1984
DOI: 10.1021/ac00277a079
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An integrated method for determining nitrogen oxide (NOx) emissions at nitric acid plants

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Cited by 8 publications
(15 citation statements)
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References 13 publications
(3 reference statements)
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“…The NH 4 + oxidation rate in solution is a linear function of the NH 4 + concentration [Margeson et al, 1984] and independent of the NO 3 À solution concentrations for collection conditions in this study where solution pH did not change significantly following collections. Based on the 2.8% increase in NO 3 À observed due to NH 3 oxidation interference at 200 ppmv NH 3 after 7 days [Margeson et al, 1984], our 200 ppbv NH 3 concentration should result in a negligible 0.0028% interference. Our experiments demonstrate negligible interference in that blank solutions with added NH 4 + reduced 1 week after solution preparation had consistent NO 3 À concentrations (within 0.2 μM) and δ 15 N-NO x (within 0.9‰) relative to those reduced 1 day after solution preparation.…”
Section: No X Collection and Isotopic Analysismentioning
confidence: 60%
See 1 more Smart Citation
“…The NH 4 + oxidation rate in solution is a linear function of the NH 4 + concentration [Margeson et al, 1984] and independent of the NO 3 À solution concentrations for collection conditions in this study where solution pH did not change significantly following collections. Based on the 2.8% increase in NO 3 À observed due to NH 3 oxidation interference at 200 ppmv NH 3 after 7 days [Margeson et al, 1984], our 200 ppbv NH 3 concentration should result in a negligible 0.0028% interference. Our experiments demonstrate negligible interference in that blank solutions with added NH 4 + reduced 1 week after solution preparation had consistent NO 3 À concentrations (within 0.2 μM) and δ 15 N-NO x (within 0.9‰) relative to those reduced 1 day after solution preparation.…”
Section: No X Collection and Isotopic Analysismentioning
confidence: 60%
“…To evaluate the potential for ammonia (NH 3 ) interference via solution collection and oxidation to NO 3 − over time [ Margeson et al ., ], we added NH 4 + to simulate solution collection of vehicle NH 3 emissions at maximum expected on‐road concentrations (~200 ppbv NH 3 ) [ Sun et al ., ]. The NH 4 + oxidation rate in solution is a linear function of the NH 4 + concentration [ Margeson et al ., ] and independent of the NO 3 − solution concentrations for collection conditions in this study where solution pH did not change significantly following collections. Based on the 2.8% increase in NO 3 − observed due to NH 3 oxidation interference at 200 ppmv NH 3 after 7 days [ Margeson et al ., ], our 200 ppbv NH 3 concentration should result in a negligible 0.0028% interference.…”
Section: Methodsmentioning
confidence: 99%
“…2. Make sampling solutions using 1 M potassium permanganate (KMnO 4 ) stock solution and 10 M sodium hydroxide (NaOH) 10 , and then dilute the solution with ultrapure water to the correct volume. NOTE: Purchase premade solutions because they tend to contain lower "blank" NO 3 -concentrations than other forms.…”
Section: Solution Preparationmentioning
confidence: 99%
“…Most other plants tested use selective catalytic reduction (SCR) or selective noncatalytic reduction (SNCR), both of which use an injection of ammonia into the stream to reduce NO x emissions (i.e., 4NO + 4 NH 3 + O 2 → 4N 2 + 6H 2 O). Ammonia is known to interfere with certain NO x collection methods, 16 and the H 2 SO 4 and H 2 O 2 collection utilized by Felix et al 10 in the rest of the power plants is very similar to the Environmental Protection Agency method for ammonia collection (EPA Conditional Test Method 027). Therefore, it is unknown if the difference in δ 15 N-NO x measured in the SCR/SNCR (13.6‰ to 25.6‰) and nonammonia NO x reduction (9.0‰ to 12.6‰) power plants (Figure 1) is driven by fractionation in the NO x removal step or by possible ammonia interference in the measurements.…”
mentioning
confidence: 99%