Dong Yang

Mr. Dong Yang

orcid

Research Focus & Metrics

Academic Career Length

6Years (2021-Present)

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

Representative Publications

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25 May 2022 in Journal of Environmental Management
Verified
Journal Article
Closed access
ACAng Chen
Ang Chen
XYXiuchun Yang
Xiuchun Yang
JGJian Guo
Jian Guo
MZMin Zhang
Min Zhang
XXXiaoyu Xing
Xiaoyu Xing
LJLiwei Jiang
Liwei Jiang

27 February 2024 in Journal of Environmental Management
Verified
Journal Article
Closed access
DYDong Yang
Dong Yang
ZYZhiyuan Yang
Zhiyuan Yang
QWQingke Wen
Qingke Wen
LMLeichao Ma
Leichao Ma
JGJian Guo
Jian Guo
XYXiuchun Yang
Xiuchun Yang

14 December 2022 in Journal of Cleaner Production
Verified
Journal Article
Closed access
XXXiaoyu Xing
Xiaoyu Xing
XYXiuchun Yang
Xiuchun Yang
JGJian Guo
Jian Guo
ACAng Chen
Ang Chen
MZMin Zhang
Min Zhang
XWXing Wang
Xing Wang

29 April 2021 in Remote Sensing
Verified
Journal Article
Open access
PDF file
ACAng Chen
Ang Chen
XYXiuchun Yang
Xiuchun Yang
BXBin Xu
Bin Xu
YJYunxiang Jin
Yunxiang Jin
JGJian Guo
Jian Guo
LZLibo Zhu
Libo Zhu
Northern China has been long threatened by aeolian desertification. In recent years, all levels of the Chinese government have performed a series of ecological protection and sand control projects. To grasp the implementation effects of these projects and adjust policies in time, it is necessary to understand the process of aeolian desertification quickly and accurately. Remote sensing technologies play an irreplaceable role in aeolian desertification monitoring. In this study, the Zhenglan Banner, which is in the hinterland of the Hunshandake Sandy Land, was considered as the research area. Based on unmanned aerial vehicle (UAV) images, ground survey data, and Landsat images called in Google Earth Engine (GEE), the aeolian desertified land (ADL) in 2000, 2004, 2010, 2015, and 2019 was extracted using spectral mixture analysis. A desertification index (DI) was constructed to evaluate the spatial and temporal dynamics of the ADL in the Zhenglan Banner. Finally, a residual analysis explored the driving forces of aeolian desertification. The results showed that (1) the ADL area in the Zhenglan Banner has been trending downwards over the past 20 years but rebounded from 2004 to 2010; (2) over the past 20 years, the area of slightly, moderately, and severely desertified land has decreased at annual rates of 0.4%, 2.7%, and 3.4%, respectively; (3) human activities had significantly positive and negative impacts on the aeolian desertification trend for 20.0% and 21.0% of the study area, respectively, but not for the rest. This paper explored new techniques for rapid aeolian desertification monitoring and is of great significance for controlling and managing aeolian desertification in this region.

1 January 2024 in Journal of Resources and Ecology
Verified
Journal Article
Closed access
PDF file
JZJia Ze
Jia Ze
XYXiuchun Yang
Xiuchun Yang
CAChen Ang
Chen Ang
DYDong Yang
Dong Yang
ZMZhang Min
Zhang Min
WLWei Lunda
Wei Lunda
The construction and operation of onshore wind farms interfere with the succession of local plant communities, and the impacts on the local ecology and climate are of great concern. The study of the relationships between onshore wind farms and local ecology and climate, as well as the accurate assessment of the impacts of onshore wind farms on local areas, are the foundation for promoting the sustainable development of green energy. In this study, we summarize the existing research methods used for field data monitoring, remote sensing data inversion and numerical model simulation, and found that onshore wind farms have obvious impacts on the local vegetation index, near-surface temperature, wind speed, soil moisture, and other parameters. Onshore wind farms reduce the local soil moisture content, increase the near-surface air temperature, and significantly alter local wind speeds. They also cause a reduction in the local vegetation index, inhibition of plant growth, and an increase in the mortality rates of birds and bats inside the wind farms. However, onshore wind farms have positive effects on the plant communities outside the wind farms, especially in the downwind direction. Overall, there is regional variability in the results and the findings are not generalizable. The mechanisms by which the onshore wind farms influence the local climate, the impact of climate on local ecology, and the direct effects of onshore wind farms on local ecology have not been clearly and accurately explained. Related research is still needed to further improve the precision, accuracy, and continuity of observational data. The construction of modeling systems also needs to incorporate indicators such as land use type, local microclimatic indicators, and plant species. Based on these considerations, this review provides support for macroscopically understanding the impacts of onshore wind farms on climate and ecology.

30 January 2022 in Remote Sensing
Verified
Journal Article
Open access
PDF file
JGJian Guo
Jian Guo
XYXiuchun Yang
Xiuchun Yang
Weiguo JiangWeiguo Jiang
Weiguo Jiang
FCFan Chen
Fan Chen
MZMin Zhang
Min Zhang
BXBin Xu
Bin Xu
Temperature and precipitation are considered to be the most important indicators affecting the green-up date. Sensitivity of the green-up date to temperature and precipitation is considered to be one of the key indicators to characterize the response of terrestrial ecosystems to climate change. We selected the main grassland types for analysis, including temperate steppe, temperate meadow steppe, upland meadow, and lowland meadow. This study investigates the variation in key meteorological indicators (daily maximum temperature (Tmax), daily minimum temperature (Tmin), and precipitation) between 2001 and 2018. We then examined the partial correlation and sensitivity of green-up date (GUD) to Tmax, Tmin, and precipitation. Our analysis indicated that the average GUD across the whole area was DOY 113. The mean GUD trend was −3.1 days/decade and the 25% region advanced significantly. Tmax and Tmin mainly showed a decreasing trend in winter (p > 0.05). In spring, Tmax mainly showed an increasing trend (p > 0.05) and Tmin a decreasing trend (p > 0.05). Precipitation showed no significant (p > 0.05) change trend and the trend range was ±10 mm/decade. For temperate steppe, the increase in Tmin in March promotes green-up (27.3%, the proportion of significant pixels), with a sensitivity of −0.17 days/°C. In addition, precipitation in April also promotes green-up (21.7%), with a sensitivity of −0.32 days/mm. The GUDs of temperate meadow steppe (73.9%), lowland meadow (65.9%), and upland meadow (22.1%) were mainly affected by Tmin in March, with sensitivities of −0.15 days/°C, −0.13 days/°C, and −0.14 days/°C, respectively. The results of this study reveal the response of vegetation to climate warming and contribute to improving the prediction of ecological changes as temperatures increase in the future.