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Water atmosphere interface

A) The presence of a saturated sublayer of water vapor at the water-atmosphere interface, which is depleted in the heavy isotopes... [Pg.144]

The circulation of water in the Arctic Basin is a complex system of cycles and currents with different scales. Block HB simulates the dynamics of Arctic Basin water by the system of sub-blocks presented in Figure 6.2. The water dynamics in 2 is presented by flows between compartments Eijk. The directions of water exchanges are represented on every level zk = z0 + (k — 1 )A k according to Aota et al. (1992) in conformity with the current maps assigned as SSMAE input. The external boundary of 2 is determined by the coastline, the sea bottom, the Bering Strait, the southern boundary of the Norwegian Sea, and the water-atmosphere interface. [Pg.372]

Figure 7.13 Theoretical down-core profiles of radon activity illustrating that 222Rn is typically not in (a) secular equilibrium with its parent 226Ra at the sediment-water and water-atmosphere interfaces because of inert characteristics and loss by (b) diffusion and (c) gas bubble ebullitive stripping from sediments to overlying waters and then to the atmosphere. (Modified from Martens and Chanton, 1989.)... Figure 7.13 Theoretical down-core profiles of radon activity illustrating that 222Rn is typically not in (a) secular equilibrium with its parent 226Ra at the sediment-water and water-atmosphere interfaces because of inert characteristics and loss by (b) diffusion and (c) gas bubble ebullitive stripping from sediments to overlying waters and then to the atmosphere. (Modified from Martens and Chanton, 1989.)...
Depth 0-200 m, photic, water-atmosphere interface, turbulent, wind-driven, variable temperature, above thermocline, no interactions with bottom Depth >200m, no light, high pressures, below thermocline, cold, no interactions with atmosphere or bottom, mostly lateral currents Depth >200 m, no light, sediment-water interface, no interactions with atmosphere, mostly lateral currents... [Pg.437]

Considerable work has been done on the behavior of pollutant species at air-water and air-soil interfaces. For example, wet and diy deposition measurements of various gaseous and particulate species have been made over a wide range of atmospheric and land-cover conditions. Still, the problem is of such complexity that species-dependent and particle-size-dependent rates of transfer from the atmosphere to water and soil surfaces are not completely understood. There is much to be learned about pollutant transfer at water-soil interfaces. Concern about groundwater contamination by mineral... [Pg.140]

The ratio PjF is evidently equal to Bjh when expressed in absolute units. Under high pressures at 0° 0. the value of h for nitrogen is 30-5 c.c. per mol. w-butyric acid at a water-air interface may be compared to nitrogen at 0° C. between the pressures 400—1600 atmospheres, since x — 0 73 for both substances. B for butyric acid = 1 49 x 10 sq. cm. per mol., hence... [Pg.52]

FIGURE 8.11 Schematic of steps involved in the transfer of S02 from the gas phase to the aqueous phase of an atmospheric water droplet and its oxidation in the liquid phase. S02(i) = S02 at the water-gas interface. [Pg.306]

The processes of transport at the atmosphere-water surface border have been well studied. The transport of moisture from the surface of a water body into the atmosphere is one of the complicated physical processes of mass and energy exchange across the water-air interface (Figure 4.12). These processes are functions of many climatic parameters and, to a large extent, are regulated by eddy motions in the surface layer of the atmosphere determined by the wind field. [Pg.266]

Figure 4.15. Block diagram for formation and transport of methane in waterlogged country. Notation FlCHi is the methane flux across the atmosphere/water body interface F2CHi is the oxidation of methane in aerobic zones FCH is the intensity of the methane source M is methane concentration. Figure 4.15. Block diagram for formation and transport of methane in waterlogged country. Notation FlCHi is the methane flux across the atmosphere/water body interface F2CHi is the oxidation of methane in aerobic zones FCH is the intensity of the methane source M is methane concentration.
Hanor (1978) also discussed the mechanisms that may be responsible for degassing of groundwaters in the supratidal zone. His ranking of processes in order of probable importance was 1) tidally-induced oscillations of the groundwater table, 2) tidal pumping at the sediment-atmosphere interface, 3) a decrease in the average depth of the water table, and 4) a seaward increase in porosity. [Pg.314]

Fig, 35. Stages in the evolution of animals (after Fisher) I = animals live in total respiratory dependence on the number of plants the atmosphere is practically devoid of free oxygen. II = the atmosphere reaches the Pasteur point , animals can leave plants but seek water-air interface. Ill = the atmosphere and water contain a large amount of oxygen, animals are widespread. [Pg.96]

Because the mean pH of the today s ocean surface layer is about 8.08 (with a range from 7.9-8.25) (Raven et al, 2005), oceanic NH3 can exist as a dissolved, non-protonated gas and, thus, it is available for gas exchange across the ocean/ atmosphere interface. For example, for a pH of 8.1, a water temperature of 25°C, and a salinity of 35, about 6% is available as dissolved NH3, [NH3], (Fig. 2.8). The NH3/NH4 equilibrium is very sensitive to changes of the pH and water temperature. Changes in salinity and pressure are comparably less important (Fig. 2.8). [Pg.77]

Treating the wafer vapor and the air as Ideal gases and noting that the total atmospheric. pressure is the sum of the vapor and dry air pressures, the densities of the wat e vapor, dry air, and their mixture at the water-air interface and far from the sOfface are determined to be... [Pg.836]

Capillary Deformation. As water evaporates, curvature of the air-water interface causes a large negative capillary pressure in the water. Atmospheric pressure... [Pg.1453]

PCB inputs into aquatic and marine reservoirs are predominantly from wet and dry deposition and from the recycling of sediment-sorbed PCBs into the water column. Eisenreich et al. (1983) demonstrated for the Great Lakes water column that the concentration of PCBs is elevated at both the air/water and water/ sediment interfaces as a result of inputs from the atmosphere and sediments, respectively. In addition, Eisenreich et al. (1992) estimated that the upper Great Lakes receive the majority of the total inputs from... [Pg.538]

Aneja, V.P., B.P. Malik, Q. Tong, D. Kang, and J.H. Overton, Measurement and Modelling of ammonia emissions at waste treatment lagoon-atmospheric interface. Water, Air, and Soil Pollution, 1, 177-188, 2001d. [Pg.108]

Finally, life needs a redox contrast in order to function. Prior to photosynthesis it is likely that organisms would have occupied habitats where naturally occurring redox contrasts were present. Such conditions are likely to have been available in the atmosphere, where there is and has been, a mixture of oxidized and reduced gases, in the oceans, and at atmosphere-rock and sea-water-rock interfaces... [Pg.217]

Sources contributing to the composition of inorganic aerosols near the ocearir-atmosphere interface are the oceans themselves, continental dust, volcanic ash, atmospheric production of particulates, and, to lesser extents, human activity and extraterrestrial inputs. Characteristic elements and elemental ratios can be used to determine some of these sources and detect ion fractionation at the sea-air interface. Rain water chemistry is not always simply related to that of the marine aerosol. [Pg.17]


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Water atmosphere

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