Individual and combined effects of earthworms and Sphingobacterium sp. on soil organic C, N forms and enzyme activities in non-contaminated and Cd-contaminated soil
文献类型： 外文期刊
作者： Jia, Li 2 ; Liu, Qing 1 ; Chen, Siyi 1 ; Liu, Kexue 4 ; Chen, Yiqing 1 ; Motelica-Heino, Mikael 2 ; Zhong, Hesen 1 ; Zhang, Menghao 1 ; Tibihenda, Cevin 1 ; Lavelle, Patrick 5 ; Dai, Jun 1 ; Zhang, Chi 1 ;
作者机构： 1.South China Agr Univ, Coll Nat Resources & Environm, Guangzhou 510642, Peoples R China
2.Univ Orleans, CNRS, ISTO, UMR 7327, F-45071 Orleans, France
3.Chinese Acad Trop Agr Sci, Guangzhou Expt Stn, Guangzhou 510642, Peoples R China
4.Guangzhou Xinhua Univ, Sch Resources & Planning, Guangzhou 510520, Peoples R China
5.Sorbonne Univ, Ctr IRD, IEES BIODIS, 32 Rue Henri Varagnat, F-93143 Bondy, France
6.South China Agr Univ, Coll Resources & Environm, Guangzhou 510642, Peoples R China
关键词： Earthworm; Sphingobacterium sp.; Cd-contaminated soil; Carbon and nitrogen forms; Enzyme activities
期刊名称：EUROPEAN JOURNAL OF SOIL BIOLOGY （ 影响因子：4.2； 五年影响因子：3.9 ）
ISSN： 1164-5563
年卷期： 2024 年 120 卷
页码：
收录情况： SCI
摘要： Earthworms and Sphingobacterium sp. are known for their strong organic compound decomposition ability and wide distribution in soil. However, interactions of soil organic matter decomposition with soil properties and whether microbial species such as Sphingobacterium sp. could assist earthworms in carbon and nitrogen transformation in soil remain poorly understood. Earthworms (Eisenia fetida, Amynthas gracilis) and Sphingobacterium sp. were introduced in non-contaminated and cadmium-contaminated soils under controlled laboratory conditions for 20 days. We examined their individual or combined effects on carbon and nitrogen forms and related enzyme activities to assess their influence on soil C and N cycling. Individual Sphingobacterium sp. inoculation led to significantly decreased organic carbon (SOC) contents, reducing it by 16.5% in non-contaminated soil and by 3.77%, in Cd-contaminated soil. It resulted in an increased microbial biomass carbon (MBC) contents, reaching 1685 +/- 292 mg center dot kg(-1) in non-contaminated soil. Individual introductions of E. fetida and A. gracilis caused a decline in SOC content in non-contaminated soil, but increased significantly dissolved organic carbon (DOC) and alkali-hydrolysable nitrogen (AN) contents by 75.8%, 53.6% and 32.9%, 20.9%, respectively. In contrast, in Cd-contaminated soil, only the significant combined effects of earthworms and Sphingobacterium sp. were linked to significant increase in SOC contents, raising by 7.22% and 9.64% in E. fetida + Sphingobacterium sp. and A. gracilis + Sphingobacterium sp. treatments, respectively. In non-contaminate soil, the combined effects of earthworm and Sphingobacterium sp. further increased DOC and AN content by 212%, 134% and 31.3%, 25.4% in the treatments of E. fetida + Sphingobacterium sp. and A. gracilis + Sphingobacterium sp., respectively; the highest ratios of DOC to SOC and AN to total Nitrogen (TN) were found in the earthworm + Sphingobacterium sp. treatments as well. In non-contaminated soil, Sphingobacterium sp. and earthworms mainly influenced beta-glucosidase (BG), urease (URE), N-acetyl-beta-D-glucosaminidase (NAG) activities and fluorescein diacetate hydrolysis (FDA) hydrolysis, while in Cd-contaminated soil, they mainly influenced invertase (INV), NAG, URE, and protease (PRO) activities. Principal component analysis indicated that in non-contaminated soil, the earthworm activities dominated the mineralization processes of soil carbon and nitrogen, and Sphingobacterium sp. can intensify this process when it was inoculated in soil along with earthworms. Furthermore, both earthworm species increased C and N levels by elevated INV and PRO activities in combined inoculation. However, in contaminated soil, the impact of earthworm inoculation on soil C stabilization showed a species dependent pattern. E. fetida reduced C mineralization by decreasing URE activities, while A. gracilis enhanced C stabilization by increasing INV activities and decreasing PRO activities. In conclusion, earthworms played a key role in enhancing C and N mineralization in non-contaminated soil and promoting C stabilization in contaminated soil. Both earthworm species followed similar strategies in the former process but adopted different strategies in the latter. When introduced individually, Sphingobacterium sp. was able to promote mineralization in both soils, primarily assisting earthworms in improving carbon and nitrogen mineralization in non-contaminated soil but hindering these processes in Cd-contaminated soil. These findings provide insights into the combined effects of earthworms and microorganisms on carbon and nitrogen cycling.
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Lili;Gao, Yuan;Tang, Bixia;Zhang, Yadong;Zhang, Hao;Qian, Qiheng;Zhang, Zhewen;Kang, Hailong;Huang, Tianhao;Wang, Zhonghuang;Zhu, Jun-wei;Zhang, Sisi;Wu, Song;Huang, Yue;Zhang, Mochen;Wang, Guoliang;Zheng, Xin-chang;Zong, Wenting;Zhao, Wei;Xing, Peiqi;Li, Rujiao;Liu, Zhaoqi;Lu, Mingming;Mai, Jialin;Gao, Qianwen;Shang, Yunfei;Qain, Qiheng;Jiang, Meiye;Bu, Congfan;Zeng, Jingyao;Pan, Siyu;Kang, Hongen;Liu, Xinxuan;Lin, Shiqi;Yuan, Na;Jia, Peilin;Zheng, Xinchang;Sun, Yanling;Xiong, Zhuang;Yang, Fei;Chen, Xu;Chen, Tingting;Yu, Caixia;Dong, Lili;Zhai, Shuang;Sun, Yubin;Chen, Qiancheng;Yang, Xiaoyu;Zhang, Xin;Sang, Zhengqi;Wang, Yonggang;Zhao, Yilin;Chen, Huanxin;Lan, Li;Wang, Yan-qing;Wang, Anke;Jia, Yaokai;Zhao, Xuetong;Pan, Yitong;Liu, Xiaonan;Zhang, Rongqin;Wang, Yi;Ma, Lina;Teng, Xufei;Li, Lun;Li, Na;Cui, Ying;Jin, Tong;Jin, Enhui;Zhang, Tao;Xu, Tianyi;Chen, Ming;Niu, Guangyi;Pan, Rong;Zhu, Tongtong;Chu, Yuan;Sang, Jian;Zhang, Yuan-sheng;Zhang, Xinran;Guo, Xutong;Li, Zhao;Liu, Lin;Feng, Changrui;Qin, Yuxin;Jing, Wei;Luo, Sicheng;Zhu, Tong-tong;Zhang, Yuansheng;Wu, Zis-han;Li, Qianpeng;Fan, Zhuojing;Zhao, Wen-ming;Xue, Yongbiao;Bao, Yiming;Zhang, Zhang;Zhao, Wenming;Xiao, Jingfa;He, Shun-min;Li, Yixue;Zhao, Guoping;Gong, Zheng;Zhao, Xue-tong;Song, Shuhui;Duan, Guangya;Wu, Gangao;Chen, Xiaoning;Li, Zhaohua;Gao, Yuan;Zhang, Hao;Qian, Qiheng;Kang, Hailong;Huang, Tianhao;Wang, Zhonghuang;Wu, Song;Huang, Yue;Zhang, Mochen;Wang, Guoliang;Zong, Wenting;Zhao, Wei;Li, Rujiao;Liu, Zhaoqi;Lu, Mingming;Mai, Jialin;Gao, Qianwen;Shang, Yunfei;Qain, Qiheng;Jiang, Meiye;Pan, Siyu;Kang, Hongen;Lin, Shiqi;Xiong, Zhuang;Yang, Fei;Pan, Yitong;Liu, Xiaonan;Zhang, Rongqin;Wang, Yi;Ma, Lina;Teng, Xufei;Cui, Ying;Jin, Tong;Jin, Enhui;Zhang, Tao;Chen, Ming;Niu, Guangyi;Pan, Rong;Zhu, Tongtong;Chu, Yuan;Sang, Jian;Zhang, Yuan-sheng;Zhang, Xinran;Guo, Xutong;Li, Zhao;Feng, Changrui;Qin, Yuxin;Jing, Wei;Zhu, Tong-tong;Zhang, Yuansheng;Wu, Zis-han;Li, Qianpeng;Zhao, Wen-ming;Yuan, Hao;Su, Tianhan;Zhang, Yong E.;Liao, Xingyu;He, Shun-min;Chen, Runsheng;Yang, Fengchun;Li, Jiao;Liao, Xingyu;He, Shun-min;Chen, Runsheng;Yang, Fengchun;Li, Jiao;Liao, Xingyu;Zhang, Guoqing;Li, Yixue;Zhao, Guoping;Ling, Yunchao;Wang, Yiwei;Yang, Jiaxin;Zhuang, Xinhao;Liu, Wan;Cao, Ruifang;Zhang, Guo-qing;Zhou, Chenfen;Wang, Pengyu;Zhang, Guoqing;Li, Yixue;Zhao, Guoping;Ling, Yunchao;Wang, Yiwei;Yang, Jiaxin;Zhuang, Xinhao;Liu, Wan;Cao, Ruifang;Zhang, Guo-qing;Zhou, Chenfen;Wang, Pengyu;Zhao, Guoping;Zhao, Guoping;Chen, Runsheng;Zhang, Zaichao;Xia, Zhiqiang;Zhou, Xincheng;Chao, Jin-quan;Tian, Weimin;Huang, Yue;Xing, Peiqi;Liu, Zhaoqi;Pan, Siyu;Kang, Hongen;Liu, Xinxuan;Lin, Shiqi;Yuan, Na;Jia, Peilin;Xu, Xiaowei;Kang, Hongyu;Hou, Li;Gao, Qianwen;Liu, Jie;Wang, Jinyue;Liu, Xinxuan;Zhang, Yuanpu;Wang, Zhennan;Yuan, Hao;Su, Tianhan;Zhang, Yong E.;Wang, Zhennan;Yuan, Hao;Su, Tianhan;Zhang, Yong E.;Yao, Qiliang;Luo, Sicheng;Shen, Wen-Kang;Guo, An-Yuan;Liu, Dan;Zhang, Chi;Xue, Yu;Gou, Yujie;Chen, Miaomiao;Peng, Di;Ning, Wanshan;Wei, Yuxiang;Liu, Chun-Jie;Xie, Gui-Yan;Zhang, Qiong;Fu, Shanshan;Tan, Xiaodan;Tang, Dachao;Zhang, Weizhi;Luo, Mei;Miao, Ya-Ru;Huang, Xinhe;Feng, Zihao;Xie, Guiyan;Han, Cheng;Tang, Qing;Zuo, Zhixiang;Ren, Jian;Xie, Yubin;Luo, XiaoTong;Zhang, Xinxin;Xiao, Yun;Li, Xia;Zhao, Zheng;Jiang, Tao;Wu, Wanying;Zhao, Fangqing;Chen, Ming;Meng, Xianwen;Zhou, Yincong;Yuan, Chunhui;Wu, Wenyi;Chen, Ming;Meng, Xianwen;Zhou, Yincong;Yuan, Chunhui;Wu, Wenyi;Luo, Hao;Gao, Feng;Luo, Hao;Gao, Feng;Luo, Hao;Gao, Feng;Luo, Hao;Gao, Feng;Zhang, Yong E.;Guo, Guoji;Gao, Xin;Liao, Xingyu;Wang, Jianxin;Yang, Dechang;Tian, Feng;Gao, Ge;Yang, Dechang;Tian, Feng;Gao, Ge;Cui, Qinghua;Cui, Qinghua;Xiao, Chunfu;Li, Chuan-Yun;Liu, Pei;Sun, Yongqing;Sang, Jian
关键词：
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Molecular identification of the key starch branching enzyme-encoding gene SBE2.3 and its interacting transcription factors in banana fruits
作者：Miao, Hongxia;Liu, Juhua;Jia, Caihong;Zhao, Dongfang;Xu, Biyu;Jin, Zhiqiang;Sun, Peiguang;Liu, Qing;Jin, Zhiqiang
关键词：
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Genome-wide analyses of SWEET family proteins reveal involvement in fruit development and abiotic/biotic stress responses in banana
作者：Miao, Hongxia;Miao, Yulu;Liu, Juhua;Zhang, Kaixing;Hu, Wei;Zhang, Jianbin;Wang, Jingyi;Wang, Zhuo;Jia, Caihong;Xu, Biyu;Jin, Zhiqiang;Sun, Peiguang;Jin, Zhiqiang;Liu, Qing;Miao, Yulu
关键词：
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The AGPase Family Proteins in Banana: Genome-Wide Identification, Phylogeny, and Expression Analyses Reveal Their Involvement in the Development, Ripening, and Abiotic/Biotic Stress Responses
作者：Miao, Hongxia;Liu, Juhua;Xu, Biyu;Jin, Zhiqiang;Sun, Peiguang;Jin, Zhiqiang;Liu, Qing
关键词：banana (Musa acuminata L.);AGPase;genome-wide identification;fruit development;abiotic stress;biotic stress
