Document pe6v5L3Da2xQ8w6REgEn57Knd
UNITED STATES ENVIRONMENTAL PROTECTION AGENCY
Enforcement and Compliance Assurance Division
Water Compliance Branch
Clean Water Act (CWA) Inspection Report
Program: Industrial StormwaterInspection Type: Compliance Evaluation Inspection (CEI)
Permittee Name: Culpeper Wood PreserversNPDES / ICIS No.: MAR05J04L
Inspection Entry Date: November 2, 2022Inspection Exit Date: November 2, 2022
Inspection Entry Time: 8:15 AMInspection Exit Time: 11:30 AM
Facility Inspected: Culpeper Wood Preservers.Lat, Long: 42.43867 , -71.71269
840 Sterling Road, Lancaster, MA 01561NAICS / SIC Code: 2491-Wood Preserving
EPA Region 1 Representative(s): Abraham Elmir - EPA Region 1 Life Scientist / Lead Inspector, (617) 918-1583,
elmir.abraham@epa.gov
State Representative(s): None
On - site Facility Representative(s): Mike Nuzzolilo, General Manager, (978) 368-7667,
mnuzzolilo@culpeperwood.com
Responsible Official: Mike Nuzzolilo, General Manager
Name and Signature of Lead InspectorAgency / Office / Phone NumberDate
Kelly DavisEastern Research Group (ERG)12/20/2022
(703) 633-1646
Kello Daniskelly.davis@erg.com
INTRODUCTION:
On November 2, 2022, staff from U.S. Environmental Protection Agency (EPA) Region 1 and an EPA
contractor from ERG (EPA Inspection Team) conducted an industrial stormwater Compliance Evaluation
Inspection (CEI) at Culpeper Wood Preservers located at 840 Sterling Road, Lancaster, Massachusetts
(hereinafter, the Facility). On May 28, 2021, the Facility submitted a Notice of Intent (NOI) to obtain coverage
under the 2021 MSGP, MAR050000, which became effective on September 29, 2021, and expires on February
28, 2026. The Facility falls under Sector A-Timber Products, Subsector A2. As part of Subsector A2 permit
requirements, the Facility is subject to benchmark monitoring of total recoverable arsenic and copper.
Ms. Kelly Davis (ERG, Lead Inspector) presented her Clean Water Act (CWA) inspector credential to the
Facility representative, Mr. Mike Nuzzolilo, and conducted an opening conference. During the opening
conference, the Lead Inspector explained the purpose of the CEI was to assess the Facility's compliance status
with respect to EPA's 2021 Industrial Stormwater Multi - Sector General Permit (MSGP).
The weather at the time of the inspection was sunny and approximately 50 F. According to precipitation data
from the National Oceanic and Atmospheric Administration (NOAA), the closest precipitation monitoring
station in the town of Berlin received approximately 0.06 inches of rainfall the day before the inspection.
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FINDINGS AND OBSERVATIONS:
Facility Description
The Facility, owned by Culpeper Wood Preservers, is a wood treating plant that includes the treatment and
preservation of raw lumber and the storage of both untreated and treated lumber. The Facility treats
approximately 41 million board - feet of raw lumber yearly using products such as Micronized Copper (MCA),
" Ecolife ", and Alkaline Copper Quaternary.
The Facility comprises 18 acres located off Sterling Road in Lancaster, Massachusetts. The Facility is bordered
by another commercial lot to the west, Sterling Street to the north, and forested land to the east and south. The
Facility contains a treated wood staging area in the north (refer to Appendix A, Photographs 1 and 2); a
treatment plant and drip pad in the mid - west area (refer to Appendix A, Photographs 3, 4, and 7 through 11); an
office building, garage, and a kiln in the mid - east area (refer to Appendix A, Photographs 5, 6, and 12); and a
raw wood staging area in the mid - west and south areas (refer to Appendix A, Photographs 7, 10, 12 and 15).
The Facility's outdoor industrial activities included the following:
* Northern portion - outdoor staging area for treated lumber
Southern and mid - west portion - outdoor staging area for raw lumber
Facility Drainage Systems and Discharges
The Facility representative stated that the Facility has four outfalls (Outfall 001 through 004) and one catch
basin onsite.
Stormwater from the northeast area of the Facility flows to Outfall 001, located at the mid - east perimeter
(refer to Appendix A, Photograph 5).
Stormwater from the northwest area of the Facility is conveyed southwest along the west perimeter via
channelized flow in a trench. The trench connects with Outfall 003 located at the mid - south area of the
Facility (refer to Appendix A, Photographs 14 through 16 and 22). The Facility representative did not
know where Outfall 003 discharged (i.e., to a water of the U.S., to a Municipal Separate Storm Sewer
System [MS4], or elsewhere). The Facility's SWPPP (March 30, 2022) on page 3-7 states that " any
excess runoff flows into nearby outfalls, numbered 1-4, then into Goodridge Brook, and eventually to
the Nashua River. " The Facility representative stated the benchmark monitoring samples are taken
upgradient of Outfall 003 (refer to Appendix A, Photograph 14).
The SWPPP identifies another outfall, Outfall 004, that the Facility representative stated does not
receive stormwater flow (refer to Appendix A, Photograph 17). Instead of discharging through Outfall
004, stormwater infiltrates into the ground along the mid - west perimeter.
Stormwater from the south area of the Facility flows either to a catch basin located in the south area of
the Facility or to Outfall 002 located at the south perimeter (refer to Appendix A, Photographs 18
through 21). The Facility representative did not know to where the catch basin discharges. The Facility
representative stated Goodridge Brook is located south of Outfall 002, following south along a swale
created by the raised railroad tracks.
The town of Lancaster maintains a Phase II NPDES MS4 permit.
Sampling and Records
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At the time of the inspection, the EPA Inspection Team reviewed the following records provided onsite:
a. Stormwater Pollution Prevention Plan (SWPPP) dated March 30, 2019 (not signed) (refer to Appendix
B. Exhibit 1)
Monthly Facility Inspection Reports - One monthly from January 27, 2021 through October 24, 2022
b c..
Quarterly Visual Assessment Forms - first quarter 2021 through fourth quarter 2022
d. Coordination with Irwin Engineers about steps to address an AIM triggering event (September 16, 2021)
(refer to Appendix B, Exhibit 2)
e. Coordination with GZA GeoEnvironmental about redesigning the site drainage (August 18, 2022) (refer
to Appendix B, Exhibit 3)
f. A site map (refer to Appendix B, Exhibit 4)
On November 7, 2022, the EPA Inspection Team requested, and on November 22, 2022 received, the following
records from the Facility representative:
a. SWPPP dated March 30, 2022 (signed) (refer to Appendix B, Exhibit 5)
b. Annual compliance evaluation reports (May 5, 2020; May 18, 2021; April 12, 2022)
Observations
The Facility representative stated the Facility receives raw lumber via railcar at the southwest perimeter. The
EPA Inspection Team observed staged raw lumber in the south area and mid - west area of the Facility. Raw
lumber is dried in the kiln and / or chemically treated in the treatment plant inside which treatment chemicals are
stored (refer to Appendix A, Photographs 7, 10, 12, and 15). Chemically treated wood dries on a covered and
contained drip pad adjacent to the treatment plant for approximately 24 to 48 hours before it is moved to the
north concrete staging area for outside storage (refer to Appendix A, Photograph 1 through 4, 7, and 10).
Lumber is visually assessed for dryness before it is placed in the outdoor staging area. The treated lumber sits
for approximately 24 to 48 hours before it is shipped to Lowes Home Improvement facilities. The Facility
representatives stated treated wood is not hosed down.
The Facility owns approximately 17 forklifts, a front - end loader, and a bobcat. This equipment is stored
outdoors when not in use. The equipment is fueled from a 500-gallon diesel aboveground storage tank (AST).
The EPA Inspection Team observed the AST inside the treatment plant, along the south wall (refer to Appendix
A, Photographs 8 and 9). The EPA Inspection Team observed a spill kit inside the treatment plant (refer to
Appendix A, Photograph 11). The EPA Inspection Team observed that the area outside the fueling area where
vehicles pull up to the AST for fueling is graded down towards the fueling area.
Routine vehicle maintenance, including replacement of fluids and battery replacement, occurs inside the garage.
Non - routine maintenance is performed in the garage onsite by outside contractors. Batteries and used oil are
stored inside the garage and the Facility representative stated the garage does not have internal floor drains. The
Facility representative stated used oil is picked up and removed by a contractor, Safety - Kleen Systems, and oil
filters are crushed and recycled. The EPA Inspection Team observed a 250-gallon diesel AST located against
the garage's east wall and a 500-gallon diesel AST south of the kiln (refer to Appendix A, Photographs 6 and
13). The AST's were covered and within secondary containment.
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CLOSING:
At the conclusion of the inspection, the EPA Inspection Team held a closing conference with the Facility
representatives and discussed the following preliminary findings and observations of the inspection. The closing
conference began at 11:15 AM (EST) and concluded at approximately 11:30 AM (EST).
POTENTIAL NONCOMPLIANCE ITEMS:
1. Permit Part 6.2.7 states, " You must sign and date your SWPPP in accordance with Appendix A, Subsection
11. "
At the time of the inspection, the Lead Inspector identified that the onsite 2019 SWPPP had not been signed
(refer to Appendix B, Exhibit 1). The Facility emailed the 2022 SWPPP to the Lead Inspector on November
11, 2022 that was certified by Mr. Mike Nuzzolilo on April 8, 2022 (refer to Appendix B, Exhibit 5).
2. Permit Part 6.5 states, " You are required to keep the following inspection, monitoring, and certification
records with your SWPPP that together keep your records complete and up - to - date, and demonstrate your
full compliance with the conditions of this permit:
6.5.1 A copy of the NOI submitted to EPA along with any correspondence exchanged between you and
EPA specific to coverage under this permit;
6.5.2 A copy of the authorization email you receive from the EPA assigning your NPDES ID;
6.5.3 A copy of this permit (either a hard copy or an electronic copy easily available to SWPPP personnel) "
The EPA Inspection Team observed that the onsite SWPPP did not include a copy of the NOI, the
authorization email, or a copy of the permit. The 2022 SWPPP also did not include these documents.
3. Permit Part 6.2.2.3 states the permittee must, " Provide a map showing:
a. Boundaries of the property and the size of the property in acres...
c. Directions of stormwater flow (use arrows), including flows with a significant potential to cause soil
erosion...
g. Locations of potential pollutant sources identified under Part 6.2.3.2...
i. Locations of all stormwater monitoring points;
j. Locations of stormwater inlets and discharge points, with a unique identification code for each discharge
point (e.g., 001, 002), indicating if you are treating one or more discharge points as " substantially identical "
under Parts 3.2.4.5, 6.2.5.3, and 4.1.1, and an approximate outline of the areas draining to each discharge
point;
k. If applicable, municipal separate storm sewer systems (MS4s) and where your stormwater discharges to
them...
m. Locations of the following activities where such activities are exposed to precipitation:
i. fueling stations;
ii. vehicle and equipment maintenance and / or cleaning areas;
iii. loading / unloading areas;
iv. locations used for the treatment, storage, or disposal of wastes;
v. liquid storage tanks;
vi. processing and storage areas;
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vii. immediate access roads and rail lines used or traveled by carriers of raw materials, manufactured
products, waste material, or by - products used or created by the facility;
viii. transfer areas for substances in bulk;
ix. machinery "
The Lead Inspector observed that the onsite map from the 2019 SWPPP did not include the size of the
property in acres, directions of stormwater flow, or locations of potential pollutant sources such as locations
of AST tanks (refer to Appendix B, Exhibit 4). The map also did not include locations of stormwater
monitoring points and the outdoor portion of the fueling station at the treatment plant. The Facility
representative stated that the location depicted on the map of Outfall 001 was inaccurate, and that it actually
was located at the mid - east perimeter (refer to Appendix A, Photograph 5). The Facility representative also
stated that the location depicted on the map of Outfall 002 was inaccurate and that it actually was located at
the southern - most point of the Facility (refer to Appendix A, Photographs 20 and 21).
The site map provided after the inspection with the 2022 SWPPP is the same as the 2019 SWPPP map with
the exceptions that the 2022 SWPPP map does identify the size of the property in acres and the locations of
AST tanks (refer to Appendix B, Exhibit 5).
4. Permit Part 3.2.1 states, " Once each quarter for your entire permit coverage, you must collect a stormwater
sample from each discharge point... and conduct a visual assessment of each of these samples. "
The Facility's NOI certified on May 28, 2021 stated that the Facility has four outfalls (Outfalls 001, 002,
003, and 004). The Facility did not consistently conduct visual outfall assessments from second quarter of
2021 through the fourth quarter 2022 as shown in Table 1.
Table 1: Quarters When Visual Assessments Were Performed at Outfalls 001-004 from Quarter 2, 2021
Through Quarter 4, 2022
Outfall 001Outfall 002Outfall 003Outfall 004
Quarter 2, 2021MissingMissingPerformedMissing
Quarter 3, 2021MissingPerformedMissingMissing
Quarter 4, 2021MissingMissing *PerformedMissing
Quarter 1, 2022PerformedMissing *Missing *Missing
Quarter 2, 2022PerformedMissing *Missing *Missing
Quarter 3, 2022PerformedMissing *Missing *Missing
Quarter 4, 2022PerformedMissingMissingMissing
* = Visual assessments were not performed although sampling results were sent to Net - DMR.
The Facility representative stated that visual assessments were not performed during missing quarters
because they did not receive flow during that quarter, however the Facility collected and submitted
benchmark monitoring samples to Net - DMR (see Potential Noncompliance Item # 5) without completing
visual assessments seven (7) times (starred in Table 1).
5. Permit Part 5.2.2 states, " If an annual average exceeds an applicable benchmark threshold based on the
following events, the AIM [Addition Implementation Measures] requirements have been triggered for that
benchmark parameter. You must follow the corresponding AIM-level responses and deadlines described in
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Parts 5.2.3, 5.2.4, and 5.2.5 unless you qualify for an exception under Part 5.2.6. An annual average
exceedance for a parameter can occur if:
5.2.2.1 The four - quarterly annual average for a parameter exceeds the benchmark threshold, or
5.2.2.2 Fewer than four quarterly samples are collected, but a single sample or the sum of any
sample results within the sampling year exceeds the benchmark threshold by more than four times
for a parameter. This result indicates an exceedance is mathematically certain (i.e., the sum of
quarterly sample results to date is already more than four times the benchmark threshold). "
Permit Part 5.2.3.1 states, " If any modifications to or additional control measures are necessary in response
to AIM Level 1, you must implement those modifications or control measures within 14 days of receipt of
laboratory results, unless doing so within 14 days is infeasible. If doing so within 14 days is infeasible, you
must document per Part 5.3 why it is infeasible and implement such modifications within 45 days. "
The Facility reported the following benchmark exceedances of copper from July 1, 2021 to June 30, 2022 as
shown in Table 2. The Facility's arsenic levels did not exceed the benchmark concentration.
Table 2: Total Recoverable Copper Benchmark Exceedances (g / L) from Quarter 3, 2021 through Quarter
3, 2022
Four Times
LimitOutfall 001Outfall 002Outfall 003Outfall 004
Quarter Parameter
Quarter 3, 20215.1920.8N / A *Not Received Not ReceivedN / A *
Quarter 4, 20215.1920.8Not Received85.791Not Received
Quarter 1, 2022 5.19 20.8 5380 2300 2330 N / A *
Quarter 2, 2022 5.19 20.8 1430 1370 1420 N / A *
Quarter 3, 2022 5.19 20.8 3790 659 892 N / A *
N / A * = Outfall did not have measurable flow during the quarter.
All measured total recoverable copper events trigger AIM action levels because each sample exceeds four
times the parameter limit of 5.19 g / L such that an exceedance of the benchmark is mathematically certain
for four quarters of sampling. The Facility representative stated that to address copper exceedances, the
Facility has multiple plans, including coordinating with both Irwin Engineer and GZA GeoEnvironmental,
Inc. on site redesign projects (refer to Appendix B, Exhibits 2 and 3).
The Facility is planning to repave the site with asphalt. The Facility representative stated that the
surface of the Facility is contaminated with arsenic and copper due to the Facility's previous use of
treatment materials that contained those elements (before the current permit term). The Facility
representative stated the asphalt would cap the chemicals and prevent their contaminating
stormwater runoff. The Facility representative estimated that the project will be complete in the
spring of 2023.
The Facility contracted GZA GeoEnvironmental, Inc. to redesign Facility stormwater drainage
towards treatment methods before reaching Outfalls 001, 002, and 003. This includes performing
maintenance on the stormwater trench along the west perimeter of the Facility to direct channelized
flow towards rip rap before reaching Outfall 003. The Facility representative stated the area that
drains to Outfall 002 is also being redesigned, but that plans had not been finalized. The Facility
representative stated that designs were not finalized but that construction would start approximately
in 2023.
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* The Facility contracted Irwin Engineers to perform an evaluation of the Facility's current outfall
conditions and associated control measures. Irwin Engineers also plans to take samples from the
outfalls and Goodridge Brook and review options to achieve AIM compliance.
The Facility's 2021 Annual Report stated the Facility was in AIM Level 2 (refer to Appendix B, Exhibit 6).
The Annual Report also stated the Facility would install filter units near Outfall 003, regrade the area to
prevent stormwater flow from bypassing the structural control, and begin construction by spring 2022. At
the time of the inspection, the Facility had not begun any of the planned actions.
6. Permit Part 7.3.4 states, "... for any of your monitored discharge points that did not have a discharge within
the reporting period, using Net - DMR, you must report that no discharges occurred for that discharge point
no later than 30 days after the end of the reporting period. "
The Facility did not submit sample results for Outfall 002 and Outfall 003 during the third quarter of 2021
and Outfall 001 and Outfall 004 during the fourth quarter of 2021. The Facility failed to state if the outfalls
did not receive measurable flow.
7. Permit Part 2.1.2.8.b states, " Personnel must be trained in at least the following if related to the scope of
their job duties (e.g., only personnel responsible for conducting inspections need to understand how to
conduct inspections):
i. An overview of what is in the SWPPP;
ii. Spill response procedures, good housekeeping, maintenance requirements, and material management
practices;
iii. The location of all the controls required by this permit, and how they are to be maintained;
iv. The proper procedures to follow with respect to the permit's pollution prevention requirements; and
v. When and how to conduct inspections, record applicable findings, and take corrective actions; and
vi. The facility's emergency procedures, if applicable per Part 2.1.1.8. "
Page 2-6 of the Facility's SWPPP (both the onsite 2019 SWPPP and the 2022 SWPPP) states, " Employees
at the Culpeper facility are trained in the following areas, at least once per year:
Preventative measures, including spill prevention and responses, facility inspections and
preventative maintenance. (All personnel)
The facility's SWPPP. (Conner Burke, Mike Nuzzolilo and Mark Plouffe)
Features and operations of the facility that are designed to minimize discharges of Section 313 water
priority chemicals, particularly spill prevention procedures. (All personnel)
Annual Hazardous Waste Training. (All personnel) "
The Facility representative stated that regular stormwater training is not performed, although he leads
quarterly trainings that cover general safety and pollution prevention. The attendance of the training is not
tracked, and the topics do not cover stormwater - related material.
AREAS OF CONCERN:
The Facility representative stated benchmark monitoring samples are taken upgradient of Outfall 003
(refer to Appendix A, Photograph 14). Rip rap, sediment, and leaves are located in between the
sampling location and Outfall 003.
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The Facility representative stated stormwater from the south area of the Facility flows either to a
catch basin located in the south area of the Facility or to Outfall 002 located at the south perimeter
(refer to Appendix A, Photographs 18 through 21). The Facility representative did not know where
the catch basin discharged.
ATTACHMENTS:
Appendix A-Photograph Log
Appendix B-Exhibit Log
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CEI Report Appendix A, Photograph Log
Appendix A
Photograph Log
Inspection Date: November 2, 2022
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CEI Report - Appendix A, Photograph Log
Treated Lumber
Photograph 1.
stored.
View, facing west, of the north staging area where treated lumber is
Treated Lumber
11.02.2022 09:13
Photograph 2. View, facing north, of treated lumber in the Facility's north staging area.
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Drip Pad
Concrete Berm
2022 09:47
Photograph 3. View, facing southwest, of the drip pad on the north side of the treatment
plant where treated lumber dries before it is moved to the north staging area. The drip pad
is contained by concrete berms and is slanted inward towards floor drains.
11.02 2022 09:50
Photograph 4.
View, facing west, of the drip pad on the east side of the treatment plant,
circled in red, where treated lumber dries before it is moved in the north staging area.
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CEI Report Appendix A, Photograph Log
Outfall 001
Direction of
Stormwater Flow
Photograph 5.
View, facing north, of Outfall 001. The EPA Inspection Team did not
observe flow from Outfall 001 at the time of the inspection.
11 0202 09:53
Photograph 6.
View, facing west, of a 250-gallon diesel aboveground storage tank
(AST). The tank was contained under a roof and within secondary containment.
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CEI Report - Appendix A, Photograph Log
Raw Lumber
Concrete Berm9: 55
Photograph 7.
View, facing northwest, of a raw lumber staging area. A concrete berm
separates the drip pad and the raw lumber staging area.
11.02.2022 09:57
Photograph 8.
View of a 500-gallon diesel AST inside the treatment plant's fueling
location adjacent to the Facility's south wall. This AST was under cover and within
secondary containment.
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CEI Report Appendix A, Photograph Log
11.02
Photograph 9.
View, facing northeast, of the vehicle fueling area at the treatment plant's
south wall. The Facility representative stated vehicles back up to the garage door where
they are fueled from the AST shown in Photograph 8.
11.02.2022 09: 5
Photograph 10. View, facing northwest, of the drip pad outside the southwest corner of the
treatment plant. Raw lumber is stored on the drip pad but not under the roof.
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CEI Report Appendix A, Photograph Log
28
Spill
Ki
11.02.2022 / 09: 59
Photograph 11. View of a spill kit inside the treatment plant.
11.02.2022 10.307
Photograph 12. View, facing south, of the paved south staging area. Raw wood was stored
in the south area. The pavement was wet from stormwater.
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CEI Report Appendix A, Photograph Log
02.2022 10 02
Photograph 13. View, facing east, of a 500-gallon diesel AST south of the kiln. This AST
was stored under cover and within secondary containment.
Outfall 003
Direction of
Stormwater Flow
Location of
Monitoring Sample
02 2022-40-04
Photograph 14. View, facing south, upgradient of Outfall 003. The Facility representative
stated stormwater flows from the point where the image was taken to the outfall. The
Facility representative stated they take samples upgradient of Outfall 003.
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CEI Report - Appendix A, Photograph Log
11.02.2022 10.04
Photograph 15. View, facing north, of the drainage area to Outfall 003.
Direction of
Stormwater Flow
Outfall 003
11.02.2022 10: 09-
Photograph 16. View, facing northeast, of concrete outlet structure at Outfall 003. The
EPA Inspection Team did not observe flow to Outfall 003 at the time of the inspection.
The Facility representative did not know where the outfall discharged.
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CEI Report Appendix A, Photograph Log
Outfall 004
02.2022 103
Photograph 17. View, facing east, of Outfall 004. The EPA Inspection Team did not
observe flow from the outfall at the time of the inspection.
Direction of
Stormwater Flow
Catch Basin
Photograph 18. View, facing east, of a catch basin in the south area of the Facility. The
Facility representative was not aware where the catch basin discharged.
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CEI Report Appendix A, Photograph Log
11.02.2022 1: 20
Photograph 19. View inside the catch basin shown in Photograph 20.
Outfall 002
Direction of
Stormwater Flow
11.02.2022 10: 2
Photograph 20. View, facing south, of Outfall 002. The EPA Inspection Team did not
observe flow at the outfall at the time of the inspection.
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CEI Report Appendix A, Photograph Log
02.2022 10:23
Photograph 21. View, facing north, of Outfall 002.
Sediment
Direction of
Stormwater Flow
1022 10:34
Photograph 22. View, facing northwest, of the trench along the west perimeter. The
Facility representative stated stormwater flows along the trench to Outfall 003. The EPA
Inspection Team observed sediment in the trench.
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Attachment B
Exhibit Log
ED_019088A_00012854-00021
Exhibit 1
Onsite Stormwater Pollution Prevention Plan
(SWPPP) - March 30, 2019
ED_019088A_00012854-00022
STORMWATER POLLUTION
CULPEPER OF NEW ENGLAND, LLC
PS. RLANECASVTERE, MNASSTACHIUSEOTTSN
PLAN09:20
SECTION II PLANNING, ORGANIZATION AND CERTIFICATION
SWPPP CERTIFICATION
Name:Mr. Mike Nuzzolilo
Title:Operations Manager / S. Lancaster Facility
Wood Preserving Facility Name:Culpeper of New England, LLC
840 Sterling Road
S. Lancaster, Massachusetts
" I certify under penalty of law that this document and all attachments were prepared under
my direction or supervision in accordance with a system designed to ensure that qualified
personnel properly gather and evaluate the information submitted. Based on my inquiry of
the person or personsw hwoh omathnea gsey
stem, or those persons directly responsible for
gathering the information, the information submitted, is, to the best of my knowledge and
belief, true, accurate, and complete. I am aware that there are significant penalties for
false Infor
submitting false information, including the possibility of fine and imprisonment for knowing
violations. "
Signature:
Title:Operations Manager / S. Lancaster Facility
Date:
11.02.2022
McPherson Design Group, p.c.
2-4
ED_019088A_00012854-00023
Exhibit 2
Coordination with Irwin Engineers - September 16,
2021
ED_019088A_00012854-00024
33 West Central Street
IRWIN EngineersNatick MA 01760-4503
Phone (508) 653 8007ENVIRONMENTAL
Fax (508) 653 8194CHEMICAL &
September 16, 2021
Mr. Mike Nuzzolilo
Culpeper Wood Preservers
840 Sterling Road
Lancaster, MA 01561
11-02-2022-09-10
Re MSGP Additional ImplementationMeasures for Copper in Stormwater
Dear Mr. Nuzzolilo:
(Irwin Engineers) is pleased to submit this
response to your request, Irwin Engineers, Inc.services in connection with
InCulpeper Wood Preservers (Client) for professional(the Site or Facility).
pernvoiproosnamlen ttaol amatt t8e4r0s
Sterling Road in Lancaster, Massachusetts
SITE BACKGROUND INFORMATION
conducts pressure treating for
Culpeper Wood Preservers'facility in Lancaster, Massachusetts 2021 Multi - Sector General Permit
constructionlumber. The Facility is covered under EPA's
(MSGP) for industrial stormwater discharge.
samples from Outfalls 002 and 003
As required by the permit the Facility collected stormwater copper were each more than 4 times the
for the third quarter of 2021 and the sampling results for the benchmark is mathematically
applicable MSGP benchmarks, such that an exceedance of requirement to conduct Additional
for four quarters of sampling. This result triggers the We understand that the Facility
cIemrptlaeimnenMetaastuiroens t(oAI Mc)o lLleevcetl 1s afmoprl etsh ofser otmw oO uotuftafallllss .00a1n
d 004, but based on
is awaiting a qualifying dischargein these outfalls are expected to trigger
historical sampling results the copper concentrations are required to review the selection,
AIM Level I as well. Facilities subject to AIM Level 1measures to evaluate whether
design, installation, and implementation of stormwater control that would be reasonably
modifications are necessary, and implement additional measures. We understand that the
expected to reduce the copper concentration below the benchmark and is also considering particle
Facility has arranged for maintenance to be done on Outfall 003copper is present in a
filtration for the storm drain that discharges to Outfall 002. Whether the copper that would
rsuesqpuenidrede faornm tahlattewronuladt bee camoennatbrloe lt os ptarrtaitceleg yfi,l thraatsi
on, or as solublenot yet been established by testing.
353-22 P01 Culpeper stormwater copper AIM
ED_019088A_00012854-00025
Culpeper Wood Preservers
September 16, 2021
Page 209:10
You have also asked whether the Facility may be eligible for one of the exceptions from AIM
that are available under the MSGP. As part of this scope of work we propose to conduct
sampling at the Facility during a storm event to prepare an initial evaluation of the Facility's
potential for eligibility under one or more of the following exceptions:
Benchmark exceedance that does not result in an exceedance of water quality standards
in the receiving water (Goodridge Brook).
Benchmark exceedance for copper that does not result in the receiving water in - stream
copper concentrations above a facility - specific threshold value derived using EPA's
Biotic Ligand Model,
Benchmark exceedance attributable to run - on from a neighboring source. The Facility is
located across the street from a wire and cable manufacturer and stormwater from that11.02.2022
plant has reportedly been observed discharging to the Facility.
Once a compliance option for AIM is selected the Facility's Stormwater Pollution Prevention
Plan (SWPPP) will need to be updated to reflect changes that are implemented at the Site.
Updates to the Facility's SWPPP will be proposed separately. We understand that the Facility
undertook a construction project in August 2021 to expand its lumber storage yard behind the
office building on the east side of the Site, and we anticipate incorporating that change into the
SWPPP concurrently with the AIM implementation.
SCOPE OF SERVICES
Task 1Site Visit
IRWIN will visit the Site to observe the expanded lumber storage yard area, current conditions of
each outfall and associated control measures, and access for upstream and downstream locations
on Goodridge Brook for later sample collection. We anticipate that the Site visit will take up to
two hours.
Task 2Stormwater and Receiving Water Sampling
IRWIN will visit the Facility during a storm event to collect grab samples from Outfalls 001,
002, 003, and 004. Assuming access is available without trespass, we will also collect grab
samples from Goodridge Brook upstream and downstream of the Facility. Sample temperature
and pH will be measured in the field and samples will be submitted for laboratory analysis for
total and dissolved copper, total and dissolved organic carbon, calcium, magnesium, sodium,
potassium, sulfate, chloride, alkalinity, and hardness. If run - on flow is observed from the
property across the street a sample of the run - on will be collected for total and dissolved copper
analysis.
ICHREMWICIAL N& ENEVInROgNMiENnTAe
ers353-22 P01 Culpeper stormwater copper AIM
ED_019088A_00012854-00026
10
:
CSeptuembler 1p6, e202p1
er Wood Preservers02
Page 3:
Task 3
Advice on AIM ComplianceOptions
IRWIN will prepare a memo summarizing the results of the sampling
ofpotliloonwsi nfgor:
Addition ImplementationMeasures compliance. We anticipate discussing theand reviewing possible
11.02.2022
Comparison of the concentrations of total and dissolved copper rienmwohevtahelr foufrt hderi sacstoiolnv meady bceo npepedeerd .f
orstormwater, and
Comparison of the upstream and downstream copper concentrations in GoodridgeBrook
to EPA's water quality standards, and whether full - storm compositesampling is
suggested to attempt to demonstrate an AIM exception.
Results of EPA's Biotic Ligand Model for samples collected from GoodridgeBrook, and
wexhceetphteiro nf.u
rther seasonal sampling is suggested to attemptto demonstrate an AIM
Whether run - on from the adjacent wire and cable manufacturer appears to bemaking a
msetaosrumrwaabtleer .c
ontribution to the amount of copper being dischargedin the Facility's
COST AND SCHEDULE
Irwin Engineers proposes to complete the Scope of Services for a lump sum fee of $ 8,000.
Pwroorgkr.e
ss invoices will be issued based upon our estimate of the percentage completion of the
Should additional work be required beyond the current Scope of Services, we will contact you to
discuss the change. Subsequent to your approval we may adjust the total lump sum or we will
bill you for additional labor at the hourly rates indicated on the attached billing schedule.
Irwin Engineers is prepared to initiate work upon receipt of a signed agreement. The Site visit
will be scheduled for a mutually convenient date within two weeks followingauthorization.
Sfrtoomr mewaacthe ro fs tahmep lfionugr woiultfla lbles .s
cheduled at a time when a stormwaterdischarge is likely to occur
The estimated budgets and schedules contained in this proposal are based upon
st igno ed a ccepc tanch e wia thinn thig rtye (30. ) da ys. m Aftea r thy at t imeb , bue dget s ans d scu hedub les j ante icipc atiot n of
a
this proposal. If you choose to accept thisPlease do not hesitate to call should you have any questionsor require clarification on any part of
authorized individualsign below and return a copy to us.proposal and initiate our services, please have an
IRWIN Engineers
CHEMICAL & ENVIRONMENTAL353-22 P01 Culpeper stormwatercopper AIM
ED_019088A_00012854-00027
Exhibit 3
Coordination with GSA GeoEnvironmental - - August
18, 2022
ED_019088A_00012854-00028
www
waz 091
Thorsday, August 18, 2027 2:13 PM
biectevisit to review Stormwater discharges
you don't often get email or.comLearn why this is important
XTERNAL TVS email originated from outside of the organization. Do not click links or open attachments unless you
men sender and know the content is safe!!!
en
I was great to get to meet you by phone call last week and learn a little more about your facility. Thanks so much for
ending over the site drainage figure and other plans last week. I was wondering if it would be possible for me to meet
Stormwater sampling, discharge, or permitting. This would help Brian and I get a better handle on the situation and
determine the best next steps to address your concern. I had a last minute change to my week and am available
tomorrow, or else I could swing by Monday, Wednesday, or Friday of next week. I believe you mentioned last week that
you work an early shift, and I am an early riser... so I can be there at whatever time works best for you.
Thanks
Mel
MSyeeolnuii soasrta PKtrehomeje ercfgtae cnM
ialniatgye rt
o take a quick tour and review any other data or plans you may have at the facility related to11.02.2022
QIAI 243 verven Wenue | Norwood, MA 02062
80.2785312 02-323-6517 | Melissa Kenerson@gza.com www.g2a.com
KATENKINS MONTAL) ECOLOGICAL WATER CONSTRUCTION MANAGEMENT
Kawn (wVxZA KAMU can trust.
Cass elec Dianetended to be viewed only by the individual or entity to which it is addressed and may
za eneghdental information intended for the exclusive, we of the addrensretty. If you are
please be aware thatdisclosure, printing, copying distribution or use of this
(you have received this message in error, please notify the sender immediately and
MAN Kerer ved at mascheras from var
Para posegomez Kanan Mut 6A Catharkonamento, M. bed in servers, please visit our website at wwAM SEO COM
rsage is reader to the red oate by the individuds or entity to which it is addressed and may
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JA SAMME tezav 13 4oz Bekarekete), lac zad to DVIERS, POSSE vist our weesite of www.X91m
ED_019088A_00012854-00029
Exhibit 4
Site Map
ED_019088A_00012854-00030
STERLING
ROAD
U UNTREATED WOOD
112 TREATING
OUTFALS RES
STORAGE ARA
CHAT & GRAVEL
QUIPAL HA
08:42
11.02.2022
OUTFALL
OUTFALL NO. 003
ROAD
TRACK
DISMICAL SYSTEM
DAVE FIELD
STORM DRUM
STORAGE BALDO
+
OUTFALL HO. 503
OUTFALL HO. 001
ED_019088A_00012854-00031
Exhibit 5
SWPPP - - March 30, 2022
ED_019088A_00012854-00032
MCPHERSON
DESIGN
PLLC
108 BRITTANY LANE
SUFFOLK, VA 23435
(757) 630-2881
WWW.MCPHERSONDESIONPLLC.COM
STORMWATER POLLUTION PREVENTION PLAN
(SWPPP)
for
CULPEPER OF NEW ENGLAND, LLC
WOOD TREATING PLANT
SOUTH LANCASTER, MASSACHUSETTS
OF
MASSA
COMMORWESMNTCT PRNRoHUO.ECL R4ATS8NU4OD3R N0E A
.HL
U
SETTS
GISTERED
PROFESSIONAL ENGINEER
SUBMITTED TO:
Culpeper of New England, LLC
840 Sterling Road
South Lancaster, Massachusetts 01561
March 30, 2022
ED_019088A_00012854-00033
MCPHERSON DESIGN, PLLC
Structural Engineers
Wood Treating Industry Consultants
March 30, 2022
Mr. Mike Nuzzolilo
Culpeper of New England, LLC
840 Sterling Road
Lancaster, Massachusetts 01523
RE:Stormwater Pollution Prevention Plan (SVVPPP)
for Culpeper Facility at 840 Sterling Road
S. Lancaster, Massachusetts
Dear Mike,
McPherson Design is pleased to provide the SWPPP document for your use and records. Enclosed is one (1) copy of this
document. Please note that a copy of this document must be kept at the site and must be readily available should an EPA
or State inspector visit the site.
As you are aware, the SWPPP document requires that certain amounts of recordkeeping be maintained by Culpeper that
will become a part of the SWPPP document. Although the recordkeeping required by the SWPPP document in conjunction
with the recordkeeping required by the drip pad is a large amount of work, we implore you to keep good records of all
required documents so that your facility will be considered to be in total compliance with EPA and State regulations.
We have enjoyed working with Culpeper on this project. If there are any questions concerning the report or other facets
of our involvement, please advise.
Sincerely,
MCPHERSON DESIGN
R &E. MahersonOF
Roland E. McPherson, P.E.ROLAND E.
COMMORS MTCRNPoUH.CE 4RT6SU4O3RN0A
CLH
USETTS
PROFESSIONAL STEVEER
'
1
MDPLLC
757-630-2861
MCPHERSON
108 BRITTANY LANE, SUFFOLK, VA 23435
DESIGN mdpllcrem@outlook.com
PLLC. www.mcphersondesignpllc.com
ED_019088A_00012854-00034
STORMWATER POLLUTION
PREVENTION PLAN
CULPEPER OF NEW ENGLAND, LLC
S. LANCASTER, MASSACHUSETTS
2
TABLE OF CONTENTS
SECTION I: INTRODUCTION
INTRODUCTION AND PURPOSE..................... 1-1
ACTIVITIES AT THE FACILITY AND BACKGROUND INFO...1-2
SECTION II: PLANNING, ORGANIZATION AND CERTIFICATION
POLLUTION PREVENTION PERSONNEL........ 2-1
POLLUTION PREVENTION COMMITTEE MEMBERS.....2-2
SWPPP CERTIFICATION.2-3
SPECIAL REQUIREMENTS.2-5
SECTION III: POTENTIAL POLLUTANT SOURCES
POTENTIAL POLLUTANT SOURCES..3-1
BULK CHEMICAL AND FUEL STORAGE OR TRANSFER AREAS.***********... 3-2
RETORT, DRIP PAD AND RAMP ACCESS AREAS..3-3
FINISHED PRODUCT STORAGE / DRYING AREAS......3-5
VEHICLE AND EQUIPMENT FUELING AREAS....3-6
VEHICLE AND EQUIPMENT MAINTENANCE AREAS.. 3-7
ON-SITE SEWAGE DISPOSAL SYSTEM....... ... 3-7
RECEIVING WATERS
SECTION IV: FACILITY DATA COLLECTION
INTRODUCTION OF COLLECTED DATA.
SITE MAP WITH TOPOGRAPHIC INFORMATION.4-1
TOPOGRAPHIC MAP4-2
DESCRIPTION OF SIGNIFICANT MATERIAL HANDLING4-2
POLLUTANT LIST.4-9
WOOD PRESERVING FACILITY SIZE4-10
SIGNIFICANT SPILLS OR LEAKS.EYYYYY _________4-10
OUTFALL MAINTENANCE AND SAMPLING REQUIREMENTS4-11
SUMMARY OF SAMPLING DATA.........***********************................ 4-15
SECTION V: STORMWATER MANAGEMENT CONTROLS
INTRODUCTION.5-1
THE NON-POINT SOURCE POLLUTION PROCESS5-1
PREVENTATIVE MAINTENANCE.5-2
DRAINAGE SYSTEM.5-4
PAVED AREAS ..5-5
DRIP PAD5-6
CLEANING FACILITIES AND EQUIPMENT. EMPTYYYYYYYYYYYYYYYYYYYYYY5-7
MATERIALS STORAGE AREAS**** 5-7
FUEL / CHEMICAL TRANSFER PIPELINES.5-8
MATERIAL TRANSFER, LOADING AND UNLOADING.................. 5-8.
MAINTENANCE AND INSPECTION OF WOOD
TREATING EQUIPMENT5-9
GOOD HOUSEKEEPING...........
WRITTEN PROTOCOL.............5-10
McPherson Design
1
ED_019088A_00012854-00035
STORMWATER POLLUTION
PREVENTION PLAN
CULPEPER OF NEW ENGLAND, LLC
S. LANCASTER, MASSACHUSETTS
TABLE OF CONTENTS
EMPLOYEE INVOLVEMENT..5-11
SPILL CONTROL AND COUNTERMEASURES ...... ******...... 5-12
STORMWATER MANAGEMENT PRACTICES..............5-13
EMPLOYEE TRAINING
ENDANGERED SPECIES OR CRITICAL HABITAT PROTECTION...5-14
NATIONAL HISTORIC PRESERVATION ACT..5-15
SECTION VI: NON-STORMWATER DISCHARGES
CERTIFICATION..6-1
NON-STORMWATER CERTIFICATION......
SECTION VII: COMPREHENSIVE SITE COMPLIANCE EVALUATION
INSPECTIONS...................7-1
SITE COMPLIANCE EVALUATION FORM REPORT
SECTION VIII: SUMMARY OF RECOMMENDATIONS FOR SWPPP
COMPLIANCE
RECOMMENDATIONS..._ 8-1
SECTION IX: ENGINEERS CERTIFICATION
ENGINEERS CERTIFICATION... 9-1
APPENDIX A: MAPS
LOCATION MAP........... A-1
SITE MAP.....A-2
APPENDIX B: SAMPLE TABLES AND FORMS
B-1 POLLUTANT LIST..B-1
B-2 HISTORY OF PAST SPILLS............................ B-2
B-3 SAMPLING EVENT RECORDS. . ........ B-3
B-4 MAINTENANCE AND INSPECTION..B-4
B-5 DRAINAGE SYSTEM MAINTENANCE AND INSPECTION..B-5
B-6 EMPLOYEE TRAINING SCHEDULE.... B-6
APPENDIX C: PHOTOGRAPHS
McPherson Design
2
ED_019088A_00012854-00036
INTRODUCTION
ED_019088A_00012854-00037
STORMWATER POLLUTION
PREVENTION PLAN
CULPEPER OF NEW ENGLAND, LLC
S. LANCASTER, MASSACHUSETTS
SECTION I
INTRODUCTION
INTRODUCTION AND PURPOSE
The Environmental Protection Agency (EPA) promulgated stormwater regulations on November 16, 1990.
These regulations set forth National Pollutant Discharge Elimination System (NPDES) permit application
requirements for stormwater discharges associated with specific industrial activities and stormwater
discharges from specific municipal separate storm sewer systems. The regulations presented three permit
application options for stormwater discharges associated with industrial activity. The first option was to
submit an individual application. The second was to become a participant in a group application, and the
third, was to file a notice of intent (NOI) to be covered under a general permit in accordance with the
requirements of an issued general permit. All wood preserving facilities, regardless of size, must comply
with these regulations. Culpeper submitted for a multi - sector general permit and initially obtained coverage
under this permit on June 4, 2015. The multi - sector general permit has been extended to cover March 1,
2021 through February 28, 2026 by way of submitting a Notice of Intent (NOI) on May 28, 2021.
" The Stormwater Pollution Prevention Plan (SWPPP) is considered, by EPA, to be the most important
requirement of the NPDES permit ", as stated in the press briefing of September 3, 1992, as follows: " A
SWPPP shall be developed for each facility covered by this multi - sector general permit. SWPPPs shall be
prepared in accordance with good engineering practices. The Plan shall identify potential sources of
pollution which may reasonably be expected to affect the quality of stormwater discharges associated with
industrial activity from the facility. In addition, the Plan shall describe and ensure the implementation of
practices which are to be used to reduce the pollutants in stormwater discharges associated with industrial
activity at the facility and to assure compliance with the terms and conditions of this permit. Facilities must
implement the provisions of the SWPPP required under this part as a condition of this permit. "
Furthermore, the SWPPP must emphasize stormwater Best Management Practices (BMPs) and be designed
to comply with Best Available Technology Economically Achievable (BAT) and Best Conventional Pollutant
Control Technology (BCT). The SWPPP has two major objectives: (1) to identify the source of pollutants
that affect the quality of the industrial stormwater discharge; and (2) to describe practices which may be
implemented to reduce the pollutants in the industrial stormwater discharge. The SWPPP is a requirement
McPherson Design
1-1
ED_019088A_00012854-00038
STORMWATER POLLUTION
PREVENTION PLAN
CULPEPER OF NEW ENGLAND, LLC
S. LANCASTER, MASSACHUSETTS
SECTION I
INTRODUCTION
of the industrial stormwater discharge permit, whether the latter was obtained as an individual permit,
under group auspices, or by way of the NOI path.
ACTIVITIES AT THE FACILITY AND BACKGROUND INFO
BACKGROUND INFORMATION
The drip pad was constructed on this site of approximately eighteen (18) acres in 1989. Various treating
chemicals have been used to treat wood since that time. From 1989 to 2003, lumber was treated with
Chromated Copper Arsenate (CCA). The EPA declared in March 2003 that wood treated with CCA could
not be used for residential purposes after December 30, 2003; therefore, Culpeper switched from CCA to
Alkaline Copper Quaternary (ACQ). In 2006, Culpeper switched from ACQ to using Copper Azole (CAC).
In 2011, Culpeper changed from CAC to using Micronized Copper (MCA), " Ecolife " and ACQ. Between
2012 and 2017, they used Copper Azole Type C Plus (CAC Plus). In 2018, Culpeper switched from using
CAC Plus back to using MCA, along with continuing to use " Ecolife " and ACQ. It is our understanding that
the facility did not go through " partial closure " of the drip pad so all materials that come into contact with
the drip pad must be handled in accordance with Subpart W requirements and F035 waste.
The activities at the site include bringing in untreated lumber (white lumber) by railway and storing it on site
until the white lumber is ready for treatment. The white lumber is then pushed into a pressure vessel
(retort or cylinder) and the treating chemicals are added and then pressurized. After this is complete, the
treated lumber is removed from the cylinder and allowed to stay on the drip pad until all drippage ceases.
The treated lumber is then stored on site or in a building until it is ready to be shipped out, via tractor
trailer trucks.
McPherson Design
1-2
ED_019088A_00012854-00039
STORMWATER POLLUTION
PREVENTION PLAN
CULPEPER OF NEW ENGLAND, LLC
S. LANCASTER, MASSACHUSETTS
SECTION I INTRODUCTION
The treating facility at S. Lancaster is located approximately fifty (50) miles west of Boston. It is about five
(5) miles west of Interstate I-495 and fifteen (15) miles north of Interstate I-90. The location can be seen on
the Location Map, Appendix A-I.
ACTIVITIES AT THE SITE
The primary activity at this site is the application of a wood preservative to increase the life of untreated
wood. White lumber (untreated lumber) is pressure treated in a pressure vessel and then allowed to drip
on a concrete drip pad until drippage has ceased. It is then moved to the site or to a building until it is ready
to be shipped to a lumber sales facility.
The purpose of this SWPPP document is to comply with Federal Regulation 40 CFR Part 122, which
prohibits point source discharges of storm water to United States waters without a NPDES permit. This
SWPP Plan is an update to previous SWPP Plans for this site as completed by Industrial Compliance Group,
Inc. on November 1, 2015. This SWPPP delineates potential pollution sources, outfalls where storm water
leaves the site, and Best Management Practices (BMP's) that are in place to minimize polluted discharges..
McPherson Design
1-3
ED_019088A_00012854-00040
PLANNING, ORGANIZATION AND CERTIFICATION
ED_019088A_00012854-00041
STORMWATER POLLUTION
PREVENTION PLAN
CULPEPER OF NEW ENGLAND, LLC
S. LANCASTER, MASSACHUSETTS
SECTION II
PLANNING, ORGANIZATION AND CERTIFICATION
POLLUTION PREVENTION PERSONNEL
It is necessary to establish a list of personnel who will be responsible for overseeing and
coordinating, and, when necessary, amending the policies, practices, and procedures of the SWPPP.
These people should be knowledgeable concerning wood preserving facility operations and capable
of understanding the technical aspects of the plan. Trained personnel, responsible for the execution
of the SWPPP requirements, should be available at the wood preserving facility.
The SWPPP Committee will be responsible for overseeing the activities as outlined below and shall
meet at least annually to address the implementation of these activities:
Coordination of management in carrying out SWPPP objectives.
Implementation of spill reporting procedures.
Employee chemical safety training programs.
Raw material / waste storage inspection programs.
Identification of potential pollutant sources.
Coordination of spill cleanup and containment activities.
Reviewing the effectiveness of the SWPPP program.
Updating the SWPPP program to comply with BMP policies and objectives.
Preparation and submittal of documents described in the Introduction.
McPherson Design
2-1
ED_019088A_00012854-00042
STORMWATER POLLUTION
PREVENTION PLAN
CULPEPER OF NEW ENGLAND, LLC
S. LANCASTER, MASSACHUSETTS
SECTION IIPLANNING, ORGANIZATION AND CERTIFICATION
POLLUTION PREVENTION COMMITTEE MEMBERS
Operations Manager / S. Lancaster Facility:
Mr. Mike Nuzzolilo
Phone:978-273-4007E-mail:mnuzzolilo@culpeperwood.com
Designated Individuals:
Name:Mark PlouffeTitle:Plant Manager
Phone:978-479-5703
Name:Javier RodriguezTitle:Shop Manager
Phone:978-368-7667
McPherson Design
2-2
ED_019088A_00012854-00043
STORMWATER POLLUTION
PREVENTION PLAN
CULPEPER OF NEW ENGLAND, LLC
S. LANCASTER, MASSACHUSETTS
SECTION II
PLANNING, ORGANIZATION AND CERTIFICATION
SWPPP CERTIFICATION
The SWPPP certification must be signed in accordance with the provisions of the multi - sector general
permit. All reports, certifications, or other information required by the permit or requested by the permit
authority shall be signed by a responsible corporate officer, a general partner, a proprietor, or a duly.
authorized representative.
The duly authorized representative must be authorized in writing by either a corporate officer, a general
partner, or a proprietor. A duly authorized representative may be either a named individual or any
individual occupying a named position. If an authorization is no longer accurate because a different individual
or position has responsibility for the overall operation of the facility, a new authorization must be attached
to the SWPPP prior to submittal of any reports, certifications, or information signed by the authorized
representative.
McPherson Design
2-3
ED_019088A_00012854-00044
STORMWATER POLLUTION
PREVENTION PLAN
CULPEPER OF NEW ENGLAND, LLC
S. LANCASTER, MASSACHUSETTS
SECTION II PLANNING, ORGANIZATION AND CERTIFICATION
SWPPP CERTIFICATION
Name:Mr. Mike Nuzzolilo
Title:Operations Manager / S. Lancaster Facility
Wood Preserving Facility Name:Culpeper of New England, LLC
840 Sterling Road
S. Lancaster, Massachusetts
" I certify under penalty of law that this document and all attachments were prepared under
my direction or supervision in accordance with a system designed to ensure that qualified
personnel properly gather and evaluate the information submitted. Based on my inquiry of
the person or persons who manage the system, or those persons directly responsible for
gathering the information, the information submitted, is, to the best of my knowledge and
belief, true, accurate, and complete. I am aware that there are significant penalties for
submitting false information, including the possibility of fine and imprisonment for knowing
violations. "
Signature:
Title:Operations Manager / S. Lancaster Facility.
Date:
4-8-22
McPherson Design
2-4
ED_019088A_00012854-00045
STORMWATER POLLUTION
PREVENTION PLAN
CULPEPER OF NEW ENGLAND, LLC
S. LANCASTER, MASSACHUSETTS
SECTION II
PLANNING, ORGANIZATION AND CERTIFICATION
SPECIAL REQUIREMENTS
In addition to the minimum requirements of the " multi - sector " permit, facilities may be subject to additional
" special " requirements. Not all facilities will have to include these special requirements in their SWPPP.
SARA Title III, Section 313 Facilities
The following are specific permit requirements for all CCA and copper azole facilities that use more
than the threshold level of 10,000 lbs./year of copper (Appendix D of 40 CFR 122, Table 111),
because of the reporting requirements under SARA Title III, Section 313 [also known as the
Emergency Planning and Community Right - to - Know Act (EPCRA)].
Control measures must be practiced in areas where Section 313 water priority chemicals are
stored, handled, processed, or transferred. Culpeper currently implements the following control
measures:
Provide containment, drainage control, and / or diversionary structures.
Minimize discharges from liquid storage areas (install liquid materials in compatible
storage containers and / or provide secondary containment or equivalent measures
designed to hold the volume of the largest storage tank plus precipitation).
Minimize discharges from material storage areas.
Minimize discharges from loading / unloading areas (use drip pans and / or implement a
strong spill contingency and integrity testing plan).
Minimize discharges from handling / processing / transferring areas (use covers, guards,
overhangs, door skirts and / or conduct visual inspections or leak tests for overhead
piping).
Minimize discharges from all the above areas (use manually activated valves with
drainage controls in all areas, and / or equip the plant with a drainage system to return
spilled material to the facility).
McPherson Design
2-5
ED_019088A_00012854-00046
STORMWATER POLLUTION
PREVENTION PLAN
CULPEPER OF NEW ENGLAND, LLC
S. LANCASTER, MASSACHUSETTS
SECTION II
PLANNING, ORGANIZATION AND CERTIFICATION
Introduce facility security programs to prevent spills (use fencing, lighting, traffic
control, and / or secure equipment and buildings). All chemical storage locations are
locked.
Preventative Maintenance
When a leak or spill of a Section 313 water priority chemical has occurred, the contaminated soil,
material, or debris must be removed promptly and disposed of in accordance with Federal, State,
and local requirements and as described in the Stormwater Pollution Prevention Plan. In order to
prevent such spills in the future, these facilities are also required to designate a person responsible
for spill prevention, response, and reporting procedures. All areas of the Culpeper facility are
currently inspected for the following at appropriate intervals as specified in the plan:
Leaks or conditions that would lead to discharges of Section 313 water priority
chemicals are inspected on a daily basis.
Conditions that could lead to direct contact of stormwater with raw materials,
intermediate materials, waste materials or products.
Piping, pumps, storage tanks and bins, pressure vessels, process and material handling
equipment, and material bulk storage areas for leaks, corrosion, support or foundation
failure, or other deterioration or non - containment problems.
Training
Employees at the Culpeper facility are trained in the following areas, at least once per year:
Preventative measures, including spill prevention and response, facility inspections and
preventative maintenance. (All personnel)
The facility's SWPPP. (Connor Burke, Mike Nuzzolilo and Mark Plouffe)
Features and operations of the facility that are designed to minimize discharges of
Section 313 water priority chemicals, particularly spill prevention procedures. (All
personnel)
Annual Hazardous Waste Training. (All personnel)
McPherson Design
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CULPEPER OF NEW ENGLAND, LLC
S. LANCASTER, MASSACHUSETTS
SECTION II
PLANNING, ORGANIZATION AND CERTIFICATION
Engineering Certification
The plan must be reviewed and certified by a Registered Professional Engineer and
recertified every 3 years or after the plan is significantly changed. At the end of this
SWPP plan is the certification provided by McPherson Design. Recertification will be provided
before March 30, 2025. Review for significant changes will occur annually when the drip pad is
recertified for Subpart W.
Monitoring Requirements
Wood preserving plants using copper azole on a CCA contaminated drip pad are required to
monitor stormwater discharges as the stormwater leaves the site. Under the multi - sector general
permit, Culpeper is required to sample stormwater discharges (outfalls) twice per year of their
permit. If samples are above the benchmark established by the EPA, Culpeper must also install
BMPs to try and eliminate the high sample readings. There are many other parts to the monitoring
requirements that need to be reviewed and understood by Culpeper prior to beginning the
monitoring process. These requirements should be reviewed annually by Culpeper and the
certifying engineer.
This Culpeper facility has four (4) outfalls where stormwater samples can be taken. The
estimated areas for each outfall are shown on the site map (Appendix A-2). In general,
stormwater drains from the north end of the property to the south end of the property.
Therefore, all of the outfalls are located on the south end of the property. The site drops
thirty - seven feet (37'- 0 ") in elevation from the north end to the south end of the property,
which provides good, positive drainage. This topographic information was provided by
McPherson Design:
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S. LANCASTER, MASSACHUSETTS
SECTION II
PLANNING, ORGANIZATION AND CERTIFICATION
Culpeper in a survey developed by Prime Engineering dated August 31, 2018. Most of the site
has dirt and gravel which could lead to erosion; however, we did not see any signs of erosion at
the outfalls. Due to inclement weather, we were only able to photograph three (3) of the
outfalls. See Photograph No. I for Outfall # 1, Photograph No. 2 for Outfall # 3, and Photograph
No. 3 for Outfall # 4.
McPherson Design
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CULPEPER OF NEW ENGLAND, LLC
S. LANCASTER, MASSACHUSETTS
SECTION III
POTENTIAL POLLUTANT SOURCES
POTENTIAL POLLUTANT SOURCES
In general, wood preserving facilities are engaged in treating wood, sawed or planed, with chromated copper
arsenate (CCA), CCA and Fire Retardant, CCA, ammoniacal copper zinc arsenate (ACZA), copper azole or
borates. The S. Lancaster site treats with MCA, " Ecolife " and ACQ. Each facility has been identified as 2491
SIC code. A brief description of the activities associated with the 2491 SIC code is as follows:
SIC 2491 Pressure Treating Wood
Untreated wood is loaded onto small rail or tram cars and moved into the treating
cylinder, or retort. The cylinder door is sealed via a pressure tight door, and a
vacuum is applied to remove most of the air from the cylinder and the pressure
raised to about 150 psi. Total treating time varies depending on the species of
wood, the commodity being treated and the desired chemical retention. At the
end of the process, the excess treating solution is pumped out of the retort and
back to storage for reuse. The cylinder door is opened, and the trams loaded with
treated wood are removed from the cylinder onto an impermeable drip pad where
they are left to dry, or in some instances are kiln dried. The drying time is
dependent on the impregnated material, temperature, humidity, and other
parameters. In all cases, the treatment process remains in a closed system.
The types of wood preserving operations are listed below in approximate descending order of
concern based on their potential to discharge hazardous materials into stormwater. The ranking
considers the quantity of material handled, the potential for discharge and the toxicity or hazard of
the materials involved.
Bulk Chemical and Fuel Storage or Transfer Areas
Retort, Drip Pad and Ramp Access Areas including Tracking of Drippage off
the Drip Pad Forklifts or Pedestrians
Finished Product Storage / Drying Areas including Treated Wood Stored
Outside
McPherson Design
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S. LANCASTER, MASSACHUSETTS
SECTION III
POTENTIAL POLLUTANT SOURCES
Vehicle and Equipment Fueling
Vehicle and Equipment Washing
On - site Sewage Disposal System
BULK CHEMICAL AND FUEL STORAGE OR TRANSFER AREAS
Above ground tanks are used for the bulk storage of treating solutions and this facility has two (2) above-
ground one thousand (1,000) gallon diesel fuel tanks and one (1) above ground five hundred (500) gallon
diesel fuel tank. The one thousand (1,000) gallon tank that is north of the garage is a dispensing tank and the
one thousand (1,000) gallon tank that is south of the kiln building is a storage tank. The five hundred (500)
gallon tank is in the boiler room and is used as boiler fuel. There is also a two hundred seventy - five (275)
gallon fuel oil tank behind the garage. The diesel fuel tanks can be seen in Photographs No. 4 and 5. Bulk
shipments of MCA, " Ecolife " and ACQ are received from tank trucks. This chemical concentrate is off
loaded in a contained area (drip pad) near the storage tanks.
Hazardous waste generated from wood preserving facility operations primarily consist of contaminated
sludge from the drip pad, sumps, and retort and also waste oils from vehicle maintenance. The sludge and
any material contaminated by the treating solutions (MCA, " Ecolife " and ACQ) are regulated by EPA
through the RCRA program.
Bulk chemical tanks at this site are:
MCA-C Work Tank (horizontal) - 20,000 gallons
MCA-C Work Tank (horizontal) - 20,000 gallons
MCA-C Work Tank (vertical) - 5,500 gallons
MCA-C Work Tank (vertical) - 6,900 gallons
MCA-C Work Tank (vertical) - 6,000 gallons
ACQ C2 Concentrate Tank (vertical) - 6,000 gallons
" Ecolife " Concentrate Tank (vertical) - 6,000 gallons
" Ecolife " Concentrate Tank (vertical) - 20,000 gallons
McPherson Design
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CULPEPER OF NEW ENGLAND, LLC
S. LANCASTER, MASSACHUSETTS
SECTION III
POTENTIAL POLLUTANT SOURCES
Effluent Water Tank (vertical) - 8,400 gallons
Water Tank (vertical) - 10,000 gallons
Treating Cylinder 20,000 gallons
RETORT, DRIP PAD AND RAMP ACCESS AREAS
On December 6, 1990, the EPA amended the Resource Conservation and Recovery Act (RCRA) by listing
as hazardous waste any drip pad drippage generated during the wood preserving process. These include
requirements for drip pad design, operation, and closure.
Waste Removal
Effective February 6, 1992, the drip pad and all associated collection systems will be cleaned of
process residuals at least once every ninety days. Process residual solids collected during the
cleaning of the drip pad containment and collection system will be placed into DOT approved
hazardous waste containers. All wash water will be pumped back into the effluent system for reuse
as make - up water.
Control of All Effluent Run - on / Run - off
The drip pad containment / collection system will be constructed and maintained to prevent the run-
on of water accumulated from the areas outside of the drip pad.
Lumber Treatment Building and Drip Pad Tanks
MCA-C Treating Solution
" Ecolife " Treating Solution
ACQ Treating Solution
BARamine
McPherson Design
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PREVENTION PLAN
CULPEPER OF NEW ENGLAND, LLC
S. LANCASTER, MASSACHUSETTS.
SECTION III
POTENTIAL POLLUTANT SOURCES
Arch Defoamer WE
Arch Moldicide WE
Arch Mold Inhibitor K-18500.
Treated Lumber Drip Pad Residence Time
The drip pad is designed and used to collect and contain preservative drippage that may occur
following wood treatment. A Treated Lumber Drip Pad Residence Form (Drippage Record) will be
completed recording the charge number, time of drip pad placement, time drippage ceased, etc.
Following each charge, the treated lumber will be: (1) Removed from the treating cylinder. (2)
Placed on the drip pad. (3) Retained on the drip pad until all drippage has ceased. (4) The date,
charge number, as well as the time drippage stopped and charge removed from the drip pad will be
recorded on the " Cease Drippage Form. "
The drip pad has received an initial assessment and certification that it is in accordance with EPA regulations.
McPherson Design provided the annual certification of the drip pad as of August 31, 2022. This certification
signifies that the drip pad has been inspected and has been certified that it:
Is constructed of non - earthen material (concrete) with an adequate coating or a liner (two
layers of protection).
Has berms or curbs around all sides preventing run - on or run - off.
Meets all requirements for maintenance and recordkeeping such as
Waste is removed at least once every 90 days.
The drip pad is cleaned as often as necessary to inspect it at least once every seven (7)
days.
Drippage records are kept to meet EPA requirements.
Meets all other EPA requirements for drip pads.
McPherson Design
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CULPEPER OF NEW ENGLAND, LLC
S. LANCASTER, MASSACHUSETTS
SECTION III
POTENTIAL POLLUTANT SOURCES
Culpeper minimizes the tracking of drippage off of the drip pad from pedestrians by restricting pedestrian
traffic to only those personnel who are part of the treating operation. Culpeper provides control of forklift
traffic on and off the drip pad by having a designated forklift. Culpeper actually has two (2) dedicated
forklifts.
FINISHED PRODUCT STORAGE / DRYING AREAS
Before treated lumber may be moved to the storage yard area, the EPA has directed that freshly treated
wood be held on the drip pad until drippage has ceased. After removal to the storage yard area, any
infrequent and incidental drippage (hereafter known as de minimis drippage) that may occur must be handled
immediately and cleanup procedures addressed in a Contingency Plan. This Plan includes procedures for
proper removal of contaminated waste in a timely manner and maintaining proper documentation. Although
this plant now treats with MCA, " Ecolife " and ACQ, these still come in contact with a CCA contaminated
drip pad, and as such, any waste materials that come into contact with the drip pad must be removed with a
F035 (CCA) waste code. De minimus drippage in the storage yard from wood treated with MCA, " Ecolife "
and ACQ is not considered hazardous waste.
VEHICLE AND EQUIPMENT FUELING AREAS
Fuel is delivered to the Culpeper facility by tank truck. Dispensing to vehicles and equipment is usually
accomplished through standard fuel dispensers. Most spills, if they occur, would be relatively minor. If any
spills were to occur, they would be cleaned up by facility personnel and / or private contractors under the
supervision of the local fire department. In the event that a spill does occur, and happens to reach the
storm sewer system, a licensed cleanup contractor will be immediately dispatched to clean out the storm
McPherson Design
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PREVENTION PLAN
CULPEPER OF NEW ENGLAND, LLC
S. LANCASTER, MASSACHUSETTS
SECTION III
POTENTIAL POLLUTANT SOURCES
lines and recover spilled fuel. The diesel fuel tanks have a person present at all times during refueling. The
diesel fuel tanks can be seen in Photographs No. 4 and 5.
VEHICLE AND EQUIPMENT MAINTENANCE AREAS
All maintenance is completed on - site in the garage, located at the east side of the site. Culpeper stores the
following in the garage, as of the date of our visit:
Anti - freeze - Two (2) fifty - five (55) gallon drums
Motor Oil - One (1) fifty - five (55) gallon drum
Brake Fluid - One (1) five (5) gallon container
Hydraulic Fluid - One (1) fifty - five (55) gallon drum
Used Oil - wwww Two (2) fifty - five (55) gallon drums
The secondary containment for the above petroleum products are two (2) prefabricated plastic containment
units. The sizes are twenty - six inches (26 ") wide by fifty - one inches (51 ") long by seven inches (7 ") deep.
ON-SITE SEWAGE DISPOSAL SYSTEMS
On - site sewage disposal systems (OSDS) include conventional septic systems, large scale conventional
systems, alternative and innovative designs, and private sewage treatment facilities. The term applies to any
residential or industrial sewage that is not treated or planned for treatment in a centralized public sewer
system.
Proper treatment of wastewater effluent with on - site disposal systems is an essential component of surface
water quality protection. Treated wastewater usually reaches surface waters by groundwater recharge or by
groundwater / surface water interfaces.
McPherson Design
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CULPEPER OF NEW ENGLAND, LLC
S. LANCASTER, MASSACHUSETTS
SECTION III
POTENTIAL POLLUTANT SOURCES
Culpeper currently has two (2) on - site sewage disposal systems that are a septic tank for the office
restrooms and a septic tank for yard office / employee breakroom restrooms. The septic tanks are shown on
the site map.
RECEIVING WATERS
Drainage across the property generally flows from north to south. A small percentage of the Culpeper
property is covered by impervious surfaces (i.e., buildings, concrete, asphalt, etc.). Due to the gravelly
nature of the pervious surfaces across the property, it is believed that storm water runoff from the
Culpeper property is generally absorbed into the ground. Any excess runoff flows into nearby outfalls,
numbered 1-4, then into Goodridge Brook, and eventually to the Nashua River.
McPherson Design
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ED_019088A_00012854-00057
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ED_019088A_00012854-00058
STORMWATER POLLUTION
PREVENTION PLAN
CULPEPER OF NEW ENGLAND, LLC
S. LANCASTER, MASSACHUSETTS
SECTION IV
FACILITY DATA COLLECTION
INTRODUCTION OF COLLECTED DATA
The multi - sector general permit requires that the following information be gathered in order to
determine and evaluate pollution sources:
Site Map with topographic information.
Description of significant material handling.
Pollutant lists.
Wood preserving facility size.
Significant spills or leaks.
Summary of sampling data.
SITE MAP WITH TOPOGRAPHIC INFORMATION
The wood preserving facility site map must show the following: discharge structures, drainage areas,
impervious areas, areas of stormwater runoff contact with pollutants, actual or potential, location of existing
structural control measures (i.e., ditches, berms, or retention ponds), surface water locations and areas of
existing or potential soil erosion. All of the above information should be marked or delineated on the wood
preserving facility site map. Appendix A-2 is a copy of the site map at Culpeper. This site map lists
improvements made by Culpeper to enhance stormwater management.
TOPOGRAPHIC MAP
The topographic map should extend beyond the property boundaries of the wood preserving facility,
showing the following: the building structures, surface water bodies (including springs and wells) and the
wood preserving facility discharge points where the wood preserving facility's stormwater discharge leaves
the property and enters the municipal storm drainage system or enters a water body. The topographic map
must accompany the walking tour of the wood preserving facility so that any outfalls that are not shown on
McPherson Design
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S. LANCASTER, MASSACHUSETTS
SECTION IV
FACILITY DATA COLLECTION
the present map can be added and the drainage area determined. A copy of the site map and the
topographic map should be inserted into the SWPPP document. Appendix A-2 is the Site Map.
Culpeper is not including a topographic map as a separate enclosure to the SWPPP document. The
information required on the topographic map is shown on the site map and drainage and direction of slope
is obvious.
As part of the SWPPP requirements, the facility must list the receiving waters that receive the storm water
from the facility site. Water leaving the site eventually makes its way to the Nashua River.
DESCRIPTION OF SIGNIFICANT MATERIAL HANDLING
Wood preserving facilities must provide a description of the following items:
Significant materials that have been treated or disposed of within the past three years. Any
material that has been spilled or leaked in significant quantities to the stormwater discharge
since November 19, 1988.
Materials, equipment, and vehicle management practices employed to minimize contact
of the stormwater discharge and significant materials.
Material loading, unloading and access areas.
Existing structural control measures to reduce pollutants in the stormwater discharge.
Methods of on - site storage and disposal of significant materials.
Outdoor storage, manufacturing, and processing activities including activities that
generate significant quantities of dust or particulates.
Significant Materials Treated
Significant materials include but are not limited to: raw materials, fuels, solvents, detergents,
plastics, finished materials such as metallic products, food processing or production raw materials,
hazardous substances designated under Section 101 (14) of CERCLA, any chemical the facility is
McPherson Design
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PREVENTION PLAN
CULPEPER OF NEW ENGLAND, LLC
S. LANCASTER, MASSACHUSETTS
SECTION IV
FACILITY DATA COLLECTION
required to report pursuant to Section 313 Title III of SARA, fertilizers, pesticides, and waste
products.
The significant materials treated at Culpeper Cortland include raw white lumber that is treated with
MCA, " Ecolife " and ACQ.
Significant Materials Stored
1. Micronized Copper Azole (MCA), bulk storage in containment area (tank farm).
" Ecolife, " bulk storage in containment area (tank farm).
Alkaline Copper Quaternary (ACQ), bulk storage in containment area (tank farm).
BARamine, totes stored in treating building.
Mold Inhibitor, totes stored in treating building. Mold inhibitors include WE and K18500.
Diesel Fuel.
2. 4. 3. 5. 6. 7. 8. 9.
Anti - Freeze, stored in containment area (garage).
Motor Oil, stored in containment area (garage).
Brake Fluid, stored in containment area (garage).
10. Hydraulic Fluid, stored containment area (garage).
11. Used Oil, stored in containment area (garage).
Significant Materials Disposed
1. Micronized Copper Azole (MCA) contaminated solid waste stored in drums in containment
area (tank farm).
2. " Ecolife " contaminated solid waste stored in drums in containment area (tank farm).
3. Alkaline Copper Quaternary (ACQ) contaminated solid waste stored in drums in
containment area (tank farm).
4. Used Oil stored in fifty - five (55) gallon drums in containment area (garage).
McPherson Design
4-3
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S. LANCASTER, MASSACHUSETTS
SECTION IV
FACILITY DATA COLLECTION
This includes any storage yard drippage tank clean outs and pit clean outs.
Materials Management Practices
Any practices designed to limit contact of pollutant with the stormwater discharge. A roof
constructed over an above ground storage tank, containing diesel fuel, would be an example of a
material management practice that would limit contact of significant material with rainfall. The
following are materials management practices used at Culpeper:
1. All freshly treated lumber kept on drip pad and under a roof until drippage has ceased.
2. All of the significant materials either stored or disposed of are under a building roof or in a
containment device. The treating chemical storage tanks in the tank farm are under a roof
and have secondary containment.
3. There is a liner below the drip pad.
4. MCA, " Ecolife " and ACQ are unloaded in the containment area.
5. The drip pad is not sealed but does have a concrete berm and a roof to prevent run - on and
run - off.
Equipment Management Practices
Many types of equipment are associated with wood preserving facilities including pressure retorts,
bark strippers, sawmills, fueling trucks, maintenance equipment, freight transfer vehicles, and
forklifts.
Some of the equipment management practices that are adhered to at Culpeper are as follows:
1. Equipment goes through a preventative maintenance program.
2. Spills or leaks from equipment are cleaned up immediately.
3. Washing of equipment does not occur on - site. The equipment is rinsed off from time to
time in several places throughout the site. There is no vehicle washing area.
McPherson Design
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ED_019088A_00012854-00062
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PREVENTION PLAN
CULPEPER OF NEW ENGLAND, LLC
S. LANCASTER, MASSACHUSETTS
SECTION IV
FACILITY DATA COLLECTION
Vehicle Management Practices
Maintenance of vehicles can be a significant source of stormwater pollutants. Materials associated
with vehicle maintenance include waste oil, and other degreasers used to clean engine parts, anti-
freeze, radiator flush, brake fluid and battery acids and sludges.
Vehicle maintenance is handled on - site in the garage, which is in a building, under a roof with
secondary containment.
Material Loading Areas
Describe and define areas (marked on site map as well) in which materials are loaded, unloaded, or
stored at the wood preserving facility and a potential exists for exposure to stormwater. Culpeper
has the following loading areas:
1. Finished product is loaded on trucks throughout the site.
2. Hazardous waste for disposal is loaded at drip pad.
Material Unloading Areas
1. Micronized Copper Azole (MCA), " Ecolife, " and Alkaline Copper Quaternary (ACQ) are
unloaded to bulk storage while the truck is on the pavement beside the drip pad and is in a
containment area.
2. Diesel fuel is unloaded from a tanker truck directly into two (2) one thousand (1,000).
gallon and one (1) five hundred (500) gallon above ground tanks.
Material Storage Areas
1. Micronized Copper Azole (MCA), " Ecolife " and Alkaline Copper Quaternary (ACQ) bulk:
storage tanks are in a contained area (tank farm).
2. Diesel fuel is stored in three (3) above ground tanks.
McPherson Design
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ED_019088A_00012854-00063
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CULPEPER OF NEW ENGLAND, LLC
S. LANCASTER, MASSACHUSETTS
SECTION IV
FACILITY DATA COLLECTION
Existing Structural Controls
Existing structural controls could include berms around drip pads, sealing drip pad surfaces, liner
under drip pad, enclosure of the drip pad, retort, or copper azole tanks, storing finished wood
under cover, oil / water separators installed on drain lines which then discharge to a sanitary sewer.
Other structural controls could include detention ponds and / or marsh systems which can provide
for settling, oxidation of volatiles, and water quality benefits from plant uptake of nutrients and
other pollutants. Culpeper has the following structural controls:
1. All pressure treating activities occur inside buildings or under a roof or in a containment
area.
2. Drip pads are constructed to meet or exceed Subpart W in RCRA Regulations.
3. Drip pads and berms are structurally sound.
4. Berms or curbs are located around drip pads.
Existing Non - Structural Controls
Existing non - structural controls could consist of directives and policies concerning suitable locations
for cleaning and maintenance activities and policed bans against performing such activities in non-
designated locations. Culpeper has the following non - structural controls:
1. Culpeper will provide impacted employees with orientation on spill prevention and good
housekeeping.
2. Culpeper has established regulatory compliance manuals.
3. Culpeper has established an employee training procedure.
Industrial Stormwater Treatment Facilities (If Any)
Culpeper does not currently have an on - site stormwater treatment facility. The stormwater sheds
off - site through natural slope and outfalls.
McPherson Design
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S. LANCASTER, MASSACHUSETTS
SECTION IV
FACILITY DATA COLLECTION
Methods of Off - Site Disposal of Significant Materials
An example of this type includes the contracted removal of sludge from the retort and sump areas
on a regular and scheduled basis. Also included here are provisions for services from a contracted
hazardous material disposal specialist firm on an as - needed basis.
1. All Micronized Copper Azole (MCA), " Ecolife " and Alkaline Copper Quaternary (ACQ)
contaminated materials at Culpeper are disposed of as per RCRA.
Methods of On - Site Storage of Significant Materials
1. All waste materials (oil, filters, grease) are stored in secondary containment in the garage
until removed per RCRA requirements.
2. All virgin materials (MCA, " Ecolife, " ACQ, fuel oil, mold inhibitor) are stored in confined
areas.
Activities That Generate Significant Quantities of Dust or Particulates
1. Vehicle traffic (forklifts, trucks) in unpaved areas of the plant.
McPherson Design
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ED_019088A_00012854-00065
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S. LANCASTER, MASSACHUSETTS
SECTION IVFACILITY DATA COLLECTION
POLLUTANT LIST
The wood preserving facility is required to list any pollutants that have a reasonable potential to be present
in the stormwater discharge in significant quantities. The definition of significant quantities varies from item
to item. In general, a significant quantity can be taken to be any quantity that is not consumed within a
normal day's operations or would result in spills beyond the immediate clean - up capabilities of the individual
charged with the use of the materials. A significant quantity also relates to a " reportable " quantity for those
substances that are regulated. A list of pollutants at Culpeper and their use is as follows:
POLLUTANT PRESENTUSE
Micronized Copper Azole (MCA) Wood Preservative
" Ecolife "Wood Preservative
Alkaline Copper Quat (ACQ)Wood Preservative
WE and K18500Mold Inhibitor
BARamineWood Preservative
Diesel FuelFuel for Vehicles
Anti - freezeFor Vehicles
Motor OilFor Vehicles
Brake FluidFor Vehicles
Hydraulic FluidFor Vehicles
Used OilFor Vehicles
Table B-I in Appendix B is a sample " Pollutant List " form for your use in the future should the pollutant list
change.
WOOD PRESERVING FACILITY SIZE
The wood preserving facility size should be estimated as well as the percentage of impervious area.
Impervious areas are paved areas and buildings. It is also useful to break the wood preserving facility into
subdrainage areas within which " industrial activity " occurs to each significant outfall.
McPherson Design
4-8
S
ED_019088A_00012854-00066
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CULPEPER OF NEW ENGLAND, LLC
S. LANCASTER, MASSACHUSETTS
SECTION IV
FACILITY DATA COLLECTION
Wood Preserving Facility Size is approximately 18 acres or 784,000 square feet.
Impervious Surface Area Estimate 2.17 acres or 94,525 square feet or 12% of the total property.
SIGNIFICANT SPILLS OR LEAKS
The wood preserving facility must list all historical spills or leaks of toxic or hazardous pollutants to the
stormwater system that have occurred in the last three years. This list must include: toxic chemicals, listed
in 40 CFR 372 that have been discharged to stormwater as reported on EPA Form R, and oil or hazardous
substances in excess of reportable quantities, 40 CFR 110, 117 or 302. There have been no spills or leaks of
a reportable quantity at this site in the last three years.
Table B-2 in Appendix B is a sample " History of Past Spills " form for your use in recordkeeping of future
spills.
OUTFALL INSPECTIONS AND SAMPLING REQUIREMENTS
If Most states require a visual inspection of the outfalls on an interim basis that is quarterly up to annually.
In addition, stormwater samples must be taken at the outfalls at various intervals, depending on the state.
The visual inspections should be completed by personnel that are trained on what to look for. The
employees'training needs to be documented and the results of the inspections should be recorded on a
typical state form or on the form included with this SWPP Plan, in Appendix B, Table B-5 titled " Drainage
System Maintenance and Inspection. "
The inspection interval needs to be confirmed for your state. In a SWPP Plan previously provided to
Culpeper by the Industrial Compliance Group in 2017, stated that the visual inspection of the outfalls and
drainage features leading to the outfalls should be completed quarterly. It is our understanding that
Massachusetts only requires an annual visual inspection. The visual inspection includes walking the drainage
features, like swales and ditches, as well as inspecting the outfalls for the following:
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Color of foliage or dirt
Odor
Displaced solids
Settled solids
Foam
Oil sheen
Other obvious indicators of stormwater pollution
The standard form used for this inspection is the same as mentioned previously in Appendix B, Table B-5.
This form lists other info needed. It is our understanding that Culpeper of New England, LLC does not have
to submit this info to the State unless specifically requested to do so.
As for stormwater sampling at the outfalls, Culpeper of New England, LLC needs to purchase the proper
grab sample containers. Before starting, personnel should be properly trained on how to sample and how
to process the sample. The training should be kept on a " training log. " The proper procedure for taking
the grab samples is as follows:
Procedure:
Take a minimum of one (1) grab sample from the discharge associated with industrial activity
resulting from a measurable storm event, providing the interval from the preceding measurable
storm is at least 72 hours. The 72-hour storm interval is waived when the preceding measurable
storm did not yield a measurable discharge, or if you are able to document that less than a 72-hour
interval is representative for local storm events during the sampling period. Take the grab sample
during the first 30 minutes of the discharge. If it is not practicable to take the sample during the
first 30 minutes, sample as soon as practicable and describe why a grab sample during the first 30
minutes was impracticable.
Prior to taking the samples, the discharge and accumulated water needs to be inspected for:
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Color
Odor
Clarity
Floating solids.
Settled solids
Suspended solids
Foam:
Oil sheen
Other obvious indicators of stormwater pollution
Frequency of Outfall Sampling
Timber Products, Wood Preserving, SIC Code 2491 falls within the Benchmark Monitoring
Program. This means that Culpeper needs to establish benchmark readings starting in the first full
quarter following the date of September 2, 2015, or the date of your NPDES permit date,
whichever comes later. Benchmark monitoring requires that Culpeper sample at least once in each
of the following three (3) month intervals:
January - March 31
April 1-June 30
July - September 30
October
December 31
This completes one (1) year of benchmark monitoring.
After establishing the Benchmark Monitoring, if the average of your next four (4) quarterly readings
do not exceed the benchmark, Culpeper of New England, LLC would have fulfilled the monitoring
requirements for the rest of the NPDES permit term.
If the average of your next four (4) quarterly readings exceed the benchmark, Culpeper would
continue to take quarterly readings for the duration of the NPDES permit term. Culpeper must
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make modifications to try and reduce pollutant readings. These BMP's need to be documented
along with their results.
All samples are to be taken properly, sampled properly, transported to the lab properly and the lab
shall provide the results along with the state's allowable limits for that pollutant. If the readings are
above the allowable limit, Culpeper shall make modifications (BMP's) to reduce the readings.
Outfall Maintenance
Culpeper of New England, LLC shall inspect the outfalls on a quarterly basis and make adjustments
as needed to make the outfalls function better. This shall not be done during or just prior to a
required sampling event. Adjustments can include cutting excessive grass, removing excessive
weeds, rebuilding of eroded dirt or structure, or maybe just adjusting stone or gravel to allow for
an easier way to take the readings.
SUMMARY OF SAMPLING DATA
If the wood preserving facility has conducted sampling of the stormwater discharges, the data should be
included in the SWPPP document. Previous sampling data will be useful in determining the source of
pollutants and initiating controls. Culpeper has four (4) outfalls at this site. Most of the Stormwater leaves
the site by way of the four outfalls. Although we have not included sampling data in this report, Culpeper of
New England, LLC is currently working on a program to update this sampling data.
Table B-3 in Appendix B is a sample " Sampling Event Record " that can be used to list sampling results, in
the future.
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STORMWATER MANAGEMENT CONTROL
INTRODUCTION
This section of the SWPPP describes stormwater management measures to control and abate water
quality impairment associated with the activities described in the preceding sections. Culpeper has
initiated a positive attitude in providing stormwater control management for their facility. The
following paragraphs along with the site map delineate stormwater control management practices
introduced by Culpeper.
THE NON-POINT SOURCE POLLUTION PROCESS
Non - point source pollutants are transported to surface water by a variety of means, including run - off and
ground water infiltration. Ground water and surface water are both considered part of the same hydrologic
cycle when designing management measures. Ground water contributions of pollutant loadings to surface
waters are often very significant. The transport of non - point source pollutants to surface waters through
ground water discharge is governed by physical and chemical properties of the water, pollutant, soil, and
aquifer.
Source control is the first opportunity in any non - point source control effort. Source control methods vary
for different types of non - point source problems. Some examples of source control which have been
implemented at the Culpeper Facility are as follows:
1. Culpeper has reduced / eliminated the introduction of pollutants to the land area by providing a
drip pad in the treating area to collect all treating chemicals which are pumped back into the
effluent tank for reuse in treating future wood. Culpeper has a portion of the treated lumber
under buildings that have a roof; thus, reducing the amount of rainwater that can wash the
pollutants to the ground.
2. Preventing non - introduced pollutants (such as loose dirt and sediments) from leaving the site
during land disturbing activities such as rainstorms. Culpeper has added gravel to areas that
showed signs of erosion.
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3. Preventing interaction between precipitation and introduced pollutants. Culpeper has provided
a roof over the drip pad so that precipitation is not allowed to come into direct contact with
the treating chemicals.
In addition to source control measures, a good SWPP plan should also include delivery reduction measures.
This involves preventing the pollutants from leaving the discharge area through surface run - off or ground
water contact. The pollutants at Culpeper are controlled by the use of a concrete drip pad with a liner.
The drippage reaches the drip pad that has a positive slope towards a drain that goes through a filter and
then is pumped back into an effluent tank for reuse. The use of the roof and drip pad with liner is an
example of delivery reduction measures that does not allow the pollutant to come into direct contact with
surface run - off or ground water. In addition, an engineering control is in place involving a longer final
vacuum to reduce the amount of drippage of freshly treated lumber. The drip pad also has curbs to control
run - on of stormwater or run - off of source pollutant.
PREVENTATIVE MAINTENANCE
A Preventative Maintenance program is an effective and cost - efficient measure in pollution prevention. It is
easily performed at a relatively low cost and may yield great savings in the long run. Preventative
maintenance includes inspection of facility / tenant equipment and systems, such as pressure cylinder and drip
pad areas, equipment cleaning facilities, all vehicular and maintenance facilities, and any structural source
controls already in place, such as drip pad sumps and tank farm containment.
The preventive maintenance program at Culpeper includes the following:
1. Forklifts are serviced every 6 to 12 weeks.
Sump areas are inspected every week.
Overflow safety system is inspected once a month.
4. 5. 6. 2. 3. Drip pad surface is swept or pressured washed weekly.
Drip pad is inspected weekly for cracks.
Storage tank containment is inspected weekly for cracks.
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7. Storage yard has daily inspection for drippage.
8. Hazardous waste storage area is inspected weekly.
9. Treating solution transfer piping is inspected daily.
The preventive maintenance inspections are carried out by trained personnel who are designated SWPPP
Committee Members. These committee members are familiar with the systems and equipment to be
monitored and tested. The inspection schedules have been established by the committee in conjunction
with the facility manager and brought to the attention of all employees.
Documentation and retention of inspection records is currently a part of the preventive maintenance and
inspection program at Culpeper. A tracking or follow - up procedure is used to ensure that the appropriate
response to the inspection findings has been made. All inspection documentation and records will be
maintained with the SWPPP documentation for a period of five years.
Table B-4 in Appendix B is a sample " Maintenance and Inspection " form that could be used when inspecting
vehicles and equipment.
DRAINAGE SYSTEM
Stormwater drainage system will be inspected at least four times a year. The inspection will consist of
physical observation and possibly chemical sampling as required at the discharge points. The physical
inspection of the outfalls will include observation of flow, odor, clarity, floatables, stains, and vegetation. A
description of each of these items to be inspected is as follows:
Flow
Odor
If flow is present, and rain has not occurred within the past three days,
there may be a problem requiring further investigation unless the source is
positively known and is non - polluting
The presence of any odor from the drainage system
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Clarity
If water is present, standing or flowing, and it is anything but clear
Floatables
If there is floating debris, garbage, sewage, or oily sheen
Stains, etc.
If stains are present on lined channels / pipes, or other than the normal
vegetation or soil color, may be an indicator requiring further investigation
Vegetation
If vegetation in the discharge channel is more luxurious or, conversely
appears stressed in comparison to adjacent vegetation, this is likely an
indicator of excess nutrients or excess contaminants and requires further
investigation.
In addition to the above items, the inspection will also note siltation or scour problems below the outfall.
Table B-5 titled " Drainage System Maintenance and Inspection " can be used to record inspections of the
stormwater drainage system. This table is included in Appendix B.
PAVED AREAS
Inspection of paved areas will be focused on checking the surfaces to ensure that they are clean of
chemicals, grease, oil, solvents and fuels, and other pollutants. In order to reduce the amount of pollutants.
on paved areas, the pollutants will be kept covered in most cases under roofed areas. Other maintenance
activities, such as periodic inspections of containment areas as well as equipment that contains the
pollutants, will help to ensure that the paved areas are not a source of pollutant transport.
In addition to inspecting the surface of the paved areas for pollutants, the paved areas should also be
inspected for large cracks which would allow the potential for pollutants to enter into the ground water
system.
The use of herbicides and petroleum products to reduce vegetation growth in paved areas will be
monitored. The use of herbicides or other chemicals will be kept to a minimum and those used will have a
low toxicity and persistence. Frequency of application will be reduced to a minimum. Grouting of joints and
cracks will be used whenever possible as an alternative to herbicidal application.
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DRIP PAD
The drip pad receives a yearly certification which includes review of all documentation, inspection of the
drip pad for cracks, and inspection of curb and berms to ensure that pollutants are not reaching the
environment.
As part of the certification program for the drip pad, Culpeper is required to conduct weekly inspections of
the drip pad, as well as after every storm event, to ensure that there are no cracks in the drip pad itself. In
addition, Culpeper is required to maintain a facility operating log that keeps a record of treatment time, etc.
and documentation when the drippage has ceased prior to removing the product from the drip pad.
If any cracks, chips, or any other deterioration are discovered, these areas are taken out of use until the
deficiency is corrected. The repairs are documented in a drip pad weekly inspection report and is included
as part of the yearly certification for the drip pad. We have not included the recordkeeping for the drip pad
in this report. Information concerning the recordkeeping for the drip pad can be found in the yearly Subpart
W certification.
It should be noted that the drip pad was originally assessed in 2012 and exhaustive corrections were
completed to provide a drip pad that was in accordance with EPA regulations. Since that time, the drip pad
has been recertified from 2017 through 2022 to be in full compliance with the EPA regulations.
CLEANING FACILITIES AND EQUIPMENT
The maintenance and cleaning of equipment is very important where a large number of vehicles are
concerned. Vehicle maintenance is done on - site in the garage. Washing of vehicles is not completed on
site, however the vehicles are rinsed off from time to time throughout the site. There is no designated
vehicle washing area.
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MATERIALS STORAGE AREAS
Tanks for material storage will be inspected for leaks, corrosion, deterioration of the foundation, masonry
retaining walls and slab of the tank farm, and closure of drainage valves. Inspection of the seams, rivets,
nozzle connections, valves, connecting pipelines, hoses, and evidence of corrosion, pitting, cracks, dry rot,
abnormalities, and deformation will be required. The tanks and equipment for material storage areas will be
inspected on a weekly basis. Records of the inspections will be kept at the Culpeper facility.
All storage tank levels will be logged daily and whenever products are loaded or off - loaded. Tank levels are
also to be monitored during operational use. Tank levels will be carefully noted when use is discontinued
and remeasured whenever operations are restarted. Major differences in levels, of course, will be indicative
of leakage.
Liquid storage facilities will have sumps or leak trays located below valves and drain points and will be
contained in a bermed area having removable absorbent materials to soak up any spillage. Areas where
liquids are stored will have a ready supply of absorbent materials depending on the volume of liquid material
stored. Micronized Copper Azole (MCA), " Ecolife " and Alkaline Copper Quaternary (ACQ) containment
area drip pads and tram areas are to drain into a sump. The liquid is then reused in subsequent treatment.
FUEL / CHEMICAL TRANSFER PIPELINES
Inspections of fuel / chemical transfer pipelines will include visual examination for evidence of deterioration of
pipelines, hoses, sumps, pumps, valves, seals, and fittings. Particular attention will be given to the items
above and any sensors required to interact with the tank being filled. (Many facility spills result from fueling
attendants depending on such sensors and being inattentive while the tank is being overfilled.) A person is
present at all times during filling of tanks..
At Culpeper, all piping runs through containment areas such that there is no piping on the outside of the
containment area and spillage can be controlled. In addition, Culpeper takes level readings before and after
pumping has finished to determine if any fuel / chemical has leaked between transfer.
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Absorbent material will be readily available to maintenance and / or tank truck personnel in these areas
should a spillage occur.
MATERIAL TRANSFER, LOADING AND UNLOADING
Staged materials for loading or unloading will be kept out of stormwater flow paths by storage within
bermed areas or on platforms surrounded by dikes or berms which direct stormwater flow away from the
materials.
Inspections of loading and handling areas will be quite frequent in the early phases of implementation of the
SWPPP to ensure that loading and unloading practices are correctly done. Areas will be inspected for clean
and dry loading platforms, clean equipment, proper storage of loading equipment and maintenance of any
equipment used.
Diesel fuel is delivered by tanker trucks to two (2) one thousand (1,000) gallon and one (1) five hundred
(500) gallon above ground storage tanks. These storage tanks can be seen in Photograph No. 4 and 5.
MAINTENANCE AND INSPECTION OF WOOD TREATING EQUIPMENT
Inspection and maintenance guidelines for pressure treating equipment will follow the manufacturer's
specifications. The equipment itself will be serviced in designated areas as indicated above. Special attention
will be paid to those portions of the equipment that come into contact with the treating solution including
among others: pressure retorts, trams or conveyor mechanisms, pipes (including vacuum hoses for liquid
extraction), tanks for liquid conveyance, and associated valves, fittings, nozzles, and tank seams. Particular
attention will be paid to correcting leaks and replacement of deteriorated rubber or plastic hoses, pipes,
washers, and gaskets.
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GOOD HOUSEKEEPING
Good housekeeping refers to the cleaning and maintenance practices conducted at the facility. Good
housekeeping is an important component of the pollution prevention plan. Periodic training of employees in
housekeeping techniques for those areas of the facility where pollutant sources are found reduces the
significant material contamination of stormwater. Housekeeping practices used at Culpeper are as follows:
1. Floors are swept clean on a regular basis.
All chemicals are stored inside containment areas and devices.
Overflow sensor is installed on the fuel pumps.
Unloading areas are kept clean..
Oil leaks from forklifts, etc. are cleaned up immediately.
A written protocol is established on Subpart W drip pad procedures.
4. 7. E8m. p2l.o 3y.e e5. i6.n tAellr ehsazta ridonu sg woaosdte hios ukseeptk eien ptihne gc ohntaasi nmbeenet na rseat.i
mulated and maintained.
Disposal of those materials used to collect spills are handled by a qualified hazardous material handling
contractor. Material loading and unloading areas are kept clean by manual sweeping.
Micronized Copper Azole (MCA), " Ecolife " and Alkaline Copper Quaternary (ACQ) drippage is collected
and returned to the collection sump which passes the solution back through a filter back into the effluent
tank for reuse.
WRITTEN PROTOCOL
A written protocol for the Subpart W drip pad for the Culpeper facility has been prepared and will be
followed in the future. Included within this protocol is a description of areas, operations, and equipment to
be inspected, frequency of inspection, checklists and procedures to be used, records of inspection and filing
requirements, and a mechanism for revising protocols.
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EMPLOYEE INVOLVEMENT
Maintaining employee interest is a vital part of a good housekeeping program. Good housekeeping goals will
be established, and regular inspections performed by managers. Some of these goals will include the
following:
1. Training program
2. Safety meetings
3. Periodic on - site training
4. Periodic housekeeping inspections
SPILL CONTROL AND COUNTERMEASURES
Spill control has been delineated in all the previous documentation. The potential areas of spill are
maintained in a containment area or in an area that is bermed or curbed and sloped to maintain any spillage.
In addition, numerous inspections are completed to ensure that spillage is kept to an absolute minimum.
Culpeper has also installed such items as overflow switches on fuel tanks.
As part of spill control and countermeasures, the following table lists the location, potential chemical,
equipment committed to this area and the personnel that will be responsible. As you can see from this
table, the three main areas of potential spillage are the tank farm, the diesel fuel storage tank area, and the
garage. The potential chemicals in the tank farm are Micronized Copper Azole (MCA), " Ecolife " and
Alkaline Copper Quaternary (ACQ). Equipment committed to the tank farm is shovel, brooms, vacuum,
sand, cement, sawdust, absorbent material, rubber boots and gloves, rain suits, respirators, and face shields.
The personnel responsible for spill control and countermeasures in the tank farm area are the personnel
working on the drip pad in the treatment process.
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SPILL CONTROL AND COUNTERMEASURES
LOCATION POTENTIAL EQUIPMENT PERSONNEL
CHEMICAL COMMITTED
Tank Farm1. Micronized I. ShovelsTreating plant
Copper personnel
2." Ecolife "2. Brooms
3.ACQ3. Vacuums
4. Sand
Vehicle Maint.
Garage1. Anti - freeze 5. CementPersonnel
2. Motor Oil 6. Sawdust
3.Brake Fluid7.Absorbent
matting
4. Hydraulic Fluid8. Rubber boots,
gloves
5.Used Oil9. Rain suits
10. Respirators
11. Face shields
Diesel Fuel Storage Tank1. Diesel Fuel1. VacuumStorage Yard
Area Personnel
2. Shovels
Absorbent
STORMWATER MANAGEMENT PRACTICES
The SWPPP document needs to identify measures that are used to enhance stormwater management
practices. One of these measures that is a part of the Culpeper facility SWPPP documents is sediment
control and erosion prevention. As part of this SWPPP document, Culpeper has installed concrete and
gravel to reduce erosion. Culpeper has also decided to enclose the vehicle maintenance building to reduce
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potential for stormwater runoff. They also have a plastic secondary containment in the vehicle maintenance
area. The BMPs are located on the site map.
Some additional BMP's that Culpeper has installed are as follows:
I. Installed engineering controls for a longer final vacuum on treating process (less drippage).
2. Yard basins and storm drains have been installed on site to control stormwater.
3. Small spills are cleaned up immediately.
4. Hazardous materials are stored in 55-gallon drums and properly sealed. Drums are disposed of
through a professional company (Safety Kleen, Inc.).
5. Drippage controls and drip pad cleaning are maintained.
6. Chemical and diesel fuel is loaded and unloaded under a strict written protocol.
EMPLOYEE TRAINING
A large part of the success of a SWPPP is the capability and interest of the employees responsible for
implementing and maintaining the program. Personnel need to understand the importance of the program
and the goals of the SWPPP. Personnel must be trained in the techniques of response, removal, and
documentation. The permit authority representatives will be inspecting the multi - sector general permit
participants, and it is important that they are received by trained, knowledgeable personnel who have access
to the SWPPP, environmental files, and other documentation. The SWPPP documentation must be current
and complete when inspected.
Annual training workshops and meetings should be established, at which time employee participation and
input should be encouraged. Training schedules can be recorded in Table B-6 in Appendix B. New
techniques of stormwater management controls as well as changes in permit compliance or limits should be
explained to the employees. Training as a whole should address:
Spill response.
Good housekeeping and material management practices.
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Particular facility features and operations designed to minimize stormwater pollution.
ENDANGERED SPECIES OR CRITICAL HABITAT PROTECTION
It is not expected that discharge - related activities from this facility are likely to jeopardize the continued
existence of any species that are listed as endangered or threatened under the Endangered Species Act
(ESA) or result in the adverse modification or destruction of their habitat. It is beyond the scope of our
work to research or evaluate this information under all of the available sources; to mention just a few
include the National Marine Fisheries Service (NMFS), the Fish and Wildlife Service (FWS), the Endangered
Species Map for this State and other Local, State or National sources. The lists change frequently, so any
confirmation would only apply to a specific point in time anyway. We suggest that the client stay somewhat
familiar with these sources and maintain open communication with the State DEQ or DEP so that the client
will hear of any changes that affect this determination.
NATIONAL HISTORIC PRESERVATION ACT
It is our opinion that discharge - related activities from this facility are not expected to have an effect on any
property that is listed or eligible for listing on the National Register of Historic Places. It is beyond the
scope of our work to research or evaluate this information under all of the available sources; to mention
just a few include the National Register (NRHP), the State Cultural Resource Information System (example:
MACRIS for Massachusetts), the State Historic Preservation Officer (SHPO), the Tribal Historic.
Preservation Officer (THPO) and other Local, state, or National sources. The lists change frequently, so
any confirmation would only apply to a specific point in time anyway. We suggest the client stay somewhat
familiar with these sources and maintain open communication with those sources so that the client will hear
of any changes that affect this determination.
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SECTION VI
NON-STORMWATER DISCHARGES
CERTIFICATION
The multi - sector general permit requires non - stormwater discharges to be eliminated prior to the
implementation of the SWPPP. Facilities must certify that there are no non - stormwater discharges
present in the stormwater drainage system. All facilities must certify and monitor outfalls for dry
weather discharges.
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NON-STORMWATER CERTIFICATION
The regulations require that the appropriate person certify that there are no non - stormwater discharges
present.
Name:Mr. Mike Nuzzolilo
Title:Operations Manager / S. Lancaster Facility
Wood Preserving Facility Name:Culpeper of New England, LLC
840 Sterling Road, S. Lancaster, Massachusetts
" I certify under penalty of law that this document and all attachments were prepared
under my direction or supervision in accordance with a system designed to ensure that
qualified personnel properly gather and evaluate the information submitted. Based on my
inquiry of the person or persons who manage the system, or those persons directly
responsible for gathering the information, the information submitted, is, to the best of my
knowledge and belief, true, accurate, and complete. I am aware that there are significant
penalties for, submitting false information, including the possibility of fine and
imprisonment for knowing violations. "
Signature:
Male Nurse
Title:Operations Manager / S. Lancaster Facility
Date:
4-8.22
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STORMWATER POLLUTION
PREVENTION PLAN
CULPEPER OF NEW ENGLAND, LLC
S. LANCASTER, MASSACHUSETTS
SECTION VII
COMPREHENSIVE SITE COMPLIANCE EVALUATION
INSPECTIONS
Inspections of the facility will be conducted by the permit authority to verify elements of the SWPPP
are accurate and have been implemented. The inspection may yield comments which require a
response to comments by the board and are required to be retained as part of the SWPPP. As
listed under Section 311 of the Clean Water Act this SWPPP is considered a report that shall be
available to the public.
Because the requirements of the evaluation overlap with the requirements of this SWPPP format, it
is recommended that Table 7-1 be completed for each evaluation at a frequency required by the
regulator. Summary information should be listed with specific sections referenced in the
documentation.
Amendments to the SWPPP are required to include the dated signature and title of the person
responsible for preparation of the SWPPP.
McPherson Design
7-1
ED_019088A_00012854-00088
STORMWATER POLLUTION
PREVENTION PLAN
CULPEPER OF NEW ENGLAND, LLC
S. LANCASTER, MASSACHUSETTS
SECTION VII
COMPREHENSIVE SITE COMPLIANCE EVALUATION
TABLE 7-1
SITE COMPLIANCE EVALUATION FORM REPORT
Date and Time of Inspection(s):
Inspector:
Name and Title:
Pollutant Potential To Enter Drainage System:
McPherson Design
7-2
ED_019088A_00012854-00089
STORMWATER POLLUTION
PREVENTION PLAN
CULPEPER OF NEW ENGLAND, LLC
S. LANCASTER, MASSACHUSETTS
SECTION VII
COMPREHENSIVE SITE COMPLIANCE EVALUATION
MEASURE(S)
MEASURES TO REDUCE STATUS
EVALUATED
Pollutant Loadings:
McPherson Design
7-3
:
ED_019088A_00012854-00090
STORMWATER POLLUTION
PREVENTION PLAN
CULPEPER OF NEW ENGLAND, LLC
S. LANCASTER, MASSACHUSETTS
SECTION VII
COMPREHENSIVE SITE COMPLIANCE EVALUATION
STATUS
EQUIPMENT
INSPECTED
EQUIPMENT INCLUDING SPILL RESPONSE EQUIPMENT INSPECTED:
ACTION RECOMMENDED AS A RESULT OF THIS EVALUATION:
CHANGES TO SWPPP:
DATE:
COMMENTS:
McPherson Design
7-4
ED_019088A_00012854-00091
STORMWATER POLLUTION
PREVENTION PLAN
CULPEPER OF NEW ENGLAND, LLC
S. LANCASTER, MASSACHUSETTS
SECTION VII
COMPREHENSIVE SITE COMPLIANCE EVALUATION
McPherson Design
7-5
ED_019088A_00012854-00092
SUMMARY OF RECOMMENDATIONS FOR SWPPP COMPLIANCE
ED_019088A_00012854-00093
STORMWATER POLLUTION
PREVENTION PLAN
CULPEPER OF NEW ENGLAND, LLC
S. LANCASTER, MASSACHUSETTS
SECTION VIII
SUMMARY OF RECOMMENDATIONS
FOR SWPPP COMPLIANCE
RECOMMENDATIONS
The following is a summary of recommendations to be implemented as part of the SWPPP
document
1. Culpeper of New England, LLC has four (4) discernable outfalls where water samples can
be taken. If not currently in place, Culpeper needs to discuss water sampling requirements
with the State and develop a sampling program that meets the State requirements. This
needs to include one (1) location where sampling equipment is kept, training for personnel
so that the sampling procedure is done consistently and per State regulations, written
procedure for submitting samples to a lab and a set of guidelines on what to do with the
sampling test results.
McPherson Design
8-1
+ -
ED_019088A_00012854-00094
ENGINEER'S CERTIFICATION
ED_019088A_00012854-00095
STORMWATER POLLUTION
PREVENTION PLAN
CULPEPER OF NEW ENGLAND, LLC
S. LANCASTER, MASSACHUSETTS
SECTION IXENGINEER'S CERTIFICATION
ENGINEERS CERTIFICATION
The multi - sector general permit requires that a Registered Professional Engineer review the SWPPP
document to ensure that the facility has made a conscientious attempt to comply with EPA
regulations. This certification satisfies that requirement.
" I certify under penalty of law that this SWPPP document and all attachments
have been prepared by McPherson Design in conjunction with Culpeper
Enterprises. The personnel at Culpeper were highly qualified to gather and
evaluate the information submitted. Based on my involvement with those
persons who helped prepare this document and those persons directly
responsible for gathering the information, the information submitted is, to
the best of my knowledge and belief, true, accurate and complete. I am
aware that there are significant penalties for submitting false information. "
COMPANY:McPherson Design
NAME:Roland E. McPherson, P.E.
SIGNATURE:
Roland E. Maherson
TITLE: Founder
DATE: 03/30/2022
McPherson Design
9-1
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ED_019088A_00012854-00098
ED_019088A_00012854-00098
SAMPLE TABLES AND FORMS
ED_019088A_00012854-00099
STORMWATER POLLUTION
PREVENTION PLAN
CULPEPER OF NEW ENGLAND, LLC
S. LANCASTER. MASSACHUSETTS
APPENDIX BSAMPLE TABLES AND FORMS
TABLE B-I-POLLUTANT LIST
DATE POLLUTANT USE QUANTITY
PRESENT ESTIMATE
McPherson Design
B-I
ED_019088A_00012854-00100
STORMWATER POLLUTION
PREVENTION PLAN
CULPEPER OF NEW ENGLAND, LLC
S. LANCASTER. MASSACHUSETTS
APPENDIX B
SAMPLE TABLES AND FORMS
TABLE B-2-HISTORY OF PAST SPILLS
DATE LOCATION OF TYPE OF AMOUNT OF CLEANUP
SPILL MATERIAL MATERIAL RESPONSE
McPherson Design
B-2
ED_019088A_00012854-00101
STORMWATER POLLUTION
PREVENTION PLAN
CULPEPER OF NEW ENGLAND, LLC
S. LANCASTER. MASSACHUSETTS
APPENDIX B
SAMPLE TABLES AND FORMS
TABLE B-3-SAMPLING EVENT RECORDS
DATE OF OUTFALL ANALYSIS ANALYSIS SAMPLING
SAMPLED SAMPLED PERFORMED METHOD
TEAM
McPherson Design
B-3
ED_019088A_00012854-00102
STORMWATER POLLUTION
PREVENTION PLAN
CULPEPER OF NEW ENGLAND, LLC
S. LANCASTER. MASSACHUSETTS
APPENDIX BSAMPLE TABLES AND FORMS
TABLE B-4-MAINTENANCE AND INSPECTION
INSPECTION / MAINTENANCE LOCATION / CONDUCTED DATE
CONDUCTED & COMMENTSEQUIPMENTBY
OBSERVATIONS
McPherson Design
B-4
ED_019088A_00012854-00103
STORMWATER POLLUTION
PREVENTION PLAN
CULPEPER OF NEW ENGLAND, LLC
S. LANCASTER. MASSACHUSETTS
APPENDIX B
SAMPLE TABLES AND FORMS
TABLE B-5-DRAINAGE SYSTEM MAINTENANCE AND INSPECTION
OUTFALL CONDITION DISCHARGE FOLLOW - UP INSPECTOR
PRESENT
McPherson Design
B-5
ED_019088A_00012854-00104
STORMWATER POLLUTION
PREVENTION PLAN
CULPEPER OF NEW ENGLAND, LLC
S. LANCASTER. MASSACHUSETTS
APPENDIX B
SAMPLE TABLES AND FORMS
TABLE B-6-EMPLOYEE TRAINING SCHEDULE
WORKSHOP TOPIC
DATES PERSONNEL ATTENDING
McPherson Design
B-6
ED_019088A_00012854-00105
APPENDIX C
ED_019088A_00012854-00106
STORMWATER POLLUTION
PREVENTION PLAN
CULPEPER OF NEW ENGLAND, LLC
S. LANCASTER, MASSACHUSETTS
APPENDIX C
PHOTOGRAPHS
Photo No. I
Outfall No. I
02/26/2019
McPherson Design
C-1
ED_019088A_00012854-00107
STORMWATER POLLUTION
PREVENTION PLAN
CULPEPER OF NEW ENGLAND, LLC
S. LANCASTER, MASSACHUSETTS
APPENDIX C
PHOTOGRAPHS
Photo No. 2
Outfall No. 3
McPherson Design
C-2
:
ED_019088A_00012854-00108
STORMWATER POLLUTION
PREVENTION PLAN
CULPEPER OF NEW ENGLAND, LLC
S. LANCASTER, MASSACHUSETTS
APPENDIX C
PHOTOGRAPHS
Photo No. 3
Outfall No. 4
McPherson Design
C-3
ED_019088A_00012854-00109
STORMWATER POLLUTION
PREVENTION PLAN
CULPEPER OF NEW ENGLAND, LLC
S. LANCASTER, MASSACHUSETTS
APPENDIX C
PHOTOGRAPHS
02/26/2019
Photo No. 4
Diesel Fuel Tank by Kiln Building
McPherson Design
C-4
ED_019088A_00012854-00110
STORMWATER POLLUTION
PREVENTION PLAN
CULPEPER OF NEW ENGLAND, LLC
S. LANCASTER, MASSACHUSETTS
APPENDIX C
PHOTOGRAPHS
02/26/2019
Photo No. 5
Diesel Fuel Tank in Boiler Room
McPherson Design
C-5
ED_019088A_00012854-00111
STORMWATER POLLUTION
PREVENTION PLAN
CULPEPER OF NEW ENGLAND, LLC
S. LANCASTER, MASSACHUSETTS
APPENDIX C
AMPLE
SAMPLE
MASC
PHOTOGRAPHS
Photo No. 6
Storm Drain
02/26/2019
McPherson Design
C-6
ED_019088A_00012854-00112
Culpeper of New England, LLC
Storm Water Pollution Prevention Plan
Inspection / Action Documentation Form
Date of Action: 4-12-22 Time of Day: 8:05 AM
Name of person performing the inspection or taking action:
Michael
Nuzzolilo
Name of person filling out this report:
Michael Nuz201110
Infiltration Point ID, Outfall or other location description:
Out Fall # 3 3 Storm Drain, Both Clead of ANY Debris
Describe the inspection or action (more than one might apply):
Monthly facility inspection
Inspect sheet flow areas for obstructions or debris
Clean sheet flow areas
Inspect trench drains, drywells, detention basin, pond, or infiltration trench inlets for
obstructions or debris
Clean inlets
Training (Describe type of training and persons trained in space provided below)
Annual dry weather flow monitoring (after at least 3 consecutive days of no
precipitation)
No NON-storm water flows to the storm water drainage systems were identified
o A NON-storm water flow was discovered (discuss below, further action is
required)
Other (describe)
I and My Yard Foreman go thru 3 Clear - UP 3
Maintance the out Fall area's, Replacement of Hay bails
we Also Clean Up And Debris From the Fall
3 Winter,
ED_019088A_00012854-00113
Culpeper of New England, LLC
Storm Water Pollution Prevention Plan
Annual Compliance Evaluation Report
Date of Action: 4-12-22 Time of Day: 10:18 A.M
Name of person performing the inspection or taking action:
Inspectors should look for but are not limited to:
Industrial materials, residue or trash that could contaminate stormwater,
Leaks or spills from industrial equipment, drums, barrels, tanks or similar containers,
Unauthorized non - stormwater discharges (or unidentified allowable discharges),
Off - site tracking of industrial materials or sediment where vehicles enter or exit the site,
Migrating of raw, final, or waste materials from areas of no exposure to exposed areas,
Evidence of or potential for pollutants to enter the drainage system,
Evidence that all BMP's are operating correctly,
Evidence, at each discharge location, that BMP's are effective in preventing pollutants from
contaminating stormwater discharges.
Observations:
Location(s) of discharge of pollutants from the site out FAll # 3
Location(s) of BMP's that need to be maintained Same as above Outfall # 3
Location(s) of BMP's that failed to operate or are inadequate # 5 1, 2, 34 outfalls.
Location(s) where additional BMP's are needed None
Identify any incidents of noncompliance NON
Other: As stated # 1, 2, 34 Don't AllWAYS Produce Storm water.
If no noncompliance items were identified by this inspection, a signature of the following certification
statement shall certify that the facility is in compliance with the SWPPP and the SPDES Multi - Sector
General Permit for Stormwater Discharges Associated with Industrial Activity (GP-0-17-004).
I certify under penalty of law that this document and all attachments were prepared under my direction or
supervision in accordance with a system designed to assure that qualified personnel properly gathered and
evaluated the information submitted. Based on my inquiry of the person or persons who manage the
system, or those directly responsible for gathering the information, the information submitted is, to the
best of my knowledge and belief, true, accurate, and complete. I am aware that there are significant
penalties for submitting false information, including the possibility of fine and imprisonment for knowing
violations.
Name: Michael Nuzzglito Title: General Manager
Signature: M
Date: 4-12-22
ED_019088A_00012854-00114
Culpeper of New England, LLC
Storm Water Pollution Prevention Plan
Inspection / Action Documentation Form
Date of Action: 5-18-21 Time of Day: 1:00 PM
Name of person performing the inspection or taking action:
Michael Nu220 / 110
Name of person filling out this report:
Michael Nuzzolilo
Infiltration Point ID, Outfall or other location description:
Out Fall # 1 33 3 Storm Drain
Describe the inspection or action (more than one might apply):
Monthly facility inspection.
inspect sheet flow areas for obstructions or debris
Clean sheet flow areas
Inspect trench drains, drywells, detention basin, pond, or infiltration trench inlets for
obstructions or debris
Clean inlets
Training (Describe type of training and persons trained in space provided below)
Annual dry weather flow monitoring (after at least 3 consecutive days of no
precipitation)
No NON-storm water flows to the storm water drainage systems were identified
A NON-storm water flow was discovered (discuss below, further action is
required)
Other (describe)
All out Falls Will Need Maintance 3 will be looking
To out Source To Profesiortals To Update 3 Rework, this
Mey take time due to collent Couid Restrictions.
There were Chauge's made to the swipp Report
Photo # 4 ON Page C-4 Has been sold 3 RAMoved
From Site.
ED_019088A_00012854-00115
Culpeper of New England, LLC
Storm Water Pollution Prevention Plan
Annual Compliance Evaluation Report
Date of Action: 5.18-21 Time of Day: 2; 46.P.M
Name of person performing the inspection or taking action:
Inspectors should look for but are not limited to:
Industrial materials, residue or trash that could contaminate stormwater,
Leaks or spills from industrial equipment, drums, barrels, tanks or similar containers,
Unauthorized non - stormwater discharges (or unidentified allowable discharges),
Off - site tracking of industrial materials or sediment where vehicles enter or exit the site,
Migrating of raw, final, or waste materials from areas of no exposure to exposed areas,
Evidence of or potential for pollutants to enter the drainage system,
Evidence that all BMP's are operating correctly,
, at each discharge location, that BMP's are effective in preventing pollutants from
contaminating stormwater discharges.
Observations:
Location(s) of discharge of pollutants from the site Out Fall # 3 3
Location(s) of BMP's that need to be maintained All Need MaintaiNace From WithR
Location(s) of BMP's that failed to operate or are inadequate out Fall # 4 gets No RUNOFF
Location(s) where additional BMP's are needed NoNe
Identify any incidents of noncompliance Out Fall # 14 the Stormwater Disapates Into the ground
Other:
If no noncompliance items were identified by this inspection, a signature of the following certification
statement shall certify that the facility is in compliance with the SWPPP and the SPDES Multi - Sector
General Permit for Stormwater Discharges Associated with Industrial Activity (GP-0-17-004).
I certify under penalty of law that this document and all attachments were prepared under my direction or
supervision in accordance with a system designed to assure that qualified personnel properly gathered and
evaluated the information submitted. Based on my inquiry of the person or persons who manage the
system, or those directly responsible for gathering the information, the information submitted is, to the
best of my knowledge and belief, true, accurate, and complete. I am aware that there are significant
penalties for submitting false information, including the possibility of fine and imprisonment for knowing
violations.
Name: Michael Nuzzolilo
Signature: Mul Mahal
Title: General MudaseR
Date: 5-18-21
ED_019088A_00012854-00116
Culpeper of New England, LLC
Storm Water Pollution Prevention Plan
Inspection / Action Documentation Form
Date of Action: 4-29-20 Time of Day: 2:37 P.N
Name of person performing the inspection or taking action:
Michael Nuzzolilo
Name of person filling out this report:
Michael Nuzz0 / 1 / 0
Infiltration Point ID, Outfall or other location description:
OutFalls # 1, 2, 3 3 Stormdrain
Describe the inspection or action (more than one might apply):
Monthly facility inspection
Inspect sheet flow areas for obstructions or debris
Clean sheet flow areas
Inspect trench drains, drywells, detention basin, pond, or infiltration trench inlets for
oCblesatnr uicntlieotnss
or debris
Training (Describe type of training and persons trained in space provided below)
Annual dry weather flow monitoring (after at least 3 consecutive days of no
precipitation)
No NON-storm water flows to the storm water drainage systems were identified
A NON-storm water flow was discovered (discuss below, further action is
required)
Other (describe)
I myself am the ONLY Person who takes Sample's
For this location,
I Have
Person who works
Here 3 Help with Clead - up From Fall 3 winter. we
go Thro & Replace All HAY bails From the wiNteR 3
Cleart - Up All Debris in and around out fall apea's,
ED_019088A_00012854-00117
Culpeper of New England, LLC
Storm Water Pollution Prevention Plan
Annual Compliance Evaluation Report
Date of Action: 5-2-2020 Time of Day: 9:22 A.M
Name of person performing the inspection or taking action: Michael Nuzzolilo
Inspectors should look for but are not limited to:
Industrial materials, residue or trash that could contaminate stormwater,
Leaks or spills from industrial equipment, drums, barrels, tanks or similar containers,
Unauthorized non - stormwater discharges (or unidentified allowable discharges),
Off - site tracking of industrial materials or sediment where vehicles enter or exit the site,
*
Migrating of raw, final, or waste materials from areas of no exposure to exposed areas,
Evidence of or potential for pollutants to enter the drainage system,
Evidence that all BMP's are operating correctly,
Evidence, at each discharge location, that BMP's are effective in preventing pollutants from
contaminating stormwater discharges.
Observations:
Location(s) of discharge of pollutants from the site # 3 outfAll
Location(s) of BMP's that need to be maintained # 1,233 outfall's # 4 No generation.
Location(s) of BMP's that failed to operate or are inadequate # 4
Location(s) where additional BMP's are needed will Discuss with Proper Perler & MAHOSE Management MYUT
Identify any incidents of noncompliance # 4 outfall Doesn't Produce Que to Locations.
Other:
If no noncompliance items were identified by this inspection, a signature of the following certification
statement shall certify that the facility is in compliance with the SWPPP and the SPDES Multi - Sector
General Permit for Stormwater Discharges Associated with Industrial Activity (GP-0-17-004).
I certify under penalty of law that this document and all attachments were prepared under my direction or
supervision in accordance with a system designed to assure that qualified personnel properly gathered and
evaluated the information submitted. Based on my inquiry of the person or persons who manage the
system, or those directly responsible for gathering the information, the information submitted is, to the
best of my knowledge and belief, true, accurate, and complete. I am aware that there are significant
penalties for submitting false information, including the possibility of fine and imprisonment for knowing
violations.
Name: Michael Nuzzofilo
Signature:
Title: General Manager
Date: 5-2-2020
ED_019088A_00012854-00118
Exhibit 6
Annual Report - - January 28, 2021
ED_019088A_00012854-00119
8/9/22, 7:37 AMNeT Document
UNITED STATES ENVIRONMENTAL PROTECTION AGENCY
NPDESWASHINGTON, DC 20460FORM
FORMEPAANNUAL REPORT FOR STORMWATER DISCHARGES ASSOCIATED WITHApproved OMB No.
6100-28INDUSTRIAL ACTIVITY UNDER THE NPDES MULTI - SECTOR GENERAL PERMIT2040-0300
Permit Information
Report Year: 2021
Reporting Period: 1/1/2021 to 12/31/2021
NPDES ID: MAR05J04L
Facility Information
Facility Name: CULPEPER WOOD PRESERVERS
Facility Point of Contact
First Name Middle Initial Last Name: MICHAELNUZZOLILO
$$$$$$ &&&&&
Phone: 978-368-7667Ext.:
Email: mnuzzolilo@culpeperwood.com
Facility Mailing Address
Address Line 1: 840 STERLING ROAD
Address Line 2:City: LANCASTER
ZIP / Postal Code: 01561State: MA
County or Similar Division: Worcester
General Findings
Provide a summary of your past year's routine facility inspection documentation, including dates (see Part 3.1.6 of the permit). In addition, if you are an operator of an airport facility (Sector S) that is subject to
the airport effluent limitations guidelines, and are complying with the MSGP Part 8.S.9 effluent limitation through the use of non - urea - containing deicers, provide a statement certifying that you do not use
pavement deicers containing urea (e.g., " Urea was not used at [name of airport] for pavement deicing in the past year and will also not be used in 2021. " (Note: Operators of airport facilities that are complying
with Part 8.S.9 by meeting the numeric effluent limitation for ammonia do not need to include this statement.)
ROUTINE FACILITY INSPECTIONS WERE CONDUCTED MONTHLY AS REQUIRED FOR FACILITIES IN SECTOR A2 ON THE FOLLOWING DATES: 1/27/21,
2/4/21, 3/23/21, 4/22/21, 5/12/21, 6/23/21, 7/28/21, 8/16/21, 9/7/21, 10/11/21, 11/16/21, 12/9/21. AT LEAST ONE INSPECTION
(7/28/21 AND 10/11/21) WERE CONDUCTED DURING RAIN EVENTS AS REQUIRED BY THE MSGP. SCHEDULED REPLACEMENT OF HAY BALES FOR SED
IMENT CONTROL WERE ALSO DONE CONCURRENTLY WITH EACH INSPECTION.
THE FACILITY'S PRIMARY STORMWATER POLLUTION CONTROL STRATEGY INVOLVES MANAGEMENT PRACTICES FOR PREVENTING WOOD TREATING SOLU
TION FROM CONTACTING STORMWATER BY ALLOWING PRODUCT TO DRY IN A ROOFED AREA WITH SECONDARY CONTAINMENT BEFORE MOVING IT INTO
THE STORAGE YARD; THOSE MANAGEMENT PRACTICES WERE FOUND TO BE OPERATING EFFECTIVELY DURING EACH INSPECTION. DURING SOME INSP
ECTIONS PERSONNEL OBSERVED THAT STORMWATER AT THE SOUTH EDGE OF THE PLANT HAD FLOWED AROUND THE HAY BALES IN PLACE FOR SEDIM
ENT CONTROL AND FORMED A PUDDLE NEAR OUTFALL 003. THE FACILITY HAS INITIATED A CORRECTIVE ACTION TO REGRADE THE AREA NEAR TH
AT OUTFALL TO PREVENT STORMWATER FLOW FROM BYPASSING THE SEDIMENT CONTROLS. THAT CONSTRUCTION WORK IS SCHEDULED FOR SPRING 2
022.
Provide a summary of your past year's quarterly visual assessment documentation, including dates (see Part 3.2.3 of the permit).
FOUR QUARTERLY VISUAL ASSESSMENTS WERE CONDUCTED ON THE FOLLOWING DATES: 3/23/21, 6/23/21, 9/7/21, 11/16/21. OUTFALLS 2 AND
3 WERE INSPECTED AS OUTFALLS 1 AND 4 HAVE NOT HAD SUFFICIENT FLOW FOR SAMPLING.
QUARTERLY VISUAL ASSESSMENTS NOTED THE PRESENCE OF SUSPENDED SOLIDS IN DISCHARGE AT OUTFALL 003; THIS IS BELIEVED TO BE THE
RESULT OF STORMWATER THAT HAS BEEN OBSERVED FLOWING AROUND THE HAY BALES THAT ARE USED FOR SEDIMENT CONTROL. AS DESCRIBED AB
OVE CORRECTIVE ACTIONS HAVE BEEN INITIATED TO ADDRESS THIS.
SOME QUARTERLY VISUAL ASSESSMENTS ALSO NOTED FOAM IN THE DISCHARGE. THIS LED TO THE FINDING THAT FORK TRUCKS ARE PERIODICALL
Y WASHED USING A SODIUM METASILICATE CLEANING SOLUTION AND THAT THE WASH WATER IS NOT AN AUTHORIZED NON-STORMWATER DISCHARGE
UNDER THE MSGP. THAT DISCHARGE WAS DISCONTINUED IN NOVEMBER 2021, AND IF FORK TRUCKS ARE WASHED AGAIN IN THE FUTURE OPERATOR
S WILL BE INSTRUCTED TO COLLECT THE WASH WATER INSIDE THE FACILITY'S DESIGNED SECONDARY CONTAINMENT AREA TO AVOID A NON-STOR
MWATER DISCHARGE. FACILITY PERSONNEL REPORTED THAT THE FORK TRUCKS BEING WASHED HAD NOT CONTACTED WOOD TREATING SOLUTION SO
NO TREATING SOLUTION WAS DISCHARGED.
Provide a summary of your past year's corrective action and / or additional implementation measures (AIM) documentation (See Part 5.3 of the permit). (Note: If corrective action is not yet completed at the time of
submission of this annual report, you must describe the status of any outstanding corrective action(s).) Note that you must modify your SWPPP based on the corrective actions and deadlines required under
Part 5. Also describe any incidents of noncompliance in the past year or currently ongoing, or if none, provide a statement that you are in compliance with the permit.
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BENCHMARK EXCEEDANCES FOR COPPER HAVE BEEN IDENTIFIED DURING MONITORING AND THE FACILITY IS CURRENTLY IN TIER 2 OF ADDITIONA
L IMPLEMENTATION MEASURES. THE FACILITY HAS INITIATED THE TRIAL IMPLEMENTATION OF STRUCTURAL CONTROLS FOR COPPER IN STORMWAT
ER AND HAS CONTRACTED FOR THE INSTALLATION OF FILTER UNITS NEAR OUTFALL 003 USING SPECIALIZED SORPTIVE MEDIA FOR REMOVAL OF
DISSOLVED COPPER. THE AREA NEAR THIS OUTFALL WILL ALSO BE REGRADED TO PREVENT STORMWATER FLOW FROM BYPASSING THE STRUCTURAL
CONTROLS. CONSTRUCTION WORK IS SCHEDULED FOR SPRING 2022, FOLLOWED BY PERFORMANCE TESTING DURING THE COURSE OF A STORM EVENT
TO EVALUATE THE EFFECTIVENESS OF THE STRUCTURAL CONTROL AND WHETHER USAGE OF SIMILAR SORPTIVE MEDIA IS WARRANTED FOR OTHER O
UTFALLS.
AS DESCRIBED ABOVE THE FACILITY LEARNED OF AN UNAUTHORIZED NON-STORMWATER DISCHARGE FROM THE PERIODIC WASHING OF FORK TRUCKS
THAT HAD NOT CONTACTED WOOD TREATING SOLUTION USING A SODIUM METASILICATE CLEANING SOLUTION. THAT DISCHARGE WAS DISCONTINUED
IN NOVEMBER 2021. CULPEPER WOOD PRESERVERS IS OTHERWISE IN COMPLIANCE WITH THE MULTI - SECTOR GENERAL PERMIT.
Certification Information
I certify under penalty of law that this document and all attachments were prepared under my direction or supervision in accordance with a system designed to assure that qualified personnel properly gathered and evaluated the
information submitted. Based on my inquiry of the person or persons who manage the system, or those persons directly responsible for gathering the information, the information submitted is, to the best of my knowledge and
belief, true, accurate, and complete. I have no personal knowledge that the information submitted is other than true, accurate, and complete. I am aware that there are significant penalties for submitting false information,
including the possibility of fine and imprisonment for knowing violations.
Certified By: Joshua J. Adkins
Certifier Title: EHS Director
Certifier Email: jadkins@culpeperwood.com
Certified On: 01/28/2022 10:42 AM ET
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