Code of Maine Rules
10 - DEPARTMENT OF HEALTH AND HUMAN SERVICES
144 - DEPARTMENT OF HEALTH AND HUMAN SERVICES - GENERAL
Chapter 241 - SUBSURFACE WASTEWATER DISPOSAL RULE
Section 144-241-6 - APPLICATION FOR DISPOSAL SYSTEM PERMIT
Universal Citation: 10 ME Code Rules ยง 144-241-6
Current through 2024-38, September 18, 2024
A. GENERAL
1. The Subsurface
Wastewater Disposal System Application (HHE-200 Form) and all other required
forms must be completed on forms developed by the Department for permits to
install disposal systems. The application must be complete and include, but is
not limited to, the following minimum information as outlined in the following
sections. Except for soils and system design information, the owner/applicant
or authorized agent is responsible for accuracy of the information provided in
the application:
2. Page one of the
HHE-200 form:
a. Property Location,
Owner/Applicant Information;
b.
Permit Information;
c. Design
Details including the projected design flow of wastewater and method of
calculation; and the geodetic latitude and longitude of the disposal field
center, expressed as degrees, minutes, and seconds to an accuracy of ±
30 feet and referenced to in the NAD 83 datum; and
d. The Site Evaluator
Statement.
3. Page two of
the HHE-200 form:
a. The Site Plan must be
drawn at a scale that clearly depicts the following site features that directly
affect the system design and compliance with this rule, and if practical,
within the following distances within at least a 100-foot radius around systems
with design flows less than 1,000 gallons per day, 200-foot radius around
systems with design flows between 1,000 and 2,000 gallons per day, and at least
a 300-foot radius around engineered systems (systems with design flows of 2,000
gallons per day or more) and depict the following:
i. Property boundaries: The boundaries of the
lot as indicated by the property owner;
ii. Existing manmade features: Locations of
existing and proposed structures, roadways, water wells and disposal fields on
the same lot and on abutting or neighboring lots to show compliance with the
applicable setbacks;
iii. Water
bodies: Location of all surface water bodies, natural and artificial, and all
springs;
iv. Wetlands: The
boundaries of any potential wetland area;
v. Locations of all observation
holes;
vi. The location of the
proposed system and existing disposal system if present including, but not
limited to, disposal fields, septic tank, pump/dosing tanks and grease
interceptors and connecting piping (a supplemental site plan may be included
should additional space be required);
vii. Surface water diversions: Location of
existing and proposed surface water diversions;
viii. Site location map;
ix. North arrow; and
x. Graphic Scale: Each design on this page
must include a graphic scale.
b. Soil Profile Description and Soil
Condition Logs, pursuant to Section
5:
i.
Soil profile and condition, limiting factor and depth to limiting
factor;
ii. Ground Slope: Magnitude
and direction of the maximum ground slope at the observation
hole.
4. Page
three of the HHE-200 form:
a. The Subsurface
Wastewater Disposal Plan must be drawn at a scale that clearly depicts the
following:
i. The location and type of the
proposed system including, but not limited to, disposal fields, pump/dosing
tanks, distribution pipes, connecting piping, fill material extensions with
their shoulders and limits, septic tanks, grease interceptors and curtain
drains;
ii. Elevations: The
original ground elevation at the highest point along the uphill edge of each
disposal field, and the original ground elevation of the four corners of each
disposal field, all referenced to the elevation reference point. The number of
ground surface elevation measurements taken within and around a disposal field
must be sufficient to adequately determine the required elevation of the
disposal field and the extent of the fill material extension;
iii. Elevation Reference Point: The location
and description of a system elevation reference point (ERP) set at elevation
zero and located outside the fill extension areas (preferably within 100 feet
of the field). When feasible, the ERP must be established at an easily located,
reasonably-expected-to-be-permanent feature, (for example, a fire hydrant, a
surveying monument, a structure, etc.) When such a feature is not available,
the site evaluator shall set their own reasonably-expected-to-be-permanent
feature for the ERP, (for example, using a grade stake with rebar in a flagged
tree), which must be shown on the design or in specific notes as "no alteration
or termination without site evaluator's approval". The distance in inches of
the ERP above ground level at the ERP location must also be indicated.
Elevations must be given in inches above or below the ERP except for large
systems, those greater than 1,000 GPD, which may use a reference point set to
the datum for the entire project and may use elevations in feet and decimal
(tenths of feet).
iv. System ties:
three measurements from two or more known horizontal reference points or two
measurements from one horizontal reference point with compass bearings for each
horizontal measurement, to a minimum of two proposed disposal field corners.
System ties must be located outside the fill extension areas and preferably
within 100 feet of the disposal field(s). When feasible, the system ties must
be established at an easily located, reasonably-expected-to-be-permanent
feature, (for example, a fire hydrant, a surveying monument, or a structure).
When such a feature is not available, the site evaluator must set their own
reasonably-expected-to-be-permanent feature for tie points, (for example, using
a grade stake with rebar or setting a nail in a flagged tree), which must be
shown on the design or in specific notes as "no alteration or termination
without site evaluator's approval". Alternatively, system tie details may be
shown on page 2;
v. Staked Corners:
All four corners of the disposal field must be staked by the site evaluator
and/or engineer. Wooden stakes or wire flags are recommended to use as
stakes;
vi. Cross-section line: a
line running across the proposed disposal field (perpendicular to the long axis
of the field) which identifies the location of the cross-section diagram for
the disposal field;
vii. The limits
of the fill extension must be shown for each corner of the disposal area with
dimensions shown; and
viii. Scale:
Each design must include a graphic scale.
b. Backfill Requirements: Depths of fill
material required at each corner of each disposal field.
c. Construction Elevations: The elevation of
the bottom of each disposal field, the top of the distribution pipes or
proprietary disposal devices within each disposal field and finish grade
elevation.
d. Disposal Field
Cross-Section: Cross-section diagrams must be drawn for each proposed disposal
field at a scale that clearly depicts the following features:
i. Original ground surface with notes for
site preparation including scarification and transitional horizon;
ii. Height and width of disposal field stone
or proprietary devices with dimensions;
iii. Pipes and on-center spacing with
dimensions;
iv. Depths of fill
material required;
v. Fill crown
slope and shoulders with dimensions;
vi. Limits of all fill extensions with
dimensions:
5.
Proprietary Products: The site evaluator shall clearly indicate on the HHE-200
form or on an attachment to same, his or her relationship with a company or
concern that sells or distributes proprietary devices.
6. Applicable Laws, Ordinances, and
Regulations: The completed HHE-200 Form must conform to all provisions of
applicable laws, ordinances, and regulations, including those administered by
public water systems.
7. The LPI
may authorize changes to the location(s) of treatment tanks, lift stations,
building sewers, distribution boxes, drop boxes, and force mains provided that
applicable minimum setback distances are maintained. Such alterations must be
documented by the LPI.
B. LOCATION, DEPTH, AND MINIMUM NUMBER OF OBSERVATION HOLES
1. General:
Because Maine soil conditions can change dramatically within a few feet, more
than one observation hole is often necessary to allow a site evaluator to
better define the true soil conditions beneath a proposed disposal field.
Observation holes used for design purposes must be located at representative
points clearly within the footprints of proposed non-engineered subsurface
wastewater disposal fields.
2.
Minimum number of observation holes: The number of observation holes must be
sufficient to determine the soil and site characteristics beneath the entire
disposal field.
3. Minimum depth of
observation holes: The minimum depth of observation holes is based upon the
soil horizons and conditions present at the site of a proposed disposal field,
as follows:
a. Hydraulically restrictive
horizons: Observation holes must extend at least 12 inches into the
hydraulically restrictive horizon to check for bedrock except that no
excavation is required greater than 48 inches in depth.
b. Seasonal ground water table: Observation
holes must extend at least 12 inches below the seasonal ground water table to
check for bedrock except no excavation is required greater than 48 inches in
depth.
4. Dig Safe Law:
The "Dig Safe Law" requires notification if other than hand tools are utilized
to dig observation holes (See
23 MRS
§
3360-A).
Disclaimer: These regulations may not be the most recent version. Maine may have more current or accurate information. We make no warranties or guarantees about the accuracy, completeness, or adequacy of the information contained on this site or the information linked to on the state site. Please check official sources.
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