微波消解-高分辨电感耦合等离子体质谱法测定土壤中8种金属元素

微波消解结合电感耦合等离子体质谱(ICP-MS)是土壤样品中金属元素测定的常用方法,其前处理可以采用不同的消解体系,但是消解体系对分析结果的准确性影响较大。此外,应用ICP-MS测定某些元素时干扰的存在会影响结果的准确性。基于上述问题,本文优选三个酸体系微波消解溶样,采用高分辨电感耦合等离子体质谱(HR-ICP-MS)测定土壤样品中8种金属元素(Cr、Co、Ni、Cu、Zn、Pb、Cd和U)的含量,对比研究了由不同用量硝酸、盐酸、氢氟酸混合组成的三个酸消解体系对国家土壤标准物质的消解效果,确定了最优前处理方法。结果表明：经国家土壤标准物质验证,采用HR-ICP-MS检测,在不需要干扰校正的情况下,酸体系Ⅰ(6mL硝酸+3mL盐酸+3mL氢氟酸)和酸体系Ⅱ(2mL硝酸+6mL盐酸+1mL氢氟酸)的测定值与标准值相吻合,方法检出限为0.001～0.715μg/g,精密度(RSD,n=6)小于7.0%。从消解情况、准确度和精密度比较,酸体系Ⅰ稍优于酸体系Ⅱ;从酸用量比较,酸体系Ⅱ酸用量最少。两种酸体系的样品处理方法均具有较高的适用性和可靠性,都可用于土壤样品中8种金属元素含量的直接测定。     

密闭酸溶-电感耦合等离子体发射光谱/质谱法测定花岗伟晶岩中32种微量元素

花岗伟晶岩富集锂铍铷铯铌钽等稀有金属元素,准确测定其中的大离子亲石元素、高场强元素和稀土等微量元素,可用于判断成矿流体物质来源、成岩构造环境。目前的测试方法研究主要集中在锂铍铷铯铌钽等少数元素,样品消解方法有四酸敞开法、五酸敞开法、密闭酸溶法等,存在难溶矿物分解不完全、锆铪钍铀和稀土等元素回收率偏低等问题。本文对比了盐酸-硝酸-氢氟酸-高氯酸敞开消解法、盐酸-硝酸-氢氟酸-高氯酸-硫酸敞开消解法、硝酸-氢氟酸密闭消解法三种方法的分解效果。结果表明：四酸消解法中,铌钽锆铪钨和重稀土元素结果严重偏低;五酸消解法由于采用硫酸-氢氟酸-过氧化氢体系提取,有效地防止了铌钽的水解,铌钽钨等元素测定结果准确,但锆铪钡铅和轻稀土元素测定结果偏低。硝酸-氢氟酸密闭消解法使用王水代替硝酸进行残渣复溶,促进了铌钽锆铪和稀土等元素的复溶,采用电感耦合等离子体发射光谱和质谱法(ICP-OES/MS)可以准确测定花岗伟晶岩中稀有金属、稀土元素等32种元素,方法检出限为0.004～2.50μg/g,精密度(RSD,n=12)为1.0%～8.3%。将该方法应用于8种花岗岩、伟晶岩及稀有金属矿标准物质和三种类型实际样品...     

五酸溶样-电感耦合等离子体质谱法同时测定地质样品中的稀土等28种金属元素

电感耦合等离子体质谱法(ICP-MS)测定大批量地质样品中的稀土和钴铪铟锰铌钽铊铬镉镓锗钒锡等金属元素,主要采用三酸或四酸溶解样品。由于地质样品组分复杂,稀土等金属元素含量低,各元素性质差异大,三酸或四酸溶样经常出现易挥发元素如钒铬镉镓锡的测定结果不稳定、镧铈镨钕等稀土元素溶解不完全的问题。本文在盐酸-硝酸-氢氟酸-高氯酸四酸基础上引入硫酸,形成盐酸-硝酸-氢氟酸-高氯酸-硫酸五酸溶样体系,用于水系沉积物、土壤和岩石等不同类型地质样品的一次敞口溶解,采用在线加入~(185)Re和~(103)Rh内标方式,建立了应用ICP-MS同时测定稀土等28种金属元素的方法。钒铬镉镓锡元素的准确度提高了1.4%～14.6%,镧和铈元素的准确度提高了0.2%～8.9%。该方法应用于分析水系沉积物、土壤、岩石标准物质(分别为GBW07301a、GBW07408、GBW07107),其测定值与认定值相一致,相对标准偏差(RSD)为1.14%～9.84%,准确度(△lgC)均≤0.1。该方法分析过程较简单,结果准确可靠,可满足测定大批量地质样品中稀土和钴铪铟锰铌钽等金属元素含量的要求。     

高压密闭消解-电感耦合等离子体质谱法测定锰矿石中的稀土元素前处理方法研究

高压密闭消解因称样量小、用酸量少、空白低等优点成为测定稀土元素前处理的主要方法。但锰矿石组分复杂,锰含量差别较大且具有多种不同价态,常含有伴(共)生金属和其他杂质,该方法采用常规酸溶体系很难将其消解完全,造成ICP-MS测试结果不准确。本文从样品前处理消解效果出发,选择锰矿石标准物质GBW07261、GBW07263、GBW07266和一个锰矿石样品,试验了三种酸溶前处理方法对锰矿石稀土元素测试的影响。结果表明:方法一(氢氟酸-硝酸密闭消解,硝酸复溶提取)不能将锰矿石样品完全消解,测定值偏低0. 28%～61. 31%;方法二(氢氟酸-硝酸-双氧水密闭消解,硝酸-双氧水复溶,硝酸提取)和方法三(氢氟酸-硝酸密闭消解,盐酸复溶,硝酸提取)均可将锰矿石样品消解完全,用ICP-MS测定稀土元素的数据较为接近,与传统的过氧化钠熔融ICP-MS法测定值吻合。但实验过程中发现对于锰含量较高的样品,方法三需多次重复加入盐酸复溶后方可将样品消解完全,而方法二复溶一次即可。因此,方法二对锰矿石样品的消解效率更高,精密度好(0. 96%～2. 68%),加标回收率在95. 0%～107. 0%之间,更适用于锰矿石中稀土元素的分析。     

电感耦合等离子体发射光谱技术测定多金属伴生矿中钨钼铋两种消解方法的对比

当前多金属伴生矿中钨钼铋元素的测定方法主要是传统的硫氰酸钾比色法和EDTA容量法,均为单元素分析,操作过程繁琐,分析效率低,检测周期长,难以满足大批量样品简便、快速的分析要求。本文改进了传统的单元素分析法,对比了盐酸-磷酸-高氯酸-硝酸四酸和盐酸-硝酸-高氯酸三酸两种消解体系,并结合电感耦合等离子体发射光谱法（ICP-OES）,建立了一种同时测定多金属伴生矿中钨、钼、铋的快速分析法。结果表明：合理引入磷酸的四酸消解法对样品的消解更为彻底,钨、钼、铋的测定结果准确度更高,各元素测定值和标准值的相对误差介于-5.36%~-1.39%,精密度较高（RSD ≤ 4.18%）,方法检出限介于0.0027%~0.0037%。本方法应用于分析湖南郴州某地区多金属伴生矿实际样品,各元素加标回收率介于95.0%~103.0%,各项技术指标均优于三酸消解法。本方法提高了分析效率,结果准确可靠,适用于多金属伴生矿样品中钨钼铋及其他主次量元素的批量检测。     

混合酸敞开或高压密闭溶样-ICPMS测定地质样品中稀土元素

测定地质样品中的稀土元素时,用碱熔法处理样品过程繁琐,混合酸敞开酸溶法的酸种类多,用量较大,而微波消解法批次处理样品少,效率不高。本文比较了7种混合酸敞开酸溶体系、硝酸-氢氟酸高压密闭体系对样品溶样的效果,采用电感耦合等离子体质谱测定15个稀土元素的含量,建立了一套样品前处理体系简单、酸用量少、相对快捷的测定地质样品中稀土元素的方法。通过对59件国家标准物质的测试分析,结果表明硫酸-氢氟酸敞开酸溶和硝酸-氢氟酸高压密闭溶样两套体系的方法检出限、精密度、准确度均能达到地质行业相关标准测试要求。硫酸-氢氟酸敞开酸溶体系对于样品中钡含量较高,或样品量较少时适用;硝酸-氢氟酸高压密闭溶样体系的检出限更低,适用于大批量样品的分析测试。两套体系均不需要进行数学干扰校正,且酸用量少（最多6 mL）,分析效率高（平均每日分析测试300件）,有较大的推广应用价值。     

五酸和硝酸微波消解法结合ICP-OES技术测定多金属矿中多种元素的对比研究

快速、准确测定多金属矿中的主次量元素需要根据多金属矿的具体类型选择不同的预处理方法。本文采集我国典型区域的铅锌、锡、钼、钒和铜镍等5种多金属矿,对比了盐酸-硝酸-高氯酸-氢氟酸-硫酸五酸微波消解和硝酸微波消解的溶样效果,应用电感耦合等离子体发射光谱法(ICP-OES)测定铜铅锌锡钨钼锰钛钒9种元素。通过国家标准物质分析验证,五酸微波消解的溶样时间较长,但一次可测定铜铅锌钼锰钒6种元素;硝酸微波消解的溶样时间短,但一次只能测定铜铅锌钼4种元素;两种方法的准确度和精密度高(RSD5%),检出限低(5.3~30 mg/kg),均适合在地质行业推广应用。而由于锡钨钛3种元素不能完全被酸溶解,上述两种消解方法均不适合。     

四酸敞口溶解-电感耦合等离子体发射光谱法测定土壤中的硫

当前土壤中硫元素的测定方法主要是X射线荧光光谱法和燃烧法,上述两种方法分析速度慢,对高、低含量样品的分析精度较差,难以满足大批量样品快速、准确分析的要求。为提高分析速度和结果的准确度,本文建立了用盐酸-硝酸-氢氟酸-高氯酸(四酸)溶解土壤样品,电感耦合离子体发射光谱法测定硫的方法。通过考察王水消解、王水水浴消解和四酸消解的溶样效果,测定结果表明采用四酸能更好地溶解土壤样品中的硫。方法检出限为10μg/g,测量范围为33.3~50000μg/g,相对标准偏差为0.47%~4.05%。本方法简单快速,准确度高,已经过数千件实际样品验证,在不增加分析成本的情况下,一份溶液还可以同时测定钾钠钙镁铁锰铍锂镧铈钪钒钴镍钛等元素,适合在地质行业推广应用。     

微波消解-氢化物发生原子荧光光谱法测定粉煤灰中的硒

粉煤灰中含有的硒元素较高,有综合利用价值.由于基体的复杂性,并未形成成熟可靠的测定技术.本文参考煤炭样品和土壤样品中硒的原子荧光光谱分析方法,采用氢化物发生-原子荧光光谱法测定粉煤灰中的硒.样品经氢氟酸-硝酸-双氧水体系微波消解得到清亮、透明的消解液,消解液经浓盐酸还原后,加入三价铁盐消除共存元素的干扰,所加的铁盐量不干扰硒的测定.方法检出限为0.020 μg/g;平行测定5份粉煤灰样品,相对标准偏差低于4.2％;加标回收率为94.0％～105.0％.应用建立的方法对煤飞灰标准物质进行分析,测定值与标准值基本相符;对不同地区的实际粉煤灰样品进行分析,证实方法可靠,可用于粉煤灰中硒元素的测定.     

敞开酸溶-电感耦合等离子体质谱法同时测定钨矿石和锡矿石中14种微量元素

钨矿石和锡矿石成分复杂,具有丰富的共生或伴生元素。在国家标准方法中,对其中的微量共生或伴生元素含量多采用单元素测定,分析强度大,效率低。本文采用混合酸在敞开体系中消解样品,以50%盐酸提取盐类,电感耦合等离子体质谱仪(ICP-MS)同时测定钨矿石和锡矿石中的锂钪铬钴镍铜铅锌铷钼铯锑铋钍等14种微量元素。通过比较碱熔法、盐酸+氢氟酸+硝酸+高氯酸四酸溶矿法、氢氟酸+硝酸+高氯酸三酸溶矿法这三种样品前处理方法,确定选择使用氢氟酸+硝酸+高氯酸三酸溶矿法溶解样品。ICPMS测定过程中,选择铑和铼作为内标元素,有效监控分析信号的漂移。测定结果表明,各元素的检出限为0.003~1.64μg/g,相对标准偏差在0.1%~3.1%,方法回收率在93.1%~104.3%。方法应用于实际钨矿石和锡矿石分析,测定结果与各元素标准测定值吻合较好。相对于传统处理方法,本法一次溶样,多元素同时测定,使分析效率得到了有效提高,更适合大批量多元素钨矿石和锡矿石样品的分析。     

四种前处理方法对电感耦合等离子体质谱测定植物样品中27种微量元素的影响

采用HNO₃-HClO₄-HF常压消解、HNO₃-H₂O₂-HF高压密闭消解、HNO₃-H₂O₂微波消解,干法灰化后残渣用HNO₃-HF-HClO₄溶解等四种方法对植物样品进行前处理,使用电感耦合等离子体质谱(ICP-MS)对植物样品中的27种元素进行定量分析,探讨了不同前处理方法对ICP-MS测定植物样品中微量元素的影响。分析结果表明: HNO₃-HClO₄-HF常压消解使用大量试剂,污染环境,造成空白值高;在常压体系中HClO₄的加入能提高样品的消解效率,但赶酸不完全,会造成复合离子对钒和砷的干扰;干法灰化过程中某些元素(硼、汞等)会损失;常压消解和高压密闭消解中加入HF能有效地提高铍、稀土、钇、钛、锑、铀等元素的回收率,但在蒸干赶HF的过程中,会造成硼和汞的损失,并且钢套的生锈会造成铬、镍空白值高。尽管没有一种方法能适用于所有元素的分析,但相比较而言,HNO₃-H₂O₂微波消解体系操作简单,大部分元素(除铍、钛、锑、铋、稀土)能得到满意的结果,精密度(RSD)均小于10%(n=10),相对误差(RE)为-4.6%~13.6%。     

土壤中重金属元素电感耦合等离子体质谱定量分析方法的研究

分别采用HNO3-HF、HNO3-HF-HCl和HNO3-HF-H2O2三种消解体系,通过微波和PTFE密封罐电热板对土壤标准物质进行前处理,采用电感耦合等离子体质谱(ICP-MS)对样品中的重金属元素Cr、Ni、Cu、Zn、As、Cd和Pb进行定量分析。探讨了前处理试剂(主要为HNO3、HCl和HF)以及土壤基体效应对Cr、Ni、Cu、Zn、As、Cd和Pb定量分析的影响。研究结果表明,前处理试剂对Cr、Ni、Cu、Zn、As、Cd和Pb的定量分析具有不同程度的影响;对于土壤基体,在三种消解体系下均可观察到基体抑制效应;采用PTFE密封罐电热板消解方法前处理,待测元素及相同元素不同同位素的方法空白和检出限均较低,效果整体优于微波消解法。特别是HNO3-HF-HCl消解体系,通过选用52Cr、60Ni、65Cu、66Zn、75As和206Pb等同位素,重金属元素Cr、Ni、Cu、Zn、As、Cd和Pb的测定值均能保证在标准值的允许误差范围内,可以满足大批量土壤样品中重金属元素同时定量分析的需要,为高效准确地开展土壤的风险评估以及为土壤的修复治理提供科学依据。     

微波消解-电感耦合等离子体质谱法同时测定金属硫化矿中的稀散元素

铜精矿、镍精矿和锌精矿是金属硫化矿物,且为大宗进口商品,准确分析其中的稀散元素有利于矿物的综合利用。这类矿物中的稀散元素含量极低,各元素性质各异,尤其Ge和Se在湿法消解中由于挥发损失而无法准确定值,很难进行多种元素的同时测定,传统的方法需要通过预先分离富集,采用不同的仪器进行测定。本文以铜精矿、锌精矿和镍精矿为代表性硫化矿,采用微波消解对样品进行密闭前处理,电感耦合等离子体质谱法(ICP-MS)测定稀散元素含量,实现了多种元素的同时测定。条件实验表明在同时检测镓、锗、硒、镉、铟、碲、镧、铊的过程中,总固溶量、内标、质谱干扰消除的条件对三种金属硫化矿均一致,只是前处理过程中用酸的选择有些差异。硝酸-盐酸-氢氟酸-过氧化氢体系适合于测定镍精矿和锌精矿中的Ga、Ge、Se、Cd、In、Te、La、Tl和铜精矿中的Ga、Ge、Se、Cd、In、La、Tl,各元素的回收率在85.5%～116.6%之间;王水溶样法更适合测定铜精矿中的Te。     

Quantification of Cl,Br and I in Geological Materials by NH4F Digestion: Comparison with Rapid Acid Digestion

The lack of analytical techniques for halogens in geological materials is mainly due to the loss of analytes during sample preparation. This study describes a rapid bulk rock digestion method (NH₄F digestion) for determination of the abundances of Cl, Br and I in geological materials by SF-ICP-MS. During high temperature (200–240 °C) digestion, NH₃ released from the decomposition of molten NH₄F can effectively prevent the loss of halogens released from geological samples. Chlorine, Br and I were not lost during NH₄F digestion at 220 °C for 0.25–6 h. The limits of quantitation for NH₄F digestion were 2.8, 0.018 and 0.003 μg g^-1 Cl, Br and I, respectively. Most results for halogens in geological reference materials by NH₄F digestion were in agreement with their certified values, confirming that the high-performance rapid bulk rock NH₄F digestion has sufficient digestion capability to extract Cl, Br and I from rocks, sediments and soils. In comparison, results obtained following acid digestion showed that HNO₃ + HF digestion could effectively extract Br and I from soil and sediment samples, and that HNO₃ acid digestion is only suitable to use for the determination of Br and I in soil samples.     

电感耦合等离子体质谱法测定灌木枝叶中微量元素的样品预处理方法研究

利用电感耦合等离子体质谱法(ICP-MS)测定植物样品中微量元素的关键技术是消除植物样品的有机基体效应,本文通过预处理方法中的酸消解体系、称样量和消解方式消除其影响。以国家标准物质灌木枝叶组合样(GBW07603)为材料进行研究,对比分析了硝酸-过氧化氢、硝酸-氢氟酸、硝酸-氢氟酸-过氧化氢3种酸溶体系的消解效果,以确定最佳酸溶体系,进而定量研究2种称样量(50 mg和100 mg)和3种消解方式(密封高压二次消解、密封高压一次消解、微波消解)的消解效果,并以In作为内标采用ICP-MS测定微量元素含量。结果表明:硝酸-氢氟酸-过氧化氢酸溶体系的消解效果最好;50 mg的测定值更接近于参考值;微波消解法的测定值明显偏低,而密封高压二次消解法是灌木枝叶样品预处理的有效方法。     

Reassessment of HF/HNO3 Decomposition Capability in the High‐Pressure Digestion of Felsic Rocks for Multi‐Element Determination by ICP‐MS

Complete dissolution is essential to obtain accurate analytical results for geological samples. Felsic rocks are known to be very difficult to dissolve because of the presence of refractory minerals such as zircon. In this study, we undertook a systematic evaluation of the effect of the HF/HNO₃ ratio, digestion time, digestion temperature, digested test portion mass and the presence of insoluble fluorides on analytical results for the felsic rock GSP‐2 using high‐pressure HF and HF/HNO₃ digestion. Digestion in mixtures of HF and HNO₃ acids is a commonly used method of dissolution for geological samples. However, our results clearly indicate that adding HNO₃ inhibited the digestion capabilities of HF for refractory minerals such as zircon. It took 8–12 hr for Zr to be completely recovered in GSP‐2 at 190 °C, whereas it needed about 36 and 72 hr at 160 and 140 °C, respectively. White precipitates were observed in the final solution for test portion mass > 100 mg, irrespective of which of the five different digestion solutions was used (1 ml HF, 2 ml HF, 1 ml HF + 0.5 ml HNO₃, 1 ml HF + 1 ml HNO₃ and 1.5 ml HF + 1.5 ml HNO₃). Environmental scanning electron microscopy showed that these precipitates were mainly composed of AlF₃. Instead of further HCl, HNO₃ or HClO₄ attack, we propose that using ultra‐fine samples and a small sample size is a good way to avoid the formation of insoluble residues (e.g., fluorides). To further investigate the precision and accuracy of the proposed method (using HF alone as the digestion solution during the first acid attack step), a suite of silicate rock reference materials was analysed. Most of the results were found to be in reasonable agreement with the reference values, with a relative error of < 10%.     

Direct Current Plasma Emission Spectrometric Determination of Major, Minor and Trace Elements in Microwave Oven Acid Leachates of Powdered Whole Coal Samples

Major concentrations of Al₂O₃, Fe₂O₃, MgO, CaO, Na₂O and K₂O, minor levels of TiO₂, P₂O₅ and thirty petrologically, geochemically and environmentally significant trace elements have been determined in microwave oven acid leachates of whole powdered coal samples by direct current plasma‐atomic emission spectrometry (DCP‐AES). A single sample preparation procedure was suitable for all the determinations with no additional dilution step for major elements solution. Dried samples (0.5 g) were treated in low‐pressure PFA digestion vessels with HF/HCl/HNO₃/HClO₄ acids to quantitatively extract the analytes from the bulk material, while leaving the major part of organic matrix as a residue. The major constituents of geological samples, in particular the easily ionised elements (EIEs) such as alkali and alkaline earths, may complicate the instrumental determinations in DCP‐AES because of differential enhancements of elemental emission intensities and stray light interferences. Taking account of these factors, the coal matrix is considered to have very low major oxide totals as compared to many other common geo‐environmental and related materials (rocks, sediments, soil, ashes etc.). The sample size employed here, while yielding a relatively concentrated solution to cover a wide range of elemental determinations, provided a sample matrix that significantly diminished interferences for DCP measurements. The need for closely matching the unknowns and calibrators was eliminated except for overall acidity and an excess quantity of caesium for EIE buffering. Calibration of the spectrometer was accomplished by simple aqueous single element solutions as high concentration calibrators in addition to a reagent blank as a low concentration calibrator. Two point working curves were established to allow for the maximum concentrations of each element expected in the unknowns. The precision of determinations under routine conditions as well as the reproducibility of the leaching and precision of instrumental measurements have been evaluated. Relative standard deviations (RSD) were of 1–2% for those elements whose concentrations in solid samples were well above the limits of quantification. Method detection limits in the buffered solutions were also evaluated. To evaluate the accuracy of the microwave oven‐DCP method a suite of eight certified coal reference materials of differing rank, were analysed with good agreement with the certified and/or available published data. Results are presented for the uncertified major oxides in the AR series reference materials.     

A Rapid Acid Digestion Technique for the Simultaneous Determination of Bromine and Iodine in Fifty‐Three Chinese Soils and Sediments by ICP‐MS

Bromine and iodine are important tracers for geochemical and environmental studies. In this study, a rapid acid digestion (HNO₃ + HF) with ammonia dilution for the simultaneous determination of bromine and iodine in soils and sediments using ICP‐MS was developed. The recoveries of Br and I were controlled by the synergic effect of temperature and time. It took only 15 min at 140 °C for the complete recovery of Br and I in sediment (GSD‐2) and soil (GSS‐24) reference materials, which is a process that needs 2–6 h at 90 °C. A serious loss of Br and I was found at a higher digestion temperature of 190 °C. A 5% v/v NH₄OH dilution effectively eliminated the memory effects and stabilised the signals of Br and I. Moreover, ammonia dilution also avoided the corrosiveness of HF on the sample introduction system and torch of ICP‐MS. Tellurium is a more suitable internal standard element than In in the ammonia medium. To avoid the adsorption of residues of dissolution on Te, addition of Te should be carried out after centrifuging the solution. The developed method was successfully applied to determine Br and I in fifty‐three Chinese soil and sediment reference materials. This simple method shows great potential for the rapid determination of Br and I in large batches of geological and environmental samples commonly analysed for mineral exploration and environmental geochemistry studies.     

电感耦合等离子体串联质谱法测定电解二氧化锰废渣浸出液中的重金属元素

电解二氧化锰废渣中的重金属元素在雨水淋滤下,通过地表径流对下游水生态系统及农业生态系统造成不同程度的环境污染和安全隐患,因此,准确测定电解二氧化锰废渣浸出液中的重金属元素含量具有重要的现实意义。电解二氧化锰废渣浸出液中的重金属元素含量通常很低,采用原子吸收光谱法、电感耦合等离子体发射光谱法测定,检出限通常难以满足测定要求。采用电感耦合等离子体质谱法(ICP-MS)测定,消除复杂质谱干扰面临挑战。本文采用电感耦合等离子体串联质谱(ICP-MS/MS)测定电解二氧化锰废渣浸出液中的重金属元素含量。电解二氧化锰废渣中6种重金属元素Cr、Ni、As、Cd、Hg、Pb经硫酸和硝酸混合酸浸出后直接采用ICP-MS/MS进行测定,利用串联质谱的O_2反应模式消除分析过程中Cr、Ni、As、Cd受到的质谱干扰,通过考察不同分析模式下~(52)Cr、~(60)Ni、~(75)As、~(111)Cd的背景等效浓度(BEC),评价质谱干扰对分析结果的影响。结果表明:在MS/MS模式下选择O_2为反应气,采用质量转移法和原位质量法可以消除~(52)Cr、~(60)Ni、~(75)As、~(111)Cd的所有质谱干扰。Cr、Ni、As、Cd、Hg、Pb检出限分别为3.06、9.31、3.50、2.72、2.03、1.89ng/L,加标回收率在95.6%～106.2%之间,相对标准偏差(RSD)≤3.9%。所建立的方法已应用于电解二氧化锰废渣浸出液中重金属元素的测定。