使用热处理、震摇、超声波等手段改善水产品中的河鲀毒素提取率, 利用多种固相萃取柱纯化提取液, 采用高效液相色谱-紫外检测法进行检测, 重点对河鲀毒素的提取和固相萃取纯化进行了研究。试验发现, 结合振荡和加热双重作用的索氏提取法和超声波加热辅助提取法具有较高的提取能力, 其中超声波(35kHz, 强度100%, 60℃)提取10min即可达到最好效果, 耗时短, 效率更高; 比较SCX、PRS、WCX、C18、SAX 5种固相萃取柱对河鲀毒素的吸附作用, SCX、PRS、WCX柱则能够将河鲀毒素完全保留在其上。样品纯化试验结果显示, C18-WCX小柱的组合纯化样品的效果最好, 回收率在75%—82%之间, 相对标准偏差小于15%。研究结果对河鲀毒素的提取、纯化和检测工作具有重要的参考意义。
Tetrodotoxin (TTX) accumulated in some aquatic products can be extremely dangerous to human beings. Detecting the content of TTX in aquatic products can help to avoid consuming the toxic products. Due to the complexity of sample composition, TTX detection method has not been developed. The new methods of extracting TTX in puffer fish were studied and presented here. A variety of solid phase extraction column for purification were compared, the high performance liquid chromatography (HPLC) coupled with a UV detector was adopted in the detection. The results showed that both the Soxhlet extraction method and ultrasound treatment method have higher extraction efficiency. Solid-phase extraction (SPE) cartridges were compared in the TTX adsorption experiments, which revealed that the strong cation exchanger (SCX), the propanesulfonic acid SPE cartridge (PRS), and the weak cation exchanger (WCX) had good capacity of retaining TTX. The combination of the octadecyl silane SPE cartridge (C18) and WCX cartridge is even better. The best result can be achieved by extracting 10 min at 35 kHz, 100% intensity, 60℃ ultrasound treatments. The recovery rate is 75%—82%, with the relative standard deviation (RSD) of less than 15%. This newly developed method is efficient and ready to be used in the laboratory.
[1] 伍汉霖, 陈永豪, 牟阳, 等. 中国有毒及药用鱼类新志 [M]. 北京: 中国农业出版社, 2002: 79-90.
[2] 郭柏坤, 宫庆礼. 反相高效液相-PDA法测定虫纹东方纯(Takifugu vermicularis)肝脏中的河豚毒素 [D].青岛: 中国海洋大学, 2006: 8-18.
[3] 陈正冬.河豚毒素检测原理与发展趋势[J]. 中国农学通报, 2005, 21(8): 93-94.
[4] 曹爱英, 吴成业. 河豚毒素及其检测方法的研究新进展[J]. 渔业现代化, 2007, 34(3): 31-33.
[5] 刘燕婷, 雷红涛, 钟青萍. 河豚毒素的研究进展[J]. 食品开发与研究, 2008, 29(2): 156-160.
[6] 黄枝梅, 陈绍军, 刘智禹. 河豚毒素及其分离纯化研究进展[J]. 福建水产, 2009, (4): 80-90.
[7] 郭柏坤, 宫庆礼, 吴韶菊, 等. 反相离子对高效液相-PDA法测定虫纹东方魨肝脏中的河鲀毒素 [J].中国海洋药物杂志, 2006, 25(5): 34-37.
[8] 崔建洲, 申雪艳, 宫庆礼, 等. 高效液相色谱-紫外/荧光检测方法测定河鲀毒素[J]. 色谱, 2006, 24(3): 317.
[9] 易瑞灶, 许晨, 洪专, 等. 河豚毒素高纯单体规模化制备方法: 中国, 02121463[P]. 2002-06-24.
[10] 林文銮, 黄惠莉, 陈少欣. 河鲀毒素的提取研究[J].华侨大学学报, 1999, 20(4): 412-414.
[11] NAGASHIMA Y, TANAKA N, SHIMAKURA K, et al. Occurrence of tetrodoxin-related substances in the nontoxic puffer Takifugu xanthopterus [J]. Toxicon, 2001, 39: 415-418.
[12] TSAI Y H, HO P H, HWANG C C, et al. Tetrodotoxin in several species of xanthid crabs in southern Taiwan [J]. Food Chemistry, 2006, 95: 205-212.
[13] 骆和东, 贾玉珠, 朱宝平. 固相萃取-超过滤-液相色谱/质谱联用法测定织纹螺中的河豚毒素[J]. 色谱, 2007, 25(6): 917-921.
[14] MARGARET A O, JENNIFER J S, GEOFFREY K I. Use of high performance Liquid chromatography to measure tetrodotoxin in serum and urine of poisoned patients [J]. Toxicon, 2004, 44: 549-553.