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ASHRAE Standard 62.1
The IAQ Procedure and LEED
Chris Muller
ASHRAE Distinguished Lecturer
Technical Director - Purafil, Inc.
Important Notice
COPYRIGHT © 2014 by PURAFIL, INC.
Neither this document nor any part may be reproduced or
transmitted in any form or by any means, electronic or
mechanical, including photocopying, microfilming, and
recording, or by any information storage and retrieval
system, without written permission from Purafil, Inc.
Corporate Offices: Purafil, Inc.: 2654 Weaver Way, Doraville, Georgia 30340 U.S.A.
Tel: 770-662-8545  Fax: 770-263-6922  Laboratory Fax: 770-263-0520
Page 2CIAQ Webinar – June 4, 2014
Introduction
• An important challenge today is
how to improve and maintain
IAQ in buildings while, at the
same time, reducing their
overall energy consumption.
• One cannot discuss the
issue of IAQ without giving
some attention to the role that
energy conservation
measures may play.
Introduction (2)
• Ventilation standards and mechanical codes have
evolved to address both IAQ and energy conservation.
• Air cleaning technologies have developed to provide
healthy and comfortable indoor environments.
• There are ever-increasing numbers of
applications for both particulate and gas-
phase air filtration in HVAC system
designs.
– Selecting and specifying the appropriate control
strategies requires special consideration.
Introduction (3)
• Air cleaning – for both
particulate and gas-
phase contaminants -
can be a critical
component in
achieving acceptable
Indoor Air Quality as
well as implementing
energy conservation
measures with ASHRAE
Standard 62.1-2013.
Trending Towards “Net Zero”
• A Net Zero Building is one that produces as much energy
as it uses over the course of a year.
– Net Zero Energy Buildings are by design very energy efficient and
any remaining energy needs are typically met with on-site
renewable energy.
Understand that there is
no such thing as a "zero
energy building! EVERY
building uses energy, or
you may as well be in a
cave!
Net Zero – Momentum is Building
ASHRAE Standard 62.1
62-1973 62-1981
62-1989
62.1-2001
62.1-2004
62.1-2010
???
62.1-2013
ASHRAE Definition of Acceptable IAQ
“Air in which there are no known contaminants at
harmful concentrations as determined by cognizant
authorities and with which a substantial majority
(80% or more) of the people exposed do not
express dissatisfaction.”
• Since 2001, Standard 62.1 has been written to be code-
enforceable containing only mandatory language.
– New update to be published in 2013.
• User’s Manual
– First published in 2005, updated in 2007, 2010, and 2013, next
scheduled update 2016.
– Provides information on how to use and apply Standard
62.1 with practical examples of compliance.
• Advanced IAQ Design Guide
– Best practices for design, construction &
commissioning.
ASHRAE Standard 62.1-2013
Ventilation for Acceptable Indoor Air Quality
ASHRAE Standard 62.1-2013 (2)
Ventilation for Acceptable Indoor Air Quality
• IAQ is based upon subjective criteria.
– Comfort not health !!
– Intended to minimize adverse health effects !!
– Not carbon dioxide concentration !!!!
• Ventilation Rate Procedure (VRP)
– Minimum acceptable outdoor air quality !!
– Requires air cleaning for ozone, PM10 and PM2.5 !!
• Indoor Air Quality Procedure (IAQP)
– Allows a balance to be struck between IAQ
and energy conservation.
Energy Conservation Potential
Why Not Use the IAQ Procedure?
• If you have to apply air cleaning for ozone, PM10, or PM2.5
the use of the IAQP could pay for upgrades to the air
cleaning system AND provide for a reduction in overall
HVAC operating costs.
• The IAQP allows credit to be taken - in the form of a
reduction of the outside air intake rate(s) for controls
that remove contaminants and that result in
indoor contaminant concentrations equal to
or lower than those achieved using the
ventilation rate procedure (VRP).
IAQP Requirements
• Specific requirements for compliance:
– Outdoor Air Quality Investigation (Section 4)
– Outdoor Air Treatment (Section 6.2.1)
– Contaminant Sources (Section 6.3.1)
• Identify contaminants of concern (COC)
– Contaminant Concentration (Section 6.3.2)
– Perceived Indoor Air Quality (Section 6.3.3)
– Design Approaches (Section 6.3.4)
– Documentation (Section 6.3.6)
The IAQP and Energy Savings
• The IAQP provides improved IAQ and reduces the
amount of energy used to condition ventilation air.
• It provides direct control of indoor air contaminants.
• Many different applications can be designed using the
IAQ Procedure.
• The most common applications, and
those with the greatest potential for
capital cost savings and operational cost
reductions, involve new construction
and renovation.
Example 1 - Movie Theater, New Construction
• An engineer applied the IAQP in the construction of a new
General Cinema movie theater in Houston, TX with air
cleaning (filtration) and recirculation would be used in an
effort to reduce the outdoor air below the 20 cfm per
person prescribed by the VRP.
• A reduction in the amount of outside air also meant that
less air would have to be tempered by the HVAC system.
Operational savings of $15,000/year.
Example 2 - Office Building Renovation
• An office building built in Atlanta, GA in the mid-1970s
was being renovated for a new owner.
• The IAQP was recommended and a cost/benefit analysis
was performed.
Item Amount
Cost Avoided: $300,000
Energy Savings ($/yr): $10,400
Media Replacement ($/yr): + (US $21,000)
Annual Operation: + (US $11,000)
Time to Equalization: 28 years
Example 3 - Lecture Hall, New Construction
• Design considerations…
• For all of the contaminants of concern, 5 cfm per person
provided space concentrations less than the target
concentrations and therefore complied with the
requirements of the IAQP.
• Summary of savings for reduction of conditioned
outside air.
Capital Equipment Savings: $8,643.00
Operational Savings: $1,136.00 / year
Example 4 - Retail Store, New Construction
• A retail store design with a number of different zone
types…
• All of the contaminants of concern were less than the
target concentration limits when using a mass balance
analysis design approach.
• Summary of savings for reduction of conditioned
outside air.
Capital Equipment Savings: $8,845.00
Operational Savings: $2,641.00 / year
Example 5 - North East ISD, San Antonio, TX
• 1 of 13 school districts in San
Antonio, TX.
• 62,000 students - increasing by
2,000 students per year.
• Elementary Schools: 42
• Middle Schools: 13
• High Schools: 7
Example 5 - New Schools
Operating Cost Savings
Net operating cost savings of over $2,000 per year for classroom addition.
• Twelve Schools
– 6 High Schools
– 4 Elementary Schools
– 2 Middle Schools
• 85 Separate HVAC Systems
– VAV Systems
– Roof Top Units
– Constant Volume Systems
Over 110,000 CFM of OA reduction!!
Example 5 – Schools, New Construction
Example 5 - Energy Cost Comparisons
Total energy Costs
IAQ
Procedure
Vent. Rate
Procedure
IAQ
Procedure
Vent. Rate
Procedure
Quarterly energy costs are up to $0.10 less per square foot of space.
•Bldg Type: Middle Schools (Selected Sites)
•056 - Tejeda M.S.
•050 - Bush M.S.
•057 - Lopez M.S.
•058 - Harris M.S.
•0.00 •0.05 •0.10 •0.15 •0.20 •0.25 •0.30
Example 5 - Sustainable Impacts
• Annual estimates for enhanced filtration and outdoor air
reduction:
• Outdoor Air Reduction = 9,760 cfm
– VRP2007 = 12,000 cfm
– IAQP2007 = 2,240 cfm
• Energy Related Savings = $11,900
– Electricity Savings = 68,897 kWh
– Gas Savings = 4,091 therms
• CO2 Emissions Reduction = 72 tons
Based on San Antonio, TX weather and utility rate data
Group 1 Group 2 Group 3 NEISD
MERV Av. Eff. % Av. Eff. % Av. Eff. % Standard
Valve (0.30 to 1.00) (1.00 to 3.00) (3.00 to 10.00) Application
1 n/a n/a E3<20
2 n/a n/a E3<20
3 n/a n/a E3<20 Window Unit
4 n/a n/a E3<20
5 n/a n/a 20<35
6 n/a n/a 35<50
7 n/a n/a 50<70
8 n/a n/a 70 Classrooms
9 n/a E2<50 85
10 n/a 50<65 85
11 n/a 65<80 85
12 n/a 80 90
13 E1<75 90 90
14 75<85 90 90
15 85<95 90 90 Near IS Hwy.
16 95 95 95 Rifle Ranges
Example 5 - Particulate Air Filter Types
Selected filters for removal of airborne particle contaminants.
Contaminant Guideline Limits VRP Levels VRP %
Ozone 0.08 ppm 0.104 130%
TVOC 1.0 ppm 0.764 76%
Formaldehyde 0.12 mg/m3 0.07 58%
Nitrogen Dioxide 0.053 ppm 0.017 32%
Carbon Monoxide 9 ppm 2.6 29%
Phenol 0.1 mg/m3 0.029 29%
Hydrogen Sulfide 0.04 mg/m3 0.008 22%
Ammonia 0.5 mg/m3 0.103 21%
Methyl Alcohol 1.5 mg/m3 0.228 15%
Sulfur Dioxide 0.03 ppm 0.004 13%
Acetone 7 mg/m3 0.171 2%
Example 5 - VRP Analysis
Unacceptable levels of contamination still possible with Ventilation Rate Procedure.
Example 5 - IAQ Procedure Analysis
Contaminant Guideline Limits IAQP Levels IAQP %
Ozone 0.08 ppm 0.024 30%
TVOC 1.0 ppm 0.483 48%
Formaldehyde 0.12 mg/m3 0.044 37%
Nitrogen Dioxide 0.053 ppm 0.004 7%
Carbon Monoxide 9 ppm 2.6 29%
Phenol 0.1 mg/m3 0.019 20%
Hydrogen Sulfide 0.04 mg/m3 0.006 14%
Ammonia 0.5 mg/m3 0.211 42%
Methyl Alcohol 1.5 mg/m3 0.153 10%
Sulfur Dioxide 0.03 ppm 0.0009 3%
Acetone 7 mg/m3 0.107 2%
Contaminant levels are less than 50% of Guideline Limits.
Example 5 - Classroom CO2 Levels
CO2 Monitoring shows that a classroom is empty for half of day-time hours.
Example 5 - Elementary Schools Experience
Use of medical inhalers by asthmatic students has been
reduced by as much as 50% from prior year’s usage!!
No complaints about IAQ from teachers!!
Example 5 - High Schools Experience
• IAQP – Primary solution for high school air quality
concerns.
• District’s evaluation favored the continued use of the IAQP.
• Currently available air cleaning technology can be used to
apply the IAQP.
• Additional school operational experience has
been successful in using the IAQP.
Example 5 - North East ISD Conclusions
• IAQP Summary.
– Enhanced air cleaning, both gas-phase & particulate decreased
outside air requirements.
– Decreased energy usage.
– Provided improved indoor air quality.
• Energy and environmental incentive.
– An IAQP design can reduce HVAC energy requirements,
saving money and cutting carbon emissions.
• Acceptable air quality & lower outdoor air
amounts.
– An IAQP Design incorporating enhanced air cleaning
can provide acceptable air quality with lower outdoor air.
The World According to 62.1
• What about those other guys?
– International Code Council and the International Mechanical
Code (IMC)
– U.S. Green Building Council and Leadership in Energy and
Environmental Design (LEED) Green Building Rating System
What about where the IMC is King?
• Section 105.2 on alternative materials, methods, equipment and
appliances.
“An alternative material or method of construction shall be
approved where… the proposed design is satisfactory and
complies with the intent of the provisions of this code…”
• Does not prevent the use of the IAQ Procedure.
What about LEED?
• LEED Indoor Environmental Quality (EQ) Prerequisite 1
requires that the mechanical ventilation system is to be
designed using the Ventilation Rate Procedure (VRP) of
Standard 62.1 or the applicable local code – whichever is
more stringent.
• There are LEED certified buildings located in non-
attainment areas for PM10 and PM2.5 as well as those
located in parts of the country where air cleaning
for ozone is required that are not in full
compliance with these provisions of the VRP.
LEED-NC and the IAQP?
“If I’m going for LEED certification AND I’m
required to use air cleaning for compliance with
the VRP anyway, why can’t I just go ahead and
use the IAQ Procedure?”
• A few questions remain about its application and some of
the design considerations that have to made.
– How many and which
contaminants are chosen for
modeling?
– What are the recommended
control levels?
LEED-NC and the IAQP?
It Can Be Done (and has been done)!
• Duke Energy Center, Charlotte, NC (USA)
– Owner demanded LEED certification AND to use
the IAQ Procedure for energy savings and IAQ.
– LEED consultants said:
– Owner said: “Find me a way!”
Result: “Wells Fargo’s Duke Energy
Center, in Charlotte, N.C., has
earned the U.S. Green Building
Council’s Leadership in Energy and
Environmental Design (LEED)
Platinum certification.”
(Environmental Leader, June 8, 2010).
The IAQP: Current Work
• ASHRAE Technical Resource Group (TRG 4.IAQP), IAQ
Procedure Development
– Developing specific guidance to allow users to apply the IAQP
method as defined under ASHRAE Standard 62.1.
• USGBC IAQ Performance Testing Working Group
(IAQP WG)
– Charged with developing a performance methodology
for IAQ using the IAQP as outlined in ASHRAE 62.1
as a basis.
– In order for a building to use gas phase filtration, the
manufacturer data from the testing performed on the
filters using ASHRAE Standard 145.2 is required.
LEED IAQP Pilot Credit
• Pilot Credit Intent
– To contribute to the comfort and well-being of building occupants
by establishing minimum standards for IAQ.
• Requirements
– This prerequisite is available for pilot testing by the following LEED
rating systems:
• New Construction
• Retail NC (excluding restaurants)
• Schools (excluding laboratories within school buildings)
• Commercial Interiors
• Retail CI (excluding restaurants)
• Existing Buildings Operation & Maintenance
IAQ Procedure for LEED
IAQP Pilot Credit presentation from Greenbuild 2012
• Part 1: Introduction and Credit Overview
– Amy Boyce, PE, LEED AP BD+C
• LEED Energy and Atmosphere Technical Specialist, USGBC
• Part 2: What Do You Do, What Do You Look For, and
How Do You Do It?
– Charlene Bayer, Ph.D.
• Hygieia Sciences LLC and The Georgia Institute of Technology
• Part 3: Applying the IAQ Procedure to Retail
and Office Buildings: Selected Case Studies
– Jeremy R. Poling, PE, LEED AP BD+C, LEED AP
O+M
• Goby LLC
Proceedings of Greenbuild 2012 – San Francisco, CA
IAQ Procedure for LEED
IEQ Pilot Credit 68
SO….• Not in LEED 2009 – alternate route used VOC testing to
receive credit, not health based.
• Recent emphasis on health issues is being brought to the
forefront in LEED v4.
– Heavy health emphasis – LEED v4 certification is not going to be
as easy as in previous versions.
– Applies to all buildings whether VRP or IAQP.
– Performance standards are used for everything.
– LEED vs. ASHRAE does not require gas-phase air filtration.
– Clearly defined occupant perception procedure.
– CoCs all have PELs and health-based endpoints and pilot program
is health-based.
IAQ PROCEDUREIAQ PROCEDUREVENTILATION RATE PROCEDUREVENTILATION RATE PROCEDURE
• Currently only option allowed
in LEED
• Basis for IMC code language
• Design, not performance
standard
– Difficult for existing buildings
• Prescriptive
– Does not take into account
individual building conditions
• Currently only option allowed
in LEED
• Basis for IMC code language
• Design, not performance
standard
– Difficult for existing buildings
• Prescriptive
– Does not take into account
individual building conditions
• Less defined
– Which contaminants to test for?
• Less used
– Not much public test data
available for Standard 145.2.
• Better option for existing
buildings
– Minimizes need to track down
existing documentation.
– Confirms or invalidates building’s
presumption of good IAQ.
• Less defined
– Which contaminants to test for?
• Less used
– Not much public test data
available for Standard 145.2.
• Better option for existing
buildings
– Minimizes need to track down
existing documentation.
– Confirms or invalidates building’s
presumption of good IAQ.
Determining Ventilation Rates
ASHRAE 62.1 VRP vs. IAQP
Proceedings of Greenbuild 2012 – San Francisco, CA
Pilot Credit Development
Alternative Compliance Path for IEQ Prerequisite 1
• Cross-disciplinary working group
– Engineers
– Industrial hygienists
– Filter manufacturers
– Owner groups
• Goals
– Defined contaminant list
– Include perceived IAQ
– Identify standards for testing that are both comprehensive yet not
overly onerous
• Available as Pilot ACP in the Pilot Credit Library
Proceedings of Greenbuild 2012 – San Francisco, CA
IEQ Pilot Credit 68
Indoor Air Quality Procedure
• Loosely follows structure
of 62.1, Section 6.3
• Four main parts:
– Contaminants of Concern
– Acceptable thresholds
– Testing procedures
– Corrective Action
http://www.usgbc.org/node/2616403?view=language
Proceedings of Greenbuild 2012 – San Francisco, CA
EXISTING BUILDINGSEXISTING BUILDINGSNEW CONSTRUCTIONNEW CONSTRUCTION
• Furnishings & building
materials
• Cleaning products
• Outdoor air
• People and Personal care
products
• Pesticides
• Cooking
• Plants
• Finishes, paints, varnishes
• Combustion devices
• Furnishings & building
materials
• Cleaning products
• Outdoor air
• People and Personal care
products
• Pesticides
• Cooking
• Plants
• Finishes, paints, varnishes
• Combustion devices
• Cleaning products
• People and Personal care
products
• Pesticides
• Outdoor air
• Cooking
• Plants
• Ventilation systems
• Furnishings
• Combustion devices
• Cleaning products
• People and Personal care
products
• Pesticides
• Outdoor air
• Cooking
• Plants
• Ventilation systems
• Furnishings
• Combustion devices
Typical Sources of Contaminants
Proceedings of Greenbuild 2012 – San Francisco, CA
ASHRAE STANDARD 62.1-
2013
Appendix B Tables
Selected CoCs and target
concentrations and regulations.
ASHRAE INDOOR AIR QUALITY
GUIDE: BEST PRACTICES FOR
DESIGN, CONSTRUCTION, &
COMMISSIONING
ASHRAE developed resource
covering the full range of IAQ
issues important to practitioners
in the building community.
ASHRAE PERFORMANCE
MEASUREMENT PROTOCOLS
FOR COMMERCIAL BUILDINGS
ASHRAE developed protocols
identifying what to measure, how
it is measured, and how often it is
measured.
Resources: Determining Contaminants
and Measurement Methods
Proceedings of Greenbuild 2012 – San Francisco, CA
CALIFORNIA DEPARTMENT OF PUBLIC HEALTH
Office of Environmental Health Hazard Assessment (OEHHA)
http://www.oehha.ca.gov/air/allrels.html
• List of acute, 8-hour, and chronic exposure levels
• Includes organic and inorganic gaseous pollutants, particulate
matter, and inorganic and metallic non-gaseous pollutants
• Target levels are health-based
• Hazard index and target organ-system listed
CALIFORNIA DEPARTMENT OF PUBLIC HEALTH
Office of Environmental Health Hazard Assessment (OEHHA)
http://www.oehha.ca.gov/air/allrels.html
• List of acute, 8-hour, and chronic exposure levels
• Includes organic and inorganic gaseous pollutants, particulate
matter, and inorganic and metallic non-gaseous pollutants
• Target levels are health-based
• Hazard index and target organ-system listed
Resources: Determining Contaminants
Proceedings of Greenbuild 2012 – San Francisco, CA
WORLD HEALTH ORGANIZATION (WHO)
Guidelines for indoor air quality: selected pollutants
http://www.euro.who.int/__data/assets/pdf_file/0009/128169/e94535.pdf
WORLD HEALTH ORGANIZATION (WHO)
Guidelines for indoor air quality: selected pollutants
http://www.euro.who.int/__data/assets/pdf_file/0009/128169/e94535.pdf
Guidelines and evidence to protect health globally from the
impact of indoor air pollutants by recommending target levels for
CoCs to significantly reduce exposure health risks and providing
a scientific basis for legally enforceable standards in all world
regions.
Benzene Carbon Monoxide
Formaldehyde Naphthalene
Nitrogen Dioxide Tetrachloroethylene
Radon Trichloroethylene
Polycyclic Aromatic Hydrocarbons
Resources: Determining Contaminants
Proceedings of Greenbuild 2012 – San Francisco, CA
Resources: Air Filter Testing
ASHRAE Standard 52.2-2012
• Method of Testing General
Ventilation Air-Cleaning
Devices for Removal
Efficiency by Particle Size
(ANSI Approved)
ASHRAE Standard 145.2-2011
• Laboratory Test Method for
Assessing the Performance
of Gas-Phase Air Cleaning
Systems: Air Cleaning
Devices (ANSI approved)
Resources: IAQ Testing
ASHRAE 189.1-2009: Standard for the Design of High-Performance
Green Buildings
• Section 10.3.1.4: Similar to LEED NC
• Post-Construction, Pre-Occupancy Baseline IAQ
Monitoring
– IAQ testing to be conducting with HVAC system operating using
protocols consistent with EPA Compendium, and ASTM Method
D5197
– Concentrations in HVAC return airstreams not to exceed
maximum concentration levels in Table 10.3.1.4
– Testing locations (choose either):
• One location per 25,000 ft2 (2,500 m2)
• In each contiguous floor air
Proceedings of Greenbuild 2012 – San Francisco, CA
• Section 10.3.2.1.4.5: Similar to LEED EBOM
• Plan for Operation documenting procedures for maintaining
& monitoring IAQ after occupancy
• Biennial monitoring of IAQ by one of 3 methods:
– IAQ testing
– Monitoring occupant perceptions of IAQ by any method
– Occupant complaint/response program for IEQ
Resources: IAQ Testing
ASHRAE 189.1-2009: Standard for the Design of High-Performance
Green Buildings
Proceedings of Greenbuild 2012 – San Francisco, CA
MUST DEMONSTRATE THAT MAXIMUM CONCENTRATION LEVELS OF
COCS ARE NOT EXCEEDED IN HVAC RETURN AIRSTREAM
Contaminant Maximum Allowable Concentration
Formaldehyde 33 ppb
Particulates (PM10) 150 ÎĽg/m3 (24-hr)
Particulates (PM25) 35 ÎĽg/m3 (24-hr)
TVOCs Shall be reported in accordance with CA/DHS/EHB/R-174
CO 9 ppm or < 2 ppm above outdoor levels
Ozone 0.075 ppm (8-hr)
Acetaldehyde 140 ÎĽg/m3
Benzene 60 ÎĽg/m3
Styrene 900 ÎĽg/m3
Phenol 200 ÎĽg/m3
Toluene 300 ÎĽg/m3
ASHRAE 189.1-2009
Selected CoCs in Table 10.3.1.4
Contaminant
Compound
Concentration
Limit
(µg/m3)
Contaminant
Compound
Concentration
Limit
(µg/m3)
Acetaldehyde 140 Formaldehyde 33
Benzene 60 Hexane (n-) 7,000
Carbon disulfide 800 Isophorone 2,000
Carbon tetrachloride 40 Isopropanol 7,000
Chlorobenzene 1000 Methyl chloroform 1,000
Chloroform 300 Methylene chloride 400
Dichlorobenzene (1,4-) 800 Methyl t-butyl ether 8,000
Dichloroethylene (1,1) 70 Naphthalene 9
Dimethylformamide (N,N-) 80 Phenol 200
Dioxane (1,4-) 3,000 Propylene glycol monomethyl ether 7,000
Epichlorohydrin 3 Styrene 900
Ethylbenzene 2,000 Tetrachloroethylene 35
Ethylene glycol 400 Toluene 300
Ethylene glycol monoethyl ether 70 Trichloroethylene 600
Ethylene glycol monoethyl ether acetate 300 Vinyl acetate 200
Ethylene glycol monomethyl ether 60 Xylenes 700
Ethylene glycol monomethyl ether acetate 90
IAQP – Alternate Compliance Path
EQpc68 | Required
LEED IAQP Pilot Credit
Summary and Conclusions
• The Indoor Air Quality Procedure may be used as an alternative
to the Ventilation Rate Procedure
• The IAQP provides a direct solution for reducing and controlling
contaminants.
• Allows for a more cost-effective solution to providing good air
quality since all design strategies may be
considered and compared.
• There is much more interest in using the IAQP now
that it can be used as part of the LEED certification
process.
…but it ain’t gonna be easy.
Summary and Conclusions (3)
Applying the IAQ Procedure shows that
using as little as 5 cfm/person of
outdoor air can reduce the total space
contaminant concentration to levels low
enough to be below published guidelines,
provide BETTER indoor air quality,
and meet the requirements of
ASHRAE Standard 62-2001-2013.
Contact Information
Chris Muller
Technical Director
Purafil, Inc.
2654 Weaver Way
Doraville, Georgia 30340
T: 770-662-8545 x349 F: 770-263-6922
E-mail: cmuller@purafil.com
Charlene Bayer
linkedin.com/charlenebayer
www.gtri.gatech.edu
charlene.bayer@gmail.com
twitter.com/charlenebayer
Amy Boyce
linkedin.com/in/amyboyce
www.usgbc.org
aboyce@usgbc.org
twitter.com/AmyLBoyce
Jeremy Poling
linkedin.com/in/jeremypoling
www.gobyllc.com
jpoling@gobyllc.com
Contacts
IEQ Pilot Credit 68: Indoor Air Quality Procedure

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ashrae 62.1

  • 1. ASHRAE Standard 62.1 The IAQ Procedure and LEED Chris Muller ASHRAE Distinguished Lecturer Technical Director - Purafil, Inc.
  • 2. Important Notice COPYRIGHT © 2014 by PURAFIL, INC. Neither this document nor any part may be reproduced or transmitted in any form or by any means, electronic or mechanical, including photocopying, microfilming, and recording, or by any information storage and retrieval system, without written permission from Purafil, Inc. Corporate Offices: Purafil, Inc.: 2654 Weaver Way, Doraville, Georgia 30340 U.S.A. Tel: 770-662-8545 Fax: 770-263-6922 Laboratory Fax: 770-263-0520 Page 2CIAQ Webinar – June 4, 2014
  • 3. Introduction • An important challenge today is how to improve and maintain IAQ in buildings while, at the same time, reducing their overall energy consumption. • One cannot discuss the issue of IAQ without giving some attention to the role that energy conservation measures may play.
  • 4. Introduction (2) • Ventilation standards and mechanical codes have evolved to address both IAQ and energy conservation. • Air cleaning technologies have developed to provide healthy and comfortable indoor environments. • There are ever-increasing numbers of applications for both particulate and gas- phase air filtration in HVAC system designs. – Selecting and specifying the appropriate control strategies requires special consideration.
  • 5. Introduction (3) • Air cleaning – for both particulate and gas- phase contaminants - can be a critical component in achieving acceptable Indoor Air Quality as well as implementing energy conservation measures with ASHRAE Standard 62.1-2013.
  • 6. Trending Towards “Net Zero” • A Net Zero Building is one that produces as much energy as it uses over the course of a year. – Net Zero Energy Buildings are by design very energy efficient and any remaining energy needs are typically met with on-site renewable energy. Understand that there is no such thing as a "zero energy building! EVERY building uses energy, or you may as well be in a cave!
  • 7. Net Zero – Momentum is Building
  • 8. ASHRAE Standard 62.1 62-1973 62-1981 62-1989 62.1-2001 62.1-2004 62.1-2010 ??? 62.1-2013
  • 9. ASHRAE Definition of Acceptable IAQ “Air in which there are no known contaminants at harmful concentrations as determined by cognizant authorities and with which a substantial majority (80% or more) of the people exposed do not express dissatisfaction.”
  • 10. • Since 2001, Standard 62.1 has been written to be code- enforceable containing only mandatory language. – New update to be published in 2013. • User’s Manual – First published in 2005, updated in 2007, 2010, and 2013, next scheduled update 2016. – Provides information on how to use and apply Standard 62.1 with practical examples of compliance. • Advanced IAQ Design Guide – Best practices for design, construction & commissioning. ASHRAE Standard 62.1-2013 Ventilation for Acceptable Indoor Air Quality
  • 11. ASHRAE Standard 62.1-2013 (2) Ventilation for Acceptable Indoor Air Quality • IAQ is based upon subjective criteria. – Comfort not health !! – Intended to minimize adverse health effects !! – Not carbon dioxide concentration !!!! • Ventilation Rate Procedure (VRP) – Minimum acceptable outdoor air quality !! – Requires air cleaning for ozone, PM10 and PM2.5 !! • Indoor Air Quality Procedure (IAQP) – Allows a balance to be struck between IAQ and energy conservation.
  • 12. Energy Conservation Potential Why Not Use the IAQ Procedure? • If you have to apply air cleaning for ozone, PM10, or PM2.5 the use of the IAQP could pay for upgrades to the air cleaning system AND provide for a reduction in overall HVAC operating costs. • The IAQP allows credit to be taken - in the form of a reduction of the outside air intake rate(s) for controls that remove contaminants and that result in indoor contaminant concentrations equal to or lower than those achieved using the ventilation rate procedure (VRP).
  • 13. IAQP Requirements • Specific requirements for compliance: – Outdoor Air Quality Investigation (Section 4) – Outdoor Air Treatment (Section 6.2.1) – Contaminant Sources (Section 6.3.1) • Identify contaminants of concern (COC) – Contaminant Concentration (Section 6.3.2) – Perceived Indoor Air Quality (Section 6.3.3) – Design Approaches (Section 6.3.4) – Documentation (Section 6.3.6)
  • 14. The IAQP and Energy Savings • The IAQP provides improved IAQ and reduces the amount of energy used to condition ventilation air. • It provides direct control of indoor air contaminants. • Many different applications can be designed using the IAQ Procedure. • The most common applications, and those with the greatest potential for capital cost savings and operational cost reductions, involve new construction and renovation.
  • 15. Example 1 - Movie Theater, New Construction • An engineer applied the IAQP in the construction of a new General Cinema movie theater in Houston, TX with air cleaning (filtration) and recirculation would be used in an effort to reduce the outdoor air below the 20 cfm per person prescribed by the VRP. • A reduction in the amount of outside air also meant that less air would have to be tempered by the HVAC system. Operational savings of $15,000/year.
  • 16. Example 2 - Office Building Renovation • An office building built in Atlanta, GA in the mid-1970s was being renovated for a new owner. • The IAQP was recommended and a cost/benefit analysis was performed. Item Amount Cost Avoided: $300,000 Energy Savings ($/yr): $10,400 Media Replacement ($/yr): + (US $21,000) Annual Operation: + (US $11,000) Time to Equalization: 28 years
  • 17. Example 3 - Lecture Hall, New Construction • Design considerations… • For all of the contaminants of concern, 5 cfm per person provided space concentrations less than the target concentrations and therefore complied with the requirements of the IAQP. • Summary of savings for reduction of conditioned outside air. Capital Equipment Savings: $8,643.00 Operational Savings: $1,136.00 / year
  • 18. Example 4 - Retail Store, New Construction • A retail store design with a number of different zone types… • All of the contaminants of concern were less than the target concentration limits when using a mass balance analysis design approach. • Summary of savings for reduction of conditioned outside air. Capital Equipment Savings: $8,845.00 Operational Savings: $2,641.00 / year
  • 19. Example 5 - North East ISD, San Antonio, TX • 1 of 13 school districts in San Antonio, TX. • 62,000 students - increasing by 2,000 students per year. • Elementary Schools: 42 • Middle Schools: 13 • High Schools: 7
  • 20. Example 5 - New Schools Operating Cost Savings Net operating cost savings of over $2,000 per year for classroom addition.
  • 21. • Twelve Schools – 6 High Schools – 4 Elementary Schools – 2 Middle Schools • 85 Separate HVAC Systems – VAV Systems – Roof Top Units – Constant Volume Systems Over 110,000 CFM of OA reduction!! Example 5 – Schools, New Construction
  • 22. Example 5 - Energy Cost Comparisons Total energy Costs IAQ Procedure Vent. Rate Procedure IAQ Procedure Vent. Rate Procedure Quarterly energy costs are up to $0.10 less per square foot of space. •Bldg Type: Middle Schools (Selected Sites) •056 - Tejeda M.S. •050 - Bush M.S. •057 - Lopez M.S. •058 - Harris M.S. •0.00 •0.05 •0.10 •0.15 •0.20 •0.25 •0.30
  • 23. Example 5 - Sustainable Impacts • Annual estimates for enhanced filtration and outdoor air reduction: • Outdoor Air Reduction = 9,760 cfm – VRP2007 = 12,000 cfm – IAQP2007 = 2,240 cfm • Energy Related Savings = $11,900 – Electricity Savings = 68,897 kWh – Gas Savings = 4,091 therms • CO2 Emissions Reduction = 72 tons Based on San Antonio, TX weather and utility rate data
  • 24. Group 1 Group 2 Group 3 NEISD MERV Av. Eff. % Av. Eff. % Av. Eff. % Standard Valve (0.30 to 1.00) (1.00 to 3.00) (3.00 to 10.00) Application 1 n/a n/a E3<20 2 n/a n/a E3<20 3 n/a n/a E3<20 Window Unit 4 n/a n/a E3<20 5 n/a n/a 20<35 6 n/a n/a 35<50 7 n/a n/a 50<70 8 n/a n/a 70 Classrooms 9 n/a E2<50 85 10 n/a 50<65 85 11 n/a 65<80 85 12 n/a 80 90 13 E1<75 90 90 14 75<85 90 90 15 85<95 90 90 Near IS Hwy. 16 95 95 95 Rifle Ranges Example 5 - Particulate Air Filter Types Selected filters for removal of airborne particle contaminants.
  • 25. Contaminant Guideline Limits VRP Levels VRP % Ozone 0.08 ppm 0.104 130% TVOC 1.0 ppm 0.764 76% Formaldehyde 0.12 mg/m3 0.07 58% Nitrogen Dioxide 0.053 ppm 0.017 32% Carbon Monoxide 9 ppm 2.6 29% Phenol 0.1 mg/m3 0.029 29% Hydrogen Sulfide 0.04 mg/m3 0.008 22% Ammonia 0.5 mg/m3 0.103 21% Methyl Alcohol 1.5 mg/m3 0.228 15% Sulfur Dioxide 0.03 ppm 0.004 13% Acetone 7 mg/m3 0.171 2% Example 5 - VRP Analysis Unacceptable levels of contamination still possible with Ventilation Rate Procedure.
  • 26. Example 5 - IAQ Procedure Analysis Contaminant Guideline Limits IAQP Levels IAQP % Ozone 0.08 ppm 0.024 30% TVOC 1.0 ppm 0.483 48% Formaldehyde 0.12 mg/m3 0.044 37% Nitrogen Dioxide 0.053 ppm 0.004 7% Carbon Monoxide 9 ppm 2.6 29% Phenol 0.1 mg/m3 0.019 20% Hydrogen Sulfide 0.04 mg/m3 0.006 14% Ammonia 0.5 mg/m3 0.211 42% Methyl Alcohol 1.5 mg/m3 0.153 10% Sulfur Dioxide 0.03 ppm 0.0009 3% Acetone 7 mg/m3 0.107 2% Contaminant levels are less than 50% of Guideline Limits.
  • 27. Example 5 - Classroom CO2 Levels CO2 Monitoring shows that a classroom is empty for half of day-time hours.
  • 28. Example 5 - Elementary Schools Experience Use of medical inhalers by asthmatic students has been reduced by as much as 50% from prior year’s usage!! No complaints about IAQ from teachers!!
  • 29. Example 5 - High Schools Experience • IAQP – Primary solution for high school air quality concerns. • District’s evaluation favored the continued use of the IAQP. • Currently available air cleaning technology can be used to apply the IAQP. • Additional school operational experience has been successful in using the IAQP.
  • 30. Example 5 - North East ISD Conclusions • IAQP Summary. – Enhanced air cleaning, both gas-phase & particulate decreased outside air requirements. – Decreased energy usage. – Provided improved indoor air quality. • Energy and environmental incentive. – An IAQP design can reduce HVAC energy requirements, saving money and cutting carbon emissions. • Acceptable air quality & lower outdoor air amounts. – An IAQP Design incorporating enhanced air cleaning can provide acceptable air quality with lower outdoor air.
  • 31. The World According to 62.1 • What about those other guys? – International Code Council and the International Mechanical Code (IMC) – U.S. Green Building Council and Leadership in Energy and Environmental Design (LEED) Green Building Rating System
  • 32. What about where the IMC is King? • Section 105.2 on alternative materials, methods, equipment and appliances. “An alternative material or method of construction shall be approved where… the proposed design is satisfactory and complies with the intent of the provisions of this code…” • Does not prevent the use of the IAQ Procedure.
  • 33. What about LEED? • LEED Indoor Environmental Quality (EQ) Prerequisite 1 requires that the mechanical ventilation system is to be designed using the Ventilation Rate Procedure (VRP) of Standard 62.1 or the applicable local code – whichever is more stringent. • There are LEED certified buildings located in non- attainment areas for PM10 and PM2.5 as well as those located in parts of the country where air cleaning for ozone is required that are not in full compliance with these provisions of the VRP.
  • 34. LEED-NC and the IAQP? “If I’m going for LEED certification AND I’m required to use air cleaning for compliance with the VRP anyway, why can’t I just go ahead and use the IAQ Procedure?” • A few questions remain about its application and some of the design considerations that have to made. – How many and which contaminants are chosen for modeling? – What are the recommended control levels?
  • 35. LEED-NC and the IAQP? It Can Be Done (and has been done)! • Duke Energy Center, Charlotte, NC (USA) – Owner demanded LEED certification AND to use the IAQ Procedure for energy savings and IAQ. – LEED consultants said: – Owner said: “Find me a way!” Result: “Wells Fargo’s Duke Energy Center, in Charlotte, N.C., has earned the U.S. Green Building Council’s Leadership in Energy and Environmental Design (LEED) Platinum certification.” (Environmental Leader, June 8, 2010).
  • 36. The IAQP: Current Work • ASHRAE Technical Resource Group (TRG 4.IAQP), IAQ Procedure Development – Developing specific guidance to allow users to apply the IAQP method as defined under ASHRAE Standard 62.1. • USGBC IAQ Performance Testing Working Group (IAQP WG) – Charged with developing a performance methodology for IAQ using the IAQP as outlined in ASHRAE 62.1 as a basis. – In order for a building to use gas phase filtration, the manufacturer data from the testing performed on the filters using ASHRAE Standard 145.2 is required.
  • 37. LEED IAQP Pilot Credit • Pilot Credit Intent – To contribute to the comfort and well-being of building occupants by establishing minimum standards for IAQ. • Requirements – This prerequisite is available for pilot testing by the following LEED rating systems: • New Construction • Retail NC (excluding restaurants) • Schools (excluding laboratories within school buildings) • Commercial Interiors • Retail CI (excluding restaurants) • Existing Buildings Operation & Maintenance
  • 38. IAQ Procedure for LEED IAQP Pilot Credit presentation from Greenbuild 2012 • Part 1: Introduction and Credit Overview – Amy Boyce, PE, LEED AP BD+C • LEED Energy and Atmosphere Technical Specialist, USGBC • Part 2: What Do You Do, What Do You Look For, and How Do You Do It? – Charlene Bayer, Ph.D. • Hygieia Sciences LLC and The Georgia Institute of Technology • Part 3: Applying the IAQ Procedure to Retail and Office Buildings: Selected Case Studies – Jeremy R. Poling, PE, LEED AP BD+C, LEED AP O+M • Goby LLC Proceedings of Greenbuild 2012 – San Francisco, CA
  • 39. IAQ Procedure for LEED IEQ Pilot Credit 68 SO….• Not in LEED 2009 – alternate route used VOC testing to receive credit, not health based. • Recent emphasis on health issues is being brought to the forefront in LEED v4. – Heavy health emphasis – LEED v4 certification is not going to be as easy as in previous versions. – Applies to all buildings whether VRP or IAQP. – Performance standards are used for everything. – LEED vs. ASHRAE does not require gas-phase air filtration. – Clearly defined occupant perception procedure. – CoCs all have PELs and health-based endpoints and pilot program is health-based.
  • 40. IAQ PROCEDUREIAQ PROCEDUREVENTILATION RATE PROCEDUREVENTILATION RATE PROCEDURE • Currently only option allowed in LEED • Basis for IMC code language • Design, not performance standard – Difficult for existing buildings • Prescriptive – Does not take into account individual building conditions • Currently only option allowed in LEED • Basis for IMC code language • Design, not performance standard – Difficult for existing buildings • Prescriptive – Does not take into account individual building conditions • Less defined – Which contaminants to test for? • Less used – Not much public test data available for Standard 145.2. • Better option for existing buildings – Minimizes need to track down existing documentation. – Confirms or invalidates building’s presumption of good IAQ. • Less defined – Which contaminants to test for? • Less used – Not much public test data available for Standard 145.2. • Better option for existing buildings – Minimizes need to track down existing documentation. – Confirms or invalidates building’s presumption of good IAQ. Determining Ventilation Rates ASHRAE 62.1 VRP vs. IAQP Proceedings of Greenbuild 2012 – San Francisco, CA
  • 41. Pilot Credit Development Alternative Compliance Path for IEQ Prerequisite 1 • Cross-disciplinary working group – Engineers – Industrial hygienists – Filter manufacturers – Owner groups • Goals – Defined contaminant list – Include perceived IAQ – Identify standards for testing that are both comprehensive yet not overly onerous • Available as Pilot ACP in the Pilot Credit Library Proceedings of Greenbuild 2012 – San Francisco, CA
  • 42. IEQ Pilot Credit 68 Indoor Air Quality Procedure • Loosely follows structure of 62.1, Section 6.3 • Four main parts: – Contaminants of Concern – Acceptable thresholds – Testing procedures – Corrective Action http://www.usgbc.org/node/2616403?view=language Proceedings of Greenbuild 2012 – San Francisco, CA
  • 43. EXISTING BUILDINGSEXISTING BUILDINGSNEW CONSTRUCTIONNEW CONSTRUCTION • Furnishings & building materials • Cleaning products • Outdoor air • People and Personal care products • Pesticides • Cooking • Plants • Finishes, paints, varnishes • Combustion devices • Furnishings & building materials • Cleaning products • Outdoor air • People and Personal care products • Pesticides • Cooking • Plants • Finishes, paints, varnishes • Combustion devices • Cleaning products • People and Personal care products • Pesticides • Outdoor air • Cooking • Plants • Ventilation systems • Furnishings • Combustion devices • Cleaning products • People and Personal care products • Pesticides • Outdoor air • Cooking • Plants • Ventilation systems • Furnishings • Combustion devices Typical Sources of Contaminants Proceedings of Greenbuild 2012 – San Francisco, CA
  • 44. ASHRAE STANDARD 62.1- 2013 Appendix B Tables Selected CoCs and target concentrations and regulations. ASHRAE INDOOR AIR QUALITY GUIDE: BEST PRACTICES FOR DESIGN, CONSTRUCTION, & COMMISSIONING ASHRAE developed resource covering the full range of IAQ issues important to practitioners in the building community. ASHRAE PERFORMANCE MEASUREMENT PROTOCOLS FOR COMMERCIAL BUILDINGS ASHRAE developed protocols identifying what to measure, how it is measured, and how often it is measured. Resources: Determining Contaminants and Measurement Methods Proceedings of Greenbuild 2012 – San Francisco, CA
  • 45. CALIFORNIA DEPARTMENT OF PUBLIC HEALTH Office of Environmental Health Hazard Assessment (OEHHA) http://www.oehha.ca.gov/air/allrels.html • List of acute, 8-hour, and chronic exposure levels • Includes organic and inorganic gaseous pollutants, particulate matter, and inorganic and metallic non-gaseous pollutants • Target levels are health-based • Hazard index and target organ-system listed CALIFORNIA DEPARTMENT OF PUBLIC HEALTH Office of Environmental Health Hazard Assessment (OEHHA) http://www.oehha.ca.gov/air/allrels.html • List of acute, 8-hour, and chronic exposure levels • Includes organic and inorganic gaseous pollutants, particulate matter, and inorganic and metallic non-gaseous pollutants • Target levels are health-based • Hazard index and target organ-system listed Resources: Determining Contaminants Proceedings of Greenbuild 2012 – San Francisco, CA
  • 46. WORLD HEALTH ORGANIZATION (WHO) Guidelines for indoor air quality: selected pollutants http://www.euro.who.int/__data/assets/pdf_file/0009/128169/e94535.pdf WORLD HEALTH ORGANIZATION (WHO) Guidelines for indoor air quality: selected pollutants http://www.euro.who.int/__data/assets/pdf_file/0009/128169/e94535.pdf Guidelines and evidence to protect health globally from the impact of indoor air pollutants by recommending target levels for CoCs to significantly reduce exposure health risks and providing a scientific basis for legally enforceable standards in all world regions. Benzene Carbon Monoxide Formaldehyde Naphthalene Nitrogen Dioxide Tetrachloroethylene Radon Trichloroethylene Polycyclic Aromatic Hydrocarbons Resources: Determining Contaminants Proceedings of Greenbuild 2012 – San Francisco, CA
  • 47. Resources: Air Filter Testing ASHRAE Standard 52.2-2012 • Method of Testing General Ventilation Air-Cleaning Devices for Removal Efficiency by Particle Size (ANSI Approved) ASHRAE Standard 145.2-2011 • Laboratory Test Method for Assessing the Performance of Gas-Phase Air Cleaning Systems: Air Cleaning Devices (ANSI approved)
  • 48. Resources: IAQ Testing ASHRAE 189.1-2009: Standard for the Design of High-Performance Green Buildings • Section 10.3.1.4: Similar to LEED NC • Post-Construction, Pre-Occupancy Baseline IAQ Monitoring – IAQ testing to be conducting with HVAC system operating using protocols consistent with EPA Compendium, and ASTM Method D5197 – Concentrations in HVAC return airstreams not to exceed maximum concentration levels in Table 10.3.1.4 – Testing locations (choose either): • One location per 25,000 ft2 (2,500 m2) • In each contiguous floor air Proceedings of Greenbuild 2012 – San Francisco, CA
  • 49. • Section 10.3.2.1.4.5: Similar to LEED EBOM • Plan for Operation documenting procedures for maintaining & monitoring IAQ after occupancy • Biennial monitoring of IAQ by one of 3 methods: – IAQ testing – Monitoring occupant perceptions of IAQ by any method – Occupant complaint/response program for IEQ Resources: IAQ Testing ASHRAE 189.1-2009: Standard for the Design of High-Performance Green Buildings Proceedings of Greenbuild 2012 – San Francisco, CA
  • 50. MUST DEMONSTRATE THAT MAXIMUM CONCENTRATION LEVELS OF COCS ARE NOT EXCEEDED IN HVAC RETURN AIRSTREAM Contaminant Maximum Allowable Concentration Formaldehyde 33 ppb Particulates (PM10) 150 ÎĽg/m3 (24-hr) Particulates (PM25) 35 ÎĽg/m3 (24-hr) TVOCs Shall be reported in accordance with CA/DHS/EHB/R-174 CO 9 ppm or < 2 ppm above outdoor levels Ozone 0.075 ppm (8-hr) Acetaldehyde 140 ÎĽg/m3 Benzene 60 ÎĽg/m3 Styrene 900 ÎĽg/m3 Phenol 200 ÎĽg/m3 Toluene 300 ÎĽg/m3 ASHRAE 189.1-2009 Selected CoCs in Table 10.3.1.4
  • 51. Contaminant Compound Concentration Limit (µg/m3) Contaminant Compound Concentration Limit (µg/m3) Acetaldehyde 140 Formaldehyde 33 Benzene 60 Hexane (n-) 7,000 Carbon disulfide 800 Isophorone 2,000 Carbon tetrachloride 40 Isopropanol 7,000 Chlorobenzene 1000 Methyl chloroform 1,000 Chloroform 300 Methylene chloride 400 Dichlorobenzene (1,4-) 800 Methyl t-butyl ether 8,000 Dichloroethylene (1,1) 70 Naphthalene 9 Dimethylformamide (N,N-) 80 Phenol 200 Dioxane (1,4-) 3,000 Propylene glycol monomethyl ether 7,000 Epichlorohydrin 3 Styrene 900 Ethylbenzene 2,000 Tetrachloroethylene 35 Ethylene glycol 400 Toluene 300 Ethylene glycol monoethyl ether 70 Trichloroethylene 600 Ethylene glycol monoethyl ether acetate 300 Vinyl acetate 200 Ethylene glycol monomethyl ether 60 Xylenes 700 Ethylene glycol monomethyl ether acetate 90 IAQP – Alternate Compliance Path EQpc68 | Required
  • 52. LEED IAQP Pilot Credit
  • 53. Summary and Conclusions • The Indoor Air Quality Procedure may be used as an alternative to the Ventilation Rate Procedure • The IAQP provides a direct solution for reducing and controlling contaminants. • Allows for a more cost-effective solution to providing good air quality since all design strategies may be considered and compared. • There is much more interest in using the IAQP now that it can be used as part of the LEED certification process. …but it ain’t gonna be easy.
  • 54. Summary and Conclusions (3) Applying the IAQ Procedure shows that using as little as 5 cfm/person of outdoor air can reduce the total space contaminant concentration to levels low enough to be below published guidelines, provide BETTER indoor air quality, and meet the requirements of ASHRAE Standard 62-2001-2013.
  • 55. Contact Information Chris Muller Technical Director Purafil, Inc. 2654 Weaver Way Doraville, Georgia 30340 T: 770-662-8545 x349 F: 770-263-6922 E-mail: cmuller@purafil.com