Abstract:Nitrobenzene (NB) pollution of the Songhua River caused by an explosion at a petrochemical plant in Jilin City, Jilin Province, China, attracted public concern over the fate of NB in the river. As one of the efforts to predict the fate of residual NB in the river, the kinetics and mechanism of phototransformation of NB in natural water from four sections of the Songhua River were investigated. It was found that photodegradation of NB in water proceeded via pseudo-first-order reaction kinetics under simulated s… Show more
“…Analysis by GC/MS showed the presence of phenol, nitrophenols, dinitrophenol, and one of the isomers of azobenzene in the final solution. The results are in accordance with the results of previous researchers (Wang et al 2008;Kochany 1992;Miguel et al 2000). Fendler and Gasowski (1968) suggested that the enhanced conjugation of the nitro group with benzene ring might be responsible for the selective activation of the ortho and para positions of nitrobenzene (NB).…”
The paper presents the kinetics and proposed pathways photodegradation and photooxidation of p-arsanilic acid, in a neutral environment by ozone and hydrogen peroxide. The results showed that in a neutral environment, photoozonation process was characterized by the highest decomposition rate constant (k) (k = 31.8 × 10(-3) min(-1)). The rate constants decreased in the order UV/O3 > O3 > UV/H2O2 > H2O2 > UV. It was also found that under pH = 7, decomposition of p-arsanilic acid leads mainly to the formation of aniline, which undergoes secondary reactions. Intermediate products of oxidation and photooxidation by hydrogen peroxide like nitrobenzene, nitrophenol, azobenzenes, and phenylazophenol were identified depending on processes. However, in the photodegradation process, formation of nitrasone as a reaction product of p-arsanilic acid with oxygen in the singlet state was observed. In the case of ozonation and photoozonation, in addition, aniline formation of carboxylic acids was observed.
“…Analysis by GC/MS showed the presence of phenol, nitrophenols, dinitrophenol, and one of the isomers of azobenzene in the final solution. The results are in accordance with the results of previous researchers (Wang et al 2008;Kochany 1992;Miguel et al 2000). Fendler and Gasowski (1968) suggested that the enhanced conjugation of the nitro group with benzene ring might be responsible for the selective activation of the ortho and para positions of nitrobenzene (NB).…”
The paper presents the kinetics and proposed pathways photodegradation and photooxidation of p-arsanilic acid, in a neutral environment by ozone and hydrogen peroxide. The results showed that in a neutral environment, photoozonation process was characterized by the highest decomposition rate constant (k) (k = 31.8 × 10(-3) min(-1)). The rate constants decreased in the order UV/O3 > O3 > UV/H2O2 > H2O2 > UV. It was also found that under pH = 7, decomposition of p-arsanilic acid leads mainly to the formation of aniline, which undergoes secondary reactions. Intermediate products of oxidation and photooxidation by hydrogen peroxide like nitrobenzene, nitrophenol, azobenzenes, and phenylazophenol were identified depending on processes. However, in the photodegradation process, formation of nitrasone as a reaction product of p-arsanilic acid with oxygen in the singlet state was observed. In the case of ozonation and photoozonation, in addition, aniline formation of carboxylic acids was observed.
“…The JUA covers 1267.89 km 2 and is located between 4840,000 and 4905,000 north and 260,000 and 320,000 east in the central of Jilin Province, China ( Figure 1). JUA has a population of 1.60 million and is an important irrigation and industrial district of China.…”
Section: Study Areamentioning
confidence: 99%
“…The area of JUA is 1267.89 km 2 and it is assumed to be a rectangular shape. The grid cells were designated as "inactive" outside the model domain and as "active" inside the model domain.…”
Abstract:In order to evaluate the groundwater resources and aquifer system of the Jilin urban area (JUA), a groundwater numerical flow model was established by using the groundwater modeling system based on data from 190 boreholes. River stages were interpolated to control the groundwater flow field. The input parameters such as hydraulic conductivity and specific yield were based on data from 260 pumping test data. The model was calibrated by trial and error, simulated results were compared to the observed head and contour maps, which were generally in good agreement, and the root mean squared error was 0.66 m. Sensitivity analysis was carried out and recharge proved to be the most sensitive factor in this model. The water budget showed that the input was 2.07× 10
“…Thus, volatilization should be one of the main processes responsible for the loss of NB from river water. On the other hand, photolysis could also be responsible for the loss of NB (Wang et al, 2008).…”
Section: Contribution Of Biodegradation To the Loss Of Nb Flux Duringmentioning
confidence: 99%
“…For controlling the losses and impact of the accident at a level as low as possible, the government started a wide range of investigations to understand the behavior and fate of residual NB in the river. Evaluation of NB degradation abilities of microbes at different river sections was one of the main tasks of the investigation Wang et al, 2008).…”
More than 100 t of nitrobenzene (NB) and related compounds were discharged into the Songhua River, the fourth longest river in China, because of the world-shaking explosion of an aniline production factory located in Jilin City on November 13, 2005. As one of the efforts to predict the fate of residual NB in the river, NB biodegradation abilities by microbes in the water and sediments from different river sections were evaluated systematically. The results indicated that microbial communities from any section of the river, including one section at the upper stream of the NB discharging point, had the ability to biodegrade NB under aerobic (for river water samples) conditions at 22±1°C or anaerobic (for sediment samples) conditions at 10±1°C. NB degradation rates of microbial communities in the downstream sites were markedly higher than those in the upstream site, indicating that NB degradation abilities were enhanced because of the pollution of NB. Aerobic degradation got neglected at a temperature of 10°C or lower. The production of nitrosobenzene and aniline during aerobic biodegradation suggested the existence of at least two different NB degradation pathways, and the occurrence of the catechol-2,3-dioxygenase (C23O) gene and the significant decrease of dissolved organic carbon (DOC) indicated that NB could be mineralized under aerobic conditions. Although it was a fact that the river have frozen-up during the NB accident, it was speculated that biodegradation was not the major process responsible for the decrease of NB flux in the river.
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