欢迎访问《渔业研究》官方网站,今天是 2024年10月14日 星期一 分享到:

渔业研究, 2024, 46(2): 207-214 DOI: 10.14012/j.cnki.fjsc.2024.02.012

综述

水产品中麻痹性贝类毒素研究进展

牛耀路,1, 苏捷,2,*

1.厦门大学环境与生态学院,福建 厦门 361102

2.福建省水产研究所,福建省海洋生物增养殖与高值化利用重点实验室,福建 厦门 361013

Research progress of paralytic shellfish toxins in aquatic products

NIU Yaolu,1, SU Jie,2,*

1. College of Environment and Ecology, Xiamen University, Xiamen 361102, China

2. Key Laboratory of Cultivation and High-value Utilization of Marine Organisms in Fujian Province, Fisheries Research Institute of Fujian, Xiamen 361013, China

通讯作者: 苏 捷(1980—),男,博士,研究方向:海洋生物学。E-mail:23256438@qq.com

收稿日期: 2023-08-16  

基金资助: 福建省海洋服务与渔业高质量发展专项资金项目(闽财指〔2022〕0061号)
福建省海洋经济发展专项资金项目(FJHJF-L-2022-8)
厦门市海洋与渔业发展资金(23CZP012HJ10)

Received: 2023-08-16  

作者简介 About authors

牛耀路(1999—),女,硕士研究生,研究方向为环境微生物组学。E-mail:niuyaolu0213@163.com

摘要

近年来,有害藻华在中国沿海水域频繁发生。在有害藻华产生的藻毒素中,麻痹性贝类毒素(Paralytic shellfish toxins,PST)分布最广、危害最大,因而受到广泛关注。在被海洋生物摄食后,PST经食物链逐级向上传递、累积,这不仅影响生态环境安全,也威胁人类生命健康。因此,本文重点介绍了PST的定义、来源分布、危害、毒性机制、富集转化和检测方法(生物法、化学法和生物化学法),以及阐述PST的研究趋势、监管建议,旨在为完善PST研究资料、检测及防控措施提供参考。

关键词: 麻痹性贝类毒素; 毒性机制; 富集转化; 检测方法

Abstract

In recent years, harmful algal blooms have frequently occurred in coastal waters of China. Among the microcystins produced by these blooms, paralytic shellfish toxins (PST) are the most widely distributed and harmful, leading to significant concerns. When marine organisms ingest PST, they are passed up the food chain and accumulate, eventually posing a serious threat to human health, the environment, and the ecosystem.Therefore, this paper primarily introduces the definition, distribution, harm, toxicity mechanism, enrichment, and transformation of PST. It also discusses the methods used to detect PST, including biological, chemical, and biochemical approaches. The paper expounds on research trends and regulatory recommendations for PST. Its aim is to serve as a reference for the improvement of research, detection, and prevention of PST.

Keywords: paralytic shellfish toxins; toxic mechanism; enrichment and transformation; detection method

PDF (923KB) 元数据 多维度评价 相关文章 导出 EndNote| Ris| Bibtex  收藏本文

本文引用格式

牛耀路, 苏捷. 水产品中麻痹性贝类毒素研究进展[J]. 渔业研究, 2024, 46(2): 207-214 DOI:10.14012/j.cnki.fjsc.2024.02.012

NIU Yaolu, SU Jie. Research progress of paralytic shellfish toxins in aquatic products[J]. Journal of Fujian Fisheries, 2024, 46(2): 207-214 DOI:10.14012/j.cnki.fjsc.2024.02.012

有害藻华已成为全球性海洋生态环境问题[1],近些年在中国沿海水域也频繁发生,严重威胁到人类健康和生态安全。海洋中能引起藻华的藻类有260多种,其中有70多种能产生藻毒素[2],依据中毒的症状,通常将藻毒素划分为麻痹性贝类毒素(Paralytic shellfish toxins,PST)、腹泻性贝类毒素(Dirraretic shellfish toxins,DST)、神经性贝类毒素(Neurotoxic shellfish toxins,NST)、失忆性贝类毒素(Amnesic shellfish toxins,AST)和西加鱼毒素(Ciguatoxin,CTX)五种[3]。在这些贝类毒素中,PST是世界范围内分布最广、危害最大的一类海洋生物毒素,危及海洋生物,破坏海洋生态,被认为是对人体健康造成严重威胁的藻毒素之一,因而受到了广泛关注[4-6]。因此,了解PST的性质对生态保护和人类健康保障有着重要的意义。基于此,本文结合近年PST研究进展提出展望,为PST的深入探索提供参考资料。

1 PST的研究概况

1.1 PST的定义、化学结构与种类

PST是一种神经毒素。人们如果误食含有PST的贝类,会产生麻痹性中毒的现象[7]。PST是一类带有2个胍基的三环氨基甲酸酯化合物,种类繁多,分子式为C10H17N7O4[8],具有热稳定、不挥发[6]、酸性条件稳定和碱性条件发生氧化、难以被人体内的消化酶破坏[9]等特性。

目前,已被鉴定的PST衍生物有50余种[8],根据R4基团的不同,主要分为四类:1)氨基甲酸酯类毒素,包括石房蛤毒素(STX)、膝沟藻毒素1-4(GTX1-4)等,毒性最强;2)N-磺氨甲酰基类毒素(N-sulfocarbamoyltoxins),包括膝沟藻毒素5-6(GTX5-6)等,毒性中等;3)脱氨甲酰基类毒素(Decarbamoyltoxins),包括dcSTX、dcGTX1-4等,毒性较低;4)脱氧脱氨甲酰基类毒素(Deoxydecarbamoyltoxins),包括doSTX、doGTX2-3等[10-11],毒性尚未得到充分评估。中国对 PST的限量值标准为≤4 MU/g[12](约800 g STX eq./kg),与日本、韩国等国家的规定一致[9,13]

1.2 PST的来源和分布

近岸海域富营养化问题日益突出,当水体的营养结构发生变化时,浮游植物优势类群也会随之更替,而当有毒藻类占据优势时,藻细胞快速繁殖,并产生大量藻毒素[14]。PST主要由甲藻类产生,目前已经发现的能产生PST的藻类主要包括亚历山大藻属(Alexandrium)、裸甲藻属(Gymnodinium)、膝沟藻属(Gonyaulax)等,以及生活在淡水环境中的蓝绿藻属(Cyanobacteria)[15]

PST广泛存在于全球的海洋生态系统及淡水生态系统[16]。到21世纪,PST已分布至环北太平洋沿海、欧洲沿海、北美南部、澳大利亚等地区[17],以及中国的福建沿海、广东沿海、长江口邻近海域、北黄海等区域,并且分布范围还在持续扩大,检出率也持续上升,中毒事件显著增加[18],引发的生态问题日益突出[19-20]

1.3 PST对海洋生态和人类的危害

PST经摄食进入海洋生物体内后,会导致细胞中自由基水平的上升,尤其是活性氧水平,而当活性氧增加到超过机体的抗氧化防御时,会诱发严重的氧化应激反应,这可能导致DNA、蛋白质和脂质等生物分子的氧化损失。此外,PST还会导致海洋生物发生细胞水平上的变化,以及个体水平上的不良生理生化反应,如免疫防御等[21-22]。在海洋生态系统中,PST可沿着食物链,从营养水平较低的浮游动物传递至贝类、鱼类等其他海洋生物,并在其体内富集、转化,最终传递至食物链顶端的人类体内,对人类健康产生负面影响。人类食用了被PST污染的海产品后,会产生一系列的毒效应,如初期出现唇舌刺痛、指尖麻木,之后蔓延至四肢及全身,后期产生发热头晕、呼吸急促、恶心呕吐等反应,并出现四肢肌肉麻痹、运动障碍等全身症状,有些甚至可能因呼吸麻痹而死亡[6,10]。PST导致的症状和死亡与其实际毒性水平有关,但也取决于个体敏感性的差异,例如在同样的PST剂量下,儿童的死亡率比成人高[10]

1.4 PST的毒性机制

电压门控钠通道是PST的分子靶点。这类通道有一个共同的结构基序,由一个220 ~ 260 kDa的主亚基和一个或两个33 ~ 36 kDa的辅助β亚基组成[23-25]。有许多神经毒素能与钠通道的受体位点结合,影响离子渗透或电压依赖性门控,如STX的功能效应是阻断钠传导[26-28],主要是通过与α亚基的位点1结合,而结合需要α和β1两个亚基[29],构成受体位点1的氨基酸残基位于孔环,因此被认为形成了离子选择性过滤器[30-31]

PST是一类神经肌肉麻痹剂,其毒性机制是带有正电荷的胍基基团与电压门控钠离子通道的羧基基团相互作用,阻止钠离子通过神经细胞膜,抑制动作电位转导[32],对神经系统产生麻痹作用,从而导致中毒,甚至死亡[6,14]

1.5 PST的富集和生物转化

生物受PST污染具有一定的地域性和季节性,南北差异大,其中南方海域 PST检出率和含量较高,多发生在冬、春季;而北方海域则较低,多为秋季[15]。PST可通过食物链在海洋生物体内蓄积,如滤食性软体动物、甲壳类、双壳类、腹足类、鱼类等摄食和浓缩有毒藻类[33],而这种蓄积作用具有物种特异性[34-35]。Terrazas J O等[36]在智利部分海域的海洋生物中检测到PST,其中甲壳类GTX1/GTX4的检出率为80.5%;沙质双壳贝类GTX2/GTX3的检出率为77.7%;棘皮类动物neoSTX的检出率较高,占44.9%;腹足类和岩石双壳类STX的检出率也较高,分别为63.9%和58.8%;不同生物体内毒素的平均浓度为甲壳类>腹足类>被囊类>棘皮类>头足类>鱼类。在评估海域内,在双壳类、腹足类和被囊动物中没有发生死亡现象[35,37]。此外,虽然贝类对PST的积累明显高于鱼类,但鱼类对毒素更敏感,表现为PST在体内蓄积一定量后,贝类没有明显的反应,而鱼类体内积累少量即可致死[34]。PST在海洋生物体内的蓄积,不仅具有物种特异性,而且同一物种不同器官或组织中的分布也有差异,例如在头足类动物中,PST仅能在体液和内脏中被检测到,而不存在于肌肉和神经系统中;在鱼类中,PST可在内脏中被检测到,很少存在于消化系统中,在组织和鳃中也未被检出[36];扇贝则主要在消化系统中积累PST[38]。PST的葡萄糖醛酸形态和可溶性类似物具有较高的代谢率,这意味着其在人体组织中具有更强的分布能力,对人体的毒性也更大[39]

PST在食物链的蓄积和转移过程中可以进行生物转化,由弱毒性毒素转化为具有强毒性的类似物,如较弱和不稳定的毒素同系物N-磺氨甲酰基类,可被生物转化为毒性更强的氨基甲酸酯类,从而增强其对人类的潜在毒性;相反,强毒性毒素也可以通过生物转化成毒性较弱的类似物[40- 41]。PST的生物转化包括酶促和非酶促转化反应,其代谢机制包括脱硫、氧化、还原和异构化等。早期研究表明,细菌可通过生物转化使PST的毒性增强,如从海蟹、蜗牛的内脏分离出来的细菌,已被证明能够将GTX1-4转化为STX和neoSTX[42-43]。Sullivan J[44]发现,GTX5向STX的转化主要发生在翡翠贻贝(Mytilus edulis)中;毒性较低的毒素(如GTX 1-3)转化为毒性较高的毒素(如STX和neoSTX)通常与O-22-硫酸盐和N1-羟基的还原消除有关[43,45 -46]。而细菌磺基转移酶可通过酶促氧化将毒性较大的GTX 2/3和GTX 1/4分别转化为毒性较小的C1/C2和C3/C4[47-48]

2 PST的检测方法

为分析检测PST,中国、美国等国家及欧盟国际组织都已推出相应的贝类水产品的限量标准和检验方法,例如美国实施的“Food and Drug Administration’s Fish and Fisheries Products Hazards and Controls Guidance”对海洋毒素的管理[10];中国已制定和实施的国家标准《GB/T 5009.213—2016 食品安全国家标准 贝类中麻痹性贝类毒素的测定》等。但由于PST的复杂性,传统检测法难以解决其检测中出现的问题,例如灵敏度不够高、无法确定毒素组成等。目前,PST的检测和分析方法主要有生物法、化学法和生物化学法。

2.1 生物检测法

2.1.1 小鼠生物检测法

小鼠生物检测法被认为是测定贝类中PST的官方管理方法[49-50]。这种测定方法的原理是采用鼠单位计算PST的毒素量,通过观察记录注射了贝类软体组织提取液后的小鼠的死亡时间,并根据小鼠的体重进行校正,从而计算出每100 g贝肉中所含的PST。该方法操作相对简便,并且不需要特定的仪器,可以表示所检测样品中的PST总毒性,因而应用广泛。但其也存在一些缺陷,如不能确定样品中毒素的组成部分、灵敏度低、特异性差、受环境因素影响,以及涉及动物伦理等[51-52]。鉴于小鼠生物检测法存在的局限性,特别是使用动物的伦理问题,各国都在努力建立检测PST的替代方法。

2.1.2 细胞检测法

细胞检测法的原理是基于PST与Na+离子通道的特异性结合,在培养的细胞中加入Na+通道活化剂乌苯苷,使细胞因过多的Na+内流而肿胀死亡,但PST可以阻断Na+的内流,因此可通过检测细胞活力来实现对PST的检测[53]。该方法的灵敏度远高于小鼠生物检测法[50],但因组织培养周期长、操作繁琐、无法确定毒素组成及需要特殊的装置等局限性,其普遍推广受到制约[54]

2.1.3 免疫检测法

免疫检测法以抗原抗体反应为基础[53],现已被广泛地应用于PST的检测。在贝类毒素的免疫分析法中,酶联免疫吸附测定法(Enzyme linked immunosorbent assay,ELISA)最为常用,通过测定酶催化底物生成的有色产物的吸光值,绘制标准曲线,再进行定量计算[55]。已有研究表明,ELISA法的检测结果与小鼠生物检测法有较好的一致性[56],且该方法操作简单便捷、重现性良好且灵敏度高,适合于PST快速检测。但不同的PST之间会发生交叉反应,且抗体一般针对主要成分建立,导致结果的准确性受到一定程度的影响,检测PST的种类受限[55]

2.2 化学检测法

化学检测法主要包括高效液相色谱法(HPLC)和液相色谱-质谱联用法(LC-MS)[57-58],原理是碱性环境下离子交换层析分离PST及后置柱反应器氧化洗脱生成可检测的稳定的衍生物。此方法具有很高的灵敏度,可以实现高通量检测,并能准确测定出样品中各毒素的成分和含量。其中,HPLC法根据碱性条件下PST被氧化而产生的荧光信号,以二氧化硅为固定相,使用柱后衍生技术进行检测[50],但样品的前处理步骤较繁琐和复杂;LC-MS法结合了色谱和质谱的优点,灵敏度高于HPLC法,不仅可以对已知PST进行定量和定性分析,还可发现未知的毒素,已逐渐发展成为PST的主要检测方法[55,59],但该方法仍存在设备昂贵、标准品较难获得等缺点。

2.3 生物化学检测法

生物化学检测法利用新型的生物传感器技术,采用一种结合特定生物活性物质的识别元件,与样品发生生化反应,将PST浓度转化为电信号,然后通过信号转化和放大,实现对PST的检测[57-58]。此方法检测速度快、特异性好,但存在稳定性差、自动化程度低、使用寿命较短等局限性。

常用的PST检测生物传感器主要包括组织和细胞生物传感器、免疫生物传感器和核酸适配体生物传感器[60-62]。与小鼠生物检测法相比,组织生物传感器的检测结果具有良好的相关性,且检出限更低,但灵敏度不够高、制备及测试过程较为复杂,因而其应用受到一定的限制[63];细胞生物传感器以更为敏感的生物活细胞作为识别元件,而具有更高的对外部刺激的灵敏度,但该方法存在细胞传递和保藏限制、离子通道的不同会产生特异性等一些较难克服的技术问题。近些年,免疫传感器发展迅速,以其组成的方法基于抗原抗体结合反应的免疫学原理[64],采用等离子体共振技术对PST进行定量检测,不仅稳定性高,可实现高通量检测,而且已有越来越多的核酸适配体被筛选出来作为生物传感器的重要元件。与免疫检测法所用的抗体相比,核酸适配体具有更高的亲和力和特异性,并且具有操作简单、费用低廉等优点,但其灵敏度与HPLC、HPLC-MS /MS 等大型仪器分析技术相比仍不够高。

3 PST的研究趋势

3.1 高效脱毒

目前已鉴定出的PST约有30种,它们在化学性质和毒性方面差异很大,这提高了对海产品或饮用水安全法规的制定难度。目前暂无PST特效解毒剂[34],因此对海产品和饮用水的高效脱毒仍需进一步研究。目前PST的脱毒净化方法可分为化学法、物理法和生物法,其中生物法对人体伤害较小,且不会对环境造成二次污染[65],因而其已成为PST脱毒的研究热点[66],壳聚糖、海藻多糖、黏土和活性炭等均可用作PST脱毒的吸附剂[67-68]。此外,对具有降解PST能力的菌株的解毒机理及代谢机制等的研究,以及对生物吸附、微生物代谢等方法的优化或结合,均可能成为未来水产品高效脱毒的研究趋势[65]

3.2 检测方法

PST在世界范围内分布广泛[53],因此仍然非常迫切地需要开发简单、灵敏、经济的分析和检测方法,以加强PST的监测管理,保护世界各地区生态和生命安全。目前,检测的方法正向着多样化、检测速度更快、检测限更低、检测范围更广,以及便携、高通量、具“特异性”的方向发展[69]。在今后PST检测方法的研究中,仍需要在以下几个方向努力:提取和制备PST纯品,为进一步的检测分析提供保证;建立高效、便捷、稳定的多组分集成化检测方法,以实现多组分毒素的同步分析;开发灵敏度高、检测速度快、小型便携的市场化检测产品,以实现精确检测现场样品。随着对PST研究的深入及更多新材料的应用,PST检测方法将不断被优化完善,迈向新的台阶。

3.3 PST富集和转化机制

近年来已发现多种与PST合成相关的基因,如直接参与STX合成的基因sxt Bsxt Dsxt Ssxt U[14]等,但有些基因在合成PST的过程中所发挥的具体作用和PST的生物合成在分子水平上的机制及受环境因素的影响等研究仍需进一步探索。现阶段已鉴定出一些与PST合成相关的蛋白质,如甲硫氨酸S-腺苷转移酶(Methionine S-adenosyltransferase,MAT)、醇脱氢酶(Alcohol dehydrogenase, ADH)等,但这些蛋白质在PST合成过程中的具体作用也尚未明确。此外,研究具有耐PST或降解PST能力菌株的发酵条件、代谢机理、基因克隆表达等,在对微生物制剂的研发等应用中具有广泛的前景[65]。多组学技术的应用为系统性鉴别PST积累转化的关键基因提供了有力的支持,在后续的研究中,应加强新技术、新方法的应用,进一步阐明PST富集和转化过程中的关键基因功能及重要分子途径,为保障水产品质量安全和海水养殖业的持续发展提供支撑。

4 结语

随着人类活动对海洋影响的不断扩大,近海富营养化问题突出,世界范围内赤潮发生频率升高、范围逐渐扩大,PST对人类健康、渔业资源和海洋生态构成了严重威胁。PST成分多且复杂,这使其检测和监管分析较为困难,亟待建立快速便捷、灵敏度高、特异性强的检测方法,未来PST的高效脱毒及其富集转化的关键功能基因和蛋白质仍需被进一步深入研究。在中国沿海地区,许多食用海产品导致的中毒事件均被怀疑与PST有关[70]。为了避免或减少PST的危害,对其监测和防控已经出台了相应的措施,如加大政府科研经费的投入、增加PST的监测对象[9]、将PST监测纳入到食品污染物及有害因素监测等,但现在多以被动应对、事后监管的方式为主,主动防范意识不足[19],因此监管部门可以借鉴国外发达国家的风险预警体系,如建立浮游植物的预警浓度、对养殖生产区PST安全性评价方法等,实现有效监管[9];建立多部门防控管理协作机制,如联合赤潮防治办公室、渔政站、海洋环境监测站、水产养殖、环境保护、卫生监督等有关部门建立PST防控管理体系,实现政府部门之间、专业技术机构之间的信息共享和协调合作,及时采取预防措施,以避免更大规模的PST中毒事件。

参考文献

Wang D, Zhang S, Zhang H, et al.

Omics study of harmful algal blooms in China: current status, challenges, and future perspectives

[J]. Harmful Algae, 2021, 107: 102079.

DOI      URL     [本文引用: 1]

王思远, 张保军, 王昊, .

基于三维荧光的产麻痹性贝毒藻浓度监测研究

[J]. 光谱学与光谱分析, 2021, 41(11): 3480-3485.

[本文引用: 1]

Hess P.

Poisoning caused by marine biotoxins

[J]. Bundesgesundheitsblatt-Gesundheitsforschung-Gesundheitsschutz, 2017, 60(7): 757-760.

DOI      URL     [本文引用: 1]

包振民, 孔令玲, 史姣霞, .

双壳贝类积累转化麻痹性贝毒的研究进展

[J]. 中国海洋大学学报(自然科学版), 2021, 51(10): 1-11.

[本文引用: 1]

杜克梅, 江天久, 吴霓.

黄海海域贝类麻痹性贝类毒素污染状况研究

[J]. 海洋环境科学, 2013, 32(2): 182-184.

[本文引用: 1]

闫鹏, 郑代丰, 章群.

麻痹性贝类毒素分析技术研究进展

[J]. 中国卫生检验杂志, 2021, 31(12): 1532-1536.

[本文引用: 4]

孙烨. 麻痹性贝类毒素细胞检测法的建立与评价[D]. 长沙: 湖南师范大学, 2016.

[本文引用: 1]

Wiese M, D’Agostino P M, Mihali T K, et al.

Neurotoxic alkaloids: saxitoxin and its analogs

[J]. Marine Drugs, 2010, 8(7): 2185-2211.

DOI      PMID      [本文引用: 2]

Saxitoxin (STX) and its 57 analogs are a broad group of natural neurotoxic alkaloids, commonly known as the paralytic shellfish toxins (PSTs). PSTs are the causative agents of paralytic shellfish poisoning (PSP) and are mostly associated with marine dinoflagellates (eukaryotes) and freshwater cyanobacteria (prokaryotes), which form extensive blooms around the world. PST producing dinoflagellates belong to the genera Alexandrium, Gymnodinium and Pyrodinium whilst production has been identified in several cyanobacterial genera including Anabaena, Cylindrospermopsis, Aphanizomenon Planktothrix and Lyngbya. STX and its analogs can be structurally classified into several classes such as non-sulfated, mono-sulfated, di-sulfated, decarbamoylated and the recently discovered hydrophobic analogs--each with varying levels of toxicity. Biotransformation of the PSTs into other PST analogs has been identified within marine invertebrates, humans and bacteria. An improved understanding of PST transformation into less toxic analogs and degradation, both chemically or enzymatically, will be important for the development of methods for the detoxification of contaminated water supplies and of shellfish destined for consumption. Some PSTs also have demonstrated pharmaceutical potential as a long-term anesthetic in the treatment of anal fissures and for chronic tension-type headache. The recent elucidation of the saxitoxin biosynthetic gene cluster in cyanobacteria and the identification of new PST analogs will present opportunities to further explore the pharmaceutical potential of these intriguing alkaloids.

田娟娟, 韩刚, 刘海棠, .

国内外麻痹性贝类毒素风险预警及管控措施的比对分析

[J]. 海洋环境科学, 2019, 38(3): 464-470.

[本文引用: 4]

Etheridge S M.

Paralytic shellfish poisoning: seafood safety and human health perspectives

[J]. Toxicon, 2010, 56(2): 108-122.

DOI      PMID      [本文引用: 4]

Paralytic shellfish poisoning (PSP) is the foodborne illness associated with the consumption of seafood products contaminated with the neurotoxins known collectively as saxitoxins (STXs). This family of neurotoxins binds to voltage-gated sodium channels, thereby attenuating action potentials by preventing the passage of sodium ions across the membrane. Symptoms include tingling, numbness, headaches, weakness and difficulty breathing. Medical treatment is to provide respiratory support, without which the prognosis can be fatal. To protect human health, seafood harvesting bans are in effect when toxins exceed a safe action level (typically 80 microg STX eq 100 g(-1) tissue). Though worldwide fatalities have occurred, successful management and monitoring programs have minimized PSP cases and associated deaths. Much is known about the toxin sources, primarily certain dinoflagellate species, and there is extensive information on toxin transfer to traditional vectors - filter-feeding molluscan bivalves. Non-traditional vectors, such as puffer fish and lobster, may also pose a risk. Rapid and reliable detection methods are critical for toxin monitoring in a wide range of matrices, and these methods must be appropriately validated for regulatory purposes. This paper highlights PSP seafood safety concerns, documented human cases, applied detection methods as well as monitoring and management strategies for preventing PSP-contaminated seafood products from entering the food supply.Published by Elsevier Ltd.

汪宇. 贻贝中麻痹性贝类毒素的来源解析及其形成机制初步研究[D]. 上海: 上海海洋大学, 2021.

[本文引用: 1]

中华人民共和国国家卫生和计划生育委员会. 食品安全国家标准鲜、冻动物性水产品: GB 2733—2015[S]. 北京: 中国标准出版社, 2015.

[本文引用: 1]

刘智勇, 计融.

各国贝类水产品中麻痹性贝类毒素限量标准的比对

[J]. 中国热带医学, 2006, 6(1): 176-178.

[本文引用: 1]

宋维佳, 宋秀贤, 俞志明, .

海洋中麻痹性贝类毒素的合成转化及其影响因素研究进展

[J]. 海洋科学, 2022, 46(9): 117-129.

[本文引用: 3]

刘仁沿, 马德毅, 梁玉波.

赤潮甲藻毒素麻痹性贝毒的生物合成研究进展

[J]. 海洋环境科学, 2004, 23 (4): 71-75.

[本文引用: 2]

Peacock M B, Gibble C M, Senn D B, et al.

Blurred lines: multiple freshwater and marine algal toxins at the land-sea interface of San Francisco Bay, California

[J]. Harmful Algae, 2018, 73: 138-147.

DOI      PMID      [本文引用: 1]

San Francisco Bay (SFB) is a eutrophic estuary that harbors both freshwater and marine toxigenic organisms that are responsible for harmful algal blooms. While there are few commercial fishery harvests within SFB, recreational and subsistence harvesting for shellfish is common. Coastal shellfish are monitored for domoic acid and paralytic shellfish toxins (PSTs), but within SFB there is no routine monitoring for either toxin. Dinophysis shellfish toxins (DSTs) and freshwater microcystins are also present within SFB, but not routinely monitored. Acute exposure to any of these toxin groups has severe consequences for marine organisms and humans, but chronic exposure to sub-lethal doses, or synergistic effects from multiple toxins, are poorly understood and rarely addressed. This study documents the occurrence of domoic acid and microcystins in SFB from 2011 to 2016, and identifies domoic acid, microcystins, DSTs, and PSTs in marine mussels within SFB in 2012, 2014, and 2015. At least one toxin was detected in 99% of mussel samples, and all four toxin suites were identified in 37% of mussels. The presence of these toxins in marine mussels indicates that wildlife and humans who consume them are exposed to toxins at both sub-lethal and acute levels. As such, there are potential deleterious impacts for marine organisms and humans and these effects are unlikely to be documented. These results demonstrate the need for regular monitoring of marine and freshwater toxins in SFB, and suggest that co-occurrence of multiple toxins is a potential threat in other ecosystems where freshwater and seawater mix.Copyright © 2018 The Authors. Published by Elsevier B.V. All rights reserved.

Anderson D M, Cembella A D, Hallegraeff G M.

Progress in understanding harmful algal blooms: paradigm shifts and new technologies for research, monitoring, and management

[J]. Annual Review of Marine Science, 2012, 4: 143-176.

PMID      [本文引用: 1]

The public health, tourism, fisheries, and ecosystem impacts from harmful algal blooms (HABs) have all increased over the past few decades. This has led to heightened scientific and regulatory attention, and the development of many new technologies and approaches for research and management. This, in turn, is leading to significant paradigm shifts with regard to, e.g., our interpretation of the phytoplankton species concept (strain variation), the dogma of their apparent cosmopolitanism, the role of bacteria and zooplankton grazing in HABs, and our approaches to investigating the ecological and genetic basis for the production of toxins and allelochemicals. Increasingly, eutrophication and climate change are viewed and managed as multifactorial environmental stressors that will further challenge managers of coastal resources and those responsible for protecting human health. Here we review HAB science with an eye toward new concepts and approaches, emphasizing, where possible, the unexpected yet promising new directions that research has taken in this diverse field.

Shin C, Jo H, Kim S H, et al.

Exposure assessment to paralytic shellfish toxins through the shellfish consumption in Korea

[J]. Food Research International, 2018, 108: 274-279.

DOI      PMID      [本文引用: 1]

Paralytic shellfish poisoning is caused by saxitoxin and its analogues. The paralytic shellfish toxins (PSTs) are produced by marine dinoflagellates and can be accumulated in filter feeding shellfish, such as mussel, clam, oyster and ark shell. The worldwide regulatory limits for PSTs in shellfish are set at 80 μg STX eq./100 g meat and this is widely accepted as providing adequate public health protection. In this study, we have determined five individual PSTs (STX, GTX1, GTX2, GTX3 and GTX4) in shellfish using LC-MS/MS and assessed the human acute and chronic exposures to PSTs through shellfish consumption. Food consumption data was obtained from the Korea National Health and Nutrition Examination Survey (KNHANES 2010-2015). The acute exposure using a large portion size of 88 g/day (95th percentile for consumers only) with maximum toxin level of 198.7 μg/kg was 0.30 μg/kg bw. Even though we estimated the acute exposure with a conservative manner, it was below the ARfDs (0.5 or 0.7 μg STX eq./kg bw) proposed by the international organizations, representing 43-60% of the ARfDs. The chronic exposures using mean consumption data for whole population with mean concentration of PSTs were ranged from 0.002 to 0.026 μg STX eq./kg bw/day. For consumers only, the chronic exposures were in the range of 0.012-0.128 μg STX eq./kg bw/day.Copyright © 2018 Elsevier Ltd. All rights reserved.

翟毓秀, 郭萌萌, 江艳华, .

贝类产品质量安全风险分析

[J]. 中国渔业质量与标准, 2020, 10(4): 1-25.

[本文引用: 2]

于仁成, 吕颂辉, 齐雨藻, .

中国近海有害藻华研究现状与展望

[J]. 海洋与湖沼, 2020, 51(4): 768-788.

[本文引用: 1]

Fernández B, Campillo J A, Martínez-Gómez C, et al.

Assessment of the mechanisms of detoxification of chemical compounds and antioxidant enzymes in the digestive gland of mussels, Mytilus galloprovincialis, from Mediterranean coastal sites

[J]. Chemosphere, 2012, 87(11): 1235-1245.

DOI      PMID      [本文引用: 1]

In this study the effects of the main marine pollutants (metals, PAHs, PCBs and DDTs) were assessed in native mussels from the Mediterranean coast of Spain. For this purpose several biomarkers such as benzo[a]pyrene hydroxylase (BPH), DT-diaphorase (DTD), glutathione S-transferase (GST), superoxide dismutase (SOD), catalase (CAT), glutathione peroxidases (GPs), glutathione reductase (GR), metallothionein (MT) and lipid peroxidation (LPO) were measured in the digestive gland. Results showed increased LPO levels in mussels which accumulated high loads of organic compounds and arsenic in their tissues. BPH levels correlated to the concentrations of organic compounds in mussel tissues, though the range of BPH response was low in relation to the high gradient of accumulation of organic pollutants. Increased BPH levels, concomitant to low DTD and GST activities, were detected in mussels which presented high levels of organic pollutants in their tissues. This suggests that signs of LPO present in these organisms are related to the imbalance between phase I and phase II biotransformation processes. Furthermore, the increased levels of MT and CAT detected in mussels which showed high levels of Cd in their tissues appear to reflect a coordinated response which protects against the toxicity of this metal. The application of these biomarkers in environmental assessment is discussed.Copyright © 2012 Elsevier Ltd. All rights reserved.

Fernández B, Campillo J A, Martínez-Gómez C, et al.

Antioxidant responses in gills of mussel (Mytilus galloprovincialis) as biomarkers of environmental stress along the Spanish Mediterranean coast

[J]. Aquatic Toxicology, 2010, 99(2): 186-197.

DOI      PMID      [本文引用: 1]

Antioxidant response was used to assess the effects of the main pollutants in wild mussels (Mytilus galloprovincialis) along the Mediterranean coast of Spain. Antioxidant enzyme activities - those of catalase, superoxide dismutase, glutathione peroxidases, glutathione reductase, glutathione S-transferase and DT-diaphorase - as well as lipid peroxidation and metallothionein concentrations were measured in gills of mussels from 16 selected sites. Furthermore, concentrations of the main contaminants (Hg, Pb, Cd, Cu, Zn, As, PAH, PCB, and DDT) were quantified in mussel tissue, and environmental parameters were measured in water samples collected at each site. Results showed that the glutathione-dependent antioxidant enzymes offered an increased and coordinated response against metal (Hg, Pb and Cd) contamination. These enzymatic activities correlated positively to temperature, suggesting the influence of this environmental parameter on antioxidant responses in gill tissues. Furthermore, although temperature did not reach stressful levels in the study area, it seemed to add a synergistic effect to that produced by metals to induce antioxidant enzymes in the most metal-polluted sites. Catalase activity appeared to be involved in a different antioxidant pathway, more related to organic pollutant bioaccumulation, offering an efficient protection mechanism against reactive oxygen species generation due both to organic exposure and high physiological activity, reflected by high condition indices. In general terms, increased levels of antioxidant enzymes at some sites suffering from metal and organic pollution indicated a situation of oxidative stress that nevertheless did not appear to be harmful, since lipid peroxidation levels showed no peroxidative damage in gill tissues of mussels collected from even the most heavily polluted sites. On the other hand, metallothionein and DT-diaphorase did not reflect pollutant exposure and seemed to be more influenced by environmental variables than by the pollutants.(c) 2010 Elsevier B.V. All rights reserved.

Catterall W A.

The molecular basis of neuronal excitability

[J]. Science, 1984, 223(4637): 653-661.

PMID      [本文引用: 1]

Neurons process and transmit information in the form of electrical signals. Their electrical excitability is due to the presence of voltage-sensitive ion channels in the neuronal plasma membrane. In recent years, the voltage-sensitive sodium channel of mammalian brain has become the first of these important neuronal components to be studied at the molecular level. This article describes the distribution of sodium channels among the functional compartments of the neuron and reviews work leading to the identification, purification, and characterization of this membrane glycoprotein.

Catterall W A.

From ionic currents to molecular mechanisms: the structure and function of voltage-gated sodium channels

[J]. Neuron, 2000, 26(1): 13-25.

DOI      PMID      [本文引用: 1]

Catterall W A, Cestèle S, Yarov-Yarovoy V, et al.

Voltage-gated ion channels and gating modifier toxins

[J]. Toxicon, 2007, 49(2): 124-141.

DOI      PMID      [本文引用: 1]

Voltage-gated sodium, calcium, and potassium channels generate electrical signals required for action potential generation and conduction and are the molecular targets for a broad range of potent neurotoxins. These channels are built on a common structural motif containing six transmembrane segments and a pore loop. Their pores are formed by the S5/S6 segments and the pore loop between them, and they are gated by bending of the S6 segments at a hinge glycine or proline residue. The voltage sensor domain consists of the S1-S4 segments, with positively charged residues in the S4 segment serving as gating charges. The diversity of toxin action on these channels is illustrated by sodium channels, which are the molecular targets for toxins that act at six or more distinct receptor sites on the channel protein. Both hydrophilic low molecular weight toxins and larger polypeptide toxins physically block the pore and prevent sodium conductance. Hydrophobic alkaloid toxins and related lipid-soluble toxins act at intramembrane sites and alter voltage-dependent gating of sodium channels via an allosteric mechanism. In contrast, polypeptide toxins alter channel gating by voltage-sensor trapping through binding to extracellular receptor sites, and this toxin interaction has now been modeled at the atomic level for a beta-scorpion toxin. The voltage-sensor trapping mechanism may be a common mode of action for polypeptide gating modifier toxins acting on all of the voltage-gated ion channels.

Kang H M, Lee J, Lee Y J, et al.

Transcriptional and toxic responses to saxitoxin exposure in the marine copepod Tigriopus japonicus

[J]. Chemosphere, 2022, 309: 136464.

DOI      URL     [本文引用: 1]

Akbar M A, Mohd Yusof N Y, Tahir, N I, et al.

Biosynthesis of saxitoxin in marine dinoflagellates: an omics perspective

[J]. Marine Drugs, 2020, 18(2): 103.

DOI      URL     [本文引用: 1]

Saxitoxin is an alkaloid neurotoxin originally isolated from the clam Saxidomus giganteus in 1957. This group of neurotoxins is produced by several species of freshwater cyanobacteria and marine dinoflagellates. The saxitoxin biosynthesis pathway was described for the first time in the 1980s and, since then, it was studied in more than seven cyanobacterial genera, comprising 26 genes that form a cluster ranging from 25.7 kb to 35 kb in sequence length. Due to the complexity of the genomic landscape, saxitoxin biosynthesis in dinoflagellates remains unknown. In order to reveal and understand the dynamics of the activity in such impressive unicellular organisms with a complex genome, a strategy that can carefully engage them in a systems view is necessary. Advances in omics technology (the collective tools of biological sciences) facilitated high-throughput studies of the genome, transcriptome, proteome, and metabolome of dinoflagellates. The omics approach was utilized to address saxitoxin-producing dinoflagellates in response to environmental stresses to improve understanding of dinoflagellates gene–environment interactions. Therefore, in this review, the progress in understanding dinoflagellate saxitoxin biosynthesis using an omics approach is emphasized. Further potential applications of metabolomics and genomics to unravel novel insights into saxitoxin biosynthesis in dinoflagellates are also reviewed.

Stevens M, Peigneur S, Tytgat J.

Neurotoxins and their binding areas on voltage-gated sodium channels

[J]. Frontiers in Pharmacology, 2011, 2:71.

DOI      PMID      [本文引用: 1]

Voltage-gated sodium channels (VGSCs) are large transmembrane proteins that conduct sodium ions across the membrane and by doing so they generate signals of communication between many kinds of tissues. They are responsible for the generation and propagation of action potentials in excitable cells, in close collaboration with other channels like potassium channels. Therefore, genetic defects in sodium channel genes can cause a wide variety of diseases, generally called "channelopathies." The first insights into the mechanism of action potentials and the involvement of sodium channels originated from Hodgkin and Huxley for which they were awarded the Nobel Prize in 1963. These concepts still form the basis for understanding the function of VGSCs. When VGSCs sense a sufficient change in membrane potential, they are activated and consequently generate a massive influx of sodium ions. Immediately after, channels will start to inactivate and currents decrease. In the inactivated state, channels stay refractory for new stimuli and they must return to the closed state before being susceptible to a new depolarization. On the other hand, studies with neurotoxins like tetrodotoxin (TTX) and saxitoxin (STX) also contributed largely to our today's understanding of the structure and function of ion channels and of VGSCs specifically. Moreover, neurotoxins acting on ion channels turned out to be valuable lead compounds in the development of new drugs for the enormous range of diseases in which ion channels are involved. A recent example of a synthetic neurotoxin that made it to the market is ziconotide (Prialt(®), Elan). The original peptide, ω-MVIIA, is derived from the cone snail Conus magus and now FDA/EMA-approved for the management of severe chronic pain by blocking the N-type voltage-gated calcium channels in pain fibers. This review focuses on the current status of research on neurotoxins acting on VGSC, their contribution to further unravel the structure and function of VGSC and their potential as novel lead compounds in drug development.

O’Neill K, Musgrave I F, Humpage A.

Low dose extended exposure to saxitoxin and its potential neurodevelopmental effects: a review

[J]. Environmental Toxicology and Pharmacology, 2016, 48: 7-16.

DOI      PMID      [本文引用: 1]

Saxitoxin (STX) and its analogs, the paralytic shellfish toxins (PSTs), are a group of potent neurotoxins well known for their role in acute paralytic poisoning by preventing the generation of action potentials in neuronal cells. They are found in both marine and freshwater environments globally and although acute exposure from the former has previously received more attention, low dose extended exposure from both sources is possible and to date has not been investigated. Given the known role of cellular electrical activity in neurodevelopment this pattern of exposure may be a significant public health concern. Additionally, the presence of PSTs is likely to be an ongoing and possibly increasing problem in the future. This review examines the neurodevelopmental toxicity of STX, the risk of extended or repeated exposure to doses with neurodevelopmental effects, the potential implications of this exposure and briefly, the steps taken and difficulties faced in preventing exposure.Copyright © 2016 Elsevier B.V. All rights reserved.

Noda M, Suzuki H, Numa S, et al.

A single point mutation confers tetrodotoxin and saxitoxin insensitivity on the sodium channel Ⅱ

[J]. FEBS Letters, 1989, 259(1): 213-216.

PMID      [本文引用: 1]

A single point mutation of the rat sodium channel II reduces its sensitivity to tetrodotoxin and saxitoxin by more than three orders of magnitude. The mutation replaces glutamic acid 387 with a glutamine and has only slight effects on the macroscopic current properties, as measured under voltage-clamp in Xenopus oocytes injected with the corresponding cDNA-derived mRNA.

Terlau H, Heinemann S H, Stühmer W, et al.

Mapping the site of block by tetrodotoxin and saxitoxin of sodium channel Ⅱ

[J]. FEBS Letters, 1991, 293(1-2): 93-96.

PMID      [本文引用: 1]

The SS2 and adjacent regions of the 4 internal repeats of sodium channel II were subjected to single mutations involving, mainly, charged amino acid residues. These sodium channel mutants, expressed in Xenopus oocytes by microinjection of cDNA-derived mRNAs, were tested for sensitivity to tetrodotoxin and saxitoxin and for single-channel conductance. The results obtained show that mutations involving 2 clusters of predominantly negatively charged residues, located at equivalent positions in the SS2 segment of the 4 repeats, strongly reduce toxin sensitivity, whereas mutations of adjacent residues exert much smaller or no effects. This suggests that the 2 clusters of residues, probably forming ring structures, take part in the extracellular mouth and/or the pore wall of the sodium channel. This view is further supported by our finding that all mutations reducing net negative charge in these amino acid clusters cause a marked decrease in single-channel conductance.

Llewellyn L E.

Saxitoxin, a toxic marine natural product that targets a multitude of receptors

[J]. Natural Product Reports, 2006, 23(2): 200-222.

PMID      [本文引用: 1]

Saxitoxin (STX) was discovered early last century and can contaminate seafood and drinking water, and over time has become an invaluable research tool and an internationally regulated chemical weapon. Among natural products, toxins obtain a unique reputation from their high affinity and selectivity for their target pharmacological receptor, which for STX has long been considered to only be the voltage gated sodium channel. In recent times however, STX has been discovered to also bind to calcium and potassium channels, neuronal nitric oxide synthase, STX metabolizing enzymes and two circulatory fluid proteins, namely a transferrin-like family of proteins and a unique protein found in the blood of pufferfish.

Shumway S E.

A review of the effects of algal blooms on shellfish and aquaculture

[J]. Journal of the World Aquaculture Society, 1990, 21(2): 65-104.

DOI      URL     [本文引用: 1]

呼晓群, 解万翠, 李敏, .

贝类中麻痹性贝类毒素的蓄积及代谢研究进展

[J]. 食品与机械, 2021, 37(3): 187-194.

[本文引用: 3]

江天久, 尹伊伟, 骆育敏, .

大亚湾和大鹏湾麻痹性贝类毒素动态分析

[J]. 海洋环境科学, 2000, 19(2): 1-5.

[本文引用: 2]

Terrazas J O, Contreras H R, García C.

Prevalence, variability and bioconcentration of saxitoxin-group in different marine species present in the food chain

[J]. Toxins, 2017, 9(6): 190.

DOI      URL     [本文引用: 2]

Navarro J M, González K, Cisternas B, et al.

Contrasting physiological responses of two populations of the razor clam Tagelus dombeii with different histories of exposure to paralytic shellfish poisoning (PSP)

[J]. PLoS One, 2014, 9(8): e105794.

DOI      URL     [本文引用: 1]

Li A, Ma J, Cao J, et al.

Analysis of paralytic shellfish toxins and their metabolites in shellfish from the North Yellow Sea of China

[J]. Food Additives & Contaminants: Part A, 2012, 29(9): 1455-1464.

[本文引用: 1]

García C, Barriga A, Díaz J C, et al.

Route of metabolization and detoxication of paralytic shellfish toxins in humans

[J]. Toxicon, 2010, 55(1): 135-144.

DOI      PMID      [本文引用: 1]

Paralytic shellfish toxins (PST) are a collection of over 26 structurally related imidazoline guanidinium derivatives produced by marine dinoflagellates and freshwater cyanobacteria. Glucuronidation of drugs by UDP-glucuronosyltransferase (UGT) is the major phase II conjugation reaction in mammalian liver. In this study, using human liver microsomes, the in vitro paralytic shellfish toxins oxidation and sequential glucuronidation are achieved. Neosaxitoxin (neoSTX), Gonyautoxin 3/2 epimers (GTX3/GTX2) and Saxitoxin (STX) are used as starting enzymatic substrates. The enzymatic reaction final product metabolites are identified by using HPLC-FLD and HPLC/ESI-IT/MS. Four metabolites from GTX3/GTX2 epimers precursors, three of neoSTX and two of STX are clearly identified after incubating with UDPGA/NADPH and fresh liver microsomes. The glucuronic-Paralytic Shellfish Toxins were completely hydrolysed by treatment with beta-glucuronidase. All toxin analogs were identified comparing their HPLC retention time with those of analytical standard reference samples and further confirmed by HPLC/ESI-IT/MS. Paralytic Shellfish Toxins (PST) were widely metabolized by human microsomes and less than 15% of the original PST, incubated as substrate, stayed behind at the end of the incubation. The apparent V(max) and Km formation values for the respective glucuronides of neoSTX, GTX3/GTX2 epimers and STX were determined. The V(max) formation values for Glucuronic-GTX3 and Glucuronic-GTX2 were lower than Glucuronic-neoSTX and Glucuronic-STX (6.8+/-1.9x10(-3); 8.3+/-2.8x10(-3) and 9.7+/-2.8x10(-3)pmol/min/mg protein respectively). Km of the glucuronidation reaction for GTX3/GTX2 epimers was less than that of glucuronidation of neoSTX and STX (20.2+/-0.12; 27.06+/-0.23 and 32.02+/-0.64microM respectively). In conclusion, these data show for the first time, direct evidence for the sequential oxidation and glucuronidation of PST in vitro, both being the initial detoxication reactions for the excretion of these toxins in humans. The PST oxidation and glucuronidation pathway showed here, is the hepatic conversion of its properly glucuronic-PST synthesized, and the sequential route of PST detoxication in human.

邱江兵. 双壳贝类对麻痹性贝毒的代谢转化及其生理生化响应[D]. 青岛: 中国海洋大学, 2014.

[本文引用: 1]

Blanco J, Reyero M I, Franco J.

Kinetics of accumulation and transformation of paralytic shellfish toxins in the blue mussel Mytilus galloprovincialis

[J]. Toxicon, 2003, 42(7): 777-784.

PMID      [本文引用: 1]

Mussels (Mytilus galloprovincialis) were fed cultures of the Paralytic Shellfish Poisoning agent Alexandrium minutum (Strain AL1V) for a 15-day period and, for the next 12 days, they were fed the non-toxic species Tetraselmis suecica, in order to monitor the intoxication/detoxification process. The toxin content in the bivalve was checked daily throughout the experiment. During the time-course of the experiment, the toxin profile of the bivalves changed substantially, showing increasingly greater differences from the proportions found in the toxigenic dinoflagellate used as food. The main processes involved in the accumulation of toxins and in the variation of the toxic profiles were implemented in a series of numerical models and the usefulness of those models to describe the actual intoxication/detoxification kinetics was assessed. Models that did not include transformations between toxins were unable to describe the kinetics, even when different detoxification rates were allowed for the toxins involved. The models including epimerization and reduction provided a good description of the kinetics whether or not differential detoxification was allowed for the different toxins, suggesting that the differences in detoxification rates between the toxins are not an important factor in regulating the change of the toxic profile. The implementation of Michaelis-Menten kinetics to describe the two reductive transformations produced a model that had a poorer fit to the data observed than the model that included only a first order kinetics. This suggests that, it is very unlikely that any enzymatic reaction is involved in the reduction of the hydroxycarbamate (OH-GTXs) to carbamate (H-GTXs) gonyautoxins.

Kotaki Y.

Screening of bacteria which convert gonyautoxin 2, 3 to saxitoxin

[J]. Nippon Suisan Gakkaishi, 1989, 55(7): 1293-1293.

DOI      URL     [本文引用: 1]

Kotaki Y, Oshima Y, Yasumoto T.

Bacterial transformation of paralytic shellfish toxins in coral-reef crabs and a marine snail

[J]. Nippon Suisan Gakkaishi, 1985, 51(6): 1009-1013.

DOI      URL     [本文引用: 2]

Sullivan J.

Paralytic shellfish poisoning: analytical and biochemical investigations

[J]. ИНФОРМАЦИЯ О ПУБЛИКАЦИИ, 1983, 1:7381772.

[本文引用: 1]

Shimizu Y, Yoshioka M.

Transformation of paralytic shellfish toxins as demonstrated in scallop homogenates

[J]. Science, 1981, 212(4494): 547-549.

PMID      [本文引用: 1]

Toxins in shellfish, which are responsible for paralytic poisonings, undergo reductive transformation when incubated with the homogenate of various portions of the scallop, Placopecten magellanicus. The transformation includes the reductive elimination of O-sulfate groups, a change that is most evident in the locomotor tissue homogenates. The commercially important adductor muscles can also inactivate the toxins.

Jones G J, Bourne D G, Blakeley R L, et al.

Degradation of the cyanobacterial hepatotoxin microcystin by aquatic bacteria

[J]. Natural Toxins, 1994, 2(4): 228-235.

PMID      [本文引用: 1]

Bacterial degradation of the cyanobacterial cyclic peptide hepatotoxin microcystin was confirmed in natural waters and by isolated laboratory strains. Degradation of 1 mg L-1 microcystin LR typically began 2-8 days after addition to surface water samples. At concentrations greater than 1 mg L-1 there was an initial slow removal of microcystin LR, rather than a distinct lag (or conditioning) phase, before rapid degradation commenced. The lag phase was absent upon re-addition of microcystin LR to the water. Both single strains and mixed bacterial cultures capable of degrading microcystin LR were isolated from surface water samples. One single strain isolated was a gram-negative rod and appeared to be a Pseudomonas sp., although standard taxonomic tests have given inconclusive results. Degradative activity was mostly intracellular and equally active against microcystin LR and RR, but not against nodularin.

Smith E A, Grant F, Ferguson C M, et al.

Biotransformations of paralytic shellfish toxins by bacteria isolated from bivalve molluscs

[J]. Applied and Environmental Microbiology, 2001, 67(5): 2345-2353.

PMID      [本文引用: 1]

Due to the possibility that bacteria could be involved in the clearance of paralytic shellfish toxins (PST) from bivalve molluscs, investigations into which, if any, bacteria were able to grow at the expense of PST focused on several common shellfish species. These species were blue mussels, oysters, razor fish, cockles, and queen and king scallops. Bacteria associated with these shellfish were isolated on marine agar 2216 and characterized by their carbon utilization profiles (BIOLOG). Selected isolates from groups demonstrating 90% similarity were screened for their ability to metabolize a range of PST (gonyautoxins 1 and 4 [GTX 1/4], GTX 2/3, GTX 5, saxitoxin, and neosaxitoxin) using a novel screening method and confirming its results by high-performance liquid chromatography. Results suggest that molluscan bacteria have different capacities to utilize and transform PST analogues. For example, isolates M12 and R65 were able to reductively transform GTX 1/4 with concomitant production of GTX 2/3, while isolate Q5 apparently degraded GTX 1/4 without the appearance of other GTXs. Other observed possible mechanisms of PST transformations include decarbamoylation by isolate M12 and sulfation of GTXs by isolates Q5, R65, M12, and C3. These findings raise questions as to the possible role of bacteria resident in the shellfish food transport system. Some researchers have suggested that the microflora play a role in supplying nutritional requirements of the host. This study demonstrates that bacteria may also be involved in PST transformation and elimination in molluscan species.

Lee N S, Kim B T, Kim D H, et al.

Purification and reaction mechanism of arylsulfate sulfotransferase from Haemophilus K-12, a mouse intestinal bacterium

[J]. The Journal of Biochemistry, 1995, 118(4): 796-801.

DOI      URL     [本文引用: 1]

周磊, 杨宪立, 武爱波, .

麻痹性贝类毒素的安全评价与检测技术研究进展

[J]. 世界科技研究与发展, 2014, 36(3):336-342.

[本文引用: 1]

Tan K, Ransangan J.

Factors influencing the toxicity, detoxification and biotransformation of paralytic shellfish toxins

[J]. Reviews of Environmental Contamination and Toxicology, 2015, 235: 1-25.

DOI      PMID      [本文引用: 3]

黄宗锈, 林健, 陈冠敏, .

麻痹性贝类毒素小鼠生物法检测中位数法与均数法差异性比较

[J]. 中国卫生检验杂志, 2008, 18(2): 369-370.

[本文引用: 1]

朱敬萍, 金雷, 张小军, .

小鼠生物法检测麻痹性贝类毒素技术探讨及应用

[J]. 中国渔业质量与标准, 2017, 7(2): 30-35.

[本文引用: 1]

丁君.

赤潮毒素中腹泻性贝毒和麻痹性贝毒的研究及进展

[J]. 大连水产学院学报, 2001, 16(3): 212-218.

[本文引用: 3]

黄奕雯.

石房蛤毒素胶体金快速检测试纸卡的应用研究

[J]. 渔业研究, 2020, 42(6): 614-621.

[本文引用: 1]

麻痹性贝类毒素是世界范围内分布最广、危害最大的一类赤潮生物毒素,其主要毒素 为石房蛤毒素。本研究对一种石房蛤毒素胶体金快速检测试纸卡进行了实际应用测试。经试 验,该试纸卡在贝类产品中具有普遍适用性,对石房蛤毒素的检测限为500 ug/kg。同时, 用试纸卡对30个不同贝类实际样品中的石房蛤毒素进行检测,结果与液相色谱-串联质谱 法完全一致,单个样品检测耗时约20 min。结果表明,该试纸卡具有较高的灵敏度和特异性,操作便捷、稳定可靠,能够满足现场检测需要,可供基层监管部门开展麻痹性贝毒快速 检测筛查工作,对提高赤潮期间贝类质量安全风险防控能力具有重要意义。

黄爱君, 黄海燕, 刘建军.

麻痹性和腹泻性贝类毒素的检测方法研究进展

[J]. 环境与健康杂志, 2010, 27(1): 84-86.

[本文引用: 3]

杜伟, 王扬, 张晓辉, .

小鼠生物法与ELISA法检测麻痹性贝类毒素的比较

[J]. 浙江农业科学, 2015, 56(11): 1726-1728.

[本文引用: 1]

汤云瑜, 黄冬梅, 蔡友琼.

麻痹性贝类毒素检测技术研究

[J]. 农产品质量与安全, 2020(6): 29-34.

[本文引用: 2]

张杭君, 张建英.

麻痹性贝毒素的毒理效应及检测技术

[J]. 海洋环境科学, 2003, 22(4): 76-80.

[本文引用: 2]

杨云辉.

HPLC-MS/MS法检测福建中部海域养殖贝类麻痹性贝类毒素

[J]. 渔业研究, 2020, 42(5): 473-480.

[本文引用: 1]

实验采用高效液相色谱-串联质谱法(HPLC-MS/MS)检测2017—2018年福建中部海域养殖贝类麻痹性贝类毒素(PSTs)。结果表明:2018年采集的贝类样本均未检出麻痹性贝类毒素,2017年采集的贝类样本有17批次检出麻痹性贝类毒素,主要检出成分为脱氨甲酰基石房蛤毒素(dcSTX)、膝沟藻毒素(GTX1、GTX2、GTX3、GTX4、GTX5),脱氨甲酰基膝沟藻毒素(dcGTX2、dcGTX3)也占有一定比例,未发现石房蛤毒素(STX)。2017年福建中部海域链状裸甲藻(Gymnodinium catenatum)暴发事件对该海域养殖贝类的麻痹性贝类毒素有一定影响,其中有毒赤潮对贻贝的影响大于牡蛎,而对缢蛏和蛤类则无影响。

Deng Y, Zheng H, Yi X, et al.

Paralytic shellfish poisoning toxin detection based on cell-based sensor and non-linear signal processing model

[J]. International Journal of Food Properties, 2019, 22(1): 890-897.

DOI      URL     [本文引用: 1]

Ferreira N S, Cruz M G N, Gomes M T S R, et al.

Potentiometric chemical sensors for the detection of paralytic shellfish toxins

[J]. Talanta, 2018, 181: 380-384.

DOI      PMID      [本文引用: 1]

Potentiometric chemical sensors for the detection of paralytic shellfish toxins have been developed. Four toxins typically encountered in Portuguese waters, namely saxitoxin, decarbamoyl saxitoxin, gonyautoxin GTX5 and C1&C2, were selected for the study. A series of miniaturized sensors with solid inner contact and plasticized polyvinylchloride membranes containing ionophores, nine compositions in total, were prepared and their characteristics evaluated. Sensors displayed cross-sensitivity to four studied toxins, i.e. response to several toxins together with low selectivity. High selectivity towards paralytic shellfish toxins was observed in the presence of inorganic cations with selectivity coefficients ranging from 0.04 to 0.001 for Na and K and 3.6*10 to 3.4*10 for Ca. Detection limits were in the range from 0.25 to 0.9 μmolL for saxitoxin and decarbamoyl saxitoxin, and from 0.08 to 1.8 μmolL for GTX5 and C1&C2, which allows toxin detection at the concentration levels corresponding to the legal limits. Characteristics of the developed sensors allow their use in the electronic tongue multisensor system for simultaneous quantification of paralytic shellfish toxins.Copyright © 2018 Elsevier B.V. All rights reserved.

Li H, Wei X, Gu C, et al.

A dual functional cardiomyocyte-based hybrid-biosensor for the detection of diarrhetic shellfish poisoning and paralytic shellfish poisoning toxins

[J]. Analytical Sciences, 2018, 34(8): 893-900.

DOI      PMID      [本文引用: 1]

Okadaic acid (OA) and saxitoxin (STX) are typical toxins of diarrhetic shellfish poisoning (DSP) and paralytic shellfish poisoning (PSP), respectively, which are highly toxic marine toxins threatening human health and environmental safety. OA is a potent inhibitor of serine/threonine protein phosphatases that can cause cellular death, while STX is an inhibitor of sodium channel that can lead to neurological damage. In this work, a dual functional cardiomyocyte-based biosensor was proposed to detect DSP and PSP toxins by monitoring the viability and electrophysiology of cardiomyocytes. The results showed that the viability of cardiomyocytes was sensitive to the OA and STX, resulting in significant changes of the electrophysiological properties, including amplitude, firing rate and duration of the extracellular field potential (EFP). The detection limits of the hybrid-biosensor are as low as 7.16 ng/mL for OA and 5.19 ng/mL for STX. In summary, all of the results indicate that the dual functional cardiomyocyte-based hybrid-biosensor will be a promising and utility tool for shellfish toxin detection.

Campàs M, Marty J L.

Enzyme sensor for the electrochemical detection of the marine toxin okadaic acid

[J]. Analytica Chimica Acta, 2007, 605(1): 87-93.

PMID      [本文引用: 1]

An enzyme sensor for the electrochemical detection of the marine toxin okadaic acid (OA) has been developed. The strategy was based on the inhibition of immobilised protein phosphatase (PP2A) by this toxin and the electrochemical measurement of the enzyme activity by the use of appropriate enzyme substrates, electrochemically active after dephosphorylation by the enzyme. Colorimetric inhibition assays have demonstrated the PP2A from human red blood cells to be more sensitive and to provide a wider linear range than the one produced by genetic engineering. Catechyl monophosphate (CMP) and p-aminophenyl phosphate (p-APP) have been tested as enzyme substrates, the former providing higher electrochemical currents at convenient working potentials (+450 mV vs. Ag/AgCl). Biosensors with 19.1 and 5.0 U of immobilised enzyme have been applied to the OA detection. Whereas the 19.1-U biosensor has provided higher electrochemical currents and more reliable determinations, the 5.0-U one has attained a lower 50% inhibition coefficient (IC50) value (22.19 in front of 154.84 microg L(-1)) and a larger working range (2.69-171.87 in front of 42.97-171.87 microg L(-1)). The analysis of toxicogenic dinoflagellate extracts with both biosensors and the comparison with the colorimetric assay and liquid chromatography coupled to tandem mass spectrometry (LC-MS/MS) have demonstrated the applicability of the developed electrochemical devices as screening biotools for the assessment of the toxicity of a sample.

Campàs M, Prieto-Simón B, Marty J L.

Biosensors to detect marine toxins: assessing seafood safety

[J]. Talanta, 2007, 72(3): 884-895.

DOI      PMID      [本文引用: 1]

This article describes the different types of marine toxins and their toxic effects, and reviews the bio/analytical techniques for their detection, putting special emphasis to biosensors. Important health concerns have recently appeared around shellfish (diarrheic, paralytic, amnesic, neurologic and azaspiracid) and fish (ciguatera and puffer) poisonings produced by different types of phycotoxins, making evident the urgent necessity of counting on appropriate detection technologies. With this purpose, several analysis methods (bioassays, chromatographic techniques, immunoassays and enzyme inhibition-based assays) have been developed. However, easy-to-use, fast and low-cost devices, able to deal with complicated matrices, are still required. Biosensors offer themselves as promising biotools, alternative and/or complementary to conventional analysis techniques, for fast, simple, cheap and reliable toxicity screening. Nevertheless, despite the wide range of seafood toxins and the already rooted biosensing systems, the literature on biosensors for phycotoxins is scarce. This article discusses the existing biosensor-based strategies and their advantages and limitations. Finally, the article gives a general overlook about the regulation toxin levels and monitoring programmes currently established around the world concerning seafood safety.

张庆芳, 韩鹏飞, 谢丹丹, .

海洋降解麻痹性贝类毒素细菌的筛选及其耐毒能力初探

[J]. 饲料博览, 2021(10): 5-10.

[本文引用: 3]

Reboreda A, Lago J, Chapela M J, et al.

Decrease of marine toxin content in bivalves by industrial processes

[J]. Toxicon, 2010, 55(2-3): 235-243.

DOI      PMID      [本文引用: 1]

Harmful algal blooms cause important economical losses due to the accumulation of toxins in shellfish. Natural detoxification occurs but this mechanism is very slow in most cases. The achievement of a method for the rapid detoxification of commercial bivalves would be very interesting for the shellfish harvesting sector in order to diminish economical losses due to harvesting areas closure. In this work, four different methods easily applicable in the food industry (freezing, evisceration, ozonization and thermal processing) were studied to gain the detoxification of four species of bivalves (mussels, scallops, clams and cockles) contaminated with the three main types of toxins (ASP, DSP, PSP). Results show that for ASP a significant decrease of the toxin levels below the legal limit (20 microg/g) is achieved by using hepatopancreas ablation or combination of simple steps (evisceration and/or thermal processing/and or freezing). In our hands, PSP toxin levels are sharply decreased under the limit of detection (35 microg STX eq/100g) after a thermal processing, inducing percentages of detoxification higher than 50%. The effect of freezing on the levels of PSP is very dependent on the matrix studied. DSP toxins are not significantly reduced with none of these methods.Copyright 2009 Elsevier Ltd. All rights reserved.

Xie W C, Liu X L, Yang X H, et al.

Accumulation and depuration of paralytic shellfish poisoning toxins in the oyster Ostrea rivularis Gould-chitosan facilitates the toxin depuration

[J]. Journal of Food Control, 2013, 30(2): 446-452.

DOI      URL     [本文引用: 1]

Li J, Song X X, Zhang Y, et al.

Effect of modified clay on the transition of paralytic shellfish toxins within the bay scallop Argopecten irradians and sediments in laboratory trials

[J]. Aquaculture, 2019, 505: 112-117.

DOI      URL     [本文引用: 1]

Qiu J B, Fan H, Liu T, et al.

Application of activated carbon to accelerate detoxification of paralytic shellfish toxins from mussels Mytilus galloprovincialis and scallops Chlamys farreri

[J]. Ecotoxicology and Environmental Safety, 2018, 148: 402-409.

DOI      URL     [本文引用: 1]

吴益春, 郭海波, 罗海军, .

海产品中麻痹性贝类毒素快速检测技术研究进展

[J]. 食品安全质量检测学报, 2019, 10(8): 2092-2096.

[本文引用: 1]

于仁成, 罗璇.

我国近海有毒藻和藻毒素的研究现状与展望

[J]. 海洋科学集刊, 2016(1): 155-166.

/