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Saturated zone, layer

The water table refers to the surface (i.e. two dimensional) between the saturated zone and the overlying capillary fringe or unsaturated zone. In Figure 3.5, the water table passes through a homogeneous and permeable sand layer. If a water table is under atmospheric influence, as shown in Figure 3.5, its water is at atmospheric pressure (Freeze and Cherry, 1979), 39. [Pg.146]

Advective air and water currents are much smaller in soil systems but still influence the movement of chemicals that reside in soil. Advection of water in the saturated zone is usually solved numerically from hydrodynamic models. Advection of air and water in the unsaturated zone is complicated by the heterogeneity of these soil systems. Models are usually developed for specific soil property classes, and measurements of these soil properties are made at a specific site to determine which soil-model layers to link together. [Pg.484]

In piston flow, groundwater is layered in the saturated zone of the intake area, younger water layers over older water layers. Such systems provide... [Pg.267]

Groundwater is abstracted from many different types of aquifers, some of which may be highly susceptible to pollution as a consequence of human activity. The vulnerability of groundwater sources is important when assessing the risks to groundwater posed by various activities, Some aquifers are protected by one or more layers of impermeable material, such as clay, that lie above the saturated zone and that will prevent or retard the transport of chemicals from their sources to the saturated zone. Also, aquifers at certain depths may be protected from chemicals (even from some naturally occurring chemicals) that may be present at other depths in the geological profile. [Pg.16]

The Deeper Unsaturated Soil The deeper unsaturated soil includes the soil layers below the root zone and above the saturated zone, where all pore spaces are filled with water. This compartment can encompass both the B and the C soil horizons. The soil in this layer typically has a lower organic carbon content and lower porosity than the root-zone soil. Contaminants in this layer move downward to the groundwater zone primarily by capillary motion of water and leaching. Chemical transformation in this layer is primarily by biodegradation. [Pg.2076]

Soil structure, geologic strata, and topography influence the location and movement of variable source areas of surface runoff in a watershed. Eragipans or other layers, such as clay pans of distinct permeability changes, can determine when and where perched water tables occur. Shale or sandstone strata also influence soil moisture content and location of saturated zones. For example, water will perch on less permeable layers in the subsurface profile and become evident as surface flow or springs at specific locations in a watershed. Converging topography in vertical or horizontal planes, slope breaks, and hill slope depressions or spurs, also influence... [Pg.131]

The distribution and the nature of past, existing and potential pollution sources have also to be thoroughly established and assessed in light of the pollution vulnerability of the aquifer system concerned. A general appreciation of the reactive processes which may take place during contaminant transport, in ah sub-surface compartments (soils, cappings layers, unsaturated and saturated zones in aquifers, river beds,. ..) is required too. [Pg.211]

Soil is a complex matrix consisting of air pockets, water, mineral matter and organic matter. It can vary enormously in its composition and texture and consists of various layers with different properties. The upper layer, which is more directly involved in the input of chemical substances and where distribution and fate processes are more complex, is the so-called vadose or unsaturated zone. This means that the pore spaces in the soil materials are not fully filled with water. Below the vadose zone, there is the saturated zone, where pore spaces are completely filled with water. The top of the saturated zone is the water table, corresponding to the level to which water will rise at atmospheric pressure in a hole dug in the earth. [Pg.85]

Boieshan [91,9S] considers that the superficial layers of the emulsifier in the particle surface are important in the emulsion polymerization of vinyl chloride. The author suggests that the polymerization of vinyl chloride is a homogeneous process in which the number of the latex particles is only a secondary factor. The adsorbed layer zone of emulsifier saturated with monomer and oligomer radicals governs the overall rate of polymerization. The monomer saturated zone favors the growth events as well as the decomposition of... [Pg.170]

Approximately 0.75 mL of sample is introduced into a special g ass adsorption column packed with activated silica gel. A small layer of the silica gel contains a mixture of fluorescent dyes. When all the sample has been adsorbed on the gel, alcohol is added to desorb the sample down the column. The hydrocarbons are separated according to their adsorption affinities into aromatics, olefins, and saturates. The fluorescent dyes are also separated selectively, with the hydrocarbon types, and make the boundaries of the aromatic, olefin, and saturate zones visible under ultraviolet light. The volume percentage of each hydrocarbon type is calculated from the length of each zone in the column. [Pg.258]

As noted above, there are cases where we need more accurate representations of how chemical concentration varies with depth. For example, we may be interested in transfers of chemicals from air to shallow ground water or want to consider how long-term applications of pesticides to the soil surface can impact terrestrial ecosystems—including burrowing creatures. However, we also wish to maintain a simple mathematical mass-balance structure of the multimedia model. To illustrate how we can set up a multilayer model that accurately captures soil mass transport processes, we next derive a vertical compartment structure with an air and three soil compartments, but any number of environmental compartments and soil layers can be employed in this scheme. Figure 8.6 provides a schematic of three soil layers linked to an air compartment and carrying pollutants downward to a saturated zone. We represent the inventory in each vertical compartment i, as M, (mol), transformation rate constants as kt, and transfer factors as ky (d ). The latter account for the rate of transfer between each i and j compartment pair. [Pg.182]

FIGURE 8.6 A schematic of three soil layers linked to an air compartment and carrying pollutants downward to a saturated zone. [Pg.183]

In stacked reservoirs, such as those found in deltaic series, it is common to find that some zones are not drained effectively. Through-casing logs such as thermal neutron and gamma ray spectroscopy devices can be run to investigate whether any layers with original oil saturations remain. Such zones can be perforated to increase oil production at the expense of wetter wells. [Pg.361]

In practice a few iodine crystals are usually placed on the bottom of a dry, closed trough chamber. After the chamber has become saturated with violet iodine vapor the solvent-free plates are placed in the chamber for 30 s to a few minutes. The iodine vapor condenses on the TLC layers and is enriched in the chromatogram zones. Iodine vapor is a universal detector, there are examples of its application for all types of substances, e.g. amino acids, indoles, alkaloids, steroids, psychoactive substances, lipids (a tabular compilation would be too voluminous to include in this section). [Pg.46]


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See also in sourсe #XX -- [ Pg.105 , Pg.115 , Pg.132 ]




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