Big Chemical Encyclopedia

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

Articles Figures Tables About

Alkalinity, water

Most water analysis results are rather easily interpreted. However, two simple and useful tests need explanation. These are the P and M alkalinity. The water is titrated with N/30 HCl to the phenolphthalein end point at pH 8.3. This is called the P alkalinity. Similar titration to the methyl orange end point at pH 4.3 is called the M alkalinity. They are reported as ppm CaCO,. [Pg.145]

This applies to waters having alkalinity caused by one or all of the followina  [Pg.145]

In natural waters, the alkalinity is usually caused by bicarbonate. Carbonate or hydroxide is rarely encountered in untreated water. The M alkalinity equals the sum of all three forms of alkalinity. The P alkalinity equals A the [Pg.145]

Branan, C. R., The Process Engineer s Pocket Elandbook, Vol. 1, Gulf Publishing Co., 1976. [Pg.145]


In water pollution studies, the oxygen content can be measured by making the water alkaline and shaking a measured volume with an oxygen-free solution containing Mn- (aq). The solution is acidified with sulphuric acid, potassium iodide added and the liberated iodine titrated with sodium thiosulphate. [Pg.389]

The alkalinity is determined by titration of the sample with a standard acid (sulfuric or hydrochloric) to a definite pH. If the initial sample pH is >8.3, the titration curve has two inflection points reflecting the conversion of carbonate ion to bicarbonate ion and finally to carbonic acid (H2CO2). A sample with an initial pH <8.3 only exhibits one inflection point corresponding to conversion of bicarbonate to carbonic acid. Since most natural-water alkalinity is governed by the carbonate—bicarbonate ion equiUbria, the alkalinity titration is often used to estimate their concentrations. [Pg.230]

Table 1 Hsts a number of common inorganic coagulants. Typical iron and aluminum coagulants are acid salts that lower the pH of the treated water by hydrolysis. Depending on initial raw water alkalinity and pH, an alkah such as lime or caustic must be added to counteract the pH depression of the primary coagulant. Iron and aluminum hydrolysis products play a significant role in the coagulation process, especially in cases in which low turbidity influent waters benefit from the presence of additional colHsion surface areas. Table 1 Hsts a number of common inorganic coagulants. Typical iron and aluminum coagulants are acid salts that lower the pH of the treated water by hydrolysis. Depending on initial raw water alkalinity and pH, an alkah such as lime or caustic must be added to counteract the pH depression of the primary coagulant. Iron and aluminum hydrolysis products play a significant role in the coagulation process, especially in cases in which low turbidity influent waters benefit from the presence of additional colHsion surface areas.
Alkalinity Reduction. Treatment by lime precipitation reduces alkalinity. However, if the raw water alkalinity exceeds the total hardness, sodium bicarbonate alkalinity is present. In such cases, it is usually necessary to reduce treated water alkalinity in order to reduce condensate system corrosion or permit increased cycles of concentration. [Pg.260]

MetaUic arsenic is not readily attacked by water, alkaline solutions, or nonoxidizing acids. It reacts with concentrated nitric acid to form orthoarsenic acid [7778-39-4] H AsO. Hydrochloric acid attacks arsenic only in the presence of an oxidant. [Pg.326]

Water. The character of the water has a great influence on the character of the beer and the hardness of water (alkalinity) manifests itself by the extent of its reaction with the weak acids of the mash. Certain ions are harm fill to brewing nitrates slow down fermentation, iron destroys the colloidal stabihty of beer, and calcium ions give beer a purer flavor than magnesium or sodium ions (Table 7). [Pg.17]

Chemical Treatment. The most iavolved regeneration technique is chemical treatment (20) which often follows thermal or physical treatment, after the char and particulate matter has been removed. Acid solution soaks, glacial acetic acid, and oxalic acid are often used. The bed is then tinsed with water, lanced with air, and dried ia air. More iavolved is use of an alkaline solution such as potassium hydroxide, or the combination of acid washes and alkaline washes. The most complex treatment is a combination of water, alkaline, and acid washes followed by air lancing and dryiag. The catalyst should not be appreciably degraded by the particular chemical treatment used. [Pg.509]

Environment Treated cooling water, alkaline program, pH 8.5-9.5, 50-105°F (10 0°C), total hardness 150 ppm, chlorides 70 ppm, calcium 90 ppm... [Pg.367]

Calcium hydroxide (Ca(OH)2 (slaked lime) ) White powder soluble in water yielding lime water. Alkaline... [Pg.28]

S< o Ni) caustic alkalis halogenated in water- (alkaline freedom from ... [Pg.796]

It has been found that red lead, litharge and certain grades of metallic lead powder render water alkaline and inhibitive this observation has been confirmed by Pryor . The effect is probably due to a lead compound, e.g. lead hydroxide, in solution. Since, however, atmospheric carbon dioxide converts these lead compounds into insoluble basic lead carbonate, thereby removing the inhibitive materials from solution, these pigments may have only limited inhibitive properties in the absence of soap formation. [Pg.596]

Where high residual calcium leakage occurs in the FW, the phosphate reserve is lost and the boiler water alkalinity is reduced. This is not the same problem as hideout, which is the apparent loss ofBWphosphate and other salts in higher pressure WT power boilers operating under high load conditions. [Pg.235]

Where the natural MU water alkalinity is particularly high, the overall FW alkalinity may be reduced somewhat by the use of sodium bisulfite, rather than sulfite. Combinations of sulfite and bisulfite (usually with some caustic) produce a range of concentrations and formulation pH levels, generally within the range of 4 to 9. [Pg.488]

The elements Na, K, Cl, SO, Br, B, and F are the most conservative major elements. No significant variations in the ratios of these elements to chlorine have been demonstrated. Strontium has a small (< 0.5%) depletion in the euphotic zone (Brass and Turekian, 1974) possibly due to the plankton Acantharia, which makes its shell from SrS04 (celestite). Calcium has been known since the 19th century to be about 0.5% enriched in the deep sea relative to surface waters. Alkalinity (HCOf") also shows a deep enrichment. These elements are controlled by the formation... [Pg.259]

Sodium hydroxide (NaOH) (caustic soda) Potassium hydroxide (KOH) (caustic potash) Calcium hydroxide (Ca(OH)2) (slaked lime) Ammonium hydroxide (NH4OH) (aqueous ammonia solution) White deliquescent solid. Sticks, flakes, pellets. Dissolution in water is highly exothermic. Strongly basic. Severe hazard to skin tissue White deliquescent solid. Sticks, flakes, pellets. Dissolution In water is highly exothermic. Strongly basic. Severe hazard to skin tissue White powder soluble in water yielding lime water. Alkaline Weakly alkaline. Emits ammonia gas. Severe eye irritant... [Pg.28]

Of the 20 residues that react with A-ethylmaleimide in the non-reduced denatured Ca -ATPase at least 15 are available for reaction with various SH reagents in the native enzyme [75,239,310]. These residues are all exposed on the cytoplasmic surface. After reaction of these SH groups with Hg-phenyl azoferritin, tightly packed ferritin particles can be seen by electron microscopy only on the outer surface of the sarcoplasmic reticulum vesicles [143,311-314]. Even after the vesicles were ruptured by sonication, aging, or exposure to distilled water, alkaline solutions or oleate, the asymmetric localization of the ferritin particles on the outer surface was preserved [311,313,314]. [Pg.91]

Organism and Exposure Period (days) Water Alkalinity, (mg CaC03/L) MATC, (pg Cd/L)... [Pg.55]

Prause et al. 1985). At pH 6.5 and water alkalinity of 25 mg CaC03/L, elemental Pb+2 is soluble to 330 pg/L however, Pb+2 under the same conditions is soluble to 1000 pg/L (Demayo et al. 1982). In acidic waters, the common forms of dissolved lead are salts of PbS04 and PbCl4, ionic lead, cationic forms of lead hydroxide, and (to a lesser extent) the ordinary hydroxide Pb(OH)2. In alkaline waters, common species include the anionic forms of lead carbonate and hydroxide, and the hydroxide species present in acidic waters (NRCC 1973). Unfortunately, the little direct information available about the speciation of lead in natural aqueous solutions has seriously limited our understanding of lead transport and removal mechanisms (Nriagu 1978a). [Pg.241]

Water Alkaline Neutral amm. amm. citrate Citric Formic citrate (Petermann acid 2% acid (Fresenius) or Joulie) (Wagner) 2% ... [Pg.113]

Additive or more-than-additive toxicity of free cyanide to aquatic fauna has been reported in combination with ammonia (Smith et al. 1979 Leduc et al. 1982 Alabaster et al. 1983 Leduc 1984) or arsenic (Leduc 1984). However, conflicting reports on the toxicity of mixtures of HCN with zinc or chromium (Towill et al. 1978 Smith et al. 1979 Leduc et al. 1982 Leduc 1984) require clarification. Formation of the nickelocyanide complex markedly reduces the toxicity of both cyanide and nickel at high concentrations in alkaline pH. At lower concentrations and acidic pH, solutions increase in toxicity by more than 1000-fold, owing to dissociation of the metallo-cyanide complex to form hydrogen cyanide (Towill et al. 1978). Mixtures of cyanide and ammonia may interfere with seaward migration of Atlantic salmon smolts under conditions of low dissolved oxygen (Alabaster et al. 1983). The 96-h toxicity of mixtures of sodium cyanide and nickel sulfate to fathead minnows is influenced by water alkalinity and pH. Toxicity decreased with increasing alkalinity and pH from 0.42 mg CN/L at 5 mg CaCOj/L and pH 6.5, to 1.4 mg CN/L at 70 mg CaCOj/L and pH 7.5 to 730 mg CN/L at 192 mg CaCOj/L and pH 8.0 (Doudoroff 1956). [Pg.930]

Alkalinity and hardness (dissolved Ca24 and Mg2+, Box 12-3) are important characteristics of irrigation water. Alkalinity in excess of the Ca2+ + Mg2+ content is called residual sodium carbonate. " Water with a residual sodium carbonate content equivalent to 2.5 mmol H+/L is not suitable for irrigation. Residual sodium carbonate between 1.25 and 2.5 mmol H+/L is marginal, whereas si.25 mmol H+/L is suitable for irrigation. [Pg.209]

High boiler-water alkalinity tends to increase carryover, particularly in the presence of an appreciable quantity of suspended matter. This effect may be corrected by various methods, dependent on the cause of the high alkalinity. For example, if trisodium phosphate is being added to the boiler water, a less alkaline phosphate, such as disodium or monosodium phosphate will help in reducing alkalinity. [Pg.1744]

One more method of determining the form of the function f(R) is based on approximating the experimental kinetics with the help of some equation. For example, the kinetics of the trapped electrons decay with respect to the reaction with anion radicals O in the irradiated water alkaline matrices (see Chap. 6, Sect. 2.2) is well described by the equation... [Pg.153]


See other pages where Alkalinity, water is mentioned: [Pg.180]    [Pg.138]    [Pg.145]    [Pg.148]    [Pg.552]    [Pg.154]    [Pg.546]    [Pg.713]    [Pg.777]    [Pg.801]    [Pg.200]    [Pg.116]    [Pg.252]    [Pg.930]    [Pg.103]    [Pg.274]    [Pg.252]    [Pg.3]    [Pg.126]    [Pg.158]    [Pg.162]   
See also in sourсe #XX -- [ Pg.2 , Pg.49 ]

See also in sourсe #XX -- [ Pg.198 ]

See also in sourсe #XX -- [ Pg.160 ]

See also in sourсe #XX -- [ Pg.47 ]

See also in sourсe #XX -- [ Pg.361 ]

See also in sourсe #XX -- [ Pg.2 , Pg.49 ]




SEARCH



Alkaline water

© 2024 chempedia.info