Fla. Admin. Code Ann. R. 62-610.523 - Design and Operation Requirements
(1)
Hydraulic loading rates shall be developed on the basis of representative
percolation tests (drainfield percolation tests described in Chapter 64E-6,
F.A.C., are inappropriate) which simulate actual loading conditions that will
prevail during the design life of the rapid-rate system. This shall involve
bench-scale or pilot-scale hydraulic testing with either the actual reclaimed
water to be applied, or other water properly adjusted to correspond to the
composition of the reclaimed water to be applied. The design loading rate shall
allow for the expected gradual reduction in percolation rate due to long-term
application of reclaimed water.
(2)
The design hydraulic loading (and application) rate shall be related to the
hydraulic conductivity and transmissivity and of the geologic formations at the
project site which shall be evaluated in-depth by the permittee, with
assistance from organizations or individuals qualified by training or
experience in soil science, geology, and hydrology.
(3) Initial average annual hydraulic loading
rates shall be limited to 3 inches per day, or 1.9 GPD/FT2, as an annual
average where hydrogeologically feasible and as applied to the total bottom
area of rapid infiltration basins, percolation cells, or absorption fields. For
absorption fields, the bottom area shall be calculated by multiplying the
bottom width of the absorption field trench by the length of the absorption
field application/distribution lines. An applicant may request higher average
annual loading rates based on justification provided in the engineering report,
but such rates shall not exceed 9 inches per day (5.6 GPD/FT2), unless the
requirements of Rule 62-610.525, F.A.C., are met. The
average annual hydraulic loading rate shall be related to the clear water
saturated vertical hydraulic conductivity for the most restrictive layer in the
unconsolidated medium underlying the site. However, application rates during
the loading cycle for individual rapid infiltration basins, percolation cells,
or portions of the absorption field comprising the system will depend on the
average annual hydraulic loading rate and the loading/resting cycle for the
system. Application rates during the loading cycle shall be conservative and
shall not exceed 25 percent of the documented vertical hydraulic conductivity,
as described above, to control ground water mounding and ensure hydraulic
performance of the system. Application rates during the loading cycle may
exceed the maximum average annual hydraulic loading rates specified above.
Justification for the use of selected design hydraulic criteria shall be
required in the engineering report. These design criteria shall be based on the
pollutant load in the reclaimed water to be applied, the characteristics of the
underlying soil and aquifer system, loading and resting cycles to be used, and
other process design considerations (including denitrification reactions that
may be incorporated into the facility's design).
(4) Hydraulic loading and resting cycles
shall be developed so as to restore operating percolation rates of the pond
system to design levels by the end of the resting period. Hydraulic loading
periods of 1-7 days with resting periods of 5-14 days to dry the cell bottoms
and enable scarification or removal of deposited solids are required. Design
loading and resting cycles and other maintenance measures required to ensure
system performance shall be described in the engineering report. Systems which
achieve restoration of design operating percolation rates on a diurnal cycle
shall meet the requirements of Rule
62-610.525, F.A.C. Loading and
resting cycles are required for absorption fields. Loading and resting periods
for absorption fields may vary from the requirements for rapid infiltration
basins, if the applicant provides an affirmative demonstration that the
alternative loading and resting cycle will enable compliance with the ground
water criteria at the edge of the zone of discharge.
(5) A ground water mounding analysis based on
site-specific information shall be included in the engineering report. This
analysis shall demonstrate acceptable long-term hydraulic performance of the
system. The ground water mounding analysis shall demonstrate that the ground
water mound will not intercept the ground surface during any portion of the
loading cycle during any time of the year. The ground water mounding analysis
shall demonstrate that increases in ground water elevations shall not interfere
with reasonable uses of adjacent properties.
(6) Rapid infiltration basins, percolation
ponds, basins, trenches, or cells shall be routinely maintained to control
vegetation growth and to maintain percolation capability by scarification or
removal of deposited solids.
(7)
Rapid infiltration basin, percolation pond, and trench bottoms shall be
designed, constructed, and maintained to be level.
(8) Provisions shall be made in the design to
ensure reasonably uniform distribution of reclaimed water across the entire
bottom area of rapid infiltration basins, percolation ponds, basins, or cells.
Multiple discharge points (normally three or less) may be needed to accomplish
this. Elaborate sprinkler distribution systems shall not be required for rapid
infiltration basins. Absorption fields shall be designed and constructed to
ensure reasonably uniform distribution of reclaimed water across each portion
of the absorption field system.
(9)
The physical characteristics of unconsolidated materials overlying the bedrock
shall be such that direct rapid movement (short-circuit) of the applied
reclaimed water to underlying aquifers does not occur, unless the requirements
of Rule 62-610.525, F.A.C., are
met.
Notes
Rulemaking Authority 403.051, 403.061, 403.087 FS. Law Implemented 403.021, 403.051, 403.061, 403.062, 403.085, 403.086, 403.087, 403.088 FS.
New 4-4-89, Amended 4-2-90, Formerly 17-610.523, Amended 1-9-96, 8-8-99, 4-1-21.
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