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TITLE 30ENVIRONMENTAL QUALITY
PART 1TEXAS COMMISSION ON ENVIRONMENTAL QUALITY
CHAPTER 217DESIGN CRITERIA FOR DOMESTIC WASTEWATER SYSTEMS
SUBCHAPTER JSLUDGE PROCESSING
RULE §217.249Sludge Stabilization

      (ii) a higher concentration is justified by the use of a sludge thickening unit upstream of a digester.

    (B) A diffuser must be designed to minimize clogging.

    (C) A diffuser must be removable without dewatering a tank for inspection, maintenance, and replacement. Removable diffusers are not required if the wastewater treatment facility is designed with a redundant basin.

    (D) The volatile solids loading rate must be designed to be at least 100 pounds but not more than 200 pounds of volatile solids per 1,000 cubic feet per day, unless otherwise justified in the engineering report.

    (E) The dissolved oxygen concentration maintained in the liquid in an aerobic digester must be at least 0.5 milligrams per liter.

    (F) If mechanical aerators are used, the energy input for mixing must be at least 0.5 horsepower per 1,000 cubic feet.

    (G) If diffused air mixing is used, the energy input for mixing must be at least 20 standard cubic feet per minute per 1,000 cubic feet of aeration tank.

    (H) An aerobic digester must be able to separate and withdraw solids, or must decant the supernatant.

(u) Heat Stabilization.

  (1) The design of a heat treatment system must be based on the anticipated sludge flow, sludge characteristics, and sludge concentration.

  (2) A heat treatment system must operate continuously to minimize the additional heat input necessary to start up the system, unless justified in the engineering report.

  (3) A heat treatment system must have multiple units, unless storage or an alternate stabilization method is available.

  (4) A single unit heat treatment system must have a standby grinder, a fuel pump, an air compressor, and dual sludge pumps.

  (5) The engineering report must identify the expected downtime for maintenance and repair, based on data from a comparable wastewater treatment facility.

  (6) The engineering report must include a design for adequate storage for process feed and downtime.

  (7) A heat treatment system must provide heat stabilization in a reaction vessel:

    (A) at a minimum of 175 degrees Celsius (350 degrees Fahrenheit) for 40 minutes, but not more than 205 degrees Celsius (400 degrees Fahrenheit) for 20 minutes and at a pressure of not less than 250 pounds per square inch, gauge, but not more than 400 pounds per square inch, gauge; or

    (B) provide for pasteurization at temperatures of 30 degrees Celsius (85 degrees Fahrenheit) or more and gauge pressure of more than 1.0 standard atmosphere (14.7 pounds per square inch) for a period of at least 25 days.

  (8) A heat treatment system must have a sludge grinder to protect a heat exchanger from damage or clogging caused by rags or other debris.

  (9) A heat treatment system must include an acid wash or high-pressure water wash system to remove scale from heat exchangers and reactors.

  (10) A decant tank must have a sludge scraper mechanism and must be covered.

  (11) A heat exchanger must be constructed of corrosion-resistant material.

  (12) A heat treatment system must have a continuous temperature recorder.

(v) Recycle Loads.

  (1) The engineering report must identify a method of treatment for the recycle stream from the heat treatment system.

  (2) A recycle stream must not impact effluent quality or the wastewater treatment facility's treatment processes.

(w) Alkaline Stabilization.

  (1) Design Basis.

    (A) Alkaline Dosage. The engineering report must include the calculation of the alkaline dosage required to stabilize sludge based on the type of sludge, chemical composition of sludge, and the solids concentration in the sludge. Performance data taken from a pilot test program or from a comparable wastewater treatment facility must be used to determine the proper dosage.

    (B) Temperature, pH, and Contact Time. An alkaline stabilization system must uniformly mix an alkaline additive-sludge mixture to maintain the pH, temperature, and contact time, as specified in §312.82 of this title (relating to Pathogen Reduction) and §312.83 of this title (relating to Vector Attraction Reduction).

  (2) Reliability.

    (A) An alkaline stabilization system must have multiple units, unless storage or an alternate stabilization method is available to continue operations when a unit is not in service.

    (B) A single unit that has adequate storage or an alternate stabilization method must have a standby conveyance and mixer, a backup heat source, and dual blowers.

    (C) A design must include:

      (i) the expected downtime for maintenance and repair based on data from a comparable wastewater treatment facility; and

      (ii) adequate storage for process, feed, and downtime.

  (3) Alkaline Stabilization Housing Unit.

    (A) A housing unit must meet the requirements in §217.247(r)(1) of this title (relating to Chemical Pretreatment of Sludge).

    (B) A housing unit must have mechanical or air agitation to ensure uniform discharge from the storage bins.

  (4) Feeding Equipment.

    (A) The alkaline additive feeding equipment must meet the requirements of §217.247(r)(1) of this title.

    (B) Hydrated lime must be fed as a slurry consisting of at least 6% calcium hydroxide (Ca(OH)2) by weight but not more than 18% Ca(OH)2 by weight, unless otherwise justified in the engineering report.

    (C) The engineering report must identify a means for controlling the feed rate of any other dry additive.

  (5) Mixing Equipment.

    (A) An additive and sludge blending or mixing vessel must be large enough to hold the mixture for a minimum of 30 minutes at the maximum feed rate.

    (B) A batch process must maintain a pH greater than 12 standard units in a mixing tank during the blending period.

    (C) A continuous flow process must maintain a pH greater than 12 standard units in an exit pipe.

    (D) A continuous flow process must be designed for a detention time that is the tank volume divided by the volumetric input flow rate.

    (E) A slurry mixture may be mixed with either a diffused air mixer or a mechanical mixer.

    (F) The mixing equipment must maintain an alkaline slurry mixture in complete suspension.

    (G) If using a diffused air mixer, the following requirements apply:

      (i) a coarse bubble diffuser must have a minimum air supply of 20 standard cubic feet per minute per 1,000 cubic feet (cf) of tank volume; and

      (ii) a mixing tank must be ventilated and include odor control equipment.

    (H) If using a mechanical mixer, the following requirements apply:

      (i) a mechanical mixer must provide at least 5.0 horse power per 1,000 cf of tank volume but not more than 10 horse power per 1,000 cf of tank volume; and

      (ii) the impellers must minimize debris fouling in the sludge.

  (6) Detention Time. A pasteurization vessel must provide a minimum detention period of 30 minutes.

  (7) External Heat. The engineering report must include specifications about any supplemental external heat necessary for sludge stabilization.


Source Note: The provisions of this §217.249 adopted to be effective August 28, 2008, 33 TexReg 6843; amended to be effective December 4, 2015, 40 TexReg 8254

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