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不同种植与养殖废弃物堆肥对温室西葫芦产量及根际土壤环境的影响

Yield and Rhizosphere Soil Environment of Greenhouse Zucchini in Response to Different Planting and Breeding Waste Composts.

作者信息

Tie Jianzhong, Qiao Yali, Jin Ning, Gao Xueqin, Liu Yayu, Lyu Jian, Zhang Guobin, Hu Linli, Yu Jihua

机构信息

College of Horticulture, Gansu Agricultural University, Lanzhou 730070, China.

Gansu Provincial Key Laboratory of Arid Land Crop Science, Gansu Agricultural University, Lanzhou 730070, China.

出版信息

Microorganisms. 2023 Apr 14;11(4):1026. doi: 10.3390/microorganisms11041026.

DOI:10.3390/microorganisms11041026
PMID:37110447
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC10143665/
Abstract

Composting, planting, and breeding waste for return to the field is the most crucial soil improvement method under the resource utilization of agricultural waste. However, how the vegetable yield and rhizosphere soil environment respond to different composts is still unknown. Therefore, eight formulations were designed for compost fermentation using agricultural waste [sheep manure (SM), tail vegetable (TV), cow manure (CM), mushroom residue (MR), and corn straw (CS)] without fertilizer (CK1) and local commercial organic fertilizer (CK2) as controls to study the yield and rhizosphere soil environment of greenhouse zucchini in response to different planting and breeding waste compost. Applying planting and breeding waste compost significantly increased the soil's organic matter and nutrient content. It inhibited soil acidification, which T4 (SM:TV:CS = 6:3:1) and T7 (SM:TV:MR:CS = 6:2:1:1) treatments affected significantly. Compared to CK2 treatment, T4 and T7 treatments showed a greater increase, with a significant increase of 14.69% and 11.01%, respectively. Therefore, T4, T7, and two control treatments were selected for high-throughput sequencing based on yield performance. Compared with the CK1 treatment, although multiple applications of chemical fertilizers led to a decrease in bacterial and fungal richness, planting and breeding waste compost maintained bacterial diversity and enhanced fungal diversity. Compared to CK2, the relative abundance increased in T7-treated (, , and ) and T4-treated () among bacteria. An increase in T4-treated ( and ) and among fungi and a decrease in T7-treated have been observed. Functional predictions of the bacterial Tax4Fun and fungal FUNGuild revealed that applying planting and breeding waste compost from the T4 treatment significantly increased the abundance of soil bacterial Metabolism of Cities, Genetic Information Processing, and Cellular Processes decreased the abundance of Pathotroph and Saprotroph-Symbiotroph fungi and increased the abundance of Saprotroph fungi. Overall, planting and breeding waste compost increased zucchini yield by improving soil fertility and microbial community structure. Among them, T4 treatment has the most significant effect, so T4 treatment can be selected as the optimized formulation of local commercial organic fertilizer. These findings have valuable implications for sustainable agricultural development.

摘要

堆肥、种植和养殖废弃物还田是农业废弃物资源化利用中最关键的土壤改良方法。然而,蔬菜产量和根际土壤环境如何响应不同的堆肥仍不清楚。因此,设计了8种利用农业废弃物(羊粪(SM)、尾菜(TV)、牛粪(CM)、菌渣(MR)和玉米秸秆(CS))进行堆肥发酵的配方,并以不施肥(CK1)和当地商业有机肥(CK2)作为对照,研究温室西葫芦的产量和根际土壤环境对不同种植和养殖废弃物堆肥的响应。施用种植和养殖废弃物堆肥显著增加了土壤有机质和养分含量,抑制了土壤酸化,其中T4(SM:TV:CS = 6:3:1)和T7(SM:TV:MR:CS = 6:2:1:1)处理的影响显著。与CK2处理相比,T4和T7处理的增幅更大,分别显著增加了14.69%和11.01%。因此,基于产量表现,选择T4、T7和两个对照处理进行高通量测序。与CK1处理相比,虽然多次施用化肥导致细菌和真菌丰富度下降,但种植和养殖废弃物堆肥维持了细菌多样性并增强了真菌多样性。与CK2相比,T7处理(、和)和T4处理()的细菌相对丰度增加。在真菌中,观察到T4处理的(和)增加,而T7处理的减少。细菌Tax4Fun和真菌FUNGuild的功能预测表明,施用T4处理的种植和养殖废弃物堆肥显著增加了土壤细菌“城市代谢”、“遗传信息处理”和“细胞过程”的丰度,降低了“致病营养型”和“腐生营养型 - 共生营养型”真菌的丰度,增加了“腐生营养型”真菌的丰度。总体而言,种植和养殖废弃物堆肥通过改善土壤肥力和微生物群落结构提高了西葫芦产量。其中,T4处理效果最显著,因此可选择T4处理作为当地商业有机肥的优化配方。这些发现对可持续农业发展具有重要意义。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/44b0/10143665/a0d19b457dcf/microorganisms-11-01026-g010.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/44b0/10143665/0ebfa9043f0e/microorganisms-11-01026-g001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/44b0/10143665/fc5504dc6a9a/microorganisms-11-01026-g002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/44b0/10143665/9675129d704b/microorganisms-11-01026-g003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/44b0/10143665/9c027e4295e5/microorganisms-11-01026-g004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/44b0/10143665/7734f885a33e/microorganisms-11-01026-g005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/44b0/10143665/78b5bc85f2fd/microorganisms-11-01026-g006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/44b0/10143665/cf592775b79d/microorganisms-11-01026-g007.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/44b0/10143665/33f07fc47058/microorganisms-11-01026-g008.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/44b0/10143665/5375733d5f32/microorganisms-11-01026-g009.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/44b0/10143665/a0d19b457dcf/microorganisms-11-01026-g010.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/44b0/10143665/0ebfa9043f0e/microorganisms-11-01026-g001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/44b0/10143665/fc5504dc6a9a/microorganisms-11-01026-g002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/44b0/10143665/9675129d704b/microorganisms-11-01026-g003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/44b0/10143665/9c027e4295e5/microorganisms-11-01026-g004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/44b0/10143665/7734f885a33e/microorganisms-11-01026-g005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/44b0/10143665/78b5bc85f2fd/microorganisms-11-01026-g006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/44b0/10143665/cf592775b79d/microorganisms-11-01026-g007.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/44b0/10143665/33f07fc47058/microorganisms-11-01026-g008.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/44b0/10143665/5375733d5f32/microorganisms-11-01026-g009.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/44b0/10143665/a0d19b457dcf/microorganisms-11-01026-g010.jpg

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