长期秸秆还田对德阳地区稻田土壤镉赋存形态的影响

Effects of long-term straw incorporation on cadmium speciation and bioavailability in paddy soils in Deyang Area

  • 摘要: 明确长期秸秆还田对稻田土壤Cd污染阻控或促进效应, 有利于制定针对性的农田Cd污染治理措施, 对保障粮食安全生产具有重要意义。以四川省德阳市旌阳区Cd污染稻田为研究对象, 通过田间实地调查与采样分析, 探讨了秸秆还田不同年限(0 a、1 a、4 a、8 a)对农田土壤Cd赋存形态及其生物有效性的影响。结果表明, 研究区稻田土壤Cd形态含量分布为: 残渣态>铁锰氧化物结合态>有机结合态>碳酸盐结合态>可交换态; 秸秆还田(4 a以上)显著增加了土壤有机质含量, 进而促进了稻田耕作层(0~20 cm)土壤有机结合态Cd含量水平显著上升(以秸秆还田4 a, 其含量增加了45%为最高), 对土壤可交换态Cd含量略有增加效应; 土壤pH则随秸秆还田年限的延长呈先升高后缓慢下降趋势, 主要影响土壤碳酸盐结合态Cd含量水平的变化。从土壤Cd形态的生物利用性角度评价, 随秸秆还田年限延长(1~4 a), 能减轻稻田耕作层(0~20 cm)土壤有效态Cd的分配, 促进其向潜在态Cd转移; 而对犁底层(20~40 cm)土壤Cd形态的生物有效利用性的影响未达显著水平。总体来看, 秸秆还田(1~4 a)提高了土壤有机质含量, 显著增加了耕作层(0~20 cm)土壤有机结合态Cd含量水平, 促进了耕作层(0~20 cm)稻田土壤Cd由有效态向潜在态转化, 降低稻田土壤Cd污染状况; 持续长期的秸秆还田(连续秸秆还田8 a以上), 则可能因土壤pH下降而促进土壤Cd由潜在态向有效态转化, 增加稻田土壤Cd的生物吸收累积效率。

     

    Abstract: Long-term incorporation of crop straw into soil affects soil heavy metal speciation and bioavailability. In order to develop feasible control measures of cadmium pollution of the soil and food production, the effects of long-term incorporation of crop straw into soil on the enhancement or inhibition of cadmium contamination of paddy soils was investigated. The cadmium contaminated paddy soil was from Jinyang District, Deyang City, Sichuan Province. Field-investigated and field-sampled data were analyzed to determine the characteristics of cadmium fractions in straw-incorporated (returned rice straw into soil in autumn and returned wheat straw into soil in summer) paddy soils for 0, 1, 4 and 8 years. The results showed that the average content of total soil cadmium in the ploughing layer (020 cm soil layer) was 0.478 mg·kg-1. The average content of total soil cadmium in plough pan (2040 cm soil layer) was 0.419 mg·kg-1. The average contents of cadmium in both soil layers exceeded environmental quality standard for agricultural soils (farmland soil cadmium < 0.30 mg·kg-1 of GB15618—1995). The distribution of cadmium speciation in the paddy soil was as follows: residual Cd > Fe-Mn oxide bonded Cd > organically bonded Cd > carbonate bonded Cd > exchangeable Cd. The incorporation of crop straw for over 4 years in paddy soils significantly improved soil organic matter content. It also obviously increased soil organically bonded Cd ions. The content of organically bonded Cd in soil with crop straw incorporation for 4 years was increased by 45%. The incorporation of crop straw in paddy soils slightly increased soil exchangeable Cd in the ploughing layer (020 cm soil layer). With increasing years of the incorporation of crop straw into soil, soil pH initially increased significantly (crop straw incorporation for 14 years) before decreasing slowly (crop straw incorporation for 48 years). This mainly affected the speciation of soil carbonate bonded Cd. The bioavailability of soil cadmium speciation under different years of crop straw incorporation was evaluate too. For short term crop straw incorporation (14 years), the bioavailability of cadmium in ploughing soil layer (020 cm) significantly decreased with increasing number of years. However, the bioavailability of soil cadmium fractions in the plough pan (2040 cm soil layer) did not significantly change with increasing number of years of crop straw incorporation. In conclusion therefore, short-term (14 years) incorporation of crop straw into paddy soils increased soil organic matter content. It also significantly enhanced soil organically bonded Cd and reduced soil availability of cadmium in the ploughing soil. This somehow reduced soil cadmium hazards and the risk of crop absorption and accumulation from soil cadmium. The findings of the study were beneficial for controlling heavy metal pollution in paddy soils induced by crop straw incorporation. It was also beneficial for designing more efficient and environmentally-friendly crop straw incorporation methods to prevent future soil cadmium pollution.

     

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