Current through Register Vol. 48, No. 9, September 27, 2024
The following conditions, in addition to those set forth in
section505.41, apply to all Land Application permit or State permits within the
categories specified below:
(a)R.61-9.122.42(a) and (b)(a) and (b) shall
apply.
(b) Irrigation of treated
wastewater. This includes all methods of surface application, including but not
limited to, fixed gun application, travelling or mobile gun application, or
center pivot application.
(1) Spray field
slopes shall not exceed 10 percent unless approved by the Department. The
Department may require that slopes be less than 10% based on site
conditions.
(2) Effluent
distribution systems shall be designed so that the distribution pattern
maximizes uniform application. The Department may require the permittee to
modify existing land application site(s) distribution systems based on site
conditions (e.g., potential for ponding, runoff, or discharges to open
ditches).
(3) Soil borings may be
required by the Department to depict the lithologic and hydrogeologic
characteristics of the subsurface. The requirements of R.61-67 would apply.
(4)
(i) At
proposed spray sites with satisfactory soil conditions, design application
rates for hydraulic loading shall not exceed (with the exception of seasonal
application) the rates shown in Table I (unless one of the conditions in
(4)(ii)-(vi) apply) :
Table I
|
Depth to Seasonal High Water (or measured high
water depth, e.g. piezometer readings)
|
Design Application Rate (gallons per day per
acre) (gpd/acre)
|
5 feet or more
|
2 inches/week (in/wk), 7,758 gpd/acre
|
4 feet
|
1 in/wk, 3,879 gpd/acre
|
3 feet
|
0.5 in/wk, 1,940 gpd/acre
|
less than 3 feet
|
no application (unless otherwise
|
(ii) The applicant may request intermediate
loading rates, if the seasonal high water table is between the depths shown in
the table.
(iii) If the seasonal
high water table (or measured high water depth e.g. piezometer readings), is
less than three (3) feet, the Department may consider permitting the land
application site if the domestic wastewater facilities are designed to meet
monthly average effluent limits for 5-day Biochemical Oxygen Demand
(BOD5) of 10 mg/l, Ammonia nitrogen
(NH3-N) of 2 mg/l and Nitrate (N) of 10 mg/l, or
industrial facilities with non-process wastewater or other suitable wastes. The
Department may eliminate some or all of the groundwater monitoring requirements
for these facilities.
(iv) The
application rate may be limited based on pollutant loading including any
pollutant required for monitoring under effluent guidelines ( 40 CFR Part 136;
Subchapter N ( 40 CFR Parts 400 through 402 and 404 through 471). The
applicant for domestic wastewater or other systems with a nitrate/nitrogen
loading may be required to provide the Department, a nitrate to nitrogen
loading balance to determine if the application rates shown in Table I shall be
adjusted.
(v) The Department may
consider application rates in excess of two (2) inches per week for sites that
meet the depth to groundwater shown in Table I, provided the application period
is only for a portion of the year, or the application is for reclaimed water.
The applicant must provide sufficient information to the Department to justify
a higher application rate (information required may include, but is not limited
to a water balance for the summer season).
(vi) For Domestic wastewater facilities
designed to meet monthly average effluent limits of a 5-day Biochemical Oxygen
Demand (B0D5) of 10 mg/l, NH3-N
of 2 mg/l and Nitrate of 10 mg/l, or industrial facilities with non-process
wastewater, or other suitable wastes. If the seasonal high water table (or
measured high water depth e.g. piezometer readings), for the land application
site is three (3) feet or more, the Department may eliminate some or all of the
groundwater monitoring requirements for these facilities.
(5) The design application frequency for
effluent irrigation shall not exceed a spray to rest ratio suitable for the
soil conditions. A spray to rest ratio of 1:20 shall be used unless an
alternative rate is approved by the Department. The application frequency for
other activities (such as sludge or septage application) would be determined on
a site specific basis.
(6) The
application site shall be divided into designed spray areas to meet this spray
to rest ratio and a continuous application period per defined spray area shall
be designed not to exceed 1.2 hours per day, or up to 8 consecutive hours per
week (only under those limited conditions when excessive rainfall on the
application sites requires application in one day). If the design application
rate on a daily basis is exceeded, the Department may require the permittee to
provide additional spray application area or alternative disposal methods may
be required (e.g. expanding storage capacity for effluent at the facility).
Alternative application periods (such as golf course irrigation) may be
approved by the Department.
(7) For
permitted spray disposal areas which already receive irrigation (e.g.
stormwater, potable water or well water), the effluent application rates may be
modified by the Department to correspond to the depth to the measured high
water table or to the seasonal high water table, whichever is more
shallow.
(8) The new or expanding
spray field shall be at least 200 feet from surface waters of the State,
occupied buildings and potable water wells unless otherwise approved by the
Department. The new or expanding spray field shall be at least 100 feet from
the property boundary except for golf courses where it shall be at least 75
feet. The Department may require modification to existing permitted spray
fields to control the application areas by the addition or expansion of a
buffer zone. The applicant may request the buffer zone for specific spray areas
be eliminated for sites where the adjacent property owner agree to the
elimination of the buffer in writing. The Department may approve an elimination
of the buffer zone based on the information provided by the
applicant.
(9) A dike or berm
around the perimeter of the spray field may be required in specific areas
determined by the Department as necessary to prevent potential surface runoff
from entering or leaving the spray site. The Department may consider alternate
methods of runoff controls that may be proposed by the applicant.
(10) A system for monitoring the quality of
groundwater shall also be established for the proposed spray site (for those
systems requiring groundwater monitoring). The location of all the monitor
wells shall be approved by the Department. The applicant shall provide at least
one monitoring well up-gradient of the spray area and at least two groundwater
monitoring wells down-gradient. For larger spray fields, more than three
groundwater monitoring wells may be required. For land application on golf
courses with secondary effluent limits, nine monitor wells shall be provided
for 18 fairways (or one groundwater well per two fairways for differing course
sizes). The Department may reduce the number of groundwater monitoring wells
required based on site conditions (e.g. a significant number of existing
groundwater monitoring wells in a small area with multiple golf courses, or
existing groundwater monitoring data).
(11) Groundwater samples for new application
sites (for those systems requiring groundwater monitoring) shall be analyzed
for the following parameters. Background groundwater sampling data may be
required for new sites prior to the use of the site using similar parameters.
For existing or expanding sites the Department may eliminate any parameter
based on actual site information, wastewater characteristics or the groundwater
data from consistent wastewater plant operations. Groundwater sampling may be
required for existing sites (with no current groundwater monitoring wells), or
expanding sites prior to the permitting of the expansion, to determine actual
groundwater conditions.
(i) Water table
elevation and water table depth
(ii) [Reserved]
(iii) Chloride
(iv) Ammonia
(NH3)
(v)
Nitrate (N)
(vi)
[Reserved]
(vii) pH
(field)
(viii) Sodium
(ix) Total dissolved solids (TDS) This
parameter may be added to the continuing groundwater monitoring based on the
result of field specific conductance.
(x) Field specific conductance
(12) Additional parameters may be
required in the initial background groundwater analysis and subsequent
monitoring thereafter, but such needs will be assessed on an individual project
basis. Any pollutant required for monitoring under effluent guidelines ( 40 CFR
Part 136; Subchapter N ( 40 CFR Parts 400 through 402 and 404 through 471))
may be required (in a permit) to be monitored in groundwater.
(13) The Department may require the applicant
provide a nutrient balance which may include, but not be limited to, nutrient
uptake of the proposed groundcover, crop or silviculture, design application
rates, size and soil conditions present, and the total nutrient loading to the
application site. The Department may adjust the application rates to each site
based on the nutrient balance.
(c) Rapid Infiltration.
(1) New or expansions.
(i) New or expanding rapid infiltration
basins must be limited to sites where the minimum separation of seasonal high
groundwater table will remain 15 feet or more below the basin bottom throughout
the year. Consideration may be given to separation of the seasonal high water
table by less than 15 feet based on an evaluation of the quality of the
effluent being applied. Consideration may also be given to a site when the
seasonal high water table is less than 15 feet at some times but the actual
separation of the water table is at least 15 feet at any time application
occurs.
(ii) The annual hydraulic
loading rates shall be no greater than fifteen percent (15%) of the lowest
measured basin infiltration rate, unless approved by the Department. Loading
rates may also be adjusted by the Department based on the pollutant loading
parameters, including any pollutant required for monitoring under effluent
guidelines ( 40 CFR Part 136; Subchapter N ( 40 CFR Parts 400 through 402 and
404 through 471). The applicant for domestic wastewater or other systems with
a nitrate or nitrogen loading may be required to provide the Department, a
nitrate to nitrogen loading balance to determine if the application rates shall
be adjusted.
(iii)
(A) cation to rest cycle shall consist of no
less than a 1:4 ratio in the summer period (March-October) and a 1:6 ratio in
the winter period (November-February). The Department may consider other
information (e.g., temperature data) to modify the design summer and winter
periods for specific sites.
(B) The
Department may require the permittee whenever the scheduled resting cycle fails
to restore infiltration rates to acceptable levels, to recondition the basin
surface (e.g. by scraping and/or loosening of the soil surface by discing or
harrowing).
(iv) The
design hydraulic loading rate to the rapid infiltration basin shall be
calculated to include monthly average precipitation rates for the site area.
The most restrictive soil horizon shall have a 2 inches/hour infiltration rate
or greater.
(v) The water table
mound shall be maintained 6 feet or more below the bottom of the infiltration
basin during effluent application. The Department may require the permittee to
modify the application rate to achieve this separation.
(vi) Drinking water supply wells shall be
protected from potential groundwater contamination by a minimum buffer zone of
at least 1,000 feet beyond the rapid infiltration basin. A greater distance may
be required by the Department in some cases depending on local hydrogeologic
conditions.
(vii) The minimum
number of groundwater monitoring wells shall be one up-gradient and one
down-gradient for each infiltration basin. Additional wells may be required
depending on the hydrogeologic conditions and/or basin size and number of
basins. There shall be a minimum of two down-gradient wells or one per
infiltration basin, whichever is greater.
(viii) Groundwater samples for new rapid
infiltration basins shall be analyzed for the following parameters. For
expanding rapid infiltration basins, the Department may eliminate any parameter
based on actual site information, wastewater characteristics or the groundwater
data from consistent wastewater plant operations:
(A) Water table elevation and water table
depth
(B) [Reserved]
(C) Chloride
(D) Ammonia
(NH3)
(E)
Nitrate (N)
(F)
[Reserved]
(G) pH (field)
(H) Sodium
(I) Total dissolved solids (TDS)
(J) [Reserved]
(ix) Additional parameters may be required in
the initial background groundwater analysis and subsequent monitoring
thereafter, but such needs will be assessed on an individual project basis. Any
pollutant required for monitoring under effluent guidelines ( 40 CFR Part 136;
Subchapter N ( 40 CFR Parts 400 through 402 and 404 through 471)) may be
required (in a permit) to be monitored in groundwater.
(2) All other rapid infiltration facilities.
(i) The minimum number of groundwater
monitoring wells shall be one up-gradient and one down-gradient per each
infiltration basin. Additional wells may be required depending on the
hydrogeologic conditions and/or basin size and number of basins. There shall be
a minimum of two down-gradient wells or one per infiltration basin, whichever
is greater.
(ii) Groundwater
samples for other rapid infiltration basins shall be analyzed for the following
parameters. The Department may eliminate any parameter based on actual site
information or the groundwater data from consistent wastewater plant
operations:
(A) Water table elevation and
water table depth
(B)
[Reserved]
(C) Chloride
(D) Ammonia
(NH3)
(E)
Nitrate (N)
(F)
[Reserved]
(G) pH (field)
(H) Sodium
(I) Total dissolved solids (TDS)
(J) (Reserved]
(iii) Additional parameters may be required
in the initial background groundwater analysis and subsequent monitoring
thereafter, but such needs will be assessed on an individual project basis. Any
pollutant required for monitoring under effluent guidelines ( 40 CFR Part 136;
Subchapter N ( 40 CFR Parts 400 through 402 and 404 through 471)) may be
required (in a permit) to be monitored in groundwater.
(d) Overland Flow.
(1) New or expansions.
(i) Any discharge to Surface Waters of the
State shall require an NPDES permit issued in accordance with
R.61-9.122.
(ii) Overland flow
systems shall be designed so that the surface water and groundwater standards
(R.61-68) shall be
maintained.
(iii)
(A) The applicant must include as part of the
design for a new or expanding overland flow project, at least three ring and
infiltrometer tests which shall be performed on the most permeable soil type(s)
encountered during the soil borings.
(B) If, during the infiltration tests, the
soils at the site are found to be more permeable than 0.2 in/hr, groundwater
monitoring wells around the system as specified in paragraph (vi)(A) below
shall be provided.
(iv)
The permittee shall be required to maintain a water-tolerant turf grass that
will facilitate the treatment of wastewater. Alternative proposed groundcover,
crops or silviculture may be requested by the applicant. The Department may
approve alternative covers.
(v) The
overland flow design application period shall not exceed 12 hours per day for
each terrace or slope or portion thereof. The NPDES or land application permit
issued for the overland flow facility shall provide specific discharge flow
limits or application rates.
(vi)
(A) For those overland flow systems requiring
groundwater monitoring, the minimum number of groundwater monitoring wells is
one up-gradient of the entire overland flow system and two down-gradient of
each area to be monitored.
(B)
Groundwater monitoring wells may not be required at overland flow systems
containing surficial permeable soils if they are engineered such that partially
treated wastewater will not contact groundwater.
(vii) Groundwater monitoring (if required by
the Department) for overland flow systems shall be analyzed for the following
parameters. The Department may eliminate any parameter based on actual site
information, wastewater characteristics or the groundwater data from consistent
wastewater plant operations:
(A) Water table
elevation and water table depth
(B)
(Reserved)
(C) Chloride
(D) Ammonia
(NH3)
(E)
Nitrate (N)
(F)
[Reserved]
(G) pH (field)
(H) Sodium
(I) Total dissolved solids (TDS)
(J) [Reserved]
(viii) Additional parameters may be required
in the initial background groundwater analysis and subsequent monitoring
thereafter, but such needs will be assessed on an individual project basis. Any
pollutant required for monitoring under effluent guidelines ( 40 CFR Part 136;
Subchapter N ( 40 CFR Parts 400 through 402 and 404 through 471)) may be
required (in a permit) to be monitored in groundwater.
(2) All other facilities.
(i)
(A) The
minimum number of monitoring wells is one up-gradient of the entire overland
flow system and two down-gradient of each area to be monitored.
(B) Groundwater monitoring wells may not be
required at overland flow systems containing surficial permeable soils if they
are engineered such that partially treated wastewater will not contact
groundwater.
(ii)
Groundwater monitoring (if required by the Department) for overland flow
systems shall be analyzed for the following parameters. The Department may
eliminate any parameter based on actual site information or the groundwater
data from consistent wastewater plant operations:
(A) Water table elevation and water table
depth
(B) [Reserved]
(C) Chloride
(D) Ammonia
(NH3)
(E)
Nitrate (N)
(F)
[Reserved]
(G) pH (field)
(H) Sodium
(I) Total dissolved solids (TDS)
(J) [Reserved]
(iii) Additional parameters may be required
in the initial background groundwater analysis and subsequent monitoring
thereafter, but such needs will be assessed on an individual project basis. Any
pollutant required for monitoring under effluent guidelines ( 40 CFR Part 136;
Subchapter N ( 40 CFR Parts 400 through 402 and 404 through 471)) may be
required to be monitored (in a permit) in groundwater.
(e) Tile Field.
(1) New or expanding.
(i) The submission and information
requirements will be determined by the Department.
(ii) A public entity shall own the system and
shall be responsible for the operation, maintenance and replacement of all
components unless otherwise approved by the Department. The Department may
consider a request for a private entity or person, however the proposal must be
evaluated on a case by case basis. The Department can evaluate the capability
of reliable system operation in its evaluation.
(iii) If the project is owned by a private
entity or person, the Department shall require financial assurances for the
operation and maintenance of the system. This financial assurance would
typically be required for residential or domestic wastewater sources.
(iv) [Reserved]
(v) A program for monitoring the quality of
groundwater may be established for domestic systems (having contributions from
industrial facilities), for applicable industrial wastewater systems and other
systems, if required by the Department.
(vi) Groundwater monitoring (if required by
the Department) for tile field systems shall be analyzed for the following
parameters. The Department may eliminate any parameter based on actual site
information, wastewater characteristics or the groundwater data from consistent
wastewater plant operations:
(A) Water table
elevation and water table depth
(B)
[Reserved]
(C) Chloride
(D) Ammonia
(NH3)
(E)
Nitrate (N)
(F)
[Reserved]
(G) pH (field)
(H) Sodium
(I) Total dissolved solids (TDS) This
parameter may be added to the continuing groundwater monitoring based on the
result of field specific conductance.
(J) Field Specific Conductance
(vii) Additional parameters may be
required in the initial background groundwater analysis and subsequent
monitoring thereafter, but such needs will be assessed on an individual project
basis. Any pollutant required for monitoring under effluent guidelines ( 40 CFR
Part 136; Subchapter N ( 40 CFR Parts 400 through 402 and 404 through 471))
may be required to be monitored (in a permit) in groundwater.
(2) All other tile field
facilities.
(i) A program for monitoring the
quality of groundwater may be established for domestic systems (having
contributions from industrial facilities), for applicable industrial wastewater
systems and other systems, if required by the Department.
(ii) Groundwater monitoring (if required by
the Department) for other tile field systems shall be analyzed for the
following parameters. The Department may eliminate any parameter based on
actual site information or the groundwater data from consistent wastewater
plant operations:
(A) Water table elevation
and water table depth
(B)
[Reserved]
(C) Chloride
(D) Ammonia
(NH3)
(E)
Nitrate (N)
(F)
[Reserved]
(G) pH (field)
(H) Sodium
(I) Total dissolved solids (TDS) or Field
specific conductance
(J)
[Reserved]
(iii)
Additional parameters may be required in the initial background groundwater
analysis and subsequent monitoring thereafter, but such needs will be assessed
on an individual project basis. Any pollutant required for monitoring under
effluent guidelines ( 40 CFR Part 136; Subchapter N ( 40 CFR Parts 400 through
402 and 404 through 471)) may be required (in a permit) to be monitored in
groundwater.
(f) Percolation or Evaporation Basins.
(1) A groundwater monitoring program may be
required by the Department for existing systems to determine if there is a need
to evaluate the groundwater conditions at the site to assure compliance with
State Water Quality Standards R.61-68. If a deleterious impact
to the groundwaters of the State from the permitted use or disposal practices
is documented, through groundwater monitoring levels exceeding the standards
set forth in R.61-68 or a significant adverse
trend occurs, then it will be the obligation of the permittee as directed by
the Department to conduct an investigation to determine the vertical and
horizontal extent of groundwater impact. The Department may require remediation
of the groundwater to within acceptable levels for groundwater as set forth in
R.61-68.
(2) A program for
monitoring the quality of groundwater may be established for domestic systems
(having contributions from industrial facilities), for applicable industrial
wastewater systems and other systems, if required by the Department. The
Department may consider influent characteristics in this determination.
(i) Groundwater monitoring (if required by
the Department). for percolation or evaporation basins shall be analyzed for
the following parameters. The Department may eliminate any parameter based on
actual site information or the groundwater data from consistent wastewater
plant operations:
(A) Water table elevation
and water table depth
(B)
[Reserved]
(C) Chloride
(D) Ammonia
(NH3)
(E)
Nitrate (N)
(F)
[Reserved]
(G) pH (field)
(H) Sodium
(I) Total dissolved solids (TDS)
(J) [Reserved]
(ii) Additional parameters may be required in
the initial background groundwater analysis and subsequent monitoring
thereafter but such needs will be assessed on an individual project basis. Any
pollutant required for monitoring under effluent guidelines ( 40 CFR Part 136;
Subchapter N ( 40 CFR Parts 400 through 402 and 404 through 471)) may be
required (in a permit) to be monitored in groundwater.
(g)
(1) Spray irrigation or land application of
sewage sludge shall be in accordance with R.61-9.503. Spray irrigation or
land application of Industrial sludge shall be in accordance with
R.61-9.504.
(2) If total suspended
solids concentration of the treated wastewater solids or sludge is less than
2000 mg/l the Department may require the facility to comply with the additional
requirements for land application of wastewater
(R.61-9.505.42(b)(b)).
(h) Reclaimed wastewater systems.
(1) Provided the level of treatment meets the
requirement outlined in section505.45(i)(i), there would not be specific buffer
area requirements.
(2) A
groundwater monitoring program may be required by the Department for existing
or new systems to determine if there is a need to evaluate the background
groundwater conditions at the site to assure compliance with State Water
Quality Standards R.61-68.
(3)
Piping shall be clearly marked to identify reclaimed water lines and the
Department may establish specific guidelines for use of reclaimed water
systems.
(4) Reclaimed wastewater
systems may be required to provide covered storage systems (or other
alternative methods) to maintain effluent quality prior to
distribution.