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长江中游双季稻田不同轮作方式对土壤质量的影响

本站小编 Free考研考试/2022-01-01

王志强1, 3,,
缪建群2,
刘英3,
唐海鹰3,
张鹏3,
钟川3,
黄国勤3,,,
赵其国4
1.九江学院江西长江经济带研究院/九江学院经济与管理学院 九江 332005
2.江西农业大学理学院 南昌 330045
3.江西农业大学生态科学研究中心/江西省高校生态学学科联盟 南昌 330045
4.中国科学院南京土壤研究所 南京 210008
基金项目: 国家重点研发计划课题2016YFD0300208
国家自然科学基金项目41661070
江西省科技厅重点研发项目20161BBF60058
江西省教育厅科学技术研究项目GJJ181379

详细信息
作者简介:王志强, 主要从事农业生态学研究。E-mail:289459509@qq.com
通讯作者:黄国勤, 主要研究方向为耕作制度、农业生态和农业可持续发展等。E-mail:hgqjxes@sina.com
中图分类号:S55;S365

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出版历程

收稿日期:2020-03-09
录用日期:2020-05-30
刊出日期:2020-11-01

Effect of various crops rotations on soil quality in double cropping rice field in the middle reaches of the Yangtze River

WANG Zhiqiang1, 3,,
MIU Jianqun2,
LIU Ying3,
TANG Haiying3,
ZHANG Peng3,
ZHONG Chuan3,
HUANG Guoqin3,,,
ZHAO Qiguo4
1. Jiangxi Yangtze River Economic Belt Research Institute, Jiujiang University/School of Economics and Management, Jiujiang University, Jiujiang 332005, China
2. College of Science, Jiangxi Agriculture University, Nanchang 330045, China
3. Research Center on Ecological Science, Jiangxi Agriculture University/Ecology Discipline Alliance of Universities in Jiangxi Province, Nanchang 330045, China
4. Institute of Soil Science, Chinese Academy of Sciences, Nanjing 210008, China
Funds: the National Key R&D Project of China2016YFD0300208
the National Natural Science F oundation of China41661070
the Key Research and Development Project of Science and Technology Department of Jiangxi Province20161BBF60058
the Science and Techmology Research Project of Department of Education of Jiangxi ProvinceGJJ181379

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Corresponding author:HUANG Guoqin, E-mail:hgqjxes@sina.com


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摘要
摘要:研究长江中游地区不同种植模式和秸秆还田管理下农田土壤养分、有机碳及其酶活性的变化,评估农业管理措施对土壤质量的影响,可为长江中游双季稻区农业资源高效利用及可持续发展提供理论依据。2012—2017年进行不同轮、连作长期定位试验,设置冬季休耕—双季稻,冬种紫云英—、油菜—、大蒜—和轮作(马铃薯、大蒜、油菜和紫云英年际轮作)—双季稻5个处理,在冬季作物秸秆和水稻秸秆双重还田条件下,通过运用多元方差分析、相关性分析和主成分分析等统计方法,结合南方双季稻田土壤的适宜性,筛选出最小数据集(minimum data set,MDS)中土壤质量指标并测定,最后采用模糊数学方法对双季稻区的土壤质量进行定量评价。结果表明,在长江中游双季稻区,经过6年的冬季种植合适作物并秸秆双重还田,相比冬季休闲处理,除冬季种植大蒜处理外,其他冬种处理均能有效提高稻田土壤质量10.73%~12.91%,不同冬种方式下双季稻田的土壤质量高低依次为不同冬种轮作(0.726)>冬季种植油菜(0.723)>冬季种植紫云英(0.712)>冬季休闲(0.643)>冬季种植大蒜(0.638)。由此可见,适宜的轮作方式及秸秆双重还田能显著提高双季稻土壤质量,这为南方稻田健康可持续发展提供了理论支撑。
关键词:双季稻田/
秸秆双重还田/
轮作方式/
土壤质量
Abstract:Improved knowledge that may support the efficient utilization and sustainable development of agricultural resources in the middle reaches of the Yangtze River is still needed. Herein, changes on soil nutrients, organic carbon, and enzyme activities under different planting patterns and straw retention were assessed, and the impact of agricultural management measures on soil quality was evaluated in this particular geographical region. The long-term positioning experiment of different rotational and continuous cropping was carried out from 2012 to 2017, and five treatments of rotation patterns including winter fallow-early rice-late rice, winter Chinese milk vetch-early rice-late rice, winter oilseed rape-early rice-late rice, winter garlic-early rice-late rice, and winter rotation (interannual rotation of potato, Chinese milk vetch, oilseed rape, and garlic)-early rice-late rice were set up. Under the condition of winter crop straw and rice straw retention, the soil quality indexes in minimum data set were selected and determined using multiple variance analysis, correlation analysis, and principal component analysis combined with the suitability of the soil in the southern double cropping rice field. Lastly, the fuzzy mathematics method was used to evaluate the soil quality in the double cropping rice area. The data indicated that six years of winter planting suitable crops and straw retention in the double cropping rice area could effectively improve the soil quality of paddy field by 10.73%-12.91% compared with the winter fallow treatment, with exception of the garlic treatment. The soil quality of double cropping rice field under different rotation patterns was in the order of winter rotation (planting different crops in different years during winter) (0.726) > planting oilseed rape in winter (0.723) > planting Chinese milk vetch in winter (0.712) > winter fallow (0.643) > planting garlic in winter (0.638). Therefore, the soil quality of double cropping rice can be significantly improved by suitable rotation with winter crops and double straw returning, which provides a solid foundation for the healthy and sustainable development of paddy fields in southern China.
Key words:Double cropping rice field/
Straw double return/
Crop rotation/
Soil quality

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表1稻田不同轮处理的试验设计
Table1.Trial design of different paddy field rotation treatments
轮作模式
Rotation pattern
简写
Abbreviation
说明
Instruction
冬休—早稻—晚稻
Winter fallow-early rice-late rice
WF-R-R(CK) 冬季休耕
Fallow in winter
紫云英—早稻—晚稻
Chinese milk vetch-early rice-late rice
MV-R-R 冬季连作紫云英翻压还田
Continuous growing Chinese milk vetch in winter with its straw returned to the field
油菜—早稻—晚稻
Oilseed rape-early rice-late rice
RP-R-R 冬季连作油菜收籽, 并秸秆还田
Continuous cropping oilseed rape in winter and harvesting oilseeds with its straw returned to the field
大蒜—早稻—晚稻Garlic-early
rice-late rice
GC-R-R 冬季连作大蒜收茎块
Continuous cropping growing garlic in winter and harvesting the bulbs with its straw returned to the fields
马铃薯(轮)—早稻—晚稻
Potato (rotation)-early rice-late rice
PO-R-R 冬季轮作, 即2012—2015年冬季分别种马铃薯(收茎块)、大蒜、油菜和紫云英, 周年冬季之间循环轮作, 之后依次递推, 相应秸秆还田
Winter crops rotation, namely planting potato (harvesting stalks), garlic, oilseed rape and Chinese milk vetch in the winter of each year from 2012 to 2015, respectively, and the corresponding straws of crops returned to the field


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表2不同轮作方式的试验品种及肥料用量
Table2.Trial varieties and fertilizer dosage under various treatments of cropping rotations
处理
Treatment
冬种作物
Winter crop
肥料用量
Amount of fertilizer (kg·hm-2)
作物
Crop
品种
Variety
冬种作物
Winter planting
早、晚稻
Early and late rice
WF-R-R(CK) 休耕
Fallow
0 尿素(N46%) 193.2、过磷酸钙(P2O5 12%) 420、氯化钾(K2O 60%) 202
MV-R-R 紫云英
Chinese milk vetch
余江大叶籽
Yujiang big leaf seed
尿素
Urea (N46%)17.25
RP-R-R 油菜
Oilseed rape
绵丰油18
Mianfeng Oil 18
尿素(N46%) 11.04, 三元复合肥600
Urea (N46%)11.04, compound fertilizer 600
Urea (N46%) 193.2, superphosphate (P2O5 12%)420, potassium chloride (K2O 60%) 202
GC-R-R 大蒜
Garlic
金乡
J inxiang Garlic
尿素(N46%) 124.2, 三元复合肥600
Urea (N46%) 124.2, compound fertilizer 600
PO-R-R 马铃薯、大蒜、油菜和紫云英轮作
Annual rotation of potato, garlic, oilseed rape and Chinese milk vetch
尿素(N46%) 103.52, 三元复合肥600
Urea (N46%) 103.52, compound fertilizer 600
??WF-R-R(CK)、MV-R-R、RP-R-R、GC-R-R和PO-R-R含义见表 1。The meaning of WF-R-R(CK), MV-R-R, RP-R-R, GC-R-R and PO-R-R is shown in the table 1.


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表3不同轮作方式下土壤(指标)因子的测定值
Table3.Values of soil (indexes) factors of various rotation patterns
土壤(指标)因子
Soil (index) factor
轮作方式
Rotation pattern
WF-R-R(CK) MV-R-R RP-R-R GC-R-R PO-R-R
容重
Bulk density (g·cm-3)
1.11±0.15a 0.94±0.11ab 0.92±0.18ab 1.01±0.13ab 0.96±0.08ab
> 0.5 mm团聚体含量
> 0.5 mm aggregates content (%)
16.67±0.29e 20.70±0.20d 21.23±0.40a 21.13±0.15b 20.53±0.25c
< 0.5 mm团聚体含量
< 0.5 mm aggregates content (%)
83.23±0.00a 79.30±0.20bc 78.77±0.26c 78.87±0.62bc 79.47±0.51b
最大持水量
Maximum water holding capacity (%)
53.50±3.38a 56.32±4.20a 55.80±5.26a 54.27±4.62a 55.57±6.52a
含水量
Water content (%)
0.21±0.05a 0.26±0.03a 0.24±0.03a 0.21±0.03a 0.26±0.04a
Simpson
生物多样性指数Simpson biodiversity index
0.62±0.08a 0.57±0.07ab 0.58±0.05ab 0.59±0.07ab 0.56±0.06ab
Pielou生物均匀度指数
Pielou biological uniformity index
0.78±0.12ab 0.78±0.13ab 0.73±0.13ab 0.69±0.09ab 0.82±0.14a
Margalef生物丰富度指数
Margalef biological richness index
0.70±0.15a 0.70±0.13a 0.62±0.09a 0.63±0.08a 0.61±0.07a
pH 6.62±0.22a 6.43±0.11a 6.55±0.15a 6.55±0.05a 6.69±0.06a
有机质含量
Organic matter content (g·kg-1)
41.66±0.98b 47.34±1.68ab 50.15±5.99a 44.96±2.36ab 46.53±3.33ab
全氮含量
Total N content (g·kg-1)
1.16±0.21ab 1.36±0.15a 1.23±0.13ab 1.21±0.12ab 1.35±0.19ab
全磷含量
Total P content (g·kg-1)
0.21±0.03a 0.25±0.05a 0.24±0.04a 0.22±0.04a 0.24±0.05a
碱解氮含量
Alkali-hydrolysis N content (mg·kg-1)
105.00±7.00ab 126.00±4.04ab 133.00±13.51ab 143.15±14.57ab 144.23±14.00a
速效磷含量
Available P content (mg·kg-1)
13.55±1.23b 17.39±0.42a 16.67±2.15a 15.58±1.26a 16.85±3.27a
全钾含量
Total K content (g·kg-1)
0.25±0.04a 0.28±0.06a 0.26±0.04a 0.25±0.03a 0.28±0.06a
速效钾含量
Available K content (mg·kg-1)
71.86±3.47a 78.79±6.00a 64.34±3.49ab 58.56±3.50ab 65.31±5.51ab
微生物生物量碳含量
Microbial biomass C content (mg·kg-1)
314.48±14.11b 427.46±14.44a 426.54±12.62a 389.95±10.53a 419.23±10.12a
微生物生物量氮含量
Microbial biomass N content (mg·kg-1)
96.25±5.12b 141.88±5.62a 148.25±7.96a 121.42±6.42a 149.54±7.54a
转化酶活性
Invertase activity (mg·g-1)
2.03±0.15ab 2.86±0.17a 2.61±0.16a 2.59±0.24a 2.84±0.11ab
脲酶活性
Urease activity (mg·g-1)
0.034±0.005ab 0.052±0.009a 0.042±0.007a 0.038±0.006ab 0.045±0.008a
蔗糖酶活性
Sucrase activity (mg·g-1)
63.21±4.34b 76.46±5.45a 79.25±7.46a 72.23±5.11a 75.24±6.41a
磷酸酶活性
Phosphatase activity (mg·g-1)
1.65±0.12a 1.68±0.10a 1.78±0.20a 1.62±0.14a 1.79±0.13a
细菌数量
Bacterial amount [x105(CFU)·g-1]
90.47±20.00b 101.28±10.20a 96.13±15.12ab 92.63±17.49ab 101.18±4.66a
真菌数量
Fungus amount [x105(CFU)·g-1]
20.24±2.54a 17.52±2.11ab 19.20±1.98ab 19.07±2.52ab 18.42±1.98b
放线菌数量
Actinomycetes amount [x105(CFU)·g-1]
5.43±0.24a 4.28±0.58ab 5.23±0.48a 5.27±0.47a 5.64±0.18a
固氮菌数量
Azotobacter amount [x105(CFU)·g-1]
3.76±0.17ab 3.98±0.24ab 3.91±0.23ab 3.85±0.31ab 4.06±0.43a
??WF-R-R(CK)、MV-R-R、RP-R-R、GC-R-R和PO-R-R含义见表 1。数据为3个重复的平均值; 同行不同小写字母表示不同轮作模式间差异显著(P < 5%)。The meaning of WF-R-R(CK), MV-R-R, RP-R-R, GC-R-R and PO-R-R is shown in the table 1. Data is mean±S.E. of 3 replicates. Different lowercase letters in the same line indicate significant differences among various rotation patterns at P < 5% level.


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表4不同轮作方式下稻田土壤(指标)因子主成分旋转载荷矩阵及各因子得分计算结果
Table4.Calculation results of the principal component load matrix of paddy soil (indexes) factors of different rotation patterns and scores of each (index) factor
土壤(指标)因子
Soil (index) factor
分组
Grouping
主成分旋转载荷矩阵
Matrix of principal component rotation loadings
Norm值
Norm value
调整R2
Adjusted R2
因子得分和Sum
主成分1
PC 1
主成分2
PC 2
主成分3
PC 3
主成分4
PC 4
容重
Bulk density
1 -0.812 -0.363 0.083 0.112 3.763 0.861 4.653
含水量
Water content
1 0.797 0.354 -0.089 -0.234 3.264 0.885 4.327
最大持水量
Maximum water holding
1 0.854 0.231 -0.184 -0.254 3.756 0.825 4.675
有机质含量
Organic matter content
1 0.764 0.451 0.237 0.031 3.875 0.912 4.867
全氮含量
Total N content
1 0.876 0.354 0.218 0.064 3.776 0.814 4.568
全磷含量
Total P content
1 0.759 0.239 0.512 -0.034 3.567 0.754 4.238
碱解氮含量
Alkali-hydrolysis N content
1 0.756 0.426 0.231 -0.046 3.689 0.863 4.356
速效磷含量
Available P content
1 0.654 0.543 0.124 -0.258 3.642 0.914 4.756
全钾含量
Total K content
1 -0.875 -0.384 0.045 0.389 3.684 0.946 4.667
微生物生物量碳含量
Microbial biomass C content
1 0.876 0.216 0.224 -0.134 3.669 0.975 4.668
微生物生物量氮含量
Microbial biomass N content
1 0.842 0.346 0.127 0.063 3.687 0.889 4.675
> 0.5 mm团聚体含量
> 0.5 mm aggregates content
2 0.234 0.763 0.175 0.035 3.246 0.752 3.866
Simpson多样性指数
Simpson biodiversity index
2 0.124 0.642 0.234 0.013 3.867 0.769 3.457
转化酶活性
Invertase activity
2 0.213 0.897 -0.053 -0.087 2.876 0.917 3.876
脲酶活性
Urease activity
2 0.145 -0.647 0.234 0.147 2.476 0.875 3.671
蔗糖酶活性
Sucrase activity
2 0.243 0.763 -0.126 -0.076 3.147 0.874 3.476
磷酸酶活性
Phosphatase activity
2 0.657 0.689 -0.023 -0.116 3.897 0.915 4.868
细菌数量
Bacterial amount
2 0.337 0.856 0.237 -0.128 3.577 0.889 4.459
真菌数量
Fungus amount
2 0.446 0.759 0.016 -0.017 3.447 0.914 4.426
放线菌数量
Actinomycetes amount
2 0.337 0.756 0.129 -0.121 3.764 0.867 4.454
固氮菌数量
Azotobacter amount
2 0.356 0.853 0.234 -0.124 3.876 0.887 3.863
速效钾含量
Available K content
3 0.653 0.346 0.128 -0.314 3.517 0.886 4.661
pH 3 0.003 -0.429 0.214 0.854 1.654 0.813 2.347
Pielou均匀度指数
Pielou biological uniformity index
4 -0.031 0.217 0.086 0.568 3.756 0.723 3.456
Margalef丰富度指数
Margalef biological richness index
4 -0.129 0.128 0.079 0.579 3.891 0.812 3.674
< 0.5 mm团聚体含量
< 0.5 mm aggregates content
4 0.138 -0.561 0.037 0.231 3.411 0.764 3.861
特征值
Eigenvalue
12.336 3.547 2.316 1.023
方差贡献率
Variance explained (%)
59.510 15.336 7.304 4.236
累计贡献率
Cumulative variance explained (%)
59.510 74.846 82.150 86.386


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表5不同轮作方式下土壤最小数据集的统计特征及土壤质量综合评价结果
Table5.Statistical characteristics of the minimum data set and comprehensive evaluation results of soil quality of paddy fields under different rotation patterns
处理
Treatment
容重
OKBulk density (g·cm-3)
pH 有机质含量
Organic matter content (g·kg-1)
微生物量氮含量
Microbial biomass N (mg·kg-1)
碱解氮含量
Alkali- hydrolysis N content (mg·kg-1)
速效钾含量
Available K content (mg·kg-1)
磷酸酶活性
Phosphatase activity (mg·g-1)
细菌数量
Bacterial amount [105(CFU)·g -1]
> 0.5 mm团聚体含量
> 0.5 mm aggregates content (%)
土壤质量值
Value of soil quality
WF-R-R(CK) 1.11±0.15a 6.62±0.22a 41.66±0.98a 96.25±5.12a 105.00±7.00b 71.86±3.47a 1.65±0.12a 90.47±20.00a 16.67±0.29e 0.643
MV-R-R 0.94±0.11ab 6.43±0.11a 47.34±1.68ab 141.88±5.62b 126.00±4.04ab 78.79±6.00a 1.68±0.10a 101.28±10.20b 20.70±0.20d 0.712
RP-R-R 0.92±0.18ab 6.55±0.15a 50.55±5.99b 148.25±7.96b 133.00±13.51ab 64.34±3.49ab 1.78±0.20a 96.13±15.12ab 21.23±0.40a 0.723
GC-R-R 1.03±0.13ab 6.55±0.05a 44.96±2.36ab 111.42±6.42ab 143.15±14.57ab 58.56±3.50ab 1.62±0.14a 92.63±17.49ab 21.13±0.15b 0.638
PO-R-R 0.96±0.08ab 6.69±0.06a 46.53±3.33ab 149.54±7.54b 144.23±14.00ab 65.31±5.51ab 1.79±0.13ab 101.18±4.66b 20.53±0.25c 0.726
??WF-R-R(CK)、MV-R-R、RP-R-R、GC-R-R和PO-R-R含义见表 1。数据为3个重复的平均值±标准误; 同列不同小写字母表示不同轮作方式间差异显著(P < 0.05)。The meaning of WF-R-R(CK), MV-R-R, RP-R-R, GC-R-R and PO-R-R is shown in the table 1. Data is mean±S.E. of 3 replicates. Different lowercase letters in the same column indicate significant differences among different rotation patterns at P < 0.05 level.


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