Simple and reliable procedures have been developed for analyses of N03-, total N, and organic N in freshwaters. NO,is determined by second-derivative UV spectroscopy. Total N and organic N are determined based on secondderivative analyses of NO,following persulfate digestion. Resolution of organic N determinations was increased by using ion-exchange resins to remove NO,from samples with high concentrations of N03prior to persulfate oxidation of the organic N. Although numerous methods have been developed for the determination of N in aqueous samples, there is continued need for simple and reliable procedures for both inorganic and organic N analyses. The most widely accepted methods for N03analysis include Cd reduction and ion chromatography (Am. Public Health Assoc. 1989). Both methods have been adapted for automated analysis and, with proper consideration of potential interferences, both are accurate and precise. Ion chromatography has the advantage of also measuring several additional anions in a single aliquot of samAcknowledgments This work was supported in part by the Iowa State Water Resour. Res. Inst., the Iowa DNR, the U.S. EPA, and Wetlands Res. Inc., Chicago, Illinois. We thank Iowa State University staff and researchers for their contributions to this research. Automated Cd reduction analyses were performed by the Analytical Services Laboratory (Iowa State Univ. Eng. Res. Inst.) and by the U.S. EPA ERL, Duluth, Minnesota. ple. Ion chromatography and Cd reduction, however, are relatively complicated and expensive. Samples must normally be filtered to remove suspended matter before analysis, and in the case of Cd reduction, sample color, metal ions, and phosphate are potential interferences (Olson 1980). The principal methods for organic N determination are based on conversion of organic N to NH,+ or N03and subsequent analysis of these inorganic forms. Separate analysis of ambient inorganic N allows organic N levels to be calculated by difference. For freshwater samples, conversion of organic N to inorganic forms is most commonly based on either Kjeldahl digestion (U.S. EPA 1979; Am. Public Health Assoc. 1989), photo-oxidation (Armstrong et al. 1966), or persulfate digestion (Koroleff 1976; D’Elia et al. 1977; Solorzano and Sharp 1980). Photo-oxidation requires more specialized equipment and may be ineffective for some compounds (Henriksen 1970). Kjeldahl digestion is a complicated and expensive procedure and may be unsuitable for systems receiving high inorganic N loads. High concentrations of N03severely interfere with standard Kjeldahl N determinations (Schlueter 1977; U.S. EPA 1979; Am. Public Health Assoc. 1989). N03--N concentrations 10-20 times greater than those of organic N result in >90% inhibition of Kjeldahl N determinations (Schlue-
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