1998
DOI: 10.1021/ie9704253
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Nitroaromatic Hydrocarbon Ozonation in Water. 1. Single Ozonation

Abstract: Single ozonation of two nitroaromatic hydrocarbons (nitrobenzene and 2,6-dinitrotoluene) under different experimental conditions (ozone feed rate, pH, temperature, hydroxyl radical scavengers) has been studied. The absence of hydroxyl radical scavengers, pHs 7−9, and temperatures below 30 °C are optimum conditions for nitroaromatic removal. Due to the importance of hydroxyl radical reactions, removal rates in natural water are much lower than those observed in laboratory ultrapure water. Rate constants of the … Show more

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Cited by 89 publications
(74 citation statements)
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“…In this treatment combination, the supplied UV energy interacts with O 3 as described in the following reaction (Beltrán et al 1998;Esplugas et al 2002;Guittonneau et al 1990):…”
Section: Ozone/uvmentioning
confidence: 99%
“…In this treatment combination, the supplied UV energy interacts with O 3 as described in the following reaction (Beltrán et al 1998;Esplugas et al 2002;Guittonneau et al 1990):…”
Section: Ozone/uvmentioning
confidence: 99%
“…6). It is well known that the oxidizing ability of ozone comes from molecular either Ozone or hydroxyl free radicals (Beltran et al, 1998). Eq.…”
Section: Rate Constants For the Degradation Of 4c2np At Different Phsmentioning
confidence: 99%
“…Nitroaromatic compounds are used in many industrial processes, including the preparation of pesticides, explosives, textiles and paper. Therefore, these compounds are often detected as water pollutants as a result of their release in industrial effluents (Beltran et al, 1998;Sarasa et al, 1998). If these effluents are discharged into water without proper treatment, they are hazardous to humans and the environment (Song et al, 2007).…”
Section: Introductionmentioning
confidence: 99%
“…There were still residual 2-ClNB and 4-ClNB in the solution, at concentrations of 2.37 and 0.45 mg/L, respectively, even after 120 min of reaction time. The removal rates of major pollutants were in the order of 2-ClA>4-NP>>4-ClNB>2-ClNB, with respective reaction rate constants of 20.22 mg/(L·min), 3.73 mg/(L·min), 0.0287 min −1 , and 0.0215 min −1 , which can be understood by the different reaction mechanisms; that is, the majority of 4-ClNB and 2-ClNB removal is due to hydroxyl radical oxidation whereas 4-NP and 2-ClA are very reactive towards both ozone and hydroxyl radicals (Beltrán et al, 1998;Li et al, 2009). Interestingly, it can also be seen in Fig.…”
Section: Catalytic Ozonation Of Industrial Wastewater Containing Cnacsmentioning
confidence: 99%