固相萃取-衍生化-气相色谱/质谱测定水中类固醇类环境内分泌干扰物

建立了固相萃取-衍生化-气相色谱/质谱联用同时测定水中4种类固醇类环境内分泌干扰物雌酮(E1)、17β-雌二醇(E2)、17α-乙炔基雌二醇(EE2)、雌三醇(E3)的分析方法.通过对比衍生化试剂 N,O-双三甲基硅基三氟乙酰胺(BSTFA)和N-甲基-N-三甲基硅基三氟乙酰胺(MSTFA)的衍生化条件及效果,解释了文...     

高效液相色谱-串联质谱法检测生物样品中6种雌激素

建立了雌酮、雌二醇、雌三醇、己烯雌酚、己烷雌酚和炔雌醇6种雌激素在生物体中的HPLC-MS/MS分析方法.采用加速溶剂萃取、固相萃取技术进行提取、富集及净化,有效降低了基质的干扰.以甲醇-0.1％氨水溶液为流动相,以C18色谱柱进行分离,质谱采用电喷雾负离子扫描模式,6种雌激素的回收率为88％～104％,相对标准偏差在1.3％～8.3％之间.雌酮、雌二醇、雌三醇在生物体中的方法检出限0.35ng/g;己烯雌酚、己烷雌酚、17α-乙炔基雌二醇在生物体中的方法检出限为0.13ng/g.方法适用于生物体内雌激素的分析和检测.     

气相色谱-质谱法测定尿及河底泥中的环境雌激素

报道了尿及河底泥中环境雌激素(壬基酚、双酚A、己烯雌酚、17α-乙炔基雌二醇)和内源性雌激素(17α-雌二醇、17β-雌二醇、雌三醇、雌酮)的气相色谱-质谱(GC-MS)测定法。尿样经盐酸溶液水解后用固相萃取(SPE)柱浓缩净化,底泥样品用甲醇-乙酸乙酯萃取。被测组分经五氟丙酸酐(PFPA)衍生化后用GC-MS进行定性定量检测。该法测定的峰面积的日内相对标准偏差为1.22%-5.55%,检出限为0.05-1.27 μg/L(或μg/kg)。被测组分的加标回收率除尿样中17α-乙炔基雌二醇和己烯雌酚分别为2     

固相萃取-衍生化-气相色谱-质谱法测定水中类固醇类雌激素

采用固相萃取-衍生化-气相色谱-质谱法同时测定水中4种类固醇类雌激素雌酮(E1)、17β-雌二醇(E2)、17α-乙炔基雌二醇(EE2)、雌三醇(E3)。样品经Oasis HLB固相萃取柱,以丙酮为溶剂进行洗脱后,采用吡啶、N-甲基-N-三甲基硅基三氟乙酰胺于40℃衍生化20min后,采用气相色谱-质谱仪分析。E1、E2、EE2和E3的线性范围分别为5.00~500μg·L-1和10.0~500μg·L-1,4种类固醇类雌激素的检出限(3S/N)在1.5~3.0μg·L-1之间,测定下限(10S/N)在5.0~10μg·L-1之间;方法用于实际水样的分析,加标回收率在86.8%~93.8%之间,测定值的相对标准偏差(n=7)在7.1%~11%之间。     

固相萃取-气相色谱/质谱联用法同时检测水体中9种环境雌激素

建立了固相萃取-气质联用法(SPE-GC-MS)测定水体中9种环境雌激素:雌酮(E1)、17b-雌二醇(E2)、雌三醇(E3)、4-辛基酚(OP)、4-壬基酚(NP)、双酚A(BPA)、己烯雌酚(DES)、美雌醇(EE3ME)和17a-炔雌醇(EE2)的检测方法,优化了萃取和衍生化反应条件,实验结果表明:HLB柱回收率较高,衍生化反应的温度为75℃,衍生时间为90 min;本方法对9种环境雌激素的加标回收率为60.5%～126.7%,对应的相对标准偏差为0.8%～11.1%,方法检出限为1.08～8.60 ng/L,并将本方法应用于实际环境水样的检测。     

气相色谱-质谱法检测动物肌肉组织中残留的甾类同化激素

建立了不同动物肌肉中甾类同化激素残留的气相色谱/质谱（GC/MS）检测方法。样品经酶解、组织捣碎和超声提取后,用叔丁基甲醚萃取和反相固相萃取柱净化,进一步衍生后进行GC/MS分析,分别测定雄激素（表睾酮（ETS）、丙酸睾酮（PTS）、19-去甲基睾酮（17β-NT）、甲基睾酮（MTS）)和雌激素（雌二醇（17β-ES）、雌三醇（EST）、炔雌醇（EES）、雌酮（ESN）、苯甲酸雌二醇（BES)）。实验结果表明,ETS、17β-NT、MTS、PTS、BES、ESN、17β-ES、EES和EST的定量检测限为1.0~2.0 μg/kg。在2.0 μg/kg的定量检测低限添加水平,上述9种激素的平均回收率为62.5%~80.5%,相对标准偏差为12.5%~26.8%。该法可实现对样品进行灵敏、准确的定性定量分析。     

液相色谱串联质谱法测定牛奶中的内源性雌激素

建立了液相色谱-串联质谱法测定牛奶中4种内源雌激素的方法,可用于牛奶中17-α-雌二醇、17-β-雌二醇、雌三醇和雌酮等4种内源雌激素的同时测定。牛奶样品中添加内标化合物后,经过酶解、提取、净化、衍生等步骤获得上机试液,用LC-MS/MS测定,采用多反应监测正离子模式扫描。实验表明,4种化合物溶液质量浓度在0.0625~5.0μg/L之间有较好的线性关系,相关系数(R2)0.995,方法检出限在0.28~0.64 ng/kg之间。17-α-雌二醇回收率较低,只有60%左右,其它化合物的回收率均在72%~115%、相对标准偏差10%。在对57个样品的实际检测中,牛初乳E1,αE2,βE2,E3平均含量为3220,727,889,167 ng/kg;常乳中E1,αE2,βE2,E3含量为19.3~520 ng/kg,2.3~90.2 ng/kg,3.3~46.0 ng/kg,未检出~19.2 ng/kg。     

分散液液微萃取-柱前衍生-高效液相色谱法测定水样中双酚A

建立了分散液液微萃取-柱前衍生-高效液相色谱法测定水样中双酚A的分析方法.通过交互正交试验和混合型优化实验设计对影响因素(萃取剂体积、分散剂类型及其体积、水样体积、pH值及离子强度)进行了优化.优化后的分散液液微萃取条件为:60 μL萃取剂,0.4 mL分散剂(甲醇),pH 4.0;优化后的柱前衍生化条件:0.1 mL 2.0 g/L衍生剂(对硝基苯甲酰氯)、衍生化时间30 min;方法的线性范围:0.002～0.2 mg/L(r=0.9997),检出限0.007 μg/L(S/N=3);不同浓度双酚A的萃取率为59.0%～63.0%,相对标准偏差(RSD)2.5%～9.2%(n=5);水样中双酚A的加标率为86.5%～107.1%,RSD为4.0%～11.9%(n=5),其它雌激素(雌酮、雌二醇、雌三醇和17α-乙炔基雌二醇)对双酚A的测定无干扰.本方法可以对水环境中的痕量BPA进行检测,具有操作简便、快速等优点.     

固相萃取-超高效液相色谱-三重四极杆质谱法同时测定不同水体中的6种雌激素

建立了固相萃取-超高效液相色谱-三重四极杆质谱（SPE-UPLC-MS/MS）联用技术同时测定不同水体中6种雌激素（雌三醇、17-β-雌二醇、17- α-雌二醇、雌酮、炔雌醇、己烯雌酚）的分析方法。样品经HLB固相萃取柱提取和净化后经BEH C18色谱柱分离,采用MS/MS多反应监测模式（MRM）进行分析。采用内标法定量,以雌三醇-D3、17-β-雌二醇-D2、己烯雌酚-D8为内标。当6种雌激素的质量浓度在1.0~100 μg/L线性范围内时,所得回归方程的相关系数（r）均不小于0.9982;方法检出限为0.27~0.45 ng/L,定量限为1.08~1.78 ng/L;在高、中、低3个添加水平下的回收率为68.3%~97.4%,相对标准偏差（RSD）小于15%。该方法灵敏、准确,检测范围广,分析速度快,适用于地表水、废水、饮用水源水及生活用水等不同水体中6种雌激素的同时检测。     

固相萃取-分散液液微萃取-柱前衍生法测定水样中痕量雌激素

建立了碳纳米管的固相萃取-分散液液微萃取-柱前荧光衍生化(SPE-DLLME-PFD)测定水体中痕量雌三醇(E3)、双酚A(BPA)、17α-乙炔基雌二醇(EE2)及17β-雌二醇(E2)的高效液相色谱方法.采用中心复合设计和响应曲面法分析并优化SPE、DLLME及PLD条件,最佳条件为210 mL水样以2.0 mL/min的流速过固相萃取柱(碳纳米管量30 mg),甲醇洗脱,氮气浓缩并定容至0.6 mL(分散剂),将100 μL C6MIM[PF6]与分散剂的混合液注入到NaCl含量为25％的2.0 mL去离子水中,离心,移取20 μL下层有机相于样品瓶中,与4.0 mg衍生剂混合,在40℃水浴中衍生25 min;用0.1mL甲醇溶解过量的衍生剂颗粒,取20 μL进样分析.在优化条件下.4种雌激素的线性范围为0.05～5.00 μg/L,相关系数R2=0.9966～0.9999;,检出限介于0.13～6.33 ng/L(S/N=3)之间.不同加标浓度条件下,雌激素的加标回收率在83.1％～122.4％范围内(RSD=1.7％～9.6％).在实际水样中E3和BPA检出率较高.与其它方法相比,本方法虽然萃取时间长、水样量大、步骤多,但具有检出限低、操作简便、环境友好等优点.     

Determination of estrogenic steroids in surface water and wastewater by liquid chromatography-electrospray tandem mass spectrometry

An analytical method is presented which permits trace level determination of 17alpha-ethynylestradiol (EE2), 17beta-estradiol (E2), and estrone (E1). Using this method, the estrogenic steroids were analyzed in drinking water, surface water, and wastewater (sewage influents and effluents) at concentrations down to 0.1 ng/L. Sample volumes between 100 and 500 mL are concentrated using automated solid-phase extraction. Analysis is performed by liquid chromatography with detection by tandem mass spectrometry. Applying simple clean-up procedures and internal standard calibration, recovery losses resulting from matrix-dependent ion suppression during electrospray ionization could be compensated for all of the investigated compounds. Recoveries around 100% were obtained for all analytes after correction using the internal standards. Limits of quantification (LOQ) were between 0.1 and 0.4 ng/L for purified sewage, surface, ground, and drinking water and between 1 and 2 ng/L in the case of raw sewage. Water treatment by wastewater treatment plants (WWTPs) or by a surface water treatment plant affected the removal of all estrogenic steroids. Thus, E1, E2, and EE2 were removed in the municipal WWTPs to the extent of 93%, 93%, and 80%, respectively. In the effluents of the WWTP in Ruhleben (Berlin, Germany), E1, E2, and EE2 were detected at the low ng/L level. E2 and EE2 were, however, not present in the Berlin surface water above the LOQ (0.2 ng/L). E1 was the only compound that could be detected in surface water samples. After additional surface water treatment it was still detectable but only at trace-level concentrations with a mean value of 0.16 ng/L.     

固相萃取–HPLC–ICP/MS法测定水中的烷基汞

建立了固相萃取、高效液相色谱与电感耦合等离子体质谱联用技术测定水中烷基汞的方法。对固相萃取、高效液相色谱和电感耦合等离子体质谱的实验条件进行了优化。在优化条件下,甲基汞和乙基汞的检出限分别为0.5,0.7 ng/L。对地表水、工业废水和生活污水3种水样分别加标10.0,50.0 ng/L进行测定,测定结果的相对标准偏差为3.3%~9.6%(n=6),加标回收率在81.0%~103.0%之间。该方法灵敏度高,实用性强。     

Trace analysis of 28 steroids in surface water, wastewater and sludge samples by rapid resolution liquid chromatography-electrospray ionization tandem mass spectrometry

A sensitive rapid resolution liquid chromatography-tandem mass spectrometry (RRLC-MS/MS) method, combined with solid-phase extraction, ultrasonic extraction and silica gel cartridge cleanup, was developed for 28 steroids including 4 estrogens (estrone (E1), 17β-estradiol (E2), 17α-ethynyl estradiol (EE2), diethylstilbestrol (DES)), 14 androgens (androsta-1,4-diene-3,17-dione (ADD), 17α-trenbolone, 17β-trenbolone, 4-androstene-3,17-dione, 19-nortestoserone, 17β-boldenone, 17α-boldenone, testosterone (T), epi-androsterone (EADR), methyltestosterone (MT), 4-hydroxy-androst-4-ene-17-dione (4-OHA), 5α-dihydrotestosterone (5α-DHT), androsterone (ADR), stanozolol (S)), 5 progestagens (progesterone (P), ethynyl testosterone (ET), 19-norethindrone, norgestrel, medroxyprogesterone (MP)), and 5 glucocorticoids (cortisol, cortisone, prednisone, prednisolone, dexamethasone) in surface water, wastewater and sludge samples. The recoveries of surface water, influents, effluents and sludge samples were 90.6-119.0% (except 5α-DHT was 143%), 44.0-200%, 60.7-123% and 62.6-138%, respectively. The method detection limits for the 28 analytes in surface water, influents, effluents and freeze-dried sludge samples were 0.01-0.24 ng/L, 0.02-1.44 ng/L, 0.01-0.49 ng/L and 0.08-2.06 ng/g, respectively. This method was applied in the determination of the residual steroidal hormones in two surface water of Danshui River, 12 wastewater and 8 sludge samples from two wastewater treatment plants (Meihu and Huiyang WWTPs) in Guangdong (China). Ten analytes were detected in surface water samples with concentrations ranging between 0.4 ng/L (17β-boldenone) and 55.3 ng/L (5α-DHT); twenty analytes in the wastewater samples with concentrations ranging between 0.3 ng/L (P) and 621 ng/L (5α-DHT); and 12 analytes in the sludge samples with concentrations ranging between 1.6 ng/g (E1) and 372 ng/g (EADR).     

分散液-液微萃取-气相色谱/质谱联用法测定机械加工水基切削液及其废水中的三氯苯

建立了以丙酮为分散剂、氯苯为萃取剂,采用分散液-液微萃取、气相色谱/选择离子质谱联用测定机械加工水基切削液及其废水中三氯苯的方法。该方法与顶空萃取、液-液萃取和固相萃取结合气相色谱/电子捕获检测法相比,具有线性范围广、富集倍数高、重现性好、操作简便、干扰小等优点。样品中三氯苯的加标回收率为94.7％~104.3％,相对标准偏差为2.3％～7.8％。三氯苯的3种同分异构体1,3,5-,1,2,4-和1,2,3-三氯苯的检出限分别为2.0,6.0和3.0 μg/L。重点探讨了萃取剂和分散剂的种类、体积、萃取时间和盐效应等对三氯苯萃取效率的影响,优化了萃取条件。考察了机械加工水基切削液中常用的添加剂对检测结果的影响,结果表明1.0％的亚硝酸钠和聚乙二醇对三氯苯的检测基本无影响。采用该方法对4种实际样品中的三氯苯进行了测定,其中两个样品中含有三氯苯,质量浓度范围为0.15～1.67 mg/L。     

QuEChERS结合UPLC-M S/M S检测血液中苯丙胺类及其相关9种物质

对QuEChERS前处理方法从提取、分离、净化等方面进行优化以减弱样本中的基质效应,提高灵敏度;使用提取试剂(含0.1%甲酸的乙腈:甲醇=70:30,V/V)进行提取,加入无水硫酸镁、硼酸钠、研磨珠进行提取分离,使用混合净化剂(十八烷基硅烷(C18):乙二胺-N-丙基硅烷(PSA)=1:2,m/m)进行净化,UPLC-MS/MS测定,外标法定量。结果表明:在优化条件下,苯丙胺类及其相关9种物质的色谱峰分离良好,且各标准化合物的线性相关系数均大于0.991,检出限(LODs)为0.3~1.0 ng/mL,定量限(LOQs)均为2.5 ng/mL;血液添加标准品样本在低(20 ng/mL)、中(100 ng/mL)、高(400 ng/mL)3个浓度的加标回收率为80.1%~103.1%,精密度相对标准偏差(RSD)为1.5%~8.6%;临床4份检测样本中有3份检出苯丙胺类阳性,准确率为71.5%~99.1%。所建立的QuEChERS方法与UPLC-MS/MS结合的分析方法可应用于血液样本中苯丙胺类及其相关9种药物的同时检测分析。     

HS-SPME–GC–MS法测定水中2-甲基异冰片及土臭素

采用顶空固相微萃取–气质联用(HS-SPME–GC–MS)的方法对地表水中2-甲基异冰片(2-MIB)和土臭素(GSM)进行分析测定。通过试验确定了HS-SPME的最佳萃取条件:萃取头为DVB/CAR/PDMS,萃取时间为30 min,萃取温度为70℃,NaCl的加入量为30%(质量分数),萃取纤维在GC上的解吸温度为250℃。用内标法进行定量,2-MIB,GSM的质量浓度在5~100 ng/L范围内与色谱峰面积呈良好的线性关系,线性相关系数(r2)分别为0.999 7,0.997 0,检出限分别为0.8,1.7 ng/L。采用该法对水样进行测定,2-MIB,GSM测定结果的相对标准偏差为2.6%~6.3%(n=6),加标回收率为92%~112%。该方法能简单、快速地测定水中痕量嗅味物质。     

Optimization of large volume injection-programmable temperature vaporization-gas chromatography-mass spectrometry analysis for the determination of estrogenic compounds in environmental samples

Large volume injection-programmable temperature vaporization-gas chromatography-mass spectrometry (LVI-PTV-GC-MS) was optimized for the determination of estrone (E1), 17β-estradiol (E2), 17α-ethynyl estradiol (EE2), mestranol (MeEE2) and estriol (E3) for their determination in environmental samples (estuarine water, wastewater, fish bile and fish homogenate) after derivatization with 25 μL (BSTFA+1% TMCS) and 125 μL of pyridine. Experimental designs such as Plackett-Burman (PBD) and central composite designs (CCDs) were used to optimize the LVI-PTV variables (cryo-focusing temperature, vent time, vent flow, vent pressure, injection volume, purge flow to split vent, splitless time and injection speed). Optimized conditions were as follows: 45 μL of n-hexane extract are injected at 60°C and 6 μL/s with a vent flow and a vent pressure of 50 mL/min and 7.7 psi, respectively, during 5 min; then the split valve is closed for 1.5 min and afterwards the injector is cleaned at 100 mL/min before the next injection. The method was applied to the determination of estrogenic compounds in environmental samples such as estuarine water, wastewater, and fish homogenate and bile. Limits of detection (0.04-0.15 ng/L for water samples, 0.04-0.67 ng/g for fish bile and 0.1-7.5 ng for fish homogenate) obtained were approx. ten times lower than those obtained by means of a common split/splitless inlet.     

固相萃取/液相色谱-串联质谱法检测医院废水中21种抗生素药物残留

应用固相萃取及高效液相色谱-串联质谱技术,建立了医院废水中12种磺胺、4种喹诺酮、3种四环素以及罗红霉素和甲氧苄氨嘧啶等21种抗生素的定性定量方法。水样经HLB小柱萃取富集,使用10%甲醇溶液净化,经甲醇洗脱定容后,以高效液相色谱-串联质谱多反应监测离子模式(MRM)对目标物进行分析。在优化实验条件下,21种抗生素的线性范围为1.0～500μg/L,相关系数r2>0.99,方法检出限为0.005～0.022μg/L。在加标量为0.05μg/L和1.0μg/L时,空白加标回收率分别为71%～105%和76%～111%,RSD均小于15%。以医院废水为基质,21种抗生素的加标回收率为71%～135%,RSD小于25%。该方法简捷、快速、准确,能够实现医院废水中多种抗生素药物残留的同时分析。     

Rapid simultaneous determination of 14 sulfonamides in wastewater by liquid chromatography tandem mass spectrometry

This paper describes a rapid method for the determination of 14 kinds of sulfonamides (SAs) in wastewater using SPE, and LC-MS/MS with positive ESI (ESI(+)) and selected reaction monitoring (SRM) mode. The SPE was performed on an Oasis hydrophilic-lipophilic-balanced (HLB) cartridge. Chromatographic separation on a C18 column was achieved using a binary eluent containing methanol and water with 0.2% formic acid. Typical recoveries of the analytes ranged from 22.3 to 87.0% at a fortification level of 100 ng/L. The LODs in wastewater except sulfathiazole (3 ng/L) could be detected and quantified at levels as low as 1 ng/L. Finally, the method was applied to water from the municipal outlet and the aquaculture wastewater effluent. Sulfamethazine (SM(2)), sulfamethoxypyridazine (SMP), and sulfamethoxazole (SMZ) were most frequently found in wastewater in a concentration range between 1.2 and 31.7 ng/L.     

固相萃取-超高效液相色谱-串联质谱法检测环境水体中18种农药残留

建立了固相萃取-超高效液相色谱-串联质谱（SPE-UPLC-MS/MS）同时检测环境水体中不同极性范围的18种农药残留的分析方法。样品经大体积固相萃取装置，以2 mL/min的速率通过Cleanrt^®-PEP固相萃取柱进行净化和富集，浓缩50倍后结合UPLC-MS/MS检测，外标法定量。研究表明，目标化合物在0.5~50 μg/L范围内线性关系良好，线性相关系数（R²）≥0.995；在10、100和1000 ng/L 3个添加水下，18种农药在3种不同环境水体中的平均回收率为71.3%~105.9%，相对标准偏差（RSD，n=5）为1.3%~9.9%；定量限（LOQ）均为10 ng/L。该方法应用于泰安市区周围水环境的检测，各采集位点均未检出农药残留。该方法具有净化效果好、通用性强、灵敏度高、准确度高和操作简单等优点，适用于环境水体中18种农药的残留检测。