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Particle detachment during hydraulic shock loads in granular media filtration.

Particle breakthrough can occur by either the breakoff of previously captured particles (or flocs) or the direct passage of some influent particles through the filter. Filtration experiments were performed in a laboratory-scale filter using spherical glass beads with a diameter of 0.55 mm as collectors. A single type of particle suspension (Min-U-Sil 5) and three different destabilisation methods (pH control, alum and polymer destabilisation) were used to destabilise particles. The filtration velocity of 5 m/h was similar to that used in standard media filtration practice. To assess the possibility of particle detachment during normal filtration, a hydraulic shock load (20% increase of flow rate) was applied after 4 h of normal filtration. The magnitude of particle detachment was proportional to the particle size for non-Brownian particles. At the same time, less favourable particles, i.e. particles with larger surface charge, were easily detached during the hydraulic shock load. Therefore, proper particle destabilisation before filtration is crucial for maximum particle removal, as well as minimum particle breakthrough.

Alum Compounds↗

Removal of boron (B) from waste liquors.

This paper explores the use of electrocoagulation to remove boron from waste effluent in comparison with alum coagulation. In treating model test wastes, greater boron removals were achieved with electrocoagulation at low doses than conventional alum coagulation when reaction was undertaken for the same conditions (pH 8.5, and initial boron concentration was 500 mg/L). Al electrocoagulation can achieve good boron removal performance (68.3%) at a dose of 2.1 (as molar ratio of Al:B, and for current density of 62.1 A/m2), while alum coagulation can only achieve the maximum boron removal of 56% at a dose of 2.4. Also, Al electrocoagulation can remove 15-20% more boron than alum coagulation for the same dose compared in the treatment of both model test wastes and industry effluent. The estimation of running costs shows that to achieve 75% boron removal from industry waste effluent, i.e. removing 150 g of boron from 1 m3 of effluent, electrocoagulation was 6.2 times cheaper than alum coagulation. The economic advantage of electrocoagulation in the treatment of boron-containing waste effluent is thus significant.

Alum Compounds↗

Dewatered alum sludge: a potential adsorbent for phosphorus removal.

Alum sludge refers to the by-product from the processing of drinking water in water treatment works. In this study, groups of batch experiments were designed to identify the characteristics of dewatered alum sludge for phosphorus adsorption. Air-dried alum sludge (moisture content 10.2%), which was collected from a water treatment works in Dublin, was subjected to artificial P-rich wastewater adsorption tests using KH2PO4 as a model P source. Adsorption behaviours were investigated as a function of amount and particle size of alum sludge, pH of solution and adsorption time. The results have shown that pH plays a major role not only in the adsorption process but also in the adsorption capacity. With regard to adsorption capacity, this study reveals the Langmuir adsorption isotherm being the best fit with experimental data (R2 = 0.98-0.99). The maximum adsorption capacities range from 0.7 to 3.5 mg-P/g when the pH of the synthetic P solution was varied from 9.0 to 4.3, accordingly. The outcome of this study indicated that alum sludge is suitable for use as an adsorbent for removal of phosphate from wastewater.

Adsorption↗

The REAL process--a process for recycling sludge from water works.

In order to produce drinking water, coagulants--such as aluminium salts--are widely used for precipitation and separation of impurities from raw water. The residual from the process is sludge, which presents a disposal problem. The REAL process is a method for recycling the aluminium from the sludge. In a first step, the aluminium hydroxide is dissolved in sulphuric acid. In a second step, an ultra filtration will separate all suspended matter and large molecules, leaving a concentrate of 15-20% dry solids. The permeate will contain the trivalent aluminium ions together with 30-50% of the organic contaminants. In a third step, by concentrating the permeate in a nano filter, the concentration of aluminium will be high enough to, in a fourth step, be precipitated with potassium sulphate to form a pure crystal: potassium aluminium sulphate. The potassium aluminium sulphate is comparable to standard aluminium sulphate. The process will give a residual in form of a concentrate from the ultra filtration, representing a few per cent of the incoming volume. This paper presents the results from a long time pilot-scale continuous test run at Västerås water works in Sweden, as well as calculations of costs for full-scale operations.

Alum Compounds↗

A strategy for controlling deposition of struvite in municipal wastewater treatment plants.

This paper presents strategies to reduce the risk of struvite deposition by controlling its location of formation. Two technical routes were investigated: (1) to fix the phosphate into the dewatered sludge cake, and (2) to remove phosphate from centrate or filtrate. Chemicals used include magnesium hydroxide [Mg(OH)2], both of reagent grade and reclaimed from a flue gas desulfurization system, magnesium chloride (MgCl2), calcium hydroxide [Ca(OH)2], ferric chloride (FeCl3) and aluminum sulfate [Al2(SO4)3]. Research results indicate that (1) for anaerobically well-digested sludge, Mg(OH)2 is effective in fixing phosphate into sludge cake and improving sludge dewaterability, and (2) adding Mg(OH)2 into a reactor, located between the sludge dewatering facilities and the centrate or filtrate discharge line, and using air for mixing and carbon dioxide stripping, proves feasible in reducing struvite deposition in centrate or filtrate discharge lines and can generate a potentially valuable plant fertilizer--struvite.

Alum Compounds↗

An unusual local reaction after microsclerotherapy with chromated glycerin.

A case of papular itching lesions after microsclerotherapy with chromated glycerin (CG) at a 72% concentration for telangiectases of the thighs is reported. Patch-test results were strongly positive for nickel sulfate (+++/+++) and thimerosal (++/++) whereas results were negative for the sclerosing agent CG 72% and glycerol (control). Intradermal injection of CG 72% in the thigh and intravascular injection of CG 72% into telangiectases of the knee produced erythematous papular itching lesions in about 5 to 6 hours. As a negative control, glycerol and sodium chloride 0.9% injected intradermically on the thigh did not cause any reaction. CG can elicit allergic reactions in patients who are sensitive to chromium and can cause new sensitizations to chromium. In our case, no positivity to potassium dichromate was observed.

Alum Compounds↗

Effects of various adjuvants on efficacy of a vaccine against Streptococcus bovis and Lactobacillus spp in cattle.

OBJECTIVE: To determine efficacy of vaccines incorporating QuilA, alum, dextran combined with mineral oil, or Freund adjuvant for immunization of feedlot cattle against Streptococcus bovis and Lactobacillus spp. ANIMALS: 24 steers housed under feedlot conditions. PROCEDURE: Steers were randomly assigned to 4 experimental groups and a control group. Animals in experimental groups were inoculated on days 0 and 26 with vaccines containing Freund adjuvant (FCA), QuilA, dextran combined with mineral oil (Dex), or alum as adjuvant. Serum anti-S bovis and anti-Lactobacillus IgG concentrations were measured, along with fecal pH, ruminal fluid pH, and number of S bovis and Lactobacillus spp in ruminal fluid. RESULTS: Throughout the study, serum anti-S bovis and anti-Lactobacillus IgG concentrations for animals in the Dex, QuilA, and alum groups were similar to or significantly higher than concentrations for animals in the FCA group. Serum anti-S bovis and anti-Lactobacillus IgG concentrations were significantly increased on days 26 through 75 in all 4 experimental groups, and there was a linear relationship between anti-S bovis and anti-Lactobacillus IgG concentrations. For animals in the QuilA and Dex groups, mean pH of feces throughout the period of experiment were significantly higher and numbers of S bovis and Lactobacillus spp in ruminal fluid on day 47 were significantly lower than values for control cattle. CONCLUSIONS AND CLINICAL RELEVANCE: Results suggest that immunization of feedlot steers against S bovis and Lactobacillus spp with vaccines incorporating Freund adjuvant, QuilA, dextran, or alum as an adjuvant effectively induced high, long-lasting serum anti-S bovis and anti-Lactobacillus IgG concentrations. Of the adjuvants tested, dextran may be the most effective.

Adjuvants, Immunologic↗

Reduction of house-dust mite allergen concentrations in carpets by aluminium potassium sulfate dodecahydrate (alum).

Special tools and skilled labor are required to reduce house-dust mite allergens in carpets. The main house-dust mite allergen is Der p 1, a soluble protein found in high abundance in woolen carpets. Current chemical treatment options are either unsafe or ineffective in eradicating Der p 1. Here, we present an effective, safe, and easy application reagent to reduce the allergen levels in carpets. Sixty woolen carpets with Der p 1 concentrations >2 microg/g in fine dust were divided into three homogeneous groups of 20 carpets each, according to their allergen load. We tested alum dissolved in 60 mL of water at doses of 3, 6, and 9 g/m2 against Der p 1 in groups 1, 2, and 3, respectively. The test side of the carpets was sprayed with the reagent. The control side was treated with the 60 mL of tap water. Dust particles were collected from a 1-m2 area on each carpet side 24 hours after treatment and were analyzed for Der p 1 content with a monoclonal ELISA. Alum reduced the Der p 1 concentrations by 48.6 +/- 6.2%, 78.8 +/- 7.2%, and 95.2 +/- 3.0% at 3, 6, and 9 g/m2 in the carpets, respectively. Moreover, there were no complaints registered by the residents against the alum applications. Alum, at 9 g/m2 (in a solution at 15%) in water, can be used for decreasing existing Der p 1 concentrations in woolen carpets.

Air Pollution, Indoor↗

Influence of aluminum as sulfate, chloride and citrate on magnesium and calcium metabolism in sheep.

Three metabolism trials were conducted to determine the effects of Al as sulfate (SO4), chloride (Cl) and citrate on metabolism of Al, Mg, Ca and serum concentrations of Mg and Ca. Twelve wether lambs, equipped with rumen cannulas and blocked by breeding and weight, were allotted randomly to the following six treatments during each of three trials: 0, 1,000 and 2,000 pm Al as SO4 or Cl; or 2,000 ppm Al as citrate. Treatments were administered in 200 ml of deionized water twice daily in divided doses via rumen cannula. Lambs were fed 1,000 g/d of chopped tall fescue hay (Festuca arundinacea, Schreb. IFN 1-09-187). Aluminum, Mg and Ca in feces and urine, and Mg and Ca in blood serum were determined daily over the 10-d treatment period. Means were calculated for d 6 through d 10. By d 6, serum Mg was lowered (P less than .05) for lambs administered 2,000 ppm Al as citrate. Serum Ca was not affected by Al treatments. Neither Mg nor Ca absorption was significantly affected by Al treatment. Urinary excretion of Ca increased linearly (P less than .001) with all treatments. Absorption of Al occurred with all forms of the element and was highest for Al2(SO4)3, expressed as percentage of intake.

Alum Compounds↗

Consumption of simulated acid mine water by sheep.

Water consumption by sheep in 48-h periods was measured in three replicated experiments. Intake was expressed as ml X kg body weight-.73 X d-1 and treatments were compared with intake of tap water or distilled water in no-choice situations. Neutralizing two acid mine drainage (AMD) polluted waters having pH values of 2.4 and 2.8, with Ca(OH)2 did not make either as acceptable to sheep as unpolluted water (P less than .01). Simulating AMD with sources of H+, HSO4-, SO4 =, Fe , Al++, Mn++, Zn++ or Na+ revealed several significant differences in acceptance. The ferric ion at 2.6 mM was rejected when presented as Fe2(SO4)3 but not as equimolar FeCl3. Moreover, SO4 = at 3.9 mM was not rejected when presented as Na2SO4 or ZnSO4. Neither AlSO4 nor MnSO4 at levels found in the two sources of AMD was rejected. Effects of prolonged consumption of the various components have not been determined.

Alum Compounds↗

Effect of certain ulcer-healing agents on amphibian gastroduodenal bicarbonate secretion.

The effect of luminal application of aluminum sulphate, sucralfate, and bismuth subcitrate on gastroduodenal alkali secretion has been studied with isolated amphibian mucosa. The mucosa, stripped of its external muscle layer, was mounted in chambers that allowed titration of alkali secretion and measurement of transmucosal potential difference and electrical resistance. Neutral aluminum sulphate (3 X 10(-3) M) increased bicarbonate secretion by fundic (mean +/- SEM = 144 +/- 48%, n = 5, P less than 0.05), antral (mean +/- SEM = 214 +/- 63%, n = 4, P less than 0.05), and duodenal (mean +/- SEM = 133 +/- 44%, n = 6, P less than 0.005) mucosa. Sucralfate (0.5 g/l) stimulated fundic (mean +/- SEM = 183 +/- 87%, n = 4, P less than 0.05) and antral (mean +/- SEM = 156 +/- 58%, n = 5, P less than 0.005) alkali secretion and, at a concentration of 1 g/l, duodenal output (mean +/- SEM = 42 +/- 15%, n = 6, P less than 0.05). Bismuth subcitrate (10(-4) M) produced a significant rise in fundic (mean +/- SEM = 80 +/- 21%, n = 5, P less than 0.05) and duodenal (mean +/- SEM = 62 +/- 7%, n = 6, P less than 0.05) alkali secretion. None of these agents altered transmucosal potential difference or electrical resistance. The actions of these agents on gastroduodenal bicarbonate secretion may be important in their ulcer healing effects.

Alum Compounds↗

Aluminum exacerbates cyclosporin induced nephrotoxicity in rats.

Cyclosporin (CSA) has been universally used as an immunosuppressant for the management of allotransplantation and autoimmune diseases. However, nephrotoxicity of CSA limits its use to optimum level. Aluminum (Al) is an extensively distributed element in the environment and human exposure to this metal is unavoidable. Recent studies suggest that even a slight impairment of renal function may increase the Al body burden significantly, which may lead to neurotoxicity, nephrotoxicity, osteodystrophy or hypochromic anemia. In the present study, an attempt was made to study the effect of concomitant use of Al and CSA on structure and function of kidney in rats. This study was undertaken in two steps. In the first set of experiments, the effect of single dose of Al (1% Al2(SO4)3 18H2O) on the nephrotoxicity of multiple doses of CSA (12.5 mg/kg, 25 mg/kg and 50 mg/kg) was studied, where as in the second set of experiments the effect of multiple doses of Al (0.25%, 0.5% and 1%) on single dose of CSA (50 mg/kg) was undertaken. Male Sprague-Dawley rats (weighing 230 +/- 20 g) were used in this study. CSA was given once a day by gavage for seven days, where as Al was given in drinking water for the same period. Twenty four hours after the last dose of CSA, animals were sacrificed and blood and kidney were collected for biochemical and histopathological studies. The bio-chemical parameters included blood urea nitrogen (BUN), serum creatinine (SCr), CSA and Al levels. The kidney homogenates were assayed for malondialdehyde (MDA) and lipid hydroperoxides (LPH). Treatment of rats with CSA alone produced dose-dependent structural and functional changes in kidney. Although Al alone failed to produce any deleterious effect on renal function, it significantly increased the bioavailability and nephrotoxicity of CSA. Al also exacerbated CSA induced increase in oxidative stress (as evident by increased MDA and LPH). Thus, the exacerbation of CSA nephrotoxicity by Al may be attributed to increased bioavailability of CSA and excessive generation of free radicals following concomitant use of these drugs.

Alum Compounds↗