Use of drones and hyperspectral imagery to remotely sense vegetation … · Use of drones and...

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Use of drones and hyperspectral imagery to remotely sense vegetation patterns at wetland restoration sites Columbia River Estuary Conference April 2018 Astoria, OR Carla Cole Robert Erdt, Joe Aga, George Pierce Amy Borde, Andre Coleman Curtis Roegner

Transcript of Use of drones and hyperspectral imagery to remotely sense vegetation … · Use of drones and...

Page 1: Use of drones and hyperspectral imagery to remotely sense vegetation … · Use of drones and hyperspectral imagery to remotely sense vegetation patterns at wetland restoration sites

Use of drones and hyperspectral imagery to remotely

sense vegetation patterns at wetland restoration sites

Columbia River

Estuary Conference

April 2018

Astoria, OR

Carla Cole

Robert Erdt,

Joe Aga,

George Pierce

Amy Borde,

Andre Coleman

Curtis Roegner

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EVALUATION OF RESTORATION PROJECTS

1. Each restoration project is

essentially an experiment with its

own particular variables:

1. History/age

2. Forcing functions (hydraulic reach)

3. Desire outcome / goals

2. Hydrology and landscape so

altered that there is no going back

to past conditions

1. Freshet/ disturbance, sedimentation

levels all reduced and timing changed

➢ Ecological engineering requires

post-restoration evaluations to

determine Restoration trajectories

1. Time series data of key metrics for change

analysis and adaptive management

✓ Hydrological Data

Fish habitat utilization –PIT/Acoustic

tags

Vegetation –from transect t remote

sensing

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Monitoring restoration trajectories

Key metrics:

Structural

• tidal channel geometry

• Topography

✓ Vegetation community

• Salmo –centric: prey production

➢ Equip a drone system with a

hyperspectral imager and develop

methods to measure restoration

trajectories.

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Principals of Hyperspectral Imagery

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Hyperspectral Datacube:

(Spatial pixels) * spectral channels

(X * Y) * l

Principles of Remote Sensing - Centre for

Remote Imaging, Sensing

...www.crisp.nus.edu.sg

Spectral signatures used for

object identification

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PROJECT GOALS

1. Equip and test a UAV system

with a hyperspectral imager.

2. Conduct field measurements,

and build Spectral Library

3. Develop data analysis

routines and analytics for

critical metrics.

4. Test Procedures at other

Field Sites

Colewort Creek National Historical Park

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April 16, 2018 6

Hyperspectral Camera Characteristics

BaySpec OCI-100 BP150

Pushbroom Hyperspectral Imager

Spatial Pixels: 2000 pix x scan-length

Spectral Range: 450-970nm

Spectral Resolution: 5nm

Spectral Bands: 104

Speed: 120 fps

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SPECTRAL LIBRARY

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Catalog of object-specific spectra

Data Acquisition

Spectral signatures of vegetation

and topographic features:

Plant1

Plant3

Plant2

Water

Herb

Sps 1

Sps 2

Sps 3…

Shrub

Sps1

Sps 2

Sps 3…

Tree

Sps 1

Sps 2

Sps 3…

Other Object

Bare Ground

Water

Structure

Spectral Library

1. Ground-truthed for PNW

habitats

2. Open sourced

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Wavelength

300 400 500 600 700 800 900 1000 1100

Ref

lect

ance

(D

evia

tio

n)

-60

-40

-20

0

20

40

60

80

CattailReed CanarygrassCommon spikerushLyngby sedge

Spectral signatures of Key

vegetation Types

Colewort Creek Ground truth stations

INFRARED

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Automation of Object Identification

OUTPUT (categorized maps & statistics)

A

Survey wetlands

DataCube

DATA COLLECTION

Spectral

Library Filters

Dialogs

ANALYITICS

Herb

Sps 1

Sps 2

Sps 3…

Shrub

Sps1

Sps 2

Sps 3…

Tree

Sps 1

Sps 2

Sps 3…

Other Object

Bare Groun

d

Water

Structure

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April 16, 2018 10

Hyperspectral Processing: Colewort Creek NHP test site

Example Hyperspectral Classification

Distinct spectral signature

AA = Water

B = Common spikerush & bentgrass

C = Lyngby sedge

RBGIMAGE

CATEGORIZED IMAGE

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Dead Typha latifolia(common cattail)

Carex lyngbyei(Lyngby sedge)

Bare Ground &20% Eleocharis palustris

(Common spikerush)

Eleocharis palustris(Common spikerush)

HyperspectralTrue Color (RGB) Classified

Utility

1. Mapping habitats

2. Restoration trajectory

3. Tidal channel evolution

4. Invasive monitoring

5. Spatial modeling

6. ….others!

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RGB True Color Classification

Limited spectral

information in RGB

data leads to poor

discrimination in

classification

True Color Hyperspectral

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Orthophotogammetry

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KARLSON

124.47 124.52 124.57 124.62

10

8

6

4

2

0

ChironomidTotal prey

Day of year 201

129.58 129.63 129.68 129.73

(10

3 I

nd/5

min

)

0

2

4

6

8

10

Forested

Emergent

Forested

Emergent

Pre

y Ex

po

rt

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COLEWORT

steamboat

KARLSON

Algal Blooms

Seagrasses//

Oyster culture

Bird colonies

& Sea lion Haul-

outs

OTHER APPLICATIONSNOAA UAS project

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Funding from NOAA UAS and NOAA Fisheries