Jiachun Zhang

Jiachun Zhang


Research Focus & Metrics

Academic Career Length

8Years (2019-Present)

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

Representative Publications

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21 November 2022 in Science of The Total Environment
Verified
Journal Article
Closed access
ZZZhenming Zhang
Zhenming Zhang
XWXianliang Wu
Xianliang Wu
HLHuijuan Liu
Huijuan Liu
Xianfei HuangXianfei Huang
Xianfei Huang
QCQina Chen
Qina Chen
JZJiachun Zhang
Jiachun Zhang

7 October 2023 in Science of The Total Environment
Verified
Journal Article
Closed access
ZZZhenming Zhang
Zhenming Zhang
FZFudong Zhang
Fudong Zhang
XYXiuyuan Yang
Xiuyuan Yang
JZJiachun Zhang
Jiachun Zhang

29 June 2020 in Environmental Science and Pollution Research
Verified
Journal Article
Closed access
PDF file
ZZZhenming Zhang
Zhenming Zhang
XWXianliang Wu
Xianliang Wu
QWQiusheng Wu
Qiusheng Wu
Xianfei HuangXianfei Huang
Xianfei Huang
JZJiachun Zhang
Jiachun Zhang
HFHui Fang
Hui Fang

27 December 2021 in Forests
Verified
Journal Article
Open access
PDF file
XWXingfu Wang
Xingfu Wang
Xianfei HuangXianfei Huang
Xianfei Huang
KXKangning Xiong
Kangning Xiong
JHJiwei Hu
Jiwei Hu
ZZZhenming Zhang
Zhenming Zhang
JZJiachun Zhang
Jiachun Zhang
To study the spatial distribution characteristics of soil organic carbon (SOC) coupled with rocky desertification, 1212 soil samples from 152 soil profiles were sampled from different karst landforms, including karst low hills/virgin forest (KLH) in Libo County, a karst peak-cluster depression (KPCD) in Xingyi County, a karst canyon (KC) in Guanling County, a karst plateau basin (KPB) in Puding County and a karst trough valley (KTV) in Yinjiang County. The spatial distribution characteristics of the responses of SOC, SOC density (SOCD), rocky desertification and soil bulk density (SBD) to different influencing factors were analyzed. The relationships among SOC, SOCD, rocky desertification and SBD were analyzed using Pearson correlation analysis. The SOC storage capacity was characterized by using SOCD, and then the SOC storage capacity in different evolution stages of karst landforms was assessed. The SOC contents of KLH, KPCD, KC, KPB and KTV ranged from 6.16 to 38.20 g·kg−1, 7.42 to 27.08 g·kg−1, 6.28 to 35.17 g·kg−1, 4.62 to 23.79 g·kg−1 and 5.24 to 37.85 g·kg−1, respectively, and their average SOCD values (0–100 cm) were 7.37, 10.79, 7.06, 8.51 and 7.84 kg·m−2, respectively. The karst landforms as ordered by SOC storage capacity were KPCD > KPB > KLH > KTV > KC. The SOC content was negatively correlated with the SBD; light rocky desertification may lead to SOC accumulation. The rocky desertification degree and SBD were closely associated with slope position and gradient. Rocky desertification first increased, then decreased from mountain foot to summit, and increased with increasing slope gradient. However, the SBD decreased from mountain foot to summit and with increasing slope gradient. The SOC contents on the northern aspect of the mountains were generally higher than the other aspects. In summary, rock outcrops controlled the SOC contents in the studied regions. The slope position, gradient and aspect influenced the composition and distribution of vegetation, which influenced the evolution of rocky desertification. Therefore, these factors indirectly affected the SOC content. Additionally, the SOCD decreased with increasing rocky desertification. During the different evolution stages of karst landforms, the SOC storage capacity first decreases, then increases.

1 June 2020 in Tropical Ecology
Verified
Journal Article
Closed access
PDF file
ZZZhenming Zhang
Zhenming Zhang
Xianfei HuangXianfei Huang
Xianfei Huang
JZJiachun Zhang
Jiachun Zhang

5 January 2024 in Frontiers in Plant Science
Verified
Journal Article
Open access
GMGuiting Mu
Guiting Mu
LXLifu Xu
Lifu Xu
JZJiachun Zhang
Jiachun Zhang
Although straw returning to the field (SRTTF) is conducive to promoting sustainable agricultural production and protecting the environment, straw resources are still wasted due to the lack of suitable straw-returning technology in southern China. Based on the statistical yearbook and a large number of studies, different methods were used to calculate the total straw resources and SRTTF potential, and differences in these methods were compared. The results indicate that the total amount of straw resources in southern China in 2021 was 3.35×108 t. The nutrient content of K2O in the straw accounted for the highest proportion of total nutrient resources (63.66%), followed by N (26.88%) and P2O5 (9.46%). In theory, total SRTTF could replace almost all K2O and part of N and P2O5, indicating that the nutrient substitution potential of SRTTF was high. It is suggested that the SRTTF method be adopted in the middle and lower reaches of the Yangtze River, which mainly uses direct returning (DR) supplemented by indirect returning (IDR). In southeast China, straw returning is carried out by the combination of IDR and IR. In southwest China, straw returning is mainly carried out by IR and supplemented by MDR. This study will provide theoretical support for the government to formulate straw-returning policy.