METHOD: 2532, Issue 1 EVALUATION: PARTIAL Issue 1: 15 August PRECISION ( r

Similar documents
METHOD: 1403, Issue 3 EVALUATION: FULL Issue 1: 15 August 1990 Issue 3: 15 March 2003

FORMALDEHYDE by GC 2541

HYDROCARBONS, AROMATIC 1501

HYDROGEN CYANIDE 6017

METHYL ETHYL KETONE PEROXIDE 3508

METHYLTIN CHLORIDES 5526

ALDEHYDES, SCREENING 2539

ORGANOPHOSPHORUS PESTICIDES 5600

TABLE 2 MW: TABLE 1 CAS: TABLE 2 RTECS: TABLE 2. METHOD: 1450, Issue 2 EVALUATION: PARTIAL Issue 1: 15 February 1984 Issue 2: 15 August 1994

ANALYTICAL METHOD DETERMINATION OF VOLATILE ALDEHYDES IN AMBIENT AIR Page 1 of 11 Air sampling and analysis

METHOD: 3601, Issue 1 EVALUATION: PARTIAL Issue 1: 15 March NAMES & SYNONYMS: manganous ethylenebis(dithiocarbamic acid), Manzate; Dithane M-22

Sep-Pak XPoSure Aldehyde Sampler

VINYL CHLORIDE. Recommended by NIOSH, partially evaluated by OSHA Laboratory.

Determination of Carbonyl Compounds In Water by Dinitrophenylhydrazine Derivatization and HPLC/UV*

METHOTREXATE mg/m 3 (arbitrary). There is no OSHA PEL or AGGIH TLV for

Technical Procedure for Concentration Determination of Methamphetamine in Liquids via HPLC

ACETIC AND FORMIC ACIDS IN WORKPLACE ATMOSPHERES ppm for Acetic Acid, CH 3 COOH

CHROMIUM, HEXAVALENT 7605 by Ion Chromatography

ANALYTICAL METHOD PROCEDURES

The analysis of organic acid content of additives, premix, feed, and water.

C = concentration as ppm sulfide V t = volume of titrant at endpoint V s = volume of standard used (10 ml)

637. Thiamethoxam. HPLC method

METHOD 3510B SEPARATORY FUNNEL LIQUID-LIQUID EXTRACTION

Industrial Hygiene Report

Draft Method proposal: determination of glucoheptonic acid (HGA) in fertilizers.

CORESTA Recommended Method No. 86

GB/T Translated English of Chinese Standard: GB/T

METHOD 3520C CONTINUOUS LIQUID-LIQUID EXTRACTION

METHOD 13B - DETERMINATION OF TOTAL FLUORIDE EMISSIONS FROM STATIONARY SOURCES (SPECIFIC ION ELECTRODE METHOD)

Validation of. Tetrahydrofuran Using. SKC Passive Sampler Cat. No

METHOD 8030A ACROLEIN AND ACRYLONITRILE BY GAS CHROMATOGRAPHY

METHOD 3520B CONTINUOUS LIQUID-LIQUID EXTRACTION

Functional Genomics Research Stream. Lecture: February 17, 2009 Masses, Volumes, Solutions & Dilutions

Annex 2 Formaldehyde

IDENTIFICATION OF STEROIDS IN COSMETIC PRODUCTS BY TLC AND HPLC 1 02/12/2005 ACM 007 A. THIN LAYER CHROMATOGRAPHY (TLC)

CIPAC. CIPAC Free relevant impurities methods:

A biphasic oxidation of alcohols to aldehydes and ketones using a simplified packed-bed microreactor

METHOD 8033 ACETONITRILE BY GAS CHROMATOGRAPHY WITH NITROGEN-PHOSPHORUS DETECTION

STANDARD OPERATING PROCEDURES SOP: 1828 PAGE: 1 of 14 REV: 0.0 DATE: 05/12/95 ANALYSIS OF METHYL PARATHION IN CARPET SAMPLES BY GC/MS

CHAPTER V ANALYTICAL METHODS ESTIMATION OF DICLOFENAC. Diclofenac (gift sample from M/s Micro Labs Ltd., Pondicherry)

This method describes the identification of the following prohibited colorants in cosmetic products:

METHOD 9035 SULFATE (COLORIMETRIC, AUTOMATED, CHLORANILATE)

PA-DEP 3686, Rev. 1. Light Hydrocarbons in Aqueous Samples via Headspace and Gas Chromatography with Flame Ionization Detection (GC/FID)

COLE-PARMER LABORATORY CALCIUM ION ELECTRODE INSTRUCTION MANUAL

Sulfotepp impurities in Chlorpyrifos EC formulations

IDENTIFICATION AND DETERMINATION OF HYDROQUINONE IN COSMETIC PRODUCTS 2 14/11/17 ACM 003 BY TLC AND HPLC

EPA IP-6 METHOD UPDATE. Year DETERMINATION OF FORMALDEHYDE AND OTHER ALDEHYDES IN INDOOR AIR

VOLATILE ACIDS by Ion Chromatography (Hydrogen Chloride, Hydrogen Bromide, Nitric Acid)

Determination of Trace Cations in Power Plant Waters Containing Morpholine

Tex-620-J, Determining Chloride and Sulfate Contents in Soil

TECHNETIUM-99 IN WATER

Use a pipet bulb when pipeting cyanide solutions, as these solutions are highly toxic.

Method for estimation of iodine in urine

H 3 CO H 3 CO S CH 3

Determination of trace anions in concentrated hydrofluoric acid

VALIDATION OF A UPLC METHOD FOR A BENZOCAINE, BUTAMBEN, AND TETRACAINE HYDROCHLORIDE TOPICAL SOLUTION

Determination of Polymer Modifier in Asphalt

The Oakton Cadmium Ion Electrodes are used to quickly, simply, accurately, and economically measure cadmium ions in aqueous solutions.

Introduction to IH Analytical Chemistry

METHYLISOBUTYLKETONE (4-methyl-2 pentanone) IN URINE BY GC/MS Headspace Code GC10510

COLE-PARMER LABORATORY AMMONIUM ION ELECTRODE INSTRUCTION MANUAL

Quality Assurance is what we do to get the right answer for our purpose FITNESS FOR PURPOSE

METHOD 8032A ACRYLAMIDE BY GAS CHROMATOGRAPHY

INTERNATIONAL CHEMISTRY TESTING. 258 Main Street- Suite 311- Milford, MA Tel: Fax:

Diquat 1,1 -ethylene-2,2 -bipyridium dibromide salt Paraquat 1,1 -dimethyl-4,4 -bipyridium dichloride salt Initial Preparation

Chemistry 3200 High Performance Liquid Chromatography: Quantitative Determination of Headache Tablets

METHOD 3665 SULFURIC ACID/PERMANGANATE CLEANUP

12 Nicarbazin Nicarbazin (4,4 -dinitro carbanilid (DNC) and 2-hydroxy-4,6-dimethyl pyrimidine (HDP))

2017 Reaction of cinnamic acid chloride with ammonia to cinnamic acid amide

1) A ph/mv meter or an ion meter, either line operated or portable.

Method Formaldehyde, Isobutyraldehyde, and Furfural by Derivatization Followed by High Performance Liquid Chromatography

Automated Sample Preparation of Headspace Standards Using the Agilent 7696 WorkBench

Method for the determination of 1,3-butadiene

STANDARD OPERATING PROCEDURES SOP: 1826 PAGE: 1 of 18 REV: 0.0 DATE: 03/30/95 ANALYSIS OF METHYL PARATHION IN WIPE SAMPLES BY GC/MS

Anion and Cation analysis with Professional IC - automatic dilution and sample preparation with SPM

Method for the determination of dimethyl sulfate

The Cole-Parmer Ammonium Ion Electrode is used to quickly, simply, accurately, and economically measure ammonium ions in aqueous solutions.

1. A gas chromatograph equipped with flame ionization detection and a computing integrator.

NICKEL-63/59 IN WATER

METHOD 5000 SAMPLE PREPARATION FOR VOLATILE ORGANIC COMPOUNDS

Media blank result for a single-section sampler (e.g., membrane filter). Media blank result for back section of a sampler.

TKI CU01 V-1.0_EN Cu separation from irradiated targets 01/12/10

Rapid Screening and Confirmation of Melamine Residues in Milk and Its Products by Liquid Chromatography Tandem Mass Spectrometry

Impact factor: 3.958/ICV: 4.10 ISSN:

Chemistry Determination of Mixed Acids

POLYDEXTROSES. SYNONYMS Modified polydextroses; INS No DEFINITION DESCRIPTION. FUNCTIONAL USES Bulking agent, humectant, stabilizer, thickener

NCASI METHOD CI/SG/PULP-94.02

Tetraphenylborate Method Method to 7.0 mg/l K Powder Pillows

COLE-PARMER LABORATORY CUPRIC ION ELECTRODE INSTRUCTION MANUAL

Dilutions 4/8/2013. Steps involved in preparing solutions from pure solids. Steps involved in preparing solutions from pure solids

METHOD 9012 TOTAL AND AMENABLE CYANIDE (COLORIMETRIC, AUTOMATED UV)

Anethole. Gas chromatograhpy determination of trans-anethole in Spirit srinks of viti-vinicultural origin

To see how this data can be used, follow the titration of hydrofluoric acid against sodium hydroxide:

(CATION EXCHANGE AND LN RESIN, WITH VACUUM BOX SYSTEM)

Z/zs. tnitiats: wu\ Z-z* I A. sop-c-102. Determination of Chemical Oxygen Demand. Revision 6. Approval: Effective date: 3. Renewat date: 7lt:,:

1,2-Dibromoethane (EDB) and 1,2-dibromo-3-chloropropane (DBCP), gas chromatography, microextraction

Corn Sugar (crude & refined) Analysis F MOISTURE (Karl Fischer)

Waters. Ion Chromatography

DRAFT EAST AFRICAN STANDARD

Citric Acid Analysis L-6-1. MOISTURE (Karl Fischer)

Transcription:

GLUTARALDEHYDE 2532 O=CH(CH 2 ) 3 CH=O MW: 100.12 CAS:111-30-8 RTECS: MA2450000 METHOD: 2532, Issue 1 EVALUATION: PARTIAL Issue 1: 15 August 1994 OSHA : NIOSH: ACGIH: no PEL C 0.2 ppm C 0.2 ppm (1ppm = 4.09 mg/m 3 @ NTP) PROPERTIES: oil; d 0.72 g/ml @ 20 C; BP 188 C; MP -14 C; VP 2.2 kpa (17 mm Hg) @ 20 C SYNONYMS: glutaric dialdhyde; 1,5-pentanedial; glutaral; 1,3-diformylpropane SAMPLING MEASUREMENT SAMPLER: SOLID SORBENT TUBE (silica gel coated with 2,4- dinitrophenylhydrazine HCL, 300 mg/150 mg) TECHNIQUE: ANALYTE: HPLC, UV DETENTION glutaraldehyde dinitrophenylhydrazone FLOW RATE: 0.05 to 0.5 L/min EXTRACTION: 3 ml acetonitrle; shaken 2 h VOL-MIN: -MAX: 1 L @ 0.2 ppm 30 L INJECTION VOLUME: 25 L SHIPMENT: routine MOBILE PHASE: 65% acetonitrile/35% water SAMPLE STABILITY: at least 30 days @ 25 C BLANKS: 2 to 10 field blanks per set; 10 to 20 media blanks per set ACCURACY FLOWRATE: COLUMN: DETECTOR: 1.5 ml/min reverse phase C8, 5- m particle size (Alltech Altima C8, 5- m or equivalent) UV at 365 nm RANGE STUDIED: ACCURACY: BIAS: OVERALL PRECISION ( rt ): none CALIBRATION: RANGE: standard solutions spiked onto sampler tubes 0.8 to 24 g per sample ESTIMATED LOD: 0.3 g per sample PRECISION ( r ): 0.007 @ 12 g per sample; 0.025 @ 1.2 g per sample APPLICABILITY: The working range is 0.01 to 0.3 ppm (0.04 to 1.2 mg/m 3 ) for a 20-L air sample. INTERFERENCES: Other aldehydes and ketones react with 2,4-dinitrophenylhydrazine but can be resolved using proper HPLC parameters. OTHER METHODS: OSHA Method 64 [1] uses a glass fiber filter coated with 2,4-dinitrophenylhydrazine and phosphoric acid for collection, with HPLC analysis.

GLUTARALDEHYDE: METHOD 2532, Issue 1, dated 15 August 1994 - Page 2 of 5 REAGENTS: 1. Glutaraldhyde, 25% (w/v) solution in water (Aldrich D19,93 0-3 or equivalent).* 2. Water, distilled, deionized. 3. Acetonitrile, HPLC grade. 4. Sodium sulfite, 1.13 M. Prepare fresh immediately before use. 5. Sulfuric acid, 0.02 N. 6. Sodium hydroxide, 0.01 N * See SPECIAL PRECAUTIONS EQUIPMENT: 1. Sampler: Glass tube, 110 mm long, 6- mm O D, flame -sealed ends and plastic caps containing two sections of silica gel coated with 2,4- dinitrophenylhydrazine HCl. The front section contains 300 mg, the back 150 mg, and sections are retained and separated by small plugs of silanized glass wool. (SKC 226-119 or equivalent). NOTE: The hy drochlo ride salt provides an acid catalyst for the reaction of glutaraldehyde with the dinitrophenylhydrazine. Other acids m ay be used as catalyst. 2. Perso nal sam pling pump, 0.05 to 0.5 L/min, with flexible connecting tubing. 3. High performance liquid chromatograph (HPLC), UV detector (365 nm), column, and integrator (page 2532-1). 4. Shaker, mec hanical. 5. Syringe, 10-mL, disposable. 6. Vials, gla ss, scintillation, 20-m L, with PTFE-lined caps. 7. Syringes, microliter, readable to 0.1- L. 8. Flasks, volumetric, various sizes. 9. Pipets, various sizes. 10. Burets, 50-mL. 11. Stirrer, magnetic. 12. ph meter. 13. Beakers, 50-mL. 14. File. SPECIAL PRECAUTIONS: Glutaraldehyde can irritate the mucous membrane and act on the central nervou s system [2]. W ork with this com pound only in a w ell-ventilated hood. SAMPLING: 1. Calibrate each personal sampling pump with a representative sampler in line. 2. Break ends of the sampler immediately before sampling. Attach sampler to personal sampling pump with flexible tubing. 3. Sample at an accurate ly know n flow rate betwee n 0.05 an d 0.5 L/m in for a total sample size of 1 to 30 L. NOTE: Glutaraldehyde reacts with the 2,4-dinitrophenylhydrazine to form a hydrazone derivative which provides sample stability and UV chromophores for analysis. 4. Immediately after sampling, cap the sample tubes, including blanks, and pack securely for shipment, include 10-20 unused tubes from the same lot to be used for standard preparation.

GLUTARALDEHYDE: METHOD 2532, Issue 1, dated 15 August 1994 - Page 3 of 5 SAMPLE PREPARATION: 5. Score each sampler with a file in front of the front sorbent section and break the tube at the score line. 6. Remove and place front glass wool plu g and front sorbent section (300 mg) in a vial. 7. Transfer back section (150 mg) with remaining glass wool plu gs to a se cond vial. 8. Add 3.0 ml of acetonitrile to each v ial. Screw cap tightly onto eac h vial. 9. Agitate vials in a mechanical shaker for at least 2 h. NOTE: The use of ultrasonic bath yields incom plete recovery. CALIBRATION AND QUALITY CONTROL: 10. Calibrate daily w ith at least six working standards o ver the range of interest. a. Prepare and standardize glutaraldehyde stock solution. (See APPENDIX.) Make serial dilutions of the stock solution with water. b. Using a microliter syringe, add known amounts of glutaraldehyde directly onto the DNPH-coated silica gel tubes over the range of interest. Allow the tubes to stand overnight for solvent evaporation and equilibration. c. Prepare the standards as described in Steps 5 through 9 and analyze with samples and blanks. d. Prepare a calibration graph (peak area or height vs. concentration). NOTE: Because the working standards are prepared on media blanks, no additional blank correction or extraction efficiency correction is necessary. Check extraction efficiency occas ionally in the range of interest. 11. Analyze three quality control blind spikes and three analyst spikes to ensure that the calibration graph and reco very gra ph are in control. MEASUREMENT: 12. Set the liquid chromatograph to manufacturer's recommendations and parameters given on page 5512-1. 13. Inject 25-µL sam ple aliquo t. 14. Measure peak area or height for each UV response. The two isom ers of glutaraldehyde are separated using these chromatographic conditions. Sum the peak area or height of both isomers to obtain the total area of height. CALCULATIONS: 15. Dete rmine the m ass, µ g, of glutaraldehyde found in the sa mp le front (W f ) and b ack (W b ) sorbent sections. NOTE 1: Corrections for extraction efficiency and blanks are incorporated into the method by using spiked media as standards. NOTE 2: If W b > W f /10, report breakthrough and possible sample loss. 16. Calculate conce ntration (C) of glutaralde hyde in the air volum e sam pled in liters (V):

GLUTARALDEHYDE: METHOD 2532, Issue 1, dated 15 August 1994 - Page 4 of 5 EVALUATION OF METHOD: The pressure dro p at 0.2 L/min across represen tative tub es w as 6" H 2 O, at 0.5 L/min about 14" H 2 O, bu t at 1 L/m in it was abou t 46" H 2 O. This method incorporates the use of spiked media as standards eliminating recovery bias. Mechanical agitation gave better recovery and linearity of the calib ration cu rve ra ngin g from 0.6 to 24 µ g pe r sam ple. R eco verie s from tube s ag itated by son ic bath decreased as the concentration increased. Recoveries of glutaraldehyde from the DNPHcoated tubes were determined by spiking 6 tubes each at concentrations of 1.2, 2.4, and 12 µg per sample. After standing overnight to allow the solvent to evaporate, the sorbent was transferred to a vial, 3 ml of acetonitrile was added, and the sample was agitated in a mechanical shaker for at least 1 h. At the same time, 6 more tubes were spiked at each of these concentrations and stored in the laboratory at ambient conditions for 42 days. The data are shown in Table 1. Table 1. Recovery and Stability Study of Glutaraldehyde Concentration Day Rec overy S r (µg/sample) Analyzed (%) 1.2 1 95.028 42* 100.014 2.4 1 97.027 42 98.034 12 1 96.034 42 98.023 * Samples stored at 25 C for 42 days. A 20-point, 4-concentration curve was used to determine a LOD of 0.24 µg/sample and a LOQ of 0.78 µ g/sam ple. No air sam ples w ere ge nerate d during this ev aluation. Audit sam ples w ere prepared with liquid spikes of glutaraldehyde in water added directly onto the DNPH -coated silica gel tube. The se au dit sam ples w ere sh ipped, stored, and a nalyzed by an independent laboratory using this method. The results were acceptable with recoveries of about 100% at 1.2 µg per tube, 94% at 2.4 µ g per tu be, 85 % a t 12 µg per tub e, and <0.3 µg pe r tube for the blanks [3]. REFERENCES: [1] OS HA Ana lytical M ethod s Manual, Glutaraldehyde, Method 6 4. OS HA Tech nical C enter, Salt La ke C ity, UT. U.S. Dep t. of Lab or (198 5). [2] The Me rck Index, 11 th ed., M erck & Co., R ahw ay, N J (198 9). [3] Use r Che ck, DataC hem Labs, Seq uence #7 958-J (unpublishe d, 3/14 /94). METHOD WRITTEN (REVISED) BY: Charles E. Neum eister, NIOSH /DPSE, and Gordon Hill, DataChem Laboratories, Salt Lake City, UT.

GLUTARALDEHYDE: METHOD 2532, Issue 1, dated 15 August 1994 - Page 5 of 5 APPENDIX: PREPARATION AND STANDARDIZATION OF GLUTARALDEHYDE STOCK SOLUTION Dilute 1 ml 25% aqueous glutaraldehyde to 25 ml with distilled, deionized water. Place 10.0 ml 1.13 M sodium sulfite solution in a b eake r and stir mag netically. With a ph m eter, ad just ph to betw een 8.5 an d 10 w ith base or acid. Record the ph. Add 1.0 m L glutaraldeh yde stock so lution. The ph should be about 12. Titrate the solution back to its original ph with 0.02 N sulfuric acid. If the endpoint ph is overrun, back-titrate to the endpoint with 0.01 N sodium h ydroxide. Calculate the concentration, Cs (µg/µl) of the glutaraldehyde stock solution. where: 50.06 = equivalent weight of glutaraldehyde N a = norm ality o f sulfu ric ac id V a = volume of sulfuric acid (ml) used for titration N b = normality of sodium hydroxide V b = volume of sodium hydroxide (ml) used for back titration V s = volum e of glutaraldehyde stock s olution (1.0 m L).