SANS 5220-2010 Water - Oxygen absorption《水 氧含量》.pdf
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1、 Collection of SANS standards in electronic format (PDF) 1. Copyright This standard is available to staff members of companies that have subscribed to the complete collection of SANS standards in accordance with a formal copyright agreement. This document may reside on a CENTRAL FILE SERVER or INTRA
2、NET SYSTEM only. Unless specific permission has been granted, this document MAY NOT be sent or given to staff members from other companies or organizations. Doing so would constitute a VIOLATION of SABS copyright rules. 2. Indemnity The South African Bureau of Standards accepts no liability for any
3、damage whatsoever than may result from the use of this material or the information contain therein, irrespective of the cause and quantum thereof. ISBN 978-0-626-24321-0 SANS 5220:2010Edition 2.2SOUTH AFRICAN NATIONAL STANDARD Water Oxygen absorption Published by SABS Standards Division 1 Dr Lategan
4、 Road Groenkloof Private Bag X191 Pretoria 0001Tel: +27 12 428 7911 Fax: +27 12 344 1568 www.sabs.co.za SABS SANS 5220:2010 Edition 2.2 Table of changes Change No. Date Scope Amdt 1 2005 Amended to change the designation of SABS standards to SANS standards, to update referenced standards and to corr
5、ect the concentration of the potassium permanganate solution. Amdt 2 2010 Amended to update referenced standards. Foreword This South African standard was approved by National Committee SABS SC 147A, Water Water sampling and analysis, in accordance with procedures of the SABS Standards Division, in
6、compliance with annex 3 of the WTO/TBT agreement. This document was published in April 2010. This document supersedes SANS 5220:2005 (edition 2.1). A vertical line in the margin shows where the text has been technically modified by amendment No. 2. SANS 5220:2010 Edition 2.2 1 Water Oxygen absorptio
7、n 1 Scope and field of application This standard specifies a method of determining the oxygen absorption value of water and wastewater. The method is an empirical measure of both organic and inorganic matter that can be oxidized by an acidified permanganate solution over a period of 4 h at 27 C 2 C.
8、 2 Normative references The following referenced documents are indispensable for the application of this document. For dated references, only the edition cited applies. For undated references, the latest edition of the referenced document (including any amendments) applies. Information on currently
9、valid national and international standards can be obtained from the SABS Standards Division. Amdt 1 SANS 111/ISO 835, Laboratory glassware Graduated pipettes. Amdt 1; amdt 2 SANS 112/ISO 648, Laboratory glassware Single volume pipettes. Amdt 1 SANS 115/ISO 385, Laboratory glassware Burettes. Amdt 1;
10、 amdt 2 SANS 128/ISO 1042, Laboratory glassware One-mark volumetric flasks. Amdt 1 SANS 3696/ISO 3696, Water for analytical laboratory use Specification and test methods. 3 Principle The test portion is incubated for 4 h at 27 C 2 C in an acidified permanganate solution. The permanganate is partiall
11、y reduced by the oxidizable material present in the sample. The remainder of the permanganate is titrated with sodium thiosulfate and the oxygen absorption value calculated from the amount of permanganate reduced. The half-reaction for the reduction of permanganate is: MnO4 + 8H+ 5e= Mn2+ 4H2O The r
12、emaining permanganate is titrated with a standard thiosulfate solution: 2MnO4+ 10S2O32+ 16H+= 2Mn2+ 5S4O62+ 8H2O The equivalence point is indicated by the disappearance of the blue starch-iodine complex by reduction of the iodine to iodide with the excess thiosulfate. SANS 5220:2010 Edition 2.2 2 4
13、Reagents NOTE Unless otherwise specified, only use water that complies with the requirements of SANS 3696 and reagents of analytical grade. 4.1 Potassium permanganate solution, c(1/5 KMnO4) = 0,0125 mol/L Amdt 1 Dissolve 4,0 g of potassium permanganate in 1 L of hot water and heat to just under boil
14、ing-point for approximately 2 h. Allow the solution to cool and dilute with water to 10 L. Cover and store overnight in the dark to allow the oxidation of any organic matter and precipitation and settling of manganese dioxide. Carefully decant or siphon off the supernatant or filter through a sinter
15、ed glass funnel or glass wool. Store this solution in a glass stoppered bottle in the dark. 4.2 Potassium dichromate, standard reference solution, c(1/6 K2Cr2O7) = 0,025 mol/L Dissolve 1,226 g of potassium dichromate, previously dried at 105 C 2 C for 2 h and cooled in a desiccator, in water and dil
16、ute to 1 000 mL in a volumetric flask. 4.3 Sodium thiosulfate, stock volumetric solution, c(Na2S2O35H2O) = 0,25 mol/L Dissolve 62 g of sodium thiosulfate pentahydrate in freshly boiled and cooled water. Add 0,1 g of sodium carbonate (Na2CO3) and 10 mg of mercuric iodide (HgI2) and dissolve. Dilute t
17、o 1 000 mL with freshly boiled and cooled water in a volumetric flask. Transfer to an amber stoppered bottle and store in the dark. Allow solution to stand for at least 5 d before use. Discard this solution if it becomes turbid or within three months of the date of preparation. 4.4 Sodium thiosulfat
18、e, standard volumetric solution, c(Na2S2O35H2O) = 0,025 mol/L 4.4.1 Preparation Pipette 100,0 mL of the sodium thiosulfate stock solution (see 4.3) into a 1 000 mL volumetric flask. Add 10 mg of mercuric iodide (HgI2) and dilute to the mark with freshly boiled and cooled water. Standardize this solu
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