Chrysene Environmental Hazard Summary
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Polycyclic Aromatic Hydrocarbon Structure Index
NIST Special Publication 922 Polycyclic Aromatic Hydrocarbon Structure Index Lane C. Sander and Stephen A. Wise Chemical Science and Technology Laboratory National Institute of Standards and Technology Gaithersburg, MD 20899-0001 December 1997 revised August 2020 U.S. Department of Commerce William M. Daley, Secretary Technology Administration Gary R. Bachula, Acting Under Secretary for Technology National Institute of Standards and Technology Raymond G. Kammer, Director Polycyclic Aromatic Hydrocarbon Structure Index Lane C. Sander and Stephen A. Wise Chemical Science and Technology Laboratory National Institute of Standards and Technology Gaithersburg, MD 20899 This tabulation is presented as an aid in the identification of the chemical structures of polycyclic aromatic hydrocarbons (PAHs). The Structure Index consists of two parts: (1) a cross index of named PAHs listed in alphabetical order, and (2) chemical structures including ring numbering, name(s), Chemical Abstract Service (CAS) Registry numbers, chemical formulas, molecular weights, and length-to-breadth ratios (L/B) and shape descriptors of PAHs listed in order of increasing molecular weight. Where possible, synonyms (including those employing alternate and/or obsolete naming conventions) have been included. Synonyms used in the Structure Index were compiled from a variety of sources including “Polynuclear Aromatic Hydrocarbons Nomenclature Guide,” by Loening, et al. [1], “Analytical Chemistry of Polycyclic Aromatic Compounds,” by Lee et al. [2], “Calculated Molecular Properties of Polycyclic Aromatic Hydrocarbons,” by Hites and Simonsick [3], “Handbook of Polycyclic Hydrocarbons,” by J. R. Dias [4], “The Ring Index,” by Patterson and Capell [5], “CAS 12th Collective Index,” [6] and “Aldrich Structure Index” [7]. In this publication the IUPAC preferred name is shown in large or bold type. -
ALABAMA SEAFOOD SURVEILLANCE SAMPLES NPH = Naphthalene, FLU = Fluorene, PHN = Phenanthrene, ANT = Anthracene, FLA = Fluoranthene
ALABAMA SEAFOOD SURVEILLANCE SAMPLES NPH = Naphthalene, FLU = Fluorene, PHN = Phenanthrene, ANT = Anthracene, FLA = Fluoranthene, Polycyclic Aromatic Hydrocarbon (PAH) and PYR = Pyrene, BaA = Benz(a)anthracene, CHR = Chrysene, BbF = Benzo(b)fluoranthene, DOSS Results Summary BkF = Benzo(k)fluoranthene, BaP = Benzo(a)pyrene, DBA = Dibenz(a,h)anthracene, IcdPy = Indeno(1,2,3-cd)pyrene, DOSS = Dioctylsulfosuccinate **The estimated maximum total PAH value represents a "worst case" estimate of the PAHs including alkyl homologs that could potentially be in the that happens to yield fluorescence responsesample. Results reported using FDACS Screening Method 521, based on It may include fluorescent compounds other than PAHs and background signal that happens to yield fluorescence response FDA LC Fluorescence Screening Method and FDACS DOSS Levels of Concern bases on FDA's Protocol for Interpretation and Use of Sensory Testing and Analytical Chemistry Results for Reopening In order to "PASS" Method 522 based on FDA's Determination of Levels of Concern (ppm) Oil-Impacted Areas closed to Seafood Harvesting. 7/26/10 samples must not Dioctylsulfosuccinate in Select Seafoods using LC/MS Shrimp and Crab 123 246 1846 246 185 1.32 1.32 13.2 0.132 0.132 1.32 61.5 500 exceed any Sorted by seafood type (crab, finfish, oyster, shrimp), Oysters 133 267 2000 267 200 1.43 143 1.43 14.3 0.143 0.143 1.43 66.5 500 FDA Levels of harvest area and sample # Finfish 32.7 65.3 490 65.3 49 0.35 35 0.35 0.35 0.035 0.035 0.35 16.35 100 Concern <LOD = less than Limit of Detection, -
Azulene—A Bright Core for Sensing and Imaging
molecules Review Azulene—A Bright Core for Sensing and Imaging Lloyd C. Murfin * and Simon E. Lewis Department of Chemistry, University of Bath, Bath BA2 7AY, UK; [email protected] * Correspondence: lloyd.murfi[email protected] Abstract: Azulene is a hydrocarbon isomer of naphthalene known for its unusual colour and fluores- cence properties. Through the harnessing of these properties, the literature has been enriched with a series of chemical sensors and dosimeters with distinct colorimetric and fluorescence responses. This review focuses specifically on the latter of these phenomena. The review is subdivided into two sec- tions. Section one discusses turn-on fluorescent sensors employing azulene, for which the literature is dominated by examples of the unusual phenomenon of azulene protonation-dependent fluorescence. Section two focuses on fluorescent azulenes that have been used in the context of biological sensing and imaging. To aid the reader, the azulene skeleton is highlighted in blue in each compound. Keywords: fluorescence; azulene; sensor; dosimeter; bioimaging; chemosensor; chemodosimeter 1. Introduction Azulene, 1, is an isomer of naphthalene, 2, composed of fused 5- and 7-membered ring systems (Figure1) and named for its vibrant blue colour. Unlike naphthalene, azulene is a non-alternant hydrocarbon, possessing nodal points at C-2 and C-6 of the HOMO and C-1 and C-3 of the LUMO [1]. The location of these nodes results in low electronic repulsion in the S1 singlet excited state, affording a relatively small HOMO-LUMO gap. Hence, the S0!S1 transition arises from absorption in the visible region. Conversely, in naphthalene, coefficient magnitudes remain consistent for each position in both the HOMO Citation: Murfin, L.C.; Lewis, S.E. -
Determination of Petroleum Hydrocarbons in Sediments
UNITED NATIONS ENVIRONMENT PROGRAMME NOVEMBER 1992 Determination of petroleum hydrocarbons in sediments Reference Methods For Marine Pollution Studies No. 20 Prepared in co-operation with IOC IAEA UNEP 1992 ~ i - PREFACE The Regional Seas Programme was initiated by UNEP in 1974. Since then the Governing Conncil ofUNEP has repeatedly endorsed a regional approach to the control of marine pollution and the management of marine and coastal resources and has requested the development of regional action plans. The Regional Seas Progranune at present includes ten regions and has over 120 coastal States participating in it (1),(2). One of the basic components of the action plans sponsored by UNEP in the framework of the Regional Seas Programme is the assessment of the state of the marine em~ronment and of its resources, and of the sources and trends of the pollution, and the impact of pollution on human health, marine ecosystems and amenities. In order to assist those participating in this activity and to ensure that the data obtained through this assessment can be compared. on a world-wide basis and thns contribute to the Global Environment Monitoring System (GEMS) of UNEP, a set of Reference Methods and Guidelines for marine pollution studies is being developed as part of a programme of c9mprehensive technical support which includes the provision of expert advice, reference methods and materials, training and data quality assurance (3). The Methods are recommended to be adopted by Governments participating in tbe Regional Seas Programme. The methods and guidelines are prepared in co-operation with the relevant specialized bodies of the United Nations system as well as other organizations and are tested by a number of experts competent in the field relevant to the methods described. -
Summary of Information for ABC for Polycyclic Aromatic Hydrocarbons
Air Toxics Science Advisory Committee Summary of Information for ABC for Polycyclic Aromatic Hydrocarbons September 16, 2015 ATSAC Meeting #10 Presenter: Sue MacMillan, DEQ ATSAC lead Sue MacMillan | Oregon Department of Environmental Quality 26 Individual PAHs to Serve as Basis of ABC for Total PAHs Acenaphthene Cyclopenta(c,d)pyrene Acenaphthylene Dibenzo(a,h)anthracene Anthracene Dibenzo(a,e)pyrene Anthanthrene Dibenzo(a,h)pyrene Benzo(a)pyrene Dibenzo(a,i)pyrene Naphthalene Benz(a)anthracene Dibenzo(a,l)pyrene has separate Benzo(b)fluoranthene Fluoranthene ABC. Benzo(k)fluoranthene Fluorene Benzo( c)pyrene Indeno(1,2,3-c,d)pyrene Benzo(e)pyrene Phenanthrene Benzo(g,h,i)perylene Pyrene Benzo(j)fluoranthene 5-Methylchrysene Chrysene 6-Nitrochrysene Use of Toxic Equivalency Factors for PAHs • Benzo(a)pyrene serves as the index PAH, and has a documented toxicity value to which other PAHs are adjusted • Other PAHs adjusted using Toxic Equivalency Factors (TEFs), aka Potency Equivalency Factors (PEFs). These values are multipliers and are PAH-specific. • Once all PAH concentrations are adjusted to account for their relative toxicity as compared to BaP, the concentrations are summed • This summed concentration is then compared to the toxicity value for BaP, which is used as the ABC for total PAHs. Source of PEFs for PAHs • EPA provides a range of values of PEFs for each PAH • Original proposal suggested using upper-bound value of each PEF range as the PEF to use for adjustment of our PAHs • Average PEF value for each PAH is a better approximation of central tendency, and is consistent with the use of PEFs by other agencies • Result of using average, rather than upper-bound PEFs: slightly lower summed concentrations for adjusted PAHs, thus less apt to exceed ABC for total PAHs Documents can be provided upon request in an alternate format for individuals with disabilities or in a language other than English for people with limited English skills. -
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 -
Health Risks of Structural Firefighters from Exposure to Polycyclic
International Journal of Environmental Research and Public Health Systematic Review Health Risks of Structural Firefighters from Exposure to Polycyclic Aromatic Hydrocarbons: A Systematic Review and Meta-Analysis Jooyeon Hwang 1,* , Chao Xu 2 , Robert J. Agnew 3 , Shari Clifton 4 and Tara R. Malone 4 1 Department of Occupational and Environmental Health, Hudson College of Public Health, University of Oklahoma Health Sciences Center, Oklahoma City, OK 73104, USA 2 Department of Biostatistics and Epidemiology, Hudson College of Public Health, University of Oklahoma Health Sciences Center, Oklahoma City, OK 73104, USA; [email protected] 3 Fire Protection & Safety Engineering Technology Program, College of Engineering, Architecture and Technology, Oklahoma State University, Stillwater, OK 74078, USA; [email protected] 4 Department of Health Sciences Library and Information Management, Graduate College, University of Oklahoma Health Sciences Center, Oklahoma City, OK 73104, USA; [email protected] (S.C.); [email protected] (T.R.M.) * Correspondence: [email protected]; Tel.: +1-405-271-2070 (ext. 40415) Abstract: Firefighters have an elevated risk of cancer, which is suspected to be caused by occupational and environmental exposure to fire smoke. Among many substances from fire smoke contaminants, one potential source of toxic exposure is polycyclic aromatic hydrocarbons (PAH). The goal of this paper is to identify the association between PAH exposure levels and contributing risk factors to Citation: Hwang, J.; Xu, C.; Agnew, derive best estimates of the effects of exposure on structural firefighters’ working environment in R.J.; Clifton, S.; Malone, T.R. Health fire. We surveyed four databases (Embase, Medline, Scopus, and Web of Science) for this systematic Risks of Structural Firefighters from literature review. -
Design and Synthesis of Novel Symmetric Fluorene-2,7-Diamine Derivatives As Potent Hepatitis C Virus Inhibitors
pharmaceuticals Article Design and Synthesis of Novel Symmetric Fluorene-2,7-Diamine Derivatives as Potent Hepatitis C Virus Inhibitors Mai H. A. Mousa 1, Nermin S. Ahmed 1,*, Kai Schwedtmann 2, Efseveia Frakolaki 3, Niki Vassilaki 3, Grigoris Zoidis 4 , Jan J. Weigand 2 and Ashraf H. Abadi 1,* 1 Department of Pharmaceutical Chemistry, Faculty of Pharmacy and Biotechnology, German University in Cairo, Cairo 11835, Egypt; [email protected] 2 Faculty of Chemistry and Food Chemistry, Technische Universität Dresden, 01062 Dresden, Germany; [email protected] (K.S.); [email protected] (J.J.W.) 3 Molecular Virology Laboratory, Hellenic Pasteur Institute, 11521 Athens, Greece; [email protected] (E.F.); [email protected] (N.V.) 4 Department of Pharmacy, Division of Pharmaceutical Chemistry, School of Health Sciences, National and Kapodistrian University of Athens, 15771 Athens, Greece; [email protected] * Correspondence: [email protected] (N.S.A.); [email protected] (A.H.A.); Tel.: +202-27590700 (ext. 3429) (N.S.A.); +202-27590700 (ext. 3400) (A.H.A.); Fax: +202-27581041 (N.S.A. & A.H.A.) Abstract: Hepatitis C virus (HCV) is an international challenge. Since the discovery of NS5A direct-acting antivirals, researchers turned their attention to pursue novel NS5A inhibitors with optimized design and structure. Herein we explore highly potent hepatitis C virus (HCV) NS5A Citation: Mousa, M.H.A.; Ahmed, inhibitors; the novel analogs share a common symmetrical prolinamide 2,7-diaminofluorene scaffold. N.S.; Schwedtmann, K.; Frakolaki, E.; Modification of the 2,7-diaminofluorene backbone included the use of (S)-prolinamide or its isostere Vassilaki, N.; Zoidis, G.; Weigand, J.J.; (S,R)-piperidine-3-caboxamide, both bearing different amino acid residues with terminal carbamate Abadi, A.H. -
Technical Background Document (U.S
Part 5: CHEMICAL-SPECIFIC PARAMETERS Chemical-specific parameters required for calculating soil screening levels include the organic carbon normalized soil-water partition coefficient for organic compounds (Koc), the soil-water partition coefficient for inorganic constituents (Kd), water solubility (S), Henry's law constant (HLC, HN), air diffusivity (Di,a), and water diffusivity (Di,w). In addition, the octanol-water partition coefficient (Kow) is needed to calculate Koc values. This part of the background document describes the collection and compilation of these parameters for the SSL chemicals. With the exception of values for air diffusivity (Di,a), water diffusivity (Di,w), and certain Koc values, all of the values used in the development of SSLs can be found in the Superfund Chemical Data Matrix (SCDM). SCDM is a computer code that includes more than 25 datafiles containing specific chemical parameters used to calculate factor and benchmark values for the Hazard Ranking System (HRS). Because SCDM datafiles are regularly updated, the user should consult the most recent version of SCDM to ensure that the values are up to date. 5.1 Solubility, Henry's Law Constant, and Kow Chemical-specific values for solubility, Henry's law constant (HLC), and Kow were obtained from SCDM. In the selection of the value for SCDM, measured or analytical values are favored over calculated values. However, in the event that a measured value is not available, calculated values are used. Table 36 presents the solubility, Henry's law constant, and Kow values taken from SCDM and used to calculate SSLs. Henry's law constant values were available for all but two of the constituents of interest. -
Substituent Effects in Hydrogen Abstraction by Trichloromethyl Radical from 10-Substituted-9
AN ABSTRACT OF THE THESIS OF GARY SCOTT NOLAN for the degree of MASTER OF SCIENCE in CHEMISTRY presented on e IP tcv-vi Title: SUBSTITUENT EFFECTS IN HYDROGEN ABSTRACTION BY TRICHLOROMETHYL RADICAL FROM 10-SUBSTITUTED-9- METHYLANTHRACENES; A LINEAR FREE ENERGY STUDY Abstract approved: Redacted for Privacy Dr. Gerald° Jay Gleicher Hydrogen abstraction by the trichloromethy-1 radical from a series of 10-substituted-9-methylanthracenes at 70° has been examined. The logarithms of the relative rates, measured against hydrogen abstraction from fluorene, correlate very well with sigma plus parameters within the Hammett formalism. A rho value of -0.78 ± 0.05 was observed with a correlation constant of.99 and a standard regression from the mean of .06.This result implies a charge separated character to the transition state with stabilization by electron donating groups. The present work serves as a rigorous test of "Pryor's Postulate".That statement holds that the reaction con- stant or rho value for aryl methyl hydrogen abstraction is, within experimental uncertainties, the same as that for aromatic substitu- tion into the nonmethylated arene.Since a substitution study within the Hammett framework has already been performed, the present study makes a comparison of rho values possible.The rho value obtained in the trichloromethylation of 9-substituted-anthracenes at 70° was -0.83 ± 0.04.This agrees well with the present result. This agreement tends to substantiate and extend "Pryor's Postulate" by treating relatively selective radicals and polycyclic -
2. HEALTH EFFECTS 2.1 INTRODUCTION the Primary
PAHs 11 2. HEALTH EFFECTS 2.1 INTRODUCTION The primary purpose of this chapter is to provide public health officials, physicians, toxicologists, and other interested individuals and groups with an overall perspective of the toxicology of polycyclic aromatic hydrocarbons (PAHs). It contains descriptions and evaluations of toxicological studies and epidemiological investigations and provides conclusions, where possible, on the relevance of toxicity and toxicokinetic data to public health. A glossary and list of acronyms, abbreviations, and symbols can be found at the end of this profile. 2.2 DISCUSSION OF HEALTH EFFECTS BY ROUTE OF EXPOSURE To help public health professionals and others address the needs of persons living or working near hazardous waste sites, the information in this section is organized first by route of exposure-inhalation, oral, and dermal; and then by health effect-death, systemic, immunological, neurological, reproductive, developmental, genotoxic, and carcinogenic effects. These data are discussed in terms of three exposure periods-acute (14 days or less), intermediate (15-364 days), and chronic (365 days or more). Levels of significant exposure for each route and duration are presented in tables and illustrated in figures. The points in the figures showing no-observed-adverse-effect levels (NOAELs) or lowest-observed-adverse-effect levels (LOAELs) reflect the actual doses (levels of exposure) used in the studies. LOAELs have been classified into “less serious” or “serious” effects. “Serious” effects are those that evoke failure in a biological system and can lead to morbidity or mortality (e.g., acute respiratory distress or death). “Less serious” effects are those that are not expected to cause significant dysfunction or death, or those whose significance to the organism is not entirely clear. -
Maine Remedial Action Guidelines (Rags) for Contaminated Sites
Maine Department of Environmental Protection Remedial Action Guidelines for Contaminated Sites (RAGs) Effective Date: May 1, 2021 Approved by: ___________________________ Date: April 27, 2021 David Burns, Director Bureau of Remediation & Waste Management Executive Summary MAINE DEPARTMENT OF ENVIRONMENTAL PROTECTION 17 State House Station | Augusta, Maine 04333-0017 www.maine.gov/dep Maine Department of Environmental Protection Remedial Action Guidelines for Contaminated Sites Contents 1 Disclaimer ...................................................................................................................... 1 2 Introduction and Purpose ............................................................................................... 1 2.1 Purpose ......................................................................................................................................... 1 2.2 Consistency with Superfund Risk Assessment .............................................................................. 1 2.3 When to Use RAGs and When to Develop a Site-Specific Risk Assessment ................................. 1 3 Applicability ................................................................................................................... 2 3.1 Applicable Programs & DEP Approval Process ............................................................................. 2 3.1.1 Uncontrolled Hazardous Substance Sites ............................................................................. 2 3.1.2 Voluntary Response Action Program