(1) Zones of
mixing for non-thermal components of discharges.
(a) The Department may allow the water
quality adjacent to a point of discharge to be degraded to the extent that only
the minimum conditions described in subsection
62-302.500(1),
F.A.C., apply within a limited, defined region known as the mixing zone. Under
the circumstances defined elsewhere in this section, a mixing zone may be
allowed to provide an opportunity for mixing and thus to reduce the costs of
treatment. However, no mixing zone or combination of mixing zones shall be
allowed to significantly impair any of the designated uses of the receiving
body of water.
(b) A zone of mixing
shall be determined based on the following:
1.
The condition of the receiving body of water including present and future flow
conditions and present and future sources of pollutants.
2. The nature, volume and frequency of the
proposed discharge including any possible synergistic effects with other
pollutants or substances which may be present in the receiving body of
water.
3. The cumulative effect of
the proposed mixing zone and other mixing zones in the
vicinity.
(c) Except for
the thermal components of discharges and nitrogen and phosphorus acting as
nutrients, mixing zones which do not adhere to all of provisions paragraphs
(1)(d) through (j), shall be presumed to constitute a significant impairment of
the designated uses of surface waters of Classes I, II and III. An applicant
for a mixing zone may obtain an exemption from these limitations as follows:
1. The applicant shall provide public notice,
which shall be prepared or approved by the Department, in a newspaper of
general circulation in the area in which the mixing zone is proposed. The
notice shall identify the specific exemption it is seeking and notice the time,
date and place of a public meeting at which, if the meeting is requested, the
Department will consider comments to the requested exemption. The notice shall
allow a person to request such a public meeting by contacting the Department
within 14 days of the publication of the notice. If there is no such request, a
public meeting is not required.
2.
The applicant shall arrange for a public meeting which will be held if
requested at which the Department will consider public comments on the
exemption that is being sought. The Department shall also provide for public
notice of the meeting in the Florida Administrative Register.
3. The applicant shall affirmatively
demonstrate to the Department that the mixing zone exemption will not produce a
significant adverse effect on the established community of organisms in the
receiving body of water or otherwise significantly impair any of the designated
uses of the receiving body of water.
4. The applicant shall affirmatively
demonstrate to the Department that the requirements of paragraph (5)(c), of
this rule, will be met.
(d) A mixing zone shall not include an
existing drinking water supply intake or any other existing water supply intake
if the constituents of such mixing zone would significantly impair the purposes
for which the supply is used.
(e) A
mixing zone shall not include a nursery area of indigenous aquatic life or any
area approved by the Department of Environmental Protection for shellfish
harvesting.
(f) In canals, rivers,
streams, and other similar water bodies, the maximum length of a mixing zone
shall be no more than 800 meters. In no case shall a mixing zone be larger than
is necessary for the discharge to completely mix with the receiving water to
meet water quality standards, and in no case shall a mixing zone significantly
impair the designated use of the water body other than within the boundaries of
the mixing zone.
(g) In lakes,
estuaries, bays, lagoons, bayous, sounds, and coastal waters, the area of
mixing zone shall be 125, 600 square meters unless a lesser area is necessary
to prevent significant impairment of a designated use. In no case shall a
mixing zone be larger than is necessary to meet water quality
standards.
(h) In open ocean
waters, the area of a mixing zone shall be 502, 655 square meters unless a
lesser area is necessary to prevent significant impairment of a designated use.
In no case shall a mixing zone be larger than is necessary to meet water
quality standards.
(i) The mixing
zones in a given water body shall not cumulatively exceed the limits described
below:
1. In rivers, canals, and streams, and
tributaries thereto and other similar water bodies: 10% of the total length,
2. In lakes, estuaries, bays,
lagoons, bayous and sounds: 10% of the total area.
(j) Within mixing zones in Class I, Class II,
and Class III waters, the turbidity shall not average greater than 41
Nephelometric Turbidity Units above natural background.
(k) Mixing zones in Class IV and V waters are
subject only to the provisions of paragraph (d), above, and of Rule
62-302.500, F.A.C., and shall
not significantly impair the designated uses of the receiving body of
water.
(3)
(a) Waters within mixing zones shall not be
degraded below the minimum standards prescribed for all waters at all times in
Rule
62-302.500, F.A.C. In
determining compliance with the provisions of subsection
62-302.500(1),
F.A.C., the average concentration of wastes in the mixing zone shall be
measured or computed using generally accepted scientific techniques; provided
that, the maximum concentration of wastes in the mixing zone shall not exceed
the amount lethal to 50% of the test organisms in 96 hours (96 hr.
LC
50) for a species significant to the indigenous
aquatic community, except as provided in paragraph (b), (c) or (d), below. The
dissolved oxygen value within any mixing zone shall not be less than 1.5
milligrams per liter at any time or place, except for an open ocean discharge,
which must be above 1.5 milligrams per liter within 20 feet of the outfall
structure.
(b) Except for open
ocean discharges described in paragraph (c), and ionic imbalanced
demineralization concentrate discharges, described in paragraph (d), below, the
maximum concentration of wastes in the mixing zone may exceed the 96 hr.
LC
50 only when all of the following conditions are
satisfied.
1. Dilution ratio of the effluent
exceeds 100:1 under critical conditions. That is, flow in the receiving waters
exceeds 100 units for every unit of effluent flow under critical conditions.
Critical conditions are defined as those under which least dilution of the
effluent is expected, e.g., maximum effluent flow and minimum receiving stream
flow.
2. High rate diffusers or
other similar means are used to induce rapid initial mixing of the effluent
with the receiving waters such that exposure of organisms to lethal
concentrations is minimized.
3.
Toxicity must be less than acute [as defined in subsection
62-302.200(1),
F.A.C.] no more than a distance of 50 times the discharge length scale in any
spatial direction. The discharge length scale is defined as the square root of
the cross-sectional area of any discharge outlet. In the case of a multiport
diffuser, this requirement must be met for each port, using the appropriate
discharge length scale for that port. This restriction will ensure a dilution
factor of at least 10 within this distance under all possible circumstances,
including situations of severe bottom interaction, surface interaction, or
lateral merging.
4. The effluent
when diluted to 30% of full strength, shall not cause more than 50% mortality
in 96 hours (96 hr. LC50) in a species significant to
the indigenous aquatic community.
5. If the following pollutants are present in
the effluent, their concentrations (in the effluent) shall not exceed the
values listed:
Acrylonitrile 65 ug/l
Aldrin 7.5 ng/l
Dieldrin 7.5 ng/l
Benzene 4 mg/l
Benzidine 53 ng/l
Beryllium 6.4 ug/l
Cadmium 100 ug/l
Carbon Tetrachloride 694 ug/l
Chlordane 48 ng/l
Chlorinated ethanes:
1, 2-dichloroethane 24.3 mg/l
1, 1, 2-trichloroethane 4.2 mg/l
1, 1, 2, 2-tetrachloroethane 1 mg/l
Hexachloroethane 874 ug/l
Chloroalkyl Ethers:
bis(chloromethyl) ether 184 ng/l
bis(2-chloroethyl) ether 136 ug/l
Chloroform 1.57 mg/l
Chromium (hexavalent) 0.5 mg/l
DDT 2.4 ug/l
Dichlorobenzidine 2 ug/l
1, 1-Dichloroethylene 185 ug/l
Dinitrotoluene 11 ug/l
Diphenylydrazine 56 ug/l
Ethylbenzene 33 mg/l
Fluoranthene 540 ug/l
Halomethanes 1.6 mg/l
Heptachlor 29 ng/l
Hexachlorobenzene 74 ng/l
Hexachlorocyclohexane
aHexachlorocyclohexane 310 ng/l
bHexachlorocyclohexane 547 ng/l
gHexachlorocyclohexane 625 ng/l
Lead 0.5 mg/l
Mercury 1.5 ug/l
Nickel 1 mg/l
Nitrosamines 124 ug/l
Polynuclear aromatic hydrocarbons 3 ug/l
Polychlorinated biphenyls (PCBs) 8 ng/l
Selenium 100 ug/l
Tetrachloroethylene 885 ug/l
Thallium 480 ug/l
Toxaphene 73 ng/l
Trichloroethylene 8 mg/l
Vinyl Chloride 52 mg/l
(c) For open ocean discharges:
1. The effluent, when diluted to 30% full
strength with water having a salinity representative of the average
receiving-water's salinity, shall not cause more than 50% mortality in 96 hours
(96 hr. LC50) in a species significant to the indigenous
aquatic community.
2. Rapid
dilution shall be ensured by the use of multiport diffusers, or a single port
outfall designed (by a professional engineer registered in Florida) to achieve
a minimum of 20:1 dilution of the effluent prior to reaching the surface. This
dilution shall be determined using the appropriate plume model described in the
EPA document, "Initial Mixing Characteristics of Municipal Ocean Discharges:
Volume 1. Procedures and Applications, " using the "Single plume, stagnant
ambient" procedures or current speeds as established by field measurements.
Miami-Dade Central District, Miami-Dade North District, City of Hollywood, and
Broward County may use 12.3 cm/sec as a default value for ambient current speed
at the present location of their respective outfalls. Alternatively, dilution
studies for facilities not using the "Single plume, stagnant ambient"
procedures or the 12.3 cm/sec default ambient current speed (as appropriate)
shall be conducted in accordance with a site-specific Department approved Plan
of Study. The Plan of Study shall be approved upon a demonstration by the
applicant that the plan will produce data to characterize the daily, seasonal,
and annual fluctuations in current speed and direction. The discharge shall
otherwise comply with federal law.
3. For open ocean dischargers that comply
with the requirements of subparagraphs
62-4.244(3)(c)
1. and 2., F.A.C., compliance with applicable water quality criteria specified
in Rule
62-302.530, F.A.C. (criteria),
must be achieved by the point the discharge attains 20:1 dilution rather than
at the point of discharge. Mixing zones shall not be necessary for any
parameter that requires 20:1 dilution or less to attain criteria. However,
effluent limitations will be set by permit, and dilutions will be granted up to
20:1 in these limitations, for parameters that exceed criteria at the
end-of-pipe.
a. The demonstration of required
dilution shall be determined by the ratio of the worst case effluent
concentration (WCEC) minus the worst case background concentration to the
criterion minus the worst case background concentration, i.e.:
(Worst case effluent concentration - Worst case background
concentration)
_______________________________________________________________
(Criterion - Worst case background
concentration)
b. The WCEC
for parameters that exceed criteria in the effluent shall be the 95th
percentile effluent concentration (of DMR or other data collected in accordance
with the sampling requirements of the permit measured for the most recent
3-year monitoring period, at the time of permit renewal) for each such
parameter and not based on the maximum amount of dilution available. The WCEC
used to demonstrate the required dilution for a parameter shall also be used as
a facility performance check for each such parameter. Any exceedance of the
WCEC shall provide sufficient cause for the Department to re-evaluate the
applicability of this section and revise the permit. Additionally, any measured
value(s) of sufficient concentration to require greater than 20:1 dilution to
attain criteria shall be considered as a violation of the
permit.
4. Subparagraph
62-4.244(3)(c)
3., F.A.C., does not apply to bacterial criteria or silver in marine
waters.
(d) Discharges of
demineralization concentrate, as defined in Section
403.0882(2)(a),
F.S., for which ionic imbalance is demonstrated, may exceed the 96 hr.
LC
50 in a mixing zone no greater than the area defined
in sub-subparagraphs
62-4.244(3)(d)
1.b. and 2.a., F.A.C. Ionic imbalance is defined as the failure of whole
effluent toxicity tests caused predominantly by the presence of major ionic
constituents naturally occurring in the source water (limited to calcium,
potassium, sodium, magnesium, chloride, bromide, and other constituents
designated by the Department). Ionic imbalance is shown using the protocols
contained in "Technical Guidance Document for Conducting the Florida Department
of Environmental Protection's Protocols for Determining Major-Seawater-Ion
Imbalance Toxicity (MSIIT) in Membrane-Technology Water-Treatment Concentrate"
(FDEP, Bureau of Laboratories, May 4, 2004), which is adopted and incorporated
by reference herein. Mixing zones for toxicity caused by ionic imbalance, as
described in this paragraph, are allowed under the following conditions:
1. For all demineralization concentrate
discharges defined in Section
403.0882(2)(a),
F.S., except for small water utility businesses defined in Section
403.0882(2)(b),
F.S.:
a. The effluent, when diluted to 20%
full strength with laboratory pure water having a salinity representative of
the receiving water's salinity, shall not cause more than 50% mortality in 96
hours (96 hr. LC50) in a species significant to the
indigenous aquatic community; and,
b. Under all ambient receiving water flow
conditions, the effluent, mixed with receiving waters, must meet water quality
standards within a distance not in excess of two times the natural water depth
at the point of discharge. The natural water depth is defined as either the
depth at Mean Lower Low Water (MLLW) Level in tidally affected waters or the
depth at the seven-day, ten-year low flow (7Q10) conditions for non-tidal
rivers, streams, canals, or ship channels. In no case shall the depth be
artificially changed from its existing depth for the purpose of extending the
area for complying with water quality standards and the acute toxicity
requirements of paragraph
62-4.244(3)(d),
F.A.C.
2. For small water
utility businesses, as defined in Section
403.0882(2)(b),
F.S.;
a. The discharge must achieve a minimum
of 4-to-1 dilution within a distance not in excess of two times the natural
water depth, as described in subparagraph
62-4.244(3)(d)
1.b., F.A.C., at the point of discharge; and,
b. The effluent, when diluted to 20% full
strength with laboratory pure water having a salinity representative of the
receiving water's salinity, shall not cause more than 50% mortality in 96 hours
(96 hr. LC50) in a species significant to the indigenous
aquatic community.
(5) Mixing zones for dredge and fill permits
shall not be subject to the provisions in paragraphs (1)(c) through (j),
subsection (2), (3), or (4) of this rule, provided that applicable water
quality standards are met at the boundary and outside the mixing zone.
(a) The dimensions of dredge and fill mixing
zones shall be proposed by the applicant and approved, modified or denied by
the Department.
(b) Criteria for
departmental evaluation of a proposed mixing zone shall include site-specific
biological and hydrographic or hydrological considerations.
(c) In no case shall the boundary of a Joint
Coastal Permit mixing zone be more than 1000 meters from the point of discharge
into the waterbody or the boundary of a dredge and fill mixing zone be more
than 150 meters downstream in flowing streams or 150 meters in radius in other
bodies of water, where these distances are measured from the cutterhead, return
flow, discharge, or other points of generation of turbidity or other
pollutants.
(d) When determining
the appropriate size of a turbidity mixing zone for a Joint Coastal Permit, the
Department shall also use the following criteria:
1. Measures will be implemented to minimize
the magnitude and duration of turbidity to the maximum extent
practicable;
2. Mixing zones shall
be kept to the minimum size necessary to meet the turbidity standard; and,
3. Mixing zones shall not
encompass hardbottom communities, coral resources, or submerged aquatic
vegetation beds outside of the authorized impact sites unless those areas are
also evaluated as impact sites.
(6) Where a receiving body of water fails to
meet a water quality standard for pollutants set forth in department rules, a
steam electric generating plant discharge of pollutants that existed or was
licensed on July 1, 1984, may be granted a mixing zone, provided that:
(a) The standard would not be met in the
water body in the absence of the discharge; and,
(b) The discharge is in compliance with all
applicable technology-based effluent limitations; and,
(c) The discharge does not cause a measurable
increase in the degree of noncompliance with the standard at the boundary of
the mixing zone; and,
(d) The
discharge otherwise complies with the mixing zone provisions specified in this
section.
(7) Additional
relief from mixing zone restrictions necessary to prevent significant
impairment of a designated use is through:
(a)
Reclassification of the water body pursuant to Rule
62-302.400, F.A.C.;
(b) Variance granted pursuant to Section
403.201, F.S., and Rule
62-103.100, F.A.C.
(c) Modification
of the requirements of this section for specific criteria by the Secretary upon
compliance with the notice and hearing requirements for mixing zones set forth
in paragraph (1)(c), above, and upon affirmative demonstration by an applicant
that the applicant's discharge from a source existing on the effective date of
this rule complies with best technology economically achievable, best
management practices, or other requirements set forth in Chapter 62-600,
F.A.C., and the economic, environmental and social costs of compliance with the
existing criteria outweigh the social, environmental, and economic benefits of
compliance with more stringent discharge limitations necessary to comply with
mixing zone requirements of subsection
62-4.244(1),
F.A.C., and the provisions relating to dissolved oxygen in Rule
62-4.244, F.A.C.
1. No discharger may be issued more than one
permit or permit modification or renewal which allows a modification pursuant
to this subsection unless the applicant affirmatively demonstrates that it has
undertaken a continuing program, approved by the Department, designed to
consider water quality conditions and review or develop any reasonable means of
achieving compliance with the water quality criteria from which relief has been
granted pursuant to this subsection.
2. With respect to paragraphs
62-4.244(1)(c)
and
62-4.244(7)(c),
F.A.C., the applicant must affirmatively demonstrate the minimum area of the
water body necessary to achieve compliance with either subsection. Within a
minimum area determined by the Secretary to be necessary to achieve compliance,
the discharger shall be exempt from the criterion for which a demonstration has
been made.
(d) Whenever
site specific alternative criteria are established pursuant to Rule
62-302.800 or paragraph
62-302.510(2)(g), F.A.C., a mixing zone may be issued for dissolved oxygen if
all provisions of Rule
62-4.244, F.A.C., are met with
the exception of subparagraph
62-4.244(1)(j)
1., F.A.C.