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Town of Mashpee Conservation Commission <br /> 16 Great Neck Road North <br /> Mashpee, MA 02649 <br /> single on-site systems serving individual homes, cluster systems serving a small group of properties, and <br /> "ecological sanitation" approaches such as urine-diverting toilets, composting toilets, and incinerating toilets. <br /> With on-site or ecological systems, infrastructure consists less of pipes and plants and more of people and <br /> information: staff must visit numerous locations to monitor and maintain systems rather than operating a single <br /> centralized facility. <br /> Turning to ecological sanitation, Mr. Baumgaertel described urine diversion as an emerging tool with <br /> substantial nutrient-reduction potential. Specialized fixtures separate urine from the rest of the wastewater <br /> stream so that it can follow a different treatment and reuse pathway. He noted that urine contains roughly 80- <br /> 85% of the nitrogen and a similar share of the phosphorus in domestic wastewater, the same nutrients that <br /> appear as N-P-K values on fertilizer bags. Current work with the Green Center in Falmouth and the Rich Earth <br /> Institute in Vermont is exploring how to collect, treat, and reuse urine as fertilizer on a larger scale. Early <br /> estimates suggest that installing urine-diverting fixtures and a storage tank in a small, one-bedroom home <br /> could cost on the order of$10,000—$15,000, in addition to maintaining a Title 5 system to handle graywater. <br /> He stressed that urine diversion would not replace sewers or I/A systems,but could complement them, much <br /> like solar panels complement the electric grid by reducing load. <br /> Mr. Baumgaertel then reviewed how nutrients behave in a conventional Title 5 septic system. A standard <br /> system consists of a septic tank and a soil absorption area or leach field. In the tank, about 25% of phosphorus <br /> is removed with settled solids, but essentially all nitrogen passes through, changing chemically from urea to <br /> ammonia. The leach field converts most of that ammonia to nitrate in the unsaturated soil. Standard Title 5 <br /> systems remove only about 35% of incoming nitrogen overall, with the remainder traveling as nitrate to <br /> groundwater and eventually to estuaries. Phosphorus removal is also poor: beyond the roughly 25% captured in <br /> tank solids, most phosphorus (often around three-quarters of the incoming load) passes through sandy Cape <br /> Cod soils, which have low capacity to bind phosphorus. New systems may temporarily remove more <br /> phosphorus until the soil's limited storage capacity is exhausted. <br /> He contrasted conventional systems with"black box" I/A technologies—tank-based nitrogen-removal units <br /> installed between the septic tank and leach field. Older FA systems, such as FAST and Bioclere units, were <br /> originally designed to remove basic wastewater pollutants (biochemical oxygen demand and total suspended <br /> solids) rather than nitrogen. They incidentally remove some nitrogen but typically only achieve effluent <br /> concentrations around 19 mg/L, which the data show is not sufficient to solve watershed nitrogen problems. <br /> Within the last five to seven years, newer technologies have been developed that specifically target nitrogen, <br /> including the Nitrex system(by Lombardo Associates) and the NitROE system (by KleanTu). Both use a <br /> wood-chip—based denitrification process and, in testing, have demonstrated approximately 85-90% nitrogen <br /> removal, with average effluent nitrogen concentrations in the range of 7-8 mg/L over a full year—sometimes <br /> as low as 3 mg/L in summer, and somewhat higher (10-15 mg/L) during winter when microbial activity slows. <br /> Mr. Baumgaertel described the Massachusetts Department of Environmental Protection (MassDEP) <br /> approval process for FA systems. Technologies begin with"pilot" approval, allowing up to 12 installations to <br /> demonstrate that they are at least no worse than a standard system. To progress to general nitrogen-removal <br /> approval, a system must obtain"provisional" approval, install at least 50 units, and collect three full years of <br /> monitoring data on all of them. MassDEP then analyzes that dataset and assigns an official effluent nitrogen <br /> concentration for regulatory purposes. At present, both Nitrex and NitROE are still under provisional approval, <br /> with provisional effluent numbers of 10 mg/L (Nitrex) and 11 mg/L (NitROE), compared to 19 mg/L for older <br /> I/A systems. NitROE is further along in the process, with roughly 200 installations between Cape Cod and <br /> Martha's Vineyard and near completion of its three-year monitoring period. Mr. Baumgaertel expects <br /> MassDEP will issue general approval for Nitro in the near future, though the final effluent concentration <br /> assigned will depend on MassDEP's analysis. He noted that towns such as Falmouth have used MassDEP's <br /> 3 <br />