Nitrogen species control the interaction between NO3--N reduction and aniline degradation and microbial community structure in the oxic-anoxic transition zone
Contrary to the fact that NO 3 − -N can serve as electron acceptor to promote organics degradation, it was also found NO 3 − -N reduction does not necessarily promote organics degradation. We speculate nitrogen (N) species may control the interaction between NO 3 − -N reduction and organics degradat...
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Veröffentlicht in: | Environmental science and pollution research international 2021-06, Vol.28 (23), p.29650-29664 |
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Format: | Artikel |
Sprache: | eng |
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Zusammenfassung: | Contrary to the fact that NO
3
−
-N can serve as electron acceptor to promote organics degradation, it was also found NO
3
−
-N reduction does not necessarily promote organics degradation. We speculate nitrogen (N) species may control the interaction between NO
3
−
-N reduction and organics degradation via shifting related microbial community structure. To prove the hypothesis, oxic-anoxic transition zone (OATZ) microcosms simulated by lake water and sediment were conducted with the addition of N species (NO
3
−
-N, NO
2
−
-N, and NH
4
+
-N) and aniline as typical organics. High-throughput sequencing was used to analyze the microbial community structure and functional enzyme in the microcosms. Results show that, NO
2
−
-N inhibited NO
3
−
-N reduction while enhanced aniline degradation. For NH
4
+
-N, it promoted NO
3
−
-N reduction when NH
4
+
-N/NO
3
−
-N concentration ratio ≤ 2 and inhibited aniline degradation when NH
4
+
-N/aniline concentration ratio ≥ 0.5. The presence of NO
2
−
-N or NH
4
+
-N weakened the interaction between NO
3
−
-N reduction and aniline degradation, which might be caused by significant changes in the diversity and abundance of microbial communities controlled by N species. The microbial mechanism indicates that NO
2
−
-N weakened the interaction by affecting both denitrification enzyme activity and electron transfer capability, while NH
4
+
-N weakened the interaction mainly by affecting electron transfer capability. These results imply that N species, as well as other electron acceptors and donors, in the contaminated OATZ should be fully considered, when performing in situ remediation technology of NO
3
−
-N reduction. |
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ISSN: | 0944-1344 1614-7499 |
DOI: | 10.1007/s11356-021-12627-0 |