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Distribution in Soil

Agricultural and forestry soils are the direct victims of the notorious chiral pesticides, which are used directly on the soil in agricultural and forestry pest [Pg.50]

Soil sample Enantiomeric ratio of cis-chlordane Enantiomeric ratio of trans-chlordane [Pg.53]


Two groups of chemical elements can be considered related to their distribution in soil profiles. The first group includes the essential nutrients actively absorbed by vegetation and relatively tightly bound in soil organic matter (Figure 11). [Pg.157]

The Analysis of Agricultural Materials, 2nd edn, R.B. 427. HMSO, London, (1979) Method 2, p. 6. Preparation of Samples of soil Method 8, p. 21. Boron, water soluble in soil Method 57, p. 134. Nitrogen in soil Method 62, p. 148. Organic matter in soil Method 63, p. 151. Particle size distribution in soil... [Pg.507]

The particle size and distribution in soils can be easily determined by the sedimentation method. It is based on the fact that large particles will settle faster than smaller ones. No special equipment is needed. [Pg.459]

Although the occurrence of the non-ionic surfactant nonylphenol ethoxylate (NPEO Fig. 6.7.1) and its biodegradation intermediates in the aquatic environment has attracted large interest [18] because of the potential of some biotransformation products to mimic estrogenic effects, their fate and distribution in soil environments has been only investigated in a few cases. [Pg.818]

Tab. 8.2 Nitrogen distribution in soils from widely differing climatic zones (means and standard deviations). Modified from Sowden et al. [4]... [Pg.120]

PI Chromium is a metal widely distributed in soil and plants (J). (From Plaper et ah, 2002)... [Pg.207]

Figure 4.5 Explosive molecule distribution in soil at 50% pore saturation, 23°C, Kj 4. Figure 4.5 Explosive molecule distribution in soil at 50% pore saturation, 23°C, Kj 4.
Bacillus cereus is an aerobic spore-forming bacterium that is widely distributed in soil and on plant material. Therefore, its occurrence of... [Pg.166]

Fluoride is widely distributed in soil and is present naturally in drinking water. [Pg.133]

Environmental applications of FIFFF have been carefully collected in a review by Gimbert et al. [35]. Separations of nanoparticles belong to the FIFFF tradition and this sector has recently found new, fully deserved impulse for microparticle separations. The FIFFF technique has been applied to analyze humic material and submicron Fe colloids. Coupled with ICP-MS, FIFFF has been applied to detect the major and trace element chemistry of aquatic colloids in groundwaters and to determine the trace element distribution in soil and compost-derived humic and colloidal fractions in municipal wastewater. Recently, the ICP-AES has also been proposed as a specific detector for FIFFF to analyze inorganic nanoparticles (Figure 12.12). [Pg.352]

Yan-Chu, H. (1994) Arsenic distribution in soils, in Arsenic in the Environment Part I Cycling and Characterization (ed. J.O. Nriagu), John Wiley Sons, Ltd., New York, pp. 17-49. [Pg.234]

Swanson, R.A., and G.R. Dutt. 1973. Chemical and physical processes that affect atrazine and distribution in soil systems. Soil Sci. Soc. Am. Proc. 37 872-876. [Pg.207]

Simpson, M. J., Simpson, A. J., Gross, D., Spraul, M., and Kingery, W. L. (2007b). ll and 19F nuclear magnetic resonance microimaging of water and chemical distribution in soil columns. Environ. Toxicol. Chem. 26,1340-1348. [Pg.647]

Research has previously shown that bacteria are not uniformly distributed in soil, reflecting soil structure and available nutrients (Richaume et al., 1993). The distribution of microorganisms throughout the soil can also be considered from the applied ecological perspective of patch dynamics, where patch formation is a reflection of intrinsic and extrinsic forces (Rao et al., 1986). The same authors also showed spatial variability in the degradation of pesticides applied to a soil system. [Pg.317]

Sadeghi, A.M. and A.R. Isensee (1992). Effect of tillage systems and rainfall patterns on atrazine distribution in soil. J. Environ. Qual., 21 464 169. [Pg.382]

Camilion, C., Manassero, M., Hurtado, M. and Ronco, A. (2003) Copper, Lead and Zinc distribution in soils and sediments of the South Western coast of the Rio de la Plata estuary, Journal of Soils and Sediments 3, 213-220. [Pg.254]

In environmental studies in particular, very often one is not able to adjust these concomitant variables but only to measure them. Typical situations occur during sampling. In principle all sampling circumstances are concomitant variables, for example pH, temperature, salinity in water sampling, or humidity in air sampling, redox potential, and particle size distribution in soil sampling. [Pg.88]

Contaminant distribution in soil and water depends on such factors as soil properties the physical and chemical properties of the contaminant contaminant fate and transport in soil, groundwater or surface water and even the manner in which the contaminant was introduced into the environment. The knowledge of these issues coupled with available information on site history and background allows us to make valid assumptions in the planning phase on contaminant distribution and variability at the site. [Pg.71]

Cave, M.R. and Wragg, J. (1997) Measurement of trace element distributions in soils and sediments using sequential leach data and a non-specific extraction system with chemo-metric data processing. Analyst, 122, 1211-1221. [Pg.289]

Swaine DJ, Mitchell RL. 1960. Trace-element distribution in soil profiles. J Soil Sci ll(2) 347-368. [Pg.465]

Figure 8.1 Regional and local anomaly threshold applied to an urban environment. The concentration graph shows the influence of anthropogenic sources (industrial area, downtown and main roads) on pollutant distribution in soils. Figure 8.1 Regional and local anomaly threshold applied to an urban environment. The concentration graph shows the influence of anthropogenic sources (industrial area, downtown and main roads) on pollutant distribution in soils.
Ljung, K., Selinus, O., Otabbong, E., andBerglund, M. (2006). Metal and arsenic distribution in soil particle sizes relevant to soil ingestion by children. Appl. Geochem. 21, 1613—1624. [Pg.173]

Determination of pore-size distribution in soils. Soil Science, 49 347-360. Leaver, E. S., Woolf, J. A, and Head, R. E. [Pg.520]

Phytoextraction is the best approach to remove the contamination primarily from soil and isolate it, without substantially alternating the soil structure and fertility. It is also referred as phytoaccumulation. As the plant absorbs, concentrates, and accumulates toxic metals and radionuclides from contaminated soils and waters into plant tissues, it is best suited for the remediation of diffusely polluted areas, where pollutants occur only at relatively low concentrations and superficial distribution in soil (Rulkens et al., 1998). Several approaches have been studied to enhance the effectiveness of phytoextraction, including the use of chelators to increase the bioavailability and plant uptake of metal contaminants. In order to make this... [Pg.129]

Alternaria has been knovm for centuries to cause various plant diseases such as early blight of potato and various leaf spots and fruit rot. Species of this fungus are widely distributed in soil and on aerial plant parts. Because Alternaria requires high moisture levels (28-34%) for growth, infection of seeds occurs when the seed moisture is high, either in early stages of development or after wetting of crops from rain. [Pg.190]


See other pages where Distribution in Soil is mentioned: [Pg.99]    [Pg.64]    [Pg.168]    [Pg.163]    [Pg.121]    [Pg.73]    [Pg.862]    [Pg.204]    [Pg.466]    [Pg.191]    [Pg.343]    [Pg.628]    [Pg.361]    [Pg.254]    [Pg.257]    [Pg.505]    [Pg.348]    [Pg.216]    [Pg.846]    [Pg.872]    [Pg.54]   


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Soil distribution

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