柱后光化学衍生高效液相色谱法同时测定牛奶中黄曲霉毒素

建立了高效液相色谱法同时测定牛奶中黄曲霉毒素B1,B2,G1,G2的方法。用乙腈和水的混合溶液(体积比为80∶20)提取牛奶样品中4种黄曲霉毒素,提取液经Mycosep 228 AflaPat多功能净化柱净化,浓缩后采用C18色谱柱分离,光化学衍生后进入荧光检测器测定,外标法定量。对牛奶样品进行加标回收和精密度试验,黄曲霉毒素B1,B2,G1,G2的检出限分别为0.50,0.10,0.50,0.10μg/kg,回收率均在85%以上,测定结果的相对标准偏差为1.72%～3.52%(n=6)。该方法操作简单,速度快,重现性好,满足牛奶中黄曲霉毒素检测的要求。     

免疫亲和柱高效液相色谱法快速测定牛奶和奶粉中黄曲霉毒素M1、B1、B2、G1、G2

采用单克隆抗体免疫亲和技术作为直接从样品中分离提取黄曲霉毒素的特效手段,提取液挥干后,经衍生用HPLC荧光检测器测定.对鲜奶和高脂奶粉(脂肪含量25%)在0.01,0.05,0.1和0.1,0.5,1.0 μg·L-1水平对黄曲霉毒素M1、B1、B2、G1、G2测定平均回收率(n=10)为66.0%～97.0%;相对标准偏差(n=10)为1.04%～14.0%.方法的检出限低于0.01 μg·L-1(鲜奶), 0.1 g·kg-1(奶粉).     

高效液相色谱法测定牛奶中黄曲霉毒素M1含量的不确定度评定

根据方法GB 5009.24-2016《食品安全国家标准食品中黄曲霉毒素M族的测定》,建立高效液相色谱法测定牛奶中黄曲霉毒素M₁含量不确定度的数学模型,分析检测过程中的不确定度来源,并对不确定度分量进行量化和合成.当牛奶中黄曲霉毒素M₁的质量分数为0.842 μg/kg时,其扩展不确定度为0.048 4 μg/kg（k=2）.方法相对不确定度主要来源于标准品纯度和样品回收率.     

集成免疫磁珠富集和免疫层析的黄曲霉毒素M1快速检测法

以喷涂了检测抗原黄曲霉毒素M1-BSA和驴抗鼠二抗形成检测线和质控线的硝酸纤维膜制备免疫层析试纸条,采用EDC/NHS法制备偶联了抗黄曲霉毒素M1单克隆抗体的免疫磁珠。免疫磁珠与待检样本混合,经捕获、磁分离后,浓缩重悬液直接用免疫层析试纸条检测,首次建立了集浓缩样本与免疫层析于一体的黄曲霉毒素M1快速检测法。该方法用于检测原料乳中黄曲霉毒素M1,检出限为0.1μg/L,低于我国制定的黄曲霉毒素M1限量标准(0.5μg/L),与其它真菌毒素和原料乳中常检违法添加物无交叉反应,分析结果与酶联免疫吸附法(ELISA)结果一致。本方法适合现场快速检测原料乳中黄曲霉毒素M1。     

乳及乳制品中黄曲霉毒素B_1、M_1测定方法改进

建立了一种检测乳及乳制品中黄曲霉毒素B1、M1的高效液相色谱-荧光检测(HPLC-FD)方法。样品经60%乙腈溶液提取,自制固相萃取柱净化,流出液经正己烷、三氟乙酸衍生后荧光检测器检测。考察了填料、柱容量、取样量、提取溶液和流速等对检测的影响,优化了实验条件。结果表明,黄曲霉毒素B1、M1的检测线性范围为0.40~100μg/L,线性系数为0.9991~0.9998,方法检出限为0.050μg/kg。对样品进行0.40、1.0和15μg/L 3种浓度水平的加标回收实验,回收率为53%~105%,相对标准偏差为2.6%~5.1%。该方法操作简单、灵敏度高、准确度好,可用于乳及乳制品中黄曲霉毒素B1、M1的测定。     

反相高效液相色谱法测定乳品及乳制品中的黄曲霉毒素M_1

采用反相高效液相色谱测定乳品及乳制品中黄曲霉毒素M_1(AFM_1)的含量。样品经氯仿提取,过硅胶固相萃取柱净化,用氯仿-丙酮(1+1)混合溶液将黄曲霉毒素M_1从固相萃取柱上洗脱下来。以ZORBAX SB C_(18)色谱柱为分离柱,水和乙腈为流动相梯度淋洗,用荧光检测器检测,外标法定量。黄曲霉毒素M_1在1.0～25μg·L~(-1)质量浓度范围内与其峰面积呈线性关系,检出限(3S/N)为0.05μg·kg~(-1)。应用此法测定了牛奶和乳粉中AFM_1的含量,并测得其平均回收率分别在76.0%～80.0%和76.7%～90.8%之间,相对标准偏差(n=6)均小于7.0%。     

基于背景荧光猝灭-免疫层析法黄曲霉毒素B_1检测卡的研制

基于背景荧光猝灭-免疫层析技术研制快速检测食用油中黄曲霉毒素B1的定量检测卡。依据黄曲霉毒素B1抗原和抗体的活性,筛选检测系统中最佳的黄曲霉毒素B1抗原浓度和抗体标记浓度,应用最佳检测系统进行食用油中黄曲霉毒素B1检测的方法学验证和样品测定。最佳检测系统中黄曲霉毒素B1抗原浓度为0.5 mg/m L,黄曲霉毒素B1抗体标记浓度为1.0μg/m L;用于测定食用油中黄曲霉毒素B1的浓度范围为1.3~50.0 ng/m L,RSD均值为0.42%,平均加标回收率为96.3%~103.2%,RSD均值为2.8%(n=9)。使用有样品采用本法与国标方法的检测结果无显著性差异(p0.05)。本方法专属性强,灵敏度高,可快速、准确的检测食用油中黄曲霉毒素B1。     

自制混合型固相萃取柱-高效液相色谱法同时测定食品中黄曲霉毒素B1、M1

建立了基于自制混合型固相萃取柱的样品净化/高效液相色谱测定食品中黄曲霉毒素B1、M1的方法。样品经60%乙腈水溶液提取、离心后,通过自制固相萃取柱排除杂质干扰,流出液以Shim-pack VP-ODS C18色谱柱为分离柱,水和乙腈为流动相,用荧光检测器检测,外标法定量。考察了柱类型、柱容量、取样量、提取溶液和流速等对检测的影响,优化了实验条件。在优化条件下,2种毒素在0.40～100μg/L质量浓度范围内与峰面积呈良好的线性关系,相关系数为0.999 4～0.999 7,检出限(S/N=3)为0.050μg/kg。在样品中分别加入0.40、1.0、100μg/L 3种浓度水平的标准品,其加标回收率为53%～112%,相对标准偏差为2.7%～7.1%。该法灵敏度高,操作简单﹑快速,适用于花生、开心果和奶粉等食品中痕量黄曲霉毒素B1和M1的测定。     

超高效液相色谱-四极杆/静电场轨道阱高分辨质谱法测定花生中4种黄曲霉毒素和11种农药残留

建立了花生样品中4种黄曲霉毒素(黄曲霉毒素B_1、黄曲霉毒素B_2、黄曲霉毒素G_1、黄曲霉毒素G_2)和11种农药残留(啶虫脒、乙草胺、多菌灵、克百威、毒死蜱、苯醚甲环唑、烯酰吗啉、吡虫啉、嘧霉胺、戊唑醇、噻虫嗪)的超高效液相色谱-四极杆/静电场轨道阱高分辨质谱法(UPLC-HRMS)。样品经乙腈-水-乙酸提取液(84∶15∶1,体积比)提取,1.0 g硫酸镁、100 mg PSA与400 mg C_(18)硅胶混合体系净化后进行检测。采用Hypersil Gold C_(18)柱(100 mm×2.1 mm,1.9μm)分离,用UPLC-HRMS进行检测。结果显示,4种黄曲霉毒素和11种农药残留在各自的质量浓度范围内线性关系良好,相关系数(r~2)均大于0.996,方法定量下限为0.25～1.0μg/kg,样品的加标回收率为79.4%～120%,相对标准偏差(RSD,n=6)为4.2%～10%。该方法的灵敏度高、结果准确、可靠,能够实现对花生样品中4种黄曲霉毒素和11种农药残留含量的同时检测。     

凝胶渗透色谱-超高效液相色谱-串联质谱法测定奶及奶粉中黄曲霉毒素M_1

建立了用凝胶渗透色谱-超高效液相色谱/串联三重四级杆质谱测定牛奶中黄曲霉毒素M_1的方法。方法以乙腈超声提取,凝胶渗透色谱净化后,以乙腈-0.1%甲酸(3:7,V/V)为流动相,UPLC BEH C18分离,ESI+模式质谱检测,外标法定量。黄曲霉毒素M_1在0.1~4.0μg/L范围内线性关系良好,相关系数r为0.9955,检出限为0.01μg/kg,定量限为0.05μg/kg。牛奶样品在0.1,0.2,0.5μg/kg 3个加标浓度下,黄曲霉毒素M_1的回收率为72.4%~92.2%,相对标准偏差为4.0%~7.8%。     

ICP-AES测定铀污染土壤植物中铀的研究

采用电感耦合等离子体发射光谱(ICP-AES)对铀污染土壤植物中铀的测定方法进行了研究.在λU385.958 nm处,选择了仪器的最佳工作条件,考察了酸度和常见共存元素对测定的干扰情况,并且对比了干灰化消解和湿式消解对测定的影响.研究发现2%硝酸溶液为最佳介质,干扰离子对测定没有显著影响,干灰化消解比湿式消解得彻底.在选定条件下,方法检出限为0.18 mg·L-1,测定下限为0.61 mg·L-1,5.0000 mg·L-1的铀标准溶液的相对标准偏差RSD(n=10)为0.81%,方法回收率为96.2%～106.2%.该方法操作简单,快速.结果表明,用ICP-AES测定铀污染土壤植物样品中的铀是可行的.     

测定血清中Na 含量不确定度的评定

对血清中Na离子含量的测量不确定度进行评定。不确定度的来源主要包括Na离子标准工作液的配制过程、血清样品的定容消化制备、标准曲线拟合、钠离子各分量不确定度的合成等引入的不确定度计算出各分量的不确定度,通过合成得到测量结果的合成不确定度、扩展不确定度及测试结果的报告形式。     

Interpretation of inorganic arsenic metabolism in humans in the light of observations made in vitro and in vivo in the rat

The toxicity of inorganic trivalent arsenic for living organisms is reduced by in vivo methylation of the element. In man, this biotransformation leads to the synthesis of monomethylarsonic (MMA) and dimethylarsinic (DMA) acids, which are efficiently eliminated in urine along with the unchanged form (As_i). In order to document the methylation process in humans, the kinetics of As_i, MMA and DMA elimination were studied in volunteers given a single dose of one of these three arsenicals or repeated doses of As_i. The arsenic methylation efficiency was also assessed in subjects acutely intoxicated with arsenic trioxide (As₂O₃) and in patients with liver diseases. Several observations in humans can be explained by the properties of the enzymic systems involved in the methylation process which we have characterized in vitro and in vivo in rats as follows: (1) production of As_i metabolites is catalyzed by an enzymic system whose activity is highest in liver cytosol; (2) different enzymic activities, using the same methyl group donor (S-adenosylmethionine), lead to the production of mono- and di-methylated derivatives which are excreted in urine as MMA and DMA; (3) dimethylating activity is highly sensitive to inhibition by excess of inorganic arsenic; (4) reduced glutathione concentration in liver moderates the arsenic methylation process through several mechanisms, e.g. stimulation of the first methylation reaction leading to MMA, facilitation of As_i uptake by hepatocytes, stimulation of the biliary excretion of the element, reduction of pentavalent forms before methylation, and protection of a reducing environment in the cells necessary to maintain the activity of the enzymic systems.     

Production of radicals in the ozonolysis of propene in air

Radical production in the ozonolysis of propene in air was monitored directly by a peroxy radical chemical amplification (PERCA) instrument at room temperature (298±2 K) and atmospheric pressure (1×105 Pa). The ozonolysis reactions were conducted in a flow tube under pseudo-first-order conditions for ozone. The decay in ozone was calculated based on reaction time tr and effective rate constant keff (keff = k1[C3H6]0)) for the ozone-propene reaction. The total radical yields relative to consumed ozone were d...     

Kinetics of dehydration in chelates of quinones involved in photosystem-II

The solid-state deaquation of thetrans- andcis-oximates of lawsone (I) and phthiocol (II) with cobalt(II) was investigated by means of non-isothermal thermogravimetry. The modes of deaquation during the thermolyses of hydrated oximates of (I) and (II) with compositions CoL₂·2H₂O were compared. The weight lossvs. temperature data were treated by using the Coats and Redfern relations. The kinetic data support a rearrangement-type mechanism for the deaquation of the oximate of phthiocol. TheE _a values for both the ligands and water molecules were found to be 23 kJ/mol.

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Zusammenfassung Mittels nichtisothermer Thermogravimetrie wurde die Dehydratation der trans- und cis-Kobalt(II)-oximate von Lawson (I) und Phthiokol (II) untersucht. Die Arten der Dehydratation während der Thermolyse der hydratierten Oximate von (I) und (II) mit der Zusammensetzung CoL₂·2H₂O wurden verglichen. Bei der Auswertung der Massenverlust-Temperatur-Daten wurden Coats-Redfern Beziehungen angewendet. Die kinetischen Daten bekräftigen einen Umlagerungsmechanismus für die Dehydratation des Oximates von Phthiokol. DieE _a Werte betragen sowohl für die Liganden als auch für Wasser etwa 23 kJ/mol.

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- - (I) (II) . I II CoL₂ · 2₂ . -. . _a , 23 · ^–1

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Use of matrix-modifiers in atomic-absorption determination of chromium in argillites

The direct atomic-absorption determination of chromium in argillites, without preliminary concentration and separation, has been studied. A map of selective flame zones for determining Cr in argillites has been designed. An express method for determining Cr in Estonian argillites has been suggested.     

Effect of vibration in processes of structure formation in polymers

It was shown that the strength characteristics of the samples produced from thermoplastics (low density polyethylene, polyamide 6, Armamid, and polyethylene terephthalate) increase as a result of short vibration treating with a frequency close to that of natural vibrations of the structural elements.