Severity: Warning
Message: file_get_contents(https://...@pubfacts.com&api_key=b8daa3ad693db53b1410957c26c9a51b4908&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: 3122
Function: getPubMedXML
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
Atmospheric nitrate, including nitric acid (HNO), particulate nitrate (pNO), and organic nitrate (RONO), is a key atmosphere component with implications for air quality, nutrient deposition, and climate. However, accurately representing atmospheric nitrate concentrations within atmospheric chemistry models is a persistent challenge. A contributing factor to this challenge is the intricate chemical transformations involving HNO formation, which can be difficult for models to replicate. Here, we present a novel model framework that utilizes the oxygen stable isotope anomaly (ΔO) to quantitatively depict ozone (O) involvement in precursor nitrogen oxides photochemical cycling and HNO formation. This framework has been integrated into the US EPA Community Multiscale Air Quality (CMAQ) modeling system to facilitate a comprehensive assessment of NO oxidation and HNO formation. In application across the northeastern US, the model ΔO compares well with recently conducted diurnal ΔO(NO) and spatiotemporal ΔO(HNO) observations, with a root mean square error between model and observations of 2.6 ‰ for ΔO(HNO). The model indicates the major formation pathways of annual HNO production within the northeastern US are NO+OH (46 %), NO hydrolysis (34 %), and organic nitrate hydrolysis (12 %). This model can evaluate NO chemistry in CMAQ in future air quality and deposition studies involving reactive nitrogen.
Download full-text PDF |
Source |
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http://www.ncbi.nlm.nih.gov/pmc/articles/PMC11151734 | PMC |
http://dx.doi.org/10.1021/acsestair.3c00056 | DOI Listing |
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