Kinetic Study of the Reaction of Bromine with Phenylhydrazine in Sulfuric Acid *Media

Total Page:16

File Type:pdf, Size:1020Kb

Kinetic Study of the Reaction of Bromine with Phenylhydrazine in Sulfuric Acid *Media DAEHAN HWAHK HWOCJEE (Journal of the Korean Chemical Society) Vol. 21, No. 4, 1977 . Printed in Repulic of Korea 페닐히드라진과 브롬의 반응메카니즘에 관한 연구* **朴炳彬 -朴一鉉•孔永建•***崔圭源 성 균관대 학교 이 공대학 화학과 **원광대학교 문리과대학 화학과 ***서울대학교 자연과학 대학 화학과 (1976. 11. 9 접수 ) Kinetic Study of the Reaction of Bromine with Phenylhydrazine in Sulfuric Acid *Media Byoung Bin Park**, Il H. Park, Young Kun Kong and Q. Won Choi*** Department of Chemistry, Sung-Gyun Gwan University, Seoul, Korea ^Department of Chemistry, Won Kwang UniversityIri, Korea **^Department of Chemistry, Seoul National University, Seoul, Korea (Received Nov. 29, 1976) 요 약 . 황산산성 에 서 페 닐 히 드라진 과 브롬의 반응을 속도론적 으로 검 토하였 다 . 겉 보기 2차 반응 속도상수는 LM 이 하의 황산농도에 서 는 수소이 온 농도 에 대 략 역 비 레 한다 . KBr• 첨 가의 영 향을 검 토 하여 Bl 및 Br厂가 반응화학종이고 , 이들의 속도상수는 20°C의 O.OIMH2SO4용액에서 각각 5X 105M-\ sec기 및 O.TXIO5^1, sec-】 임 을 밝혔다 . 2,4-디 니 트로 페 닐히 드라진의 브롬과의 반응속 도상수는 수소이온 농도에 거의 무관계하며 Br2 및 Br厂에 대하여 각각 1. 2X105A/"\ sec'1 및 2. OX 104M~\ sec-】이다 . ABSTRACT. The reaction of phenylhydrazine with bromine in sulfuric acid solution has been studied kinetically. The pseudo-second-order rate constant is approximately inversely proportional to hydrogen-ion concentration when the concentration of sulfuric acid is lower than IM. From the study of the effect of potassium bromide concentrration on the rate constant, it is concluded that both neutral bromine and tribromide ion participate in the reaction, the rate constants in 0. 01M H2SO4 being 5X105Af-1, sec-1 and 0. 7 X105M-1, sec"1, respectively at 20°C. The pseudo-second-order rate constant of 2,4-dinitrophenylhydrazine-bromine reaction is inde­ pendent of hydrogen ion concentration. From the KBr addition experiment, the rate constants for Bi2* and Bi■厂 were obtained as 1. 2 X105A/-1, sec-1 and 2. 0 X 104Af-1, sec-1, rspectively. *Based in part on the thesis submitted to Graduate School of Sung-Gyun Gwan University by Y. K. K. in partial fullfilment of Masters Degree. ***To whom correspondences should be addressed. 一 227 — 228 朴炳彬 •朴 一鉉 •孔永建 •崔圭源 concentration in the kinetics study. INTRODUCTION GALVANOSTAT (0M-1A type of TO-A The reaction of hydrazine with bromine pro­ Co., Japan) was used in coulometric generation ceeds via formation of a slowly decomposing of bromine. intermediate that is probably formed by bromi­ Electrodes. A platinum wire (2mm long) nation of the fist-step reaction product, N2H2.1 indicator electrode and a mercurous sulphate Since only very little amount of hydrazoic acid reference electrode connected by a K2SO4 salt is detectable in the reaction product, the bro­ bridge were used in conjunction with the pola- mination of diimide proceeds much faster than rograph mentioned above to record the limiting its dimerization. It has been reported that phen­ current of bromine while stirring the solution ylhydrazine reacts with bromine quantitatively with a magnetic stirrer powered by a Sola con­ and a coulometric titration with electrolytically stant-voltage transformer. A workin흥 electrode generated bromine can be carried out sucess- and an auxilliary electrode both made by using fully2. The characteristics of the possible 2cm2 platinum foils were used for coulometric intermediate in this reaction, phenyldiazene, generation of bromine. The auxilliary electrode are rather well known3 compared to those of compartment was separated from the reaction diimide, because the former is much more stable chamber by a fritted glass membrane. The ar­ than the latter. Therefore, one can expect rangement of electrodes in the reaction vessel that comparison of N2H4-Br2 reaction with and electric circuit are similar to those described ^NHNH2~Br2 reaction would lead to better previously.1 understanding of both reactions. Two platinum wire (2mm) electrodes were The present study was undertaken to clarify used in biamperometric titration with 0. 25 volts the mechanism of the reaction of phenylhydra­ potential impressed across them. zine with bromine. Since the reaction is quite Reagents. All reagents were of reagent grade fast, the concentration of the reactions were and were used without further purification. kept rather samll. For this purpose, bromine Doubly distilled water was used through out was generated coulometrically. After adding the kinetics study. Nitrogen used for deoxygen­ known amounts of phenylhydrazine solution, ating the reaction media was purfied by bubling the bromine concentration was followed by am­ through an alkaline solution of pyrogallol. perometric method using a platinum microelec- Aqueous solution of 0.1 molar phenylhydrazine trode and mercury-mercurous sulphate electrode hydrochlo호 ide and 0- Olmolar 2,4-dinitrophenyl- as described in the previous report.1 hydrazine in IM sulfuric acid were the stock solutions used in kinetic measurements. EXPERIMENT Determination of Stoichiometry. A satura­ ted bromine solution in IM H2SO4 was prepared Apparatus. POTENTIOSTAT and GALVA­ and standardized against hydrazine sulfate by NOMETER (OM-1A type of TO-A Co., Japan) biamperometric titration method. The solutions were used in biamperometric titration of phen­ of hydrazine derivatives were titrated with the ylhydrazine with bromine standard solution. standardized bromine solution biamperometri­ POLAROGRAPH (RP-2 type of Shimadzu cally. Co. , Japan) was used to record the bromine Measurement of Reaction Rate. Fifty mil­ Journal of the Korean Chemical Society 페닐히드라진과 브롬의 반옹메카니즘에 관한 연구 229 liliters of aqueous solution containing known rate of bromine generation. The amperometric amounts of H2SO4 and KBr was transferred to reading was calibrated by titrating electroge­ the reaction chamber of the reaction vessel im­ nerated bromine with hydrazine standard 온 olu- mersed in a 바 lermostat kept at 20±l°C. At tion. After turning off the electrolysis current, the same time, the auxilliary electrode compart­ keeping the polarograph circuit on, a measured ment was filled with the same solution up to volume of 1.0X10-3 m사 ar or more 击lute the same level. Deoxygenated nitrogen was phenylhydrazine solution was quickly injected passed through the s시 ution in the reaction into the reaction chamber by using a hyperder- compartment for fifteen minutes while agitating mic syring. The initial concentration of phen­ vigorously by means of the magnetic stirrer. ylhydrazine was in the range of 10~5~10~6AA Then bromine was generated by passing a con­ A typical recording of the bromine current is stant current in the range 1~4 mA for a pre­ shown in Fig. 1 by the curve CD. determined period of time, ranging from 30 to 120 seconds to produce bromine at the concent­ RESULTS AND DISCUSSION ration range 10-5~10-6M The bromine con­ The stoichiometry of bromine나 lydrazine deri­ centration was followed amperometrically by vative reaction determined in 1A/ sulfuric acid recording the limiting current of the indicator medium is shown in Table 1. In the case of electrode kept at 0- 20 valts vs. mercurous sulfate-mercury reference electrode using the Dinitrophenylhydrazine, gas evolution started when about two equivalents of bromine per polarograph. A typical recording shown by the mole was added. Whereas, in the case of phen­ dotted line AB in Fig. 1 confirms a constant ylhydrazine, gas evolution was observable when about four equivalents of bromine per mole was added. In a qualitative test, it was found that phen­ ylhydrazine reacted with an excess of bromine in IM H2SO4 to produce 2,4,6-tribromophenol which was confirmed by melting point (96°C) and IR spectrum, and it has been reported4 that the final product is ^N2Br. From these facts it was inferred that the reaction proceeds in the following sequance: RNHNH2+Br2쓰 RN=NH+2H++2Br- (i)' RN=NH+B.쓰 RN=N++H+ + 2Br~ (ii)} (1) RN=N++H2O A.ROH+H++N2 (iii). where it is known that k3 for benznee diazo- TIME (sec) nium chloride is of the order of 10-4 sec-1 at Fig. 1. A typical recording of bromine concentration: room temperature5. Thus, because of the sta­ in H2SO4, 3. 0 M KBr at 20° C. a:〔&2〕=2.87X10-6M, b: (C6H8N2)=1.84X10-6M bility of the benzene diazonium salt in acid (see Table 2) media, nitrogen evolution becomes perceptible Vol - 21, No. 4, 1977 230 朴炳彬 •朴 一鉉 •孔永建 •崔圭源 Table 1. Number of equivalents of bromine consumed by one mole of hydrazine dervative when titrated with bromine solution in 1A/ H2SO4. Concetration of Phenylhydrazine- 2, 4-Dinitrophenyl- Hydrazine hydrazines, M hydrochloride hydrazine 1X10-2 4. 00 4. 02 4. 04 1X10-3 4. 00 4. 02 4. 02 only at the latter stage of the titration. Since shown by Table 1. the second order rate constant of bromination The pseudo-second-order rate constants were of phenol i오 of the order of 1051 mole~1sec~1, computed according to the formula part of bromine must be consumed by phenol 2 30 (2) formed by slow decomposition of the diazonium ^obs — log “(0—Q, salt. Therefore, it is expected that a mole of where a and b are the initial concentrations phenylhydrazine shou너 consume slightly more of bromine and phenylhydrazine, respectively, than four equivalents of bromine, and the and x is the concentration decrease of bromine experimental results given in. Table 1 are in at the time t. The result for the run recorded accord with this expectation. in Fig. 1 is shown in Table 2. The pseudo- Furthermore, when 2 mmoles of phenylhy­ second-order rate constant increases gradually drazine dissolved in 100 mZ of deaerated 1M with time. If the reaction mechanism is repre­ sulfuric acid was treated with 4 mmoles of bro­ sented by (1), the pseudo-second-order rate mine by adding dropwise its saturated solution constant is expected to increase gradually when in lAf H2SO4 and mixed with 2 5mmoles of 尅 is slightly larger than kit as can be shown dimethylaniline, a red substance preciptated.
Recommended publications
  • Hydrazine Sulfate Hazard Summary Identification
    Common Name: HYDRAZINE SULFATE CAS Number: 10034-93-2 RTK Substance number: 2360 DOT Number: None Date: December 1994 Revision: May 2001 ------------------------------------------------------------------------- ------------------------------------------------------------------------- HAZARD SUMMARY * Hydrazine Sulfate can affect you when breathed in and * Exposure to hazardous substances should be routinely may be absorbed through the skin. evaluated. This may include collecting personal and area * Hydrazine Sulfate should be handled as a air samples. You can obtain copies of sampling results CARCINOGEN—WITH EXTREME CAUTION. from your employer. You have a legal right to this * Hydrazine Sulfate can irritate and burn the eyes and skin. information under OSHA 1910.1020. * Breathing Hydrazine Sulfate can irritate the nose, throat * If you think you are experiencing any work-related health and lungs causing coughing and shortness of breath. problems, see a doctor trained to recognize occupational * Exposure can cause you to feel dizzy and lightheaded. diseases. Take this Fact Sheet with you. Higher levels can cause trembling, a feeling of excitement, and even convulsions (fits). WORKPLACE EXPOSURE LIMITS * Hydrazine Sulfate may damage blood cells causing a low No occupational exposure limits have been established for blood count (anemia). Hydrazine Sulfate. This does not mean that this substance is * Exposure may damage the liver and kidneys. not harmful. Safe work practices should always be followed. * Hydrazine Sulfate may cause a skin allergy. If allergy develops, very low future exposure can cause itching and a * Hydrazine Sulfate may be a CARCINOGEN in humans. skin rash. There may be no safe level of exposure to a carcinogen, so all contact should be reduced to the lowest possible level.
    [Show full text]
  • Toxicological Profile for Hydrazines. US Department Of
    TOXICOLOGICAL PROFILE FOR HYDRAZINES U.S. DEPARTMENT OF HEALTH AND HUMAN SERVICES Public Health Service Agency for Toxic Substances and Disease Registry September 1997 HYDRAZINES ii DISCLAIMER The use of company or product name(s) is for identification only and does not imply endorsement by the Agency for Toxic Substances and Disease Registry. HYDRAZINES iii UPDATE STATEMENT Toxicological profiles are revised and republished as necessary, but no less than once every three years. For information regarding the update status of previously released profiles, contact ATSDR at: Agency for Toxic Substances and Disease Registry Division of Toxicology/Toxicology Information Branch 1600 Clifton Road NE, E-29 Atlanta, Georgia 30333 HYDRAZINES vii CONTRIBUTORS CHEMICAL MANAGER(S)/AUTHOR(S): Gangadhar Choudhary, Ph.D. ATSDR, Division of Toxicology, Atlanta, GA Hugh IIansen, Ph.D. ATSDR, Division of Toxicology, Atlanta, GA Steve Donkin, Ph.D. Sciences International, Inc., Alexandria, VA Mr. Christopher Kirman Life Systems, Inc., Cleveland, OH THE PROFILE HAS UNDERGONE THE FOLLOWING ATSDR INTERNAL REVIEWS: 1 . Green Border Review. Green Border review assures the consistency with ATSDR policy. 2 . Health Effects Review. The Health Effects Review Committee examines the health effects chapter of each profile for consistency and accuracy in interpreting health effects and classifying end points. 3. Minimal Risk Level Review. The Minimal Risk Level Workgroup considers issues relevant to substance-specific minimal risk levels (MRLs), reviews the health effects database of each profile, and makes recommendations for derivation of MRLs. HYDRAZINES ix PEER REVIEW A peer review panel was assembled for hydrazines. The panel consisted of the following members: 1. Dr.
    [Show full text]
  • Roc Appendix G
    Report on Carcinogens, Fourteenth Edition For Table of Contents, see home page: http://ntp.niehs.nih.gov/go/roc Appendix G: 91-59-8 see 2-Naphthylamine 91-94-1 (3,3′-dichlorobenzidine) see 3,3′-Dichlorobenzidine and Its Dihydrochloride List of Substances by CAS Number 92-67-1 see 4-Aminobiphenyl 92-87-5 (benzidine) see Benzidine and Dyes Metabolized to Benzidine 50-00-0 see Formaldehyde 93-15-2 see Methyleugenol 50-18-0 see Cyclophosphamide 94-59-7 see Safrole 50-29-3 see Dichlorodiphenyltrichloroethane 95-06-7 see Sulfallate 50-32-8 (benzo[a]pyrene) see Polycyclic Aromatic Hydrocarbons: 15 Listings 95-53-4 (o-toluidine) see o-Toluidine and Its Hydrochloride 50-55-5 see Reserpine 95-69-2 (p-chloro-o-toluidine) see p-Chloro-o-toluidine and Its Hydrochloride 51-52-5 see Propylthiouracil 95-80-7 see 2,4-Diaminotoluene 51-79-6 see Urethane 95-83-0 see 4-Chloro-o-phenylenediamine 52-24-4 see Thiotepa 96-09-3 see Styrene-7,8-oxide 53-70-3 (dibenz[a,h]anthracene) see Polycyclic Aromatic Hydrocarbons: 15 Listings 96-12-8 see 1,2-Dibromo-3-chloropropane 53-96-3 see 2-Acetylaminofluorene 96-13-9 see 2,3-Dibromo-1-propanol 55-18-5 (N-Nitrosodiethylamine) see N-Nitrosamines: 15 Listings 96-18-4 see 1,2,3-Trichloropropane 55-86-7 see Nitrogen Mustard Hydrochloride 96-45-7 see Ethylene Thiourea 55-98-1 see 1,4-Butanediol Dimethansulfonate 97-56-3 see o-Aminoazotoluene 56-23-5 see Carbon Tetrachloride 98-07-7 see Benzotrichloride 56-53-1 see Diethylstilbestrol 98-82-8 see Cumene 56-55-3 (benz[a]anthracene) see Polycyclic Aromatic Hydrocarbons: 15 Listings
    [Show full text]
  • HYDRAZINE Method Number: 108 Matrix: Air Target Concentration
    HYDRAZINE Method number: 108 Matrix: Air Target concentration: 10 ppb (13 µg/m3) and 1 ppm (1.3 mg/m3) OSHA PEL: 1 ppm (1.3 mg/m3) ACGIH TLV: 10 ppb (13 µg/m3) Procedure: Samples are collected closed-face by drawing known volumes of air through sampling devices consisting of three-piece cassettes, each containing two sulfuric acid treated 37-mm glass fiber filters separated by the ring section. The filters are extracted with a buffered EDTA disodium solution. An aliquot of the extract is derivatized with a benzaldehyde solution to form benzalazine from any hydrazine in the samples. The benzalazine is quantitated by LC using a UV detector. Recommended air volume and sampling rate: 240 L at 1.0 L/min Reliable quantitation limit: 0.058 ppb (0.076 µg/m3) Standard error of estimate at the target concentration: 7.5% at 10 ppb Target Concentration 5.2% at 1 ppm Target Concentration Status of method: Evaluated method. This method has been subjected to the established evaluation procedures of the Organic Methods Evaluation Branch. Date: February 1997 Chemist: Carl J. Elskamp Organic Methods Evaluation Branch OSHA Salt Lake Technical Center Salt Lake City, UT 84165-0200 1 of 19 T-108-FV-01-9702-M 1. General Discussion 1.1 Background 1.1.1 History In 1980, an air sampling and analytical procedure to determine hydrazine was validated by the OSHA Analytical Laboratory. (Ref. 5.1) The method (OSHA Method 20) is based on a field procedure developed by the U.S. Air Force that involves collection of samples using sulfuric acid coated Gas Chrom R and colorimetric analysis using p¯dimethylaminobenzaldehyde.
    [Show full text]
  • Hydrazine/Hydrazine Sulfate; CASRN 302-01-2
    Integrated Risk Information System (IRIS) U.S. Environmental Protection Agency Chemical Assessment Summary National Center for Environmental Assessment Hydrazine/Hydrazine sulfate; CASRN 302-01-2 Human health assessment information on a chemical substance is included in the IRIS database only after a comprehensive review of toxicity data, as outlined in the IRIS assessment development process. Sections I (Health Hazard Assessments for Noncarcinogenic Effects) and II (Carcinogenicity Assessment for Lifetime Exposure) present the conclusions that were reached during the assessment development process. Supporting information and explanations of the methods used to derive the values given in IRIS are provided in the guidance documents located on the IRIS website. STATUS OF DATA FOR Hydrazine/Hydrazine sulfate File First On-Line 09/07/1988 Category (section) Assessment Available? Last Revised Oral RfD (I.A.) not evaluated Inhalation RfC (I.B.) not evaluated Carcinogenicity Assessment (II.) yes 09/07/1988 I. Chronic Health Hazard Assessments for Noncarcinogenic Effects I.A. Reference Dose for Chronic Oral Exposure (RfD) Substance Name — Hydrazine/Hydrazine sulfate CASRN — 302-01-2 Not available at this time. 1 Integrated Risk Information System (IRIS) U.S. Environmental Protection Agency Chemical Assessment Summary National Center for Environmental Assessment I.B. Reference Concentration for Chronic Inhalation Exposure (RfC) Substance Name — Hydrazine/Hydrazine sulfate CASRN — 302-01-2 Not available at this time. II. Carcinogenicity Assessment for Lifetime Exposure Substance Name — Hydrazine/Hydrazine sulfate CASRN — 302-01-2 Last Revised — 09/07/1988 Section II provides information on three aspects of the carcinogenic assessment for the substance in question; the weight-of-evidence judgment of the likelihood that the substance is a human carcinogen, and quantitative estimates of risk from oral exposure and from inhalation exposure.
    [Show full text]
  • Interagency Committee on Chemical Management
    DECEMBER 14, 2018 INTERAGENCY COMMITTEE ON CHEMICAL MANAGEMENT EXECUTIVE ORDER NO. 13-17 REPORT TO THE GOVERNOR WALKE, PETER Table of Contents Executive Summary ...................................................................................................................... 2 I. Introduction .......................................................................................................................... 3 II. Recommended Statutory Amendments or Regulatory Changes to Existing Recordkeeping and Reporting Requirements that are Required to Facilitate Assessment of Risks to Human Health and the Environment Posed by Chemical Use in the State ............................................................................................................................ 5 III. Summary of Chemical Use in the State Based on Reported Chemical Inventories....... 8 IV. Summary of Identified Risks to Human Health and the Environment from Reported Chemical Inventories ........................................................................................................... 9 V. Summary of any change under Federal Statute or Rule affecting the Regulation of Chemicals in the State ....................................................................................................... 12 VI. Recommended Legislative or Regulatory Action to Reduce Risks to Human Health and the Environment from Regulated and Unregulated Chemicals of Emerging Concern ..............................................................................................................................
    [Show full text]
  • Download MSDS
    SAFETY DATA SHEET Issuing Date 05-Jul-2016 Revision Date 05-Jul-2016 Revision Number 3 This safety data sheet was created pursuant to the requirements of 29 CFR 1910.1200 1. IDENTIFICATION OF THE SUBSTANCE/PREPARATION AND OF THE COMPANY/UNDERTAKING Product identifier Product Name Turbidity Product Number 893 Synonyms None Recommended use of the chemical and restrictions on use Recommended Use Laboratory use only Uses advised against No information available Details of the supplier of the safety data sheet Supplier ERA, A Waters Company Supplier Address 16341 Table Mountain Parkway, Golden, CO 80403 USA Non-Emergency Telephone Number +1-303-431-8454 E-mail address [email protected] Emergency telephone number Company Emergency Phone In case of EMERGENCY call CHEMTREC Day or Night Number Within USA and Canada: 800-424-9300 International Call Collect: +1-703-527-3887 2. HAZARDS IDENTIFICATION Classification This chemical is considered hazardous by the 2012 OSHA Hazard Communication Standard (29 CFR 1910.1200). Skin corrosion/irritation Category 1 Serious eye damage/eye irritation Category 1 Skin sensitization Category 1 Carcinogenicity Category 1B GHS Label elements, including precautionary statements Emergency Overview Signal word Danger Hazard Statements Causes severe skin burns and eye damage May cause an allergic skin reaction May cause cancer _____________________________________________________________________________________________ Page 1 / 10 893 - Turbidity Revision Date 05-Jul-2016 _____________________________________________________________________________________________
    [Show full text]
  • Chemical Importance of Brady's Reagent
    IJRPC 2012, 2(4) Sachin S Kadam et al ISSN: 22312781 INTERNATIONAL JOURNAL OF RESEARCH IN PHARMACY AND CHEMISTRY Available online at www.ijrpc.com Review Article REVIEW ARTICLE ON: CHEMICAL IMPORTANCE OF BRADY’S REAGENT Sachin S Kadam*, Tambe ST, Grampurohit ND and Gaikwad DD Vishal Institute of pharmaceutical education and research, Ale. Tal-Junnar, Pune, Maharashtra, India. ABSTRACT Since the action of 2, 4-dinitrophenylhydrazine (Brady’s reagent) on aldehydes and ketones was first investigated by Purgotti in 1894, its usefulness as an analytical reagent for carbonyl containing compounds has been thoroughly exploited. The 2, 4 -DNHP reagent is an orange crystalline solid melting at 1990C. Its usefulness as a reagent stems from the fact that it forms crystalline derivatives which are easily purified and have melting points supposedly characteristic of the aldehyde or ketone used in preparing the derivative. In principle, each aldehyde and ketone should form a single 2,4-dinitrophenylhydrazone (DNPH) with a characteristic melting point. In practice, however, a number of the aldehydes and ketones do not follow this general rule but form multiple derivatives, differing either in melting point, crystal structure, or both. Even the colors of pure DNPH's of a partîcular aldehyde or ketone are sometimes different. Keywords: 2,4-DNPH, Brady’s reagent, 2, 4, - dinitrophenyl hydrazine. INTRODUCTION Structure of 2, 4-dinitrophenylhydrazine Aldehydes and ketones have been identified Although the name sounds complicated, and for a number of years by virtue of the fact that its structure looks quite complicated. they form crystalline condensation products with a number of amines.
    [Show full text]
  • Download This Topic [PDF]
    cancer.org | 1.800.227.2345 Known and Probable Human Carcinogens In general, the American Cancer Society does not determine if something causes cancer (that is, if it is a carcinogen). Instead, we rely on the determinations of other respected agencies, such as the International Agency for Research on Cancer (IARC) and the US National Toxicology Program (NTP). The lists below are from IARC and NTP, and more information on each of these known and probable human carcinogens can be found on their websites. To learn more about these agencies and how they study and classify cancer causes, see Determining if Something Is a Carcinogen1. What you should know ● The IARC and NTP act independently. Many known or suspected carcinogens appear on both organization’s lists; however, if a substance or exposure is only on one agency’s list, this it does not necessarily mean there is a controversy, as one agency may not have evaluated it. ● These lists are alphabetical, but many of the substances and exposures here can go by different names. This can make it hard to find a particular substance on one or both of these lists. ● These lists include only those agents that have been evaluated by the agencies. These agencies tend to focus on substances and exposures most likely to cause cancer, but there are many others that have not been fully studied yet. ● These lists include agents that have been classified as known and probable human carcinogens. The lists do not include substances that have been classified as possible carcinogens, for which the evidence is not as strong.
    [Show full text]
  • Safety Data Sheet SECTION 1: Identification 1.1
    Safety Data Sheet SECTION 1: Identification 1.1. Product Identifier Trade Name or Designation: Turbidity Standard, 1000 NTU, Formazin Product Number: 8825 Other Identifying Product Numbers: 8825-1, 8825-16 1.2. Recommended Use and Restrictions on Use General Laboratory Reagent 1.3. Details of the Supplier of the Safety Data Sheet Company: Ricca Chemical Company Address: 448 West Fork Drive Arlington, TX 76012 USA Telephone: 888-467-4222 1.4. Emergency Telephone Number (24 hr) CHEMTREC (USA) 800-424-9300 CHEMTREC (International) 1+ 703-527-3887 SECTION 2: Hazard(s) Identification 2.1. Classification of the Substance or Mixture (in accordance with OSHA HCS 29 CFR 1910.1200) For the full text of the Hazard and Precautionary Statements listed below, see Section 16. Hazard Hazard Class Category Statement Precautionary Statements Respiratory Sensitizer Category 1 H334 P261, P285, P304+P341, P342+P311, P501 Skin Sensitizer Category 1 H317 P261, P272, P280, P302+P352, P332+P313, P321, P363, P501 Carcinogenicity Category 1 H350 P201, P202, P280, P308+P313, P405, P501 Reproductive Toxicity Category 2 H361 P201, P202, P280, P308+P313, P405, P501 Specific Target Organs/Systemic Toxicity Following Repeated Category 1 H372 P260, P264, P270, P314, P501 Exposure Product Number: 8825 Page 1 of 11 Safety Data Sheet 2.2. GHS Label Elements Pictograms: Signal Word: Danger Hazard Statements: Hazard Number Hazard Statement H317 May cause an allergic skin reaction. H334 May cause allergy or asthma symptoms or breathing difficulties if inhaled. H350 May cause cancer. H361 Suspected of damaging fertility or the unborn child. H372 Causes damage to organs through prolonged or repeated exposure.
    [Show full text]
  • New York City Department of Environmental Protection Community Right-To-Know: List of Hazardous Substances
    New York City Department of Environmental Protection Community Right-to-Know: List of Hazardous Substances Updated: 12/2015 Definitions SARA = The federal Superfund Amendments and Reauthorization Act (enacted in 1986). Title III of SARA, known as the Emergency Planning and Community Right-to-Act, sets requirements for hazardous chemicals, improves the public’s access to information on chemical hazards in their community, and establishes reporting responsibilities for facilities that store, use, and/or release hazardous chemicals. RQ = Reportable Quantity. An amount entered in this column indicates the substance may be reportable under §304 of SARA Title III. Amount is in pounds, a "K" represents 1,000 pounds. An asterisk following the Reporting Quantity (i.e. 5000*) will indicate that reporting of releases is not required if the diameter of the pieces of the solid metal released is equal to or exceeds 100 micrometers (0.004 inches). TPQ = Threshold Planning Quantity. An amount entered in this column reads in pounds and indicates the substance is an Extremely Hazardous Substance (EHS), and may require reporting under sections 302, 304 & 312 of SARA Title III. A TPQ with a slash (/) indicates a "split" TPQ. The number to the left of the slash is the substance's TPQ only if the substance is present in the form of a fine powder (particle size less than 100 microns), molten or in solution, or reacts with water (NFPA rating = 2, 3 or 4). The TPQ is 10,000 lb if the substance is present in other forms. A star (*) in the 313 column= The substance is reportable under §313 of SARA Title III.
    [Show full text]
  • THE CERIOMETRIC DETERMINATION of HYDRAZINE and ALUMINUM Oy CLIFFORD JAMES DERNBACH
    THE CERIOMETRIC DETERMINATION OF HYDRAZINE AND ALUMINUM oy CLIFFORD JAMES DERNBACH A THESIS submitted to the OREGON STATE COLLEGE in partial fulfillment of the requirements for the degree of DOCTOR OF PHILOSOPHY A3?ROTED: Redacted for Privacy Profegsor of Chentetry Redacted for Privacy Eeail of De nt of Chenlstry Redacted for Privacy Chatrman of Sohool, 0r Corurlttee Redacted for Privacy Chalrnan of State College Oraduate Conaoll ACKNOLEDGEMENTS The writer wishes to express his utmost thanks to Dr . J. P. Mehl ig for his constructive suggestions throughout this work . Thanks are also given to Dr . E. c. Gilbert for informing the writer of the existence of a published article which had a bearing on part of this work. TABLE OF CONTENTS Page I. THE DETERMINATION OF HYDRAZINE 1 PREPARATION OF SOLUTIONS 3 PROCEDURE 3 EFFECT OF AiiKAI·INITY 6 EFFECT OF EXCESS POTASSIUM FERRICYANIDE 6 EFFECT OF T!ME 7 EFFECT OF FINAL ACIDITY 8 RECOMMENDED PROCEDURE 8 RESULTS 9 DISCUSSION 11 S~Y 11 A NOTE ON THE DETERMINATION OF PHENYLHYDRAZINE 12 BIBLIOGRAPHY 13 LIST OF TABLES TABLE I. 5 TABLE II. 6 TABLE III. 7 TABLE IV. 10 TABLE V. 10 ii Page II. THE DET:ERMINATION OF ALUMINUM 14 PREPARATION OF SOLUTIONS 15 PROCEDURE WITH CERIC SULFATE 16 PROCEDURE 19 DETERMINATION OF UNKNOWNS 23 DISCUSSION 26 SUMMARY 28 BIBLIOGRAPHY 30 LIST OF TABLES TABLE I. 18 TABLE II. 19 TABLE III. 22 TABLE IV. 23 TABLE V. 24 TABLE VI. 25 TABLE VII. 26 1 flm CERIOMETRIC DETERMINATION OF HYDRAZINE AND ALUMINUM I THE DETERMINATION OF HYDRAZINE The use of eerie sulfate as a standard oxidant in titrimetry has become more and more widespread in the last few years, due, in part, to the, availability of an increas­ ing number of good reversible redox indicators (8).
    [Show full text]