DNR Homepage Search the DNR Web Site DNR Events Calendar Send the DNR Comments DNR Web Site Index Three of North America's ecological regions, or biomes, converge in Minnesota: the prairie, deciduous forest and coniferous forest.

Change Detection Methods

Landsat Satellite Images

DNR Forestry uses Landsat Thematic Mapper (TM) images to map Minnesota land cover and to set priorities for forest inventory work. For a fuller introduction to TM images and to view all the satellite scenes in DNR's collection, you can jump from here to another ForNet application, ImageView.

Landsat TM scenes are digital images, like pictures from digital cameras. Each is an array of dots called picture elements (pixels) in rows and columns. Every pixel (some 38 million in a full scene, each pixel covering about 1/4 acre) contains numerical values expressing its brightness. Whereas an ordinary digital camera records only blue, green and red brightness corresponding to the range of human vision, Landsat records an additional four sets from the near, middle and thermal infrared portions of the spectrum.

Analysis Overview

Digital images can be manipulated by arithmetic, as everyone who has brightened up a scanned snapshot on a PC knows. And just as time-lapse pictures can be used to illustrate natural processes, we can use Landsat images to show where changes have taken place between two images taken years apart. All we have to do is subtract a digital image taken at "Time 1" from a corresponding image taken at "Time 2." The results form a "difference image." Such image differencing is one of the simplest and most reliable change-detection techniques in remote sensing.

Trouble is, all sorts of irrelevant things can cause differences between images. If there is a cloud in the Time 2 image and none in the Time 1 scene, it will create a big patch of "difference." If Time 1 is a spring scene and Time 2 a fall scene, we'll detect a lot of seasonal "differences" that don't mean much in terms of long-term landscape change. Or if the two images aren't accurately registered to each other beforehand, the misregistrations will appear as "changes." So it's necessary to set certain conditions before attempting change detection:

  • Both images must show the same season--preferably summer, when vegetation conditions are relatively stable.
  • The two images must be accurately registered ("matched up") to the ground and to each other.
  • Cloud-affected areas must be removed from analysis.
  • The two images must be "radiometrically calibrated" to minimize effects of variations in sensing instrument performance and atmospheric haze between the two dates.

When these conditions are met, a difference image can reveal where significant changes have taken place in surface phenomena like vegetation. But that still may not be very informative. In Minnesota, the biggest vegetation changes between successive summers take place on the farm, as crops and cultivation methods rotate from field to field. These bold shifts--which don't mean much in terms of landscape ecology--overwhelm the subtler patterns of forest change we seek to trace. So before image differencing, we must also:

  • Broadly differentiate between forest and nonforest areas in both the Time 1 and Time 2 images.
  • Exclude from consideration all areas shown to be nonforest in both images.

If we carry out these preparatory steps satisfactorily, the pattern of between-date differences can tell us something about what kind of change is taking place in the forest. Green plants tend to absorb red light, for example, so a substantial increase in red brightness may indicate less vegetation at a location in the image. Near-infrared light is reflected by plants, so an increase in its brightness may mean more vegetation.

A typical look at the ChangeView interface, displaying data from an area of severe windstorm damage, is shown below. We present the Time 1 image on the left and the Time 2 image on the right, with the difference image between them.

8/30/90 TM Image Change Image 8/30/96 TM Image

A simple legend is employed to explain the difference image. It is based on the fact that brightness differences between corresponding pixels in the two images tend to form a bell-shaped distribution about a mean of "no difference."


The values in the central 80 per cent of the curve (1.3 standard deviations from the mean, in statistical terms) are considered to represent negligible "background" differences, while the outer portions of the curve represent significant changes. These change thresholds are arbitrary: we could depict virtually the entire forest as "change," and that would be true--everything in the forest is changing all the time--but our purpose is to show where the large, landscape-affecting alterations are occurring. Values on the left of the distribution (red and orange in the difference image) are changes in the direction of less vegetation: land clearing, forest cutting, roadbuilding. Values on the right (dark and light green in the difference image) are changes in the direction of more vegetation: reforestation and regrowth. These classes are labelled in the ChangeView interface legend using the more readable English phrasing shown here, however, it is useful to keep in mind the statistical basis of the classes.

Analytical Strengths and Weaknesses

This sort of strictly statistical presentation of forest change is both relatively easy to perform and objective in nature, but it has disadvantages as well. For example, it says nothing about the causes of vegetation loss and gain: wind damage, timber harvesting and beaver flooding are lumped together as losses; desirable and undesirable regrowth as gains.

Most importantly, as indicated in the diagram above, the arbitrary statistical thresholds will display roughly the same proportionate acreages of "change" and "no change" no matter what has actually happened in the area analyzed! This means it is not possible, using this method of presenting forest change, to compare analysis units and say which has shown most vegetation loss; nor can a user determine whether vegetation gain or loss is more prevalent within an analysis unit, as both will be depicted at approximately the same level. Satellite image analysis can in fact answer these questions (and others), but the answers are more costly to obtain and more difficult to standardize across large regions.

The strength of the current presentation is that it quickly pinpoints where major forest changes have occurred within the area covered by two images taken at different dates. Future versions of ChangeView may allow the user a greater choice of change detection displays, and perhaps even identify causative agents. For now, we hope this provides some insight into the workings of a new and powerful tool for exploring changes in the patterns of Minnesota's landscapes.

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