Ecological and toxicological assessment of the influence of the chemical enterprise on soil

A. Krainiukov, I. Kryvytska
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Abstract

Technogenic pollution of the territory firstly leads to decrease of productivity of the land, since the main part of the technogenic loading, as a result of such pollution, assumes to the soil and vegetation. Soils those have been contaminated are characterized by changed structural and physical-and-chemical properties, which does not allow them to be used for economic purposes. To detect the technogenic loading on the soil as a result of the chemical plant operation, soil quality studies were carried out using the bio-testing method. The most informative data towards ecological danger of ecosystem pollution is the results of the determination of phytotoxicity for soil organisms. Such information can be obtained by an integral assessment of the biological usefulness of the habitat of organisms using the bio-testing method, which provides registration in controlled, standard conditions of the corresponding reactions of test organisms to the toxic effects of ecologically hazardous chemical compounds and their mixes. The following higher plants were selected as test cultures: Raphanus sativus L., Hordeum vulgare L. and Triticum aestivum L. As the test-response of higher plants, the energy of seed germination, the length of the sprout and the length of the root were taken into account. Four zones were selected for the research. The largest difference between the values of germination energy between control and experiment was observed on the results of a test-response to Hordeum vulgare L. in a sample of soil from zone Nr 4. The indicator of the toxic effect detected on the territory of zone Nr 4 - 43,64% reduction in the length of the roots relative to the control; 33.81% reduction in the length of the germs relative to the control based on the results of the test-response to Hordeum vulgare L. The soil sample from the zone Nr 1 showed no toxic properties in any test reaction (6.32% decrease in root length relative to control one, 5.68% reduction length of germs relative to the control one based on the results of the test reaction on Raphanus sativus L. Sample of soil from zone Nr 2 did not show toxicity (-45.26% decrease in root length relative to control one and 8.61% decrease in germination length relative to control one revealed by the results of the test-response to Raphanus sativus L. Soil samples from zone Nr 3 also showed no toxicity (3.83% decrease in root length relative to control and 11.02% reduction in germination length relative to control revealed by test-reaction results on Raphanus sativus L. The table value of the Student's criterion for the probability level is P = 0.5 and the number of measures of freedom 58 is 2.01. The calculation of the actual value of Student's criterion for the length of the roots (2.68) and the germs (2.05) showed an excess of the table value based on the results of the test-response on Hordeum vulgare L. in the soil sample from zone Nr 4, what confirms the presence of toxic properties of the soil. In order to assess the risk of soil contamination, the "measure of soil contamination" indicator was used in accordance with defined levels of inhibition of growth processes, the quantitative characteristics of which are expressed by the soil contamination coefficient, while the soil contamination coefficient is differentiated according to the levels of inhibition of growth processes. According to the calculated data, in the sample Nr 4, the phytotoxic factor or percentage reduction in the length of the roots relative to the control is 43.64% based on the results of the test-response to Hordeum vulgare L. By level of contamination, the soil is moderately polluted, belongs to the III class of quality and shows the measure of contamination of 1,3. Soil samples №1, №2 and №3 showed no toxicity (А˂20), i.e., they are non-contaminated and belong to the I class of quality. Therefore, for the integrated assessment of soil quality, in addition to chemical indicators, it is recommended to use integral indicators, in particular phytotoxicity of the soil, which characterizes the biological usefulness of the habitat of organisms.
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化工企业对土壤影响的生态毒理学评价
土地的技术污染首先导致土地生产力的下降,因为这种污染导致的技术负荷的主要部分是土壤和植被。被污染的土壤的特征是结构和物理化学性质发生了变化,这就不允许它们用于经济目的。为了检测化工厂运行对土壤的技术负荷,采用生物试验方法对土壤质量进行了研究。关于生态系统污染的生态危害,最翔实的数据是土壤生物的植物毒性测定结果。这种信息可以通过使用生物测试方法对生物体栖息地的生物有用性进行综合评估来获得,该方法在受控的标准条件下登记测试生物体对生态有害化合物及其混合物的毒性作用的相应反应。选择高等植物Raphanus sativus L.、Hordeum vulgare L.和Triticum aestivum L.作为高等植物的试验响应,考虑种子萌发能量、芽长和根长。选择了四个区域进行研究。在第4区土壤样品中,对普通Hordeum vulgare L.的试验响应结果显示,对照与试验组的萌发能值差异最大。在n4 - 43区检测到的毒效指标显示,与对照相比,根长减少64%;1区土壤样品在所有试验反应中均未表现出毒性(根长较对照减少6.32%);减少5.68%的细菌相对于控制一个基于测试的结果反应萝卜l .土壤样本区Nr 2根长度下降未显示毒性(-45.26%相对于控制和降低8.61%发芽长度相对于测试响应的结果显示,控制一个萝卜l .土壤样本区Nr 3根长度下降还显示没有毒性(3.83%相对于控制和减少11.02%对Raphanus sativus L.试验反应结果揭示的相对于对照的萌发长度。学生的概率水平判据表值为P = 0.5,自由度58的测度数为2.01。根据nr4区土壤样品中对普通Hordeum vulgare L.的试验响应结果,对根长(2.68)和芽长(2.05)的Student标准的实际值进行了计算,结果显示超出了表值,证实了土壤存在毒性。为了评估土壤污染的风险,根据生长过程的抑制程度使用“土壤污染测度”指标,土壤污染系数表示土壤污染的定量特征,土壤污染系数根据生长过程的抑制程度进行区分。根据计算得到的数据,在样品Nr 4中,根据试验响应的结果,根系长度相对于对照的植物毒性因子或百分比减少为43.64%。按污染程度计算,土壤为中度污染,属于III类质量,污染程度为1,3。土壤样品№1、№2和№3显示没有毒性(А依据20),即它们没有污染,属于I类质量。因此,对于土壤质量的综合评价,除了化学指标外,建议使用综合指标,特别是土壤的植物毒性,它表征了生物栖息地的生物有用性。
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