Denaturing Polyacrylamide Gel Electrophoresis APPENDIX 3B
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Chemicals Used for Chemical Manufacturing Page 1 of 2
Chemicals used for Chemical Manufacturing Page 1 of 2 Acetic Acid (Glacial, 56%) Glycol Ether PMA Acetone Glycol Ether PNB Acrylic Acid Glycol Ether PNP Activated Carbon Glycol Ether TPM Adipic Acid Glycols Aloe Vera Grease Aluminum Stearate Gum Arabic Aluminum Sulfate Heat Transfer Fluids Amino Acid Heptane Ammonium Acetate Hexane Ammonium Bicarbonate Hydrazine Hydrate Ammonium Bifluoride Hydrochloric Acid (Muriatic) Ammonium Chloride Hydrogen Peroxide Ammonium Citrate Hydroquinone Ammonium Hydroxide Hydroxylamine Sulfate Ammonium Laureth Sulfate Ice Melter Ammonium Lauryl Sulfate Imidazole Ammonium Nitrate Isobutyl Acetate Ammonium Persulfate Isobutyl Alcohol Ammonium Silicofluoride Calcium Stearate Dipropylene Glycol Isopropanolamine Ammonium Sulfate Carboxymethylcellulose Disodium Phosphate Isopropyl Acetate Antifoams Caustic Potash D'Limonene Isopropyl Alcohol Antifreeze Caustic Soda (All Grades) Dodecylbenzene Sulfonic Acid Isopropyl Myristate Antimicrobials Caustic Soda (Beads, Prills) (DDBSA) Isopropyl Palmitate Antimony Oxide Cetyl Alcohol Dowfrost Itaconic Acid Aqua Ammonia Cetyl Palmitate Dowfrost HD Jojoba Oil Ascorbic Acid Chlorine, Granular Dowtherm SR-1 Keratin Barium Carbonate Chloroform Dowtherm 4000 Lactic Acid Barium Chloride Chromic Acid EDTA Lanolin Beeswax Citric Acid (Dry and Liquid) EDTA Plus Lauric Acid Bentonite Coal Epsom Salt Lauryl Alcohol Benzaldehyde Cocamide DEA Ethyl Acetate Lecithin Benzoic Acid Copper Nitrate Ethyl Alcohol (Denatured) Lime Benzyl Alcohol Copper Sulfate Ethylene Glycol Linoleic Acid Bicarbonate -
Ammonium Persulfate
SAFETY DATA SHEET Ammonium Persulfate Section 1. Identification GHS product identifier : Ammonium Persulfate Code : 76322 Other means of : ammonium persulphate; Peroxydisulfuric acid, diammonium salt; diammonium identification peroxodisulfate; Diammonium persulfate Supplier/Manufacturer : 3420 Central Expressway, Santa Clara CA 95051 In case of emergency : Chemtrec: 1 800 424 9300 Outside USA & Canada: +1 703 527 3887 Section 2. Hazards identification OSHA/HCS status : This material is considered hazardous by the OSHA Hazard Communication Standard (29 CFR 1910.1200). Classification of the : OXIDIZING SOLIDS - Category 3 substance or mixture ACUTE TOXICITY (oral) - Category 4 SKIN CORROSION/IRRITATION - Category 2 SERIOUS EYE DAMAGE/ EYE IRRITATION - Category 2 RESPIRATORY SENSITIZATION - Category 1 SKIN SENSITIZATION - Category 1 SPECIFIC TARGET ORGAN TOXICITY (SINGLE EXPOSURE) (Respiratory tract irritation) - Category 3 GHS label elements Hazard pictograms : Signal word : Danger Hazard statements : May intensify fire; oxidizer. Harmful if swallowed. Causes serious eye irritation. Causes skin irritation. May cause allergy or asthma symptoms or breathing difficulties if inhaled. May cause an allergic skin reaction. May cause respiratory irritation. Precautionary statements Prevention : Wear protective gloves. Wear eye or face protection. In case of inadequate ventilation wear respiratory protection. Keep away from heat. - No smoking. Keep away from clothing, incompatible materials and combustible materials. Take any precaution to avoid mixing with combustibles and other incompatible materials. Use only outdoors or in a well-ventilated area. Avoid breathing dust. Do not eat, drink or smoke when using this product. Wash hands thoroughly after handling. Contaminated work clothing should not be allowed out of the workplace. Response : IF INHALED: Remove victim to fresh air and keep at rest in a position comfortable for breathing. -
Acrylamide Polymerization — a Practical Approach
electrophoresis tech note 1156 Acrylamide Polymerization — A Practical Approach Paul Menter, Bio-Rad Laboratories, 2000 Alfred Nobel Drive, Polyacrylamide Gel Polymerization Hercules, CA 94547 USA AcrylamideBis Polyacrylamide Introduction The unparalleled resolution and flexibility possible with CH2 CH + CH2 CH CH2 CH CH2 CH CH2 CH polyacrylamide gel electrophoresis (PAGE) has led to its CO CO CO CO CO widespread use for the separation of proteins and nucleic NH2 NH NH2 NH2 NH acids. Gel porosity can be varied over a wide range to meet CH2 CH2 specific separation requirements. Electrophoresis gels and NH NH NH NH buffers can be chosen to provide separation on the basis of CO 2 2 CO CO C O charge, size, or a combination of charge and size. CH2 CH CH2 CH CH2 CH CH2 CH The key to mastering this powerful technique lies in the polymerization process itself. By understanding the important Purity of Gel-Forming Reagents parameters, and following a few simple guidelines, the novice Acrylamide can become proficient and the experienced user can optimize Gel-forming reagents include the monomers, acrylamide and bis, separations even further. as well as the initiators, usually ammonium persulfate and TEMED or, occasionally, riboflavin and TEMED. On a molar This bulletin takes a practical approach to the preparation of basis, acrylamide is by far the most abundant component in the polyacrylamide gels. Its purpose is to provide the information monomer solution. As a result, acrylamide may be the primary required to achieve reproducible, controllable polymerization. source of interfering contaminants (Dirksen and Chrambach For those users interested only in the “bare essentials,” the 1972). -
Dispersion Polymerization of Anionic Polyacrylamide in an Aqueous Salt Medium
410 Pet.Sci.(2010)7:410-415 DOI 10.1007/s12182-010-0086-9 Dispersion polymerization of anionic polyacrylamide in an aqueous salt medium Lu Jiao, Peng Bo , Li Mingyuan, Lin Meiqin and Dong Zhaoxia Enhanced Oil Recovery Research Center, China University of Petroleum, Beijing 102249, China © China University of Petroleum (Beijing) and Springer-Verlag Berlin Heidelberg 2010 Abstract: Anionic polyacrylamide dispersions were prepared by dispersion polymerization in an aqueous salt medium, using acrylamide(AM) and acrylic acid(AA) as monomers and anionic polyelectrolytes as stabilizer. Effects of salt concentration, and molecular weight and concentration of stabilizers on the stability of the dispersions were investigated using a HAAKE rheometer and optical microscopy. The results showed that stable anionic polyacrylamide dispersions, consisting of smooth, spherical, polydisperse particles, could be obtained under the conditions of salt concentration ranging from 26 wt% to 30 wt%, concentration of stabilizers from 1.2 wt% to 1.8 wt%, and intrinsic viscosity of stabilizers from 2.98 dL·g-1 to 3.74 dL·g-1. The apparent viscosity of the stable dispersions changed very little with the shear rate, showing Newton fl uid behavior. Key words: Dispersion polymerization, aqueous salt medium, stability, micromorphology, apparent viscosity 1 Introduction chain length during polymerization. The precipitated polymers form spherical micro-particles through aggregation Polyacrylamide (PAM) is an important water-soluble and the particles are suspended in the medium by the polymer. It can be used as a flocculant for water disposal, adsorption of stabilizer. There are several advantages of strength additives for paper manufacture, oil displacement dispersion polymerization, such as no secondary pollution, agents for enhanced oil recovery, and so on (Yan, 1998). -
Optimizing Chemically Enhanced Primary Treatment Processes for Simultaneous Carbon Redirection and Phosphorus Removal
water Article Optimizing Chemically Enhanced Primary Treatment Processes for Simultaneous Carbon Redirection and Phosphorus Removal Tianchen Dong 1, Wudneh Ayele Shewa 1, Kyle Murray 2 and Martha Dagnew 1,* 1 Department of Civil and Environmental Engineering, Western University, 1151 Richmond Street, London, ON N6A 3K7, Canada; [email protected] (T.D.); [email protected] (W.A.S.) 2 City of London, 300 Dufferin Avenue, London, ON N6B 1Z2, Canada; [email protected] * Correspondence: [email protected]; Tel.: +1-519-661-2111 (ext. 87427) Received: 25 February 2019; Accepted: 13 March 2019; Published: 16 March 2019 Abstract: There has been increased interest towards maximizing wastewater energy recovery by enhancing the carbon captured through the primary treatment process such as chemically enhanced primary treatment (CEPT). This research was conducted to optimize the CEPT performance in terms of redirection of carbon and nutrients in both bench- and full-scale operations. In order to improve the CEPT process, the performance of ferric chloride and seven types of polymers were evaluated through jar testing. The optimal coagulant (15 mg/L ferric chloride) and flocculant (0.5 mg/L poly aluminum chloride (PACl)) combination achieved total COD, soluble COD, total suspended solids (TSS), and total phosphorus (TP) removal efficiencies of 76, 58, 89, and 84, respectively, in a full-scale primary clarifier operation. In doing so the organic matter and phosphorus were concentrated in CEPT sludge, making them available for recovery. Furthermore, the relationship between influent characteristics and removal rates under varying operating conditions was investigated. It was found that soluble COD removal appeared to be season-dependent, and TSS removals were independent of influent TSS concentrations in all scenarios. -
Chitosan Based Hydrogels and Their Applications for Drug Delivery in Wound Dressings: a Review T ⁎ Hamid Hamedi, Sara Moradi, Samuel M
Carbohydrate Polymers 199 (2018) 445–460 Contents lists available at ScienceDirect Carbohydrate Polymers journal homepage: www.elsevier.com/locate/carbpol Chitosan based hydrogels and their applications for drug delivery in wound dressings: A review T ⁎ Hamid Hamedi, Sara Moradi, Samuel M. Hudson, Alan E. Tonelli Textile Engineering Chemistry and Science, Fiber & Polymer Science Program, College of Textiles, North Carolina State University, Raleigh, North Carolina 27606-8301, United States ARTICLE INFO ABSTRACT Keywords: Advanced development of chitosan hydrogels has led to new drug delivery systems that can release their active Chitosan hydrogel ingredients in response to environmental stimuli. This review considers more recent investigation of chitosan Wound dressing hydrogel preparations and the application of these preparations for drug delivery in wound dressings. Drug delivery Applications and structural characteristics of different types of active ingredients, such as growth factors, na- Growth factor noparticles, nanostructures, and drug loaded chitosan hydrogels are summarized. Nanoparticles 1. Introduction 2012), pullulan (Li et al., 2011; Wong et al., 2011) and/or synthetic polymers like polyvinyl alcohol (Kokabi et al., 2007; Razzak, 2001; Hydrogels are three-dimensional, cross-linked networks which can Yang et al., 2008), polyacrylamide (Ezra et al., 2009; Risbud & Bhonde, absorb and retain significant amounts of water, without dissolving or 2000; Rosiak et al., 1983) and polyethylene glycol (Ajji et al., 2005; losing their three dimensional structures (Ahmed, 2015; Kashyap, 2005; Gupta et al., 2011; Lih et al., 2012) form hydrogels. Y.B. et al., 2008). The gelation and biodegradation are two key factors Hydrogels are classified into two categories: chemical or permanent affecting the fate of cells (Li et al., 2012). -
Poly(Sodium Acrylate)-Based Antibacterial Nanocomposite Materials
Poly(Sodium Acrylate)-Based Antibacterial Nanocomposite Materials Samaneh Khanlari Thesis submitted to the Faculty of Graduate and Postdoctoral Studies in partial fulfillment of the requirements for the degree of Doctorate in Philosophy in Chemical Engineering Department of Chemical and Biological Engineering Faculty of Engineering UNIVERSITY OF OTTAWA © Samaneh Khanlari, Ottawa, Canada, 2015 i ii Abstract Polymer-based bioadhesives for sutureless surgery provide a promising alternative to conventional suturing. In this project, a new poly(sodium acrylate)-based nanocomposite with antibacterial properties was developed. Poly(sodium acrylate), was prepared using a redox solution polymerization at room temperature; this polymer served as a basis for a nanocomposite bioadhesive material using silver nanoparticles. In-situ polymerization was chosen as a nanocomposite synthesizing method and three methods were applied to quantify the distribution and loadings of nanofiller in the polymer matrices. These included the Voronoi Diagram, Euclidean Minimum Spanning Tree (EMST) method and pixel counting. Results showed that pixel counting combined with the EMST method would be most appropriate for nanocomposite morphology quantification. Real-time monitoring of the in-situ polymerization of poly(sodium acrylate)- based nanocomposite was investigated using in-line Attenuated Total Reflectance/Fourier Transform infrared (ATR-FTIR) technique. The ATR-FTIR spectroscopy method was shown to be valid in reaction conversion monitoring using a partial least squares (PLS) multivariate calibration method and the results were consistent with the data from off-line water removal gravimetric monitoring technique. Finally, a second, more degradable polymer (i.e., gelatin and poly(vinyl alcohol)) was used to modify the degradation rate and hydrophilicity of the nanocomposite bioadhesive. -
High Performance of Chitosan-Co-Polyacrylamide-Tio2 Crosslinked Glutaraldehyde Hydrogel As Soil Conditioner for Soybean Plant (Glycine Max)
SOIL SCIENCE ANNUAL 2020, 71(3), 194–204 https://doi.org/10.37501/soilsa/125847 High Performance of Chitosan-co-Polyacrylamide-TiO2 Crosslinked Glutaraldehyde Hydrogel as Soil Conditioner for Soybean Plant (Glycine max) Halimahtussaddiyah Ritonga1, Muhammad Ihram Basri1, Fransiskus S. Rembon2, La Ode Ahmad Nur Ramadhan1, Muhammad Nurdin1* 1 Department of Chemistry, Faculty of Mathematics and Natural Sciences, Universitas Halu Oleo, Kendari 93232, Southeast Sulawesi, Indonesia 2 Department of Soil Science, Faculty of Agriculture, Universitas Halu Oleo, Kendari 93232, Southeast Sulawesi, Indonesia * Prof. Muhammad Nurdin, Ph.D, [email protected], ORCID ID: https://orcid.org/0000-0002-6727-9283 Abstract Received: 10.01.2020 Research on hydrogels as soil conditioners has been developed based on hydrogels copolymerized Accepted: 29.07.2020 with composite materials in the form of chitosan and TiO2 to overcome low physical properties and Associated editor: J. Antonkiewicz low swelling of polyacrylamide. The aims of the study are synthesis, characterization, application of hydrogels, and determination of the physical and chemical properties of soil and the growth of soy- bean plants. Synthesis of chitosan-co-polyacrylamide-TiO2 crosslinked glutaraldehyde hydrogel was Keywords prepared by the chemical crosslinking method. The characterization of hydrogel was performed by using Fourier Transform Infra-Red (FTIR) and Scanning Electron Microscope (SEM). FTIR spectrum Composite shows the functional groups of chitosan co-polyacrylamide-TiO2 crosslinked glutaraldehyde which –1 –1 –1 –1 Hydrogel includes OH functional groups (3408.22 cm ), NH (1602.85 cm ), C=O (1502 cm ), CN (1600.92 cm ), –1 Soil conditioner and Ti-O (619.15 cm ). The SEM image shows the formation of pores and cavities in the hydrogel. -
Ac. H' UY1 : T 'I 7 April23,2004
F'll'J 'J.'t/032.770 i!,P,P, it> 0~ -'II-~ I ;J..¾,5 Aece; 11(:c/. WDNR., O'f/?.1 I01i Ac. h' UY1 : t 'I 7 April23,2004 Ms. Pam Mylotta Wisconsin Department of Natural Resources 2300 North Martin Luther King Jr. Street P.O. Box 12436 Milwaukee, Wisconsin 53212-0436 Re: Request for Source Area Chemical Injection Permit C & D Technologies, Inc. 900 Keefe A venue Milwaukee, Wisconsin 53212-1709 Dear Ms. Mylotta: On behalf of the Johnson Controls Battery Group, Inc. (JCBGI) and C & D Technologies, Inc. (C&D), MWH Americas, Inc. (MWH) has prepared this request for an injection permit for groundwater treatment in the acid unloading area at the above referenced site. The purpose of the permit request is to provide information to the Wisconsin Department of Natural Resources (WDNR) for approval to conduct a pilot study and full-scale injection of sodium persulfate into the acid unloading area for treatment of volatile organic compounds (VOCs) in groundwater. BACKGROUND INFORMATION Soil and groundwater contamination were found to exist on the Facility property exceeding State environmental standards, based on the August 1999 Phase II Environmental Site Assessment (ESA) of the Facility. In May and June 2001, remedial action was completed for the on-site lead, PCB, and VOC impacted soils. A summary of the remedial activities is contained in the February 2002 On Site Remedial Actions Construction Completion Report. Approximately 400 tons of VOC impacted soil was removed during this investigation. Temporary wells were installed in July 2001 and November 2001 as part of the groundwater VOC characterization investigations documented in the June 2001 and October 2001 Work Plans, respectively. -
Chemical Analyses for Selected Minor Elements in Pierre Shale
Chemical Analyses for Selected Minor Elements in Pierre Shale GEOLOGICAL SURVEY PROFESSIONAL PAPER 391-A Chemical Analyses for Selected Minor Elements in Pierre Shale By L. F. RADER and F. S. GRIMALDI ANALYTICAL METHODS IN GEOCHEMICAL INVESTIGATIONS OF THE PIERRE SHALE GEOLOGICAL SURVEY PROFESSIONAL PAPER 391-A UNITED STATES GOVERNMENT PRINTING OFFICE, WASHINGTON : 1961 UNITED STATES DEPARTMENT OF THE INTERIOR STEW ART L. UDALL, Secretary GEOLOGICAL SURVEY Thomas B. Nolan, Director For sale by the Superintendent of Documents, U.S. Government Printing Office Washington 25, D.C. CONTENTS Page Page Abstract--_________________________________________ A-l Methods for the determination of individual Introduction ___-----_-_--_________________-__--__-_ 1 constituents Continued General remarks._________________________ ______ 1 Copper lead, and zinc Continued Laboratories. -._---____-_-______________________ 2 Zinc, dithizone method._____^_______________ A-20 Acknowledgments. ___-_-_-_--______--_-_________ 2 Lead, dithizone method______------_-____-__- 22 Division of work________________________________ 2 Arsenic.___________,__________-_-_--___-__---_- 23 Methods selected and treatment of data ___________ 3 Acid digestion, heteropoly blue method________ 23 Sample preparation _________________________________ 4 Alternative fusion-heteropoly blue method_____ 24 Methods for the determination of individual constituents. 4 Titanium. _____________________________________ 4 Selenium, distillation, visual-estimation method.____ 25 Peroxide method._--_--_-____._____________ 4 Molybdenum and tungsten______-____------_---_- 27 Alternative tiron method, ___________________ 5 Isolation by method 1, alpha-benzoinoxime pre Vanadium. _--.---_____-_-___.__________________ 7 cipitation. ___----_-_-_-__--_----_-----_-- 27 Fusion-leach separation method. _____________ 7 Isolation by alternative method 2, alpha-ben Alternative cupferron separation method...... -
A Guide to Using Polyacrylamide (PAM) Polymers for Control of Irrigation Run-Off on the Central Coast Michael Cahn, Irrigation A
A Guide to Using Polyacrylamide (PAM) Polymers for Control of Irrigation Run-off on the Central Coast Michael Cahn, Irrigation and Water Resources Advisor, Monterey County Introduction Federal and state water quality regulations require that growers implement management practices to minimize impairments to surface and ground water quality. Although many farmers are currently using recommended practices such as drip irrigation, cover crops, and integrated pest management to reduce the impacts of agriculture on water quality, additional management tools could help achieve more dramatic improvements to water quality. Irrigation run-off can often be difficult to control on soils with low infiltration capacity such as poorly aggregated sandy soils, or soils susceptible to crusting. Sediments suspended in irrigation tail water carry adsorbed nutrients and some classes of pesticides such as pyrethroids. Nitrogen, phosphorus, and several classes of pesticides have been determined to impair the quality of surface water on the Central Coast. The use of practices such as retention ponds and drip irrigation can significantly control irrigation tail water, but these practices can be expensive and may not be suited for all crops and farms. Baby greens, for example, are typically irrigated with overhead sprinklers, and although many cool season vegetables can be grown with drip, almost all of these crops are established with overhead sprinklers during the first 2 to 4 weeks of stand establishment. Research studies conducted since 2003 on the Central Coast have repeatedly demonstrated that polyacrylamide (PAM), a chemical polymer can significantly reduce sediment, nutrient, and pesticide concentrations in irrigation run-off from sprinkler and furrow systems. -
Download/2014-Ghg-Emissions-From-Oil-Sands-Tailings-Ponds-Overview- And-Modelling-Based-On-Fermentable-Sub.Pdf (Accessed on 14 May 2021)
minerals Review Geochemical Stability of Oil Sands Tailings in Mine Closure Landforms Heidi L. Cossey 1, Anya E. Batycky 1 , Heather Kaminsky 2 and Ania C. Ulrich 1,* 1 Department of Civil & Environmental Engineering, University of Alberta, Edmonton, AB T6G 1H9, Canada; [email protected] (H.L.C.); [email protected] (A.E.B.) 2 Centre for Oil Sands Sustainability, Northern Alberta Institute of Technology (NAIT), Edmonton, AB T5G 0Y2, Canada; [email protected] * Correspondence: [email protected]; Tel.: +1-780-492-8293 Abstract: Oil sands surface mining in Alberta has generated over a billion cubic metres of waste, known as tailings, consisting of sands, silts, clays, and process-affected water that contains toxic organic compounds and chemical constituents. All of these tailings will eventually be reclaimed and integrated into one of two types of mine closure landforms: end pit lakes (EPLs) or terrestrial landforms with a wetland feature. In EPLs, tailings deposits are capped with several metres of water while in terrestrial landforms, tailings are capped with solid materials, such as sand or overburden. Because tailings landforms are relatively new, past research has heavily focused on the geotechnical and biogeochemical characteristics of tailings in temporary storage ponds, referred to as tailings ponds. As such, the geochemical stability of tailings landforms remains largely unknown. This review discusses five mechanisms of geochemical change expected in tailings landforms: consolidation, chemical mass loading via pore water fluxes, biogeochemical cycling, polymer degradation, and surface water and groundwater interactions. Key considerations and knowledge gaps with regard Citation: Cossey, H.L.; Batycky, A.E.; Kaminsky, H.; Ulrich, A.C.