草业学报 ›› 2026, Vol. 35 ›› Issue (9): 8-21.DOI: 10.11686/cyxb2025410
陈雪姣1(
), 马黎华1(
), 王喜1, 尹仲毅1, 靳皓琛2, 蒋先军1
收稿日期:2025-10-13
修回日期:2025-12-15
出版日期:2026-09-20
发布日期:2026-07-27
通讯作者:
马黎华
作者简介:Corresponding author. E-mail: malh@swu.edu.cn基金资助:
Xue-jiao CHEN1(
), Li-hua MA1(
), Xi WANG1, Zhong-yi YIN1, Hao-chen JIN2, Xian-jun JIANG1
Received:2025-10-13
Revised:2025-12-15
Online:2026-09-20
Published:2026-07-27
Contact:
Li-hua MA
摘要:
为探究水稻不同生育时期土壤无机氮的变化规律以及与土壤环境条件的响应关系,选取垄作(RT)、平作(CT)两种水稻耕作模式,开展连续两年(2021-2022)的田间监测试验。结果表明:1)RT和CT土壤铵态氮含量峰值出现在分蘖期-拔节期(RT:89.7 mg?kg-1,CT:52.1 mg?kg-1),硝态氮含量峰值出现在成熟期(RT:42.7 mg?kg-1,CT:58.4 mg?kg-1)。在0~20 cm深度的稻田土层中,不同耕作模式的铵态氮含量为RT>CT,硝态氮含量为CT>RT。2)两种耕作模式下植物全株平均含氮量最高出现在分蘖时期,氮利用率最高也出现在分蘖期,在拔节期-抽穗期全株氮素吸收量较大,并伴随着土壤铵态氮含量的明显降低。3)土壤温度和电导率呈上升趋势,而土壤含水率在不同生育时期因灌溉和排水呈现波动。在拔节期,RT的铵态氮与土壤温度呈现显著相关关系,硝态氮与土壤温度在抽穗期和成熟期呈现显著相关关系,CT的铵态氮在分蘖期和抽穗期与土壤温度均呈现显著相关关系,硝态氮在抽穗期与土壤含水率呈现显著相关关系。4)根据非线性回归的模拟结果,RT和CT的铵态氮含量表现为先增加后降低的变化趋势,RT的硝态氮含量变化也为先增加后降低的趋势,CT的硝态氮含量变化呈现非线性增加的趋势。铵态氮、硝态氮在生育早期主要受作物吸收调控,其贡献最高(78.5%),在生育后期环境因子的影响增强,贡献率升至61.1%,相较于硝态氮,铵态氮对环境因子的响应更为敏感。综上,水稻分蘖期的土壤无机氮变化最剧烈,分蘖期和成熟时期土壤无机氮对于土壤环境温度的变化最为敏感。垄作能够增加稻田铵态氮含量,降低硝态氮的积累。研究结果可为区域性水稻种植养分资源优化管理提供科学依据。
陈雪姣, 马黎华, 王喜, 尹仲毅, 靳皓琛, 蒋先军. 垄作稻田土壤无机氮变化及其对环境因子的响应[J]. 草业学报, 2026, 35(9): 8-21.
Xue-jiao CHEN, Li-hua MA, Xi WANG, Zhong-yi YIN, Hao-chen JIN, Xian-jun JIANG. Dynamics of soil inorganic nitrogen and its response characteristic to environmental factors in paddy fields under ridge tillage[J]. Acta Prataculturae Sinica, 2026, 35(9): 8-21.
图1 垄作、平作田块土壤剖面结构及采样点分布
Fig. 1 The distribution of soil profile and sampling points under ridge tillage (RT) and conventional tillage (CT) in paddy fields
处理 Treatment | pH | 有机质 Organic matter (g?kg-1) | 速效钾 Available potassium (mg?kg-1) | 速效磷 Available phosphorus (mg?kg-1) | 速效氮 Available nitrogen (mg?kg-1) | 全钾 Total potassium (g?kg-1) | 全磷 Total phosphorus (g?kg-1) | 全氮 Total nitrogen (g?kg-1) | 容重 Bulk density (g?cm-3) | 孔隙度 Porosity (%) |
|---|---|---|---|---|---|---|---|---|---|---|
| RT | 7.5 | 28.2 | 65.5 | 20.2 | 149.5 | 19.7 | 0.84 | 1.64 | 1.25 | 49.8 |
| CT | 7.2 | 29.1 | 68.0 | 31.3 | 154.5 | 18.9 | 1.01 | 1.64 | 1.32 | 47.6 |
表1 不同耕作方式下耕作土壤的基本理化指标
Table 1 Basic physical and chemical properties of soil under different tillage practices
处理 Treatment | pH | 有机质 Organic matter (g?kg-1) | 速效钾 Available potassium (mg?kg-1) | 速效磷 Available phosphorus (mg?kg-1) | 速效氮 Available nitrogen (mg?kg-1) | 全钾 Total potassium (g?kg-1) | 全磷 Total phosphorus (g?kg-1) | 全氮 Total nitrogen (g?kg-1) | 容重 Bulk density (g?cm-3) | 孔隙度 Porosity (%) |
|---|---|---|---|---|---|---|---|---|---|---|
| RT | 7.5 | 28.2 | 65.5 | 20.2 | 149.5 | 19.7 | 0.84 | 1.64 | 1.25 | 49.8 |
| CT | 7.2 | 29.1 | 68.0 | 31.3 | 154.5 | 18.9 | 1.01 | 1.64 | 1.32 | 47.6 |
图2 2021-2022年日均降水量和气温Ⅰ:第1次施肥时间First fertilization time;Ⅱ:第2次施肥时间Second fertilization time. TS:分蘖期 Tillering stage;JS:拔节期 Jointing stage;HS:抽穗期 Heading stage;MS:成熟期 Maturation stage.下同The same below.
Fig.2 Daily mean precipitation and temperature during 2021-2022
图3 耕作模式与生育时期对0~20 cm土壤铵态氮和硝态氮含量的影响*表示P<0.05,**表示P<0.01,NS表示没有显著相关性,下同。* indicates P<0.05,** indicates P<0.01,NS indicates no significant correlation, the same below.
Fig. 3 Effets of tillage mode and growth stage on the content of ammonium nitrogen and nitrate nitrogen in the 0-20 cm soil layer
生育时期 Growth stage | 处理 Treatment | 含氮量Nitrogen content (g?kg-1) | 生物量Biomass (g?m-2) | 氮利用率Nitrogen use efficiency (%) | |||
|---|---|---|---|---|---|---|---|
| 2021 | 2022 | 2021 | 2022 | 2021 | 2022 | ||
分蘖期 Tillering stage | RT | 45.45 | 42.78 | 202.12 | 256.78 | 21.86 | 20.58 |
| CT | 38.64 | 41.48 | 208.88 | 198.45 | 18.59 | 19.95 | |
| P值 P value | 0.024 | 0.456 | 0.104 | 0.036 | 0.009 | 0.553 | |
拔节期 Jointing stage | RT | 42.88 | 42.33 | 404.53 | 492.89 | 20.63 | 20.36 |
| CT | 38.59 | 39.12 | 392.41 | 423.67 | 18.56 | 18.82 | |
| P值 P value | 0.057 | 0.043 | 0.098 | 0.100 | 0.204 | 0.040 | |
抽穗期 Heading stage | RT | 41.93 | 41.21 | 974.36 | 1086.56 | 20.17 | 19.82 |
| CT | 36.91 | 38.45 | 896.60 | 981.23 | 17.75 | 18.49 | |
| P值 P value | 0.061 | 0.067 | 0.126 | 0.021 | 0.131 | 0.219 | |
成熟期 Maturation stage | RT | 41.15 | 42.56 | 1497.44 | 1659.78 | 19.79 | 20.47 |
| CT | 36.03 | 37.80 | 1334.52 | 1517.89 | 17.33 | 18.18 | |
| P值 P value | 0.459 | 0.491 | 0.031 | 0.044 | 0.191 | 0.201 | |
表2 两种耕作模式下水稻在不同生育时期的含氮量、生物量和氮利用率
Table 2 The nitrogen content, biomass and nitrogen use efficiency of paddy rice under two tillage modes at different growth stages
生育时期 Growth stage | 处理 Treatment | 含氮量Nitrogen content (g?kg-1) | 生物量Biomass (g?m-2) | 氮利用率Nitrogen use efficiency (%) | |||
|---|---|---|---|---|---|---|---|
| 2021 | 2022 | 2021 | 2022 | 2021 | 2022 | ||
分蘖期 Tillering stage | RT | 45.45 | 42.78 | 202.12 | 256.78 | 21.86 | 20.58 |
| CT | 38.64 | 41.48 | 208.88 | 198.45 | 18.59 | 19.95 | |
| P值 P value | 0.024 | 0.456 | 0.104 | 0.036 | 0.009 | 0.553 | |
拔节期 Jointing stage | RT | 42.88 | 42.33 | 404.53 | 492.89 | 20.63 | 20.36 |
| CT | 38.59 | 39.12 | 392.41 | 423.67 | 18.56 | 18.82 | |
| P值 P value | 0.057 | 0.043 | 0.098 | 0.100 | 0.204 | 0.040 | |
抽穗期 Heading stage | RT | 41.93 | 41.21 | 974.36 | 1086.56 | 20.17 | 19.82 |
| CT | 36.91 | 38.45 | 896.60 | 981.23 | 17.75 | 18.49 | |
| P值 P value | 0.061 | 0.067 | 0.126 | 0.021 | 0.131 | 0.219 | |
成熟期 Maturation stage | RT | 41.15 | 42.56 | 1497.44 | 1659.78 | 19.79 | 20.47 |
| CT | 36.03 | 37.80 | 1334.52 | 1517.89 | 17.33 | 18.18 | |
| P值 P value | 0.459 | 0.491 | 0.031 | 0.044 | 0.191 | 0.201 | |
图4 不同生育时期水稻氮吸收总量与土壤无机氮浓度的变化
Fig. 4 Changes in total nitrogen uptake of paddy rice and concentration of soil inorganic nitrogen during different growth stages
图5 两种耕作模式和生育时期下土壤温度、含水率、电导率特征及其与无机氮含量的相关性土壤温度、含水率和电导率均为0~20 cm土层连续监测值,按生育期进行平均计算。The data in the soil temperature, moisture content, and electrical conductivity were continuously monitored at 0-20 cm depth and averaged by growth stage.
Fig.5 Soil temperature, moisture content and electrical conductivity characteristics and their relationships with inorganic nitrogen content under different tillage practices and growth stages
图6 土壤铵态氮、硝态氮含量随水稻移栽后种植天数的变化模拟RMSE:均方根误差 Root mean square error;MAE:平均绝对误差 Mean absolute error.
Fig.6 Changes simulated in soil NH4+-N and NO3--N content with days after transplanting of paddy rice
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