Qifang Chen , Yuemin Hu , Fan Chen , Junfeng Zhang , Zanfang Jin , Linyun Xiao , Xiang Chen , Yasheng Shi , Feili Li
{"title":"实验室规模模拟含水层条件下的反硝化和同位素分馏效应","authors":"Qifang Chen , Yuemin Hu , Fan Chen , Junfeng Zhang , Zanfang Jin , Linyun Xiao , Xiang Chen , Yasheng Shi , Feili Li","doi":"10.1016/j.jconhyd.2025.104749","DOIUrl":null,"url":null,"abstract":"<div><div>Denitrification plays a critical role in controlling the fate of nitrate (NO<sub>3</sub><sup>−</sup>) in groundwater. The nitrogen isotope enrichment factor (εN) during denitrification is essential for quantifying the role of denitrification in nitrate reduction in groundwater. Experimental columns containing groundwater and sediment were established to simulate aquifer conditions. Denitrification rates and the N and O isotope fractionation effects of NO<sub>3</sub><sup>−</sup> in both groundwater and sediment during dentrification were measured in experimental columns using four organic substances as electron donors (ethanol, acetate, glucose and brown sugar) under two different dissolved oxygen (DO) concentrations of 1 and 2 mg·L<sup>−1</sup>, respectively. Significant variations in denitrification rates and stable isotope enrichment factors were observed in both overlying groundwater (εN<sub>o</sub> and εO<sub>o</sub>) and sediment pore water (εN<sub>p</sub> and εO<sub>p</sub>), depending on the carbon source and DO concentration. At DO =2 mg·L<sup>−1</sup>, acetate (εN<sub>o</sub>, −9.2 ‰; εN<sub>p</sub>, −7.4 ‰), glucose (εN<sub>o</sub>, −7.4 ‰; εN<sub>p</sub>, −4.3 ‰), brown sugar (εN<sub>o</sub>, −2.6 ‰; εN<sub>p</sub>, −2.4 ‰) exhibited less negative isotope enrichment factors compared to ethanol (εN<sub>o</sub>, −11.7 ‰; εN<sub>p</sub>, −10.0 ‰). For brown sugar, more negative isotope enrichment factors was observed at DO =1 (εN<sub>o</sub>, −5.0 ‰; εN<sub>p</sub>, −3.5 ‰) than at DO = 2 mg·L<sup>−1</sup>. Higher denitrification rates correlated with more negative εN<sub>o</sub> and εN<sub>p</sub> values, reflecting stronger nitrogen fractionation. Due to the O-exchange fraction and NO<sub>3</sub><sup>−</sup> reduction processes, positive εO<sub>o</sub> and εO<sub>p</sub> values were observed in the denitrification columns, ranging from 5.0 ‰ to 29.2 ‰ for εO<sub>o</sub> and from 3.9 ‰ to 22.8 ‰ for εO<sub>p</sub>. Fractionation by diffusive transport of NO<sub>3</sub><sup>−</sup> resulted in higher absolute values of εN<sub>o</sub> (εO<sub>o</sub>) compared to those of εN<sub>p</sub> (εO<sub>p</sub>). The calculated isotope enrichment factors (εN<sub>o</sub> and εN<sub>p</sub>) may be applied to quantify denitrification linked to C sources application under in situ conditions.</div></div>","PeriodicalId":15530,"journal":{"name":"Journal of contaminant hydrology","volume":"276 ","pages":"Article 104749"},"PeriodicalIF":4.4000,"publicationDate":"2025-10-06","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"","citationCount":"0","resultStr":"{\"title\":\"Denitrification and isotope fractionation effects under simulated aquifer conditions at a laboratory scale\",\"authors\":\"Qifang Chen , Yuemin Hu , Fan Chen , Junfeng Zhang , Zanfang Jin , Linyun Xiao , Xiang Chen , Yasheng Shi , Feili Li\",\"doi\":\"10.1016/j.jconhyd.2025.104749\",\"DOIUrl\":null,\"url\":null,\"abstract\":\"<div><div>Denitrification plays a critical role in controlling the fate of nitrate (NO<sub>3</sub><sup>−</sup>) in groundwater. The nitrogen isotope enrichment factor (εN) during denitrification is essential for quantifying the role of denitrification in nitrate reduction in groundwater. Experimental columns containing groundwater and sediment were established to simulate aquifer conditions. Denitrification rates and the N and O isotope fractionation effects of NO<sub>3</sub><sup>−</sup> in both groundwater and sediment during dentrification were measured in experimental columns using four organic substances as electron donors (ethanol, acetate, glucose and brown sugar) under two different dissolved oxygen (DO) concentrations of 1 and 2 mg·L<sup>−1</sup>, respectively. Significant variations in denitrification rates and stable isotope enrichment factors were observed in both overlying groundwater (εN<sub>o</sub> and εO<sub>o</sub>) and sediment pore water (εN<sub>p</sub> and εO<sub>p</sub>), depending on the carbon source and DO concentration. At DO =2 mg·L<sup>−1</sup>, acetate (εN<sub>o</sub>, −9.2 ‰; εN<sub>p</sub>, −7.4 ‰), glucose (εN<sub>o</sub>, −7.4 ‰; εN<sub>p</sub>, −4.3 ‰), brown sugar (εN<sub>o</sub>, −2.6 ‰; εN<sub>p</sub>, −2.4 ‰) exhibited less negative isotope enrichment factors compared to ethanol (εN<sub>o</sub>, −11.7 ‰; εN<sub>p</sub>, −10.0 ‰). For brown sugar, more negative isotope enrichment factors was observed at DO =1 (εN<sub>o</sub>, −5.0 ‰; εN<sub>p</sub>, −3.5 ‰) than at DO = 2 mg·L<sup>−1</sup>. Higher denitrification rates correlated with more negative εN<sub>o</sub> and εN<sub>p</sub> values, reflecting stronger nitrogen fractionation. Due to the O-exchange fraction and NO<sub>3</sub><sup>−</sup> reduction processes, positive εO<sub>o</sub> and εO<sub>p</sub> values were observed in the denitrification columns, ranging from 5.0 ‰ to 29.2 ‰ for εO<sub>o</sub> and from 3.9 ‰ to 22.8 ‰ for εO<sub>p</sub>. Fractionation by diffusive transport of NO<sub>3</sub><sup>−</sup> resulted in higher absolute values of εN<sub>o</sub> (εO<sub>o</sub>) compared to those of εN<sub>p</sub> (εO<sub>p</sub>). The calculated isotope enrichment factors (εN<sub>o</sub> and εN<sub>p</sub>) may be applied to quantify denitrification linked to C sources application under in situ conditions.</div></div>\",\"PeriodicalId\":15530,\"journal\":{\"name\":\"Journal of contaminant hydrology\",\"volume\":\"276 \",\"pages\":\"Article 104749\"},\"PeriodicalIF\":4.4000,\"publicationDate\":\"2025-10-06\",\"publicationTypes\":\"Journal Article\",\"fieldsOfStudy\":null,\"isOpenAccess\":false,\"openAccessPdf\":\"\",\"citationCount\":\"0\",\"resultStr\":null,\"platform\":\"Semanticscholar\",\"paperid\":null,\"PeriodicalName\":\"Journal of contaminant hydrology\",\"FirstCategoryId\":\"93\",\"ListUrlMain\":\"https://www.sciencedirect.com/science/article/pii/S0169772225002542\",\"RegionNum\":3,\"RegionCategory\":\"环境科学与生态学\",\"ArticlePicture\":[],\"TitleCN\":null,\"AbstractTextCN\":null,\"PMCID\":null,\"EPubDate\":\"\",\"PubModel\":\"\",\"JCR\":\"Q2\",\"JCRName\":\"ENVIRONMENTAL SCIENCES\",\"Score\":null,\"Total\":0}","platform":"Semanticscholar","paperid":null,"PeriodicalName":"Journal of contaminant hydrology","FirstCategoryId":"93","ListUrlMain":"https://www.sciencedirect.com/science/article/pii/S0169772225002542","RegionNum":3,"RegionCategory":"环境科学与生态学","ArticlePicture":[],"TitleCN":null,"AbstractTextCN":null,"PMCID":null,"EPubDate":"","PubModel":"","JCR":"Q2","JCRName":"ENVIRONMENTAL SCIENCES","Score":null,"Total":0}
Denitrification and isotope fractionation effects under simulated aquifer conditions at a laboratory scale
Denitrification plays a critical role in controlling the fate of nitrate (NO3−) in groundwater. The nitrogen isotope enrichment factor (εN) during denitrification is essential for quantifying the role of denitrification in nitrate reduction in groundwater. Experimental columns containing groundwater and sediment were established to simulate aquifer conditions. Denitrification rates and the N and O isotope fractionation effects of NO3− in both groundwater and sediment during dentrification were measured in experimental columns using four organic substances as electron donors (ethanol, acetate, glucose and brown sugar) under two different dissolved oxygen (DO) concentrations of 1 and 2 mg·L−1, respectively. Significant variations in denitrification rates and stable isotope enrichment factors were observed in both overlying groundwater (εNo and εOo) and sediment pore water (εNp and εOp), depending on the carbon source and DO concentration. At DO =2 mg·L−1, acetate (εNo, −9.2 ‰; εNp, −7.4 ‰), glucose (εNo, −7.4 ‰; εNp, −4.3 ‰), brown sugar (εNo, −2.6 ‰; εNp, −2.4 ‰) exhibited less negative isotope enrichment factors compared to ethanol (εNo, −11.7 ‰; εNp, −10.0 ‰). For brown sugar, more negative isotope enrichment factors was observed at DO =1 (εNo, −5.0 ‰; εNp, −3.5 ‰) than at DO = 2 mg·L−1. Higher denitrification rates correlated with more negative εNo and εNp values, reflecting stronger nitrogen fractionation. Due to the O-exchange fraction and NO3− reduction processes, positive εOo and εOp values were observed in the denitrification columns, ranging from 5.0 ‰ to 29.2 ‰ for εOo and from 3.9 ‰ to 22.8 ‰ for εOp. Fractionation by diffusive transport of NO3− resulted in higher absolute values of εNo (εOo) compared to those of εNp (εOp). The calculated isotope enrichment factors (εNo and εNp) may be applied to quantify denitrification linked to C sources application under in situ conditions.
期刊介绍:
The Journal of Contaminant Hydrology is an international journal publishing scientific articles pertaining to the contamination of subsurface water resources. Emphasis is placed on investigations of the physical, chemical, and biological processes influencing the behavior and fate of organic and inorganic contaminants in the unsaturated (vadose) and saturated (groundwater) zones, as well as at groundwater-surface water interfaces. The ecological impacts of contaminants transported both from and to aquifers are of interest. Articles on contamination of surface water only, without a link to groundwater, are out of the scope. Broad latitude is allowed in identifying contaminants of interest, and include legacy and emerging pollutants, nutrients, nanoparticles, pathogenic microorganisms (e.g., bacteria, viruses, protozoa), microplastics, and various constituents associated with energy production (e.g., methane, carbon dioxide, hydrogen sulfide).
The journal''s scope embraces a wide range of topics including: experimental investigations of contaminant sorption, diffusion, transformation, volatilization and transport in the surface and subsurface; characterization of soil and aquifer properties only as they influence contaminant behavior; development and testing of mathematical models of contaminant behaviour; innovative techniques for restoration of contaminated sites; development of new tools or techniques for monitoring the extent of soil and groundwater contamination; transformation of contaminants in the hyporheic zone; effects of contaminants traversing the hyporheic zone on surface water and groundwater ecosystems; subsurface carbon sequestration and/or turnover; and migration of fluids associated with energy production into groundwater.