Formulas: See Table 1 MW: Table 1 CAS: Table 1 RTECS: Table 1. METHOD: 2555, Issue 1 EVALUATION: PARTIAL Issue 1: 15 March 2003

Similar documents
HYDROCARBONS, BP C 1500

ANILINE, o-toluidine, AND NITROBENZENE 2017

MERCAPTANS, METHYL-, ETHYL-, and n-butyl- 2542

THIOPHANATE-METHYL in air 5606

POLYCHLOROBENZENES 5517

Corn Syrup Analysis E-1a- 1. ACETALDEHYDE and ISOVALERALDEHYDE (Gas Chromatography)

Determination of Diesel Range Organics (DROs) Using SPE and GC/FID by Method 8015D*

ACETALDEHYDE. The procedure is applicable to corn syrups including those containing fructose, and to most other starch hydrolyzates (Note 1).

By Authority Of THE UNITED STATES OF AMERICA Legally Binding Document

CORESTA Recommended Method No. 57

2.1 This procedure provides steps and conditions for the determination of Vapor Space Organic Compounds in ground waters, and industrial waste waters.

METHOD: 2016, Issue 2 EVALUATION: FULL Issue 1: 15 January 1998 Issue 2: 15 March 2003

STANDARD OPERATING PROCEDURES

METHOD 3610B ALUMINA CLEANUP

Standard Operation Procedure (SOP) for the Extraction and Instrument Analysis of Siloxanes from Cartridges

Method of determination of phthalates by gas chromatography / mass spectrometry in wines

Quantitative determination of residual 2-(2-chloroethoxy) ethanol (CEE) in quetiapine fumarate by gas chromatogaraphy

10. Validated Normal Phase HPLC Method for the Determination. Fulvestrant is primarily used in the treatment of hormone receptor

Performance Characteristics of the Agilent 1220 Infinity Gradient LC system

Optimization of Volatile Petroleum Hydrocarbons Analysis by Automated Headspace Using Method Development Tools

Analytical Method of Limit Test for Hexachlorobenzene. in Picloram TC and Method Validation Data*

JAI RESEARCH FOUNDATION A Global Contract Research Organisation

METHOD 310A - DETERMINATION OF RESIDUAL HEXANE THROUGH GAS CHROMATOGRAPHY

A Rapid Method for Trace Analysis of Organophosphorus Pesticides in Drinking Water

Performance characteristics of the 1260 Infinity Quaternary LC system

Validation of Sulfur Dioxide Using. SKC UME x 200 Passive Sampler Cat. No Page 1 of 14 Publication 1781 Rev 1607

Ethylene Oxide. Fully validated method. This method has been subjected to the established evaluation procedures of the Methods Development Team.

Gas Chromatography SSI-GC-003

Field Tests of Chloroform Collection/Analysis Methods

Amy Nutter, Applications Chemist; Teledyne Tekmar P a g e 1

Forensic Toxicology. Analysis of Ethanol in Blood using Master SHS Static Headspace Sampler and Master GC Gas Chromatograph APPLICATION NOTE.

US EPA Method 8260 with the Atomx XYZ and the Thermo Scientific TRACE 1310 GC and ISQ MS

Large Volume Injection of Organochlorine Pesticide Extracts Using a Programmable Temperature Vaporizer in the Solvent Split Mode

STANDARD OPERATING PROCEDURES SOP: 1502 PAGE: 1 of 11 REV: 0.0 DATE: 10/24/94

NWTPH-Gx. Volatile Petroleum Products Method for Soil and Water

Separation and Quantitation of a Mixture of Alcohols by Gas Chromatography

Validation of Nitrous Oxide Using SKC Passive Sampler SKC Inc. 863 Valley View Road Eighty Four, PA 15330

CORESTA Recommended Method No. 63

Course Outline. in Soil/Sediment&WasteSediment&Waste by. Overview of VOCs Analysis Sample Collection VOCs Analysis

Application Note AN1501

Using Alternative Carrier Gas for US EPA Application Note. Abstract. Introduction. Experimental-Instrument Conditions

Analysis of Semivolatiles by GC/FID using the Ultra Inert Inlet Liners with Wool

NCASI METHOD CI/SG/PULP CHILLED IMPINGER TEST METHOD FOR USE ON PULP MILL SOURCES TO QUANTIFY METHANOL EMISSIONS

Protocol for Quantitative Determination of Residual Solvents in Cannabis Concentrates Prepared by: Amanda Rigdon, May 23 rd, 2016

Certified Reference Material - Certificate of Analysis

POLYCHLOROBIPHENYLS in serum 8004

EDB July ETHYLENE DlBROMlDE. F. Analytical Quantitation... I. Determinative Method. Contents. A. Introduction I3. Equipment...

Validation Data for the Analysis of Chlorotalonil in Leek Using Mini-Luke Method Followed by GC-QqQ-MS/MS

EURL-SRM - Analytical Observations Report

Certified Reference Material - Certificate of Analysis

EXTRACTION OF BIOLOGICAL TISSUES FOR AROMATIC AND CHLORINATED HYDROCARBONS

Scale-up with the Agilent SD-1 Purification System analytical and preparative runs on a single system

Industrial Hygiene Report Control of Glycol Ether Solvent Fumes Using Activated Carbon Filter Media: Ethylene Glycol Monobutyl Ether.

PuriTox Aflatoxin Product Code: P25

Chem 321 Lecture 23 - Liquid Chromatography 11/19/13

Optimizing Productivity and Reliability for Monocyclic Aromatic Hydrocarbon Purity Analysis According to ASTM D7504 on the Agilent 8890 GC System

C146-E096 TD-20. Shimadzu Thermal Desorption System

VOA Calibration Mix #1

CHROMATOGRAPHY/MASS SPECTROMETRY

Two Headspace Solutions for the Analysis of Dissolved Gases in Water by Method RSKSOP-175

Evaluation by Competent Authorities

Joette L. Steger, Joan T. Bursey, and David Epperson

METHCATHINONE Latest Revision: July 11, 2005

ANALYSIS OF PESTICIDE RESIDUES IN DRINKING WATER AS PER BUREAU OF INDIAN STANDARDS USING THE AGILENT 7000 GC/MS/MS WITH PESTICIDES ANALYZER

Capillary GC Troubleshooting: a Practical Approach

Certified Reference Material - Certificate of Analysis

2023 Reduction of D-(+)-camphor with lithium aluminium hydride to an isomeric mixture of (+)-borneol and ( )-isoborneol

Volatile Organic Compounds in Solids PBM

Agilent Consumables Improve Performance with Shimadzu GC/MS

Volatile Organic Carbon Contaminated Site Assessment

4002 Synthesis of benzil from benzoin

Contract Laboratory Program (CLP) Pesticide Analysis with 0.18 mm ID High-Efficiency GC Columns Utilizing Helium Carrier Gas. Application.

Emission Testing August 2013 EPA 4 Benzene Combustor Inlet/Outlet Testing

Validated Multi-Residue Method for Extraction and Analysis of Trace-Level Pesticides in Surface Water Application

Gas Chromatography Assignment Chem 543/443

Organohalide Pesticides in Water by GC/µECD with Agilent J&W DB-CLP1 and DB-CLP2

DETERMINATION OF ORGANIC PRIORITY POLLUTANTS AND EMERGING COMPOUNDS IN WASTEWATER BY MICRO SOLID PHASE EXTRACTION COUPLED TO GCMS

Certified Reference Material - Certificate of Analysis

Analysis of styrene leached from polystyrene cups using GCMS coupled with Headspace (HS) sampler

Certified Reference Material - Certificate of Analysis

Experiment 11. DNA Composition by HPLC 1,2

Analysis of USP <467> Residual Solvents using the Agilent 7697A Headspace Sampler with the Agilent 7890B Gas Chromatograph

Analysis of PCBs in Sewage sludge for the characterization study of ERM CC392

ELEMENTS by ICP 7301 (Aqua Regia Ashing)

Project Summary. Field Evaluation of EPA Method 0040 (Volatiles Using Bags)

Residual Solvents in medical cannabis analysis using the SRI 8610C FID GC June 2014

SOP-C-102 Determination of Chemical Oxygen Demand

Determination of Organotin Compounds in Toy Materials by Agilent 5977A GC/MSD to Meet European Regulation EN71-3: 2013, Migration of Certain Elements

New Developments in Thermal Desorption (TD) Tube & Canister Technologies for Collection & Analysis of Soil Gas

Principles, Practices, and Equipment for Performance Evaluation of Personal Monitoring Badges. Maria D.R. Peralta, PhD and C.R.

Partly O-(2-hydroxyethylated) cellulose. It may contain suitable ph-stabilisers such as phosphates.

A Direct Column-Performance Comparison for Rapid Contract Laboratory Program (CLP) Pesticide Analysis. Application. Authors. Abstract.

ELEMENTS by ICP 7301 (Aqua Regia Ashing)

Certified Reference Material - Certificate of Analysis

A Benchtop Sample Preparation Instrument: New Solutions for GC and GC/MS Applications

Provläsningsexemplar / Preview. First edition

Gas Filtration Catalogue

ELEMENTS by ICP 7300 (Nitric/Perchloric Acid Ashing)

TECHNICAL MEMORANDUM. Pamela Moss, EA Team (EA Engineering, Science, and Technology, Inc., PBC/ CH2M HILL)

Certified Reference Material - Certificate of Analysis

Transcription:

KETONES I 2555 Formulas: See Table 1 MW: Table 1 CAS: Table 1 RTECS: Table 1 METHOD: 2555, Issue 1 EVALUATION: PARTIAL Issue 1: 15 March 2003 OSHA : See Table 2 NIOSH: See Table 2 ACGIH: See Table 2 PROPERTIES: See Table 3 SYNONYMS: (1) Acetone: dimethyl ketone, ketone propane, 2-propanone. (2) Methyl ethyl ketone: methyl acetone, 2-butanone, MEK. (3) 2-Pentanone: ethyl acetone, methyl propyl ketone, MPK. (4) Methyl isobutyl ketone: hexone, 4-methyl-2-pentanone, MIBK. (5) 2-Hexanone: methyl n-butyl ketone, methyl butyl ketone, MBK. (6) Di-isobutyl ketone: sym-diisopropyl acetone, 2,6-dimethyl-4-heptanone, isovalerone, valerone, DIBK. (7) Cyclohexanone: anone, cyclohexyl ketone, pimelic ketone. SAMPLER: FLOW RATE: SAMPLING SOLID SORBENT TUBE (Anasorb CMS, 150 mg/75 mg) 0.01 to 0.2 L/min Acetone Others VOL-MIN: 0.5 L 1 L -MAX: 3.0 L 10 L SHIPMENT: Refrigerate samples. SAMPLE STABILITY: All analytes 30 days @ 5 C TECHNIQUE: MEASUREMENT ANALYTE: See Table 1 DESORPTION: INJECTION VOLUME: 1 µl GAS CHROMATOGRAPHY, FID 1 ml CS 2 for 30 minutes TEMPERATURE -INJECTION: 250 C -DETECTOR: 300 C -COLUMN: 40 C (1 min) to 200 C (8 C/min) BLANKS: 2 to 10 field blanks per set. CARRIER GAS: Helium, 1mL/min RANGE STUDIED: ACCURACY Not studied. COLUMN: Capillary, fused silica, 30 m x 0.53-mm ID, 3.00-µm film crossbonded 35% diphenyl - 65% dimethyl polysiloxane BIAS: OVERALL PRECISION ( rt ): ACCURACY: CALIBRATION: Standard solutions of analytes in CS 2 RANGE: See Table 4. ESTIMATED LOD: See Table 4. PRECISION ( r ): See Table 4. APPLICABILITY: For three-liter sample, the working range for acetone was 0.378 to 41.4 ppm (0.92 to 100.2 mg/m 3 ). For a 10-L sample the working range for methyl ethyl ketone was 0.092 to 10.2 ppm (0.275 to 30.5 mg/m 3 ), for 2-pentanone was 0.077 to 8.67 ppm (0.276 to 31.1 mg/m 3 ), for methyl isobutyl ketone was 0.066 to 6.83 ppm (0.275 to 28.5 mg/m 3 ), for 2- hexanone was 0.066 to 7.45 ppm (0.275 to 31.1 mg/m 3 ), for diisobutyl ketone was 0.052 to 5.07 ppm (0.308 to 30.1 mg/m 3 ), and for cyclohexanone was 0.075 to 9.79 ppm (0.300 to 39.2 mg/m 3 ). INTERFERENCES: Any compounds with similar retention times as the analytes of interest. Alternate columns include Rtx-1 and Rtx-5 or equivalent capillary columns. OTHER METHODS: This method was developed as part of an update for NMAM 1300, issue 2 (dated 15 August 1994) [1]. NMAM 1300, issue 2 was based on NIOSH Manual of Analytical Methods, 2 nd edition methods S1, S18, S19, S20, S178, and S358. This method includes: lower LOD/LOQ values for each analyte, improved DE recovery results for each analyte (at lower levels), inclusion of methyl ethyl ketone and methyl isobutyl ketone in the method by the use of a different sorbent tube (Anasorb CMS), a 30-day storage stability study, and replacement of the packed column with a Rtx-35 fused silica capillary column.

KETONES I: METHOD 2555, Issue 1, dated 15 March 2003 - Page 2 of 5 REAGENTS: 1. Carbon disulfide (GC grade).* 2. Analytes, reagent grade.* 3. Helium, prepurified and filtered. 4. Hydrogen, prepurified and filtered. 5. Air, compressed, purified, filtered. 6. Calibration stock solution: Add known amounts of analytes to carbon disulfide in 10-mL volum etric flask. * See SPECIAL PRECAUTIONS EQUIPMENT: 1. Sampler: glass tube, 7 cm long, 6-mm OD, 4- mm ID, flame-sealed ends with plastic caps, containing two sections of Anasorb CMS (150 mg/ 75 mg) separated by a 2-mm urethane plug. A silylated glass wool plug precedes the front section and a 3-mm urethane foam plug follows the back section. Tubes are commercially available. 2. Personal sampling pump, 0.01 to 0.2 L/min, connected with flexible tubing. 3. Gas chromatograph equipped with FID, integrator and capillary column (page 2555-1). 4. Autosampler vials, 2-mL, glass, with PTFElined crimp caps. 5. Syringes, 10-µL, 25-µL, and 1-mL. 6. Pipettes, 3-mL and 5-mL. 7. Volumetric flasks, 10-mL. 8. Bagged refrigerant, Blue-ice or equivalent. SPECIAL PRECAUTIONS: Carbon disulfide is toxic, explosive, and a fire hazard (FP = -30 C). W ork with carbon disulfide in a well ventilated hood. Analytes should be handled in a fume hood. Use protective clothing and eyewear. SAMPLING: 1. Calibrate each personal sampling pump with a representative sampler in line. 2. Break the ends of the sampling tube immediately before sampling. Attach sampling tube to personal sampling pump with flexible tubing. 3. Sample at an accurately known flow rate between 0.01 and 0.2 L/min for a total sample size of 3 L for acetone and 10 L for all other analytes. 4. Cap the sam plers with plastic (not rubber) caps and pack securely for shipm ent. SAMPLE PREPARATION: 5. Place the front and back sorbent sections of the sampler tube in separate vials. Place the glass wool preceding the front section into the vial containing the front sorbent section. Discard the urethane foam plugs. 6. Add 1.0 m L of carbon disulfide into each vial. Attach crimp caps to each vial. 7. Allow to stand for 30 m inutes with occasional agitation. CALIBRATION AND QUALITY CONTROL: 8. Calibrate daily with at least six working standards from below the LOD to 10 times the LOQ. If necessary, additional standards may be added to extend the calibration curve. a. Add known amounts of analytes to carbon disulfide solvent in a 10-mL volumetric flask and dilute to the mark. Prepare additional standards by serial dilution in 10-mL volumetric flasks. b. Analyze together with samples and blanks (steps 11 and 12). c. Prepare calibration graph (peak area vs µg analyte). 9. Determine desorption efficiency (DE) at least once for each lot of Anasorb CMS used for sampling in the calibration ranges (step 8). a. Prepare three tubes at each of five levels plus three media blanks.

KETONES I: METHOD 2555, Issue 1, dated 15 March 2003 - Page 3 of 5 b. Inject a known amount (5 to 25 µl) of DE stock solution directly onto the front sorbent section of each Anasorb CMS tube with a microliter syringe. c. Allow the tubes to air equilibrate for several minutes, then cap the ends of each tube and allow to stand overnight. d. Desorb (steps 5-7) and analyze together with standards and blanks (steps 11 and 12). e. Prepare a graph of DE vs µg analyte recovered. 10. Analyze a minimum of three quality control blind spikes and three analyst spikes to ensure that the calibration graph and DE graph are in control. MEASUREMENT: 11. Set gas chrom atograph according to manufacturer s recommendations and to conditions given on page 2555-1. Inject a 1-µL sam ple aliquot manually using the solvent flush technique or with an autosampler. NOTE: If peak area is above the linear range of the working standards, dilute with solvent, reanalyze and apply the appropriate dilution factor in the calculations. 12. Measure peak areas. CALCULATIONS: 13. Determine the mass, µg (corrected for DE), of analyte found in the sample front (W f ) and back (W b ) sorbent sections, and in the average media blank front (B f ) and back (B b ) sorbent sections. NOTE: If W b > W f /10, report breakthrough and possible sample loss. 14. Calculate concentration, C, of analyte in the air volume sampled, V(L): NOTE: g/l = mg/m 3 EVALUATION OF METHOD: This method development was based upon a prioritized list of problematic gas chromatographic methods identified in a survey of external users of the NIOSH Manual of Analytical Methods. Method improvements include the use of capillary column chromatography, lower LOD/LOQ values, improved desorption efficiency (DE) at lower quantitative levels, and a storage stability study conducted at 7, 14, and 30 days. The method also incorporates the use of an improved solid sorbent tube sampler (Anasorb CMS) resulting in improved sample recovery and allowing methyl ethyl ketone and methyl isobutyl ketone to be included in the method without loss of sample recovered from the sorbent tube. Table 4 lists the method evaluation data, the LOD/LOQ values, the range of measurements, and the precisions for each analyte. [2] The average DE determined for acetone was 98.2% (RSD = 0.019), for methyl ethyl ketone was 98.6% (RSD = 0.017), for 2-pentanone was 99.3% (RSD = 0.011), for methyl isobutyl ketone was 96.4% (RSD = 0.011), for 2-hexanone was 100.6% (RSD = 0.013), for diisobutyl ketone was 102.4% (RSD = 0.013), and for cyclohexanone was 95.4% (RSD = 0.015). The average 30-day storage stability recovery for acetone was 100.7% (RSD = 0.017), for methyl ethyl ketone was 101.7% (RSD = 0.018), for 2-pentanone was 101.5% (RSD = 0.028), for methyl isobutyl ketone was 103.8% (RSD = 0.018), for 2-hexanone was 101.4% (RSD = 0.029), for diisobutyl ketone was 103.5% (RSD = 0.019), and for cyclohexanone was 87.4% (RSD = 0.009).

KETONES I: METHOD 2555, Issue 1, dated 15 March 2003 - Page 4 of 5 REFERENCES: [1] NIOSH Manual of Analytical Methods, 4 th ed., V. 2, U.S. Dept. of Health and Human Services, Publ. (NIOSH) 94-113 (1994). [2] Pendergrass SM [1998]. Backup data for Ketones I, NIOSH Method 2555, Issue 1. Cincinnati, Oh: Department of Health and Human Services, Public Health Service, Centers for Disease Control and Prevention, National Institute for Occupational Safety and Health, (unpublished, February). METHOD WRITTEN BY: Stephanie M. Pendergrass, NIOSH/DART TABLE 1. GENERAL INFORMATION Analyte Formula MW CAS # RTECS # Acetone (CH 3 ) 2 CO 58.1 67-64-1 AL3150000 MEK CH 3 COCH 2 CH 3 72.1 78-93-3 EL6475000 2-Pentanone CH 3 CO(CH 2 ) 2 CH 3 86.1 107-87-9 SA7875000 MIBK CH 3 COCH 2 CH(CH 3 ) 2 100.2 108-10-1 SA9275000 2-Hexanone CH 3 CO(CH 2 ) 3 CH 3 100.2 591-78-6 MP1400000 Diisobutyl ketone [(CH 3 ) 2 CHCH 2 ] 2 CO 142.3 108-83-8 MJ5775000 Cyclohexanone C 6 H 10 O 98.2 108-94-1 GW 1050000 TABLE 2. ANALYTE EXPOSURE LIMITS Analyte OSHA PEL NIOSH REL ACGIH TLV Conversion ppm to mg/m 3 Acetone 1000 250 500 1 ppm = 2.42 mg/m 3 MEK 200 200 200 1 ppm = 3.00 mg/m 3 2-Pentanone 200 150 200 1 ppm = 3.58 mg/m 3 MIBK 100 50 50 1 ppm = 4.17 mg/m 3 2-Hexanone 100 1 5 1 ppm = 4.17 mg/m 3 Diisobutyl ketone 50 25 25 1 ppm = 5.92 mg/m 3 Cyclohexanone 50 25 25 (A3 - unclassified carcinogen) 1 ppm = 4.00 mg/m 3

KETONES I: METHOD 2555, Issue 1, dated 15 March 2003 - Page 5 of 5 TABLE 3. PHYSICAL PROPERTIES. Analyte State Density @ 20 o C (g/ml) BP ( o C) Vapor Pressure (@ 20 o C) kpa(mm Hg) Acetone liquid 0.7915 56.2 35.5 (266) MEK liquid 0.8050 79.6 13.0 (100) 2-Pentanone liquid 0.8120 101.7 3.6 (27) MIBK liquid 0.8042 115.8 2.0 (15) 2-Hexanone liquid 0.8120 127.2 0.4 (3) Diisobutyl ketone liquid 0.8089 168.2 0.23 (1.7) Cyclohexanone liquid 0.9470 156.7 0.3 (2) TABLE 4. METHOD EVALUATION Analyte LOD LOQ Range Precision (S r ) Acetone 0.9 2.7 2.7-295.0 0.021 Methyl Ethyl Ketone 0.9 2.7 2.7-300.0 0.008 2-Pentanone 0.9 2.7 2.7-305.0 0.009 Methyl Isobutyl Ketone 0.9 2.7 2.7-280.0 0.013 2-Hexanone 0.9 2.7 2.7-305.0 0.010 Diisobutyl Ketone 1.0 3.0 3.0-295.0 0.010 Cyclohexanone 1.0 3.0 3.0-273.0 0.006