Big Chemical Encyclopedia

Chemical substances, components, reactions, process design ...

Articles Figures Tables About

Environmental modeling

D. Mackay, Multimedia Environmental Models, Lewis, Chelsea, MI, 1991. [Pg.219]

Other Environmental Modeling (e.g., water groundwater chemical properties) ... [Pg.279]

CIBSE Application Manual 11 Building and environmental modelling. London Chartered Inst--tute of Building Services Engineers (CIBSE), I99S. [Pg.1082]

For the purposes of environmental modelling using the EUSES program, data are available regarding photodegradation of the substances, as summarized in Table 5. [Pg.12]

Mackay, D. (1991). Multimedia Environmental Models The Eugacity Approach. Chelsea Ml Lewis. [Pg.358]

This book proposes a monitoring program that will help determine trends for mercury concentrations in the environment and assess the relatiorrship between these concentrations and mercnry emissions. Environmental models are also often used to predict trends and examine relationships among variables. Models can facilitate the interpretation of data emerging from monitoring programs recommended in this book and that the data will help develop better modehng tools. [Pg.203]

Verma, K.V., George, H.V., Singh, S.K., Singh, A., Juwarkar, A., and Singh, R.N., Modeling rhizofiltration Heavy-metal uptake by plant roots, Environmental Modeling and Assessment, 11, 387-394, 2006. [Pg.402]

Schnoor, J.L., Environmental Modeling—Fate and Transport of Pollutants in Water, Air, and Soil, John Wiley Sons, New York, 1996. [Pg.569]

Particle Transport. Because many organic chemicals bind with aquatic particulate matter, particle transport can determine the fate of compounds. Sediment transport has been of interest to the engineering profession for many years. Many discussions of the dynamics of fluvial sediment transport have appeared in the literature (11, 12). As with hydrodynamic transport, one strategy for environmental modeling is to "piggy-back the transport of sorbed chemicals on a model of transport of the sediment phase. [Pg.27]

Export processes are often more complicated than the expression given in Equation 7, for many chemicals can escape across the air/water interface (volatilize) or, in rapidly depositing environments, be buried for indeterminate periods in deep sediment beds. Still, the majority of environmental models are simply variations on the mass-balance theme expressed by Equation 7. Some codes solve Equation 7 directly for relatively large control volumes, that is, they operate on "compartment" or "box" models of the environment. Models of aquatic systems can also be phrased in terms of continuous space, as opposed to the "compartment" approach of discrete spatial zones. In this case, the partial differential equations (which arise, for example, by taking the limit of Equation 7 as the control volume goes to zero) can be solved by finite difference or finite element numerical integration techniques. [Pg.34]

Information contained in this paper has been compiled under support provided by Melanie Byrne, Joanne Perwak, Kate Scow and Janet Wagner. Their contributions are appreciated. In addition, this paper will serve as a background section for an Environmental Modeling Catalogue (Bonazountas Fiksel, editors, 1983) in preparation for the EPA/TIP, Mike Alford Project Officer, EPA Contract No. 68-01-5146. [Pg.63]

In a series of recent papers Q - 4), we have advocated the use of the fugacity concept as an aid to compartmental modeling of chemicals which may be deliberately or inadvertantly discharged into the environment. The use of fugacity instead of concentration may facilitate the formulation and interpretation of environmental models it can simplify the mathematics and permit processes which are quite different in character to be compared... [Pg.175]

C) their relative adsorptivities will converge and that as the temperature increases, their relative adsorptivities will diverge as butylate becomes more strongly adsorbed and alachlor and meto-lachlor become less strongly adsorbed. This result should translate into a reduction of leaching of butylate (compared to alachlor and metolachlor) as the temperature of the soil system is raised. Thus, the effect of temperature can be handled by an environmental model for soil mobility by including the heat of adsorption of the pesticide. [Pg.246]

Environmental models which are accessible today can be used for exposure assessment of pesticides. [Pg.261]

W.M. Upholt. "Models for Extrapolation of Health Risk" Proceedings of the EPA Conference on Environmental Modeling and Simulation. April 19-22, 1976, Cincinnati, Ohio. [Pg.307]

Ramaswami A, Milford JB, Small MJ (2005) Integrated environmental modeling. Pollutant transport, fate, and risk in the environment Wiley, New York... [Pg.67]

Mackay D (1991) Multimedia environmental models the fugacity approach. Lewis Publishers, Chelsea... [Pg.70]

An extensive comparison of the most obvious positive and negative aspects from seven evaluation models (ECOSENSE, EDIP, USES-LCA, CalTOX, BETR, IMPACT 2002+, and WATSON) led to the development of USEtox, a scientific consensus environmental model for characterization of human and ecotoxicological... [Pg.100]

Mackay D (2001) Multimedia environmental models - the fugacity approach, 2nd edn. CRC Press/Taylor Francis Group, Boca Raton... [Pg.135]

Measured data on environmental concentrations and human health are scarce and scattered. Hence, environmental modeling was applied in order to generate an overview over the distribution of selected hazardous substances due to informal recycling in Guiyu. As all available models have a specific focus and various pros and cons, four models were chosen, which cover different geographical scales and address different environmental compartments and objectives in order to assess the potential risk of the selected chemicals to humans and the environment. [Pg.350]

For regional scale, EUSES, a European Union multimedia environmental model for risk assessment of new and existing substances was applied considering the region where the e-waste recycling sites are. [Pg.354]

Lohmann U, Roeckner E (1996) Design and performance of a new cloud microphysics scheme developed for the ECHAM4 general circulation model. Clim Dyn 12 557-572 Mackay D (1991) Multimedia Environmental Models The Fugacity Approach. Lewis Publishers, Chelsea, MI, USA... [Pg.100]

When conducting assessments of how a chemical is likely to behave in the environment and especially how different chemicals behave in the same environment, there is incentive to standardize the evaluations using evaluative environmental models. The nature of these calculations has been described in a series of papers, notably Mackay (1979),... [Pg.18]

Andren, A. W., Doucette, W. J., Dickhut, R. M. (1987) Methods for estimating solubilities of hydrophobic organic compounds Environmental modeling efforts. In Sources and Fates of Aquatic Pollutants. Hites, R. A., Eisenreich, S. J., Eds., pp. 3-26, Advances in Chemistry Series 216, American Chemical Society, Washington, D.C. [Pg.49]

Stiver, W., Mackay, D. (1989) The linear additivity principle in environmental modelling Application to chemical behaviour in soil. Chemosphere 19, 1187-1198. [Pg.57]

We are grateful to the University of Toronto and Trent University for providing facilities, to the Natural Sciences and Engineering Research Council of Canada and the consortium of chemical companies that support the Canadian Environmental Modelling Centre for funding of the second edition. It is a pleasure to acknowledge the invaluable contributions of Eva Webster and Ness Mackay. [Pg.924]


See other pages where Environmental modeling is mentioned: [Pg.132]    [Pg.14]    [Pg.244]    [Pg.262]    [Pg.303]    [Pg.558]    [Pg.33]    [Pg.33]    [Pg.176]    [Pg.243]    [Pg.250]    [Pg.167]    [Pg.60]    [Pg.102]    [Pg.125]    [Pg.314]    [Pg.332]    [Pg.488]    [Pg.298]    [Pg.923]    [Pg.925]   
See also in sourсe #XX -- [ Pg.12 , Pg.24 ]

See also in sourсe #XX -- [ Pg.23 , Pg.23 , Pg.24 , Pg.25 , Pg.26 ]




SEARCH



Models environmental

© 2024 chempedia.info