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Synergistic Use of Datasets from Multiple Instruments for Earth Science Research Ivan A. Csiszar, University of Maryland : Hazards Simon J. Hook, Jet Propulsion Lab. : Hydrology - Presenter Vince J. Realmuto, Jet Propulsion Lab : Hazards Thomas Schmugge, New Mexico State University: Ecology

Synergistic Use of Datasets from Multiple Instruments for ... · Atmosphere: Decreased Temperature Contrast, Increased Atmospheric Absorption and Emission Mapping Passive SO2 Emissions

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Page 1: Synergistic Use of Datasets from Multiple Instruments for ... · Atmosphere: Decreased Temperature Contrast, Increased Atmospheric Absorption and Emission Mapping Passive SO2 Emissions

Synergistic Use of Datasets fromMultiple Instruments for Earth

Science Research

Ivan A. Csiszar, University of Maryland : HazardsSimon J. Hook, Jet Propulsion Lab. : Hydrology - PresenterVince J. Realmuto, Jet Propulsion Lab : HazardsThomas Schmugge, New Mexico State University: Ecology

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Outline• Hazards

– Mapping volcanic plumes (V. Realmuto)– Active Fire monitoring (I. Csiszar)

• Ecology– Calculating broadband emissivities for climate models (T.

Schmugge)• Hydrology

– Measuring nutrient distribution in large lakes (S. Hook)• Critical factors limiting use of multi-instrument data• Wrap-up and ways to increase multi-instrument studies

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OBJECTIVES OF PLUME MAPPING

Track Changes in SO2 Emission RateDetect Passive Emissions Before an Eruption Occurs

Eruptions May be Preceded by Changes in Emission Rate

Few Volcanoes are Monitored with Necessary Frequency toEstablish Baseline Emission Rates

Satellite Remote Sensing –> Facilitate Monitoring

Study the Fate of SO2 in AtmosphereConversion to Sulfate Aerosols

Local/Regional Hazard to Respiratory Health

Regional/Global Climate Forcing

Nucleation Sites for Polar Stratospheric Clouds ->Catalysts for Ozone Depletion

Page 4: Synergistic Use of Datasets from Multiple Instruments for ... · Atmosphere: Decreased Temperature Contrast, Increased Atmospheric Absorption and Emission Mapping Passive SO2 Emissions

Mapping Passive SO2Emissions from SpacePu’u O’o Plume MapDerived from ASTER 90mTIR Data

High Spatial Resolution (90m) => High Sensitivity toPresence of SO2

Mitigating Factors

Small Plume: typically 1 kmin thickness and width

Low Altitude (typically 1.5km asl): Low TemperatureContrast

Warm, Humid TropicalAtmosphere: DecreasedTemperature Contrast,Increased AtmosphericAbsorption and Emission

Mapping Passive SO2Emissions from SpacePu’u O’o Plume MapDerived from ASTER 90mTIR Data

High Spatial Resolution (90m) => High Sensitivity toPresence of SO2

Mitigating Factors

Small Plume: typically 1 kmin thickness and width

Low Altitude (typically 1.5km asl): Low TemperatureContrast

Warm, Humid TropicalAtmosphere: DecreasedTemperature Contrast,Increased AtmosphericAbsorption and Emission

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AIRS Data Acquired over Mount Etna EruptionPlume: 28 October 2002Constituents of Volcanic Plumes Amenable to SatelliteRemote Sensing: SO2, Silicate Ash, Sulfate Aerosol

Rare in “Normal” Atmosphere - Relatively LowConcentrations Can Be Detected in the Thermal IR (TIR)

Forward ModelingResultsMODTRAN, CHARTS,LBLTran run at 1 cm-1

resolution

SO2 concentrationsbetween 0.25 – 0.50mg/m3

Silicate Ash Loading >>Sulfate Aerosol Loading

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3 November 2002

ASTER VNIR (15 m)True-Color Composite

2002-2003 Eruption Of Mount Etna

27 Oct 2002 – 29 Jan 2003

Terra/Aqua Record:

At least one daytime MODIS overpass perday

At least one daytime AIRS overpass every2 days

Two MISR overpasses (one day apart)every 16 days

90 ASTER acquisitions between June andDecember 2002

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TIR False-ColorComposite

True-Color Composite

Plume Top Altitude: 6 kmPlume Base Altitude: 5 km

TIR False-Color CompositeIndicates Dominance of ashover SO2

MODIS-Terra

27 October 200210:02 UTC

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MODIS-Aqua

28 October 2002, 12:15 UTC

Plume Top Altitude: 6 kmPlume Base Altitude: 5 km

TIR False-Color CompositeIndicates Dominance of ashover SO2

TIR Color Composite

True Color Composite

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AIRS28 October 2002

Plume Top Altitude: 6 kmPlume Base Altitude: 5 km

AIRS Misfit to Data is ~ 2XThat of MODIS

Need to Upgrade Version ofMODTRAN Used in MAP_SO2

True Color Composite

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MODIS-Aqua vs. AIRS28 October 2002

MODIS SO2 Map Re-Sampled to ~ 17 km

Lower Spatial Resolution of AIRS Results in LessSensitivity to Small (~ 3 g/m2) Changes in SO2 Burden

MODTRAN Upgrade will Improve the Sensitivity of AIRS-Based SO2 Retrievals

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True Color Composite

TIR Color Composite

MODIS-Terra

29 October 2002, 09:45 UTC

Plume Top Altitude: 6 kmPlume Base Altitude: 5 km

TIR False-Color CompositeIndicates Dominance ofAsh over SO2

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SUMMARY REMARKS…

Retrievals Appear to be ConsistentThree Days of Activity; Three Instruments

MAP_SO2 Does Not Introduce Systematic Bias

AIRS-Based Retrievals in General Agreement withMODIS- Based Retrievals

Future EffortsFocus on Days with Terra and Aqua Overpasses(eg. 27 Oct 2002)

Begin ASTER Processing (30 December 2002)

Incorporation of MISR-Based Plume Geometry

MODTRAN Upgrade

Incorporation of AIRS-Based AtmosphericProfiles

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Using ASTER data to validatethe MODIS active fire product

Ivan [email protected]

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Key Benefits

• ASTER can be used for detecting active firesthat are much smaller than the lower MODISdetection limit

• ASTER and MODIS on same platform (perfecttemporal coincidence)

• Disadvantages: ASTER has limited angularrange, saturates (partly addressed with multiplegain settings) and limited availability

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Coincident MODIS and ASTER activefire observations

ASTER, 8-3-1 RGB (30m) + 1km MODIS grid:MODIS detections in color

July 23 2002 03:18 UTC62.57N 125.72E (Siberia)

MODIS v4 detection:

Yellow gridcells:“fire”, high confidence

Blue gridcells:“fire” nominal confidence

Gridcell with vertical shading:“cloud”

Black gridcells:“clear land”

Csiszar et al., submitted

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Morisette et al., in press

ASTER imageand MODIS grid

of BrazilianACRE file

Aug 29 2003 14:56 UTC9.71S 67.15W (Brazil)

Note: fires visiblethrough clouds in lowerleft corner. No standardASTER fire products

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Morisette et al., in press

ASTER firemask and

MODIS grid

Aug 29 2003 14:56 UTC9.71S 67.15W (Brazil)

ASTER firedetectionalgorithmdeveloped byLouis Giglio

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Comparison with coincident high-resolution satellite observations

Probabilities of detection as a function ofASTER fire pixels within MODIS pixel

?á: MODIS “fire”; ?�:MODIS “no fire”

P(MNF|AF)

0

0.1

0.2

0.3

0.4

0.5

0.6

0.7

0.8

0.9

1

0 100 200 300 400 500 600 700ASTER threshold

Pro

babi

lity

Pixel-based accuracy assessmentcurve with 95% exact confidenceintervals: omission error rate

NPOESS/VIIRS/LANDSAT active fire validation!

Csiszar et al., submitted

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Calculating BroadbandEmissivities for Climate Models

Tom SchmuggeNew Mexico State University

Approach: Extend from small to largetarget, from ASTER to MODIS

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ASTER TIR Response

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ASTER VNIR White Sands May 21, 2001

63 X 63 km 22 X 22 km

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ASTER TIR White Sands May 21, 2001

GroundMeasure-mentSite

Red > 10.7 umGrn > 9.1 umBlu > 8.6 um

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Study area: Sahara Desert in NorthAfrica

200 scenes of ASTER data acquired from 2000 to2002Size of area 400 x 1500 km

35°

30°

25°

5° 10° 15°

study area

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MODIS Nadir Adjusted ReflectivityMonthly Composite – 0.05

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ASTER emissivity imageCh.10 8.3 µm Ch.11 8.6 µm Ch.12 9.1 µm Ch.13 10.7 µm Ch.14 11.3 µm

0.6

1.0

0.8

0.7

0.9

Emissivity of ASTER channels

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Broad band EmissivityDerived FromRegression of

5 ASTER Bands

0.85

1.00

0.90

0.95

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MODIS Products

0.6

1.0

0.8

0.7

0.9

Reflectivity

Emissivity8.6 µm

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Window Emissivityε8-12 = 0.987 – –

0.08316 7

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Comparison: MODIS Estimated vsASTER Observed

Bias = -0.0083RMSE = 0.0181

MODIS

ASTER

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Conclusions

• ASTER and TES work very well– Quantitative agreement ( 1 – 2%) withlab and field measures at White Sands

– ASTER Results are repetitive– Emissivity mapping on a regional scale– Extend to Global scale with MODIS

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Mapping Nutrient Transport inLakes

Simon J. [email protected]

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Measuring Nutrient TransportIn Lakes

Simon J. [email protected]

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2000-09-20-D

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Infrastructure:• Four NASA buoys• Two UCD buoys• Multiple meteorological stationsaround lake

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Temperature Trace from TR4 forJanuary of 2000TR4 Jan 6 2000 - Feb 10 2000

4.00

4.50

5.00

5.50

6.00

6.50

7.00

7.50

8.00

1/7/0010:30

1/11/0010:30

1/15/0010:30

1/19/0010:30

1/23/0010:30

1/27/0010:30

1/31/0010:30

2/4/0010:30

2/8/0010:30

Time

h303007

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ASTER

6/3/01

ASTER 6/03/2001

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ASTER 6/03/2001MODIS 6/03/2001

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ASTER

7/22/01

ASTER 7/22/2001

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MODIS 7/21/2001, 19:00 GMT MODIS 7/22/2001, 06:05 GMT

ASTER 7/22/2001, 06:05 GMTETM+ 7/21/2001, 18:28 GMT

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Landsat ETM+ ASTER

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Current Tracking withLandsat ETM+ and ASTERData using MaximumCorrelation Method

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Critical Factors Limiting Use ofMulti-Instrument Data

• Interoperability/Protocols/Standards• Information Assurance and Security• Hardware/Software• Infrastructure/Bandwidth• Human and Institutional Capacity

From: Strategic Plan for the U.S. Integrated EarthObservation System

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Critical Factors – Real World• Geospatial data but cannot be accessed geospatially

– Need to subset down to pixel level when order!• Every pixel needs a latitude and longitude

– No subset lattices or corner points – use double precision.• Data stored in multiple projections

– Need default, common projection• Data ordering should not require a human in the loop

– Implement SIMPLE subscription service• Software lacks scripting

– More toolkits with scripting support e.g. Python and PIL• Open access

– Allow users to FTP for free small subsets e.g. USGS NED approach

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Wrap-Up• Need Leadership from the top input with input

from the bottom.• Need clearly articulated vision for where we want

to go and why.• Need a system which can be used by the

individual without requiring large institutionalinfrastructure

• Need clear milestones with tangible results– Roadmaps, Data Fusion working group?

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With Special Thanks to:

Ivan A. Csiszar, University of MarylandAshley Davies, Jet Propulsion LabVince J. Realmuto, Jet Propulsion LabRob Sohlberg, University of MarylandThomas Schmugge, New Mexico State University