Health and Safety Risks for Workers Involved in Manual Tank Gauging and Sampling at Oil and Gas Extraction Sites
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Use of Solvents for Pahs Extraction and Enhancement of the Pahs Bioremediation in Coal- Tar-Contaminated Soils Pak-Hing Lee Iowa State University
Iowa State University Capstones, Theses and Retrospective Theses and Dissertations Dissertations 2000 Use of solvents for PAHs extraction and enhancement of the PAHs bioremediation in coal- tar-contaminated soils Pak-Hing Lee Iowa State University Follow this and additional works at: https://lib.dr.iastate.edu/rtd Part of the Environmental Engineering Commons Recommended Citation Lee, Pak-Hing, "Use of solvents for PAHs extraction and enhancement of the PAHs bioremediation in coal-tar-contaminated soils " (2000). Retrospective Theses and Dissertations. 13912. https://lib.dr.iastate.edu/rtd/13912 This Dissertation is brought to you for free and open access by the Iowa State University Capstones, Theses and Dissertations at Iowa State University Digital Repository. It has been accepted for inclusion in Retrospective Theses and Dissertations by an authorized administrator of Iowa State University Digital Repository. For more information, please contact [email protected]. INFORMATION TO USERS This manuscript has been reproduced from the microfilm master. UMI films the text directly from the original or copy submitted. Thus, some thesis and dissertation copies are in typewriter fece, while others may be from any type of computer printer. The quality of this reproduction is dependent upon the quaiity of the copy submitted. Broken or indistinct print colored or poor quality illustrations and photographs, print bleedthrough, substeindard margins, and improper alignment can adversely affect reproduction. In the unlilcely event that the author did not send UMI a complete manuscript and there are missing pages, these will be noted. Also, if unauthorized copyright material had to be removed, a note will indicate the deletion. -
Supporting Information of Polycyclic Aromatic Hydrocarbons (Pahs) In
Supporting Information of Polycyclic aromatic hydrocarbons (PAHs) in aerosols over the central Himalayas along two south-north transects Peng Fei Chen1,5, Chao Liu Li1, Shi Chang Kang2,3*, Maheswar Rupakheti4, Arnico K Panday6, Fang Ping Yan2,5, Quan Lian Li2, Qiang Gong Zhang1,3, Jun Ming Guo1,5, Dipesh Rupakheti1,5, Wei Luo7 1Key Laboratory of Tibetan Environment Changes and Land Surface Processes, Institute of Tibetan Plateau Research, Chinese Academy of Sciences, Beijing 100101, China 2State Key Laboratory of Cryospheric Science, Cold and Arid Regions Environmental and Engineering Research Institute, Lanzhou 730000, China 3Center for Excellence in Tibetan Plateau Earth Sciences, Chinese Academy of Sciences, Beijing 100085, China; 4Institute for Advanced Sustainability Studies, Potsdam 14467, Germany 5University of Chinese Academy of Sciences, Beijing 100039, China 6International Centre for Integrated Mountain Development, Kathmandu, Nepal 7State Key Lab of Urban and Regional Ecology, Research Center for Eco-Environmental Sciences, Chinese Academy of Sciences, Beijing 100085, China Correspondence to: S. Kang ([email protected]) Text SI-1 Sample extraction and analysis Text SI-2 Quality control Table SI-1 Percentage contribution (%) of each species to total PAHs in the atmosphere over the Himalayas. Text SI-1 Sample extraction and analysis A quarter of each filter was cut into pieces, placed into a glass tube, and immersed in 20 mL of dichloromethane (DCM) and n-hexane (1:1). The extraction was performed by sonication twice for 30 min at 27 °C. Every single sample was spiked with deuterated PAHs (naphthalene-d8, acenaphthene-d10, phenanthrene-d10, chrysene-d12, and perylene-d12) as recovery surrogates. -
Effect of Epoxide Content on the Vulcanizate Structure of Silica-Filled Epoxidized Natural Rubber (ENR) Compounds
polymers Article Effect of Epoxide Content on the Vulcanizate Structure of Silica-Filled Epoxidized Natural Rubber (ENR) Compounds Gyeongchan Ryu 1, Donghyuk Kim 1, Sanghoon Song 1, Kiwon Hwang 1, Byungkyu Ahn 2 and Wonho Kim 1,* 1 School of Chemical Engineering, Pusan National University, Busan 46241, Korea; [email protected] (G.R.); [email protected] (D.K.); [email protected] (S.S.); [email protected] (K.H.) 2 Hankook Tire & Technology Co., Ltd., R&D Center, 50 Yuseong-daero 935 beon-gil, Yuseong-gu, Daejeon 34127, Korea; [email protected] * Correspondence: [email protected]; Tel.: +82-51-510-3190 Abstract: The demand for truck–bus radial (TBR) tires with enhanced fuel efficiency has grown in recent years. Many studies have investigated silica-filled natural rubber (NR) compounds to address these needs. However, silica-filled compounds offer inferior abrasion resistance compared to carbon black-filled compounds. Further, the use of NR as a base rubber can hinder silanization and coupling reactions due to interference by proteins and lipids. Improved silica dispersion be achieved without the use of a silane coupling agent by introducing epoxide groups to NR, which serve as silica-affinitive functional groups. Furthermore, the coupling reaction can be promoted by facilitating chemical interaction between the hydroxyl group of silica and the added epoxide groups. Thus, this study evaluated the properties of commercialized NR, ENR-25, and ENR-50 compounds with or without an added silane coupling agent, and the filler–rubber interaction was quantitatively calculated using vulcanizate structure analysis. The increased epoxide content, when the silane coupling agent was not used, improved silica dispersion, abrasion resistance, fuel efficiency, and wet Citation: Ryu, G.; Kim, D.; Song, S.; grip. -
Organic Chemistry Name Formula Isomers Methane CH 1 Ethane C H
Organic Chemistry Organic chemistry is the chemistry of carbon. The simplest carbon molecules are compounds of just carbon and hydrogen, hydrocarbons. We name the compounds based on the length of the longest carbon chain. We then add prefixes and suffixes to describe the types of bonds and any add-ons the molecule has. When the molecule has just single bonds we use the -ane suffix. Name Formula Isomers Methane CH4 1 Ethane C2H6 1 Propane C3H8 1 Butane C4H10 2 Pentane C5H12 3 Hexane C6H14 5 Heptane C7H16 9 Octane C8H18 18 Nonane C9H20 35 Decane C10H22 75 Isomers are compounds that have the same formula but different bonding. isobutane n-butane 1 Naming Alkanes Hydrocarbons are always named based on the longest carbon chain. When an alkane is a substituent group they are named using the -yl ending instead of the -ane ending. So, -CH3 would be a methyl group. The substituent groups are named by numbering the carbons on the longest chain so that the first branching gets the lowest number possible. The substituents are listed alphabetically with out regard to the number prefixes that might be used. 3-methylhexane 1 2 3 4 5 6 6 5 4 3 2 1 Alkenes and Alkynes When a hydrocarbon has a double bond we replace the -ane ending with -ene. When the hydrocarbon has more than three carbon the position of the double bond must be specified with a number. 1-butene 2-butene Hydrocarbons with triple bonds are named basically the same, we replace the -ane ending with -yne. -
&EPA Ambient Water Quality Criteria for Toluene
United States Cffice of Water EPA 440/5-80-075 Environmental Protection Regula.ions and Standards O,:tober 1980 Agency Criteria and Standards Division Washington DC 20480 c.). & EPA Ambient Water Quality Criteria for Toluene tz r AMBIENT WATER QUALITY CRITERIA FOR TOLUENE Prepared By U.S. ENVIRONMENTAL PROTECTION AGENCY Office of Water Regulations and Standards Criteria and Standards Division Washington, D.C. Office of Research and Development Environmental Criteria and Assessment Office Cincinnati, Ohio Carcinogen Assessment Group Washington, D.C. Environmental Research Laboratories Corvalis, Oregon Duluth, Minnesota Gulf Breeze, Florida Narragansett, Rhode Island DISCLAIMER This report has been reviewed by the Environmental Criteria and Assessment Office, U.S. Environmental Protection Agency, and approved for publication. Mention of trade names or commercial products does not constitute endorsement or recommendation for use. AVAILABILITY NOTICE This document is available to the public through the National Technical Information Service, (NTIS), Springfield, Virginia 22161. El~TAL l'R~e1'!tjf A~ ii FOREWORD Section 304 (a)(1) of the Clear Water Act of 1977 (P.L. 95-217), requires the Administrator of the Environmental Protection Agency to publish criteria for water quality accurately reflecting the latest scientific knowledge on the kind and extent of all identifiable effects on health and welfare which may be expected from the presence of pollutants in any body of water, including ground water. Proposed water quality criteria for the 65 toxic pollutants listed under section 307 (a) (1) of the Cl ean Water Act were deve loped and a notice of thei r availability was published for public comment on March 15, 1979 (44 FR 15926), July 25, 1979 (44 FR 43660), and October 1, 1979 (44 FR 56628). -
Introduction to Alkenes and Alkynes in an Alkane, All Covalent Bonds
Introduction to Alkenes and Alkynes In an alkane, all covalent bonds between carbon were σ (σ bonds are defined as bonds where the electron density is symmetric about the internuclear axis) In an alkene, however, only three σ bonds are formed from the alkene carbon -the carbon thus adopts an sp2 hybridization Ethene (common name ethylene) has a molecular formula of CH2CH2 Each carbon is sp2 hybridized with a σ bond to two hydrogens and the other carbon Hybridized orbital allows stronger bonds due to more overlap H H C C H H Structure of Ethylene In addition to the σ framework of ethylene, each carbon has an atomic p orbital not used in hybridization The two p orbitals (each with one electron) overlap to form a π bond (p bonds are not symmetric about the internuclear axis) π bonds are not as strong as σ bonds (in ethylene, the σ bond is ~90 Kcal/mol and the π bond is ~66 Kcal/mol) Thus while σ bonds are stable and very few reactions occur with C-C bonds, π bonds are much more reactive and many reactions occur with C=C π bonds Nomenclature of Alkenes August Wilhelm Hofmann’s attempt for systematic hydrocarbon nomenclature (1866) Attempted to use a systematic name by naming all possible structures with 4 carbons Quartane a alkane C4H10 Quartyl C4H9 Quartene e alkene C4H8 Quartenyl C4H7 Quartine i alkine → alkyne C4H6 Quartinyl C4H5 Quartone o C4H4 Quartonyl C4H3 Quartune u C4H2 Quartunyl C4H1 Wanted to use Quart from the Latin for 4 – this method was not embraced and BUT has remained Used English order of vowels, however, to name the groups -
Stability Studies of Selected Polycyclic Aromatic Hydrocarbons in Different Organic Solvents and Identification of Their Transformation Products
Polish J. of Environ. Stud. Vol. 17, No. 1 (2008), 17-24 Original Research Stability Studies of Selected Polycyclic Aromatic Hydrocarbons in Different Organic Solvents and Identification of Their Transformation Products D. Dąbrowska1, A. Kot-Wasik2, J. Namieśnik*2 1Polish geological institute, Central Chemical laboratory, warsaw, Poland 2Department of Analytical Chemistry, gdansk university of technology, ul. Narutowicza 11/12, 80-892 gdańsk, Poland Received: May 7, 2007 Accepted: October 1, 2007 Abstract one of the problems in an hPlC laboratory is the preservation of samples and extracts prior to analysis without any changes. It has been found that degradation processes cannot be eliminated entirely, but they can be slowed down considerably. Photodegradation kinetics of fluorene, anthracene and benzo(a)pyrene were studied in various organic solvents. Solvents known as good media to store PAhs for a long time were selected with respect to avoid degradation. in the case of fluorene, 9-fluorenone and 9-hydroxyfluorene were detected as main photoproducts. Formation of anthraquinone and 1,8-dihydroxyanthraquinone during the degradation of anthracene was observed. Benzo(a)pyrene-4,5-dihydrodiol and one of the isomers of hydroxy-BaP-dione as products of benzo(a)pyrene photodegradation have been identified. Keywords: polycyclic aromatic hydrocarbons, photodegradation, degradation products, sample stability Introduction 4 or more rings and their metabolites, have a variety of mutagenic and carcinogenic effects on microorganisms, Polycyclic aromatic hydrocarbons (PAhs) are ubiq- plants and animals, and are classified as compounds with uitous contaminants originating from natural and anthro- significant human health risks [6]. pogenic pyrolysis of organic matter such as forest fires, In the environment, primary removal processes of low automobile exhaust, coal and oil refining processes.t heir molecular weight PAhs are microbial degradation and abundance and persistence in several polluted environ- evaporation. -
INVESTIGATION of POLYCYCLIC AROMATIC HYDROCARBONS (Pahs) on DRY FLUE GAS DESULFURIZATION (FGD) BY-PRODUCTS
INVESTIGATION OF POLYCYCLIC AROMATIC HYDROCARBONS (PAHs) ON DRY FLUE GAS DESULFURIZATION (FGD) BY-PRODUCTS DISSERTATION Presented in Partial Fulfillment of the Requirements for the Degree Doctor of Philosophy in the Graduate School of The Ohio State University By Ping Sun, M.S. ***** The Ohio State University 2004 Dissertation Committee: Approved by Professor Linda Weavers, Adviser Professor Harold Walker Professor Patrick Hatcher Adviser Professor Yu-Ping Chin Civil Engineering Graduate Program ABSTRACT The primary goal of this research was to examine polycyclic aromatic hydrocarbons (PAHs) on dry FGD by-products to determine environmentally safe reuse options of this material. Due to the lack of information on the analytical procedures for measuring PAHs on FGD by-products, our initial work focused on analytical method development. Comparison of the traditional Soxhlet extraction, automatic Soxhlet extraction, and ultrasonic extraction was conducted to optimize the extraction of PAHs from lime spray dryer (LSD) ash (a common dry FGD by-product). Due to the short extraction time, ultrasonic extraction was further optimized by testing different organic solvents. Ultrasonic extraction with toluene as the solvent turned out to be a fast and efficient method to extract PAHs from LSD ash. The possible reactions of PAHs under standard ultrasonic extraction conditions were then studied to address concern over the possible degradation of PAHs by ultrasound. By sonicating model PAHs including naphthalene, phenanthrene and pyrene in organic solutions, extraction parameters including solvent type, solute concentration, and sonication time on reactions of PAHs were examined. A hexane: acetone (1:1 V/V) ii mixture resulted in less PAH degradation than a dichloromethane (DCM): acetone (1:1 V/V) mixture. -
Managing Exposure to Benzene and Total Petroleum Hydrocarbons at Two Oil Refineries 1977–2014
International Journal of Environmental Research and Public Health Article Managing Exposure to Benzene and Total Petroleum Hydrocarbons at Two Oil Refineries 1977–2014 Tapani Tuomi *, Henna Veijalainen and Tiina Santonen Finnish Institute of Occupational Health (FIOH), Topeliuksenkatu 41 B, P.O. Box 40, Työterveyslaitos, FI-00032 Helsinki, Finland; henna.veijalainen@ttl.fi (H.V.); tiina.santonen@ttl.fi (T.S.) * Correspondence: tapani.tuomi@ttl.fi; Tel.: +358-9-4747-2926 Received: 15 December 2017; Accepted: 18 January 2018; Published: 24 January 2018 Abstract: Air concentrations of and inhalation exposure to total petroleum hydrocarbons (TPH) and benzene was monitored separately at two oil refineries from 1977 to 2014. Prevention policies and control measures that may explain changes were surveyed. The aim was to evaluate how the application of of Occupational Health and Safety Assessment Series OHSAS 18001.04 principles as well as Environmental protection Agency EPA and European Oil Company Organisation for Environment, Health and Safety CONCAWE practices have influenced air concentrations. Benzene air concentrations declined in 11 of 17 units, six of which were associated with declining exposures. Benzene air concentrations declined across all units on average by 46%. This amounts to an average yearly decline of 1.7%. TPH air concentrations declined in 10 of 17 units, seven of which were associated with declining exposures. The average decline in TPH air concentrations was 49%, corresponding to 1.3% per year. As a result, average working day exposure in 10 of 17 units have declined significantly and today, benzene and TPH exposure in most units are well below 10% of the current Occupational Exposure Limit (OEL8h:s). -
Organic Nomenclature: Naming Organic Molecules
Organic Nomenclature: Naming Organic Molecules Mild Vegetable Alkali Aerated Alkali What’s in a name? Tartarin Glauber's Alkahest Alkahest of Van Helmot Fixed Vegetable Alkali Russian Pot Ash Cendres Gravellees Alkali Mild Vegetable Oil of Tartar Pearl Ash Tartar Alkahest of Reapour K2CO3 Alkali of Reguline Caustic Sal Juniperi Potassium Carbonate Ash ood Alkali of Wine Lees Salt of Tachenius W Fixed Sal Tartari Sal Gentianae Alkali Salt German Ash Salt of Wormwood Cineres Clavellati Sal Guaiaci exSal Ligno Alkanus Vegetablis IUPAC Rules for naming organic molecules International Union of Pure and Applied Chemists 3 Name Molecular Prefix Formula Methane CH4 Meth Ethane C2H6 Eth Alkanes Propane C3H8 Prop Butane C4H10 But CnH2n+2 Pentane C5H12 Pent Hexane C6H14 Hex Heptane C7H16 Hept Octane C8H18 Oct Nonane C9H20 Non Decane C10H22 Dec 4 Structure of linear alkanes propane butane pentane hexane heptane octane nonane decane 5 Constitutional Isomers: molecules with same molecular formula but differ in the way in which the atoms are connected to each other 6 Physical properties of constiutional isomers 7 Isomers n # of isomers 1 1 2 1 The more carbons in a 3 1 molecule, the more 4 2 possible ways to put 5 3 them together. 6 5 7 9 8 18 9 35 10 75 15 4,347 25 36,797,588 8 Naming more complex molecules hexane C6H14 9 Naming more complex molecules Step 1: identify the longest continuous linear chain: this will be the root name: this is the root name 2 4 6 longest chain = 6 (hexane) 1 3 5 2 4 3 4 3 2 2 1 5 4 1 3 5 correct 1 incorrect longest chain = 5 (pentane) longest chain = 5 (pentane) 1 3 1 2 2 3 4 4 longest chain = 4 (butane) longest chain = 4 (butane) 10 Naming more complex molecules Step 2: identify all functional group (the groups not part of the “main chain”) CH3 2 4 4 3 2 1 5 1 3 5 CH3 main chain: pentane main chain: pentane CH3 1 3 1 2 2 3 4 4 CH3 CH3 CH3 main chain: butane main chain: butane 11 Alkyl groups: fragments of alkanes H H empty space (point where it H C H H C attaches to something else) H H methane methyl CH4 CH3 12 More generally.. -
25WORDS ETHYLENE Ethylene, C2H4 ,Is an Unsaturated
25WORDS ETHYLENE Ethylene, C2H4 ,is an unsaturated hydrocarbon that is used in industrial plants and sometimes as a hormone in an average medicine cabinet. It also is the most globally produced organic compound in the world. Ethylene, C2H4, is a hydrocarbon gas that is widely used in the world's industry for purposes like ripening fruit, making detergents, and for making soda. It is also highly flammable and colorless. Ethylene is an unsaturated hydrocarbon, composed of four hydrogen atoms bound to a pair of carbon atoms by means of a double bond. Ethylene has a molar mass of 28.05 g/mol Ethylene is the simplest member of the class called alkenes. It is a colorless, quite sweet- smelling gas. This gas is very reactive and burns with a very bright flame. ethylene (C2H4); Ethylene is known as the simplest alkene and an important hormone in organic chemistry. Over 80% of ethylene is used as a main component of polyethylene and to ripen fruit faster. Ethylene, C2H4, is a colorless gas that can be used as an inhalation anesthetic. This gas is also commonly used to keep fruit ripe as well as to cut and wield metals. Ethylene, C2H4, is an unsaturated hydrocarbon. It is used in anesthetic agents and in detergents. It is the most widely produced organic compound in the world. Ethylene (C2H4): Ethylene is an unsaturated hydrocarbon that is used in the production of polyethylene, a widely used plastic. It can be modified to become ethylene glycol (an antifreeze) and ethylene dichloride (used in creating polyvinyl chloride Ethlyene; Ethylene, C2H4, is a colorless, odorless gas that can be produced in nature as well as man-made processes. -
Polycyclic Aromatic Hydrocarbons (Pahs)
Polycyclic Aromatic Hydrocarbons (PAHs) Factsheet 4th edition Donata Lerda JRC 66955 - 2011 The mission of the JRC-IRMM is to promote a common and reliable European measurement system in support of EU policies. European Commission Joint Research Centre Institute for Reference Materials and Measurements Contact information Address: Retiewseweg 111, 2440 Geel, Belgium E-mail: [email protected] Tel.: +32 (0)14 571 826 Fax: +32 (0)14 571 783 http://irmm.jrc.ec.europa.eu/ http://www.jrc.ec.europa.eu/ Legal Notice Neither the European Commission nor any person acting on behalf of the Commission is responsible for the use which might be made of this publication. Europe Direct is a service to help you find answers to your questions about the European Union Freephone number (*): 00 800 6 7 8 9 10 11 (*) Certain mobile telephone operators do not allow access to 00 800 numbers or these calls may be billed. A great deal of additional information on the European Union is available on the Internet. It can be accessed through the Europa server http://europa.eu/ JRC 66955 © European Union, 2011 Reproduction is authorised provided the source is acknowledged Printed in Belgium Table of contents Chemical structure of PAHs................................................................................................................................. 1 PAHs included in EU legislation.......................................................................................................................... 6 Toxicity of PAHs included in EPA and EU