Ecology and Environment ›› 2023, Vol. 32 ›› Issue (3): 492-499.DOI: 10.16258/j.cnki.1674-5906.2023.03.007
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TANG Haiming*(), SHI Lihong, WEN Li, CHENG Kaikai, LI Chao, LONG Zedong, XIAO Zhiwu, LI Weiyan, GUO Yong
Received:
2023-02-22
Online:
2023-03-18
Published:
2023-06-02
Contact:
TANG Haiming
唐海明*(), 石丽红, 文丽, 程凯凯, 李超, 龙泽东, 肖志武, 李微艳, 郭勇
通讯作者:
唐海明
作者简介:
唐海明(1980年生),男,研究员,博士,研究方向为土壤微生态与农作制。E-mail: tanghaiming66@163.com
基金资助:
CLC Number:
TANG Haiming, SHI Lihong, WEN Li, CHENG Kaikai, LI Chao, LONG Zedong, XIAO Zhiwu, LI Weiyan, GUO Yong. Effects of Different Long-term Fertilizer Managements on Rhizosphere Soil Nitrogen in the Double-cropping Rice Field[J]. Ecology and Environment, 2023, 32(3): 492-499.
唐海明, 石丽红, 文丽, 程凯凯, 李超, 龙泽东, 肖志武, 李微艳, 郭勇. 长期施肥对双季稻田根际土壤氮素的影响[J]. 生态环境学报, 2023, 32(3): 492-499.
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URL: https://www.jeesci.com/EN/10.16258/j.cnki.1674-5906.2023.03.007
处理 | pH | w(有机碳)/(g∙kg-1) | w(总氮)/(g∙kg-1) | w(碱解氮)/(g∙kg-1) | w(硝态氮)/(g∙kg-1) | w(氨态氮)/(g∙kg-1) | w(无机氮)/(g∙kg-1) |
---|---|---|---|---|---|---|---|
MF | 6.32±0.17ab | 21.46±0.68c | 2.07±0.06c | 0.145±0.001c | 0.17±0.01c | 0.16±0.01c | 0.49±0.01c |
RF | 6.70±0.17a | 24.82±0.72b | 2.45±0.07b | 0.183±0.001b | 0.21±0.01b | 0.20±0.01b | 0.61±0.02b |
OM | 6.81±0.18a | 29.62±0.71a | 3.08±0.08a | 0.213±0.001a | 0.27±0.01a | 0.23±0.01a | 0.71±0.02a |
CK | 6.21±0.16b | 19.68±0.56d | 1.91±0.06c | 0.127±0.001d | 0.13±0.01d | 0.12±0.01d | 0.37±0.02d |
Table 1 Effects of different long-term fertilizer treatments on rhizosphere soil physical and chemical characteristics in the double-cropping rice field
处理 | pH | w(有机碳)/(g∙kg-1) | w(总氮)/(g∙kg-1) | w(碱解氮)/(g∙kg-1) | w(硝态氮)/(g∙kg-1) | w(氨态氮)/(g∙kg-1) | w(无机氮)/(g∙kg-1) |
---|---|---|---|---|---|---|---|
MF | 6.32±0.17ab | 21.46±0.68c | 2.07±0.06c | 0.145±0.001c | 0.17±0.01c | 0.16±0.01c | 0.49±0.01c |
RF | 6.70±0.17a | 24.82±0.72b | 2.45±0.07b | 0.183±0.001b | 0.21±0.01b | 0.20±0.01b | 0.61±0.02b |
OM | 6.81±0.18a | 29.62±0.71a | 3.08±0.08a | 0.213±0.001a | 0.27±0.01a | 0.23±0.01a | 0.71±0.02a |
CK | 6.21±0.16b | 19.68±0.56d | 1.91±0.06c | 0.127±0.001d | 0.13±0.01d | 0.12±0.01d | 0.37±0.02d |
Figure 1 Effects of different long-term fertilizer treatments on rhizosphere soil microbial biomass nitrogen content in the double-cropping rice field
Figure 2 Effects of different long-term fertilizer treatments on rhizosphere soil aerobic N mineralization rate (a) and anaerobic N mineralization rate (b) in the double-cropping rice field
Figure 3 Effects of different long-term fertilizer treatments on rhizosphere soil nitrification rate (a) and ammonification rate (b) in the double-cropping rice field
处理 | 项目 | ||||
---|---|---|---|---|---|
硝化细菌量/(105 cfu∙g-1) | 反硝化细菌量/(105 cfu∙g-1) | 氨化细菌量/(106 cfu∙g-1) | 纤维素分解菌量/(103 cfu∙g-1) | 固氮菌量/(106 cfu∙g-1) | |
MF | 13.39±1.15c | 27.37±1.58c | 28.53±1.81c | 32.06±1.13b | 14.46±0.63c |
RF | 26.42±0.75b | 36.26±1.04b | 37.95±1.09b | 36.26±1.03a | 24.78±0.80a |
OM | 39.88±1.37a | 54.93±1.79a | 48.12±1.39a | 38.68±1.12a | 21.76±0.72b |
CK | 8.92±0.26d | 15.47±1.44d | 10.14±1.29d | 13.35±0.78c | 8.79±0.26d |
Table 2 Effects of different long-term fertilizer treatments on rhizosphere soil microorganisms with nitrogen cycle in the double-cropping rice field
处理 | 项目 | ||||
---|---|---|---|---|---|
硝化细菌量/(105 cfu∙g-1) | 反硝化细菌量/(105 cfu∙g-1) | 氨化细菌量/(106 cfu∙g-1) | 纤维素分解菌量/(103 cfu∙g-1) | 固氮菌量/(106 cfu∙g-1) | |
MF | 13.39±1.15c | 27.37±1.58c | 28.53±1.81c | 32.06±1.13b | 14.46±0.63c |
RF | 26.42±0.75b | 36.26±1.04b | 37.95±1.09b | 36.26±1.03a | 24.78±0.80a |
OM | 39.88±1.37a | 54.93±1.79a | 48.12±1.39a | 38.68±1.12a | 21.76±0.72b |
CK | 8.92±0.26d | 15.47±1.44d | 10.14±1.29d | 13.35±0.78c | 8.79±0.26d |
项目 | pH | 有机碳 | 总氮 | 微生物量氮 | 碱解氮 | 硝态氮 | 氨态氮 | 无机氮 | 硝化细菌 | 反硝化细菌 | 氨化细菌 | 水稻产量 |
---|---|---|---|---|---|---|---|---|---|---|---|---|
有氧氮矿化率 | 0.627* | -0.642* | -0.705* | -0.416 | -0.683* | -0.301 | -0.842** | -0.763* | 0.715* | 0.689* | 0.308 | 0.685* |
厌氧氮矿化率 | 0.675* | -0.625* | -0.674* | -0.352 | -0.655* | -0.276 | -0.837** | -0.705* | 0.662* | 0.637* | 0.412 | 0.664* |
硝化速率 | 0.786* | -0.782* | -0.713* | -0.427 | -0.702* | -0.151 | -0.903** | -0.684* | 0.741* | 0.703* | 0.457 | 0.413 |
氨化速率 | -0.106 | -0.087 | -0.165 | -0.248 | -0.143 | -0.427 | -0.135 | -0.262 | 0.418 | 0.385 | 0.736* | 0.337 |
Table 3 Relationship between rhizosphere soil nitrogen mineralization and soil phychemical characteristics, soil microorganisms under different long-term fertilizer conditions
项目 | pH | 有机碳 | 总氮 | 微生物量氮 | 碱解氮 | 硝态氮 | 氨态氮 | 无机氮 | 硝化细菌 | 反硝化细菌 | 氨化细菌 | 水稻产量 |
---|---|---|---|---|---|---|---|---|---|---|---|---|
有氧氮矿化率 | 0.627* | -0.642* | -0.705* | -0.416 | -0.683* | -0.301 | -0.842** | -0.763* | 0.715* | 0.689* | 0.308 | 0.685* |
厌氧氮矿化率 | 0.675* | -0.625* | -0.674* | -0.352 | -0.655* | -0.276 | -0.837** | -0.705* | 0.662* | 0.637* | 0.412 | 0.664* |
硝化速率 | 0.786* | -0.782* | -0.713* | -0.427 | -0.702* | -0.151 | -0.903** | -0.684* | 0.741* | 0.703* | 0.457 | 0.413 |
氨化速率 | -0.106 | -0.087 | -0.165 | -0.248 | -0.143 | -0.427 | -0.135 | -0.262 | 0.418 | 0.385 | 0.736* | 0.337 |
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