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Sediments matrix

Trichloroethylene was qualitatively detected in the soil/sediment matrix of the Love Canal waste site near Niagara Falls (Hauser and Bromberg 1982). Sediment concentrations were found to be <0.5 pg/kg (dry weight) (<0.5 ppb) near a discharge point for effluent containing 17 ppb trichloroethylene in Los Angeles (Gossett et al. 1983). [Pg.219]

This matrix was not analyzed in the Ebro river basin until 1999. The first study was the largest study to date, because it combined the analyses of OCs and PCBs in water and sediment samples [80], It was not until 2004 that sediments from the Ebro basin were analyzed again, but in this case the study was focused on the lower course of the Ebro [81], with special attention to the Ebro Delta [24], and the area of Flix [82], downstream of the location of the organochlorine compounds industry in this village, where concentrations of up to 5,000 pg kg 1 of polychloronaphthalene were found. The number of studies that consider the sediment matrix is much lower than for water, and the number of chemical families is smaller, focused mainly on organochlorine compounds and PCBs (Fig. 4). [Pg.150]

The elements deposited within the sediment matrix show that mobilization processes may be occurring in the upper layers. At Station SIN 3, figure 4d for example, the element deposited (pg-cm-2) in the topmost layers decreases, often much more than in the concentration (Mg g 1). This may be due to organic matter decomposition and/or to environmental chemical reactions of solubility and precipitation of the given element. The metal must have been removed rapidly from the water column since the sediment concentration is shown to decrease rapidly with distance from the shipyard (Stations SIN 3 and SIN 2). Lead may not be mobilized significantly after deposition since any diffusion in the pore water would tend to "smooth" the concentration profile with time. [Pg.339]

All eompounds showing an affinity towards the Ah receptor are detected by the DR-Luc bioassay. The average interlaboratory repeatability ranged from 14.6% for the analysis of pure eompounds to 26.1% for the analysis of the whole sediment matrix. [Pg.118]

It is eoncluded that the determination of dioxin-like activity in cleaned sediment extracts using the DR-Luc bioassay has a consistent reproducibility, and can be used as a reliable and robust tool in the hazard assessment of dredged materials in a licensing system. Its advantage over ehemical analysis is that it also detects the effects of combined exposure as well as the effect of unidentified congeners or chemicals present in concentrations below the limit of detection of chemical analysis with a similar mode of action. In addition the use of cleaned sediment extracts circumvents the problem of disturbing sediment matrix effects. [Pg.118]

Let us now come back to the issue of linearity of the isotherm and dependency of Kld on the sorbate concentration. In numerous field studies in which both particle-associated and dissolved concentrations of PAHs are measured, apparent Kioc values are up to two orders of magnitude higher than one would have predicted from a simple absorption model (Gustafsson and Gschwend, 1999). If a natural soil or sediment matrix includes impenetrable hydrophobic solids on which the chemical of interest may absorb, the overall Kioc value must reflect both absorption into recent natural organic matter and absorption onto these surfaces. [Pg.304]

A study to explore the effect of the sample matrix in SFE was done with a set of polychlorinated biphenyl (PCBs) and a river sediment matrix. Figure 12 shows the on-line SFE/GC characterization of a PCB standard ranging from monochloro to decachlorolbiphenyl compounds present at concentration levels from 5 to 100 microgram per milliliter. An election capture GC detector (ECD) was used for the determination of these PCB s. Since this PCB standard was made up in liquid... [Pg.355]

Fish and sediment Add water containing acrolein and acrylonitrile to sample freeze sample, extract in vacuum GC/MS 0.025 /Jg/8 Sediment matrix 1011 recovery. Fish matrix 90% recovery Hiatt 1981... [Pg.70]

It is clear that, extraction of organometals from sedimentary phases should be carried out with extractants which liberate organometals as much as possible without destroying them. Mineralization techniques, dissolving all or a large part of the sediment matrix should be avoided because the metal-carbon bonds of the organometal species will also be broken. The ideal extraction scenario is where ... [Pg.746]

Figure 10.10. Distribution of HCB in sediment matrix. The pH of purging solution controlled at above 9 by the addition of NaOH. The test was conducted at a potential gradient of 2V/... Figure 10.10. Distribution of HCB in sediment matrix. The pH of purging solution controlled at above 9 by the addition of NaOH. The test was conducted at a potential gradient of 2V/...
Sediments from Liverpool Bay, England, were found to contain concentrations ranging from 0.03 to 6 ppm, with most detections at the lower limit (Pearson and McConnell 1975). Sediment levels from nondetectable to 0.3 ppb (wet weight) tetrachloroethylene were identified in samples from Lake Pontchartrain, near New Orleans (Ferrario et al. 1985). The detection limit of the method used in this study was not stated. An analysis of the EPA STORET Data Base showed that tetrachloroethylene had been positively detected in 5% of 359 sediment observation stations, with median levels of <5 ng/g (5 ppb) (Staples et al. 1985). Tetrachloroethylene was qualitatively detected in the soil/sediment matrix of the Love Canal waste site near Niagara Falls, New York (Hauser and Bromberg 1982). [Pg.206]

The generally very small effects of grain interactions can lead to a measured value of magnetic susceptibility that is lower than the true or intrinsic susceptibility. However, this effect is normally ignored in mineral magnetic studies where the magnetic grains are normally assumed to be dispersed and randomly orientated within the bulk sediment matrix. [Pg.229]

SCPs are not produced from wood, biomass or charcoal combustion, and hence have no natural sources. Therefore, they are unambiguous indicators of deposition from industrial combustion of fossil-fuels. Their use as markers in sediments and other depositional sinks is enhanced by their easily identifiable morphology and, because of their elemental carbon composition, by their relatively simple extraction from the sediment matrix. IASs, on the other hand, or rather particles morphologically identical to them, do have natural sources from volcanic emissions (LeFbvre et al., 1986) and micro-meteorites (Handy Davidson, 1953 Hodge Wright, 1964). In addition, their aluminosilicate composition makes tliem less able to withstand chemical attack and, compositionally, similar to many of the sediment... [Pg.322]


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