Che-Jen Lin

Dr. Che-Jen Lin


Research Focus & Metrics

Academic Career Length

30Years (1997-Present)

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

Representative Publications

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13 February 2002 in Environmental Science & Technology
Verified
Journal Article
Closed access
SLSteve E. Lindberg
Steve E. Lindberg
SBSteve Brooks
Steve Brooks
Che-Jen LinChe-Jen Lin
Che-Jen Lin
KSKaren J. Scott
Karen J. Scott
MLMatthew Landis
Matthew Landis
ARAndreas Richter
Andreas Richter

1 June 1999 in Atmospheric Environment
Verified
Journal Article
Closed access
Che-Jen LinChe-Jen Lin
Che-Jen Lin
SPSimo O. Pehkonen
Simo O. Pehkonen

1 January 2010 in Desalination
Verified
Journal Article
Closed access
SSSaqib Shirazi
Saqib Shirazi
Che-Jen LinChe-Jen Lin
Che-Jen Lin
DCDong Chen
Dong Chen

1 May 2006 in Atmospheric Environment
Verified
Journal Article
Closed access
Che-Jen LinChe-Jen Lin
Che-Jen Lin
PPPruek Pongprueksa
Pruek Pongprueksa
SLSteve E. Lindberg
Steve E. Lindberg
SPSimo O. Pehkonen
Simo O. Pehkonen
DBDaewon Byun
Daewon Byun
CJCarey Jang
Carey Jang

24 August 2015 in Atmospheric Chemistry and Physics
Verified
Journal Article
Open access
PDF file
XFX. W. Fu
X. W. Fu
Haoran ZhangHaoran Zhang
Haoran Zhang
BYB. Yu
B. Yu
XWXUN Wang
XUN Wang
Che-Jen LinChe-Jen Lin
Che-Jen Lin
Xinbin FengXinbin Feng
Xinbin Feng
China presently contributes the largest amount of anthropogenic mercury (Hg) emission into the atmosphere in the world. Over the past decade, numerous studies have been conducted to characterize the concentration and forms of atmospheric Hg in China, which provide insights into the spatial and temporal distributions of atmospheric Hg through ground-based measurements at widely diverse geographical locations and during cruise and flight campaigns. In this paper, we present a comprehensive review of the state of understanding in atmospheric Hg in China. Gaseous elemental mercury (GEM) and particulate-bound mercury (PBM) measured at the remote sites in China are substantially elevated compared to the background values in the Northern Hemisphere. In Chinese urban areas, the highly elevated GEM, PBM and gaseous oxidized mercury (GOM) were mainly derived from local anthropogenic Hg emissions, whereas regional anthropogenic emissions and long-range transport from domestic source regions are the primary causes of the elevated GEM and PBM concentrations at remote sites. Using 7–9 years of continuous observations at a remote site and an urban site, a slight increase in atmospheric GEM (2.4–2.5 % yr−1) was identified (paired samples test: p < 0.01), which is in agreement with the increasing domestic anthropogenic emissions. Anthropogenic GEM emission quantity in China estimated through the observed GEM / CO concentration ratios ranged from 632 to 1138 t annually over the past decade, 2–3 times larger than published values using emission activity data. Modeling results and filed measurements show dry deposition is the predominant process for removing Hg from the atmosphere, 2.5–9.0 times larger than wet deposition, due to the elevated atmospheric GEM and PBM concentrations that facilitate dry deposition to terrestrial landscapes. Further studies to reconcile the observed and simulated Hg concentrations, to understand the impact of domestic emission reduction on Hg concentration and deposition and to delineate the role of Hg emission and deposition of China in the global Hg biogeochemical cycle, are needed.

11 April 2016 in Atmospheric Chemistry and Physics
Verified
Journal Article
Open access
PDF file
Wei ZhuWei Zhu
Wei Zhu
Che-Jen LinChe-Jen Lin
Che-Jen Lin
XWXUN Wang
XUN Wang
JSJonas Sommar
Jonas Sommar
Xuewu FuXuewu Fu
Xuewu Fu
Xinbin FengXinbin Feng
Xinbin Feng
Reliable quantification of air–surface fluxes of elemental Hg vapor (Hg0) is crucial for understanding mercury (Hg) global biogeochemical cycles. There have been extensive measurements and modeling efforts devoted to estimating the exchange fluxes between the atmosphere and various surfaces (e.g., soil, canopies, water, snow, etc.) in the past three decades. However, large uncertainties remain due to the complexity of Hg0 bidirectional exchange, limitations of flux quantification techniques and challenges in model parameterization. In this study, we provide a critical review on the state of science in the atmosphere–surface exchange of Hg0. Specifically, the advancement of flux quantification techniques, mechanisms in driving the air–surface Hg exchange and modeling efforts are presented. Due to the semi-volatile nature of Hg0 and redox transformation of Hg in environmental media, Hg deposition and evasion are influenced by multiple environmental variables including seasonality, vegetative coverage and its life cycle, temperature, light, moisture, atmospheric turbulence and the presence of reactants (e.g., O3, radicals, etc.). However, the effects of these processes on flux have not been fundamentally and quantitatively determined, which limits the accuracy of flux modeling. We compile an up-to-date global observational flux database and discuss the implication of flux data on the global Hg budget. Mean Hg0 fluxes obtained by micrometeorological measurements do not appear to be significantly greater than the fluxes measured by dynamic flux chamber methods over unpolluted surfaces (p = 0.16, one-tailed, Mann–Whitney U test). The spatiotemporal coverage of existing Hg0 flux measurements is highly heterogeneous with large data gaps existing in multiple continents (Africa, South Asia, Middle East, South America and Australia). The magnitude of the evasion flux is strongly enhanced by human activities, particularly at contaminated sites. Hg0 flux observations in East Asia are comparatively larger in magnitude than the rest of the world, suggesting substantial re-emission of previously deposited mercury from anthropogenic sources. The Hg0 exchange over pristine surfaces (e.g., background soil and water) and vegetation needs better constraints for global analyses of the atmospheric Hg budget. The existing knowledge gap and the associated research needs for future measurements and modeling efforts for the air–surface exchange of Hg0 are discussed.