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利用海胆(Paracentrotus lividus)、牡蛎(Crassostrea gigas)和贻贝(Mytilus galloprovincialis)对淘析物进行胚胎毒性试验,制定毒性评分标准。

Developing toxicity scores for embryotoxicity tests on elutriates with the sea urchin Paracentrotus lividus, the oyster Crassostrea gigas, and the mussel Mytilus galloprovincialis.

作者信息

Losso Chiara, Picone Marco, Novelli Alessandra Arizzi, Delaney Eugenia, Ghetti Pier Francesco, Ghirardini Annamaria Volpi

机构信息

Department of Environmental Sciences, University of Venice, Campo della Celestia 2737/b, I-30122, Venice, Italy.

出版信息

Arch Environ Contam Toxicol. 2007 Aug;53(2):220-6. doi: 10.1007/s00244-006-0136-x. Epub 2007 Jun 1.

Abstract

Bioassays are routinely employed for sediment quality assessment. In order to be able to effectively use Bioassays responses in regulatory and management frameworks, toxicity scores, which rank toxicity data in defined classes that are continuous and difficult to interpret, should be reliable and suitable tools to support decisions about the presence or absence of toxicity in tested samples and on how toxic a sample is. A statistical approach is needed to define thresholds for toxicity scores. The Minimum Significance Difference (MSD) criterion allowed the evaluation of toxicity thresholds for each test-matrix and organism pair, based on large sets of experimental data. The MSD values were normalized with respect to the control, ranked in ascending order, and the 90th percentile was identified; the Toxicity Threshold (TT) was calculated by subtracting the 90th percentile from 100 and the Toxicity Limit (TL) was estimated as the percentage of control response multiplied by TT. Taking into account sample responses normalized with respect to control (S), when S > TL, the sample is considered nontoxic; when S <or= TL, toxicity is statistically present. The MSD criterion was applied on a dataset of results from both published and ongoing projects using the validated embryotoxicity tests with the echinoid Paracentrotus lividus, the oyster Crassostrea gigas, and the mussel Mytilus galloprovincialis, on elutriates from sediments of the Venice Lagoon. Once the threshold defining presence or absence of toxicity had been calculated, four other toxicity classes were developed: low (for toxicity data expressed as percentage of effect), medium, high, and very high toxicity (for toxicity data expressed as TU50).

摘要

生物测定法通常用于沉积物质量评估。为了能够在监管和管理框架中有效利用生物测定法的响应结果,毒性评分(将毒性数据按连续且难以解释的特定类别进行排序)应是支持有关测试样品中是否存在毒性以及样品毒性程度决策的可靠且适用的工具。需要一种统计方法来定义毒性评分的阈值。最小显著性差异(MSD)标准允许基于大量实验数据评估每个测试基质与生物对的毒性阈值。MSD值相对于对照进行归一化处理,按升序排列,并确定第90百分位数;毒性阈值(TT)通过从100中减去第90百分位数来计算,毒性限度(TL)估计为对照响应百分比乘以TT。考虑到相对于对照进行归一化处理的样品响应(S),当S > TL时,样品被视为无毒;当S≤TL时,统计学上存在毒性。MSD标准应用于来自已发表和正在进行项目的数据集,这些项目使用经过验证的胚胎毒性测试,测试对象为海胆Paracentrotus lividus、牡蛎Crassostrea gigas和贻贝Mytilus galloprovincialis,测试样品为威尼斯泻湖沉积物的淘析物。一旦计算出定义毒性存在与否的阈值,就制定了另外四个毒性类别:低(对于以效应百分比表示的毒性数据)、中、高和非常高毒性(对于以TU50表示的毒性数据)。

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