Current through Register Vol. 48, No. 38, September 20, 2024
a)
The use of rapid rate gravity filters requires pretreatment.
b) For community water supplies treating
surface water, groundwater under the direct influence of surface water, or
using lime soda softening treatment, unless otherwise approved by the Agency
under Section 604.145(b), the
nominal filtration rates must not exceed 3
gal/min/ft2 of filter area for single media filters
and 5 gal/min/ft2 for multi-media filters.
Filtration rates must be reduced when treated water turbidity exceeds the
standards in 35 Ill. Adm. Code 611.
c) For community water supplies treating
groundwater and not using lime soda softening treatment, unless otherwise
approved by the Agency under Section
604.145(b), the
rate of filtration must not exceed 4 gal/min/ft2 of
filter area.
d) Number of Filter
Units
1) A minimum of two units must be
provided. Each unit must be capable of meeting the plant design capacity or the
projected maximum daily demand at the approved filtration rate.
2) Where more than two filter units are
provided, the filters must be capable of meeting the plant design capacity at
the approved filtration rate with one filter removed from service.
3) Where declining rate filtration is
provided, the variable aspect of filtration rates and the number of filters
must be considered when determining the design capacity for the
filters.
e) Structural
Details and Hydraulics. The filter structure must be designed to provide for
the following:
1) vertical walls within the
filter;
2) no protrusion of the
filter walls into the filter media;
3) cover by superstructure;
4) head and walking room to permit normal
inspection and operation;
5)
minimum depth of filter box of
8.5 feet;
6) minimum water depth over the surface of
the filter media of 3 feet;
7)
trapped effluent to prevent backflow of air to the bottom of the
filters;
8) prevention of floor
drainage to the filter with a minimum 4-inch curb around the filters;
9) prevention of flooding by providing
overflow;
10) maximum velocity of
treated water in pipe and conduits to filters of 2 ft/sec;
11) cleanouts and straight alignment for
influent pipes or conduits where solids loading is heavy, or following lime
soda softening;
12) construction to
prevent cross-connections, short-circuiting, or common walls between potable
and non-potable water; and
13) wash
water drain capacity to carry maximum flow.
f) Wash water troughs must be constructed
such that:
1) the bottom elevation is above
the maximum level of expanded media during washing;
2) a 2-inch freeboard is provided at the
maximum rate of wash;
3) the top
edge is level and is all at the same elevation;
4) troughs are spaced so that each trough
serves the same number of square feet of filter area; and
5) the maximum horizontal travel of suspended
particles to reach the trough does not exceed 3 feet.
g) The filter media must be composed of clean
silica sand or other natural or synthetic media free from detrimental chemical
or bacterial contaminants and must meet the following requirements:
1) a total depth of not less than 24
inches;
2) a uniformity coefficient
of the smallest material not greater than
1.65;
3) a minimum of 12 inches of media with an
effective size range of
0.45 mm to
0.55 mm;
4) filter media specifications:
A) Filter anthracite must consist of hard,
durable anthracite coal particles of various sizes. Blending of non-anthracite
material is not acceptable. Anthracite must have:
i) an effective size of
0.45 mm to
0.55 mm with a uniformity
coefficient not greater than
1.65 when used alone;
ii) an effective size of
0.8 mm to
1.2 mm with a uniformity
coefficient not greater than
1.7 when used as a
cap;
iii) an effective size less
than 0.8 mm for anthracite used as a
single media on potable groundwater for iron and manganese removal only
(effective sizes greater than
0.8 mm may be approved based
upon on-site pilot plant studies);
iv) a specific gravity greater than
1.4;
v) an acid solubility less than 5 percent;
and
vi) a Moh's scale of hardness
greater than 2.7.
B) Sand must have:
i) an effective size of
0.45 mm to
0.55 mm;
ii) a uniformity coefficient of not greater
than 1.65;
iii) a specific gravity
greater than 2.5; and
iv) an acid solubility less than 5
percent.
C) High-density
sand must consist of hard, durable, and dense grain garnet, ilmenite, hematite
or magnetite, or associated minerals of those ores that will resist degradation
during handling and use, and must:
i) contain
at least 95 percent of the associated material with a specific gravity of
3.8 or higher;
ii) have an effective size of
0.2 to
0.3 mm;
iii) have a uniformity coefficient of not
greater than 1.65; and
iv) have an
acid solubility less than 5 percent.
D) Granular activated carbon as a single
media may be considered for filtration only after pilot or full-scale testing
and with prior approval of the Agency. The design must include the following:
i) The media must meet the basic
specifications for filter media in subsections (g)(1) through (g)(3).
ii) There must be provisions for a free
chlorine residual and adequate contact time in the water following the filters
and prior to distribution.
iii)
Provisions must be made for frequent replacement or regeneration.
E) Other media types or
characteristics must be approved by the Agency;
5) supporting media designed as follows based
on the type of filter material:
A) A
three-inch layer of torpedo sand must be used as a supporting media for filter
sand when supporting gravel is used, and must have:
i) an effective size of
0.8 mm to
2.0 mm; and
ii) a uniformity coefficient not greater than
1.7.
B) Gravel
i) When gravel is used as the supporting
media, it must consist of cleaned and washed, hard, durable, rounded silica
particles and must not include flat or elongated particles.
ii) The coarsest gravel must be
2.5 inches in size when the
gravel rests directly on a lateral system, and must extend above the top of the
perforated laterals.
iii) Not less
than four layers of gravel must be provided in accordance with the following
size and depth distribution:
Size |
Depth |
21/2 to 11/2 inches |
5 to 8 inches |
11/2 to 3/4 inches |
3 to 5 inches |
3/4 to 1/2 inches |
3 to 5 inches |
1/2 to 3/16 inches |
2 to 3 inches |
3/16 to 3/32 inches |
2 to 3 inches |
iv)
Reduction of gravel depths and other size gradations may be approved by the
Agency upon justification for slow sand filtration or when proprietary filter
bottoms are specified.
h) Filter Bottoms and Strainer Systems
1) Water quality must be reviewed before the
use of porous plate bottoms to prevent clogging and failure of the underdrain
system.
2) The design of manifold
type collection systems must:
A) minimize loss
of head in the manifold and laterals;
B) ensure even distribution of washwater and
even rate of filtration over the entire area of the filter;
C) provide the ratio of the area of the
strainer systems' final openings to the area of the filter at about
0.003;
D) provide the total cross-sectional area of
the laterals at about twice the total area of the final openings;
E) provide the cross-sectional area of the
manifold at 1.5 to 2 times the total area of
the laterals; and
F) direct lateral
perforations without strainers downward.
3) The Agency may approve departures from
these standards for high-rate filters and propriety bottoms.
i) The following appurtenances
must be provided for every filter:
1) influent
and effluent sampling taps;
2) a
gauge indicating loss of head;
3) a
meter indicating the instantaneous rate of flow;
4) a pipe for filtering to waste that has a
six-inch or larger air gap, or other Agency-approved cross-connection control
measure;
5) a continuously
recording Nephelometer capable of measuring and recording filter effluent
turbidity at maximum 15-minute intervals, and with alarm capability to notify
the operator if filtered water turbidity exceeds
0.3 NTU (Nephelometric
Units);
6) an adjustable-rate valve
to allow the operator to gradually control the flow rate increase when placing
the filters back into operation; and
7) a hose and storage rack for washing filter
walls.
j) Backwash.
Provisions must be made for washing filters as prescribed in this subsection.
1) The community water supply must use
filtered water provided at the required rate by washwater tanks or a dedicated
washwater pump to wash the filters.
2) Backwash rate must meet the following
requirements:
A) a minimum rate of 15
gal/min/ft2, consistent with water temperatures and
specific gravity of the filter media;
B) a rate sufficient to provide for a 50
percent expansion of the filter bed; and
C) a reduced rate of 10
gal/min/ft2 for full depth anthracite or granular
activated carbon filters, upon approval by the Agency.
3) Washwater pumps in duplicate must be
provided unless an alternate means of obtaining washwater is
available.
4) The main washwater
line must have a regulator or valve to obtain the desired rate of filter wash
with the washwater valves on the individual filters open wide.
5) The main washwater line or backwash waste
line must have a rate of flow indicator, preferably with a totalizer, located
so that it can be easily read by the operator during the washing
process.
6) Rapid changes in
backwash water flow must be prevented.
7) Backwash must be completed with an
operator in attendance to initiate the backwash cycle and to control the
return-to-service procedure to assure that the effluent turbidity is less than
0.3 NTU when the filter is
placed back into operation for discharge to the clearwell.
8) Appropriate measures for cross-connection
control must be provided.
k) Surface or subsurface wash facilities are
required except for filters used exclusively for iron, radionuclides, arsenic,
or manganese removal. Wash facilities may include a system of fixed nozzles or
a revolving-type apparatus. All devices must be designed:
1) to provide water pressures of at least 45
psi;
2) to prevent back-siphonage
by properly installing a vacuum breaker or other approved device, if connected
to the treated water system; and
3)
to provide a rate of flow of
2.0
gpm/ft2 of filter area with fixed nozzles or
0.5
gpm/ft2 with revolving arms.
l) Air scouring may be used in place of
surface wash if the air scouring meets the following requirements:
1) Air flow for air scouring the filter must
be 3 to 5 ft3/min/ft2 of
filter area when the air is introduced into the underdrain; a lower air rate
must be used when the air scour distribution system is placed above the
underdrains;
2) A method to avoid
filter media loss during backwashing must be provided;
3) Air scouring must be followed by a
fluidization wash sufficient to restratify the media;
4) Air must be free from
contamination;
5) If air scour
distribution systems are placed at the media and supporting bed interface, the
air scour nozzles must be designed to prevent media from clogging the nozzles
or the air entering the air distribution system;
6) Piping for the air distribution system
must not be flexible hose or other soft material;
7) Air delivery piping must not:
A) pass down through the filter media;
and
B) have any arrangement in the
filter design that would allow short-circuiting between the applied unfiltered
water and the filtered water;
8) When air scouring is being used, the
backwash rate must be variable and must not exceed 8 gal/min, unless a higher
rate is necessary to remove scoured particles from filter media surfaces;
and
9) Air scouring piping must not
be installed in the underdrain unless the underdrain was designed to
accommodate the piping.