NR 106.89(4)(4) Chloride limits in lieu of chronic wet limits. Chloride limitations shall be included in the permit in lieu of chronic whole effluent toxicity testing requirements and chronic whole effluent toxicity limitations until source reduction actions are completed if either of the following applies: NR 106.89(4)(a)(a) The permittee can demonstrate to the satisfaction of the department that the effluent concentration of chloride exceeds 2 times the calculated chronic water quality-based effluent limitation. NR 106.89(4)(b)(b) The permittee can demonstrate to the satisfaction of the department that the effluent concentration of chloride is less than 2 times the calculated chronic water quality-based effluent limitation, but in excess of the calculated chronic water quality-based effluent limitation, and additional data are submitted which demonstrate that chloride is the sole source of chronic toxicity. NR 106.89(5)(5) Decision documentation. The department shall specify the decision to include chloride limitations instead of whole effluent toxicity limitations in the permit fact sheet. NR 106.89(6)(6) Reevaluation. The department shall reevaluate the need for whole effluent toxicity and chloride monitoring or limitations upon permit reissuance. NR 106.89 HistoryHistory: Cr. Register, January, 2000, No. 529, eff. 2-1-00; CR 15-085: r. and recr. Register August 2016 No. 728, eff. 9-1-16; correction in (2) (c) made under s. 35.17, Stats., Register August 2016 No. 728. NR 106.90(1)(1) Introduction. A 3-tiered system of source reduction measures is established in ascending order of increasing capital and operating costs. NR 106.90(2)(2) Tier 1 source reduction measures are those voluntary source reduction activities that identify and quantify chloride and softened water sources and usage, educate users and system operators on the need to minimize salt and softened water demands and promote better housekeeping practices that will reduce chloride and softened water consumption, and other activities similar in nature. Tier 1 source reduction measures may include any of the following: NR 106.90(2)(a)2.2. Educate homeowners on the impact of chloride from residential softeners, discuss options available for increasing softener salt efficiency, and request voluntary reductions. NR 106.90(2)(a)4.4. Request voluntary support from local water softening businesses in the efforts described in subds. 2. and 3. NR 106.90(2)(a)5.5. Educate licensed installers and self-installers of softeners on providing optional hard water for outside faucets for residences. NR 106.90(2)(a)6.6. Request voluntary reductions in chloride input from industrial and commercial contributors. NR 106.90(2)(a)7.7. Where a public water utility has been identified as a significant contributor of chloride to the sewer system, request that the water utility conduct activities listed in par. (b). NR 106.90(2)(b)(b) For direct-discharging municipal or commercial water softening plants: NR 106.90(2)(b)1.1. Identify the users of soft water or the processes using soft water, and the amounts they use. NR 106.90(2)(b)2.2. Determine which users or processes can tolerate unsoftened water, and determine their impact on demand. NR 106.90(2)(b)3.3. Determine which users can close-loop their once-through cooling system or which processes can be close-looped, and determine their impact on demand. NR 106.90(2)(c)(c) For dairies, train plant personnel to be more aware of salt conservation, emphasizing simple, cost effective housekeeping measures. For example, spilled salt can be cleaned up as a solid waste rather than flushed down the floor drain. NR 106.90(2)(d)2.2. Optimize softener operation to ensure the appropriate regeneration interval and salt dosage are used. NR 106.90(2)(e)(e) For any other facility not listed in pars. (a) to (d), conduct activities that identify and quantify chloride and softened water sources and usage and educate personnel on appropriate housekeeping practices and the need to minimize salt and softened water demands. NR 106.90(3)(3) Tier 2 source reduction measures are those voluntary source reduction activities that improve and optimize equipment and processes, encourage restricted chloride use by users, eliminate wasteful practices and establish recycling practices where feasible, and other activities similar in nature. Tier 2 source reduction measures may include any of the following: NR 106.90(3)(a)1.1. Require significant industrial and commercial contributors to evaluate their water treatment systems with regard to softened water requirements, with the results of that evaluation being the basis for potential restrictions of chloride inputs. NR 106.90(3)(a)2.2. Mandate a DIR and high salt efficiency standard for new residential softeners. NR 106.90(3)(a)3.3. Mandate participation in a residential softener tune-up program, which involves qualified periodic servicing to ensure proper control settings and adjustments. NR 106.90(3)(a)4.4. Where a public water utility has been identified as a significant contributor of chloride to the sewer system, request that the water utility conduct activities listed in par. (b). NR 106.90(3)(b)(b) For direct-discharging municipal or commercial water softening plants: NR 106.90(3)(b)1.1. Optimize softener operation to ensure the appropriate regeneration interval and salt dosage are used. NR 106.90(3)(b)2.2. If the regeneration is manual or timer-initiated, switch to a DIR controller. NR 106.90(3)(c)1.1. Improve the handling of salt brines and the handling of cheese into and out of brine systems. Consider capital improvements such as automating the brine system, properly designed drip pans and splash guards. NR 106.90(3)(c)2.2. Optimize softener operation to ensure the appropriate regeneration interval and salt dosage are used. NR 106.90(3)(c)3.3. If the regeneration is manual or timer-initiated, evaluate the feasibility of switching to a DIR controller. NR 106.90(3)(c)5.5. Determine which subprocesses can tolerate unsoftened water, and make appropriate changes. NR 106.90(3)(c)6.6. Determine whether once-through cooling systems can be close-looped, and make appropriate changes. NR 106.90(3)(c)7.7. For plants that condense whey, evaluate the feasibility of using condensate of whey (COW) water for the first rinse for clean-in-place (CIP) systems and for boiler makeup water. NR 106.90(3)(d)1.1. If the regeneration is manual or timer-initiated, evaluate the feasibility of switching to a DIR controller. NR 106.90(3)(d)3.3. Investigate the feasibility of using a phosphonate additive instead of softening the cooling water. NR 106.90(3)(d)4.4. Evaluate the feasibility of reusing once-through cooling water as boiler make-up. NR 106.90(3)(d)5.5. Investigate the feasibility of using unsoftened water for container fill. NR 106.90(3)(e)1.1. If the regeneration is manual or timer-initiated, evaluate the feasibility of switching to a DIR controller. NR 106.90(3)(f)(f) For any other facility not listed in pars. (a) to (e), conduct activities that improve and optimize equipment and processes, eliminate wasteful practices and establish recycling practices to achieve chloride reductions. NR 106.90(4)(4) Tier 3 source reduction measures are those voluntary source reduction activities that evaluate the feasibility of replacing or upgrading equipment and processes or evaluate the feasibility of using alternative technologies or processes, and other activities similar in nature. Tier 3 source reduction measures may include any of the following: NR 106.90(4)(a)(a) For POTWs, where residential point-of-use softening is the primary chloride input: NR 106.90(4)(a)1.1. Evaluate the requirement for new and replacement softeners to be metered demand type, with a higher, greater than 3350 grains of hardness exchange per pound of salt, efficiency capability. NR 106.90(4)(a)2.2. Evaluate the imposition of installation restrictions so that outside hose bibs are on unsoftened water. If restrictions are imposed, new homes and those in real estate transfers should be required to have plumbing restrictions for hard water by-passes, and the requirement should apply to self-installed equipment as well. NR 106.90(4)(b)(b) For POTWs, where a central water supply softener is the primary chloride input, conduct activities listed in par. (c). NR 106.90(4)(c)(c) For direct-discharging municipal or commercial water softening plants: NR 106.90(4)(c)1.1. Evaluate the feasibility of achieving greater salt efficiencies, greater than 3350 grains of hardness exchange per pound of salt. NR 106.90(4)(c)2.2. Evaluate softening alternatives that replace the sodium cycle ion exchange method of softening. NR 106.90(4)(c)3.3. Blend softened and unsoftened water to strike a balance between delivered water quality and environmental protection. NR 106.90(4)(d)1.1. For plants that make brine salted cheeses, evaluate the feasibility of membrane filtration for reconditioning the brine so that it can be reused. NR 106.90(4)(d)2.2. For plants that make brine salted cheeses, evaluate the feasibility of using a no-brine make procedure in which salt is added directly to curd during the manufacturing procedure, thereby reducing salt discharges from spent brines. NR 106.90(4)(e)1.1. Evaluate the feasibility of eliminating brine flotation for quality grading, if applicable. NR 106.90(4)(e)2.2. Evaluate the feasibility of installing a closed-loop system for cooling water. NR 106.90(4)(e)3.3. Evaluate the feasibility of installing a brine recovery and reuse system for reducing salt waste at the point of supplying flavorings to containers. NR 106.90(4)(f)1.1. Investigate the feasibility of replacing brine chills with air, water or air-water chills. NR 106.90(4)(f)3.3. Investigate the feasibility of chill brine reconditioning and reuse. NR 106.90(4)(f)4.4. Evaluate the feasibility of reusing once-through cooling water, or installing a closed-loop cooling water system. NR 106.90(4)(g)(g) For any other facility not listed in pars. (a) to (f), evaluate the feasibility of replacing or upgrading equipment and processes, and the use of alternative softening technologies to affect chloride reductions. NR 106.90(5)(5) Source reduction reporting. Following the completion of tier 1, 2 or 3 source reduction activities specified in the permit, but no later than 6 months prior to permit expiration, the permittee shall file a written report to the department documenting the current reduction as well as the anticipated future reduction in salt usage and chloride effluent concentrations. NR 106.90 HistoryHistory: Cr. Register, January, 2000, No. 529, eff. 2-1-00. NR 106.91NR 106.91 Variances for POTWs which accept wastewater from public water systems treating water to meet primary safe drinking water act standards. Publicly owned treatment works that accept wastewater from a public water system treating water to meet the primary maximum contaminant levels specified in ch. NR 809, if not able to meet the calculated limitation, may apply to the department for a variance from the water quality standard used to derive the limitation following the procedure specified in this subchapter. The department shall seek U.S. environmental protection agency approval before a variance is included in a permit. Upon approval, the permittee may be given an interim limitation, a target value, a target limitation and appropriate source reduction requirements, under s. NR 106.83 in the permit upon permit reissuance or modification. No calculated limitation, interim limitation, target value, target limitation, or source reduction requirement shall interfere with the attainment of the primary maximum contaminant levels specified in ch. NR 809. NR 106.92NR 106.92 Authority of a publicly owned treatment works to regulate chloride discharges. A publicly owned treatment works has the authority to regulate the discharge of chloride as enumerated in s. NR 211.40. NR 106.92 HistoryHistory: Cr. Register, January, 2000, No. 529, eff. 2-1-00. NR 106.93NR 106.93 New discharges. Any point source which has not been authorized under a WPDES permit prior to February 1, 2000, shall be required to meet the calculated limitations. Relocation of an existing discharge which was issued a WPDES permit prior to February 1, 2000, may not be considered a new discharge. NR 106.93 HistoryHistory: Cr. Register, January, 2000, No. 529, eff. 2-1-00. NR 106.94NR 106.94 Relocation of an existing discharge. An existing discharge which was issued a WPDES permit prior to February 1, 2000, and which is relocated after February 1, 2000, may be subject to voluntary source reduction activities and both an interim limitation and a target value or an interim limitation and a target limitation pursuant to s. NR 106.83 if the provisions of ch. NR 207 are met. Relocation includes the diversion of a discharge from a land treatment system to a surface water. NR 106.94 HistoryHistory: Cr. Register, January, 2000, No. 529, eff. 2-1-00. NR 106.95NR 106.95 Multiple discharges. The provisions of s. NR 106.11 are applicable to multiple discharges of chloride.
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