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UNITED STATES ENVIRONMENTAL PROTEC'TION A6ENCY mSSlQNIII
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841 Chestnut Building
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May 5, 19$7
In reply Refer to: 3HW90
CERTIFIED MAHt RETURN RECEIPT REQUESTED
DATI JIKCIIVKD
57/3^7
ENVIRONMENTAL
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W.M. Stewart Sr. Environmental Control Consultant DuPont Washington Works P.O. Boae 1217 Parkersburg, Wv 26102-1217
Re; Notice of Deficiency Verification Investigation Report
Washington Works WVD 045 87 5291
Dear Msr. Stewart;
The Vex-lflcation Jnvestigatioa, S.J. du Font de jyeznoures lE Co., Washington Works (Report), dated April 1992 has been reviewed and, although the Environmental Protection Ageaey (SPA) finds deficiencies in the Report, sufficient information i@ included to
warrant proceeding with the RCRA Facility Investigation (RFI). Therefore, a RFI work plan ia due within 90 days of receipt of this
letter.
GENERAL COMMENTS
Enclosed is a table identifying deficiencies in the Report. While the comments are written as though the Report is to be
revised, EPA is not requiring that the Report be revised. It is
considered more important to proceed with the RFI than expend resources revising the Report. However, the items (in the table) in bold do need a response. Please provide a-response within 30
days of receipt of this letter.
It is difficult to locate the precise locations of sampling
points using the Report's Figure 6. The Report contains a divider marked "Plates" but that section is empty. Please provide three copies of the plate locating the actual sampling points on the
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topographic map used in the Verification Investigation Plan, Page
4.
Permit Requirement
The Corrective Action Permit Attachment 1 required soil and groundwater analyses for inorganics, volatiles, and semivolatiles. The Verification investigation Plan, Table 18 listed the EPA Constituent List but omitted chromium. EPA's September 30, 1991
.conditional approval letter required.surficial soil sampling and
analysis at the DuPonfc Road Landfill and referred to parameters listed"in the permit, which includes chromium. DuPont modified Table 18 but added chloride instead of chromium.
In addition, ERA'S conditional approval, and DuPont's acceptance, specifically identified chromium as an analyte for the Polyacetal Product Incinerator. The Report failed to include chromium as required.
Therefore, the Report in deficient and additional sampling and analysis ifl required, see below.
Gz-oundwater
Section 7.1 discusses the use of dissolved versus total metals
when evaluating groundwater quality.
The second paragraph
incorrectly paraphrases the referenced EPA Directive submitted in
Appendix P.
The EPA Directive, upon which is based the
justification for looking at dissolved metals concentrations only,
states that, "if the historical information shows inconsistency
between the filtered and untiltered' data, and high levels of
aluminum are present in the unfiltersd data, only filtered samples
are needed." Neither historical information nor has aluminum
analyses been included in previous or present sample analysis. In
addition, the field sampling logs indicate that almost all wells
are "muddy," "thick muddy," or have "medium to high turbidity."
Evaluating groundwater quality with respect to metals when the
samples are turbid is difficult. The practice is tending to total
metals, or unfiltered samples, often using low-flow sampling techniques. Redeveloping a groundwater monitoring well and sampling with low-flow techniques can reduce total metals from above the groundwater protection standard in 40 CFR 264.94 to nondeteet levels.
Therefore, no metal may be eliminated from further consideration at this time.
Section 7.2 discusses that C-0 and TRITOM*, found in wells at the Riverbank Landf-ill, the Anaerobic Digestion Ponds, and the .Burning Grounds, are not 40 CPR Part 264, appendix IX constituents
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and PALs or MCLs assigned to them. toxicological information.
S>AL
Please provide known
The Report uses EEA proposed action levels (PALs) (July 27,
1990) for screening purposes, a more current list used by Region
III III is the Region
Risk-Based Concentrations; R.L. Smith
(4/18/96) using the residential exposure scenario for soils. The
significant difference between the Region
table and the Report
III Table 4 is arsenic. The value in Table 4 fails to consider arsenic
as a carcinogen. As reported values for arsenic in the soil exceed
the Region HI number, it may be necessary to determine a site-
specific soil arsenic background number.
Background Soil Samples
III Determination of inorganic, soil background levels becomes
important when the inorganic constituents exceed the Region Risk-Based Concentrations. Soil arsenic levels exceed the residential/industrial values for arsenic as a carcinogen of
0 .43/3.8 nig/kg. A statistically valid determination for background
levels of arsenic is needed. A one-sided tolerance levels is appropriate.
Seven samples were taken to represent background inorganic constituent conditions. Seven samples is less than the minimum number generally required (eight samples are generally necessary to calculate an upper tolerance level to represent background) but more importantly, the background samples need to be from the same soil series and horizon as the samples taken to evaluate releases
from a solid waste management unit. in addition, background soil
samples must be taken from areas unimpacted by facility operations
Enclosed is a copy of EPA's Engineering Forum Issue paper, DeterndBStiozi of Background CMceoitrations of Inorcyanica in Soils and Sediments at .Hazardous wsiste Sites, BPA/540/S-96/500, December 1995. The paper identified some of the concerns in determining inorganic soil background levels.
EVAMtBSIOH O? SSCOiamslDATIONS
Eelyaoetal Waste Incinerator The Work Plan specified soil analysis for cadmium, chromium,
lead, selenium, m-Cresol, and phenol. The Report, Table 3, fails to provide results for chromium and m-Cresol. Provide the missing
data.
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Local Landfill
DuPont's "no further investigation" recommendation may be unacceptable given that the groundwater protection standard of 40 CFR 254.94 is exceeded for arsenic, barium, and lead.
In 1995 DuPont notified EPA that the Local Landfill was being closed and one additional groundwater monitoring well was being installed, and in January 1997 DuPont notified BPA that the landfill surface impoundment is to be closed. Please provide the Local Landfill closure information and the schedule and plans regarding closure of the surface iinpoundment (a).
RiverbanJc fc.mdfill
A RCRA Facility Investigation (RFI) needs to b@ performed while maintaining the pump-and-treat for the methylene chloride spill. The statement that groundwater contamination is limited to the western and central parts of the Riverbank Landfill is
inaccurate as extreme eastern groundwater sampling point exceeded
the groundwater protection standard of 40 CfR 264.94 for arsenic and mercury. The RFI shall include the DuPont-Lubeck well field/
the Ranney water production wells, and well 336. Wells 331 through 335 and 337 shall be included in the RPI with' respect to groundwater elevations.
The Report contains insufficient data to evaluate the effectiveness of the pump-and-treat system. Although DuPont submits quarterly seepage reports, please submit a report, within
60 days of receipt of this letter, on the punrp-and-treat system
which includes a complete description of the system, a discussion
of attempts to locate the source of the spring and to reduce its .flow, a demonstration that the contaminated groundwater i intercepted, and a summary of treated seepage quality.
Anaerobic! Digestion Ponds
:
The Anaerobic Digestion Ponds ar essentially located within
the Riverbank Landfill and ahall therefore be included in the .RFI.
The Report states that DuPont has initiated a study to evaluate the
uae of electrochemical techniques for in-situ stabilization of the
C-8 contaminated soils.
Please submit a report on your
investigation to date within 30 days of receipt of this letter.
Bura-ing CiroimdB
The groundwater protection standard at 40 CFR 264.94 is exceeded for arsenic, lead, and mercury, therefore, the burning grounds shall be included in the Riverbank Landfill RPI.
Excavation for a drainage ditch in March l9$0 uncovered
hazardous waste and DuPont's April 4, 1990 letter submitted soil
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analytical soil. The
results Report,
for "excavated soil" and "Burning Ground Trench" page 22, states that "(p)ostt-excavation soil
sample analytical results . . . demonstrate that the pot-
excavation levels of contaminants were significantly lower,"
however, DuPont's March 16, 1990 letter states that all of the
hazardous waste encountered was not excavated. Therefore, soil
contaminated to the "excavated soil" level are remaining at the
Burning Ground and soil ia a medium of concern for the RPI.
SuBMITTALS
SuteLttal e>( the SPI Work Plan
of reAceccipotrdoinfgtthoispelremttitercoonrdiAtuiognusItI.1D1,.I.1,99w7,ithwihnic9h0evcearlenisdalratdeayr,a
submit to EPA and the Protection a work plan
West Virginia Department of Environmental for the RCRA Facility Investigation for the
Local Landfill. Riverbank Landfill including the Anaerobic
Digestion Ponds and Burning Orounds, and the Polyacetal Waste
Incinerator. EPA'8 portion action contains, in permit
of the RCRA permit
condition II.D.,
for corrective
provisions (or
requirements)
enclosed is a
for
cop
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y
he o
f
RFI
EP
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supp rent
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permi equire
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langu ents.
a
ge, Of
particular importance are attachment conditions D.2. and g
regarding screening risk assessment and base-line risk assessment.
Within 30 days of receipt of this letter, for by June 11, 1997, - whichever is later, submit to EPA and WVDBP information
identified above or in the enclosed table.
Within 60 days of receipt of this letter, or by July 11, 1997, whichever is later, subnu.tt to EPA and WVDEP a report on the puropand-treat system as identified above.
It is
Plan, that
strongly suggested DuPont meets with
that prior to submitting the EPA in the Regional office.
RFI Work Please
call me at 215-566-3429 to set up a meeting.
Sincere!)
"w^y/.
Mary/F. Beck Remedial Project Manager RCRA Operations Branch
enel. ee; G.S. Atwal, WVPEP
Celtbrdting IS Years of Environmental Progress
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