Table Ac-1 Permissible Exposure Limits for Chemical Contaminants
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Chemistry (55)
156 Chemistry (55) Introduction 3) To expose the students to various emerging According to NCF 2005, the new and new areas of chemistry and apprise them updated curriculum is introduced at +2 stage. with their relevance in their future studies There is a need to provide the sufficient and their applications in various spheres conceptual background of chemistry which will of chemical sciences and technology. help the students to appear for different common 4) To equip students to face various changes entrance test at the state level and the national related to health, nutrition, environment, level. This new syllabus will make them population, weather, industries and competent to meet the challenges of academic agriculture. and professional courses like medicine, 5) To develop problem solving skills in engineering, technology, etc, after the +2 stage. students. The syllabus is comparable to the international 6) To expose the students to different level. processes used in industries and their The syllabus contains areas like physical, technological applications. organic, inorganic, industrial, analytical and 7) To apprise students with interface of polymer chemistry. The upgraded syllabus has chemistry with other disciplines of science taken care of new formulations and such as physics, biology, geology, nomenclature of elements, compounds and engineering, etc. IUPAC units of physical quantities. New nomenclature, symbols and formulations, Std. XI (Theory) fundamental concepts, modern techniques are given importance. Unit 1: Some Basic Concepts of Chemistry Objectives : General Introduction: Importance and The broad objectives of teaching scope of chemistry. Historical approach to Chemistry at Higher Secondary stage are to particulate nature of matter, laws of help the learners : chemical combination, Dalton’s atomic 1) To promote understanding of basic facts theory : concept of elements, atoms and and concepts in chemistry while retaining molecules. -
Effect of Diethylenetriamine and Triethylamine Sensitization on the Critical Diameter of Nitromethane’
CP505, Shock Compression of Condensed Matter - 1999 edited by M. D. Furnish, L. C. Chhabildas, and R. S. Hixson 0 2000 American Institute of Physics l-56396-923-8/00/$17.00 EFFECT OF DIETHYLENETRIAMINE AND TRIETHYLAMINE SENSITIZATION ON THE CRITICAL DIAMETER OF NITROMETHANE’ J.J. Lee*, J. Jiang?, K.H. Choong’, J.H.S. Lee’ *Graduate Aeronautics Laboratory, California Institute of Technology, Pasadena, CA 9112.5, USA ‘Dept. of Mechanical Engineering, McGill University, Montr&al, Que’bec, Canada, H3A 2K6 In this work, the critical diameter for detonation was measured for Nitromethane (NM) sensitized with two different amines: Diethylenetriamine (DETA) and Triethylamine (TEA). The critical diameter in glass and polyvinylchloride tubes is found to decrease rapidly as the amount of sensitizer is increased, then increase past a critical amount of sensitizer. Thus the critical diameter reaches a minimum at a critical concentration of sensitizer. It was also found that the critical diameter is lower with DETA than with TEA. INTRODUCTION propagation in various tubes and channels, and the critical conditions for propagation in porous media Previous studies have shown that small (3) . concentrations of certain substances can strongly The effect of DETA on the critical diameter of increase the explosive sensitivity nitromethane NM has been reported by Engelke (4), who (NM). Amines are found to be the most effective performed measurements with up to 2.5% DETA by chemical sensitizing agent for NM with mass in NM. Engelke observed a reduction in the ethylenediamine and diethylenetriamine (DETA) critical diameter of over 50% in the range of DETA producing the largest increase in the card gap value concentrations used. -
Alcohols Combined 1405
ALCOHOLS COMBINED 1405 Formulas: Table 1 MW: Table 1 CAS: Table 2 RTECS: Table 2 METHOD: 1405, Issue 1 EVALUATION: PARTIAL Issue 1: 15 March 2003 OSHA : Table 2 PROPERTIES: Table 1 NIOSH: Table 2 ACGIH: Table 2 COMPOUNDS: (1) n-butyl alcohol (4) n-propyl alcohol (7) cyclohexanol (2) sec-butyl alcohol (5) allyl alcohol (8) isoamyl alcohol (3) isobutyl alcohol (6) diacetone alcohol (9) methyl isobutyl carbinol SYNONYMS: See Table 3. SAMPLING MEASUREMENT SAMPLER: SOLID SORBENT TUBE TECHNIQUE: GAS CHROMATOGRAPHY, FID (Coconut shell charcoal, 100 mg/50 mg) ANALYTE: Compounds above FLOW RATE: 0.01 to 0.2 L/min DESORPTION: 1 mL 5% 2-propanol in CS2 Compounds: (1-3 ) (4-9) VOL-MIN: 2 L 1 L INJECTION -MAX: 10 L 10 L VOLUME: 1 µL SHIPMENT: Routine TEMPERATURE -INJECTION: 220 °C SAMPLE -DETECTOR: 250 - 300 °C STABILITY: See Evaluation of Method. -COLUMN: 35 °C (7 minutes), to 60 °C at 5 °C/minute, hold 5 minutes, up to BLANKS: 2 to 10 field blanks per set 120 °C at 10 °C /minute, hold 3 minutes. CARRIER GAS: He, 4 mL/min ACCURACY COLUMN: Capillary, fused silica, 30 m x 0.32-mm RANGE STUDIED: Not studied [1, 2]. ID; 0.5 µm film polyethylene glycol, DB- wax or equivalent BIAS: Not determined CALIBRATION: Solutions of analyte in eluent (internal OVERALL standard optional) PRECISION (Ö ): Not determined rT RANGE: See EVALUATION OF METHOD. ACCURACY: Not determined ESTIMATED LOD: 1 µg each analyte per sample PRECISION: See EVALUATION OF METHOD. APPLICABILITY: This method may be used to determine two or more of the specified analytes simultaneously. -
Air Contaminants – Permissible Exposure Limits (Pels)
SUBPART Z -- TOXIC AND HAZARDOUS SUBSTANCES 1910.1000-AIR CONTAMINANTS An employee’s exposure to any substance listed in Table Z-1-A of this section shall be limited in accordance with the requirements of the following paragraphs of this section. (a) Table Z-1-A. Limits for Air Contaminants (1) & (2) Enforcement of Transitional Limits has expired. See Paragraph (3) for Limits. (3) Limits for Air Contaminants Columns. An employee’s exposure to any substance listed in Table Z-1-A shall not exceed the Time Weighted Average (TWA), Short Term Exposure Limit (STEL) and Ceiling Limit specified for that substance in Table Z-1-A. (4) Skin Designation. To prevent or reduce skin absorption, an employee’s skin exposure to substances listed in Table Z-1-A with an “X” in the Skin Designation column following the substance name shall be prevented or reduced to the extent necessary in the circumstances through the use of gloves, coveralls, goggles, or other appropriate personal protective equipment, engineering controls or work practices. (5) Definitions. The following definitions are applicable to the Limits for Air Contaminants columns of Table Z- 1-A: (i) Time weighted average (TWA) is the employee’s average airborne exposure in any 8-hour work shift of a 40-hour work week which shall not be exceeded. (ii) Short term exposure limit (STEL) is the employee’s 15-minute time weighted average exposure which shall not be exceeded at any time during a work day unless another time limit is specified in a parenthetical notation below the limit. -
EPA Handbook: Optical and Remote Sensing for Measurement and Monitoring of Emissions Flux of Gases and Particulate Matter
EPA Handbook: Optical and Remote Sensing for Measurement and Monitoring of Emissions Flux of Gases and Particulate Matter EPA 454/B-18-008 August 2018 EPA Handbook: Optical and Remote Sensing for Measurement and Monitoring of Emissions Flux of Gases and Particulate Matter U.S. Environmental Protection Agency Office of Air Quality Planning and Standards Air Quality Assessment Division Research Triangle Park, NC EPA Handbook: Optical and Remote Sensing for Measurement and Monitoring of Emissions Flux of Gases and Particulate Matter 9/1/2018 Informational Document This informational document describes the emerging technologies that can measure and/or identify pollutants using state of the science techniques Forward Optical Remote Sensing (ORS) technologies have been available since the late 1980s. In the early days of this technology, there were many who saw the potential of these new instruments for environmental measurements and how this technology could be integrated into emissions and ambient air monitoring for the measurement of flux. However, the monitoring community did not embrace ORS as quickly as anticipated. Several factors contributing to delayed ORS use were: • Cost: The cost of these instruments made it prohibitive to purchase, operate and maintain. • Utility: Since these instruments were perceived as “black boxes.” Many instrument specialists were wary of how they worked and how the instruments generated the values. • Ease of use: Many of the early instruments required a well-trained spectroscopist who would have to spend a large amount of time to setup, operate, collect, validate and verify the data. • Data Utilization: Results from path integrated units were different from point source data which presented challenges for data use and interpretation. -
Growth Regulation and Other Secondary Effects of Herbicides Edivaldo D
Weed Science 2010 58:351–354 Growth Regulation and Other Secondary Effects of Herbicides Edivaldo D. Velini, Maria L. B. Trindade, Luis Rodrigo M. Barberis, and Stephen O. Duke* As all herbicides act on pathways or processes crucial to plants, in an inhibitory or stimulatory way, low doses of any herbicide might be used to beneficially modulate plant growth, development, or composition. Glyphosate, the most used herbicide in the world, is widely applied at low rates to ripen sugarcane. Low rates of glyphosate also can stimulate plant growth (this effect is called hormesis). When applied at recommended rates for weed control, glyphosate can inhibit rust diseases in glyphosate-resistant wheat and soybean. Fluridone blocks carotenoid biosynthesis by inhibition of phytoene desaturase and is effective in reducing the production of abscisic acid in drought-stressed plants. Among the acetolactate synthase inhibitors, sulfometuron-methyl is widely used to ripen sugarcane and imidazolinones can be used to suppress turf species growth. The application of protoporphyrinogen oxidase inhibitors can trigger plant defenses against pathogens. Glufosinate, a glutamine synthetase inhibitor, is also known to improve the control of plant diseases. Auxin agonists (i.e., dicamba and 2,4-D) are effective, low-cost plant growth regulators. Currently, auxin agonists are still used in tissue cultures to induce somatic embryogenesis and to control fruit ripening, to reduce drop of fruits, to enlarge fruit size, or to extend the harvest period in citrus orchards. At low doses, triazine herbicides stimulate growth through beneficial effects on nitrogen metabolism and through auxin-like effects. Thus, sublethal doses of several herbicides have applications other than weed control. -
Website F Prolonged Or Repeated Exposure Can Cause Drying and ( Or in Your Facility’S RTK Cracking of the Skin
Right to Know Hazardous Substance Fact Sheet Common Name: ISOAMYL ALCOHOL Synonyms: Isopentyl Alcohol; Isobutylcarbinol CAS Number: 123-51-3 Chemical Name: 1-Butanol, 3-Methyl- RTK Substance Number: 1039 Date: April 1999 Revision: March 2008 DOT Number: UN 1105 Description and Use EMERGENCY RESPONDERS >>>> SEE BACK PAGE Isoamyl Alcohol is a colorless liquid with a strong Alcohol-like Hazard Summary odor. It is used in photographic chemicals and pharmaceutical Hazard Rating NJDOH NFPA products, as a solvent, as a flavor in food, and in the HEALTH - 1 manufacture of other chemicals. FLAMMABILITY - 2 REACTIVITY - 0 f ODOR THRESHOLD = 0.042 ppm COMBUSTIBLE f Odor thresholds vary greatly. Do not rely on odor alone to POISONOUS GASES ARE PRODUCED IN FIRE determine potentially hazardous exposures. CONTAINERS MAY EXPLODE IN FIRE Hazard Rating Key: 0=minimal; 1=slight; 2=moderate; 3=serious; Reasons for Citation 4=severe f Isoamyl Alcohol is on the Right to Know Hazardous Substance List because it is cited by OSHA, ACGIH, DOT, f Isoamyl Alcohol can affect you when inhaled and by NIOSH and NFPA. passing through the skin. f Contact can severely irritate and burn the skin and eyes with possible eye damage. f Inhaling Isoamyl Alcohol can irritate the nose, throat and lungs. f Isoamyl Alcohol can cause nausea, vomiting and diarrhea. f Exposure can cause headache, dizziness, lightheadedness, and passing out. f Prolonged or repeated exposure can cause drying and SEE GLOSSARY ON PAGE 5. cracking of the skin. f Isoamyl Alcohol may affect the liver and kidneys. FIRST AID Eye Contact f Immediately flush with large amounts of water for at least 15 Workplace Exposure Limits minutes, lifting upper and lower lids. -
Rhode Island Hazardous Substance List
Rhode Island Hazardous Substance List Source: T - ACGIH F - NFPA49 C - IARC Alphabetical Order C.A.S. ACGIH NFPA IARC CHEMICAL NAME 13010-47-4 C 1,-(2-Chloroethyl)-3-cyclohexyl-1-Nitrosourea 76-11-9 T 1,1,1,2-tetrachloro-2,2-difluoroethane 76-12-0 T 1,1,2,2-tetrachloro-1,2-difluoroethane 79-34-5 T 1,1,2,2-tetrachloroethane - skin 76-13-1 T 1,1,2-trichloro-1,2,2-trifluoroethane 79-00-5 T F C 1,1,2-trichloroethane - skin 594-72-9 T 1,1-Dichloro-1-nitroethane 74-34-3 T 1,1-dichloroethane 57-14-7 T 1,1-dimethylhydrazine (udmh) 96-18-4 T 1,2,3-trichloropropane 120-82-1 T 1,2,4-Trichlorobenzene 106-88-7 F 1,2-Butylene oxide 107-15-3 T F 1,2-Diaminoethane 96-12-8 C 1,2-Dibromo-3-chloropropane 106-93-4 T F C 1,2-Dibromoethane - skin 107-06-2 T F 1,2-Dichlorethane 540-59-0 T F 1,2-Dichloroethene 540-59-0 T F 1,2-Dichloroetylene 1615-80-1 C 1,2-Diethylhydrazine C 1,2-Dimethyl hydrazine - skin 106-99-0 T F 1,3-Butadiene 118-52-5 T 1,3-Dichloro-5,5-dimethylhydantoin 542-75-6 T F 1,3-Dichloropropene (cis and trans) 542-75-6 T F 1,3-Dichloropropylene 110-56-5 F 1,4-Dichlorobutane 123-91-1 T F C 1,4-Dioxane 1120-71-4 1-3-Propane sultone 110-53-2 F 1-Bromopentane 106-89-8 T F C 1-Chloro,2,3-epoxy-propane 600-25-9 T 1-Chloro-1-nitropropane 97-00-7 F 1-chloro-2,4-dinitrobenzene 543-59-9 F 1-Chloropentane 112-30-1 F 1-Decanol 111-27-3 F 1-Hexanol 141-79-7 T F 1-Isobutenyl methyl ketone 108-03-2 T F 1-Nitropropane 71-41-0 F 1-Pentanol 110-58-7 F 1-Pentylamine 111-40-0 T F 2,2'-Diaminodiethylamine 111-44-4 F 2,2'Dichlorodiethyl ether 75-99-0 T 2,2-dichloropropionic acid 556-52-5 T 2,3-Epoxy-1-propanol 93-76-5 T 2,4,5-T 95-95-4 F 2,4,5-trichlorophenol 88-06-2 F C 2,4,6-trichlorophenol 118-96-7 T F 2,4,6-Trinitro Toluene 479-95-8 T 2,4,6-Trinitrophenyl-methylnitramine 94-75-7 T 2,4-d (2,4-dichlorophenoxyacetic acid) 97-02-9 F 2,4-dinitroaniline 584-84-9 T F 2,4-Tolylene diisocyanate 108-83-8 T 2,6-Dimethyl-4-heptanone 108-83-8 T 2,6-Dimethyl-4-heptanone 128-37-0 T 2,6-Ditert. -
The Calcium Arsenates
Station RuIletin 131. June, 1918 Oregon Agricultural College Experiment Station AGRICULTURAL CHEMISTRY DEPARTMENT The Calcium Arsenates By R. H. ROBINSON Acting Chemist, Oregon Agricultural Experiment Station. CORVALLIS, OREGON The regular huIlejne of the Station are sent free to the residents of Oregon who request them. THE CALCIUM ARSENATES By R. H. ROBINSON Acting Chemist, Oregon Agricultural Experiment Station INTRODUCTION Chemical investigations on the calcium arsenates relative to their economfic value and practicability as insecticides have been carried on by the department of Agricultural Chemistry of this Station during the past two years.The results obtained from these investigations are presented in this bulletin.The work was supported by the annual funds provided by the Adams Act of the United States Government.. Commercial calcium arsenate is an arsenical now being produced by reliable manufacturers of spray material and offered for sale as a sub- stitute for the arsenates of lead.The value of the latter as a stomachic insecticide has been demonstrated, and itis now used extensively for the successful controlof the codling moth, the destructionof the cotton boll worm., the tobacco worm, and the Colorado potato beetle. Previous inveatigations on the toxic values and killing power of calcium arsenate and lead arsenate indicate equal efficiency. A consideration of a few figures will show the economic advantages which might be gained if calcium arsenate could be substituted for lead arsenate.A conservative estimate of the quantity of lead arsenate used annually in the United States, as stated by one of the largest manufac- turers of spray materials, is probably more than 30,000,000 pounds. -
Preparation and Purification of Atmospherically Relevant Α
Atmos. Chem. Phys., 20, 4241–4254, 2020 https://doi.org/10.5194/acp-20-4241-2020 © Author(s) 2020. This work is distributed under the Creative Commons Attribution 4.0 License. Technical note: Preparation and purification of atmospherically relevant α-hydroxynitrate esters of monoterpenes Elena Ali McKnight, Nicole P. Kretekos, Demi Owusu, and Rebecca Lyn LaLonde Chemistry Department, Reed College, Portland, OR 97202, USA Correspondence: Rebecca Lyn LaLonde ([email protected]) Received: 31 July 2019 – Discussion started: 6 August 2019 Revised: 8 December 2019 – Accepted: 20 January 2020 – Published: 9 April 2020 Abstract. Organic nitrate esters are key products of terpene oxidation in the atmosphere. We report here the preparation and purification of nine nitrate esters derived from (C)-3- carene, limonene, α-pinene, β-pinene and perillic alcohol. The availability of these compounds will enable detailed investigations into the structure–reactivity relationships of aerosol formation and processing and will allow individual investigations into aqueous-phase reactions of organic nitrate esters. Figure 1. Two hydroxynitrate esters with available spectral data. Relative stereochemistry is undefined. 1 Introduction derived ON is difficult, particularly due to partitioning into the aerosol phase in which hydrolysis and other reactivity Biogenic volatile organic compound (BVOC) emissions ac- can occur (Bleier and Elrod, 2013; Rindelaub et al., 2014, count for ∼ 88 % of non-methane VOC emissions. Of the to- 2015; Romonosky et al., 2015; Thomas et al., 2016). Hydrol- tal BVOC estimated by the Model of Emission of Gases and ysis reactions of nitrate esters of isoprene have been stud- Aerosols from Nature version 2.1 (MEGAN2.1), isoprene is ied directly (Jacobs et al., 2014) and the hydrolysis of ON estimated to comprise half, and methanol, ethanol, acetalde- has been studied in bulk (Baker and Easty, 1950). -
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Test for Acetone in Urine 189 AN IMPROVED TEST FOR ACETONE IN URINE. R. E. Lyons and J. T. Brundage, Indiana University. Lieben's test for acetone 1 depends upon the formation of iodoform when potassium iodide, iodine solution, and a few drops of sodium hydroxide solution are added to an acetone containing mixture. The iodoform is recognized by its distinctive odor and, microscopically, by the 1 star, or hexagonal crystals. The test is not specific since both ethyl alcohol and acetic aldehyde also react with these reagents to yield iodo- form. This sometimes leads to erroneous results because of alcohol formed through sugar fermentation in diabetic urine. The difficulty is obviated" by substituting ammonium hydroxide for the caustic alkali as proposed by Gunning'5 in a modification of the Lieben Test. In either test the reaction is much more sensitive if a urine dis- tillate is used. The distillation not only frees the acetone from non- volatile interfering substances, but converts some acetonacetic (di-acetic) 4 acid, if present, into acetone. Protein interferes and, if present, the separation of acetone by distillation or aeration is necessary. M. KohlthofF' states that 100 mg. each of potassium iodide and chlor- amine T, 10-20 drops of 4N ammonium hydroxide and 10 cc. of a solu- tion of one part acetone in 10,000 parts of 2 per cent ethyl alcohol when warmed to 60 °C. gave an iodoform precipitate in two hours. The object of our investigation has been to determine (a) whether this reaction could be applied as a specific test for acetone in urine, (b) what urinary constituents or preservatives interfere, (c) if the necessity of distillation, or aeration, of the urine could be dispensed with, and (d) the conditions for attaining the maximum sensitiveness of the reaction. -
South Umpqua Pilot Study 2014-19 Findings and Recommendations | Oregon Water Quality Management Team
South Umpqua Pilot Study 2014-19 Findings and Recommendations | Oregon Water Quality Management Team Background waters resulting from various types of land uses. The monitoring locations were chosen to represent the A pesticide water quality pilot study of the South predominant land use types existing within the various Umpqua subbasin (USGS 8-digit HUC 17100302)1 was watersheds as noted in the United States Geological initiated in the fall of 2014. The South Umpqua was Survey’s (USGS) 2016 National Land Cover Dataset. selected by the Water Quality Pesticide Management Initially, five monitoring locations were chosen. At Team (WQPMT) as one of four potential pilot projects the end of the spring 2015 sampling season two sites after the Pesticide Stewardship Partnership Program (Cow Creek at Mouth and Myrtle Creek at Mouth) received its first funding allocation from the Oregon were discontinued due to both the limited number of Legislature in 2013. The watersheds were selected pesticides detected and the low concentrations of those because of the multiple types of land uses in areas detections during the 2015 sampling period. In 2017 that use pesticides, the presence of municipal drinking two additional sites were added (Lookingglass Creek at water intakes, as well as existing water quality data the Happy Valley Bridge and the North of Myrtle Creek collected by DEQ and other entities. Within the South downstream of the Bilger Creek confluence) at the Umpqua subbasin, prospective local partners were suggestion of local partners (Table 1). contacted and expressed interest in participating in the pilot effort. Initial reconnaissance monitoring sites Based on the initial sampling results, the WQPMT were selected by a group comprised of state agencies approached the local stakeholder group about on the WQPMT, Partners for Umpqua Rivers (PUR), conducting a second phase of pilot monitoring in the Douglas Soil and Water Conservation District, Oregon South Umpqua 2017 which extended through the State University Extension, and the Cow Creek Band of spring of 2019.