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
Nitrogen dioxide (NO) and nitric acid (HNO) are nitrogen-containing acidic gases in the atmosphere, and they are important precursors of nitrate in aerosol and rainwater. The emission intensity of atmospheric nitrogen oxides is high in the subtropical region of China, but the concentrations and deposition rates of atmospheric nitrogen dioxide, nitric acid, particulate nitrate-nitrogen (NO-N), and rainwater nitrate-nitrogen (NO-N) in a double rice region in subtropical China are still unclear,. In this study, the atmosphere concentrations of NO-N, HNO-N, NO-N in PM, and NO-N and related meteorological parameters were simultaneously monitored in a typical double rice region within a subtropical hilly region of China, with the aim of determining the characteristics and influencing factors of NO-N, HNO-N, NO-N, and NO-N concentrations and quantifying the wet and dry deposition rates. The results showed that the annual mean concentrations of NO-N, HNO-N, NO-N, and NO-N were 4.2 μg·m, 0.7 μg·m, 4.0 μg·m, and 1.0 mg·L, respectively, and the deposition rates were 1.5, 3.2, 2.3, and 6.1 kg·hm, respectively. The NO-N concentrations were negatively correlated with air temperatures, and the HNO-N concentrations were negatively correlated with wind speeds. TheNO-N concentrations were negatively correlated with air temperatures, positively correlated with NO-N concentrations, but not significantly correlated with HNO-N concentrations, thus indicating that NO-N concentrations were an important limiting factor forNO-N pollution in this study area. The NO-N concentrations were negatively correlated with rainfall, as well as the concentrations of HNO-N and NO-N. The annual total dry and wet depositions of the atmospheric NO-N, HNO-N, NO-N, and NO-N were 13.0 kg·hm, which indicates that these compounds are important sources of nitrogen in paddy fields and may have significant impacts on paddy fields and surrounding ecosystems.
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Source |
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http://dx.doi.org/10.13227/j.hjkx.201810252 | DOI Listing |
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