特选榨菜对铀污染土壤的修复评价

本文通过两种不同的加铀方式,加入不同种类及浓度的螯合剂,以及土壤改良剂(有机肥、微生物肥料、腐殖酸、尿素)的方法,研究了不同因素对特选榨菜修复铀污染土壤的影响。结果表明:在pH=5时把UO_2(NO_3)_2·6H_2O溶液喷洒入土壤,使土壤中铀污染浓度为100 mg·kg~(-1)时,特选榨菜地上部铀富集的浓度最大可以达到1103.42 mg·kg~(-1),根部为1909.49 mg·kg~(-1),去除率为7.81%;上述含铀土壤放置2年后制备成模拟铀污染的土壤,进而栽种特选榨菜进行修复,在100 mg·kg~(-1)铀污染浓度下,植物上部铀富集浓度最大为295.83 mg·kg~(-1),根部为268.42 mg·kg~(-1),年去除率为2.52%。用Tessier五步连续提取法测定两次修复土壤中铀的形态,发现模拟铀污染土壤比铀喷洒于土壤中有效态的铀(交换态和碳酸盐结合态)要低52.7%;加入柠檬酸、苹果酸等螯合剂以及有机肥、微生物肥料、腐殖酸、尿素等土壤改良剂,在模拟铀污染土壤修复时发现有机肥会降低植物上部对铀的富集;而柠檬酸和微生物肥会增强植物上部对铀的富集。     

连续流动注射法测定土壤和植物中全磷

应用AA3型连续流动分析仪测定了土壤和植物中全磷.结果表明:对于采用高氯酸-硫酸消解的土壤样品以及硫酸-过氧化氢消解的植物样品,在测定时调节反应混合液的酸度使其在显色的适宜范围内,磷的质量浓度在6 mg·L-1(土壤)和7.5 mg·L-1(植物)以内呈线性,相关系数分别为0.999 2(土壤)和0.999 6(植物);加标回收率98.5%～100.5%,相对标准偏差小于2%,检出限分别为0.010 mg·L-1(土壤)和0.013 mg·L-1(植物).     

电感耦合等离子体发射光谱法测定蚕蛹、蝎子、海肠中20种元素含量

采用电感耦合等离子体发射光谱法(ICP-AES)直接快速测定蚕蛹、蝎子、海肠中20种元素含量,采用微波炉消解样品,试验了微波消解的条件.并对微波消解溶样和常规酸法溶样分别进行了测定和比较.方法的检出限为0.01～0.12 mg·L-1,相对标准偏差为1.4%～4.6%.     

电感耦合等离子体发射光谱法测定低合金钢中痕量硼

研究了用标准加入法、电感耦合等离子体发射光谱法(ICP-AES)测定低合金钢中痕量硼的方法,对试样溶样方法、元素分析谱线、共存元素干扰、背景校正、仪器分析最佳条件等因素进行了研究.试验结果表明,在选定的最佳条件下测定,硼的检出限为0.002 mg·L-1,相对标准偏差小于2%,加标回收率为95.0%～108.6%.     

电感耦合等离子体原子发射光谱法测定锆铀合金中微量铪

应用电感耦合等离子体原子发射光谱法(ICP-AES),采用标准加入法对锆铀合金中微量铪进行了测定.当锆的共存量为8 g·L-1时,铪的测定范围是50～400 μg·g-1.在Zr-U合金的基础上分别加入铪50μg·g-1及400 μg·g-1作回收试验,测得回收率依次为106%及101%,相应的相对标准偏差为5.8%和3.7%.     

微波消解样品-电感耦合等离子体原子发射光谱法测定土壤中铀

提出了电感耦合等离子体原子发射光谱法测定土壤中铀含量的方法。土壤样品称样0.200 0 g,用硝酸6.0 mL、盐酸2.0 mL、氢氟酸2.0 mL于微波消解仪中消解完全。选择波长为385.958 nm的谱线作为铀的分析线。方法的检出限（3σ）为0.15 mg·L^-1。方法用于分析国家标准物质GBW（E）080173,测定值与认定值相符。方法的回收率在92%～106%之间,测定值的相对标准偏差（n=10）为1.0%。     

三种植物对铀耐性及土壤中铀吸收积累差异的研究

采用溶液培养结合土壤培养的方法,研究了小白菜、冬苋菜和菠菜对铀的耐性及土壤中铀吸收积累的差异.结果表明:水培条件下(U 50mg/L),与小白菜和冬苋菜相比,菠菜对铀具有较强的耐性;在100mg/kg 土U的条件下,菠菜表现出比小白菜和冬苋菜更高吸收和积累铀的能力,其地上部分铀含量为232mg/kg DW(Dry Weight 干重),而根部铀含量达433mh/kg DW(Dry Weight 干重).菠菜可能对铀污染土壤的植物修复具有潜在的应用价值.     

原子荧光光谱法测定土壤中的砷和汞

采用原子荧光光谱法测定土壤中的砷和汞。样品经微波消解后,采用On-Guard H前处理柱去除消解液中的干扰离子,然后进行测定。在最佳条件下,砷和汞的线性范围为0.50~8.00μg·L-1,检出限(3s/k)分别为0.005,0.002μg·g-1。方法用于分析标准物质,测定值与认定值相符,测定值的相对标准偏差(n=6)小于4%。     

微波消解样品-电感耦合等离子体原子发射光谱法测定中草药中微量铜锌钴锰

采用微波消解样品,电感耦合等离子体原子发射光谱法(ICP-AES)测定了野菊花、菊花、蒲公英、枇杷叶和蝉蜕5种中草药中铜、锌、钴、锰4种微量金属元素的含量.在最佳仪器条件下,对野菊花样品平行测定6次,各元素的加标回收率在96.0%～106.5%之间,相对标准偏差(n=6)均小于2.0%.铜、锌、钴、锰4元素的检出限(3S/N)依次为0.011,0.018,0.001 1,0.024 mg·L-1.     

氢化物发生-原子荧光光谱法测定土壤中砷

采用氢化物发生-原子荧光光谱法测定土壤中砷的含量.样品经硝酸-盐酸(1+1)混合酸于沸水浴中加热1 h消解.对测定的影响因素:仪器的负高压、灯电流、载气和屏蔽气流量;硼氢化钾的浓度、酸的种类及其浓度、共存离子的干扰等试验条件作了研究并予以优化.荧光强度与砷的质量浓度在100 μg·L-1以内呈线性关系,方法的检出限(3s/b)为0.6 μg·L-1,方法的相对标准偏差(n=6)小于5%.应用此法对标准物质ESS-1和土壤样品进行分析,测得砷的回收率在93%～105%之间.     

虾粉中总砷测定方法的探讨

用氢化物原子荧光光度法测定虾粉中总砷含量时,对干法灰化、湿法消解、微波消解3种样品处理方法对虾粉中砷元素测定结果的影响进行了比较。通过试验确定了最佳消解条件。砷元素浓度在0~10μg/L的范围内与荧光强度呈线性关系,线性相关系数r=0.999 6,检出限为0.2μg/L。比对结果表明,干法灰化适合于测定虾粉中总砷的含量,湿法消解测定总砷的含量偏低,微波消解不适合测定虾粉中总砷的含量。采用干法灰化-氢化物原子荧光光度法测定虾粉中总砷含量,加标回收率为76.2%~106.0%。     

TXRF法测定松花粉中的9种生命元素

建立了微波消解前处理,全反射X射线荧光法(TXRF)同时测定松花粉中K、Ca、Ti、Mn、Fe、Ni、Cu、Zn和Rb9种生命元素含量的分析方法.松花粉原料经过微波消解前处理后,采用全反射X射线荧光光谱净计数、QXAS分析软件解谱和单一内标法进行定量分析.比较了干灰化法、湿消解法和微波消解法3种前处理方法的效果,并确立微波消解法作为样品前处理方法.用微波消解- TXRF法测定了花粉标准物质中的上述9种元素,并计算得到其仪器检出限(LLD)为0.002～0.054 mg/L,方法检出限(LDM)为0.004～0.122 mg/kg.TXRF法测定各元素的相对标准偏差(RSDs)为1.0％～5.5％.该方法操作简单、样品用量少、检出限低,对实际样品松花粉的测定结果与ICP - MS法无显著性差异.     

Arsenic determination in certifiable color additives by dry ashing followed by hydride generation atomic absorption spectrometry

The preparations of digested samples of certifiable color additives by dry ashing and wet digestion for arsenic analysis by hydride generation atomic absorption spectrometry (AAS) were compared. The dry ashing technique was based on the preparation used in ASTM D4606-86 for determination of As and Se in coal. The acid digestion method used nitric and sulfuric acids heated by microwaves in sealed vessels. The digested color additives were analyzed for As by using hydride generated from sodium borohydride mixed with the acidified solution on a flow injection system leading to an atomic absorption spectrometer. Dry ashing was preferable to wet digestion because wet digestion yielded poor recoveries of added As. Dry ashing followed by hydride generation AAS gave determination limits of 0.5 ppm As in the color additives. At a specification level of 3 ppm As, the precision of the method using dry ashing was +/- 0.4 ppm (95% confidence interval).     

Determination of heavy metals in soil, mushroom and plant samples by atomic absorption spectrometry

The concentrations of heavy metals in the soil, mushroom and plant samples collected from Tokat, Turkey have been determined by flame and graphite furnace atomic absorption spectrometry after dry ashing, wet ashing and microwave digestion. The study of sample preparation procedures showed that the microwave digestion method was the best. Good accuracy was assured by the analysis of standard reference materials. The relative standard deviations for all measured metal concentrations were lower than 10%. In all cases, quantitative analytical recoveries ranging from 95 to 103% were obtained. Metal accumulation factors were calculated for mushroom and plant samples. High ratio of plants to soil cadmium, zinc and copper concentrations indicate that these elements are accumulated by mushrooms. Results obtained are in agreement with data reported in the literature.     

ICP–AES法同时检测生蚝中铅、铜、镉、铬、铁含量时3种样品前处理方法比较

采用干法、湿法和微波消解法处理珠海生蚝样品,用电感耦合等离子体发射光谱仪在谱线Pb 220.3 nm,Cu 324.7 nm,Cd 228.8 nm,Cr 283.5 nm,Fe 259.9 nm下测定样品中铅、铜、镉、铬、铁5种重金属元素的含量。结果表明,珠海市4个养殖基地的生蚝重金属含量均在国标限量范围内。铅、铜、镉、铬、铁各元素线性相关系数分别为0.999 8,0.999 4,0.999 9,0.999 2,0.997 8,检出限分别为0.020,0.014,0.001,0.036,0.120 mg/kg。干法、湿法、微波消解法的加标回收率分别为72.8%~99.3%,88.0%~102.0%,89.0%~103.0%。微波消解处理样品,ICP–AES法同时测定4种样品中5种重金属的含量,其测定结果的相对标准偏差均小于17%。微波消解–ICP–AES适合生蚝中铅、铜、镉、铬、铁含量的快速测定。     

火焰原子吸收光谱法测定煤矸石土种植的农作物中金属元素含量

采用干灰化法消化样品,火焰原子吸收光谱法测定了煤矸石土种植植物中的钙、镁、铜、锌、铁、锰等6种金属元素的含量。6种元素均在一定的质量浓度范围内与其吸光度呈线性关系,方法的检出限(3s)在0.002～0.017mg.L-1之间。回收率在96.8%～106.1%之间,相对标准偏差(n=6)在0.17%～4.25%之间。方法用于煤矸石土和沙土上种植的玉米、蚕豆和豌豆中6种金属元素含量的测定,结果表明:煤矸石土上种植粮食中6种元素的含量均高于沙土上种植的,矸石土壤种植的蚕豆中镁含量较高,豌豆中铁和锰含量较高。     

Determination of selenium, zinc and cadmium in antidandruff shampoos by atomic spectrometry after microwave assisted sample digestion

Microwave assisted pre-treatments for atomic spectrometric determination (inductive coupled plasma-optical emission spectrometry, ICP-OES or flame atomic absorption spectrometry, FAAS) of metallic elements, usually present in antidandruff shampoos, are proposed. They are based on the digestion of the sample with HNO₃ into a closed reactor, which is irradiated at 800 W for a few minutes. Selenium was determined by ICP-OES. The limit of detection was 0.11 mg l⁻¹; the relative standard deviation (R.S.D.) for the selenium content in the samples was in the 0.6–3.6% range. The results obtained were in agreement with the label contents and the recovery of the proposed method was in the 100–106% range. Zinc and cadmium were determined by FAAS. The limit of detection for zinc determination was 0.078 mg l⁻¹; the R.S.D. for zinc contents was in the 0.8–8.6% range. A limit of detection of 0.09 mg l⁻¹ was obtained for cadmium determination; the R.S.D. for cadmium contents was in the 0.7–2.7% range. The determinations were performed after two different sample mineralization pre-treatments — dry ashing (in an electric furnace) and wet mineralization (in a microwave oven). Both methodologies provided comparable results for zinc and cadmium determination in shampoos. The proposed microwave assisted digestion procedures allow a precise and accurate determination of selenium, zinc and cadmium in commercial antidandruff shampoos, and the sample pre-treatment is less time-consuming than the classic methods.     

Revisitation of mineralization modes for arsenic and selenium determinations in environmental samples

Mineralization procedures for arsenic and selenium analysis are usually limited to wet digestion methods owing to high volatility of these analytes. On the other hand, variable amounts of silicon in some types of samples imply elaborated mineralization procedures to liberate analytes which may be retained in an insoluble residue. Consequently, methods for such material generally include an hydrofluoric step followed by an evaporation to dryness. This type of mineralization is most easily accomplished using a dry ashing procedure. For plant analysis, a well validated and readily applicable dry ashing method is used for a long time in several laboratories but up today one could suppose that As and Se determinations cannot be performed after such a type of mineralization. Surprisingly, it has been observed that for plant samples these analytes are detected even after a calcination at 450 degrees C. The general usefulness of a dry ashing method for analysis of all other analytes (main, minor and trace elements) incitates us to also verify As and Se recoveries. Results obtained in this work indicate clearly that plants of terrestrial origin may be mineralized using dry ashing procedure without As and Se losses. This statement was confirmed by analyses of several reference terrestrial plant samples (RMs) and laboratory control samples. Another confirmation was given by the direct graphite furnace analysis of the same plant samples but in slurried form (SS-ETAAS). As a direct consequence, As and Se analysis in terrestrial plants no more necessitates a separate preparation methodology. On the other hand, significant losses of As and Se were observed for aquatic plants, e.g. algaes. For the analysis of this type of samples, a separate wet digestion procedure remains unavoidable if the determination of As and Se has to be considered. Also some preparation procedures were tested for As and Se-analysis of soil and sediment reference samples. In these cases the wet digestion with a mixture of nitric, perchloric and hydrofluoric acids seems to remain the best alternative.     

Determinations of uranium at trace and subtrace levels in organic substances by wet ashing-Arsenazo III method

A method was developed for the determination of trace and subtrace amounts of uranium in organic substances used during the industrial process of nuclear fuel production. The method is based on decomposing 50 g of the sample by wet ashing with 25 g conc. sulfuric acid. The residue from the ashing process was ignited at 525 °C to remove all carbonaceous materials. The residue was boiled with 10 ml of 11 nitric acid. The resulting solutions was analyzed for uranium concentration using a modification of the arsenazo III method which allows for uranium determination after separating it by TBP extraction from all the interfering elements. The proposed method proved to be sensitive (detection limit: 15 ppb). The relative standard deviation of the method for a sample containing 200 ppb uranium is 5%. The dynamic range of the method is wide, since the method is applicable. for trace and subtrace levels of uranium in organic substances.