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Salinity behavior

The previous analysis of SAH behavior in the soil clearly shows that their application for improving the water-holding capacity is not universal. Hydrogel swelling in a porous, partially salinized medium is affected by numerous factors, most often negative, and therefore a rational application of SAH demands an accurate consideration of these factors. It is evident that certain principles for adjustment of hydrogels to physical and chemical soil parameters, as well as appropriate laboratory tests and calculation algorithm systems should be worked out. [Pg.129]

Adsorption and retention studies of surfactants to sand in high-salinity reservoirs showed no differences between nonionics and ether carboxylates [185— 187] low retention and a positive behavior for good oil recovery has been found. [Pg.343]

The conclusion from the work by Baviere et al. [41] is that the main advantage of AOS is that it has optimum phase behavior (i.e., high solubilization parameters and low IFTs) from low to high temperatures across a range of salinities. [Pg.397]

Typical adsorption isotherms are shown in Figs. 16 and 17. Despite the large experimental scatter, a steep increase in adsorption can be seen at low concentrations, followed by a plateau at concentrations exceeding the CMC. Similar behavior has been observed before with model surfactants [49-54] and has also been predicted by modem theories of adsorption [54]. According to Fig. 16, adsorption increases modestly with salinity provided that the calcium ion concentration remains low. The calcium influence, shown in Fig. 17, cannot be explained by ionic strength effects alone but may be due to calcium-kaolinite interactions. [Pg.405]

In a subsequent study, the effect of reducing the ELP molecular weight on the expression and purification of a fusion protein was investigated. Two ELPs, ELP [V-20] and ELP[VsA2G3-90], both with a transition temperature at 40°C in phosphate-buffered saline (PBS) containing 1 M NaCl, were applied for the purification of thioredoxin. Similar yields were observed for both fusion proteins, resulting in a higher thioredoxin yield for the ELP[V-20] fusion, since the ELP fraction was smaller. However, a more complex phase transition behavior was observed for this ELP and therefore a selection of an appropriate combination of salt concentration and solution temperature was required [39]. [Pg.82]

To characterize the responses to PbTx-2, five dose rates (0, 12.5, 25, 50, and 100 ig/kg/hr in 2 ml saline) were infused into the jugular catheters of rats (four per group). Heart rates, systolic and diastolic arterial blood pressures, pulse pressures, respiratory rates, core and peripheral body temperatures, lead VI0 ECCjs, and arterial blood gases were monitored. Clinical signs and behaviors were recorded by video camera. After infusion, animals were monitored for 6 hr, by which time most had either died or recovered to near baseline physiological levels. [Pg.183]

Clays or shales have the ability to absorb water, thus causing the instability of wells either because of the swelling of some mineral species or because the supporting pressure is suppressed by modification of the pore pressure. The response of a shale to a water-based fluid depends on its initial water activity and on the composition of the fluid. The behavior of shales can be classified into either deformation mechanisms or transport mechanisms [1765]. Optimization of mud salinity, density, and filter-cake properties is important in achieving optimal shale stability and drilling efficiency with water-based mud. [Pg.61]

Examination of the stimulus properties of a large number of phenalkylamines and related derivatives shows many can be characterized as producing either AMPH-like stimulus effects or DOM-like stimulus effects. The structures of some of these agents are shown in figure 1. Certain other agents could not be reliably classified as either AMPH-like or DOM-like because, at the highest dose tested, they either produced vehicle-appropriate (i.e., saline-appropriate) responding or resulted in disruption of behavior. [Pg.44]

Kraemer T, Reid D (1984) The occurrence and behavior of radium in saline formation water of the US gulf coast region. Isot Geosci 2 153-174... [Pg.571]

Toole J, Baxter MS, Thomson J (1987) The behavior of uranium isotopes with salinity change in three UK estuaries. Est Coast Shelf Sci 25 283-297... [Pg.575]

An important issue that influences estuarine behavior is the determination of the riverine component. Variations in the riverine endmember may occur over timescales that are short compared to the residence times of water in the estuary, which result in nonlinear relationships between salinity and trace elements across the estuary as different riverine compositions progress through the estuary (Loder and Reichard 1981 Officer... [Pg.578]

India (Borole et al. 1982) and the Forth estuary in the UK (Toole et al. 1987), nonconservative behavior of uranium was also demonstrated. In the Amazon estuary, uranium showed elevated concentrations compared to simple mixing (McKee et al. 1987). Release of uranium from bottom sediments on the shelf was suggested to be a source of dissolved (<0.4 im) uranium. However, subsequent studies in the Amazon also demonstrated that U removal (Fig. 3) occurred at salinities <12 (Swarzenski et al. 1995, Swarzenski et al. 2003). Overall, it was established that the behavior of U is highly variable examples have been found of conservative behavior as well as both additions and removal of U by interaction with sediments. [Pg.585]

In the Delaware and Chesapeake estuaries (USA), uranium shows distinctly nonconservative behavior at salinities <5 (Sarin and Church 1994 Church et al. 1996). This was suggested to be due to sedimentary redox processes in the extensive salt marshes in the Delaware and Chesapeake bays. From mass balance calculations it was concluded that almost two-thirds of the uranium in the tidal waters were retained in the sediments. It was also suggested that, extrapolated globally, uranium removal in salt marshes and marine wetlands, including mangroves, are important sinks for U that may responsible for up to 50% of the total marine removal (Church et al. 1996). Removal of U is also observed within the Baltic Sea, related to the association of U with colloids (see Section 2.5). [Pg.586]

Toole J, Baxter M S and Thomson J (1987) The behavior of uranium isotopes with salinity change in three U.K. Estuaries. Estuarine Coastal Shelf Sci. 25 283-297 Torgersen T, Turekian KK, Turekian VC, Tanaka N, DeAngelo E, O Donnell JO (1996) " Ra distribution in surface and deep water of Long Island Sound Sources and horizontal transport rates. Cont Shelf Res 16 1545-1559... [Pg.605]

Only the (+) isomer of SKF-10,047, which very weakly inhibited the binding of 3H- PC P, induced stereotyped behavior. This finding is consistent with the results of the PCP receptor assay showing that (+)SKF-10,047 is one-tenth as potent as PCP, but is fivefold more potent than (-)SKF-10,047 (table 1). However, it was not possible to determine whether SKF-10,047 was a full agonist because of its poor solubility in saline. Also, SKF-10,047 produced weaving and circling behavior that was much less pronounced than that induced by PCP. In contrast to the results of the assays for stereotyped... [Pg.95]

A complete dose-response analysis was generated for PCP for doses from 0.625 to 20 mg/kg IP (data not shown). PCP exhibited dose-related anticonvulsant action when day one minus day three differ ence scores were compared for all doses tested. When retested with saline only on day five, no reduction in convulsant sever it or super-sensitive response was observed (day one minus day five), indicating no carryover drug effect 48 hours after dosing. At behavioral ly equivalent doses, all compounds assayed were clearly anticonvulsant (table 3). TCP was most potent at the doses tested. PCA was the most efficacious, and reduced convulsant severity by 2.58 points. As with PCP, none of the other phencycli-noids had any carryover effects 48 hours after dosing (day one minus day five). [Pg.118]


See other pages where Salinity behavior is mentioned: [Pg.150]    [Pg.192]    [Pg.156]    [Pg.41]    [Pg.32]    [Pg.152]    [Pg.260]    [Pg.1302]    [Pg.242]    [Pg.8]    [Pg.35]    [Pg.49]    [Pg.51]    [Pg.184]    [Pg.848]    [Pg.340]    [Pg.344]    [Pg.495]    [Pg.529]    [Pg.578]    [Pg.579]    [Pg.584]    [Pg.584]    [Pg.586]    [Pg.586]    [Pg.590]    [Pg.592]    [Pg.600]    [Pg.109]    [Pg.50]    [Pg.74]    [Pg.41]    [Pg.128]    [Pg.129]    [Pg.245]   
See also in sourсe #XX -- [ Pg.152 , Pg.153 ]




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