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Distribution speciation

Equilibrium constants have been measured for (41)-(45) using a variety of techniques spectrophotometry 49), conductivity, 170-NMR line broadening (50), isopiestic measurements, potentiometry, and others 51). From these data, speciation distribution estimates have been calculated 52). As the equilibrium constants for (41)—(45) are quite sensitive to ionic strength, so are the speciation distributions. Thus, for pH = 1, Cr(VI)T = 10-2 M and T = 25°C, the [H2Cr04] is calculated to be 29%at/ = 0 and 1% at I = 1.0M(52). Nevertheless, a considerable proportion ( 50%) of Cr(VI) in the pH range 1-6 is estimated to be in the HCr04 form. [Pg.351]

Each of these steps can modify the natural speciation distribution, and so the goal is to minimize their number. These steps will now be discussed for two groups of trace metals Cr, Fe, Mn, and As (Section 7.2), and Hg (Section 7.3). [Pg.122]

Speciation Distribution of species in a particular sample or matrix... [Pg.538]

Van Landeghem GF, De Broe ME, D Elaese PC. Al and Si Their speciation, distribution, and toxicity - A critical review. Clin Biochem... [Pg.891]

Due to the ubiquitous occurrence of humic substances and colloids (defined as entities of Inm-lpm size) in natural waters, their specific properties, in particular their scavenging capacities towards metallic cations and also their well-established mobility (1-6), these organic and inorganic species could have important effects on the fate and mobility of these cations in natural systems. On one hand, the formation of organic complexes or pseudocolloidal species will modify the speciation (distribution of chemical species) of the cation of interest and its solubility. On the other hand, they can retard cation migration... [Pg.259]

The Antarctic food chains are unique, both on land and in the sea. It is not therefore possible to directly transfer temperate data and models of toxicity to Antarctica since several of the trophic levels are missing, many organisms live for much longer than in temperate regions and grow much more slowly. In addition it appears that for many compounds little is known of their behaviour (such as chemical speciation, distribution and life time in the environment) at very low temperatures. Research is essential to fill both of these gaps. [Pg.48]

Speciation of an element speciation. Distribution of an element amongst defined chemical species in a system. The term fractionation has been defined as follows. [Pg.92]

Distribution of silicon speciation in the initial sediments The silicon released from the surface sediments of the PRE was exposed in vitro under different environmental conditions of agitation time, pH value, and salinity. Then the consequent speciation distribution of silicon in the leached sediments was also analyzed through comparison with the silicon speciation in the initial (unleached) sediments, and the sampling stations are shown in Fig. 5.11 (Qin and Weng, 2006). [Pg.552]

Table 5.5. Speciation distribution of silicon in the initial sediments of the Pearl River Estuary (pg Si/g) (Qin and Weng, 2006) (With permission from Elsevier s Cop5rright Clearance Center)... Table 5.5. Speciation distribution of silicon in the initial sediments of the Pearl River Estuary (pg Si/g) (Qin and Weng, 2006) (With permission from Elsevier s Cop5rright Clearance Center)...
With respect to the three sediments, the speciation distribution of silicon is quite similar in samples D1 and D2 due to close composition of clay minerals, whereas sample D3, retrieved close to Lantau Island, Hong Kong, is fine sand, exhibiting relatively low bioavailability. In addition, affected likely by anthropogenic activities, silicon bound to organics in sample D3 is relatively high. Silicon speciation distribution in sediments is hence related to the deposit environments and sediment composition. [Pg.553]

Fig. 5.12. Speciation distribution of silicon in the sediment samples Dl, D2, and D3 from the Pearl River Estuary after leaching under different conditions of agitation time (al dl), pH (a2 2), and salinity (a3 d3). (a) Exchangeable (b) Bound to carbonates (c) Bound to Fe-Mn oxides (d) Bound to organics (Qin and Weng, 2006) (With permission from Elsevier s Copyright Clearance Center)... Fig. 5.12. Speciation distribution of silicon in the sediment samples Dl, D2, and D3 from the Pearl River Estuary after leaching under different conditions of agitation time (al dl), pH (a2 2), and salinity (a3 d3). (a) Exchangeable (b) Bound to carbonates (c) Bound to Fe-Mn oxides (d) Bound to organics (Qin and Weng, 2006) (With permission from Elsevier s Copyright Clearance Center)...
Qin YC, Weng HX (2006) Silicon release and its speciation distribution in the surficial sediments of the Pearl River Estuary, China. Estuar Coast Shelf Sci 67(3) 433-440... [Pg.623]

The study of biochemical natural products has also been aided through the application of two-dimensional GC. In many studies, it has been observed that volatile organic compounds from plants (for example, in fruits) show species-specific distributions in chiral abundances. Observations have shown that related species produce similar compounds, but at differing ratios, and the study of such distributions yields information on speciation and plant genetics. In particular, the determination of hydroxyl fatty acid adducts produced from bacterial processes has been a successful application. In the reported applications, enantiomeric determination of polyhydroxyl alkanoic acids extracted from intracellular regions has been enabled (45). [Pg.68]

A development of the study of adsorption currents is referred to as Tensammetry, and a useful review50 refers to the application of this technique to the examination of natural waters as an aid to speciation , the procedure for deciding how a metal ion is distributed between the various species in which the metal may be present. [Pg.616]

Because of these differences, it is not surprising that speciation differs significantly in the two systems. The contrast in oxidation-state distributions between the single-phase studies and the leaching experiments is noteworthy. In the latter,... [Pg.341]

The distribution of metals between dissolved and particulate phases in aquatic systems is governed by a competition between precipitation and adsorption (and transport as particles) versus dissolution and formation of soluble complexes (and transport in the solution phase). A great deal is known about the thermodynamics of these reactions, and in many cases it is possible to explain or predict semi-quantita-tively the equilibrium speciation of a metal in an environmental system. Predictions of complete speciation of the metal are often limited by inadequate information on chemical composition, equilibrium constants, and reaction rates. [Pg.415]

The chemical speciation of the metal is defined as its distribution among different phases and different dissolved forms. When heavy metals enter aquatic... [Pg.46]

Therefore, the pH values of these solutions are between 11 and 12. The speciation model used by 8chwarzenbach and Fischer is certainly too simple but these authors have been the first to demonstrate the strong dependence of the polysulfide anion distribution on the alkalinity. According to Eqs. (26)-(28) higher pH values in dilute solutions will favor smaller anion sizes. [Pg.139]

When TBTO is released into ambient water, a considerable proportion becomes adsorbed to sediments, as might be expected from its lipophilicity. Studies have shown that between 10 and 95% of TBTO added to surface waters becomes bound to sediment. In the water column it exists in several different forms, principally the hydroxide, the chloride, and the carbonate (Figure 8.5). Once TBT has been adsorbed, loss is almost entirely due to slow degradation, leading to desorption of diphenyl-tin (DPT). The distribution and state of speciation of TBT can vary considerably between aquatic systems, depending on pH, temperature, salinity, and other factors. [Pg.174]

Gray JE, Theodorakos PM, Bailey EA, Turner RR. 2000. Distribution, speciation, and transport of mercury in stream-sediment, stream-water, and fish collected near abandoned mercury mines in southwestern Alaska, USA. Sci Total Environ 260 21-33. [Pg.84]

Field and laboratory bioassay of chemosignals from related sympatric and allopatric species (overlapping and discrete distributions) are essential to an understanding of the relatedness or otherwise of functionally active compounds. The semiochemicals involved in speciation surely utilise the main and vomeronasal senses, but their relative contributions cannot be predicted at present. [Pg.68]

Speciation involves a number of discrete analytical steps comprising the extraction (isolation) of the analytes from a solid sample, preconcentration (to gain sensitivity), and eventually derivatisation (e.g. for ionic compounds), separation and detection. Various problems can occur in any of these steps. The entire analytical procedure should be carefully controlled in such a way that decay of unstable species does not occur. For speciation analysis, there is the risk that the chemical species can convert so that a false distribution is determined. In general, the accuracy of the determinations and the trace-ability of the overall analytical process are insufficiently ensured [539]. [Pg.674]

Logical Structures. When a synthetic organic chemical is released into an aquatic system, the entire array of transport, transfer, and transformation processes begins at once to act on the chemical. Transport from the point of entry into the bulk of the system takes place by advection and by turbulent dispersion. Transfers to sorbed forms and irreversible transformation processes proceed simultaneously with the transport of the chemical. After the elapse of sufficient time, the chemical comes to be distributed throughout the system, with relatively smooth concentration gradients resulting from dilution, speciation, and... [Pg.32]

An evaluation of the fate of trace metals in surface and sub-surface waters requires more detailed consideration of complexation, adsorption, coagulation, oxidation-reduction, and biological interactions. These processes can affect metals, solubility, toxicity, availability, physical transport, and corrosion potential. As a result of a need to describe the complex interactions involved in these situations, various models have been developed to address a number of specific situations. These are called equilibrium or speciation models because the user is provided (model output) with the distribution of various species. [Pg.57]

If required by the model(s) to be used, back-up data for each entry in the matrix or table may be supplied to resolve the total mass flow into spatial cells (UTM coordinates, depth or height), temporal cells (hourly frequency distributions, diurnal cycles, seasonal subdivisions or secular trends on annual intervals) or speciation cells (by valency state of anions or by hydrocarbon structure, for example). The level of difficulty encountered by the user in supplying these data may influence the choice of model(s). [Pg.100]


See other pages where Distribution speciation is mentioned: [Pg.339]    [Pg.155]    [Pg.128]    [Pg.1284]    [Pg.351]    [Pg.46]    [Pg.110]    [Pg.339]    [Pg.155]    [Pg.128]    [Pg.1284]    [Pg.351]    [Pg.46]    [Pg.110]    [Pg.445]    [Pg.144]    [Pg.4]    [Pg.258]    [Pg.333]    [Pg.334]    [Pg.561]    [Pg.581]    [Pg.674]    [Pg.14]    [Pg.18]    [Pg.322]    [Pg.25]    [Pg.93]    [Pg.210]    [Pg.360]    [Pg.32]    [Pg.87]    [Pg.89]   
See also in sourсe #XX -- [ Pg.10 ]

See also in sourсe #XX -- [ Pg.140 ]




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