Experts Conferred on Improving Emissions Inventory
Contributed by Gerardo Mejía, Francisco Obregon and Robert
Slott
The Integrated Program on Urban, Regional and Global Air Pollution
organized the “Workshop on Mexico Emissions Inventory”
at the Hotel Royal Pedregal, México D.F., México on
February 25 and 26, 2003. The purpose of this workshop was to bring
experts from both the United States and from Mexico to discuss the
current state of knowledge in emissions inventories and to help
improve the development of the Mexico emission inventory. Better
defining the emission inventory in the Mexico City metropolitan
area (MCMA) is of particular importance due to the large population
exposed to air pollutants that often exceed the national standards.
The workshop was sponsored by the North American Commission for
Environmental Cooperation, the Mexican Ministry of Environment and
Natural Resources (SEMARNAT) and the Mexican Metropolitan Environmental
Commission (CAM).
Uncontrolled air pollution in our modern age can lead to serious
adverse health effects, threaten the viability of ecosystems and
contribute significantly to global climate change. Studies have
shown that increased morbidity and mortality accompany air pollution
that exceeds air quality standards. Pollutants may be directly emitted
from air pollution sources and other pollutants may be formed in
the atmosphere as a result of reactions often catalyzed by sunlight.
Establishing the appropriate control strategy portfolio requires
understanding how secondary air pollutants are formed, especially
ozone, and particulate matter.
Reducing air pollution requires controlling emission sources.
An accurate emission inventory is needed to help design and monitor
the emission control program by defining the important emission
sources and watching air pollution trends. Emission inventories
can be approached by measuring source emissions (bottom-up) or monitoring
pollutants in the atmosphere using ambient concentrations, source
receptor analysis, or other methods (top-down). Air pollutant concentrations
vary in time (time of day, day of the week, season of the year)
and space. Because many of the sources are difficult to measure
and monitoring cannot take place everywhere, every emission inventory
should be considered as a best estimate with an associated uncertainty.
Methods of estimating the accuracy and uncertainty of emission inventories
are important.
The workshop was divided into six sessions:
- Emission Inventory Applications, Uncertainties, and Data Requirements
- Mexico Emissions Inventory
- Innovative Techniques for Measuring Emissions
- Bottom-up Methods
- Top-Down Methods
- Wrap up Session
In the introduction to the workshop, Mario Molina, MIT, gave an
overview of the research and education activities of the Integrated
Program’s Mexico City Case Study (hereafter referred as Mexico
City Project). A review of the 1998 Mexico City Emission Inventory
is included in a book published in 2002 (Air Quality in the Mexico
Megacity: An Integrated Assessment, edited by L.T. Molina and M.J.
Molina). The Project used emissions information from the 1997 IMADA
measurement campaign to calculate the ambient ozone concentration
as a function of time and location. The ambient ozone measurements
did not agree with the air modeling calculation unless the hydrocarbon
concentrations were multiplied by a factor of two to three. The
Project conducted an exploratory field study in the MCMA to gather
additional emissions measurements in February 2002 in preparation
for an intensive field measurement campaign in the MCMA in April
2003. More than two dozens institutions from the US, Europe and
Mexico, involving more than a hundred investigators will participate
in this campaign. The 2003 effort adds a significant number of new
state-of-the-art instruments, some on the Aerodyne Inc. mobile lab
and some on a supersite installed at CENICA (Centro Nacional de
Capacitación Ambiental), as well as in the boundary sites
of the MCMA. We expect to generate lots of information that will
enable us to further elucidate the atmospheric chemistry of the
Mexico City Valley and reduce uncertainties in emission inventories.
The insight obtained will be crucial for protecting human health
and ecosystem viability in Mexico City as well as other megacities
around the world.
Another important activity of the Project is the integrated scenarios
analysis. While we cannot predict the future, we can estimate what
might happen if Mexico City continues to grow and if different severity
of control strategies are implemented. One of the unique features
of the Project is the close collaboration with the Mexican government
officials, so that our research findings can provide the scientific
foundation for the decision making. Communicating to the public
on how their actions can improve air quality is also part of the
outreach program that is an important component of the Project.
Session 1: Emission Inventory Applications, Uncertainties, and
Data Requirements
Bill Kuykendahl, US Environmental Protection Agency (EPA), described
the emission inventory and air modeling requirements for states
in the US that did not meet the National Ambient Air Quality Standards
(NAAQS) to demonstrate that their control strategies were indeed
working to reduce air pollution. The public in the US has access
to these studies. The rules were established in the Clean Air Act.
However, the Clean Air Act failed to account for the importance
of pollutant transport from one state to another. Transport is especially
a problem for long-lived pollutants and secondary pollutants such
as ozone and particulate matter. Regional control strategies are
now also important in the US. Jim Wilson, Pechan, described the
shift from state to regional emission inventories. In the US power
plant emissions are closely followed; hourly emissions are reported
to the EPA. J. David Mobley, EPA, described the new NARSTO assessment
on particulate matter to be released in March 2003. Robert Harley,
University of California at Berkeley, and David Allen, University
of Texas at Austin, each talked about the criteria for emission
inventories that will be used as sources of information for air
quality modeling. For air quality modeling emissions must be specified
spatially and temporally. Spatial coordinates are a few square kilometers
in area in a three-dimensional grid. Times are specified as hours
of the day, days of the week, and seasons of the year. Particulate
matter inventories need to account for size and chemical composition
of the pollutant. Based on studies in Houston, TX, extreme values
of point source hydrocarbon emissions from chemical plants and refineries
can have a large effect on the ozone concentrations. Intermittent
high hydrocarbon emission events caused an underestimation of the
point source hydrocarbon emission inventory by factors of five to
ten. This illustrates the critical role that field measurements
play in the development and performance evaluation of emissions
inventory.
Session 2: Mexico Emissions Inventory
Adrian Fernandez, INE/SEMARNAT, described the Mexico National
Emission Inventory Project, which started in 1996 with the support
of US EPA and the Western Governors Association (WGA), later with
help from the North American Commission for Environmental Cooperation
(NACEC). The national emission inventory is starting in the border
area for the cities of Aguascalientes, Mexicali and Tijuana, but
will cover the entire country. Richard Halvey, WGA, described the
decision making process in forming an emission inventory and the
importance of the public having access to the information. Gathering
emissions inventory information in Mexico presents unique challenges:
jurisdictional issues, confidentiality laws, reporting requirements,
data availability must all be considered during the planning and
implementation portions of any project.
Session 3: Innovative Techniques for Measuring Emissions
Charles Kolb, Aerodyne Research Inc., talked about new opportunities
for emission information by using new measurement tools. He illustrated
this with some on-road formaldehyde data obtained in 2002 in real
time in both Boston and Mexico City. The much higher formaldehyde
concentrations and their association with carbon dioxide indicated
much of the increase in formaldehyde in Mexico City could be due
to primary emissions from automobiles. Brain Lamb, Washington State
University, described the Urban Tower Flux Experiments to be established
near CENICA and the instruments that will be used in the MCMA-2003
field campaign. Gene Tierney, US EPA, mentioned that EPA is promoting
the development and commercialization of Portable Emissions Measurement
Systems (PEMS) because they offer many benefits over traditional
laboratory measurement techniques.
Session 4: Bottom-up Methods
Rodrigo Perrusquía, Gobierno del Distrito Federal, reviewed
the recommendations given by the MIT Mexico City Project to the
1998 emissions inventory. He said that the three most important
recommendations for mobile sources are knowing better the number
of vehicles, the distribution by model-year and the emission factors
used. He discussed the basis and uncertainties in the vehicle counts.
Sandeep Kishan, ERG, described the adoption of the US EPA MOBILE6
to conditions in Mexico. Matt Barth, University of California at
Riverside, discussed the history and recent advances in mobile source
emission modeling. He described in some details the Comprehensive
Modal Emissions Model (CMEM) and the International Vehicle Emission
(IVE) Model developed at UC Riverside. The later has been successfully
developed and applied to locations outside the U.S., including Chile,
Kenya, India, and China. Gene Tierney pointed out that EPA’s
upcoming mobile source emissions model, MOVES, will be based much
more on on-road vehicle emissions and will have the capability to
make a life cycle analysis. Robert Harley commented to gain confidence
in the estimates of emissions we need to make multiple independent
estimates. His research activities use a highway tunnel as a laboratory
to measure changes in vehicle emissions over a number of years.
Vehicle emissions are estimated from emissions per fuel used multiplied
by the amount of fuel sold in the area. The results from 1994 to
2001 showed an emission decrease of about 50% for NOx, 62% for CO
and to 67% for VOC even though the amount of fuel used was increasing.
The vehicle emission reduction is caused by better vehicle emission
control equipment, especially better catalytic converters.
Sergio Sánchez, SEMARNAT, said all industries in Mexico
are required to provide data related to general information of the
industry, processes, raw material and inputs, air, water and soil
emissions and pollutant transfers. Information about proprietary
processes is confidential similar to US regulations. There is a
list of 104 substances and the criteria pollutants are included
as well as greenhouse gases. Jesús Contreras, SEMARNAT, gave
an introduction to the stationary emissions inventory efforts in
previous years and the air quality programs. The last EI is the
1998 estimate. Following the recommendation from Mario Molina’s
team at MIT, several techniques were used in refining the 1998 EI:
source monitoring, emission factors, materials balance, and extrapolation.
A large effort is being made to reduce uncertainties in the estimation
of emissions. The focus is on NOx, HC, PM10 and PM2.5 emissions.
Jim Wilson talked about similarities between data registered in
the US and Mexico and about differences in confidentiality of information.
He discussed uncertainty analysis results found by the National
Academy of Science (NAS). Proper characterization of uncertainty
is essential; most analyses underestimate uncertainties, thus giving
decision makers a false sense of confidence.
Rocío Reyes and Cuitlahuac Cruz, Secretaría de Ecología
del Estado de México, reviewed the biogenic emission inventory
for the Valley of Mexico. These talks included a description of
the data requirements to be used in the Biogenic Emissions Inventory
System (BEIS) model developed by EPA. They included climatology,
humid and dry seasons, and land use, and emissions of isoprene,
terpenes, VOC, and NOx. Luis Gerardo Ruiz Suárez, Centro
de Ciencias de la Atmósfera, UNAM, discussed limitations
in the use of the PC BEIS and in the use of the data for modeling.
There is also no uncertainty analysis or validation with other methodologies.
Thomas Pierce, National Oceanic and Atmospheric Administration (NOAA),
described the evolution and advances of the BEIS and its application
to air quality simulation modeling within the United States. Biogenic
emissions are estimated to contribute more than 50% of VOC emissions
in the US. However, depending on the methodology used, large differences
in isoprene emissions may be estimated. He recommended ways to improve
the estimation of biogenic emissions.
Jorge Sarmiento, Gobierno del Distrito Federal commented on the
air quality problems and the efforts to estimate emissions inventories
in the MCMA. The goal is to have a new estimate every 2 years. Mobile
and area sources were considered the most important. The PM10 estimate
is known to be low because it does not include emissions from either
paved or unpaved roads. Many sources were not included in the 1998
EI due to lack of data and uncertainty about their reliability,
especially in the informal sector (e.g., street vendors).
Session 5: Top-Down Methods
Rafael Ramos, Gobierno del Distrito Federal, described the current
Mexico City Air Quality Monitoring Network. The cost of the monitoring
operation is in the order of 2 million dollars per year. David Allen
talked about the use of the results of an air quality study to assess
the accuracy of the EI using aircraft data and its application to
areas of Texas. Results of ozone formation and HC reactivity in
Houston showed that VOC emissions are underestimated. Interaction
with stakeholder and community leaders has increased the confidence
on policy-making and the value of scientific partnerships. Eric
Fujita, Desert Research Institute, talked about how tunnel studies
have shown that gasoline and heavy-duty diesel vehicle emissions
have been greatly reduced over time except for particle emissions,
which have shown only a small decrease. He discussed how emissions
could be traced to their source using chemical composition.
Session 6: Wrap up Session
As part of the project’s outreach efforts, this session
was transmitted via the Mexican Education Network (EDUSAT) to other
cities in Mexico. Sergio Sánchez gave an introduction to
the session and explained the importance of reaching other audiences.
Mario Molina emphasized the importance of the emission inventory
and how it fits under the study being developed for the MCMA. A
very precise emission inventory is expensive to produce and update,
so only the degree of precision that is necessary should be used.
However, different approaches to the inventory, using independent
data, should be made so that the uncertainty can be estimated. These
include measurements, fuel consumption, levels of activities, etc.
The wrap up session included questions addressed to a panel of speakers
and other workshop participants by Mario Molina and follow-up questions
and comments from the audience. Topics discussed include what kind
of training is needed to compile and use emissions inventories;
what can Mexico learn from the international experience; how should
Mexico decide which emissions control strategies should be put in
place and how do we know whether the control strategies are working;
and finally what can average person do to reduce emissions and hence
to help improve the air quality. Luisa Molina closed the workshop
by thanking the speakers, the participants and the sponsors for
a very productive workshop.
Gerardo Mejía is a Professor and Francisco
Obregon is a graduate student at Tecnológico de Monterrey
(ITESM). Robert Slott is a Visiting Engineer with the Integrated
Program on Urban, Regional, and Global Air Pollution. |