Big Chemical Encyclopedia

Chemical substances, components, reactions, process design ...

Articles Figures Tables About

Concentrations in water

The main reason for the importance of aeration Hes in the limited solubiUty of oxygen in water, a value which decreases in the presence of electrolytes and other solutes and as temperature increases. A typical value for the solubiUty of oxygen (the equiUbrium saturation concentration) in water in the presence of air at atmospheric pressure at 25°C is about 0.008 kg 02/m (= Sparts per million = 0.25 mmol/L). Thus, for a yeast or bacterial bioreaction demanding oxygen at the rates given in Table 1, all oxygen is utilized in about 10 to 40 s (3,7). [Pg.331]

As httle as lO " g of ATP can be detected with carefiiUy purified luciferase. Commercial luciferase contains enough residual ATP to cause background emission and increase the detection limit to 10 g (294). The method has been used to determine bacterial concentrations in water. As few as lO" cells/mL of Lscherichia coli, which contains as Httle as 10 g of ATP per cell, can be detected (294). Numerous species of bacteria have been studied using this technique (293—295). [Pg.275]

A detailed review of the methods for deterrnination of low manganese concentration in water and waste is available (179). A review on the speciation of Mn in fresh waters has been reported (180). Reviews for the chemical analysis of Mn in seawater, soil and plants, and air are presented in References 181, 182, and 183, respectively. [Pg.524]

Other. A large variety of additives are used in paper-coatiag colors primarily to modify the physical properties of the colors (102). At high soHds concentrations in water, mineral pigment particles tend to associate and form viscous pastes. Dispersants (qv) are used to prevent this and to provide low viscosity slurries. Common dispersants include polyphosphates and sodium polyacrylate [9003-04-7]. Various water-soluble polymers are added to coatiag colors and act as water-retention agents and as rheology modifiers. [Pg.22]

AMP, AEPD, and AB are purified by distillation. TRIS AMINO and AMPD are purified by crystallization. TRIS AMINO concentrate in water (40% assay) is also available. [Pg.18]

Sucralose is quite stable to heat over a wide range of pH. However, the pure white dry powder, when stored at high temperature, can discolor owing to release of small quantities of HCl. This can be remedied by blending it with maltodextrin (93) and other diluents. The commercial product can be a powder or a 25% concentrate in water, buffered at pH 4.4. The latter solution may be stored for up to one year at 40°C. At lower pH, there is minimal decomposition. For example, in a pH 3.0 cola carbonated soft drink stored at 40°C, there is less than 10% decomposition after six months. The degradation products are reported to be the respective chlorinated monosaccharides, 4-chloro-4-deoxy-galactose (13) and l,6-dichloro-l,6-dideoxy-fmctose (14) (94). [Pg.279]

Component CAS Registry Number Molecular formula Concentration in water, wt % Freeze point depression, °C... [Pg.185]

The index i represents the type of ion and c is its concentration. In water, the ions have velocity wY-, giving the relation ... [Pg.34]

A major disadvantage of this system is the limitation of the single-pass gas-chlorination phase. Unless increased pressure is used, this equipment is unable to achieve higher concentrations of chlorine as an aid to a more complete and controllable reaction with the chlorite ion. The French have developed a variation of this process using a multiple-pass enrichment loop on the chlorinator to achieve a much higher concentration of chlorine and thereby quickly attain the optimum pH for maximum conversion to chlorine dioxide. By using a multiple-pass recirculation system, the chlorine solution concentrates to a level of 5-6 g/1. At this concentration, the pH of the solution reduces to 3.0 and thereby provides the low pH level necessary for efficient chlorine dioxide production. A single pass results in a chlorine concentration in water of about 1 g/1, which produces a pH of 4 to 5. If sodium chlorite solution is added at this pH, only about 60 percent yield of chlorine dioxide is achieved. The remainder is unreacted chlorine (in solution) and... [Pg.474]

The solubility coefficient S is used as a measure of water solubility. It is the ratio between the concentrations in water and air phases at equilibrium. Ethanol, a very soluble gas, has a solubility coefficient of 1 100 at, 37 C while the coefficient for nitrous oxide, a poorly soluble gas, is 0.1.5. [Pg.259]

The last term in Eq. (6-32) describes the temperature dependence of the molar concentration in water, this contributes only about —45 cal mol to E at room temperature. In a strong mineral acid solution, the temperature dependence of the activity coefficient term contributes about —90 cal mol . These are small quantities relative to the uncertainty in E s-... [Pg.256]

On-line LC-GC has frequently been used as a clean-up technique for the analysis of trace levels of contaminants (pesticides, plasticizers, dyestuffs and toxic organic chemicals) in water and food products. Several different approaches have been proposed for the analysis of contaminants by on-line LC-GC. Since pesticide residues occur at low concentration in water, soil or food, extraction and concentration is needed before GC analysis is carried out. [Pg.238]

The optical purities were determined solely from the optical rotations of the (/ -cyanohydrins thus obtained. Only for (/ )-a-hydroxybcnzeneacetonitrile, available from benzaldehyde, was an optical purity determined by comparison with the natural product. Variation of the reaction conditions (pH, temperature, concentration) in water/ethanol led to no appreciable improvementsl4. The use of organic solvents that are not miscible with water, but in which the enzyme-catalyzed reaction can still take place, resulted in suppression of the spontaneous addition to a significant extent, whereas the enzyme-catalyzed formation of cyanohydrins was only slightly slower (Figure l)13. [Pg.668]

However, we have to criticize more specifically the paper by Lown et al. (1984), who characterized alkanediazonium ions, as well as (E)- and (Z)-alkanediazoate ions, by 15N NMR spectroscopy. They also report NMR data on the (E)- and (Z)-benzenediazohydroxides as reference compounds, describing the way they obtained these compounds in only three lines. Obviously the authors are not familiar with the work on the complex system of acid-base equilibria which led 30 years earlier to the conclusion that the maximum equilibrium concentration of benzenediazohydroxide is less than 1 % of the stoichiometric concentration in water (see Ch. 5). The method of Lown et al. consists in adding 10% (v/v) water to a mixture of benzenediazonium chloride and KOH in dimethylsulfoxide. In the opinion of the present author it is unlikely that this procedure yields the (Z)- and CE>benzenediazohydroxides. Such a claim needs more detailed experimental evidence. [Pg.79]

For Pond 3513, the cycle of 2 3 8U and 239,2 °pu concentrations in water (filtered with a 0.22y membrane) is out of phase with the cycle of plutonium concentrations in Lake Michigan. In this shallow pond, the concentrations of the two actinides peak in summer and decline in winter. An explanation for this cycle of plutonium is that photosynthetic activity depletes dissolved CO2 which results in an increase in pH and this in turn shifts the oxidation state in favor of Pu(V) which is desorbed from the sediments(26). [Pg.304]

Surfactants have a unique long-chain molecular structure composed of a hydrophilic head and hydrophobic tail. Based on the nature of the hydrophilic part surfactants are generally categorized as anionic, non-ionic, cationic, and zwitter-ionic. They all have a natural tendency to adsorb at surfaces and interfaces when added in low concentration in water. Surfactant absorption/desorption at the vapor-liquid interface alters the surface tension, which decreases continually with increasing concentrations until the critical micelle concentration (CMC), at which micelles (colloid-sized clusters or aggregates of monomers) start to form is reached (Manglik et al. 2001 Hetsroni et al. 2003c). [Pg.65]

Concentrations in Water and Particles. In order to obtain the rates of reaction, the concentrations of the two monomers and the chain transfer agent in the water and polymer phases were calculated using equilibrium partition coefficients (H). ... [Pg.364]

By dynamic light scattering it was found that, in surfactant stabilized dispersions of nonaqueous polar solvents (glycerol, ethylene glycol, formamide) in iso-octane, the interactions between reversed micelles are more attractive than the ones observed in w/o microemulsions, Evidence of intermicellar clusters was obtained in all of these systems [262], Attractive intermicellar interactions become larger by increasing the urea concentration in water/AOT/ -hexane microemulsions at/ = 10 [263],... [Pg.495]

Poly(acrylic acid) is very soluble in water as are its copolymers with maleic and itaconic acids. Solutions of 50 % by mass are easily obtained. The isomer of PAA, poly(ethylene maleic acid), is not so soluble. However, solutions of PAA tend over a period of time to gel when their concentration in water approaches 50 % by mass (Crisp, Lewis Wilson, 1975) this is attributed to a slow increase in the number of intermolecular hydrogen bonds. Copolymers of acrylic acid and itaconic acid are more stable in solution and their use has been advocated by Crisp et al. (1975, 1980). [Pg.98]


See other pages where Concentrations in water is mentioned: [Pg.267]    [Pg.145]    [Pg.233]    [Pg.478]    [Pg.159]    [Pg.225]    [Pg.181]    [Pg.409]    [Pg.210]    [Pg.177]    [Pg.300]    [Pg.293]    [Pg.758]    [Pg.255]    [Pg.201]    [Pg.51]    [Pg.153]    [Pg.107]    [Pg.16]    [Pg.16]    [Pg.768]    [Pg.391]    [Pg.52]    [Pg.80]    [Pg.235]    [Pg.279]    [Pg.226]    [Pg.359]    [Pg.423]    [Pg.144]   
See also in sourсe #XX -- [ Pg.10 ]




SEARCH



Concentration in fresh water

Concentration in pore water from

Concentration in sea water

Concentration in water column

Concentrations of lead in water

Contaminant Concentrations Allowable in Drinking Water (Action Levels)

Copper concentration in, natural waters

Factors Determining the Lead Concentration in Drinking Water

Hydrogen ion concentrations, in water

Ion concentration in water

Water concentrate

Water concentration

Water concentration in solvent

Water structure and cavity formation in concentrated sugar solutions

© 2024 chempedia.info