Study on the Migration, Transformation and Prediction Model of Cadmium in the Whole Growth Stage of Late Rice

Yang Guohang, Li Qiong, He Lizhao, Gu Jing, Niu Jing, Zhang Haiou, Zheng Zijian, Zhao Zhen

PDF(1548 KB)
PDF(1548 KB)
Chinese Agricultural Science Bulletin ›› 2021, Vol. 37 ›› Issue (25) : 1-10. DOI: 10.11924/j.issn.1000-6850.casb2020-0680

Study on the Migration, Transformation and Prediction Model of Cadmium in the Whole Growth Stage of Late Rice

Author information +
History +

Abstract

To better understand the migration, transformation and prediction model of cadmium (Cd) in the whole growth stage of late rice, we used soil-rice point-to-point data of Cd in field test in Wangcheng Changsha to study the differences of absorption, accumulation and distribution of Cd in different parts (root, stem and leaf, grain) of rice and its four typical growth stages (seedling stage, tillering stage, filling stage and mature stage). The results indicate that the Cd content and enrichment ability of each part in the same growth stage are all the roots> stems and leaves> grains, and the Cd content in roots are significantly higher than that in other parts, and there are significant differences in different growth stages, namely mature stage> filling stage> tillering stage> seedling stage. The transport capacity of Cd is soil root> root-stem and leaf> stem and leaf-grain> root-grain, most of the Cd in grain is from the transfer of the stem and leaf, and the transport capacity of Cd in tillering stage is significantly higher than that in other stages. The accumulation and distribution differences of Cd are stem and leaf> root> grain, and the tillering stage and mature stage are much higher than seedling stage and filling stage. The main factors affecting the Cd absorption are soil pH and available cadmium (ACd) content, pH has a negative effect and available cadmium has a positive effect, and the Cd content in stems and leaves of tillering stage is most affected by them, therefore it is the key stage to control Cd into grain. The pH and available cadmium in tillering stage could be used to predict Cd content of grains in mature stage, and the optimal prediction model is lgCdthe grain in maturity stage= 0.158- 0.099pHtillering stage+ 0.261lgACdtillering stage. The research results could provide a theoretical basis and data support for the risk assessment and controlling of soil Cd pollution in rice fields in Changzhutan area of China.

Key words

late rice / growth stage / cadmium / migration and transformation / physical and chemical properties of soil / prediction model

Cite this article

Download Citations
Yang Guohang , Li Qiong , He Lizhao , Gu Jing , Niu Jing , Zhang Haiou , Zheng Zijian , Zhao Zhen. Study on the Migration, Transformation and Prediction Model of Cadmium in the Whole Growth Stage of Late Rice. Chinese Agricultural Science Bulletin. 2021, 37(25): 1-10 https://doi.org/10.11924/j.issn.1000-6850.casb2020-0680

References

[1]
Williams P N, Zhang H, Davison W, et al. Evaluation of in situ DGT measurements for predicting the concentration of Cd in Chinese field-cultivated rice: impact of soil Cd: Zn ratios[J]. Environmental Science & Technology, 2012,46(15):8009-8016.
[2]
环境保护部, 国土资源部. 全国土壤污染状况调查公报[J]. 中国环保产业, 2014,36(5):10-11.
[3]
Joseph T, Dubey B, Mcbean E A. Human health risk assessment from arsenic exposures in Bangladesh[J]. Science of the Total Environment, 2015(527-528):552-560.
[4]
安宁, 范明生, 张福锁. 水稻最佳作物管理技术的增产增效作用[J]. 植物营养与肥料学报, 2015,21(4):846-852.
[5]
雷鸣, 曾敏, 王利红, 等. 湖南市场和污染区稻米中As、Pb、Cd污染及其健康风险评价[J]. 环境科学学报, 2010,30(11):2314-2320.
[6]
Römkens P F A M, Guo H Y, Chu C L, et al. Prediction of Cadmium uptake by brown rice and derivation of soil-plant transfer models to improve soil protection guidelines[J]. Environmental Pollution, 2009,157(8-9):2435-2444.
Cadmium (Cd) levels in paddy fields across Taiwan have increased due to emission from industry. To ensure the production of rice that meets food quality standards, predictive models or suitable soil tests are needed to evaluate the quality of soils to be used for rice cropping. Levels of Cd in soil and rice grains were measured in 19 paddy fields across the western plains in Taiwan. Cadmium levels in soil range from less than 0.1 mg kg(-1) to 30 mg kg(-1). Measured Cd levels in brown rice were predicted very well (R(2) > 0.8) based on Cd and Zinc in a 0.01 M CaCl(2) extract or a soil-plant transfer model using the reactive soil Cd content, pH, and cation exchange capacity. In contrast to current soil quality standards used in Taiwan, such models are effective in identifying soils where Cd in rice will exceed food quality standards.
[7]
莫争, 王春霞, 陈琴, 等. 重金属Cu,Pb,Zn,Cr,Cd在水稻植株中的富集和分布[J]. 环境化学, 2002,21(2):110-116.
[8]
仲晓春, 陈京都, 郝心宁. 水稻作物对重金属镉的积累、耐性机理以及栽培调控措施进展[J]. 中国农学通报, 2015,31(36):1-5.
[9]
胡莹, 黄益宗, 黄艳超, 等. 不同生育期水稻根表铁膜的形成及其对水稻吸收和转运Cd的影响[J]. 农业环境科学学报, 2013,3(3):432-437.
[10]
Wang X, Yao H, Ming H W, et al. Dynamic changes in radial oxygen loss and iron plaque formation and their effects on Cd and as accumulation in rice (Oryza sativa L.)[J]. Environmental Geochemistry & Health, 2013,35(6):779-788.
[11]
张振兴, 纪雄辉, 谢运河, 等. 水稻不同生育期施用生石灰对稻米镉含量的影响[J]. 农业环境科学学报, 2016,35(10):1867-1872.
[12]
李志博, 骆永明, 宋静, 等. 基于稻米摄入风险的稻田土壤镉临界值研究:个案研究[J]. 土壤学报, 2008,45(1):76-81.
[13]
张厦, 宋静, 高慧, 等. 贵州铅锌冶炼区农田土壤镉铅有效性评价与预测模型研究[J]. 土壤, 2017,49(2):328-336.
[14]
蒋红群, 王彬武, 刘晓娜, 等. 北京市土壤重金属潜在风险预警管理研究[J]. 土壤学报, 2015,52(4):731-746.
[15]
叶长城, 陈喆, 彭鸥, 等. 不同生育期Cd胁迫对水稻生长及镉累积的影响[J]. 环境科学学报, 2017,37(8):3201-3206.
[16]
Jing S, Lianqing L I, Pan G. Variation of grain Cd and Zn concentrations of 110 hybrid rice cultivars grown in a low-Cd paddy soil[J]. Journal of Environmental Sciences, 2009,21(2):168-172.
[17]
Dunbar K R, Mclaughlin M J, Reid R J. The uptake and partitioning of cadmium in two cultivars of potato (Solanum tuberosum L.)[J]. Journal of Experimental Botany, 2003,54(381):349-354.
The uptake and distribution of Cd in potatoes over the course of a growing season was investigated in two cultivars of potatoes that differed in tuber Cd concentration. Plants were grown in soil with supplemental Cd. The concentrations of Cd in different tissues varied greatly in the order roots>shoots>> tubers. After the initiation of tuber bulking, shoot growth ceased and the increase in total plant Cd was mostly due to accumulation in the tubers. The constancy of the Cd concentration in shoots suggested that import of Cd via the xylem must be matched by export in the phloem, which implied that Cd must have significant phloem mobility. It was found that the differences in tuber Cd between cultivars Wilwash and Kennebec were not due to differences in total uptake or growth, but to differences in Cd partitioning within the plant. This partitioning was specific to Cd and was not observed for a range of nutrient elements. Most of the differences in tuber Cd concentration between the cultivars could be accounted for by a 3-fold higher retention of Cd in the roots of cv. Wilwash. The involvement of root sequestration, and xylem and phloem pathways in the loading of Cd into tubers is considered.
[18]
肖美秀, 林文雄, 陈祥旭, 等. 镉在水稻体内的分配规律与水稻镉耐性的关系[J]. 中国农学通报, 2006,22(2):379-379.
[19]
Li Y, Pang H D, He L Y, et al. Cd immobilization and reduced tissue Cd accumulation of rice (Oryza sativa wuyun-23) in the presence of heavy metal-resistant bacteria[J]. Ecotoxicology & Environmental Safety, 2017,138:56-63.
[20]
周静, 杨洋, 孟桂元, 等. 不同镉污染土壤下水稻镉富集与转运效率差异[J]. 生态学杂志, 2018(1):89-94.
[21]
Nocito F F, Lancilli C, Dendena B, et al. Cadmium retention in rice roots is influenced by cadmium availability, chelation and translocation[J]. Plant Cell & Environment, 2011,34(6):994-1008.
[22]
龙小林, 向珣朝, 徐艳芳, 等. 镉胁迫下籼稻和粳稻对镉的吸收、转移和分配研究[J]. 中国水稻科学, 2014,28(2):177-184.
[23]
Kobayashi N I, Keitaro T, Atsushi H, et al. Characterization of rapid intervascular transport of cadmium in rice stem by radioisotope imaging[J]. Journal of Experimental Botany, 2013,64(2):507-517.
Participation of the intervascular transport system within the rice stem during cadmium (Cd) partitioning was investigated by characterizing (109)Cd behaviour in the shoot. In addition, (45)Ca, (32)P, and (35)S partitioning patterns were analysed for comparison with that of (109)Cd. Each tracer was applied to the seedling roots for 15 min, and the shoots were harvested either at 15 min (i.e. immediately after tracer application) or at 48 h. Distribution patterns of each element at 15 min were studied to identify the primary transport pathway before remobilization was initiated. (32)P was preferentially transported to completely expanded leaf blades having the highest transpiration rate. The newest leaf received minimal amounts of (32)P. In contrast, the amount of (35)S transported to the newest leaf was similar to that transported to the other mature leaf blades. Preferential movement towards the newest leaf was evident for (109)Cd and (45)Ca. These results directly indicate that elemental transport is differentially regulated in the vegetative stem as early as 15 min before the elements are transported to leaves. Cd behaviour in the stem was investigated in detail by obtaining serial section images from the bottom part of shoots after (109)Cd was applied to a single crown root. At 30 min, the maximum amount of (109)Cd was distributed in the peripheral cylinder of the longitudinal vascular bundles (PV) and, interestingly, some amount of (109)Cd was transported downwards along the PV. This transport manner of (109)Cd provides evidence that Cd can be loaded on the phloem at the stem immediately after Cd is transported from the root.
[24]
唐非, 雷鸣, 唐贞, 等. 不同水稻品种对镉的积累及其动态分布[J]. 农业环境科学学报, 2013(6):1092-1098.
[25]
刘昭兵, 纪雄辉, 彭华, 等. 水分管理模式对水稻吸收累积镉的影响及其作用机理[J]. 应用生态学报, 2010,21(4):908-914.
[26]
Liu J, Qian M, Cai G, et al. Uptake and translocation of Cd in different rice cultivars and the relation with Cd accumulation in rice grain[J]. Journal of Hazardous Materials, 2007,143(1):443-447.
[27]
Liu W, Zhou Q, Jing A, et al. Variations in cadmium accumulation among Chinese cabbage cultivars and screening for Cd-safe cultivars[J]. Journal of Hazardous Materials, 2010,173(1-3):737-743.
[28]
Yu H, Wang J, Fang W, et al. Cadmium accumulation in different rice cultivars and screening for pollution-safe cultivars of rice[J]. Science of the Total Environment, 2006,370(2-3):302-309.
[29]
龙新宪, 王艳红, 刘洪彦. 不同生态型东南景天对土壤中Cd的生长反应及吸收积累的差异性[J]. 植物生态学报, 2008,32(1):168-175.
采用盆栽方法研究了两种生态型东南景天(Sedum alfredii)对土壤中不同含量Cd(即对照, 12.5, 25, 50, 100, 200, 300, 400 mg•kg–1)的生 长反应、吸收和积累Cd的差异性。结果表明,土壤添加重金属Cd后,矿山生态型东南景天生长正常,地上部和根系Cd含量随着土壤中Cd含量的 增加而增加,在400 mg•kg–1 Cd处理下含量分别高达2 900和500 mg•kg–1,其地上部显著大于根部;然而,土壤添加Cd后,非矿山生态型东 南景天的生长受到抑制,地上部和根部的生物量显著降低。当土壤Cd含量为50~100 mg•kg–1 时,非矿山生态型东南景天的地上部和根系Cd含 量随着土壤中Cd含量的增加而增加,而且根系Cd含量则大于地上部。当土壤Cd≤50 mg•kg–1时,矿山生态型东南景天根系Cd含量比非矿山生态 型高,但当土壤Cd≥100 mg•kg–1,两者之间无显著差异;然而,但在同一Cd处理水平下,矿山生态型东南景天地上部Cd含量总是高于非矿山 生态型。这些结果表明,矿山生态型东南景天有很强的忍耐和吸收土壤Cd的能力,再次证明其为一种Cd超积累植物。

RIGHTS & PERMISSIONS

Copyright reserved © 2021. Chinese Agricultural Association Bulletin. All articles published represent the opinions of the authors, and do not reflect the official policy of the Chinese Agricultural Association or the Editorial Board, unless this is clearly specified.
Share on Mendeley
PDF(1548 KB)

Accesses

Citation

Detail

Sections
Recommended

/