This work aims to obtain full-scale NO emission characteristics translatable into viable NO control strategies and conduct full-scale testing of the proposed NO control concepts. Data of a long-term monitoring campaign was first used to quantify full-scale NO emission and probe into the seasonal pattern. Then trends between NO production/emission and process variables/conditions during typical operating cycles were revealed to explore the dynamic NO emission behavior. A multivariate statistical analysis was performed to find the dependency of NO emission on relevant process variables. The results show for the first time that relatively low/high NO emission took place in seasons with a decreasing/increasing trend of water temperature, respectively. Aerobic phase contributed to NO production/emission probably mainly through the hydroxylamine pathway. Comparatively, heterotrophic bacteria had a dual role in the anoxic phase and could be responsible for both net NO production and consumption. Incomplete denitrification might contribute mainly to the NO production/emission in the anoxic phase and the accumulation of NO to be significantly emitted in the following cycle due to the competition between different denitrification steps for electron donors. Therefore, properly extending the length of anoxic phase could serve as a potential control means to regulate NO accumulation in the anoxic phase. The full-scale testing not only verified the efficacy of reduced dissolved oxygen set-point in reducing NO emission by 60%, but also confirmed the proposed concepts of control over the aerobic and anoxic phases collectively.
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http://dx.doi.org/10.1021/acs.est.9b04889 | DOI Listing |
Water Res
January 2025
Hampton Roads Sanitation District, Virginia Beach, VA, USA.
Research on low dissolved oxygen (DO) enhanced biological phosphorus removal (EBPR) at full-scale remains limited, a knowledge gap this study aims to fill by investigating EBPR performance and microbial community shifts at a Water Resource Recovery Facility (WRRF) transitioning to low DO conditions. Average DO concentrations decreased from 2.62 mg O/L in 2019 to 0.
View Article and Find Full Text PDFWater Res X
December 2024
School of Energy and Environment, City University of Hong Kong, Hong Kong SAR, China.
The biological nitrogen removal process in wastewater treatment inevitably produces nitrous oxide (NO), a potent greenhouse gas. Coarse bubble mixing is widely employed in wastewater treatment processes to mix anoxic tanks; however, its impacts on NO emissions are rarely reported. This study investigates the effects of coarse bubble mixing on NO emissions in a pilot-scale mainstream nitrite shunt reactor over a 50-day steady-state period.
View Article and Find Full Text PDFSci Rep
January 2025
Grant Institute, School of Geosciences, University of Edinburgh, James Hutton Road, Edinburgh, EH9 3FE, UK.
Glendonites (from the precursor of ikaite, CaCO.6HO) preferentially precipitate within sediments in cold waters (- 2 to 7°C) via either organotrophic or methanogenic sulphate reduction. Here, we report the first occurrence of possible glendonites associated with the end Permian mass extinction in the earliest Triassic (ca.
View Article and Find Full Text PDFEnviron Sci Technol
January 2025
Department of Chemical Engineering and Applied Chemistry, University of Toronto, Toronto, Ontario M5S 3E5, Canada.
Environ Pollut
December 2024
Key Laboratory of Arable Land Conservation (Middle and Lower Reaches of Yangtse River), Ministry of Agriculture and Rural Affairs, College of Resources and Environment, Huazhong Agricultural University, Wuhan, 430070, China; Hubei Key Laboratory of Soil Environment and Pollution Remediation, College of Resources and Environment, Wuhan, 430070, China. Electronic address:
Organoarsenicals are toxic pollutants of global concern, and their environmental geochemical behavior might be greatly controlled by iron (Fe) (hydr)oxides through coprecipitation, which is rarely investigated. Here, the effects of the incorporation of dimethylarsenate (DMAs(V)), a typical organoarsenical, into the ferrihydrite (Fh) structure on the mineral physicochemical properties and Fe(II)-induced phase transformation of DMAs(V)-Fh coprecipitates with As/Fe molar ratios up to 0.0876 ± 0.
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