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Frontiers of Agricultural Science and Engineering

ISSN 2095-7505

ISSN 2095-977X(Online)

CN 10-1204/S

Postal Subscription Code 80-906

Front. Agr. Sci. Eng.    2019, Vol. 6 Issue (4) : 419-430    https://doi.org/10.15302/J-FASE-2019273
REVIEW
Cadmium pollution from phosphate fertilizers in arable soils and crops: an overview
Andrea Giovanna NIÑO-SAVALA1(), Zhong ZHUANG2, Xin MA2, Andreas FANGMEIER1, Huafen LI2, Aohan TANG2, Xuejun LIU2
1. Institute of Landscape and Plant Ecology, University of Hohenheim, 70599 Stuttgart, Germany
2. College of Resources and Environmental Sciences, China Agricultural University, Beijing 100193, China
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Abstract

The application of mineral and organic phosphorus fertilizers to arable land has greatly increased crop yield to meet the world food demand. On the other hand, impurities in these fertilizers, such as heavy metals, are being added to agricultural soils, resulting both from the raw materials themselves and the processes used to obtain the final product. Cadmium, a non-essential and toxic heavy metal, has been found in relatively high amounts in common P fertilizers obtained from sediments. This metal poses a high risk for soil fertility, crop cultivation, and plants in general. Furthermore, human health might be compromised by the cadmium concentrations in agricultural and livestock products, due to the bioaccumulation effect in the food web. The accumulation in the different matrixes is the result of the high mobility and flexible availability of this harmful metal. This review summarizes risks to human health, the factors influencing cadmium movement in soils and crop uptake, as well as common plant responses to its toxicity. In addition, it summarizes cadmium balances in soils, trends, long-term experiments, and further studies. Cadmium inputs and outputs in arable soil, together with their calculated concentrations, are compared between two different regions: the European countries (in particular Germany) and China. The comparison appears useful because of the different proportions in the inputs and outputs of cadmium, and the diverse geographical, environmental and social factors. Moreover, these variables and their influences on cadmium contamination improve the understanding of the pollution from phosphate fertilizers and will help to establish future mitigation policies.

Keywords soil pollution      arable land      crop production      cadmium balance      P fertilizer      cadmium toxicity     
Corresponding Author(s): Andrea Giovanna NIÑO-SAVALA   
Just Accepted Date: 28 June 2019   Online First Date: 05 August 2019    Issue Date: 29 November 2019
 Cite this article:   
Andrea Giovanna NIÑO-SAVALA,Zhong ZHUANG,Xin MA, et al. Cadmium pollution from phosphate fertilizers in arable soils and crops: an overview[J]. Front. Agr. Sci. Eng. , 2019, 6(4): 419-430.
 URL:  
https://academic.hep.com.cn/fase/EN/10.15302/J-FASE-2019273
https://academic.hep.com.cn/fase/EN/Y2019/V6/I4/419
Year Country Phosphate Rock USGS 2019 IFAData 2019
Production Reservesa P2O5 content Production (P2O5) Demand (P2O5)
2010 All countries 181000 65000000 56000 42532 41663
China 68000 3700000 20400 15998 13092
Germany 3 286
Morocco and Western Sahara 26600 50000000 8800 1875 191
United States 25800 1400000 7400 6297 3890
2015 All countries 223000 69000000 73900 44139 43912
China 120000 3700000 36000 17224 12111
Germany 25 225
Morocco and Western Sahara 30000 50000000 9100 2169 221
United States 27600 1100000 7710 5257 4302
2018 All countries 270000 70000000
China 140000 3200000
Germany
Morocco and Western Sahara 33000 50000000
United States 27000 1000000
Tab.1  Phosphate rock production and reserves (kt; data from US Geological Survey[6,7]), and production and demand of P fertilizers (kt; data from International Fertilizer Industry Association[8])
Fig.1  General scheme of cadmium balance in an air-soil-crop system
Inorganic P fertilizers China Brazil (sold) Germany (sold) Morocco Russia South Africa USA
PR 5.00 [31] 20.00[41] 19.00b[42] 30.00–60.00 [40] 0.25a[39] 1.00[20] 60.00–340.00[31]
<2.00[20] 12.00–38.00[20,31] 1.00[20] 6.00–92.00[20]
4.48a[43] 46.00–120.00a[39] 0.15[14] 1.45–199.00[14]
2.60b[28] 507.00[14]
DAP 5.10a[39] 28.10a[44] 29.50–68.00a[39] 2.10a[39] 2.20a[39] 18.20–185.40[39]
2.20[45] 61.00a[44] 9.36[45] 0.84[46]
MAP 5.30a[39] 17.12[41] 30.60–70.60a[39] 2.20a[39] 2.20a[39] 18.8–192.4a[39]
0.14[45] 50.92[45]
NPK 0.60–1.51[45] 5.80[41] 15.80b[47] 0.80–11.45[45] 3.23–3.66[45]
2.30[48]
PK 55.60b[47]
SP 0.22b[49] 8.50[41] 34.00[48]
TSP 24.40[48] 31.50–72.70a[39] 2.30a[39] 2.30a[39] 13.30–198.10a[39]
62.00b[42]
36.70–73.10b[47]
28.10b[44]
Tab.2  Cadmium concentrations (mg·kg1) in inorganic and organic P fertilizers from different countries
Location in China Cadmium deposition Reference
Heilongjiang, Northeast 1.46 [62]
Mongolian Plateau, Northwest 1.04 [63]
Beijing, North China 4.75 [64]
Tianjin, North China 5.30 [64]
Hebei, North China 5.57 [64]
Henan, North China 4.93 [65]
Shanxi, North China 2.04 [65]
Fujian, South-east 0.91 [65]
Lianyuan, Southeast 17.00 [66]
Shenzhen, Southeast 7.42 [66]
Guizhou, Southwest 2.01 [65]
Jiaozhou Bay, Central Yellow Sea 1.30 [67]
Daya Bay, South China Sea 1.60 [68]
East China Sea 1.78 [69]
Southern Yellow Sea 1.80 [69]
Tab.3  Atmospheric cadmium deposition (g·ha1·yr1) in different regions of China
Organic P fertilizers China Europe Germany
Manure 0.67a[72] 0.20[70] 0.30a[44]
Swine manure 1.30[73]
12.05[74] 0.46[70] 0.74[44]
0.64–21.02[75]
Cattle manure 0.92[73] 0.43a[44]
5.61[76] 0.80[42]
Poultry manure 1.48[73] 0.25a [44]
15.38[74]
Sewage sludge 1.65[77] 1.80[70] 1.00a[42,77]
0.30–5.10[77] 1.50–4.50[78]
Tab.4  Cadmium concentrations (mg·kg1) in organic P fertilizers from China, European region and Germany
Type Europe China
Finland[83] Austria[84] Germany[44] Northern Sweden[85] Europe[70] Central Europe[42] France[61] China[86] Heilongjiang[87] Hunan[88] Yangtze River delta[89] Hainan Island[90]
Cadmium inputs
Atm. Dep. 0.30 2.10 1.70 0.34 0.35 0.35 0.20 4.04 0.36 6.85–40.25 2.66 0.91
P fertilizers 0.025 0.79 5.60 0.80 3.40 2.84 0.20 0.40 0.06–2.39 0.11 3.20
Manure 0.32 0.46 0.64 0.47 0.06–0.14 1.40 0.25 6.38
Sewage sludge/Irrigation watera 0.023 0.04 0.05 0.30 1.80 <0.10 0.002–8.19 5.65 0.11
Lime 0.035 0.02–0.09 0.15 0.02
Total input 0.71 3.39 7.94 0.81 1.43 5.60 3.31 12.42 0.76 6.91–50.83 8.42 4.22
Cadmium outputs
Crop offtake 0.14 0.13 0.68 0.17 0.20 0.99 0.20 15.66–61.45 0.61 0.41
Leaching 0.06 0.26 0.28 0.61 2.56 3.00, 0.56 and 0.28 0.033–0.412 1.11 0.64
Total output 0.20 0.39 0.96 0.78 2.76 0.50 3.99, 1.55 and 1.28 1.46 0.20 15.66-61.66 1.72 1.05
Tab.5  Cadmium inputs and outputs (g·kg1·yr1) in arable land from studies in Europe and China
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