首页 | 本学科首页   官方微博 | 高级检索  
相似文献
 共查询到20条相似文献,搜索用时 234 毫秒
1.
采用紫外光与臭氧结合消解水样,用离子色谱法测定水质总磷含量,色谱峰高与磷酸盐质量浓度在0-20mg/L范围内线性关系良好,检出限和测定下限分别0.008mg/L和0.03mg/L。此方法无需添加化学试剂,避免了标准分析方法中各种因素的影响,操作简单快速、省时,测定水质总磷的相对标准偏差为0.07%(n=5o对实际样品进行分析,总磷的加标回收率为94.5%~105.5%,表明该方法测定结果可靠,具有一定的应用价值。  相似文献   

2.
微波消解-紫外分光光度法测定水中总氮   总被引:5,自引:0,他引:5  
研究了用微波消解-紫外分光光度法测定水样中的总氮,结果表明,所提出的消解方法具有操作简单、省时、消解完全的特点,精密度和准确度均令人满意.方法的线性范吲为0.0242~9.60mg/L,水样加标回收率为101%~103%,相对标准偏差为0.13%~0.44%。  相似文献   

3.
建立离子色谱法测定水样中氯化物的方法,Cl^-浓度在0.40~4.00mg/L范围内与色谱峰面积呈线性关系,线性方程为A=0.0680c+0.0011,线性相关系数r=0.9995。样品6次测定结果的相对标准偏差为1.01%,加标回收率为91.8%~97.3%。与硝酸银滴定法进行比对试验,两种方法测定结果基本一致。离子色谱法操作方便快捷,污染少,测定结果准确、可靠。  相似文献   

4.
离子色谱法测定水中总氮   总被引:1,自引:0,他引:1  
用离子色谱法检测水中总氮,检测波长为205nm,整个分析过程仅需7min。方法的检出限为0.03mg/L.测定结果的相对标准偏差为2.1%~3.5%(n=7),加标回收率为99.0%~103.5%。用离子色谱法和分光光度法对水样进行测定,两种方法测定结果的相对偏差不大于2.1%。  相似文献   

5.
用稀硫酸吸收,离子色谱法测定乙烯中微量的氨,对吸收瓶、吸收溶液的浓度进行选择,同时对方法的吸收效率、加标回收率、检出限、精密度进行测试。该方法快速、简便,不需要复杂的样品前处理,完成一次测定只需16min。该方法检出限为0.003mg/L,当采样体积为100L时,最低检出浓度为0.003mg/m^3。样品测定结果的相对标准偏差为2.8%(n=4),加标回收率为93.8%-109%。  相似文献   

6.
单扫示波极谱法测定氰化物的方法研究   总被引:3,自引:0,他引:3  
在pH7.0磷酸盐底液中,经氯胺T作用生成的氯化氰与异烟酸一吡唑酮反应生成的蓝色染料,在滴汞电极上于峰电位-0.78V(vs.SCE)处产生十分灵敏的极谱还原波,该波二阶导数峰电流与氰化物含量成正比。据此建立了单扫示波极谱法测定痕量氰化物的分析方法。方法的线性范围为0~0.05mg/L,检出限为:酒样0.005mg/L,杏仁露饮料0.0006mg/L,水样0.00006mg/L。加标回收率为85.8%~102.0%,RSD为3.0%~6.7%。适用于食品和水中痕量氰化物的测定。  相似文献   

7.
ICP-AES法测定玻璃器皿中铅、镉、砷、锑溶出量的研究   总被引:1,自引:0,他引:1  
采用ICP-AES法同时测定玻璃器皿中铅、镉、砷、锑的溶出量,对ICP-AES法测定4%乙酸浸泡液时分析线的选择和射频功率、载气压力的影响,以及基体和共存离子的干扰情况等进行了研究。4种元素的检出限分别为铅0.012mg/L,镉0.0009mg/L,砷0.015mg/L,锑O.015mg/L,加标回收率为97.3%~102.0%,测定结果的相对标准偏差为0.45%~1.36%(n=6).  相似文献   

8.
亚甲蓝分光光度法测定水体中的阴离子表面活性剂   总被引:2,自引:0,他引:2  
利用三氯甲烷萃取水体样品中的阴离子表面活性剂,用50mL比色管代替50mL容量瓶对三氯甲烷萃取液进行定容,以亚甲蓝分光光度法进行测定。该方法操作简便,测定阴离子表面活性剂的线性范围为0.150~1.70mg/L,检出限为0.050mg/L,样品加标回收率为89%~98%。  相似文献   

9.
采用固体吸附-毛细管气相色谱法测定环境空气中偏二甲肼的含量,色谱峰高与偏二甲肼浓度在0~13.8mg/L范围内线性关系良好,当采样体积为60L时,检出限和测定下限分别为0.37μg/m^3和1.2μg/m^3。低、中、高3种浓度的偏二甲肼标准溶液测定结果(n=6)的相对标准偏差分别为3.5%,2.6%,1.9%,样品加标回收率为84.5%~101.0%。  相似文献   

10.
对地下水样品除氯后,选用1.35mmol/LNa2CO3-1.00mmol/LNaHCO3混合溶液作淋洗液,用离子色谱法测定地下水样品中乙酸根的含量,乙酸根浓度在0~5.00mg/L范围内与电导率峰高呈线性关系,线性回归方程为H=15950.6c-442.7,相关系数为0.9994,方法的检出限为0.05mg/L,加标回收率为101%-110%,测定结果的相对标准偏差为2.3%。  相似文献   

11.
A simple field method which allows the determination of fluoride in drinking water with a small handheld instrument called Arsenator was developed. Arsenator is a commercially available instrument which was used successfully for reliable determination of arsenic. In the proposed method the functionality of the Arsenator which is based on a photometric measurement of a spot on the reagent paper is expanded to analyse fluoride. A polymeric aluminium complex of 5-(2-carboxyphenylazo)-8-hydroxyquinoline (LH2) has been prepared as a new specific reagent for fluoride. Job's method of continuous variation was adopted for the determination of the composition of the coloured complex, which was further characterized by UV-VIS spectroscopic studies. The molar absorptivity of the complex formation is 8.48?×?103?L?mol?1?cm?1 at 410?nm. The coloured complex reacts with fluoride on an impregnated paper where its colour changes are dependent on the concentration of fluoride in water samples. The change in the colour was measured using the Arsenator. The method allows a reliable determination of fluoride in the range 0.3 to 2.0?mg?L?1. Further spectophotometric determinations of fluoride in drinking water were also studied. The determination is based on the reaction of aluminium complex with fluoride in the examined samples. Beer's law is obeyed in the range 0.3 to 2.0?mg?L?1 of fluoride at 495?nm. Sensitivity, detection limit and quantitation limit of the method were found to be 0.251?±?0.007?µg?1?mL, 0.1?mg?L?1 and 0.3?mg?L?1, respectively. The optimum reaction conditions and other analytical conditions were evaluated. The effect of interfering ions on the determination is described. There is no interference by nitrate or chloride. Sulphate interfered only at high concentrations which are not expected in drinking water.  相似文献   

12.
A satisfactory method was described for separation and preconcentration of ultratrace amounts of fluoride ions enriched by zirconia (ZrO2) as an inorganic ion exchanger. Fluoride ions can be adsorbed rapidly and selectively on zirconia from an acidic solution (pH 4.8) then reversibly desorbed by increasing pH up to 13. A flow system consisting of a column packed with zirconia impregnated on cellulose fibers and an ion-selective electrode was used for the determination of fluoride. The RSD was found to be 1.6% and the detection limit defined by S/N = 3 was 3 × 10−9 mol L−1. The interference effects of various ions, such as nitrate, sulfate, halides, alkaline, and alkaline earth ions, which may be found in the environmental water, were studied, and it was found that they were tolerated even at high concentrations. The method was applied to determine fluoride in drinking water, which contains ultratrace amounts of fluoride. The concentration of fluoride was found to be 42 μg L−1, which is confirmed by spiking 2 μmol fluoride to the drinking water with a recovery of 99%. Published in Russian in Zhurnal Analiticheskoi Khimii, 2006, Vol. 61, No. 2, pp. 179–183. The text was submitted by the authors in English.  相似文献   

13.
This work was concerned with developing an electrophoretic method for rapid determination of nitrites and nitrates in drinking water. The background electrolyte was Tris-HCl buffer with an addition of cetyltrimethylammonium chloride to reverse the electro-osmotic flow. Online preconcentration of samples using the field-amplified sample stacking method provided detection limits of 0.003 mg L?1 (i.e. 65 nM) for nitrites and 0.010 mg L?1 (i.e. 160 nM) for nitrates, which are sufficiently low for quality control of drinking water. The method was tested in a concentration range corresponding to real drinking water samples and the differentiation between nitrites and nitrates was sufficient for simultaneous determination of nitrites at their concentrations of the order of tenths of mg L?1 and nitrates at their concentrations of the order of units to tens of mg L?1. A number of authors have neglected this important aspect when concentrating only on achieving the lowest possible detection limits. Separation of the two analytes and iodate as an internal standard was achieved in only three minutes. Total analysis time including preconditioning was eight minutes.  相似文献   

14.
A cloud point extraction procedure for pre-concentration and determination of cadmium and lead in drinking water using sequential multi-element flame atomic absorption spectrometry is described. 4-(2-thiazolylazo)-orcinol (TAO) has been used as complexing agent and the micellar phase was obtained using the non-ionic surfactant octylphenoxypolyethoxyethanol (Triton X-114) and centrifugation. The conditions for reaction and extraction (surfactant concentration, reagent concentration, effect of incubation time, etc) were studied and the analytical characteristics of the method were determined. The method allows the determination of cadmium and lead with quantification limits of 0.30?µg?L?1 and 2.6?µg?L?1, respectively. A precision expressed as relative standard deviation (RSD, n?=?10) of 2.3% and 2.6% has been obtained for cadmium concentrations of 10?µg?L?1 and 30?µg?L?1, respectively, and RSD of 1.3% and 1.7% for lead concentrations of 10?µg?L?1 and 30?µg?L?1, respectively. The accuracy was confirmed by analysis of a natural water certified reference material. The method has been applied for the determination of cadmium and lead in drinking water samples collected in the cities of Ilhéus and Itabuna, Brazil. Recovery tests have also been performed for some samples, and results varied from 96 to 105% for cadmium and 97 to 106% for lead. The cadmium and lead concentrations found in these samples were always lower than the permissible maximum levels stipulated by World Health Organization and the Brazilian Government.  相似文献   

15.
An alternative method for gas chromatographic determination of haloacetic acids (HAAs) in water using direct derivatization followed by hollow fiber membrane liquid-phase microextraction (HF-LPME) has been developed. The method has improved the sample preparation step according to the conventional US EPA Method 552.2 by combining the derivatization and the extraction into one step prior to determination by gas chromatography electron captured detector (GC-ECD). The HAAs were derivatized with acidic methanol into their methyl esters and simultaneously extracted with supported liquid hollow fiber membrane in headspace mode. The derivatization was attempted directly in water sample without sample evaporation. The HF-LPME was performed using 1-octanol as the extracting solvent at 55 °C for 60 min with 20% Na2SO4. The linear calibration curves were observed for the concentrations ranging from 1 to 300 μg L−1 with the correlation coefficients (R2) being greater than 0.99. The method detection limits of most analytes were below 1 μg L−1 except DCAA and MCAA that were 2 and 18 μg L−1, respectively. The recoveries from spiked concentration ranged from 97 to 109% with %R.S.D. less than 12%. The method was applied for determination of HAAs in drinking water and tap water samples. The method offers an easy one step high sample throughput sample preparation for gas chromatographic determination of haloacetic acids as well as other contaminants in water.  相似文献   

16.
A semiautomatic method has been proposed for the determination of different types of amines in water samples including anilines, chloroanilines, N-nitrosamines and aliphatic amines. The analytes were retained on a solid-phase extraction sorbent column and after elution, 1 μL of the extract was analysed by gas chromatography coupled with electron impact ionization mass spectrometry. A systematic overview is given of the advantages and disadvantages of several sorbents (LiChrolut EN, Oasis HLB, RP-C18, graphitized carbon black, fullerenes and nanotubes) in the retention of amine compounds and based on sensitivity, selectivity and reliability. The retention efficiency for the studied amines was higher (ca. 100%) with LiChrolut EN and Oasis HLB than it was with RP-C18 and fullerenes (53 and 62%, respectively, on average). Detection limits of 0.5-16 ng L−1 for the 27 amines studied were obtained when using a sorbent column containing 75 mg of LiChrolut EN for 100 mL of sample, the RSD being lower than 6.5%. The method was applied with good accuracy and precision in the determination of amines in various types of water including river, pond, tap, well, drinking, swimming pool and waste.  相似文献   

17.
In the present study, the ?5-(4-dimethylaminobenzylidene)rhodanin-modified SBA-15? was applied as stable solid sorbent for the separation and preconcentration of trace amounts of cobalt ions in aqueous solution. SBA-15 was modified by ?5-(4-dimethylaminobenzylidene)rhodanin reagent. The sorption of Co2+ ions was done onto modified sorbent in the pH range of 6.8–7.9 and desorption occurred in 5.0 mL of 3.0 mol L?1 HNO3. The results exhibit a linear dynamic range from 0.01 to 6.0 mg L?1 for cobalt. Intra-day (repeatability) and inter-day (reproducibility) for 10 replicated determination of 0.06 mg L?1 of cobalt was ±1.82% and ?±1.97%?. Detection limit was 4.2 µg L?1 (3Sb, n = 5) and preconcentration factor was 80. The effects of the experimental parameters, including the sample pH, flow rates of sample and eluent solution, eluent type and interference ions were studied for the preconcentration of Co2+. The proposed method was applied for the determination of cobalt in standard samples, water samples and agricultural products.  相似文献   

18.
The determination of manganese(II) in tap water and effluent streams, using a solid-phase reactor incorporated into a sequential injection system was investigated. Mn2+-ions in samples injected into a carrier stream, were oxidised by solid lead(IV) dioxide suspended on silica gel beads to form MnO4 -ions which were detected spectrophotometrically at 526 nm. The linear range of the system is from 1 to 7 mg L–1 with a detection limit of 0.62 mg L–1. The proposed system is suitable for the determination of manganese(II) in tap and effluent streams at a rate of approximately 50 samples per hour with a relative standard deviation of better than 3%. Statistical comparison between the proposed sequential injection system and a standard ICP method revealed that there is no significant difference between the two methods at the 95% confidence level for effluent streams and at 99.9% for tap water.  相似文献   

19.
建立了离子色谱仪测定环境水中氟离子的方法.优化了试验条件,即淋洗液选1.8 mmol/L Na_2CO_3-1.7mmol/L NaHCO_3,流速0.8 m L/min.试验选择了活性炭作为固体吸附剂,采用固相萃取消除环境水中有可能存在的痕量乙酸对检测F~-的干扰.方法的检出限为0.022 2 mg/L,回收率为97.6%~98.9%,相对标准偏差小于2%.结果表明方法处理简单、准确度高,可用于环境水中低含量氟化物的测定.  相似文献   

20.
This paper describes a new voltammetric procedure for the inorganic speciation of As(III) and As(V) in water samples. The procedure is based on the chemical reduction of arsenate [As(V)] to arsenite [As(III)] followed by the voltammetric determination of total arsenic as As(III) at the hanging mercury drop electrode (HMDE) by adsorptive cathodic stripping voltammetry (AdCSV) in the presence of sodium diethyl dithiocarbamate (SDDC). The reduction step involved the reaction with a mixture of Na2S2O5 and Na2S2O3 in the concentrations 2.5 and 0.5 mg mL?1, respectively, and the sample heating at 80 °C for 45 min. The linear range for the determination of total arsenic as As(III) in the presence of SDDC was between 5 and 150 μg L?1 for a deposition time of 60 s (r=0.992). A detection limit of 1.05 μg L?1 for total As was calculated for the method in water samples using a deposition time of 60 s. The detection limits of 4.2 μg L?1 and 15.0 μg L?1 for total As in seawater and dialysis concentrates, respectively, were calculated using a deposition time of 60 s. The relative standard deviations calculated were 2.5 and 4.0% for five measurements of 20 μg L?1 As(V) as As(III) in water and dialysis concentrates, respectively, after chemical reduction under optimized conditions. The method was applied for the determination of As(III) and total As in samples of dialysis water, mineral water, seawater and dialysis concentrates. Recovery values between 86.0 and 104.0% for As(III) and As(V) added to the samples prove the satisfactory accuracy and applicability of the procedure for the arsenic monitoring.  相似文献   

设为首页 | 免责声明 | 关于勤云 | 加入收藏

Copyright©北京勤云科技发展有限公司  京ICP备09084417号