Scientia Agricultura Sinica ›› 2017, Vol. 50 ›› Issue (2): 310-319.doi: 10.3864/j.issn.0578-1752.2017.02.010

• SOIL & FERTILIZER·WATER-SAVING IRRIGATION·AGROECOLOGY & ENVIRONMENT • Previous Articles     Next Articles

Effect of Residual Plastic Film on Soil Nutrient Contents and Microbial Characteristics in the Farmland

ZHANG Dan1, LIU HongBin1, MA ZhongMing2, TANG WenXue3, WEI Tao3, YANG HuDe3, LI JunGai1, WANG HongYuan2   

  1. 1Institute of Agricultural Resources and Regional Planning, Chinese Academy of Agricultural Sciences/Ministry of Agriculture Key Laboratory of Nonpoint Source Pollution Control, Beijing 100081; 2Gansu Academy of Agricultural Sciences, Lanzhou 730070; 3Institute of Soil, Fertilizer and Water-saving Agriculture, Gansu Academy of Agricultural Sciences, Lanzhou 730070
  • Received:2016-07-13 Online:2017-01-16 Published:2017-01-16

Abstract: 【Objective】 The purpose of this study was to explore the effect of residual plastic film on soil fertility and soil microbial characteristics, clarify the risk threshold of residual plastic film in the field and promote effective control and management of residual plastic film pollution in China.【Method】Five residual plastic film gradients were designed in representative farmlands in Zhangye county of Gansu province from 2011 to 2015, including 0 (CK), 150 kg·hm-2 (T1), 300 kg·hm-2 (T2), 450 kg·hm-2 (T3) and 600 kg·hm-2 (T4). After crop harvesting in 2015, soil physical and chemical properties, microbial biomass carbon and nitrogen, enzyme activity and microbial abundance were monitored.ResultThe amount of residual plastic film had a great effect on soil water content, organic matter (SOM), total nitrogen (TN), ammonium (NH4+-N), nitrate nitrogen(NO3--N) and available phosphorus (Olsen-P), in which the soil water content was significantly increased with increasing residual plastic film in field, however the SOM, TN, NO3--N and Olsen-P were declined, the NH4+-N was increased and then decreased with the increase of residual plastic film. In the lower residual plastic film treatment, the soil microbial biomass carbon (MBC) and microbial biomass nitrogen (MBN) were improved because of soil water content increased compared with CK, however, they were significantly reduced in the high residual plastic film treatments (T3 and T4) (P<0.05). In addition, the soil microbial community abundance (AWCD, richness, Shannon, Simpson and McIntosh) of CK and T1 were significantly higher than that of T3 and T4 (P<0.05). The variation trend between soil enzyme activity and residual plastic film was similar to MBC and MBN, and the activities of α-1,4-glucosidase (AG), β-1,4-glucosidase (BG), Cellobiohydrolase (CBH), β-1,4-xylosidase (BXYL) and β-1,4-N-acetyl-glucosaminidase (NAG) were high in the treatments of 300-450 kg·hm-2 of residual plastic film, however, they were significantly decreased when the residual in the treatment with plastic film at 600 kg·hm-2.【Conclusion】In the treatment with lower residual plastic film, the soil microbial activity was improved though increasing soil water content, whereas the soil microbial biomass carbon, microbial biomass nitrogen, microbial community abundance and soil enzyme activity were significantly decreased if the residual plastic film higher than 450 kg·hm-2. Moreover, the soil organic matter, total nitrogen, ammonium nitrogen, nitrate nitrogen and Olsen-P all reduced with long-term effect of high residual plastic film, and caused soil fertility degradation. It was concluded that management of the residual plastic film should be strengthened in order to reduce the risk of soil degradation, especially in the regions with serious residual plastic film pollution.

Key words: residual plastic film, soil fertility, microbial biomass, microbial abundance, enzyme activity

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