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ACD
Achievements
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Overview
Regional and Global Air Quality
Improvements
to PeRCIMS instrument Peroxyacyl
Nitrates (PAN) instrument Actinic
flux Spectroradiometer Continued Development of
New High Performance Airborne DFG Instrument for the Measurement of CH2O Continued Improvements to
Present Airborne TDLAS System Hardware and Software Community Instruments, Measurement, and Science
Support Chemistry Community Instruments Managing the National Science Foundation Atmospheric
Chemistry Program Field Campaigns Complementary to MIRAGE International
Consortium for Atmospheric Research on Transport and Transformation (ICARTT) NASA The Intercontinental Chemical Transport
Experiment (INTEX-NA) Measurement of Pollution In The Troposphere (MOPITT) MOPITT
Participation in INTEX-A Long-range
Transport of CO Emissions from Russian Fires Involvement
with Other Satellite Missions Seasonal
and Inter-Annual CO Variability Data
Assimilation and Inverse Modeling Comparison of CO and Aerosol Emissions from Biomass
Burning Regional and Global
Chemical Transport Models and Air Pollution Studies Weather
Research Forecasting with Chemistry (WRF-Chem) Global
chemical transport models and air pollution studies Reactive Carbon Research
Emissions of Primary Organic
Compounds Reactive Carbon
Species as Sources and Reservoirs of Radical Species Oxygenated
Volatile Organic Carbon (OVOC) Contribution to
the HOx Cycle Gas-aerosol Partitioning of
Organic Species Oxidation Pathways for Alkyl Iodides Nitrate Production from Toluene Oxidation Oxidation Mechanisms of Methyl Formate
and Methyl Acetate Multiphase Processes in the Troposphere
Clouds – Cloud Chemistry Modeling Intercomparison of Convective Cloud Chemistry
Models Cloud Chemistry Process Studies -
The Importance of the Cloud Drop Representation on Cloud Chemistry Mid-latitude Snow Chemistry
Experiment Deployment of a Snowpack UV
Radiation Profiler to Summit, Greenland Chemistry in the Climate System
Climate
Simulations
Tropospheric ozone interannual variability Studies of the Arctic Oscillation Role of convective versus synoptic transport Intergovernmental Panel on Climate Change (IPCC)
simulations Off-line Community Atmosphere Model (CAM) Interactive Community Atmosphere Model (CAM3) Biogeochemical Cycles
Regional Modeling Studies: U.S. Regional Modeling Studies: International Model and Database Development Trace Organic Gas Analyzer
(TOGA): Measurements, Standards,
and Intercomparisons (MSI) Group HIAPER Radiation Package
(HARP): ARIM Group Development of autonomous actinic flux
instrumentation for high altitude aircraft – NASA WB-57 Development of a prototype HIAPER OH
instrument Fourier-Transform Infrared (FTIR)
Spectrometer for HIAPER Middle
Atmosphere Science
WACCM - model development and
results Impacts of El Niño-Southern Oscillation (ENSO) on the
middle atmosphere Seasonal variability of trace
species in the UTLS region Stratospheric influence on seasonal
cycles of tropospheric tracers Monsoon impacts on
stratosphere/troposphere exchange (STE) Parameterization of gravity wave
fluxes due to convective excitation Stratospheric trends in temperature
and water vapor Chemical transition across the
extratropical tropopause Structure and variability of the SE
Asia monsoon system Chemistry of the middle atmosphere sodium layer Oxygen – hydrogen chemistry and
emissions in the mesosphere Strategic Initiatives
Biogeosciences
BGS Achievements (Division Narratives) Atmospheric Chemistry Division: ACDCarbon-Nitrogen cycling (Tasks 1 & 2) International field studies (Task 2) Regional modeling studies, U.S. (Task 2) Regional modeling studies, International (Task 2) Global modeling studies (Task 1) Model and database development (Tasks 1 & 2) Instrument development (Task 2) Climate and Global
Dynamics Division: CGD
Community land model (Tasks 1 &
4) Land cover and land use change
(Tasks 1 & 4) Development of carbon and nitrogen
capabilities in CLM (Task 1) Community land model diagnostics
package (Task 1) First results from CCSM3 with
coupled C and N cycles (Task 1) Multi-century carbon cycle
simulations (Task 1) Coupled climate carbon cycle model
intercomparison project (C4MIP) (Task 1) High-resolution carbon cycle model
user interface project (Task 1) Mineral Aerosols in CCSM (Tasks 1
& 4) Carbon
in the Mountains
Experiment: CSME
and ACME Carbon in the mountains experiment
(CME) (Tasks 2 & 3) Airborne carbon in the mountains
experiment (ACME I) (Tasks 2 & 3) CO2 transport over
complex terrain (Tasks 2 & 3) Atmospheric Technology
Division: ATD Airborne CO2 Measurements
(Task 2) Tower CO2 measurements:
autonomous inexpensive robist CO2 analyzer (AIRCOA) (Task 2) NCAR CO2 and O2
calibration facility (Task 2) Synthesis of global light aircraft
CO2 data (Task 2) Wisconsin Tall-tower atmospheric O2
measurements (Task 2) Wildfires
UTLS
MIRAGE
The ACD (Atmospheric Chemistry Division) mission is (1) to understand the chemical composition of the atmosphere, the processes that modify and control the composition, and potential changes that may result from natural and human induced forcings; (2) to provide relevant, reliable, accessible, unbiased, and timely information on atmospheric chemistry to government and society; and (3) to act as an intellectual resource and enabler to the wider atmospheric sciences community through the development of new measurement capabilities and methodologies, development and application of numerical models that reliably simulate present and future atmospheric conditions, and the planning and execution of field experiments to address specific scientific questions of regional and global significance. Over the next few years, ACD staff will direct their research efforts at two grand challenges that confront society and where atmospheric chemical processes play a crucial role, namely Regional and Global Air Quality and Chemistry in the Climate System. The directions and priorities of the division’s research efforts have been chosen for their societal relevance and scientific merit. These plans were developed and formalized in the ACD Science Plan and were developed with the recognition that the accomplishment of any of the major goals will require significant collaboration with other NCAR divisions and with the university community. The goals were determined as a result of an iterative process involving the division director, the division internal management and external advisory committees. The main goal for Regional and Global Air Quality is to understand and quantify the impact of urban emissions on air quality. Priority will be given to studying the large-scale impacts of intense emissions originating from megacities, and the multiphase (gas-aerosol-cloud) processes that transform pollutants in the atmosphere. The goals for Chemistry in the Climate System are to understand the interactions between the physical climate system, the chemical climate system, and the biosphere. Priority will be given to the simulation of the recent past and future chemical climate states based on current climate simulations and to the study of the crucial role of the upper troposphere/lower stratosphere (UTLS) in the physical and chemical climate system. The two primary research areas, Regional and Global Air Quality and Chemistry in the Climate System, encompass the research areas outlined in the 2003 ACD program plan. The table below shows the relationship between the 2003 ACD Program Plan, the ACD Science Plan, and the 2004 ACD Program Plan.
Regional and Global Air
Quality Characterization of air quality is an important issue, not only in urban areas, but also on regional and global scales. Satellite, aircraft, and ground-based observations throughout the global atmosphere are confirming that air pollution can be transported over large distances, e.g., from eastern Asia to the western U.S., from North America to Europe, and from mid-latitudes to the Arctic. Discussions of air quality generally center on issues related to atmospheric oxidants and particulates. Increases in ozone are of particular concern as this compound may impact humans and natural ecosystems, and is currently ranked as the third most important “greenhouse” gas. Thus, future trends in its concentration have strong links to both global air quality issues and to climate change. Potential global changes in OH radical concentrations are another major concern. OH is responsible for initiating the oxidation of many compounds emitted to the atmosphere into more soluble species that are removed from the atmosphere by wet and dry deposition or adsorbed into aerosols in multiphase processes. Critical challenges within the context of global change will be to determine if the capacity of the atmosphere to remove these gaseous species will be reduced or if climate change will affect the oxidation or emission processes and lead to significant change in the chemical composition of the troposphere. There is ample evidence for increases in oxidants and other pollutants in urban and regional environments, where air quality is a major issue. Furthermore, transport of ozone and some ozone precursors from densely populated areas has led to increases on the global scale (estimated at 30% since the preindustrial era), and larger increases are expected with the demands of population growth. One of the major research themes within ACD is to investigate the influence of the export of urban pollution on regional and global air quality. Reactive carbon species, also referred to as volatile organic compounds (VOC), play a central role in determining tropospheric air quality. Primary VOC emissions are extremely diverse chemically, with both natural and anthropogenic sources, and range in complexity from simple gases such as CO and methane to more complex chemical forms like the terpenes (naturally-occurring isomeric compounds of general formula C10H16). Once in the atmosphere, these gases are oxidized to more soluble forms (carbonyl compounds, organic nitrates, organic acids, multi-functional species, etc.) that are more readily removed from the atmosphere by deposition, or that can couple back into the HOx and NOx chemical cycles - often at significant distances from the original source regions. The cycle of VOC emission, transformation, and heterogeneous loss is a major topic of research within ACD. Multiphase
processes (gas-aerosol-cloud interactions)
are increasingly recognized as important
to tropospheric air quality. High
particulate concentrations, now common in
and around urban centers but increasingly
present on continental scales, pose a significant
health risk. Many
aerosols serve as cloud condensation nuclei
and therefore influence cloud particle properties
(e.g., albedo) and precipitation. They also scatter or
absorb light, thus altering the atmospheric
radiation field and reducing visibility. In addition, particles
can act as sinks for some atmospheric oxidation
products including sulfuric and nitric acid,
ammonia, and many products of reactive carbon
oxidation. Clouds also influence both tropospheric
air quality and climate through their impact
on the hydrologic cycle, as transporters,
processors, and scavengers of pollutants,
and via their
effects on the tropospheric radiation field. Convective
clouds play a particularly important role
as transporters of trace species from the
polluted boundary layer to the upper troposphere,
which enhances ozone production in the upper
troposphere where absolute changes in ozone
have their largest radiative impact. Elucidation
of the many complex physical/chemical processes
involved in the multiphase chemistry of the
troposphere - from particle nucleation and
growth, to impacts of aerosols on gas phase
composition, and the impacts of clouds as
transporters and processors of trace gases
is a major focus of ACD research activity. Influence of Urban Pollution on Regional and Global Air Quality (Influence of Urban Emissions on Atmospheric Composition) ACD efforts in this area include planning for the MIRAGE-Mex (Megacity Impacts on Regional and Global Environments, 2005 Mexico City campaign) field campaign, development of instruments to be used for tropospheric chemistry studies, development and deployment of community instruments and continued measurement support, participation in field campaigns that are complementary to MIRAGE, improvements to and use of MOPITT (Measurements of Pollution In The Troposphere) retrievals, photochemical research, and development and use of regional chemical transport models. Community Involvement and C-130 Deployment (Megacity Impacts on Regional and Global Environments [MIRAGE] Planning) While the importance of urban pollution to regional and global environments is widely acknowledged, it remains poorly quantified because of the complexity of physical and chemical processes that must be understood over a broad span of spatial and temporal scales. The MIRAGE program is a new activity under development by scientists at NCAR and the university community, based on the recognized need for an integrated, multidisciplinary approach to this complex environmental issue. Planning is underway for a major field campaign in Mexico City in 2005 (MIRAGE-Mex). Sasha Madronich, Frank Flocke, and John Orlando were involved in preparing and submitting a MIRAGE-Mex proposal to NSF. The proposal will be reviewed by the National Science Foundation’s Observing Facilities Advisory Panel (OFAP) in April 2005. Additional information on MIRAGE-Mex logistical and scientific planning is found below under the Strategic Initiatives – MIRAGE section. A
number of instruments have been developed
or improved by ACD staff for use in tropospheric
chemistry studies. These include the Peroxy
Radical Chemical Ionization Mass Spectrometer
(PeRCIMS), peroxyacyl nitrates (PAN), radiation,
isotopes, and formaldehyde instruments. Improvements to PeRCIMS Instrument Chris Cantrell of the Atmospheric Radical Studies (ARS) Group has developed an instrument to measure peroxy radicals in the atmosphere. The PeRCIMS instrument operates on the principle of chemical conversion of ambient or calibrator-generated peroxy radicals to gas-phase sulfuric acid, followed by chemical ionization by reaction with negatively charged nitrate ions, and separation and detection of the ions via mass spectrometry. Signals for the total peroxy radical concentration [HO2+RO2] and for the hydroperoxy radical concentration [HO2] have been acquired by greatly changing the concentration of the reagent gases, nitric oxide (NO) and sulfur dioxide (SO2). For HO2+RO2 measurements, the reagent concentrations in the inlet were in the tens of ppmv range. For HO2 measurements, they were in the thousands of ppmv range. This necessitated the use of pure NO and pure SO2 for the HO2 quantification. Recently, we have investigated the use of oxygen or nitrogen dilution as an alternative to changing the reagent gas concentrations. The separation of HO2 and RO2 exploits the competition between the reaction of alkoxy radicals (RO), which are generated in the reaction of RO2 with NO, with oxygen and NO. When RO radicals react with oxygen, HO2 is usually a product (depending somewhat on the structure of RO), which leads to measurement of the RO2. When RO radicals react with NO, alkyl nitrate stable products (RONO) are formed, which leads to RO2 not being measured. Thus, the parameter which affects the sensitivity to RO2 is the NO/O2 ratio. At low NO/O2 values, RO2 radicals are measured efficiently, and at high values they are not. Dilution of ambient air in a ratio of 1:10 with either oxygen or nitrogen leads to modulation of the oxygen concentration by a factor of 49, allowing RO2 measurements with high efficiency (>80%) in the HO2+RO2 mode or fairly low efficiency (<30%) in the HO2 mode. The non-ideal responses (100% and 0% in the two modes, respectively) can be corrected using laboratory measurements of RO2/HO2 response factors and model estimates of the makeup of RO2 species. Comparisons of the reagent gas concentration change versus the oxygen modulation method were performed in the laboratory, and representative results are shown in Figure 1, along with a numerical model of the expected results. These preliminary results are promising, and suggest that the oxygen modulation technique may be nearly as efficient at separating HO2 and RO2, with the advantage that change between the two modes of operation can be accomplished quickly. Development will continue in FY05, with a design goal to quantify atmospheric HO2 and HO2+RO2 within one minute. This will require modifications to the inlet and the computer control software.
Figure
1: Measured and modeled response of
PeRCIMS to RO2 radicals versus
the ratio of the concentrations of NO to
O2. The large colored triangles
show normal operating conditions using
the method of changing reagent concentrations. The large colored squares
show potential operating conditions using
oxygen dilution modulation. Open circles show laboratory
measurements of sensitivity for other operating
conditions, using changing reagent concentrations. The
lines represent models of the sensitivity
of RO2 when changing reagent
concentrations (blue shades) and oxygen
dilution modulation (green shades). The different curves correspond
to different SO2/NO ratios,
in which the chain length (CL) is the SO2/NO
ratio divided by five. Implicit
in the model is an assumption about the
rate of the reaction of RO with SO2 to
form HO2 (inferred from laboratory
studies).
Peroxyacyl Nitrates (PAN) instrument Frank
Flocke and Aaron Swanson (University of Colorado,
Boulder (CU); NOAA Aeronomy Laboratory) flew
a new instrument for fast (1-2 sec), continuous
measurements of PAN and related species on
the NOAA P-3B aircraft as part of the NOAA-led
International Consortium for Atmospheric
Research on Transport and Transformation
(ICARTT) and New England Air Quality Study
(NEAQS) programs. The instrument, called
PAN-CIGAR (PAN-CIMS [Chemical Ionization
Mass Spectrometer] Instrument by Georgia
Institute of Technology [GIT] and NCAR),
has been a joint development with Greg Huey
and David Tanner (GIT). Prior to deployment, much
of the year was spent on redesigning a prototype
instrument to make it ready for unattended
aircraft operation. The
pump system was redesigned and gas loads
were lightened. The
operation and data acquisition software was
improved as well as some electronics to allow
unattended operation and controlled recovery
from power outages, etc. Additional
instrument characterization (investigation
of the sensitivity dependence on humidity,
flow, and pressure) was performed. Other
instrument improvements were made with help
from David Hanson (ACD). From October 2003 to early
April 2004, Sandra Lopes, a graduate student
from the University of Wiesbaden, Germany
worked with Swanson and Flocke. She
successfully completed her Master’s degree
in Chemical Engineering with them by participating
in the development and construction of a
new in situ calibration source for the instrument,
a unit that is 50% smaller than the old unit
and has augmented control capabilities for
use with PAN-CIGAR.
Actinic Flux Spectroradiometer Members
of ACD’s Atmospheric Radiation Investigations
and Measurement (ARIM) Group, Rick Shetter,
Sam Hall, Barry Lefer, and Edward Riedel,
developed a new generation actinic flux spectroradiometer. The
ARIM Group has deployed ground-based and
airborne Scanning Actinic Flux Spectroradiometer
(SAFS) instruments for the determination
of actinic fluxes and photolysis frequencies
for the last seven to eight years. These
have operated well, but have limited time
resolution (~10 seconds for a spectrum) and
require frequent calibration and maintenance. A new instrument based
on a monolithic monochromator with a UV-enhanced
windowless CCD detector has been developed.
This instrument is smaller and lighter with
a new PC-104+ data acquisition and control
system. The instrument has been quite reliable
and has the ability to collect actinic flux
spectra from 280 to 680 nm at 1-10 Hz, allowing
for fast photochemistry investigations. The
smaller design will allow deployment on aircraft
platforms with limited space for instruments
and operators including the NSF HIAPER (High-performance
Instrumented Airborne Platform for Environmental
Research) aircraft and future Unmanned Aerial
Vehicles (UAV) platforms. One of these new
generation instruments was deployed on the
NASA DC-8 for the INTEX-NA experiment.
Alan
Fried, James Walega, and Dirk Richter of
the joint Atmospheric Technology Division
(ATD)/ACD APOL have developed and improved
several instruments.
The Annual Scientific Report (ASR) last year described this project in detail along with progress achieved in designing and constructing the new instrument (APOL_(ACD/ASR03)). Figure 2, which illustrates a modified version of the optical setup shown last year, has been constructed and a number of tests have been carried out. This new setup allows the sample and reference beams to make two traversals of the absorption cells for improved measurement precision. As discussed in our previous ASR, the absorption signals from the two cells containing the sample gas and an isotopic reference standard are rapidly compared using online fitting analysis. The fitting procedures have been developed and wait further testing on CO2 absorption features, which should take place within the next month or two.
Figure
2: Optical schematic of modified Differential
Frequency Generator (DFG)-based system for
high precision carbon dioxide isotopic ratio
measurements. Figure
3 shows the design of the inlet system, which
represents the second major task associated
with high precision CO2 measurements.
This system, which is in the testing phase,
allows various combinations of reference standards
and ambient samples to be introduced to the
absorption cells under closely matched conditions
of pressure and flow. Other studies frequently
do not take such precautions.
Figure
3: Schematic of inlet and outlet plumbing
system. The two absorption cells are designated
by Abs Cell A and B in this figure.
As in the previous year, the APOL Group worked in close collaboration with NCAR’s Education and Outreach Program to host two teachers and students from local area high schools to help with all phases of this project. The following Web link (http://www.atd.ucar.edu/apol/biocomplexity.htm) further describes the full project and also shows one important aspect of the teacher and student involvement: organization and dissemination of the material to the broader public. Continued Development of New High Performance Airborne DFG Instrument for the Measurement of CH2O As
discussed in last year’s ASR, the trace gas
CH2O is one of many important atmospheric
trace species involved in ozone production
and radical formation. The APOL Group has been
actively involved in a long-term effort to
carry out ever more accurate and precise measurements
of this gas throughout the troposphere and
lower stratosphere. As
discussed previously, such measurements have
been exclusively acquired using the APOL Group’s
liquid-nitrogen cooled tunable diode laser
absorption spectroscopy (TDLAS) system. Although
the Group has continued to implement a number
of significant improvements to this system
in terms of hardware and software (to be discussed
below) and achieved consequent gains in instrument
performance, the Group is fast approaching
an ultimate limit to such gains. The
present instrument sensitivity (15 – 50 pptv,
1s precision
for 1 minute of averaging) needs to be further
improved for routine CH2O measurements
in the background atmosphere, particularly
in the upper troposphere/lower stratosphere
where CH2O decomposition becomes
a major source of reactive hydrogen radicals. In addition, the instrument
is large and requires periodic operator intervention. To
address this critical need as well as the need
to develop smaller, lighter, and autonomous-operation
instruments for future HIAPER campaigns, the
APOL Group has been developing a new high performance
airborne CH2O instrument based upon
difference frequency generation. A comprehensive description
of this approach, as well as its many advantages
over lead-salt TDLAS systems, has been discussed
in last year’s ASR and will not be repeated
here. (“Technology Development
in Airborne Observing Systems and Chemical
Sensor Systems,” at TDLAS_(ACD/ASR03)). However,
for size comparison purposes, APOL Figures
3 and 4 show the present airborne TDLAS system
and the compact new DFG system. The
Herriott absorption cells in both systems are
approximately the same size. With this in mind, a comparison
of these two figures immediately reveals that
the DFG system is significantly smaller than
the TDLAS system; the DFG-Herriott cell configuration
in Figure 5 has replaced the entire optical
setup of the TDLAS system in Figure 4. A further advantage of
the DFG system is that no liquid cryogens are
required, in stark contrast to the present
TDLAS system. Although
laboratory tests with the new DFG system are
not yet complete, evidence strongly indicates
that this new system will ultimately achieve
higher performance than the TDLAS system for
CH2O and other molecules.
Figure
4: Schematic of optical system with cutaway
view of temperature-stabilized enclosure employed
during INTEX-A. Two separate laser channels
with separate beam collection optics are shown.
However, during INTEX-A only one laser channel
was employed. The enclosure dimensions are
approximately 33” long x 24” wide x 12” high.
Figure 5: Photograph of the APOL Group’s DFG stage mounted to a new, more stable Herriott cell. The size of the DFG stage with enclosure is 7”long x 9.5” wide x 3.5” high. For comparative purpose, the cell here is the same size as the cell in Figure 4.
Continued Improvements to Present Airborne TDLAS System Hardware and Software
Despite the significant progress achieved in the DFG development, the laboratory prototype system has not yet been tested on airborne platforms. Rather than risk flying such a system for the first time during a critical field mission, the APOL Group decided to pursue the more prudent course of action by employing the TDLAS system during the 2004 summer INTEX-NA study. However, numerous small modifications were implemented to this system this past year to further improve the system robustness, reliability, and performance. Many of these modifications, which are too numerous to list here, focused on improving the optical-mechanical stability of the system. In addition, numerous software changes were also implemented for improved performance, reliability, and enhanced data quality assurance. Community Instruments, Measurement, and Science Support ACD supports several analytical instruments that are available by request from the community to support airborne field campaigns. These include instruments to measure carbon dioxide (CO2), carbon monoxide (CO), ozone (O3), and water vapor (H2O). Teresa Campos (ACD/ATD) is responsible for the maintenance, deployment, data collection, and data reduction for these instruments. ACD also supports ongoing hydrocarbon calibration efforts by Eric Apel. Chemistry Community Instruments Teresa Campos and Sam Hall of the ARIM Group were responsible for instrument preparation and calibration, data acquisition software development, instrument deployment, and data analysis during several field campaigns. Preliminary results from the Gulf of Tehuantepec (GOTEX) airborne field experiment, conducted in the Eastern Pacific marine boundary layer near Salina Cruz, Mexico, indicate successful measurement of CO2 air-sea exchange by the eddy covariance method. The sensitivity to aircraft acceleration was quantified and found to contribute to the flux signal only at frequencies less than 2 Hz. Even at these frequencies, however, the amplitude of the artifact is a factor of 50 smaller than equivalent power spectral content of ambient marine boundary layer data measured at the same altitudes, as shown in Figures 6 and 7. |