自动电位滴定法标定硫酸铈溶液和测定硫酸亚铁片中铁含量

采用自动电位滴定法标定硫酸铈溶液,并进行硫酸亚铁片中铁含量的测定。自动电位滴定法以电位突跃监测终点,在45℃~50℃之间,以草酸钠溶液标定硫酸铈溶液,测定值的相对标准偏差(n=5)为0.070%。取硫酸亚铁片1片用0.01mol·L-1硫酸溶液30mL溶解,直接用硫酸铈溶液滴定测定铁含量。方法用于硫酸亚铁片样品分析,回收率为100%,测定值的相对标准偏差(n=5)在1.2%~2.6%之间。     

自动电位滴定法测定高纯氯化铵的纯度

建立自动电位滴定法测定高纯试剂氯化铵纯度的方法。以硝酸银标准滴定溶液作滴定剂,采用自动电位滴定仪测定高纯氯化铵的含量。测定结果的相对标准偏差为0.03%(n=6)。采用该法与化学滴定法对高纯氯化铵样品进行测定,两种方法的测定结果无显著性差异。该方法操作简便、快捷,自动化程度高,滴定终点判断敏锐,测定结果准确可靠。     

电位滴定法测定抛光液中的三酸含量

探讨了利用自动电位滴定仪对抛光液中磷酸、硫酸及硝酸的分析方法,以及对溶剂的标定方法。电位滴定法测定三酸,先用硫酸亚铁铵滴定硝酸,再用氢氧化钠滴定磷酸和硫酸,从而计算三酸含量。结果表明,与传统滴定法相比,电位滴定法标定硫酸亚铁铵的相对标准偏差(RSD)从1.1%降至0.13%,标定氢氧化钠的RSD从0.72%降至0.06%。电位滴定法测定自配样品及工厂抛光产品中的硝酸,回收率分别在96%及93%以上。电位滴定法测定自配样品及工厂抛光产品中磷酸和硫酸的回收率偏差在3%以内。手动滴定法测定磷酸和硫酸的回收率偏差在5%~10%,回收效果不如电位滴定法。电位滴定法测定工厂抛光液的三酸加标回收率偏差均小于3%。自动电位滴定法比手工滴定的准确性和精密度明显提高,弥补了手工滴定法只能分析磷酸和硫酸,而无法测定硝酸的缺陷。     

电位滴定法测定抛光液中的三酸含量

探讨了利用自动电位滴定仪对抛光液中磷酸、硫酸及硝酸的分析方法,以及对溶剂的标定方法。电位滴定法测定三酸,先用硫酸亚铁铵滴定硝酸,再用氢氧化钠滴定磷酸和硫酸,从而计算三酸含量。结果表明,与传统滴定法相比,电位滴定法标定硫酸亚铁铵的相对标准偏差(RSD)从1.1%降至0.13%,标定氢氧化钠的RSD从0.72%降至0.06%。电位滴定法测定自配样品及工厂抛光产品中的硝酸,回收率分别在96%及93%以上。电位滴定法测定自配样品及工厂抛光产品中磷酸和硫酸的回收率偏差在3%以内。手动滴定法测定磷酸和硫酸的回收率偏差在5%～10%,回收效果不如电位滴定法。电位滴定法测定工厂抛光液的三酸加标回收率偏差均小于3%。自动电位滴定法比手工滴定的准确性和精密度明显提高,弥补了手工滴定法只能分析磷酸和硫酸,而无法测定硝酸的缺陷。     

冷空气蒸馏分离酸滴定法测定复合肥中铵态氮

提出了用冷空气蒸馏分离酸滴定法在多种形态氮共存时测定复合肥料中铵态氮含量的方法。取适量复合肥料样品于蒸馏瓶中,与550g.L-1碳酸钾溶液60mL反应,溶液总体积以不宜超过110mL。通过空气在流量为3L.min-1和不加热条件下蒸馏8h,生成的氨馏出并先后吸收于相互连接的3个吸收瓶中,每一吸收瓶中预置硼酸吸收溶液50mL,用0.05mol.L-1盐酸标准溶液滴定3溶液至指示剂呈暗红色,记录所耗盐酸标准溶液的总量。将吸收瓶重新按装在蒸馏系统中继续蒸馏1h后再进行滴定,以所耗盐酸标准溶液量不超过0.03mL认为测定完成。根据滴定所耗盐酸标准溶液的总量计算样品中铵态氮的含量。根据3个样品各5次测定结果计算,得到方法的回收率在99.7%～100.1%之间,相对标准偏差在0.12%～0.55%之间。     

称量滴定法测定亚硝酸盐

采用称量滴定法测定NO2的含量.通过使用KMnO4溶液标准物质及草酸钠纯度标准物质,对样品直接进行氧化还原滴定测量.其测定结果具有溯源性,保证了测量结果的可靠性.该方法具有较高的测量精度,实验结果的RSD小于0.1%.     

十六烷基三甲基溴化铵光度滴定法测定硫酸外国佬骨素钠盐

建立一种测定硫酸软骨素的新方法。十六烷基三甲基溴化铵在KH2PO4-Na2HPO4缓冲溶液中、乳化剂OP共存下与硫酸软骨素反应形成离子对缔合物，溶液转变成稳定的乳化液。用光度滴定法测定硫酸软骨素。用标准加入法做加收试验，回收率为99.9%-100.2%，相对标准偏差0.32%-0.40%。方法应用于外贸样品测定，结果满意，方法准确、简便、快速。     

库仑滴定法快速测定白酒中总酯的含量北大核心CSCD

提出了库仑滴定法测定白酒中总酯含量的方法。以铂电极为工作电极对,pH复合玻璃电极为指示电极,0.80 mol·L^(-1)硫酸钾溶液为支持电解质,通过恒电流电解生成的H~+滴定预处理后样品中剩余的OH^(-),直至滴定终点pH 7.70,根据法拉第电解定律测得样品中总酯的含量。结果表明:测定过程约10 min完成。按标准加入法进行回收试验,回收率为88.0%~106%。方法用于实际白酒样品中总酯含量的测定,测定结果与国家标准规定的电位滴定法测定结果无显著性差异。     

可见光光谱滴定法测定水中总硬度北大核心CSCD

提出了可见光光谱滴定法测定水中总硬度的方法。在整个滴定过程采用颜色真实测量体系替代人的感官判定,建立了光谱计量参数与试剂量的色变滴定曲线,用曲线上的突变峰标识滴定终点或结构变化点。可见光光谱滴定法可以克服感官滴定存在色评价条件不统一、操作人员个体生理条件不一致、无法量值溯源等困难,能实现测定的自动化。上述方法用于测定水质总硬度标准样品,结果显示测定值均在标准样品认定值的不确定度范围内。按照标准加入法对实际样品进行回收试验,回收率为99.7%~101%。分别采用可见光光谱滴定法和目视滴定法[即乙二胺四乙酸(EDTA)络合滴定法]测定8种水体样品的总硬度,配对t检验结果表明两种方法的测定结果无显著性差异。     

纳氏试剂分光光度法测定土壤中全氮含量

提出了纳氏试剂分光光度法测定土壤中全氮含量。以硫酸铜为加速剂,用硫酸对土壤样品进行消解。消解完毕的溶液用400g·L-1氢氧化钠溶液调节其酸度至pH 10左右,溶液与沉淀一起移入容量瓶中,定容至200mL。移取上清液10mL于50mL比色管中,加入酒石酸钾钠溶液作掩蔽剂,加入纳氏试剂显色后,加水定容,于波长420nm处测量其吸光度并计算土壤样品中全氮含量。氮的质量浓度在2mg·L-1以内与吸光度呈线性关系。方法用于土壤样品分析,测定值与滴定法测定值相符,测定值的相对标准偏差(n=10)为0.24%;回收率在92.3%~112%之间。     

过硫酸铵氧化-亚铁容量法测定高温合金及钢铁中高铬含量

在航空行业标准HB 5220.15-1995的基础上,采用过硫酸铵氧化-亚铁容量法测定高温合金及钢铁中高铬含量的试验方法,通过试验确定了试样量、硫酸和磷酸等试剂用量。该方法对高温合金样品中铬含量测定结果的相对标准偏差不大于0.13%(n=8),回收率为100.04%~100.49%。方法稳定性和重复性好,适用于铬含量为30.00%~50.00%的高温合金及钢铁样品。     

滤纸还原–硫酸铈滴定法测定含锑铅精矿中锑

建立滤纸还原-硫酸铈滴定法测定含锑铅精矿中锑含量的方法。采用硫酸、硝酸溶解样品,以滤纸作还原剂,在盐酸介质中,用磷酸掩蔽高价铁,以甲基橙和亚甲基蓝为指示剂,于80~90℃下,用硫酸铈标准溶液滴定至溶液突变至亮蓝色(铁含量高时为黄绿色)为终点。在实验条件下对3个含锑铅精矿样品进行分析,测定结果的相对标准偏差为0.7%~2.2%(n=8),加标回收率为95%~106%。分别采用该方法和锑矿石中锑的国家标准分析方法GB/T 15925-2010对含锑铅精矿样品进行测定,两种方法的测定值基本一致,相对误差为1.4%~4.5%。该方法准确度高,精密度好,成本低,适用于铅精矿中锑含量的测定。     

硫酸铅分离-EDTA滴定法测定铜闪速冶炼烟尘中的铅

建立了用硫酸形成硫酸铅沉淀加以分离,再用EDTA络合滴定法测定铜闪速冶炼烟尘中铅量的方法。试样用盐酸、硝酸、硫酸、氟化氢铵和高氯酸溶解,用硫酸沉淀铅与其它干扰元素分离,沉淀溶解于乙酸-乙酸钠缓冲溶液中,以巯基乙酸掩蔽铋,抗坏血酸掩蔽铁,二甲酚橙作指示剂,用Na2EDTA标准滴定溶液滴定溶液中铅含量,采用火焰原子吸收光谱法测定滤液中铅含量加以补正。实验结果表明,沉淀时硫酸(1+24)加入量为50 mL,无水乙醇加入量为10 mL,乙酸-乙酸钠缓冲溶液加入量为30 mL。方法相对标准偏差(RSD)在0.35%~1.5%,加标回收率为在99.0%~101%。完全满足生产控制分析的要求,同时也可以作为类似物料中铅分析的参考方法。     

Determination of crude protein in animal feed, forage, grain, and oilseeds by using block digestion with a copper catalyst and steam distillation into boric acid: collaborative study

A collaborative study was conducted to evaluate the repeatability and reproducibility of an extension of AOAC Official Method 991.20, Nitrogen (Crude) in Milk, to animal feed, forage (plant tissue), grain, and oilseed materials. Test portions are digested in an aluminum block at 420 degrees C in sulfuric acid with potassium sulfate and a copper catalyst. Digests are cooled and diluted, and concentrated sodium hydroxide is added to neutralize the acid and make the digest basic; the liberated ammonia is distilled by using steam distillation. The liberated ammonia is trapped in a weak boric acid solution and titrated with a stronger standardized acid, hydrochloric acid; colorimetric endpoint detection is used. Fourteen blind samples were sent to 13 collaborators in the United States, Denmark, Sweden, Germany, and the United Kingdom. Recoveries of nitrogen from lysine, tryptophan, and acetanilide were 86.8, 98.8, and 100.1%, respectively. The within-laboratory relative standard deviation (RSDr, repeatability) ranged from 0.40 to 2.38% for crude protein. The among-laboratories (including within-) relative standard deviation (RSD(R), reproducibility) ranged from 0.44 to 2.38%. It is recommended that the method be adopted First Action by AOAC INTERNATIONAL. A lower concentration (1% H3BO3) of trapping solution was compared with the concentration specified in the original protocol (4% H3BO3) and was found comparable for use in an automatic titration system in which titration begins automatically as soon as distillation starts. The Study Directors recommend that 1% H3BO3 as an optional alternative to 4% boric acid trapping solution be allowed for automatic titrators that titrate throughout the distillation.     

一种自动微量滴定新方法

本文依据传统滴定分析原理，利用流动注射装置提出一种新的自动微量滴定方法，它不仅具有流动注射滴定分析法简便快速，试剂和试样消耗少，仪器装置简单等优点，而且测定信号怀被测组分的浓度直接成线性关系，结果的准确度和精度优于一般流动注射滴定方法。通过用盐酸滴定氢氧化钠进行验证，相关系数为０．９９９９，相对标准偏差（ＲＳＤ）为０．４％。     

用自动凯氏定氮仪测定水中氨氮

用MgO控制预蒸馏水中的pH值,以硼酸溶液为吸收液,用稀硫酸进行中和滴定,用自动凯氏定氮仪测试水中的氨氮,检测下限为1mg/L,相对标准偏差在0.32%~1.04%范围内,加标回收率为96%~104%,并将该法与纳氏试剂比色法和离子色谱法进行了比较。     

水杨酸钠紫外分光光度法测定烟草中的总氮

建立水杨酸钠紫外分光光度法测定烟草中总氮含量的方法。烟草样品经硫酸铜–硫酸钾–浓硫酸消化,用水杨酸钠–二氯异氰尿酸钠显色后用紫外分光光度计检测,并对波长、显色剂用量和反应时间等实验条件进行了优化。总氮的质量浓度在5~60 mg/L范围内与其吸光度呈良好的线性关系,线性相关系数为0.998 8,方法的检出限为0.14 mg/L。样品分析结果的相对标准偏差为3.22%(n=6),样品加标回收率为99.30%~101.62%。该方法具有较高的精密度和准确度,尤其适用于样品量少时对烟草中总氮的测定。     

Determination of Nitrates in Water Samples by In‐Electrode Coulometric Titration in Copper Coated Porous Vitreous Carbon Electrode

Nitrate in water samples was determined by in‐electrode coulometric titration in porous electrode made of vitreous carbon particles coated with copper. The sample was mixed with diluted sulfuric acid containing 1 mmol/L hydrochloric acid, the solution was filled into the cell and electrode and the nitrate ions were directly reduced by constant current to ammonium ions. The stoichiometry of the electrode reaction was found by coulometric and photometric measurements. The detection limit and precision were found to be 0.2 mg/L and 1.7 %, respectively. The interfering effect of high chloride contents was eliminated by precipitating chlorides with silver sulfate. The method was applied for the analysis of various water samples and beverages. The results were in good agreement with data from isotachophoretic and photometric measurements.     

Effect of acidity and alkalinity on the distillation of phenol: interferences of aromatic amines and formaldehyde with the 4-aminoantipyrine spectro-photometric method for phenol

As determined by the 4-aminoantipyrine (4-AAP) spectrophotometric method, the distillation of phenol is quantitative over the range from about pH 6 to very strongly acidic solutions. Recovery from alkaline solutions decreases with increasing alkalinity. Aromatic amines can interfere with the 4-AAP method by producing colors. The extent of the interference varies markedly with different aromatic amines and is much greater for the extraction method than the direct method. The interference can be considerably reduced by distillation from a strongly acidic solution (10 ml of concentrated sulfuric acid per 500 ml); for large amounts of aromatic amines, double distillation may be necessary. Formaldehyde can interfere by reacting with phenol and repressing the color development. This interference can be eliminated by treatment with ammonium sulfate and sodium hydroxide to form hexamethylenetetramine, followed by acidification and distillation.