高效液相色谱-电感耦合等离子体质谱法同时测定果蔬中6种砷形态

建立了一种同时测定果蔬中亚砷酸根、砷酸根、砷胆碱、砷甜菜碱、一甲基砷酸和二甲基砷酸等6种砷形态的高效液相色谱-电感耦合等离子体质谱分析方法。样品经甲醇水提取,采用阴离子分析柱,50 mmol/L碳酸铵溶液和水作为流动相进行梯度洗脱,高效液相色谱分离,电感耦合等离子体质谱进行定性和定量分析。在0.5～50μg/kg范围内...     

高效液相色谱-电感耦合等离子体质谱联用技术测定花茶中砷形态

应用高效液相色谱-电感耦合等离子体质谱(HPLC-ICP-MS)联用技术,建立了花茶中6种砷形态:亚砷酸根、砷酸根、一甲基砷酸、二甲基砷酸、砷胆碱、砷甜菜碱的分析方法。样品在真空条件下采用水-磷酸进行提取,用Hamilton PRP-X100阴离子交换柱,以碳酸铵溶液和硝酸铵+磷酸氢二铵作为流动相进行梯度洗脱,电感耦合等离子体质谱进行定性和定量分析。方法学验证表明:在0.5～50μg/L范围内各砷形态线性良好,线性相关系数(r2)都大于0.999,定量限为0.5μg/L,加标回收率在89.9%～104.1%之间,相对标准偏差(RSD)在1.4%～4.2%之间。方法适用于各类花茶中的6种砷形态分析。     

高效液相色谱-电感耦合等离子体质谱法分析食用菌中6种砷形态及其分布特征

建立同时测定食用菌中亚砷酸根、砷酸根、一甲基砷酸、二甲基砷酸、砷甜菜碱、砷胆碱6种砷形态化合物的高效液相色谱-电感耦合等离子体质谱分析方法。选择5 mmol/L和80 mmol/L(pH 8.0)碳酸铵溶液作为梯度洗脱的流动相，0.50 mol/L乙酸溶液作为提取剂，采用微波萃取的提取方式进行分析。6种砷形态化合物的质量浓度在0～100μg/L范围内与色谱峰面积线性关系良好，相关系数均大于0.999 0，亚砷酸根、砷酸根、一甲基砷酸、二甲基砷酸、砷甜菜碱、砷胆碱的检出限分别为0.04、0.05、0.08、0.07、0.05、0.09μg/L，定量限分别为0.13、0.15、0.20、0.20、0.16、0.28μg/L。样品加标回收率为88.3%～96.3%，测定结果的相对标准偏差为4.37%～8.98%(n=6)。采用该方法研究市售食用菌中砷形态分布特征，结果表明，不同类型食用菌中砷形态分布种类和含量不同，需综合无机砷和有机砷的含量评估食用菌中砷的危害性。     

HPLC–ICP–MS法测定地表水体中砷的形态

建立了高效液相色谱和电感耦合等离子体质谱联用技术测定水中砷形态的方法。对高效液相色谱和电感耦合等离子体质谱的实验条件如流动相的p H值及浓度、RF功率、采样深度、载气和补偿气流速等进行了优化。测定5种砷形态的线性范围为2.5~30.0μg/L,线性相关系数大于0.999,5种砷形态的检出限在0.10~0.15μg/L之间。对江、湖和河流3类地表水体样品分别加入2.0,5.0,15.0μg/L砷形态混合标准溶液进行回收试验,加标回收率为91.6%~104.5%,测定结果的相对标准偏差为1.5%~4.6%(n=6)。该方法灵敏、高效,适合于水中砷形态的测定。     

浒苔中有毒有害元素及砷化学形态的研究

建立了微波消解-电感耦合等离子体质谱(ICP-MS)法测定浒苔中Cu、As、Cd、Hg、Pb等元素含量的分析方法,对各元素的线性关系良好(r=0.999 3～0.999 9),检出限为0.28～2.3 μg/L,元素加标回收率为83%～108%,符合痕量分析要求.并利用高效液相色谱(HPLC)与电感耦合等离子体质谱(ICP-MS)联用技术对浒苔样品中的砷化学形态进行了初步探讨,发现其中砷主要以无机As(Ⅴ)和某种未知的砷形态存在,推测该未知砷形态为砷糖类物质.     

高效液相色谱-电感耦合等离子体质谱联用测定鸡肉及鸡肝中10种砷形态化合物

建立了一种有效分离检测鸡肉及鸡肝样品中洛克沙砷(ROX)、阿散酸(ASA)、硝苯胂酸(NPAA)、卡巴胂(CBS)、砷酸(AsⅤ)、亚砷酸(AsⅢ)、一甲基胂酸(MMA)、二甲基胂酸(DMA)、砷甜菜碱(As B)和砷胆碱(As C)共10种砷形态化合物的高效液相色谱-电感耦合等离子体质谱(HPLC-ICP-MS)分析方法。采用10%甲醇为提取液,碳酸铵溶液为流动相,以阴离子分析柱将样品提取液进行分离,最后进行ICP-MS测定。10种砷形态化合物在0.1~100μg/L范围内线性关系良好,相关系数(r2)均大于0.999,检出限为0.3~1.5μg/kg,定量下限为1.0~5.0μg/kg,加标回收率为81.3%~97.7%,相对标准偏差为0.1%~3.5%。该法重现性好、灵敏度高,且采用组织研磨仪机械振荡5 min即可成功提取10种砷形态化合物,与常规水浴加热振荡提取相比更加简便、高效。该法适用于鸡肉及鸡肝样品中10种砷形态化合物的同时检测,通过对实际样品的分析测定,在鸡肝样品中检出阿散酸和亚砷酸。     

超声辅助热酸提取液相色谱-电感耦合等离子体质谱联用法测定香辛料中6种砷形态

建立液相色谱-电感耦合等离子体质谱(LC-ICP-MS)联用法测定香辛料中6种砷形态(亚砷酸盐、砷酸盐、一甲基砷、二甲基砷、砷甜菜碱和砷胆碱)含量的分析方法。样品采用质量分数为1%的硝酸溶液在80℃条件下超声辅助提取10 min，使用PRP X-100阴离子色谱柱，以25 mmol/L NH₄H₂PO₄-乙醇(体积比为99∶1)溶液为流动相进行等度洗脱。6种砷形态的质量浓度在1.0～100μg/L范围内线性良好，线性相关系数为0.999 0～0.999 9，检出限为0.26～0.76 g/kg。肉蔻样品加标回收率为97.6%～104.7%,6种砷形态测定结果的相对标准偏差为1.73%～2.80%(n=6)。将所建方法应用于茴香、草果、胡椒、肉蔻、辣椒5种香辛料的测定，总砷提取率为96.7%～102.0%,6种砷形态检测回收比率为96.5%～103.9%。不同种类香辛料存在2～6种不同砷形态，其中无机砷含量为0.078～0.40 mg/kg，均占总砷的80%以上，砷酸盐为香辛料中砷的主要存在形态，参考国家标准食品中污染物限...     

HPLC-ICP-MS测定中药中砷的形态

报道了高效液相色谱-电感耦合等离子体质谱(HPLC-ICP-MS)联用技术测定中药中砷的形态.采用阴离子交换柱,以含0.2 mmol/L乙二胺四乙酸(EDTA)和2 mmol/L NaH2PO4的水溶液为流动相,pH 6.0,流速为1.0 mL/min,成功分离了亚砷酸(AsⅢ)、砷酸(AsⅤ)、甲基砷(MMA)和二甲基砷(DMA).检出限分别为0.67 μg/L (AsⅢ),0.85 μg/L (DMA),0.43 μg/L (MMA),0.70 μg/L (AsⅤ).中药样品经过(1 1)甲醇水溶液超声提取,离心、过滤、氮气吹干甲醇,超纯水定容.样品加标平均萃取回收率分别为: 92.8% (AsⅢ),108% (DMA),104% (MMA),101% (AsⅤ),RSD (n=7)均小于10%.     

15种中药材中砷的形态分析

利用高效液相色谱(HPLC)与电感耦合等离子体质谱(ICP-MS)联用技术对6种砷形态[砷胆碱(AsC)、砷甜菜碱(AsB)、三价砷As(Ⅲ)、二甲基砷酸(DMA)、甲基砷酸(MMA)和五价砷As(Ⅴ)]进行了分离,测定了0 ～100 μg/L范围内6种砷形态的混合标准工作曲线,相关系数(r2)优于0.990,方法检出限均为0.2 μg/L.采用甲醇-水(体积比1 : 1)超声法提取了15种中药材中的砷形态,用HPLC-ICP-MS进行分析,结果表明,15种中药材中存在的主要砷形态是有毒的As(Ⅴ),另外还有少量的砷甜菜碱和砷胆碱,并且动物用药中的有机砷含量明显高于植物用药.     

HPLC-ICP-MS测定植物样品中6种砷形态化合物

通过优化色谱分离、样品前处理条件,同时对比了电感耦合等离子体质谱的标准模式(STD)、碰撞模式(KED)、氧气反应模式(Oxygen-DRC)、甲烷反应模式(Methane-DRC)的检测结果,建立了一种有效分离植物样品中砷甜菜碱(AsB)、二甲基砷酸(DMA)、亚砷酸(As(Ⅲ))、砷胆碱(AsC)、一甲基砷酸(MMA)、砷酸(As(Ⅴ))6种砷形态化合物的高效液相色谱-电感耦合等离子体质谱(HPLC-ICP-MS)分析方法。样品以1%HNO₃溶液为提取溶剂,90℃加热提取2.5 h,RP小柱净化,然后采用AS7阴离子交换柱分离,25~80 mmol/L(NH₄)₂CO₃溶液梯度洗脱,在STD模式下测定,6种砷形态化合物在9 min内完全分离。方法检出限为0.10~0.25μg/L,加标回收率为87.5%~117.8%,相对标准偏差(RSDs)为1.2%~1.8%。方法适用于植物样品中6种砷形态化合物的测定。     

Distribution and cycle of arsenic compounds in the ocean

In order to understand the distribution and the cycle of arsenic compounds in the marine environment, the horizontal distributions of arsenic(V) [As(V)], arsenic(III) [As(III)], monomethylarsonic acid (MMAA) and dimethylarsinic acid (DMAA) in the Indian Pacific Oceanic surface waters have been investigated. This took place during cruises of the boat Shirase from Tokyo to the Syowa Station (15 November–19 December 1990), of the tanker Japan Violet from Sakai to Fujayrah (28 July–17 August 1991) and of the boat Hakuho-maru from Tokyo to Auckland (19 September–27 October 1992). Vertical distributions of arsenic in the west Pacific Ocean have also been investigated. The concentration of As(V) was found to be relatively higher in the Antarctic than in the other areas. Its concentration varied from 340 ng dm^?3 (China Sea) to 1045 ng dm^?3 (Antarctic). On the other hand, the concentrations of the biologically produced species, MMAA and DMAA, were extremely low in the Antarctic and southwest Pacific waters. Their concentrations in Antarctic waters were 8 ng dm^?3 and 22 ng dm^?3 and those in the southwest Pacific were 12 ng dm^?3 and 25 ng dm^?3. In the other regions the concentration varied from 16 ng dm^?3 (China Sea) to 36 ng dm^?3 (north Indian Ocean) for MMAA and from 50 ng dm^?3 (east Indian Ocean) to 172 ng dm^?3 (north Indian Ocean) for DMAA. As a result, with the exception of Antarctic and southwest Pacific waters, the percentages of each arsenic species in the surface waters were very similar and varied from 52% (east Indian Ocean) to 63% (northwest Pacific Ocean) for As(V), from 22% (northwest Pacific Ocean) to 27% (east Indian Ocean) for As(III) and from 15% (northwest Pacific Ocean) to 21% (north and east Indian Oceans) for the methylated arsenics (MMAA+DMAA). These percentages in Antarctic waters were 97%, 0.2% and 2.8%, respectively, and those in the southwest Pacific Ocean were 97% for As(V)+As(III) and 3% for MMAA+DMAA. The very low concentrations of the biologically produced species in Antarctic waters and that of methylated arsenic in southwest Pacific waters indicated that the microorganism communities in these oceans was dominated by microorganisms having a low affinity towards arsenic. Furthermore, microorganism activity in the Antarctic was also limited due to the much lower temperature of the seawater there. The vertical profile of inorganic arsenic was 1350 ng dm^?3 in surface waters, 1500 ng dm^?3 in bottom waters with a maximum value of 1700 ng dm^?3 at a depth of about 2000 m in west Pacific waters. This fact suggested the uptake of arsenic by microorganisms in the surface waters and the co-precipitation of arsenic with hydrated heavy-metal oxides in bottom waters. The suggested uptake of inorganic arsenic and subsequent methylation was also supported by the profile of DMAA, with a high concentration of about 26 ng dm^?3 in surface water and a significant decrease to a value of 9 ng dm^?3 at a depth of 1000 m.     

液相色谱-电感耦合等离子体质谱法测定稻米中的5种砷形态

建立了稻米中砷酸根[As（Ⅴ）]、亚砷酸根[As（Ⅲ）]、砷甜菜碱（AsB）、一甲基砷（MMA）和二甲基砷（DMA）的液相色谱-电感耦合等离子体质谱（LC-ICP-MS）检测方法。以0.3 mol/L硝酸水溶液为提取试剂,样品在石墨消解仪中于95 ℃消解1.5 h,上清液供LC-ICP-MS分析。5种砷形态采用Dionex IonPac AS19阴离子交换柱（250 mm×4 mm）分离,经ICP-MS检测。比较了4种提取液对稻米中5种砷形态的提取效率,并对提取溶剂的浓度、提取温度和提取时间等条件进行了优化。通过加标回收试验结合测定标准物质考察了方法准确度及精密度,在2个加标水平上各形态的回收率为89.6%~99.5%,RSD（n=5）不大于3.6%,大米标准物质中各形态之和的测定结果与其标准值吻合,5种砷形态的线性范围AsB和DMA为0.05~200 μg/L,As（Ⅲ）和MMA为0.10~400 μg/L,As（V）为0.15~600 μg/L,方法检出限为0.15~0.45 μg/kg。结果表明,本方法简单、灵敏、耐用,可用于稻米中5种砷形态的准确定量和风险评估。     

毛细管电泳-电感耦合等离子体质谱法测定藻类中6种不同形态的砷化合物

建立了一种利用毛细管电泳与电感耦合等离子体质谱联用技术(CE-ICP-MS)分析检测6种不同形态砷化合物的方法。详细研究了缓冲溶液的种类、pH值和浓度,分离电压以及进样时间等因素对6种砷化合物的分离度、灵敏度和重现性等的影响。结果表明,在最佳条件下,三价砷(As3+)、一甲基砷(MMA)、二甲基砷(DMA)、五价砷(As5+)、砷胆碱(AsC)和砷甜菜碱(AsB)6种化合物在25 min内得到完全分离。6次平行测定中,6种砷化合物峰面积的相对标准偏差(RSD)为3%～5%,检出限(以As计)(3倍信噪比)为0.08～0.12 μg/L。应用该方法成功地对海带中6种砷化合物进行了分析,回收率为90%～103%。该方法具有耗时短、灵敏度高、样品消耗量少、稳定性好等优点,可用于藻类样品中不同形态砷化合物的分析。     

The Contrasting Behaviour of Arsenic and Germanium Species in Seawater

The vertical profiles of inorganic arsenic [As(III)+As(V)], monomethylarsonic acid (MMAA), dimethylarsinic acid (DMAA), inorganic germanium and monomethylgermanium (MMGe) were investigated at three sampling stations in the Pacific Ocean. In addition, the concentrations of these species in various surface waters have also been determined. The vertical profile of both inorganic arsenic and germanium displayed low concentrations, 1100 to 1450 ng dm³ for inorganic arsenic and <0.7 to 2 ng dm³ for inorganic germanium, in the surface zone. The concentrations of inorganic arsenic increased with depth to maximum concentrations that varied from 1500 to 2200 ng dm³ at a depth of 2000 m and then slowly decreased to concentrations that varied from 1300 to 1900 ng dm³ at a depth of 5000 m. On the other hand, the vertical profiles of inorganic germanium displayed a relatively constant concentration (4 to 8 ng dm³) from a depth of 2000 m to 5000 m. These vertical profiles of inorganic germanium were linearly correlated with those of silicate with a Ge/Si molar ratio of 0.715×10⁶. Both MMAA and DMAA displayed maximum concentrations in surface water and abruptly dropped with depth from 0 to 200 m. The concentration in surface water was 12 ng dm³ for MMAA and varied from 48 to 185 ng dm³ for DMAA. At depths >200 m, MMAA and DMAA were generally at comparable concentrations of about 3 ng dm³. In the case of MMGe, it was uniformly distributed throughout the water column at a concentration of approximately 16 ng dm³, indicating that MMGe was not involved in the biogeochemical cycling of inorganic germanium. In deep waters (>200 m), the concentrations of both inorganic arsenic and germanium increased from the southern Tasman Sea to the north. The increase in inorganic arsenic concentration was linearly correlated with that of phosphate and the increase in inorganic germanium concentration was linearly correlated with that of silicate, with apparent δAs/δP and δGe/δSi molar ratios of 4.53×10³ and 0.73×10⁶, respectively. © 1997 by John Wiley & Sons, Ltd.     

微波酸提取/液相色谱-电感耦合等离子体质谱法测定动物源性中药中6种砷形态

建立了微波酸提取/液相色谱-电感耦合等离子体质谱联用(LC-ICP-MS)测定动物源性中药中6种砷形态(亚砷酸盐As(Ⅲ),砷酸盐As(V),一甲基砷MMA,二甲基砷DMA,砷甜菜碱As B和砷胆碱As C)的分析方法。采用1%HNO_3溶液在80℃微波提取10 min,经离心分层,过固相萃取SEP C18柱和0.45μm滤膜,以25 mmol/L NH_4H_2PO_4溶液(p H 6.7)-乙醇(99∶1,体积比)为流动相进行等度洗脱,各砷形态在10 min内实现基线分离。结果显示,6种砷形态在1.0~100.0μg/L范围内线性关系良好,相关系数为0.999 5~0.999 7,方法检出限(LOD)为0.24~1.0μg/kg,相对标准偏差(RSD)为0.96%~2.0%。将方法应用于地龙、水蛭、海螵蛸、桑螵蛸、石决明和鸡内金中6种砷形态的测定,加标回收率为94.2%~103.8%,提取效率为95.5%~102.8%,优于热提取法。方法快速、准确、重现性好,适用于动物源性中药及类似样品中的砷元素形态分析及质量监控。     

Enzymatic digestion and chromatographic analysis of arsenic species released from proteins

A method combining gel filtration chromatography (GFC), protease digestion, and ion pair chromatography with inductively coupled plasma mass spectrometry detection was developed for the determination of arsenic species bound to proteins. The method was first established by examining the interactions of two model proteins, metallothionein (MT) and hemoglobin, with three reactive trivalent arsenic species. It was then successfully applied to the speciation of arsenic in red blood cells of rats. Inorganic arsenite (iAs^III), monomethylarsonous acid (MMA^III), and dimethylarsinous acid (DMA^III) were efficiently released from the proteins by protease digestion at pH 8.0, with the recovery ranging from 93% to 106%. There was no oxidation of iAs^III or MMA^III during the protease digestion process. Up to 61% DMA^III (the least stable arsenic species) was unchanged, and the rest was oxidized to the pentavalent dimethylarsinic acid (DMA^V). The arsenic species in the red blood cells of control rats was present as DMA^III complex with hemoglobin. The method enabling the determination of the specific arsenic species that bind to cellular proteins is potentially useful for studying arsenic distribution, metabolism, and toxicity.     

Identification of arsenic species in sheep‐wool extracts by different chromatographic methods

Sheep on the island of North Ronaldsay (Orkney, UK) feed mostly on seaweed, which contains high concentrations of dimethylated arsenoribosides. Wool of these sheep contains dimethylated, monomethylated and inorganic arsenic, in addition to unidentified arsenic species in unbound and complexed form. Chromatographic techniques using different separation mechanisms and detectors enabled us to identify five arsenic species in water extracts of wool. The wool contained 5.2 ± 2.3 µg arsenic per gram wool. About 80% of the arsenic in wool was extracted by boiling the wool with water. The main species is dimethylarsenic, which accounted for about 75 to 85%, monomethylated arsenic at about 5% and the rest is inorganic arsenic. Depending on the separation method and condition, the chromatographic recovery of arsenic species was between 45% for the anion exchange column, 68% for the size exclusion chromatography (SEC) and 82% for the cation exchange column. The SEC revealed the occurrence of two unknown arsenic compounds, of which one was probably a high molecular mass species. Since chromatographic recovery can be improved by either treating the extract with CuCl/HCl (CAT: 90%) or longer storage of the sample (CAT: 105%), in particular for methylated arsenic species, it can be assumed that labile arsenic–protein‐like coordination species occur in the extract, which cannot be speciated with conventional chromatographic methods. It is clear from our study of sheep wool that there can be different kinds of ‘hidden’ arsenic in biological matrices, depending on the extraction, separation and detection methods used. Hidden species can be defined as species that are not recordable by the detection system, not extractable or do not elute from chromatographic columns. Copyright © 2003 John Wiley & Sons, Ltd.     

Speciation of arsenic compounds by coupling high-performance liquid chromatography with inductively coupled plasma mass spectrometry

There is considerable evidence that toxicity and physiological behavior of arsenic depends on its chemical forms. Arsenic speciation became therefore the subject of increasing interest in recent years. A sensitive method for the determination of arsenic species has been developed. The proposed procedure involves the use of high-performance liquid chromatography and inductively coupled plasma mass spectrometry (HPLC-ICP-MS). Six arsenic compounds were separated by anion-exchange chromatography with isocratic elution using tartaric acid as mobile phase with an elution order: arsenocholine, arsenobetaine, dimethylarsinic acid, methylarsonic acid, arsenous acid and arsenic acid. The chromatographic parameters affecting the separation of the arsenic species were optimized. Analytical characterization of the method has been realized with standard solutions. The detection limits for six arsenic compounds were from 0.04 to 0.6 g/L as As element. The repeatability (expressed by R.S.D) was better than 7% for all investigated compounds. The HPLC-ICP-MS system was successfully applied to the determination of arsenic compounds in environmental and biological samples in g/L level.     

液相色谱-双通道原子荧光检测联用法同时测定砷和硒的形态

建立了一种利用高效液相色谱-双通道原子荧光检测联用同时进行砷和硒形态分析的方法。以10 mmol/L NH4H2PO4溶液(pH 5.6)(添加2.5%(体积分数)的甲醇)为流动相,在12 min内同时分离了三价砷(As(III))、一甲基砷(MMA)、二甲基砷(DMA)、五价砷(As(V))、硒代胱氨酸(SeCys)、硒代蛋氨酸(SeMet)和四价硒［Se(IV)］等化合物。As(III)、DMA、MMA、As(V)、SeCys、SeMet和Se(IV)的检出限分别为1,3,2,3,4,18和3 μg/L (进样量为200 μL),5次测定的相对标准偏差为1.9%～6.1%(As 100 μg/L, Se 300 μg/L)。应用该方法对人体尿样及硒酵母片中砷和硒的形态进行了分析,目标物在尿样中的加标回收率为83%～108%,在硒酵母片中的加标回收率为88%～105%。实验结果表明,该方法可用于尿样及药品中砷和硒形态的日常分析。该方法减少了样品的分析时间和试剂用量,降低了工作强度,提高了工作效率。