Environmental fate concerns

In this step, the assessor qiuuitifies tlie magnitude, frequency and duration of exposure for each patliway identified in Step 2. Tliis step is most often conducted in two stages estimation of exposure concentrations and calculation of intakes. The later estimation is considered in Step 4. In tliis part of step 3. the exposure assessor determines the concentration of chemicals tliat will be contacted over the exposure period. E.xposure concentrations are estimated using monitoring data and/or chemical transport and environmental fate models. Modeling may be used to estimate future chemical concentrations in media tliat are currently contaminated or tliat may become contaminated, and current concentrations in media and/or at locations for which tliere are no monitoring data. The bulk of the material in tliis chapter is concerned witli tliis step. 

Most hydraulic fluid preparations start as chemical mixtures. For instance, there is a considerable area of overlap in the specific petroleum hydrocarbon chemicals contained in the mineral oil and polyalphaolefin hydraulic fluids. For all classes of hydraulic fluids, there may be similarities with other original products intended for use as lubricants. The complications involved in documenting the environmental fate of mixtures increase under conditions encountered at many NPL sites, where it may be hard to determine the precise original product associated with chemicals identified at an area in need of remediation. In most instances, available peer-reviewed literature, supplemented with data obtained from manufacturers of particular formulations and information in trade magazines, can supply information about the original hydraulic fluid preparations. At NPL sites, site-specific evaluations of specific chemicals may be the only feasible way to address concerns over environmental fate and potential exposure risks. 

Mineral Oil Hydraulic Fluids and Polyalphaolefin Hydraulic Fluids. Limited information about environmentally important physical and chemical properties is available for the mineral oil and water-in-oil emulsion hydraulic fluid products and components is presented in Tables 3-4, 3-5, and 3-7. Much of the available trade literature emphasizes properties desirable for the commercial end uses of the products as hydraulic fluids rather than the physical constants most useful in fate and transport analysis. Since the products are typically mixtures, the chief value of the trade literature is to identify specific chemical components, generally various petroleum hydrocarbons. Additional information on the properties of the various mineral oil formulations would make it easier to distinguish the toxicity and environmental effects and to trace the site contaminant s fate based on levels of distinguishing components. Improved information is especially needed on additives, some of which may be of more environmental and public health concern than the hydrocarbons that comprise the bulk of the mineral oil hydraulic fluids by weight. For the polyalphaolefin hydraulic fluids, basic physical and chemical properties related to assessing environmental fate and exposure risks are essentially unknown. Additional information for these types of hydraulic fluids is clearly needed. 

Environmental Fate. Having characterized the entry of materials into the environment, we move into the second step of our procedure. The goal at this stage of analysis is to define ambient concentration of the material or its products in areas of concern for receptor (e.g., people, materials or ecosystem components) exposure. A family of computer simulation models has been developed for calculating the ambient levels of a... 

Dispersion modelling of the emissions concerns how air pollutants disperse in the ambient atmosphere. This step is also called environmental fate analysis, especially when it involves more complex pathways that pass through the food chain. The pollutants dispersed to the atmosphere are in general modelled using dispersion models. 

No information was found in the available literature concerning on-going studies dealing with the environmental fate or human exposure potential of di- -octylphthalate. 

Physical and Chemical Properties. Some of the physical and chemical properties (i.e., K°w K°<= and Henry s law constant) that are often used in the estimation of environmental fate of organic compounds are not useful or relevant for most inorganic compounds including thorium and its compounds. Relevant data concerning the physical and chemical properties, such as solubility, stability, and oxidation-reduction potential of thorium salts and complexes have been located in the existing literature. 

Environmental Fate. Little experimental data on the resonance time and half-life of chlorine dioxide and chlorite (ions or salts) in the atmosphere are available. Additional information on the transport of chlorine dioxide in the atmosphere may be useful, considering that over 900,000 pounds are released annually to air (TRIOO 2002). Additional information about the mechanism of reformation of chlorine dioxide in water distribution systems from chlorite ion is needed (Hoehn et al. 1990). Additional information concerning the transport and partitioning of chlorite (ions or salts) is also needed. 

These models require accurate data on physico-chemical properties of organic substances, which is the subject of Dr. Mackay s other interest, namely their measurement and correlation. This includes the compilation and critical review of these properties and their quantitative structure property relationships. He is co-author of the five-volume Illustrated Handbook of Physical Chemical Properties and Environmental Fate of Organic Chemicals, which documents data reported in the literature, and is also available in CD-ROM format from CRC Press. Dr. Mackay s hope is that a combination of the information reported in these handbooks, and the estimated data as described in the present volume, can provide a sound basis for assessment of the large and growing number of chemical substances of environmental concern. 

Palm, A., Cousins, I.T., Mackay, D., Tysklind, M., Metcalfe, C., Alaee, M., 2002. Assessing the environmental fate of chemicals of emerging concern A case study of the polybro-minated diphenyl ethers. Environ. Pollut. 117, 195-213. 

Environmental fate models make use of chemical properties to describe transfer, partitioning, and degradation (Mackay et al. 1992a Cahill et al. 2003). For organic chemicals, quantitative structure-property relationships (QSPRs) may be used to predict partitioning from physical-chemical properties, such as Kow and Kov Such properties may also allow for a prediction of the transfer of chemicals between compartments. Recently, some successful attempts have also been made to predict persistency of chemicals (Raymond et al. 2001), although this mainly concerns... 

Recent work has involved classification for environmental effects with respect to environmental fate and toxicity to aquatic organisms. Discussions are ongoing concerning toxicity to terrestrial organisms. Classification and labelling are cornerstones of chemical safety, and today tens of thousands of substances are classified as hazardous. 

Tingle CC, Rother JA, Dewhurst CE, Lauer S, and King WJ (2003) Fipronil Environmental fate, ecotoxicology, and human health concerns. Reviews of Environmental Contamination and Toxicology 176 1-66. 

Mixtures Risk Assessment The mere occurrence of chemicals and contaminants in the environment does not increase the potential of risk to human or environment, but their exposure does. A five-step process is used to determine the extent, route, and duration of exposure and includes its environmental fate and transport. This process allows identification of likely site-specific exposure to chemicals and chemical mixtures, the extent of exposure, and the conditions under which the exposure occurred. This way contaminants of concern can be identified in a systematic manner by combining the chemical hazard and exposure data [7],... 

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