Transcript Document
Using Airborne
Remote Sensing in
GM Risk Assessment
Luisa Elliott, Dave Mason
Joel Allainguillaume & Mike Wilkinson
AIM:
To model gene flow
from oilseed rape to
Brassica rapa (a wild
relative) on a national
scale
What is GENE FLOW?
Gene flow is the movement of
genes between populations
CROP
CROP
WILD RELATIVE
Why does gene flow need to be
modelled?
•The safety of Genetically Modified (GM)
crops is the subject of much debate worldwide.
•For a hazard to occur from the movement of
transgenes a series of events must occur.
•Gene flow represents the first step and can be
measured by the formation of hybrid plants.
Current gene flow model
•Landsat images used to detect the oilseed rape
•B. rapa grows mainly on riverbanks –
historical information was combined with
ground survey data to work out which river
systems contain the wild relative
•Oilseed rape fields that grew next to
waterways were identified and a spatial model
of gene flow was developed
Hybrid numbers
•Amount of oilseed rape growing next to
waterways was combined with river survey
data to enable estimation of hybrid numbers
•Number of hybrids = 26,000 per annum in the
UK
•BUT … this prediction has a large confidence
range of 22,000 …
•The large error margin is mainly due to
uncertainties in the distribution of B. rapa
•138,000km of banks predicted to contain B.
rapa
•We have surveyed about 500km of river and
canal banks by boat and foot (less than 1% of
total!)
•The tributaries are generally not accessible
•Therefore, we need to assume that the
surveyed areas represent all waterway banks
Airborne remote sensing provides
a useful tool for surveying
inaccessible places and at a much
faster rate than field work
NERC-ARSF obtained approx 85km of both
ATM and CASI –2 data in May 2003 (7 flight
lines).
Hypotheses to test
1. B. rapa occurs on the tributaries in the
same frequency as along the main rivers
2. B. rapa seeds are carried in waterways and
dispersed onto the banks during flooding
events
How to test the hypotheses
•Compare the distribution of B. rapa along
the banks of main rivers with that of their
tributaries
•Compare the distribution of B. rapa along
river banks with that of along canal banks
(canals do not flood)
First step is to identify B. rapa
in the aircraft images
•Unsupervised K-means classification (in
conjunction with ground survey information)
successfully used to detect the larger
populations (>2m x 2m)
•Populations detected more accurately in the
ATM images than the CASI
i.e. extra spectral information more
important that increased spatial resolution
•Unsupervised K-means classification is not
suitable for all images because it is not
possible to obtain sufficient ground reference
data for all flight paths.
•Need to calibrate images, to enable
classification of one image using ground
reference data from a different image.
•Cross-track illumination correction function
in ENVI used to correct for reflectance
differences across the width of each swath
•Flat field correction then carried out to
correct for differences between images (dark
water pixels used to represent the flat field
pixels).
An example of an image before and
after cross-track and flat field
calibration
•After calibration, a supervised maximum
likelihood classification was used for one
image using spectral information from a
separate image to train the classifier.
•This method was tested for an image in
which all B. rapa positions were known and
resulted in the detection of 94% of the correct
total number of plants.
Therefore, large B. rapa
populations can successfully be
identified in the ATM images,
even if we have no ground
reference data for that image.
But what about the smaller
populations?
The large populations account for 95% of the
total plant numbers and 14% of the total
population numbers
Matched filtering (in ENVI) can
be used to detect smaller
population (>1m x 1m)
•Combining results of matched filtering with
results of large population classification
enables detection of 99% of the plants and
79% of the populations (of at least 1m x 1m
in size)
•Populations >1m x 1m for 98% of plant
numbers and 32% of population numbers.
Progress so far …
•Cross-track illumination correction followed
by flat-field calibration can be used to
normalize images and enable classification of
one image using spectral information from an
independent image
•Supervised maximum likelihood
classification can detect large populations
(>2m x 2m)
•Matched filtering can be used to detect
smaller populations (>1m x 1m)
Still to do …
•Classify all images and look at overall
distribution of B. rapa.
•Test the hypotheses and update current
model of gene flow.