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1.
UV/TiO 2/H 2O 2, UV/TiO 2 and UV/H 2O 2 were compared as pre-treatment processes for the detoxification of mixtures of 4-chlorophenol (4CP), 2,4-dichlorophenol (DCP), 2,4,6-trichlorophenol (TCP) and pentachlorophenol (PCP) prior to their biological treatment. When each chlorophenol was initially supplied at 50 mg l −1, UV/TiO 2/H 2O 2 treatment supported the highest pollutant removal, COD removal, and dechlorination efficiencies followed by UV/TiO 2 and UV/H 2O 2. The remaining toxicity to Lipedium sativum was similar after all pre-treatments. Chlorophenol photodegradation was always well described by a first order model kinetic ( r2 > 0.94) and the shortest 4CP, DCP, TCP and PCP half-lives of 8.7, 7.1, 4.5 and 3.3 h, respectively, were achieved during UV/TiO 2/H 2O 2 treatment. No pollutant removal was observed in the controls conducted with H 2O 2 or TiO 2 only. Inoculation of all the photochemically pre-treated mixtures with activated sludge microflora was followed by complete removal of the remaining pollutants. Combined UV/TiO 2/H 2O 2-biological supported the highest detoxification, dechlorination (99%) and COD removal (88%) efficiencies. Similar results were achieved when each chlorophenol was supplied at 100 mg l −1. COD and Cl mass balances indicated UV, UV/H 2O 2, and UV/TiO 2 treatments lead to the formation of recalcitrant photoproducts, some of which were chlorinated. 相似文献
2.
The degradation of a common textile dye, Reactive-brilliant red X-3B, by several advanced oxidation technologies was studied in an air-saturated aqueous solution. The dye was resistant to the UV illumination (wavelength λ 320 nm), but was decolorized when one of Fe 3+, H 2O 2 and TiO 2 components was present. The decolorization rate was observed to be quite different for each system, and the relative order evaluated under comparable conditions followed the order of Fe 2+–H 2O 2–UV Fe 2+–H 2O 2 > Fe 3+–H 2O 2–UV > Fe 3+–H 2O 2 > Fe 3+–TiO 2–UV > TiO 2–UV > Fe 3+–UV > TiO 2–visible light ( λ 450 nm) > H 2O 2–UV > Fe 2+–UV. The mechanism for each process is discussed, and linked together for understanding the observed differences in reactivity. 相似文献
3.
Aqueous 4-nitrophenol solutions containing TiO 2 or Al 2O 3 nanoparticles were irradiated with electron beam. 4-nitrophenol was decomposed by the ionizing radiation process in the absence of the nanoparticles. The addition of TiO 2 or Al 2O 3 (2 g l −1) before irradiation improved the removal of 4-nitrophenol, total organic carbon (TOC) but also nitrogen (TN). To identify the origin of the loss (catalysis or simply adsorption), TiO 2 or Al 2O 3 nanoparticles were added after irradiation. Experiments show that the effect of the presence of TiO 2 or Al 2O 3 during irradiation is just due to adsorption. 相似文献
4.
In this study, the rates of degradation of organic compounds by several AOPs (H 2O 2/UV, Fe(III)/UV, Fe(III)/H 2O 2/UV, Fe(II)/H 2O 2 and Fe(III)/H 2O 2) have been compared. Experiments were carried out at pH ≈ 3 (perchloric acid / sodium perchlorate solutions) and with UV reactors equipped with a low-pressure mercury vapour lamp (emission at 253.7 run). The data obtained with atrazine ([Atrazine] o = 100 μg/L) showed that the rate of degradation of atrazine in very dilute aqueous solution is much more rapid with Fe(III)/UV than with H 2O 2/UV. Photo-Fenton process (Fe(III)/H 2O 2/UV) was found to be more efficient than H 2O 2/UV and Fe(II)/H 2O 2 for the mineralization of acetone ([Acetone] o = 1 mM). 相似文献
5.
A novel paper-based material containing titanium dioxide (TiO 2) photocatalyst was successfully prepared by a papermaking technique with the internal addition of inorganic fibers on which TiO 2 particles were supported. Photodegradation performance of acetaldehyde gas, an indoor pollutant, and the durability of the TiO 2-containing papers were investigated under UV irradiation. Ceramic fiber suspension and polydiallyldimethylammonium chloride as a cationic flocculant were mixed, followed by the addition of TiO 2 suspension and anionic polyacrylamide. Subsequently, the inorganic mixture was poured into a pulp suspension, and TiO 2 handsheets then prepared by a papermaking method. The tensile strength of TiO 2-containing paper without a ceramic carrier decreased by more than 30% after 240-h UV irradiation (2 mW/cm 2), although the strength of the TiO 2 sheet with ceramic fibers remained reasonably stable. The efficiency of acetaldehyde decomposition by the TiO 2 paper containing an inorganic carrier was nearly equal to that of the carrier-free TiO 2 paper. Scanning electron microscopic observation suggested that most TiO 2 particles were predominantly supported on the inorganic fiber matrix, and were mostly out of contact with organic pulp fibers. The TiO 2 paper with an inorganic carrier demonstrated both excellent photocatalytic performance and durability, which before had been mutually incompatible for organic materials containing TiO 2 photocatalyst. The two-stage mixing procedure for TiO 2 sheet-making is promising for the simple manufacture of high performance paper with photocatalytic ability. 相似文献
6.
Lanthanum-doped anatase TiO 2 thin films on glass prepared via a sol–gel process have been shown to have much higher photocatalytic activity for the degradation of gaseous benzene than pure anatase TiO 2 thin film. The photodecomposition of benzene on both types of TiO 2 films follows the first-order kinetics while the CO 2 and CO formation followed the zero-order kinetics. GC/MS identification of the intermediates produced during the photodegradation of benzene revealed that doping lanthanum into TiO 2 thin film favors a cleavage of benzene ring. An optimal lanthanum amount with respect to photocatalytic activity was about 2.5 wt% (La 2O 3/TiO 2). 相似文献
7.
Fourteen sediment samples with different content of Fe 2O 3 were collected from the lower reaches of the Liao River in China. The photodegradation of lindane on the surfaces of these sediments was investigated to observe the effects of Fe 2O 3 and other photoinducable substances, such as TiO 2 and organic substances, on photodegradation of lindane. A partial least-squares (PLS) analysis model was developed to find out the statistical relationship between the photodegradation and the contents of these photoinducable substances. It was concluded from the PLS analysis that inorganic carbon and organic carbon have negative effects, whereas Fe 2O 3 and TiO 2 accelerate the photodegradation of lindane in the sediment samples when 365 nm UV light was used as light source. In all cases of the experiments, the photodegradation of lindane in the sediment samples were fitted for pseudo-first-order kinetics. 相似文献
8.
TiO 2 powder-containing paper composites, called TiO 2 paper, were prepared by a papermaking technique, and their photocatalytic efficiency was investigated. The TiO 2 paper has a porous structure originating from the layered pulp fiber network, with TiO 2 powders scattered on the fiber matrix. Under UV irradiation, the TiO 2 paper decomposed gaseous acetaldehyde more effectively than powdery TiO 2 and a pulp/TiO 2 mixture not in paper form. Scanning electron microscopy and mercury intrusion analysis revealed that the TiO 2 paper had characteristic unique voids ca. 10 μm in diameter, which might have contributed to the improved photocatalytic performance. TiO 2 paper composites having different void structures were prepared by using beaten pulp fibers with different degrees of freeness and/or ceramic fibers. The photodecomposition efficiency was affected by the void structure of the photocatalyst paper, and the initial degradation rate of acetaldehyde increased with an increase in the total pore volume of TiO 2 paper. The paper voids presumably provided suitable conditions for TiO 2 catalysis, resulting in higher photocatalytic performance by TiO 2 paper than by TiO 2 powder and a pulp/TiO 2 mixture not in paper form. 相似文献
9.
Natural humic water was treated with ultraviolet (UV) light and UV + hydrogen peroxide (UV/H 2O 2. The effects on the dissolved organic carbon content (DOC), the UV-absorbance at 254 nm (UV-abs.), the molecular size distribution, pH, and mutagenic activity were monitored, and the identity and concentrations of the most abundant gas chromatographable organic degradation products were determined. The DOC content and the UV-abs. of the water decreased substantially during treatment with UV/H2O2. The decreases were dependent on the time of irradiation (UV dose) as well as on the H2O2 dose applied. The humus macromolecules were degraded to smaller fragments during irradiation. At higher UV doses, however, part of the dissolved organic matter (DOM) was found to precipitate, probably as a result of polymerization. Oxalic acid, acetic acid, malonic acid, and n-butanoic acid were the most abundant degradation products detected. These acids were found to account for up to 20% and 80% of the DOM in UV- and UV/H2O2-treated waters, respectively. No mutagenic activity was generated by the UV irradiation or the UV/H2O2 treatment. It is further concluded that the substantial mutagenic activity formed during chlorination of humic waters cannot be decreased by using UV irradiation as a pretreatment step. 相似文献
10.
UV/Fenton, near-UV-visible/Fenton, dark Fenton, and H 2O 2/UV reactions have been used to treat simulated dyehouse effluents representing wastewater from the textile dyeing and rinsing process. Experiments were carried out in a lab - scale photochemical reactor using concentrations of 0.5–25 mM H 2O 2, 0.04-0.5 mM Fe 2+-ion and different dilutions of textile wastewater. To assess the extent of mineralization, decolourization kinetics and the effect of different fight sources on treatment efficiency, DOC, optical density at 254 nm and 600 nm wavelength and residual H 2O 2 concentrations were measured during the course of the advanced oxidation reactions. Comparative evaluation of the obtained results revealed that the decolourization rate increased with applied H 2O 2 and Fe 2+-ion dose as well as the strength of the synthetic textile wastewater. The best results were obtained by the near - UV/visible/Fenton process with a decolourization rate constant of 1.57 min −1, a UV 254nm reduction of 97% and a DOC removal of 41% at relatively low doses of the H 2O 2 oxidant and Fe 2+-ion catalyst within 60 min treatment time. 相似文献
11.
Biotreatment of various ratios of H 2S and NH 3 gas mixtures was studied using the biofilters, packed with co-immobilized cells ( Arthrobacter oxydans CH8 for NH 3 and Pseudomonas putida CH11 for H 2S). Extensive tests to determine removal characteristics, removal efficiency, removal kinetics, and pressure drops of the biofilters were performed. To estimate the largest allowable inlet concentration, a prediction model was also employed. Greater than 95% and 90% removal efficiencies were observed for NH 3 and H 2S, respectively, irrespective of the ratios of H 2S and NH 3 gas mixtures. The results showed that H 2S removal of the biofilter was significantly affected by high inlet concentrations of H 2S and NH 3. As high H 2S concentration was an inhibitory substrate for the growth of heterotrophic sulfur-oxidizing bacteria, the activity of H 2S oxidation was thus inhibited. In the case of high NH 3 concentration, the poor H 2S removal efficiency might be attributed to the acidification of the biofilter. The phenomenon was caused by acidic metabolite accumulation of NH 3. Through kinetic analysis, the presence of NH 3 did not hinder the NH 3 removal, but a high H 2S concentration would result in low removal efficiency. Conversely, H 2S of adequate concentrations would favor the removal of incoming NH 3. The results also indicated that maximum inlet concentrations (model-estimated) agreed well with the experimental values for space velocities of 50–150 h −1. Hence, the results would be used as the guideline for the design and operation of biofilters. 相似文献
12.
While a postulated intermediate, 1,3,4,5-tetrachlorocyclohexa-1,4-diene(1,4-TCDN), is one of the key-compounds in γ-hexachlorocyclohexane(γ-HCH) degradation by Pseudomonas paucimobilis UT26(UT26), it has neither been isolated nor identified yet. Thus, an indirect identification was attempted to demonstrate its existence by a chemical oxidation of the microbial degradation products in situ. 1,2,4,5-Tetrachlorobenzene(1,2,4,5-TeCB) was newly produced by the chemical oxidation with hydrogen peroxide under iron(II) of W medium containing degradation products in situ of γ-1,3,4,5,6-pentachlorocyclohexene(γ-PCCH) by Escherichia coli MV1184(E. coli) which possesses the dehydrochlorinating activity of UT26. The chemical oxidation required the preceding enzymatic reactions to γ-PCCH by E. coli for the production of 1,2,4,5-TeCB. In facts, 1,2,4,5-TeCB was not produced from γ-PCCH by either of the chemical or enzymatic reaction alone. Considering these results and the fact that hydrogen peroxide is known to dehydrogenate chemical compounds, it was concluded that 1,2,4,5-TeCB was produced directly from the unstable intermediate, 1,4-TCDN, on yielded from γ-PCCH by an enzymatic dehydrochlorination. 相似文献
13.
The synthesis of TiO 2 and Fe–TiO 2 by sol–gel method is demonstrated and characterized. The characterization of TiO 2 and Fe–TiO 2 is performed with instruments, including TGA/DTA, FTIR, UV–Vis, N 2 adsorption and SEM. Dichloromethane is used for the photocatalytic activity test. From the results of dichloromethane photocatalyitc degradation, the calcined temperature of TiO 2 and the presence of water vapor influence the photocatalytic activity. The optimum doping amount of iron ions is 0.005 mol%, and this can enhance the photocatalytic activity, while too great an amount will make the iron ions become recombination centers for the electron–hole pairs and reduce the photocatalytic activity. UV–Vis diffuse reflectance spectra of Fe–TiO 2 show an increase in absorbency in the visible light region with the increase in iron ions doping concentration The intermediate of dichloromethane photodegradation includes CHCl 3, CCl 4, CH 2Cl 2 and COCl 2. The presence of iron ions may reduce the adsorption of Cl element on the surface of the photocatalyst. 相似文献
14.
The photodegradation of two common and very stable azo-dyes, i.e. methyl-orange (C 14H 14N 3SO 3Na) and orange II (C 16H 11N 2SO 4Na), is reported. The photocatalytic oxidation was carried out in aqueous suspensions of polycrystalline TiO 2 irradiated by sunlight. Compound parabolic collectors, installed at the “Plataforma Solar de Almería” (PSA, Spain) were used as the photoreactors and two identical reacting systems allowed to perform photoreactivity runs for the two dyes at the same time and under the same irradiation conditions. The disappearance of colour and substrates together with the abatement of total organic carbon content was monitored. The main sulfonate-containing intermediates were found to be in lower number in respect to those obtained under artificial irradiation. In particular there were no more evidence of the presence of hydroxylated transients. The dependence of dye photooxidation rate on: (i) substrate concentration; (ii) catalyst amount; and (iii) initial pH was investigated. The influence of the presence of strong oxidant species (H 2O 2, S 2O 82−) and some ions (Cl −, SO 42−) on the process was also studied. 相似文献
15.
An experiment was carried out to decompose chlorinated dioxins (PCDDs, PCDFs) Chlorobenzenes, NOx and odourous compounds (H 2S, CH 4S, C 2H 6S 2, C 8H 8, C 2H 6S, C 2H 4O, NH 3) simultaneously using a catalyst in the MSW incineration plant. The experiments were conducted at temperatures from 200°C to 400°C and from 3000h −1 to 6000h −1 at space velocity. A catalyst containing V 2O 5 and WO 3 on the basis of TiO 2 is used, an oxidizing catalyst of the honeycomb type. The average decomposition efficiencis were 95%, 98%, 92% for PCDDs(48CDDs), PCDFs(48CDFs) and Chlorobenzenes(36CLBs) at a reaction temperature of 350°C and a space velocity of 3000h −1, more than 90% for NOx at a reactiont temperature of 300°C and more than 80% for odourous compounds at the reaction temperature of 300°C and a space velocity of 6000h −1. All those compounds were decomposed successfully with increasing contact time and surface. The rate-determing step was the chemical reaction of catalyst surface. 相似文献
16.
聚酰胺类微塑料(PA-MPs)和磺胺类抗生素(SAs)均为新兴污染物且已广泛检出,其中聚酰胺6微塑料由常用的聚酰胺6塑料产生,磺胺噻唑(ST)是典型的SAs.由于微塑料在环境暴露中普遍易老化,因此探究了聚酰胺6微塑料在未老化、紫外老化、紫外和H2 O2老化(分别记为PA6、PA6-UV、PA6-UV+H2 O2)下对S... 相似文献
17.
This study evaluates the effects of Fenton's reagent (FR) on the rate and extent of the oxidative degradation of individual mono, di-, tri- and tetrachlorobiphenyls in the commercial mixture DELOR 103, equivalent to AROCLOR 1248. The oxidation effect of FR strongly increased with increasing the molar ratio of Fe 2+/H 2O 2. The most effective oxidation of DELOR 103 (10 μg.ml −1) was achieved in a solution containing 1M H 2O 2 and 1 mM Fe 2+. The FR elimination rate constants of PCB congeners decrease with increasing number of chlorine substituents in the biphenyl molecule and show a good correlation with the values of molecular weights of the PCB congeners and their 1-octanol/water partition coefficients. 相似文献
18.
Recent studies indicate that secondary ozonides of cyclic alkenes are formed in atmospheric reactions and may be relatively stable. The secondary ozonides (SOZs) of cyclohexene (1), 1-methylcyclohexene (2), 4-isopropyl-1-methylcyclohexene (3) and 4-isopropenyl-1-methylcyclohexene (limonene) (4) have been characterized by rapid gas chromatography electron ionization (EI), negative and positive chemical ionization (CI: ammonia, isobutane and methane) and collision-induced dissociation (CID) mass spectrometry. Both EI and positive CI spectra were found unsuitable for reproducible analysis. However, negative CI showed stable (M−H) − ions with minor fragmentation. CID of the (M−H) − ions resulted in simple and reproducible fragmentation patterns for all four SOZs with loss of m/ z 18, 44 and 60, tentatively assigned as H 2O, CO 2 and C 2H 4O 2 or CO 3, respectively. Thus, negative CI-MS–MS in combination with rapid gas chromatography is the preferred method for identification of secondary ozonides of cyclohexenes. 相似文献
19.
The combined electrochemical oxidation-solar-light/immobilized TiO 2 film process was conducted to degrade an azo dye, Reactive Black 5 (RB5). The toxicity was also monitored by the Vibrio fischeri light inhibition test. The electrochemical oxidation rapidly decolorized RB5 (55, 110 μM) with a supporting electrolyte of 2 g l −1 NaCl at current density 277 A m −2 and pH 4. However, TOC mineralization and A 310 removal were low. Additionally, the treated solution showed high biotoxicity. RB5 at 110 μM significantly retarded the de-colorization efficiency by using the solar-light/immobilized TiO 2 film process. The combined electrochemical oxidation-solar-light/immobilized TiO 2 process effectively increased the removal of color, A 310, and TOC. The toxicity was also significantly reduced after 3 h of solar irradiation. The results indicated that the low-cost combined process is a potential technique for rapid treatment of RB5. 相似文献
20.
The presence of disinfection byproducts (DBPs) such as trihalomethanes (THMs) and haloacetic acids (HAAs) in drinking water is of great concern due to their adverse effects on human health. Emerging regulation limiting the concentration of DBPs in drinking water has increased demands for technologies and processes which reduce the formation of DBPs in drinking water. In this study, UV-H 2O 2 based advance oxidation process (AOP) was used to treat raw surface water. Experiments were conducted using low pressure mercury vapor UV lamps in collimated beam and flow-through annular photoreactors. The effect of UV fluence (0–3500 mJ cm −2) and hydrogen peroxide concentration (0–23 mg l −1) in reducing the concentration of THMs and HAAs was examined. The UV-H 2O 2 AOP was then coupled with a downstream biological activated carbon (BAC) treatment to assess the synergetic benefits of combining the two treatments. It was observed that UV-H 2O 2 AOP was only effective at reducing DBPs at UV fluences of more than 1000 mJ cm −2and initial H 2O 2 concentrations of about or greater than 23 mg l −1. However, the combined AOP–BAC treatment showed significant reductions of 43%, 52%, and 59% relative to untreated raw water for DBPs, TOC, and UV 254, respectively. 相似文献
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