分光光度法测定水中氟离子的优化

氟离子在弱酸性缓冲介质中与显色剂反应生成蓝色三元络合物,络合物在620 nm波长处的吸光度与氟离子浓度成正比,据此建立检测水中氟化物含量的分光光度法.研究了缓冲液和显色剂加入量、络合物稳定剂、稳定时间对测定结果的影响,并确定了最佳分析条件:向适量水样中加入1 mL缓冲液、1 mL显色剂、1 mL乙醇,静置20 min,...     

AgDDC光度法测定砷的探讨

砷是环保、卫生防疫等部门的一个重要分析项目。目前 ,Ag DDC光度法测定砷用得比较普遍。1　试验部分1 .1　仪器与试剂72 2分光光度计 ;1 0 0 ml测砷装置氯化亚锡溶液 :40 0 g·L-1碘化钾溶液 :1 50 g· L-1吸收液及以上试剂按文献 [1 ]配制砷标准溶液 (国家一级标准物质 GBW0 861 1 ) :1 mg· ml-1;砷中间液 :1 0 .0μg· ml-1;砷工作液 :1 .0 0μg· ml-1。无砷锌粒甲 :1 0～ 2 0目无砷锌粒乙 :颗粒较大 ,约绿豆大小。1 .2　试验方法在砷化氢发生瓶中加入砷工作液 (或水样适量 ) ,加水至 50 ml。分别加入浓硫酸 4ml,碘化钾溶液 4ml和…     

原子荧光光谱法测定砷过程中还原反应条件的优化

自然界中砷和砷的化合物一般可通过水、大气和食物等途径进入人体,危害人体健康,原子荧光光谱法测定砷含量被广泛应用。为准确测定样品中砷的含量,以原子荧光光谱法(AFS)测定土壤中总砷含量为例,重点研究高价态砷(Ⅴ)还原为低价态砷(Ⅲ)的实验条件,采用正交实验进行条件优化,建立适合的实验方法。通过设计L9(34)正交实验,高价态砷的还原反应与四个因素有关,即与反应温度、反应时间、盐酸加入量和硫脲的用量呈一定的正相关,结果表明,四个因素中硫脲用量的影响最为显著,其次是盐酸加入量、反应时间和反应温度。通过对四个因素的多水平检验,优化后的实验条件为：硫脲用量2.0 mL、盐酸加入量10%、反应时间20 min、温度20～35 ℃(即普通室温)。采用土壤标准物质验证优化后条件的可行性,得出砷的测定值在标准值范围内,RSD在2.2%～4.2%,精密度和准确性均满足质控要求。优化后的实验条件使得操作简便易行,提高了工作效率。     

氢化物发生-原子荧光光谱法同时测定饮用水中砷和锑

采用氢化物发生-原子荧光光谱法同时测定饮用水中砷和锑。在盐酸(1+9)溶液中,加入硼氢化钾溶液作还原剂,使其与溶液中砷(Ⅲ)及锑(Ⅲ)离子反应生成氢化物。分析中采用载气及屏蔽气的流量依次为400mL·min~(-1)及800mL·min~(-1)。试样溶液中加入硫脲及抗坏血酸混合溶液作为预还原剂,于仪器中引入1.0mL试样溶液,按所选定的工作条件操作。砷及锑的质量浓度均在10.0μg·L~(-1)以内与其对应的荧光强度呈线性关系,砷和锑的检出限(3S/N)依次为0.087μg·L~(-1)和0.048μg·L~(-1)。应用此法对饮用水进行分析,测得砷和锑的回收率分别在90.5%～93.3%和92.5%～95.3%之间。     

应用双通道原子荧光光度计同时测定饮用水中的砷和汞

使用XGY-6080型双通道原子荧光光度计,同时测定饮用水中的砷和汞。在最佳仪器工作条件下,砷和汞的检出限分别为0.0273μg/L、0.0034μg/L,测定结果的相对标准偏差为1.09%~3.34%(n=7),砷和汞的加标回收率分别为96.59%~103.97%和96.78%~98.95%。     

食用仙人掌中葡萄糖的测定方法

对食用仙人掌中葡萄糖的测定方法进行了研究,采用单因素和正交实验法测定食用仙人掌中葡萄糖含量,其最佳条件为:水解时加入盐酸20 mL,反应滴定温度60℃,反应液pH 5.0,水解时间30 min.该方法简便、可行.     

Na_2EDTA滴定法测定复杂高铋物料中铅

复杂高铋物料中铋、砷、锑、锡4种元素含量高且共存时会影响铅的测定。特别是铋含量高时对铅的测定影响较大。实验用EDTA-酒石酸联合掩蔽铋、砷、锑、锡,在稀硫酸介质中以硫酸钾为沉淀剂,使铅生成硫酸铅钾复盐沉淀而与铋、砷、锑、锡、铁、铜、锌、铝、钴、镍等干扰离子分离,沉淀以乙酸-乙酸钠浸取,二甲酚橙为指示剂,Na2EDTA滴定法测定铅含量。实验进一步优化了测定条件,确定的最佳条件:硫酸(1+1)加入量为7mL、硫酸钾用量为5g、煮沸时为5min、沉淀陈化时间为2h、EDTA(50g/L)加入量为10mL、酒石酸用量为0.5g,铅的加标回收率99.7%~104%。将实验方法应用于测定复杂高铋物料中铅,标准样品BY0111-1的测定值与给定值一致,相对标准偏差(n=11)RSD 0.20%~0.23%,满足生产测定要求。     

湿法消解/干灰化-氢化物发生-原子荧光光谱法测定基围虾中总砷

建立了一种采用湿法消解/干灰化-氢化物-原子荧光光谱法分析测定基围虾中总砷的方法。样品中加入6mL硝酸,冷消解120min,电热板160℃预消解至澄清,并赶酸至约1mL,加入灰化辅助剂硝酸镁,550℃马弗炉灰化5min。盐酸溶解灰分,采用氢化物发生-原子荧光光谱法分析测定。通过优化仪器条件,砷含量在0.0-20.0mg.L-1范围内,标准曲线相关线性优于0.999,检出限为0.025mg.L_^-1,相对标准偏差RSD为2.54%-3.13%,加标回收率为93.6%-103.0%。本方法结果准确,可用于基围虾中总砷测定。     

石墨炉原子吸收法测定合金钢中痕量砷的干扰抑制

研究了石墨炉原子吸收法测定合金钢中痕量砷的实验条件和干扰抑制方法。在合金钢样品溶液中加入硝酸镍溶液作基体改进剂,不仅提高了砷的灰化温度,而且提高了测定灵敏度。砷的含量与吸光度呈良好的线性关系,线性相关系数r=0．9846。测定结果的相对标准偏差小于6．5％,加标回收率为95％～106％。检出限为0．01ug／mL。     

复杂高铋物料中铅的Na2EDTA滴定法测定

复杂高铋物料中,铋、砷、锑、锡四元素含量高且共存时会影响铅的测定。特别是铋含量高时对铅的测定影响大。实验用EDTA—酒石酸联合掩蔽铋、砷、锑、锡,在稀硫酸介质中以硫酸钾为沉淀剂,使铅生成硫酸铅钾复盐沉淀而与铋、砷、锑、锡、铁、铜、锌、铝、钴、镍等干扰离子分离,沉淀以乙酸-乙酸钠浸取,二甲酚橙为指示剂,Na2EDTA滴定法测定铅。试验进一步优化了测定条件,确定最佳条件：硫酸（1 1）加入量为7mL、硫酸钾用量为5g、煮沸时为5min、沉淀陈化时间为2h、EDTA 50g/L 加入量为10mL、酒石酸用量为0.5g,铅的回收率99.70% ～100.65%。将实验方法应用于测定复杂高铋物料中铅,标样BY0111-1与给定值一致,相对标准偏差（n=11）RSD 0.20%～0.23%,满足生产测试要求。     

Arsenic in drinking water and in scalp hair by EDXRF: A major recent health hazard in Bangladesh

Arsenic content in drinking water and in scalp hair of the arsenic affected areas in Bangladesh were measured using energy dispersive X-ray fluorescence (EDXRF) to determine the contribution of drinking water to body burden and health risks. Around 61% of the water analyzed from tube-wells has arsenic content above 0.05 mg/l and about 13% have arsenic content above 0.01 mg/l. The mean concentration of arsenic in contaminated water is about 0.26 mg/l with the maximum level of 0.83 mg/l. The contaminated water thus contributes a significant amount to the arsenic budget in humans in Bangladesh and consequently, to their health hazards. The average concentration of arsenic in hair of a patient group drinking contaminated water is 14.1 mg/kg where the normal levels are <3.0 mg/kg. The distribution of arsenic in water and in hair is compared and discussed with the data reported in the literature. The daily dietary intake value of arsenic by the adult population in Bangladesh is estimated and assessed signifying health effects.     

Effect of acidification rate,acidification temperature,final pH,and stabilizer content on colloidal stability of whey-based pomegranate beverage

The effect of acidification rate (during 0, 30, and 60 minutes), acidification temperature (25, 50, and 75°C), final pH (3.4, 3.6, and 3.8), and pectin content (0.2, 0.4, and 0.6%) on the stabilization of whey-based pomegranate beverage was studied. Serum separation, particle size distribution, viscosity, zeta potential, pH, and acidity of beverage samples were observed during storage. Results revealed that acidification rate, acidification temperature, and pectin content had a significant effect; however, final pH (of the studied range) had no significant effect on the phase separation. The amount of phase separation decreased and the stability increased with increasing acidification rate, acidification temperature, and stabilizer content. In addition, the results of particle size, zeta potential, and viscosity confirmed the results of phase separation and also the most stable beverage had a pH near 3.8.     

粒径可控阳离子型聚苯乙烯纳米粒子的制备及表征

在采用阳离子型双子（gemini）表面活性剂作为乳化剂,不使用任何助乳化剂的条件下,通过改进微乳液聚合工艺制备了窄分布粒径可控的阳离子型聚苯乙烯（PS）纳米乳液。 改进微乳液聚合的主要特点是：大部分苯乙烯以预乳液的形式恒速滴入引发聚合的微乳液中,使用具有高乳化性能的gemini表面活性剂作为乳化剂能明显降低乳胶粒粒径。 实验结果表明,少量阳离子单体三甲基烯丙基氯化铵作为共聚单体能够明显减小Z均粒径、降低粒度分布,乳化剂用量、引发剂用量和反应温度均能影响制备乳胶粒的粒径及其粒度分布。 乳化剂和引发剂用量分别为苯乙烯质量的5%~10%和1.0%~1.5%、反应温度为70~75 ℃时,能够制备粒径小分布窄的阳离子型聚苯乙烯纳米粒子。 Z均粒径与苯乙烯质量之间的线性关系表明,Z均粒径可以通过苯乙烯用量来控制。 不同聚合工艺下制备的聚合物粒度分布曲线表明,改进微乳液聚合工艺（半连续预乳化工艺）在制备窄分布的聚合物纳米粒子方面具有很强的优越性。     

溶剂热法制备小粒径无皂均聚物纳米胶乳粒子

采用溶剂热法，用过硫酸钾引发苯乙烯均聚，制备出分散性好、粒径约30nm的无皂聚苯乙烯肢乳纳米粒子。讨论了引发剂的用量、助溶剂丙酮的含量、反应温度对粒子尺寸及其粒径分布的影响。实验结果表明：在一定范围内，温度改变，粒径变化较快；引发剂、丙酮和单体用量改变时，粒径变化较缓慢。     

微波炉浓缩甲基橙光度法测定饮用水中溴酸盐的研究

建立了一种微波浓缩甲基橙分光光度法测定水中溴酸根离子的方法。考察了酸度、时间、温度和甲基橙用量对测定方法的影响。分别对从各大超市购买的不同瓶装饮用水,经过微波炉浓缩后,用甲基橙分光光度法进行测定。其结果与离子色谱标准方法对比,结果表明:两种方法测定同一水样的相对误差小于7.0%。溴酸根离子氧化甲基橙使其褪色的最大吸收波长为510nm;溴酸根离子的浓度在0.0～1.0 mg/L范围内符合比尔定律。回归方程为:Y=0.9299X-0.0001,相关系数为r=0.9992。     

Speciation analysis of arsenic in groundwater from Inner Mongolia with an emphasis on acid-leachable particulate arsenic

Arsenic in drinking water affects millions of people around the world. While soluble arsenic is commonly measured, the amount of particulate arsenic in drinking water has often been overlooked. We report here determination of the acid-leachable particulate arsenic and soluble arsenicals in well water from an arsenic-poisoning endemic area in Inner Mongolia, China. Water samples (583) were collected from 120 wells in Ba Men, Inner Mongolia, where well water was the primary drinking water source. Two methods were demonstrated for the determination of soluble arsenic species (primarily inorganic arsenate and arsenite) and total particulate arsenic. The first method used solid phase extraction cartridges and membrane filters to separate arsenic species on-site, followed by analysis of the individual arsenic species eluted from the cartridges and filters. The other method uses liquid chromatography separation with hydride generation atomic fluorescence detection to determine soluble arsenic species. Analysis of acidified water samples using inductively coupled plasma mass spectrometry provided the total arsenic concentration. Arsenic concentrations in water samples from the 120 wells ranged from <1 to ∼1000 μg L⁻¹. On average, particulate arsenic accounted for 39 ± 38% (median 36%) of the total arsenic. In some wells, particulate arsenic was six times higher than the soluble arsenic concentration. Particulate arsenic can be effectively removed using membrane filtration. The information on particulate and soluble arsenic in water is useful for optimizing treatment options and for understanding the geochemical behavior of arsenic in groundwater.     

Hydride generation for the direct determination of trace and ultra-trace level of arsenic and antimony in waters using derivative atomic absorption spectrometry

A new method is developed for the direct determination of trace and ultra-trace level of arsenic and antimony in waters by hydride generation derivative atomic absorption spectrometry (DHGAAS). The signal model and fundamentals of DHGAAS are described. The effects of atomization temperature, argon flow rate, acidity and concentration of KBH(4)and KI were investigated and analytical conditions were optimized. The sensitivities for arsenic and antimony were increased 36.4 and 27.6 times better than those of conventional hydride generation atomic absorption spectrometry (HGAAS). For a 2 mV min(-1) sensitivity range setting, the characteristic concentration was 0.003 microg L(-1) for arsenic and 0.004 microg L(-1)for antimony, and the detection limits (3sigma) were 0.015 micro g L(-1) for arsenic and 0.020 microg L(-1) for antimony. The proposed method was applied to the determination of arsenic and antimony in several water samples with satisfactory results.     

The effect of particle size and metal contents on arsenic distribution in coal-fired fly ash

Fly ash samples were collected from a Chinese power station and divided according to particle size. The solid fly ash samples were digested according to ASTM methods. The arsenic contents of samples with different particle sizes were analyzed using atomic fluorescence spectroscopy after digestion. Other metals were analyzed using inductively coupled plasma-atomic emission spectrometer after digestion, and the carbon content was analyzed by a CHN elemental analyzer. The results show that the arsenic components are enriched in smaller fly ash particles. The arsenic contents have a positive relationship with calcium, magnesium, and iron contents, which indicate that stable compounds are formed between these components. Thermogravimetric experiments of fly ash samples with different particle sizes were conducted, and the results indicate the combination of calcium hydroxide with arsenic form stable compounds.     

Arsenic speciation in natural water samples by coprecipitation-hydride generation atomic absorption spectrometry combination

A speciation procedure for As(III) and As(V) ions in environmental samples has been presented. As(V) was quantitatively recovered on aluminum hydroxide precipitate. After oxidation of As(III) by using dilute KMnO₄, the developed coprecipitation was applied to determination of total arsenic. Arsenic(III) was calculated as the difference between the total arsenic content and As(V) content. The determination of arsenic levels was performed by hydride generation atomic absorption spectrometry (HG-AAS). The analytical conditions for the quantitative recoveries of As(V) including pH, amount of aluminum as carrier element and sample volume, etc. on the presented coprecipitation system were investigated. The effects of some alkaline, earth alkaline, metal ions and also some anions were also examined. Preconcentration factor was calculated as 25. The detection limits (LOD) based on three times sigma of the blank (N: 21) for As(V) was 0.012 μg L⁻¹. The satisfactory results for the analysis of arsenic in NIST SRM 2711 Montana soil and LGC 6010 Hard drinking water certified reference materials for the validation of the method was obtained. The presented procedure was successfully applied to real samples including natural waters for arsenic speciation.     

Removal of aqueous As(III) and As(V) by hydrous titanium dioxide

Dissolved arsenic in drinking water is a global concern as it causes serious health problems. The purpose of this research was to study the applicability of an industrial intermediate product, a mixture of titanium hydroxide and titanium dioxide for removing aqueous arsenic. The material is common, inexpensive, and non-toxic, making it an attractive choice for drinking water purification. The kinetics and equilibrium of removing both primary inorganic arsenic forms, As(III) and As(V), were studied by separate batch experiments. The tested material functioned well in removing both of these arsenic forms. The apparent values for Langmuir monolayer sorption capacities were 31.8 mg/g for As(III) and 33.4 mg/g for As(V) at pH 4. The studied TiO(2) performed the best in acidic conditions, but also reasonably well in other pH conditions.