Standard Methods: 2310 B:  Acidity by Titration

  • Summary
  • Analytes
  • Revision
  • Data and Sites
Official Method Name
2310 B. Titration Method
Current Revision
Standard Methods Online
Media
WATER
Instrumentation
pH Meter
Method Subcategory
Physical
Method Source
  Standard Methods
Citation
  Standard Methods Online - Standard Methods for the Examination of Water and Wastewater
Brief Method Summary
Hydrogen ions present in a sample as a result of dissociation or hydrolysis of solutes react with additions of standard alkali. Acidity thus depends on the end-point pH or indicator used. The construction of a titration curve by recording sample pH after successive small measured additions of titrant permits identification of inflection points and buffering capacity, if any, and allows the acidity to be determined with respect to any pH of interest.
Scope and Application
Applicable to wastewater, surface water, and drinking water.
Applicable Concentration Range
Interferences
Dissolved gases contributing to acidity or alkalinity, such as CO2, hydrogen sulfide, or ammonia, may be lost or gained during sampling, storage, or titration. Minimize such effects by titrating to the end point promptly after opening sample container, avoiding vigorous shaking or mixing, protecting sample from the atmosphere during titration, and letting sample become no warmer than it was at collection. In the potentiometric titration, oily matter, suspended solids, precipitates, or other waste matter may coat the glass electrode and cause a sluggish response. Do not remove interferences from sample because they may contribute to its acidity. In samples containing oxidizable or hydrolyzable ions such as ferrous or ferric iron, aluminum, and manganese, the reaction rates at room temperature may be slow enough to cause drifting end points. Do not use indicator titrations with colored or turbid samples that may obscure the color change at the end point. Residual free available chlorine in the sample may bleach the indicator. Eliminate this source of interference by adding 1 drop of 0.1M sodium thiosulfate.
Quality Control Requirements
See Section 2020 Quality Assurance/Quality Control.
Sample Handling
Collect samples in polyethylene or borosilicate glass bottles and store at a low temperature. Fill bottles completely and cap tightly. Because waste samples may be subject to microbial action and to loss or gain of CO2 or other gases when exposed to air, analyze samples without delay, preferably within 1 d. If biological activity is suspected analyze within 6 h. Avoid sample agitation and prolonged exposure to air.
Maximum Holding Time
14 days (regulatory)
Relative Cost
$51 to $200
Sample Preparation Methods