The Ubiquitous Triclosan a Common Antibacterial Agent Exposed
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Chemical Disinfectants for Biohazardous Materials (3/21)
Safe Operating Procedure (Revised 3/21) CHEMICAL DISINFECTANTS FOR BIOHAZARDOUS MATERIALS ____________________________________________________________________________ Chemicals used for biohazardous decontamination are called sterilizers, disinfectants, sanitizers, antiseptics and germicides. These terms are sometimes equivalent, but not always, but for the purposes of this document all the chemicals described herein are disinfectants. The efficacy of every disinfectant is based on several factors: 1) organic load (the amount of dirt and other contaminants on the surface), 2) microbial load, 3) type of organism, 4) condition of surfaces to be disinfected (i.e., porous or nonporous), and 5) disinfectant concentration, pH, temperature, contact time and environmental humidity. These factors determine if the disinfectant is considered a high, intermediate or low-level disinfectant, in that order. Prior to selecting a specific disinfectant, consider the relative resistance of microorganisms. The following table provides information regarding chemical disinfectant resistance of various biological agents. Microbial Resistance to Chemical Disinfectants: Type of Microbe Examples Resistant Bovine spongiform encephalopathy (Mad Prions Cow) Creutzfeldt-Jakob disease Bacillus subtilis; Clostridium sporogenes, Bacterial Spores Clostridioides difficile Mycobacterium bovis, M. terrae, and other Mycobacteria Nontuberculous mycobacterium Poliovirus; Coxsackievirus; Rhinovirus; Non-enveloped or Small Viruses Adenovirus Trichophyton spp.; Cryptococcus sp.; -
Sodium Dodecyl Sulfate
Catalog Number: 102918, 190522, 194831, 198957, 811030, 811032, 811033, 811034, 811036 Sodium dodecyl sulfate Structure: Molecular Formula: C12H25NaSO4 Molecular Weight: 288.38 CAS #: 151-21-3 Synonyms: SDS; Lauryl sulfate sodium salt; Dodecyl sulfate sodium salt; Dodecyl sodium sulfate; Sodium lauryl sulfate; Sulfuric acid monododecyl ester sodium salt Physical Appearance: White granular powder Critical Micelle Concentration (CMC): 8.27 mM (Detergents with high CMC values are generally easy to remove by dilution; detergents with low CMC values are advantageous for separations on the basis of molecular weight. As a general rule, detergents should be used at their CMC and at a detergent-to-protein weight ratio of approximately ten. 13,14 Aggregation Number: 62 Solubility: Soluble in water (200 mg/ml - clear, faint yellow solution), and ethanol (0.1g/10 ml) Description: An anionic detergent3 typically used to solubilize8 and denature proteins for electrophoresis.4,5 SDS has also been used in large-scale phenol extraction of RNA to promote the dissociation of protein from nucleic acids when extracting from biological material.12 Most proteins bind SDS in a ratio of 1.4 grams SDS to 1 gram protein. The charges intrinsic to the protein become insignificant compared to the overall negative charge provided by the bound SDS. The charge to mass ratio is essentially the same for each protein and will migrate in the gel based only on protein size. Typical Working Concentration: > 10 mg SDS/mg protein Typical Buffer Compositions: SDS Electrophoresis -
Decontamination of Rooms, Medical Equipment and Ambulances Using an Aerosol of Hydrogen Peroxide Disinfectant B.M
Journal of Hospital Infection (2006) 62, 149–155 www.elsevierhealth.com/journals/jhin Decontamination of rooms, medical equipment and ambulances using an aerosol of hydrogen peroxide disinfectant B.M. Andersena,*, M. Rascha, K. Hochlina, F.-H. Jensenb, P. Wismarc, J.-E. Fredriksend aDepartment of Hospital Infection, Ulleva˚l University Hospital, Oslo, Norway bDivision of Pre-hospital Care, Ulleva˚l University Hospital, Oslo, Norway cDepartment of Medical Equipment, Ulleva˚l University Hospital, Oslo, Norway dHealth and Environment AS, Oslo, Norway Received 17 November 2004; accepted 1 July 2005 KEYWORDS Summary A programmable device (Sterinis, Gloster Sante Europe) Room decontamina- providing a dry fume of 5% hydrogen peroxide (H2O2) disinfectant was tion; Ambulance tested for decontamination of rooms, ambulances and different types of decontamination; medical equipment. Pre-set concentrations were used according to the Medical equipment decontamination; volumes of the rooms and garages. Three cycles were performed with Hydrogen peroxide increasing contact times. Repetitive experiments were performed using fume decontamina- Bacillus atrophaeus (formerly Bacillus subtilis) Raven 1162282 spores to tion; Spore test control the effect of decontamination; after a sampling plan, spore strips were placed in various positions in rooms, ambulances, and inside and outside the items of medical equipment. Decontamination was effective in 87% of 146 spore tests in closed test rooms and in 100% of 48 tests in a surgical department when using three cycles. One or two cycles had no effect. The sporicidal effect on internal parts of the medical equipment was only 62.3% (220 tests). When the devices were run and ventilated during decontamination, 100% (57/57) of spore strips placed inside were decontaminated. -
Evaluating Disinfectants for Use Against the COVID-19 Virus
When it comes to choosing a disinfectant to combat the COVID-19 virus, research and health authorities suggest not all disinfectants are equally effective. The difference is in their active ingredient(s). HEALTH CANADA AND U.S. EPA ASSESSMENTS The work to evaluate disinfectants perhaps best starts with lists of approved disinfectants compiled by government health authorities. Health Canada has compiled a list of 85 hard surface disinfectant products (as of March 20, 2020) that meet their requirements for disinfection of emerging pathogens, including the virus that causes COVID-19. It can be accessed here. You can wade through the entire list. But if you locate the Drug Identification Number (DIN) on the disinfectant product label or the safety data sheet (SDS), then you can use the search function to quickly see if the product meets Health Canada requirements. A second list, updated on March 19, 2020, provides 287 products that meet the U.S. Environmental Protection Agency’s (EPA) criteria for use against SARS-CoV-2, the novel coronavirus that causes the disease COVID-19. This list can be found here. Like the Health Canada list, you can wade through this one too. However, to best use this list, you should locate the U.S. EPA registration number on the product label or SDS, and use that number to search the list. The U.S. EPA registration number of a product consists of two sets of numbers separated by a hyphen. The first set of numbers refers to the company identification number, and the second set of numbers following the hyphen represents the product number. -
Safer Disinfectant Use in Child Care and Schools During the COVID-19 Pandemic
Safer Disinfectant Use in Child Care and Schools During the COVID-19 Pandemic Vickie Leonard, PhD Environmental Health in Early Care and Educaon Project, Western States Pediatric Environmental Health Specialty Unit (WSPEHSU) 1 Why Should We Be Concerned about Environmental Health in ECE? 2 Why Should We Be Concerned about Environmental Health in ECE? • There are 8 million children in child care centers in the U.S. A child may spend up to 12,500 hours in an ECE facility. A million child care providers work in these centers in the U.S. Half are child-bearing age. • Many toxicants found in child care facilities are not addressed in state child care health and safety regulations. • No agency at the state or federal level is charged with ensuring children’s health and safety in and around schools and ECE facilities. • No systematic means exists for collecting data on environmental exposures in these buildings. • Teachers have more protection in these buildings (unions, OSHA) than children do 3 Why Should We Be Concerned about Environmental Health in ECE? • Many people think that adults and children are exposed to, and affected by, toxic chemicals in the same way. • This is not the case. • Children • have higher exposures to toxicants in the environment, • are more vulnerable to the effects of those toxicants than adults. 4 Cleaning and Disinfec?ng Products: A Major Source of Exposure in Child Care and Schools • Products used to clean, sanitize and disinfect child care facilities and schools are a good example of the pervasive and unregulated use of toxic chemicals that put the health of our children at risk. -
Triclosan Disrupts Thyroid Hormones: Mode-Of-Action, Developmental Susceptibility, and Determination of Human Relevance
Triclosan Disrupts Thyroid Hormones: Mode-of-Action, Developmental Susceptibility, and Determination of Human Relevance Katie Beth Paul “A dissertation submitted to the faculty of the University of North Carolina at Chapel Hill in partial fulfillment of the requirements for the degree of Doctor of Philosophy in the Curriculum of Toxicology.” Chapel Hill 2011 Approved by: Kim L. R. Brouwer, Pharm.D., Ph.D. Kevin M. Crofton, Ph.D. Michael J. DeVito, Ph.D. Philip C. Smith, Ph.D James A. Swenberg, D.V.M., Ph.D. ©2011 Katie Beth Paul ALL RIGHTS RESERVED ii Abstract Katie Beth Paul Triclosan Disrupts Thyroid Hormones: Mode-of-Action, Developmental Susceptibility, and Determination of Human Relevance (Under the direction of Kevin M. Crofton, Ph.D.) Preliminary study demonstrated that triclosan (TCS), a bacteriostat in myriad consumer products, decreases serum thyroxine (T4) in rats. Adverse neurodevelopmental consequences result from thyroid hormone (TH) disruption; therefore determination of whether TCS disrupts THs during development, its mode-of-action (MOA), and the human relevance is critical. This research tested the hypothesis that TCS disrupts THs via activation of pregnane X and constitutive androstane receptors (PXR, CAR), mediating Phase I-II enzyme and hepatic transporter expression and protein changes, thereby increasing catabolism and elimination of THs, resulting in decreased TH concentrations. For Aim One, the hypothesized MOA was assessed using weanling female Long-Evans rats orally exposed to TCS (0-1000 mg/kg/day) for four days. Serum T4 decreased 35% at 300 mg/kg/day. Activity and expression of markers of Phase I (Cyp2b, Cyp3a1) and Phase II (Ugt1a1, Sult1c1) metabolism were moderately induced, consistent with PXR and/or CAR activation and increased hepatic catabolism. -
Tutorial on Working with Micelles and Other Model Membranes
Tutorial on Working with Micelles and Model Membranes Chuck Sanders Dept. of Biochemistry, Dept. of Medicine, and Center for Structural Biology Vanderbilt University School of Medicine. http://structbio.vanderbilt.edu/sanders/ March, 2017 There are two general classes of membrane proteins. This presentation is on working with integral MPs, which traditionally could be removed from the membrane only by dissolving the membrane with detergents or organic solvents. Multilamellar Vesicles: onion-like assemblies. Each layer is one bilayer. A thin layer of water separates each bilayer. MLVs are what form when lipid powders are dispersed in water. They form spontaneously. Cryo-EM Micrograph of a Multilamellar Vesicle (K. Mittendorf, C. Sanders, and M. Ohi) Unilamellar Multilamellar Vesicle Vesicle Advances in Anesthesia 32(1):133-147 · 2014 Energy from sonication, physical manipulation (such as extrusion by forcing MLV dispersions through filters with fixed pore sizes), or some other high energy mechanism is required to convert multilayered bilayer assemblies into unilamellar vesicles. If the MLVs contain a membrane protein then you should worry about whether the protein will survive these procedures in folded and functional form. Vesicles can also be prepared by dissolving lipids using detergents and then removing the detergent using BioBeads-SM dialysis, size exclusion chromatography or by diluting the solution to below the detergent’s critical micelle concentration. These are much gentler methods that a membrane protein may well survive with intact structure and function. From: Avanti Polar Lipids Catalog Bilayers can undergo phase transitions at a critical temperature, Tm. Native bilayers are usually in the fluid (liquid crystalline) phase. -
Phenol Health and Safety Guide
C - z_ IPCS INTERNATIONAL._ PROGRAMME ON CHEMICAL SAFETY OD 341 Health and Safety Guide No. 88 .P5 94 Ph c.2 PHENOL HEALTH AND SAFETY GUIDE ' UNITED NATIONS INTERNATIONAL ENVffiONMENTPROG~E LABOUR ORGANISATION WORLD HEALTH ORGANIZATION WORLD HEALTH ORGANIZATION, GENEVA 1994 1 I) 1\ ' ~Ii>cs Other HEALTH AND SAFETY GUIDES available: (continued on inside back cover) Acrolein (No . 67, 1992) Endrin (No. 60, 1991) Acrylamide (No. 45 , 1991) Epichlorohydrin (No. 8, 1987) Acrylonitrile (No. I, 1986) Ethylene oxide (No. 16, 1988) Aldicarb (No. 64, 1991) Fenitrothion (No. 65, 1991) Aldrin and dieldrin (No. 21 , 1988) Fenvalerate (No. 34, 1989) Allethrins (No. 24, 1989) Folpet (No. 72, 1992) Amitrole (No. 85 , 1994) Formaldehyde (No. 57, 1991) Ammonia (No. 37, 1990) Heptachlor (No. 14, 1988) Arsenic compounds, inorganic, other than Hexachlorobutadiene (No. 84, 1993) arsine (No. 70, 1992) Hexachlorocyclohexanes, alpha- and Atrazine (No. 47, 1990) beta- (No. 53, 1991) Barium (No. 46 , 1991) Hexachlorocyclopentadiene (No. 63 , 1991) Benomyl (No. 81, 1993) n-Hexane (No. 59, 1991) Bentazone (No. 48, 1990) Hydrazine (No. 56, 1991) Beryllium (No. 44, 1990) Isobenzan (No. 61 , 1991) !-Butanol (No. 3, 1987) Isobutanol (No. 9, 1987) 2-Butanol (No. 4, 1987) Kelevan (No. 2, 1987) ten-Butanol (No. 7, 1987) Lindane (No. 54 , 1991) Camphechlor (No. 40, 1990) Magnetic fields (No. 27, 1990) Captafol (No. 49, 1990) Methamidophos (No. 79, 1993) Captan (No. 50, 1990) Methyl bromide (Bromomethane) (No. 86, 1994) Carbaryl (No. 78, 1993) Methyl isobutyl ketone (No. 58, 1991) Carbendazim (No. 82, 1993) Methyl parathion (No. 75, 1992) Chlordane (No. 13 , 1988) Methylene chloride (No. -
Chemical Matricectomy with Phenol Versus Aesthetic Reconstruction. a Single Blinded Randomized Clinical Trial
Journal of Clinical Medicine Article The Treatment of Ingrown Nail: Chemical Matricectomy With Phenol Versus Aesthetic Reconstruction. A Single Blinded Randomized Clinical Trial Juan Manuel Muriel-Sánchez 1, Ricardo Becerro-de-Bengoa-Vallejo 2 , Pedro Montaño-Jiménez 1 and Manuel Coheña-Jiménez 1,* 1 Facultad de Enfermería, Fisioterapia y Podología, Universidad de Sevilla, 41009 Sevilla, Spain; [email protected] (J.M.M.-S.); [email protected] (P.M.-J.) 2 Facultad de Enfermería, Fisioterapia y Podología, Universidad Complutense de Madrid, 28040 Madrid, Spain; [email protected] * Correspondence: [email protected] Received: 29 January 2020; Accepted: 18 March 2020; Published: 20 March 2020 Abstract: Background: In onychocryptosis surgery, incisional and non-incisional matricectomy is indicated according to the stage. The chemical matricectomy with 88% phenol solution is the gold standard and a wedge resection is indicated for more advanced stages. The aesthetic reconstruction has the advantages of the incisional procedure without eponychium incisions and an effectiveness similar to the chemical matricectomy with phenol. Objective: To compare the recurrence and the healing time between the chemical matricectomy with phenol and the aesthetic reconstruction. Methods: A comparative, prospective, parallel, randomized, and one-blinded clinical trial was registered with the European Clinical Trials Database (EudraCT) with identification number 2019-001294-80. Thrity-four patients (56 feet) with 112 onychocryptosis were randomized in two groups. Thirty-six were treated with chemical matricectomy with phenol and 76 with aesthetic reconstruction. Each patient was blind to the surgical procedure assigned by the investigator. The primary outcome measurements were healing time and recurrence. The secondary outcome measurements were post-surgical bleeding, pain, inflammation, and infection rate. -
Pharmaceuticals and Endocrine Active Chemicals in Minnesota Lakes
Pharmaceuticals and Endocrine Active Chemicals in Minnesota Lakes May 2013 Authors Mark Ferrey Contributors/acknowledgements The MPCA is reducing printing and mailing costs This report contains the results of a study that by using the Internet to distribute reports and characterizes the presence of unregulated information to wider audience. Visit our website contaminants in Minnesota’s lakes. The study for more information. was made possible through funding by the MPCA reports are printed on 100 percent post- Minnesota Clean Water Fund and by funding by consumer recycled content paper manufactured the U.S. Environmental Protection Agency without chlorine or chlorine derivatives. (EPA), which facilitated the sampling of lakes for this study. The Minnesota Pollution Control Agency (MPCA) thanks the following for assistance and advice in designing and carrying out this study: Steve Heiskary, Pam Anderson, Dereck Richter, Lee Engel, Amy Garcia, Will Long, Jesse Anderson, Ben Larson, and Kelly O’Hara for the long hours of sampling for this study. Cynthia Tomey, Kirsten Anderson, and Richard Grace of Axys Analytical Labs for the expert help in developing the list of analytes for this study and logistics to make it a success. Minnesota Pollution Control Agency 520 Lafayette Road North | Saint Paul, MN 55155-4194 | www.pca.state.mn.us | 651-296-6300 Toll free 800-657-3864 | TTY 651-282-5332 This report is available in alternative formats upon request, and online at www.pca.state.mn.us. Document number: tdr-g1-16 Contents Contents ........................................................................................................................................... -
Effect of Antimicrobial Triclosan on Reproductive System of Male
A tica nal eu yt c ic a a m A r a c t h a P Ibtisham et al., Pharm Anal Acta 2016, 7:11 Pharmaceutica Analytica Acta DOI: 10.4172/2153-2435.1000516 ISSN: 2153-2435 Review Article Open Access Effect of Antimicrobial Triclosan on Reproductive System of Male Rat Fahar Ibtisham, Aamir Nawab, Yi Zhao, Guanghui Li, Mei Xiao and Lilong An* Agricultural Collage, Guangdong Ocean University, Zhanjiang, Guangdong, China *Corresponding author; Lilong An, Agricultural Collage, Guangdong Ocean University, Haida Road, Mazhang District, Zhanjiang 524088, Guangdong, China, Tel: +86-759-2383247; E-mail: [email protected] Received date: October 31, 2016; Accepted date: November 26, 2016; Published date: November 28, 2016 Copyright: © 2016 Ibtisham F, et al. This is an open-access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited. Abstract Triclosan (5-chloro-2-(2,4-dichlorophenoxy)phenol: TCS) is a synthetic, broad-spectrum antibacterial agent used in broad range of household and personal care products including hand soap, toothpaste, and deodorants. Recently, concerns have been raised over TCS’s potential for endocrine and reproductive disruption. This review contains the information about deleterious toxic effects of TCS on reproductive system of male rat and the possible mechanism. The literature findings showed that TCS deadly affects the reproductive profile of male rats. According to literature TCS depress the testicular function of male rat including spermatogenesis and steroidogenesis by decreasing the androgen production. 3-hydroxysteroid dehydrogenase (3β-HSD) and 17β-hydroxysteroid dehydrogenase (17β- HSD) are two critical enzymes in the steroidogenesis pathway, while according to findings TCS treated rats had lowered concentration of androgen. -
Identification of Methyl Triclosan and Halogenated Analogues
SCIENCE OF THE TOTAL ENVIRONMENT 407 (2009) 2102– 2114 available at www.sciencedirect.com www.elsevier.com/locate/scitotenv Identification of methyl triclosan and halogenated analogues in male common carp (Cyprinus carpio) from Las Vegas Bay and semipermeable membrane devices from Las Vegas Wash, Nevada Thomas J. Leikera,1, Sonja R. Abneya, Steven L. Goodbredb, Michael R. Rosenc,⁎ aUS Geological Survey, Box 25046, MS 407, Denver, CO 80225-0046, USA bUS Geological Survey, California State University, Modoc Hall, 3020 State University Drive East, Suite 3005, Sacramento, CA 95819-6129, USA cUS Geological Survey, 2730 North Deer Run Road, Carson City NV, 89701, USA ARTICLE DATA ABSTRACT Article history: Methyl triclosan and four halogenated analogues have been identified in extracts of individual Received 22 August 2008 whole-body male carp (Cyprinus carpio) tissue that were collected from Las Vegas Bay, Nevada, Received in revised form and Semipermeable Membrane Devices (SPMD) that were deployed in Las Vegas Wash, Nevada. 3 November 2008 Methyl triclosan is believed to be the microbially methylated product of the antibacterial agent Accepted 9 November 2008 triclosan (2, 4, 4'-trichloro-4-hydroxydiphenyl ether, Chemical Abstract Service Registry Number Available online 2 December 2008 3380-34-5, Irgasan DP300). The presence of methyl triclosan and four halogenated analogues was confirmed in SPMD extracts by comparing low- and high-resolution mass spectral data and Keywords: Kovats retention indices of methyl triclosan with commercially obtained triclosan that was Triclosan derivatized to the methyl ether with ethereal diazomethane. The four halogenated analogues of Methyl triclosan methyltriclosandetectedinbothwhole-body tissue and SPMD extracts were tentatively Common carp identified by high resolution mass spectrometry.