HomeMy WebLinkAboutAppendix B: Stearns Cty Ord....
Appendix B
Stearns County - Erosion Control and Storm Water Ordinances, Jan. 2004
Erosion and Sediment Control Standards
The purpose of this Section is to prevent or reduce, to the most practicable extent,
erosion and sedimentation and their associated effects and to provide for the
protection of public waters as well as natural and artificial water storage and retention
areas within the County. An erosion and sediment control plan shall be submitted to
and approved by the Department prior to construction of a new plat or a commercial
or industrial facility, or when the Department detennines an erosion and sediment
control plan is necessary due to potential impacts of construction on the property or
surrounding properties.
7.5.1 General Standards
Proper erosion and sediment control practices shall be followed within the
County as described in this Section. All land disturbing activities, whether
or not a pennit is required, shall be subject to the following perfonnance
standards:
A. No land owner, operator, contractor or applicant shall cause or
conduct any land disturbing activity which causes erosion or
sedimentation, damages water or soil resources or creates off-site
impacts.
B. All development shall confonn to the natural limitations presented
by the topography and soil types in order to minimize soil erosion
and sedimentation.
C. Land disturbing activities shall only occur in increments of
workable size such that adequate erosion and sediment controls
can be provided throughout all phases of a development. The
smallest practical area ofland shall be exposed or otherwise
disturbed at anyone period of time.
D. Every applicant for a construction site pennit, interim use pennit,
provisional use pennit, alteration pennit, conditional use pennit or
subdivision approval shall, at a minimum, adhere to erosion
control measure standards and specifications contained in the
MPCA publication "Protecting Water Quality in Urban Areas"; or
successor publication.
7 .5.2 Specific Standards
A. No land disturbing activity shall result inactive gully erosion or
create negative off-site impacts.
B. No land disturbing activity shall result in an increase in channel
erosion in any watercourse, whether pennanent or intennittent, at
any time during or following development.
C. No land disturbing activity shall result in the creation of unstable
slopes which persist after the completion of the development.
D. Pennanent or temporary soil stabilization shall be applied to
disturbed areas (areas where vegetation has been removed or
where cuts have been made), as soon as possible, but not to exceed
fourteen (14) days after a substantial portion of rough grading has
been conducted unless an extension is granted by the Director.
Soil stabilization measures shall be selected to be appropriate for
the time of year, site conditions and estimated duration of use.
E. An erosion and sediment control plan, when required by the
Department shall include the following:
(1) Location map. An 11 'x17" map locating the site in relation to the
surrounding area.
(2) Indicate north. Show the direction of north in relation to the site.
(3) Scale. Indicate scale in relation to the actual size of the site,
usually in feet per inch.
(4) Benchmark. Show the established elevation affixed to a
permanent object which can be used to check grade.
(5) Plan preparer. Indicate the name and phone number of the
individual or agency responsible for preparation of the plan.
(6) Contact person. Give the name and phone number of the
individual responsible for plan implementation.
(7) Existing contours. Show existing two foot contours of the site
extending at least 200 feet beyond the property boundaries.
(8) Final contours. Show all proposed changes to the existing
contours due to land disturbance.
(9) Existing vegetation. Indicate existing woods, tree lines, cultivated
areas, grasslhay fields, CRP, wetlands and other vegetative types.
(10) Disturbed area. Identify the disturbed acreage for each drainage
area. Include roads and lot clearing.
(11) Utilities. Show the locations of stonn sewer, sanitary sewer,
water supply, electrical and other utilities in the area ofthe
proposed development.
(12) Location ofBMP. Indicate the location of erosion and sediment
control practices proposed for the site.
(13) Implementation schedule. Outline the proposed order ofland
clearing, road installation and other aspects of construction.
(14) Critical erosion areas. Identify areas susceptible to erosion during
and after construction. Critical erosion areas are areas which are
prone to accelerated erosion, areas which have slopes of 12% or
greater, areas oflong, continuous slopes or areas which contain
erosive soils.
(15) Limits of disturbed areas. Show the extent of the areas which
must be disturbed to accommodate the proposed construction.
(16) Sediment pond. Show the location of any temporary pond to be
used to collect sediment during construction.
(17) Adjacent areas. Describe neighboring areas which could be
affected by land disturbance.
(18) Temporary erosion control plan. Indicate how erosion on the site
will be temporarily controlled until permanent erosion control can
be implemented (seeding and mulching rates, sod installation,
etc.)
F. Soil stockpiles shall be stabilized or protected with sediment trapping
measures to prevent soil loss.
G. A permanent vegetative cover shall be established on disturbed areas
not otherwise permanently stabilized.
H. Properties adjacent to the site of a land disturbance shall be protected
rrom sediment deposition.
1. Sediment basins and traps, perimeter dikes (for diversion), sediment
barriers (silt fences) and other measures intended to trap sediment on-
site shall be constructed prior to or concurrent with any grading and
shall be functional before upslope land disturbance takes place.
Earthen structures such as dams, dikes and diversions shall be seeded
and mulched within fourteen (14) days of installation.
J. Storm water runoff rrom drainage areas with more than five (5) acres of
disturbed area must pass through a temporary sediment trapping basin
or other suitable sediment trapping facility.
K. Cut and fill slopes shall be designed and constructed in a manner which
will minimize erosion. Slopes which will not be vegetated within one
(1) year of construction shall be provided with additional slope
stabilizing measures until the problem is corrected. Slopes that are
found to be eroding excessively shall immediately be provided with
additional slope stabilizing measures until the problem is corrected.
L. Properties and waterways downstream rrom development sites shall be
protected rrom erosion due to increases in the volume, velocity and
peak flow rate of storm water runoff.
M. All on-site storm water conveyance channels shall be designed and
constructed to withstand the expected velocity of flow rrom a 1 O-yea~
rrequency storm without eroding.
N. Rip-rap shall be placed at culvert outfalls in accordance with applicable
MnDOT standard specifications.
O. All stonn sewer inlets which are made operable during construction
shall be protected so that sediment laden water will not enter the
conveyance system without first being filtered or otherwise treated to
remove sediment.
P. Construction vehicles and other equipment shall be kept out of
watercourses to the maximum extent possible.
Q. Wherever construction vehicle access routes intersect paved public
roads, provisions, such as rock construction entrances, shall be made to
minimize the transport of sediment by runoff or vehicle tracking onto
the paved surfaces.
R. All temporary erosion and sediment control measures shall be properly
disposed of within thirty (30) days after final site stabilization is
achieved or after the temporary measures are no longer needed, unless
otherwise authorized by the Department.
S. All temporary and permanent erosion and sediment control practices
shall be maintained and repaired as needed to assure continued
performance of their intended functions.
Storm Water Management
The purpose of this Section is to prevent or reduce, to the most practicable extent, the
effect or impacts of storm water runoff and to provide for the protection of public
waters and natural and artificial water storage and retention areas within the County.
Further, this Section clarifies the performance standards as they pertain to standards
and specifications for conservation practices and storm water planning activities.
7.21.1 Performance Standards
Proper storm water management practices shall be followed within the County as
described in this Section.
A. General Standards.
(1) The need for storm water management facilities may be reduced by
incorporating or restoring the use of natural topography and
features, such as wetlands, ponds, natural swales and depressions
to the degree that they can accommodate the additional flow of
water without compromising the integrity of the natural feature.
When development density, topographic features, soil or
vegetation conditions are such that natural features are not
sufficient to handle storm water runoff, various types of
constructed facilities, such as diversions, settling basins, skimming
devices, dikes, waterways and ponds may be used.
(2) Soil laden runoff shall be treated before it is allowed to enter any
water body. Preference shall be given to designs using surface
drainage, vegetation and infiltration rather than buried pipes,
manmade materials and facilities.
(3) Storm water rate control. When required by the Director, a storm
water management plan shall include the design of all storm water
management facilities necessary to manage increased runoff so that
the 2-year, 10-year and 100-year storm peak discharge rates from
the property boundary do not exceed pre-development conditions
and so that accelerated channel erosion on and off-site will not
occur as a result of the proposed land disturbing or development
acti vi ty.
(4) The minimum design capacity of all drainage systems shall
accommodate the runoff from a ten (10) year storm event. All
drainage systems and facilities shall be designed to withstand the
runoff from the critical one hundred (100) year event or
accumulative antecedent conditions without damage to the system
or facility, downstream areas and without significant risk to human
health and safety.
~(1) The applicant or their successors shall be responsible for the
installation and maintenance of any temporary or permanent
measures identified in the storm water management plan. At the
time of completion of the development, those structures,
measures and systems constituting the storm water runoff facility
may be permanently maintained by the Township after official
acceptance by the Township Board, by a legally organized
homeowner's association, by a watershed district after official
acceptance by the district or by other means acceptable to the
County.
-1 91· An application for a storm water management plan shall be
accompanied by a financial guarantee in the form of a letter of
credit, cash deposit or bond in favor of the County equal to one
hundred twenty-five (125) percent of site grading and
erosion/sediment control costs necessary to ensure the
satisfactory installation, completion and maintenance of the
measures as required in the storm water management plan.
~ 0') Storm water volume control. For protection of downstream water
bodies and properties, post development runoff volumes shall not
exceed pre-development conditions. For protection of
downstream water bodies, the most current Best Management
Practices (BMPs) shall be employed to reduce the general
impacts of runoff volume and rates. Development resulting in
the creation of impervious surfaces must explicitly address the
use of BMPs to limit the loss of pervious areas, BMPs to be
evaluated shall include, but not be limited to, vegetated swales,
pond outlets perched above ground water levels, roof drainage to
pervious areas, depressed casual storage areas, minimization of
the number and width of parking stalls, "rural section" roads and
road width minimizatïon and mitigation of disturbed soils.
l\. /(4) Prevention of downstream nuisance and damage. When conditions
do not permit post-development runoff volumes to be equal to
pre-development conditions, the applicant shall provide a study
which demonstrates that increased storm water runoff volumes
above pre-development conditions will not adversely affect
downstream properties or water resources. The study shall
include, at a minimum, an evaluation of downstream landlocked
lakes and ponds and lakes and ponds with inadequate outlets
where flood levels could be increased by added runoff volume;
and downstream drainage paths that are not public waters that are
inadequate to convey added runoff volumes as evidenced by (a) a
lack of public easements or access to the drainage facility; (b)
existing channel erosion prior to discharge to public waters; (c)
undersized drainage systems or drainage systems in disrepair;
and (d) other downstream drainage conditions that would tend to
create nuisance conditions or safety problems.
\ Û ø5 Storm water management facilities must be designed, installed and
maintained consistent with the most current Best Management
Practices.
\\ (},Ø}Developments shall be planned and conducted in a manner that
will minimize the extent of disturbed area, runoff velocities,
erosion potential and both reduce and delay runoff volumes.
Disturbed areas shall be stabilized and protected and facilities or
V methods used to retain sediment on site.
\ (J1)All storm water management facilities shall be designed to
minimize the need for maintenance, to provide access for
maintenance purposes and to be structurally sound. All storm
water management facilities shall have a plan of operation,
maintenance and clean-out that assures continued effective
removal of sediment carried in storm water runoff. It shall be the
responsibility of the applicant to obtain any necessary easements or
other property interests to allow access to the storm water
management facilities for inspection and maintenance purposes.
B. Specific Standards for Storm Water Conveyance and Rate Control
Facilities.
(1) All storm water management calculations submitted to the
Department for review as part of a storm water management plan
shall include sufficient information for the Department to evaluate
the changes to the storm water drainage characteristics within the
watershed areas affected by the proposed land disturbing activity.
The applicant shall include calculations which clearly show the
effects of this development on the peak rate of discharge, the time
of concentration, channel velocities and other potential drainage
impacts to water and soil resources both on and off the
development site. The Director may require the applicant to
provide any additional information, calculations or data needed to
complete the review of a storm water management plan.
(2) The storm water calculations submitted for review shall be based
upon standard hydrological and hydraulic analysis methods that are
acceptable to the Director. Calculations that are based upon
unproven methodologies or apply proven methodologies
incorrectly shall be determined by the County to be unacceptable
and shall be returned to the applicant for correction and be
resubmitted.
(3) Acceptable hydrological methods and procedures to determine
peak runoff discharge rates and runoff volumes for all
development, except for street and highway pavement drainage
systems, shall be the standard methods of the Natural Resources
Conservation Service SCS TR 55 and the SCS TR 20 Methods as
defined in the current Hydrology Guide for Minnesota.
(4) Precipitation events for the Rational Method shall be for the two
(2), ten (10) and one hundred (100) year twenty-four (24) hour
frequency storm events using the US. Weather Bureau Technical
Paper No. 40 rainfall intensity duration curves for a Type II
rainfall distribution.
(5) Acceptable hydrological methods and procedures to determine
peak runoff discharge rates for street and highway pavement
drainage systems, inlet capacities and piped storm sewer systems
shall be based upon the Rational Method as defined in the current
Minnesota Department of Transportation Drainage Manual.
(6) Where development site drainage discharges to an existing
roadway, ditch, stonn sewer or other public facility, the applicant
shall provide, as part of the calculations, all survey, utility or other
topographic data of the existing condition needed for the Director
to detennine that the proposed development does not impact or
degrade any critical roadway element or negatively impact the
safety, maintenance or function of the public facility.
(7) Drainage areas. Stonn water management plans shall show
existing and proposed drainage areas used for stonn water analysis,
including off-site portions of subwatersheds that are partly located
on the property for which the plan is being prepared. Where
drainage areas include runoff from off-site areas, those areas may
be shown and measured from maps at larger scales (e.g. United
States Geological Survey Quadrangle Maps) if better mapping is
not reasonably available. In all drainage areas, the direction of
flow for each area and the travel path used for detennining the
Time of Concentration shall be shown. No direct entries for
detennining the Time of Concentration shall be allowed without
prior approval by the Director.
(8) Runoff curve numbers (RCN). Stonn water management plans
shall include a detailed breakdown of existing and proposed runoff
curve numbers.
(9) Soil types. Stonn water management plans shall identify the
boundaries of the soil types present on-site and their hydrologic
classification and acreage.
(10) Pre-settlement conditions. The following runoff curve numbers
shall be use to analyze pre-settlement conditions:
Hydrologic Soil Group Runoff Curve Number:
A-30
B-55
C-71
D-77
(11) For evaluation of post-development runoff, drained hydric soils
shall be assumed to revert to an undrained condition unless the
applicant demonstrates that publicly owned and maintained
drainage facilities will be adequate to maintain the drained
condition.
(12) Impervious coverage. Stonn water management calculations
shall list the new impervious area created in each subwatershed
and shall include the assumptions and calculations used for
detennining impervious areas, such as house pad, driveway and
outbuildings.
(13) Runoff calculations. The applicant shall provide calculations for
two (2), ten (10) and one hundred (100) year peak discharge rates
for each subwatershed comparing pre-settlement conditions and
proposed post-development conditions.
(14) Where pre-settlement conditions indicate no runoff, the
infiltration capacity required elsewhere in this Ordinance may be
used to demonstrate compliance with a no runoff requirement for
the stonn frequency and duration being considered.
(15) Stonn water management plans shall show preexisting drains and
tile lines. Stonn water facilities shall be designed assuming that
tile lines will no longer function unless an easement is supplied
for future maintenance and the applicant demonstrates that the tile
line has design capacity and service condition that makes it a
suitable component of the stonn water management system.
(16) Stonn water management plans shall include an evaluation of
landlocked lakes and ponds in the design analysis and
demonstrate that runoff from a full year of runoff in the 100 year
wet year will not exceed the predicted 100 year flood level.
(17) Stonn water management plans shall identify the location of
conveyance systems and clearly identify all dimensions, cross
sections and outlet elevations.
(18) Stonn water management plans shall include the locations of all
property lines, lot lines, section lines and adjacent plats.
(19) Stonnwater management plans shall contain infonnation which
clearly identifies all elevations and grades for streets, ditches,
ponds, wetlands, lakes, pipe inverts and pipe outlets.
C. Specific Standards for Wet Detention Basins.
(1) All wet detention basins shall be designed and constructed in
accordance with the W.W.Walker Method (1987) described in the
Best Management Practices.
(2) Designs for wet detention basins shall include, but not be limited
to, calculations for estimated inflow and outflow, pennanent and
temporary storage volumes, mean depth, outlet design,
downstream stabilization, emergency spillways, basin profiles and
basin cross sections.
(3) In the LI, GI and CR zoning districts, skimmers shall be included
on the outlet of wet detention basins. Construction details of the
skimmers shall be shown on the construction plans for the wet
detention basin.
(4) Ground water sensitivity. Wet detention basins located in areas
identified as being highly susceptible to ground water
contamination, except ground water discharge areas, shall be
designed so that the bottom of the basin is located at least three
feet above the seasonal high ground water elevation and/or
bedrock and be lined with two (2) feet of soil having a
penneability less than five (5) minutes per inch.
D. Specific Standards for Volume Control.
(1) Infiltration practices for control of storm water runoff volume
shall be capable of infiltrating one-half (112) inch of runoff from
all new impervious surfaces within the development within
seventy two (72) hours.
(2) Infiltration volume and facility sizes shall be calculated using the
appropriate hydrologic soil group calculation and saturation
infiltration rate from the table below. Documented site specific
infiltration or hydraulic conductivity measurements may be used
in place of the values in the following table, if approved by the
Director. The goals of these BMPs are to minimize the amount of
directly connected impervious surface created, to preserve the
infiltration capacity of the soil and to incorporate practices into
the design which are capable of allowing the infiltration of one~
half (1/2) inch of runoff from impervious surfaces within seventy-
two (72) hours.
Soil Group Infiltration Rate (in/hr) Soil Texture
A. 0.3 sandy, loamy sand or sand loam
B. 0.15 silt loam or loam
C. 0.07 sandy clay loam
D. 0.03 clay loam, silty clay loam, silty clay or clay
Source: Urban Hydrology for Small Watersheds (SCS,
June 1986)
(3) Infiltration areas shall be limited to the horizontal areas subject to
prolonged wetting.
(4) Areas of permanent pools tend to lose infiltration capacity over
time and shall not be accepted as an infiltration practice.
(5) New constructed storm water outfalls to any public waters must
provide for filtering or settling of suspended solids and skimming
of surface debris before discharge.
E. Specific Standards for Areas of Moderate or High Susceptibility to
Ground Water Contamination.
(1) Infiltration areas shall have either natural undisturbed soil or be
lined with at least two feet of soil with a permeability of five (5)
minutes per inch or slower as defined in the Ground Water
Protection Plan.
(2) Infiltration areas shall be at least three feet above the seasonal
high ground water elevation and/or bedrock.
F. Compliance with storm water management plans. If an applicant does
not implement the requirements of a storm water management plan, the
Director may issue a restoration order as outlined in Section 4.23 of this
Ordinance.