1. 湖南农业大学资源环境学院,长沙,410128
2. 中国农业科学院农业资源与农业区划研究所, 耕地培育技术国家工程实验室,北京,100081
3. 农业农村部耕地质量监测保护中心,北京,100125
4. 江西省红壤研究所, 国家红壤改良工程技术研究中心, 江西 进贤,331717
[ "李冬初(1979-),男,副研究员,主要从事土壤改良与培育研究。E-mail:lidongchu@caas.cn" ]
纸质出版:2020
移动端阅览
李冬初, 黄晶, 马常宝, 等. 中国农耕区土壤有机质含量及其与酸碱度和容重关系[J]. 水土保持学报, 2020,34(6):252-258.
LI Dongchu, HUANG Jing, MA Changbao, et al. Soil Organic Matter Content and Its Relationship with pH and Bulk Density in Agricultural Areas of China[J]. 2020, 34(6): 252-258.
李冬初, 黄晶, 马常宝, 等. 中国农耕区土壤有机质含量及其与酸碱度和容重关系[J]. 水土保持学报, 2020,34(6):252-258. DOI: 10.13870/j.cnki.stbcxb.2020.06.035.
LI Dongchu, HUANG Jing, MA Changbao, et al. Soil Organic Matter Content and Its Relationship with pH and Bulk Density in Agricultural Areas of China[J]. 2020, 34(6): 252-258. DOI: 10.13870/j.cnki.stbcxb.2020.06.035.
对我国农耕区土壤有机质区域变化及其与酸碱度和容重关系进行系统分析,为耕地地力提升和改善土壤结构提供支撑。基于国家级耕地长期定位监测点913个,统计分析全国及7大区域(东北NE、华北NC、西北NW、长江中游MYR、长三角YRD、华南SC、西南SW)耕层土壤有机质含量、酸碱度及容重变化特征。结果表明,全国农耕区耕层土壤有机质含量平均值为22.4~24.8 g/kg。其中有机质含量中等偏低的监测点位占比达72.5%。不同区域耕层土壤有机质含量差异显著(p<0.05),MYR耕层土壤有机质含量显著高于其他6个区域。全国农耕区耕层土壤pH和容重平均分别为(6.90±1.20),(1.30±0.15) g/cm3。不同土壤利用方式对土壤有机质、酸碱度及容重产生影响。水田耕层土壤有机质含量显著高于旱地,旱地耕层土壤pH和容重则显著高于水田。亚当斯方程和指数函数分别推荐拟合土壤容重对有机质含量响应关系(R2=0.09,RMSE=0.17,n=759),以及土壤pH对土壤有机质含量响应(R2=0.16,RMSE=1.24,n=886)。全国农耕区耕层土壤有机质含量总体中等偏低,呈现出东南向西北依次降低趋势。土壤pH及容重与土壤有机质呈现显著的负相关关系。亚当斯模型及指数方程能较好地拟合土壤容重及pH对有机质的响应关系,可用于非线性插值法补充土壤容重及pH缺失值。
Analysis of the regional changes of soil organic matter (SOM) and its relationship with pH and bulk density (BD) in agricultural areas of China were conducted. That would provide support for improvement of cultivated land fertility and soil structure. The characteristic of SOM changes were analyzed based on 913 national long-term monitoring sites which were carried out in 7 regions (Northeast
NE; North China
NC; Northwest
NW; Middle of Yangtze River
MYR; Yangtze River Delta
YRD; South China
SC; and Southwest
SW). Soil pH and bulk density were also evaluated. The results showed that the averaged SOM content in the agricultural cultivation areas were between 22.4 and 24.8 g/kg.
and 72.5% of total monitoring sites were with SOM content grade <30.0 g/kg (grade 3~6). There were significantly difference of SOM content in soil cultivated layer among regions (p<0.05). Soil organic matter content in MYR was significantly higher than that in other regions. Soil pH and BD in the agricultural cultivation areas were (6.90±1.20)
and (1.30±0.15) g/cm3. Soil utilization patterns affected SOM content
pH
and BD. The SOM content in paddy fields were significantly higher than that in upland. The pH and BD in upland were significantly higher than that in paddy fields. The Adams equation and exponential equation were recommended to fit response relationship between BD and SOM (R2=0.09
RMSE=0.17
n=759)
pH and SOM (R2=0.16
RMSE=1.24
n=886).The SOM content was generally low in plowed layer in the agricultural areas
and that showing a decreasing trend from southeast to northwest of China. Soil pH and BD showed significant negative correlation with SOM. The Adams and exponential equation could well fit the responses relationship between soil BD and pH to SOM
and that could be used for nonlinear interpolation to supplement BD and pH missing values.
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