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310 Mass. Reg. 10.58
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Current through Register 1447, July 9, 2021
Section 10.58 - Riverfront Area
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(1) Preamble. Riverfront areas are likely to be significant to protect the private or public
water supply; to protect groundwater; to provide flood control; to prevent storm damage; to
prevent pollution; to protect land containing shellfish; to protect wildlife habitat; and to
protect the fisheries. Land adjacent to rivers and streams can protect the natural integrity of
these water bodies. The presence of natural vegetation within riverfront areas is critical to
sustaining rivers as ecosystems and providing these public values. The riverfront area can
prevent degradation of water quality by filtering sediments, toxic substances (such as heavy
metals), and nutrients (such as phosphorus and nitrogen) from stormwater, nonpoint
pollution sources, and the river itself. Sediments are trapped by vegetation before reaching
the river. Nutrients and toxic substances may be detained in plant root systems or broken
down by soil bacteria. Riverfront areas can trap and remove disease -causing bacteria that
otherwise would reach rivers and coastal estuaries where they can contaminate shellfish beds
and prohibit safe human consumption. Natural vegetation within the riverfront area also
maintains water quality for fish and wildlife.
Where rivers serve as water supplies or provide induced recharge to wells, the riverfront area
can be important to the maintenance of drinking water quality and quantity. Land along
rivers in its natural state with a high infiltration capacity increases the yield of a water supply
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riverfront areas provides shade to moderate water temperatures and slow algal growth,
which can produce odors and taste problems in drinking water.
Within riverfront areas, surface water interaction with groundwater significantly influences
the stream ecosystem. The dynamic relationship between surface and groundwater within
the "hyporheic zone" sustains communities of aquatic organisms which regulate the flux of
nutrients, biomass and the productivity of organisms including fish within the stream itself.
The hyporheic zone extends to greater distances horizontally from the channel in large,
higher order streams with alluvial floodplains, but the interaction within this zone is
important in smaller streams as well.
By providing recharge and retaining natural flood storage, as well as by slowing surface water
runoff, riverfront areas can mitigate flooding and damage from storms. The root systems of
riverfront vegetation keep soil porous, increasing infiltration capacity. Vegetation also
removes excess water through evaporation and transpiration. This removal of water from the
soil allows for more infiltration when flooding occurs. Increases in storage of floodwaters can
decrease peak discharges and reduce storm damage. Vegetated riverfronts also dissipate the
energy of storm flows, reducing damage to public and private property.
Riverfront areas are critical to maintaining thriving fisheries. Maintaining vegetation along
rivers promotes fish cover, increases food and oxygen availability, decreases sedimentation,
and provides spawning habitat. Maintenance of water temperatures and depths is critical to
many important fish species. Where groundwater recharges surface water flows, loss of
recharge as a result of impervious surfaces within the riverfront area may aggravate low flow
conditions and increase water temperatures. In some cases, summer stream flows are
maintained almost exclusively from groundwater recharge. Small streams are most readily
impacted by removal of trees and other vegetation along the shore.
Riverfront areas are important wildlife habitat, providing food, shelter, breeding, migratory,
and overwintering areas. Even some predominantly upland species use and may be seasonally
dependent on riverfront areas. Riverfront areas promote biological diversity by providing
habitats for an unusually wide variety of upland and wetland species, including bald eagles,
osprey, and kingfishers. Large dead trees provide nesting sites for bird species that typically
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connective function, from activities that create barriers to wildlife movement within
riverfront areas, results in habitat fragmentation and causes declines in wildlife populations.
Wildlife must also be able to move across riverfront areas, between uplands and the river.
Vernal pools are frequently found within depressions in riverfront areas. These pools are
essential breeding sites for certain amphibians which require isolated, seasonally wet areas
without predator fish. Most of these amphibians require areas of undisturbed woodlands as
habitat during the non -breeding seasons. Some species require continuous woody vegetation
between woodland habitat and the breeding pools. Depending on the species, during non -
breeding seasons these amphibians may remain near the pools or travel % mile or more from
the pools. Reptiles, especially turtles, often require areas along rivers to lay their eggs. Since
amphibians and reptiles are less mobile than mammals and birds, maintaining integrity of
their habitat is critical.
In those portions so extensively altered by human activity that their important wildlife
habitat functions have been effectively eliminated, riverfront areas are not significant to the
protection of important wildlife habitat and vernal pool habitat.
(2)Definitions, Critical Characteristics and Boundaries.
(a) A Riverfront Area is the area of land between a river's mean annual high water line and
a parallel line measured horizontally. The riverfront area may include or overlap other
resource areas or their buffer zones. The riverfront area does not have a buffer zone.
1. A river is any natural flowing body of water that empties to any ocean, lake, pond, or
other river and which flows throughout the year. Rivers include streams (see 310 CMR
10.04: Stream) that are perennial because surface water flows within them throughout
the year. Intermittent streams are not rivers as defined herein because surface water
does not flow within them throughout the year. When surface water is not flowing within
an intermittent stream, it may remain in isolated pools or it may be absent. When
surface water is present in contiguous and connected pool/riffle systems, it shall be
determined to be flowing. Rivers begin at the point an intermittent stream becomes
perennial or at the point a perennial stream flows from a spring, pond, or lake.
Downstream of the first point of perennial flow, a stream normally remains a river
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b. A river or stream shown as intermittent or not shown on the current USGS map or
more recent map provided by the Department, that has a watershed size greater than
or equal to one square mile, is perennial.
c. A stream shown as intermittent or not shown on the current USGS map or more
recent map provided by the Department, that has a watershed size less than one
square mile, is intermittent unless:
i. The stream has a watershed size of at least % (o.5o) square mile and has a
predicted flow rate greater than or equal to o.oi cubic feet per second at the 99%
flow duration using the USGS Stream Stats method. The issuing authority shall find
such streams to be perennial; or
ii. When the USGS StreamStats method cannot be used because the stream does not
have a mapped and digitized centerline (including but not limited to streams located
in the following basins: North Coastal Basin, Taunton Basin, Buzzards Bay Basin,
Cape Cod and Islands Basin, and that portion of the South Coastal Basin that is
south of the Jones River sub -basin), and the stream has a watershed size of at least
(o.5o) square mile, and the surficial geology of the contributing drainage area to
the stream at the project site contains 759 or more stratified drift, the issuing
authority shall find such streams to be perennial. Stratified drift shall mean sand and
gravel deposits that have been layered and sorted by glacial meltwater streams. Areal
percentages of stratified drift may be determined using USGS surficial geologic
maps, USGS Hydrological Atlases, Massachusetts Geographical Information System
(MassGIS) surficial geology data layer, or other published or electronic surficial
geological information from a credible source.
d. Notwithstanding 310 CMR io.58(2)(a)i.a. through c., the issuing authority shall find
that any stream is intermittent based upon a documented field observation that the
stream is not flowing. A documented field observation shall be made by a competent
source and shall be based upon an observation made at least once per day, over four
days in any consecutive 12 month period, during a non -drought period on a stream not
significantly affected by drawdown from withdrawals of water supply wells, direct
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submitted to the issuing authority with a statement signed under the penalties of
perjury attesting to the authenticity and veracity of the field notes, photographs or
video and other credible evidence. Department staff, conservation commissioners, and
conservation commission staff are competent sources; issuing authorities may
consider evidence from other sources that are determined to be competent.
e. Rivers include the entire length and width to the mean annual high-water line of the
major rivers (Assabet, Blackstone, Charles, Chicopee, Concord, Connecticut,
Deerfield, Farmington, French, Hoosic, Housatonic, Ipswich, Merrimack, Millers,
Nashua, Neponset, Parker (Essex County), Quinebaug, Shawsheen, Sudbury, Taunton,
Ten Mile, and Westfield).
f. Rivers include perennial streams that cease to flow during periods of extended
drought. Periods of extended drought for purposes of 310 CMR io.00 shall be those
periods, in those specifically identified geographic locations, determined to be at the
"Advisory" or more severe drought level by the Massachusetts Drought Managment
Task Force, as established by the Executive Office of Energy and Environmental Affairs
and the Massachusetts Emergency Management Agency in Zoos, in accordance with
the Massachusetts Drought Management Plan (MDMP). Rivers and streams that are
perennial under natural conditions but are significantly affected by drawdown from
withdrawals of water supply wells, direct withdrawals, impoundments, or other
human -made flow reductions or diversions shall be considered perennial.
g. Human -made canals (e.g., the Cape Cod Canal and canals diverted from rivers in
Lowell and Holyoke) and mosquito ditches associated with coastal rivers do not have
riverfront areas.
h. Where rivers flow through lakes or ponds, the Riverfront Area stops at the inlet and
begins again at the outlet. A water body identified as a lake, pond, or reservoir on the
current USOS. map or more recent map provided by the Department, is a lake or pond,
unless the issuing authority determines that the water body has primarily riverine
characteristics. When a water body is not identified as a lake, pond, or reservoir on the
current USGS. map or more recent map provided by the Department, the water body
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Great Ponds (i.e., any pond which contained more than ten acres in its natural state, as
calculated based on the surface area of lands lying below the natural high water mark;
a list is available from the Department) are never rivers.
2. Mean Annual High-water Line of a river is the line that is apparent from visible
markings or changes in the character of soils or vegetation due to the prolonged
presence of water and that distinguishes between predominantly aquatic and
predominantly terrestrial land. Field indicators of bankfull conditions shall be used to
determine the mean annual high-water line. Bankfull field indicators include but are not
limited to: changes in slope, changes in vegetation, stain lines, top of pointbars, changes
in bank materials, or bank undercuts.
a. In most rivers, the first observable break in slope is coincident with bankfull
conditions and the mean annual high-water line.
b. In some river reaches, the mean annual high-water line is represented by bankfull
field indicators that occur above the first observable break in slope, or if no observable
break in slope exists, by other bankfull field indicators. These river reaches are
characterized by at least two of the following features: low gradient, meanders,
oxbows, histosols, a low -flow channel, or poorly -defined or nonexistent banks.
c. In tidal rivers, the mean annual high-water line is coincident with the mean high
water line determined under 310 CMR 10.23.
3. The Riverfront Area is the area of land between a river's mean annual high-water line
measured horizontally outward from the river and a parallel line located 200 feet away,
except that the parallel line is located:
a. 25 feet away in Boston, Brockton, Cambridge, Chelsea, Everett, Fall River, Lawrence,
Lowell, Malden, New Bedford, Somerville, Springfield, Winthrop, and Worcester;
b. 25 feet away in densely developed areas, as designated by the Secretary of the
Executive Office of Energy and Environmental Affairs pursuant to 301 CMR io.00:
Densely Developed Areas; and
c. ioo feet away for new agricultural and aquacultural activities.
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stops at a perpendicular line at the upstream end of the culvert and resumes at the
downstream end. When a river contains islands, the riverfront area extends landward
into the island from and parallel to the mean annual high-water line.
(b) The physical characteristics of a Riverfront Area as described in 310 CMR 10.58(2) (a)
are critical to the protection of the interests specified in 310 CMR io.58(1).
(c) The boundary of the Riverfront Area is a line parallel to the mean annual high-water
line, located at the outside edge of the riverfront area. At the point where a stream
becomes perennial, the riverfront area begins at a line drawn as a semicircle with a 2oo
foot (25 foot in densely developed areas; ioo foot for new agriculture) radius around the
point and connects to the parallel line perpendicular to the mean annual high-water line
which forms the outer boundary. When a river flows into coastal waters or an embayment,
the river shall end at the mouth of coastal river line as delineated on the current mouth of
coastal river map series maintained by the Department, subject to revisions after public
notice and referred to as the Massachusetts Mouth of Coastal River Maps. If a mouth of
coastal river line is not delineated on the current map series, the issuing authority shall
determine the mouth of coastal river line in accordance with the Department's most
current Mouth of Coastal River Policy. A mouth of coastal river line shown on the
Department's mouth of coastal river map series is not evidence that a stream is perennial;
such a determination shall only be made pursuant to 310 CMR io.58(2) (a)1.
(3)Presumption. Where a proposed activity involves work within the riverfront area, the
issuing authority shall presume that the area is significant to protect the private or public
water supply; to protect the groundwater; to provide flood control; to prevent storm damage;
to prevent pollution; to protect land containing shellfish; to protect wildlife habitat; and to
protect fisheries.
The presumption is rebuttable and may be overcome by a clear showing that the riverfront
area does not play a role in the protection of one or more of these interests. In the event that
the presumption is deemed to have been overcome as to the protection of all the interests,
the issuing authority shall make a written determination to this effect, setting forth its
grounds on Form 6. Where the applicant provides information that the riverfront area at the
site of the activity does not play a role in the protection of an interest, the issuing authority
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not overcome, the applicant shall prove by a preponderance of the evidence that there are no
practicable and substantially equivalent economic alternatives to the proposed project with
less adverse effects on the interests identified in M.O.L. c.131 § 4o and that the work,
including proposed mitigation, will have no significant adverse impact on the riverfront area
to protect the interests identified in M.O.L. C. 131 § 40. In the event that the presumption is
partially overcome, the issuing authority shall make a written determination setting forth its
grounds in the Order of Conditions and the partial rebuttal shall be taken into account in the
application of 310 CMR io.58(4) (d)i.a. and c.; the issuing authority shall impose conditions in
the Order that contribute to the protection of interests for which the riverfront area is
significant.
(a) Protection of Other Resource Areas. The work shall meet the performance standards
for all other resource areas within the riverfront area, as identified in 310 CMR 10.30
(Coastal Bank),10.3a (Salt Marsh), 10.55 (Bordering Vegetated Wetland), and 10.57 (Land
Subject to Flooding). When work in the riverfront area is also within the buffer zone to
another resource area, the performance standards for the riverfront area shall contribute
to the protection of the interests of M.O.L. c. 131, § 40 in lieu of any additional
requirements that might otherwise be imposed on work in the buffer zone within the
riverfront area.
(b)Protection of Rare Species. No project may be permitted within the riverfront area
which will have any adverse effect on specified habitat sites of rare wetland or upland,
vertebrate or invertebrate species, as identified by the procedures established under 310
CMR io.59 or 10.37, or which will have any adverse effect on vernal pool habitat certified
prior to the filing of the Notice of Intent.
(c)Practicable and Substantially Equivalent Economic Alternatives. There must be no
practicable and substantially equivalent economic alternative to the proposed project with
less adverse effects on the interests identified in M.O.L. c. 131 § 40.
1.Definition of Practicable. As set forth in 310 CMR 10.04, an alternative is practicable
and substantially equivalent economically if it is available and capable of being done
after taking into consideration costs, existing technology, proposed use, and logistics, in
light of overall project purposes. Available and capable of being done means the
alternative is obtainable and feasible. Project purposes shall be defined generally (e.g.,
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proposed use or project purpose in the Notice of Intent nor the Order of Conditions
should specify the number of rooms, bedrooms, etc. within a building). Transactions
shall not be arranged to circumvent the intent of alternatives analysis review. The four
factors to be considered are:
a. Costs, and whether such costs are reasonable or prohibitive to the owner. The
owner means the individual or entity which owns the area where the activity will occur
or which will implement the project purpose. Cost includes expenditures for a project
within the riverfront area, such as land acquisition, site preparation, design,
construction, landscaping, and transaction expenses. Cost does not include
anticipated profits after the project purpose is achieved or expenditures to achieve the
project purpose prior to receiving an Order with the exception of land acquisition
costs incurred prior to August 7,1996. In taking costs into account, the issuing
authority shall be guided by these principles:
i. The cost of an alternative must be reasonable for the project purpose, and cannot
be prohibitive.
ii. Higher or lower costs taken alone will not determine whether an alternative is
practicable. An alternative for proposed work in the riverfront area must be a
practicable and substantially equivalent economic alternative (i.e., will achieve the
proposed use and project purpose from an economic perspective).
iii. In considering the costs to the owner, the evaluation should focus on the
financial capability reasonably expected from the type of owner (e.g., individual
homeowner, residential developer, small business owner, large commercial or
industrial developer) rather than the personal or corporate financial status of that
particular owner. Applicants should not submit, nor should issuing authorities
request, financial information of a confidential nature, such as income tax records or
bank statements.
iv. Issuing authorities may require documentation of costs, but may also base their
determinations on descriptions of alternatives, knowledge of alternative sites,
information provided by qualified professionals, comparisons to costs normally
associated with similar projects, or other evidence. Any documentation of costs
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date technology or the best designs, measures, or engineering practices that have been
developed and are commercially available);
c.The Proposed Use. This term is related to the concept of project purpose. In the
context of typical single family homes, the project purpose (construction of a single
family house) and proposed use (family home) are virtually identical. In the context of
projects where the purpose implies a business component, such as residential
subdivision, commercial, and industrial projects, the proposed use typically requires
economic viability. Practicable and substantially equivalent economic alternatives
include alternatives which are economically viable for the proposed use from the
perspective of site location, project configuration within a site, and the scope of the
project. In the context of publically financed projects, the proposed use includes
consideration of legitimate governmental purposes (e.g., protection of health and
safety, providing economic development opportunities, or similar public purposes);
and
d.Logistics. Logistics refers to the presence or absence of physical or legal
constraints. Physical characteristics of a site may influence its development. Legal
barriers include circumstances where a project cannot meet other applicable
requirements to obtain the necessary permits at an alternative site. An alternative site
is not practicable if special legislation or changes to municipal zoning would be
required to achieve the proposed use or project purpose. An alternative is not
practicable if the applicant is unable to obtain the consent of the owner of an
alternative site for access for the purpose of obtaining the information required by the
Notice of Intent or of allowing the issuing authority to conduct a site visit.
2.Scope of Alternatives. The scope of alternatives under consideration shall be
commensurate with the type and size of the project. The issuing authority shall presume
that alternatives beyond the scope described below are not practicable and therefore
need not be considered. The issuing authority or another party may overcome the
presumption by demonstrating the practicability of a wider range of alternatives, based
on cost, and whether the cost is reasonable or prohibitive to the owner; existing
technology; proposed use; and logistics in light of the overall project purpose.
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b. The area under consideration for practicable alternatives is limited to the lot, the
subdivided lots and any adjacent lots formerly or presently owned by the same owner
for:
L activities associated with the construction or expansion of a single family house on
a lot recorded after August 1, 1996;
ii. any expansion of an existing structure, including enlargement of the footprint of
any structure or the addition of associated structures for single family homes (e.g., a
garage) on lots recorded after August 1, 1996;
iii. any activity other than the construction or expansion of a single family house
where the applicant owned the lot before August 7,1996, including the creation of a
real estate subdivision but excluding public projects, and the applicant will
implement the project purpose;
iv. new agriculture or aquaculture projects;
v. any activity by a public entity when funds for the purchase of the site for the
project purpose have been appropriated through action of the appropriate municipal
board or state agency prior to the August 7,1996; or
vi. any lot shown on a definitive subdivision plan approved under M.G.L. c. 41, §§ 81K
to 8iGG, provided there is a recorded deed restriction limiting the total alteration to
S000 square feet or io%, whichever is greater, of the riverfront area allocated to the
lots within the entire subdivision.
c. Except as allowed under 310 CMR 10.58(4)(c)2.b., the area under consideration for
practicable alternatives extends to the original parcel and the subdivided parcels, any
adjacent parcels, and any other land which can reasonably be obtained within the
municipality for:
L activities associated with residential subdivision or housing complexes,
institutional, industrial, or commercial projects; or
ii. activities conducted by municipal government.
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for Determination or Notice of Intent, within the municipality.
d. Alternatives extend to any sites which can reasonably be obtained within the
appropriate region of the state for:
L residential, institutional, commercial, or industrial activities required to evaluate
off -site alternatives in more than one municipality in an Environmental Impact
Report under M.G.L. C. 30, §§ 61 through 62H, or an alternatives analysis conducted
by the Corps of Engineers for a Section 404 permit under the federal Clean Water
Act, 33 U.S.C.1251 et seq., and used for 401 Water Quality Certification under 314
CMR 9.00: 401 Water Quality Certification for Discharge of Dredged or Fill Material,
Dredging, and Dredged Material Disposal in Waters of the United States Within the
Commonwealth; or
ii. activities conducted by district, county, state or federal government entities.
The area to be considered is the service area within the governmental unit boundary
or jurisdictional authority, or the municipality if there is no defined service area,
consistent with the project purpose.
3.Evaluation of Alternatives. The applicant shall demonstrate that there are no
practicable and substantially equivalent economic alternatives as defined in 310 CMR
io.58(4)(c)1., within the scope of alternatives as set forth in 310 CMR io.58(4)(c)2., with
less adverse effects on the interests identified in M.G.L. c. 131 § 40. The applicant shall
submit information to describe sites and the work both for the proposed location and
alternative site locations and configurations sufficient for a determination by the issuing
authority under 310 CMR io.58(4) (d). The level of detail of information shall be
commensurate with the scope of the project and the practicability of alternatives.
Where an applicant identifies an alternative which can be summarily demonstrated to be
not practicable, an evaluation is not required.
The purpose of evaluating project alternatives is to locate activities so that impacts to
the riverfront area are avoided to the extent practicable. Projects within the scope of
alternatives must be evaluated to determine whether any are practicable. As much of a
project as feasible shall be sited outside the riverfront area. If siting of a project entirely
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substantially equivalent adverse impacts. If an alternative would result in no identifiable
difference in impact, the issuing authority shall eliminate the alternative. If there would
be no less adverse effects on the interests identified in M.O.L. c. 131, § 40, the proposed
project rather than a practicable alternative shall be allowed, but the criteria in 310 CMR
io.58(4)(d) for determining no significant adverse impact must still be met. If there is a
practicable and substantially equivalent economic alternative with less adverse effects,
the proposed work shall be denied and the applicant may either withdraw the Notice of
Intent or receive an Order of Conditions for the alternative, provided the applicant
submitted sufficient information on the alternative in the Notice of Intent.
(d)No Significant Adverse Impact. The work, including proposed mitigation measures,
must have no significant adverse impact on the riverfront area to protect the interests
identified in M.O.L. c. 131, § 40.
1. Within 20o foot riverfront areas, the issuing authority may allow the alteration of up
to 500o square feet or io% of the riverfront area within the lot, whichever is greater, on a
lot recorded on or before October 6, 1997 or lots recorded after October 6, 1997 subject
to the restrictions of 310 CMR 10.58(4) (c)2.b.vi., or up to io% of the riverfront area
within a lot recorded after October 6,1997, provided that:
a. At a minimum, a ioo foot wide area of undisturbed vegetation is provided. This area
shall extend from mean annual high-water along the river unless another location
would better protect the interests identified in M.O.L. c. 131 § 40. If there is not a 100
foot wide area of undisturbed vegetation within the riverfront area, existing vegetative
cover shall be preserved or extended to the maximum extent feasible to approximate a
ioo foot wide corridor of natural vegetation. Replication and compensatory storage
required to meet other resource area performance standards are allowed within this
area; structural stormwater management measures may be allowed only when there is
no practicable alternative. Temporary impacts where necessary for installation of
linear site -related utilities are allowed, provided the area is restored to its natural
conditions. Proposed work which does not meet the requirement of 310 CMR io.58(4)
(d)i.a. may be allowed only if an applicant demonstrates by a preponderance of
evidence from a competent source that an area of undisturbed vegetation with an
overall average width of ioo feet will provide equivalent protection of the riverfront
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c. Proposed work does not impair the capacity of the riverfront area to provide
important wildlife habitat functions. Work shall not result in an impairment of the
capacity to provide vernal pool habitat identified by evidence from a competent
source, but not yet certified. For work within an undeveloped riverfront area which
exceeds 5,000 square feet, the issuing authority may require a wildlife habitat
evaluation study under 310 CMR io.6o.
d. Proposed work shall not impair groundwater or surface water quality by
incorporating erosion and sedimentation controls and other measures to attenuate
nonpoint source pollution.
The calculation of square footage of alteration shall exclude areas of replication or
compensatory flood storage required to meet performance standards for other
resource areas, or any area of restoration within the riverfront area. The calculation
also shall exclude areas used for structural stormwater management measures,
provided there is no practicable alternative to siting these structures within the
riverfront area and provided a wildlife corridor is maintained (e.g. detention basins
shall not be fenced).
2. Within 25 foot riverfront areas, any proposed work shall cause no significant adverse
impact by:
a. Limiting alteration to the maximum extent feasible, and at a minimum, preserving
or establishing a corridor of undisturbed vegetation of a maximum feasible width.
Replication and compensatory storage required to meet other resource area
performance standards are allowed within this area; structural stormwater
management measures shall be allowed only when there is no practicable alternative;
b. Providing stormwater management according to standards established by the
Department;
c. Preserving the capacity of the riverfront area to provide important wildlife habitat
functions. Work shall not result in an impairment of the capacity to provide vernal
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incorporating erosion and sedimentation controls and other measures to attenuate
nonpoint source pollution.
3. Notwithstanding the provisions of 310 CMRio.58(4)(d)1. or 2., the issuing authority
shall allow the construction of a single family house, a septic system if no sewer is
available, and a driveway, on a lot recorded before August 7,1996 where the size or shape
of the lot within the riverfront area prevents the construction from meeting the
requirements of 310 CMR io.58(4)(d)1. or 2., provided that:
a. The lot can be developed for such purposes under the applicable provisions of other
municipal and state law; and
b. The performance standards of 310 CMR io.58(4)(d) are met to the maximum extent
feasible. In difficult siting situations, the maximum extent of yards around houses
should be limited to the area necessary for construction. Except where the lot contains
vernal pool habitat or specified habitat sites of rare species, a wildlife habitat
evaluation study shall not be required.
4. Notwithstanding the provisions of 310 CMR io.58(4)(d)1. or 2., the issuing authority
may allow the construction of a commercial structure of minimum feasible dimension,
on a lot recorded before August 7, 1996 where the size or shape of the lot within the
riverfront area prevents the construction from meeting the requirements of 310 CMR
io.58(4)(d)1. or 2., only if:
a. The lot can be developed for such purposes and cannot be developed for any other
purposes under the applicable provisions of other municipal and state law;
b. The work is not eligible for 310 CMR io.58(5); and
c. The performance standards of 310 CMR io.58 (4) (d)1. or 2. are met to the maximum
extent feasible.
(5)Redevelopment Within Previously Developed Riverfront Areas; Restoration and
Mitigation. Notwithstanding the provisions of 310 CMR io.58(4) (c) and (d), the issuing
authority may allow work to redevelop a previously developed riverfront area, provided the
proposed work improves existing conditions. Redevelopment means replacement,
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previously developed riverfront areas shall conform to the following criteria:
(a) At a minimum, proposed work shall result in an improvement over existing conditions
of the capacity of the riverfront area to protect the interests identified in M.G.L. c. 131 § 40.
When a lot is previously developed but no portion of the riverfront area is degraded, the
requirements of 310 CMR io.58(4) shall be met.
(b) Stormwater management is provided according to standards established by the
Department.
(c) Within zoo foot riverfront areas, proposed work shall not be located closer to the river
than existing conditions or ioo feet, whichever is less, or not closer than existing
conditions within 25 foot riverfront areas, except in accordance with 310 CMR io.58(5) (f)
or (g).
(d) Proposed work, including expansion of existing structures, shall be located outside the
riverfront area or toward the riverfront area boundary and away from the river, except in
accordance with 310 CMR io.58(5)(f) or (g).
(e) The area of proposed work shall not exceed the amount of degraded area, provided that
the proposed work may alter up to io% if the degraded area is less than io% of the
riverfront area, except in accordance with 310 CMR io.58(5) (f) or (g).
(f) When an applicant proposes restoration on -site of degraded riverfront area, alteration
may be allowed notwithstanding the criteria of 310 CMR io.58 (5) (c), (d), and (e) at a ratio
in square feet of at least 1:1 of restored area to area of alteration not conforming to the
criteria. Areas immediately along the river shall be selected for restoration. Alteration not
conforming to the criteria shall begin at the riverfront area boundary. Restoration shall
include:
1. removal of all debris, but retaining any trees or other mature vegetation;
z. grading to a topography which reduces runoff and increases infiltration;
3. coverage by topsoil at a depth consistent with natural conditions at the site; and
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the same general area of the river basin, alteration may be allowed notwithstanding the
criteria of 310 CMR io.58(5) (c), (d), or (e) at a ratio in square feet of at least z:1 of
mitigation area to area of alteration not conforming to the criteria or an equivalent level of
environmental protection where square footage is not a relevant measure. Alteration not
conforming to the criteria shall begin at the riverfront area boundary. Mitigation may
include off -site restoration of riverfront areas, conservation restrictions under M.G.L. c.
184, §§ 31 through 33 to preserve undisturbed riverfront areas that could be otherwise
altered under 310 CMR io.00, the purchase of development rights within the riverfront
area, the restoration of bordering vegetated wetland, projects to remedy an existing
adverse impact on the interests identified in M.G.L. c. 131, § 40 for which the applicant is
not legally responsible, or similar activities undertaken voluntarily by the applicant which
will support a determination by the issuing authority of no significant adverse impact.
Preference shall be given to potential mitigation projects, if any, identified in a River Basin
Plan approved by the Secretary of the Executive Office of Energy and Environmental
Affairs.
(h) The issuing authority shall include a continuing condition in the Certificate of
Compliance for projects under 310 CMR io.S8(5)(f) or (g) prohibiting further alteration
within the restoration or mitigation area, except as may be required to maintain the area in
its restored or mitigated condition. Prior to requesting the issuance of the Certificate of
Compliance, the applicant shall demonstrate the restoration or mitigation has been
successfully completed for at least two growing seasons.
(6)Notwithstanding the Provisions of 310 CMR io.S$(i) through (5)., Certain Activities or
Areas Are Grandfathered or Exempted from Requirements for the Riverfront Area:
(a) Any excavation, structure, road, clearing, driveway, landscaping, utility line, rail line,
airport owned by a political subdivision, marine cargo terminal owned by a political
subdivision, bridge over two miles long, septic system, or parking lot within the riverfront
area in existence on August 7,1996. Maintenance of such structures or areas is allowed
(including any activity which maintains a structure, roads (limited to repairs, resurfacing,
repaving, but not enlargement), clearing, landscaping, etc. in its existing condition)
without the filing of a Notice of Intent for work within the riverfront area, but not when
such work is within other resource areas or their buffer zones except as provided in 3io
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(b) Certain minor activities as identified in 310 CMR io.o2(2) (b)1.
(c) On -site sewage disposal systems in existence on August 7,1996 and the repair or
upgrade of existing systems in compliance with 310 CMR 15.000: The State Environmental
Code, Title 5: Standard Requirements for the Siting, Construction, Inspection, Upgrade
and Expansion of On -site Sewage Treatment and Disposal Systems and for the Transport
and Disposal of Septage. New construction of a system under 310 CMR 15.00o must
comply with 310 CMR io.58, subject to the presumption for the siting of systems in 310
CMR io.o3.
(d) The expansion of structures, airports, and marine cargo terminals, provided they are
owned by a political subdivision and the expansion activity was physically begun on or
before November 1, 1996.
(e) Projects for which a draft environmental impact report was prepared and submitted
pursuant to M.O.L. C. 30, § 62B, on or before November 1, 1996, or as extended by the
Department for just cause but no later than December 31,1996.
(f) Projects for which a building permit conforming to local requirements was filed on or
before October 1, 1996 and granted on or before April 1, 1997, or as extended by the
conservation commission for just cause by no more than 6o days.
(g) The road and infrastructure shown on a definitive subdivision plan approved or
endorsed under M.O.L. c. 41, § 81U, on or before August 1, 1996. Activities on the
subdivided lots are subject to 310 CMR 10.58 unless they received a building permit under
310 CMR io.58(6)(f).
(h) Construction, expansion, repair, restoration, alteration, replacement, operation and
maintenance of public or private local or regional wastewater treatment plants and their
related structures, conveyance systems, and facilities, including utility lines.
(i) Structures and activities subject to a M.O.L. c. 91 waterways license or permit, or
authorized prior to 1973 by a special act, are exempt, provided the structure or activity is
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the Scenic Rivers Act.
(k) Activities within an Historic Mill Complex.
310 CMR 10.58
Amended by Mass Register Issue 12,72, eff. 10/24/2014.
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Section 10.57 - Land Subject to Flooding
(Bordering and Isolated Areas)
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Section 10.59 - Estimated Habitats of Rare
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