The Effect of Various Hydroxide and Salt Additives on the Reduction of Fluoride Ion Mobility in Industrial Waste
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SDS Contains All of the Information Required by the HPR
SAFETY DATA SHEET Preparation Date: 7/7/2015 Revision Date: 7/6/2018 Revision Number: G2 1. IDENTIFICATION Product identifier Product code: C1115 Product Name: CALCIUM HYDROXIDE, POWDER, REAGENT, ACS Other means of identification Synonyms: Calcium hydrate Carboxide Calcium dihydroxidede calcium (French) CAS #: 1305-62-0 RTECS # EW2800000 CI#: Not available Recommended use of the chemical and restrictions on use Recommended use: Fireproofing coatings. water treatment. Buffering agent. In paper manufacture process. Chemical intermediate. In dental cement. In lubricants. In mortar, plaster, cement and other building and paving materials. In fungicides. In pesticides. In SBR rubber vulcanization. Uses advised against No information available Supplier: Spectrum Chemical Mfg. Corp 14422 South San Pedro St. Gardena, CA 90248 (310) 516-8000 Order Online At: https://www.spectrumchemical.com Emergency telephone number Chemtrec 1-800-424-9300 Contact Person: Martin LaBenz (West Coast) Contact Person: Ibad Tirmiz (East Coast) 2. HAZARDS IDENTIFICATION Classification This chemical is considered hazardous according to the 2012 OSHA Hazard Communication Standard (29 CFR 1910.1200) Considered a dangerous substance or mixture according to the Globally Harmonized System (GHS) Skin corrosion/irritation Category 2 Serious eye damage/eye irritation Category 1 Specific target organ toxicity (single exposure) Category 3 Label elements Danger Product code: C1115 Product name: CALCIUM 1 / 13 HYDROXIDE, POWDER, REAGENT, ACS Hazard statements Causes skin irritation Causes serious eye damage May cause respiratory irritation Hazards not otherwise classified (HNOC) Not Applicable Other hazards Not available Precautionary Statements - Prevention Wash face, hands and any exposed skin thoroughly after handling Avoid breathing dust/fume/gas/mist/vapors/spray Use only outdoors or in a well-ventilated area Wear protective gloves Wear eye/face protection Precautionary Statements - Response IF IN EYES: Rinse cautiously with water for several minutes. -
Trisodium Hexafluoroaluminate Product Stewardship Summary February 2011
Trisodium hexafluoroaluminate Product Stewardship Summary February 2011 Na3AlF6 Chemical Name: Trisodium hexafluoroaluminate Chemical Category (if applicable): Alkali Metal Halide Synonyms: Aluminate (3-), hexafluoro-, trisodium; Aluminium trisodium hexafluoride; Sodium aluminium fluoride; and Sodium hexafluoroaluminate; Icestone; Synthetic cryolite CAS Number: 13775-53-6 CAS Name: Aluminate(3-), hexafluoro-, trisodium, (OC-6-11)- EC (EINECS) Number: 237-410-6 Document Number: GPS0046 V1.0 Trisodium hexafluoroaluminate (synthetic cryolite) is primarily used a flux agent or bath material by aluminum smelters in the production of aluminum. It is also used in the production of synthetic resins for abrasives and in the manufacture of cutting or grinding discs. Minor uses are as a coloring agent (opacifier) in the glass, ceramic and pyrotechnic industries, and as a component of insecticides in the U.S. Exposure can occur at either a synthetic cryolite manufacturing facility or at other manufacturing, packaging or storage facilities that handle synthetic cryolite. Persons involved in maintenance, sampling and testing activities, or in the loading and unloading of synthetic cryolite packages are at risk of exposure, but worker exposure can be controlled with the use of proper general mechanical ventilation and personal protective equipment. Workplace exposure limits for fluoride ion have been established for use in worksite safety programs. When synthetic cryolite is a component of consumer products, users should follow manufacturer’s use and/or label instructions. Synthetic cryolite dusts released to the atmosphere and deposited in soil or surface water in the vicinity of production sites have negligible impact on the environment. Please see the MSDS for additional information. Synthetic cryolite is a nonflammable solid that is stable under normal conditions. -
The Solubility of Aluminium in Melts Containing Aluminium Halides
THE SOLUBILITY OF ALUMINIUM IN MELTS CONTAINING ALUMINIUM HALIDES A Thesis presented for the degree of Doctor of Philosophy in the University of London by John Dyson Usher London, May 1965 ABSTRACT A technique for measuring the solubility of aluminium in NaF-A1F3 and Nall-A1F3+5%A1203 melts has been developed using a refractory titanium boride- carbide crucible and a gas volumetric method of analysis. Experiments were conducted at 10209 1100 and 1180°C; in both systems no change in solubility limit was detected over the experimental composition range of 25.6 - 36.6 and 25.8 - 31.9 mol % AlF3 respectively. The figures in the pure fluoride are 0.022 0.041 and 0.072 wt %; in the alumina melts 0.073, 0.121 and 0.169 wt %. Solution mechanisms have been suggested which account for the observed behaviour, and an attempt has been made to interpret the current inefficiency process in the reduction cell in terms of the results. CONTENTS 1. INTRODUCTION Page 1.1 Aluminium Reduction Cell - Brief Description 1 1.2 Current Efficiency 3 1.2.1 Measurement 3 1.2.2 Cell Variables and Current Efficiency 5 1.2.2 Postulated Mechanisms of Metal Lose 6 1.3 Origins of Present Work 7 1.3.1 Information Required 7 1.3.A Preliminary Theoretical Approach 9 1.4 Metal-Molten Salt Solutions 11 1.4.1 General 11 1.4.2 Nature of Metal-Molten Salt Solutions 16 1.4.3 Extent of Solubility 19 1.4.4 Effect of Foreign Ions on Metal Solubility 23 1.5 Structure of Cryolite and Cryolite-Alumina Melts 25 1.5.1 Pure Molten Cryolite 25 1.5.2 Cryolite-Alumina Melts 33 1.6 Thermodynamics of Aluminium+Cryolite 40 1.6.1 Equilibrium 1.6(i): Experimental 40 1.6.2 Equilibrium 1.6(i): Calculations 42 1.6.3 Equilibrium 1.6(ii) 45 1.7 Previous Experimental Work 46 1.7.1 Analysis by Metal Weight Loss 48 1.7.2 Gas Volumetric Method 52 2. -
Determination of Aluminium As Oxide
DETERMINATION OF ALUMINIUM AS OXIDE By William Blum CONTENTS Page I. Introduction 515 II. General principles 516 III. Historical 516 IV. Precipitation of aluminium hydroxide. 518 1. Hydrogen electrode studies 518 (a) The method 518 (b) Apparatus and solutions employed 518 (c) Results of hydrogen electrode experiments 519 (d) Conclusions from hydrogen electrode experiments 520 2. Selection of an indicator for denning the conditions of precipita- '. tion . 522 3. Factors affecting the form of the precipitate 524 4. Precipitation in the presence of iron 525 V. Washing the precipitate . 525 VI. Separation from other elements 526 VII. Ignition and weighing of the precipitate 528 1. Hygroscopicity of aluminium oxide 529 2. Temperature and time of ignition 529 3. Effect of ammonium chloride upon the ignition 531 VIII. Procedure recommended 532 IX. Confirmatory experiments 532 X. Conclusions '534 I. INTRODUCTION Although a considerable number of precipitants have been pro- posed for the determination of aluminium, direct precipitation of aluminium hydroxide by means of ammonium hydroxide, fol- lowed by ignition to oxide, is most commonly used, especially if no separation from iron is desired, in which latter case special methods must be employed. While the general principles involved in this determination are extremely simple, it has long been recog- nized that certain precautions in the precipitation, washing, and ignition are necessary if accurate results are to be obtained. While, however, most of these details have been studied and dis- cussed by numerous authors, it is noteworthy that few publica- tions or textbooks have taken account of all the factors. In the 515 ; 516 Bulletin of the Bureau of Standards [Voi.i3 present paper it seems desirable, therefore, to assemble the various recommendations and to consider their basis and their accuracy. -
Microstructural and Compressive Strength Analysis for Cement Mortar with Industrial Waste Materials
Available online at www.CivileJournal.org Civil Engineering Journal Vol. 6, No. 5, May, 2020 Microstructural and Compressive Strength Analysis for Cement Mortar with Industrial Waste Materials Zahraa Fakhri Jawad a, Rusul Jaber Ghayyib a, Awham Jumah Salman a* a Al-Furat Al-Awsat Technical University, Najaf, Kufa, Iraq. Received 06 December 2019; Accepted 02 March 2020 Abstract Cement production uses large quantities of natural resources and contributes to the release of CO2. In order to treat the environmental effects related to cement manufacturing, there is a need to improve alternative binders to make concrete. Accordingly, extensive study is ongoing into the utilization of cement replacements, using many waste materials and industrial. This paper introduces the results of experimental investigations upon the mortar study with the partial cement replacement. Fly ash, silica fume and glass powder were used as a partial replacement, and cement was replaced by 0%, 1%, 1.5%, 3% and 5% of each replacement by the weight. Compressive strength test was conducted upon specimens at the age of 7 and 28 days. Microstructural characteristic of the modified mortar was done through the scanning electron microscope (SEM) vision, and X-ray diffraction (XRD) analysis was carried out for mixes with different replacements. The tests results were compared with the control mix. The results manifested that all replacements present the development of strength; this improvement was less in the early ages and raised at the higher ages in comparison with the control specimens. Microstructural analysis showed the formation of hydration compounds in mortar paste for each replacement. This study concluded that the strength significantly improved by adding 5% of silica fume compared with fly ash and glass powder. -
ACUMER™ 9000 Mineral Slurry Dispersant
Technical Data ACUMER™ 9000 Mineral Slurry Dispersant Description ACUMER™ 9000 is a sodium salt of an acrylic acid-based polymer. It is a highly effective dispersant for aqueous calcium hydroxide and magnesium hydroxide slurries. Features and • Controlling phase separation Benefits • Reducing caking and clogging of equipment • Aiding the remixing of slurries after settling Typical Properties Property Typical Value Appearance Clear, light amber solution Total solids, % 44 pH 7.5 Density (lb/gal, @ 25°C) 10.8 Brookfield viscosity, (mPa.s/cps @ 25°C) 500 These properties do not constitute specifications. Performance Many problems can be encountered in producing calcium hydroxide or magnesium hydroxide slurries, including: • Wettability • Phase separation • Caking • Pumping • Pipe clogging • Remixing after setting • Slurry viscosity Calcium Hydroxide Figure 1 shows the efficiency of ACUMER 9000 as a dispersant for 30% calcium hydroxide slurry. Figure 1. ACUMER 9000 Dosage vs. Viscosity (30% Lime Slurry) Page 1 of 4 ®™Trademark of The Dow Chemical Company (“Dow”) or an affiliated company of Dow Form No. 812-00352-0216BBI ACUMER™ 9000 / Dow Oil, Gas & Mining The following table shows the positive effect of ACUMER™ 9000 dosage on lime slurry stability. Lower dosage (0.2%) gives higher slurry viscosity and lower syneresis (liquid phase separation). The desired slurry properties can be controlled by optimizing the dispersant dosage. Effect of ACUMER 9000 Dispersant on 30% Lime Slurry1 Stability After 8 Days at Room Temperature Initial Make-Down Dosage, % (solids basis) Syneresis Gel3 Flowed4 Viscosity2 0.2 2080 1.7 98.3 93.3 0.4 810 12.0 88.0 97.1 0.6 382 16.5 83.5 96.3 130% lime slurry was prepared by mixing 210 grams of slaked lime with 490 grams of deionized water (including additives) for five minutes in a Waring blender at high speed. -
Ffinmffiffih$Nry3fhrt
aaourlll q*{Jl}ll ol:f,Ul Arab lnt'|. Organization ,i*If, i*fr* .it*^ Srab Fertilizers ft ssociation Since: L975 flrf*r* ffinmffiffih$nry3Fhrt AFA P FluJsilisic acid: Recovery System and Aluminum Fluoride production Prepared by Eng. Kamal SAMRANE, R&D Direction, OCP Group Eng. Mohammad Al-hjouj - EHS Manager - JPMC Revised by Eng. Faisal Doudin Technical advisor to the Chairman JPMC Dr. Abdelaali KOSSIR R&D Director - OCP Group acid: Recovery Fluosilisic ffiliilrTi roride production l. lntroduction Fluosilisic acid (HrSiFu) is mainly produced as a by-product from the wet process of Phosphoric Acid production from fluorapatite. Phosphate rock always contains fluorine. For F/P2O5 ratios, the fluorine content in rock of sedimentary origin ranges in general from 0.10 to 0.14. Rock of igneous origin shows lower ratios, from 0.04 to 0.006. About 50kg of fluorine (as H2SiF6) per tonne of phosphoric acid (as P2O5) is evolved with the concentration of phosphoric acid in the evaporation step. Currently, most of this evolved fluorine is absorbed into the cooling pond water causing alarge environmental problem.The phosphoric and hydrofluoric acids are liberated from Phosphate rock by the action of sulfuric acid. Some of the HF in turn reacts with silicate minerals, which are an unavoidable constituent of the mineral feedstock, to give silicon tetrafluoride. Thus the formed silicon tetrafluoride reacts further with HF. The net process can be described as: SiO, + 6 HF <-- H2SiF6 + ZH.-O - ------) Neutralization of solutions of fluosilisic acid with alkali metal bases produces the corresponding alkali metal fluorosilicate salts: H2SiF6 + 2 NaOH ) NarSiFu + 2HrO The resulting salt Na2SiF6 is mainly used in water fluoridation. -
Aluminium Distearate, Aluminium Hydroxide Acetate, Aluminium Phosphate and Aluminium Tristearate
The European Agency for the Evaluation of Medicinal Products Veterinary Medicines Evaluation Unit EMEA/MRL/393/98-FINAL April 1998 COMMITTEE FOR VETERINARY MEDICINAL PRODUCTS ALUMINIUM DISTEARATE, ALUMINIUM HYDROXIDE ACETATE, ALUMINIUM PHOSPHATE AND ALUMINIUM TRISTEARATE SUMMARY REPORT 1. Aluminium is an ubiquitous element in the environment. It is present in varying concentrations in living organisms and in foods. Aluminium compounds are widely used in veterinary and human medicine. Other uses are as an analytical reagent, food additives (e.g. sodium aluminium phosphate as anticaking agent) and in cosmetic preparations (aluminium chloride). Aluminium distearate is used for thickening lubricating oils. Aluminium hydroxide acetate and phosphate are antacids with common indications in veterinary medicine: gastric hyperacidity, peptic ulcer, gastritis and reflux esophagitis. A major use of antacids in veterinary medicine is in treatment and prevention of ruminal acidosis from grain overload, adsorbent and antidiarrheal. The dosage of aluminium hydroxide is 30 g/animal in cattle and 2 g/animal in calves and foals. Gel preparations contain approximately 4% aluminium hydroxide. Aluminium potassium sulphate is used topically as a antiseptic, astringent (i.e. washes, powders, and ‘leg tighteners’ for horses (30 to 60 g/animal) and antimycotic (1% solution for dipping or spraying sheeps with dermatophilus mycotic dermatitis). In cattle it is occasionally used for stomatitis and vaginal and intrauterine therapy at doses of 30 to 500 g/animal. In human medicine, aluminium hydroxide-based preparations have a widespread use in gastroenterology as antacids (doses of about 1 g/person orally) and as phosphate binders (doses of about 0.8 g/person orally) in patients an impairment of renal function. -
Ep 3106176 B1
(19) TZZ¥_Z__T (11) EP 3 106 176 B1 (12) EUROPEAN PATENT SPECIFICATION (45) Date of publication and mention (51) Int Cl.: of the grant of the patent: A61K 39/12 (2006.01) A61K 39/39 (2006.01) 11.10.2017 Bulletin 2017/41 (21) Application number: 16183076.5 (22) Date of filing: 06.12.2012 (54) ALUMINIUM COMPOUNDS FOR USE IN THERAPEUTICS AND VACCINES ALUMINIUMVERBINDUNGEN ZUR VERWENDUNG FÜR THERAPEUTIKA UND IMPFSTOFFE COMPOSÉS D’ALUMINIUM POUR UTILISATION DANS DES PRODUITS THÉRAPEUTIQUES ET VACCINS (84) Designated Contracting States: (56) References cited: AL AT BE BG CH CY CZ DE DK EE ES FI FR GB WO-A2-2009/158284 US-A1- 2005 158 334 GR HR HU IE IS IT LI LT LU LV MC MK MT NL NO PL PT RO RS SE SI SK SM TR • SRIVASTAVA A K ET AL: "A purified inactivated Japaneseencephalitis virus vaccine made in vero (30) Priority: 06.12.2011 EP 11192230 cells", VACCINE, vol. 19, no. 31, 14 August 2001 13.03.2012 PCT/EP2012/054387 (2001-08-14), pages 4557-4565, XP027321987, ELSEVIER LTD, GB ISSN: 0264-410X [retrieved (43) Date of publication of application: on 2001-08-14] 21.12.2016 Bulletin 2016/51 • ANONYMOUS: "Rehydragel Adjuvants. Product profile", General Chemical , 2008, pages 1-2, (60) Divisional application: XP002684848, Retrieved from the Internet: 17185526.5 URL:http://www.generalchemical.com/assets/ pdf/Rehydragel_Adjuvants_Product_Profile.p df (62) Document number(s) of the earlier application(s) in [retrieved on 2012-10-08] accordance with Art. 76 EPC: • LINDBLAD, EB: "Special feature. Aluminium 12795830.4 / 2 788 023 compoundsfor usein vaccines", IMMUNOL. -
How to Make Concrete More Sustainable Harald Justnes1
Journal of Advanced Concrete Technology Vol. 13, 147-154, March 2015 / Copyright © 2015 Japan Concrete Institute 147 Scientific paper How to Make Concrete More Sustainable Harald Justnes1 A selected paper of ICCS13, Tokyo 2013. Received 12 November 2013, accepted 16 February 2015 doi:10.3151/jact.13.147 Abstract Production of cement is ranking 3rd in causes of man-made carbon dioxide emissions world-wide. Thus, in order to make concrete more sustainable one may work along one or more of the following routes; 1) Replacing cement in con- crete with larger amounts of supplementary cementing materials (SCMs) than usual, 2) Replacing cement in concrete with combinations of SCMs leading to synergic reactions enhancing strength, 3) Producing leaner concrete with less cement per cubic meter utilizing plasticizers and 4) Making concrete with local aggregate susceptible to alkali silica reaction (ASR) by using cement replacements, thus avoiding long transport of non-reactive aggregate. 1 Introduction SCMs, also uncommon ones like calcined marl 2. Replacing cement in concrete with combinations of The cement industry world-wide is calculated to bring SCMs leading to synergic reactions enhancing about 5-8% of the total global anthropogenic carbon strength dioxide (CO2) emissions. The general estimate is about 3. Producing leaner concrete with less cement per cubic 1 tonne of CO2 emission per tonne clinker produced, if meter utilizing plasticizers. fossil fuel is used and no measures are taken to reduce it. 4. Making concrete with local aggregate susceptible to The 3rd rank is not because cement is such a bad mate- alkali silica reaction (ASR) by using cement re- rial with respect to CO2 emissions, but owing to the fact placements, thus avoiding long transport of non- that it is so widely used to construct the infrastructure reactive aggregate and buildings of modern society as we know it. -
United States Patent to 1 4,010,247 Wassermann Et Al
United States Patent to 1 4,010,247 Wassermann et al. 45 Mar. 1, 1977 54 METHOD FOR MAKING WATER 3,385,663 5/1968 Hughes .............................. 4231626 DSPERSIBLE ALUMINUM HYDROXDE 3,411,876. 1 1/1968 Michel et al. ..................... 4231626 3.41 1,877 1 1/1968 Michel et al. ..................... 4231626 75 Inventors: Martin Wilhelm Wassermann, 3,653,937 4/1972 Koenig et al. ..................... 423/625 Hamburg; Arnold Wilhelm Meyer, 3,743,709 7/1973 Shaw et al. ........................ 423/630 St. Michaelisdonn, both of Germany 3,839,536 10/1974 Sato et al. ......................... 423/630 73 Assignee: CONDEA Petrochemie-Gesellschaft 3,907,982 9/1975 Leach ................................ 423f630 m.b.H., Brunsbuettel, Germany FOREIGN PATENTS OR APPLICATIONS 22) Filed: Feb. 10, 1975 562,372 8/1958 Canada .............................. 4231628 21 678,220 1/1964 Canada ......... ... 4231625 Appl. No.: 548,804 6,407,784 1/1965 Netherlands ...................... 423/626 30 Foreign Application Priority Data 1,062,124 3/1967 United Kingdom ............... 4231629 Feb. 21, 1974 Germany .......................... 2408233 52) U.S. Cl. ............................... 423/626; 423/629; Primary Examiner-Herbert T. Carter 423/630; 423/631 Attorney, Agent, or Firm-Cushman, Darby & 51 Int. Cl”........................................... C01F 7/02 Cushman 58 Field of Search .......... 423/626, 629, 630,625, 423/631 57 ABSTRACT - References Cited Water dispersible aluminum hydroxide is prepared by 56) treating an acid dispersible aluminum hydroxide with 1 UNITED STATES PATENTS to 9 weight % of a gaseous acid. 2,377,547 6, 1945 Fuchs ................................ 4231626 3,207,578 9/1965 Brown et al. ...... A A 4231626 3,262,754 7/1966 Lindsay et al.................... -
Pathological Effect of Aluminium Hydroxide Compared with Polymer-Based Nanoparticles on Neonatal Mice Brain
Al-Murshedy & Fares (2020): Pathological effect of nanoparticles on neonatal mice brain Nov 2020 Vol. 23 Issue 19 Pathological effect of Aluminium hydroxide compared with polymer-based nanoparticles on neonatal mice brain Noor Alhuda K. Al-Murshedy1*, BushraH.Fares2 1, 2 Department of Pathology and Poultry disease, University of Kufa, College of Veterinary Medicine, Najaf,Iraq. *Corresponding author: Noor Alhuda K. Al-Murshedy Email:[email protected] Abstract The present study carried to investigate the toxic pathology effect of both bulk Al(OH)3 and Al(OH)3 nanoparticles materials. Also, to examined cerebral cortex-kb p65 expression level by immunohistochemistry test. The crystalline and grain size of nanoparticles and it is morphology are tested by XRD, AFM, SEM, and EDEX respectively. This study included 40 neonatal mice of both sexes were randomly divided into 7 groups. This group's immunized subcutaneously, two times, the first dose was at third postnatal, and the second dose was at 17 days postnatal. These groups classified as follows:-the 1st group of mice injected by normal saline which serves as control negative, while the 2nd group immunized by oval albumin which serves as control positive. The 3rd group immunized by bulk-Al(OH)3, the 4th group immunized by Al(OH). The Brain tissue samples were collected from each at 4 weeks and 8weeks post first immunization for histological examination. The Histopathological results of the 1st group, 2nd group do not show clear histopathological changes. Whereas, histopathological changes of the 3rd group was severe at 4 weeks post first immunization, while at 8 weeks post first immunization pathological changes were more severe.