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Water solids

FIG. 19-65 Schematic representation of air hubhle-water-solid particle system (a) before, (h) after particle-bubble attachment, and (c) equilibrium force balance. [Pg.1810]

Physical-Chemical Phenomena. Several physical-chemical phenomena occur when chemical reagents are added to an air-water solid system due to the interaction of the reagents with the air-water, water-sohd, and air-solid interfaces. This causes changes in the solution chemistry in which the particles are suspended. Some of the... [Pg.1810]

Liquid Dispersion Spray columns are used with slurries or when the reaction product is a solid. The absorption of SO9 by a hme slurry is an example. In the treatment of phosphate rock with sulfuric acid, offgases contain HF and SiF4. In a spray column with water, solid particles of fluorosilic acid are formed but do not harm the spray operation. The coefficient /cl in spray columns is about the same as in packed columns, but the spray interfacial area is much lower. Considerable backmixing of the gas also takes place, which helps to make the spray volumetri-caUy inefficient. Deentrainment at the outlet usually is needed. [Pg.2115]

Chemical Reactivity - Reactivity with Water Solid has very slow reaction no hazard. Liquid spatters when in contact with water Reactivity with Common Materials No reaction Stability During Transport Stable Neutralizing Agents for Acids and Caustics Water and sodium bicarbonate Polymerization Not pertinent Inhibitor of Polymerization Not pertinent. [Pg.319]

The Agency s mission is to control and abate pollution in the areas of air, water, solid waste, pesticides, radiation, and toxic substances. The EPA coordinates and supports research and anti-pollution activities by state and local governments, private and public groups, individuals, and educational institutions. [Pg.288]

Fig, 1. Ultraviolet spectrum of quiuazoline in water. Solid line, neutral molecule dotted line, cation. [Pg.256]

Fig. 2. (A) Ultraviolet spectra of quinazoline in water. Solid line, neutral species dotted line, cation. (B) Ultraviolet spectra of 4-methylquinazoline in water. Solid line, neutral species dotted line, cation. Fig. 2. (A) Ultraviolet spectra of quinazoline in water. Solid line, neutral species dotted line, cation. (B) Ultraviolet spectra of 4-methylquinazoline in water. Solid line, neutral species dotted line, cation.
Environmental Protection Agency regulations related to air, water, solid waste, and land contamination with toxic substances that a plant might emit/release into immediate plant area, or discharge as waste into public streams, or inject into underground aquafiers, or dump or store [29, 30, 31]. [Pg.33]

Water Solid (snow, ice), liquid (rain, condensation, standing water), vapour (relative humidity). Rain, hail, sleet or snow may have physical effects... [Pg.402]

Example 5.3 Predict the degrees of freedom for (a) pure liquid water and solid ice in equilibrium (b) pure liquid water, solid ice, and water vapor in equilibrium, and (c) solid ice in equilibrium with a liquid mixture of (ethanol + water). [Pg.238]

Most gases are more soluble in warm water than in cold water solids show a more varied behavior. [Pg.444]

Fig. 3. Radial profiles of the bubble size with Fig. 4. Influence of internals on the gas holdup different gas distributors (air-water system) [22]. (air-water-solid slurry system) [23]. Fig. 3. Radial profiles of the bubble size with Fig. 4. Influence of internals on the gas holdup different gas distributors (air-water system) [22]. (air-water-solid slurry system) [23].
Abdelrazig, Sharp El-Jazairi (1988, 1989) prepared a series of mortars based on a powder blend of MgO and ADP with a quartz sand filler. They were hydrated by mixing with water. A mortar I (MgO ADP silica water = 17T 12-9 70-0 12-5), with a water/solid ratio of 1 8, formed a workable paste which set in 7 minutes with evolution of ammonia. The main hydration product, struvite, was formed in appreciable amounts within 5 minutes and continued to increase. Schertelite also appeared, but only in minor amounts, within the first 5 minutes and persisted only during the first hour of the reaction. Dittmarite appeared in minor amounts after 15 minutes, and persisted. [Pg.227]

Fig. 2.4. Relation between the Cs+ and Cl concentrations of geothermal waters. Solid lines 1 and 2 indicate the equilibrium condition between feldspars and solution, assuming that the Cs content of the feldspar is between 10 wt% and 10 wt%. For symbols used, see caption to Fig. 2.2 (Shikazono, 1978a). Fig. 2.4. Relation between the Cs+ and Cl concentrations of geothermal waters. Solid lines 1 and 2 indicate the equilibrium condition between feldspars and solution, assuming that the Cs content of the feldspar is between 10 wt% and 10 wt%. For symbols used, see caption to Fig. 2.2 (Shikazono, 1978a).
Fig. 2.39. Na /K+ atomic ratios of well discharges plotted at measured downhole temperatures. Curve A is the least squares fit of the data points above 80°C. Curve B is another emperical curve (from Truesdell, 1976). Curves C and D show the approximate locations of the low albite-microcline and high albite-sanidine lines derived from thermodynamic data (from Fournier, 1981). Small solid subaerial geothermal water Solid square Okinawa Jade Open square South Mariana Through Solid circle East Pacific Rise 11°N Open circle Mid Atlantic Ridge, TAG. Fig. 2.39. Na /K+ atomic ratios of well discharges plotted at measured downhole temperatures. Curve A is the least squares fit of the data points above 80°C. Curve B is another emperical curve (from Truesdell, 1976). Curves C and D show the approximate locations of the low albite-microcline and high albite-sanidine lines derived from thermodynamic data (from Fournier, 1981). Small solid subaerial geothermal water Solid square Okinawa Jade Open square South Mariana Through Solid circle East Pacific Rise 11°N Open circle Mid Atlantic Ridge, TAG.
Very finely disperse solids, which are adsorbed at the liquid/liquid interfaces, forming films of particles around the disperse globules. Certain powders can very effectively stabilize against coalescence. The solid s particle size must be very small compared with the emulsion droplet size and must exhibit an appropriate angle of contact at the three-phase (oil/water/solid) boundary [141]. [Pg.269]

Figure 5.7 Comparison of liposome-water (solid lines) to octanol-water (dashed lines) lipophilicity profiles for a weak acid, a weak base, and an ampholyte. [Avdeef, A., Curr. Topics Med. Chem., 1, 277-351 (2001). Reproduced with permission from Bentham Science Publishers, Ltd.]... Figure 5.7 Comparison of liposome-water (solid lines) to octanol-water (dashed lines) lipophilicity profiles for a weak acid, a weak base, and an ampholyte. [Avdeef, A., Curr. Topics Med. Chem., 1, 277-351 (2001). Reproduced with permission from Bentham Science Publishers, Ltd.]...
Most of the pollutants may be effectively removed by precipitation of metal hydroxides or carbonates using a reaction with lime, sodium hydroxide, or sodium carbonate. For some, improved removals are provided by the use of sodium sulfide or ferrous sulfide to precipitate the pollutants as sulfide compounds with very low solubilities. After soluble metals are precipitated as insoluble floes, one of the water-solid separators (such as dissolved air flotation, sedimentation, centrifugation, membrane filtration, and so on) can be used for floes removal.911 The effectiveness of pollutant removal by several different precipitation methods is summarized in Tables 5.15-5.17. [Pg.220]

In its simplest form a partitioning model evaluates the distribution of a chemical between environmental compartments based on the thermodynamics of the system. The chemical will interact with its environment and tend to reach an equilibrium state among compartments. Hamaker(l) first used such an approach in attempting to calculate the percent of a chemical in the soil air in an air, water, solids soil system. The relationships between compartments were chemical equilibrium constants between the water and soil (soil partition coefficient) and between the water and air (Henry s Law constant). This model, as is true with all models of this type, assumes that all compartments are well mixed, at equilibrium, and are homogeneous. At this level the rates of movement between compartments and degradation rates within compartments are not considered. [Pg.106]

Fig. 3. Circular dichroism at 15°C in water (solid line) and in 6 M sodium perchlorate (dashed line), (a) Ac-Ala-NHMe. (b) cyclo (-Ala-Ala-). (c) Ac-Ala-OMe. (d) Ac-Ala-Ala-OMe. (e) Ac-Ala-Ala-Ala-OMe. From Mattice (1974), Biopolymers 13, 169-183, 1974. Reprinted by permission of John Wiley 8c Sons, Inc. Fig. 3. Circular dichroism at 15°C in water (solid line) and in 6 M sodium perchlorate (dashed line), (a) Ac-Ala-NHMe. (b) cyclo (-Ala-Ala-). (c) Ac-Ala-OMe. (d) Ac-Ala-Ala-OMe. (e) Ac-Ala-Ala-Ala-OMe. From Mattice (1974), Biopolymers 13, 169-183, 1974. Reprinted by permission of John Wiley 8c Sons, Inc.
When Plaster of Paris, CaSC>4 5H2O (s), is mixed with water, solid gypsum, CaS04- 2 H2O (s), is formed in an exothermic reaction, that is, a heat-releasing reaction. Thus, as the cast hardens, the plaster cast becomes warm ... [Pg.133]

Maintenance of constant relative humidity environments is essential for studying water-solid interactions. There are primarily four techniques that are frequently employed to maintain constant relative humidity ... [Pg.395]


See other pages where Water solids is mentioned: [Pg.7]    [Pg.1810]    [Pg.1810]    [Pg.124]    [Pg.1120]    [Pg.681]    [Pg.62]    [Pg.70]    [Pg.203]    [Pg.801]    [Pg.867]    [Pg.963]    [Pg.344]    [Pg.229]    [Pg.230]    [Pg.57]    [Pg.260]    [Pg.284]    [Pg.1157]    [Pg.378]    [Pg.45]    [Pg.293]    [Pg.388]    [Pg.389]    [Pg.391]   
See also in sourсe #XX -- [ Pg.64 , Pg.67 , Pg.68 ]




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Amorphous solids water

Amorphous solids water vapor absorption

Amorphous solids, water sorption

Amorphous systems water-solid interactions

Bottom solids and water

Card room water, solids

Dissolution of Ionic Solids in Water

Dissolved solids, produced water

Dissolved solids, produced water treatment

Dissolved solids, produced water types

Equilibrium-partitioning coefficient water-solid

Feed water quality system design total dissolved solids

Feed water quality total dissolved solids

Glass transition temperatures water-solid interactions

Heats of Hydration Ionic Solids in Water

Hydrogen Bonding Patterns, Water Uptake, and Distribution in Amorphous Solids

Ionic solids in water

Liquid phase preparation, amorphous solid water

Near solid phase water

Partitioning, solid-water

Perspectives in Using Solid Catalysts for the Treatment of Water

Pharmaceutical solids water sorption

Pressurized water reactors solid waste processing

Probing water-solid interactions

Produced water treatment precipitated solids

Produced water treatment solids

Pure Water—Solid Polymer Electrolyte Systems

Ratio, solid/water

Reorientation water-solid interactions

Rugosities and Stability of Air-Water-Solid Films

Saturated Water Solid-Vapor

Soil Colloids and Water-Suspended Solids

Solid adsorbents water

Solid electrolyte water electrolyser

Solid pesticides water-dispersible granule

Solid phase extraction separating herbicides from water

Solid phase extraction water partitioning

Solid phase organic carbon-water partition

Solid phase organic carbon-water partition phases

Solid solution water interlayer

Solid state fermentation water activity

Solid surfactant-water systems, alkyl

Solid waste form, ground-water

Solid wastes water-soluble polymers

Solid water affinity

Solid water brittle fracture

Solid water crystallization

Solid water desorption

Solid water dielectric relaxation

Solid water hydrogen-filled

Solid water ionization

Solid water irradiated

Solid water radical chemistry

Solid water treatment process monitoring

Solid-phase extractions water-soluble organic matter

Solid-to-water phase ratio

Solid-water distribution coefficient

Solid-water distribution coefficient compound

Solid-water interface

Solid-water partition coefficient

Solids, in fresh water

Solids, water solubility

Solubility of solid substances in water

Solutions of Solids Dissolved in Water How to Make Rock Candy

Sucrose water-solid interactions

Surface Between Water and a Solid

Surfaces solid-water interface

Testing Unknown Solids with Water

The Density of Solid and Liquid Water

Use of Solid Catalysts in Promoting Water Treatment and Remediation Technologies

Vicinal water solid interface

Water Issue and the Role of Solid Catalysis in Promoting New Technologies

Water Retention Properties of Solid Foods

Water Sorbed Onto Solids

Water dissolved solids

Water in solids

Water in the Solid State

Water in the solid phase ices

Water interaction with solids

Water liquid versus solid

Water of crystallization, aquo complexes and solid hydrates

Water quality guidelines suspended solids

Water release from solid

Water solid phase preparation

Water solid states

Water solid, irradiation

Water solid-phase extraction

Water solid-state structure

Water solids determination

Water sorption, crystalline solids

Water testing solids measurements

Water transfer between solid components

Water transport, liquid-solid systems

Water transport, liquid-solid systems drying

Water-free and high solid finishing formulations

Water-insoluble solids

Water-reactive solid

Water-solid interactions

Water-solid interactions amorphous polymer systems

Water-solid interactions determination ways

Water-solid interactions measurement

Water-solid interactions mechanisms

Water-solid interactions mixture solution

Water-solid interactions relative humidity

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