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微生物菌剂施用量对土壤化学性质、酶活性及细菌群落的影响OA

Effects of microbial inoculant application rates on soil chemical properties,enzyme activities,and bacterial com-munities

中文摘要英文摘要

为确定微生物菌剂在麦玉轮作区玉米季施用量,探究菌剂不同施用量对玉米土壤化学性质、酶活性及细菌群落结构的影响.于2023年6月设置了微生物菌剂4个施用量处理[0 kg/hm2(CK)、45 kg/hm2(M1)、75 kg/hm2(M2)和 105 kg/hm2(M3)],分析了土壤化学性质、酶活性、细菌群落结构及功能代谢的变化特征,并明确各指标间的相互关系.在 0~20 cm土层,M2 处理较CK处理显著提高了土壤有机质含量 10.06%,各菌剂用量处理较CK处理显著提高了土壤碱解氮和有效磷含量,分别提高了 6.50%~20.12%和 11.58%~42.90%(P<0.05),且M3 处理提高效果最显著;相较CK处理,M1 和M3 处理土壤蔗糖酶活性显著提高,各菌剂用量处理土壤碱性磷酸酶活性较CK显著提高了 15.94%~76.81%(P<0.05).在 20~40 cm土层,相较CK处理,M2 处理土壤有机质、碱解氮和有效磷含量分别提高了9.37%、6.10%和 22.59%,土壤脲酶、蔗糖酶和碱性磷酸酶活性分别提高了16.82%、3.81%和 97.43%(P<0.05).随着玉米生育期的推进,各处理土壤细菌α多样性和群落结构有明显变化:施用 15 d时,相较CK处理,微生物菌剂施用可提高土壤细菌ACE、Chao1 和Shannon指数;施用 30 和 90 d时,M3 处理ACE、Chao1 和Shannon指数均低于其他处理.在不同时期,M2 处理相较其他处理土壤γ-变形菌纲、α-变形菌纲和拟杆菌纲相对丰度分别提高了 5.16%~7.77%、5.11%~12.85%和 4.71%~17.00%.PICRUSt功能预测表明,M2 处理在 15 d促进了碳水化合物代谢的增强,在 15 和 30 d促进了能量代谢、辅助因子和维生素代谢、翻译和核苷酸代谢,在 90 d使氨基酸代谢更强,有益于土壤养分循环.研究表明,施用 75 kg/hm2 微生物菌剂可显著提高土壤养分含量及酶活性,改善土壤细菌群落结构多样性,而高量的微生物菌剂施用(105 kg/hm2)可能会抑制细菌群落结构的健康发展.

The study aimed to determine the application rate of microbial inoculants during the maize season in the wheat-maize rotation zone,and to investigate the effects of different application rates of inoculants on soil chemical properties,enzyme activities,and bacterial community structure of maize.In June 2023,four application rates of microbial inoculants were set up[0 kg/hm²(CK),45 kg/hm²(M1),75 kg/hm²(M2),and 105 kg/hm²(M3)].The variation characteristics of soil chemical properties,enzyme activities,bacterial community structure,and functional metabolism were analyzed,and the relationships between these indicators were identified.In the 0-20 cm soil layer,the M2 treatment significantly increased soil organic matter content by 10.06%,compared with the CK treatment.All inoculant application rates significantly increased soil alkali-nitrogen and available phosphorus contents compared with the CK treatment,by 6.50%-20.12%and 11.58%-42.90%(P<0.05),respectively,with the M3 treatment showing more significant effects.Compared with the CK treatment,soil sucrase activity was significantly increased in the M1 and M3 treatments,and soil alkaline phosphatase activity was significantly increased by 15.94%-76.81%(P<0.05)in all inoculant application treatments compared with the CK treatment.In the 20-40 cm soil layer,compared with the CK treatment,the M2 treatment increased soil organic matter,alkali-nitrogen,and available phosphorus contents by 9.37%,6.10%,and 22.59%,respectively,and soil urease,sucrase,and alkaline phosphatase activities by 16.82%,3.81%,and 97.43%(P<0.05),respectively.As the maize growth stage progressed,there were significant changes in soil bacterial α-diversity and community structure in each treatment.At 15 d after application,compared with the CK treatment,the application of microbial inoculants increased the soil bacterial ACE,Chao1,and Shannon indices.At 30 and 90 d after application,the ACE,Chao1,and Shannon indices of the M3 treatment were lower than those of the other treatments.Compared with the other treatments,the M2 treatment increased the relative abundance of Gammaproteobacteria,Alphaproteobacteria,and Bacteroidia in the soil by 5.16%-7.77%,5.11%-12.85%,and 4.71%-17.00%,respectively.PICRUSt functional prediction showed that the M2 treatment enhanced carbohydrate metabolism at 15 d,promoted energy metabolism,co-factor and vitamin metabolism,translation,and nucleotide metabolism at 15 and 30 d,and made amino acid metabolism stronger at 90 d,thereby benefiting soil nutrient cycling.The study showed that the application of microbial inoculants at 75 kg/hm² could significantly increase soil nutrient content and enzyme activity,and improve the diversity of soil bacterial community structure.However,the application of a high amount of microbial inoculants(105 kg/hm²)might inhibit the development of bacterial community structure.

曾正群;任文欣;李旭;李敬宇;翟英芳;彭正萍;付鑫

华北作物改良与调控国家重点实验室,河北 保定 071033||河北农业大学资源与环境科学学院/河北省农田生态环境重点实验室,河北 保定 071033河北农业大学资源与环境科学学院/河北省农田生态环境重点实验室,河北 保定 071033河北农业大学资源与环境科学学院/河北省农田生态环境重点实验室,河北 保定 071033河北农业大学资源与环境科学学院/河北省农田生态环境重点实验室,河北 保定 071033河北农业大学资源与环境科学学院/河北省农田生态环境重点实验室,河北 保定 071033河北农业大学资源与环境科学学院/河北省农田生态环境重点实验室,河北 保定 071033华北作物改良与调控国家重点实验室,河北 保定 071033||河北农业大学国土资源学院,河北 保定 071033

华北地区微生物菌剂土壤化学性质酶活性细菌群落结构功能预测

north China regionmicrobial agentssoil chemical propertiesenzyme activitybacterial community structurefunctional prediction

《中国土壤与肥料》 2026 (1)

11-21,11

国家重点研发计划(2022YFD1901304)河北省省级科技计划(23567601H).

10.11838/sfsc.1673-6257.25216

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