Biomed 153-4.Indb

Total Page:16

File Type:pdf, Size:1020Kb

Biomed 153-4.Indb Biomed Pap Med Fac Univ Palacky Olomouc Czech Repub. 2009 Dec; 153(4):259–262. 259 © K. Kuca, K. Musilek, M. Pohanka, V. Dohnal, J. Patocka REACTIVATION POTENCY OF THE ACETYLCHOLINESTERASE REACTIVATOR OBIDOXIME IS LIMITED Kamil Kucaa, b*, Kamil Musilekb, Miroslav Pohankaa, Vlastimil Dohnalb, c, Jiri Patockad a Center of Advanced Studies, Faculty of Military Health Sciences, University of Defence, Hradec Kralove, Czech Republic b Department of Toxicology, Faculty of Military Health Sciences, University of Defence, Hradec Kralove c Department of Chemistry, Department of Chemistry, Faculty of Sciences, J. E. Purkinje University, Usti nad Labem, Czech Republic d Faculty of Health and Social Studies, University of South Bohemia, Ceské Budejovice, Czech Republic e-mail: [email protected] Received: July 10, 2009; Accepted: November 11, 2009 Keywords: Obidoxime/Acetylcholinesterase/Nerve agent/Pesticide/Antidote/Reactivator/Oxime Background: Obidoxime is the only one reactivator of acetylcholinesterase (AChE) approved in Czech Republic for the treatment of nerve agent and pesticide poisonings for civilian sector. Due to the fact that misuse of nerve agents by terrorists or by an accidental poisoning by farmers is possible, re-evaluation of its universality is needed. It is also needed by the fact that clinical findings considering this oxime are controversial. Aim: In this study, we wanted to summarize if obidoxime is a universal reactivator or if its reactivation potency in case of some organophosphorus inhibitors is limited. Method: Using our in vitro method, rat brain AChE was inhibited by eleven organophosphorus AChE inhibitors and then reactivated by obidoxime. Results and Conclusion: It was found that obidoxime could not be termed as universal antidote. Due to this, devel- opment of new promising candidates as replacement of obidoxime is recommended. INTRODUCTION agent, Russian VX were chosen as members of nerve agent group. Chlorpyrifos, paraoxon, methyl-chlorpyrifos, Nerve agents (sarin, tabun, agent VX, etc.) and pes- DDVP and DFP were chosen as members of the pesticide ticides (paraoxon, chlorpyrifos, DDVP, etc.) pose rela- family. In vitro potentiometric method was used for the tively high threat to mammals. They are extremely toxic evaluation of obidoxime reactivation. compounds, especially nerve agents, influencing nerve system. They inhibit enzyme acetylcholinesterase (AChE; EC 3.1.1.7) by the covalent binding to the hydroxyl group MATERIAL AND METHODS of serine in enzyme’s active site. After the inhibition, en- zyme is not able to split the neuromediator – acetylcho- Obidoxime (1,3-bis(4-hydroxyiminomethylpyridinium)- line (ACh). ACh cumulates at the synaptic clefts, and due 2-oxapropane dichloride) was prepared at our depart- to this, subsequent cholinergic crisis occurs1–4. ment using the modified approach published earlier12. Its At present time, only five AChE reactivators (pral- purity was determined prior its use by using TLC and idoxime, obidoxime, trimedoxime, methoxime and HI-6) HPLC13–14. Nerve agents were obtained from the Military together with atropine (cholinergic drug) and diazepam Facility Brno (Czech Republic). Pesticides and all other (anticonvulsive) are clinically used worldwide. In Czech chemicals used were obtained from Sigma-Aldrich (Czech Republic, three reactivators of them are available. Republic). However, only obidoxime can be used in civilian sector5–6. The whole in vitro method is described in the work Because of the fact, that we are living at the present of Musilek et al.15. Shortly: Lightly narcotized rats were time in the global war against terrorism, there is still a killed (narcosis does not influence cholinesterase activ- very high probability of the misuse of these compounds. ity)16. Their brains were removed and then homogenized Due to this, preparedness for the possible misuse of these with water to obtain 10% rat brain homogenate as the en- agents is of high priority. As mentioned above, obidoxime zyme source. The brain homogenate (0.5 ml) was mixed is the only oxime introduced in the Czech civilian sector with isopropanol solution of AChE inhibitor and then (Fig. 1). However in the current literature, the data dis- incubated at 25°C for 30 minutes to achieve 95% inhi- cussing obidoxime antidotal potency are controversial7–11. bition of AChE. 2.5 ml of solution of sodium chloride Owing to the above mentioned factors, summariza- (3 M) were added to the mixture and filled to the volume tion of the reactivation activities of obidoxime are shown 23 ml with distilled water. Finally, 2 ml of acetylcholine in this article. For this purpose, eleven AChE inhibi- iodide solution (0.02 M) were added. The enzyme activ- tors were selected. Tabun, sarin, cyclosarin, soman, VX ity was measured at pH 8.0 and temperature 25°C on 260 K. Kuca, K. Musilek, M. Pohanka, V. Dohnal, J. Patocka HON=HC CH=NOH autotitrator RTS 822 (Radiometer, Denmark). Activities of intact AChE (a0) and inhibited AChE (ai) were de- ducted from influence of consumption of NaOH solution 2 X (0.01 M) on time. After the incubation with nerve agent N N or pesticide-inhibited AChE (30 minutes), the reactivator CH2OCH2 was added to the solution and the mixture and incubated for 10 minutes. Activity of reactivated AChE (ar) was Fig. 1. Chemical structure of obidoxime. calculated from the influence of consumption of NaOH solution on time. The percentage of reactivation (%) was calculated from measured data according to formula: a0 ar x 1 100 % a0 ai RESULTS All the obtained results are summarized in Table 1 and Fig. 2. As resulted, obidoxime was able to reactivate AChE inhibited by all tested nerve agents and pesticides. As it is known, the sufficient reactivation potency caus- Fig. 2. Efficacy of oxime obidoxime in reactivation of ing survival of the intoxicated organism should be over 17 different AChE inhibitors (% reactivation); con- 10% . From this point of view, cyclosarin-, soman – and centration of the obidoxime 10–3 M and 10–5 M. methylchlorpyrifos-inhibited AChE was not sufficiently reactivated. At low for human relevant concentrations (10–5 M), obtained results are worse. At this concentra- tion, only tabun, Russian VX, chorpyrifos, paraoxon, Table 1. Reactivation of nerve agents – and pesticide- DDVP and DFP (limiting activity) reached sufficient inhibited AChE; concentration reactivation activity. of the obidoxime 10–3 M and 10–5 M. Reactivation [%] Reactivation [%] Nerve agent DISCUSSION (10–5 M) (10–3 M) Probability of organophosphorus pesticide poisoning Tabun 28 37 is in Czech Republic relatively rare. Number of people Sarin 4 41 intoxicated by pesticides is increased mostly in developing countries18–20. On the contrary, possibility of nerve agent Cyclosarin 2 4 misuse or misuse of pesticides as low-toxic and accessible Soman* 0 5 nerve agents is more probable in advanced countries by terrorists who do not like this kind consumer society. VX 8 79 Owing to this, preparedness for this threat is of great Russian VX 17 66 interest of scientists working in this area. Obidoxime is the only accessible reactivator available for the civilian Chlorpyrifos 35 63 sector in the Czech Republic. Its reactivation potency is Paraoxon 37 76 according to the literature not so good to think that it is a universal antidote21–24. In our in vitro experiment, we Methyl- 03confirmed this statement. If inhibitors such as cyclosarin, chlorpyrifos soman or methyl-chlorpyrifos would be misused, no anti- DDVP 31 51 dote is available. Moreover, high doses of this oxime are needed to reactivate sufficiently – sarin and VX. However, DFP 11 18 high concentration of obidoxime could exert many side effects and in very high doses also death due to the cholin- * In case of soman, only 15 min inhibition was used be- ergic crisis25. cause of aging. Intoxication of those nerve agents, which were not reactivated by obidoxime, could be then treated by us- ing atropine only, anticonvulsives and other supportive treatment. Second possibility is to use military antidotes, especially oxime HI-6, which is considered to be broad- Reactivation potency of the acetylcholinesterase reactivator Obidoxime is limited 261 spectrum reactivator26–29. However, it is at present time 11. El-Naggar AR, Abdalla MS, El-Sebaey AS, Badawy SM. Clinical not approved for civilian purposes. findings and cholinesterase levels in children of organophosphates Other possibility is to find quite new oxime which will and carbamates poisoning. Eur J Pediatr 2009; 168: 951–956. 12. Musilek K, Holas O, Kuca K, Jun D, Dohnal V, Dolezal M. be really universal antidote able to reactivate AChE inhib- Synthesis of the novel series of asymmetrical bispyridinium com- ited by all nerve agents and pesticides. For this purpose, pounds bearing xylene linker and evaluation of their reactivation many laboratories throughout the world are working on activity against tabun and paraoxon-inhibited acetylcholinesterase. this topic5, 12, 15, 30–35. J Enzyme Inhib Med Chem 2007; 22: 425–432. Finally, combination of two oximes could solve 13. Jun D, Stodulka P, Kuca K, Koleckar V, Dolezal B, Simon P, Veverka M. HPLC analysis of HI-6 dichloride and dimethanesul- this problem. This topic was already discussed in1989 fonate – antidotes against nerve agents and organophosphorus (ref.36, 37). Nowadays, several scientists re-open this ap- pesticides. Anal Lett 2007; 40: 2783–2787. proach. However, there will be probably problem with 14. Jun D, Stodulka P, Kuca K, Koleckar V, Dolezal B, Simon P,Veverka licensing of such antidotal mixture consisting of two com- M. TLC analysis of intermediates arising during the preparation of pounds38. oxime HI-6 dimethanesulfonate. J Chrom Sci 2008; 46: 316–319. 15. Musilek K, Holas O, Kuca K, Jun D, Dohnal V, Opletalova V, Dolezal M. Synthesis of Monooxime-Monocarbamoyl Bispyri- dinium Compounds bearing (E)-but-2-ene Linker and Evaluation of CONCLUSION their Reactivation Activity against Tabun – and Paraoxon-Inhibited Acetylcholinesterase. J Enzyme Inhib Med Chem 2008; 23: 70–76. In conclusion, AChE reactivator obidoxime is not a 16.
Recommended publications
  • Chlorpyrifos (Dursban) Ddvp (Dichlorvos) Diazinon Malathion Parathion
    CHLORPYRIFOS (DURSBAN) DDVP (DICHLORVOS) DIAZINON MALATHION PARATHION Method no.: 62 Matrix: Air Procedure: Samples are collected by drawing known volumes of air through specially constructed glass sampling tubes, each containing a glass fiber filter and two sections of XAD-2 adsorbent. Samples are desorbed with toluene and analyzed by GC using a flame photometric detector (FPD). Recommended air volume and sampling rate: 480 L at 1.0 L/min except for Malathion 60 L at 1.0 L/min for Malathion Target concentrations: 1.0 mg/m3 (0.111 ppm) for Dichlorvos (PEL) 0.1 mg/m3 (0.008 ppm) for Diazinon (TLV) 0.2 mg/m3 (0.014 ppm) for Chlorpyrifos (TLV) 15.0 mg/m3 (1.11 ppm) for Malathion (PEL) 0.1 mg/m3 (0.008 ppm) for Parathion (PEL) Reliable quantitation limits: 0.0019 mg/m3 (0.21 ppb) for Dichlorvos (based on the RAV) 0.0030 mg/m3 (0.24 ppb) for Diazinon 0.0033 mg/m3 (0.23 ppb) for Chlorpyrifos 0.0303 mg/m3 (2.2 ppb) for Malathion 0.0031 mg/m3 (0.26 ppb) for Parathion Standard errors of estimate at the target concentration: 5.3% for Dichlorvos (Section 4.6.) 5.3% for Diazinon 5.3% for Chlorpyrifos 5.6% for Malathion 5.3% for Parathion Status of method: Evaluated method. This method has been subjected to the established evaluation procedures of the Organic Methods Evaluation Branch. Date: October 1986 Chemist: Donald Burright Organic Methods Evaluation Branch OSHA Analytical Laboratory Salt Lake City, Utah 1 of 27 T-62-FV-01-8610-M 1.
    [Show full text]
  • Ambient Water Quality Criteria for Chlorpyrifos
    United State. Office of Water EPA 440/5-86~05 Environmental Protection Regulations and Standards September 1986 Amy l. lea~erry Agency Criteria and Standards Division Washington DC 20460 Water &EPA Ambient Wat'er Quality Criteria for Chlorpyrifos - 1986 &~IENT AQUATIC LIFE WATER QUALITY CRITERIA FOR CHLORPYRIFOS U.S. ENVIRONMENTAL PROTECTION AGENCY OFFICE OF RESEARCH AND DEVELOPMENT ENVIRONMENTAL RESEARCH LABORATORIES DULUTH, MINNESOTA NARRAGANSETT, RHODE ISLAND NOTICES This document has been reviewed by the Criteria and Standards Division, Office of Water Regulations and Standards, U.S. Environmental Protection Agency, and approved for publication. Mention of trade names or commercial products does not constitute endorsement or recommendation for use. This document is availaryle to the public throu~h the National Technical Inf0rmation Service (NTIS), 5285 Port Royal Road, Springfield, VA 22161. 11 FOREWORD Section 304(a)(1) of the Clean Water Act of 1977 (P.L. 95-217) requires the Administrator of the Environmental Protection Agency to publish water quality criteria that accurately reflect the latest scientific knowledge on the kind and extent of all identifiable effects on health and welfare that might be expected from the presence of pollutants in any body of water~ including ground water. This document is a revision of proposed criteria based upon consideration of comments received from other Federal agencies~ State agencies~ special interest groups~ and individual scientists. Criteria contained in this document replace any previously published EPA aquatic life criteria for the same pollutant(s). The term "water quality criteria" is used in two sections of the Clean Water Act~ section 304(a)(1) and section 303(c)(2).
    [Show full text]
  • Pesticides and Toxic Substances
    UNITED STATES ENVIRONMENTAL PROTECTION AGENCY WASHINGTON D.C., 20460 OFFICE OF PREVENTION, PESTICIDES AND TOXIC SUBSTANCES MEMORANDUM DATE: July 31, 2006 SUBJECT: Finalization of Interim Reregistration Eligibility Decisions (IREDs) and Interim Tolerance Reassessment and Risk Management Decisions (TREDs) for the Organophosphate Pesticides, and Completion of the Tolerance Reassessment and Reregistration Eligibility Process for the Organophosphate Pesticides FROM: Debra Edwards, Director Special Review and Reregistration Division Office of Pesticide Programs TO: Jim Jones, Director Office of Pesticide Programs As you know, EPA has completed its assessment of the cumulative risks from the organophosphate (OP) class of pesticides as required by the Food Quality Protection Act of 1996. In addition, the individual OPs have also been subject to review through the individual- chemical review process. The Agency’s review of individual OPs has resulted in the issuance of Interim Reregistration Eligibility Decisions (IREDs) for 22 OPs, interim Tolerance Reassessment and Risk Management Decisions (TREDs) for 8 OPs, and a Reregistration Eligibility Decision (RED) for one OP, malathion.1 These 31 OPs are listed in Appendix A. EPA has concluded, after completing its assessment of the cumulative risks associated with exposures to all of the OPs, that: (1) the pesticides covered by the IREDs that were pending the results of the OP cumulative assessment (listed in Attachment A) are indeed eligible for reregistration; and 1 Malathion is included in the OP cumulative assessment. However, the Agency has issued a RED for malathion, rather than an IRED, because the decision was signed on the same day as the completion of the OP cumulative assessment.
    [Show full text]
  • Qsar Analysis of the Chemical Hydrolysis of Organophosphorus Pesticides in Natural Waters
    QSAR ANALYSIS OF THE CHEMICAL HYDROLYSIS OF ORGANOPHOSPHORUS PESTICIDES IN NATURAL WATERS. by Kenneth K. Tanji Principal Investigator and Jonathan 1. Sullivan Graduate Research Assistant Department of Land, Air and Water Resources University of California, Davis Technical Completion Report Project Number W-843 August, 1995 University of California Water Resource Center The research leading to this report was supported by the University of California Water Resource Center as part of Water Resource Center Project W-843. Table of Contents Page Abstract 2 Problem and Research Objectives 3 Introduction 5 Theoretical Background 6 QSAR Methodology 7 Molecular Connectivity Theory 8 Organophosphorus Pesticides 12 Experimental Determination of Rates 15 Results and Discussion 17 Principal Findings and Significance 19 References 34 List of Tables Page Table 1. Statistical relationship between OP pesticides and first-order MC/'s. 30 Table 2. Inherent conditions of waters used in experimental work. 16 Table 3. Estimated half-lives for organophosphorus esters derived from model. 31 Table 4. Half-lives and first-order MCI' sfor model calibration data set. 31 Table 5. Experimental kinetic data for validation set compounds, Sacramento. 33 List of Figures Page Figure 1. Essential Features OfQSAR Modeling Methodology. 21 Figure 2. Regression plot for In hydrolysis rate vs. 1st order MCl' s. 22 Figure 3. a 3-D molecular model, a line-segment model and a graphical model. 23 Figure 4. Molecular connectivity index suborders. 24 Figure 5. Chlorpyrifos and its fourteen fourth order path/cluster fragments. 25 Figure 6. Abridged MClndex output. 26 Figure 7. Parent acids of most common organophosphorus pesticides. 12 Figure 8.
    [Show full text]
  • Efficacy of Trimedoxime in Mice Poisoned with Dichlorvos, Heptenophos Or Monocrotophos
    CORE Metadata, citation and similar papers at core.ac.uk Provided by FarFar - Repository of the Faculty of Pharmacy, University of Belgrade C Basic & Clinical Pharmacology & Toxicology 2005, 96, 111–117. Printed in Denmark . All rights reserved Copyright C ISSN 1742-7835 Efficacy of Trimedoxime in Mice Poisoned with Dichlorvos, Heptenophos or Monocrotophos Biljana Antonijevic´1, Dubravko Bokonjic´2, Milosˇ P. Stojiljkovic´2, Vesna Kilibarda2, Zoran A. Milovanovic´2, Mirjana Nedeljkovic´1 and Matej Maksimovic´1 1Institute of Toxicological Chemistry, School of Pharmacy, University of Belgrade, Vojvode Stepe 450, and 2National Poison Control Centre, Military Medical Academy, Crnotravska 17; 11000 Belgrade, Serbia and Montenegro (Received June 18, 2004; Accepted September 3, 2004) Abstract: The aim of the study was to examine antidotal potency of trimedoxime in mice poisoned with three direct dimethoxy-substituted organophosphorus inhibitors. In order to assess the protective efficacy of trimedoxime against dichlorvos, heptenophos or monocrotophos, median effective doses and efficacy half-times were calculated. Trimedoxime (24 mg/kg intravenously) was injected 5 min. before 1.3 LD50 intravenously of poisons. Activities of brain, diaphragmal and erythrocyte acetylcholinesterase, as well as of plasma carboxylesterases were determined at different time intervals (10, 40 and 60 min.) after administration of the antidotes. Protective effect of trimedoxime decreased according to the following order: monocrotophos Ͼ heptenophos Ͼ dichlorvos. Administration of the oxime produced a significant reacti- vation of central and peripheral acetylcholinesterase inhibited with dichlorvos and heptenophos, with the exception of erythrocyte acetylcholinesterase inhibited by heptenophos. Surprisingly, trimedoxime did not induce reactivation of mon- ocrotophos-inhibited acetylcholinesterase in any of the tissues tested.
    [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]
  • For Aldicarb Reregistration Eligibility Decision (RED) Document for Aldicarb
    United States Prevention, Pesticides EPA Environmental Protection and Toxic Substances September 2007 Agency (7508P) Reregistration Eligibility Decision for Aldicarb Reregistration Eligibility Decision (RED) Document for Aldicarb List A Case Number 0140 Approved by: Date: Steven Bradbury, Ph.D. Director Special Review and Reregistration Division Page 2 of 191 Table of Contents Aldicarb Reregistration Eligibility Decision Team ........................................................................ 5 Glossary of Terms and Abbreviations ............................................................................................ 6 Abstract........................................................................................................................................... 8 I. Introduction ................................................................................................................................. 9 II. Chemical Overview.................................................................................................................. 11 A. Chemical Identity..................................................................................................................11 B. Regulatory History ................................................................................................................12 C. Use and Usage Profile...........................................................................................................12 D. Tolerances .............................................................................................................................13
    [Show full text]
  • Chlorpyrifos Hazards to Fish, Wildlife, and Invertebrates: a Synoptic Review
    Biological Report Contaminant Hazard Reviews March 1988 Report No. 13 CHLORPYRIFOS HAZARDS TO FISH, WILDLIFE, AND INVERTEBRATES: A SYNOPTIC REVIEW By Edward W. Odenkirchen Department of Biology The American University Washington, DC 20016 And Ronald Eisler U.S. Fish and Wildlife Service Patuxent Wildlife Research Center Laurel, MD 20708 SUMMARY Chlorpyrifos (phosphorothioic acid O, O,-diethyl 0-(3,5,6,-trichloro-2-pyridinyl) ester), an organophosphorus compound with an anticholinesterase mode of action, is used extensively in a variety of formulations to control a broad spectrum of agricultural and other pestiferous insects. Domestic use of chlorpyrifos in 1982 was about 3.6 million kg; the compound is used mostly in agriculture, but also to control mosquitos in wetlands (0.15 million kg applied to about 600,000 ha) and turf-destroying insects on golf courses (0.04 million kg). Accidental or careless applications of chlorpyrifos have resulted in the death of many species of nontarget organisms such as fish, aquatic invertebrates, birds, and humans. Applications at recommended rates of 0.028 to 0.056 kg/surface ha for mosquito control have produced mortality, bioaccumulation, and deleterious sublethal effects in aquatic plants, zooplankton, insects, rotifers, crustaceans, waterfowl, and fish; adverse effects were also noted in bordering invertebrate populations. Degradation rate of chloropyrifos in abiotic substrates varies, ranging from about 1 week in seawater (50% degradation) to more than 24 weeks in soils under conditions of dryness, low temperatures, reduced microbial activity, and low organic content; intermediate degradation rates reported have been 3.4 weeks for sediments and 7.6 weeks for distilled water.
    [Show full text]
  • Acetylcholinesterase: the “Hub” for Neurodegenerative Diseases And
    Review biomolecules Acetylcholinesterase: The “Hub” for NeurodegenerativeReview Diseases and Chemical Weapons Acetylcholinesterase: The “Hub” for Convention Neurodegenerative Diseases and Chemical WeaponsSamir F. de A. Cavalcante Convention 1,2,3,*, Alessandro B. C. Simas 2,*, Marcos C. Barcellos 1, Victor G. M. de Oliveira 1, Roberto B. Sousa 1, Paulo A. de M. Cabral 1 and Kamil Kuča 3,*and Tanos C. C. França 3,4,* Samir F. de A. Cavalcante 1,2,3,* , Alessandro B. C. Simas 2,*, Marcos C. Barcellos 1, Victor1 Institute G. M. ofde Chemical, Oliveira Biological,1, Roberto Radiological B. Sousa and1, Paulo Nuclear A. Defense de M. Cabral (IDQBRN),1, Kamil Brazilian Kuˇca Army3,* and TanosTechnological C. C. França Center3,4,* (CTEx), Avenida das Américas 28705, Rio de Janeiro 23020-470, Brazil; [email protected] (M.C.B.); [email protected] (V.G.M.d.O.); [email protected] 1 Institute of Chemical, Biological, Radiological and Nuclear Defense (IDQBRN), Brazilian Army (R.B.S.); [email protected] (P.A.d.M.C.) Technological Center (CTEx), Avenida das Américas 28705, Rio de Janeiro 23020-470, Brazil; 2 [email protected] Mors Institute of Research (M.C.B.); on Natural [email protected] Products (IPPN), Federal (V.G.M.d.O.); University of Rio de Janeiro (UFRJ), CCS,[email protected] Bloco H, Rio de Janeiro (R.B.S.); 21941-902, [email protected] Brazil (P.A.d.M.C.) 32 DepartmentWalter Mors of Institute Chemistry, of Research Faculty of on Science, Natural Un Productsiversity (IPPN),
    [Show full text]
  • United States Patent (19) 11 Patent Number: 5,703,064 Yokoi Et Al
    US005703064A United States Patent (19) 11 Patent Number: 5,703,064 Yokoi et al. 45) Date of Patent: Dec. 30, 1997 54 PESTICIDAL COMBINATIONS FOREIGN PATENT DOCUMENTS 75 Inventors: Shinji Yokoi; Akira Nishida, both of 0 196524 10/1986 European Pat. Of.. Shiga-ken; Tokio Obata; Kouichi Golka, both of Ube, all of Japan OTHER PUBLICATIONS 73) Assignees: Sankyo Company, Limited, Tokyo; Worthing et al, The Pesticide Manual, 9th Ed. (1991), pp. Ube industries Ltd., Ube, both of 747 and 748. Japan L.C. Gaughan et al., "Pesticide interactions: effects of orga nophosphorus pesticides on the metabolism, toxicity, and 21 Appl. No.: 405,795 persistence of selected pyrethroid insecticides". Chemical Abstracts, vol. 94, No. 9, 1981, No. 59740k of Pestic. 22 Filed: Mar 16, 1995 Biochem. Physio., vol. 14, No. 1, 1980, pp. 81-85. 30 Foreign Application Priority Data I. Ishaaya et al., "Cypermethrin synergism by pyrethroid esterase inhibitors in adults of the whitefly Bemisia tabaci". Mar 16, 1994 JP Japan ............................ HE6045.405 Chemical Abstracts, vol. 107, No. 9, 1987, No. 72818y of (51) Int. Cl................. A01N 43/54; A01N 57/00 Pestic Biochem. Physiol., vol. 28, No. 2, 1987, pp. 155-162. 52 U.S. C. ......................................... 51480; 514/256 (58) Field of Search ..................................... 514/80, 256 Primary Examiner Allen J. Robinson Attorney, Agent, or Firm-Frishauf, Holtz, Goodman, 56 References Cited Langer & Chick, P.C. U.S. PATENT DOCUMENTS 57 ABSTRACT 4,374,833 2/1983 Badmin et al. ...................... 424/225 Combinations of the known compound pyrimidifen with 4,845,097 7/1989 Matsumoto et al... 514/234.2 phosphorus-containing pesticides have a synergistic pesti 4,935,516 6/1990 Ataka et al.
    [Show full text]
  • OHA 8964 Technical Report: Marijuana Contaminant Testing
    TECHNICAL REPORT: OREGON HEALTH AUTHORITY’S PROCESS TO DETERMINE WHICH TYPES OF CONTAMINANTS TO TEST FOR IN CANNABIS PRODUCTS, AND LEVELS FOR ACTION Author David G. Farrer, Ph.D. Public Health Toxicologist PUBLIC HEALTH DIVISION Technical Report: Oregon Health Authority’s Process to Determine Which Types of Contaminants to Test for in Cannabis Products, and Levels for Action* Author: David G. Farrer, Ph.D., Public Health Toxicologist Acknowledgments OHA would like to thank the following individuals and organizations for their valuable contributions to the development of cannabis testing Oregon Administrative Rules (OAR 333-7-0010 through 333-7-0100 and OAR 333-7-0400 and 333-7-0410 Exhibit A) and this report: Brian Boling Rose Kachadoorian Laboratory Program Manager Oregon Department of Agriculture Oregon Department of Environmental Quality Jeremy L. Sackett Cascadia Labs, Cannabis Safety Theodore R. Bunch, Jr. Institute, and Oregon Cannabis Pesticide Analytical and Response Association Center Coordination Leader Oregon Department of Agriculture Bethany Sherman Oregon Growers Analytical and Keith Crosby Cannabis Safety Institute Technical Director Synergistic Pesticide Lab Shannon Swantek Oregon Environmental Laboratory Ric Cuchetto Accreditation Program, Public The Cannabis Chemist Health Division, Oregon Health Authority Camille Holladay Lab Director Rodger B. Voelker, Ph.D. Synergistic Pesticide Lab Lab Director Oregon Growers Analytical Mowgli Holmes, Ph.D. Phylos Bioscience and Cannabis Safety Institute For information on this report, contact David Farrer at [email protected]. * Please cite this publication as follows: Farrer DG. Technical report: Oregon Health Authority’s process to decide which types of contaminants to test for in cannabis. Oregon Health Authority.
    [Show full text]
  • List of Lists
    United States Office of Solid Waste EPA 550-B-10-001 Environmental Protection and Emergency Response May 2010 Agency www.epa.gov/emergencies LIST OF LISTS Consolidated List of Chemicals Subject to the Emergency Planning and Community Right- To-Know Act (EPCRA), Comprehensive Environmental Response, Compensation and Liability Act (CERCLA) and Section 112(r) of the Clean Air Act • EPCRA Section 302 Extremely Hazardous Substances • CERCLA Hazardous Substances • EPCRA Section 313 Toxic Chemicals • CAA 112(r) Regulated Chemicals For Accidental Release Prevention Office of Emergency Management This page intentionally left blank. TABLE OF CONTENTS Page Introduction................................................................................................................................................ i List of Lists – Conslidated List of Chemicals (by CAS #) Subject to the Emergency Planning and Community Right-to-Know Act (EPCRA), Comprehensive Environmental Response, Compensation and Liability Act (CERCLA) and Section 112(r) of the Clean Air Act ................................................. 1 Appendix A: Alphabetical Listing of Consolidated List ..................................................................... A-1 Appendix B: Radionuclides Listed Under CERCLA .......................................................................... B-1 Appendix C: RCRA Waste Streams and Unlisted Hazardous Wastes................................................ C-1 This page intentionally left blank. LIST OF LISTS Consolidated List of Chemicals
    [Show full text]