文章摘要
王学霞,宋宁宁,薛颖昊,王甲辰,梁丽娜,李梦佳,刘淑丽,刘东生.山东省花生种植区耕层土壤残膜赋存特征[J].农业环境科学学报,2021,40(8):1729-1737.
山东省花生种植区耕层土壤残膜赋存特征
Occurrence characteristics of residual film in cultivated soil of peanut planting area in Shandong Province, China
投稿时间:2021-01-15  
DOI:10.11654/jaes.2021-0059
中文关键词: 土壤残膜  残膜含量  残片数  覆膜年限  残膜回收
英文关键词: soil residual film  residual film amounts  residual film quantity  film mulching years  recovery of plastic film
基金项目:农业农村部农业生态环境保护专项(13200214);北京市农林科学院院创新能力建设项目(KJCX20200419);北京市农林科学院改革与发展计划项目(YZS202001)
作者单位E-mail
王学霞 北京市农林科学院植物营养与资源研究所, 北京 100097  
宋宁宁 青岛农业大学资源与环境学院, 山东 青岛 266109  
薛颖昊 农业农村部农业生态与资源保护总站, 北京 100125  
王甲辰 北京市农林科学院植物营养与资源研究所, 北京 100097  
梁丽娜 北京市农林科学院植物营养与资源研究所, 北京 100097  
李梦佳 青岛农业大学资源与环境学院, 山东 青岛 266109  
刘淑丽 禹城市农业农村局, 山东 禹城 251200  
刘东生 北京市农林科学院植物营养与资源研究所, 北京 100097 LLSLDS@163.com 
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中文摘要:
      通过对山东省花生典型种植区耕层土壤地膜残留量分布特征及影响因素的调查研究,准确评估花生种植农田系统地膜残留污染现状,为该地区农田地膜污染防控措施的提出提供科学依据。选择覆膜年限为1~15 a的18个农田为研究对象,调查土壤质地、地膜使用情况等指标,同时分析不同耕层土壤中地膜残留量和残片数量。结果表明,覆膜1~15 a的4个典型花生种植区耕层(0~30 cm)土壤残膜量在2.48~46.01 kg·hm-2,不同区域间差异不明显,均低于我国农田残留量限值。随着覆膜年限的增加,耕层土壤中残膜的含量和数量均呈逐年上升趋势。残膜含量和残片数量随土壤深度增加而逐渐降低,分布在0~10 cm土层内的残膜显著高于10~20 cm和20~30 cm土层,随着覆膜年限增加,残膜呈现向深层土壤下移的趋势。>25、4~25 cm2和<4 cm2残片数均随土壤深度的增加而降低。随覆膜年限增加,耕层(0~30 cm)土壤中小面积残膜数量和比例不断提高,且在20~30 cm深层土壤<4 cm2的小残片呈明显增多趋势,加大了长期覆膜农田的残膜回收难度,可能对耕层土壤环境造成长期影响。因此,采取适当措施增加地膜回收,以减少该地区地膜污染,对保护该地区花生产地健康有积极作用。
英文摘要:
      The distribution characteristics and influencing factors of residual film amounts were investigated to accurately evaluate regional plastic film pollution in the peanut cultivated farmland system of Shandong Province, which can provide a scientific basis for preventing and reducing of farmland plastic film pollution in this area. The soil texture, use of plastic film, and other indicators were investigated in 18 farmland samples with 1~15 years of film mulching. The amount and quantity of residual film in different soil layers were analyzed. Results showed that the amount of residual film was 2.48~46.01 kg·hm-2 in the soil layers(0~30 cm) of four typical peanut planting areas in Shandong Province, lower than the limit of residual film in China. The difference was not as evident among different areas. The quantities of residual film increased with the increase of film mulching years. The residual films were mainly found in the 0~10 cm soil layer, significantly higher than that in the 10~20 cm and 20~30 cm soil layers. The amount of residual film significantly decreased with the increase in depth; the residual film tended to move into deep soil with the increase in film mulching years. The film quantity residuals >25 cm2, 4~25 cm2, and <4 cm2 significantly decreased with soil depth. The quantity and ratio of small residuals increased with the increase in mulching years; in particular, the film residuals <4 cm2 increased in the 20~30 cm soil layer, making it difficult to recover film residue in long-term mulched farmland; this may have long-term effects on the soil environment. Therefore, mitigation measures should be taken to increase the recovery of plastic film to reduce plastic film pollution, which can play a positive role in protecting the health of peanut production in this region.
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