35 Ill. Adm. Code 3700.370.1130
Low Rate Intermittent or Periodically Dosed Sand Filters
Section 370
TITLE 35: ENVIRONMENTAL PROTECTION
SUBTITLE C: WATER POLLUTION
CHAPTER II: ENVIRONMENTAL PROTECTION AGENCY
PART 370 ILLINOIS RECOMMENDED STANDARDS FOR SEWAGE WORKS
SECTION 370.1130 LOW RATE INTERMITTENT OR PERIODICALLY DOSED SAND FILTERS
Section 370.1130 Low Rate
Intermittent or Periodically Dosed Sand Filters
a) Applicability
1) Intermittent sand filters may be used to polish secondary
effluents. The process removes residual suspended solids and soluble
biochemical oxygen demand and converts ammonia to nitrate. (See Section
370.1210(b).)
2) Cold weather operational problems may preclude the use of this
process unless the influent temperature to the filter is adequate to allow
efficient filter operation necessary to meet the applicable effluent standards.
3) Because of manual labor necessary to clean, maintain and
replace sand on the filters, the application is usually limited to small waste
treatment plants.
b) Design Criteria
The criteria
of Section 370.940(b), (c), and (f)(3), are generally applicable to
intermittent sand filters used as tertiary filtration units.
1) Dosing Volumes
The dosing
facilities shall be sized to provide for a 12-hour dosing cycle for each bed.
2) Siphon or Pump Capacity
Siphons (at
minimum head) or pumps shall have a discharge capacity at least 100 percent in
excess of the maximum rate of inflow to the dosing tank, including
recirculation, and at average head, at least 90 gallons per minute per 1,000
square feet being dosed.
3) Recirculation
Provision for
recirculation of filter effluent may be included to improve process
flexibility.
A) Rate
A
recirculation rate of up to 100% of design average flow to the filter may be
provided.
B) Variability
Capability for
varying the recirculation rate shall be provided.
4) Loading Rates
The hydraulic
load of secondary wastewater applied to supplemental intermittent sand filters
shall not exceed 15 gallons per day (gpd)/sq. ft. More conservative
application rates should be provided for low quality filter influents. Refer
to subsection (d)(3) below.
c) Construction Details
The criteria
of Section 370.940(g) are generally applicable to tertiary intermittent sand
filters. Also, refer to subsection (d).
d) Special Design Considerations in Lagoon Systems
1) General
Low rate sand
filter systems that are intermittently or periodically dosed may be used to
reduce suspended solids from multicell aerated or nonaerated sewage lagoon
treatment plants.
2) Cold Weather Design
Lagoons which
have sand filters shall be designed to provide storage of flows received during
cold weather when the filter is expected to be inoperable.
3) Hydraulic Loading
A) The filter area design considerations must include the following:
i) The total annual flow volume to be treated (Section
370.520(c)(1)) including wet weather flows if the lagoons are to be used for
wet weather storage.
ii) The effective net days annually for filter operation
excluding cold weather shut-down and filter maintenance time.
iii) Lagoon
effluent quality.
iv) Extent
and reliability of flow data from the sewer system.
B) Where sewer system conditions are not favorable or industrial
waste loadings are expected to increase algae blooms, the loading rate should
be limited to 10 gal./ft.(2)/day.
4) Dosing Considerations
A) Methods of Operation
The design
should include allowance for periodic dosing of varied volumes onto the filter
while the filter discharge is shut off, then to be followed by a filtration
period to completely empty the filter at a controlled rate.
B) Depth
The filter
shall be designed for flexibility of dosing depth from 6 inches to 2 feet.
C) Valving, Piping, Flow Measurement
i) The filter shall be provided with valving to allow shutting
off and controlling rate of flow both onto and from the filter. A flow
measurement weir or flume shall be provided both on the inlet and outlet of the
filter for operator control of the dosing and filtration rates under the
falling head conditions.
ii) The outlet valving, piping and flow measurement shall be
designed to allow complete drainage of the filter underdrains at the end of the
filter cycle to insure aerobic conditions in the filter during the rest period.
D) Dosing Inlet Structures
The dosing
inlet structures shall be designed to dissipate inlet velocity and prevent sand
scouring during the dosing period at the high dose rates. The inlet structures
should be arranged to not interfere with maintenance of the sand surface.
5) Filter Containment Structure
The filter
containment may be of vertical concrete walls on three sides (refer to
subsection (d)(6) below) or sloped earthen berms with impervious lining,
constructed to insure that no ground surface runoff or silts get onto the sand
surface. A freeboard of 1 foot above the maximum design dosing depth should be
provided.
6) Access Ramps
The filter
should be designed with a ramp on one end sloped and surfaced for access to the
edge of the bed by wheeled vehicle to facilitate removing and replacement of
sand. For larger filters, concrete tracks at the level of the sand surface may
be desirable to reduce distance sand must be handled.