Turner Andrew D, Stubbs Ben, Coates Lewis, Dhanji-Rapkova Monika, Hatfield Robert G, Lewis Adam M, Rowland-Pilgrim Stephanie, O'Neil Alison, Stubbs Patrycja, Ross Stuart, Baker Clothilde, Algoet Myriam
Centre for Environment, Fisheries and Aquaculture Science (Cefas), Barrack Road, The Nothe, Weymouth, Dorset DT4 8UB, United Kingdom.
Centre for Environment, Fisheries and Aquaculture Science (Cefas), Barrack Road, The Nothe, Weymouth, Dorset DT4 8UB, United Kingdom.
Harmful Algae. 2014 Jan;31:87-99. doi: 10.1016/j.hal.2013.10.014. Epub 2013 Nov 5.
As the official control monitoring laboratory in Great Britain for the analysis of marine biotoxins in shellfish, Cefas have for the past five years conducted routine monitoring for paralytic shellfish poisoning toxins (PST) using a non-animal alternative method to the mouse bioassay reference method; a refined version of the AOAC 2005.06 pre-column oxidation liquid chromatography method. Application of this instrumental methodology has enabled the generation of data not only on the occurrence and magnitude of PST events, but also the quantitation and assessment of different PST profiles. Since implementation of the method in 2008, results have shown huge variabilities in the occurrence of PSTs, with large spatial and temporal variabilities around the coastline. Mean PST profiles were not found to correlate either with total PST content of the shellfish, the year of sampling or with a few notable exceptions, the shellfish species. Toxin profiles were found to fall into one of four distinct profile types, with one relating solely to the exclusive presence of decarbamoyl toxins in surf clams. The other profile types contained variable proportions of gonyautoxins, N-sulfocarbamoyl toxins, neosaxitoxin and saxitoxin. While some indications of geographical repeatability were noted, this was not observed for all profile types. Consequently, the application of rapid immunochemical testing methods to end product testing would need to be considered carefully given the large differences in PST congener cross-reactivities.
作为英国官方负责分析贝类中海洋生物毒素的控制监测实验室,在过去五年里,英国食品与环境研究署(Cefas)一直使用一种非动物替代方法,而非小鼠生物测定参考方法,即AOAC 2005.06柱前氧化液相色谱法的改进版本,对麻痹性贝类中毒毒素(PST)进行常规监测。这种仪器方法的应用不仅能够生成关于PST事件的发生情况和规模的数据,还能对不同的PST谱进行定量和评估。自2008年实施该方法以来,结果显示PST的发生存在巨大差异,在海岸线周围存在较大的空间和时间变异性。未发现平均PST谱与贝类的总PST含量、采样年份相关,除了少数显著例外,也与贝类物种无关。毒素谱被发现分为四种不同的谱型之一,其中一种仅与冲浪蛤蜊中脱氨甲酰毒素的唯一存在有关。其他谱型包含不同比例的膝沟藻毒素、N - 磺氨甲酰毒素、新石房蛤毒素和石房蛤毒素。虽然注意到了一些地理重复性的迹象,但并非所有谱型都是如此。因此,鉴于PST同系物交叉反应性存在巨大差异,在最终产品检测中应用快速免疫化学检测方法时需要仔细考虑。