Groundwater
Protection Health Regulation
Regulatory
Authority - M.G.L. c. 111 s. 31 and s. 122
Because groundwater is a source of
drinking water for 251 of 351 communities in the Commonwealth of Massachusetts
the state and local governments share responsibility for maintaining high
quality groundwater in sufficient quantities to meet current and future need.
Board of Health regulations are one way to protect this most important
resource at the local level.
The regulation conforms with the
requirements of the Massachusetts' Drinking Water Regulations, 3 10 CMR
22.21(2), for source approval and with the Water Management Act and its
regulatory permit program for water withdrawals, M.G.L. c.21G and 310
CMR 36.00. In sensitive water supply recharge areas not subject to the
referenced regulations, the town of Belchertown has applied zoning or
non‑zoning controls to the Zone Il area or Interim Wellhead Protection
Area JWPA) for all public water supply sources within the boundaries of the
municipality. Although these regulations and permits require zoning and
non‑zoning controls within the DEP approved Zone H or IWPA, a
municipality may choose to expand the protective zones beyond the Zone R. A
board of health regulation can apply to existing and future land uses, for the
purposes of protecting public health (see M.G.L. c. 111 - s.3 1). This
regulation complements zoning or local bylaw controls for groundwater
protection to provide a more complete suite of water supply protection tools.
These proposed bylaws or regulations are compatible with existing municipal
ordinances, bylaws, and regulations.
This health regulation applies to the
water protection district and the wetlands buffer zones as appear on the
Belchertown zoning map as well as buffers zones which might not appear on the
zoning map due to the fact that the Belchertown zoning map is not an actual
depiction of protected resource areas. Many areas are not included due to
scale, size or other reasons. In those cases, the Massachusetts Orthophotoquad
maps that are of medium scale (1" = 417') will be utilized. The wetland
delineations on these photo-based maps are photointerpreted and thus represent
a very accurate inventory of wetlands but do not replace the wetland boundary
that is determined by an on-site investigation under the Wetlands Protection
Act. Another reference to be
utilized will be past permits
and/or Orders of Conditions by the Conservation Commission. These typically
contain on-site verification of wetland resource areas.
Wetlands
and their vicinity constitute the very worst locations for the dumping of
salts or refuse or for the installation of sanitary landfills, fuel storage or
septic tanks. It is in this area that the zone of aeration is thinnest (in
many wetlands non‑existent for at least several seasons of the year)
producing a considerable reduction in the effectiveness of oxygen,
microorganisms, and plants to screen pollutants from the infiltrating water.
Further, the upper zone of many organic deposits is highly permeable so water
moves through it rapidly to the zone of saturation or to surface drainage
undergoing little filtration or biological / chemical breakdown. Since
ground‑water in the wetlands area is so close to the surface, refuse
installations would, of necessity, be below the water table for at least a
portion of the year and contaminants would be discharged directly to the
ground‑water body where they would undergo little decay. This would be
of concern where wells lower the hydraulic head in or near wetlands or where
wetlands are recharge areas for part of the year. More importantly, the
seasonal flooding that occurs in most wetlands would result in direct contamination of surface water, which
may then drain rapidly into a reservoir or affect biota.
The preservation of wetlands and their environs for ground-water development is consistent with wise land use. It is good practice
to maintain a protected zone around a well for proper sanitation. This is
quite compatible with the preservation of wetlands for wildlife preservation,
aesthetic purposes, or open space within a town.
Although it is important to protect wetland
discharge areas, particularly in the vicinity of wells, it is equally
important to protect the recharge areas.
Both the quantity and quality of water available in an aquifer depend upon the
recharge it receives. Thus the recharge areas of aquifers, which may extend
for many miles beyond areas suitable for well fields, are also important. (Motts, W. and O'Brien, Geology and hydrology of
wetlands in Massachusetts, Publication No. 123, Special
report, Water resources research center, University of Massachusetts at
Amherst).
GROUNDWATER AND RECHARGE PROTECTION REGULATION
Belchertown
BOARD OF HEALTH
Date
of Issuance: May 30, 2002
Section 1. PURPOSE OF REGULATION
The text in
this section of the regulation includes the land use prohibitions in 3 10 CMR
22.21(2)(a) and (b), and additional prohibitions as listed below. Whereas:
siting of land uses that have the potential to release hazardous waste,
petroleum products, or other contaminants significantly increases the risk of
contamination; and poor management practices, accidental discharges, and
improper maintenance of these facilities may lead the release of pollutants;
and discharges of hazardous wastes, leachate, pathogens, and other pollutants
that have repeatedly threatened surface and ground water quality throughout
Massachusetts; and surface and ground water resources in the town of
Belchertown that contribute to the town's drinking water supplies; therefore,
the Town of Belchertown adopts the following regulation, under its authority
as specified in Section H, as a preventative measure for the purposes of
preserving and protecting the Belchertown's drinking water resources from
discharges of pollutants; and minimizing the risk to public health and the
environment to Belchertown due to such discharges.
Section 11. SCOPE OF AUTHORITY
The Town of Belchertown Board of Health
adopts the following regulation pursuant to authorization granted by M.G.L. c.
111 s.31 and s. 122. The regulation shall apply, as specified herein, to all
applicable facilities within the Zone Ils and/or the Interim Wellhead
Protection Areas (IWPA), and to all designated wetland buffer zones. These
regulations supersede all inconsistent
regulations adopted by the Board of Health prior to the effective date.
The
effective date is May 30, 2002, the date of publication in the Sentinel.
Section 111. DEFINITIONS
For the purposes of this regulation,
the following words and phrases shall have the following meanings:
Commercial
fertilizers: Any substance containing one or more
recognized plant nutrients which is used for its plant nutrient content and
which is designed for use, or claimed by its manufacturer to have value in
promoting plant growth. This will include composted municipal sludge of type A
or B including that designated as "Exceptional Quality." Commercial
fertilizers do not include unmanipulated animal and vegetable manures, lime,
limestone, wood ashes, and gypsum.
Department:
The Massachusetts Department of Environmental
Protection.
Discharge:
The accidental or intentional disposal, deposit,
injection, dumping, spilling, leaking, incineration, or placing of toxic or
hazardous material or waste upon or into any land or water so that such
hazardous waste or any constituent thereof may enter the land or waters of the
Commonwealth. Discharge includes, without limitation, leakage of such
materials from failed or discarded containers or storage systems and disposal
of such materials into any on‑site leaching structure or sewage disposal
system.
Hazardous
Material: A product, waste or combination of
substances which because of its quantity, concentration, or physical,
chemical, toxic, radioactive, or infectious characteristics may reasonably
pose a significant, actual, or potential hazard to human health, safety,
welfare, or the environment when improperly treated, stored, transported,
used, disposed or otherwise managed. Hazardous materials include, without
limitation, synthetic organic chemicals, petroleum products, heavy metals,
radioactive or infectious materials, and all substances defined as
"toxic" or "hazardous" under Massachusetts General Laws (M.G.L.)
Chapter 21C and 21E, using the Massachusetts Oil and Hazardous Substance List
(3 10 CMR40.0000). The definition may also include acids and alkalis,
solvents, thinners, and pesticides.
High Groundwater Table Elevation: The maximum highest seasonal elevation of the surface of the zone of saturation that has been historically documented or calculated.
Interim
Wellhead Protection Areas (IWPA): For public supply wells
or well fields that lack a Department approved Zone 111, the Department will
apply an interim wellhead protection area. This interim wellhead protection
area shall be a one‑half mile radius measured from the well or well
field for sources whose approved pumping rate is 100,000 gpd or greater. For
wells that pump less than 100,000 gpd, the IWPA radius is proportional to the
well's approved daily volume following the IWPA Chart as referenced in
Division Water Supply Policy 92-01.
Landfill:
A facility established (in accordance with a valid
site assignment) for the purposes of disposing solid waste into or on the
land, pursuant to 310 CMR 19.006.
Non-sanitary
wastewater: Wastewater discharges from industrial
and commercial facilities containing wastes from any activity other than
collection of sanitary sewage, including, but not limited to, activities
specified in the Standard Industrial Classification (SIC) Codes set forth in 3
10 CMR 15.004(6).
Open
Dump: A facility which is operated or
maintained in violation of the Resource Conservation and Recovery Act (42
U.S.C. 4004(a)(b)), or the regulations and criteria for solid waste disposal.
Recharge
Area: The area through which water enters
an aquifer. Also known as an intake area. The recharge area includes all the
areas over and within 0.25 miles of the designated aquifers and area subject
to protection under M.G.L. ch. 131, section 40, or resource areas regulated
pursuant to 310 CMR 10.21 through 10.66.
Septage:
The liquid, solid, and semi-solid contents of privies, chemical toilets,
cesspools, holding tanks, or other sewage waste receptacles. Septage does not
include any material which is a hazardous waste, pursuant to 3 10 CMR 30.000.
Sludge: The solid, semi-solid, and
liquid residue that results from a process of wastewater treatment or drinking
water treatment. Sludge does not include grit, screening, or grease and oil
which are removed at the headworks of a facility.
Treatment
Works: Any and all devices, processes and
properties, real or personal, used in the collection, pumping, transmission,
storage, treatment, disposal, recycling, reclamation, or reuse of waterborne
pollutants, but not including any works receiving a hazardous waste from off
the site of the works for the purpose of treatment, storage, or disposal.
Use
of Toxic or Hazardous Material: The handling,
generation, treatment, storage, or management of toxic or hazardous materials.
Very Small Quantity Generator: Any public or private entity, other than residential, which produces less than 27 gallons (100 kilograms) a month of hazardous waste or waste oil, but not including any acutely hazardous waste as defined in 3 10 CMR 30.136.
Waste
Oil Retention Facility: A waste oil collection facility
for automobile service stations, retail outlets, and marinas which is
sheltered and has adequate protection to contain a spill, seepage, or
discharge of petroleum waste products in accordance with M.G.L. c. 21.5. 52A.
Wetland
buffer zones: Wetland buffer zones: That area of land
extending 100' (one hundred feet) horizontally outward from the boundary of
any area subject to protection under M.G.L. ch. 131, section 40, or resource
areas regulated pursuant to 310 CMR 10.21 through 10.66.
Section IV. PROHIBITIONS
A. Notwithstanding any land uses which
are otherwise permitted by local, state, and/or other federal laws, the siting
of any of the following is prohibited in the Zone 11, IWPA, wetlands buffer
zones, or recharge areas in Belchertown:
1. landfills,
2. open dumps,
3. sludge, septage monofils, and
4. field storage of commercial
fertilizers
5. stockpiles (disposal) of chemically
treated snow and ice that have been removed from highways and roadways outside
the Zone 11.
B. Facilities for the treatment or
disposal of non‑sanitary wastewater are prohibited, with the following
exceptions:
1. Replacement or repair of an existing
system is exempt if the existing design capacity is not exceeded.
2. Treatment works approved and in
compliance with M.G.L. c.21E and 310 CNIR 40.000 designed for the treatment of
contaminated ground or surface waters.
The city/town should consider whether it is more appropriate to control hazardous waste facilities with a zoning bylaw. Under Chapter 40A, industrial zones are permitted and industrial facilities within an industrial zone may expand;
5
C. Facilities that generate, treat,
store, or dispose of hazardous waste are prohibited, with the following
exceptions:
1. very small quantity
generators,
2. household hazardous waste collection
centers or collection events,
3. waste oil retention facilities, and
4. treatment works for the restoration
of contaminated ground or surface waters in compliance with M.G.L. c.21E and
310 CMR 40.000.
D. Removal of soil, loam, sand, gravel,
or any other mineral substances within six feet of the historical high
groundwater table elevation is prohibited with the following exceptions:
1. substances which are removed and
redeposited within 45 days of removal on site to achieve a final grade greater
than four feet above the historical high water mark; and
2. excavations for the construction of
building foundations or the installation of utilities.
E. Land uses that result in impervious
cover of more than 15% of any
lot, whichever is greater, are prohibited; unless a system of artificial
recharge of precipitation is provided that will not result in the degradation
of groundwater quality.
Section V. CONDITIONAL PROHIBITIONS
The storage of certain waste materials,
chemicals, and petroleum products is prohibited except if contained in
accordance with the following requirements.
1. Storage of sludge and septage
is prohibited unless storage is in compliance with 310 CMR32.00.
2. Storage of roadway de‑icing chemicals (sodium chloride, chemically treated abrasives, or other chemicals) and the storage of chemical fertilizers are both prohibited, unless the storage is in a structure that prevents the generation and release of contaminants or contaminated runoff.
3. Storage of animal manure is
prohibited unless covered or contained in accordance with the standards and
guidelines of the US Soil Conservation Service.
4. Storage of liquid hazardous
materials is prohibited unless the materials are either in a free standing
container within a building outdoors or in a free standing covered container
above ground level with spill containment capacity of 110 % of the volume
stored.
5. Storage of any type of liquid
petroleum products is prohibited, unless any of the following applies:
a. the products are incidental to
normal household use, including outdoor maintenance, or for the heating of a
structure;
b. waste oil retention facilities;
c. emergency
generators; and
d. treatment works in compliance with
M.G.L. c.21E and 310 CMR 40.000 designed for the restoration of contaminated
ground or surface waters.
Storage of the exempted liquid
petroleum products (5. a through 5.d) must be either in a free standing
container within a building outdoors or in a free standing covered container
above ground level with spill containment capacity of I 10 % of the volume
stored.
6. Compliance with all provisions of
this regulation must be accomplished in a manner consistent with Massachusetts
Plumbing, Building, and Fire Code requirements.
Section VI. EFFECTIVE DATES FOR ALL FACILITIES
The effective date of this regulation
is the date posted on the front page of the regulation, which shall be
identical to the date of adoption of the regulation.
1. As of the effective date of the
regulation, all new construction and/or applicable change of use within the
Town Belchertown shall comply with the provisions of this regulation.
2. Certification of conformance with the provisions of this regulation by the Board of Health shall be required prior to issuance of construction and occupancy permits.
The Building Inspector should be
notified once a regulation is approved by the Board of Health.
Section VII. PENALTIES
Penalties may be used as a means to
achieve compliance with the BOH regulations. Effective 1992, maximum fines for
health violations increased. Under Chapter 111, Section 31 (violation of health
regulation) the maximum penalty has increased from $500 to $1000 and Section 122
(violation of nuisance regulations) the maximum penalty has increased from $100
to $1000.
Public education and training may make
it unnecessary to institute a significant penalty program. If sufficient
attention is given to education and training of those affected by the and if
enough lead time is provided for program implementation, it may be possible to
avoid dependency on a penalty system for compliance. Nonetheless, local
enforcement is an essential component of this regulation and it is necessary for
effective groundwater protection. Failure to comply with provisions of this
regulation will result in the levy of fines of not less than $ 200.00, but no
more than $1000.00. Each day's failure to comply with the provisions of this
regulation shall constitute a separate violation.
Section VIII. SEVERABILITY
Each provision of this regulation shall be construed as separate to the end that, if any provision, or sentence, clause or phrase thereto shall be held invalid for any reason, the remainder of that section and all other sections shall continue in full force and effect.
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