9045D - 1 Revision 4 November 2004 METHOD 9045D SOIL AND WASTE pH

1.0 SCOPE AND APPLICATION 1.1 This method is an electrometric procedure for measuring pH in soils and waste samples. Wastes may be solids, sludges, or non-aqueous liquids. If water is present, it must constitute less than 20% of the total volume of the sample.

2.0 SUMMARY OF METHOD 2.1 The sample is mixed with reagent water, and the pH of the resulting aqueous solution is measured.

3.0 INTERFERENCES 3.1 Samples with very low or very high pH may give incorrect readings on the meter. For samples with a true pH of >10, the measured pH may be incorrectly low. This error can be minimized by using a low-sodium-error electrode. Strong acid solutions, with a true pH of <1, may give incorrectly high pH measurements. 3.2 Temperature fluctuations will cause measurement errors. 3.3 Errors will occur when the electrodes become coated. If an electrode becomes coated with an oily material that will not rinse free, the electrode can (1) be cleaned with an ultrasonic bath, or (2) be washed with detergent, rinsed several times with water, placed in 1:10 HCl so that the lower third of the electrode is submerged, and then thoroughly rinsed with water, or (3) be cleaned per the manufacturer's instructions.

4.0 APPARATUS AND MATERIALS 4.1 pH meter with means for temperature compensation. 4.2 Glass electrode. 4.3 Reference electrode -- A silver-silver chloride or other reference electrode of constant potential may be used. NOTE : Combination electrodes incorporating both measuring and referenced functions are convenient to use and are available with solid, gel-type filling materials that require minimal maintenance. 4.4 Beaker -- 50-mL. 4.5 Thermometer and/or temperature sensor for automatic compensation. 4.6 Analytical balance -- capable of weighing 0.1 g.9045D - 2 Revision 4 November 2004 5.0 REAGENTS 5.1 Reagent grade chemicals shall be used in all tests. Unless otherwise indicated, it is intended that all reagents shall conform to the specifications of the Committee on Analytical Reagents of the American Chemical Society, w here such specifications are available. Other grades may be used, provided it is first ascertained that the reagent is of sufficiently high purity to permit its use without lessening the accuracy of the determination. 5.2 Reagent water. All references to water in this method refer to reagent water, as defined in Chapter One. 5.3 Primary standard buffer salts are available from the National Institute of Standards and Technology (NIST) and should be used in situations where extreme accuracy is necessary. Preparation of reference solutions from these salts requires some special precautions and handling, such as low-conductivity dilution wate r, drying ovens, and carbon-dioxide-free purge gas. These solutions should be replaced at least once each month. 5.4 Secondary standard buffers may be prepared from NIST salts or purchased as solutions from commercial vendors. These commercially available solutions, which have been validated by comparison with NIST standards, are recommended for routine use.

6.0 SAMPLE PRESERVATION AND HANDLING Samples should be analyzed as soon as possible.

7.0 PROCEDURE 7.1 Calibration 7.1.1 Because of the wide variety of pH meters and accessories, detailed operating procedures cannot be incorporated into this method. Each analyst must be acquainted with the operation of each system and familiar with all instrument functions. Special attention to care of the electrodes is recommended. 7.1.2 Each instrument/electrode system must be calibrated at a minimum of two points that bracket the expected pH ofthe samples and are approximately three pH units or more apart. Repeat adjustments on successive portions of the two buffer solutions until readings are within 0.05 pH units of the buffer solution value. If an accurate pH reading based on the conventional pH scale [0 to 14 at 25 EC] is required, the analyst should control sample temperature at 25 ± 1 EC when sample pH approaches the alkaline end of the scale (e.g., a pH of 11 or above). 7.2 Sample preparation and pH measurement of soils: 7.2.1 To 20 g of soil in a 50-mL beaker, add 20 mL of reagent water, cover, and continuously stir the suspension for 5 min. Additional dilutions are allowed if working with hygroscopic soils and salts or other problematic matrices. 7.2.2 Let the soil suspension stand for about 1 hr to allow most of the suspended clay to settle out from the suspension or filter or centrifuge off the aqueous phase for pH measurement.9045D - 3 Revision 4 November 2004 7.2.3 Adjust the electrodes in the clamps of the electrode holder so that, upon lowering the electrodes into the beaker, the glass electrode will be immersed just deep enough into the clear supernatant solution to establish a good electrical contact through the ground-glass joint or the fiber-capillary hole. Insert the electrodes into the sample solution in this manner. For combination electrodes, immerse just below the suspension. 7.2.4 If the sample temperature differs by more than 2 E C from the buffer solution, the measured pH values must be corrected. 7.2.5 Report the results as "soil pH measured in water at EC" where " EC" is the temperature at which the test was conducted. 7.3 Sample preparation and pH measurement of waste materials 7.3.1 To 20 g of waste sample in a 50-mL beaker, add 20 mL of reagent water, cover, and continuously stir the suspension for 5 min. Additional dilutions are allowed if working with hygroscopic wastes and salts or other problematic matrices. 7.3.2 Let the waste suspension stand for about 15 min to allow most of the suspended waste to settle out from the suspension or filter or centrifuge off aqueous phase for pH measurement. NOTE : If the waste is hygroscopic and absorbs all the reagent water, begin the experiment again using 20 g of waste and 40 mL of reagent water. NOTE : If the supernatant is multiphasic, decant the oily phase and measure the pH of the aqueous phase. The electrode may need to be cleaned (Step 3.3) if it becomes coated with an oily material. 7.3.3 Adjust the electrodes in the clamps of the electrode holder so that, upon lowering the electrodes into the beaker, the glass electrode will be immersed just deepenough into the clear supernatant to establish good electrical contact through the groundglass joint or the fiber-capillary hole. Insert the electrode into the sample solution in this manner. For combination electrodes, immerse just below the suspension. 7.3.4 If the sample temperature differs by more than 2 E C from the buffer solution, the measured pH values must be corrected. 7.3.5 Report the results as "waste pH measured in water at EC" where " EC" is the temperature at which the test was conducted.

8.0 QUALITY CONTROL 8.1 Refer to Chapter One for the appropriate QC protocols. 8.2 Electrodes must be thoroughly rinsed between samples.

9.0 METHOD PERFORMANCE 9.1 No data provided.9045D - 4 Revision 4 November 2004 10.0 REFERENCES 1. Black, Charles Allen; Methods of Soil Analysis ; American Society of Agronomy: Madison, WI, 1973. 2. National Bureau of Standards, Standard Reference Material Catalog, 1986-87, Special Publication 260.9045D - 5 Revision 4 November 2004 METHOD 9045D SOIL AND WASTE pH