Xionghui Qiu

Xionghui Qiu


Research Focus & Metrics

Academic Career Length

4Years (2023-Present)

(Calculated once Scilit publication data is synced: current year − year of first publication + 1)

Representative Publications

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11 May 2023 in Science of The Total Environment
Verified
Journal Article
Closed access
QCQingwang Cai
Qingwang Cai
XQXionghui Qiu
Xionghui Qiu
LPLin PENG
Lin PENG
QLQi Li
Qi Li
YZYuelin Zhang
Yuelin Zhang

11 March 2025 in Environmental Pollution
Verified
Journal Article
Closed access
WJWenyi Jin
Wenyi Jin
YYYulong Yan
Yulong Yan
XQXionghui Qiu
Xionghui Qiu
LPLin PENG
Lin PENG
ZLZhen Li
Zhen Li
YTYuying Tang
Yuying Tang

12 November 2024 in Environmental Pollution
Verified
Journal Article
Closed access
JZJiayu Zhang
Jiayu Zhang
XGXiaodong Ge
Xiaodong Ge
XQXionghui Qiu
Xionghui Qiu
LLLei Liu
Lei Liu
JMJan Mulder
Jan Mulder
Lei DuanLei Duan
Lei Duan

14 August 2024 in Atmosphere
Verified
Journal Article
Open access
PDF file
XYXiao Yan
Xiao Yan
XQXionghui Qiu
Xionghui Qiu
ZYZhen Yao
Zhen Yao
JLJiye Liu
Jiye Liu
LWLin Wang
Lin Wang
Oxygenated volatile organic compound (OVOC) emissions play a critical role in tropospheric ozone (O3) formation. This paper aims to establish an emission inventory and source profile database for OVOCs in Beijing, utilizing revised and reconstructed data from field measurements and existing literature. The study also assesses their potential impact on the O3 base on the ozone formation potential (OFP). Results indicate that OVOC emissions in Beijing predominantly originate from natural and residential sources, encompassing commercial solvent usage, cooking, residential combustion, construction adhesives, and construction coatings. OVOCs contributed 5.6% to OFP, which is significantly less than their emission contribution of 20.1%. Major OFP contributors include plant sources (26.2%), commercial solvent use (21.0%), cooking (20.5%), and construction adhesives (8.4%). The primary OVOC species contributing to OFP for OVOCs are acetaldehyde, methanol, hexanal, ethanol, and acetone, collectively contributing 59.0% of the total OFP. Natural sources exhibit significant seasonal variability, particularly in summer when plant emissions peak, constituting 78.9% of annual emissions and significantly impacting summer ozone pollution (OFP of 13,954 t). Conversely, emissions from other OVOC sources remain relatively stable year-round. Thus, strategies to mitigate summer ozone pollution in Beijing should prioritize plant sources while comprehensively addressing residential sources in other seasons. District-specific annual OVOC emissions are from Fangshan (3967 t), Changping (3958 t), Daxing (3853 t), and Chaoyang (3616 t), which reflect year-round forested areas in these regions and high populations.

10 July 2023 in Journal of Public Health
Verified
Journal Article
Open access
PDF file
CYChunyu Yang
Chunyu Yang
CHChunxu Hao
Chunxu Hao
LHLianzhen Huang
Lianzhen Huang
XQXionghui Qiu
Xionghui Qiu
XCXiaoyan Chen
Xiaoyan Chen
Background: Air pollution has aroused global concerns because of its adverse effects on individuals’ physical and psychological health and behavior. Although there has been substantial traditional consideration of the objective impact of air pollution, more knowledge is needed about perceived air quality (PAQ), its association with objective air pollution (OAP), and the relationship between OAP and PAQ with respect to pro-environmental behavior (PEB). Methods: To delineate and investigate the effect of air pollution on both perceived and objective perspectives of PEB and its underlying psychological mechanisms, this study distributed a survey questionnaire related to PAQ, the Positive and Negative Affect Schedule (PANAS), satisfaction with local governmental control of air quality (SAT), and the PEB scale. The monitored data of objective city-level air pollution and 391 samples of survey data were included in this study. Results: The results reveal that both PAQ and OAP increase individuals’ negative affect (NA) and decrease SAT, which sequentially restrains PEB. More importantly, PAQ, NA, and SAT played mediating roles in the relationship between OAP and PEB. Empirical testing for group difference also indicated that while there is no gender-related difference with respect to caring about SAT and PEB caused by air pollution, gender effects on NA were significantly different. Age-related differences exist among younger, medium, and older age groups with respect to NA, SAT, and PEB caused by air pollution, and there are also background differences with respect to NA, SAT, and PEB, although income does not generate a significant group difference effect on NA, SAT, and PEB. Conclusions: The findings corroborate the important roles of affect and SAT in activating public concern about air quality. We discuss the possible ways that affect and SAT might enhance PEB as well as the limitations of this study. More pollutants and mechanisms could be considered in future studies.