Hose J E
J Appl Toxicol. 1985 Aug;5(4):245-54. doi: 10.1002/jat.2550050406.
A method for evaluating pollutant genotoxicity, embryotoxicity and teratogenicity using sea urchin embryos has been developed and was tested using benzo(a)pyrene (BP). Initial results suggested that the bioassay may be a sensitive indicator of pollutant toxicity and mutagenicity since several endpoints can be simultaneously assessed. The bioassay is rapid, inexpensive and appears applicable to a variety of toxicants and delivery methods. The test is based upon the standard 48 h sea urchin development assay and incorporates cytologic-cytogenetic analysis of embryos. Following toxic exposure of gametes, fertilization success is assessed. Embryos then develop for 48 h at which time survival and teratogenesis are evaluated. A subsample of embryos is stained and dissociated into monolayers and mitotic configurations are examined using light microscopy. Embryo mitotic rates are used as an indicator of overall embryonic health. Cytotoxic effects are concomitantly evaluated. Genotoxicity is measured using two methods: (1) anaphase aberration analysis, a technique which assesses abnormalities in the chromosome configurations (such as bridges and fragments) as the groups of chromosomes move to opposite poles and (2) micronucleus formation, a procedure examining the incidence of smaller, secondary nuclei composed of whole chromosomes or chromatid fragments. These two measurements preclude the need to examine individual chromosomes for deletions and exchanges, a laborious process in most aquatic organisms which possess numerous relatively small chromosomes. This genotoxicity-teratogenicity test appears promising for laboratory evaluations of individual substances or of complex chemical mixtures as well as for environmental monitoring of nearshore areas. The standard development assay has been used to screen pharmaceuticals and environmental contaminants and some recent investigations have included mitotic aberration analysis. Experiments in our laboratory suggest that the genotoxicity-teratogenicity test may be a feasible approach to field monitoring. Mutagen loads of spawning adult urchins could be assessed by conducting cytologic-cytogenetic analysis of resulting embryos although initial studies suggest that this method is less sensitive than direct embryo exposures.
已开发出一种利用海胆胚胎评估污染物遗传毒性、胚胎毒性和致畸性的方法,并使用苯并(a)芘(BP)进行了测试。初步结果表明,该生物测定法可能是污染物毒性和致突变性的敏感指标,因为可以同时评估多个终点。该生物测定法快速、廉价,似乎适用于多种有毒物质和给药方法。该测试基于标准的48小时海胆发育试验,并纳入了胚胎的细胞细胞学 - 细胞遗传学分析。配子经毒性暴露后,评估受精成功率。然后胚胎发育48小时,此时评估存活率和致畸情况。取一部分胚胎样本进行染色并解离成单层,使用光学显微镜检查有丝分裂形态。胚胎有丝分裂率用作整体胚胎健康的指标。同时评估细胞毒性作用。使用两种方法测量遗传毒性:(1)后期畸变分析,一种在染色体组移向相反两极时评估染色体构型异常(如桥和片段)的技术;(2)微核形成,一种检查由整条染色体或染色单体片段组成的较小的次级核发生率的程序。这两种测量方法无需检查单个染色体的缺失和交换情况,而在大多数拥有众多相对较小染色体的水生生物中,检查单个染色体的缺失和交换是一个费力的过程。这种遗传毒性 - 致畸性测试对于单个物质或复杂化学混合物的实验室评估以及近岸区域的环境监测似乎很有前景。标准发育试验已用于筛选药物和环境污染物,最近的一些研究包括有丝分裂畸变分析。我们实验室的实验表明,遗传毒性 - 致畸性测试可能是一种可行的现场监测方法。虽然初步研究表明这种方法不如直接胚胎暴露敏感,但通过对所产生胚胎进行细胞细胞学 - 细胞遗传学分析,可以评估产卵成年海胆的诱变负荷。