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Fresh water systems

Smith, J.H., Mabey, W.R., Bahonos, N., Holt, B.R., Lee, S.S., Chou, T.W., Venberger, D.C., Mill, T. (1978) Environmental Pathways of Selected Chemicals in Fresh Water Systems Part II. Laboratory Studies. Interagency Energy-Environment Research Program Report. EPA-600/7-78-074. Environmental Research Laboratory Office of Research and Development. US EPA, Athens, GA 30605, pp. 304. [Pg.915]

The bottom line as serious as the former employee s intrusions were they pale in comparison with what he could have done to the fresh water system—he could have done anything he liked. (Gellman 2002)... [Pg.116]

Methylmercury, which we referred to in the neurotoxicity section, occurs in fish and shellfish found in both the ocean and fresh water systems. The mercury that is the source of methylmercury arises from power plant emissions and industrial processes. Some even comes from... [Pg.133]

It is known that, in a water phase, immiscible liquids such as gasoline or other petroleum products may form multicomponent droplets of various forms and sizes, under dispersive conditions. These droplets are transported by convection and diffusion, which contributes to the contamination of fresh water systems. However, during droplet transport, more volatile substances partition to the gas phase at the droplet surface, leaving less volatile material that volatilizes more slowly. More volatile material still exists in the droplet interiors, and it tends to diffuse toward the surface because of concentration gradients created by prior volatilization. Different components in a droplet have different volatilization rates, which may vary significantly during droplet transport, and as a result, the contamination of fresh water is affected accordingly. [Pg.149]

Tana, T.S., 1996. Water quality impact on the fisheries and aquaculture of Cambodian fresh water system. Water Report, 38 11. [Pg.816]

The pH is controlled by various reactions and the presence of different compounds. In fresh water systems the carbonate system C02—HC03—C03 plays a primary role in determining the pH. In other cases the presence of H2S or its oxidized form, sulfuric acid, determines low pH. The pH value is an important parameter in water quality assessment in relation to corrosion problems and taste. [Pg.173]

These BCF values of these very lipophilic polycyclic musk fragrances are relatively low compared to the predicted BCF values calculated by means of Eq. (26). At this time no exact explanation for this phenomenon can be given. It is known that the parent chemicals HHCB and AHTN are metabolized in the fish to more polar compounds that will be eliminated at a higher rate. It is also possible that the low BCF value of C-AHTN may be due to the low radiochemical purity of 78.8%. It seems therefore necessary to perform bioconcentration tests with PMFs of high purity in the absence of a solubilizer and to use water concentrations of these very lipophilic PMFs in the lower ng range, which are found in fresh water systems [362], and to use the kinetic approach. At this time no exact water solubility data are available. [Pg.137]

Tranter M., Davies T. D., Wigington P. J., and Eshleman K. N. (1994) Episodic acidification of fresh-water systems in Canada— physical and geochemical processes. Water Air Soil Pollut. 72, 19-39. [Pg.4944]

Bioalkylation does not only take place in the ocean, but also in fresh water systems where biological species exist which are able to produce such compounds. During summer meltwater ponds are formed at many places in Antarctica. The green colour of some meltwater ponds on the McMurdo Ice Shelf indicates high biological activity and cyanobacteria were found to be the dominant organisms in these ponds. [Pg.202]

Ribeyre F, Boudou A, Maurybrachet R. 1991. Multicompartment ecotoxicological models to study mercury bioaccumulation and transfer in fresh water systems. Water, Air, Soil Pollution 56 641-652. [Pg.640]

The bicarbonate radical, HC03 , is more acidic than HC03 (pKa = 10.3 vs. 10, respectively), but the pK for equilibrium (16) is poorly constrained with reported values between 7.0-9.6 [150-152]. In many fresh water systems the predominant species will be the bicarbonate radical, while both the bicarbonate and carbonate radicals will be important in seawater. As may be expected, the reactivity of the carbonate radical with many organic and inorganic species will be pH dependent [153]. [Pg.272]

Table 1. Vertical attenuation coefficients (K d-eff) DNA effective UVBR in various marine and fresh water systems, measured with DNA dosimeters. Attenuation coefficients were determined from linear regressions of natural logarithmic biologically effective irradiation against depth using the log-linear part of the curve... Table 1. Vertical attenuation coefficients (K d-eff) DNA effective UVBR in various marine and fresh water systems, measured with DNA dosimeters. Attenuation coefficients were determined from linear regressions of natural logarithmic biologically effective irradiation against depth using the log-linear part of the curve...
Further on, the protection of the fresh water systems is a big challenge also for the politics not only of the individual nations but also of the European Union. As a first result of EU-activities the Water Framework Directive (WFD) was introduced in 2002 in order to organise and optimise the national activities in the field of water science and technology (s.a. Irmer 2000). [Pg.3]

Kaplan, W. A., J. W. Elkins, C. E. Kolb, M. B. McElroy, S. Wofsy, and C. R. Duran (1978). Nitrous oxide in fresh water systems. An estimate for the yield of atmospheric N20 associated with disposal of human waste. Pure Appl. Geophys. 116, 423-438. [Pg.672]

Compared to the extensive data describing the ocean particulate (10, 11), size distribution data on particulates in fresh water systems and wastewaters are relatively scarce. Particle size distribution data for several low ionic strength solutions are shown in Figure 1 with the water source, particulate counting method, and references as noted. The size frequency distribution of the four heterogeneous suspensions shown can be modeled by a two-parameter power-law distribution function (2) given by the expression... [Pg.309]

Stable activable tracers are powerful tools for the study of many environmental problems. Compared with fluorescent dyes or radiotracers, they offer many advantages that are reviewed herein. Our research group has emphasized the use of rare earth nuclides with short-lived activation products as stable activable tracers. Use of rare earth nuclides is cost-competitive with conventional tracers and allows rare earth "fingerprints to mark individual sources with subsequent simultaneous tracing of effluents from several sources. We present results from the application of these tracers to monitor pollutant dispersal from multiple industrial stacks, monitor fluid-bound pollutant dispersal in estuarine and fresh-water systems, monitor herbicide dispersal, and trace toxic organic chemicals in the marine environment. [Pg.523]

Regulation of Trace Metal Concentrations in Fresh Water Systems Peter Baccini... [Pg.293]

Amides Commonly used as foam stabilizers. Coconut or lauryl diethanolamide shows excellent performance for fresh water systems. [Pg.308]

This effect is not only seen in high electrolyte systems. Certain beneficial hydrotropic effects can be observed in fresh water systems as well. This is shown in Table 7, where sodinm snlfonates of xyleii , cumene and toluene are added to a fresh water foaming system. [Pg.310]

Among the fresh water systems an extended study for 1979 has revealed the pattern of the heavy metal burden (Cd, Pb, Cu) in the River Rhine and the contributions from its tributaries[47]. The suitability of the vol-tammetric approach for river studies are emphasized by a recent methodological inter-comparison[48]. [Pg.133]


See other pages where Fresh water systems is mentioned: [Pg.21]    [Pg.139]    [Pg.27]    [Pg.206]    [Pg.56]    [Pg.164]    [Pg.8]    [Pg.181]    [Pg.344]    [Pg.113]    [Pg.118]    [Pg.294]    [Pg.295]    [Pg.319]    [Pg.16]    [Pg.89]    [Pg.127]    [Pg.750]    [Pg.115]    [Pg.661]    [Pg.399]    [Pg.568]    [Pg.140]    [Pg.306]    [Pg.371]    [Pg.169]    [Pg.251]    [Pg.44]    [Pg.178]   
See also in sourсe #XX -- [ Pg.8 ]




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