Title: Assessing forest cover from the air and space
1Assessing forest cover from the air and space
2Group Work
- How well equipped is your country to use remotely
sensed data? - How will remotely sensed data fit into your REDD
plans?
3How well equipped is your country to use remotely
sensed data?
- Human resource
- FA GIS/RS unit 8people
- GIS specialist 3 people but need more training,
especially skill in data interpretation and the
use of other algorithms in data processing - Data Currently has satellite data for 2002-2006
(Landsat ETM) Need more time series satellite
image data with higher resolution. - Financial support for Improving GIS unit within
the Forestry Administration to monitor forest
cover change on regular basis.
4 How will remotely sensed data fit into
Cambodia REDD plans?
- Remote sensing data might be fit well as we
already have a GIS unit that has done forest
cover change analysis. But the current unit need
to be improved for enabling the system to do
forest monitoring in regular basis
5Laos
- Use of RS data
- Use is made of Spot 1, 2, 3, 4, ALOS
- Several institutes are involved
- Forest Department has RS/GIS facility
- Capacity must be upgraded, training, software
- RS REDD
- RS for baseline survey, forest classification
- Pilot studies for carbon stock determination in
shifting cultivation areas
6Nepal
- Use of RS
- Institutional Department of Forest Survey, well
equipped, not enough resources, technical experts
in RS and GIS but need more training - Monitoring systems, but not compatible with REDD
- Financially not a priority, expensive to afford
- REDD RS
- Identification of priority areas
- Identification of deforestation and degradation
7Vietnam
- Use of RS
- Forest inventory started long ago, 1950s, with
aerial photography in northern Vietnam - In 1990s forest assessment and monitoring, using
RS Spot 1 - 1996-2000 use of Landsat ETM
- 2004 Landsat ETM
- Ongoing program with plans for 2005-2010
- Also use of QB, Aster, PALSAR, etc
- Software Erdas Imagine, ENVI, ILWIS
- RS for REDD
- Spot-5 for baseline survey in 10 out of 45
provinces area, volume - RS for biomass in the future, needs more research
- Capacity building in latest technology, also in
univerities - Knowledge on biomass assessment required
8Why assess forest cover?
- Easiest forest attribute to measure remotely from
above (air or space) - Measure of deforestation (forest cover goes from
100 to 0) and degradation (forest cover goes
from 100 to between, say, 20 and 80) - But is it human-induced or natural decrease in
health? - Difficulties
- Comparability over time
- Scale (resolution) needs to be right
- Image problems clouds, topographic shadowing
- Relating to ground estimates
9Forest cover, degradation deforestation
FC60
Degradation
Deforestation
FCgt100
FCgt0
10Aerial photography
- Positives
- 110 000 to 180 000 OK for interpreting forest
cover - Past (historic) images often available
- Easily handled manually
- Familiar view (especially if natural colour)
stereo - Can be collected on demand (avoiding cloud cover)
- Negatives
- Geometric distortions make transfer to maps
difficult - Usually, limited to visible band of spectrum
- Difficult to handle large numbers and to automate
- Manual interpretation open to bias
- Quite expensive unless multi-purpose
11Satellite imagery
- Positives
- Minor geometric distortions easily corrected
- (Relatively) Easily transferred to maps
- Measurement of forest cover easily automated -
unbiased - Not limited to visible region of spectrum
- Wide range of sensors and resolutions now
available - Now (except very high resolution) relatively
cheap - Historical data back to 1972
- Negatives
- Rarely can collect on demand (so cant dodge
clouds, etc) - Satellites have limited life no guarantees of
carry-on - Each satellite/sensor has unique
characteristics/challenges
12Remote sensing systems for REDD
- What kinds of remotely sensed data are needed for
REDD projects? - Reasonably high resolution (1 ha or better)
- Spectral bands that can detect vegetation changes
and differences (e.g., visible, NIR, radar) - Previous historical data needed
- At least annual, cloud-free complete coverage
- Assured continuity of data-types
- No one system meets all these criteria but
Landsat and SPOT come closest
13Landsat
- Common characteristics
- Altitude about 700 km
- Repeat cycle 18-16 days vertical views
- Sun-synchronous (about 930am), near polar orbit
- Global coverage, now mostly available at nominal
cost - Landsat MSS (multispectral scanner) (NASA, USA)
- First 1972-85 Landsats 1, 2, 3 4
- Pixel size about 60m X 80m
- 3 visible (blue, green, red), 1 NIR bands
- Landsat TM (Thematic Mapper)
- 1982- Landsats 3, 4 5
- Pixel size 30 m
- 7 bands (3 visible, 3 IR, 1 TIR)
- Landsat ETM (Enhanced TM plus)
- 1999- Landsat 7 rest similar to TM but 15m
panchromatic added
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15SPOT (Satellites pour lObservation de la Terre)
(France)
- Common characteristics
- Altitude about 800 km
- Repeat cycle 26 days but pointable (oblique)
views possible - SPOT 1, 2 3
- 1986-
- Resolution 20 m MSS 10 m Panchromatic
- 3 spectral bands (2 visible, 1 NIR)
- SPOT 4
- 1998-
- Extra 20m band in MIR
- SPOT 5
- 2002-
- 4 MSS bands with 10m resolution panchromatic
with 2.5/5m resolution - Stereo-pairs (N-S) possible
16SPOT 5 data bands 3 (NIR) 4 (MIR)
17Other possible RS systems
- MODIS (NASA)
- Launched 1999 one-off
- Frequent coverage (1-2 days), so easier to find
cloud free - Much larger pixels than L/S (250 m 1 km)
- 36 bands over visible to MIR (better
discrimination) - ALOS PALSAR (Japan)
- Launched 2006 (10 years after JERS-1)
- 10 m resolution
- L-band active radar
- Excellent delineation of topography, cuts through
cloud smoke - Indian and Chinese Landsat-look-alikes
- IRS-1A-D, first in 1988
- Chinese launches in 2006/7
18Classification of multispectral data
- Supervised classification
- Locate a number of typical sites on the ground,
e.g. mature natural forest, recently disturbed
forest, secondary forest, plantation, rice field - Determine average spectral pattern (signature)
for each - Examine every pixel in scene and classify it
according to the closest signature and map the
scene accordingly - Unsupervised classification
- Examine every pixel and put them into classes
according to how close they are to each other - Determine the class means and limits and map the
scene - Use ground truth information to give the
classes a label.
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20More complex classification
- Classify groups of pixels rather than individual
ones, e.g., stands rather than trees - Classify based (partly) on texture, i.e.,
relationship of pixel to its neighbours - Classify based on time-series (multi-date)
information, e.g. if a pixel shows the following
(annual) temporal pattern - WWWWRWWW -? mature forest
- WWBBRRRWR -? regenerating forest
- WWBBAAABAA -? cleared forest
- WWRRWWRW -? degraded forest
- where Wforest, Bundergrowth, Rregrowth,
Afarming
21A REDD monitoring system based on Landsat
- Basic characteristics
- Baseline dataset
- Annual updates
- Classification of each pixel according to whether
woody vegetation or not - Multi-date algorithm to determine whether forest
or not - More detailed analysis to determine whether
degradation has occurred and degree - Models to determine change in biomass ? C.
22- Australian National Carbon Accounting System-
- Forest subsystem
23REDD monitoring system more details
- Desirably should be part of a national carbon
accounting system for consistency - Only way to detect (within-country) leakages?
- What remote sensing data are most suitable?
- Overall, Landsat TM (or something like it) seems
best appropriate resolution spectrally
spatially, temporal frequency OK, continuity
probable, historical data available,
idiosyncracies known - But radar (like PALSAR) may be necessary if
clouds are a problem and to detect (degree of)
degradation (experiments on this currently in
Tasmania Kalimantan)
24PALSAR data over the Amazon(2006)
(http//www.eorc.jaxa.jp/ALOS/img_up/l_jers_palsar
_amazon_e.htm)