Using Carbon Dioxide as a Tracer Gas to Measure Air Change Rate in a Single Zone



Similar documents
Exposure and Control of Ten High Priority MSHA Contaminants in Metal Mines. Presented by: Shannon E. Newton, MPH, CIH

Measuring Air Changes per Hour with Carbon Dioxide

Why Measure Carbon Dioxide Inside Buildings? By Rich Prill, Washington State University Extension Energy Program

HVAC Systems and Indoor Air Quality. Douglas K. Spratt, M.Sc., P.Eng.

Exposures to Coal Fly Ash During Maintenance of Air Cleaning Devices in Power Plants

THE EFFECTS OF LAMINAR AIRFLOW IN SEMICONDUCTOR FABS ON THE VENTILATION DESIGN FOR EXHAUSTED ENCLOSURES

Calculations and OELs

Risk Assessment of Lab Bench Top Processes to Ensure Safety in Smart Labs

THE LEADER IN PERFORMANCE INDOOR AIR QUALITY MEASUREMENTS

Asbestos in the Workplace: A Guide to Removal of Friable Asbestos Containing Material

Using Assigned Protection Factors (APFs) for Respirator Selection Use with Chapter WAC, Respirators

A Report of Air Sampling for Mercury Vapor and Particulates During Fluorescent Tubes Disposal Operation Maywood, Illinois Survey date: 9/28/2000

A Series of Negative Exposure Assessments Related to Asbestos Containing Components Still Used in Railroad Equipment Today

How To Test For Residual Dust

Specification. Indoor Air Quality Management

PERCENT OUTDOOR AIR (%OA) CALCULATION AND ITS USE

Trace Gas Exchange Measurements with Standard Infrared Analyzers

Introduction to Industrial Hygiene

Unit 3.4 Decontamination (Core)

WATER DAMAGE INVESTIGATION. Massachusetts Department of Public Utilities 1 South Station Boston, Massachusetts

Technical Cleaning Ó

Excerpts from EPA s Mold Remediation in Schools and Commercial Buildings

Case Study: Successful Decontamination of an HVAC System s Ductwork Using Chlorine Dioxide Gas

Course Guidelines. Occupational Health and Safety for the Asbestos Worker

Asbestos Abatement Management Program. Facilities Operations and Development Environmental Health & Safety

SLMA Meeting. Boiler MACT and Related Rules. Atlanta, GA March 2, Martin Rollins, P. E. H. M. Rollins Company, Inc. Gulfport, Mississippi

Performance Assessment of EAGLE 5000 in Tobacco Smoke Environment. REPORT

APPENDIX B. EPA s Investigating, Evaluating, and Remediating Moisture and Mold Problems (see EPA website for complete details)

Principles of Ventilation. Patrick N. Breysse, PhD, CIH Peter S.J. Lees, PhD, CIH Johns Hopkins University

SAFETY AND HEALTH PROGRAM

READ FIRST. Confined Space Entry Procedure. San José State University Environmental Health and Safety. Confined Space Entry Procedure

Mould Mould A Basic Guide

Radford University. Indoor Air Quality Management Plan

CAT CG132. Series Gas Generator Sets

CeramClean II Aluminum Safe

Comparison of Analytical Methods for Evaluating Mold in Carpet Dust

International Refrigerant Standards and their Influence on the Global HVAC Industry and Refrigerant Replacement

Quantifying the energy and carbon effects of water saving summary report

SUMMARY OF ASHRAE S POSITION ON CARBON DIOXIDE (CO 2 ) LEVELS IN SPACES. Stephen Petty, P.E., C.I.H.

Industrial Ventilation Design Guidebook Chapter 10 LOCAL VENTILATION

Standardized Terminology for Combustion Appliances and. Combustion Safety Testing

Decontamination Units

Training Requirements for the Revised Hazard Communication Standard

XYZ Contract Company Industrial Hygiene Program

Not All 3A Recovery Wheels Limit Contaminant Transfer

Occupational Health and Safety. Course Guidelines. for the Asbestos Worker

VAV Laboratory Room Airflow The Lowdown on Turndown

Benzene Exposures from Petroleum- Derived Solvents Containing Trace Levels of Benzene in Occupational Settings

Mechanical and Natural Ventilation

MISSION CRITICAL FACILITIES DESIGN UPS BATTERY ROOM ENVIRONMENT CRITICAL DESIGN CONSIDERATIONS

UNIVERSITY OF KENTUCKY CONFINED SPACE PROGRAM

Hazardous Drug. Cleanroom. Standards

Case Studies: Infrared Heating in Industrial Applications

Ammonia Detection System Codes and Design Specifications. Brian EuDaly, P.E. Calibration Technologies, Inc.

************************************************************************ *** SECTION 1 PRODUCT IDENTIFICATION

White Paper. Best Practices for Gas Monitoring in the Commercial Kitchen

MOLD REMEDIATION KEY STEPS

Sandblasting & Silica Exposure Control Plan

CONFINED SPACE ENTRY (PROJECT STANDARDS AND SPECIFICATIONS) KLM Technology Group

CSA Z Infection Control during Construction, Renovation and Maintenance of Health Care Facilities Overview and Case Studies

Confined Space Air Monitoring

Guide Specification for Laboratory Fume Hood Commissioning

WHMIS Material Safety Data Sheet Product Information VP-TECH CHEMICAL PRODUCT AND COMPANY IDENTIFICATION. Water Soluble Metalworking Fluid Concentrate

A practical guide to restrictive flow orifices

Generation of Vapor-Phase Hydrogen Peroxide Test Atmospheres for the Evaluation of Respirator Cartridges and Air Samplers

HEPA-filtered Negative Air Machines and their Role in Creating Airborne Infection Isolation Rooms with the ECU AnteRoom. Frequently Asked Questions

Visualisation and control of solder fume exposure

Questions & Answers (Q & A) Regarding Asbestos Treatment with the Fire Suppression and Renovation Project

Components HVAC General Standards HVAC Guidelines HVAC System Selection Life Cycle Cost Analysis

LANCOM4 PORTABLE FLUE GAS MONITORING. NO NO2 NOx CO2 H2S SO2 CxHy. CO low CO high O 2 QUALITY CUSTOMER SOLUTIONS

GUIDELINES ON SAMPLING STRATEGY AND SUBMISSION OF AIR MONITORING / SAMPLE ANALYSIS REPORT

Information paper 20. Prepared by: David Clark. book:

Selective Catalytic Reduction (SCR) and Diesel Exhaust Fluid (DEF) Training Module

SAP 2012 IN A NUTSHELL

Lead Exposure Management Plan

Indoor Air Quality Issues for Hotels

9/15/2011. Presented by: Jason Reason, CIH, CSP, CHMM Senior Industrial Hygienist Indiana Occupational Safety and Health Administration

Alternative to Fossil Fuel

Nitrous Oxide: Hazards and Proper Use

Ammonia Detection System Codes and Design Specifications

DUST AND DEBRIS MANAGEMENT PROCEDURES HPD HOUSING REHABILITATION PROGRAMS

A Multi-Application, Multi-Industry Asbestos Exposure Assessment During Maintenance of Surfaces and Joints Sealed with Gaskets and Packing

A Comparison of Tchebycheff, Equal Area and Tracer Gas Air Flow Rate Measurements

Mold and Mildew Mold and mildew can be detected by sight, smell and touch.

Real-Time DPM Ambient Monitoring in Underground Mines

BEST PRACTICE IN DESIGN AND TESTING OF ISOLATION ROOMS IN NORDIC HOSPITALS

Independent Forensics of Illinois

Plumbing Code in Commercial Kitchens

Maximize energy savings Increase life of cooling equipment More reliable for extreme cold weather conditions There are disadvantages

ANSI/BPI-1200-S-2015:

MONITORING SCHOOL ENERGY CONSUMPTION

Veterinary Clinics and Hospitals

How Sensors Work. How Oxygen, Electrochemical Toxic, and Metal Oxide Semiconductor Sensors Work *

Transcription:

Using Carbon Dioxide as a Tracer Gas to Measure Air Change Rate in a Single Zone C. Simmons, F. Boelter, G. Crawford, Boelter & Yates, Inc., Park Ridge, IL Presented by: Catherine E. Simmons, CIH

Situation Ventilation information was needed to perform a retrospective exposure assessment. Procedure was needed to determine the ventilation rate in air changes per hour (ACH) for representative boiler rooms and an isolation test chamber.

Boiler Room Ventilation Research Published Information on Boiler Room Air Change Rates ASHRAE, BOCA and NFPA reviewed for ventilation requirements in ACH Ventilation Models Using Tracer Gas Published Ventilation Models using Tracer Gas Standard Test Method for Determining Air Change in a Single Zone by Means of a Tracer Gas Dilution ASTM E 741 00

Problem Existing methods allow for the use of a variety of tracer gases to be used. Each has advantages and disadvantages. Selected method highly portable easily measured non-toxic or very low toxicity inexpensive Tracer gas acceptable to school district personnel.

Research Standard Test Method for Determining Air Change in a Single Zone by Means of a Tracer Gas Dilution ASTM E 741 00 Tracer gases (examples) CO 2 PEL 5000 ppm SF 6 PEL 1000 ppm CO PEL 50 ppm Selection of test method Concentration Decay Constant Injection Constant Concentration

Resolution Selection of tracer gas Carbon dioxide Relatively high PEL Inexpensive Easy to obtain and measure Acceptable to School personnel Selection of method Concentration Decay Test Method Measures the decay rate of carbon dioxide over time to calculate the air exchange rate. Regression Analysis InC(t) = -At + C(0)

Sample Time Air Change Rate (1/hr) 0.25 0.5 1 2 4 Minimum Duration (hour) 4 2 1.5.25 Minimum sample duration based on 10% uncertainty at the 95% confidence level in the detection of air change rate, a tracer gas concentration measurement precision error of 5% of reading and various air change rate. Using the regression method reduces the minimum test duration due to more than 2 data points.

Boiler Room Ventilation Testing Using Tracer Gas Representative Boiler Rooms Elementary School - IN Elementary School - IL Middle School - IL

Gas Injection and Distribution

Direct Reading Equipment TSI Q-Trak Log Data

School Indiana 5500 ft 3 Boiler Room Volume of gas needed Calculated based on room size and target concentration of 4000 ppm V tracer = C target X V zone 2 boilers Input BTU/hr. - 117,000 Input BTU/hr. 156,000 Both boilers operating during the testing No mechanical ventilation

Average CO2 Concentration vs Time Indiana Boiler Room - 2 Boilers Operating March 26, 2003 Carbon Dioxide Concentration in Parts Per Million (PPM) 4500 4000 3500 3000 2500 2000 1500 1000 500 0 1 7 13 19 25 31 37 43 49 55 61 67 73 Trial 1 - Average CO2 Concentration (PPM) 5.2 Air Changes Per Hour Trial 2 - Average CO2 Concentration (PPM) 5.3 Air Changes Per Hour Time in Minutes Trial 1 5.2 ACH Trial 2 5.3 ACH Average 5.2 ACH

Elementary School Illinois Measured Volume 24,322 ft 3. 2 Boilers Ventilation tracer gas testing conducted with boilers on and off.

Elementary School Ventilation Rate - Boilers Off 1.8 Air Changes Per Hour March 27, 2003 Average CO2 Concentration vs Time March 27, 2003 4000 3000 2000 1000 0 0 18.75 37.5 56.25 Time in Minutes Carbon Dioxide Concentration (ppm) Carbon Dioxide Concentration (ppm) 5000 4000 3000 2000 1000 0 0 2.25 4.5 6.75 9 11.3 13.5 15.8 18 20.3 22.5 24.8 27 29.3 31.5 Time in Minutes Trial 2 - Average Carbon Dioxide Concentrations with 2 Boilers Operating Trial 3 - Average Carbon Dioxide Concentrations with 2 Boilers Operating Trial 1 Boilers On Boilers Off - 1.8 ACH Trial 2 3.5 ACH Trial 3 3.9 ACH Average 3.7 ACH

Middle School Illinois 16,372 ft 3 Boiler Room 2 Identical Boilers

Middle School 5000 4000 3000 2000 1000 0 Average Carbon Dioxide Concentration (ppm) vs Time Middle School March 21, 2003 0 25 50 75 Time in Minutes Carbon Dioxide Concentration (ppm) Carbon Dioxide Concentration (PPM) 5000 4000 3000 2000 1000 0 Average CO2 Concentration vs Time Boiler Room - 2 Boilers March 31, 2003 1 112131415161718191 Time in Minutes Boilers On (1 boiler on part time): Trial 2 - Average CO2 Concentration 4.4 Air Changes Per Hour, GlenCrest School March 31, 2003 Boilers On: Trial 3 - Average CO2 Concentration 5.3 Air Changes Per Hour, GlenCrest School March 31, 2003 Boilers Off Boilers On 1.2 ACH Trial 2-4.4 ACH Trial 3-5.3 ACH Average 4.9 ACH

Measured Range of Boiler Room Ventilation Summary Boilers Off Range: 1.2 to 1.8 ACH Boilers On Range: 3.7 to 4.9 ACH

Isolation Test Chamber Approximately 20 x 20 x 9 (3600 ft 3 ) Wood Frame Polyethylene sheeting on walls and floors 2 viewing windows Entrance airlock Decontamination Shower (if needed) HEPA filtered exhaust machines for ventilation

HEPA Filtered Exhaust Machines for Chamber Ventilation System Note: Using various configurations, both machines operated as exhaust (tubing was attached to machines to exhaust outside the building).

Installation and Measurement of Ventilation System Various configurations to achieve approximately 1, 3, 5 and 10 ACH Carbon dioxide tracer gas used to measure ventilation rate. Each rate tested twice to assure repeatability. Final ventilation rates were: 1.2, 2.9, 5.7, 10.7 ACH.

Carbon Dioxide Concentration (ppm) vs Time B & Y Test Chamber 5.7 Air Changes Per Hour April 29, 2003 6000 5000 4000 3000 2000 1000 0 16:28 16:30 16:32 16:34 16:36 16:38 16:40 16:42 16:44 16:46 16:48 16:50 Carbon Dioxide Concentration (ppm) Trial 1 - high Trial 1 - low Trial 2 - high Trial 2 - low Time Trial 1 5.8 ACH Trial 1 5.8 ACH Average 5.7 Trial 2 5.8 ACH Trial 2 5.5 ACH

Conclusions Ventilation rates for representative boiler rooms were between 1 and 5 ACH. Using carbon dioxide as a tracer gas and following ASTM E 741 00, Standard Test Method for Determining Air Change in a Single Zone by Means of a Tracer Gas Dilution met the objectives and goals of the project.

Benefits Carbon Dioxide as a tracer gas Inexpensive, reliable procedure for IH s to determine ventilation rates. Measuring Equipment is readily available The method provides an additional tool for industrial hygienists to better characterize workplace conditions during the initial stages of an exposure assessment. Ventilation information is critical to the ability to perform and validate mathematical modeling for exposure estimation.

C(t) Well Mixed Room Model - Constant Contaminant Emission Rate G + C Q Q + k V Q + k V IN L + L = 1 exp t C exp t Q + k V V 0 V L Input Variables C IN mg/m 3 Concentration in incoming air G mg/min Q m 3 /min Generation Rate Exhaust air flow V m 3 Volume of Room K L per min Loss Pathway (sinks) C 0 mg/m 3 Initial concentration

0.7 0.6 0.5 0.4 0.3 0.2 0.1 0 0 3 6 9 Predicted Concentration at 0.01, 0.1, 1, 3, 4, 5 and 10 Air Changes Per Hour 12 Effect of Ventilation Rate on Concentration of Contaminant 15 18 21 24 27 30 33 36 39 42 45 0.01 ACH 0.1 ACH 1 ACH 3 ACH 4 ACH 5 ACH 10 ACH

Thank you! Questions? Speaker Contact Information: Catherine E. Simmons, CIH Boelter & Yates, Inc. Park Ridge, IL csimmons@boelter-yates.com