玉米镍中毒症状及临界值的研究

Minyi Zhou, Jin-hua Liu, Ya-qing Wang, Jingming Yang, Xiao-bin Yu
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引用次数: 0

摘要

镍(Ni)在植物的生长中起着重要的作用,但它也是一种重金属,极易在土壤中富集,对植物产生毒害作用。为评价Ni胁迫对玉米生长的影响,在吉林中部黑土上进行了盆栽试验。镍在土壤中的平衡水平为0 ~ 800mg kg - 1土壤。主要结果如下:玉米中Ni浓度与植株干重呈负相关。镍中毒的症状表现为:玉米根短而细,叶卷曲,叶尖有条纹,叶尖褪色,叶柄与根连接处呈褐色腐烂。在本研究中,Y=0.3071+0.0012X+-0.0001CX2的拟合方程描述了土壤中有效镍含量(低于30mg/kg时)与玉米干物质重的极显著关系。土壤中能使玉米达到最佳生长状态的有效镍含量为6.00mg/kg,毒性临界值为11.48mg/kg,奢侈镍吸收范围为6.00 ~ 11.48mg/kg。11.48- 32.77mg/kg对玉米造成轻度毒性;32.77 ~ 67.38mg/kg为中度毒性,67.38mg/kg以上为重度毒性。轻度毒性玉米中Ni含量为33.40 ~ 66.40mg/kg。中毒性66.40 ~ 111.40mg/kg。严重毒性超过111.40mg/kg。用方程Y=-0.0013X+0.3126, Y=-0.0010X+0.3364可以表示毒性发生时土壤有效镍、玉米有效镍与玉米干物质重的关系。当Ni浓度为25mg/kg时,土壤的Ni固定点最高,为23.98%。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Research on the Symptoms and the Critical Value of Nickel Toxicity of Maize
Nickel (Ni) plays an important role in the growth of plants, but it is also a kind of heavy metal which can easily enrich in soil and exert toxic effect on plants. To evaluate the Ni stress on the maize growth, a pot experiment was conducted by black soils sampled from the field in the middle of Jilin province. And Ni was equilibrated in the soils to graded levels from 0 to 800mg kg−1 soil. The main results were as follows: The concentration of Ni in maize had a negative correlation with the plant dry weight. The symptom of Ni toxicity was as follows: maize root was short and thin, leaf curled with barred vain and fade blade tip, and it was brown and rotten at the connection of the petiole and roots. In this study, the fitting equation of Y=0.3071+0.0012X+-0.0001CX2 described the extremely significant relationship between the amount of effective Ni in soil (when it was below 30mg/kg) and the dry matter weight of maize. The amount of effective Ni in soil (DTPA extracted) which could provide maize with the best growing state was 6.00mg/kg, the toxicity critical value was 11.48mg/kg, the range of Ni luxury absorption was 6.00 -11.48mg/kg. 11.48- 32.77mg/kg caused maize mild toxicity; 32.77-67.38mg/kg caused moderate toxicity and over 67.38mg/kg leaded to serious toxicity. When maize took place mild toxicity, the content of Ni in maize was 33.40-66.40mg/kg. Moderate toxicity was 66.40-111.40mg/kg. Serious toxicity was over 111.40mg/kg. The equations of Y=-0.0013X+0.3126, Y=-0.0010X+0.3364 could be used to express the relationship between effective Ni in soil, Ni in maize and the dry matter weight of maize when toxicity happened. The highest Ni fixed rate was 23.98% when the soil received 25mg/kg Ni.
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