Scientia Agricultura Sinica ›› 2018, Vol. 51 ›› Issue (18): 3542-3550.doi: 10.3864/j.issn.0578-1752.2018.18.010

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

Cd Accumulation and Safety Assessment of Soil-Crop System Induced by Long-Term Different Fertilization

Ke WANG1(), ChunLi XU1, YuTing ZHANG1, ZhiBin ZHENG1, DingYong WANG1,2, XiaoJun SHI1,2()   

  1. 1College of Resources and Environment, Southwest University/Key Laboratory of Arable Land Conservation (Southwest China), Ministry of Agriculture, Chongqing 400716
    2Academy of Agricultural Sciences, Southwest University, Chongqing 400716
  • Received:2018-02-28 Accepted:2018-04-09 Online:2018-09-16 Published:2018-09-16

Abstract:

【Objective】 This study focused on cadmium (Cd) accumulation in soil and availability in crop induced by 23 years (1997-2013) fertilization to evaluate the extent of soil Cd contamination and the safety threshold, so that which could offer suggestions to the fertilization strategy and soil Cd safety standard of Southwest China. 【Method】 Eight fertilization treatments were employed, including only nitrogen (N), nitrogen and potassium (NK), nitrogen plus phosphorus and potassium (NPK), chemical fertilizer plus pig manure (NPK+M), chemical fertilizer plus rice straw (NPK+S), 1.5 times chemical fertilizer plus rice straw (1.5NPK+S), chloride-based fertilizers plus rice straw ((NK)ClP+S), as well as no fertilizer control (CK). Soil available Cd, soil total Cd concentration and Cd uptake by crop among different years were measured to evaluate the Cd accumulation. 【Result】 The results showed that the soil total Cd increased with the extension of fertilization time, the total Cd accumulation in soil treated with CK, N and NK for a long time without phosphorus fertilizer increased slowly, the total Cd accumulation in soil treated with phosphate fertilizer, organic fertilizer and chlorinated fertilizer increased rapidly, and NPK+M, 1.5NPK+S and (NK)ClP+S had more accumulation, increasing 1.18, 1.18 and 1.15 mg·kg-1 after 23 years fertilization, respectively. Except for without phosphate fertilizer treatments, the total Cd accumulation of all the other soils above 0.6 mg·kg-1 had the soil environmental quality risk control standard for soil contamination of agricultural land. The soil available Cd was significantly higher under all fertilization treatments than that under CK, thereinto, the content of soil available Cd increased significantly with long-term application of N, (NK) ClP+S and 1.5NPK+S. The Cd concentration in rice grain was all raised with the increasing of fertilization time, while it didn’t exceed the national food safety standard of China (Cd≤0.2 mg·kg-1). There were no obvious changes of wheat grain Cd concentration among different years, but only the Cd concentration in grain of (NK)ClP+S treatment exceeded the pollutant limit standards of food of China (Cd≤0.1 mg·kg-1). 【Conclusion】 Under the conditions of this experiment, long-term different fertilization, especially the application of phosphate fertilizer and swine manure organic manure, increased the soil total Cd content and increased the ecological risk; The long-term application of chlorinated fertilizers increased the soil available Cd content because of the decrease of soil pH, and reduced the Cd content in wheat grains. Therefore, preventing Cd from entering farmland by fertilization is an important link to ensure the safe production of agricultural products.

Key words: long-term fertilization, purple soil, wheat, rice, Cd accumulation

Fig. 1

Soil total Cd content in purple soil under long-term fertilization (1991-2014)"

Fig. 2

Soil of available Cd content in purple soil under long-term fertilization (1991-2014)"

Fig. 3

The changes of Cd content in rice straw and grain with fertilization years"

Table 1

Cd uptake by rice grain and straw (1991-2013)"

处理
Treatment
年吸收量
Annual uptake (mg?hm-2·a-1)
年吸收总量
Total annual uptake
(mg?hm-2·a-1)
籽粒 Grain 秸秆 Straw
CK 47.3 55.3 102.6
N 165.3 259.4 424.7
NK 206.2 220.5 426.7
NPK 234.5 240.9 475.5
NPK+M 313.2 227.3 540.5
NPK+S 247.2 258.7 505.9
1.5NPK+S 239.5 356.7 596.1
(NK)ClP+S 367.8 450.7 818.5

Fig. 4

The changes of Cd content in wheat straw and grain with fertilization years"

Table 2

Cd uptake by wheat grain and straw (1991-2013)"

处理
Treatment
年吸收量
Annual uptake (mg?hm-2·a-1)
年吸收总量
Total annual uptake
(mg?hm-2·a-1)
籽粒Grain 秸秆Straw
CK 61.7 260.8 322.4
N 94.5 449.2 543.7
NK 101.6 505.0 606.7
NPK 310.1 939.6 1249.7
NPK+M 293.0 1115.5 1408.5
NPK+S 233.3 769.7 1003.1
1.5NPK+S 380.3 1520.4 1900.8
(NK)ClP+S 547.1 2247.7 2794.7
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