, .. •(UIS!S
GREENHORNE & O'MARA, INC.
9001 EDr,'lQ\/STOr~ ROAD. GREENBELT, MARYLArJD :-0770
13011 9'82.28C()
.i. .. ~,s ... ::l_!•Hh!O C.••,tC•ll• -•CUl'"l""t• ·••ot"•i• (1,1.t,"O•T ••• ,.,a,., ••
,;irfllS,,l,CJ~O o,c ... o,,,aO( ... ,.a,,1,c.,, ..C••oc, ..... u .. g,h .. •• '\• .. ,.us10,,•ua ••
SITE LAYOUT AND SAMPLING POINTS
NOT TO SCALE I FIGURE 2b
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Photo 1 -Location of background groundwater
sample (G\101) and background surface soil sample
(SSOl).
Photo 2 -Location of surface soil composite sample (SSOZ).
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"""1fl'l~"!~~j[ ~~--s ~.,,.,, ' ,I ' " ..
lumber mill. the former
'1·;,(
C )J _i::,j,
'lled. reportedly spi
I • ;:::-···. . . : .. ;,.,.,.,;ijj
·. '-. . ,' ,·4• _.;;,.-
A~ --~.
. ' ,/ :,
'S:, ,,~,
' I '-- • ~-_" I, ~
' , .
~z·-_ ·-~.:-,
-· .. '~,,. . -.,, .: ~ -' --·.
in area w
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Photo 5 -Location of suspected _green chain dip area of the former
lumber mill.
Photo 6 -Old belts of the green chain system.
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Photo 7 -Former area where lumber was temporarily stacked when it
came off of the green chain.
-Photo 8 -Stacks to the old boiler room which heated the kilns and
incinerated sawdust. Machine r9om is on the right.
----- -- -- ----
TABLE 2A
SUMMARY OF CHEMICAL ANALYSES FOR
THE GEORGIA-PACIFIC HARDWOOD SAWMILL SITE
NCD000813592
SAMPLE IDENTIFICATION
Sample Collection Information
and Parameters
Date Collected
Laboratory
Well Water Depth (Feet)
G&O Sample ID No.
EPA Case No.
Case No.
Back-
ground
Ground-
water
7/11/91
!EA
3.5
GUGU01
GN180
1041-037
Green
Chain &
Dip Area
Ground-
water
7 /11/91
!EA
5 .0
GWGW02
GN181
1041-037
Physical Waste
State
Gas
Gas
Gas
Gas
Liquid
Liquid
Liquid
Liquid
Liquid
Liquid
Liquid
Liquid
Liquid
Liquid
Characteristics* Category Compounds Detected
VOLATILE ORGANICS
Matrix
A,D,G, I DCC
A,D,G, I DCC
A,D,G, I DCC
A,D,G, I DCC
A,D,H, I SOL
E,H, I, A SOL
A,H, I SOL
A,D,G, I SOL
A,D,H,G SOL
A,D,G SOL
A,D SOL
A,D,G · SOL
A,E,G SOL
Level
¾ Moisture
Concentration Units
chloromethane
bromomethane
vinyl chloride
chloroethane
methylene chloride
acetone
carbon disulfide
1,1-dichloroethene
1,1-dichloroethane
1,2-dichloroethene
chloroform
1,2-~ichLOrOethane
2-butanone (MEK)
(total)
A,D SOL 1,1,1-trichloroethane
Water
Low
100
ug/l
[10U]
Water
Low
100
ug/l
-
Back-
ground
Surface
Soil
7/11/91
!EA
NA
GWSS01
GN182
1041-037
Soil
Low
18
ug/kg
- -
Green
Chain &
Dip Area
Surface Soil
Composite
7 /11/91
!EA
NA
GWSS02
GN183
1041-037
Soil
Low
19
ug/kg
-
Trip
Blank
7 /11/91
!EA
NA
GWTB01
GN186
1041-037
Water
Low
100
ug/L
--..
TCE
Spill
Area
Groundwater
7 /11/91
!EA
5.0
GWGW03
GN187
1041-037
Water
Low
100
ug/l
99011
19J
-
----- --- - -... -------.. II!!!!
TABLE 2A
SUMMARY OF CHEMICAL ANALYSES FOR
THE GEORGIA-PACIFIC HARDWOOD SAWHILL SITE
NCD000813592
SAMPLE IDENTIFICATION
Green Green
Back.-Chain & Back-Chain & TCE
ground Dip Area ground Dip Area Spill
Sample Collection Information Ground-Ground-Surface Surface Soil Trip Area
and Parameters water water Soil Composite Blank Groundwater
Physical Uaste
State Characteristics• Category VOLATILE ORGANICS (CONT.)
Liquid A,D SOL carbon tetrachloride
Liquid A,0,G SOL vinyl acetate
Liquid A,D occ bromodichloromethane
Liquid A,D,G SOL 1,2-dichloropropane
Liquid A,D,G SOL cis-1,3-dichloropropene
Liquid A,D,G,B SOL trichloroethene
Liquid A,D occ dibromochloromethane
Liquid A,D SOL 1,1,2-trichloroethane
Liquid A,G SOL benzene
Liquid A,D,G SOL trans-1,3-dichloropropene
Liquid A,D SOL bromoform
Liquid A,E,G SOL 4-methyl-2-pentanone
p A,E,G SOL 2-hexanone
Liquid A,D SOL tetrachloroethene
Liquid A,G,E SOL toluene
Liquid A,D,E SOL 1,1,2,2-tetrachloroethane
Liquid A,D,G SOL chlorobenzene
Liquid A,G SOL ethyl benzene
Liquid A,D,G occ styrene
Liquid A,G SOL xylenes (total)
Tentatively Identified Compounds
(Total)
Unknown 72JN
Substituted aromatic 63JN
Substituted benzene 12JN
------
Physical Waste
State Characteristics• Category
S, thick1 A,B,E ace
Liquid A,D,B ace
Liquid A,D,B ace
Liquid A,D,H SOL
Sol id A,D,H ace
Liquid A,D,H SOL
Liquid A,D,H ace
Liquid A,B ace
A,D ace
Liquid A,B ace
A ace
Sol id A,D ace
Liquid A,D ace
Liquid A,D ace
Sol id A,D ace
Sol id A,B ace
Sol id A ace
A,D ace
Liquid A,D ace
Liquid A,D ace
Sol id A ace
Sol id A,D ace
Liquid A,D,B ace
- - -----TABLE 2A
SUMMARY OF CHEMICAL ANALYSES FOR
THE GEORGIA-PACIFIC HARDWOOD SAWMILL SITE
NC 0000813 592
SAMPLE IDENTIFICATION
Green
Back-Chain &
ground Dip Area
Sample Collection Information Ground-Ground-
and Parameters water water
SEHIVOLATILE ORGANICS
Matrix \.later I.later
Level Low Low
% Moisture 100 100
Concentration Units ug/l ug/l
phenol
bis(2-chloroethyl)ether
2-chlorophenol
1,3-dichlorobenzene
1,4-dichlorobenzene
benzyt alcohol
1,2-dichlorobenzene
2-methylphenol
bis(2-chloroisopropyl)ether
4-methylphenol [1DUJ
n-nitroso-di-n-dipropylamine
hexachloroethane
nitrobenzene
isophorone
2-ni trophenol
2,4-dimethylphenol
benzoic acid
bis(2-chloroethoxy)methane
2,4-dichlorophenol
1,2,4-trichlorobenzene
naphthalene [10UJ
4-chloroani line
hexachlorobutadiene
-- -
Green
Back-Chain &
ground Dip Area
Surface Surface Soi t
Soil Composite
Soil Soil
Low Low
18 19
ug/kg ug/kg
-
Trip
Blank
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
--..
TCE
Spi LL
Area
Groundwater
Water
Low
100
ug/l
/RE
[1JJ/[1JJ
-
--.. ---- - -... --- -- - -.. -TABLE 2A
SUMMARY OF CHEMICAL ANALYSES FOR
THE GEORGIA-PACIFIC HARDWOOD SAWMILL SITE
NCD000813592
SAMPLE IDENTIFICATION
Green Green
Back-Chain & Back-Chain & TCE
ground Dip Area ground Dip Area Spill
Sample Collection Information Ground-Ground-Surface Surface Soil Trip Area
and Parameters water water Soil Composite Blank Groundwater
Physical Waste
State Characteristics• Category SEMIVOLATILE ORGANICS (CONT.)
Sol id A,O occ 4-chloro-3-methylphenol NA
Liquid A,O occ 2-methylnaphthalene NA
Liquid A,0,8 occ hexachlorocyclopentadiene NA
Solid A,O occ 2,4,6-trichlorophenol NA
Sol id A,D occ 2,4,5-trichlorophenol NA
Liquid A,D occ 2-chloronaphthalene NA
Sol id A,D occ 2-nitroanil ine NA
Liquid A,D occ dimethylphthalate NA
Sol id A,D occ acenaphthylene NA
Solid A,D occ 2,6-dinitrotoluene NA
Sol id A,D occ 3-nitroaniline NA
Sol id A,D occ acenaphthene NA
Sol id A,D,G occ 2,4-dinitrophenol NA
Solid A,D occ 4-nitrophenol NA
Sol id A,D occ dibenzofuran NA
Solid A,D occ 2,4-dinitrotoluene NA
Liquid A,D occ diethylphthalate [2JJ NA [2JJ/[2J]
A,D occ 4-chlorophenyl-Phenylether NA
Sol id A,D occ fluorene NA
Sol id A,D,E occ 4-nitroanil ine NA
Sol id A,D occ 4,6-dinitro-2-methylphenol NA
Sol id A,D occ n-nitrosodiphenylamine NA
Liquid A,D occ 4-bromophenyl-phenylether NA
Sol id A,D occ hexachlorobcnzene NA
Sol id A,D occ pentachlorophenol [970U] [690JJ NA
Sol id A,D occ phenanthrene NA
---- -- -- -... - ------.. l!!!l!!l!I
TABLE 2A
SUMMARY OF CHEMICAL ANALYSES FOR
THE GEORGIA-PACIFIC HARDWOOD SAYMJLL SITE
NC0000813592
SAMPLE IDENTIFICATION
Green Green
Back-Chain & Back-Chain & TCE
ground Dip Area ground Dip Area Spill
Sample Collection Information Ground-Ground-Surface Surface Soil Trip Area
and Parameters water water Soil Composite Blank Groundwater.
Physical Uaste
State Characteristics• Category SEHIVOLATILE ORGANICS (CONT.)
Sol id A; 0 occ anthracene NA
Liquid A,D DCC di-n-butylphthalate [400U] NA
Sol id A,D occ fluoranthene NA
Sol id A,O ace pyrene [10U] [400U] NA [1JJ
Liquid A,D ace butylbenzylphthalate NA
A,D ace 3,3-dichlorobenzidine NA
Sol id A,D ace benzo[a]anthracene NA
Sol id A,D ace chrysene [400UJ [100JJ NA
Liquid A,D ace bis(2-ethylhexyl)phthalate NA
Liquid A,O ace di-n-octylphthalate NA
Sol id A,0 ace benzo[b]fluoranthene [400U] . -NA
Solid A,O CCC benzo[k]fluoranthene [400U] NA
Sol id A,D,K,L ace benzo[a]pyrene [400U] [100J] NA
Solid A,O ace indeno(1,2,3-cd]pyrene NA
Sol id A,0 ace dibenz(a,h]anthracene NA
Sol id A,D ace benzo[g,h,i]perylene NA
Tentatively Identified NA
Compounds (Total) NA
Unknown (Total) NA
3BJN 370BJN NA
Unknown 225JN 77JN ·11,090JN 18590JN NA 169JN
substituted benzoic acid 9JN NA
substituted naphthalene 410JN NA
2-propanol,1-(2-methoxy-l-m) NA 6JN
substituted propanol NA 7JN
substituted bi cyclo[2. 2. 1 ]he NA 6JN
--.. --- -- -.. ----- - -
fr l!l!!!I
TABLE 2A
SUNHARY OF CHEMICAL ANALYSES FOR
THE GEORGIA-PACIFIC HARDWOOD SAWHILL SITE
NC0000813592
SAMPLE IDENTIFICATION
Green Green
Back-Chain & Back-Chain & TCE
ground Dip Area ground Dip Area Spill
Sample Collection Information Ground-Ground-Surface Surface Soil Trip Area
and Parameters water water Soil Composite Blank Groundwater
PEST IC lDES/PCBs
Matrix Water Water Soil Soil NA Water
level Low Low Low Low NA Low
Physical Waste X Moisture 100 100 18 19 NA 100
State Characteristics* Category Concentration Units ug/l ug/l ug/kg ug/kg NA ug/l
/DL
Solid A,D PSD alpha BHC [0.0SU] 0.12 [2.1U] 640XE/470 NA
Sol id A,D PSD beta BHC [0.05U] [0.045 J] [2.1U] NA
Sol id A,0 PSD delta BHC [0.05U] 0.13 [2.1U] 560XE/480 NA
Sol id A,D PS0 gamma BHC (Lindane} [0.0SU] 0,32 [2,1U] 1200XE/98G NA
Sol id A,D PSD Heptachlor 0,31 NA
Sol id A,D PSD Aldrin NA
Sol id A,D PSD Heptachlor epoxide NA
Sot id A,D PSD Endosul fan NA
Sol id A,O,E PSD Dieldrin NA
Sol id A,D PSD 4,4'-DDE NA
Sot id A,D PSD Endrin NA
Sol id A,D PSD Endosul fan II NA
Sol id A,D PSD .4,4'-DDD [4,0U] 170(f[150JD] NA
Solid A,D PS0 Endosul fan sut fate NA
Sot id A,D PSD 4,4'-DDT NA
Sol id A,D PSD Hethoxychlor (Mari ate) NA
Sol id A,0 PS0 Endrin ketone NA
Sol id A,D PSD alpha Chlordane 0,28 NA
Sol id A,D PSD gamma Chlordane NA
Sot id A,D PSD Toxaphene [210U] [450XJP]/10000U] NA
m
I ,
I
TABLE 2A
GEORGIA-PACIFIC
NCD 000 813 592
I INORGANICS
WATER
NCMCL
(PPB)
WATER
MCL
(PPB)
GWGWOl
(PPB)
GWGW02
(PPB)
GWGW03
(PPB)
I ALUMINUM 300000J 690000J 20000J
ANTIMONY 10/5 42UR 42UR 42UR
ARSENIC 50 2UJ GUJ 43J
I BARIUM 1000 5000 lOOOJ 2900J 960J
BERYLLIUM 1 2J 12J lUR
CADMIUM 5 5 4UJ 4UJ 4UR
I CALCIUM 130000J 170000J 210000J
CHROMIUM 50 100 340J 740J 81J -
COBALT 76J lOOJ llJ
COPPER 1000 1300 llOJ 270J 31J
I IRON 300 310000J 340000J 71000J
LEAD 50 50 270J 170J 140J
MAGNESIUM 25000J 40000J 28000J
WAN GANE SE 50 1300J GOOOJ 4300J
ERCURY 1.1 2 1. 7J 1. SJ 0.20UR
ICKEL 150 100 150J 420J 52J
POTASSIUM 20000J 49000J 36000J
I SELENIUM 10 50 lUR 20UJ 2UJ
SILVER 50 SUR SUR SUR
SODIUM 8000J 6500J 96000J
I THALLIUM 2/1 2UJ 2UJ 2UJ
VANADIUM 540J 920J 42J
ZINC 5000 330J 940J 320J
I CYANIDE 154 200 u u u
NOTES:
I 1) NA -NOT ANALYZED
2 ) N -PRESENCE OF CONTAMINANT PRESUMED
3) J -CONCENTRA'rI ON ESTIMATED
I 4 ) u -NON-DETECT
5) R -DATA UNUSABLE
6) B -CONTAMINANT FOUND IN THE ASSOCIATED BLANK
I 7 ) NCMCL -NORTH CAROLINA MAXIMUM CONTAMINANT LEVEL
8 ) MCL -FEDERAL MAXIMUM CONTAMINANT LEVEL
I ..
I
D
I ,
I
I INORGANICS
SOILS
NATURAL
RANGE
(PPM)
TABLE 2A
GEORGIA-PACIFIC
NCD 000 813 592
GWSSOl
(PPM)
GWSS02
(PPM)
------------------------------------------I ALUMINUM 0.7->10% 7000 5600
ANTIMONY <1-8.8 :!OUR 20UR
ARSENIC <0.1-73 3U 3U
I BARIUM 10-1500 29 320
BERYLLIUM <1-7 0.26 0.34
CADMIUM 0.01-0.7 lU lU
I CALCIUM 0.01-20% 580 79000
CHROMIUM 1-1000 8.1 8.3
COBALT <0.3-70 1. 3U 5.3
COPPER <1-700 3.0 23
I IRON 0.01->10% 6900 5600
LEAD <10-300 5.8 33
MAGNESIUM 0.005-5% 380 3600
WANGANESE <2-7000 42 850
ERCURY 0.01-3.4 0.29U 0.28U
ICKEL <3-700 4.1 9.8
I POTASSIUM 0.005-3.7% 470 1800
SELENIUM <0.1-3.9 0.26U lU
SILVER 0.01-5 1. 31J 1. 3U
SODIUM 0.05-5% 250U 480U
I THALLIUM 0.53U 0.53U
VANADIUM <7-500 13 11
ZINC <5-2900 29 81
I CYANIDE u u
NOTES: I 1) NA -NOT ANALYZED
2) N -PRESENCE OF CONTAMINANT PRESU
3) J -CONCENTRATION ESTIMATED
I 4 ) u -NON-DETECT
5) B -CONTAMINANT FOUND IN ASSOCIAT
6 ) R -DATA UNUSABLE
I
I ..
I
-----I!!!!!!
Physical Waste
State Characteristics* Category
Gas A,D,G, I CCC
Gas A.D.G. I CCC
Gas A,D,G, I CCC
Gas A,D,G, I CCC
Liquid A.D,H, I SOL
Liquid E,H, l,A SOL
Liquid A,H, I SOL
Liquid A,D,G. I SOL
Liquid A,D,H,G SOL
Liquid A,D,G SOL
Liquid A,D SOL
Liquid A,D,G SOL
Liquid A,E,G SOL
Liquid A,O SOL
!!111!1 liiii liiiill • -
TABLE 2B
SUMMARY OF CHEMICAL ANALYSES FOR
THE GEORGIA-PACIFIC HARDWOOD SAWMILL SITE
NC0000813592
SAMPLE IDENTIFICATION
--
Analyzed at the North Carolina State Laboratory of Public Health
Sample Collection Information
and Parameters
Date Collected
Laboratory
Well Depth (Feet)
G&O Semple IO No.
NCDEHNR No.
Field No.
Compounds Detected
VOLATILE ORGANICS
Matrix
Concentration Units
chloromethane
bromomethane
vinyl chloride
chloroethane
methylene chloride
acetone
carbon disulfide
1,1-dichloroethene
1,1-dichloroethane
1,2-dichloroethene (total)
chloroform
1,2-dichloroethane
2-butanone (MEK)
1,1,1-trichloroethane
Trip
Blank
7/9/91
SLPH
NA
GWTB02
15010
912625
15010
Water
ug/l
Trace
Transformer
Station TCE Lumber
Surface Surface Stacks
Soil Soil Ditch
7 /9/91 7/9/91 7 /9/91
SLPH SLPH SLPH
NA NA NA
GWSS03 GWSS04 GWSED01
15011 15012 15013
912626 912627 912628
15011 15012 15013
Soil Soil Soil
ug/kg ug/kg ug/kg
- - --r
TCE
Down-
gradient
Ditch
7/9/91
SLPH
NA
GUSED02
15014
912629
15014
Soil
ug/k.g
----- -
Physical Waste
State Characteristics* Category
Liquid A,D SOL
Liquid A,D,G SOL
Liquid A,D ace
Liquid A,D,G SOL
Liquid A,D,G SOL
Liquid A,0,G,B SOL
Liquid A,D CCC
Liquid A,D SOL
Liquid A,G SOL
Liquid A,D,G SOL
Liquid A,D SO!...
Liquid A,E,G SOL
p A,E,G SOL
Liquid A,D SOL
Liquid A,G,E SOL
Liquid A,D,E SOL
Liquid A,D,G SOL
Liquid A,G SOL
Liquid A,D,G CCC
Liquid A,G SDL
-l!!!!!!!l!!I l!!!!I liiiiiil
TABLE 2B
SUMMARY OF CHEMICAL ANALYSES FOR
THE GEORGIA-PACIFIC HARDWOOD SAWHILL SITE
NC0000813592
SAMPLE IDENTIFICATION
-
Analyzed at the North Carolina State Laboratory of Public Health
Transformer
Station TCE Lumber
Semple Collection Information Trip Surface Surface Stacks
and Parameters Blank Soil Soil Ditch
VOLATILE ORGANICS (CONT.)
carbon tetrachloride
vinyl acetate
bromodichloromethane
1,2-dichloropropane
cis-1,3-dichloropropene
trichloroethene
dibromochloromethane
1,1,2-trichloroethane
benzene
trans-1,3-dichloropropene
b;-c,;riuiur·m
4-methyl-2-pentanone
2-hexanone
tetrachloroethene
toluene
1,1,2,2-tetrachloroethane
chlorobenzene
ethyl benzene
styrene
xylenes (total)
tetrachydrofuran Trace
-- --r -
TCE
Down-
gradient
Ditch
-.. !!!!!!I 1!!!119 1111:.'1
State Characteristics* Category
S,thick1 A,B,E occ
Liquid A,0,8 occ
Liquid A,O,B occ
Liquid A,O,H SOL
Sol id A,0,H occ
Liquid A,O,H SOL
Liquid A,O,H DCC
Liquid A,B occ
A,D occ
Liquid A,B DCC
A occ
Sol id A,D occ
Liquid A,D occ
Liquid A,D occ
Sol id A,D occ
Sol id A,B DCC
Solid A occ
A,O occ
Liquid A,D occ
Liquid A,O occ
Sol id A occ
Sol id A,D occ
Liquid A,D,B occ
== liiiil ., -TABLE 28
SUMMARY OF CHEMICAL ANALYSES FOR
THE GEORGIA-PACIFIC HARDWOOD SAWHILL SITE
NC0000813592
SAMPLE IDENTIFICATION
--
Analyzed at the North Carolina State Laboratory of Public Health
Transformer
Station TCE Lumber
Sample Collection Information Trip Surface Surface Stacks
and Parameters Blank Soil Soil Ditch
Matrix Water Soil Soil Soil
Concentration Units ug/kg ug/kg ug/kg
phenol
bis(2-chloroethyl)ether
2-chlorophenol
1,3-dichlorobenzene
1,4-dichlorobenzene
benzyl alcohol
1,2-dichtorobenzene
2-methylphenol
bis ( 2-ch loroi sopro·pyl )ether
4-methylphenol
n-nitroso~di-n-diproµylaminP.
hexachloroethane
nitrobenzene
i sophorone
2-nitrophenol
2,4-dimethylphenol
benzoic acid
bis(2-chloroethoxy)methane
2,4-dichlorophenol
1,2,4-trichlorobenzene
naphthalene
4-chloroani line
hexachlorobutadiene
- ------
TCE
Down-
gradient
Ditch
Soil
ug/kg
----- -
Physical lJaste
State Characteristics• Category
Sol id A,D CCC
Liquid A,D CCC
Liquid A,0,8 CCC
Sol id A,D CCC
Sol id A,D CCC
Liquid A,D CCC
Sol id A,D CCC
Liquid A,D CCC
Sol id A,D CCC
Sol id A,D CCC
Sol id A,D CCC
Sol id A,D CCC
Sol id A,D,G CCC
Sol id A,D CCC
Sol id A,D CCC
Sol id A,D CCC
Liquid A,D CCC
A,D CCC
Sol id A,D CCC
Sol id A,D,E CCC
Sol id A,D CCC
Solid A,D CCC
Liquid A,D CCC
Sol id A,D CCC
Sol id A,D CCC
Sol id A,D CCC
- - - --TABLE 28
SUMMARY OF CHEMICAL ANALYSES FOR
THE GEORGIA-PACIFIC HARDWOOD SAWHILL SITE
NCD000813592
SAMPLE IDENTIFICATION
--
Analyzed at the North Carolina State Laboratory of Public Health
Sample Collection Information
and Parameters
SEMIVOLATILE ORGANICS (CONT.)
4-chloro-3-methylphenol
2-methylnaphthalene
hexachlorocyclopentadiene
2,4,6-trichlorophenol
2,4,5-trichlorophenol
2-chloronaphthalene
2-nitroaniline
dimethylphthalate
acenaphthylene
2,6-dinitrotoluene
3-nitroanil ine
acenaphthene
2,4-dinitroµhenol
4-ni trophenol
dibenzofuran
2,4-dinitrotoluene
diethylphthalate
4-chlorophenyl-Phenylether
fluorene
4-nitroaniline
4,6-dinitro-2-methylphenol
n-nitrosodiphenylamine
4-bromophenyl-phenylether
hexachlorobenzene
pentachlorophenol
phenanthrene
Trip
Blank
Transformer
Station
Surface
Soil
TCE
Surface
Soil
Lumber
Stacks
Ditch
- -
TCE
Down-
gradient
Ditch
--r l!II!!!!!
------
Physical Waste
State Characteristics* Category
Solid A,D DCC
Liquid A,D DCC
Sol id A,D ace
Solid A,D ace
Liquid A,D ace
A,D ace
Sol id A,D ace
Sol id A,D ace
Liquid A,D ace
Liquid A,D ace
Solid A,D ace
Sol id A,D ace
Solid A,D,K,L ace
Sol id A,D ace
Sol id A,D ace
Sol id A,D ace
- - - -.. -TABLE 28
SUMMARY OF CHEMICAL ANALYSES FOR
THE GEORGIA-PACIFIC HARDWOOD SAWMILL SITE
NC0000813592
SAMPLE IDENTIFICATION
-
Analyzed at the North Carolina State Laboratory of Public Health
Sample Collection Information
and Parameters
SEHIVOLATILE ORGANICS (CONT.)
anthracene
di-n-butylphthalate
fluoranthene
pyrene
butylbenzylphthalate
3,3-dichlorobenzidine
benzo[a)anthracene
chrysene
bis(2-ethylhexyl)phthalate
di-n-octylphthalate
benzo[b]fluoranthene
b~nzo[k]fluoranthene
benzo[a)pyrene
indeno[1,2,3-cd]pyrene
dibenz[a,h]anthracene
benzo(g,h,i]perylene
Trip
Blank
Transformer
Station
Surface
Soil
TCE
Surface
Soil
-
Lumber
Stacks
Ditch
- -
TCE
Down-
gradient
Ditch
-!11!!1!!
-.. - - --- - -.. - -- -- -
-r !I!!
TABLE 2B
SUMMARY OF CHEMICAL ANALYSES FOR
THE GEORGIA-PACIFIC HARDWOOD SAWMILL SITE
NC0000813592
SAMPLE IDENTIFICATION
Analyzed at the North Carolina State Laboratory of Public Health
Transformer TCE
Station TCE Lumber Down-
Sample Collection In format ion Trip Surface Surface Stacks gradient
and Parameters Blank Soil Soil Ditch Ditch
PESTICIDES/PCBs
Matrix NA Soil Soil Soil Soil
State Characteristics* Category Concentration Units NA mg/kg mg/kg mg/kg mg/kg
Solid A,D PSD alpha BHC NA NA NA NA NA
Sol id A,D PSD beta BHC NA NA NA NA NA
Sol id A,D PSD delta BHC NA NA NA NA NA
Sol id A,D PSD gamma BHC (L indane) NA <0.40 <0.40 <0.40 <0.40
Solid A,D PSD Heptachlor NA NA NA NA NA
Solid A,D PSD Aldrin NA NA NA NA NA
Sol id A,D PSD Heptachlor epoxide NA NA NA NA NA
Solid A,D PSD Endosul fan NA NA NA NA NA
Sol id A,D,E PSD Dieldrin NA NA NA NA NA
Solid A,D PSD 4,4'-DDE NA NA NA. ~.~ ""
Sol id A,D PSD Endrin NA <0.10 <0.10 <0.10 <0.10
Sol id A,D PSD Endosul fan II NA NA NA NA NA
Sol id A,D PSD 4,4' -DOD NA NA NA NA NA
Sol id A,D PSD Endosul fan sulfate NA NA NA NA NA
Sol id A,D PSD 4,4'-DDT NA NA NA NA NA
Sol id A,D PSD Methoxychlor (Mariate) NA <1.0 <1.0 <1.0 <1.0
Solid A,D PSD Endrin ketone NA NA NA NA NA
Solid A,D PSD alpha Chlordane NA NA NA NA NA
Sol id A,D PSD gamma Chlordane NA NA NA NA NA
Solid A,D PSD Toxaphene NA <2.0 <2.0 <2.0 <2.0
-----
Physical Waste
State Characteristics* Category
Liquid A,0 occ
Liquid A,0 occ
Liquid A,D occ
Liquid A,D occ
Liquid A,D occ
Liquid A,D occ
Liquid A,0 ace
-- --.. -TABLE 28
SUMMARY OF CHEMICAL ANALYSES FOR
THE GEORGIA-PACIFIC HARDWOOD SAWMILL SITE
NC0000813592
SAMPLE IDENTIFICATION
--
Analyzed at the North Carolina State Laboratory of Public Health
Sample Collection Information
and Parameters
PEST IC IDES/PCBS (CONT.}
Aroclor 1016
Aroclor 1221
Aroclor 1232
Aroclor 1242
Aroclor 1248
Aroclor 1254
Aroclor 1260
2,4-0
2,4,5-TP
Trip
Blank
NA
NA
NA
NA
NA
NA
NA
NA
NA
Transformer
Station
Surface
Soil
NA
NA
NA
NA
NA
1.08*
NA
<0.10.
<0.10
TCE
Surface
Soil
NA
NA
NA
NA
NA
<0.10
NA
<0.10
<0.10
Lumber
Stacks
Ditch
NA
NA
NA
NA
NA
0.30*
NA
<0.10
<0.10
- -
TCE
Down-
gradient
Ditch
NA
NA
NA
NA
NA
<O 10
NA
<0.10
<0.10
-l!!!l!!I
------
State Characteristics* Category
Sol id A,O MES
Sol id A,D MES
Sol id A,O MES
Sol id A,D MES
Sol id A,D MES
Sol id A,D MES
Sol id D MES
Sol id A,O MES
Sol id A,D HES
Solid A,0 MES
Sol id A,O MES
Sol id A,0 MES
Solid A,D MES
Sol id A,D MES
Liquid A,O MES
Solid A,O MES
Sol id 0 MES
Sol id A,0 MES
Sol id A,D HES
Sol id D MES
Sol id A,O MES
----,,. -TABLE 2B
SUMMARY OF CHEMICAL ANALYSES FOR
THE GEORGIA-PACIFIC HARDWOOD SAWMILL SITE
NC0000813592
SAMPLE IDENTIFICATION
--- -
Analyzed at the North Carolina State Laboratory of Public Health
Transformer TCE
Station TCE Lumber Down-
Sample Collection Information Trip Surface Surface Stacks gradient
and Parameters Blank Soil Soil Ditch Ditch
ANALYTE DETECTED
Matrix NA Soil Soil Soil Soil
Concentration Units NA mg/kg/mg/l mg/kg/mg/l mg/kg/mg/l mg/kg/mg/l
Total/TCLP Total/TCLP Total/TCLP Total/TCLP
aluminum NA NA NA NA NA
antimony NA NA NA NA NA
arsenic NA 32*/0.07 10•;0.02 <2.0/<0.01 9.8*/0.05
barium NA 220"'"/1 .00 30/0. 58 27/0.42 45/0.62
beryllium NA NA NA NA NA
cadmium NA <30/0.08 <20/<0.08 <15/<0.08 160*/<0.08
calcium NA NA NA NA NA
chromium NA 40*/<0.10 <20/<0.10 <20/<0.10 <20/<0.10
cobalt NA NA NA NA NA
copper NA NA NA NA NA
iron NA ~-·· nM iiA. NA
lead NA 110*/<0.50 20*/<0. 50 27*/<0.50 20*/<0.50
magnesium NA NA NA NA NA
manganese NA NA NA NA NA
mercury NA <0.09/<0.02 <0.09/<0.02 <0.1/<0.02 <0.1/<0.02
nickel NA NA NA NA NA
potassium NA NA NA NA NA
selenium NA <1.7/<0.005 <1.0/<0.005 <1.0/<0.005 <1.0/<0.005
silver NA <30/<0.10 <20/<0.10 <20/<0.10 <20/<0. 10
sodium NA NA NA NA NA
thallium NA NA NA NA NA
-l!!!e.9
- --
Physical Waste
State Characteristics* Category
Sol id A,D MES
Sol id A,D MES
Sol id A ICC
----.. -TABLE 28
SUMMARY OF CHEMICAL ANALYSES FOR
THE GEORGIA-PACIFIC HARDWOOD SAWMILL SITE
NCDOOOB13592
SAMPLE IDENTIFICATION
--
Analyzed at the North Carolina State Laboratory of Public Health
Sample Collection Information
and Parameters
ANALYTE DETECTED (CONT.)
vanadium
zinc
cyanide
NA Not Analyzed
Trip
Blank
NA
NA
NA
Transformer
Station
Surface
Soil
NA
NA
NA
* Concentrations significant, considered to be a release
TCE
Surface
Soil
NA
NA
NA
Lumber
Stacks
Ditch
NA
NA
NA
- -
TCE
Down-
gradient
Ditch
NA
NA
NA
-----
-.. ---
COMPOUND QUALIFIERS
u
J
UJ
C
B
---

-
• -
DEFINITION
Indicates compound was analyzed for
but not detected.
Indicates an estimated value.
Quantitation limit is estimated due
to a quality control (QC) protocol.
This flag applies to pesticide
results where the identification has
been confirmed by GC/MS. Single
component pesticides ~10 ng/uL in
thj final extract shall be confirmed
by GC/MS.
This flag is used when the compound
is found in the associated blank as
·well as in the sample. It indicates
possible/probable blank
contamination and warns the data
user to take appropriate action.
----
INTERPRETATION
Compound was not detected at or
above the CRDL.
Com1>ound value may be semi-
quantitative.
Compound was not detected if value
is at CRDL, e.g., 100 UJ. If a
value is reported with a UJ above
CRDL and it is <Sx blank
concentration (lOx for common
laboratory artifacts), the compound
is detected but may be a laboratory
artifac and not attributable to the
sample.
Compound was confirmed by GC/MS and
is quantitative. Use pesticide/PCB
listed value.
Compound value may be semi-
quantitative if it is <Sx the blank
concentration (<lOx the blank
concentrations for common laboratory
artifacts: phthalates, methylene
chloride, acetone, toluene, 2-
butanone).
!!!!!I
----
COMPOUND QUALIFIERS
E
D
A
R
X
ANALYTE QUALIFIERS
E E
s s
R N
.. -• -
DEFINITION
This flag identifies compounds whose
concentrations exceed the
calibration range of the GC/HS
instrument for the specific
analysis. This flag will llll..l apply
to presticides/PCBs analyzed by
GC/EC methods.
This flag identifies all compounds
identified in an analysis at a
secondary dilution factor.
This flag indicates that a TIC is a
suspected aldol-condensation
product.
Results are unusable due to a major
violation of QC protocol.
Cannot be confirmed by CLP
protocols.
DEFINITION
Estimated or not reported due to
interference. See laboratory
narrative.
Analysis by Method of Standard
Additions.
Spike recoveries outside QC
protocols, which indicates a
possible matrix problem. Data may
be baised high or low. See spike
results and laboratory narrative.
--_, --
INTERPRET A TI ON
Compound value may be semi-
quantitative. There should be
another analysis with a D qualifier,
which is to be used.
Alerts data user to
change in the CRDL.
quantitative.
a possible
Data is
Alerts data user of a laboratory
artifact in the TICs only.
Compound value is not usable.
Compound may or may not be present.
INTERPRETATION
Analyte or element was not detected,
or value may be semiquantitative.
Value is quantitative.
Value may be quantitative or semi-
quantitative.
l!!!!!I
------
* *
+ +
[ ) B
UJ
J
u u
M
II
R
llaste Cbatactei:istics
A -Toxic D
B -Corrosive E
C -Radioactive F
- - --
Duplicate value outside QC protocols
which indicates a possible matrix
problem.
Correlation coefficient for standard
additions is less than 0.995. See
review and laboratory narrative.
Value is real, but is above
instrument DL and below CRDL.
DL is estimated because of a QC
protocol. DL is possibly above or
below CRDL.
Value is above CRDL and is an
estimated value because of a QC
protocol.
Compound was analyzed for but not
detected.
Duplicate injection precision not
met.
Post-digestion spike for furnace AA
analysis is out of control limits
(35-115%), while sample absorbance
is <50% of spike absorbance.
Results are unusable due to a major
violation of QC protocols.
Identificaticc*
-Persistent G -Flammable
-Soluble H -Ignitable
-Infectious I -Highly Volatile
-I!!!! I!!!!! 11!!!1
J
K
L
Value may be quantitative or semi-
quantitative.
Data value may_ be biased.
Value may be quantitative or semi-
quantitative.
Compound or element was not
detected.
Value may be semiquantitative.
Compound was not detected at or
above the CRDL.
Value may be semiquantitative.
Value may be semiquantitative.
Analyte value is not usable.
-Explosive
-Reactive
-Incompatible
Giiiiiiil
I
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D
D
n
E
m
E
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APPENDIXB
SITE INSPECTI10N FORJ.\1
POTENTIAL HAZARDOUS WASTE SITE I. IDENTIFIC..l TION --,SEPA 01 STAT'E I 02 Sil'E "IU""8ER SITE INSPECTION REPORT NC I D000813592 PART 1 • SITE LOCATION AND INSPECTIOM INFORMATION'
D
II. SITE NAME ANO LOCATION
01 SITE NAME lt•a., ,......._ "'~'''""'',..•"-•'""•' 02 STREET. Aoure NO ~A SPECIFIC LOCATION IOE/'ITIFlEA
Georgia Pacific Corp. Hardwood Sawmill Plywood Drive
CJ ClfY o•sure \ 0!I ZIP COO~ Cl! COUNTY ,:1cou7 oe CONO
I Washin°ton
i :coe ~ST
D Plymouth NC I 27962 1094 01
09 COOROIN.,iES I \ 0 NPE OF QWNEl'lSHIP IC•or• ..,,.,
U.TITUOE \ :.ONGITUOE ~A.PRIVATE O 8. FEDERAL = C. STATE Q 0. COUNTY : S. ",l:UNICIPAL :150 SJ..'.. J. Q'.' . I _]£ o ..41.c .JQ.'.'. CF. OTHER ~ G.UNKNOWN
D lll. INSPECTION INFORMATION
0 1 DA TE CF INSPECTION I o,s,TE ST .rus OJ YEARS OF OPERATION
z , I I· 21 :X ACTIVE 1950 I I983 _UNKNOWN
"°"'"" a•, •f •• C iNACTIVE 3EGt,,jNl"IQ YE4A :NOINC, YfAR
I 04 AGENCY PEAFQFIMINGlkSPECTIQN ,c,..,., .. ,,..,_,
~ A., EPA C: 8 E?• CONT~ACTQR ~ C. MUNICIPR C: :J. MUNICIPAL CONTRACTOR
Greenh·or·ne~'o I Mara ~--,_
':: E.STATE ~F S7ATECO~TRACTOR '= G. OTHER .. _.,,_, ·s,i.c.-,1
I a~ c,.a1EF IN:;PECTCA l 06 TITLE 0 7 OFIGANllA TION I~· :~~';;:088 .Jeff Tvbnrski r.,:)0 1 ......... ist nc_n
::>9 QH-sE" ,NSPECTOAS 110TITLE ; I OFIGANllA TION ·: ~ELEPI-IONE ft,fQ I
I Jerry Johnson Land Surveyor G&O , i9191 782-9088
l I
Christopher Huff Environmental Engineer G&O I ~191182-9088
I I
Grover Nicholson Environmental Engineer NCDEHNR 119191 733-2801
I
Harvey Allen Environmental Engineer NCDEHNR I 919 1733-2301
-· I I I
I : J SI re AEPAESENTA rives INTE'=IVIEWEO \~TITLE 1 ~AOOAt:SS \ '. e rEL£PMONE NO nvironmental
Jav Johnson Manager Outer Banks Contractors I '
'
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1 1 ACCESS GAJNEO 8Y I,, nM: :,
4
:s,ecm" 19 WE,.THER CCNOITIQNS ·C~u• ..,.,
~ PERMISSION Overcast, cloudy, chance of rain 80-85° I 0 WARRANT
IV. INFORMATION A\/AJLABLE FROM
01 CONU.CT 02 OF ,..,v•,..,.,°'9_._,, OJ TEU.PHONE MO.
I Grover Nicholson NCDEHNR-Superfund Branch 19191 733-2801
o, PERSON RESPONSIBLE FOR sire INSPECTION FOAM 05 AOE~Y oe OFIGANIZA TICIN 07 TELEPHONE NO. oe OATE
IQ· 131 191 Irene Mendoza G&O [phone] -:,N"OI Q,lY llE""
'€PAFQRl'2070-'317 On
I
D
-,EPA HA ' SITE INSPECTION REPORT, : t ST.1.f'E 102 S1;: '<U.,.8ER
NC I D000813592
PART 2 · WASTE INFORMATION
POTENTIAL I IOENTIFICA TlON
'
'I. STE ST A TES. QUANTITIES. A.NO CHARACTERISTICS
PHYSICAL STATES ,c,.,.u .. ,,.,.,_,, ' J2 WASTE QUANTITY Al SITE OJ W,1,,SJE CHAFIAC1E::Isr~s ,c.,,u ~,,.., -· l ,., .. .,, .. "' ,.,.,. ow•.,M••• X • raxic .~ ~ SOLUBLE _: i Hl(JML • ·•CLA rlLE
~ SOL :0 E SL:.;RRY < -wJt .:>• -"O~.-,.-a,,.tt
3 PQW'.:lE~ H•;ES XF L'OUIO ' '.:)NS lJL.3~ =I..:-; r _ a CORRC)SI~ E : ~ 1NFECT10US _: ; f).PLCS.'YE
_ c R•o•o.,c::·,e _: ~ FLAl•ll•'-'8LE : ,,; Re•c-,·,e
X: 3LUOGE G GAS x:i PERS1:;;~..,T :. "' •GNITABLE : ~ INCQ._.P,T!BLE
: ."'J•S Y .t.FIOS -· . --------·-: '-4 N07 .;.,'PL1CA8LE
;: ... f.-l -------~ :~,-,,., •,Q QF :)RUM~ .. --------
: Ill. WASTE TYPE
-~::O"' I SUBSTANCE .•u.ME j O, GROSS AMOUNT 02 UNIT QJ: Mf,t,SURi: I CJ COMMENTS
SLUDGE I 1/; ""' nounds (KOO 11 waC"+-ewater sl·"~e
OLY'I OILY WASTE I 20 000 nounds i (DOOO D007 D00081 snent oil
rl SOL SOLVENTS 375 oounds ( FOO 1 . Fons ff'lQi;\ --.1••-.,t-c
.::,50 PESTICIDES U.,..l,-unknown lindane f..:----.... .:-..:,..:i,..)
')CC I OTHER ORGANIC CHEl.41CALS
rfi OC I :NQRGANlC Cr.€.i..4•CAL5
.:.co : ~cios I
I 3.:..5 3ASES '
I ,,,::_s ' --€AVY MET.a.LS ! I
. HAZARDOUS suasr ANCES 1.s, ...... _. ,a,_,,,,u .. -,,.. , ..• :LAS N-=••11
I -,:,_rEGQAY j ·?2 SUSST ANCE NAME I OJ CAS M,JMBfR :i, STQR,t,GE1oi':,i:ics.1.L ME TMOO ! C5 CO-~CENTA,HIQ\, I ~a MEASURE OF CONCENTFU.TIOH
ii Chromium I 741,n 4 7 -1 drums unk-----
! Lead I 7439 92 1 drums unknown
I ES Pentachloronheneate I 87 86 5 drums unknown
IC
I Sodium Metaborate drums I unknown
I Chloronhenols drums unknown I
Lindane i 58-89 9 drums i unknown
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Iv FEE0STOCKS ,s .... .,..,,..,_c .. s-
CATEGORY I 0 I Jll:E0$TOCK NAMf 02 CAS NUMBER CA!EGOAY I 0 I FEEDSTOCK NAME 02 CAS NUWBEA
=os ' FOS I !
I =-.:s I 'OS I I
=os I FQS I
.:os I I '0S , lv1. SOURCES OF INFORMATION ,c •• ,.,"'~" ,.,., ... c ... • o ' ·'" , ... ·-·· ....... ,,. , ......... , .
1. G&O Field Notes
I 2. NCDEHNR-State Files
3. Sax & Lewis; Dangerous ProEerties of Industrial )!ate rials -tt """ ,. ,. "" "
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!
COTENTIAL HAZARDOUS WASTE SITE
SITE INSPECTION REPORT
i :. 1DENTIF1CAT10N
NC D000813592 ,SEPA Pj\RT J • DESCRIPflON OF HAZARDOUS CONDITIIONS AND INCIDENTS IQ\ su.re 02 SITE NUMBER
·1 1-4AZAR00US CONDITIONS ANO INCIDENTS
.. .. ' u;:;ouNOWA TEA CONTAMINATION 02 C OBSERVED !DATE _ POTENTIAL ·~ ALLEGED -9,863 : J c,:c•~·•~:. '."1C,",' POTE"<TIALL Y AFFECTED -.::.; NAARATlVE DESCRIPTION
Groundwater wells located within a 4-mile radius of the site serve
an estimated 9,863.
: 1 ·...: = SURF ACE WATER CONTAMINATION 02 G OBSERVED (DA TE: = POTENTlAL :J ALLEGED
:2 OQPULAT!CNPOTENTIALLY AF;:'fC':"i::D Jd NAAAA rive OESCAIPTtQN
.
There are no surface water intakes within F ·' miles downstream of the site.
.. :2NTAMINATIQN QF AIR 02 C CSSEAVEOtOATI: . ) :: POTENTIAL ~ ALLEGED :-: -·= 8,172 : J 0':l='L:L.:... T\CN POTENTlALL Y At=;:-:_,: TED ~4 NARRATIVE DESCRIPTION
There are an estimated 8,172 residents living within a 4-mile radius
of the site.
:: . ;e:;:iE.'EXPLOSIVE CONDITIONS •:::2 C! CBSERVEO (DA TE = ?QTENTIAL 0 ALLEGED --:J P,:,01_1t.ATION POTENTIALLY AF;:~CTED ------.}4 NA.AAA TIVE DESCRIPTION
After a fire in 1983, The Georgia-Pacific plant was permanently closes
and ooerati.nn~ r:cased.
o, =-: t=: JIRECT CONTACT 02 :_:: CSSEAVEO !OAT,E : C POTENTIAL 0 AU.EGEO
:J POPULA TlQN POTENTIALLY AF;:ECTEO 0-4 NA.ARA nve OESCF.IPTION
N/A
_, -co.-.,4.MINAT\QN OF SOil J2 :: CSSEAVEO IOATE ' ,_: POTENTIAL :J ALLEGED
:,J .:.;;;EA PO":'E!'ITIALLY AFFECTEC ·24 NARRATIVE OESCFIIPTION
'('OIJ
Chlo roe thane was detected in soil sampling in the vicinity if an alleged TCE
,· •mill . Also, pesticides and:metals wre detected in soil samples take rt dliringi:the
I site visit. ~
J\ ,_ G CRIN!';INGWATERCONTAMINATIQN 02 0 OBSERVED (OAlE. : ·-POTENTIAL ·...J ALLEGED
OJ POPULATION POTENTIALLY AFFECTED 9,863 0-4 NA.ARA TIVE oesc1='.1PTlON
Groundwater wells· located·:within a·.4-mile radius of the site serve an estimated
9,863 residents.
•J\ ._ ~ WORKER EXPOSURE/INJURY 02 0 OSSEAVEO (□Are. I '.J POTENTIAL 0 ALLEGED
'
-JJ wQAKERS POTENTIALLY AFFECTED Q,4 NARA A nve DESCfllPTION
The site is unoccupied and inactive.
-: '. __ , ;iQPULATIQN EXPOSURE/INJURY 02 0 OBSERVED (DA 1 E · I 0 POTENTIAL C ALLEGED
OJ PCPULA TION POTENTIALLY AFFECTED. 04 NARRATIVE OESCHIPTION
N/A
H
POTENTIAL HAZARDOUS WASTE SITE
SITE INSPECTION REPORT
I. IOENTIFICA TlON
PART 3 · DESCRIPTION OF HAZARDOUS CONDITIONS ;IND INCIDENTS
AZ.AROOUS CONOITlONS ANO INCIDENTS ,c~ .. ,.-.. n•
,)2 G OBSERVED IOATE ___ · ____ , : POTENTl.&.l
Stressed vegetation was noted in the area of the alleged TCE spill .
N/A
l_ ,11 : •-c.:::~;iJ..i.AINA.nON oF FOOD CHAIN :1I"4 ,-.;AP~A; • :;. -::::SCRIPTIQN
i N/A
l _ •.1 .";$".l8LECONTAINMENTQFW&STES
02 C ::BSEAVEO !DATE ------'
02C:OBSEAVED!OATE '. : POTENTIAL
·__: ?OTE~TIAL
:,4 N,11.PAA TIVE DESCRIPnQN
= ALLEGED
.:; ALLEGED
:: "-LU:.G.EO
I Lumber was passed through a dip vat on a conveyor system. was allowed to drip drv onto the ground.
The wet wood
01 _. :,:.v.:.GE TO QFFSITE PFIQPERTY )2 ---~ CBSERVEO !DA TE ----~-' : A.LLEGEO ,1:, '"'""'''' :;sca,PnoN
N/A
• POTENTIAL .• ALLEGED
N/A
:-2:. OBSERVEO!OATE --------' POTENTIAL : A.LL.EG.:O
1)5 cc.sc;;1pt,,:-. OF ANY OTHER KNOWN. POTENTIAL. OR ALLEGED HAZARDS
N/A
, I. TOTAL ;:iQPULATION POTENTIALLY Al'FECTEO: ~.172 <4·milel
IV. COMME~TS
SOUACES :;F INFORMATION,c~ .. , ..... , ........ ..., ... J .,.,., •• , ,.._.,..,.,,, •• ,_,..
1. G&O Field Notes 3. USGS Qua,drangle Maps I
'
2. NCDEHNR Files -------. ---------------------------'
I
! POTENTIAL HAZARDOUS WASTE SITE I 1. iOENTIFICA T!ON
I ,&EPA SITE INSPECTION \o:~~ue: :h~~~u;~~ ~ ~'>
---?ART 4 · PERMIT AND DESCRIPTIVE INFORMATION
AMIT INFORMATION
a -. =!: OF" ;,':.:i,..1r 1$SiJEO :;;: PERMIT NUMBER , :J DME ,SSt:EO IO• ElPIR.lT!ONO,UE \ O~CQM1t,,1fNTS
: -., '.,,. ,.,. ,ooo .. I I '
'-IPOES
i ;
--
-IJ\C I I I
I -AIR i I -
;;:cA.t. ; I I
-'
--ACRA INTERIM ST A TUS 1 NCD0008 I 1'iG2 I ll il?/0/1 I
I -, SPCC PLAN I I I
j ST A TE ,sa,c,,., I I
--LOCAL • I '~"f"•'
I -. )THEA ,s0..,,.., I
-.;QNE i
Ill. SITE DESCRIPTION
I -: ·-~q-"GE,c,sPOS"L -~ •• ,. ,< '"'' •oo .. , =~ .1.J.IQUNT ·)3 UNIT OF" '-'E"-SUAE 1 -:, <AEATMENTrC11n,.,.,,..,_, I °' ors,,
_: ;. SURF.6.CE IMPOUNQMENT = A. INCENEF.A TION
-P•L:S : 9. UNDERGROUND INJECTION
. :{ 1 e..:;:.:1NGS ON srre
-Xe JFl.UMS. A.8Q'JE GROUND 10 C tonsLy_r. : :::. CHEMIC.,UPHVSICAL i
I --TANK A.6Q'✓E GROUND = .J. BIOLOGI :AL I ---TAN)(_ 8E~ :·.-.. GAQUNO : ~-WASTE OIL PROCESSING i JIS AAE• c: SHE -
-C _:..NQFllL i :_ F. SOLVENT RECOVERY I '3 LrNOFARM i : G. OTHER f!ECYCLINGIRECOVERY 25 i•ctNI
I : .; OPE;.'-./ DUMP -" OT~ER I I -. !..o.u"Y1
_: 1. OTHEFl i ::.,_.,
O" ::'-o.lENTS
'
I
IV CCNTAINMENT
I -.: .:r.-:-.I.INM€.NT OF N•STES ::.•oc• -••
= I.. .\DEOUA re. SS.C'JAE = 9. MOOERA re ZJ C. :~ADEQUATE. POOR ~ D. INSECURE.UNSOU~O.CANGEROUS
C< ; :SCRIPT1QN OF OPU,_.S :;:1K1NG. LINERS. 8-'AAlfRS. ETC.
I Lumber was passed through a dip vat on a conveyor system. The wet wood was
allowed to drip onto the ground. Also, it was noted during a 1981 site inspection
that a tank used in the wood treatment process was found to be leaking.
I . V ACCESSIBILITY
: 1 WASTE E,i,SILY •CCESSIBLE: CJ YES = NO I : : ::::,..1.1E'°<TS
Details regarding the accessibility to the drums during the years of operation
is not known. Access to the site is limited by fencing and a gate guardhouse.
VI SOURCES OF INFORMA. TION 1c,, 10.•""" ,.,., ... c.,_, o ,,.,. , • ., ,_,.,,. .. ,.,,, ,,.,..,.u
1. G&O Notes
2. NCDEHNR Files
I
I
0 I. IOENTIFICA T!ON
n POTENTIAL HAZARDOUS WASTE .,ITE
SITE INSPECTION REPORT
02 SITE OjUt.18ER
?ART 5 ·WATER.DEMOGRAPHIC. AND ENVIRD~IMENTAL DATA
D000813592
KING WATER SUPPLY 'IPE OF :;:lRINKING SUPPLY •.c•u•O-•-•
SUAF&CE
·]2 STATUS :J 01ST ANCE TO SITE
WELL :.~OANGEAED -'\F~ecri::· •~ONITORED
:.:::MMUNlrY A. 0 S. j! ' C B C. 0 ' 1. 2 'ml)
-COMMUNIT'Y C ,-. J l! J C: E -~ 3 (mil -
ROUNOWATER
GROUNQWA, TER USE IN VICINITY 1C•oc• ,,..., r .:. CNL V SOURCE FQR ORINl(ING : 9 0RINl<ING
c,~., '""'"' •~•-•
co,.o,1eRCU,L. INOUS~RIAL. IFIMJGA TION ... o .. ,.., •• ,., ,_ ..... ._,
~ C CCMMERCIAL. INOUSTR! ... l. lRRIGATIQN = :,, NOT USED. UNUSEABl.E
,V-..... ,,., , .............. -1
:ll0Puvr,,:NSEF1veoevaRouNow1.re11. 9,863 (4-miles) 03 DISTANCE TO NEAREST OR INKING WA TEA WELL 2.7 (mtl
3.5
j C~ DIRECTION OF GROUNOWA TER FLOW
northeast
08 OEPTM TO .>,QUIFEi~ I 07 POTENTIAL YIELD
OF CONCERN OF AQUIFER
150 " :0001
08 SOlf SOURCE AQUIFER
=iESCRIP ;,.:-~ OF WELLS ,,~c,.,.,.,.o ~•ut• :oo,,. ,,.., -•,_, ,., • .,._ ,._.,..,_, -o.,..._11
I
The City of Plymouth Public Works Water system uses 4 wells having an average
depth of approximately 175 feet; 3 of the wells are located inside the city limit
and the 4th is located within 1 mile of the city limits. Private wells within th
studv area are enerall 200 feet deep .
• EC:-. ... .:lGE •AEA I (ES COMMENrs .= YES
Cl NO
I CCMMENTS
__ NC I
FACE "'•TEAUSErC~•:•o"•'
A RESERVOIR. RECREATION
DRINKING WATER SOUF\CE
·= B. IAAIGAT10N. ECONOMICALLY
IMPORTANT RESOURCES
= C. COMMEFICIAL. INDUSTRIAL = 0. NOT CURAENTL Y USED
,.F;ECTEO. ?OTENTIALL r AFFECTEO 800-ES OF WA TEA
AFFECTED 01ST .A.NCE TO SITE
0
5.7
----------------------------------------
DEMOGRAPHIC AND PROPERTY INFORMATION
TQT AL POPUL.4 TION WITHIN
0NE I 1) MILE OF SITE l'WO (21 MILES OF SITE
, 2. 240 a 4 482
-.o o, p,~q5,()f,o!, -.o o,. i,111so,,rs
THREE (31 MILES OF SITE
C 6,573
..0 OJ l>fllSO,.~
02 OlST>.NCE TO NEAAEST POPULAIION
_______ _,m,1
(mo
~J ~UMOEA OF BUILCINGS WITHIN TWO 121 Mll.iso, SITE O• 01ST ANCE TO NEi,REST OFF-SITE BUILDING
ii
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1,651
;,O?ULA.!•0"' WITHIN VICINITY OF SITE ,_...,_ ....... .,.. • ., • .c, _ _,,..,..,. 0 ,_.,..,_, .,.,..,._..,.00,,_0 •:
The nearest residence is located approximately 700 feet east of the facility
Plymouth High School is located on the property approximately 700 south of the
facility. A baseball park and a residential area are located adjacent to the
facility to the south.
H
POTENTIAL HAZARDOUS WJISTE SITE
SITE INSPECTION REPORT ~EPA PART 5 ·WATER.DEMOGRAPHIC. ANO ENVIRONMENTAL DATA
· i\. ENVIRONMENTAL INFORMATION
I I IDENTIFICATION
lo, su.re102 SITE NU1t.18ER
NC D000813592
:o-• -1 c-J cm,,..c ,_: : GAEA re.:;, THAN IQ. l cm1sec
--: 5 RELATIVELY IMPERMEABLE :o·• -•o·~:-uc, X C REU TIVELY :JECIMEABLE ,,-; • •o·•:.,,.c,
'✓ERV PEFU,AEABLE
,=., .. ,.,,,..,. ,o·l•~•o-c•
O• DEPTH OF cci-.r U~!NATED SOIL <.ONE
ml -------•,Ill
oe SLOPE
I
j :o NET PAECIPIT A TIQN
I 9 I :a ,,oc: >OTENT>'c :in)
SITE SLOPE I CIRECT!ON OF SITE SLOPE I TERRAIN AVERAGE S~OPE
~~2~---" Northeast 2 "
~ SITE IS ON 8ARAJEA ISLAND. CC·ASTAL HIGH HAl.l.A0 AREA. RIVERINE FLOO0WAY
I' 51 TE iS •N • ~ ,R FLQOOPL.A.IN
', J157Al'<Cf TC-1>1ETLANOSrl1c,•-• i I 2 01ST A"'CE T•J CRITICAL r,ABITA T 1~ --,.•• ..,.c•u
I
I
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I
11 !
=:STUARINE ! _____ [mil
(m11 a. I ENQ.A,,.,,GEAEO SPECIES.
JISTANCE TO
·:::JMMERCIAUIN0USTRIAL
::i: S!QENTIAL ARE .a.S. NA flQN.a.L'S7 .,_ TE PMH<S. AG RIC UL TUR.4.L LANDS
FORESTS. OR WILDLIFE RESERVES ;,ci+ME AG LANO .a.G LANO
B _0"-'-.-=-lcc.3 __ ,m,1 C. _____ [m1J 0. ______ {m1)
4 oe SCR1PTIQN OF SITE IN REL.a. TION TO SURROUNOJNG roi:,OGR.a.P ......
The Georgia Pacific Hardwood Sawmill site is on a relatively flat parcel of
land surrounded by the Roanoke River on the nothwest and wetlands around the remainde
of the property. It is located in a region characterized by extensive, flat coastal
swamps adn marshes. Elevations in the vicinity of the site are slightly above
5 feet NGVD aro;und the facility and slightly below 5 feet NGVD in the nearby
wetland area.
'✓ 11. SOURCES OF INFORMATION ,c.,. ,.,~,.c,,,., • ..., .. • 0 . .,.,.,,., .. _,. ... _, .. _ ,_u
1. NCDEHNR State Files 5. So:Ll Survey for Washington County
2. USGS Topographic Maps 6. Groundwater Bulletin for Swanquarter
3. Rainfall Frequency Atlas 7. G&O Field Notes
4. Cliamtic Atlas of the U.S.
B
POTENTIAL HAZARDOUS WASTE SITE
I. IOENT1F1CA TION
l~E:~N
01 STAf'E\02 S{TE NUMBER
SITE INSPECTION REPORT NC D000813592
PART 6 · SAMPLE AND FIELD INFORMATION
I \o' ~uMBEA ~ c: S,O.APLES SENT ro ClJ ESTIMA Tl:0 OA TE
s~...,.PLE T'(PE SAMPLES T _.,KEN R:E.SULTSA\/AA....a..f
: c;.::iQUNOWATER I 1 I ... rl.1~t-ri .,:il .-..,,.:i 'C'.-.H-: e...,..,..., 1 II 1 .. er ( T ro • ~
' I SL..'~F•CE WATER ! / 2 State Analvtical Laboratorv (SAL) ' -! "NA STE ' i ' I
I >,R I I ;
C
I rlUNOFF I L I SPILL I
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r SOIL I 2 I IEA ii .,GE7AT,QN I I ' I I I ! :_:-,-e;::i. ! 2 SAL I FIELD ME.SUAEMENTS TAKEN
r,-i:>f 02 CQMMEf'(TS
I pH Temeerature Conductivitz
I GW6W01 'i 'i lQ? or. 1 0 A-n Al
GW6W02 18.4-27.0 0.27
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I Jv PHOTOGRAPHS ANO MAPS
. -. =-€ X UROU:".Q X ~ERI.A.L l C2 :~ CUSTODY Cl'" GI:~~llbQi;:ne & Q' Mar~ 1 Inc. ... -... _~•q.,..,,.,_.,__,
C.'.l M.l.::>S ; : ~ 1..oc,i.r1ON OF M•Ps
I X ,·es Gi::eeDbo:cne & Q'Mara. and NC!lEHN!l SllperEund B:cancb ·.o I
V. OTHER FIELD DAT A COLLECTED ,,,.,_ ............. ,c,.,,_,
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I Vi. SOURCES OF INFORMATION :c,,. ,0 K.,,. ·•••••ncu • g ,·,·•••fl ,.....,..,•n•'-••• ,op,ollll
1. G&O Field Notes
~ 2. NCDEHNR State Files
AFQFH,,,1 "2070•13 t1 1!11\
ff
POTENTIAL HAZARDOUS WASTE SITE ;1. IOENTIF!CA TlON
.n EPA -SITE INSPECTION REPORT lo\ ST ATE \02 SITE -"'UM8Hl
PART 7 • OWNER INFORMATION \ NC , DOOOR[>Sa7
111. RENT OWN ERIS) I PARENT COMPANY,,,,_._,
• .... Ee 1.;2 o .. e Nu...-eeA 1011 N,Oolf \09D•S-.uwafA
I I (11,rer n.,,.,,,J~ .... rn,..,-..,..,,.,,.,,.. ......... ~ I I
!:)STPEET •UDflES.S ' : 3o, ~,;;, ,,c ' 1o•s1ccooe \: 0 STl';EET •ODAESSj,, o ll<u iUDI •«, I S.C CODE
:I=-I '
1-:~Sl.&.rei::• ~:PCCOE i : ~ CITY ·JSTATfj1•l:PCCCE
'
i Plvmouth I NC I I I j
....... ,t; 1.;2o•BNUMBEA \ 011 NAME \°90+81'1UM8fA
I I I
r'.lJSfl:tfET•OOAESS ~0 &., ~•O• ,,c, 10• sic cooe l,o stAEET ADDRESS 1, o a..,. IVO •. ••c I r' SIC :□DE
f c,r, r!ISTATElo; ZIPCOOE ! 12C1T'I' \1JSU.TE 1 • liP CCOE
I :, I "'"' ... E j 02 :1+8NVM8fA l OIi NAME
09 0+8 '"1.IMBEA
sr=~~T •ODAESS ''=' a.o, ~,o, .,, 1ci• SIC CODE l tO STREET AOOAESS'1 .. 0 .... A~o,.,,c1 i , ~ CODE
l I ,c,,, I
r6 STA TEI 01 ZIP COOE ! I 2 CITY
I 1J STATE\1• l1?CCOE
. I I I
I.JI ...... ,.,t, \C2 D+QNU~BEA 08 NAME \090•6-.IJMSEA
J,, s; "" ,ooses, •? 801 MO• ,ic, 10• SIC CODE ,o STREET AOORESS1P O &o, -.10, .,,.1 r~$.ICCOOE
ti'" r· ST"
or llPCOOE 12 CITY I\ J STATE '4 l,P COOE
PREVIOUS OWNERIS\·~·••~11••c-••••1 IV. REALTY OWNEA(S) 1~•--· "''"°"'..:, ... ,~.,,
Ql NU,11; 02 0+8NUM8ER 01 N•Mf 02 0•8 '°IUM8ER
I n,..,ratur Par ...... erc::hin
JJ S7?fET AQQAES.S • o ~o• ~,,, ••<, ! oc sic cooe OJSTRffT.lr.OCAES!;rPO ao •. ,vo, ., .. , ! :, SJCCODE
i
I o:. c1:, \ 08S:;E( ,:,; ,:1P CODE 0!.i CITY \ oe ST.Ir. TE\ 01 l:P CODE
J..T...,,...,...she...,,.:i 01 ,....,..ii; \°20~8NUM8ER 01 N.1,Mf j :::;•il-.uM8fR
I ~,,,_,...,.,.,...i:::r _p,.,,...;Fir r, --.........
OJ STREET .1,,QORES.S "o 11o, ;i,o, ••• ! 10• SIC CQCE OJSTRfET.i,,OQAE~,PO ao,.1110,.,,c.1 I:• SIC CODE
Pl ..l n-.: ..
O!.IC1;"",· 1::TATE 07 ZlPCOOE 0~ CITY loesure 07llf'COOE
I Pl ·--rh 27%2
01 NA.Mf 02 0♦8NUMBEA 01 NAAtE 020•8NUM8fA
Atlas Plvwood
I OJS:;iff~AQ()AES3 °,; s.,, ~•.;. ••<• 10• SIC CODE OJ STPl_:E! AOQRESS,P O ao, .. ,o,. ••< l i J• SIC CODE
Plvwood Drive !
O~CtTY
1:::TATEI
07 ZIPCOOE O~CHY l°6ST,t.TEI01 ;:PCOOE
I Pl um,..,, .,.}.,, ?701'.?
·,1_ SOURCES OF INFORMATION ,cuoo_,.,.,._ ... , . ..... , ... _,_ ... ___ ,_.,
I I. NCDEHNR State Files
P.&.FQR"42070-IJ;; 1111
I
n
POTENTIAL HAZARDOUS WAST,E SITE
SITE INSPECTION REPORT
PART 8 · pPERATOR INFORMAr'ION
L IOENTIFICA TION
QI SU.TE 02Sl~ENUt.lBE.R
NC D ?
UARENT OPERATOR ..• ...,..., •• _.,_,_., .... ,, OPERATOR'S ,='A,qENT COMPANY ,~•-•-•
Banks Contractors, Inc.
1020+8NU"'48EA
O• SICCOOE
Q6STAfE 07Z1PCODE
I :p1 mouth NC
TE,vlSQFOPEt:l•TION 09NAMl:0F0WNl:A
ia Pac·f·c ! )J sr:=.!:CT •OORESS ,,.0 ao, ,.,o,
1 wood Drive
!Plymouth
a
02 0 + 8 NUMBER
O• SIC CODE
06 sr.ue, 07 ZIP CODE
NC
02 0+8 NUMBER
04 SIC CODE
05STATE 07ZIPCOOE
02 0• B NUM8EA
04 S•C COOE
OC!STATE 07 l!PCOOE
8 YE.-"JI.S OF OPEAATIQN 09 NAME OF OWNER OURING THIS PEA,00
I I 0+8NUJ,,1.8f,R
2 STREIT AQQFIE!~ ~ o So• 11,0, ore, \1J SICCOCE
• CITY
PREVIOUS OPE:R.UORS' PARENT COMPANIES o,..,_,.,.,
·ONAME 11 O+BNUholBEA
:2STAEETAOOAE~S •o 1o,.11,o, flCJ I' J SIC CODE
; • CITY 1•~STATE ,ez1PCOOE
I
'ONA.ME I' 1 o ... eNu...,,seA
• l STREET ,1iQQAES:> .• o So, . .oo ,_ 1,c 1 1 J SIC CODE
: • CITY l~STATE l6Z:IPCOOE
11 O+B NU""'9EA
1J S1CC.OOE
'. 4 CITY 1!lSTATE 1ez1PCOOE
IV. SOU ACES OF INFORMATION ,co __ ,_,.,_n •. , .. .,.,.,""· •--••" .,_.,
1. NCDEHNR State Files
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PA
OFF-SITE GENERA TOR(S\
Tl.EE T •OOAESS ,., o &o•. AIO • o,c,
J 5:PECT .t.QOFIESS ,P 0 801 . .-,o, ••c,
5 CIN
POTENTIAL HAZARDOUS WASTE SITE
SITE INSPECTION REPORT
PART 9 · GENERATOR/TRANSPORTER INF'ORMA TION
! Q• SIC CODE
01 NAWE
IO• 5'C CODE OJ STREET _.,OORES~i ,,. o ao,. 111•; • "c,
r6ST.4.TE 07 llPCOOE 05 crrv
1cc STATE 01 llPCOOE
I I
1020+8NUM8EA
015 Sf.I.TE 01 ZIP CODE
-:, SICCOOE
OOSTATE OIZIPCOOE
!JI NAME
OJ STREET AOOAESi 11> o i,o, ~
01 NAME
OJ STREET AOORl:S:; 1• o lo, ... ,; • "(./
O5CITV
01 N.6.ME
0JSTl=IEETA00RES5,,.o ao, .;,.,:;, ..c1
SOURCES OF INFC:1.MATION rcu a..c-,., .. ....,., •, "''"' .. '· •--.... ••-111
I. NCDEHNR State Files
A~0RM2010-1JO·&ll
! 1. IOENTlFICATION
I::: 1 STA TE( 02 SITE NUMBER
NC 1D000813592
02 0 + 8 NU1rrio18ER
o• SICCOOE
CG STATE 01 ZlPCOOE
02 0•8 "'U¥8ER
IO• SICCOOE
;;155TA.TE 01 llPCOOE
O20,..8NUM8EA
o• SIC CODE
oeSTATE 07ZIPCODE
02 0+8 NUMBER
04 SIC CODE
oeSTATE 01 ZIPCOOE
I
RESPONSE ACTIVITIES
: l ,, ~ TE.A SUPPL V CLOSED
: ! ::Esc::::i':"'JQN
N/A
POTENTIAL HAZARDOUS WASTE SITE
SITE INSPECTION REPORT
PART 10. PAST RESPONSE ACTIVll'IES
'
02 DATE _____ _
M : ' ;E~;,,·:,~RARY WATER SUPPLY pcov,oeo
N/A
·J2 CATE _______ _
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: : S;iiLLE0 MATERIAL REMOVED
: .:. .:iesc.=,:?noN
N/A
-: : -:~NTAP,,m•./A TEO SOIL REMOVED
: .:. oesc.c;;,,,-:-;-\JN '
N A
: :: ,' . .:.5;e :::i:;0 •CKAGEO
: " JESc.::1n10N
N A
-_, ·, .:.sre DISPOSED ELSEWHERE
: .:. :esc?.:-'noN
N/A
: r, 0'1 SITE BURIAL
: .:. DESCH:?TION
N/A
: I ., sm.J C~EM!CAL TREATMENT
.:. JESC~ ::i71QN
N/A
: .i . .., SITU 81()L0GICAL TREATMENT
: ! Jesc:=.1::i-:-10N
N/A
:•, SIT'..: ?"""SICAL TREATMENT
: .:. oesc~;PTIQN
N/A
:: :. :,,cAPSULAIION
-~.:. OESCFIPTIQN
N/A = 1-4 ;:!..1EAGENCY WA::iTE TAEA™ENT
: .:. DESCRIPTION
N A
:'. ,'-I C..:70FF WALLS
-::.:. 0Escn1?nON
N A
:.•.•.!:FIGENCY 01KING1SURFACE WATER OtVEASIQN
:.:. ;;esc:1_,:rnoN
--:: :•.;:OFF TPENCHES,SUMP
: ~ oesc;:.:?r10N
020ATE _______ _
U2 DATE ______ _
02 DATE _______ _
,J2 DATE _______ _
020ATE _______ _
020ATE _______ _
02 CATE------~-
020ATE -----~
020ATE _____ _
020ATE _____ _
020ATE _____ _
020ATE ___ _
020ATE ______ _
02 DATE _______ _
I I, IOENTlFlCA TION
JJ AGENCY
)J AGENCY
OJ .'IGENCY
OJ AGENCY
JJ AGENCY
-JJ AGENCY
03 AGENCY
03 AGENCY
OJ AGENCY
03 AGENCY
03 AGENCY
OJ AGENCY
OJ AGENCY
OJ AGENCY
OJ AGENCY
OJ AGENCV
g
EPA
P.&.ST RESPONSE .lCTJVITIES,c~•-i
: : ::: A 8AAAIEA WALLS CCNST'RUCT'EO
: -1 DESCRIPTION
: : = S CAPPINGiCC'.'EA1NG
: -1 DESCRIPTION
POTENTIAL HAZARDOUS WASTE'SITE
SITE INSPECTION REPORT
PART 10 · PAST RESPONSE ACTIVlllES
02 DATE ______ _
')2 DATE ______ _
-J2 DATE ______ _
I. IDENT!FiCA. TION
C1 STA~ 015,1'E ~A
NC D000813592
OJ AGENCY
OJ AGENCY __________ _
OJ AGENCY __________ ~
I .;1 -X T BULi( iAM<AGE REPAIRED
: -1 DESCRIPTION
uring an Octobe~ 1981 site inspection, a tank used in the wood treatment process was
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·Jl Q U GAOUTCL:ATAINCONSTAUCTEO
C4 DESCRIPTION
020ATE ______ _
)I:,; V BOTTOl.4 SEALED 02 Q,&,TE ______ _
:4 OESCRIPflON
:::· ::.: -.V GAS C::;.•fTAOL 02QATE ______ _
: -1 OESCR1PTIQN
·: 1 .:_: ,:, FIA::; •:C~HAOL 02 DATE ____ _
-.:.,1 DESCRIPTION
The plant burned partially and then closed in 1983.
J 1 C Y LE>-CHATE 7AEATMENT
04 DESCRIPTION
JI::_:. Z. AREA EVACUATED
04 DESCRIPTION
.; 1 ~ l ACCESS TO 5;TE P!:5 TRICii:0
:)4 DESCRIPTION
: \ = 2. ;:>C,PUL' TiQN AfaQCATED
: ~ DESCRIPTION
:)1 = J. OTHER ~EMEOlAL .i..cnvmes
,J4 DESCRIPTION
J2 DATE ______ _
020.A.TE ______ _
020.A.TE ______ _
02 CATE ______ _
02 CATE ______ _
111. SOURCES OF INFQRMA.TlON ,c ... u,K~c••••·•~••• •o. ,,.,,, .. ,. •-••~.,.,,. ,._.,
1. NCDEHNR State Files
OJ AGENCY __________ _
OJ AGENCY __________ _
OJ AGENCY __________ --'
OJ AGENCY __________ _
OJ AGENCY __________ _
OJ AGENCY __________ _
OJ AGENCY __________ _
OJ AGENCY __________ _
OJ AGENCY __________ _
D;._ ___________________ --:--:---:---:---:--:-:-:---::::-::-::7----,'--!-;,'-.-!.:1mo~E;!'Njirij1FI,1c~•~r~1_00'-N"..,---_-_-_-_-_-_l POTENTIAL HAZARDOUS WASTE SITE r
SITE INSPECTION REPOFIT !" 51'" 02 sme .svMBER
PART 11 · ENFORCEMENT INFORMATION
. ENFORCEMENT!NFORMATION
I ~2 D!:SCA1PTION oF FEOEFtA.L. sure LOCAL .::l!:·:.uLA.TORv1ENFORCEME~ .1.cno,..
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1. NCDEHNR State Files
A FOAM 2070-1317·811
, NC D000813952
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APPENDI:~ C I ANALYTICAL DATA
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D N.C. Dc_panrncnt of Enviroomcn~ SAMt'LE ANALYSIS REQ1UEST State uboratory of Public Health
llcallh. & Natural Rcwurcc, Q /) P.O. Box 28047, 306 N. Wilmington Street
Solid Waste Management D1vwon L£ I\ C.__.L/1 Raleigh, Nortb Carolina 27611
n -·te Number 9 4 )) 0 00 . 'l I 3 5 q '.?., Field Sample
1
Number / .!5 0 I D
.. , A ..st1w ,ru... 1... L... J
D NameofSite(gr,,-<;··)°'--· ac·,+;c:,,. -lJA({l)µ_)oud Site Location, PJ..Ua)DL(f"H'' k A,StfL,\_)g,-T[)N c..n. I b )
JID# 1 (o Date Collected 1 -9 -9 I Time /I: n 0 Collected By I I t3f , {E :.:.:, ... ---
I Agency: Hazardous Waste Solid Waste __0upufund TCLP Compounds ----
I Sample Type : .. Inorganic Compounds Results(mg/1)
Environmental Conaentrate Comments Arsenic = Bariu~ ~'t"L. t,~_~ \i ,,~ II
I _ Ground water (1) Solid (5) T !?Tf 13 L.ftN K -vnr+ Cadmium -
_ Liquid (6) Scl\A-E:-.oc.0Y \ Chromium :<.:•.··:,j
~;1..,& -_ Surface water (2) • Lead
__ Sludge (7) ('.;,,,,..,..,._;o.. -p o,c.;,£ (. = Mercury :iUi'cHtllNn SH:) iDN
I _ Soil (3) -Selenium
'" -
./ Other (4) A14 IIAQU+l Silver
Other (8) --
I --Organic Chemistry Inorganic Chemistry -
I Parameter Resulu(mg/1) Parameter Resulu(mg/1) (rag/kg) Organic Compounds Results(mg/1)
..1L_P&T:GC/MS Arsenic benzene --Acid:B/N Ext. Barium carbon tetrachloride -----MTBE Cadmium chlordane --Chloride chlorobenzcne ---Chromium chloroform ----I -_Copper o-cresol
Fluoride -m-cresol --= p-cresol -Iron -
I -Lead cresol --
-_Manganese 1,4-dichlorobenzcne --__ Mercury 1,2-dichloroethane
Nitrate -I, 1-dichlorocthylcne
I --Selenium -2,4-dinitrotoluenc -= beptachlor Silver -Radiochemistry Sulfates bexachlorobenzcne
I ---Zinc hexachlorobutadiene
Parameter Resulu (PCl/1) _· _pH -hexachloroethane
_ Gross Alpha _ Conductivity -methyl ethyl ketone -I Gross Beta TDS oitrobenzcnc ---pcntachlorophenol TOC -_ pyridine -
I Microbiology -tetrachlorocthylene -trichloroethylene
Parameter Resulu (Col/100ml) -2,4,5-trichlorophenol -_2,4,6-trichlorophenol
I --vinyl chloride ---endrin -
~/;J../919;lm , Dale Received Reported b~ £ )\J.P.' 0
lindane -methoxychlor
toxaphene
Dale Repo :;i-~1-C/ f -Dale Exlrnctcd 2,4-D -2,4,5-TP (Silvex) I yO~~p ~ Lab Number 9l 2G,~'5 -Dale Analyzed O I -DIIS 1 \I) I (Revised 2/91 ... , --.•. ~., , .. , -.
0 N.C. Depanmcnt ol Environm••~ SAMPLE ANALYSIS REQUEST State Labontory of P~blic Hcallh
lleailh, & Natural Resources P.O. Box 28047, 306 N. Wilmington Street
Solid Wai;tc Management Division (~ L f\ c_ L ft Raleigh, North Carolina 27611 n -· e Number CJ 'f J) DOQ 'B: I 3 ...59 ,3, Field Sample Nwnbcr ___ --'/_o.5"'--'O"---/_/ _____ _
.. +.-A R,2:!J D Ol:i .
D Name of Site(,-e.o Ca ·, Q, -Pll,c I t'c -.IA-µ) mruSite Location p L \'.\ rn O I l t I, 1,., h.s b ·, n (\ IDt'--C O. :.::, ) ·. == ) ,J
Collected By ./J A,:S v'E._\6 ALLE A J ID# 17 y Date Collecttod '7-/ I -q / Time /(). 4-.5
D Agency: Hazardous Waste Solid Waste ✓supe'rfund TCLP Compounds
D Sample Type
Environmental Concentrate. Comments
_Groundwater (1)
D _ Surface water (2)
_ Solid (5)
_ Liquid (6) i/0 ft/,3iy8j) P::.. 137/
I I ' o Lsoil (3)
_ Other (4)
_ Sludge (7) _______ ... if-t::.S::.tce_J""-q;o:=D,1,cf;..S
_ Other (8) ---------·
Organic Chemistry Inorganic Chemistry
Parameter ~ P&T:GC/MS
Resulu(mg/1) Parameter Resulu(mg/1) (1111g/kg)
....J<:'.'.'Acid:B/N Ext. ____ _
MTBE J:C'... "B /!J:i9() /, otwm
L :D.srrc::ow=----
Radiochemistry
Arsenic
Bariwn
Cadmium
Chloride
Chromium
__ Copper
Fluoride
Iron
Lead
__ Manganese
Mercury
--Nitrate
Selenium
Silver
Sulfates
Zinc
Parameter Resulu (PCl/1) pH
_ Gross Alpha _____ _
Gross Beta
Microbiology
Results (Col/lOOml)
__ Conductivity ----"---
TDS
TOC
Inorganic Compounds Results(mg/1)
Arsenic ,
=Barium ~~~"\;t~U\c[:1
Cadmium" -'
Chromium 1• .. •:: i
Lead
_· -Mercury SUP[P.fU~!D SECYiQll
Seleruum · ·
Silver
Organic Compounds
bcnu:ne
carbon tetrachloride
chlordane
chlorobenzcne
chloroform
o-acsol
m-cresol
--p-aesol
--aesol
1,4-dichlorobenu:ne
1,2-dichloroetbane
Resulls(mg/1)
------
------
1,1-dichloroethylene _____ _
2,4-dinitrotoluene
= heptachlor
bexachlorobcnu:nc
hexachlorobutadienc
hexachloroethane ------
methyl ethyl ketone _____ _
nitrobenzcne
--pentachlorophenol
--pyridine
tetracbloroethylene
trichloroetbylene
--2,4,5-trichlorophenol ---'----
--2,4,6-trichloropbenol _____ _
--vinyl chloride
endrin
lindane·
methoxychlor
toxaphene
2,4-D
2,4,5-TP (Silvex)
D N.C. Dcpanment al Enviroamen~ SAMPLE ANALYSIS REQUEST State uboraiory al Public Health
I lcalth. & Natural Resources P.O. Box 28047 . .306 N. Wilmington Slrcct
Solid Waste Management Drvilion c:. C,_ ~ C-: L ft Rllcigh, North Carolina 27611
I o• C Number 9 'i J) ao O a I 3 ...s''} o\ Field Sample Number /._5' {) I ;2
.. -U-A~illOO..b
DNamcofSitc{'-,-epc2:,·,o, -C(J,Ct;t;C -'B¼lmLLLSiteLocation PL\6,rnn,1,tl\ 1,.,1.sii', tl'.)iTir:,, (Io. ) . )
Collected By .J.J /1 I\ k'fg Al L f A) ID# ·7 Lf Date Collectc:d '7 -/I -q / Time / D ; .2 0
D Agency: Hazardous Waste Solid Waste ✓supcrfund TCLP Compounds --
I Sample Type Inorganic CompoundJ Rtsulls(mg/1)
Environmental Concentrate Comments Arsenic I --Barium ,·. ,,._ •.· 'L~\'1',·'"~ ·, --• ~ \~ :• \ , [I . ;. . I_, I ✓
1 _Groundwater(!) _ Solid (5) --,c E. -0 I Cadmium __ ... ""'. __ .., 1i ••••·1-·· --Chromium
__ Surface water (2) Liquid (6) voe-l&ictft?c &/---' . ' Lead --I J Mercury SUiit;\y~;8 SEb:t:~;i IV Soil (3) --_ Sludge (7) PF ..57TG~C]y-..:::., Selenium --Silver
_ 01her (4) _ Other (8) ----I ----Organic Chemistry Inorganic Chemistry --
I Paromeler Resulll(mll/1) Parameter Resulta(mll/l)(•mg/kg) Organic Compounds Ret!Jlll(mg/1) v P&T:GC/MS Arsenic benzene ----L Acid:B/N Ext. Barium carbon tetrachloride ----MTBE Cadmium chlordane <✓ Ws#/!1:/)i.-S
</'l1/0 -~-----Chloride chlorobenzcne ----I , Chromium chloroform
I ----__ Copper o-cresol
Eo~~·~ <~~o~ Fluoride --m-cresol --= p-cresol Iron J...;;, Ii <o;; --
I ~<f,QP/Jtn Lead cresol ----1,4--dichlorobenune <;;/,O f!I'"'--__ Manganese --~ <D,10~/!(>1 __ Mercury 1,2-dichloroethane
I ~ <"·'" ,(¥111 Nitrate = 1,1-dichlorocthylene --Selenium 2,4--dinitrotoluene ----heptachlor Silver --
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Radiochemistry Sulfates hexachlorobenzene ----Zinc hexachlorobutadiene
Parameter Rtsulll (PCl/1) ----hexachloroethane pH
_ Gross Alpha __ Conductivity --methyl ethyl ketone
I Gross Beta TDS --nitrobenzcne -----pentachlorophenol --TOC
__ pyridine --
I Microbiology tetrachlorocthylene ----__ trichlorocthylene
Parameter Ruulll (Col/lOOml) --2,4,5-trichlorophenol ---2,4,6-trichlorophenol I -__ vinyl chloride -endrin --lindane
,ate Received '1£~'fi!"' Reporled by --__ methoxychlor
toxaphene 8 fl-~~,
Dale Exlraclc~/-'/) f-/S'-~ s· ale Reported 2,4-D
' --2,4,5-TP (Silvcx) I ~.~~c,~~~~r,lfN~il .. r?:·;~. '~~ Number 912627 --
--
I N.C. Oepanment ol Environmea~ SAMPLE ANALYSIS REQUEST State ubontory o/1Publie Health
• I lcahh, & Nalural Rcsourcca P.O. Box 280t7, 306 N. Wilming1on Stn:cl n Solid w .. ,. M1n1gcmcn1 Division c.~ ~ c_ LIT Raleigh, Nonh Carolina 27611
.. le Number 9 4 J) Q() 0 6' 13 -5''] 2, Field Sampl,: Number /.5 0 /. 5
D . . ) . *Af\)j,JDO~ . r 1 . NameofS,1e('..,.e.pc'2:,10. -{11c1:tiC ...SfJk)mr:LtS1teLoca1100 ~L\6,ff'CJl!t \ (Ah.sli1 tJfsillt:::-(1 I), 7 ) . D Collected By .JJ l'l ,S k'E.J:6 Al LE A ) ID# :7 y Date Collected 1 -I I -q / Time /,'§ ; 'f 5
Agency: Hazardous Waste Solid Waste VSuperfund TCLP Compounds ----'
R Sample Type IDOl'l■ nlc Compouou Results(mg/1)
Environmental Concentra1t Comments Arsenic Ll{,,":1 •9,1:,,,, -11 :, --Barium :-..,,,'t~ .._ .. _:., l, ; ____ .~_;/
B __ Ground water (1) Solid (5) LlJ tel {3[2 -Q l --Cadmium --Chromium '.
ilOttLPiNtl.l ft!.&) --__ Surface water (2) Liauid (6) Lead ~u;j;:-,1.:-y"/i\ 0r-:: ' •: I -. I I I --I 11 11-0CO .. ;,,.,,~ I Mercury
Soil (3) _ Sludge (7) J°[s rJ:C'.Tf>:"? --Selenium --Silver L 01her (4}St...DDn, ,v, Other (8) --
I ----
Organic Chemistry --
I Inorganic Chemistly --
Parameter Results(mg/1) Parameter Results(mg/l)i[mg/kg) Orpalc Compounds Results(mg/1)
VP&T:GC/MS Arsenic benzene ✓ Acid:B/N Ext. ----Barium carbon tetrachloride
MTBE ----Cadmium chlordane ..L R1 <>.:.f1" l~1 -----Chloride chlorobenzcne ----.....e:::: fr: sac1:Dr5 .. Chromium chloroform I ------__ Copper o-acsol
> •lb e,i! <o, Jo ppm fluoride --m-crcsal ----p-crcsol __ UN72AAJL-< 0,40 Pf""'-Iron I I<. .-----Lead cresol __ ,hf DU, ~HtI,L</,0 Pf'M --1,4-dichlorobenzcne __ WX1tf .Q', <~.o,,,;t-__ Manganese --~ <tJ,iOp}) __ Mercury --1,2-dichloroethane
I . -r <o., '¥'.em Nitrate 1,1-dichlaroethylene ----Selenium 2,4-dinitrotaluene ----heptachlor Silver --I Radiochemistry Sulfates hcxachlorobenzenc ----Zinc hcxachlorobutadiene ----Parameter Results (PCl/1) pH hcxachloroethanc
__ Gross Alpha __ Conductivity --methyl ethyl ketone I --Gross Beta TDS nitrobenzcne -----pentachlorophenol TOC --pyridine I --Microbiology tetrachloraethylcoc ----__ trichloraethyleoe
Parameter Results (Col/lOOml) --__ 2,4,5-trichloraphenol --I __ 2,4,6-trichlorophenol : --__ vinyl chloride --endrin --lindane
Date Received l}P,9/ 5!i°1_ Reported by --methoxychlor --toxaphene :il·A P6S'f" ~ _q J --
I Dale Extracted Jl·/-'/1 ~ K"ffeate Reported 2,4-D --2,4,5-TP (Silvex) ~ 81'A C)1 ~fl''N --Dale Analvtc· ,;..f1 9-J.?A, -~ o I ah Numher . . "., l <.
g N.C. Dcpanmcnl ol em,;ronmcnt,
I lcalth, & Natural Resources
SAMPLE ANALYSIS REQUEST n Solid W■SIC M1n1gcmcn1 Division C..L ~ c_ L ft
State Labontory of Public Hcahh
P.O. Box 28047, 306 N. Wilmington Street
Ralcil,h, North Carolina 27611
.e Number 9 ':/ J) aoo 'is'I 3 . -5''] g Field Sample: Numbcr ____ :..,l, ... s'-'o~;_,J-:......._ ____ _
U . . ) +!-A~}j,JOO-? . p
Name of s,tcC,-e.o C Sb I Q, -f (l {' l ;t ( ._5 fHi) rnL u.S,te Locat,o O L \6, rn Q l ! t I\ ) )
Collected By ./J (l ~ ~'t,g ALL" A I ID# ·7 /_; Date Collected '7 -/ I -CJ /
D Agency:
'
Hazardous Waste Solid Waste VSuperfund TCLP Compounds ----
Time 15·; 5
D Sample Type -Inorganic Compound! Results(mg/1)
Environmental Concentrate Comments Arsenic -Barium ... " · g [: !'.'(.i ,. n _ Ground water (1) Solid (5) 1r' 1:;.h I -Cadmium u { }_i:J: \: ~ :1 ! ', -o :.:. _.,/ -Chromium
_ Surface water (2) _ Liquid (6) VD e-; AN e 1 (c..t, s. 1 -Lead -n _ Soii (3)
I l Mercury 0Ui ~;:t ~td Stt·:;J;., f, ..s T,(ls_:'t, £ ,S -Selenium _ Sludge (7) -Silver
/ Other (4).SfJ>rmf,0--Other (8) -
I -
I Organic Chemistry Inorganic Chemistry
' Parameter Results(mg/1) Parameter Raults(mg/l)(mg/kg) Organic Compounds Results(mg/1) v P&T:GC/MS Arsenic benzene ✓ Acid:B/N Ext. -Barium -carbon tetrachloride
MTBE -Cadmium -chlordane ✓PC.. t3.:~ --<O,lO /!12."' Chloride chlorobenzene v Pqzyn,E-5 -Chromium -chloroform I --_Copper o-aesol -C:ndc'ifL <n,/D ,..,~-Fluoride -m-cresol --p-aesol I __}, iAl~AJJt-<"0,"fOF/'M,-Iron -_rr1r: ru DX;f::,,c HLl!fc 1,0 PIM'--' Lead . cresol
_,oxe e1f£AJE-<;;)~ _Manganese -1,4-dichlorobenzcne -_Mercury 1,2-dichloroethane I ~ ': -b <O, v-'5 Nitrate -1,1-dichlorocthylenc j\(. 5 "T % ~do ,12/UH --Selenium 2,4-dinitrotoluene -= heptachlor Silver -I Radiochemistry Sulfates hexachlorobenzene ---··--Zinc hexachlorobutadiene -Parameter Results (PCl/1) _pH hexachloroethane -I _ Gross Alpha -Conductivity -methyl ethyl ketone
-Gross Beta TDS nitrobenzcne --pentachlorophenol TOC -pyridine I -Microbiology -tetrachlorocthylene
-_ trichloroethylene
I
Parameter Results (Col/lOOml) _2,4,5-trichlorophenol
-_2,4,6-trichlorophenol
vinyl chloride --endrin
I -lindane
Date Received 1, IJJ (j/ Dt1m Reported by -methoxychlor -lJM, -Ill-/1._sr(I llwf-3 Ji I -toxaphene • Dale Extracted 8-/·'1 /) ~.pip ~;§'i;P•tc Reported -2,4-D ~ s~11 -2,4,5-TP (Silvex)
Date Analy: ~-!// g-.1.l-'lft3'9_ Lab Number ____ 91.ZG~~'.l}
'
n
n
0
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I
SOLID WASTE MANAGEHENT DIVISION
SUPERFUND SECTION
Chain of Custody Record
Hazardous Waste Materials
Location of Sampling: Generator
--Treatment Facility
=Disposal Facility
CERCLA
Transporter
--Storage Facility
--Landfill
Other:---,-,,-,-~,.,,-,,--;:---------~~-~
(1 · ~ i-1-r-11./.-bu..XlD...b
1
•... • •8 , "H . n .
Company's Name =<'.'..Of i1 fr · iroc•,+'.'t c, 5Au~elephone =--~·--f!:1 tff~ r •, n• 11J'
Address PL !_ynourtt. ) Ld ~.s 1-fIJ\)('..,...-rn N ('
Collector•s Name Ulu,J-t... 0~Qp~ Telephone:
' ~ignature
Date sampled _ _,__-_,_~\_-_r~-1~\ _________ Time Sampled _______ _
Type of Process Generating Waste ------------------I Field Information: ________________________ _
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I
Field Sample No./.:5O1() /501/ f.'·--1)/ 2-1.5 (> l-3 1,501 '±
ti le
c1.ur.£;t:
title
signature title inclusive dates
Results Reported:
~ P11t.UZ ~ignature ti.tle date
Instructions: Complete all applicable information including
signatures, and submit with analysis request forms.
g
/NEUTRAL ANO ACID
EXTRACTABLES ll COlll'OONO
~-nitrosodimethvlamine
~2-ch loroethvl )ether
loroohenol
ohenol
~ ~ich lorobenzene
-"i ch lorobenzene
I -di ch 1 orobenzene
ois{2-chloroi 1 )ether
h ch loroethane
~ i troso~i -n...nr"f"Y'lv) dffli ne
n i trobenzene
i horone
2 it~henol
2.4-dimethvlohenol
~ ,{2-chloroethoxvlmethane
-dichloroohenol
I 4-trichlorobenzene
n hthalene -~ achlorobutadiene
4 hloro-<n-cresol -hexachlorocvcl~ntadiene
-trichlo=henol
ronaohthalene
acen•nhthvlene
d. thvl ohthalate
2 -dinitrotoluene
a n•nhthene
2 4-di ni troohenol
-dinitrotoluene
4 itroohenol
fluorene 1 hlo~henvlohenvlether
thvl ohthalate
4 ,-dinitro..o-cresol
f henvlamine
~ b<>nzene
N>r<Y,henvlohenvlether
hexachlorobenzene
ltachloroohenol
nanthrene
anthracene lutvl ohtha late
oranthene
STATE L.'180RATORY Of PUBLIC HEALTH DIVISION Of HEALTH SERVICES, N.C. OEPARTIIENT Of fl.Jl1AH RESOURCES
P.O. BOX 28047 -306 N. WIL"INGTON, ST., RALEIGH, N.C. 27611
ORGANIC OlE"ICAL ANALYSIS
LAB NO ,_,1_J/ -,r_ .._, 1.11~:i. 7 c.•1..1..1~29 <II,}._/-.;;_9
FIELD I 1,-,,., I I I ,o/ ..l. / <;7J /, '? I \ol'I-
TYPE { ' ri { -31 ( <.J. ' ( ..Ji
UNITS .. "' /kal • .. n/ko ,.,-f un/ko -/kn1 ~
''" ~ (,,(__. LA......, I
..
.,
~
Sw ~"-~O
/I}. 'f."tO
.-:-oJ '-"O
JO/ ao
"' -~O ., ~,.,
'-I'
/ti ,_,"O
/ti) 'l'Jl)
so1/1 • ..-n
IA/ ,,,.,
~
/ . .
\ , .. , ' \ '
ml>L
I Estimated value. H,.o/S0/1-
Actual value is known to be less than value given.
( l
.. n/j .. n/ko
· :1 • e , r. 1.1 ;; i .. _,_.,,-_ ·~ '
· . .. .
:·1 ,• t ·1 1. I i ~ : , l l,' I.; ......... ...,,. ~
~ Actual value is known to be greater than value given.
,
llaterial was analyzed for but not detected. The nunber
Not analyzed.
is the tlininun Detection Limit. m'JJL
..:. ---
Tentative identification.
On NROC List of Priority Pollutants.
•;a. D-tv.{.f.)-tOn 06 Heai..th SVtv-tce.6 T 3068-0 (4/86 Laboll.ll.to~yl
{ l
.. n/ 1 un/ko
~ .. ' ' ., ....
. ' I .. ......
H
STATE LABORATORY Of f'IJBi.lC iU:AllH
DIVISION Of HEALIH SERVICES, N.C. 0£PAIHIIENT Of fUt\AH RESOUHCES
P.O. BOX 28041 -306 N. WILNINGTOH, ST., RALEIGH, N.C. 27611
I
ORGANIC OlENICAL ANALYSIS
BASE/NEUTRAL ANO ACID LAB NO C//.?I •I Q/,J.t.,.J, :t::)/"'J ~o c./ / ~ /....::1~
EXTRACTABLES FIELD# /~I/ I \-0/~ I I l7'11::? I ri ft.I
CONPOONO TYPE I~ l r 31 ' I <i l ( . '.J i
I UNITS ---',V ua/kn -a un/ka' .. / /kn --.L.I, ~n71(a'
~vrene in/""" vC . I cA...:: /.1,._ -
' ,l)nzidine S'O ,,.
butvl benzvl ohthalate J0/'1'10 ~i\~ \i..l
nz (alanthracene
hrvsene ..
3.3--dichlorooenzidine S-fJ) _, P•
i s(2-<>thvlhexvl l ohtha late IA/ I "'"' >:iHJ
i..,i-octvl ohthalate 10/.J_:?o
benzo(bl fluoranthene ro•·· f nzolkl fluoranthene
nzo (a) nvrene
denoll 2 3-<:dlovrene
dibenzo(a hlanthracene . -,
nzo(a h i l=rvlene ' , .. I I
I niline <,o/Jl,,"1, IA--(,L., A , L,L-
1&anzoic acid
,enzvl alcohol
4-<:hloroani I ine ... ,,,
nzofuran ,Ul '=>11
thvln•nnthalene
2--<nethvl"""""I
~thvl"""""I .. ,
troani I ine . ..-01.J t..,;o
3-ni troani 1 ine
-itroaniline ·, . .
.4 5-trichloroohenol ~, I /
·~
■ mnL 11:1 -Estimated value. Ha.0/ SD/I...
K -Actual value is known to be less than value given.
( l ( I
un/ I un/ka ""/1 ··•/ka
I
-.. ., ,. " ' a . ir r. ~·11, ' ' ' .,I
. -. ' ..
~~11r111 -.;1-r.1• !fl
I-Actual value is known to be greater than value given.
-Material was analyzed far but not detected. The numer
NA -Nat analyzed.
is th•? Nin irrun Detect ion Limit.
-Tentative identification. fl -On NROC List of Priority Pollutants.
Iii. C. D-i.v-i..6-i.un o 6 Heo.Uli Svr.v-i.cu
~HS 3068-0 l4/86 Lo.boll.a.-to~y)
R
'-Laboratory No.
N. C. OEPARTIENT OF ENVIAONIEIIT, HEALi[H, & NAT~L RES<UICES
DIVISION Of LASORATalY SERVICES, EHVIRONIEHTAL SCIENCES SECTION
P .0. BOX 28041 -306 N. WlUIINGTON Si[, RALEIGI, N.C. 27611
f/,j &J,-f PI.IIGEAIILE !Xlll'aiNOS Date of Analysis
D
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I
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1r\ p r.,1 ;:.,,',~
COIIPOUNO
Dichlorodifluoranethane
Ch 1 oranethane
,(Yinvl Chloride
Brarunethane
Chloroethane
Trichlorofluoranethane
✓1-1-0ichloroethvlene
llethvlene Chloride
tert-&tvl llethvl Ether
trans-1-2-0ich loroethvlene
I•-r-··1 ether
1 1-0ichloroethane
2 2-0ichlo ne
cis-1 2-0ichloroethvlene
Chlorofonn
/BOO Bramch loranethane
✓1 1 I-Trichloroethane
1 1-0ichlor ne
✓Carbon Tetrachloride
✓Benzene
✓1 2-0ichloroethane
✓Tri ch loroethv 1 ene
1 2-0ichlo ne
Brarodichloranethane
Dibrmonethane
Toluene
1 1 2-Trichloroethane
Tetrachloroethvlene
1-3-0ichlo, ne
Oibrarochloranethane
1 2-0ibraooethane IEOBl
1 ~h 1 orohexane
,:I , 1.... -l ___ L __ .,
l
IDl£NTS:
119/l
I I
I
''""Le-
A
..J.,..,.. /I.,. .
11g/l
==-=-==-=---====!==--.,;=== _:Chlorcbenzene · 1
IEthvlbenzene ,
1.1.1 2-Tetrachloroetha= .n. ~ ~I .. ~""''·" ,,
J·>-xv 1 ene \! \~ 1-""' 1 ~-= ~ \J' ~-.-. .-...:,,
_Ji.-Xvlene
;:,...Xvlene ', 1-·· I
_Stvrene
_!!ranofonn ~"'' , _,._ IJ.JI•
I lbenzene
1. 1 2 2-Tetrachloroethane
l!ranobenzene
-2•-l'-··lbenzene
,1 2 3-Trichlo -ne
~2-Chlorotoluene
1 3 5-Trinethvlbenzene
'I-Ch lorotoluene
_tert-&tvl Benzene
?entachloroethane
1 2 4-Trinethvlbenzene
sec-&tvl Benzene
_J)-I ltoluene
1. 3-0 i ch 1 orol>enzene
tl 4-0ichlorol>enzene
_n-&tvlbenzene
1.2-0ichlorcbenzene
Jais 12-Chloroi 11 Ether
_ 1. 2-0 i bra,o-3-Ch 1 O• ne
_:1.2 4-Trichlorol>enzene
1-lexach lorobutadiene
_,1.2 3-Trichlorol>enzene
____________ _._ ____ _
llllL -llininun Detection Limit for water (EPA llethod 502.2), is 1.0 11g/l.
J -Estimated value.
K -Actual value is known to be less than value given.
L -Actual value is known to be greater than value given.
U -llater1al was analyzed for but not detected.
NA -Not analyzed.
1/ -Tentative identification.
✓ -Re~ulated voe
T -Tr1halarethane
N.C. Dept. of Environnent, Health, & Natural Resources
DEHNR 3068-0 (Rev. 1/91 Laboratory Services)
0
'-
STATE LABORAIOOY Of f'U~L!C HEAL IH
DIVISION Of HEALTH SERVICES, N.C. OEP,'.RTIIENT Of HUIIAH REICXJRCES
P.O. BOX 28041 -306 N. IIILMINGTON, Sl., RALEIGH, N.C. 21611
IJRGAHIC MMICAL AHALYSIS
II PURGEASLE CD'IPOJHDS a,-2,u,:-iq
IJ -----------+...!:..!.~...!..-.j-1.:.Ll.cl..J'-'----!--.!..>L~e!=--f---"--"'-';":-"'-t--"16._,0SI':-' '"'L:--+---:--:---t--,------,-----
LAB NO q,').l,11. Q/:7ln2f q12u ,'fi'
FIELD I ,.5011 1501;,._ J5oJ3
II ch I or~thane
bratarethane
II dichlorodifluoranelhane IJ vinvl chloride
ch loroethane
melhvlene chloride
11 lrich lorofluoranethane IJ ethene. 1 1-dichloro
ethane. 1 1--dichloro-
I 1 2-trans-dichloroethene
chlorofonn
ethane 1 2-dichloro--
I ethane, 1 1.1-lrichloro--
carbonlelrachloride
brorodichloranethane ·
prc,,ane. 1 2-dichloro--
I 1 3-lrans-dichlo,
trichloroethvlene
chlorodibrmorethane
nzene
hane, I I .2-trichloro--
.3-cis-dichlo ne
2-chloroethvl vinvl ether I bron:ifonn
ethane, 1. 1.2.2-tetrachloro-
ethene. tetrachloro-
I toluene
ch lorobenzene
elhvlbenzene
I acetone
2-bulanone
cart>ondi sulfide 12-hexanone
4-<tethvl-2~ntanone
stvrene
I vinvl acetate
xvlenes f+otal)
TYPE
UH ITS
10--b
,I,
5 --L..
,
10 -L
in'
,;
I ,o
,o
!',
( .3 l (."3 } I ,1 l { '-/l I l I \
un/ l('uo/ko uo/1 un/1 ,<.;;"/kn un/1 ""'""' un/1 un/ka ..n/1 ""/ko
I' , , ,. I J _' • 1-j •f! • i,'. \_l j. I _-.,. \1
~ •"' _\JtL.s V ! .L;.,
I-... i
. . . -' •\ . . . ·, .
'
' / . , /
I ---------+1"°,;;nsv1,11cr-,_t.+-----+----1----+-----1-----t-----
I J -Est 1mated value.
K -Aclual value is known to be less than value given.
L -Actua~ value· 1s known to be greater than value given.
ft -llaleria l was analyzed for but not detected. The nurber -Not analyzed.
-Tentative identification.
, -On NROC List of Priority Pollutants.
C -:'.i4~P/;c:, LAB <:.aNTAl'11NATION. ,1 N.C. Division of Health Services
'/ DIIS 3068-0 (4/86 Laboratory)
is th" Minin,,n Detection Limit.
D
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_SOLID WASTE MANAGEM,ENT DIVIS I~, 'EIVtU
SUPERFUND SECTION n1:.v
CERCLA'
Chain of Custody Record GCT l c l~S!
Hazardous waste Materials SUPERFUNDSECT/ON
Location of sampling: Generator Transocrter
--Storage Facility
Company's
Treatment Facility
=Disposal Facility
Other:
--Landfill
-i\ It 'R.!i:t D l
Name i;eoc~B: -R.ie'ifl e. -SAi<'<iliLLTelephone: __ _
Addressi-P--""~P--l.l.LS~-½t--,-~L~l)"---R!¥,;~:I.~1~~~t-2.~=--:I_0:::...,_~~1_~c=.2-.:-------
Collector's Name Telephone: 9 I 9 '133-e<''?D I
Date sampled ___ 1___,_-_1~\~--9,_I ________ Time Sampled ______ _
Type of Process Generating waste _________________ _
Field Information: ________________________ _
I Field sample No./6 303 ll3D4 /{,3()!5 I{, W0
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t:iitle
12 3v{fe~ inclus1etes
signature title inclusive dates
Resu1t7_yepprted:
dpf? ;;; /tZ/£
. signature q t?cft(
date
Instructions: Complete all applicable information including
signatures, and submit with analysis request forms.
I N.C. Depanmcn, o( Environmca~ SAMPLE ANALYSIS REQUEST
I lcallh, & Natural Ri:sourtcs
"Solid Was1e Manag<mcnt Oivili011 ('. .. L ,'\C.,. L fr
State l.abontcuy of PUblic Hcallh
P.0,..!!,1-llf4'UI Wf'1il'fafOn Stn:e1 nL~1iv .. ~--''"'"' 21611
'Number(j':f.J) 000 '8'13 .-5']2, FieldSampleNumber /{pJtf.&T 1 1
~ 199l
0 . . . ) +l-fl/{ljJOO~ .· . p . ~uptotllllB C:tl'·~
Name of S,tc{'-,-e.pc~, a, .(n,r i ;ti<' ..SA-y) tnrL!Stte Locatmn_ L ~rn QI l t ~ 'm»'-9'"''i~r:,,, (' 0. ) J '
ECoilected By .JJ H 6 ~'E.g Ii l L f A I ID# ·7 l,e Date Collected '7 -II -q / Ttme IQ.' '-/ 5
Agency: Hazardous Waste Solid Waste i,/supc,fund TCLP Compounds --
I Sample Type Inorganic Compounm Results(mg/1)
Environmental Concentrate Comments / Arsenic 9,· 01:: /Barium ,QQ 1--Ground water (1) Solid (.5) ,-!S tl~5 -QI ./Cadmium < a, o 8.
_r,<J D~i;,./l-ui:C.. /Chromium < (2,/ Q
__ Surface water (2) Liquid (6) zs.S 0 m1_ /uad ( D., .s.-o
IL soil (3)
/Mercury <'a,o?-Sludge (7) ~ Selenium <o.oo
/ Silver s'.'.Q, /Q --
1 1-Other (4) Other (8) --I I ----Organic Chemistry Inorganic Chemistry --
I ~ Parameter Ruults(mg/1) Parameter Raul ts (111allHmg/kg) Organic Compounm Results(mg/1)
_P&T:GC/MS V Arsenic J:2:,, benzene
LBarium --Acid:B/N Ext. ::')ds 0 carbon tetrachloride --MTBE _L' Cadmium L... 3o chlordane ----Chloride chlorobenzene ----I ✓Chromium --':Jo chloroform --
--__ Copper o-acsol --Fluoride m-cresol ----=p-acsol I --Iron
--__JLL-Cad II,.., cresol ----Manganese --1,4-dichlorobenzcne
I --✓Mercwy .L...Q-c:l --1,2-dichloroethane
--Nitrate 1,1-dichlorocthylene v Selenium --< /, l-· 2,4-dinitrotoluene '
::::Z-silver = heptachlor .,__ 3Q
I Radiochemistry Sulfates hcxachlorobenzcne ----Zinc hcxachlorobutadiene ----Parameter Results (PCl/1) hexachloroethane pH
I --_ Gross Alpha __ Conductivity methyl ethyl ketone --Gross Bela TDS nitrobcnzcne -----pentachlorqphcnol TOC --
I pyridine --Microbiology tetrachlorocthylene ----trichlorocthylenc
Results (Col/lOOml) ----2,4,5-trichlorophenol I Parameter --2,4,6-trichlorophenol ----__ vinyl chloride ---endrin --lindane
Dale Received Reported by = methoxychlor
--toxapbene
I Date Extracted Datl)R~rted 2,4-D
I' 569 JOL12~1 --2,4,5-TP (Silvex) --n .. ,_ ",....,1,~ .... 1 l '"'h Nurnhrr
D
N.C. Dcpanment ol Environm••~ SAMPLE ANALYSIS REQUEST ~~•-•11!'1\11184"11 ol Public Hcahh
I Jcahh, & Natural Resources I \lliilV~ 116ilcAvi1mington Street
id Wute Ma .. gcmcnt Divilion (1 z.. 0 C,_ L ff Raleiah, Nonb Caroli .. 21611 -'\. · uCT 1 ~ 1991
e Number 9 :f J) DO O 3'.13 -59 2, Field Sample Number $Ut~~s'ro~
11 . . ) . . #-FtR}j,.)00~ .· . p h 11 Name or S11e(.,..e.p C Sb I Q, -lac I t: C ..Sfty) mrus,te Locatton L :2:, rn O I I IA -S b ', n €:,IDG {' 0. ) )
• Collected By .1.J A '5 k'[_8) ALL F A I ID# ·1 /..e Date Collecti:d '7 -I / -9 / Time / 0: ::J. 0
Agency: __ Hazardous Waste __ Solid Waste i/'superfund TCLP Compounds
I Sample Type
Environmental Conaentrate
I-Ground water (1)
_ Surface water (2)
I _Lsoil (3)
1-Olher (4)
_ Solid (5) 11.:..C-""""'E,_-__.0'--'I'--~~~-~.,....,. ::;::i) D 1\(:,11 <..J.J'-'-I
liquid (6) ao o m t_
Sludge (7) __________ _
Other (8) __________ _
Organic Chemistry
RHult.s(mg/1) Parameter
P&T:GC/MS
-Acid:B/N Ext. ____ _
MTBE
Inorganic Chemistry
Parameter
/ Arsenic ~-
~rium
Resuluc:rg(mg/k&)
30
✓Cadmium
-Chloride
...:::::-Chromium
_Copper
Fluoride
Iron
&-a,o
7uad .J.o
_Manganese
/Mercury ""-.o _ c::,
--Nitrate
~Selenium ( /, 0 1----------------1 2Silvcr ..,_ a,o
Radiochemistry Sulfates
Zinc
pH
-Conductivity ______ _
Parameter
_ Gross Alpha _____ _
Resulu (PCl/1)
Gross Beta TDS
TOC
Microbiology
Results (Col/lOOml)
Date Received ________ Reported by ________ _
I Dale Extraclcu _____ Dal'tJt':'J310 JU[ 12 91 ,..... , • I 1 "},, 11, I,..-I,,. -
Inorganic Compounds
_LArsenic
..L. Barium
_LCadmium L Chromium
Luad
__..::::Mercury
~clenium
i/ Silver
Orpnlc Compounds
benzene
carbon tetrachloride
chlordane
chlorobenzene
chloroform
o-aesol
m-cresol
--p-cresol
-cresol
Results(mg/1)
Q.Q,~
< o. 0 8
( Q. IQ
(o. /o
Results(mg/1)
------
1,4-dichlorobenzene ---''----
1,2-dichloroethane
1,1-dichloroethylene _____ _
2,4-dinitrotoluene = heptachlor
hexachlorobenzene
hexachlorobutadiene _____ _
hexachloroethane
methyl ethyl ketone _____ _
nitrobenzene
-pentachlorophenol
-pyridine ·
tetrachloroethylene
trichloroethylene
-2,4,5-trichlorophenol _____ _
-2,4,6-trichlorophenol _____ _
--vinyl chloride
--endrin
lindane = methoxychlor
toxaphene
--2,4-D
2,4,5-TP (Silvex)
D N.C. Dcpan..,.nt of Environm••~ SAMPLE ANALYSIS REQUEST State Laboratory of Public Health
i
llcallh, & Natun.1 Re.source& P.O. Bo1 28047, 306 N. Wilmington Street
~lid Wutc Management Divi■ion (!_2:. ~-('.,. L ft R.llciib, North Carolina 27611
.. e Number 9 4 J) a O Q a I 3 ...5 '] 2, Field Sample Number tittililV t:.U
II . . ) . +t-AR,:t:IJOO~ . . p . t I G' . \j ' 100~ IJNameofS,tc{',-e.nc<e:,•Q, .{·aci±:lc ~A;µ)mrLLSttelocallon Lk'?,rnn11, \ L-1!.u-S-b(n IDt'--. (' o.
) ~ ' . I Collected By .JJ Ad~'E.g /ilLf A) JD# ·7 y Date Collected '7-I I -qSU ERfUftl~CTl')N:.</5
Agency: Hazardous Waste Solid Waste /supcrfund TCLP Compounds --
I Sample Type Inorganic Compounds .. Resulu(mg/1)
Environmental Conc:entral~ Comments ~Arsenic S::a-n1 I-Ground water (1)
-..L:Barium a, !i a
Solid (5) /...f.d rYlB b -[) I LCadmium < '2-08_
IAJ D f<.6.(M.iJ:Z5 ,/Chromium ( '2· I 0
_ Surface water (2) _ Liquid (6) a~n O'.l k ~ad ~0--'> 0 I _soil (3)
_u,Mercury Q,Q:2
Sludge (7) ?'Selenium <O-QQ_.i-
Silver (0./Q JL'.. Other ( 4)5E.h,..7l\£...rc._ Other (8) --
I ------
I Organic Chemistry Inorganic Chemistry --
Parameter Resulu(mg/1) Parameter lwullli (JJia/1) (mg/kg) Organic Compounds Ruults(mg/1)
P&T:GC/MS / Arsenic <2.,a__ benzene --Acid:B/N fut. ✓ Barium J,7 carbon tetrachloride --MTBE _u:::Cadmium .L..' '.:') chlordane ---Chloride chlorobenzcne ---I -~Chromium ~ d,C:, chloroform ---__ Copper o-aesol --Fluoride m-cresol -----p•crcsol I -Iron
--;:71.ead a,1 cresol ---__ Manganese --1,4-dichlorobenzcne
I -....t::::'.'Mercury .L..o,) --1,2-dichloroethanc
-Nitrate 1,1-dichloroethylene < l, ei --7selenium 2,4-dinitrotoluene
ilver -1...a_o --heptachlor
I Radiochemistry Sulfates hexachlorobenzene ----Zinc hexachlorobutadiene ----Parameter Resulu (PCl/1) hexachloroethane _pH --I _ Gross Alpha __ Conductivity methyl ethyl ketone ---Gross Beta TDS nitrobenzcne --= pentachlorqphenol TOC --__ pyridine I --Microbiology tetrachlorocthylene ----__ trichloroethylene
Parameter Results (Col/lOOml) --__ 2,4,5-trichlorophenol I --__ 2,4,6-trichlorophenol ---__ vinyl chloride ---endrin --lindane
Date Received Reported by = methoxychlor
__ toxaphene
I Dale Extracted Da\9f~ff~ , 11 II 12(n 2,4-D = 2,4,5-TP (Silvex)
n ' ' , t,. I., .. 1 " -
H N.C. Dcp1nmcn1 o/ Environm••~ SAMPLE ANALYSIS REQUEST Stile labontory o/ Public Heallh
llcallh, & Natural Resources P.O. Box i8EJ.\ft_l\ 'flmington Street
~lid w .... M1n11emen1 Division (:!..L ~ c~ L ~ t< I:,(.; c,~ C.rolina 27611
.. e Number Cf::{ J) 00 0 SI 3 ..59 3, Field Sample Number l[IR. p'.0.'f'.191:!1
D . , +¼-l't~)J._)QO.b . p .
Name of Sitcf1te.ocn 1 o, .{ QC J :\:11'.' --lfik > rnr LtSite Location L \6,rn Q J SIJl>Ei~fHtil0~U\ON'.)J:Or:,,, C' O.
:::.J ) ' R Collected By .LJ A rs k'E{_j ALL F 6 I ID# ·7 Le Date Collecti:d '7 -1 I -q I Time 1 ,;J .' 1 .:5
Agency: Hazardous Waste __ Solid Waste v'superfund TCLP Compounds --
I Sample Type ln.'.'.'.:nlc Compound,, Results(mg/1)
Environmental Concentrate Commenti Arsenic Q.o r 1--Ground water (!)
,7Barium o. 6 ~
Solid (5) ,u::z::i-o I ~ Cadmium ~ Q-~ d
.!.. >J u /\Ca, II-~ ~ Chromium s: 0, (Q
__ Surface water (2) _ Liquid (6). ,:J.,.£!i n m L__ ___k::'Lead ~0-.!,-c)
m _ Soil (3)
...---Mercury
¾lenium
a,a-;;i
_ Sludge (7) 0,0Q.C
Silver ~ Q. (~
I _L Other (4) otJmnlJJT Other (8)
I
Organic Chemistry Inorganic Chemistry
Parameter Re,ults(mg/1) Parameter ResullsuPl/f) (iiog/kg) Organic Compound, Re,ults(mg/1)
P&T:GC/MS v Arsenic q.g benzene --Acid:B/N Ext. ..JLBarium '.:l5 carbon tetrachloride --MTBE ~admium \tao chlordane ----Chloride chlorobenzenc
,,/Chromium --I -~,;>,o chloroform ---__ Copper o-cresol --Fluoride m•crcsol ---
I -Iron p-cresol
VLcad ~o cresol -------__ Manganese --1,4-dichlorobenzcne
-✓Mercury L..o -\ --1,2-dichloroelhane
I --Nitrate 1,1-dichloroethylene < /, ;'.) --~Selenium 2,4-dinilrotoluene
Silver -"--iz,O __ heptachlor
I Radiochemistry Sulfates hexachlorobenzene ----Zinc hexachlorobuladiene
Parameler Results (PCl/1) ----hexachloroethane pH
I _ Gross Alpha __ Conductivity = methyl ethyl kelone
-Gross Bela TDS nitrobcnzcne --= pentachlorophenol TOC --__ pyridine
I --Microbiology lelrachloroethylene = trichloroethylene --Parameter Results (Col/lOOml) __ 2,4,5-trichlorophenol
I --2,4,6-lrichloropheool ---= vinyl chloride --endrin --lindane
Dale Received Reported by __ methoxychlor
__ toxaphene
I Date Extracted Date Reported __ 2,4-D
U I 35l2 JUL 12~ I _ 2,4,5-TP (Silvcx)
Oatr, A nalvtt·rl I ah Num er -·--·-
I ,,
I ,,
I
' '
'-I
m
I
I
I
I
I DATA ANALY1:ED BY IEA
I See Volume II
ID
I
I
I
I
I
I
I ,
I
_',.
•,
.... -.
.. 'I
i::,.Liiihthou~e(CJ
,
phic Maps; Plymouth SOURCE: USGS Topogra West.,
G Light
th East N.C., C 1979; Pymou ' N •• , C 1979; WestO\ler, N.C.,1954 1954; Woodard, N. ·•
0S1ump
DRAWN
CHECKED SHEET
DATE JOB No.
,
/
' . s
\
200() ,u:
FILE No.