HomeMy WebLinkAbout25IWC1-167 Meetinghouse Ln-NarrativeZ:\Tringe\Resubdivision\Wetlands\Narrative.docx 1
APPLICATION OF ROBERT A. TRINGE AND JUDITH M. TRINGE (“APPLICANT”)
TO
TOWN OF MONTVILLE INLAND WETLANDS AND WATERCOURSES
COMMISSION
167 MEETING HOUSE LANE, MONTVILLE, CONNECTICUT
PROJECT AND CONSTRUCTION SEQUENCING NARRATIVE
DATE: FEBRUARY 10, 2025
PROJECT OVERVIEW
The Applicants are the owners of 18.74 acres of land situated on the southeasterly side of
Meeting House Lane in the Town of Montville, Connecticut (the “Property”). The Property is
currently improved with an existing dwelling house, well and on-site septic system located on the
southeasterly side of Meeting House Lane which is occupied by the Applicants. The Applicants
are proposing to re-subdivide the Property to create an additional two (2) building lots; a new lot
which will be a building lot for a future single-family residence (Proposed Lot 050-0B3 containing
2.41 acres); and a second new lot, which will be a building lot to accommodate a future single-
family residence (Proposed Lot 050-0B4 containing 2.15 acres). Proposed Lot 050-0B3 is
encumbered by a small, linear wetland system as delineated on the Boundary and Lot Layout Plan
and Site Development Plan. The Applicants are proposing no regulated activities in conjunction
with this development endeavor, and all activity will occur outside of the established fifty (50’)
foot upland review area and cross-gradient from the wetland system.
In conjunction with the proposed development, the Applicants are seeking a subdivision
review from the Town of Montville Inland Wetlands and Watercourses Commission and a
favorable report to the Town of Montville Planning and Zoning Commission in conjunction with
the resubdivision application pursuant to the provisions of Section 8-26 of the Connecticut General
Statutes.
Wetlands on the project site were delineated by Mark H. Sullivan, Soil Scientist on
December 26, 2017.
SOIL CHARACTERISTICS:
The Property contains a mix of upland and wetland soils. A delineation of the soil and
wetland resource characteristics on the Property is as follows:
UPLAND SOILS:
A. AfB – Agawam Fine Sandy Loam. This gently sloped, well-drained soil is found
on stream terraces and outwash plains. Mapped areas are dominantly irregular in shape and range
mostly 2 to 25 acres. Typically, this Agawam soil has a dark brown, fine sandy loam surface layer
9” thick. The subsoil is dark yellowish-brown fine sandy loam 15” thick. The substratum is light
olive brown and very gravelly coarse sand to a depth of 60” or more. Included within this soil and
mapping are small areas of somewhat excessively drained Merrimac soils, well-drained Haven
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soils, moderately well-drained Ninigret soils and poorly drained Raypol and Walpole soils.
Permeability of the Agawam soil is moderately rapid in the surface layer and subsoil and rapid in
the substratum.
B. Tisbury Soils. The Tisbury soil consists of moderately well-drained soils that
formed in water-sorted sand and gravel. Tisbury soils are found on the landscape on outwash plains
and stream terraces. Slopes range from 0% to 5%. The Tisbury soils are found near well-drained
Haven and Agawam soils, moderately well-drained Ninigret soils, and poorly drained Raypol soils.
The soil stratification of the Tisbury soil is as follows:
0” – 8” Very dark grayish brown silt loam; weak coarse granular
structures; friable; many fine roots; 5% coarse fragments;
strongly acid; abrupt wavy boundary.
8” – 18” Yellowish brown silt loam; weak medium and coarse subangular
blocky structures; very friable; common fine roots; 5% coarse
fragments; strongly acid; clear wavy boundary.
18” – 26” Brownish yellow silt loam; common medium distinct grayish
brown and strong brown mottles; massive; very friable; few
roots; 5% coarse fragments; strongly acid; clear wavy boundary.
26” – 60” Grayish brown very gravelly sand; common medium distinct
strong brown mottles and common medium light brownish gray
mottles; single grain; loose; 60% coarse fragments; strongly acid.
C. Charlton Soil. The Charlton series consists of well-drained, non-stoney to
extremely stoney soils that formed in loamy glacial till. Charlton soils are on upland hills, ridges
and glacial till plains. Slopes range from 3% - 45%. Charlton soils are in a drainage sequence on
the landscape with moderately well-drained Sutton soils and somewhat poorly-drained Leicester
soils. They are near somewhat excessively drained Hollis soils and well-drained Canton,
Narragansett, Agawam and Paxton soils. The soil stratification of the Charlton soil is as follows:
0” – 8” Very dark grayish brown fine sandy loam; weak medium
granular structures; friable; common fine and medium roots;
10% rock fragments; strongly acid; abrupt wavy boundary.
8” – 15” Dark yellowish brown fine sandy loam; weak medium
subangular blocky structures; friable; common fine and medium
roots; 15% rock fragments; medium acid; gradual wavy
boundary.
15” – 24” Yellowish brown fine sandy loam; weak medium subangular
blocky structures; friable; common fine and medium roots; 15%
rock fragments; medium acid; clear wavy boundary.
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24” – 29” Light olive brown fine sandy loam; weak medium subangular
blocky structures; friable; few fine roots; 15% rock fragments;
medium acid; clear wavy boundary.
29” – 60” Grayish brown fine sandy loam; massive; friable; 15% rock
fragments; medium acid.
WETLAND SOILS
A. Ridgebury, Leicester and Whitman Soils.
These nearly level, poorly drained and very poorly drained soils are found in drainage ways
and depressions of glacial till upland hills, ridges, plains and drumloidal landforms. Stones and
boulders cover 8 to 25 percent of the surface. Mapped areas are long and narrow or irregular in
shape and mostly 2 to 40 acres. Slopes range from 0 to 3 percent. The mapped acreage of this
undifferentiated group is about 35 percent Ridgebury soil, 30 percent Leicester soil, 20 percent
Whitman soil and 15 percent other soils. Some mapped areas consist of one (1) of these soils, and
other areas consist of 2 or 3. These soils were mapped together because there are no major
differences in use and management.
The Ridgebury soil has a black, fine sandy loam surface layer 4 inches thick. The subsoil
is gray and brown, mottled fine sandy loam 16 inches thick. The substratum is very firm, brittle,
grayish brown, mottled sandy loam to a depth of 60 inches or more. The Leicester soil has a very
dark gray, fine sandy loam surface layer 6 inches thick. The subsoil is dark grayish brown, grayish
brown and pale olive, mottled fine sandy loam 26 inches thick. The substratum is light olive gray,
mottled gravelly fine sandy loam to a depth of 60 inches or more. The Whitman soil has a black,
fine sandy loam surface layer 9 inches thick. The subsoil is dark grayish brown, mottled fine sandy
loan 7 inches thick. The substratum is very firm, brittle, grayish brown, mottled fine sandy loam
to a depth of 60 inches or more. Included with these soils on the landscape are small areas of
moderately well drained Rainbow, Sutton and Woodbridge soils and very poorly drained Adrian
and Palms soils. The Ridgebury soil has a seasonally high water table at a depth of about 6 inches.
Permeability is moderate or moderately rapid in the surface layer and subsoil and slow or very
slow in the substratum. Runoff is very slow or slow. The Leicester soil has a seasonally high water
table at a depth of about 6 inches. Permeability is moderate or moderately rapid. Runoff is very
slow or slow. The Whitman soils have a high water table at or near the surface for most of the year.
Permeability is moderate or moderately rapid in the surface layer and subsoil and slow or very
slow in the substratum. Runoff is very slow.
GENERAL PROCEDURES
1. Prior to conducting any construction activities on the Property, the Applicant shall meet
with the Montville Wetlands Enforcement Officer and the Montville Zoning Enforcement
Officer to discuss and agree upon the method of installation and maintenance of erosion
and sediment control measures during construction.
2. Subsequent to the meeting described in Paragraph 1 of the General Procedures Section of
this Narrative, the Applicant’s land surveyor shall delineate in the field the limits within
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which construction activities shall occur and will further designate the location for
installation of all erosion and sediment control measures as delineated on plans entitled
“Resubdivision Plan Prepared For Robert A. Tringe & Judith M. Tringe #167
Meetinghouse Lane Montville, Connecticut Lot Improvements – E&S Controls – Details
Project No. 24-111 Drawn By: R.A.D. Date: 10/2/24 Scale: 1” = 40’ Sheet 3 of 3 Advanced
Surveys, LLC. 60 Terry Road, Griswold, CT 06351 Phone – (860) 639-8928” (the “Plan”).
3. Upon agreement of the Montville Wetlands Enforcement Officer and the Montville Zoning
Enforcement Officer, the Applicant shall install erosion control devices and measures as
delineated on the Plan and as formulated at the meeting required pursuant to the provisions
of Paragraph 1 of the General Procedures Section of this Narrative.
4. At such time as all erosion and sediment control measures have been installed in
accordance with the Plan, and in accordance with the requirements of the Montville
Wetlands Enforcement Officer and the Montville Zoning Enforcement Officer enunciated
at the meeting described in Paragraph 1 of the General Procedures Section hereof, the
Applicant shall contact the Montville Wetlands Enforcement Officer and Montville Zoning
Enforcement Officer to perform an on-site inspection of said erosion and sediment control
measures. In no event shall soil disturbance occur, or the Applicant engage in other
construction activities other than clearing, until such time as the Montville Wetlands
Enforcement Officer and Montville Zoning Enforcement Officer have reviewed and
approved the installation of all erosion and sediment control measures.
5. All erosion and sediment control measures shall be inspected at least weekly while
construction is ongoing, and after every storm event resulting in a discharge and repaired
and maintained as necessary.
6. If any erosion or sediment control measure fails or are not installed or maintained in
accordance with the Plan or the directives of the Montville Wetlands Enforcement Officer
and Montville Zoning Enforcement Officer, the Applicant shall be required to cease all
construction activities on the lot on which construction is ongoing until such time as said
erosion and sediment control measures have been installed in accordance with the plan or
the directives of the Montville Wetlands Enforcement Officer or the Montville Zoning
Enforcement Officer and approval of the same has been certified by the Montville
Wetlands Enforcement Officer and the Montville Zoning Enforcement Officer.
7. William J. Pieniadz, 157 Simpson Lane, Oakdale, Connecticut 06370 (860) 848-2372
(telephone) (860) 608-9890 (cellular telephone) e-mail: bill@pandhconstruction.com shall
be the party responsible for compliance with all erosion and sediment control measures in
conjunction with all construction activities on the project site.
8. It is anticipated that construction of improvements on both proposed lots will commence
during the late Spring of 2025 and continue for a period of approximately six (6) months.
9. During the stabilization period (after construction on each of Proposed Lots 050-0B3 and
050-0B4 has been completed but prior to certification of approval by the Montville
Wetlands Enforcement Officer and the Montville Zoning Enforcement Officer for the
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removal of erosion and sediment control measures), all erosion and sediment control
measures shall be maintained in proper working order. All erosion and sediment control
measures shall be inspected and maintained and/or repaired, as necessary, on a weekly
basis during the stabilization period and after each storm occurrence.
10. During the stabilization period, any erosion which occurs shall be immediately repaired by
the Applicant, reseeded with the seeding mixes set forth in the Construction Sequencing
Sections of this Narrative and restabilized.
11. Once stabilization has been completed, and certification thereof obtained in writing from
the Montville Wetlands Enforcement Officer and Montville Zoning Enforcement Officer,
all erosion and sediment control measures shall be removed by the Applicant.
CONSTRUCTION SEQUENCING – TYPICAL
1. The Applicant shall clear, but not grub, within the limits of clearing delineated on each lot.
2. The Applicant shall remove the surface soil from the area for the construction of the
construction entrance for each lot as delineated on the Plan.
3. The Applicant shall install a construction entrance for each lot in accordance with the
“Construction Entrance” Detail delineated on the Plan.
4. The Applicant shall install a single row of silt fence or a woodchip berm at the down
gradient limits of disturbance on each lot.
5. Upon the completion of installation of erosion and sediment control measures, the
Applicant, or its successor, as the case may be, shall contact the Montville Wetlands
Enforcement Officer and the Montville Zoning Enforcement Officer to perform an
inspection of the installation of erosion and sediment control measures. Other than the
construction of the anti-tracking pad, no soil shall be disturbed until such time as the
installation of erosion and sediment control measures has been approved by the Montville
Wetlands Enforcement Officer and the Montville Zoning Enforcement Officer.
6. The Applicant shall strip the surface soil in the area of construction of the dwelling house,
yard and driveway on each lot. Surface soil shall be retained on each lot for eventual use
in the stabilization of disturbed areas. Surface soil stockpiles shall be stabilized by
installing a single row of silt fence around each stockpile location. The stockpile shall be
constructed at a slope not to exceed 3:1 and shall be stabilized by seeding with an annual
ryegrass mix and mulch. The annual ryegrass mix shall be applied at a rate of 40 pounds
per acre. Mulch shall be applied at the rate of 80 pounds per 1,000 square feet, and shall be
spread by hand or with a mulch blower. In conjunction with the clearing of each lot, stumps
shall either be (i) ground in place or (ii) removed to a location approved, in advance, by
the Zoning Enforcement Officer and Wetlands Enforcement Officer of the Town of
Montville. No stumps shall be buried on site.
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7. The cellar hole shall be excavated. Sufficient material shall be retained on site for
backfilling the foundation. Additional material shall be transported from the site.
8. Footings shall be poured in the cellar hole and thereafter, foundation walls shall be poured
subsequent to the approval of the footings by the Building Official of the Town of
Montville.
9. Upon completion of the construction of the foundation, footing drains shall be installed.
10. Upon completion of installation of the footing drains, the foundation and footings shall be
backfilled with stored material.
11. Construction of the dwelling house shall be completed.
12. Upon the completion of construction of improvements, all disturbed areas shall be
stabilized by loaming the same with not less than four (4”) inches of topsoil obtained from
the surface soil stockpile. Areas to be seeded will be prepared by spreading ground
limestone equivalent to 50 percent calcium plus magnesium oxide applied at a rate of 100
pounds per 1,000 square feet. Fertilizer (10-10-10) is to be applied at a rate of 15 pounds
per 1,000 square feet. Seeding shall be applied with a mix of Kentucky Bluegrass applied
at a rate of 20 pounds per acre, Creeping Red Fescue applied at a rate of 20 pounds per acre
and Perennial Ryegrass applied at a rate of 5 pounds per acre for a total application of 45
pounds per acre. After seeding, the areas seeded shall be stabilized with hay mulch
immediately applied at a rate of 80 pounds per 1,000 square feet and anchored by tracking.
Seeding shall only occur between April 1 and June 15 and August 15 to October 1.
13. Once all seeded areas have been thoroughly stabilized and cut with two cuttings, erosion
and sediment control measures shall be removed.