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Total dissolved solids concentration

The density of the leachate is a function of the temperature and the concentration of dissolved solids. Leachate with a total dissolved solid concentration of 2 X lO mgL is not uncommon (see Table 1) the density of such a leachate is >1% higher than the groundwater density. Density differences may significantly affect the vertical positioning of the plume just below the landfill. Field observations on the downward movement of the plume are often difficult to separate from the effect of local water table mounds (Christensen et al., 2001). A better understanding of the effects of higher leachate densities in field situations is needed. Density effects could be the major cause of vertical leachate spreading in aquifers since normal vertical dispersion is usually very small. [Pg.5119]

FIGURE 4.1 Total dissolved solids concentration (by analysis) versus specific conductance, shown by Gila River (Bylas, Arizona) water samples taken over a I-year period. (Reprinted from Hem [21].)... [Pg.112]

An initial state in the past was assumed as the total dissolved solids concentration in the lower water mass C = 327 grams/liter, as at present in the upper water mass it was taken as CM = 100 grams/liter. The time from the initial state to a complete homogenization of the water column was computed as follows. [Pg.52]

In the condition of sanitary-chemical laboratory and the bacteriologic one of National Scientific and Practical Center of Preventive Medicine and Municipal Center of Preventive Medicine Chisinau after the standardized methods there was accomplished the sample analysis of water from aqueducts, the well from Chisinau and suburbs as well. There were determined the following indicators turbidity, ammonia, nitrite, nitrate, total dissolved solid, concentration of fluoride, hardness, content of calcium, magnesium, K+Na, chloride, sulfate, carbohydrate, iron, NTG, coliform bacterium. [Pg.448]

Total dissolved solids concentration. Concentration of particular species. Alkalinity/acidity defined as fi-ee alkali (e.g. carbonate) fi ee acid (e.g. sulphuric) mg/l respectively. pH. [Pg.298]

Guarantees for achieving the prescribed quality of the treated effluent (which must meet the standards set by Statutory Pollution Control Authorities wherein the pH, maximum TDS—total dissolved solid concentration, minimum dissolved oxygen, and maximum permissible concentration of heavy metals, chlorides, nitrates, and sulphates are given). [Pg.141]

A question that some students ask is why, while water is not an electrical conductor, it is dangerous to expose damp hands or in general a damp body, to mains electricity, for example in a bathroom. The explanation is that dry skin has a resistance of 100 000 ohms or more, while wet skin may have a resistance of only 1000 ohms. Such a low resistance of the wet skin allows current to pass into the body more easily and give a greater electric shock. Note also that pure water should be contrasted with natural water (such as tap water), which has various substances dissolved in it, among which are electrolytes. Hence natural water has some electric conductivity, which depends on the concentration of the water in various electrolytes. Electrical conductivity measurements of natural waters are used to predict the salinity, major solute concentrations, and total dissolved solids concentrations of natural waters. [Pg.258]

All geological materials can be dissolved quantitatively, and there is an extensive literature on the various processes available. The choice of dissolution procedure will vary according to the nature of the sample, the number and size of the samples, the requirements of the analytical technique in terms of analyte concentration and total dissolved solid concentration, volatility of the analytes of interest, precision and accuracy required, contamination from... [Pg.1987]

Seawater Source Total Dissolved Solids Concentration (mg/L) Temperature (°C)... [Pg.49]

TDS Total dissolved solids, expressed as ppm (parts per million) or as mg/1 (milligrams per liter). Evaporate the water from a sample and the residue can be weighed. TSS Total suspended solids expressed in similar terms to TDS but representing a concentration of insoluble particles. [Pg.529]

An important assumption was that the solution was dilute (in this case natural water of approximately lOOp.p.m. total dissolved solids) since there are difficulties in applying mass transport equations for certain situations in concentrated electrolyte solution, where a knowledge of activities is uncertain and this can lead to large errors. [Pg.321]

The effect of water salinity on crop growth is largely of osmotic nature. Osmotic pressure is related to the total salt concentration rather than the concentration of individual ionic elements. Salinity is commonly expressed as the electric conductivity of the irrigation water. Salt concentration can be determined by Total Dissolved Solids (TDS) or by Electrical Conductivity (EC). Under a water scarcity condition, salt tolerance of agricultural crops will be the primordial parameter when the quality of irrigation water is implicated for the integrated water resources management [10]. [Pg.164]

Fig. 2.8. Relation between the Ca and CR concentrations of geothermal waters and inclusion fluids. Solid lines indicate (1) albite-K-feldspar-muscovite-quartz-caleite-solution equilibrium at OHaCOs = 10 (2) albite-K-feldspar-muscovite-quartz-calcite-solution equilibriumn at oh2C03 = 10 (3) anhydrite-solution at SSo (total dissolved sulfate concentration) = 10 and (4) anhydrite-solution equilibrium at SSq = 10. For symbols used see caption to Fig. 2.2 (Shikazono, 1978a). Fig. 2.8. Relation between the Ca and CR concentrations of geothermal waters and inclusion fluids. Solid lines indicate (1) albite-K-feldspar-muscovite-quartz-caleite-solution equilibrium at OHaCOs = 10 (2) albite-K-feldspar-muscovite-quartz-calcite-solution equilibriumn at oh2C03 = 10 (3) anhydrite-solution at SSo (total dissolved sulfate concentration) = 10 and (4) anhydrite-solution equilibrium at SSq = 10. For symbols used see caption to Fig. 2.2 (Shikazono, 1978a).
The Okuaizu geothermal system is characterized by high temperatures (maximum 340°C), high salinity (about 2 wt% total dissolved solids (TDS)) and large amounts of non-condensable gases (1 wt% CO2 and 200 ppm H2S). The pH of the hydrothermal solution measured at 25°C is 6.44 (Table 2.6). However, the pH of the original fluid in the reservoir is computed to be 4.05. This pH as well as alkali and alkali earth element concentrations are plotted near the equilibrium curve of albite, K-mica, anhydrite and calcite (Fig. 2.19) (Seki, 1991). [Pg.318]

Applications RO is primarily used for water purification seawater desalination (35,000 to 50,000 mg/L salt, 5.6 to 10.5 MPa operation), brackish water treatment (5000 to 10,000 mg/L, 1.4 to 4.2 MPa operation), and low-pressure RO (LPRO) (500 mg/L, 0.3 to 1.4 MPa operation). A list of U.S. plants can be found at www2.hawaii.edu, and a 26 Ggal/yr desalination plant is under construction in Ashkelon, Israel. Purified water product is recovered as permeate while the concentrated retentate is discarded as waste. Drinking water specifications of total dissolved solids (TDS) < 500 mg/L are published by the U.S. EPA and of < 1500 mg/L by the WHO [Williams et ak, chap. 24 in Membrane Handbook, Ho and Sirkar (eds.). Van Nostrand, New York, 1992]. Application of RO to drinking water is summarized in Eisenberg and Middlebrooks (Reverse Osmosis Treatment of Drinking Water, Butterworth, Boston, 1986). [Pg.45]

Salinity is defined as the concentration of total dissolved solids (TDS) in a solution, usually expressed in mg/L. The TDS concentration in water is usually determined from the weight of the dry residue remaining after evaporation of the volatile portion of the original solution. Groundwater may be classified into four salinity classes64 ... [Pg.809]

The methods presented so far are adequate for single contaminants (e.g. total solids, suspended solids, total dissolved solids, organic concentration, etc), but it is often required to deal with problems in which the concentration limits require multiple contaminants to be specified. Consider the problem in Table 26.7 involving two operations. [Pg.604]

Here, we define the total dissolved solids (in mg kg-1) for early releases of the REACT program (GWB 6.0 and previous), so the software can correctly convert our input constraints from mg kg-1 to molal units, as carried internally (i.e., variables nii and m.j). The print command causes the program to list in the output all of the aqueous species, not just those in greatest concentration. Typing go triggers the model to begin calculations and write its results to the output dataset. [Pg.84]

Rain Lake Fti jOr GrOuml Water Water Water Water Fig. 1. Typical total dissolved solid (TDS) concentrations (mg/L) in terrestrial waters (from various sources listed in Hamilton et al. 2007). [Pg.92]

The composition of pore water was similar in reduced and oxidized tailings with low pH (>1.8) and high total dissolved solids ( 300 g/L) at the surface, and neutral pH and lower dissolved solids with depth. In general, pH values were lower and dissolved metal concentrations higher in... [Pg.349]

The concentrations of seawater and brackish water can vary significantly, and as such there is a difference between the concentrate produced from seawater desalination plants and brackish water desahnation plants. Seawater typically has a level of total dissolved solids (TDS) between 33,000-37,000 mg/L. The average major ion concentration of seawater is shown in Table 2.1 along with water from the Mediterranean Sea, and water from Wonthaggi off the southern coast of Australia. Seawater sahnity increases in areas where water evaporates or freezes, and it decreases due to rain, river runoff, and melting ice. The areas of greatest salinity occur and latitudes of 30° N and S where there are high evaporation rates. [Pg.14]

In Figure 5.1, the fraction of iron whose concentration is being reported is identified as the total dissolved iron concentration. In practice, this fraction is operationally defined by the analytical method used in its measurement. For the data in Figure 5.1, the total dissolved iron concentration was determined by filtration to remove the solid iron, followed by colorimetric analysis to quantify the solutes. Another analytical technique, such as filtration followed by atomic absorption spectrophotometry, might yield a different total dissolved concentration, so it is important to be aware of the analytical methods used. To address this issue, marine chemists engage in intercalibration experiments to assess differences in results from various analytical methods. [Pg.104]

Concentration ([ji.mol/L) Runoff (x10 moi/y) % Contribution by Mass to Totai Dissoived Soiids Concentration ((jtmol/L) Inventory (X10 mol) % Contribution by Mass to Total Dissolved Solids [Seawater] [Riverwater] ... [Pg.538]

Salinity, or total salt concentration, is usually expressed in terms of total dissolved solids (TDS) or as the electrical conductivity (EC) of the solution. The major fractions of anions are composed of Cl", SO , and NOj" and the common cations are Ca ", Mg +, Na, and K. The composition of the snbsnrface solution varies between the composition of water entering the system and that of the solution in equilibrinm with the solid phase. [Pg.21]


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