B. S. K. Kumar, B. Sridevi, V. V. S. S. Sarma*, D. Cardinal and Mathieu Sebilo,
{"title":"密集型农业下地下水中脱硝硝酸盐的同位素证据以及与河口的交换(印度戈达瓦里河)","authors":"B. S. K. Kumar, B. Sridevi, V. V. S. S. Sarma*, D. Cardinal and Mathieu Sebilo, ","doi":"10.1021/acsestwater.4c0033810.1021/acsestwater.4c00338","DOIUrl":null,"url":null,"abstract":"<p >Nitrate is accumulated in the groundwater, modified through nitrification/denitrification, and exchanged with coastal/estuarine water bodies. To examine the sources and modifications of nitrate, the concentrations and isotopic composition of nitrate (δ <sup>15</sup>N and δ <sup>18</sup>O<sub>NO<sub>3</sub></sub>) in the groundwater was monitored at 5 locations along the bank of Godavari estuary and in the estuarine waters for 7 months during wet (August–November) and dry (March–May) periods. Though the concentration of nitrate (NO<sub>3</sub><sup>–</sup>) was higher during the wet than dry periods in both the groundwater and estuary, insignificant seasonal variability was observed in δ<sup>15</sup>N and δ<sup>18</sup>O<sub>NO<sub>3</sub></sub> indicating homogenization through mineralization–immobilization turnover of NO<sub>3</sub><sup>–</sup>. The range of δ<sup>15</sup>N to δ<sup>18</sup>O of NO<sub>3</sub><sup>–</sup> indicates soil, manure, and septic waste may be the major source of NO<sub>3</sub><sup>–</sup>. The mean ratio of δ<sup>15</sup>N/δ<sup>18</sup>O of 1.1 ± 0.3 indicates the occurrence of denitrification in the groundwater. Concentrations δ<sup>15</sup>N<sub>NO<sub>3</sub></sub> and δ<sup>18</sup>O<sub>NO<sub>3</sub></sub> of NO<sub>3</sub><sup>–</sup> displayed a significant relation between groundwater and estuarine water suggesting that NO<sub>3</sub><sup>–</sup> is possibly denitrified. This study suggests that denitrified NO<sub>3</sub><sup>–</sup> (enriched δ<sup>15</sup>N and δ<sup>18</sup>O) reported in the Godavari estuary may be contributed through submarine groundwater discharge than it is hypothesized to flux from the watershed.</p>","PeriodicalId":93847,"journal":{"name":"ACS ES&T water","volume":"4 8","pages":"3521–3531 3521–3531"},"PeriodicalIF":4.8000,"publicationDate":"2024-07-31","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"","citationCount":"0","resultStr":"{\"title\":\"Isotopic Evidence of Denitrified Nitrate in Groundwater beneath Intensive Agriculture and Exchange with Estuary (Godavari, India)\",\"authors\":\"B. S. K. Kumar, B. Sridevi, V. V. S. S. Sarma*, D. Cardinal and Mathieu Sebilo, \",\"doi\":\"10.1021/acsestwater.4c0033810.1021/acsestwater.4c00338\",\"DOIUrl\":null,\"url\":null,\"abstract\":\"<p >Nitrate is accumulated in the groundwater, modified through nitrification/denitrification, and exchanged with coastal/estuarine water bodies. To examine the sources and modifications of nitrate, the concentrations and isotopic composition of nitrate (δ <sup>15</sup>N and δ <sup>18</sup>O<sub>NO<sub>3</sub></sub>) in the groundwater was monitored at 5 locations along the bank of Godavari estuary and in the estuarine waters for 7 months during wet (August–November) and dry (March–May) periods. Though the concentration of nitrate (NO<sub>3</sub><sup>–</sup>) was higher during the wet than dry periods in both the groundwater and estuary, insignificant seasonal variability was observed in δ<sup>15</sup>N and δ<sup>18</sup>O<sub>NO<sub>3</sub></sub> indicating homogenization through mineralization–immobilization turnover of NO<sub>3</sub><sup>–</sup>. The range of δ<sup>15</sup>N to δ<sup>18</sup>O of NO<sub>3</sub><sup>–</sup> indicates soil, manure, and septic waste may be the major source of NO<sub>3</sub><sup>–</sup>. The mean ratio of δ<sup>15</sup>N/δ<sup>18</sup>O of 1.1 ± 0.3 indicates the occurrence of denitrification in the groundwater. Concentrations δ<sup>15</sup>N<sub>NO<sub>3</sub></sub> and δ<sup>18</sup>O<sub>NO<sub>3</sub></sub> of NO<sub>3</sub><sup>–</sup> displayed a significant relation between groundwater and estuarine water suggesting that NO<sub>3</sub><sup>–</sup> is possibly denitrified. This study suggests that denitrified NO<sub>3</sub><sup>–</sup> (enriched δ<sup>15</sup>N and δ<sup>18</sup>O) reported in the Godavari estuary may be contributed through submarine groundwater discharge than it is hypothesized to flux from the watershed.</p>\",\"PeriodicalId\":93847,\"journal\":{\"name\":\"ACS ES&T water\",\"volume\":\"4 8\",\"pages\":\"3521–3531 3521–3531\"},\"PeriodicalIF\":4.8000,\"publicationDate\":\"2024-07-31\",\"publicationTypes\":\"Journal Article\",\"fieldsOfStudy\":null,\"isOpenAccess\":false,\"openAccessPdf\":\"\",\"citationCount\":\"0\",\"resultStr\":null,\"platform\":\"Semanticscholar\",\"paperid\":null,\"PeriodicalName\":\"ACS ES&T water\",\"FirstCategoryId\":\"1085\",\"ListUrlMain\":\"https://pubs.acs.org/doi/10.1021/acsestwater.4c00338\",\"RegionNum\":0,\"RegionCategory\":null,\"ArticlePicture\":[],\"TitleCN\":null,\"AbstractTextCN\":null,\"PMCID\":null,\"EPubDate\":\"\",\"PubModel\":\"\",\"JCR\":\"Q1\",\"JCRName\":\"ENVIRONMENTAL SCIENCES\",\"Score\":null,\"Total\":0}","platform":"Semanticscholar","paperid":null,"PeriodicalName":"ACS ES&T water","FirstCategoryId":"1085","ListUrlMain":"https://pubs.acs.org/doi/10.1021/acsestwater.4c00338","RegionNum":0,"RegionCategory":null,"ArticlePicture":[],"TitleCN":null,"AbstractTextCN":null,"PMCID":null,"EPubDate":"","PubModel":"","JCR":"Q1","JCRName":"ENVIRONMENTAL SCIENCES","Score":null,"Total":0}
Isotopic Evidence of Denitrified Nitrate in Groundwater beneath Intensive Agriculture and Exchange with Estuary (Godavari, India)
Nitrate is accumulated in the groundwater, modified through nitrification/denitrification, and exchanged with coastal/estuarine water bodies. To examine the sources and modifications of nitrate, the concentrations and isotopic composition of nitrate (δ 15N and δ 18ONO3) in the groundwater was monitored at 5 locations along the bank of Godavari estuary and in the estuarine waters for 7 months during wet (August–November) and dry (March–May) periods. Though the concentration of nitrate (NO3–) was higher during the wet than dry periods in both the groundwater and estuary, insignificant seasonal variability was observed in δ15N and δ18ONO3 indicating homogenization through mineralization–immobilization turnover of NO3–. The range of δ15N to δ18O of NO3– indicates soil, manure, and septic waste may be the major source of NO3–. The mean ratio of δ15N/δ18O of 1.1 ± 0.3 indicates the occurrence of denitrification in the groundwater. Concentrations δ15NNO3 and δ18ONO3 of NO3– displayed a significant relation between groundwater and estuarine water suggesting that NO3– is possibly denitrified. This study suggests that denitrified NO3– (enriched δ15N and δ18O) reported in the Godavari estuary may be contributed through submarine groundwater discharge than it is hypothesized to flux from the watershed.