Xizhi Lv

Xizhi Lv

orcid

Research Focus & Metrics

Academic Career Length

10Years (2017-Present)

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

Representative Publications

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1 March 2019 in Chemosphere
Verified
Journal Article
Closed access
Huacheng XuHuacheng Xu
Huacheng Xu
LJLi Ji
Li Ji
MKMing Kong
Ming Kong
MXMengwen Xu
Mengwen Xu
XLXizhi Lv
Xizhi Lv

1 December 2020 in Ecological Indicators
Verified
Journal Article
Closed access
LDLiyi Dai
Liyi Dai
YZYinghu Zhang
Yinghu Zhang
YLYing Liu
Ying Liu
LXLumeng Xie
Lumeng Xie
SZShiqiang Zhao
Shiqiang Zhao
XLXizhi Lv
Xizhi Lv

8 February 2024 in Remote Sensing
Verified
Journal Article
Open access
PDF file
JLJie Lu
Jie Lu
TQTianling Qin
Tianling Qin
DYDenghua Yan
Denghua Yan
XLXizhi Lv
Xizhi Lv
ZYZhe Yuan
Zhe Yuan
WLWei Li
Wei Li
The vegetation and ecosystem in the source region of the Yangtze River and the Yellow River (SRYY) are fragile. Affected by climate change, extreme droughts are frequent and permafrost degradation is serious in this area. It is very important to quantify the drought–vegetation interaction in this area under the influence of climate–permafrost coupling. In this study, based on the saturated vapor pressure deficit (VPD) and soil moisture (SM) that characterize atmospheric and soil drought, as well as the Normalized Differential Vegetation Index (NDVI) and solar-induced fluorescence (SIF) that characterize vegetation greenness and function, the evolution of regional vegetation productivity and drought were systematically identified. On this basis, the technical advantages of the causal discovery algorithm Peter–Clark Momentary Conditional Independence (PCMCI) were applied to distinguish the response of vegetation to VPD and SM. Furthermore, this study delves into the response mechanisms of NDVI and SIF to atmospheric and soil drought, considering different vegetation types and permafrost degradation areas. The findings indicated that low SM and high VPD were the limiting factors for vegetation growth. The positive and negative causal effects of VPD on NDVI accounted for 47.88% and 52.12% of the total area, respectively. Shrubs were the most sensitive to SM, and the response speed of grassland to SM was faster than that of forest land. The impact of SM on vegetation in the SRYY was stronger than that of VPD, and the effect in the frozen soil degradation area was more obvious. The average causal effects of NDVI and SIF on SM in the frozen soil degradation area were 0.21 and 0.41, respectively, which were twice as high as those in the whole area, and SM dominated NDVI (SIF) changes in 62.87% (76.60%) of the frozen soil degradation area. The research results can provide important scientific basis and theoretical support for the scientific assessment and adaptation of permafrost, vegetation, and climate change in the source area and provide reference for ecological protection in permafrost regions.

1 February 2023 in Water Resources Management
Verified
Journal Article
Closed access
PDF file
JWJianwei Wang
Jianwei Wang
TQTianling Qin
Tianling Qin
XLXizhi Lv
Xizhi Lv
YNYongxin Ni
Yongxin Ni
QZQiufen Zhang
Qiufen Zhang
LMLi Ma
Li Ma

5 May 2023 in Sustainability
Verified
Journal Article
Open access
PDF file
ZQZhang Qiufen
Zhang Qiufen
XLXizhi Lv
Xizhi Lv
NYNi Yongxin
Ni Yongxin
LMLi Ma
Li Ma
JWJianwei Wang
Jianwei Wang
The rainfall in loess hilly and gully area is concentrated, and mostly comes in the form of rainstorms. The runoff on the slope caused by rainstorms is the main cause of serious soil and water loss in the loess hilly area, and the grassland vegetation has a good inhibitory effect on the runoff on the slope. Therefore, it is of great significance to reveal the role of grassland vegetation in the process of runoff generation, and the mechanisms for controlling soil erosion in this area. In this study, typical grassland slopes in hilly and gully regions of the loess plateau were taken as research objects. Through artificial rainfall in the field, the response rules of the slope rainfall-runoff process to different grass coverage were explored. The results show that: (1) With the increase in rainfall intensity, the inhibitory effect of grassland vegetation on slope runoff decreased, which was mainly reflected in the gradual decrease in runoff rate and runoff coefficient, and the time required to reach stability gradually shortened. (2) Under 60 mm/h rainfall intensity, the sensitivity of runoff coefficient to 31.5% of grass cover change is the lowest, and the cost performance of grass cover with 55% coverage is the highest. (3) Grass coverage inhibited slope runoff by changing the hydraulic characteristics of the slope, but this effect was only obvious in low rainfall intensity and early rainfall. Rainfall in the loess hilly area is characterized by intense rain. The regulating effect of grass cover on slope runoff is not particularly significant under high intensity rainfall. If only considering the regulation of grassland vegetation on slopes, more than 60% grassland coverage is more efficient in inhibiting slope runoff under medium and low intensity rainfall.