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HomeMy WebLinkAboutWQ0002284_Correspondence_20020507DIVISION OF WATER QUALITY GROUNDWATER SECTION May 3, 2002 MEMORANDUM To: Kim Colson cc: Willie Hardison, GWS-RO -- — Through: Debra Watts !J/`^l� MAY 7 2002 From: David GoodrichV, Subject: Outer Banks — Kinnakeet Shores / Changeover from Rotary to Reuse System Dare County W00002284/GW02027 The Groundwater Section is in receipt of the subject application to change an existing rotary wastewater treatment system which currently treats the domestic wastewater generated by the Kinnakeet Shore residential subdivision to a higher -capacity reuse system. The present system utilizes two high -rate infiltration rotary beds. The existing permit was issued on December 13, 2001 and allowed the applicant to construct and operate a new 220,000 GPD system which could utilize four 100-foot diameter rotary distributor units. The existing permit requires the sampling of four monitoring wells (MW-1, 2, 3, and 4) every February, June, and September for Water Levels, pH, Fecal Coliforms, Nitrate Nitrogen, Chloride, TDS, TOC, Ammonia Nitrogen, and Volatile Organic Compounds (in November only). These four monitoring wells were destroyed when dredge material was deposited on the site in the year 2000. The Groundwater Section's comments were issued after the present permit was issued, and recommended that five new (replacement) wells (MW-5, 6, 7, 8, and 9) be sampled for the parameters previously listed. The compliance monitoring data for this facility was examined to determine the effect of the rotary distributors on the groundwater quality. Data was missing for the 1999 calendar year. The historical water level data indicated the existence of groundwater mounding at all four of the former wells. The sampling data indicated elevated concentrations of TSS in monitoring wells MW-1 and MW- 4. Total Dissolved Solids (TDS) were found to be elevated in monitoring wells MW-1 and MW-2, and exceedances of the Groundwater Quality Standards were detected in monitoring wells MW-3 and MW-4. Concentrations of Nitrate Nitrogen which exceeded the Standards were detected in all four wells between 1995 and 1997. The facility is now under new management and improvements to the system have reportedly been made. The management intends to convert the treatment system from a rotary system to a spray reuse system, and it is the understanding of the Groundwater Section that the intended construction activities will destroy the five existing monitoring wells. C:/My Documents/GW02027.doc Page 1 of 3 Shel.Doc 07/01 According to the subject application package, wastewater treatment will be performed by a new 350,000-gallon/day capacity reuse system (see Figures 1 and 2). The wastewater is projected to be 90% domestic and 10% non -industrial, with a portion reportedly taken from strip malls. The new treatment system will not utilize a rotary distributor system. Under normal operating conditions, the reuse system will use the 1,800,000-gallon, lined 5-day sidestream pond for the storage of effluent which does not meet the reuse standards. In addition to meeting the standards of reuse water, the waste stream will undergo denitrification and the concentration of Nitrate Nitrogen will reportedly be reduced to a level below the 2L Groundwater Quality Standard concentration of 10 mg/L. The facility will spray irrigate up to 350,000 gallons of reuse -quality water per day onto approximately 30 acres of lawn areas in the Kinnakeet Shores residential community. This application rate is equal to approximately 0.43 inches per day over the intended application area. A 5,097,095-gallon unlined infiltration pond will be utilized (in place of rotary distributors) under conditions of inclement weather (or a plant upset) and allow the infiltration of 199,027 gallons of treated effluent per day (see Figure 2). The infiltration pond will have an infiltration rate of 1.49 gallons per day per square foot, which is just below the "High Rate" classification standard of 1.50 gallons per day per square foot. The mounding beneath the infiltration pond will be controlled by a drainage ditch to the West and Northwest (see Figure 2). The present chlorination disinfection system will be replaced by ultra -violet disinfection. A turbidimeter will be used to control the storage of the effluent and will divert it from the irrigation pond to a non -compliant storage basin if it senses a reduction in the quality of the effluent. The treatment requirements for reuse quality effluent, as defined under 15A NCAC 2H .0219(k)(1)(A)(iii), is met by this system, thus both the Compliance Boundary and the Review Boundary are situated at the property line. The. maps submitted with the application suggest spray patterns which include roads, sidewalks, and the berms of proposed ponds. The spray patterns should be examined upon installation to ensure that the spray patterns are conTned to the lawn areas. The site was hydrogeologically characterized and modeled by a consultant to evaluate its ability to accommodate the intended (and potential) loadings from the perspectives of hydraulics and the potential transport/migration of possible contaminant substances. The previous modeling indicated that mounding would take place beneath the spray application areas (lawns), the proposed infiltration pond, and the rotary distributors. Although none of these applications will be continuous, the most nearly continuous will be the spray applications. The modeling indicated that the mounding beneath the lawns will likely result in an elevated water table between one foot and three feet beneath the surface of the ground. The wastewater is 90% domestic and 10% non -industrial, placing it in the domestic wastewater category. In addition, nitrate nitrogen removal is part of the treatment process and the wastewater is being treated to meet reuse standards. Contaminant transport does not appear to be an issue, due to the high level of treatment (which includes denitrifrcation). The Groundwater Section has reviewed the subject application for the renewal / modification of an existing permit and recommends issuance of the permit with the following conditions: C:/My Documents/GW02027.doc Page 2 of 3 Shel.Doc 07/01 1. Vertical Separation Requirements: Waste application activities shall not occur when the vertical separation between depth of application and the water table is at less than one (1) foot. Verification of the water table elevation can be confirmed by water level readings obtained from the monitor well(s) near the site or auger boring(s), which must be done within 24 hours, prior to application of wastewater. Any open borings must be properly filled with native soil, prior to application to decrease the chance of any waste contaminating the groundwater. 2. Liner Requirements: The 5-Day Pond shall have either a liner of natural material at least one (1) foot in thickness and having a hydraulic conductivity of no greater than 1 x 10' centimeters per second when compacted, or a synthetic liner of sufficient thickness to exhibit structural integrity and an effective hydraulic conductivity no greater than that of the natural material liner, according to 15A NCAC 2H .0219(f). 3. Applicable Boundaries: The COMPLIANCE BOUNDARY and REVIEW BOUNDARY for the waste disposal area(s) is specified by regulations in 15A NCAC 2H, Waste Not Discharged to Surface Waters, specifically .0219(k)(1)(C)(i)(II). The Compliance Boundary and the Review Boundary for groundwater shall be established at the property boundary. An exceedance of Groundwater Quality Standards at or beyond the Compliance Boundary is subject to immediate remediation action according to 15A NCAC 2L .0106(d)(2). 4. Additional Requirements: a. Any groundwater quality monitoring, as deemed necessary by the Division, shall be provided. *b. Prior to waste disposal, Pe spray patterns of each spray head shall be tested and examined to ensure that the application of the reuse water is limited to the intended areas of application. If there are any questions please call David Goodrich at (919) 715-6162. *This verbage differs from that of the shell document. Attachments: Figures 1 and 2. C:/My Documents/GW02027.doc Page 3 of 3 Shel.Doc 07/O1 Name: BUXTON Date: 3/21/102 Scale: 1 inch equals 1666 feet 41- AV , ixvon I:s P1 e LW wjvv P) Ar z :r-w W '2 41 C I (E);L "10 20' -"M FIGURE 1 IMF K11*4NAKEET SHORES Location: 035.339! REUSE APPLICATION SYSTEM Caption: Kinnakeet Dare Cour DARE COUNTY WQPQ�4/G�WQ2027 )7, Maptech. Inc. SITE LOCATION MAP ixvon I:s P1 e LW wjvv P) Ar z :r-w W '2 41 C I (E);L "10 20' -"M FIGURE 1 IMF K11*4NAKEET SHORES Location: 035.339! REUSE APPLICATION SYSTEM Caption: Kinnakeet Dare Cour DARE COUNTY WQPQ�4/G�WQ2027 )7, Maptech. Inc. SITE LOCATION MAP "10 20' -"M FIGURE 1 IMF K11*4NAKEET SHORES Location: 035.339! REUSE APPLICATION SYSTEM Caption: Kinnakeet Dare Cour DARE COUNTY WQPQ�4/G�WQ2027 )7, Maptech. Inc. SITE LOCATION MAP $ L,,o ee-e /jWzfI,;I,y pe'Ad 2, z ----------- G $cafe 100 100 P,t,)oe,fy L- t" e. %I 111C vC All