Idaho Administrative Code
Title IDAPA 58 - Environmental Quality, Department of
Rule 58.01.08 - IDAHO RULES FOR PUBLIC DRINKING WATER SYSTEMS
Section 58.01.08.520 - FACILITY AND DESIGN STANDARDS: SURFACE WATER TREATMENT: CLARIFICATION PROCESSES

Universal Citation: ID Admin Code 58.01.08.520

Current through August 31, 2023

Treatment facilities designed to include clarification for processing surface water shall meet the following requirements: (3-24-22)

01. Two Units Required. A minimum of two (2) units for redundancy shall be provided for flocculation and sedimentation such that plant design capacity can be maintained with any component out of service for maintenance or repairs. (3-24-22)

02. Parallel or Serial Operation. The units shall be capable of being operated either in series or parallel where softening is performed. (3-24-22)

03. Independent Units. The units shall be constructed in such a way that each can be taken out of service without disrupting operation, and with drains or pumps sized to allow dewatering in a reasonable period of time. (3-24-22)

04. Manual Start-Up. The units shall be started manually following shutdown. (3-24-22)

05. Pre-Treatment. Waters exhibiting high turbidity may require pretreatment, usually sedimentation with or without the addition of coagulation chemicals. When presedimentation is provided, the following requirements must be met: (3-24-22)

a. Incoming water shall be dispersed across the full width of the line of travel as quickly as possible. Short circuiting must be prevented. (3-24-22)

b. Provisions for bypassing pre-sedimentation basins shall be included. (3-24-22)

c. The need for redundant pretreatment components shall be evaluated according to the type and necessity of the pretreatment. (3-24-22)

06. Rapid Mix. Unless otherwise approved by the Department based on documentation provided by the design engineer, a rapid mix device or chamber is required prior to flocculation, clarification, sedimentation, and settler units. The need for redundant rapid mix components shall be evaluated. Rapid mix shall mean the rapid dispersion of chemicals throughout the water to be treated, usually by violent agitation. The engineer shall submit the design basis for the velocity gradient (G value) selected, considering the chemicals to be added and water temperature, color and other related water quality parameters. Basins or mixing chambers shall be equipped with devices capable of providing adequate mixing for all treatment flow rates. (3-24-22)

07. Flocculation. Flocculation shall mean the gathering together of fine particles in water by gentle mixing after the addition of coagulant chemicals to form larger particles. (3-24-22)

a. Basin inlet and outlet design shall minimize short-circuiting and destruction of floc. A drain, pumps, or a combination of both drain and pumps shall be provided to accomplish dewatering and sludge removal. (3-24-22)

b. The flow-through velocity shall not be less than one-half (0.5) nor greater than one and one-half (1.5) feet per minute with a detention time for floc formation of at least thirty (30) minutes unless otherwise approved by the Department. (3-24-22)

c. Agitators shall be driven by variable speed drives. (3-24-22)

d. Flocculation and sedimentation basins shall be as close together as possible. The velocity of flocculated water through pipes or conduits to settling basins shall be not less than one-half (0.5) nor greater than one and one-half (1.5) feet per second. Allowances must be made to minimize turbulence at bends and changes in direction. (3-24-22)

08. Small Systems May Use Baffling. Baffling may be used to provide for flocculation in small plants upon approval by the Department. (3-24-22)

09. Sedimentation Units. The following criteria apply to conventional sedimentation units: (3-24-22)

a. A minimum of two (2) hours of settling time shall be provided following flocculation unless adequate settling in less time can be demonstrated. (3-24-22)

b. Inlets shall be designed to distribute the water equally and at uniform velocities. (3-24-22)

c. Outlet weirs or submerged orifices shall maintain velocities suitable for settling in the basin and minimize short-circuiting. Outlet weirs shall be designed so that the rate of flow over the outlet weirs or through the submerged orifices shall not exceed twenty-thousand (20,000) gallons per day per foot of the outlet launder. The entrance velocity through the submerged orifices shall not exceed one-half (0.5) feet per second. (3-24-22)

d. The velocity through settling basins shall not exceed one-half (0.5) feet per minute. The basins must be designed to minimize short-circuiting. Fixed or adjustable baffles must be provided as necessary to achieve the maximum potential for clarification. (3-24-22)

e. When an overflow weir or pipe is provided the overflow shall discharge by gravity with a free fall at a location where the discharge will be noted. (3-24-22)

f. Adequate sludge collection equipment that ensures proper basin coverage shall be provided and basins must be provided with a means for dewatering. (3-24-22)

g. Flushing lines or hydrants shall be provided and must be equipped with backflow prevention devices acceptable to the Department. (3-24-22)

h. Sludge removal design shall provide that sludge pipes are not less than three (3) inches in diameter and arranged so as to facilitate cleaning. Entrance to sludge withdrawal piping shall be designed to prevent clogging. Provision shall be made for the operator to observe and sample sludge being withdrawn from the unit. (3-24-22)

i. Sludge shall be disposed of in accordance with applicable regulations, as set forth in Section 540. (3-24-22)

10. Solids Contact Clarifiers. Solids contact clarifiers are generally acceptable for combined softening and clarification where water characteristics, especially temperature, do not fluctuate rapidly, flow rates are uniform and operation is continuous. A minimum of two (2) units are required for surface water treatment as required in Subsection 520.01. (3-24-22)

a. Chemicals shall be applied at such points and by such means as to ensure satisfactory mixing of the chemicals with the water. (3-24-22)

b. Unless otherwise approved by the Department based on documentation provided by the design engineer, a rapid mix device or chamber ahead of the solids contact clarifier is required to assure proper mixing of the chemicals applied. Mixing devices employed shall be constructed so as to provide good mixing of the raw water with previously formed sludge particles and prevent deposition of solids in the mixing zone. (3-24-22)

c. Flocculation equipment shall be adjustable as to speed, pitch, or a combination of speed and pitch and must provide for coagulation in a separate chamber or baffled zone within the unit. (3-24-22)

d. Sludge removal design shall provide that sludge pipes are not less than three (3) inches in diameter and arranged so as to facilitate cleaning. Entrance to sludge withdrawal piping shall be designed to prevent clogging. Provision shall be made for the operator to observe and sample sludge being withdrawn from the unit. (3-24-22)

e. Blow-off outlets and drains must terminate and discharge at places acceptable to the Department in regard to control of potential cross connections. Cross connection control must be included for the potable water lines used to backflush sludge lines. (3-24-22)

f. The detention time shall be established on the basis of the raw water characteristics and other local conditions that affect the operation of the unit. The Department may request data to support decisions made with respect to detention times. The Department may alter detention time requirements. (3-24-22)

g. Controls for sludge withdrawal which minimize water losses shall be provided. (3-24-22)

h. Unless otherwise approved by the Department based on documentation provided by the design engineer, weirs shall be adjustable and at least equivalent in length to the perimeter of the tank. Weir loading shall not exceed ten (10) gallons per minute per foot of weir length for units used as clarifiers or twenty (20) gallons per minute per foot of weir length for units used for softening. Where orifices are used, the loading rates per foot of launder rates shall be equivalent to weir loadings. Either shall produce uniform rising rates over the entire area of the tank. (3-24-22)

i. Upflow rates shall not exceed one (1) gallon per minute per square foot of area at the sludge separation line for units used as clarifiers or one and three-quarters (1.75) gallons per minute per foot of area at the slurry separation line for units used as softeners. The Department may consider higher rates if supporting data is provided. (3-24-22)

11. Settler Units. Settler units consisting of variously shaped tubes or plates installed in multiple layers and at an angle to the flow may be used for sedimentation following flocculation. (3-24-22)

a. Inlets and outlets shall be designed to maintain velocities suitable for settling in the basin and to minimize short-circuiting. Plate units shall be designed to minimize unequal distribution across the units. (3-24-22)

b. Drain piping from the settler units must be sized to facilitate a quick flush of the settler units and to prevent flooding other portions of the plant. (3-24-22)

c. Although most units will be located within a plant, outdoor installations must provide sufficient freeboard above the top of settlers to prevent freezing in the units. (3-24-22)

d. Water shall be applied to tube settlers at a maximum rate of two (2) gallons per minute per square foot of cross-sectional area for tube settlers, unless higher rates are justified through pilot plant or in-plant demonstration studies. See Subsection 501.19 for general information on conducting pilot studies. (3-24-22)

e. Water shall be applied to plate settlers at a maximum plate loading rate of one-half (0.5) gallons per minute per square foot, based on eighty (80) percent of the projected horizontal plate area. (3-24-22)

f. Flushing lines shall be provided to facilitate maintenance and must be properly protected against backflow or back siphonage. (3-24-22)

12. High Rate Clarification. High rate clarification processes may be approved upon demonstrating satisfactory performance under on-site pilot plant conditions or documentation of full scale plant operation with similar raw water quality conditions. Reductions in detention times and/or increases in weir loading rates shall be justified. See Subsection 501.19 for general information on conducting pilot studies. Examples of such processes include dissolved air flotation, ballasted flocculation, contact flocculation/clarification, and helical upflow. (3-24-22)

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