A Comparison of Fresh and Used Aircraft Oil for the Identification of Toxic Substances Linked to Aerotoxic Syndrome Chemosphere

Total Page:16

File Type:pdf, Size:1020Kb

A Comparison of Fresh and Used Aircraft Oil for the Identification of Toxic Substances Linked to Aerotoxic Syndrome Chemosphere Chemosphere 158 (2016) 116e123 Contents lists available at ScienceDirect Chemosphere journal homepage: www.elsevier.com/locate/chemosphere A comparison of fresh and used aircraft oil for the identification of toxic substances linked to aerotoxic syndrome David Megson a, *, Xavier Ortiz b, Karl J. Jobst b, Eric J. Reiner a, b, Michel F.A. Mulder c, Jean-Christophe Balouet d a Department of Chemistry, University of Toronto, Toronto, ON, Canada b Ontario Ministry of the Environment and Climate Change, 125 Resources Road, Canada c Aviation Medical Consult, Karbouwstraat 14, 1402 VC Bussum, The Netherlands d Environnement International, Orrouy, France highlights High resolution mass spectrometry was used to identify toxic compounds in jet oil. Ortho substituted TCP was not detected in jet oil. Alkylated TCP was detected in used jet oil at 0.13e0.69%. w/w. Previous air quality studies may have underestimated the risks from OPs. article info abstract Article history: Fresh and used aircraft engine lubricants (Mobil Jet Oil II) were analysed using a Fourier Transform Ion Received 18 March 2016 Cyclotron Resonance Mass Spectrometer (FTICRMS) and comprehensive two dimensional gas chroma- Received in revised form tography with high resolution time of flight mass spectrometry (GCxGC-HRTOFMS). The composition of 16 May 2016 the fresh oil was established, with special focus to its tricresyl phosphate (TCP) content as this has Accepted 21 May 2016 formed the focus for most investigations into aerotoxic syndrome. The results showed that only four TCP isomers were present at detectable levels in the fresh oil: mmm-TCP, mmp-TCP, ppm-TCP and ppp-TCP. Handling Editor: J. de Boer The results indicate that the formulation of Mobile Jet Oil II does not contain the more toxic ortho substituted TCP isomers at concentrations above 0.0005%. The temperatures of jet engines during Keywords: operation are greater than 200 C which creates the potential to alter the composition of the original oil Aerotoxic and create other toxic compounds. The results show there may be a significant risk from alkylated cresyl Multidimensional chromatography phosphates, which were identified in the used oils at concentrations calculated in the range of 0.13 High resolution mass spectrometry e0.69%. w/w. Several xylenyl and ethylphenyl phosphates have been shown to exhibit a similar toxicity Cresyl phosphates to ortho substituted TCP isomers which makes there discovery in used oil significant. These compounds Organophosphates should be included in future aircraft air quality studies and when assessing the risks and causes of aerotoxic syndrome. © 2016 Elsevier Ltd. All rights reserved. 1. Introduction exposure to toxic fumes and organophosphates (Abou-Donia et al., 2013; Harrison and Mackenzie Ross, 2016; Liyasova et al., 2011; Due to their widespread use as pesticides, plasticizers and flame Payne, 2015). There have been reports of headaches, loss of bal- retardants organophosphates are routinely detected in environ- ance, numbness and neurobehavioral abnormalities such as mental samples. However, a specific concern has arisen in recent emotional instability, depression and cognitive dysfunction, decades as aircraft crew have developed symptoms consistent with including impaired short term memory, blurred vision and speech, altered coordination (de Ree et al., 2014; Abou-Donia et al., 2013). Organophosphates are not just used as pesticides on crops in fields but are also used in aircraft as flame retardants, in engine oil and * Corresponding author. hydraulic fluids, and on material surfaces. This has resulted in their E-mail address: [email protected] (D. Megson). http://dx.doi.org/10.1016/j.chemosphere.2016.05.062 0045-6535/© 2016 Elsevier Ltd. All rights reserved. D. Megson et al. / Chemosphere 158 (2016) 116e123 117 link to aerotoxic syndrome by Winder and Balouet (2002). The term Many crew members who have reported conditions consistent with Aerotoxic Syndrome was first published in 1999 by an international organophosphate poisoning recover and return to their flight scientific team to describe the symptoms and exposure conditions duties, however some staff have lost their jobs, and several have reported by aircraft crew from Australia, US, Europe. Whilst aero- even passed away. When individuals are grounded they are no toxic syndrome has not been fully accepted as a medical syndrome longer exposed to aircraft air their reported symptoms can gradu- (Wolkoff et al., 2016) it is commonly used to refer to air quality in ally reduce. The underlying mechanism that caused the ill health aircraft and the associated exposure of crew and passengers to toxic may be an active auto immune reaction, set into motion by compounds. Aerotoxic syndrome is understood to be caused by repeated low dose exposure to organophosphates, causing actual long term and repeated exposure to chemicals released from smoke damage to the Blood-Brain-Barrier and apoptosis inside the brain. and fume events in aircraft. Protein filaments of these decaying cells are able to re-enter the During a flight the air cabin pressure and temperature are bloodstream, causing a secondary auto immune response. Memory maintained with outside air that is passed through the jet engine. B cells can recognise certain antigens for a long duration of time, Cabin air is recycled for 50%, whereas the flight deck air is comparable to a status after vaccination and can lead in rare in- comprised in most aircraft types of a continuous stream of bleed air stances to an anaphylactic shock (Banks and Lein, 2012), also (de Boer et al., 2015). Engine seals in use are known as “wet-seals”, known as “incapacitation”, or sudden heart failure due to lym- an inherent design feature, whereby a thin film of oil prevents phocytic myocarditis. UK Coroner Payne, recently issued a report to rotating surfaces to come into mechanical contact with each other. prevent further deaths following the death of a pilot, which was Pressure differentials over the seals cause a constant loss of oil and linked to OP poisoning (Abou-Donia et al., 2014; Payne, 2015). The vapours into the core engine. These enter the inlet of the high post mortem investigations gave the cause of death of either pressure compressor and contaminate the bleed air which is taken pentobarbital toxicity or lymphocytic myocarditis, individually or downstream. Oil leaks can result in odd smells in the cabin and in in combination. Hair analysis had shown the use of pentobarbital more extreme cases smoke events. The tricresylphosphate chemi- during the 4 weeks prior to his death, as a form of self medication cal fingerprint from wipe samples taken from a cockpit showed a against severe headaches. Pentobarbital is not known for causing statistically significant correlation (p value 0.039) with used engine the widespread infiltration of T-lymphocytes in the brain, heart and oil (Houtzager et al., 2013), indicating that this can be a significant neurological damage otherwise observed. Testing of samples taken source of exposure. Estimates of how often these events occur both prior to and after death disclosed symptoms consistent with varies depending upon whether the information is sourced from exposure to organophosphate compounds. regulatory authorities such as the UK Civil Aviation Authority (CAA), Due to the sporadic occurrence of smoke/fume incidents it is from airlines or from trade unions who represent aircrew (Harrison particularly difficult to obtain worst case air samples for analysis. and Mackenzie Ross, 2016). Reported values for the frequency of No fume events were observed on any of the flights that were smoke/fume events include 0.5% of flights (Murawski and Supplee, monitored by Crump et al. (2011) and de Ree et al. (2014). Although 2008), 0.05% (COT, 2007) and 0.02% (Shehadi et al., 2015). Lubri- this is hardly surprising as they only involved analysis on 100 and cating oil is applied to gas turbines in aeroplanes as anti-wear 20 flights respectively. Using the estimates of the frequency of fume agents. However, there have been several studies that have iden- events from Murawski and Supplee (2008), and Shehadi et al. tified subchronic neurotoxicity of aviation oils (Freudenthal et al., (2015) a sample size of between 200 and 5000 flights would be 1993; Daughtrey et al., 1996; Mackerer et al., 1999). Aircraft lubri- required to identify one event. Interestingly nine smoke/odour cating oils have remained relatively unchanged since the 1960s and events were recorded in 78 samples taken by De Nola et al. (2011). are comprised of approximately 95% synthetic esters with 3% tri- de Boer et al. (2015) used data from De Nola et al. (2011) and Craig cresyl phosphates and 1% phenyl-a-naphthalamines (Winder and and Barth (1999) to calculate that even using worst-case scenarios Balouet, 2002). Tri-cresyl phosphates (TCPs) are a group of organ- they cannot explain a relation of TCP in flight deck air to the ophosphates which contain 10 structural isomers. The ortho complaints of pilots and air crew, a similar conclusion was also substituted congeners are considered to be the most toxic and reached by de Ree et al. (2014) and Schindler et al. (2012). Available therefore the proportions of these compounds in oil have been data was reviewed by Ramsden (2013) who used jet oil consump- reduced in recent decades (Craig and Barth, 1999). Most of the focus tion as a surrogate to measure chemical contamination in aircraft of investigations in aircraft air quality and aerotoxic syndrome has cabin air. Those results show that the oil concentration in a fume been focused on tri-ortho-cresyl phosphate (ooo-TCP or ToCP), event, in which visible smoke appears in the cabin, was estimated however the mono-ortho and di-ortho isomers are also highly toxic at 50 mg/m3. The concentration of TCP was approximately 1.5 mg/ with omp-TCP the most toxic (de Boer et al., 2015; De Nola et al., m3 and using the ratio of ToCP to total TCP from Crump et al.
Recommended publications
  • Hyperactivity and Seizure Induced by Tricresyl Phosphate Are Isomer
    TOXICOLOGICAL SCIENCES, 2021, 1–15 doi: 10.1093/toxsci/kfab006 Research Article Downloaded from https://academic.oup.com/toxsci/advance-article/doi/10.1093/toxsci/kfab006/6112059 by guest on 12 February 2021 Hyperactivity and Seizure Induced by Tricresyl Phosphate Are Isomer Specific and Not Linked to Phenyl Valerate-Neuropathy Target Esterase Activity Inhibition in Zebrafish Anja Knoll-Gellida, Leslie E. Dubrana, Laure M. Bourcier, Theo Merce, Gaelle€ Gruel, Magalie Soares, and Patrick J. Babin 1 Department of Life and Health Sciences, INSERM, Maladies Rares: Gen etique et Metabolisme (MRGM), U1211, Universite de Bordeaux, F-33615 Pessac, France Anja Knoll-Gellida and Leslie E. Dubrana contributed equally to this study. 1To whom correspondence should be addressed at: Laboratoire Maladies Rares: Gen etique et Metabolisme (MRGM), Universite de Bordeaux, Allee Geoffroy St-Hilaire, Bat. B2, 2e`meetage, CS 50023, 33615 Pessac Cedex, France. E-mail: [email protected] ABSTRACT Environmental exposure to tricresyl phosphate (TCP) may lead to severe neurotoxic effects, including organophosphate (OP)-induced delayed neuropathy. TCP has three symmetric isomers, distinguished by the methyl group position on the aromatic ring system. One of these isomers, tri-ortho-cresyl phosphate (ToCP), has been reported for years as a neuropathic OP, targeting neuropathic target esterase (NTE/PNPLA6), but its mode of toxic action had not been fully elucidated. Zebrafish eleuthero-embryo and larva were used to characterize the differential action of the TCP isomers. The symmetric isomers inhibited phenyl valerate (PV)-NTE enzymatic activity in vivo with different IC50, while no effect was observed on acetylcholinesterase activity. Moreover, the locomotor behavior was also affected by tri-para-cresyl phosphate and tri- meta-cresyl phosphate, only ToCP exposure led to locomotor hyperactivity lasting several hours, associated with defects in the postural control system and an impaired phototactic response, as revealed by the visual motor response test.
    [Show full text]
  • Alphabetical Index of Substances and Articles
    ALPHABETICAL INDEX OF SUBSTANCES AND ARTICLES - 355 - NOTES TO THE INDEX 1. This index is an alphabetical list of the substances and articles which are listed in numerical order in the Dangerous Goods List in Chapter 3.2. 2. For the purpose of determining the alphabetical order the following information has been ignored even when it forms part of the proper shipping name: numbers; Greek letters; the abbreviations “sec” and “tert”; and the letters “N” (nitrogen), “n” (normal), “o” (ortho) “m” (meta), “p” (para) and “N.O.S.” (not otherwise specified). 3. The name of a substance or article in block capital letters indicates a proper shipping name. 4. The name of a substance or article in block capital letters followed by the word “see” indicates an alternative proper shipping name or part of a proper shipping name (except for PCBs). 5. An entry in lower case letters followed by the word “see” indicates that the entry is not a proper shipping name; it is a synonym. 6. Where an entry is partly in block capital letters and partly in lower case letters, the latter part is considered not to be part of the proper shipping name. 7. A proper shipping name may be used in the singular or plural, as appropriate, for the purposes of documentation and package marking. - 356 - INDEX Name and description Class UN No. Name and description Class UN No. Accumulators, electric, see 4.3 3292 Acid mixture, nitrating acid, see 8 1796 8 2794 8 2795 Acid mixture, spent, nitrating acid, see 8 1826 8 2800 8 3028 Acraldehyde, inhibited, see 6.1 1092 ACETAL 3 1088
    [Show full text]
  • Chemical Name Federal P Code CAS Registry Number Acutely
    Acutely / Extremely Hazardous Waste List Federal P CAS Registry Acutely / Extremely Chemical Name Code Number Hazardous 4,7-Methano-1H-indene, 1,4,5,6,7,8,8-heptachloro-3a,4,7,7a-tetrahydro- P059 76-44-8 Acutely Hazardous 6,9-Methano-2,4,3-benzodioxathiepin, 6,7,8,9,10,10- hexachloro-1,5,5a,6,9,9a-hexahydro-, 3-oxide P050 115-29-7 Acutely Hazardous Methanimidamide, N,N-dimethyl-N'-[2-methyl-4-[[(methylamino)carbonyl]oxy]phenyl]- P197 17702-57-7 Acutely Hazardous 1-(o-Chlorophenyl)thiourea P026 5344-82-1 Acutely Hazardous 1-(o-Chlorophenyl)thiourea 5344-82-1 Extremely Hazardous 1,1,1-Trichloro-2, -bis(p-methoxyphenyl)ethane Extremely Hazardous 1,1a,2,2,3,3a,4,5,5,5a,5b,6-Dodecachlorooctahydro-1,3,4-metheno-1H-cyclobuta (cd) pentalene, Dechlorane Extremely Hazardous 1,1a,3,3a,4,5,5,5a,5b,6-Decachloro--octahydro-1,2,4-metheno-2H-cyclobuta (cd) pentalen-2- one, chlorecone Extremely Hazardous 1,1-Dimethylhydrazine 57-14-7 Extremely Hazardous 1,2,3,4,10,10-Hexachloro-6,7-epoxy-1,4,4,4a,5,6,7,8,8a-octahydro-1,4-endo-endo-5,8- dimethanonaph-thalene Extremely Hazardous 1,2,3-Propanetriol, trinitrate P081 55-63-0 Acutely Hazardous 1,2,3-Propanetriol, trinitrate 55-63-0 Extremely Hazardous 1,2,4,5,6,7,8,8-Octachloro-4,7-methano-3a,4,7,7a-tetra- hydro- indane Extremely Hazardous 1,2-Benzenediol, 4-[1-hydroxy-2-(methylamino)ethyl]- 51-43-4 Extremely Hazardous 1,2-Benzenediol, 4-[1-hydroxy-2-(methylamino)ethyl]-, P042 51-43-4 Acutely Hazardous 1,2-Dibromo-3-chloropropane 96-12-8 Extremely Hazardous 1,2-Propylenimine P067 75-55-8 Acutely Hazardous 1,2-Propylenimine 75-55-8 Extremely Hazardous 1,3,4,5,6,7,8,8-Octachloro-1,3,3a,4,7,7a-hexahydro-4,7-methanoisobenzofuran Extremely Hazardous 1,3-Dithiolane-2-carboxaldehyde, 2,4-dimethyl-, O- [(methylamino)-carbonyl]oxime 26419-73-8 Extremely Hazardous 1,3-Dithiolane-2-carboxaldehyde, 2,4-dimethyl-, O- [(methylamino)-carbonyl]oxime.
    [Show full text]
  • Structural Dynamics of Acetylcholinesterase and Its Implications in Reactivators Design Gianluca Santoni
    Structural dynamics of acetylcholinesterase and its implications in reactivators design Gianluca Santoni To cite this version: Gianluca Santoni. Structural dynamics of acetylcholinesterase and its implications in reactivators design. Biomolecules [q-bio.BM]. Université Grenoble Alpes, 2015. English. NNT : 2015GREAY019. tel-01212481 HAL Id: tel-01212481 https://tel.archives-ouvertes.fr/tel-01212481 Submitted on 6 Oct 2015 HAL is a multi-disciplinary open access L’archive ouverte pluridisciplinaire HAL, est archive for the deposit and dissemination of sci- destinée au dépôt et à la diffusion de documents entific research documents, whether they are pub- scientifiques de niveau recherche, publiés ou non, lished or not. The documents may come from émanant des établissements d’enseignement et de teaching and research institutions in France or recherche français ou étrangers, des laboratoires abroad, or from public or private research centers. publics ou privés. THÈSE Pour obtenir le grade de DOCTEUR DE L’UNIVERSITÉ DE GRENOBLE Spécialité : Physique pour les sciences du vivant Arrêté ministériel : 7 Aout 2006 Présentée par Gianluca SANTONI Thèse dirigée par Martin WEIK et codirigée par Florian NACHON préparée au sein de l’Institut de Biologie Structurale de Grenoble et de l’école doctorale de physique Structural dynamics of acetyl- cholinesterase and its implications in reactivator design Thèse soutenue publiquement le 30/01/2015, devant le jury composé de : Dr. Yves Bourne Directeur de recherche CNRS, AFMB Marseille, Rapporteur Dr. Etienne Derat Maitre de conference, Université Pierre et Marie Curie, Paris, Rapporteur Prof. Pierre-Yves Renard Professeur, Université de Normandie, Rouen, Examinateur Prof. Israel Silman Professeur, Weizmann Institute of Science,Rehovot, Examinateur Dr.
    [Show full text]
  • Chemical Compatibility of the Tubing Materials
    Chemical Compatibility of the Tubing Materials 1: excellent; 2: good; 3: fair; 4: not recommended Tygon Tygon ST PharMed Tygon HC Tygon Tygon SI Silicone Norprene Flurane LFL R-3603 F-4040-A MH Silicone Peroxide A-60-G F-5500-A Name 2075 Platinum (Viton) Acetaldehyde 4 4 4 4 3 3 3 4 4 Acetamide, 67% in w 4 4 2 4 1 1 1 2 4 Acetate Solvents 4 4 2 4 4 4 4 2 4 Acetic Acid, 10% in w 1 1 1 1 1 1 1 1 4 Acetic Acid, 50-60% in w 1 1 2 1 1 1 1 2 4 Acetic Acid, Glacial, 100% 4 4 2 4 1 4 4 2 4 Acetic Anhydride 4 4 1 4 1 1 1 1 4 Acetone 4 4 4 4 2 3 3 4 4 Acetonitrile 4 4 4 4 4 4 4 4 2 Acetyl Bromide 4 4 3 4 4 4 4 3 4 Acetyl Chloride 4 4 3 4 4 4 4 3 4 Acetylene Gas 1 1 1 1 1 1 1 1 1 Acrylonitrile 4 4 4 4 4 4 4 4 2 Adipic Acid, 100% in alc 4 4 2 3 4 4 4 2 4 Air 1 1 1 1 1 1 1 1 1 Alcohols General 4 4 1 2 1 2 2 1 4 Aliphatic Hydrocarbons 4 4 4 2 4 4 4 4 2 Allyl Alcohol 4 4 3 1 1 4 4 3 1 Alum, 5% in w 1 1 1 1 1 1 1 1 1 Aluminum Chloride, 53% in w 1 1 1 1 1 1 1 1 1 Aluminum Hydroxide, 2% in w 1 1 1 1 1 1 1 1 1 Aluminum Salts 1 1 1 1 1 1 1 1 1 Aluminum Sulfate, 50% in w 1 1 1 1 1 1 1 1 1 Amines 443444434 Ammonia Gas 1 1 1 1 1 4 4 1 4 Ammonia, Anhydrous Liquid 2 2 1 2 2 4 4 2 4 Ammonium Acetate, 45% in w 1 1 1 1 1 1 1 1 4 Ammonium Carbonate, 20% in w 1 1 1 1 1 1 1 1 1 Ammonium Hydroxide, 30% in w 1 1 1 3 1 4 4 1 4 Ammonium Hydroxide, 5-10% in w 1 1 1 2 1 4 4 1 4 Ammonium Persulfate, 30% in w 1 1 1 1 1 1 1 1 1 Ammonium Salts 1 1 1 1 1 1 1 1 1 Ammonium Sulfate, 30% in w 1 1 1 1 1 1 1 1 1 Amyl Acetate 4 4 2 4 4 4 4 2 4 Amyl Alcohol 4 4 4 1 1 4 4 4 1 Amyl Chloride
    [Show full text]
  • Environmental Health Criteria 110 Tricresyl Phosphate
    Environmental Health Criteria 110 Tricresyl phosphate Please note that the layout and pagination of this web version are not identical with the printed version. Tricresyl phosphate (EHC 110, 1990) INTERNATIONAL PROGRAMME ON CHEMICAL SAFETY ENVIRONMENTAL HEALTH CRITERIA 110 TRICRESYL PHOSPHATE This report contains the collective views of an international group of experts and does not necessarily represent the decisions or the stated policy of the United Nations Environment Programme, the International Labour Organisation, or the World Health Organization. Published under the joint sponsorship of the United Nations Environment Programme, the International Labour Organisation, and the World Health Organization World Health Orgnization Geneva, 1990 The International Programme on Chemical Safety (IPCS) is a joint venture of the United Nations Environment Programme, the International Labour Organisation, and the World Health Organization. The main objective of the IPCS is to carry out and disseminate evaluations of the effects of chemicals on human health and the quality of the environment. Supporting activities include the development of epidemiological, experimental laboratory, and risk-assessment methods that could produce internationally comparable results, and the development of manpower in the field of toxicology. Other activities carried out by the IPCS include the development of know-how for coping with chemical accidents, coordination of laboratory testing and epidemiological studies, and promotion of research on the mechanisms of the biological action of chemicals. WHO Library Cataloguing in Publication Data Tricresyl phosphate. (Environmental health criteria ; 110) 1.Tritolyl phosphates - adverse effects 2.Tritolyl phosphates - toxicity I.Series Page 1 of 84 Tricresyl phosphate (EHC 110, 1990) ISBN 92 4 157110 1 (NLM Classification: QV 627) ISSN 0250-863X The World Health Organization welcomes requests for permission to reproduce or translate its publications, in part or in full.
    [Show full text]
  • NIOSH Method 5600: Organophosphorus Pesticides
    ORGANOPHOSPHORUS PESTICIDES 5600 Formula: Table 1 MW: Table 1 CAS: Table 1 RTECS: Table 1 METHOD: 5600, Issue 1 EVALUATION: FULL Issue 1: 15 August 1994 OSHA : Table 2 PROPERTIES: Table 3 NIOSH: Table 2 ACGIH: Table 2 SYNONYMS: Table 4 SAMPLING MEASUREMENT SAMPLER: FILTER/SOLID SORBENT TUBE (OVS-2 tube: TECHNIQUE: GC, FLAME PHOTOMETRIC DETECTION 13-mm quartz filter; XAD-2, 270 mg/140 mg) (FPD) FLOW RATE: 0.2 to 1 L/min ANALYTE: organophosphorus pesticides, Table 1 VOL-MIN: 12 L EXTRACTION: 2-mL 90% toluene/10% acetone solution -MAX: 240 L; 60 L (Malathion, Ronnel) INJECTION SHIPMENT: cap both ends of tube VOLUME: 1-2 µL SAMPLE TEMPERATURE STABILITY: at least 10 days at 25 °C -INJECTION: 240 °C at least 30 days at 0 °C -DETECTOR: 180 °C to 215 °C (follow manufacturer's recommendation) BLANKS: 2 to 10 field blanks per set -COLUMN: Table 6 CARRIER GAS: He at 15 psi (104 kPa) ACCURACY COLUMN: fused silica capillary column; Table 6 RANGE STUDIED: Table 5, Column A DETECTOR: FPD (phosphorus mode) ACCURACY: Table 5, Column B CALIBRATION: standard solutions of organophosphorus compounds in toluene BIAS: Table 5, Column C RANGE: Table 8, Column C ˆ OVERALL PRECISION (S rT): Table 5, Column D ESTIMATED LOD: Table 8, Column F PRECISION (S r): Table 5, Column E APPLICABILITY: The working ranges are listed in Table 5. They cover a range of 1/10 to 2 times the OSHA PELs. This INTERFERENCES: Several organophosphates may co-elute method also is applicable to STEL measurements using 12-L with either target analyte or internal standard causing samples.
    [Show full text]
  • Quantitation of Ortho-Cresyl Phosphate Adducts to Butyrylcholinesterase in Human Serum by Immunomagnetic- UHPLC-MS/MS
    HHS Public Access Author manuscript Author ManuscriptAuthor Manuscript Author J Mass Spectrom Manuscript Author . Author Manuscript Author manuscript; available in PMC 2017 December 04. Published in final edited form as: J Mass Spectrom. 2015 April ; 50(4): 683–692. doi:10.1002/jms.3576. Quantitation of ortho-Cresyl Phosphate Adducts to Butyrylcholinesterase in Human Serum by Immunomagnetic- UHPLC-MS/MS Darryl Johnson1, Melissa D. Carter2,*, Brian S. Crow2, Samantha L. Isenberg1, Leigh Ann Graham1, H. Akin Erol1, Caroline M. Watson1, Brooke G. Pantazides2, Marcel J. van der Schans3, Jan P. Langenberg3, Daan Noort3, Thomas A. Blake2, Jerry D. Thomas2, and Rudolph C. Johnson2 1Oak Ridge Institute for Science and Education, Centers for Disease Control and Prevention, Atlanta, GA, USA 2Division of Laboratory Sciences, National Center for Environmental Health, Centers for Disease Control and Prevention, Atlanta, GA, USA 3The Netherlands Organization for Applied Scientific Research (TNO), Technical Sciences, CBRN Protection, Rijswijk, The Netherlands Abstract Tri-ortho-cresyl phosphate (ToCP) is an anti-wear, flame retardant additive used in industrial lubricants, hydraulic fluids, and gasoline. The neurotoxic effects of ToCP arise from the liver- activated metabolite 2-(o-cresyl)-4H-1,3,2-benzodioxaphosphoran-2-one (cresyl saligenin phosphate or CBDP), which inhibits esterase enzymes including butyrylcholinesterase (BChE). Following BChE adduction, CBDP undergoes hydrolysis to form the aged adduct ortho-cresyl phosphoserine (oCP-BChE), thus providing a biomarker of CBDP exposure. Previous studies have identified ToCP in aircraft cabin and cockpit air, but assessing human exposure has been hampered by the lack of a laboratory assay to confirm exposure. This work presents the development of an immunomagnetic-UHPLC-MS/MS method for the quantitation of unadducted BChE and the long- term CBDP biomarker, oCP-BChE, in human serum.
    [Show full text]
  • Healthcare Resource
    Health Care Resource: Links between Pesticide Exposures and Mental Health Prepared by the Mental Health and Environment Working Group of the Collaborative on Health and the Environment www.healthandenvironment.org Mental Health Effects from Pesticide Exposure Exposure to pesticides can have behavioral and psychiatric consequences. The purpose of this resource is to help mental health clinicians and health care providers become aware of the association between pesticide exposure and these consequences and to provide links to relevant research findings. Many people are at risk of pesticide exposure, including those who: • work in agriculture, landscaping or other settings (such as grocery stores, schools, daycares and office buildings) in which pest problems are treated with chemicals; • live downwind from where aerial spraying of pesticides is done; • live in communities where spray and runoff can contaminate both surface and ground water; or • live in urban dwellings where pest control is used. Outside use may take months for the pesticide to degrade to half-life or roughly half potency. Indoors there are no degrading elements such as sunshine, soil or rain to degrade potency; these undegraded pesticides can be re-suspended into the air in dust particles. Health care providers should consider the possibility that the symptoms associated with mental health disorders, such as irritability, depression or anxiety, may be the result of acute or chronic pesticide exposure. No matter what the presenting ailment may be, clinicians who care for individuals either at risk of pesticide exposure or those with known exposure are encouraged to inquire about the presence of depression, anxiety, or any of the other symptoms listed below.
    [Show full text]
  • Environmental Health Criteria 63 ORGANOPHOSPHORUS
    Environmental Health Criteria 63 ORGANOPHOSPHORUS INSECTICIDES: A GENERAL INTRODUCTION Please note that the layout and pagination of this web version are not identical with the printed version. Organophophorus insecticides: a general introduction (EHC 63, 1986) INTERNATIONAL PROGRAMME ON CHEMICAL SAFETY ENVIRONMENTAL HEALTH CRITERIA 63 ORGANOPHOSPHORUS INSECTICIDES: A GENERAL INTRODUCTION This report contains the collective views of an international group of experts and does not necessarily represent the decisions or the stated policy of the United Nations Environment Programme, the International Labour Organisation, or the World Health Organization. Published under the joint sponsorship of the United Nations Environment Programme, the International Labour Organisation, and the World Health Organization World Health Orgnization Geneva, 1986 The International Programme on Chemical Safety (IPCS) is a joint venture of the United Nations Environment Programme, the International Labour Organisation, and the World Health Organization. The main objective of the IPCS is to carry out and disseminate evaluations of the effects of chemicals on human health and the quality of the environment. Supporting activities include the development of epidemiological, experimental laboratory, and risk-assessment methods that could produce internationally comparable results, and the development of manpower in the field of toxicology. Other activities carried out by the IPCS include the development of know-how for coping with chemical accidents, coordination
    [Show full text]
  • 2019 Minnesota Chemicals of High Concern List
    Minnesota Department of Health, Chemicals of High Concern List, 2019 Persistent, Bioaccumulative, Toxic (PBT) or very Persistent, very High Production CAS Bioaccumulative Use Example(s) and/or Volume (HPV) Number Chemical Name Health Endpoint(s) (vPvB) Source(s) Chemical Class Chemical1 Maine (CA Prop 65; IARC; IRIS; NTP Wood and textiles finishes, Cancer, Respiratory 11th ROC); WA Appen1; WA CHCC; disinfection, tissue 50-00-0 Formaldehyde x system, Eye irritant Minnesota HRV; Minnesota RAA preservative Gastrointestinal Minnesota HRL Contaminant 50-00-0 Formaldehyde (in water) system EU Category 1 Endocrine disruptor pesticide 50-29-3 DDT, technical, p,p'DDT Endocrine system Maine (CA Prop 65; IARC; IRIS; NTP PAH (chem-class) 11th ROC; OSPAR Chemicals of Concern; EuC Endocrine Disruptor Cancer, Endocrine Priority List; EPA Final PBT Rule for 50-32-8 Benzo(a)pyrene x x system TRI; EPA Priority PBT); Oregon P3 List; WA Appen1; Minnesota HRV WA Appen1; Minnesota HRL Dyes and diaminophenol mfg, wood preservation, 51-28-5 2,4-Dinitrophenol Eyes pesticide, pharmaceutical Maine (CA Prop 65; IARC; NTP 11th Preparation of amino resins, 51-79-6 Urethane (Ethyl carbamate) Cancer, Development ROC); WA Appen1 solubilizer, chemical intermediate Maine (CA Prop 65; IARC; IRIS; NTP Research; PAH (chem-class) 11th ROC; EPA Final PBT Rule for 53-70-3 Dibenzo(a,h)anthracene Cancer x TRI; WA PBT List; OSPAR Chemicals of Concern); WA Appen1; Oregon P3 List Maine (CA Prop 65; NTP 11th ROC); Research 53-96-3 2-Acetylaminofluorene Cancer WA Appen1 Maine (CA Prop 65; IARC; IRIS; NTP Lubricant, antioxidant, 55-18-5 N-Nitrosodiethylamine Cancer 11th ROC); WA Appen1 plastics stabilizer Maine (CA Prop 65; IRIS; NTP 11th Pesticide (EPA reg.
    [Show full text]
  • Guide for the Selection of Personal Protective Equipment for Emergency First Responders
    U.S. Department of Justice Office of Justice Programs National Institute of Justice National Institute of Justice Law Enforcement and Corrections Standards and Testing Program Guide for the Selection of Personal Protective Equipment for Emergency First Responders NIJ Guide 102–00 Volume I November 2002 U.S. Department of Justice Office of Justice Programs 810 Seventh Street N.W. Washington, DC 20531 John Ashcroft Attorney General Deborah J. Daniels Assistant Attorney General Sarah V. Hart Director, National Institute of Justice For grant and funding information, contact: Department of Justice Response Center 800–421–6770 Office of Justice Programs National Institute of Justice World Wide Web Site World Wide Web Site http://www.ojp.usdoj.gov http://www.ojp.usdoj.gov/nij U.S. Department of Justice Office of Justice Programs National Institute of Justice Guide for the Selection of Personal Protective Equipment for Emergency First Responders NIJ Guide 102-00, Volume I Dr. Alim A. Fatah1 John A. Barrett2 Richard D. Arcilesi, Jr.2 Charlotte H. Lattin2 Charles G. Janney2 Edward A. Blackman2 Coordination by: Office of Law Enforcement Standards National Institute of Standards and Technology Gaithersburg, MD 20899–8102 Prepared for: National Institute of Justice Office of Science and Technology Washington, DC 20531 November 2002 This document was prepared under CBIAC contract number SPO-900-94-D-0002 and Interagency Agreement M92361 between NIST and the Department of Defense Technical Information Center (DTIC). NCJ 191518 1National Institute of Standards and Technology, Office of Law Enforcement Standards. 2Battelle Memorial Institute. National Institute of Justice Sarah V. Hart Director This guide was prepared for the National Institute of Justice, U.S.
    [Show full text]