Phenolic compounds organic pollutants

There is a vast range of aqueous organic pollutants with a wide toxicity profile. Some, e.g. polychlorinated biphenyls, certain herbicides, fungicides and pesticides, and organo-mercury compounds, are persistent and may bioaccumulate in the food chain. Trace contaminants such as sodium chloride, iron and phenols (especially if chlorinated) may also impart a taste to water. Typical consent levels for industrial discharges are provided in Table 13.10. 

Activated carbon has high specific surface area with respect to its volume, and thus has high adsorption capacity. Activated carbon adsorption is considered to be one of the most versatile treatment technologies and can remove classical pollutants such as COD, TOC, BOD, and nitrogen, as well as toxic pollutants such as phenol, refractory organic compounds, VOCs, and soluble heavy metals.38 Activated alumina and peat have also demonstrated similar abilities. 

Organic pollutants present in aqueous-solid phase environments and discussed in the present chapter include petroleum hydrocarbons, pesticides, phthalates, phenols, PCBs, chlorocarbons, organotin compounds, and surfactants. In order to study the chemodynamic behavior of these pollutants, it is important that (1) suitable pre-extraction and preservation treatments are implemented for the environmental samples, and (2) specific extraction and/or cleanup techniques for each organic pollutant are carried out prior to the identification and characterization steps. 

The majority of systems studied have been aqueous solutions of either aromatic compounds or halogenated hydrocarbons. Such materials represent models for the major classes of organic pollutants in waste and ground water. The primary products resulting from the sonochemical treatment of phenol at 541 kHz (27 °C with bubbled air) are hydroquinone and catechol [22]. These compounds are easy to monitor and are clearly seen to be intermediates which disappear as the reaction progresses (Fig. 4.1). Similarly the sonolysis of aqueous 4-chlorophenol leads to products mainly characteristic of oxidation by OH radical e. g. 4-chlorocatechol but in both cases the final organic products are CO, CO2 and HCOOH (Scheme 4.2) [22-25]. 

Several studies are devoted to the extraction of phenolic compounds. These compounds are particularly interesting from a practical viewpoint, as phenol derivatives are toxic pollutants that have marked detrimental effects on living organisms in general therefore, the development of effective methods of phenols recovery is a long-standing problem of analytical chemistry. To determine phenolic compounds at the trace level, typically preconcentration and separation from accompanying substances is required, but the extraction of phenolic compounds with conventional solvents is often not quantitative. From a more theoretical viewpoint, phenolic compounds exhibit a wide structural variability, thus, a study of their... 

Reviewed previous SCWO research with model pollutants and demonstrated that phenolic compounds are the model pollutants studied most extensively under SCWO conditions Studied supercritical water oxidation of aqueous waste Explored reaction pathways in SCWO of phenol Studied catalytic oxidation in supercritical water Explored metal oxides as catalysts in SCWO Studied decomposition of municipal sludge by SCWO Investigated the SCWO kinetics, products, and pathways for CH3- and CHO-substituted phenols Determined oxidation rates of common organic compounds in SCWO... 

Phenolic compounds are the model pollutants studied most extensively under SCWO conditions. Equation (10.8) and Equation (10.9) describe the formation of free radicals in the absence of initiators. They are formed by the reaction of oxygen with the weakest C-H bonds of the organic compound ... 

This is applied to separate acidic or basic organics from neutral organics. The solvent extract is shaken with water that is highly basic. The acidic organics partition into the aqueous layer whereas, the basic and neutral compounds stay in the organic solvent and separate out. After this, the aqueous layer is acidified to a pH below 2, and then extracted with methylene chloride. The organic layer now contains the acid fraction Phenols, chlorophenoxy acid, herbicides, and semivolatile organic pollutants are cleaned up by the procedure described above. 

Oxidation The chemical addition of oxygen to break down pollutants or organic waste (e.g., destruction of chemicals such as cyanides, phenols, and organic sulfur compounds in sewage by bacterial and chemical means). 

The combination of photo-Fenton and ozonation results in an important enhancement of the destruction efficiency of organic compounds like phenol [96], 2,4-D [97], aniline or 2,4-chlorophenol ([33] and references therein). As mentioned in Sect. 2.5.1, metal ions catalyze ozone decomposition. In the dark, Fe(II) catalyzes O3 degradation giving the ferryl intermediate (Fe02+, see Sect. 2.6.9), which can directly oxidize the organic pollutant or evolve to a hydroxyl radical ... 

OEHHA Office of Environmental Health Hazard Assessment OSHA Occnpational Safety and Health Administration Osteogenic sarcoma Cancer associated with bone structures Oxidation Chemical addition of oxygen to break down pollutants or organic waste, for example, destruction of chemical substances such as cyanides, phenols, and organic sulfur compounds in sewage by bacterial and chemical means Oxidative stress Process whereby the metabolic balance of a cell is disrupted by exposure to environmental substances, resulting in accumulation of free radicals, which can damage the cell... 

An on-line technique coupling preconcentration via a precolumn packed with PGC and LC with a PGC analytical column has been applied to the trace-level determination of some polar and water-soluble organic pollutants from environmental waters.As these analytes are much more retained by the graphite surface than by silica Cig, preconcentration on the PGC precolumn cannot be coupled on-line with a widely used and more efficient Cjg silica analytical columns. In this study, applications were presented for the trace-level determination of 2-chloro-4-aminophenol, chloroanilines, amino-phenols, and cyanuric acid these organic compounds are included in the EC environmental priority pollutant list. The influence of the sample matrix was investigated with drinking and river water samples. 

The adsorption of phenol and phenolic compounds is by far the most studied of aU liquid-phase applications of carbon adsorbents [1]. This is because phenol is used as a model aromatic molecule and has been declared a priority pollutant. Therefore, this chapter devotes more attention to the adsorption of phenol and substituted phenols than to the adsorption of other organic solutes. 

Reducing agents that accumulate in soils under anaerobic conditions, such as Fe ", sulfide, and phenols (from the reduction of quinones in humic acid) may react with certain classes of organic chemicals. For instance, Fe can reduce halogenated aliphatic compounds, an important class of organic pollutants in soils. The process initially involves the transfer of a single electron, for example. 

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