35 Ill. Adm. Code 370.710
Design Considerations
Section 370
Section 370.710 Design
Considerations
a) Dimensions
The minimum length of flow from inlet to outlet should be 10
feet unless special provisions are made to prevent short circuiting. The
sidewater depth for primary clarifiers shall be as shallow as practicable, but
not less than 7 feet. Clarifiers following the activated sludge process shall
have sidewater depths of at least 12 feet to provide adequate separation zone
between the sludge blanket and the overflow weirs. Clarifiers following fixed
film reactors shall have sidewater depth of at least 7 feet.
b) Surface Settling Rates (Overflow Rates)
The hydraulic design of settling tanks shall be based on the
anticipated peak hourly flow.
1) Primary and Bypass Settling Tanks
A) Primary Settling
Some indication of BOD removals may be obtained by reference
to Appendix E, Figure No. 2. The figure should not be used to design units
which receive wastewaters which have BOD and total suspended solids
concentrations which are substantially different from normal domestic sewage.
The operating characteristics of such units should be established by
appropriate field and laboratory tests. If activated sludge is wasted to the
primary settling unit, then the design surface settling rate shall not exceed
1,000 gallons per day per square foot based on design peak hourly flow,
including all flows to the unit. Refer to subsection (b)(3) and Section
370.820.
B) Combined Sewer Overflow and Bypass Settling
The maximum surface settling rate shall not exceed 1,800
gallons per day per square foot based on peak hourly flow. Minimum liquid
depth shall not be less than 10 feet. Minimum detention shall not be less than
one hour. The minimum length of flow from inlet baffle to outlet should be 10
feet, unless special provisions are made to prevent short-circuiting.
2) Intermediate Settling Tanks
Surface settling rates for intermediate settling tanks
following series units of fixed film reactor processes should not exceed 1500
gallons per day per square foot based on design peak hourly flow. Surface
settling rates for intermediate settling tanks following the activated sludge
process shall not exceed 1000 gallons per day per square foot based on design
peak hourly flow.
3) Final Settling Tanks
Settling tests should be conducted wherever a pilot study of
biological treatment is warranted by unusual waste characteristics or treatment
requirements. Testing shall be done where proposed loadings go beyond the
limits set forth in subsections (b)(3)(A) and (b)(3)(B).
A) Final Settling Tanks - Fixed Film Biological Reactors
Surface settling rates for settling tanks following trickling
filters or rotating biological contactors shall not exceed 1000 gallons per day
per square foot based on design peak hourly flow.
B) Final Settling Tanks - Activated Sludge
i) Multiple units capable of independent operation shall be
provided at all plants. To perform properly while producing a concentrated
return flow, activated sludge settling tanks must be designed to meet
thickening as well as solids separation requirements.
ii) Since the rate of recirculation of return sludge is quite
high in activated sludge processes, surface settling rate and weir overflow
rate should be adjusted for the various processes to minimize the problems with
sludge loadings, density currents, inlet hydraulic turbulence, and occasional
poor sludge settleability.
iii) The hydraulic loadings shall not exceed 1000 gallons per day
per square foot based on design peak hourly flow, and 800 gallons per day per
square foot based on peak hourly flow for separate activated sludge
nitrification stage. Refer to Section 370.1210(c)(4).
iv) The solids loading shall not exceed 50 pounds solids per day
per square foot at the design peak hourly rate.
v) Flow equalization is recommended where the peak hourly load
exceeds 300% of the design average load.
C) Rectangular Units
Rectangular final settling tanks following the activated
sludge process frequently exhibit poor solids separation characteristics and
should therefore be avoided. If land availability or other local conditions
mandate the use of rectangular final clarifiers following the activated sludge
process, the following design modifications shall be made:
i) Within practicable limits, length shall be approximately
equal to the width.
ii) Excess
weir length shall be provided.
iii) Baffles shall be provided to interrupt longitudinal density
currents.
iv) Weir placement shall be adjustable, so as to allow
optimization of the upflow takeoff points.
c) Inlet Structures
Inlets and inlet baffling should be designed to dissipate the
inlet velocity, to distribute the flow equally both horizontally and vertically
and to prevent short circuiting. Channels should be designed to maintain a
velocity of at least one foot per second at one-half the design flow. Corner
pockets and dead ends should be eliminated and corner fillets or channeling
used where necessary. Provisions shall be made for prevention or removal of
floating materials in inlet structures.
d) Weirs
1) General
Overflow weirs shall be readily adjustable over the life of
the structure to correct for differential settlement of the tank.
2) Location
Overflow weirs shall be located to optimize actual hydraulic
detention time, and minimize short circuiting.
3) Design Rates
Weir loadings shall not exceed 20,000 gallons per day per
lineal foot based on design peak hourly flows for plants having design average
flows of 1.0 mgd or less. Overflow rates shall not exceed 30,000 gallons per
day per lineal foot based on design peak hourly flow for plants having design
average flow of greater than 1.0 mgd. Higher weir overflow rates may be
allowed for bypass settling tanks. If pumping is required, weir loadings
should be related to pump delivery rates to avoid short circuiting. Refer to
Section 370.410(c)(8).
4) Weir Troughs
Weir troughs shall be designed to prevent submergence at
maximum design flow, and to maintain a velocity of at least one foot per second
at one-half design average flow.
e) Submerged Surfaces
The tops of troughs, beams, and similar submerged construction
elements shall have a minimum slope of 1.4 vertical to 1 horizontal; the
underside of such elements should have a slope of 1 to 1 to prevent the
accumulation of scum and solids.
f) Unit Dewatering
Unit dewatering featuring shall conform to the provisions
outlined in Section 370.530. The bypass design should also provide for
redistribution of the plant flow to the remaining units.
g) Freeboard
Walls of settling tanks shall extend at least 6 inches above
the surrounding ground surface and shall provide not less than 12 inches
freeboard. Additional freeboard or the use of wind screens is recommended
where larger settling tanks are subject to high velocity wind currents that
would cause tank surface waves and inhibit effective scum removal.