PURPOSE: This amendment will retain and add minimum design standards for settling processes that are required to protect or improve public health, safety, and water quality.
PURPOSE: This rule specifies the minimum standards for the design of settling operations that are part of wastewater collection and treatment systems. This rule is to be used with rules 10 CSR 20- 8.110 through 10 CSR 20-8.210. It does not address all aspects of design, and the design engineer may refer to other appropriate reference materials so long as these minimum standards set forth in this rule are met.
Table 160-1. Minimum Side Water Depth.
Type of Settling Tank | Minimum Side Water Depth (ft) |
Primary (>100,000 gpd) | 10 |
Primary (<100,000 gpd) | 7 |
Final following activated sludge process | 12 |
Final following attached growth biological reactor (>100,000 gpd) | 10 |
Final following activated sludge and attached growth biological reactor (<100,000 gpd) | 7 |
Table 160-2. Maximum Primary Settling Tank Surface Overflow Rates.
Type of Primary Settling Tank | Surface Overflow Rates1: | |
At Design Average Flow (gpd/ft2) | At Design Peak Hourly Flow (gpd/ft2) | |
Tanks not receiving waste activated sludge | 1,000 | 3,000 |
Tanks receiving waste activated sludge | 700 | 1,700 |
Chemically enhanced | 1,400 | 1,500 |
1 Calculate surface overflow rates with all flows received at the settling tanks.
Table 160-3. Maximum Activated Sludge Final Settling Tank Rates.
Treatment Process | Surface Overflow Rate at Design Peak Hourly Flow1 (gpd/ft2) | Peak Solids Loading Rate2 (lb/day/ft2) |
With diurnal flow equalization3 | 1,000 | 35 |
Without diurnal flow equalization3 | 150 X Peaking Factor4 | 35 |
Conventional, Step Aeration, Complete Mix, Contact Stabilization, Carbonaceous Stage of Separate Stage Nitrification | 1,200 5 | 40 |
Extended Aeration Single-stage Nitrification | 1,000 | 35 |
Multi-Stage Nitrification | 800 | 35 |
Activated Sludge with Chemical addition to Mixed Liquor for Phosphorus Removal | 900 | 35 |
1 Based on influent flow only.
2 Calculate the peak solids loading rate based on the design maximum day flow rate plus the design maximum return sludge rate requirement and the design mixed liquor suspended solids under aeration.
3 Applicable to wastewater treatment facilities with a design average flow of less than one hundred thousand gaflons per day (100,000 gpd).
4 To determine the peaking factor use 10 CSR 20-8.110(3) Equation 110-1.
5 Wastewater treatment facilities needing to meet twenty milligrams per liter (20 mg/L) suspended solids or less should reduce the surface overflow rate to one thousand gallons per day per square foot (1,000 gpd/ft2).
Table 160-4. Maximum Weir Loading Rates.
Average Wastewater Treatment Facility Capacity (million gallons per day or MGD) | Loading Rate at Design Peak Hourly Flow (gpd/If) |
Less than 0.1 | 10,000 |
0.1 through 1.0 | 20,000 |
Greater than 1.0 | 0,000 |
10 CSR 20-8.160
The secretary of state has determined that the publication of this rule in its entirety would be unduly cumbersome or expensive. The entire text of the material referenced has been filed with the secretary of state. This material may be found at the Office of the Secretary of State or at the headquarters of the agency and is available to any interested person at a cost established by state law.
*Original authority 1972, amended 1973, 1987, 1993.