液相色谱-串联质谱法快速测定水产品中结晶紫及其隐色代谢物残留

采用液相色谱-串联质谱法(LC-MS/MS)测定了水产品中结晶紫以及它的隐色代谢物残留。匀质后的水产品样品用乙腈和乙酸铵缓冲液提取,合并提取液,用二氯甲烷反提取,经中性氧化铝柱和PRS柱固相萃取净化,且不使用氧化铅柱在线氧化,色谱分离后直接进入串联质谱检测器。采用电喷雾正离子,多反应监测(MRM)模式检测。方法的检出限可达0.5 ng/g,线性方程的相关系数r大于0.99,添加样品平均回收率为77.6%~93.8%,相对标准偏差均小于8.2%。     

液相色谱法同时测定水产品中孔雀石绿和结晶紫残留

用液相色谱-可见法同时测定水产品中孔雀石绿(MG)、结晶紫(CV)及其代谢物隐色孔雀石绿(LMG)和隐色结晶紫(LCV)的残留量,并用液相色谱-串联质谱法进行确证和定量。样品用乙腈提取,二氯甲烷液液分配,MCX阳离子固相萃取小柱净化,浓缩定容。以乙酸铵缓冲溶液和乙腈为流动相,经C18柱分离后,PbO2柱后衍生;用二极管阵列检测器在618nm测定孔雀石绿和隐色孔雀石绿,在588nm测定结晶紫和隐色结晶紫;并用串联质谱在电喷雾-多反应监测离子的模式下,进行质谱确证和定量;外标法定量,内标亮绿和氘代隐色孔雀石绿校正回收率。液相色谱-可见法的检出限为MG0.22,LMG0.28,CV0.22,LCV0.25μg/kg;液相色谱-串联质谱法的检出限为MG0.014,LMG0.018,CV0.014,LCV0.0084μg/kg。在2~20μg/kg范围内,回收率为75%~95%。     

QuEChERS/UPLC-MS/MS法测定水产品中孔雀石绿和结晶紫及其代谢物

建立了水产品中孔雀石绿(MG)和结晶紫(CV)及其代谢物隐色孔雀石绿(LMG)和隐色结晶紫(LCV)残留的QuEChERS/UPLC-MS/MS分析方法。样品采用乙腈提取,改进的QuEChERS(EMR-Lipid)分散固相萃取净化,经Agilent Eclipse Plus C_(18)(1.8μm,3.0 mm×100 mm)色谱柱分离,电喷雾串联四极杆质谱多反应监测正离子方式测定。4种分析物在0.2~10.0μg/L范围内线性关系良好,相关系数均大于0.997。鱼肉中4种分析物在0.5,1.0,5.0μg/kg加标浓度水平下,回收率为77.1%~106.6%,相对标准偏差(RSD)为1.3%~4.3%。该方法简单、稳定、可靠,能有效去除样品中的蛋白质、脂肪等大分子杂质,可满足水产品中孔雀石绿、结晶紫以及隐色代谢物残留检测与确证的需要。     

超高效液相色谱-串联质谱法测定水产品中孔雀石绿、结晶紫及其代谢物残留量

采用超高效液相色谱-串联质谱法同时检测水产品中孔雀石绿、结晶紫及其代谢物(隐色孔雀石绿、隐色结晶紫)。经匀浆处理的水产品样品,用乙腈提取,加入酸性氧化铝去除油脂,旋转蒸发器蒸干后,用甲酸-乙腈-水(0.1+10+89.9)溶液溶解,样品溶液用超高效液相色谱分离,电喷雾串联四极杆质谱进行检测。以氘代孔雀石绿、氘代隐色孔雀石绿为内标物。孔雀石绿、结晶紫及其代谢物的质量浓度均在5.0μg·L-1以内与其峰面积呈线性关系,检出限(3S/N)在0.10～0.12μg.kg-1之间。以空白水产品样品为基体进行回收试验,方法的回收率在90.2%～108.0%之间,相对标准偏差(n=6)在2.3%～7.6%之间。     

高效液相色谱-四极杆串联线性离子阱质谱法测定水产品及饲料中的孔雀石绿、结晶紫及其代谢物

提出了高效液相色谱-四极杆串联线性离子阱质谱法测定水产及饲料中的孔雀石绿、结晶紫及其代谢物(隐色孔雀石绿、隐色结晶紫)的方法。样品经乙腈提取,Agilent XDB C18色谱柱分离,四极杆串联线性离子阱质谱进行检测。以氘代孔雀石绿、氘代隐色孔雀石绿、氘代结晶紫、氘代隐色结晶紫为内标物。4种化合物的线性范围均为0.05~5.0μg·L-1,检出限(3S/N)均为0.5μg·kg-1。以空白样品为基体做加标回收试验,计算得4种化合物的回收率在93.3%~120%之间,相对标准偏差(n=6)在1.4%~18%之间。另外,还采用数据相关采集模式结合增强离子扫描模式对4种化合物进行定性分析,可对试样中4种化合物在定量同时进行定性确证。     

反相高效液相色谱法测定水产品中孔雀石绿、结晶紫及其代谢物

利用反相高效液相色谱研究了水产品中孔雀石绿、结晶紫及其代谢物隐性孔雀石绿、隐性结晶紫的同时测定。采用Krom asil C18色谱柱,PbO2-硅藻土柱为柱后氧化柱,以乙腈-乙酸铵缓冲溶液-冰乙酸(体积比为58∶14∶28)体系为流动相。孔雀石绿、隐性孔雀石绿、结晶紫、隐性结晶紫的加标回收率分别为84.6%、85.8%、89.8%、88.5%,相对标准偏差分别为5.0%、4.7%、4.3%、4.6%(n=6),检出限为2μg/kg。     

高效液相色谱-串联质谱法同时测定草鱼中6种阳离子染料残留量

建立了同时测定草鱼中孔雀石绿、隐色孔雀石绿、结晶紫、隐色结晶紫、亚甲基蓝和新亚甲基蓝6种阳离子染料残留量的高效液相色谱-串联质谱(HPLC-MS/MS)方法。样品经乙腈和缓冲溶液提取,用二氯甲烷萃取及中性氧化铝固相萃取柱净化。选择反应监测(SRM)正离子模式检测,内标法定量。孔雀石绿、隐色孔雀石绿、结晶紫、隐色结晶紫、新亚甲基蓝和亚甲基蓝的定量限均为0.2μg/kg。添加0.2~10μg/kg水平时加标回收率达到75.0%~98.5%,相对标准偏差为3.2%~9.1%。     

超高效液相色谱-串联质谱法测定鱼粉中孔雀石绿

建立了鱼粉中孔雀石绿及其代谢物隐色孔雀石绿残留量的超高效液相色谱-串联质谱仪(UPLC-MS-MS)测定法。样品经乙腈提取,中性Al2O3固相小柱净化,超高效液相色谱C18柱分离,电喷雾正离子多反应模式(MRM)检测,内标法定量。方法的定量限为1.00μg/kg,线性范围为0.25～20.0μg/L。在1.00～20.0μg/kg的加标量下,孔雀石绿平均回收率范围为85.3%～104.4%,隐色孔雀石绿平均回收率范围为85.7%～101.4%,相对标准偏差均小于15%。方法适用于鱼粉样品中孔雀石绿残留的快速检测。     

超高效液相色谱-串联质谱法测定水产品中孔雀石绿及其代谢物残留量

采用超高效液相色谱-串联质谱法测定水产品中孔雀石绿及其代谢物的残留量。样品经盐酸羟胺、对甲苯磺酸、乙酸铵的混合液作为提取剂均质提取,乙腈萃取,并通过-18℃冷冻离心分层。以ACQUITY UPLC BEH C18色谱柱分离,用乙腈与5mmol·L-1乙酸铵溶液(75+25)的混合液洗脱,采用正离子模式监测。以氘代孔雀石绿和氘代隐色孔雀石绿为内标物。孔雀石绿和隐色孔雀石绿的线性范围均为1.0~20.0μg·L-1,检出限(3S/N)依次为0.05,0.06μg·kg-1。在1.0,2.0,5.0μg·kg-1等3个浓度水平进行加标回收试验,回收率在90.2%~106%之间,测定值的相对标准偏差(n=6)在2.1%~11%之间。     

超高效液相色谱-串联质谱法测定养殖水和沉积物中孔雀石绿、结晶紫及其代谢物残留

建立了超高效液相色谱-串联质谱(UPLC-MS/MS)同时测定养殖水和沉积物中孔雀石绿、结晶紫及其代谢物(隐性孔雀石绿和隐色结晶紫)的多残留分析方法。沉积物样品真空冷冻干燥,乙腈和二氯甲烷提取,MCX固相萃取小柱净化;养殖水试样真空冷冻干燥,50%乙腈-水溶液(含0.1%甲酸)溶解残渣,离心过膜,上机检测。经BEH C18色谱柱分离,梯度洗脱,多反应监测正离子模式下进行定量和定性分析。采用内标法定量,药物含量在0.50~50μg/L范围内线性关系良好,相关系数大于0.99;以3倍和10倍信噪比计算出养殖水的检测限和定量限为10~25 ng/L和25~50 ng/L,沉积物的检测限和定量限为0.020~0.025μg/kg和0.04~0.05μg/kg;平均回收率为85.2%~105.6%,相对标准偏差小于12%。方法已用于实际养殖水和沉积物样品中违禁药物的测定。     

Confirmatory analysis of malachite green, leucomalachite green, crystal violet and leucocrystal violet in salmon by liquid chromatography-tandem mass spectrometry

A method has been developed to analyse for malachite green (MG), leucomalachite green (LMG), crystal violet (CV) and leucocrystal violet (LCV) residues in salmon. Salmon samples were extracted with acetonitrile:McIIIvain pH 3 buffer (90:10 v/v), sample extracts were purified on a Bakerbond strong cation exchange solid phase extraction cartridge. Aliquots of the extracts were analysed by LC-MS/MS. The method was validated in salmon, according to the criteria defined in Commission Decision 2002/657/EC. The decision limit (CCalpha) was 0.17, 0.15, 0.35 and 0.17 microg kg(-1), respectively, for MG, LMG, CV and LCV and for the detection capability (CCbeta) values of 0.30, 0.35, 0.80 and 0.32 microg kg(-1), respectively, were obtained. Fortifying salmon samples (n=6) in three separate assays, show the accuracy to be between 77 and 113% for MG, LMG, LCV and CV. The precision of the method, expressed as RSD values for the within-laboratory reproducibility, for MG, LMG and LCV at the three levels of fortification (1, 1.5 and 2.0 microg kg(-1)), was less than 13%. For CV a more variable precision was obtained, with RSD values ranging between 20 and 25%.     

Liquid chromatography-tandem mass spectrometry method for the determination of dye residues in aquaculture products: development and validation

A method is described for the identification and the quantitative determination of the triphenylmethane dyes, malachite green (MG), crystal violet (CV), brilliant green (BG) and leuco malachite green (LMG) and leuco crystal violet (LCV). The analytes were isolated from the matrix by liquid-liquid extraction with acetonitrile. Determination was performed using LC-MS/MS with positive electrospray ionisation. 4 different deuterated internal standards were introduced to improve the quantitative performance of the method. The method has been validated in line with the EU criteria of Commission Decision 2002/657/EC in accordance with the minimum required performance limit (MRPL) set at 2 μgkg(-1) for the sum of MG and LMG. For all the monitored compounds, accuracy, intra-day and inter-day precision were determined at each level of fortification (0.5, 0.75, 1.0 and 2.0 μgkg(-1)). Decision limits CCα and detection capabilities CCβ were calculated according to the standard ISO 11843-2. A study on the applicability of the method was conducted on various aquacultured species with the aim to assess the matrix effects. The presence of residues of leuco brilliant green in fish has also been confirmed from experimental study performed on trout treated with brilliant green, using LTQ-Orbitrap mass spectrometer.     

Monoclonal antibody-based enzyme-linked immunosorbent assay for detection of total malachite green and crystal violet residues in fishery products

A rapid easy-to-use trace level direct competitive enzyme-linked immunosorbent assay (dc-ELISA) detection of total residual malachite green (MG), crystal violet (CV) and their corresponding primary metabolites leucomalachite green (LMG) and leucocrystal violet (LCV) in fishery products in a single assay was developed. The monoclonal antibodies, anti-MG and anti-CV mAbs, were prepared using carboxyl-malachite green (CMG) and cationized bovine serum albumin (cBSA) conjugates as immunogen. The linear range for the quantitative detection of total MG, CV and their primary metabolites LMG and LCV was between 0.15 to 4.5?ng?mL^?1 with a half maximal inhibitory concentration (IC₅₀) at 0.56?±?0.04?ng?mL^?1 (n?=?5). The anti-MG mAbs exhibited 98% cross-reactivity to CV, less than 0.1% cross-reactivity with LMG and LCV, and no cross-reactivity with chloramphenicol, enrofloxacin, sulfadiazine, and tetracycline. Application of the dc-ELISA in fish tissue samples gave a limit of detection (LOD) of 0.37?ng?g^?1. The improved total detection lead to a recovery of 74.60?±?8.38% at 0.5?ng?g^?1 and 87.47?±?12.83% at 2.0?ng?g^?1 that was better than existing techniques. The dc-ELISA showed total MG in 7 out of 44 field fish samples that were confirmed with LC-MS/MS. The easy-to-use, inexpensive, and rapid dc-ELISA for the detection of total MG, CV and their corresponding primary metabolites holds promise for field applications.     

Simultaneous determination of malachite green, gentian violet and their leuco-metabolites in aquatic products by high-performance liquid chromatography-linear ion trap mass spectrometry

A method has been developed for the simultaneous determination of malachite green, gentian violet and their leuco-metabolites in various aquatic products using isotope dilution liquid chromatography-linear ion trap mass spectrometry without post-column oxidation. Sample was extracted with McIlvaine buffer and acetonitrile, followed by partitioning with dichloromethane, purified on basic alumina and OASIS MCX SPE column, and finally analyzed by LC-ESI-MS/MS with the select reaction monitoring (SRM) mode. Decision limits (CCalpha, alpha=0.01) and detection capability (CCbeta, beta=0.05) of the method were in the range of 0.02-0.09 and 0.04-0.13microg/kg for MG, GV, LMG and LGV in grass carp, eel, salmon, shrimp and shellfish, respectively, recoveries of MG, GV, LMG and LGV at all fortification levels (0.25-10microg/kg) were from 80.8% to 115.7%, inter-day relative standard derivations were from 1.9% to 18.4%. This method appeared suitable for the control of MG, GV, LMG and LGV residues in aquatic products.     

改进的QuEChERS方法用于鱼肉中孔雀石绿、隐色孔雀石绿、结晶紫和隐色结晶紫的快速检测(英文)

孔雀石绿（MG）和结晶紫（CV）具有抗菌等活性,常被违法用于水产养殖业。但MG、CV及其代谢产物隐色孔雀石绿（LMG）、隐色结晶紫（LCV）具有致癌性。所以水产品中染料的残留检测是食品安全分析的重要问题。由于水产品基质复杂,样品前处理尤为重要。本文发展了一种基于QuEChERS技术与高效液相色谱联用的方法,用于鱼肉中4种染料的同时检测。对QuEChERS方法中提取剂体积、提取次数以及分散固相萃取材料进行了优化。结果表明反相/强阴离子交换材料（C18SAX）能有效提高回收率。在最优条件下,4种染料在0.5~100 mg/L范围内线性良好,相关系数均大于0.998。该方法在鱼肉中的回收率为73%~91%,RSD为0.66%~5.41%。结果表明该方法简单、高效,适合于鱼肉中染料的快速检测。     

Simultaneous determination of malachite green, crystal violet, methylene blue and the metabolite residues in aquatic products by ultra-performance liquid chromatography with electrospray ionization tandem mass spectrometry

This work describes solid-phase extraction-ultra-performance liquid chromatography with electrospray ionization tandem spectrometry for determination of malachite green and metabolite leucomalachite green, crystal violet and metabolite leucocrystal violet, methylene blue and metabolites including azure A, azure B and azure C in aquatic products. Samples were extracted with acetonitrile and ammonium acetate buffer and purified by liquid extraction with dichloromethane, and then on MCAX solid-phase extraction cartridges. Then the extract was evaporated at 45°C by nitrogen blow. The residue was dissolved and separated by an Acquity BEH C18 column. The mobile phase was acetonitrile (A) and 5 mmol/L of ammonium acetate containing 0.1% formic acid (B). Analytes were confirmed and quantified using a tandem mass spectrometry system in multiple reaction mode with triple quadrupole analyzer using positive polarity mode. The limits of detection of malachite green, leucomalachite green, crystal violet and leucocrystal violet were 0.15 μg/kg, the limits of quantification were 0.50 μg/kg, and the average recoveries were more than 75% with spiked residues from 0.5 to 10 μg/kg. The relative standard deviations were less than 13%. The limits of detection of methylene blue, azure A, azure B and azure C were 0.3 μg/kg, the limits of quantification were 1.0 μg/kg, the average recoveries were more than 70% with spiked residues from 1.0 to 10 μg/kg and the relative standard deviations were less than 15%. The method has the merits of simplicity, sensitivity and rapidity, and can be used for simultaneous determination of the analytes in aquatic products.     

Determination of malachite green and leucomalachite green in a variety of aquacultured products by liquid chromatography with tandem mass spectrometry detection

A liquid chromatography/tandem mass spectrometry (LC/MS/MS) method was developed for determining the residues of malachite green (MG) and leucomalachite green (LMG) in a number of aquatic species. MG and its metabolite were extracted from homogenized tissues with a perchloric acid-acetonitrile solution; the extract was centrifuged; and an aliquot was taken, concentrated, and passed through a chemically bonded octadecyl C18 solid-phase extraction column. The compounds of interest were eluted with acetonitrile, and the eluate was evaporated to dryness. The residue was dissolved in acetonitrile and diluted with water in preparation for analysis by LC/MS/MS. MG and its metabolite were determined by reversed-phase LC using a Luna C18 column with an ammonium hydroxide-formic acid buffer in acetonitrile gradient and MS/MS detection using multiple reaction monitoring. Calibration curves were linear for all analyses between 5 and 500 pg injected for both analytes, with recoveries ranging from 81% for LMG to 98% for MG in salmon spiked at the 1 ng/g level. Detection limits of 0.1 ng/g for both MG and LMG were easily obtainable using the recommended method. The operational errors, interferences, and recoveries for spiked samples compared favorably with those obtained by established methodology. The recommended method is simple, rapid, and specific for monitoring residues of MG and LMG in a number of aquatic species.     

Liquid chromatographic determination of malachite green and leucomalachite green (LMG) residues in salmon with in situ LMG oxidation

A liquid chromatography (LC) method is presented for the quantitative determination of malachite green (MG) in salmon. MG and leucomalachite green (LMG) residues were extracted from salmon tissue with ammonium acetate buffer and acetonitrile, and then isolated by partitioning into dichloromethane. LMG was quantitatively oxidized to the chromic MG by reaction with 2,3-dichloro-5,6-dicyano-1,4-benzoquinone. Samples were then cleaned up by solid-phase extraction with alumina and propylsulfonic acid phases. Extracts were analyzed for MG by LC with visible detection at 618 nm using isocratic elution and a C18 column. The method was validated in 35 farm-raised salmon (Salmo salar) tissues fortified at 1, 2, 4, and 10 ng/g (ppb) with an average recovery of 95.4% and a relative standard deviation of +/- 11.1%, and in 5 canned salmon (Oncorhynchus gorbuscha) samples fortified at 10 ng/g with an average recovery of 88.9 +/- 2.6%. This study also included the determination of MG and LMG residues in tissues from salmon that had been treated with MG MG was quantitatively determined at the method detection limit of 1 ng/g.