HomeMy WebLinkAboutWastewater Management PLan summary1Town of Yarmouth: Comprehensive Wastewater Management Plan Notice of Project Change
Executive Summary
ES.1 Introduction
The Town of Yarmouth has worked diligently to develop a program to address wastewater
management needs to protect drinking water sources, to restore water quality in valu-
able freshwater ponds and saltwater estuaries and to allow for limited smart economic
growth. These efforts and associated recommendations are updated in this Notice of
Project Change (NPC) from the previously approved 2011 Comprehensive Wastewater
Management Plan (CMWP)/Single Environmental Impact Report (SEIR). The Town’s Water
Resources Advisory Committee (WRAC) has worked to update the Town’s CWMP.
Protecting these sources is vital to maintain the quality of life and economic health of
the Town. These efforts have led to recommendations for the Town to implement over
the next 40 years through adaptive management and are intended as guidelines for
the community moving forward as it addresses this costly and complex issue.
ES.2 Project Background and Purpose
The Town of Yarmouth, Massachusetts is submitting this Notice of
Project Change to the previously accepted Comprehensive Wastewater
Management Plan and Single Environmental Impact Report. The
Town received the final certificate for the CWMP/SEIR on August 26,
2011, from the Executive Office of Energy and Environmental Affairs,
Massachusetts Environmental Policy Act (MEPA) Unit. The Final CWMP
addressed Total Maximum Daily Loads (TMDLs) assigned to both Lewis
Bay and Parkers River watersheds. At that time, the Massachusetts
Estuaries Project (MEP) report for the Bass River watershed had
not been finalized and as such a TMDL was not assigned, and the
Barnstable Great Marshes-Bass Hole MEP Report was not yet finalized.
This NPC is being submitted to address the TMDL for the Bass River
watershed and to provide an update on the progress made by the
Town since 2011 regarding their accepted CWMP. Since then, the Town
has assessed regional opportunities and incorporated the Bass River
Watershed into its recommended plan, therefore a lapse of time has not
occurred since the MEPA certificate was issued. The NPC documents will
be submitted concurrently to the Massachusetts Department of Environmental Protection
(MassDEP) so they may complete an environmental review of the project in coordination
with the MEPA Unit and subsequently the Cape Cod Commission (CCC).
2011 CWMP
ExECUTIvE SUMMARY
2 Town of Yarmouth: Comprehensive Wastewater Management Plan Notice of Project Change
This NPC is an extension of a multiphase study that formally began in 2003. The Town of
Yarmouth contracted CDM Smith to coordinate with the Town’s Integrated Water Resources
Planning (IWRP) Committee, and later the Water Resources Advisory Committee (WRAC) to
address the community’s wastewater needs and develop a program for wastewater manage-
ment, mainly focused on nitrogen mitigation.
ES.3 Environmental Review Process and Project Drivers
While Yarmouth’s traditional approach to wastewater handling has been to rely on and
maintain Title 5 on-site septic systems and a septage-only treatment plant to handle solids
from those systems, the current regulatory environment has prompted the Town to revisit this
approach. The Town believes this approach will need to change for a variety of reasons.
First, the Town is increasingly aware of the serious impacts that on-site Title 5 septic systems
have on coastal environments. Fifty years ago, Yarmouth was a seasonal Cape Cod vacation
community, with a much smaller population and far less impact on the surrounding water-
sheds. With every passing year, increasing population densities, fertilized lawns, higher-density
developments and a noticeable shift from seasonal to more year-round use have changed the
character of the town.
Population growth has led to more septic systems and consequently an abundance
of nutrients – in particular nitrogen, an aquatic plant fertilizer – leaching into
estuaries through ground and surface waters. As abundant quantities of these
nutrients are released to the environment, changes in water quality and the buildup
of invasive weed and algae causing fish kills, beach closures, destroying productive
shellfish areas and resulting in aesthetically displeasing waters. These issues inad-
vertently affect coastal ecosystems, the valuable tourist industry, coastal property
values, and the overall quality of life.
A second reason to change the Town’s approach to wastewater handling is the MEP
conducted by MassDEP and the University of Massachusetts (UMass)/Dartmouth
School of Marine Science and Technologies (SMAST) on estuaries in southeastern
Massachusetts. That MEP Report was issued in 2011 and evaluated the pollutant
status and sensitivity of the estuaries through comprehensive water quality testing
and quantitative modeling, with the main focus on nitrogen.
Figure ES-1 shows the Town of Yarmouth’s water resources, including the locations of the
saltwater estuaries and embayments, beaches, ponds and lakes, and water supply wells.
Yarmouth embayments, including Lewis Bay (shared with Barnstable), Parkers River (totally
within Yarmouth), Barnstable Great Marsh/Bass Hole (shared with Barnstable and Dennis), and
Bass River (shared with Dennis), have been evaluated as part of the MEP to determine how
much nitrogen is acceptable to discharge into each estuary. The reports for Lewis Bay, Parkers
Algae Bloom in Mill Pond
ExECUTIvE SUMMARY
3Town of Yarmouth: Comprehensive Wastewater Management Plan Notice of Project Change
Nantucket Sound
BARNSTABLE
YARMOUTH
DENNIS
Columbus
Avenue
Flax
Pond
Thatcher
Town Park
Long
Pond
South
Middle
Sandy
Pond
Wilbur
Park
Dennis
Pond
Gray's
Beach
Bayview
Street Baxter
Avenue Bass
River
Colonial
Acres
Great Island
Ocean Club
Seagull
Bay
Road
Berry Avenue Parkers
River
Windmill
Seaview
Mathews
Pond
Lone Tree
Creek
Mill Pond
Flax
Pond
Dennis Pond
Reservoir
Short Wharf
Creek
Lewis Pond
Bass Creek
Miller
Pond
Lily
Pond
Howes
Pond
Hallets
Mill Pond
Greenough
Pond
Elishas
Pond
Perch
Pond
Bass River
Long
Pond
Bassets
Lot PondLittle
Sandy
Pond
Chase
Garden
Creek
James Pond
Crowell
Pond
Horse
Pond
Halfway Pond
Plashes
Pond Long Pond
Turtle
Pond
Jabinettes
Pond
Big Sandy
Pond
Mill Pond
Follins Pond
Parkers River
Mill Creek
Dinahs Pond
Seine Pond
Clays Creek Whites
Brook
Figure ES-1
Town of Yarmouth
Water Resources
NEWELLJD F:\Yarmouth_MA\Yarmouth_ES-1_Water_Resources.mxd 12/13/2021
Town of Yarmouth, MA
0 0.5 1
Miles
N
Notice of Project Change
1 in = 4,500 ft
Public Water Supply Well
Beaches
MEP Watershed
Lewis Bay Parkers River
Bass River
Chase
Garden
Creek
Barnstable
Harbor
ExECUTIvE SUMMARY
4 Town of Yarmouth: Comprehensive Wastewater Management Plan Notice of Project Change
River, Barnstable Great Marsh/Bass Hole, and Bass River have now been completed. Based on
the MEP studies, MassDEP is expected to issue watershed permits to the Town of Yarmouth
and surrounding communities requiring the towns to remove sufficient quantities of nitrogen
to meet TMDL requirements. Pertinent results from MEP work completed to date have been
summarized in this report and are integrated into the recommended wastewater manage-
ment program for the Town of Yarmouth so that the program removes estimates of sufficient
nitrogen to restore water quality. The MEP models for Lewis Bay, Parkers River, Barnstable
Great Marsh/Bass Hole, and Bass River, and the associated TMDLs, enable the town to strike the
appropriate balance between new sewers in high-density areas and already existing, properly
functioning septic systems in the town’s lower density areas. This approach allows scientists,
engineers and planners to select the appropriate level of technology that each water body
can sustain without over-engineering a workable solution and to arrive at a recommended
program with the highest cost-benefit. It also provides for sewers to be installed in desired
economic development growth areas.
Not only does excess nitrogen affect coastal environments, nitrogen in high concentrations
in groundwater can present a public health concern. Specifically, where nitrogen loads to
groundwater source drinking water wells are too high, United States Environmental Protection
Agency (EPA)-mandated nitrogen thresholds may be exceeded. The Town has concluded that
certain drinking-water supplies in Yarmouth are at risk for high nitrogen levels in the future if
the present wastewater management approach is not implemented.
Finally, the revitalization of Yarmouth’s Route 28 corridor and the South Shore Drive Hotel/
Motel Overlay District provides additional motivation for wastewater management planning.
Land use, traffic, and wastewater planning efforts are intended to revitalize businesses and
communities. The Hotel/Motel Overlay District 2 along South Shore Drive encompasses Motel
properties along Nantucket Sound off South Shore Drive and provides a mechanism for motel
owners to renovate, reconstruct and/or replace their properties by-right to improve our water-
front lodging offerings. These properties are presently limited by how much wastewater they
can adequately treat and dispose of on-site, with local or MassDEP approval. Planning efforts
intend to direct growth in certain areas along Route 28 and South Shore Drive, which will be
supported by existing and planned infrastructure. Wastewater management improvements
are necessary to provide off-site wastewater treatment and effluent disposal for the proposed
revitalization.
ES.4 Water Resource Advisory Committee
The Town of Yarmouth’s Water Resources Advisory Committee (WRAC; formerly referred to as
the IWRP Committee) was formed in October, 2018 to coordinate the wastewater planning
initiative for this NPC. The WRAC’s stated purpose is to investigate ways to involve and educate
the community on issues relating to water resource initiatives in Yarmouth, including water
supply, surface water, groundwater, stormwater and wastewater, with the goal of protecting
and restoring the Town’s fresh and saltwater bodies and its drinking water supplies. The
WRAC members, listed in Table ES-1, are charged with acting as a liaison between the Board
Table ES-1. Water Resources Advisory
Committee (WRAC) Members
Member Representing
Tom Baron Planning Board
Mary Craig Board of Health
John Deliso Lewis Bay Area
Tom Durkin Conservation Commission
Spyro Mitrokostas Member-at-Large
George Perkins Parker’s River Area
Tom Roche Bass River Watershed
Lee Rowley Northside Area
Curt Sears Member-at-Large, Chair
ExECUTIvE SUMMARY
5Town of Yarmouth: Comprehensive Wastewater Management Plan Notice of Project Change
of Selectmen and Town residents regarding water resource initiatives
and financial plans for such initiatives as well as focusing on specific
areas of implementation or other related wastewater, groundwater,
surface water and drinking water matters at the direction of the Board of
Selectmen. The WRAC was supported by several Town staff as needed.
The WRAC Committee held monthly meetings or as required through
the wastewater planning, all of which were open to the public. Each
meeting agenda was posted with the Town Clerk 48 hours before,
and several meetings have been taped and televised via local access
television for the town. WRAC Committee meetings and minutes are also
available for viewing on the Town’s website. The WRAC Committee has
made multiple presentations to the Board of Selectmen public meetings
as well, also available for viewing on the Town’s website.
ES.5 Previous Project Phases and Associated Documents
The Town of Yarmouth 2011 CWMP was completed in eight phases. Phases I through vII which
were completed as part of the Town’s 2011 Comprehensive Wastewater Management Plan and
Single Environmental Impact Report. The Town received the final certificate for the CWMP/SEIR
on August 26, 2011 from the Executive Office of Energy and Environmental Affairs, Massachusetts
Environmental Policy Act Unit. The full CWMP and Final MEPA EENF Certificate can be found on the
Town’s website (http://www.yarmouth.ma.us/1754/Water-Resources)
ES.6 Organization of this NPC
This NPC summarizes the wastewater management plan that was presented in Yarmouth’s CWMP
and presents the recommended revisions to the plan based on the results of the Bass River MEP
report. The report is divided into eight (8) sections. Each section includes information originating
from various wastewater-planning phases, since the analysis of many topics was ongoing from one
phase to the next. The sections are as follows:
Section 1 introduces the need for an NPC and details the purpose, scope, existing conditions,
and the organization of the report.
Section 2 summarizes the Barnstable Great Marsh/Bass Hole and Bass River Watershed
Massachusetts Estuaries Project (MEP) Results and their impact on the wastewater needs
assessment developed in Phase I of the CWMP.
Section 3 provides a summary of the wastewater collection system evaluations (pipelines and
pumping stations) that took place during the CWMP process and presents the recommended
collection system plan resulting from these evaluations with the addition of the needs in the
Bass River watershed.
River, Barnstable Great Marsh/Bass Hole, and Bass River have now been completed. Based on
the MEP studies, MassDEP is expected to issue watershed permits to the Town of Yarmouth
and surrounding communities requiring the towns to remove sufficient quantities of nitrogen
to meet TMDL requirements. Pertinent results from MEP work completed to date have been
summarized in this report and are integrated into the recommended wastewater manage-
ment program for the Town of Yarmouth so that the program removes estimates of sufficient
nitrogen to restore water quality. The MEP models for Lewis Bay, Parkers River, Barnstable
Great Marsh/Bass Hole, and Bass River, and the associated TMDLs, enable the town to strike the
appropriate balance between new sewers in high-density areas and already existing, properly
functioning septic systems in the town’s lower density areas. This approach allows scientists,
engineers and planners to select the appropriate level of technology that each water body
can sustain without over-engineering a workable solution and to arrive at a recommended
program with the highest cost-benefit. It also provides for sewers to be installed in desired
economic development growth areas.
Not only does excess nitrogen affect coastal environments, nitrogen in high concentrations
in groundwater can present a public health concern. Specifically, where nitrogen loads to
groundwater source drinking water wells are too high, United States Environmental Protection
Agency (EPA)-mandated nitrogen thresholds may be exceeded. The Town has concluded that
certain drinking-water supplies in Yarmouth are at risk for high nitrogen levels in the future if
the present wastewater management approach is not implemented.
Finally, the revitalization of Yarmouth’s Route 28 corridor and the South Shore Drive Hotel/
Motel Overlay District provides additional motivation for wastewater management planning.
Land use, traffic, and wastewater planning efforts are intended to revitalize businesses and
communities. The Hotel/Motel Overlay District 2 along South Shore Drive encompasses Motel
properties along Nantucket Sound off South Shore Drive and provides a mechanism for motel
owners to renovate, reconstruct and/or replace their properties by-right to improve our water-
front lodging offerings. These properties are presently limited by how much wastewater they
can adequately treat and dispose of on-site, with local or MassDEP approval. Planning efforts
intend to direct growth in certain areas along Route 28 and South Shore Drive, which will be
supported by existing and planned infrastructure. Wastewater management improvements
are necessary to provide off-site wastewater treatment and effluent disposal for the proposed
revitalization.
ES.4 Water Resource Advisory Committee
The Town of Yarmouth’s Water Resources Advisory Committee (WRAC; formerly referred to as
the IWRP Committee) was formed in October, 2018 to coordinate the wastewater planning
initiative for this NPC. The WRAC’s stated purpose is to investigate ways to involve and educate
the community on issues relating to water resource initiatives in Yarmouth, including water
supply, surface water, groundwater, stormwater and wastewater, with the goal of protecting
and restoring the Town’s fresh and saltwater bodies and its drinking water supplies. The
WRAC members, listed in Table ES-1, are charged with acting as a liaison between the Board
Table ES-1. Water Resources Advisory
Committee (WRAC) Members
Member Representing
Tom Baron Planning Board
Mary Craig Board of Health
John Deliso Lewis Bay Area
Tom Durkin Conservation Commission
Spyro Mitrokostas Member-at-Large
George Perkins Parker’s River Area
Tom Roche Bass River Watershed
Lee Rowley Northside Area
Curt Sears Member-at-Large, Chair
ExECUTIvE SUMMARY
6 Town of Yarmouth: Comprehensive Wastewater Management Plan Notice of Project Change
Section 4 summarizes the wastewater treatment system evaluations and presents the
revised recommended plan for wastewater treatment resulting from continued evaluations.
Section 5 summarizes the effluent recharge site evaluations conducted for the CWMP and
presents the revised recommended effluent recharge sites from continued evaluations.
Section 6 summarizes the CCCs 208 Plan technologies and how they were investigated and
addressed as part of the CWMP and this NPC.
Section 7 presents the revised Recommended Program for wastewater management
in Yarmouth and evaluates alternative management plans. This section describes the
Recommended Program in detail, including its implementation, scheduling, and budgeting.
Section 8 describes the updated environmental benefits, impacts and mitigation measures
of the recommended program, including a discussion of each item addressed on MEPA’s
ENF form and follow-up information in accordance with MEPA’s scope in the Expanded ENF
Certificate.
The appendices contain all of the backup analyses and technical memoranda developed in
relation to this NPC.
ES.7 Evaluation of Estuaries and Embayments
A wastewater needs assessment was performed as the first step of the CWMP for the Town.
Yarmouth has four estuaries located in the MEP study area: Barnstable Great Marsh/Bass Hole,
Bass River, Lewis Bay, and Parkers River.
Information available from the Lewis Bay and Parkers River watershed MEPs was utilized as
part of the initial CWMP assessment finalized in 2011. The Lewis Bay watershed is shared with
Barnstable, and the Parkers River watershed is entirely within Yarmouth. The Town was divided
into multiple areas for evaluation and potential areas that need improved methods of waste-
water treatment and recharge to meet current and future demands and nitrogen loading goals.
The main objective of the needs assessment was to assess the wastewater needs of each area of
Yarmouth, based on available data, and to prioritize these areas according to their level of need.
Since the original needs assessment was performed, additional data from the completed Bass
River Watershed MEP Report and Barnstable Great Marsh/Bass Hole Draft MEP Report became
available. Yarmouth shares the Bass River Watershed with Dennis, and shares the Barnstable
Great Marsh/Bass Hole watershed with Barnstable and Dennis.
ES7.1 Bass River Watershed Evaluation
The Bass River MEP Report became available following the completion of Yarmouth’s 2011
CWMP. The watershed is shared between Dennis and Yarmouth, with Yarmouth being responsi-
ble for approximately 56 percent of the attenuated nitrogen loads in Bass River.
ExECUTIvE SUMMARY
7Town of Yarmouth: Comprehensive Wastewater Management Plan Notice of Project Change
Because septic system loading accounts for about 80 percent of the controllable nitrogen
in the Bass River watershed, septic system nitrogen is the primary source targeted for total
reduction within the contributing watersheds. Overall, 173.5 kg/day, or roughly 63,330 kg/yr,
total attenuated nitrogen was estimated to originate from wastewater within the watershed.
In order to meet threshold total nitrogen loads, it is estimated that the present total septic load
in the whole Bass River watershed would need to be reduced by 59.5 percent, as summarized
in Table ES-2, to meet the targeted thresholds under existing development conditions, as
compared to a 47.4 percent reduction in total nitrogen loading shown in Table ES-1. A map of
the Bass River watershed and the required removals is included in Figure ES-1.
Table ES-1 Comparison of Subembayment Total Attenuated Watershed Loads
and Threshold Loads
Sub-embayment Present Total
Load (kg/day)
Threshold Total
Load (kg/day)
Threshold
% Change
Run Pond 8.384 8.384 0.0%
Bass River - Lower 36.764 36.764 0.0%
School Street Marsh 11.882 11.882 0.0%
Bass River – Middle 67.674 29.833 -55.9%
Grand Cove 7.293 7.293 0.0%
Dinah’s Pond 4.337 0.778 -82.1%
Kelleys Bay 20.126 3.860 -80.8%
Follins Pond 34.121 7.858 -77.0%
Mill Pond and Stream 27.238 7.847 -71.2%
Total 217.8 114.5 -47.4%
Source: Table vIII-3 of the Bass River MEP Report
values in RED indicate that the value is above the standard and must be reduced.
Table ES-2 Decrease in Present Bass River System Attenuated Septic Loading
to Meet Nitrogen Thresholds
MEP Watershed Present Septic
Load (kg/day)
Threshold
Septic Load
(kg/day)
Septic Load
Decrease to Meet
Threshold
(% change)
Run Pond 7.014 7.014 0.0%
Bass River - Lower 29.858 29.858 0.0%
School Street Marsh 9.496 9.496 0.0%
Bass River – Middle 54.512 16.671 -69.4%
Grand Cove 6.159 6.159 0.0%
Dinah’s Pond 3.559 0.000 -100.0%
Kelleys Bay 16.408 0.142 -99.1%
Follins Pond 27.085 0.822 -97.0%
Mill Pond and Stream 19.416 0.025 -99.9%
Total 173.507 70.187 -59.5%
Source: Table vIII-2 page 177 of Bass River MEP Report
ExECUTIvE SUMMARY
8 Town of Yarmouth: Comprehensive Wastewater Management Plan Notice of Project Change
values in RED indicate that the value is above the standard and must be reduced.
As shown in Table ES-2, the finalized Bass River MEP results concluded that approximately
59.5 percent of the total septic load will need to be removed from the watershed, of which
Yarmouth is responsible for approximately 56 percent. This is a much more significant amount
of nitrogen removal than what was initially assumed in Yarmouth’s wastewater needs analysis
(CWMP, 2011). The North and South Bass River study area rankings were re-evaluated based
on these results and the new analysis categorized both the watersheds as Category 1, need
off-site solution. This NPC discusses how the Recommended Program for wastewater manage-
ment was revised to incorporate the North and South Bass River Watershed study areas in the
off-site solution wastewater program.
Additionally, there are four major bridge crossings over the Bass River system: Route 28, Route
6, High Bank Road, and the Cape Cod Rail Trail Bridge.. Three of these four bridge crossings
(Route 6, Route 28, and the Cape Cod Rail Trail Bridge) were analyzed by MEP to determine
potential scenarios to remove the tidal restrictions present by the bridge crossings. Reduction
and removal of these tidal restrictions would increase flushing in the Bass River watershed.
ES7.2 Barnstable Great Marsh/Bass Hole Watershed Evaluation
The draft report titled, ““Linked Watershed-Embayment Model to Determine Critical Nitrogen
Loading Threshold for the Barnstable Great Marshes-Bass Hole Estuarine System” was issued
in June 2017. Figure ES-3 shows the Barnstable Great Marsh/Bass Hole Watershed System in
Yarmouth. Results from the report indicate that nitrogen removal from this watershed will not
be required.
The primary source of nitrogen in the Barnstable Great Marsh/Bass Hole watershed is septic
system effluent, which accounts for a majority of total and controllable nitrogen loading.
However, as mentioned above, the system is not currently experiencing negative impacts
due to this presence of nitrogen and as such is able to accept additional nitrogen without
deleterious impacts. It is estimated that the current total septic load in the Great Marshes/Bass
Hole watershed would need to increase by 53.1 percent, as shown in Table ES-3, to exceed the
threshold load.
Table ES-3 Decrease in Present Great Marshes-Bass Hole System Attenuated
Septic Loading to Meet Nitrogen Thresholds
Sub – Embayment Present Septic
Load (kg/day)
Threshold
Septic Load
(kg/day)
Threshold
Septic Load
Decrease
(% change)
Barnstable Great Marshes – West 26.364 50.737 +92.4%
Barnstable Great Marshes – Mid 19.488 48.719 +150.0%
Barnstable Great Marshes – East 32.397 32.397 0.0%
Millway 7.205 2.522 -65.0%
Bass Hole - West 23.107 30.385 +31.5%
Bass Hole – East 20.822 36.438 +75.0%
Bass Hole 5.847 5.847 0.0%
Total 135.230 207.045 +53.1%
ExECUTIvE SUMMARY
9Town of Yarmouth: Comprehensive Wastewater Management Plan Notice of Project Change
Nantucket Sound
W E I R
C R E E K
KELLEY'S
PONDLONG PONDYARMOUTH
DENNIS
BREWSTER
HARWICH
BASS RIVERSWAN POND RIVERSWAN
POND
KELLEYS
BAY
FOLLINS
POND
MILL POND
AND STREAM
GRAND
COVE
North
Dennis
Wells
Pine
PondBakers
Pond
Flax
Pond
Northwest
Dennis Wells
East West
Dennis Wells
Grassy Pond
Old Bass
River Wells
Simmons Ponds
North
Yarmouth
Wells
North Main
Yarmouth
Wells
Kelleys
Bay LT10
Follins
Pond
LT10
Mill Pond
GT10 Dennis
Weir Stream
LT10 Dennis
Mill Stream
GT10 Dennis
Mill
Stream
LT10
Weir Road
Gauge
LT10
Dinah's
Pond GT10
Bass River
Mid GT10
Yarmouth
Dinah's
Pond
LT10
Follins
Pond GT10
YarmouthMill Stream
GT10 Yarmouth
Mill Pond
GT10 Yarmouth
Mill
Pond
LT10
Kelleys Bay
GT10 Yarmouth
Kelleys
Bay GT10
Dennis
Follins
Pond GT10
Dennis
Bass
River Mid
LT10
Bass River
Mid GT10
Dennis
Fresh
Pond
Fresh
Pond
Gauge
Bass River
Lower LT10
Horsefoot
Cove
Grand Cove
Uncle
Stephans
Pond
Kelleys Pond
School
Street Marsh
Bass River
Lower GT10
Yarmouth
Run Pond
Weir Road
Gauge
GT10
Weir Stream
LT10
Yarmouth
Figure ES-2
Bass River Watershed
Nitrogen Removal Required
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Town of Yarmouth, MA
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N
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1 in = 4,000 ft
Watershed
Bass River
Bass River Subwatersheds
-100.0%
-74.0%
Septic Nitrogen Removal to Meet Threshold/
Total Controllable Nitrogen Removal
to Meet Threshold
0.0%
0.0%
-100%
-82.1%
-99.9%
-71.2%
0.0%
0.0%
ExECUTIvE SUMMARY
10 Town of Yarmouth: Comprehensive Wastewater Management Plan Notice of Project Change
W E I R
C R E E K
LONG PONDBARNSTABLE
YARMOUTH
DENNIS
BarnstableGreatMarshesEast
Millway
BassHoleWest
BassHoleEast
BassHole
Figure ES-3
Barnstable Marshes
Bass Hole Watershed
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Town of Yarmouth, MA
0 0.5 1
Miles
N
Notice of Project Change
1 in = 3,500 ft
Watersheds
Barnstable Marshes/Bass Hole Watershed
Subembayments
ExECUTIvE SUMMARY
11Town of Yarmouth: Comprehensive Wastewater Management Plan Notice of Project Change
Source: Table vIII-2 of the June 2017 Barnstable Great Marshes-Bass Hole MEP Report
The threshold septic loading for the Great Marshes/Bass Hole system is the sum of seven
threshold loads developed in the MEP report for Barnstable Great Marshes-west, Barnstable
Great Marshes-mid, Barnstable Great Marshes-east, Millway, Bass Hole-west, Bass Hole-east,
Bass Hole sub-embayments. Together these seven thresholds combine to give a total threshold
septic load for the watershed. To exceed the requirements of check and sentinel stations,
attenuated septic loading to the system would need to increase by 53.1 percent. Under
buildout conditions, in order to exceed the MEP established threshold total nitrogen loads, it is
estimated that the total buildout load in the Great Marshes-Bass Hole watershed would need
to increase by 10.1%.
ES.8 Recommended Program
The Town of Yarmouth proposed a Comprehensive Wastewater Management Plan
Recommended Program in 2011. Implementation of that program would allow for the town
to meet its water resources management needs, consistent with MEP nitrogen reduction goals
known at that time. However, analysis of the subsequent Bass River watershed MEP results
concluded that updates to the 2011 recommended program would be necessary to fully meet
nitrogen reduction goals. Sections 3, 4, and 5 describe the updates to the recommended
program components for collection systems, wastewater treatment, and effluent recharge,
respectively. This section summarizes the updated CWMP Recommended Plan and discusses
the updated alternatives to this program.
ES.8.1 Recommended Plan: Collection System and Wastewater Flows
The updated recommended sewer collection system plan shown in Figure ES-4 provides a
town-wide perspective of the areas proposed for sewering and locations of the Water Resource
Reclamation Facility (WRRF) and effluent recharge sites. Table ES-4 summarizes the phased
implementation plan which is expected to last a total of 40 years. This plan provides collection,
treatment and effluent recharge for about 3.54 mgd (ADF) of wastewater. This flow is a build-
out flow as discussed in Section 3. The build-out flows were originally developed from the
build-out analysis in the MEP model with assistance from the Yarmouth Planning Department.
In 2019, a town-wide buildout analysis was performed to further refine build-out projections
and related flow estimates.
ExECUTIvE SUMMARY
12 Town of Yarmouth: Comprehensive Wastewater Management Plan Notice of Project Change
Table ES-4 Updated CWMP Recommended Master Plan Sewer and
Wastewater Flow Summary
Phase Watersheds
Served
Proposed
Sewer
Type
Number
of Parcels
Served
Linear Feet
of Pipe
Total Current
Flow1 (gpd)
Total Flow
at Build-out
With I/I (gpd)
1 Lewis Bay/
Parkers River/
Bass River/ Nan.
Sound
Gravity 605 78,000 417,000 910,000
Pressure
vacuum
Force Main
2 Lewis Bay/
Parkers River/
Nan. Sound
Gravity 2,475 162,000 403,000 486,000
vacuum
Pressure
Force Main
3 Lewis Bay/
Parkers River/
Bass River
Gravity 2,125 137,000 390,000 435,000
vacuum
Pressure
Force Main
4 Parkers River/
Bass River
Gravity 1,450 101,000 252,000 290,000
vacuum
Pressure
Force Main
5 Lewis Bay/
Parkers River/
Bass River/ Nan.
Sound
Gravity 1,175 82,000 225,000 280,000
vacuum
Pressure
Force Main
6 Parkers River/
Bass River
Gravity 2,030 144,000 393,000 482,000
vacuum
Pressure
Force Main
7 Bass River Gravity 695 65,000 181,000 226,000
vacuum
Pressure
Force Main
8 Bass River/ Nan.
Sound
Gravity 1,645 144,000 290,000 432,000
vacuum
Pressure
Force Main
12,200 173 miles 2.55 MGD 3.54 MGD
1 Current flow identified through MEP Reports.
The proposed sewer collection system shown in Figure ES-1 has been developed for planning
purposes. Focus should be placed on the first couple of phases which need to be constructed
prior to future phases being built. The type of sewer to be utilized is likely to be evaluated by
town staff after the initial gravity sewers are built. While sewer types shown were selected in
discussions with prior planning committees mainly for cost reasons, there may be a greater
benefit to using a consistent type of sewer versus the hybrid approach. Similarly, the phasing
sequence may change to meet town needs going forward.
ExECUTIvE SUMMARY
13Town of Yarmouth: Comprehensive Wastewater Management Plan Notice of Project Change
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ExECUTIvE SUMMARY
14 Town of Yarmouth: Comprehensive Wastewater Management Plan Notice of Project Change
ES.8.2 Recommended Treatment Technology
The recommended treatment approach is a centralized Water Resource Reclamation Facility
(WRRF) to be located at Buck Island Road as was recommended in the 2011 CWMP and as
shown on Figure ES-4. In selecting the best treatment technology for the proposed facility, the
Town had to consider that the facility would initiate operation with much lower flows than the
design flow projected following installation of all the proposed sewers. Despite this, the major
facility components would need to be constructed during the first phase of sewer installation
to provide the complete level of treatment required to meet the anticipated Groundwater
Discharge Permit requirements and the MEP goals.
The proposed initial capacity of the WRRF is 1.8 MGD of av-
erage daily flow, which is anticipated to be the total buildout
flow for Phases 1 through 3 of the collection system project.
Therefore, the recommended treatment technology for the
first phase of sewering is a new WRRF with threeSequenc-
ing Batch Reactor (SBR) process tanks, with the intent to
construct additional tanks as the collection system expands
Phase 4 to handle flows and loads from the later phases. Final
SBR sizing will be established during design to accommodate
initial flows and loads. The key reasons for constructing a
SBR process are to both minimize the immediate capital and
operating costs and provide the best operational flexibility
associated with the initial low plant flows. The SBR option
is cost-effective, easily expandable, and is able to treat to
stringent limits. Following the SBRs, tertiary treatment
consisting of denitrification filters is also anticipated to
achieve the effluent nitrogen target.
ES.8.3 Recommended Effluent Recharge
A site screening analysis was conducted to identify candidate effluent recharge sites in the
CWMP process. The site screening identified Site R1 at Buck Island Road and Site R2 at the Bass
River Golf Course as potential recharge sites. Both of these sites remain as the recommended
recharge sites in this Notice of Project Change. Site R1 at Buck Island Road has an anticipated
recharge capacity of approximately 1.2 MGD assuming a 3 mg/L concentration of nitrogen
and 30% attenuation, allowing the site to accommodate effluent from the initial phases of the
Recommended Plan. The 2011 Buck Island Road hydrogeologic evaluation determined there is
a potential to recharge up to 2 MGD at the site.
The Parkers River bridge on Route 28 was recently widened (completed in 2021) by MassDOT
as recommended in the 2011 CWMP. This will allow for increased flushing in the Parkers River
embayment resulting in a higher effluent recharge capacity in the watershed. The treated
effluent from the first few phases of the Recommended Plan will be recharged in open infiltra-
tion basins at the Buck Island recharge site. The actual recharge rate possible is dependent on
the hydrogeologic conditions at the site and the actual attenuation rates for nitrogen within
the system. In the future, a permeable reactive barrier (PRB) could be assessed to remove
Buck Island Road Site of Proposed WRRF
ExECUTIvE SUMMARY
15Town of Yarmouth: Comprehensive Wastewater Management Plan Notice of Project Change
additional nitrogen from the effluent. This type of a system utilizes a carbon source within the
reactive barrier that removes nitrogen from effluent under anaerobic conditions. Based on limited
data, certain types of reactive barriers have the ability to consistently reduce treated wastewater
nitrogen levels.
The finalized Bass River MEP results suggested that the Bass River Golf Course (BRGC), Site R2,
could be a feasible recharge option for the town after Site R1 at Buck Island Road reaches its full
capacity. Field work and transient groundwater modeling efforts were conducted by CDM Smith
in 2018 to confirm the previous estimated recharge capacity at the BRGC. An initial assessment of
recharge loading technologies for the BRGC proposed recharge areas was done as well. The BRGC
site has an estimated effluent recharge capacity of approximately 2 to 2.5 MGD so it is sufficient
for recharging the remaining treated effluent.
ES.8.4 Non-Infrastructure Components
Non-infrastructure components of the recommended program include a public participation and
outreach program, fertilizer education, stormwater best management practices (BMPs), inflow
prevention programs, on-site system support, school education programs, and an innovative and
alternative technologies committee.
The Friends of Bass River is conducting the Upper Bass River Watershed Restoration Project,
beginning in 2022. The project “will conduct data gathering and modeling, and develop engi-
neering plans to document and demonstrate the necessary steps to achieve improved water
quality through removal of barriers, increased water exchange, and the reintroduction of 57
acres of wetlands (abandoned cranberry bogs) to the riparian ecosystem.” (source: https://www.
friendsofbassriver.org/new-page)
Public Outreach
Public participation and outreach have been a priority during the Notice of Project Change
process and previous CWMP efforts. Outreach efforts were conducted to gain participation and
feedback from residents and business owners. Buy-in from involved citizens, stakeholders like
business and community groups, and the public at large is vital to gain acceptance of proposals
to fund this water quality effort.
The Town will incorporate components from the vision Plan 2021 in its public outreach docu-
ments. The Yarmouth Community visioning project was undertaken by the Planning Board to
identify values, challenges, and shared vision for Yarmouth’s future. Providing municipal wastewa-
ter was identified as a goal in both the Environment and Economy visions identified in the Plan.
Avenues of public outreach that the WRAC have used and will continue to use throughout
implementation are listed below.
Website
Publications
Mailings
Social Media
Committee Meetings
Community Meetings
Coordination with Groups (i.e., Friends
of Bass River, Yarmouth Chamber of
Commerce)
ExECUTIvE SUMMARY
16 Town of Yarmouth: Comprehensive Wastewater Management Plan Notice of Project Change
Fertilizer Education
The fertilizer education program will focus on ideal application types
and rates of fertilizer use and on resident awareness of the negative
effects of over-fertilization or inappropriate use. The program will
target portions of Yarmouth located upstream from the most sensitive
water sources and may include website resources, handout materials,
collaboration with local landscaping companies, and other regional
and County initiatives for the benefit of the Town.
Stormwater BMPs
The stormwater BMP program will focus on ideal application of BMPs
at drainage features in Yarmouth. The program will target those
portions of town located upstream of the most sensitive water sources
in subwatersheds with the highest nitrogen loads as well as phospho-
rus in freshwater ponds from stormwater and will include several stormwater controls and/or
practices on all new work. As the program is developed, the Town will decide which types of
controls are most appropriate.
Innovative and Alternative Technologies Committee through WRAC
Because of the high costs of providing proven nitrogen removal treatment technology to the
very stringent standards required to meet the proposed TMDLs, there are several innovative
and alternative (I/A) technologies being tested. The currently available I/A technologies either
do not meet the nitrogen removal requirements or their use was not cost effective. However,
development of new technologies should always be monitored and evaluated for incorpora-
tion into this recommended wastewater program. The Yarmouth CWMP Recommended Plan
has been designed with significant flexibility such that it would allow potential technology
improvements to be incorporated in the future as appropriate. The Yarmouth WRAC will
monitor alternative systems going forward.
ES.9 Recommended Plan Costs
Based on the revised Recommended Plan, the opinion of probable project costs (OPPC) have
been updated and are summarized below in Table ES-5.
Stormwater Retention Basin
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17Town of Yarmouth: Comprehensive Wastewater Management Plan Notice of Project Change
Table ES-5 Opinion of Probable Project Costs (OPPC) by Phase
Phase Town Only
Collection
and
Conveyance
System5
Treatment
Facility
OPM Effluent
Recharge
with
Conveyance
and PRB
Non-
Infrastructure
Components
Total
1 $65.4 Mil $79.9 Mil $1.4 Mil $15.6 Mil $.03 Mil $162.4 Mil
2 $59.1 Mil $.03 Mil $59.1 Mil
3 $52.3 Mil $.03 Mil $52.3 Mil
4 $43.6 Mil $26.9 Mil $.5 Mil $27.8 Mil $.03 Mil $98.8 Mil
5 $36.8 Mil $.03 Mil $36.8 Mil
6 $49.0 Mil $.03 Mil $49.0 Mil
7 $21.2 Mil $.03 Mil $21.2 Mil
8 $61.5 Mil $.03 Mil $61.5 Mil
Total
(Rounded)
$389 Mil $107 Mil $1.9 Mil $43.4 Mil $.24 Mil $541 Mil
All costs are projected to Year 2024 with an estimated Engineering News Record (ENR)
Construction Cost Index of 13,060. As discussed in Section 3, an additional 10% contingency
has been added to collection and conveyance costs to reflect increased industry costs.
Additionally, all capital costs include 25% for construction contingency and 15% for engineer-
ing, permitting, and planning.
Estimated annual operations and maintenance (O&M) costs for the recommended program are
shown below in Table ES-6. These costs represent the estimated annual costs to operate and
maintain the entire wastewater program during the first phase and at the final phase with a
buildout flow of 3.54 mgd.
Table ES-6 Estimated Operations and Maintenance Costs
Category Estimated O&M Cost in
Phase 1 (0.43 mgd)
Estimated O&M Cost at
Build-out (3.54 mgd)
Collection System $0.5 Million $ 3.5 Million
WRRF $2.2 Million $ 8.6 Million
Effluent Recharge w/ PRB $0.1 Million $ 0.3 Million
Non-Infrastructure Components $12,000 $12,000
Total $ 2.8 Million $ 12.5 Million
The assumptions used in this estimate are based on operations and maintenance experience at
several similar facilities as well as guidance from the 208 Plan Comparison Costs for Wastewater
Management Systems Applicable to Cape Cod by the Cape Cod Commission issued in 2014.
The Town is continuing to evaluate various cost recovery models with the intent of using a
combination of funding sources to not impact the general tax rate. A potential wastewater
capital cost funding plan for Phase 1 of the program has been developed, with the potential
funding sources as listed below:
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18 Town of Yarmouth: Comprehensive Wastewater Management Plan Notice of Project Change
MassDEP SRF Zero-Percent Loan
Municipal Water Infrastructure Fund, including 0.78% property tax surcharge
Cape & Islands Water Protection Fund
Betterment program
25% capital surcharge on operating rate
Dedication of short-term rental bill revenues
Septage host fee and water operation cost sharing
Board of Selectmen Financial management policies regarding new growth
Free cash when possible
Stimulus funding and other possible grants
ES.10 Climate Change Adaptation and Resiliency and Environmental Justice Stakeholders
The Town is committed to a long term, resilient wastewater solution that allows for the
incorporation of features to address climate change. As part of this NPC, resiliency options
were identified and reviewed in conjunction with the Water Utility Resilience Program and the
Resilient MA Action Team’s “Climate Resilience Design Standards and Guidelines.” These resilien-
cy options are described in detail in Section 8.
Also as part of this NPC, the Town of Yarmouth has reviewed the environmental justice areas
located within five miles of the town-wide project. The 2020 MA Environmental Justice Map
viewer identifies environmental justice populations in Yarmouth, as well as its neighboring
communities of Barnstable and Dennis. The Town has performed public outreach as part of
its wastewater planning efforts. The Town will perform additional public outreach during the
preliminary design stage of each phase of its wastewater program, including environmental
justice outreach. Each phase of the project will ensure compliance with the state’s environmen-
tal justice protocols.
ES.11 Organization of this Notice of Project Change
This Notice of Project Change report is divided into nine (9) sections. The sections are as
follows:
Executive Summary presents an overview of the report and the findings.
Section 1 introduces the changes to the previously approved CWMP and details the
purpose, the scope, existing conditions, and the organization of the report.
Section 2 describes the findings of the MEP Reports for the watersheds not previously
included in the 2011 CWMP.
ExECUTIvE SUMMARY
19Town of Yarmouth: Comprehensive Wastewater Management Plan Notice of Project Change
Section 3 provides a summary and recommendation on the various collection system
options and changes to the Recommended Plan from the 2011 CWMP.
Section 4 provides a summary and recommendations on the wastewater treatment options
and changes from the 2011 CWMP.
Section 5 includes a summary and recommendations of the effluent recharge system
options and changes from the 2011 CWMP.
Section 6 describes the Cape Cod Commission’s 208 Plan and Technology review.
Section 7 details the components of the recommended program including, capital and
O&M costs, phasing, and non-infrastructure components.
Section 8 includes the updated Environmental Impact Analysis and Mitigation plans.