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中國水稻土酸化時空變化特征及其對氮素盈余的響應(yīng)
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國家重點研發(fā)計劃項目(2016YFD0200300)、國家綠肥產(chǎn)業(yè)技術(shù)體系項目(CARS-22-G-14),、中國科學院重點部署項目(KFZD-SW-112)和農(nóng)業(yè)農(nóng)村部委托項目(南方紅壤中低產(chǎn)田改良培肥技術(shù)模式集成)


Spatio-temporal Variation of Paddy Soil Acidification and Its Response to Nitrogen Surplus in China
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    摘要:

    針對水稻土酸化造成作物減產(chǎn)和嚴重污染環(huán)境的問題,,收集了1979—1985年全國第二次土壤普查成果和2015—2017年水稻土質(zhì)量等級調(diào)查成果,結(jié)合2005—2015年全國測土配方施肥數(shù)據(jù),,采用空間分析和統(tǒng)計分析方法,,分析了1979—2017年,39年間中國水稻土pH值空間分布的變化,;計算了39年間不同水稻土pH值分級和區(qū)域的水稻土酸化速率,,探討了39年間氮肥投入變化量和土壤理化性質(zhì)與水稻土酸化速率的關(guān)系;估算了2015—2017年水稻土單位面積氮素盈余量,,并進一步量化了氮素盈余量與水稻土pH值變化量的關(guān)系,。結(jié)果表明:39年間水稻土受土壤酸脅迫程度加劇,,特別是水稻土由酸性(pH值為5.5~6.5)轉(zhuǎn)變成強酸性(pH值小于等于5.5)的面積比例增加,,這主要集中在長江中下游中部、南部和華南區(qū)中部,、南部,。39年間水稻土平均pH值下降了0.26,其中,,東北區(qū),、長江中下游區(qū),、華南區(qū)平均pH值分別下降了0.34、0.29和0.58,,西南區(qū)平均上升了0.14,。39年間水稻土酸化速率從大到小依次為堿性水稻土、中性水稻土,、酸性水稻土,、強酸性水稻土,區(qū)域上水稻土酸化速率從大到小依次為東北區(qū),、華南區(qū),、長江中下游區(qū)、西南區(qū),。39年間,,氮肥投入量和土壤容重變化量與水稻土酸化速率存在極顯著的正相關(guān)關(guān)系,有機質(zhì)含量和耕層厚度變化量與水稻土酸化速率存在極顯著的負相關(guān)關(guān)系,。2015—2017年,,氮素盈余量與水稻土pH值變化量呈顯著的負相關(guān)關(guān)系,氮素盈余量增加會造成水稻土酸化加劇,。劃定了3類水稻土治理分區(qū),,提出“治酸、防酸,、控酸”的總體策略,,并分區(qū)域制定了治理措施,可為水稻土酸化阻控和地力提升提供參考,。

    Abstract:

    Paddy soil is the most important arable land resource in China, the acidification of paddy soil not only reduced the crop yields but also increased the risk of environmental risk. Data from the second national soil survey (1979—1985, the first period) and from the paddy soil quality grading survey (2015—2017, the second period) were collected, and were combined with the national soil testing and formula fertilization data from 2005 to 2015. The spatial analysis and the statistical analysis methods were used to analyze the spatio-temporal variation of paddy soil acidification. During the two periods, the spatial layout dynamic changes of paddy soil pH value and the acidification rate of paddy soil with different pH value levels and regions were analyzed, the correlations between nitrogen input, soil physical and chemical properties and acidification rate of paddy soil were discussed. Besides, the correlation between the nitrogen fertilizer surplus amount from 2015 to 2017 and the change of the paddy soil pH value from 2015 to 2017 was further quantified. The results showed that the intensity of soil acid stress on rice in China was increased during the two periods, especially the increase of area from the acid paddy soils (pH value was 5.5~6.5) to the strongly acid paddy soils (pH value was no more than 5.5), mainly distributed in the middle and southern parts of MLYR (middle and lower Yangtze River), and the central and southern parts of SC (Southwest China). From 1979 to 1985, the average pH value of paddy soil was 6.03, and it was dropped by 0.26 in the year from 2015 to 2017. Among them, the NC (Northeast China), the MLYR (middle and lower Yangtze River) and the SC (Southern China) were dropped by 0.34, 0.29 and 0.58 respectively, while the SW (Southwest China) was increased by 0.14. The acidification rate of the paddy soil survey sites during the two periods from high to low was as follows: alkaline paddy soil, neutral paddy soil, acid paddy soil, strongly acid paddy soil. Regionally, the acidification rate of the paddy soil survey sites during the two periods from high to low was as follows: NC, SC, MLYR, and SW. During the two periods, the paddy soil acidification rate was significantly positively correlated with the change of nitrogen input amount and soil bulk density, but was significantly negatively correlated with the change of paddy soil organic matter content and the plough layer thickness. From 2015 to 2017, there was a significant negative correlation between the nitrogen surplus amount and the change of the paddy soil pH value, such that the nitrogen surplus amount was increased with the decrease of paddy soil pH value. Therefore, the paddy soil remediation zones should apply the balanced fertilization with soil testing formula, control amount of nitrogen fertilizer, and promote environmental-friendly organic manure to replace chemical nitrogen fertilizer. Besides, in the remediation zone mainly with alkaline and neutral paddy soils, the technology of straw chopping and return to the paddy field with rotary tillage or moldboard tillage could be applied to decrease the paddy soil acidification rate. In the remediation zone mainly with acid paddy soils, the technology of straw returning could be applied to maintain the paddy soil pH value. In the remediation zone mainly with strongly acid paddy soils, the agricultural calcareous material could be used to raise the paddy soil pH value.

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葉英聰,孫波,劉紹貴,李文西,楊帆.中國水稻土酸化時空變化特征及其對氮素盈余的響應(yīng)[J].農(nóng)業(yè)機械學報,2021,52(2):246-256. YE Yingcong, SUN Bo, LIU Shaogui, LI Wenxi, YANG Fan. Spatio-temporal Variation of Paddy Soil Acidification and Its Response to Nitrogen Surplus in China[J]. Transactions of the Chinese Society for Agricultural Machinery,2021,52(2):246-256.

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  • 收稿日期:2020-09-21
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  • 在線發(fā)布日期: 2021-02-10
  • 出版日期: 2021-02-10
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