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Journal of Zhejiang University (Agriculture and Life Sciences)  2023, Vol. 49 Issue (6): 853-862    DOI: 10.3785/j.issn.1008-9209.2022.07.273
Resource utilization & environmental protection     
Study on safe utilization technology model of high acidity and mild cadmium-contaminated paddy fields: a case of the cadmium-contaminated pilot area in Yongkang City of Zhejiang Province
Simin CHEN1(),Xinzhe LU2,Chunlei HUANG2,Jiachun SHI1(),Jianming XU1
1.Institute of Soil-Water Resources and Environment, College of Environmental and Resource Sciences, Zhejiang University, Hangzhou 310058, Zhejiang, China
2.Zhejiang Institute of Geological Survey, Hangzhou 311203, Zhejiang, China
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Abstract  

In the highly acidic soil pilot area contaminated by cadmium (Cd) in Yongkang City of Zhejiang Province, we screened low-Cd-accumulating rice cultivars and soil passivators in the field and performed the combined effect tests for two consecutive years to explore the safe utilization technology model suitable for local Cd-polluted paddy fields. The results showed that ‘Xiushui 519’ (XS519), ‘Zhenuo 106’ (ZN106), ‘Zhongzheyou 1’ (ZZY1H) and ‘Zhongjia 8’ (ZJ8H) could be recommended as low-Cd-accumulating rice cultivars suitable for local planting. Among them, ‘Xiushui 519’ had the lowest and most stable Cd accumulation ability, and the average bioconcentration factors (BCFs) of Cd in the rice grains in the two years were 0.090 and 0.159, respectively; in the screening tests of passivators, the improvement effect of lime (L) on soil pH was significant. Lime, iron-modified biochar (FeC) and calcium-magnesia phosphate fertilizer (CaMgP) could reduce soil available Cd contents to a certain extent (passivation rates were 14.8%, 7.1% and 6.9%, respectively). In addition, 1 800 kg/hm2 iron-modified biochar and 2 400 kg/hm2 soil conditioner had better effects on reducing the Cd content in the rice grains of ‘Zhongjia 8’, which decreased by 32.2% and 29.0%, respectively, after application. According to the results of the combination tests of the low-Cd-accumulating cultivars and passivators, both the application of 2 250 kg/hm2 iron-modified biochar and 2 250 kg/hm2 soil conditioner increased obviously the soil pH values at the tillering stage and filling stage, the soil conditioner of which had a better improvement effect. The Cd contents in the rice grains of ‘Xiushui 519’ and ‘Zhenuo 106’ were extremely significant correlations with the soil pH values (5.19-5.61) at the mature stage. Within the range of soil pH values involved in the test, except for the combination of ‘Xiushui 519’ and the 1 500 kg/hm2 soil conditioner, the Cd content in the rice grains increased with increasing application amount of passivators. Therefore, planting ‘Xiushui 519’ (a low-Cd cultivar) directly is the best choice for the safe utilization of Cd-contaminated paddy fields in this area, which is both economical and convenient.



Key wordsmild      cadmium pollution      high acidity      paddy soil      safe utilization     
Received: 27 July 2022      Published: 25 December 2023
CLC:  S511  
Corresponding Authors: Jiachun SHI     E-mail: chensimin@zju.edu.cn;jcshi@zju.edu.cn
Cite this article:

Simin CHEN,Xinzhe LU,Chunlei HUANG,Jiachun SHI,Jianming XU. Study on safe utilization technology model of high acidity and mild cadmium-contaminated paddy fields: a case of the cadmium-contaminated pilot area in Yongkang City of Zhejiang Province. Journal of Zhejiang University (Agriculture and Life Sciences), 2023, 49(6): 853-862.

URL:

https://www.zjujournals.com/agr/10.3785/j.issn.1008-9209.2022.07.273     OR     https://www.zjujournals.com/agr/Y2023/V49/I6/853


强酸性轻度镉污染稻田安全利用技术模式探究

为探究适合强酸性镉(Cd)污染稻田土壤的安全利用技术模式,在浙江省永康市Cd污染试验区,连续2年开展田间Cd低累积水稻品种和土壤钝化材料筛选及其组合效果试验。结果表明:在品种筛选试验中,‘秀水519’(XS519)、‘浙糯106’(ZN106)、‘中浙优1号’(ZZY1H)和‘中嘉8号’(ZJ8H)可被推荐为当地适宜种植的低Cd累积水稻品种,其中‘秀水519’的Cd累积能力较低且稳定,2年的平均富集系数分别为0.090和0.159。在钝化材料筛选试验中,石灰对土壤pH值的提高效果显著,石灰、铁基生物质炭和钙镁磷肥能在一定程度上降低土壤有效态Cd含量(钝化率分别为14.8%、7.1%和6.9%),1 800 kg/hm2铁基生物质炭和2 400 kg/hm2土壤调理剂对‘中嘉8号’籽粒的降Cd效果较好,施用后籽粒含Cd量分别降低了32.2%和29.0%。在Cd低累积品种和钝化材料的组合试验中,施用2 250 kg/hm2铁基生物质炭和2 250 kg/hm2土壤调理剂均使水稻分蘖期和灌浆期的土壤pH值明显上升,其中土壤调理剂对酸性土壤的改良效果明显优于铁基生物质炭。‘秀水519’和‘浙糯106’的籽粒Cd含量与成熟期土壤pH值(5.19~5.61)呈极显著正相关,在试验所涉及的土壤pH值范围内,除‘秀水519’与1 500 kg/hm2土壤调理剂组合外,籽粒Cd含量随钝化材料施用量的升高而增加。从经济和轻简化角度考虑,种植‘秀水519’是目前该试验区Cd污染稻田安全利用的最佳选择。


关键词: 轻度,  镉污染,  强酸性,  稻田土壤,  安全利用 
指标 Index石灰 L海泡石 Sep钙镁磷肥 CaMgP铁基生物质炭 FeC土壤调理剂 SC有机肥 OF猪粪生物质炭 PBC
pH值 pH value12.358.528.3012.1912.468.3210.40
w(Cd)/(mg/kg)0.020.050.370.270.150.650.09
Table 1 pH values and Cd contents of passivators
Fig. 1 Cd contents and its bioconcentration factors (BCFs) in grains of different rice cultivarsDifferent lowercase letters above bars indicate significant differences at the 0.05 probability level, and n=3. The same as Fig. 3.
Fig. 2 Soil pH values and available Cd contents before the test and at the mature stage of rice under different treatmentsDifferent lowercase letters above bars indicate significant differences among treatments in the same stage at the 0.05 probability level, and n=3.
Fig. 3 Cd contents and its BCFs in ZJ8H rice grains under different treatments

钝化材料

Passivator

单价

Unit price/

(Chinese Yuan/t)

施用量

Application

amount/(kg/hm2)

施用成本

Application

cost/(Chinese

Yuan/hm2)

PBC2 0002 0004 000
Sep3 5001 0003 500
FeC1 8001 8003 240
OF5303 6001 908
SC2 0002 4004 800
L3 1201 8005 616
CaMgP2 7001 2003 240
Table 2 Unit price and application cost of passivators

处理

Treatment

试验前

Before the test

分蘖期

Tillering stage

灌浆期

Filling stage

成熟期

Mature stage

CK4.92±0.24a4.85±0.22c4.86±0.14c5.19±0.06b
FeC14.85±0.17a5.19±0.20ab4.99±0.05abc5.25±0.09b
FeC24.85±0.20a5.16±0.10abc4.95±0.13bc5.32±0.06b
FeC34.89±0.24a5.35±0.16a5.15±0.18ab5.39±0.13b
SC14.78±0.13a5.00±0.13bc4.94±0.13bc5.37±0.13b
SC24.80±0.02a5.01±0.26bc4.97±0.18abc5.31±0.11b
SC34.87±0.17a5.42±0.14a5.23±0.17a5.61±0.17a
Table 3 Soil pH values in diverse stages under different treatments

处理

Treatment

试验前

Before the test

分蘖期

Tillering stage

灌浆期

Filling stage

成熟期

Mature stage

CK0.205±0.027a0.305±0.014a0.260±0.028a0.191±0.017a
FeC10.194±0.049a0.237±0.016bc0.230±0.022a0.182±0.011ab
FeC20.186±0.044a0.239±0.037bc0.211±0.050a0.183±0.030ab
FeC30.180±0.050a0.201±0.017c0.222±0.024a0.150±0.008b
SC10.176±0.043a0.241±0.030bc0.248±0.058a0.180±0.020ab
SC20.155±0.021a0.236±0.012bc0.213±0.034a0.174±0.009ab
SC30.212±0.043a0.246±0.019b0.276±0.012a0.185±0.019a
Table 4 Soil available Cd contents in diverse stages under different treatments
Fig. 4 Cd contents and its BCFs in rice grains under different treatmentsDifferent lowercase letters above bars indicate significant differences among treatments in the same cultivar at the 0.05 probability level, and n=3.

指标

Index

土壤pH值

Soil pH value

土壤有效态Cd含量

Soil available Cd content

XS519籽粒Cd含量

Grain-Cd content of XS519

ZN106籽粒Cd含量

Grain-Cd content of ZN106

土壤pH值 Soil pH value1.0000.1640.789**0.573**

土壤有效态Cd含量

Soil available Cd content

1.0000.0100.057

XS519籽粒Cd含量

Grain-Cd content of XS519

1.000

ZN106籽粒Cd含量

Grain-Cd content of ZN106

1.000
Table 5 Pearson correlation analysis between soil physicochemical indexes at the mature stage of rice and grain-Cd contents
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