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Mapping the Invasive Species Chinese Tallow U.S. Department of the Interior U.S. Geological Survey

Chinese Tallow - EOC

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Page 1: Chinese Tallow - EOC

Mapping the Invasive SpeciesChinese Tallow

U.S. Department of the InteriorU.S. Geological Survey

Page 2: Chinese Tallow - EOC

Sapium sebiferum (L) Roxb.

Common names: Chinese Tallow, AsianTallow, Popcorn Tree, Florida Aspen,Chicken Tree.

Page 3: Chinese Tallow - EOC

■ Introduced in 1700’s

■ Aggressively competes

■ Spread by birds and floodwaters

■ Sold as ornamental plants

■ Sapping monetary reserves

■ Once established, extremelydifficult to eradicate

Page 4: Chinese Tallow - EOC

Distribution Has Never Been MappedA method to map Chinese Tallow has not been developed

■ Monitor success oferadication efforts

■ Control the further spread

■ Understand the sensitivity

■ Identify activities thatincrease the risk

Page 5: Chinese Tallow - EOC

Less Than 1 Minute

185 km

36 km

7.7 kmLandsatMultispectralImages(185 km @ 30 m)

705 km705 kmAltitudeAltitude

AVIRIS Underflight(10 km @ 20 m)

Multispectral Images(36 km @ 30 m)

HyperspectralAtmospheric Correction(185 km @ 125 / 250 m)

Grating-basedGrating-basedHyperspectralHyperspectralImagesImages(7.5 km @ 30 m)(7.5 km @ 30 m)

Landsat-7 EO-1

HelicopterUnderflight(Variable)

Page 6: Chinese Tallow - EOC

■ High spatial resolution color infrared photography

▼ Collected in November 1997 in coastal Louisiana

▼ Collected from an aircraft platform (about a 0.5 m IFOV)

▼ Ramsey, E., III, G. Nelson, S. Sapkota, E. Seeger, and K.Matella. Mapping Chinese Tallow with color-infraredphotography. Photogrammetric Engineering and RemoteSensing-in press.

■ Moderate spatial resolution hyperspectral data

▼ Proof of concept: Simulation of Hyperion sensor data

▼ Restricted to visible and near infrared and about a 25 mIFOV

Detecting and Mapping Chinese Tallow

Page 7: Chinese Tallow - EOC

A

B

C

D450 550 650 750 850 950400 500 600 700 800 900 1000

Wavelength nm

0.05

0.15

0.25

0.35

0.45

0.00

0.10

0.20

0.30

0.40

0.50

Ref

lec t

a nce

Leaves

A Green

B Bright Red

C Medium Red

D Dark Red

Chinese Tallow (Sapium sebiferum)Leaf Reflectance

Page 8: Chinese Tallow - EOC

Hyperspectral Reflectance Signatures and LandsatThematic Mapper (TM) Bands

TMB

and

1

TMB

and

2

TMB

a nd

3

TMB

and

4400 500 600 700 800 900 1000

Wavelength

0.00

0.10

0.20

0.30

0.40

0.50C

ano p

yan

dLe

afR

efle

c ta n

ce

Green Leaf

Red Leaf

Canopy

47% With Red Tallow

37% No Leaves

~ 100% Tallow

Page 9: Chinese Tallow - EOC

Hyperspectral Canopy Reflectance Data

■ Simultaneous collections with two radiometers

▼ One collecting downwelling sunlight at a fixed position onthe ground

▼ One collecting light reflected from the vegetation takenfrom a helicopter platform about 230 m above the ground

▼ Spectral data restricted to the visible to near infrared

▼ The ground spatial resolution was about 25 m IFOV

▼ Canopy reflectance data at over 30 sites were generatedfrom the two radiometers

Page 10: Chinese Tallow - EOC

Classified 35-mm Color PhotographyTaken From Helicopter

35-mm Color PhotographyTaken From Helicopter

Observed

Page 11: Chinese Tallow - EOC

Radiative Transfer and Optimization model

■ Inputs▼ Average red (tallow) and green (tallow and pine) leaf

reflectances

▼ Average ground reflectances (hardwood, pine, grassland)

▼ Sun and view geometries (sun zenith and azimuth at thetime of the helicopter collection at each site)

▼ Relative skylight (estimated from airport visibilities)

▼ Note: the optimization was not well conditioned and certainvariables (e.g., leaf angle) went outside reasonable limitsduring many analyses

Page 12: Chinese Tallow - EOC

Radiative Transfer and Optimization model

■ Prediction▼ The amounts of red and green leaf reflectance, leaf area

index, and leaf angle distribution were varied to givethe closest match to the site-specific generated canopyreflectance

▼ The closest match was the predicted canopyreflectance at each site

▼ The amount of red leaf reflectance added in theoptimization was the estimate of the percent of redtallow leaves at each site

Page 13: Chinese Tallow - EOC

Date Site Path Row Image Quality4/11/01 Tallow West 24 39 95% clouds4/27/01 Tallow West 24 39 90% clouds5/13/01 Tallow West 24 39 Good Image5/29/01 Tallow West 24 39 90% clouds.6/14/01 Tallow West 24 39 85% clouds8/1/01 Tallow West 24 39 100% clouds

8/17/01 Tallow West 24 39 100% clouds9/18/01 Tallow West 24 39 80% clouds

8/26/01 Lafayette 23 39 95% clouds

7/2/01 Lake DeCade 22 40 95% clouds8/3/01 Lake DeCade 22 40 100% clouds

5/8/01 Pascagoula 21 39 100% clouds8/28/01 Pascagoula 21 39 100% clouds9/29/01 Pascagoula 21 39 Good Image

10/20/01 Tallow Central 24 39 Good Image

EO1 Image Collections and Image Quality

Page 14: Chinese Tallow - EOC

Summary■ Red Chinese tallow leaves can be detected and mapped with

very high spatial resolution CIR photography

▼ The data volume and labor necessary are high, suggestingfairly high costs would be associated with mapping smallareas

■ Red Chinese tallow leaves percentages may be detected andmapped with Hyperion type sensors with about a 25 m IFOV

▼ Results from the Radiative Transfer and Optimizationanalyses may not be directly applied to Hyperion imagedata. Initial starting points were not constant in alloptimizations and some inversions resulted in negative arrayelements.

Page 15: Chinese Tallow - EOC

Summary, cont’d

■ Problems occur in marsh and prairie landscapes, but some ofthese may be linked to the IFOV’s differences between the 35mm slide and radiometer

■ Use of spectral differencing (selective broad band) may alsoincrease the detection and mapping capabilities in marsh andprairie landscapes

■ Future addition of an endmember analysis tool should furtheradvance the capabilities of detecting and mapping ChineseTallow

■ We hope for successful Hyperion and ALI collections onNovember 5, 2001