No land area in the Township shall be developed so that:
A.Â
The rate of stormwater runoff occurring at that area is increased
over what occurs there under existing conditions.
B.Â
The drainage of adjacent areas is adversely affected.
C.Â
Soil erosion during and after development is increased over what
naturally occurs there.
D.Â
Soil absorption and groundwater recharge capacity of the area is
decreased below what occurs under existing conditions.
E.Â
The natural drainage pattern of the area is significantly altered.
In order to duplicate as nearly as possible natural drainage
conditions, the regulation and control of stormwater runoff and erosion
for any land area to be developed shall be through on-site water detention
and/or ground absorption systems, which include but are not limited
to the following:
A.Â
Detention areas, which may be depressions in parking areas, excavated
basins, basins created through use of curbs, stabilized earth berms
or dikes or any other form of grading which serves to temporarily
impound and store water.
B.Â
Rooftop storage through temporary impoundment and storage of stormwater
on flat or slightly pitched building rooftops by use of drain outlets
which restrict the stormwater runoff from the roof surface.
C.Â
Dry wells or leaching basins which control stormwater runoff, ground
absorption and temporary storage.
D.Â
Porous asphalt pavement, which preserves the natural ground absorption
capacity of a site and provides a subsurface reservoir temporary storage
of stormwater.
E.Â
Any system of porous media, such as gravel trenches drained or porous
wall or perforated pipe, which temporarily stores and dissipates stormwater
through ground absorption.
F.Â
Any combination of the above-mentioned techniques which serves to
limit stormwater runoff from a given site to what presently occurs.
G.Â
Preservation of natural vegetation.
A.Â
Stormwater detention facilities shall be designed to contain an amount
equal to the increase in volume of runoff which would result from
development of any site during storm frequencies of one-, five-, ten-,
twenty-five-, fifty- and one-hundred-year storm events. The volume
of runoff shall be computed on the basis of the total rainfall which
produced the flood of record for the area involved and shall be equivalent
to the rainfall excess, as previously defined. The total rainfall
which produced the flood of record shall be determined from accurate
local records of the United States Department of Commerce, National
Weather Service, or by calculations using accepted engineering design
techniques.
B.Â
Design of the detention basin must demonstrate that stormwater runoff
from the site is so controlled that on-site and off-site erosion is
neither caused nor worsened and that the potential of downstream flooding
is not increased from the proposed development. In calculating the
foregoing, volumes and rates for one-, five-, ten-, twenty-five-,
fifty- and one-hundred-year storm frequencies having durations producing
maximum runoff rates before and after the proposed development. The
changes of runoff rates and volumes, to be caused by alterations in
land use and time of concentration. The plans for disposition of stormwater,
either by retention or detention on site, or by means of channeling
detail, so as to protect downstream property. A description of potential
flood damages, including a summary of flood stages from state and
federal sources and an erosion and sedimentation control for both
the construction phase and post-construction phase, including a review
by the Morris County Soil Conservation Service, is required.
C.Â
The runoff coefficients shall be determined for each site for both
existing and proposed conditions, and the difference in the same shall
be used to compute the volume of rainfall excess for design of stormwater
detention facilities. The volume for design is equal to the depth
of the rainfall excess multiplied by the area of the site. If any
such facility will contain water under normal conditions, the amount
so contained shall not be counted in calculating the capacity required
for the detention of water for the design storm. Rainfall intensity
shall be as recommended by the Board's engineer.
D.Â
In the case of detention facilities utilizing porous media for ground
absorption, such as dry wells, porous pavement or the like, the volume
of the porous media shall be large enough to contain the total volume
of rainfall excess within the voids. Ground, absorption systems shall
be used only where the infiltration rate of the receiving soil is
acceptable is determined by percolation tests and soil borings to
determine the soil characteristics and groundwater table elevations
or as determined by the Board's engineer. Provisions shall be made
to contain overflow of such systems on site or to surface drain the
overflow in such a way as not to adversely affect any other property.
If detention facilities utilizing surface impoundment, such as detention
basins or rooftop storage, are used, sufficient volume to fully contain
the total volume of rainfall excess shall be provided. The outlets
of such facilities shall be designed to limit the maximum discharge
rate of stormwater runoff to what occurs at the site under existing
conditions and shall discharge in such a way as not to adversely affect
any other property. If rooftop storage is proposed, the weight of
the impounded water on the roof shall be accounted for in the structural
design of the building, and the roof shall be designed to provide
maximum protection against leakage. If berms or dikes are used to
create the impounding area, they shall be adequately stabilized and
the slopes protected with vegetative cover paving or riprap to protect
against failure or breaching.
E.Â
If a combination of different stormwater detention techniques is
used, combined volume of the systems shall be large enough to fully
contain the total volume of rainfall excess.
F.Â
Stormwater detention facilities shall be constantly maintained by
the owner to ensure continual functioning of the systems at design
capacity and to prevent the health hazards associated with debris
buildup and stagnant water. In no case shall water be allowed to remain
in any facility long enough to constitute a mosquito-breeding disease
or any other type of health problem, unless approved as a multifunction
facility to include water such as a pond. If the land or stormwater
detention facility or facilities are proposed to be dedicated to the
Township and said dedication is accepted by the Township Council,
the procedures for the construction, dedication and acceptance and
maintenance of such facilities set forth in this chapter, including
but not limited to performance and maintenance bonds, inspections,
etc., shall govern.
G.Â
Detention and sediment and erosion control facilities shall be designed
in conformance with the Standards for Soil Erosion and Sediment Control
in New Jersey of the New Jersey Soil Conservation Commission as approved
by the Board's engineer or the Morris Soil Conservation District under
agreement, except where the Board's engineer has determined that conditions
peculiar to a certain site warrant exception.
H.Â
Sediment and erosion control measures shall be installed prior to
any other site development, shall apply to all aspects of the proposed
development and shall be in operation during all stages of development.
Increased runoff and sediment resulting from modified soil and surface
conditions caused by the proposed development shall be minimized and,
where possible, retained on site.
A.Â
This section presents the hydrologic method to be used by Mine Hill
Township for developing inflow hydrographs and determining maximum
release rates for proposed detention basins. It should be noted that,
wherever possible, stream flow records should be utilized in determining
design flows, and the hydrologic method presented in this section
will only be used when such records are unavailable.
B.Â
Mine Hill Township adopts the hydrologic methods of the Soil Conservation
Service (SCS) as the basis for calculations, the SCS publication "Urban
Hydrology for Small Watersheds," Technical Release No. 55, June 1986,
as published by the United States Department of Agriculture, or as
amended. Further, the SCS Type III twenty-four-hour design rainfall
distribution as presented in TR-55 is to be utilized.
C.Â
Briefly, the procedure for developing inflow and outflow hydrographs
is as follows:
(1)Â
Determine tributary drainage area to proposed detention basin
in square miles.
(2)Â
Determine the ground conditions and convert this to a runoff
curve number (CN).
(3)Â
Obtain the twenty-four-hour design rainfall in inches for the
given storm (see Table I, below).
(4)Â
Convert the twenty-four-hour rainfall into inches of runoff
using the computed CN and the SCS runoff equation.
(5)Â
Multiply the drainage area in square miles from Step 1 by the
inches of runoff computed in Step 4 to obtain a constant multiplier
with units of square miles-inches.
(6)Â
Determine the time of concentration to the proposed basin utilizing
TR-55 Chapter No. 3.
(7)Â
Construct the hydrograph by multiplying the Type III Tabular
Hydrograph Coordinates (TR-55, Exhibit 5-III) for the time of concentration
obtained in Step 6 by the multiplier in square mile-inches computed
in Step 5 to obtain flows in cubic feet per second for the various
times listed in the tabular coordinates.
(8)Â
The twenty-four-hour design rainfalls to be utilized by Mine
Hill Township are as follows:
Table I
24-Hour Principal Rainfalls
| ||
---|---|---|
Storm Frequency
(years)
|
24-Hour Rainfall
(inches)
| |
1
|
2.7
| |
2
|
3.3
| |
5
|
4.3
| |
10
|
5.2
| |
15
|
5.5
| |
25
|
6.0
| |
50
|
6.5
| |
100
|
7.5
|
(9)Â
Runoff curve numbers are parameters that reflect both the average
soil type and land use prevalent in the drainage basin. All of the
soil types in the municipality have been classified, labeled and mapped
on aerial photographs by the National Cooperative Soil Survey of the
Soil Conservation Service. Lists of these soils, by soil name and
symbol, as well as the hydrologic soil group to which they belong,
are contained in Exhibit A-1 of TR-55, June 1986. To account for varying
land uses and soil covers within each soil group, these soil groups
have been broken down into different land use categories as shown
in Tables 2-2a, 2-2b and 2-2c of TR-55.
(10)Â
"Time of concentration" is defined as the time required for
runoff to travel from the most hydraulically distant point in the
drainage area to the point at which a hydrograph or peak flow rate
is to be computed. It should be noted that separate times of concentration
representing both undeveloped and developed conditions in a watershed
are to be computed. Chapter 3 of TR-55 is to be utilized to calculate
the time of concentration.
A.Â
The hydraulics of all proposed detention basins will be reviewed
utilizing standard hydraulic formulas and parameters.
B.Â
In order to prevent the erosion of channels and spillways, the maximum
flow velocities at the outlet of proposed detention basins and erodible
spillways are of particular concern. Minimum velocities are also of
interest so as to prevent siltation and the subsequent loss of flow
capacity. In light of the concerns, maximum allowable design velocities
for unlined channels shall comply with the criteria contained in "Hydraulic
Engineering Circular No. 15 - Design of Stable Channels with Flexible
Linings," published by the Federal Highway Administration of the United
States Department of Transportation. When the maximum allowable velocities
cannot be maintained in an unlined suitable channel, channel lining
shall be provided in accordance with "Hydraulic Engineering Circular
No. 15."
C.Â
All detention basin routings will be performed using acceptable routing
methods. Selected time increments will be of short enough duration
to allow reasonable approximation of the inflow hydrograph.
The following list of general structural criteria shall be used
when reviewing a proposed stormwater detention basin:
A.Â
Principal outlets and structures.
(1)Â
To minimize the chance of clogging and to facilitate cleaning,
outlet pipes should be at least 18 inches in diameter. All pipes are
to be reinforced concrete pipe conforming to ASTM C 76 with rubber
gaskets pursuant to ASTM C 443.
(2)Â
Eight-inch-thick anti-seep collars are to be installed along
outlet pipes. Reinforcement steel shall be No. 5 at 12 inches both
ways with two inches of cover on both faces.
(3)Â
All principal outlet structures shall be steel reinforced concrete
cast in place. All construction joints are to be watertight. All pipes,
stubs, and/or fittings are to be cast ethically in the walls.
(4)Â
Trash racks and anti-vortex devices will be required where necessary
and should be designed to facilitate cleaning. A rise-type outlet
structure which conveys flow over its top should have an anti-vortex
cover constructed of reinforced concrete.
(5)Â
Suitable lining is to be placed upstream and downstream of principal
outlets as necessary to prevent scour and erosion. Such lining shall
conform to the criteria contained in "Hydraulic Engineering Circular
No. 15 - Design of Stable Channels with Flexible Linings," or "Standards
for Soil Erosion and Sediment Control in New Jersey," published by
the State Soil Conservation Committee.
(6)Â
All concrete shall have a minimum twenty-eight-day compressive
strength of 3000 PSI. Allowable extreme fiber stress in compression
shall be 1200 PSI.
(7)Â
All reinforcing steel shall be intermediate grade, new deformed
billet-steel conforming to ASTM A615 (latest edition). Grade 40 minimum.
Allowable stress in tension shall be 20,000 PSI.
B.Â
Emergency spillways.
(1)Â
Vegetated emergency spillways shall have side slopes not exceeding
four horizontal to one vertical.
(2)Â
Emergency spillways not excavated from undisturbed soil shall
be suitably lined and shall comply with criteria contained in "Hydraulic
Engineering Circular No. 15" or "Standards for Soil Erosion and Sediment
Control" mentioned above.
(3)Â
Maximum velocities in vegetated emergency spillways excavated
from undisturbed soil shall be checked based on the velocity of the
peak flow in the spillway resulting from the routed emergency spillway
hydrograph.
C.Â
Dams and embankments.
(1)Â
The minimum top widths of all dams and embankments are listed
below. These values have been adopted from the "Standards for Soil
Erosion and Sediment Control in New Jersey."
Table II
Minimum Top Widths
| ||
---|---|---|
Height
(feet)
|
Top Width
(feet)
| |
0 to 15
|
10
| |
15 to 20
|
12
| |
20 to 25
|
14
|
(2)Â
Maximum side slopes for all dams and embankments are four horizontal
to one vertical.
(3)Â
All earth fill shall be free from brush, roots and other organic
material subject to decomposition.
(4)Â
Cutoff trenches are to be excavated along the dam or embankment
center line to impervious subsoil or bedrock.
(5)Â
An impervious central core is to be constructed in the dam/embankment
consisting of compacted clay material.
(6)Â
Safety ledges shall be constructed on the side slopes of all
detention basins having a permanent pool of water. The ledges shall
be four feet to six feet in width and located approximately 2Â 1/2
feet to three feet below and one foot to 1Â 1/2 feet above the
permanent water surface.
(7)Â
The upstream face of the dam and/or embankment of a permanent
pool detention basin shall be stabilized to protect it against wave
erosion.
(8)Â
The fill material in all earth dams and embankments shall be
compacted to at least 95% of the maximum density obtained from compaction
tests performed by the appropriate method in ASTM D698.
(9)Â
A detention basin with a permanent pool shall have a gravity
drain to permit complete emptying of the basin when necessary.
A.Â
All site developments shall provide water quality storage in accordance
with this article. The standard requires that a proposed dry stormwater
detention basin must detain the runoff from a one-and-one-quarter-inch,
two-hour rainfall or the one-year twenty-four-hour SCS Type III storm
in such a way that no more than 90% of this runoff will be gradually
drained from the basin at the end of:
B.Â
The retention time shall be considered a brim-drawdown time, and
therefore shall begin at the time of peak storage. In providing the
above retention times, the required outlet diameter should not be
less than three inches. For all projects, the required detention time
shall be equal to the values given above or the time which results
from the use of a three-inch-diameter orifice, whichever is less.
C.Â
In permanent pond or wet basins, the water quality storage requirement
shall be satisfied when the volume of permanent water is at least
three times the volume of runoff produced by the water quality design
storm.
D.Â
All outlets shall be designed to function without manual, electric,
or mechanical controls. The required orifice may be constructed from
metal, concrete or appropriate material and placed over a larger opening
in the basin's outlet structure and attached with noncorrosive, removable
fittings where suitable. Gasket material should be placed behind the
plate to insure a watertight fit where appropriate. A removable trash
rack is required in front of the outlet to prevent clogging. All trash
racks should be designed to limit flow velocities through them to
a maximum of two feet per second.
E.Â
For a proposed detention basin which has off-site as well as on-site
areas tributary to it, the computation of the resultant runoff from
the one-and-one-quarter-inch, two-hour water quality design storm
should either include or exclude the off-site area depending upon
the following conditions:
F.Â
In addition, on-site areas not controlled by the detention facility should be kept to a minimum. Where the impact of an uncontrolled, on-site area is felt to be significant, special measures may be required, including, where possible, the storage of an equivalent amount of runoff from developed off-site areas normally excluded from the computations [see Subsection E(2) above]. Projects of this nature and all other projects with unusual site characteristics will be reviewed on an individual basis, and preliminary discussions with the Board's engineer. Both wet and dry basins can be utilized to comply with the requirements of the stormwater management regulations.
A.Â
A subsurface soils investigation is to be performed at all basin
sites, the results of which are to appear on the plans.
B.Â
The minimum bottom slope of the basin shall be 2% unless extraordinary
site conditions prevent practical installation. In all cases, low-flow
channels may be required to convey small inflows to the basin outlet.
C.Â
The basin is to have sod or topsoil and seeded, including the bottom,
side slopes and all earthen dams and embankments.
D.Â
The design dimensions of the detention basin shall be maintained
throughout construction unless it is to be used as a siltation basin
during construction in the watershed. If so, it shall be immediately
returned to design dimensions following the completion of such construction.
E.Â
Water quality for the basin shall be provided by controlling the
one-year storm. The minimum size of the orifice shall be three inches
in diameter.