A. Factors. The
factors related to the construction and operations of the activity which must
be addressed by the applicant and will be considered in determining
certification action are as follows:
(1)
feasible alternatives to the activity;
(2) mitigation;
(3) initial and secondary impacts on all
existing and all classified uses of the waters of the State;
(4) degree of compliance of the proposed
activity with the State of Mississippi Water Quality Criteria for Intrastate,
Interstate, and Coastal Waters;
(5)
degree of physical, chemical, and biological impacts on waters of the
State;
(6) the effect on
circulation patterns and water movement on waters of the State;
(7) degree of alteration of the aquatic
ecosystem;
(8) degree of
consistency with approved water quality management plans adopted by the
Commission;
(9) storm water
management;
(10) compliance history
of the applicant; and
(11) any
other factors deemed to be necessary by the Department to protect water
quality.
B. Denial.
After consideration of the factors in Rule 1.3.4.A, a decision to issue or deny
certification shall be made. However, it is the policy of the Department to
deny certification when any of the following determinations are made unless the
Department is assured that appropriate measures will be taken to eliminate
unreasonable degradation and irreparable harm to waters of the State.
(1) The proposed activity permanently alters
the aquatic ecosystem such that water quality criteria are violated and/or it
no longer supports its existing or classified uses. An example is the
channelization of streams.
(2)
There is a feasible alternative to the activity which reduces adverse
consequences on water quality and classified or existing uses of waters of the
State.
(3) The proposed activity
adversely impacts waters containing State or federally recognized threatened or
endangered species.
(4) The
proposed activity adversely impacts a special or unique aquatic habitat, such
as National or State Wild and Scenic Rivers and/or State Outstanding Resource
Waters.
(5) The proposed activity
in conjunction with other activities may result in adverse cumulative
impacts.
(6) Nonpoint source/storm
water management practices necessary to protect water quality have not been
proposed.
(7) Denial of wastewater
permits and/or approvals by the State with regard to the proposed
activities.
(8) The proposed
activity results in significant environmental impacts which may adversely
impact water quality.
C.
Criteria. The Department has developed a number of criteria which the applicant
must substantially satisfy when the proposed activity involves any of the items
addressed below.
(1) Excavated Canals. These
canals generally have flow and circulation less than that of the parent body of
water and can become traps for organic material, nutrients and pollutants,
resulting in a decline in water quality. Due to this potential for water
quality degradation, the Department discourages canals. If no feasible
alternatives are available, the Department has formulated a set of design and
construction criteria to minimize the anticipated adverse water quality
impacts. These criteria must be substantially satisfied in order for
certification issuance to be considered. The criteria with regard to canals is
attached hereto as Exhibit A and incorporated herein by reference.
(2) Marinas. Numerous construction,
development and operation activities at a marina can adversely impact water
quality. In order to prevent potential adverse water quality impacts, the
Department has formulated a set of criteria for marina development. These
criteria must be substantially satisfied in order for certification issuance to
be considered. The criteria with regard to marinas is attached hereto as
Exhibit B and incorporated herein by reference.
(3) Sand and Gravel Mining Within or Adjacent
to Streams. Potential physical effects of excavations adjacent to streams and
sand/gravel mining within stream banks include, but are not limited to, stream
channel modifications, such as alteration of flow patterns, sediment transport,
increased headcutting and channelization. These effects may adversely impact
water quality by causing increased turbidity, reduced light penetration,
resuspension of pollutants, increased water temperatures, and decreased
dissolved oxygen. All sand and gravel mining activities which require a Section
401 Water Quality Certification shall be evaluated in accordance with Rule
1.3.4.A and B. In addition, the Department shall consider the following in
evaluating sand and gravel mining within or adjacent to streams.
(a) Excavations Adjacent to Streams. To
prevent adverse water quality impacts resulting from excavations adjacent to
streams, the Department shall require a buffer zone between the mining activity
and adjacent water bodies. A buffer zone (natural or undisturbed greenbelt on
the perimeter of a land disturbing activity) shall be measured as the distance
between the edge of the mining activity and the highest point of the top bank
of the stream. Mining activity includes, but is not limited to, extraction
operations, stockpiling of overburden or sand and gravel, gravel washing
operations and sedimentation ponds. The purpose of the buffer zone is to
prevent nonpoint source impacts and channel and hydraulic modifications.
Channel and hydrologic modifications occur when the water body captures a
mining pit during high water. The width of the buffer zone shall be based on
the stream size. The buffer zone requirements for excavations adjacent to
streams are as follow:
(1) Intermittent
Streams. Mining activities adjacent to intermittent streams shall normally have
a 50-foot buffer zone. Intermittent streams will generally be indicated by a
broken blue line on the latest version of the United States Department of the
Interior Geological Survey Quadrangle Map (Scale 1:24,000, 7.5 minute series).
The applicant may file a written request with the Department to reroute an
intermittent stream, either temporarily or permanently, to avoid the mining
activity. The Department shall approve the applicant's request only if the
applicant can demonstrate that no significant adverse water quality impacts
will result from the rerouting. In the event the Department approves the
rerouting of an intermittent stream, appropriate erosion and siltation controls
shall be implemented. Slopes shall normally be graded to 3 to 1 (horizontal to
vertical) or flatter and seeded with a native species of grass to prevent
erosion. The Department may require a different slope, on a case-by-case basis,
as long as the slope is protective of the integrity of the stream bank and
water quality.
(2) Perennial
Streams. Mining activities adjacent to perennial streams shall normally have a
150-foot buffer zone. Perennial streams will generally be indicated by a solid
blue line on the latest version of the United States Department of the Interior
Geological Survey Quadrangle Map (Scale 1:24,000, 7.5 minute series). When a
perennial stream is also classified as a navigable waterway, the requirements
regarding navigable waterways shall be applied.
(3) Navigable Waterways. Mining activities
adjacent to navigable waterways shall normally have a 300-foot buffer zone.
Navigable waterways are defined and designated by the U. S. Army Corps of
Engineers pursuant to Section 10 of the Rivers and Harbors Act.
The Department may require a different buffer zone, on a
case by case basis, as long as the buffer zone is protective of water quality.
In determining whether a different buffer zone is appropriate, the
Department may consider factors including, but not limited
to, the stability of the stream banks and the existing uses of the stream and
adjacent areas.
(b) Sand/Gravel Mining within Stream Banks.
The two types of sand/gravel mining within stream banks include sand/gravel bar
mining in-the-dry and sand/gravel mining
in-the-wet13. To prevent adverse water quality
impacts, the Department has formulated a set of criteria for sand/gravel bar
mining in-the-dry. These criteria are attached hereto as Exhibit C and
incorporated herein by reference. Except as otherwise provided in these
regulations, sand/gravel mining in-the-wet may be allowed if the applicant can
demonstrate to the satisfaction of the Department that the water quality
impacts associated with the proposed activity are minor. In assessing the
impacts on water quality, the Department shall consider these activities on a
case-by-case basis in accordance with the factors set forth in Rule 1.3.4.A and
B.
(4) Development
Requiring Storm Water Management. Nonpoint source pollution is a significant
obstacle to preserving and improving the quality of our state's waterways. In
order to prevent adverse water quality impacts, the Department has formulated a
set of criteria for storm water management. These criteria must be
substantially satisfied in order for certification issuance to be considered.
The criteria with regard to storm water management is attached hereto as
Exhibit D and incorporated herein by reference. These storm water runoff
criteria are separate from any Storm Water Pollution Prevention Plan (SWPPP)
required under any required storm water permit.
(5) Certain Existing Subdivisions on the
Mississippi Gulf Coast originally platted in lands which, because of the
passage of the Federal Act and related laws and/or regulations, are presently
unsuitable for development. Several coastal subdivisions were platted prior to
the passage of a number of pertinent regulatory laws, including but not limited
to, Sections 401 and 404 of the Federal Act. These subdivisions typically have
waterfront access to estuarine waters by man-made canals, have inadequate
sewage treatment, and require filling of productive salt marsh. Current law and
regulatory policy would not allow the platting and/or development of such
subdivisions due to adverse environmental impacts. However, in an attempt to
allow residential development to proceed in existing platted and partially
developed subdivisions, while addressing water quality concerns, the Department
has formulated a set of criteria that must be substantially satisfied in order
for certification issuance to be considered. The
13 "Sand/gravel bar mining
in-the-dry" is mining in such a manner that no equipment or dredged material is
in contact with flowing water, that the soil/water or groundwater interface is
not touched by the equipment and that infiltration in the mining site is not
pumped into the stream. "Sand/gravel mining in-the-wet" is mining in such a
manner that equipment and dredged material may come in contact with water.
criteria with regard to residential development in such subdivisions is
attached hereto as Exhibit E and incorporated herein by reference.
Notwithstanding the criteria set forth above, the
Department may develop criteria for other proposed activities which may have an
adverse impact on water quality.