C51;Z16 标准查询与下载

JIS K 0400-55-20:1998 水质.用原子吸收光谱法测定镉含量

この規格は，カドミウムの定量に関する二つの方法;フレーム原子吸光法(第2章)及び電気加熱原子吸光法(第3章)について規定する。

Water quality -- Determination of cadmium by atomic absorption spectrometry

JIS K 0400-57-10:1998 水质.铁的测定.使用1、10-菲咯啉光谱法

この規格は水及び廃水中の鉄の1 .10ーフェナントロリンによる吸光光度法について規定する。手順は次の定量について記載する。

Water quality -- Determination of iron -- Spectrometric method using 1,10-phenanthroline

JIS K 0400-58-10:1998 水质.铝的测定.使用邻苯二酚紫罗兰光谱法

この規格は，地下水，少し汚染された陸水及び海水中のろ過性のアルミニウムをピロカテゴールバイオレット吸光光度法によって定量する方法について規定する。

Water quality -- Determination of aluminium -- Spectrometric method using pyrocatechol violet

JIS K 0400-61-10:1998 水质.总砷的测定.二乙基氨氰酸银光谱测定法

この規格は，水中及び廃水中のひ素定量のためのジエチルジチオかルバミド酸銀吸光光度法について規定する。

Water quality -- Determination of total arsenic -- Silver diethyldithiocarbamate spectropotometric method

JIS K 0400-65-10:1998 水质.总铬的测定.原子吸收光谱测定法

この規格は，原子吸光法による水中の全クロムの定量に関する二つの方法について規定する。二つの方法は，次に示す章に規定している。第2章 方法Aーフレーム原子吸光法による全クロムの定量 第3章 方法B一電気加熱原子吸光法による全クロムの定量

Water quality -- Determination of total chromium -- Atomic absorption spectrometric methods

JIS K 0400-65-20:1998 水质.铬(VI)的测定.用1、5-二苯卡巴肼的光谱测定法

この規格は，水中のクロム(Ⅵ)定量のための吸光光度法について規定する。この方法は，0.05-3 mg/lの溶存クロム(Ⅵ)の定量に適用できる。定量の範囲は，試料の希釈によって広げられる。

Water quality -- Determination of chromium(VI) -- Spectrometric method using 1,5-diphenylcarbazide

JIS K 0400-66-10:1998 水质.用无火焰原子吸收光谱法测定总汞含量.第1部分:用高锰酸钾-过氧二硫酸盐煮解后的方法

この規格は，水中，特に表層水，生活及び工場廃水の全水銀のフレームレス原子吸光法による定量について規定する。最適条件下(最小のべースラインノイズ，スべクトル線の純度が高いランプ及び水銀含有量が非常に低い試薬)の分析では，測定試料中約0.05 μgの水銀が定量できる。例えば,測定試料100 mlを用いた場合の定量下限は0.5 μg/lである。この方法は，7.3.1の操作で過マンガン酸カリウムの赤紫の色が持続できないほど多量の有機物を含む試料には適用できない。さらに。よう化物イオンの存在は，この方法の分析精度をかなり低下させる(9.参照)。

Water quality -- Determination of total mercury by flameless atomic absorption spectrometry -- Part 1: Method after digestion with permanganate-peroxodisulfate

JIS K 0400-66-30:1998 水质.用无火焰原子吸收光谱法测定总汞含量.第3部分:溴煮解后的方法

この規格は，フレームレス原子吸光法による全水銀の定量方法を規定するもので，淡水。軟水かん水(塩水)，その他有機物の少ない水に適用する。この方法は，0.2 μg/lより高い濃度の水銀を測定できる。しかしながら，測定条件を最適に整えれば(最小のべースラインノイズ，スペクトル線の純度が高いランプ及び水銀含有量が非常に低い試薬)，検出下限を0.05 μg/lを得ることができる。添加した量の臭素(7.3.1の備考参照)で，側定試料中の有機物の酸化が十分にできない場合には，この方法を適用することはできない。

Water quality -- Determination of total mercury by flameless atomic absorption spectrometry -- Part 3: Method after digestion with bromine

JIS K 0400-67-20:1998 水质.硒的测定.原子吸收分光光度计方法(氢化物技术)

この規格はフレーム原子吸光法による地下水及び表層水中の1～10μg/lのセレン及び有機結合セレンの定量法について規定する。これより高い濃度のものも適切に薄めることによって定量可能である。

Water quality -- Determination of selenium -- Atomic absorption spectrometric method (hydride technique)

ASTM D6238-98(2011) 水中总需氧量的标准试验方法

The measurement of oxygen demand parameters is critical to the control of process wastewaters. Biochemical oxygen demand (BOD) and chemical oxygen demand (COD) analyzers have long time cycles and in the case of COD analyzers use corrosive reagents with the inherent problem of disposal. Total oxygen demand analysis is faster, approximately 3 min, and uses no liquid reagents in its analysis. TOD can be correlated to both COD and BOD, providing effective on-line control. TOD offers several features which make it a more attractive measurement than carbon monitoring using Total Carbon (TC) or Total Organic Carbon (TOC) analyzers. TOD is unaffected by the presence of inorganic carbon. TOD analysis will also indicate noncarbonaceous materials that consume or contribute oxygen. For example, the oxygen demand of ammonia, sulfite and sulfides will be reflected in the TOD measurement. Also, since the actual measurement is oxygen consumption, TOD reflects the oxidation state of the chemical compound (that is, urea and formic acid have the same number of carbon atoms, yet urea has five times the oxygen demand of formic acid).1.1 This test method covers the determination of total oxygen demand in the range from 100 to 100 000 mg/L, in water and wastewater including brackish waters and brines (see 6.5). Larger concentrations, or samples with high suspended solids, or both, may be determined by suitable dilution of the sample. 1.1.1 Since the analysis is based on the change in oxygen reading of the carrier gas compared to that when a sample is introduced (see 4.1), the measurement range is a function of the amount of oxygen in the carrier gas. The higher the desired concentration range, the more oxygen required in the carrier gas. Under recommended conditions, the carrier gas concentration should be between two to four times the maximum desired oxygen demand. 1.1.2 The lower measurement range is limited by the stability of the baseline oxygen detector output. This signal is a function of the permeation system temperature, carrier gas flow rate, oxygen detector temperature, and reference sensor voltage. Combined, these variables limit the minimum recommended range to 2 to 100 mg/L. 1.1.3 The upper measurement range is limited by the maximum oxygen concentration in the carrier gas (100 %). With the recommended conditions of carrier gas concentration being two to four times the maximum oxygen demand, this limits the maximum possible oxygen demand to between 250 000 to 500 000 mg/L. However, as a practical application to water analysis, this test method will consider a maximum range of 100 000 mg/L. 1.2 This test method is applicable to all oxygen-demanding substances under the conditions of the test contained in the sample that can be injected into the reaction zone. The injector opening limits the maximum size of particles that can be injected. If oxygen-demanding substances that are water-insoluble liquids or solids are present, a preliminary treatment may be desired. These pretreatment methods are described in Annex A2. 1.3 This test method is particularly useful for measuring oxygen demand in certain industrial effluents and process streams. Its application for monitoring secondary sewage effluents is not established. Its use for the monitoring of natural waters is greatly limited by the interferences defined in Section 6. 1.4 In addition to laboratory analysis, this test method is applicable to on-stream monitoring. Sample conditioning techniques for solids pretreatment applications are noted in Annex A2. 1.5 The values stated in SI units are to be regarded as standard. No other units of measurement are included in this standard. 1.6 This standard does not purport to address all of the safety concerns, if any, associated with......

Standard Test Method for Total Oxygen Demand in Water

ISO 10304-3:1997 水质 离子色谱法测定溶解性阴离子 第3部分 铬酸盐、碘化物、亚硫酸盐、硫氰酸盐和硫代硫酸酯的测定

This part of ISO 10304 specifies methods for the determination in aqueous solution of the dissolved anions - iodide, thiocyanate and thiosulfate (clause 4); - sulfite (clause 5); - chromate (clause 6). An appropriate pretreatment of the sample (e.g. dilution) and the application of a conductivity detector (CD), UV detector (UV) or amperometric detector (AD) make the working ranges given in table 1 feasible.

Water quality - Determination of dissolved anions by liquid chromatography of ions - Part 3: Determination of chromate, iodide, sulfite, thiocyanate and thiosulfate

BS 6068-4.11:1996 水质.第4部分：微生物方法.第11节：噬菌体的检测和计数.F-具体RNA噬菌体的计数

Water quality. Microbiological methods. Detection and enumeration of bacteriophages. Enumeration of F-specific RNA bacteriophages

ASTM D5904-96 用紫外线、过(二)硫酸盐氧化物和薄膜导电率检测法测定水中总含碳量、有机碳和无机碳的标准试验方法

1.1 This test method covers the determination of total carbon (TC), inorganic carbon (IC), and total organic carbon (TOC) in water in the range from 0.5 to 30 mg/L of carbon. Higher levels may be determined by sample dilution. The test method utilizes ultraviolet-persulfate oxidation of organic carbon, coupled with a CO2 selective membrane to recover the CO2 into deionized water. The change in conductivity of the deionized water is measured and related to carbon concentration in the oxidized sample. Inorganic carbon is determined in a similar manner without the requirement for oxidation. In both cases, the sample is acidified to facilitate CO2 recovery through the membrane. The relationship between the conductivity measurement and carbon concentration is described by a set of chemometric equations for the chemical equilibrium of CO2 , HCO3 , H , and the relationship between the ionic concentrations and the conductivity. The chemometric model includes the temperature dependence of the equilibrium constants and the specific conductances. 1.2 This test method has the advantage of a very high sensitivity detector that allows very low detection levels on relatively small volumes of sample. Also, use of two measurement channels allows determination of CO2 in the sample independently of organic carbon. Isolation of the conductivity detector from the sample by the CO2 selective membrane results in a very stable calibration, with minimal interferences. 1.3 This test method was used successfully with reagent water spiked with sodium bicarbonate and various organic materials. It is the user's responsibility to ensure the validity of this test method for waters of untested matrices. 1.4 This test method is applicable only to carbonaceous matter in the sample that can be introduced into the reaction zone. The injector opening size generally limits the maximum size of particles that can be introduced. 1.5 In addition to laboratory analyses, this test method may be applied to on line monitoring. 1.6 This standard does not purport to address all of the safety concerns, if any, associated with its use. It is the responsibility of the user of this standard to establish appropriate safety and health practices and determine the applicability of regulatory limitations prior to use.

Standard Test Method for Total Carbon, Inorganic Carbon, and Organic Carbon in Water by Ultraviolet, Persulfate Oxidation, and Membrane Conductivity Detection

ISO 10304-2:1995 水质 离子色谱法测定溶解性阴离子 第2部分 对废水中溴化物、氟化物、硝酸盐、亚硝酸盐、亚磷酸盐和硫酸盐的测定

Specifies a method for the determination of the dissolved anions bromide, chloride, nitrate, nitrite, orthophosphate and sulfate in waste waters.

Water quality - Determination of dissolved anions by liquid chromatography of ions - Part 2: Determination of bromide, chloride, nitrate, nitrite, orthophosphate and sulfate in waste water

ISO 10523:1994 水质 pH值测定

The method specified (using a pH-meter) is applicable to all types of water and waste water samples in the range from pH 3 to pH 10. The temperature, some gases and organic materials interfere with the pH-measurement. Suspended materials in the sample may cause significant errors. When measuring sewage and some surface waters, there is a particularly high risk of smearing the electrodes or contaminating the membranes and diaphragm with oil, grease or other contaminants.

Water quality - Determination of pH

DIN EN 903:1994 水质.通过测量亚甲兰指数MBAS确定负离子表面活化剂

The document describes a method for photometric determination of low concentrations of methylene blue active substances (MBAS), i.e. anonic surface active material (chiefly sulfonates and sulfates) in influents and effluents of sewage plants, waste, surface and drinking water. The range of this method is 0.1 to 5.0 mg/l, the limit of detection for solutions of standard surfactants in distilled water, about 0.05 mg/l.#,,#

Water quality; determination of anionic surfactants by measurement of the methylene blue index MBAS (ISO 7875-1:1984, modified); German version EN 903:1993

BS 6068 Sec.2.45:1993 水质.第2部分:物理、化学和生化方法.第45节:硒的原子吸收光谱法测定

Water quality. Physical, chemical and biochemical methods. Determination of selenium by atomic absorption spectrometry

ISO 5667-11:1993 水质 采样 第11部分:地下水采样导则

Provides guidance on the design of sampling programmes, sampling techniques and the handling of water samples taken from groundwater for physical, chemical and microbiological assessment. The general purpose of sampling programmes for groundwaters is to survey the quality of groundwater supplies, to detect and assess groundwater pollution, to assist in groundwater resource management, and other more detailed objectives.

Water quality; sampling; part 11: guidance on sampling of groundwaters

ISO 5667-8:1993 水质 采样 第8部分:湿沉积物采样方法指南

Provides guidance on the design of sampling programmes and the choice of instrumentation and techniques for the sampling of the quality of wet deposition. Does not cover measurement of the quantity of rain, dry deposition or other types of wet deposition such as mist, fog and cloudwaters. The main objectives are control of local emissions and assessment of long range transport of airborne pollutants.

Water quality; sampling; part 8: guidance on the sampling of wet deposition

ASTM D5392-93(2006) 用两步膜滤法分离和计数水中大肠杆菌的标准试验方法

This test method is useful for measuring recreational water quality and chlorinated wastewaters, although it can be used for any water suspected of contamination by fecal wastes of warm-blooded animals. The significance of finding E. coli in recreational water samples, especially samples obtained from fresh recreational waters, is that there is a risk of gastrointestinal illness, directly related to the E. coli density, associated with swimming.4 Since small or large volumes of water or dilutions thereof can be analyzed by the MF technique, a wider range of levels of E. coli in water can be detected and enumerated than with other methods.1.1 This test method describes a membrane filter (MF) procedure for the detection and enumeration of Escherichia coli, a bacterium found exclusively in the feces of humans and other warm-blooded animals. The presence of these microorganisms in water is an indication of fecal pollution and the possible presence of enteric pathogens. These bacteria are found in water and wastewater in a wide range of densities. The detection limit of this procedure is one colony forming unit (CFU) per volume filtered.1.2 This test method has been used successfully with temperate fresh and marine ambient waters, and wastewaters. It is the user's responsibility to ensure the validity of this test method for waters of other types.This standard does not purport to address all of the safety concerns, if any, associated with its use. It is the responsibility of the user of this standard to establish appropriate safety and health practices and determine the applicability of regulatory limitations prior to use. For specific hazard statements, see Section 9.

Standard Test Method for Isolation and Enumeration ofEscherichia Coli in Water by the Two-Step Membrane Filter Procedure