Equilibrium distribution coefficients for extraction of organic priority pollutants from water

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U.S. Environmental Protection Agency, Robert S. Kerr Environmental Research Laboratory, Center for Environmental Research Information [distributor] , Ada, OK, Cincinnati, OH
Water -- Pollution -- United States -- Measur
StatementC. Judson King ... [et al.]
ContributionsRobert S. Kerr Environmental Research Laboratory
The Physical Object
Pagination6 p. ;
ID Numbers
Open LibraryOL14890745M

United States Environmental Protection Agency Robert S. Kerr Environmental Research Laboratory Ada OK Research and Development EPA/S Apr. &ERA Project Summary Equilibrium Distribution Coefficients for Extraction of Organic Priority Pollutants from Water C. Judson King, Timothy A. Barbari, Dilip K.

Joshi, Nancy E. Bell, and John J. Senetar i i Equilibrium distribution. The purpose of this project is to establish phase-equilibrium data necessary for evaluation of solvent extraction as a treatment and/or recovery process for large number of the organic Priority Pollutants in aqueous streams.

The principal piece of information sought has been the equilibrium distribution coefficient, KD, defined as the weight fraction of solute in the solvent phase divided by.

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[Robert S. Kerr Environmental Research Laboratory.;]. Phase distribution equilibria play an important role in chemical separation processes on both laboratory and industrial scales. They are also involved in the movement of chemicals between different parts of the environment, and in the bioconcentration of pollutants in the food chain.

Equilibrium distribution coefficients for extraction of chlorinated hydrocarbons and aromatics from water into undecane. Timothy A. Barbari; C. by: The equilibrium partitioning (EqP) approach described in detail by Di Toro et al. has a thermodynamic basis, namely that distribution of pollutants in sediments tends toward a thermodynamic equilibrium characterized by equal chemical activities in sediment solids, dissolved organic carbon, interstitial pore water and benthic organisms.

Di Toro. Even when the two limitations of immiscibility and constant distribution coefficient do not quite hold, Fig. does allow a quick estimate of the trade-offs between solvent/feed ratio and number of stages required to obtain a desired degree of extraction (raffinate purity).

The above solutions are all based on ideal or theoretical stages. Even in discrete stage systems, like mixer-settlers. Organic Carbon Water Partition Coefficient (log K oc) The organic carbon water partition coefficient is a dimensionless number defined as the ratio of a chemical’s concentration absorbed per unit mass of soil, to its concentration in the aqueous phase.

It represents the distribution coefficient (K d) normalized to total organic carbon. Solid-Phase Extraction, Preservation, Storage, Transport, and Analysis of Trace Contaminants for Water Quality Monitoring of Heavy Metals. Experimental Study on the Role of Sedimentation and Degradation Processes on Atmospheric Deposition of Persistent Organic Pollutants in a Subtropical Water Column.

Latitudinal Distribution of. Soxhlet Extraction and Analysis of a Soil or Sediment Sample Contaminated with n-Pentadecane. Determination of a Clay–Water Distribution Coefficient for Copper.

PART 6: WET EXPERIMENTS. Determination of Dissolved Oxygen in Water Using the Winkler Method. Determination of the Biochemical Oxygen Demand of Sewage Influent. In book: Environmental Chemistry for a Sustainable World Volume 2: Remediation of Air and Water Pollution (pp) Chapter: Extraction Procedures for Organic Pollutants Determination in Water.

tion (). The equilibrium constant is independent of the rate at which it is achieved. The analyst’s function is to optimize extracting conditions so that the distribution of solute between phases lies far to the right in equation () and the resulting value of K D is large, indicating a high degree of extraction from phase A into phase B.

Chlorophenols constitute a particular group of priority organic pollutants listed by the USEPA in the Clean Water Act and the European Directive (ECDirective, ), due to their persistence. 1. Introduction. There is an increasing requirement for the monitoring of water quality across Europe, with particular emphasis on the contaminants in the list of priority pollutants contained in the Water Framework Directive (WFD) and in the various water conventions, e.g.

Description Equilibrium distribution coefficients for extraction of organic priority pollutants from water FB2

Convention for the Protection of the Marine Environment of the North-East Atlantic (OSPAR). The distribution coefficient (DC) is defined as the weight fraction of organic in the liquid C02 phase, divided by the weight fraction of organic in the water phase at equilibrium.

The DC may be used to calculate the liquid Cto-feed (S/F) ratio required to obtain essentially complete removal (%) of an organic from wastewater. Calibration of a passive sampler based on stir bar sorptive extraction for the monitoring of hydrophobic organic pollutants in water.

Priority organic pollutants. N inf is proportional by polymer/water coefficient to the equilibrium concentration of a compound in the water phase. Phenol is one of the most common organic water pollutants as it is highly toxic even at low phenols as priority pollutants and 80//EC distribution coefficient and high selectivity.

Joseph E. Rice, in Organic Chemistry Concepts and Applications for Medicinal Chemistry, Abstract. This chapter provides an overview of the concept of partition need for drug molecules to cross lipid bilayers in passing from one body compartment to another requires that the structure has properties that impart solubility in both a hydrophobic medium and water.

The Fragment Constant Method for Predicting Octanol–Air Partition Coefficients of Persistent Organic Pollutants at Different Temperatures. Journal of Physical and Chemical Reference Data35 (3), DOI: /   Equilibrium sampling of organic pollutants into the silicone polydimethylsiloxane (PDMS) has recently been applied in biological tissues including fish.

Pollutant concentrations in PDMS can then be multiplied with lipid/PDMS distribution coefficients (D Lipid,PDMS) to obtain concentrations in fish lipids. Different extraction techniques for the analysis of organic pollutants in water samples are being developed and optimized in order to automate and miniaturize the extraction step, using low volumes of solvents or even solventless procedures in order to pre-concentrate the analytes in.

An equilibrium model of organic chemical accumulation in aquatic food webs with sediment interaction indicates the significance of the sediment/overlying water partition coefficient for systems that have a benthic component The impact of the benthic Emily C Shaw, Roger A Cropp, The distribution of persistent organic pollutants in a.

Douglas et al. () measured equilibrium distribution coefficients (K D) by using methyl isobutyl ketone (MIBK) and diisopropyl ether (DIPE) as solvents for the extraction of phenols by liquid. One of the ways to recycle millions of tons of fly ash and chitin wastes produced yearly is their utilization as low-cost sorbents, mainly for heavy metal cations and organic substances.

To improve their sorption efficiency, fly ashes have been thermally activated or modified by chitosan. We aimed to deeply characterize the physicochemical properties of such sorbents to reveal the usefulness. The concentration of phenols in the equilibrium extraction phase was determined in accordance with the material balance calculation.

The extraction distribution coefficient D is expressed in Equation (1). (1) where Ce and Cw denote the concentrations of the extraction and water phases, respectively.

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Results and Discussion. Separations based on equilibria. All equilibrium methods considered in this section involve the distribution of substances between two phases that are insoluble in one another.

As an example, consider the two immiscible liquids benzene and a coloured compound is placed in the water and the two phases are mixed, colour appears in the benzene phase, and the intensity of the colour in. Calculated leaf/air bioconcentration factors for these and other 11 organic chemical vapours are used to improve a correlation with the and air/water equilibrium partition coefficients.

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View Show. Surface modification of sodium montmorillonite (Na+-Mt) was performed using antimicrobial agents to produce an ecofriendly nanocomposite. The adsorption performance of the nanocomposite has been evaluated for the removal of Acid Blue 25 dye (AB25) as a model organic pollutant from wastewater.

Sodium montmorillonite (Na+-Mt) was modified with three different ionene compounds through ion. The Distribution Coefficients of Acetic Acid Between Water and Solvent Systems, M. Mahramanlıoğlu, M. Tuncay Mühendislik Bilimleri Dergisi 7 (3) Journal of Engineering Sciences 7 (3) addition, a high distribution coefficient lessens the extent of solute removal required during the regenaration of the solvent.

Extraction is a separation technique frequently employed in the laboratory to isolate one or more components from a mixture. Distribution coefficient (D c) is the ratio of concentrations of a compound in the two phases of a mixture of two immiscible solvents at equilibrium.

Hence these coefficients. This chapter represents the important factors determining bioavailability of organic contaminants in both the water phase and sediment in freshwater systems. Estimating dissolved organic carbon partition coefficients for nonionic organic chemicals.

(eds) Emerging and Priority Pollutants in Rivers. The Handbook of Environmental Chemistry.To investigate the environmental fate, food chain bioaccumulation, and toxicity of organic chemicals, it is often preferable to measure the chemical's fugacity rather than its concentration.

However, simple methods to do this are rare. This paper presents a novel yet simple method to measure fugacities of a range of poorly volatile hydrophobic organic chemicals ranging in octanol−air.The distribution coefficient is given by the expression: k = [I 2 (CCl 4)]/[I 2 (aq)] = But Q =in other words the value for [I 2 (CCl 4)] is relatively higher than it should be, so iodine will pass from the organic layer to the aqueous layer until the value of the distribution coefficient is attained.