• ISSN 1008-505X
  • CN 11-3996/S

扬州市耕地土壤pH值30年演变及其驱动因子

pH variation and the driving factors of farmlands in Yangzhou for 30 years

  • 摘要: 目的土壤pH值是衡量耕地质量的重要指标,开展江苏省扬州市30年来种植制度、耕作制度、施肥、降雨等对耕地土壤酸化影响的研究,为预测和控制土壤酸化提供科学依据。方法调查了1984年、1994年、2005年、2014年四个时期耕地土壤pH、成土母质、土壤类型、土壤有机质含量,以及各时期的耕作制度、种植制度、降雨量和施用化肥品种和数量。数据来源于1984年第二次土壤普查的农化样点(4107个)、1994年的土壤普查点(2862个)、2005年土壤养分调查点(4018个)、2014年土壤养分调查点(6009个),共16996个。参照《中国土壤》对我国土壤酸碱度分级指标将扬州市耕地土壤pH分为5级,分别为Ⅰ级( 7.5)、Ⅱ级(6.5~7.5)、Ⅲ级(5.5~6.5)、Ⅳ级(4.5~5.5)、Ⅴ级( 4.5)。应用地统计学中克里格法(Kriging)和相关的统计学方法,用ArcGIS10.1、SPSS19等软件进行了数据统计分析。结果扬州市1984年、1994年、2005年、2014年土壤pH平均分别为7.51(4107个)、7.07(2862个)、6.83(4018个)、6.74(6009个);1984~2014年四个时期土壤pH空间分布格局基本不变,即里下河地区 沿江圩区 通南高沙土区 丘陵地区。1984、1994年和2005年,土壤pH以Ⅰ级、Ⅱ级为主,1984年占总面积的90%以上,1994年和2005年占总面积的75%以上;2014年土壤pH空间分布以Ⅱ级、Ⅲ级水平为主,占总面积的65.7%。30年间,土壤pH值下降0~1个单位的面积占总面积的47.2%,下降大于1个单位的面积占总面积的39.3%。前20年土壤pH值下降严重,下降了0~2个单位的面积占80%以上。30年间不同成土母质、土壤类型的整体土壤pH值呈下降趋势,分别下降0.9、0.8个单位;土壤有机质含量的变化与土壤pH变化呈负相关关系,30年间土壤有机质含量平均上升了6.01 g/kg,是土壤pH整体呈下降趋势的原因之一;30年间扬州市降水pH值整体呈下降趋势,其中丘陵、沿江地区下降最快,与丘陵、沿江地区土壤pH下降较快是一致的;30年间化肥投入量与土壤pH变化呈高度的负相关,2005年化肥投入量约505300吨,比1984年化肥投入量增加了2.42倍;2005~2014年化肥投入量呈稳定趋势,与30年土壤pH变化趋势是一致的;种植大棚蔬菜的田块土壤pH平均值比周边种植稻麦田块下降1.5~2个单位,表明土地利用类型改变也会影响土壤pH值。结论扬州市耕地土壤pH值30年间持续下降,前20年下降幅度较大,后10年渐趋稳定。影响土壤pH值空间分布因子主要有成土母质、土壤类型、土壤有机质含量;影响土壤pH时间分布因子主要有酸雨、施肥及土地利用类型,其中酸雨、施肥是导致土壤酸化的主要驱动因子。

     

    Abstract: Objectives Soil pH is an important index to measure quality of cultivated lands. The influence of cropping system, cultivation system, rainfall and fertilization practices on soil acidification over the last 30 years was investigated.Methods This study investigated soil pH, soil parent material, soil type, soil organic matter content in 1984, 1994, 2005 and 2014, and the cultivation system, cropping system, rainfall, types of fertilizer application and their inputs in these years. The data came from 16996 sampling points in Yangzhou City, including 4107 agricultural chemical soil samples of the second general soil survey in 1984, 2862 general soil survey points in 1994, 4018 soil nutrients survey points in 2005, and 6009 soil nutrients survey points in 2014. Referencing to Chinese Soils, we classified the soil pH into five grades:Ⅰ ( 7.5), Ⅱ (6.5-7.5), Ⅲ (5.5-6.5), Ⅳ (4.5-5.5), and Ⅴ ( 4.5). The method of Kriging and relevant statistical methods in geostatistics were used in this study, and ArcGIS 10.1 and SPSS19 were used as tools for analyzing data.Results The results showed that the average soil pH was 7.51, 7.07, 6.83 and 6.74 respectively in 1984, 1994, 2005 and 2014. The spatial distribution of pH in the four periods was relatively constant, i.e. Lixiahe area Yangtze River diked area Sandy soil area in Tongnan Hilly region. In 1984, 1994 and 2005,the soil pH mainly belonged to Grade I and Ⅱ, which accounted for more than 90% of total area in 1984 and decreased to 75% in 1994 and 2005; in 2004, the soil pH mainly belonged to Grade Ⅱ and Ⅲ, which accounted for 65.7% of total area. In 30 years, soil pH was significantly decreased, 47.2% areas decreased by 0-1 unit and 39.3% areas decreased by more than 1 unit. In the first 20 years, soil pH was obviously declined and over 80% area soil pH declined by 0-2 units. The overall soil pH of different soil parent materials and soil varieties decreased by 0.9 unit and 0.8 unit, respectively. There was a negative correlation between changes of soil organic and pH. The average content of soil organic matter was increased by 6.01g/kg, it was one of the reasons for the decrease of soil pH as a whole. The pH value of the rainfall in this city decreased, especially rapid for the hills and areas alongside the river. This was consistent with the view of rapid decline of soil pH in hills and areas alongside rivers. The input of chemical fertilizer was negatively correlated with the change of soil pH. In 2005, the input of chemical fertilizer was about 505300 tons, increased by 2.42 times comparing with the input in 1984. From 2005 to 2014, the input of chemical fertilizer showed a steady trend, which was consistent with the trend of soil pH in these 30 years. The average soil pH in vegetable protected house was lower than that in the surrounding wheat field by 1.5-2 units, which indicated that the types of land use also affected soil pH. In general, the influencing factors were land use types and soil parent materials, and the factors of influencing temporal distribution of pH were fertilization and acid rain. Both acid rain and fertilization were the important driving factors of soil acidification.Conclusions The arable land soil pH in the study area showed an acidification tendency during 1984-2014. The spatial distribution of soil pH in the study area was mainly influenced by the parent materials of soil, soil types, content of soil organic matter, and the temporal distribution of soil pH in the study area was influenced by acid rain, fertilization and land use type. Acid rain and fertilization were the main factors causing soil acidification.

     

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