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西藏设施葡萄土壤酸化、盐渍化和养分特征 被引量:12

Soil acidification,salinization and nutrient characteristics in greenhouse vineyards in Tibet
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摘要 【目的】调查西藏不同地区设施葡萄土壤施肥方法,研究土壤酸化、盐渍化和养分现状并探索其原因,为西藏设施葡萄合理施肥和土壤可持续利用提供科学依据。【方法】以西藏主要设施葡萄产区典型温室土壤为研究对象,以室外裸地土壤为对照,研究了不同地区、不同种植年限下土壤理化性质现状。拉萨地区为种植4 a(年)(LS4)、14 a(LS14)土壤和裸地土壤(LSB),林芝地区为种植9 a土壤(LZ9)和裸地土壤(LZB),山南地区为种植3 a土壤(SN3)和裸地土壤(SNB)。【结果】(1)各地区设施土壤p H均显著低于裸地,其中LZ9(4.48)和LS14(4.58)酸化严重,过量的尿素和磷酸二铵的输入是其主要原因。(2)SN3、LZ9和LS4属于低盐度等级,LS14属于超高盐度等级,次生盐化问题严重。大量羊粪和钾肥的投入是导致LS14盐渍化的直接原因,而过量的尿素与羊粪配施也是土壤盐渍化的潜在重要因素。(3)LS14,LZ9和SN3土壤养分含量远远超出速效养分的极高供应水平,肥料投入过量问题严重。【结论】西藏地区设施葡萄土壤面临着酸化和盐渍化威胁,其酸化的主要原因是由于过量氮肥、磷酸二铵和硫酸钾的输入,而大量的羊粪和钾肥的施用是LS14盐渍化严重的直接原因。因此根据西藏不同地区设施葡萄土壤现状,测土按需施肥,优化管理措施,建立合理高效设施栽培技术标准十分必要。 【Objective】Grape is one of the largest fruit trees in facility cultivation, which develops fast in China. The planting area of facility agriculture is increasing in Tibet. However, the relatively closed micro-ecological environment and the concept held by farmers that high yield depends on high input of fertilizer have created many problems in facility cultivation of grape and the problems are becoming more severe with years. Investigation of soil acidification, salinization and nutrients characteristic in grape greenhouses in different areas of Tibet provides guidance for reasonable fertilization and sustainable utilization of soil.【Methods】The p H, electrical conductivity(EC) and nutrients in greenhouse vineyard soils in different regions were studied using the outdoor bare land soil as the controls. Lhasa's soils were sampled from the greenhouses planted with grape for 4(LS4) and 14 years(LS14) and from bare land(LSB). Nyingchi's soils were sampled from the greenhouses planted with grape for 9 years(LZ9)and from bare land(LZB). Shannan's soils were sampled from the greenhouses planted with grape for3 years(SN3) and from bare land(SNB).【Results】(1) The 0-60 cm soils of the outdoor bare land in all the areas were neutral to alkaline(p H between 7.0 and 8.0), while p H values in the 0-60 cm soil in LS14, LS4 and LZ9 were below 7.0. The p H values of the surface(0-20 cm) soils of LS14 and LZ9 were 4.48 and 4.58, respectively, which were 40.44% and 41.21% lower(p<0.05) than that of LSB and LZB, respectively. In addition, p H values of the 0-40 cm soil in LS14, LS4 and LZ9 ranged from 4.87 to 5.18, which were significantly lower(p<0.05) than that of the bare soil at 20-40 cm. In general,there were serious soil acidification problems in the grape greenhouse soils in Lhasa and Nyingchi, and the Shannan is facing severe acidification risk. Excessive urea and diammonium phosphate input was the main cause for soils acidification.(2) The EC of the soil(0-60 cm) in the grape greenhouses was significantly higher(p<0.05) than that of the bare soils and showed a decreasing trend with soil depth.The soil EC in LS14 was 0.75-2.48 m S · cm-1, which was significantly higher than in LSB by 15-31 times(p<0.05). The EC in the surface soil of LS4 was 0.48 m S · cm-1, which was significantly higher than that of the LSB(p<0.05). The soil EC of LZ9 and SN3 was less than 0.5 m S · cm-1 but still significantly higher than that of LZB and SNB. SN3, LZ9 and LS4 were mildly salinized and LS14 had high salinity. Large amount of potassium fertilizer and sheep manure application might have directly resulted in the salinization in LS14 soil. The combination of large amounts of urea and sheep manure might have exacerbated salinization.(3) The soil organic carbon, total nitrogen and total phosphorus in Lhasa increased with the increase in planting years, and the organic carbon content in LS14 was 50.10 g · kg-1,which was 2.4 times higher than that in LSB(p<0.05). Total nitrogen in LS14 was 3.0 times higher than in LSB(p<0.05), and total phosphorus was 3.4 times higher(p<0.05). Soil organic carbon content and total nitrogen content in LZ9 were not significantly different from those in LZB(p<0.05),while total phosphorus and total potassium content were significantly higher than in LZB(p<0.05).The organic carbon content in SN3 was 3.1 times higher than that in the control and was as high as67.32 g · kg-1(p<0.05). The contents of soil organic carbon, total nitrogen and total phosphorus in SN3 soil were significantly higher than those in SNB(p<0.05), but there was no significant difference in total potassium content between SN3 and SNB.(4) The available soil nutrients in different areas showed different characteristics. The available nitrogen, phosphorus, and potassium contents of the greenhouse soils were significantly higher than those of the bare land(p<0.05), with the exception that the available nitrogen content in LS4 was significantly lower than in LSB(p<0.05). The available nitrogen,phosphorus and potassium in LS14 reached the highest level among all the treatments and were 1.26,13.16, and 11.71 times higher than in LSB, respectively.【Conclusion】(1) The soils in the grape greenhouses in Tibet are threatened by acidification and salinization. The p H in the greenhouse soils ranges from 4.49 to 6.71. Soils in LS14, LZ9 and LS4 are acidic, while that in SN3 is neutral. The main reason is the excessive use of urea and diammonium phosphate.(2) SN3, LZ9 and LS4 have low salinity levels, which may cause slight obstacle to crop growth, while LS14 is highly salinized and ad adverse to crop growth. The excessive use of potassium fertilizer and large amount sheep manure input might be one of the main factors to cause soil salinization in LS14.(3) The nutrient contents of the soils in the grape greenhouses have far exceeded the high level of the quick-acting nutrients. Excessive inputs of fertilizers have undoubtedly reduced the efficiency of nutrient utilization and increased production costs. Therefore, establishing reasonable and efficient fertilization methods based on the current status of the soil is extremely urgent.
作者 王朔 李帅霖 曾秀丽 代安国 张姗姗 张凯 路贵龙 李元会 WANG Shuo;LI Shuailin;ZENG Xiuli;DAI Anguo;ZHANG Shanshan;ZHANG Kai;LU Guilong;LI Yuanhui(Institute of Vegetables,Tibet Academy of Agricultural and Animal Husbandry Sciences.The Ministry of Agriculture of Qinghai-tibet Plateau Fruit Trees Scientific Observation Test Station,Lhasa 850032,Tibet,Chin;State Key Laboratory of Soil Erosion and Dryland Farming on the Loess Plateau,Institute of Soil and Water Conservation,Chinese Academy of Sciences and Ministry of Water Resources,Yangling 712100,Shaanxi,China;University of Chinese Academy of Sciences,Beijing 100049,Chin)
出处 《果树学报》 CAS CSCD 北大核心 2018年第8期957-966,共10页 Journal of Fruit Science
基金 西藏自治区科技厅自然科学基金(2016ZR-NK-07) 西藏自治区科技厅重点研发及转化类项目(藏科发[2017]72号)
关键词 设施葡萄 土壤 施肥量 西藏 酸化 盐渍化 土壤养分 Greenhouse vineyard Soil Fertilization Tibet Acidification Salinization Soil nutrients
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