[Branch-specific detection of phenols and assessment of ground water solubility]

Abstract

There are about 500 technically relevant phenolic compounds such as cresols, chlorophenols or nitrophenols. It is most preferable to determine phenols as single compounds via gas chromatography. Further, phenols can also be assayed as photometrically as an overall parameter (Phenolindex): however, no conclusions about specific compounds can be drawn from this type of test. Also this method is not as reliable for an hazard assessment as gas chromatography. First, not all phenols, for instance resorcinol or 1-naphthol can be determined with this method. Second, phenolic groups in humic substances, which do not constitute a threat for groundwater, are determined alongside environmentally relevant phenols using this method. In most cases, it is possible to deduce which phenols can be expected in the groundwater of contaminated sites from the type of industrial usage, such as chlorophenols and pulp bleaching or nitrophenols and the production of explosives. Phenols are formed during coal combustion for instance at cokemanufactures or gasworks. They are important raw materials for the chemical industry from which resins, surfactants, pharmaceuticals, pigments, explosives, and stabilizers are produced. During the 80's phenol, cresols, nonylphenols, anisidines, aminophenols, dihydroxybenzenes, and naphthols were manufactured in amounts exceeding 10,000 t/a. Also, phenolic compounds are used as additives in many areas for example as solvents in the electric industry, in sawmills, papermanufacture, electroplating of metal sheets, as photographic developers, as textile dyes, or for the tanning of hydes. Due to the formation and use of phenols at industrial sites, groundwater contaminations are possible via infiltration through the unsaturated zone. Especially at gasworks and ammunition factories, groundwater contaminations with phenols have become known. In the vicinity of railway tracks and associated facillities contaminations due to the use of pesticides or mineral oils are possible. Input of phenols on agricultural lands can be caused by pesticides, sewage sludge or manure. The groundwater downstream of landfills often contains phenol, chlorophenols, cresols, and xylenols. The formation of phenol from other organic contaminants as benzene in groundwater has been reported. The potential for mobilization of phenols in the saturated zone can be estimated from their physical and chemical properties. Especially low molecular weight phenols are easily mobilized due to their high solubility in water and low potential for accumulation. These compounds are: phenol, cresols, xylenols, chlorophenols, hydroxybenzenes, nitrophenols, anisidines, aminophenols, anisol, 2-phenoxyethanol, and thiophenol. The stability of phenols under laboratory conditions varies. The complete mineralization depends mainly on the experimental set-up, i.e. nutrients, temperature, and type of inocula. The anaerobic degradation of phenols is generally slower than the aerobic. Phenol is readily biodegradable under both aerobic and anaerobic conditions. In general, the biodegradability depends on the type, number and position of substitutes. Phenols with nitro-, alkyl-, or chlorosubstitutes are more recalcitrant than phenol itself. Our biodegradability test show that the decomposition of alkylphenols is determined by the length and branching of the alcyllic chain. Phenols with high contamination potential are chlorophenols, xylenols, and nitrophenols. These compounds are both mobile and recalcitrant in the saturated zone. Phenolic compounds of a medium contamination risk are dichlorophenols, trichlorophenols, cresols, and phenol because they are mobile but less stable in groundwater. These compounds are known contaminants in the groundwater at gasworks, landfills, and ammunition factories. Aminophenols, anisidines, tert-butylphenols, ethylphenols, hydroxybenzenes, and 2-phenoxyethanol also constite a potential hazard for groundwater; however, no contaminations with these compounds are known. Poisoning due to oral uptake of phenol contaminated ground- or drinking water have not been reported, which might be due to the pungent odor and taste phenolic compounds have even at very low concentrations (mg/L). Because of the taste problem, the German drinking water standard for phenols is 0.5 microgram/L. In Berlin, groundwater with phenol concentrations higher than 30 micrograms/L of alkylphenols or 2 micrograms/L of chlorophenols is considered contaminated.