| Purpose
of the class:

This is a class
built around an interdisciplinary seminar series on Remote Sensing
topics. It is meant to give an introduction to this rapidly developing
research field for our students. It is meant for students in the
Minor program in Remote Sensing, which can be taken by majors in
at least 9 departments. It is also of possible interest to graduate
and undergraduate students interested in remote sensing and related
topics.
The class grade
is determined by attendance and participation. There are no exams
or written assignments.
Spring 2006 Schedule of Dates, Speakers and Topics:
|
Updated March 22, 2006
Please note that some speakers' dates may be rearranged
as the schedule is finalized.
Seminars are on Mondays at 4 pm, M&M
Room U113, unless otherwise noted.
| Date |
Time |
Room |
Title |
Author |
Abstract link |
| January 19 |
|
|
No seminar |
|
|
| January 16 |
|
|
MLK Recess |
|
|
| January 23 (Joint
w/Env Eng) |
4pm |
U113 |
What have we learned from nearly a decade
of global change research at Aspen FACE? |
Dr. Dave Karnosky, MTU School of Forest
Resources and Environmental Science |
Abstract and Link |
| Feb 3 (Joint w/Env
Eng) |
4pm |
U113 |
Meteorological analysis of mechanisms of
low-level pollution export from eastern North America |
Chris Owen, Michigan Tech |
|
| Feb 6 (Joint w/Env
Eng) |
4pm |
U113 |
Modeling contaminant behavior in Lake Superior:
A comparison of PCBs, PBDEs, and mercury |
Mark Rowe, Michigan Tech |
Abstract |
| Feb 13 (Joint w/Env
Eng) |
3pm |
Dow 642 |
Carmen Sandiego and the Case of the Increasing
Regional (and Global?) Ozone |
Dr. Dan Jaffe, University of Washington |
Abstract |
| Feb 20 (Joint w/Env
Eng) |
4pm |
U113 |
Cold clouds: Ice formation by surface crystallization |
Dr. Raymond Shaw, Michigan Tech |
Abstract |
| Feb 27 |
|
|
No seminar (faculty applicant presentation
today) |
|
|
| March 6 |
|
|
Spring break: no seminar |
|
|
| March 17 (Joint w/Env
Eng) |
3pm |
Dow 642 |
Trapping of deep convective pollution by
upper level anticyclones:
Implications for global change |
Dr. Qinbin Li, NASA JPL |
Abstract |
| March 20 (Joint w/Env
Eng) |
4pm |
U113 |
Where does all the dirty air go? Insights
from MTU and INSTAAR's research
at the PICO-NARE (Azores/Portugal) observatory |
Dr. Detlev Helmig, University of Colorado |
Abstract |
| March 27 |
4pm |
U113 |
Everglades Restoration: Coupling Science
and Engineering to Ensure Success |
Dr. Scot Hagerthy, Southern Waterways
Management Agency, Florida |
Abstract |
| Apr 3 |
4pm |
U113 |
Resurrection Ecology: Chasing Van Valen’s
Red Queen Hypothesis |
Dr. Charlie Kerfoot, Michigan Tech |
Abstract |
| April 10 |
|
|
No seminar |
|
|
| April 17 (Joint w/Env
Eng) |
4pm |
U113 |
No seminar - rescheduled
to fall semester (Monday, October 9, 4 pm |
Dr. Paul Shepson, Purdue University |
|
| What have we learned
from nearly a decade of global change research at Aspen
FACE? |
| Dr. Dave Karnosky |
| MTU School of Forest Resources and
Environmental Science |
The Aspen FACE experiment was established
near Rhinelander, Wisconsin in 1997 to examine the
impacts of elevated atmospheric CO2 and/or O3 on the
structure and functioning of model aspen/birch/maple
ecosystems. Recently, we completed our eighth fumigation
season at this Department of Energy User Facility
which has been called the world opposite manners and
we will examine some curious long-term interactions
that were unpredicted at the onset of the experiment.
Finally, we will explore remaining research questions
that have arisen.
More information on Aspen FACE
|
| Carmen Sandiego and
the Case of the Increasing Regional (and Global ?) Ozone |
| Dr. Dan Jaffe |
| Atmospheric and Environmental Chemistry
at the University of Washington-Bothell |
Carmen Sandiego is the famous crimer
solver, who's work often takes her to mysterious and
remote parts of the world. Sometime solving a scientific
problem is a bit like Carmen's detective work. You
have to take the available data and piece together
an explanation. Then you have to try to convince the
jury (peer reviewers) that your story is correct.
In this case, the problem is the observed
increase in surface ozone in the western U.S. Ozone
is an important gas in tropospheric chemistry and
is also damaging to humans and vegetation at elevated
concentrations. To quantify the changes in background
O3 in the US, we evaluated O3 data from 12 relatively
unpolluted sites in the western U.S., including 2
sites in Alaska, for the period 1987-2004. At the
2 sites in Alaska, no trend was present. At 9 out
of 10 sites in the continental U.S. there is a statistically
significant increase in O3 with a mean trend of 0.35
ppbv/year. This trend is similar to surface ozone
trends reported for background sites in Europe and
Asia.
We propose several possible explanations
for this trend including increasing western US NOx
emissions, increasing global NOx emissions and/or
increasing biomass burning (due to climate change).
I have evaluated these hypotheses using a variety
of data including emission data, observations from
the Mt.Bachelor and Pico-Azores Observatories, fire
data from around the world and global observations
of Carbon Monoxide from the MOPITT satellite instrument.
Based on this analysis, I believe that increasing
global NOx emissions and increasing biomass burning
are the most likely causes for the ozone increase.
Carmen solves another one. Case closed.... I wish.
|
| Rowe seminar
title |
| Mark Rowe |
| Doctoral student, Engineering (Environmental),
Michigan Tech |
A mass-balance model for Lake Superior
was applied to polychlorinated biphenyls (PCBs), polybrominated
diphenyl ethers (PBDEs), and mercury to determine
the major routes of entry and the major mechanisms
of loss from this ecosystem as well as the time required
for each contaminant class to approach steady state.
A two-box model (water column, surface sediments)
incorporating seasonally adjusted environmental parameters
was used. Both numerical (forward Euler) and analytical
solutions were employed and compared. For validation,
the model was compared with current and historical
concentrations and fluxes in the lake and sediments.
Results for PCBs were similar to prior work showing
that air-water exchange is the most rapid input and
loss process. The model indicates that mercury behaves
similarly to a moderately-chlorinated PCB, with air-water
exchange being a relatively rapid input and loss process.
Modeled accumulation fluxes of PBDEs in sediments
agreed with measured values reported in the literature.
Wet deposition rates were about three times greater
than dry particulate deposition rates for PBDEs. Gas
deposition was an important process for tri- and tetra-BDEs
(BDEs 28 and 47), but not for higher-brominated BDEs.
Sediment burial was the dominant loss mechanism for
most of the PBDE congeners while volatilization was
still significant for tri- and tetra-BDEs. Because
volatilization is a relatively rapid loss process
for both mercury and the most abundant PCBs (tri-
through penta-), the model predicts that similar times
(from 2 - 10 yr) are required for the compounds to
approach steady state in the lake. The model predicts
that if inputs of Hg(II) to the lake decrease in the
future then concentrations of mercury in the lake
will decrease at a rate similar to the historical
decline in PCB concentrations following the ban on
production and most uses in the U.S. In contrast,
PBDEs are likely to respond more slowly if atmospheric
concentrations are reduced in the future because loss
by volatilization is a much slower process for PBDEs,
leading to lesser overall loss rates for PBDEs in
comparison to PCBs and mercury. Uncertainties in the
chemical degradation rates and partitioning constants
of PBDEs are the largest source of uncertainty in
the modeled times to steady-state for this class of
chemicals. The modeled organic PBT loading rates are
sensitive to uncertainties in scavenging efficiencies
by rain and snow, watershed runoff concentrations,
and uncertainties in air-water exchange such as the
effect of atmospheric stability.
|
Cold
clouds: Ice formation by surface crystallization
Raymond Shaw
Department of Physics
Michigan Tech
Clouds are profoundly influenced
by the seemingly-simple process of water droplets
freezing to form ice: the formation of ice can accelerate
the formation of precipitation, it alters the interaction
of clouds with solar and infrared radiation, and it
increases the cloud buoyancy and therefore the very
dynamics of motion. Nevertheless, the formation of
ice not well understood. For example, in many instances
much more ice forms in clouds than can be accounted
for with known nucleation mechanisms. With this in
mind, we carried out laboratory experiments aimed
at understanding the mechanisms for ice formation
by a catalyst (heterogeneous nucleation). During the
course of our experiments we chanced upon an unexpected
observation: freezing rates were much higher when
an ice-forming nucleus is near the surface of an undercooled
water drop than when the nucleus is immersed in the
drop (the nucleation rate at the water surface is
a factor of 10^10 greater than in bulk water). This
"surface crystallization" has important
implications for ice formation in clouds, and may
even provide insight on the fundamental behavior of
water at interfaces.
|
Trapping
of deep convective pollution by upper level anticyclones:
Implications for global change
Dr. Qinbin Li, NASA JPL
Convective outflow of pollution and
its subsequent long-range transport plays an important
role
in linking regional air pollution and global change.
Deep convection associated with summer
monsoons effectively ventilates two monsoon regions
with large surface emissions, the southern
United States and South Asia. The semi-permanent anticyclones
centered in the upper
troposphere over these regions can circulate (hence
'trap') the convective outflows from
these regions for days.
Over the southern U.S., an ozone maximum in the upper
troposphere in summer is predicted by
the GEOS-CHEM global 3D model of tropospheric chemistry
and transport, a prediction confirmed
by observations from the ICARTT aircraft campaign.
Model results indicate that rapid ozone
production (up to 10 ppb/day) takes place in the circulating
outflow. We find that this production
is driven in part by anthropogenic and lightning NOx,
and in part by reactive radicals produced
from convectively lifted formaldehyde produced from
biogenic isoprene emissions. (The ozone
production takes place near the transition between
NOx-limited and NOx-saturated regimes
for ozone production.)
Over South Asia, observations during 25 August-6 September
2004 from the
Microwave Limb Sounder (MLS) instrument aboard the
Aura satellite reveal
elevated CO concentrations and dense high-altitude
clouds in the upper troposphere,
collocated with the upper-level Tibetan anticyclone.
The observed dense high-altitude
clouds are accompanied with relatively little precipitation.
GEOS-CHEM simulations
indicate the transport of boundary layer pollution
including aerosols by Asian summer monsoon
convection to the upper troposphere over South Asia.
Analysis of simulated CO and aerosols
indicate that the upper-level Tibetan anticyclone
effectively ‘traps’ anthropogenic emissions
lifted from northeast India and southwest China. These
aerosols may be responsible for the
formation of some of the dense high clouds.
|
Where
does all the dirty air go? Insights from MTU and INSTAAR's
research at the PICO-NARE (Azores/Portugal) observatory
Dr. Detlev Helmig, University of Colorado
Emissions and transport of air pollution from continents
bordering the North Atlantic have been studied on
top of Pico Mountain in the Azores, Portugal. A remotely
controlled analytical system for the continuous, unattended
monitoring of non-methane hydrocarbons (NMHCs) was
developed. This instrument has some unique technical
features that allow operation at this site under the
challenging power, space and access conditions. Ten
10 different C2-C6 NMHCs have been monitored at this
site for more than a year. Data from these measurements
are used to research source regions and photochemical
processing of air reaching the station. Particular
areas of interest are the investigation of anthropogenic
pollution transport and boreal biomass burning events,
as forest fires have been shown and are predicted
to further increase due to the warming and summertime
drying of high northern latitude ecosystems. Air transported
from biomass burning events is frequently observed
at Pico during the summer. Ozone production in both
the anthropogenic outflow and in boreal biomass burning
plumes has been found to be higher than model predictions,
which is of high interest and concern, as an increase
in tropospheric ozone constitutes an important climate
feedback. The value of the Pico Mountain observatory
for atmospheric and climate research has been increasingly
recognized and has motivated new initiatives for incorporating
this station in the World Meteorological Organization
(WMO) - Global Atmospheric Watch (GAW) network.
|
Everglades
Restoration: Coupling Science and Engineering to Ensure
Success
Dr. Scot Hagerthy, Southern Waterways Management
Agency, Florida
The Everglades was once a large subtropical
wetland that encompassed more than 1.2 million hectares
of south Florida. Over the past century, more than
2700 km of canals and levees and hundreds of water
control structures have been constructed to drain
the wetlands for development, to serve as a water
supply, and to protect the residents from flood waters.
What remains today of the Everglades bears little
resemblance to predrainage conditions. Less than half
of the wetland still exists. The canal and levee network
has compartmentalized this once free-flowing system
and reduced flow volumes by an estimated 70%. Water
control structures discharge nutrient enriched runoff
into the wetland resulting in eutrophication. Two
major initiatives by the South Florida Water Management
District, the Army Corp of Engineers, and many other
agencies are underway to restore the Everglades. The
Long-Term Plan is mandated by the Everglades Forever
Act to improve water quality and to accelerate the
recovery of nutrient impacted areas. The Comprehensive
Everglades Restoration Plan (CERP) focuses on restoring
Everglades hydrology. The two programs are not mutually
exclusive. In this seminar, I will present how science
and engineering are being used to ensure restoration
success.
|
Resurrection
Ecology:
Chasing Van Valen’s Red Queen Hypothesis
Charles Kerfoot
Department of Biological Sciences, Michigan Tech
Testing modern communities for reaction to change involves
a dilemma of dimension. How can you test responses that
presumably occur over generations? Caught between fossils
and genetic reconstructions of phylogenies based on
modern organisms, we advocated taking an experimental
approach to paleoecology. We found that one can evaluate
the prey portion of Van Valen’s Red Queen hypothesis,
that species “must continually evolve just to
stay in place”, by retrieving diapausing eggs
from lake sediments for laboratory tests of evolutionary
responses. In one of the original studies, the sediments
consisted of core samples from Portage Lake, which were
dated by a combination of varve counts and radioisotope
(137Cs and 210Pb) techniques. Predators and prey were
followed for nearly a century. The technique is now
being refined to address how many partners are in the
evolutionary “dance”, quantifying how fast
communities are changing, and inspecting “transitional
series” and speciation.
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