EPA Method 900
EPA Method 900 does not directly match ALS - Columbia's list of currently available methods. Please call for availability.
Method information displayed is provided for informational purposes only. No warranty (express or implied) is made as to the website accuracy, completeness, or applicability (such as the age of a method and whether or not it applies to your project). Please contact us for assistance.
View Actual EPA Method 900 (PDF File)
EPA Method 900:
Gross Alpha and Beta Activity in Water. Official Name: Gross Alpha and Gross Beta Radioactivity in Drinking Water
An aliquot of a preserved drinking water sample is evaporated to a small volume and transferred quantitatively to a tared 2-inch stainless steel counting planchet. The sample residue is dried to constant weight, reweighed to determine dry residue weight, then counted for alpha and/or beta radioactivity. Counting efficiencies for both alpha and beta particle activities are selected according to the amount of sample solids from counting efficiency vs sample solids standard curves.
This method is a screening technique that covers the measurement of gross alpha and gross beta particle activities in drinking water. This method covers the measurement of gross alpha and gross beta particle activities in drinking water. The method is a screening technique for monitoring drinking water supplies for alpha and beta particle activities according to the limits set forth under the Safe Drinking Water Act, PL 93-523, 40 FR 34324, and thereby determining the necessity for further analysis.The method is applicable to the measurement of alpha emitters having energies above 3.9 megaelectronvolts (MeV) and beta emitters having maximum energies above 0.1 MeV. For drinking waters with an extremely high solids content (>500 ppm), method 900.1 is recommended.
Prescribed Procedures for Measurement of Radioactivity in Drinking Water (EPA/600/4-80-032), August, 1980.
(1) Moisture absorbed by the sample residue. (2) Non-uniformity of sample residue in counting planchet. (3) Sample density on planchet area should not be more than 5 mg/cm2 for gross alpha and 10 mg/cm2 for gross beta. (4) Discrimination against beta/alpha activity by gas flow proportional counting.
Alpha: 1 pCi/L - * Beta: 4 pCi/L - * (* Method does not specify an upper detection limit.)
MDLs are the limits that are required for compliance with drinking water regulations (for which this method was designed).
<-- Search All Test Methods
Suggestions? The test methods page continues to expand and improve. If you have suggestions for improvement, we would enjoy hearing from you. Please contact the webmaster here.