Severity: Warning
Message: file_get_contents(https://...@gmail.com&api_key=61f08fa0b96a73de8c900d749fcb997acc09&a=1): Failed to open stream: HTTP request failed! HTTP/1.1 429 Too Many Requests
Filename: helpers/my_audit_helper.php
Line Number: 176
Backtrace:
File: /var/www/html/application/helpers/my_audit_helper.php
Line: 176
Function: file_get_contents
File: /var/www/html/application/helpers/my_audit_helper.php
Line: 250
Function: simplexml_load_file_from_url
File: /var/www/html/application/helpers/my_audit_helper.php
Line: 1034
Function: getPubMedXML
File: /var/www/html/application/helpers/my_audit_helper.php
Line: 3152
Function: GetPubMedArticleOutput_2016
File: /var/www/html/application/controllers/Detail.php
Line: 575
Function: pubMedSearch_Global
File: /var/www/html/application/controllers/Detail.php
Line: 489
Function: pubMedGetRelatedKeyword
File: /var/www/html/index.php
Line: 316
Function: require_once
Although crop residue return increases upland soil emissions of nitrous oxide (NO), a potent greenhouse gas, the mechanisms responsible for the increase remain unclear. Here, we investigate NO emission pathways, gross nitrogen (N)-cycling rates, and associated N-cycling gene abundances in an upland soil following the addition of various organic material under aerobic incubation using a combination of N tracing technique, acetylene (CH) inhibition, and real-time PCR (qPCR) methods. Increased total NO emissions following organic material amendment was attributed to both increased nitrification-derived NO emissions, following increased ammonia-oxidizing bacteria (AOB)-amoA abundance, and denitrification-derived NO emissions, following increased nirS and decreased nosZ abundance. Increasing plant residue carbon (C)/N ratio decreased total NO emissions by decreasing the contribution of denitrification to NO emissions, potentially due to higher proportions of denitrified N emitted as NO than nitrified N emitted as NO. We further propose a novel conceptual framework for organic material input effects on denitrification-derived NO emissions based on the decomposable characteristics of the added organic material. For slowly decomposing organic materials (e.g., plant residue) with insufficient available C, NO-N immobilization surpassed denitrification, resulting in gradual decrease in denitrification-derived NO emissions with an increase in mineralization of plant residue C losses. In contrast, available C provided by readily available C sources (e.g., glucose) seemed sufficient to support the co-occurrence of NO-N immobilization and denitrification. Overall, for the first time, we offer a microbial process perspective of NO emissions following organic material input. The findings could facilitate the improvement of process-orientated models of NO emissions and the formulation of appropriate NO mitigation strategies for crop residue-amended soils.
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Source |
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http://dx.doi.org/10.1016/j.envpol.2021.117176 | DOI Listing |
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