Wang Qingyun, Zhang Jiabao, Zhao Bingzi, Xin Xiuli, Zhang Congzhi, Zhang Hailin
State Key Laboratory of Soil and Sustainable Agriculture, Institute of Soil Science, Chinese Academy of Sciences, Nanjing, 210008, China.
Environ Sci Pollut Res Int. 2014 Sep;21(17):10377-85. doi: 10.1007/s11356-014-2939-z. Epub 2014 May 6.
Continuous application of organic and inorganic fertilizers can affect soil and food quality with respect to heavy metal concentrations. The risk of cadmium (Cd) contamination in a long-term (over 20 years) experimental field in North China with an annual crop rotation of winter wheat and summer maize was investigated. The long-term experiment had a complete randomized block design with seven fertilizer treatments and four replications. The seven fertilizer treatments were (1) organic compost (OM), (2) half organic compost plus half chemical fertilizer (OM + NPK), (3) NPK fertilizer (NPK), (4-6) chemical fertilizers without one of the major nutrients (NP, PK, and NK), and (7) an unamended control (CK). Soil samples from 0 to 20 cm were collected in 1989, 1999, and 2009 to characterize Cd and other soil properties. During the past 20 years, various extents of Cd accumulation were observed in the soil, and the accumulation was mainly affected by atmospheric dry and wet deposition and fertilization. In 2009, the average Cd concentration in the soil was 148 ± 15 μg kg(-1) and decreased in the order of NPK ≈ OM + NKP ≈ PK > NP ≈ NK > OM ≈ CK. Sequential extraction of Cd showed that the acid-soluble fraction (F1, 32 ± 7 %) and the residual fraction (F4, 31 ± 5 %) were the dominant fractions of Cd in the soil, followed by the reducible fraction (F2, 22 ± 5 %) and oxidizable fraction (F3, 15 ± 6 %). The acid-soluble Cd fraction in the soil and Cd accumulation in the crops increased with soil plant available K. Fraction F3 was increased by soil organic C (SOC) and crop yields, but SOC reduced the uptake of soil Cd by crops. The long-term P fertilization resulted in more Cd buildup in the soil than other treatments, but the uptake of Cd by crops was inhibited by the precipitation of Cd with phosphate in the soil. Although soil Cd was slightly increased over the 20 years of intensive crop production, both soil and grain/kernel Cd concentrations were still below the national standards for environmental and food safety.
有机肥料和无机肥料的持续施用会影响土壤和食物中重金属含量方面的质量。本研究调查了中国北方一个长期(超过20年)试验田的镉(Cd)污染风险,该试验田每年冬小麦和夏玉米轮作。长期试验采用完全随机区组设计,有七种肥料处理,重复四次。七种肥料处理分别为:(1)有机堆肥(OM);(2)半有机堆肥加半化肥(OM + NPK);(3)NPK化肥(NPK);(4 - 6)不含一种主要养分的化肥(NP、PK和NK);(7)不施肥对照(CK)。分别于1989年、1999年和2009年采集0至20厘米土层的土壤样本,以分析镉及其他土壤性质。在过去20年中,土壤中观察到不同程度的镉积累,积累主要受大气干湿沉降和施肥影响。2009年,土壤中镉的平均浓度为148 ± 15 μg kg(-1),其浓度顺序为NPK ≈ OM + NKP ≈ PK > NP ≈ NK > OM ≈ CK。镉的连续提取结果表明,酸溶态(F1,32 ± 7%)和残渣态(F4,31 ± 5%)是土壤中镉的主要形态,其次是可还原态(F2,22 ± 5%)和氧化态(F3,15 ± 6%)。土壤中酸溶态镉含量和作物中的镉积累量随土壤有效钾含量增加而增加。F3形态受土壤有机碳(SOC)和作物产量影响而增加,但SOC降低了作物对土壤镉的吸收。长期施磷导致土壤中镉积累量高于其他处理,但土壤中镉与磷酸盐沉淀抑制了作物对镉的吸收。尽管在20年的集约作物生产中土壤镉略有增加,但土壤和籽粒/谷粒中的镉浓度仍低于环境和食品安全国家标准。