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<oai_dc:dc xmlns:dc="http://purl.org/dc/elements/1.1/" xmlns:oai_dc="http://www.openarchives.org/OAI/2.0/oai_dc/" xmlns:xsi="http://www.w3.org/2001/XMLSchema-instance" xsi:schemaLocation="http://www.openarchives.org/OAI/2.0/oai_dc/ http://www.openarchives.org/OAI/2.0/oai_dc.xsd">
  <dc:contributor>D. Kirk Nordstrom</dc:contributor>
  <dc:contributor>James W. Ball</dc:contributor>
  <dc:creator>R. Blaine McCleskey</dc:creator>
  <dc:date>2003</dc:date>
  <dc:description>Hydride generation atomic absorption&#13;
spectrometry (HGAAS) is a sensitive and&#13;
selective method for the determination of total&#13;
arsenic (arsenic(III) plus arsenic(V)) and&#13;
arsenic(III); however, it is subject to metal&#13;
interferences for acid mine waters. Sodium&#13;
borohydride is used to produce arsine gas, but&#13;
high metal concentrations can suppress arsine&#13;
production.&#13;
&#13;
This report investigates interferences of&#13;
sixteen metal species including aluminum,&#13;
antimony(III), antimony(V), cadmium,&#13;
chromium(III), chromium(IV), cobalt,&#13;
copper(II), iron(III), iron(II), lead,&#13;
manganese, nickel, selenium(IV),&#13;
selenium(VI), and zinc ranging in&#13;
concentration from 0 to 1,000 milligrams per&#13;
liter and offers a method for removing&#13;
interfering metal cations with cation exchange&#13;
resin. The degree of interference for each&#13;
metal without cation-exchange on the&#13;
determination of total arsenic and arsenic(III)&#13;
was evaluated by spiking synthetic samples&#13;
containing arsenic(III) and arsenic(V) with&#13;
the potential interfering metal. Total arsenic&#13;
recoveries ranged from 92 to 102 percent for&#13;
all metals tested except antimony(III) and&#13;
antimony(V) which suppressed arsine&#13;
formation when the antimony(III)/total&#13;
arsenic molar ratio exceeded 4 or the&#13;
antimony(V)/total arsenic molar ratio&#13;
exceeded 2. Arsenic(III) recoveries for&#13;
samples spiked with aluminum,&#13;
chromium(III), cobalt, iron(II), lead,&#13;
manganese, nickel, selenium(VI), and zinc ranged from 84 to 107 percent over the entire&#13;
concentration range tested. Low arsenic(III)&#13;
recoveries occurred when the molar ratios of&#13;
metals to arsenic(III) were copper greater than&#13;
120, iron(III) greater than 70, chromium(VI)&#13;
greater than 2, cadmium greater than 800,&#13;
antimony(III) greater than 3, antimony(V)&#13;
greater than 12, or selenium(IV) greater than&#13;
1. Low recoveries result when interfering&#13;
metals compete for available sodium&#13;
borohydride, causing incomplete arsine&#13;
production, or when the interfering metal&#13;
oxidizes arsenic(III).&#13;
Separation of interfering metal cations&#13;
using cation-exchange prior to hydridegeneration&#13;
permits accurate arsenic(III)&#13;
determinations in acid mine waters containing&#13;
high concentrations of interfering metals.&#13;
Stabilization of the arsenic redox species for&#13;
as many as 15 months is demonstrated for&#13;
samples that have been properly filtered and&#13;
acidified with HCl in the field. The detection&#13;
limits for the method described in this report&#13;
are 0.1 micrograms per liter for total arsenic&#13;
and 0.8 micrograms per liter for arsenic(III).</dc:description>
  <dc:format>application/pdf</dc:format>
  <dc:identifier>10.3133/wri034117</dc:identifier>
  <dc:language>en</dc:language>
  <dc:publisher>U.S. Geological Survey</dc:publisher>
  <dc:title>Metal interferences and their removal prior to the determination of As(T) and As(III) in acid mine waters by hydride generation atomic absorption spectrometry</dc:title>
  <dc:type>reports</dc:type>
</oai_dc:dc>