Advanced nutrient removal in water resource recovery facilities (WRRFs) can reduce coastal eutrophication, but can increase economic costs and indirect environmental impacts associated with energy and materials usage for WRRF construction and operation. A strategy of interest to reduce coastal eutrophication is the cultivation of seaweeds in proximity to WRRF discharge plumes to bioextract nutrients from coastal waters. We report economic and environmental trade-offs of this proposed strategy for a 1,170 m·d (0.31 mgd) WRRF in Boothbay Harbor, Maine, targeting a Water Environment Research Federation (WERF) level 2 effluent nitrogen goal of 3 mg-N·L. The scenarios investigated include WRRF upgrade and year-round nutrient bioextractive aquaculture (Saccharina latissima and Gracilaria tikvahiae cultivation) with end uses of bioenergy feedstock, fertilizer, or food. Based on biomass production characteristics and tissue nitrogen contents in Boothbay Harbor, an aquaculture site of 5.4 hectares would bioextract equivalent nitrogen mass as WRRF upgrade to meet level 2 nitrogen effluent goals. Using a techno-economic analysis, the cost of a WRRF upgrade was estimated to be $0.31 m wastewater treated. The cost of bioextractive seaweed aquaculture depended on beneficial use of seaweed. If dried and sold as sea vegetables (for human consumption), a net revenue of $0.72 m wastewater treated could be generated. If dried and sold as commercial fertilizer, the net cost of nutrient removal would be $0.26 m wastewater treated, less than the WRRF upgrade. However, if anaerobically digested to produce biogas, the net cost of treatment was estimated to be $0.499 m wastewater treated. WRRF upgrade and bioextractive aquaculture significantly reduced marine eutrophication. Bioextractive aquaculture with use as biofuel feedstock had the best performance on human carcinogenic toxicity, global warming, and fossil resource scarcity, marine ecotoxicity, and freshwater ecotoxicity. Use of seaweed product as sea vegetables was favorable considering human non-carcinogenic toxicity, marine eutrophication, freshwater eutrophication, and terrestrial ecotoxicity. The study results imply that nutrient bioextraction by seaweed aquaculture may be attractive as an alternative to advanced nutrient removal technologies in small coastal WRRFs, providing potential economic and environmental benefits for nutrient management.
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http://dx.doi.org/10.1016/j.watres.2022.118092 | DOI Listing |
Water Environ Res
January 2024
Department of Civil and Environmental Engineering, University of Maryland, College Park, Maryland, USA.
Phosphorous (P) removal in wastewater treatment is essential to prevent eutrophication in water bodies. Side-stream enhanced biological phosphorous removal (S2EBPR) is utilized to improve biological P removal by recirculating internal streams within a side-stream reactor to generate biodegradable carbon (C) for polyphosphate accumulating organisms (PAOs). In this study, a full-scale S2EBPR system in a water resource recovery facility (WRRF) was evaluated for 5 months.
View Article and Find Full Text PDFWater Sci Technol
March 2022
modelEAU, Université Laval, 1065, Avenue de la Médecine, Québec, QC G1 V 0A6, Canada E-mail: CentrEau, Québec Water Research Center, 1065 avenue de la Médecine, Québec, QC G1 V 0A6, Canada.
Nowadays, modelling, automation and control are widely used for Water Resource Recovery Facilities (WRRF) upgrading and optimization. Influent generator (IG) models are used to provide relevant input time series for dynamic WRRF simulations used in these applications. Current IG models found in literature are calibrated on the basis of a single performance criterion, such as the mean percentage error or the root mean square error.
View Article and Find Full Text PDFWater Res
April 2022
Bigelow Laboratories for Ocean Sciences, Boothbay Harbor, ME, United States.
Advanced nutrient removal in water resource recovery facilities (WRRFs) can reduce coastal eutrophication, but can increase economic costs and indirect environmental impacts associated with energy and materials usage for WRRF construction and operation. A strategy of interest to reduce coastal eutrophication is the cultivation of seaweeds in proximity to WRRF discharge plumes to bioextract nutrients from coastal waters. We report economic and environmental trade-offs of this proposed strategy for a 1,170 m·d (0.
View Article and Find Full Text PDFWater Res
October 2021
Department of Environmental Engineering, Water Technology and Processes, Technical University of Denmark, Bygningstorvet, Building 115, Lyngby 2800, Denmark. Electronic address:
To reduce greenhouse gas emissions and promote resource recovery, many wastewater treatment operators are retrofitting existing plants to implement new technologies for energy, nutrient and carbon recovery. In literature, there is a lack of studies that can unfold the potential environmental and economic impacts of the transition that wastewater utilities are undertaking to transform their treatment plants to water resource recovery facilities (WRRFs). When existing, literature studies are mostly based on simulations rather than real plant data and pilot-scale results.
View Article and Find Full Text PDFWater Sci Technol
June 2019
University of Michigan Department of Civil and Environmental Engineering, Ann Arbor, MI, USA E-mail:
Water resource recovery facility (WRRF) modeling requires robust and reliable characterization of the wastewater to be treated. Poor characterization can lead to unreliable model predictions, which can have significant economic consequences when models are used to make important facility upgrade/expansion and operational decisions. Current wastewater characterization practice often involves a limited number of relatively short-duration intensive campaigns.
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