Yan Zhang

Dr. Yan Zhang

Department of Environmental Science and Engineering, Fudan University, Shanghai 200433, China

Research Focus & Metrics

Academic Career Length

15Years (2012-Present)

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

Representative Publications

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11 January 2016 in Environmental Science & Technology
Verified
Journal Article
Closed access
QFQianzhu Fan
Qianzhu Fan
Yan ZhangYan Zhang
Yan Zhang
WMWeichun Ma
Weichun Ma
HMHuixin Ma
Huixin Ma
JFJunlan Feng
Junlan Feng
LCLimin Chen
Limin Chen

20 December 2016 in Environmental Science & Technology
Verified
Journal Article
Closed access
ZLZhanmin Liu
Zhanmin Liu
XLXiaohui Lu
Xiaohui Lu
JFJunlan Feng
Junlan Feng
QFQianzhu Fan
Qianzhu Fan
Yan ZhangYan Zhang
Yan Zhang
XYXin Yang
Xin Yang

9 May 2019 in Atmospheric Chemistry and Physics
Verified
Journal Article
Open access
PDF file
JFJunlan Feng
Junlan Feng
Yan ZhangYan Zhang
Yan Zhang
SLShanshan Li
Shanshan Li
JMJingbo Mao
Jingbo Mao
APAllison Patton
Allison Patton
KWKatherine Walker
Katherine Walker
The Yangtze River Delta (YRD) and the megacity of Shanghai are host to one of the busiest port clusters in the world; the region also suffers from high levels of air pollution. The goal of this study was to estimate the contributions of shipping to regional emissions, air quality, and population exposure and to characterize the importance of the geographic spatiality of shipping lanes and different types of ship-related sources for the baseline year of 2015, which was prior to the implementation of China's Domestic Emission Control Areas (DECAs) in 2016. The WRF-CMAQ model, which combines the Weather Research and Forecasting model (WRF) and the Community Multi-scale Air Quality (CMAQ) model, was used to simulate the influence of coastal and inland-water shipping, port emissions and ship-related cargo transport on air quality and on the population-weighted concentrations (which is a measure of human exposure). Our results showed that the impact of shipping on air quality in the YRD was primarily attributable to shipping emissions within 12 NM (nautical miles) of shore, but emissions coming from the coastal area between 24 and 96 NM still contributed substantially to ship-related PM2.5 concentrations in the YRD. The overall contribution of ships to the PM2.5 concentration in the YRD could reach 4.62 µg m−3 in summer when monsoon winds transport shipping emissions onshore. In Shanghai city, inland-water going ships were major contributors (40 %–80 %) to the shipping impact on urban air quality. Given the proximity of inland-water ships to the urban populations of Shanghai, the emissions of inland-water ships contributed more to population-weighted concentrations. These research results provide scientific evidence to inform policies for controlling future shipping emissions; in particular, in the YRD region, expanding the boundary of 12 NM from shore in China's current DECA policy to around 100 NM from shore would include most of shipping emissions affecting air pollutant exposure, and stricter fuel standards could be considered for the ships on inland rivers and other waterways close to residential regions.

28 August 2019 in Environmental Science & Technology
Verified
Journal Article
Closed access
XZXu Zhang
Xu Zhang
Yan ZhangYan Zhang
Yan Zhang
YLYiming Liu
Yiming Liu
Junri ZhaoJunri Zhao
Junri Zhao
YZYuyan Zhou
Yuyan Zhou
JCJun Chen
Jun Chen

4 November 2021 in Environmental Science & Technology
Verified
Journal Article
Closed access
GYGuangyuan Yu
Guangyuan Yu
Yan ZhangYan Zhang
Yan Zhang
FYFan Yang
Fan Yang
BHBaoshan He
Baoshan He
CZCangang Zhang
Cangang Zhang
JCJun Chen
Jun Chen

12 October 2015 in Biogeosciences
Verified
Journal Article
Open access
PDF file
Yan ZhangYan Zhang
Yan Zhang
NMN. Mahowald
N. Mahowald
RSR. A. Scanza
R. A. Scanza
EJE. Journet
E. Journet
KDK. Desboeufs
K. Desboeufs
KFK. W. Fomba
K. W. Fomba
Trace element deposition from desert dust has important impacts on ocean primary productivity, the quantification of which could be useful in determining the magnitude and sign of the biogeochemical feedback on radiative forcing. However, the impact of elemental deposition to remote ocean regions is not well understood and is not currently included in global climate models. In this study, emission inventories for eight elements primarily of soil origin, Mg, P, Ca, Mn, Fe, K, Al, and Si are determined based on a global mineral data set and a soil data set. The resulting elemental fractions are used to drive the desert dust model in the Community Earth System Model (CESM) in order to simulate the elemental concentrations of atmospheric dust. Spatial variability of mineral dust elemental fractions is evident on a global scale, particularly for Ca. Simulations of global variations in the Ca / Al ratio, which typically range from around 0.1 to 5.0 in soils, are consistent with observations, suggesting that this ratio is a good signature for dust source regions. The simulated variable fractions of chemical elements are sufficiently different; estimates of deposition should include elemental variations, especially for Ca, Al and Fe. The model results have been evaluated with observations of elemental aerosol concentrations from desert regions and dust events in non-dust regions, providing insights into uncertainties in the modeling approach. The ratios between modeled and observed elemental fractions range from 0.7 to 1.6, except for Mg and Mn (3.4 and 3.5, respectively). Using the soil database improves the correspondence of the spatial heterogeneity in the modeling of several elements (Ca, Al and Fe) compared to observations. Total and soluble dust element fluxes to different ocean basins and ice sheet regions have been estimated, based on the model results. The annual inputs of soluble Mg, P, Ca, Mn, Fe and K associated with dust using the mineral data set are 0.30 Tg, 16.89 Gg, 1.32 Tg, 22.84 Gg, 0.068 Tg, and 0.15 Tg to global oceans and ice sheets.