利用蛋白磷酸酶活力抑制法检测牡蛎体内的腹泻性贝毒

基于腹泻性贝毒(Diarrhetic Shellfish Poison,DSP)中大田软海绵酸(Okadaic acid,OA)和鳍藻毒素(Dinophysis toxins,DTXs)能够抑制蛋白磷酸酶活力的特点,人们建立了一种利用碱性蛋白磷酸酶活力变化检测贝类中大田软海绵酸毒性当量的生物化学测试方法。本实验利用该方法对威海出入境检验检疫局采集的3个牡蛎样品进行分析,结果表明:3个牡蛎样品中不含有OA和DTXs毒素,但水解后可检出OA毒性,其中两个牡蛎水解样品的毒性当量分别为1.81和1.21μg OA eq./kg贝组织(湿重)。     

液相色谱-串联质谱法检测贝类产品中腹泻性贝类毒素

建立了贝类组织中2种腹泻性贝毒(Diamletic shellfish Poisobing,DSP)聚醚类毒素-大田软海绵酸(Okadaic acid,OA)和鳍藻毒素(Dinophysistoxin-1,DTX-1)的高效液相色谱-串联质谱分析方法.贝类样品经80%甲醇溶液提取,经正己烷脱脂和HLB固相萃取柱净化,采...     

石墨烯-管尖固相萃取-液相色谱-串联质谱法测定贝类中10种脂溶性贝类毒素

以石墨烯为吸附剂，制作了石墨烯-管尖固相萃取装置，结合液相色谱-串联质谱，建立了一种同时测定贝类中10种脂溶性贝类毒素的方法。实验对提取剂、石墨烯的用量、淋洗剂的种类和用量、洗脱剂的种类和用量等实验参数进行了详细优化。在最优的实验条件下，10种脂溶性贝类毒素在各自相应浓度范围内线性良好，相关系数均大于0.99，方法检出限（LOD）和定量限（LOQ）分别在0.1~1.1 μg/kg和0.3~3.2 μg/kg之间；对阴性牡蛎样品进行3个水平的加标回收实验，10种脂溶性贝类毒素的回收率在72.0%~101.2%之间，相对标准偏差小于15%。结果表明，该方法灵敏度高，操作简单高效，适用于贝类水产品中脂溶性贝类毒素的检测分析。     

麻痹性贝类毒素标准样品的研制

将麻痹性贝类毒素阳性的新鲜扇贝去壳后取贝肉,经过匀浆,冷冻干燥等步骤制备成冻干粉,然后进行均匀性和稳定性检验,结果表明,制备后的样品均匀,稳定,满足标准样品的要求。以多家实验室定值的方式对该标准样品进行定值,定值结果为（589±42）MU／g（k=-2）。该标准样品可用于麻痹性贝类毒素检测过程的方法验证与质量控制。     

液相色谱-高分辨质谱测定贝类中的4种贝毒素及16种兽药残留

建立了贝类组织中米氏裸甲藻贝毒素(Gymnodimine,GYM)、螺环内酯毒素(Spirolides,SPX1)、大田软骨酸贝毒素(Okadaic acid,OA-C)、蛤毒素(Pectenotoxins,PTX2)4种腹泻性贝类毒素、氯霉素、氟甲砜霉素以及14种磺胺类药物的液相色谱-高分辨质谱分析方法。样品采用甲醇提取,正己烷去除脂肪,乙酸乙酯反萃取,ODS粉分散固相萃取净化,经Agilent ZORBAX SB-C18色谱柱(3.0 mm×100 mm,1.8μm)分离,高分辨质谱仪进行检测。结果表明,各化合物在一定的质量浓度范围内线性良好,相关系数(r)均大于0.99。GYM,SPX1,OA-C,PTX2 4种腹泻性贝类毒素的定量下限分别为0.5,0.1,2.0,0.5μg/kg,各化合物在低、中、高3个浓度加标水平下的回收率为70.1%~105.8%,相对标准偏差(RSD)为10.1%~14.8%。该方法具有简单、快速、灵敏等特点,能满足贝类产品中贝类毒素、抗生素的检测要求。     

液相色谱-串联质谱检测贝类组织中5种脂溶性贝毒素

建立了液相色谱-串联质谱分析贝类组织中米氏裸甲藻(GYM)贝毒素、螺环内酯毒素(SPX1)、大田软骨酸(OA)贝毒素、蛤毒素(PTX2)、原多甲藻酸(AZA1)贝毒素的方法.用甲醇-水(4: 1, V/V)溶液对贝类组织中GYM, SPX1, OA, PTX2和AZA1进行提取,MAX阴离子交换柱净化后,采用液相色谱分离,除OA以负离子选择反应监测外,GYM, SPX1, PTX2和AZA1以电喷雾离子源正离子选择反应监测模式进行质谱分析.5种脂溶性贝毒素GYM, SPX1, OA, PTX2和AZA1在各自相应浓度范围内线性良好,相关系数＞0.99.扇贝闭壳肌空白样品添加5种贝毒素的提取率均为78.6%～94.4%(n=6); 精密度(RSD)为6.8%～14.9%.贝类组织中5种贝毒素GYM, SPX1, OA, PTX2和AZA1的检出限分别为0.10, 0.21, 2.00, 0.32和0.04 μg/kg.     

基于纳米金辅助信号生成顺序堆积的毛细管电泳免疫分析研究

短裸甲藻毒素（BTX）是具有极强毒性的生物毒素,能够通过食物链传递引起人类中毒.由于该毒素没有光学和电化学信号,检测十分困难.本工作利用纳米金作为载体,将辣根过氧化物酶（HRP）和毒素抗体同时固定到纳米金表面,通过HRP催化H₂O₂氧化邻氨基酚（OAP）产生的电化学信号检测样品中的毒素,增大纳米金表面HRP和抗体的物质的量比使电化学信号得到极大增强.免疫反应样品电动进样引入分离毛细管中,在毛细管入口端进行顺序堆积在线富集,使检测灵敏度进一步提高.该方法通过纳米金辅助信号生成和顺序堆积在线富集技术实现了对扇贝样品中BTX-B的快速灵敏检测,线性范围为0.1~120 ng/mL,检出限为26 ng/L,检出限比常规酶联免疫分析（ELISA）法低365倍.     

海产贝类脂溶性贝毒素的高效液相色谱-串联质谱分析方法及其食用安全性评价

针对海产贝类存在多种脂溶性贝毒素复合污染的现状,采用高效液相色谱-串联质谱联用技术(HPLC-MS/MS)对海产贝类中的常见脂溶性贝毒素进行同步检测,结合多种毒素复合污染的风险评估方法,用于市售海产贝类的食用安全风险评价。结果表明,在选定的实验条件下,8种典型脂溶性贝毒素加标回收率在63.2%~88.8%之间,方法的精密度(相对标准偏差(RSD)≤14.5%)和灵敏度(检出限为0.5~2.7 ng/g)良好,能满足海产贝类样品的检测要求。在采集的105个市售海产贝类样品中,42.86%的样品中至少检出了一种脂溶性贝毒素,其中鳍藻毒素-1(DTX1)的含量均值最高,为47.6μg/kg,对海产贝类污染最严重。根据每日人均贝类摄入量(TDI)和各种脂溶性贝毒素的急性中毒参考剂量(ARf D),通过计算综合风险指数∑ERI进行市售海产贝类食用安全性评价,结果表明,在所检测的样品中,存在食用安全隐患和高风险的市售海产贝类比率为19.05%,其中扇贝的食用安全风险最大。本研究建立的基于海产贝类中脂溶性贝毒素物质组复合污染的风险评价方法,与欧盟的海产品贝毒素限量标准评价方法(单指标法)相比更加严格,可以使贝类食用者更好地规避中毒风险。     

UPLC-MS/MS测定海水、悬浮颗粒物及沉积物中18种藻毒素

采用固相萃取结合超高效液相色谱-串联质谱（UPLC-MS/MS）同时检测18种海洋藻毒素,包括原多甲藻酸贝类毒素（AZAs）、裸藻毒素（BTXs）、太平洋雪卡毒素（P-CTXs）、鳍藻毒素（DTXs）、米氏裸甲藻贝类毒素（GYM）、刺尾鱼素（MTX3）、大田软骨酸毒素（OA）、扇贝毒素（PTX2）、螺环内酯毒素（SPX1）及虾夷扇贝毒素（YTXs）。海水（1 L）或悬浮颗粒物及沉积物（1 g）的超声萃取液经Agilent Bond Elut C18(500 mg/6mL)固相萃取柱净化萃取后,在洗脱液中加入10%丙三醇-甲醇溶液以减少目标物损失。以95%乙腈水和水（两相均含有0.1%甲酸和2 mmol/L甲酸铵）为流动相,目标物经Phenomenex Kinetex C18色谱柱（100 mm×2.1mm i. d.,1.7μm）分离,采用电喷雾串联质谱多反应监测模式下正、负离子同时检测,外标法定量。18种藻毒素在6 min内分离良好,在线性范围内的相关系数为0.991 1～0.999 9,定量下限为0.05～250 pg/L（或pg/g）。三水平六平行的加标回收率为77.4%～119...     

超高效液相色谱-串联质谱法测定血浆与尿液中14种麻痹性贝类毒素北大核心CSCD

人体生物基质中麻痹性贝类毒素的检测对其引起的食物中毒诊断和救治具有重要意义。研究建立了超高效液相色谱-串联质谱法测定血浆、尿液中14种麻痹性贝类毒素的分析方法。实验比较了不同固相萃取柱的影响,优化了前处理条件和色谱条件,血浆样品采用0.2 mL水、0.4 mL甲醇、0.6 mL乙腈提取后直接上机测定,尿液样品采用0.2 mL水、0.4 mL甲醇、0.6 mL乙腈提取,聚酰胺(PA)固相萃取柱净化后上机测定。采用Poroshell 120 HILIC-Z色谱柱(100 mm×2.1 mm,2.7μm)对14种贝类毒素进行分离,流动相为含0.1%(v/v)甲酸的5 mmoL/L甲酸铵缓冲溶液和0.1%(v/v)甲酸乙腈溶液,流速为0.50 mL/min。在电喷雾模式(ESI)下进行正负离子扫描,采用多反应监测(MRM)模式检测,外标法定量。结果表明,对于血浆和尿液样品,14种贝类毒素分别在0.24~84.06 ng/mL范围内线性关系良好,相关系数均大于0.995。尿液检测的定量限为4.80~34.40 ng/mL,血浆检测的定量限为1.68~12.04 ng/mL。尿液和血浆样品在1、2和10倍定量限加标水平下平均回收率为70.4%~123.4%,日内精密度为2.3%~19.1%,日间精密度为4.0%~16.2%。应用建立的方法对腹腔注射14种贝类毒素小鼠血浆和尿液进行测定,20份血浆样本中检出含量分别为19.40~55.60μg/L和8.75~13.86μg/L。该方法操作简便,样品取样量少,方法灵敏度高,适用于血浆和尿液中麻痹性贝类毒素的快速检测。     

Enzymatic hydrolysis of esterified diarrhetic shellfish poisoning toxins and pectenotoxins

Okadaic acid (OA) and dinophysistoxins-1 and -2 (DTX1, DTX2), the toxins responsible for incidents of diarrhetic shellfish poisoning (DSP), can occur as complex mixtures of ester derivatives in both plankton and shellfish. Alkaline hydrolysis is usually employed to release parent OA/DTX toxins, and analyses are conducted before and after hydrolysis to determine the concentrations of nonesterified and esterified toxins. Recent research has shown that other toxins, including pectenotoxins and spirolides, can also exist as esters in shellfish, but these toxins cannot survive alkaline hydrolysis. A promising alternative approach is enzymatic hydrolysis. In this study, two enzymatic methods were developed for the hydrolysis of 7-O-acyl esters, “DTX3,” and the carboxylate esters of OA, “diol-esters.” Porcine pancreatic lipase induced complete conversion of DTX3 to OA and DTXs within one hour for reference solutions. The presence of mussel tissue matrix reduced the rate of hydrolysis, but an optimized lipase concentration resulted in greater than 95% conversion within four hours. OA-diol-ester was hydrolyzed by porcine liver esterase and was completely converted to OA in less than 30 min, even in the presence of mussel tissue matrix. Esters and OA/DTX toxins were all monitored by LC–MS. Further experiments with pectenotoxin esters indicated that enzymatic hydrolysis could also be applied to esters of other toxins. Enzymatic hydrolysis has excellent potential as an alternative to the conventional alkaline hydrolysis procedure used in the preparation of shellfish samples for the analysis of toxins.     

超高效液相色谱-串联质谱法同时测定血浆与尿液中12种脂溶性贝类毒素

生物样品中脂溶性贝类毒素的检测,可为食物中毒等突发公共卫生事件的流行病学调查以及中毒者的临床救治提供技术支持。目前的研究存在目标化合物少,以及方法前处理复杂、灵敏度低等问题。该研究通过优化前处理和色谱分离技术,建立了超高效液相色谱-串联质谱法测定血浆、尿液中12种脂溶性贝类毒素的方法。实验对提取试剂以及流动相的选择进行了优化,采用乙腈对尿液和血浆样品进行提取。采用Phenomenex Kinetex C18色谱柱(50 mm×3 mm, 2.6 μm)进行分离,以0.05%(v/v)氨水水溶液、90%(v/v)乙腈水溶液为流动相,以流速0.40 mL/min梯度洗脱时,12种目标化合物分离效果最好。串联质谱的离子源为电喷雾离子(ESI)源,采用多反应监测(MRM)模式检测。12种目标物的基质效应均在0.8~1.1之间,表明该前处理方法的基质干扰低,采用外标法可对化合物进行准确定量。12种贝类毒素的线性范围为0.03~36.25 μg/L,相关系数均大于0.995。尿液检测的方法定量限为0.23~0.63 μg/L,血浆检测的方法定量限为0.31~0.84 μg/L。3个加标水平的回收率为72.7%~124.1%,日内精密度为2.1%~20.0%,日间精密度为2.1%~15.3%。利用该方法检测健康人尿液和血浆样本,以及经腹腔注射12种贝类毒素的小鼠尿液和血液样本。20份健康人样本中未检出目标物,20份小鼠样本中12种贝类毒素均有检出。该方法操作简便,样品取样量少,方法灵敏高,适用于血浆和尿液中脂溶性贝类毒素的快速检测。     

Dynamic adsorption of diarrhetic shellfish poisoning (DSP) toxins in passive sampling relates to pore size distribution of aromatic adsorbent

Solid-phase adsorption toxin tracking (SPATT) technology was developed as an effective passive sampling method for dissolved diarrhetic shellfish poisoning (DSP) toxins in seawater. HP20 and SP700 resins have been reported as preferred adsorption substrates for lipophilic algal toxins and are recommended for use in SPATT testing. However, information on the mechanism of passive adsorption by these polymeric resins is still limited. Described herein is a study on the adsorption of OA and DTX1 toxins extracted from Prorocentrum lima algae by HP20 and SP700 resins. The pore size distribution of the adsorbents was characterized by a nitrogen adsorption method to determine the relationship between adsorption and resin porosity. The Freundlich equation constant showed that the difference in adsorption capacity for OA and DTX1 toxins was not determined by specific surface area, but by the pore size distribution in particular, with micropores playing an especially important role. Additionally, it was found that differences in affinity between OA and DTX1 for aromatic resins were as a result of polarity discrepancies due to DTX1 having an additional methyl moiety.     

Development and validation of a high-performance liquid chromatographic method using fluorimetric detection for the determination of the diarrhetic shellfish poisoning toxin okadaic acid without chlorinated solvents

A modification of the high-performance liquid chromatographic method with fluorimetric detection method for the determination of diarrhetic shellfish poisoning toxins was developed to completely avoid the use of dangerous chlorinated solvents. The method was validated for the toxin okadaic acid (OA) over a period of 6 months where 12 calibrations were performed and 72 samples were analyzed. Analysis of toxic and non-toxic mussels, clams and scallops demonstrated its selectivity. Linearity was observed in the tested range of interest for monitoring purposes of edible shellfish, from the limit of detection (0.3 microg OA/g hepatopancreas) to 13 microg OA/g hepatopancreas. Intra-assay precision of the method was 7% RSD at the quantification limit (0.97 microg OA/g hepatopancreas at S/N=10). Accuracy was tested in triplicate recovery experiments from OA-spiked shellfish where recovery ranged from 92 to 106% in the concentration range of 0.8 to 3.6 microg OA/g hepatopancreas. Useful information on critical factors affecting calibration and reproducibility is also reported. Good correlation (R=0.87) was observed between the results of the method and those of the method of Lee, after the analysis of 45 samples of mussels from the galician rias.     

Phycotoxins in seafood--toxicological and chromatographic aspects.

Two typical clinical types of algae-related seafood poisoning have attracted medical and scientific attention: paralytic shellfish poisoning (PSP) and diarrhetic shellfish poisoning (DSP). Therefore, it became necessary to establish methods for the evaluation of possible hazards caused by contamination of seafood with these phycotoxins. Bioassays with mice or rats are the common methods for the determination of the toxin content of seafood. However, biological tests are not completely satisfactory because of a lack of sensitivity and pronounced variations. Additionally, there is growing opposition against animal testing. Therefore, many efforts have been undertaken to determine phycotoxins by chromatographic methods. PSP determination is mainly based on high-performance liquid chromatographic (HPLC) separation by ion-pair chromatography followed by postcolumn oxidation of the underivatized toxins in alkaline solution and fluorescence detection. HPLC methods for the determination of the DSP toxins okadaic acid (OA) and dinophysistoxin-1 (DTX-1) are characterized by precolumn derivatization with 9-anthryldiazomethane (ADAM) and/or 4-bromomethyl-7-methoxycoumarin (Br-Mmc), followed by chromatographic separation of the DSP esters formed and fluorescence detection. The chromatographic methods discussed in this review allow the rapid, sensitive and non-ambiguous determination of individual species of the two most important phycotoxins in seafood, PSP and DSP.     

Collaborative study for the detection of toxic compounds in shellfish extracts using cell-based assays. Part II: application to shellfish extracts spiked with lipophilic marine toxins

Successive unexplained shellfish toxicity events have been observed in Arcachon Bay (Atlantic coast, France) since 2005. The positive mouse bioassay (MBA) revealing atypical toxicity did not match the phytoplankton observations or the liquid chromatography-tandem mass spectrometry (LC-MS/MS) investigations used to detect some known lipophilic toxins in shellfish. The use of the three cell lines (Caco2, HepG2, and Neuro2a) allows detection of azaspiracid-1 (AZA1), okadaic acid (OA), or pectenotoxin-2 (PTX2). In this study, we proposed the cell-based assays (CBA) as complementary tools for collecting toxicity data about atypical positive MBA shellfish extracts and tracking their chromatographic fractionation in order to identify toxic compound(s). The present study was intended to investigate the responses of these cell lines to shellfish extracts, which were either control or spiked with AZA1, OA, or PTX2 used as positive controls. Digestive glands of control shellfish were extracted using the procedure of the standard MBA for lipophilic toxins and then tested for their cytotoxic effects in CBA. The same screening strategy previously used with pure lipophilic toxins was conducted for determining the intra- and inter-laboratory variabilities of the responses. Cytotoxicity was induced by control shellfish extracts whatever the cell line used and regardless of the geographical origin of the extracts. Even though the control shellfish extracts demonstrated some toxic effects on the selected cell lines, the extracts spiked with the selected lipophilic toxins were significantly more toxic than the control ones. This study is a crucial step for supporting that cell-based assays can contribute to the detection of the toxic compound(s) responsible for the atypical toxicity observed in Arcachon Bay, and which could also occur at other coastal areas.     

Lipophilic toxin profile in Mytilus galloprovincialis during episodes of diarrhetic shellfish poisoning (DSP) in the N.E. Adriatic Sea in 2006

Dinophysis spp. blooms and related shellfish toxicity events of diarrhetic shellfish poisoning (DSP) have been the most reported toxicity event through the Croatian National monitoring program. With the aim to characterize the DSP toxin profile in shellfish farmed in Croatia, for the first time a complete analysis of the toxin profile of Croatian mussels has been carried out using the LC-MS/MS technique. The obtained results showed okadaic acid (OA) as the main toxin contaminating Croatian mussels at that time. The maximum concentration of OA in shellfish tissue was recorded 12 days after the Dinophysis fortii bloom, thus suggesting that rapid growth of the toxin level in the shellfish occurred in the first week after the bloom while it was slower in the second week. Furthermore, the presence of only OA at concentrations which could endanger human health suggests D. fortii as the main organism responsible for the toxic event that occurred in Lim Bay. The presence of gymnodimine and spirolides in Croatian mussel has been detected for the first time, while the presence of yessotoxin and pectenotoxin-2 is confirmed.     

液相色谱-串联质谱法同时测定贝类中大田软海绵酸、鳍藻毒素、蛤毒素和虾夷扇贝毒素

建立了同时测定贝类中大田软海绵酸(okadaic acid, OA)及其衍生物鳍藻毒素(dinophysistoxin-1, DTX-1)、蛤毒素(pectenotoxin-2, PTX-2)和虾夷扇贝毒素(yessotoxin, YTX)的液相色谱-串联质谱分析方法。样品经甲醇提取,固相萃取柱净化,C18色谱柱分离,经含甲酸和甲酸铵的乙腈-水溶液为流动相梯度洗脱,选择反应监测(SRM)模式检测,正、负离子切换扫描,基质标准校正,外标法定量。结果表明,OA、DTX-1和YTX的线性范围为2.0～200.0 μg/L,定量限(以信噪比(S/N)≥10计)为1.0 μg/kg; PTX-2的线性范围为1.0～100.0 μg/L,定量限为0.5 μg/kg;几种化合物的添加平均回收率为83.1%～105.7%,相对标准偏差(RSD)为3.16%～9.29%。成功应用本法对黄海灵山湾海域采集的贝类样品进行了分析,发现部分样品中含有大田软海绵酸、鳍藻毒素、蛤毒素和虾夷扇贝毒素。     

Development of a Capillary Electrophoresis-Based Enzyme Immunoassay with Electrochemical Detection for the Determination of Okadaic Acid and Dinophysistoxin2 in Shellfish Samples

A capillary electrophoresis-based enzyme immunoassay (CE-EIA) with electrochemical (EC) detection system was developed for the determination of two diarrheic shellfish poisoning (DSP) toxins okadaic acid (OA) and dinophysistoxin2 (DTX2). In this method, after the competitive immunoreaction in liquid phase, the horseradish peroxidase (HRP)-labeled antigen (Ag*) and the bound enzyme-labeled complex (Ag*-Ab) were separated and then the system of HRP catalyzing H₂O₂/o-aminophenol (OAP) reaction was adopted. The limit of detection (S/N = 3) was determined to be 0.05 and 0.07 ng/mL for OA and DTX2, respectively. The total analysis time was less than 40 min. The developed CE-EIA with EC detection system was capable of quantitatively detecting OA and DTX2 contents in the tested contaminated samples, and the results were compared with the same samples analyzed through enzyme-linked immunosorbent assay (ELISA). Consistent results between CE-EIA with EC detection and ELISA were found in most of the tested samples. The proposed system appeared to be more sensitive and faster than ELISA for determination of OA and DTX2 in shellfish meat extracts. Real shellfish samples were validated in recovery test, and the recoveries tested by the proposed method were 91.7–108.3% and 95.2–112.5% for OA and DTX2, respectively. The CE-EIA with EC detection provides a valid and sensitive analytical approach, not previously available, for the determination of OA and DTX2 in shellfish samples.     

Determination of marine biotoxins relevant for regulations: from the mouse bioassay to coupled LC-MS methods

The frequency of occurrence and intensity of harmful algal blooms (HABs) appear to be increasing on a global scale. Consequently, methods were established for the evaluation of possible hazards caused by the enrichment of algal toxins in the marine food chain. Different clinical types of algae-related poisoning have attracted scientific attention: paralytic shellfish poisoning (PSP), diarrhetic shellfish poisoning (DSP), and amnesic shellfish poisoning (ASP). In several countries fish specialties are consumed which may be contaminated with algal toxins typical for the respective region (e.g., ciguatera and tetrodotoxins). Bioassays are common methods for the determination of marine biotoxins. However, biological tests are not completely satisfactory, due to the low sensitivity and the absence of specialized variations. Moreover, there is growing resistance against the use of animal experiments. Therefore, many efforts have been made to determine algal toxins with chemical methods. In this context LC-MS methods replaced HPLC methods with optical detectors, allowing both effective seafood control and monitoring of phytoplankton in terms of the different groups of marine biotoxins.