New technologies and architectures for sensing gases and particles in air are emerging for criteria pollutants, air toxics, and greenhouse gases. These.

Slides:



Advertisements
Similar presentations
AREP GAW Section 4 What Are We Forecasting? What is in the Air? What Are We Forecasting? Pollutants Units of Measure Averaging Time Spatial Scale.
Advertisements

Sensor Operating Theory
Office of Research and Development Frank Princiotta, Director, Air Pollution Prevention & Control Division, National Risk Management Research laboratory.
1 Policies for Addressing PM2.5 Precursor Emissions Rich Damberg EPA Office of Air Quality Planning and Standards June 20, 2007.
Basic Air Monitoring Concepts And Use Of The Altair 4 Gas Meter
IAQ Sampling Document a condition or state of the space –Adequate ventilation –Comfort Identify source of contamination –Leakage –Products.
Developments in EMEP monitoring strategy and recommendations from AirMonTech Kjetil Tørseth, NILU/EMEP-CCC.
Personal Monitoring for Air Pollution Exposure Philip M. Fine, Ph.D. Atmospheric Measurements Manager South Coast Air Quality Management District CAPCOA.
MULTI-GAS MONITOR FOR CONFINED SPACE APPLICATIONS
Major Types of Air Pollution Environmental Science.
Air Quality Management in Mumbai V.K.Phatak MMRDA.
Livestock Industry: Environmental, Health & Legislation Issues Pius Ndegwa Nutrient Management & Air Quality Specialist Biological Systems Engineering.
Air Quality Impact Analysis 1.Establish a relationship between emissions and air quality. AQ past = a EM past + b 2.A change in emissions results in an.
Air Quality, Atmospheric Deposition, and Lake Tahoe October 15, 2003 Western Regional Pollution Prevention Network Grannlibakken, Lake Tahoe Jim Pederson.
Air Quality Laboratory St.Louis Supersite Project Update Meg N.S. Yu Professor Jay R. Turner Environmental Engineering Program Washington University in.
Reducing risk with Exposure Monitoring Equipment.
1 One facility, two very different emissions. Module 5. Air Pollutant Emissions in the Mid-Atlantic United States by K.G. Paterson, Ph.D., P.E. © 2007.
ESP v2.0: Improved method for projecting U.S. greenhouse gas and air pollutant emissions through 2055 Dan Loughlin 1, Limei Ran 2, Dongmei Yang 2, Zac.
June 12 &13, 2007 Mickey Leland National Urban Air Toxics Workshop II – Houston, Texas 1 Albuquerque, New Mexico Community Scale Ambient Air Monitoring.
Air Pollution Is Tootin Pollutin?. The Science of Farting  The word "FART" can stand for: –Frequency Actuated Rectal Tremor  a.k.a. Flatulence or Intestinal.
EPA’s Related Programs and Coordination with NASA Presentation to the NASA Environmental Compatibility IV Workshop, August 12-13, Colorado Springs, CO.
Importance of Lightning NO for Regional Air Quality Modeling Thomas E. Pierce/NOAA Atmospheric Modeling Division National Exposure Research Laboratory.
1 Saxony-Anhalt EU Twinning RO 04/IB/EN/09 State Environmental Protection Agency Wolfgang GarcheWorkshop European Standards Requirements of.
Properties of Particulate Matter Physical, Chemical and Optical Properties Size Range of Particulate Matter Mass Distribution of PM vs. Size: PM10, PM2.5.
Field Methods of Monitoring Atmospheric Systems Measurement of Air Pollution Copyright © 2009 by DBS.
Global Ozone Project Curriculum
Next Generation Air Monitoring: An Overview of US EPA Activities National Air Quality Conference RTP, NC February 12, 2014 Tim Watkins US EPA/Office of.
Observations The collection of slope values were plotted against time and box plots show the distribution for each of the six daily trips of the vessel.
2015 INTERNATIONAL EMISSIONS INVENTORY CONFERENCE: APRIL 14, 2015 DEVELOPING CALIFORNIA EMISSION INVENTORIES: INNOVATION AND CHALLENGES.
H2S Gas Meter/Detector. Introduction Air monitoring data is useful for: *Assessing the health risks to the public and response workers. *Selecting personal.
Bourns College of Engineering – Center for Environmental Research and Technology University of California, Riverside Evaluation of Emissions/Residue Testing.
Urban Air Pollution GISAT 112. Learning Objectives Regions of the atmosphere Amount, composition of air we breathe Names of selected air pollutants Health.
1.
Talking About Air Toxics John D. Wilson Galveston-Houston Association for Smog Prevention
Dieterich, M.F., Gieseler, M.E., Short, D.B., and Signorelli, R.T. Abstract Formaldehyde, a group 1 carcinogen is a component of indoor air and may be.
Managing Smoke and Emissions. A new system for managing smoke and emissions in Victoria that will provide for coordinated: Investment Service delivery.
Exhaust Emissions & Air Pollution
Janice Lam Snyder, SMAQMD December 11, 2015
Opening Remarks -- Ozone and Particles: Policy and Science Recent Developments & Controversial Issues GERMAN-US WORKSHOP October 9, 2002 G. Foley *US EPA.
Air Pollution Research Group Analysis of 1999 TRI Data to Identify High Environmental Risk Areas of Ohio by Amit Joshi.
Low-cost Sensor Packages for Roadside Emissions Factor Estimation CMAS – 10/7/2015 KAROLINE K. JOHNSON, MICHAEL H. BERGIN, DUKE UNIVERSITY ARMISTEAD G.
W. T. Hutzell 1, G. Pouliot 2, and D. J. Luecken 1 1 Atmospheric Modeling Division, U. S. Environmental Protection Agency 2 Atmospheric Sciences Modeling.
Breakout Session 1 Air Quality Jack Fishman, Randy Kawa August 18.
Lecture-3. Primary air pollutants - Materials that when released pose health risks in their unmodified forms or those emitted directly from identifiable.
1 LANDFILL GAS TRAINING. 2 INTRODUCTION  TYPE OF MONITORING -Screening -Specialized  GOALS.
Outdoor Air Pollution Miller 17-1/17-2. Air Pollution One or more chemicals in concentrations high enough in the atmosphere to cause harm to life forms.
TOWARDS A TEST METHOD FOR HYDROGEN SENSOR PERFORMANCE NATHAN D. MARSH AND THOMAS G. CLEARY Fire Research Division, National Institute of Standards and.
Properties of Particulate Matter
Human Impact on the Atmosphere Human Impact on the Atmosphere Chapters 18 and 19 Living in the Environment, 11 th Edition, Miller Advanced Placement Environmental.
Misuse of Combustible Gas Meters Supervisor Training 1/11/08.
Ozone Budget From: Jacob. Ozone in the Atmosphere Lifetime: –~1 month –Highly variable – dependent on season, latitude, altitude, etc. Background concentrations:
AIR CLIMATE & ENERGY RESEARCH PROGRAM B U I L D I N G A S C I E N T I F I C F O U N D A T I O N F O R S O U N D E N V I R O N M.
Garfield County Air Quality Monitoring Network Cassie Archuleta Project Scientist Board of County Commissioners – Regular Meeting.
Environmental Science 5e
Chapter 24 Air Pollution. Stationary and Mobile Sources of Air Pollution Two Sources of Air Pollution 1. Stationary Sources: have a relatively fixed location.
Statewide Compliance Monitoring and Local Monitoring Projects
Ch. 18 Air Pollution.
Stack Sampling.
Background to Atmospheric Pollution
Modeling of Air Pollutants Dispersion from
Air Pollution Monitoring in Cities
آلودگی هوا و روشهای کنترل آن
Natural Cleaning Process of the Atmosphere
Air Monitoring Trends in New Jersey
Air Pollutants 200 Air pollutants are recognized and assessed by the USEPA Listed in the Clean Air Act.
B.O. bot Christopher Thomas EEL5666 IMDL Fall 2008 Date: 09/16/2008
1 Polluscope project from the sensors selection to their deployment during field campaigns involving volunteers B. Languille1, V. Gros1, N. Bonnaire1,
Bracelet Hardware Platform Implementation and Data Analysis
Contributions to total changes in emissions of ozone precursors
Editors: Alastair Lewis, Erika von Schneidemesser and Richard Peltier
Presentation transcript:

New technologies and architectures for sensing gases and particles in air are emerging for criteria pollutants, air toxics, and greenhouse gases. These technologies are generally designed to be mass-fabricated through innovative processes (e.g., microfabrication) and are (1) small; (2) able to autonomously and directly measure pollutant levels; (3) have low power consumption; and (4) support flexible deployment options [White et al. Environmental Manager, pp , May 2012]. These traits translate to reduced total cost of ownership, consideration of a higher spatial density of air pollution measurements and personal exposure applications. Measurements from the existing national air monitoring network can be used to infer community-wide concentrations of ozone and fine particle (< 2.5 µm) mass. However, other pollutants directly emitted into the air, such as elemental carbon, coarse particles (between 2.5 and 10 µm), carbon monoxide (CO), nitrogen oxides (NOx), and various air toxics have been shown to have much higher variability between regional air pollution monitors compared to pollutants formed in the atmosphere like ozone. Portable air pollution sensors can potentially provide more location-specific information desired by individuals and communities, and needed by exposure and health scientists to improve air quality risk assessments. There is also a desire to use portable sensors to monitor indicator pollutants or classes of pollutants, like methane and total volatile organic compounds (VOCs), as well as nuisance pollutants, like hydrogen sulfide (H2S) and ammonia, which indicate the presence of pollution sources. Current technologies for portable sensors for air pollutant gases reviewed include: electrochemical, metal oxide, spectroscopic, ionization, and pellistor sensors. Current technologies for portable particle sensors include: light scattering, light absorption, and those based on a change in frequency of an oscillating impaction surface. Attributes that indicate the appropriateness of these technologies for sensing the pollutants mentioned above are presented including: estimated range of measurement, selectivity (when applicable), appropriate deployment platforms, response and recovery time, battery lifetime, and expected range of acceptable operating conditions. Information also will be provided about the potential of emerging sensor technologies to address the deficiencies in the abilities of existing sensor technologies to measure these pollutants. New technologies and architectures for sensing gases and particles in air are emerging for criteria pollutants, air toxics, and greenhouse gases. These technologies are generally designed to be mass-fabricated through innovative processes (e.g., microfabrication) and are (1) small; (2) able to autonomously and directly measure pollutant levels; (3) have low power consumption; and (4) support flexible deployment options [White et al. Environmental Manager, pp , May 2012]. These traits translate to reduced total cost of ownership, consideration of a higher spatial density of air pollution measurements and personal exposure applications. Measurements from the existing national air monitoring network can be used to infer community-wide concentrations of ozone and fine particle (< 2.5 µm) mass. However, other pollutants directly emitted into the air, such as elemental carbon, coarse particles (between 2.5 and 10 µm), carbon monoxide (CO), nitrogen oxides (NOx), and various air toxics have been shown to have much higher variability between regional air pollution monitors compared to pollutants formed in the atmosphere like ozone. Portable air pollution sensors can potentially provide more location-specific information desired by individuals and communities, and needed by exposure and health scientists to improve air quality risk assessments. There is also a desire to use portable sensors to monitor indicator pollutants or classes of pollutants, like methane and total volatile organic compounds (VOCs), as well as nuisance pollutants, like hydrogen sulfide (H2S) and ammonia, which indicate the presence of pollution sources. Current technologies for portable sensors for air pollutant gases reviewed include: electrochemical, metal oxide, spectroscopic, ionization, and pellistor sensors. Current technologies for portable particle sensors include: light scattering, light absorption, and those based on a change in frequency of an oscillating impaction surface. Attributes that indicate the appropriateness of these technologies for sensing the pollutants mentioned above are presented including: estimated range of measurement, selectivity (when applicable), appropriate deployment platforms, response and recovery time, battery lifetime, and expected range of acceptable operating conditions. Information also will be provided about the potential of emerging sensor technologies to address the deficiencies in the abilities of existing sensor technologies to measure these pollutants. Next-Generation Air Monitoring - A Review of Portable Air Pollution Sensors Emily Snyder 1, Paul A. Solomon 2, Margaret MacDonell 3, Ronald Williams 2, Eben Thoma 4, Dena Vallano 5, Michelle Raymond 3, and David Olson 2 1 Environmental Protection Agency, Office of Research and Development, National Homeland Security Research Center, 2 Environmental Protection Agency, Office of Research and Development, National Exposure Research Laboratory, 3 Argonne National Laboratory, 4 Environmental Protection Agency, Office of Research and Development, National Risk Management Research Laboratory, 5 American Association for the Advancement of Science Fellow at EPA’s Office of Research and Development, Washington, D.C. Abstract Motivation for Next Gen Portable Air Pollution Sensor Technologies Technology Review Approach Current Technology – Fundamental Approaches Acknowledgements Contact: Paul Solomon, Ronald Williams, Scope of the Review: Real time or continuous monitoring technologies involving select gases or particles of interest (did not include sensors that detect classes of pollutants only). Only lower-cost (<10 K) portable systems were included. Pollutants of Interest Approach:  Reviewed publications, vendor websites, and patents  Detection limits were taken from independent evaluations (Environmental Technology Verification, peer reviewed publications) where available; otherwise vendor provided information was included  Cost estimates were based on a equipment AND required infrastructure  Tried to capture many different sensor systems for the gas phase pollutants Scope of the Review: Real time or continuous monitoring technologies involving select gases or particles of interest (did not include sensors that detect classes of pollutants only). Only lower-cost (<10 K) portable systems were included. Pollutants of Interest Approach:  Reviewed publications, vendor websites, and patents  Detection limits were taken from independent evaluations (Environmental Technology Verification, peer reviewed publications) where available; otherwise vendor provided information was included  Cost estimates were based on a equipment AND required infrastructure  Tried to capture many different sensor systems for the gas phase pollutants Spatially varying criteria pollutants CO, SO2, NO2, PM A subset of Hazardous Air Pollutants (HAPs) formaldehyde, acetaldehyde, benzene, 1,3-butadiene Indicator pollutants ammonia, total VOCs, hydrogen sulfide, and methane Electrochemical Sensors Metal Oxide Gas Sensors Gas Phase Pollutants* * Particulate Phase Pollutants Spectroscopic Sensors Light Scattering Light Absorption Results of Review (Gases) Sensor Type Pollutants Measured from List RangeSelectivity Response times, seconds Range of operating conditions Other Considerations Electrochemical Sensors Benzene*, H 2 S, NH 3, CO, SO 2, NO 2, O 3 single ppb /1 ppm to up to 10 /1200 ppm Not selective but characterized % RH (some have lower upper RH tolerances), 0 to 40 °C Short sensor lifetimes (1-2 years) Metal Oxide Sensors non-methane hydrocarbons, benzene, methane, CO, NO 2, NH 3, SO 2, total VOCs, NOx typically single ppb/0.1 ppm to ppm. Not selective and not well characterized % RH, - 10°C to +50°C, sensitive to changes in RH, T, and P Issues with sensor drift Spectroscopic Sensors NO (chemiluminscence), CH 4, VOCs (NDIR) DL is 9 ppb for NO, NDIR % range Selective for chemiluminscence /-20°C to +50/55 °C and 0/10 % RH - 95%RH Limitations on ability to make selective sensors inexpensive Results of Review (PM)  Mass concentration and physical properties are measured. There are no commercially available direct particle mass sensors.  Performance  Light scattering sensors - lower particle size detected ranges from 0.3 to 3.0 µm  Light absorption sensor - limit of detection of 0.16 µg/m 3  Accuracy for the light scattering systems (where available) range from ±5-10 % relative to the calibration aerosol  Mass concentration and physical properties are measured. There are no commercially available direct particle mass sensors.  Performance  Light scattering sensors - lower particle size detected ranges from 0.3 to 3.0 µm  Light absorption sensor - limit of detection of 0.16 µg/m 3  Accuracy for the light scattering systems (where available) range from ±5-10 % relative to the calibration aerosol Technology Gaps and Potential Emerging Technologies  Many of these sensor systems do not have the detection limits required to measure ambient levels of these pollutants  Many of the sensors suffer from selectivity issues and/or impacts of high RH.  There are no direct mass PM sensors and the light scattering sensors do not measure ultrafine PM  Very few of these systems have been rigorously tested *Ionization is another fundamental sensing approach but was not included because it is not specific unless used in concert with a sorbent tube. The authors would like to acknowledge Michelle Raymond, David Wyker, Molly Finster, Young-Soo Chang, Thomas Raymond, Marcienne Scofield, and Bianca Temple for the exposure bench-mark plot. *uses a pyrolizer to convert benzene to CO for electrochemical detection. Personalized Medicine Education Hot Spot Measurements (by individuals or communities) Informational (higher spatial and temporal data) Emerging Sensors for Gas Phase Pollutants - Examples of Emerging Technologies and their Potential Performance for Benzene Sensing Emerging Sensors for PM - Two systems are currently being developed for direct mass PM measurement  Quartz Crystal Microbalance (QCM) – Measures mass through Impaction on piezoelectric sensors  MEMS-PM - Employs a MEMS virtual impactor with Film- Bulk Acoustic Resonator to measure mass  Impaction on an oscillating micro tuning fork MEMS PM Mass Sensor