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Water flows, alterations

The Alteration of Water Flows in the Context of Climatic and Global Changes. 18... [Pg.17]

Alterations of water flow, independent of the cause, impact the stmcture and function of aquatic ecosystems. Extended drought produces the loss of hydrologic connectivity between stream compartments, and affects the biota. Therefore, flow cessation triggers a chain of cascading effects, eventually affecting community structure and ecosystem functioning. [Pg.26]

The rate at which a new equilibrium turgor is achieved in response to an altered external water potential depends on the water flow. The half-time (ti/2) of the response for a non-growing cell is given by ... [Pg.97]

In contrast to the conventional PRB, a permeable reactive treatment zone (PRTZ) is a geochemically manipulated subsurface zone where aquifer material is altered to promote destruction or immobilization of target chemicals (e.g., flushed with sodium dithionite to create a zone of reduced iron [20-23]). Passive reactive wells (PRWs) are a series of wells or caissons containing a treatment material, through which water flows because of a permeability contrast between the wells and aquifer. A biologically reactive barrier (BRB), sometimes called a biocurtain, is a subsurface zone where microbiological activity is enhanced or modified to provide treatment of target chemicals. [Pg.377]

For soil systems contaminated with Na+, kinematic viscosity is not significantly affected, thus the components controlling water flow velocity are the hydraulic gradient (A< >/AX) and soil permeability (k). The latter component (k) is influenced by clay dispersion, migration, and clay swelling. These processes may cause considerable alteration to such soil matrix characteristics as porosity, pore-size distribution, tortuosity, and void shape. [Pg.394]

Aquaporins comprise six transmembrane a-helices, and five interhelical loop regions (A-E) that form the extracellular and cytoplasmic vestibules. Loops B and E are hydrophobic loops which contain the highly, although not completely, conserved Asn-Pro-Ala (NPA) motif, which overlaps the middle of the lipid bilayer of the membrane, forming a 3D hourglass structure through which water flows. Two constrictions in the channel act as selectivity Alters. [Pg.170]

The forces driving water flow to form cytotoxic edema are osmotic, generated in brain injury conditions (ischemia, trauma, hypoxia) by disturbances in ionic homeostasis due to failure of the Na /K+ ATPase and/or dramatic influx of Na" and Ca " via ionotropic glutamate receptors (excitotoxicity) and other ionic channels. These pathological alterations in cellular ionic homeostasis result in Na" " and water flow from the intravascular and extracellular space into the intracellular compartment. [Pg.133]

Nephrogenic diabetes insipidus has been described in patients receiving foscarnet, either alone or associated with a distal renal tubular acidosis [66, 67, 68]. In fact, a recent review cited foscarnet as the second most common reported cause of drug-induced diabetes insipidus, second only to lithium [69]. In experiments using toad urinary bladders [70], serosal application of foscarnet enhanced water flow in the presence of submaximal ADH concentrations, but did not affect water transport in the absence of ADH or when maximal concentrations of ADH were used. Mucosal foscarnet did not affect water transport. Further studies are needed to clarify the mechanisms for altered water handling by the kidneys with foscarnet. [Pg.387]

Filtration can remove fine suspended solids and microorganisms, and microfiltration membranes of cellulose acetate or polyamides are available that have pores 0.1-20 pm in diameter. Clogging of such fine Alters is an ever-present problem, and it is usual to pass the water through a coarser conventional Alter flrst. Ultraflltration with membranes having pores smaller than 0.1 pm requires application of pressures of a few bars to keep the membrane surface free of deposits, water flows parallel to the membrane surfaces, with only a small fraction passing through the membrane. The membranes typically consist of bundles of hollow cellulose acetate or polyamide fibers set in a plastic matrix. Ultrafiltration bears some resemblance to reverse osmosis technology, described in Section 14.4, with the major difference that reverse osmosis can remove dissolved matter, whereas ultrafiltration cannot. [Pg.265]

Equation (3.4.34) can be altered by making assumptions as to the influence of molecular diffusion and rate of water flow. For example, if the molecular diffusion is negligible and the dispersion carries with the pore-water velocity,... [Pg.86]

An initial and important distinction needs to be made between two microenvironments - exposed and sheltered. Exposed surfaces have water flow across their surfaces either from direct rainfall or from runoff or both. However the magnitude and frequency of this flow may vary between surfaces. Sheltered surfaces do not experience any water flow products of degradation cannot, therefore, be removed from the surface by water flow. This can result in the build-up of a crust of degradation products that could protect the limestone surface from further alteration. On an exposed surface, the build-up of any degradation products is likely to be temporary. Microenvironmental variations in exposure begin to define the type of degradation forms that can be expected to develop on different parts of the building. [Pg.219]

When water flows through a high-rate Alter, suspended particles are trapped in its entire volume. The high-rate Alter is regenerated via expansion of the Alter layer using a stream of wash water or a mixture of wash water and air. [Pg.253]

Figures II, III. and IV display the dependence of gas production (g gas per g cellulose or % conversion) by species on gas-phase residence time for various gas-phase reactor temperatures. For these experiments, the steam superheater was maintained at SbO C, and the pyrolysis furnace at 500°C. This latter setting gave rise to a measured sample heating rate of 100°C/min. Residence times were altered by varying the peristaltic pump s water flow rate between 0.06 and 0.34 g/min, and by inserting a closed quartz cylinder into the gas-phase reactor to reduce its apparent volume. Figures II, III. and IV display the dependence of gas production (g gas per g cellulose or % conversion) by species on gas-phase residence time for various gas-phase reactor temperatures. For these experiments, the steam superheater was maintained at SbO C, and the pyrolysis furnace at 500°C. This latter setting gave rise to a measured sample heating rate of 100°C/min. Residence times were altered by varying the peristaltic pump s water flow rate between 0.06 and 0.34 g/min, and by inserting a closed quartz cylinder into the gas-phase reactor to reduce its apparent volume.

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See also in sourсe #XX -- [ Pg.18 ]




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