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THE GREAT LAKES

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such as photosynthesis and transpiration within the canopy<br />

(Sellers 1985, 1987) . The close connection of absorbed<br />

photosynthetically active radiation (APAR: .4-.7 pm) to<br />

chlorophyll density, which can be estimated remotely, leads<br />

to near-linear relationships among canopy properties of<br />

APAR, photosynthetic capacity P C , minimum 7<br />

resistance (lr), and the two vegetation indices.<br />

Theoretically, integrating multitemporal measurements of<br />

reflected radiation in a given region should provide an<br />

estimate of gross primary productivity (Tucker and Sellers<br />

1986).<br />

Likewise, satellite and aircraft sensors provide a way<br />

to observe water body dynamics and biological productivity.<br />

The greatest degree of light penetration into water occurs<br />

in the visible wavelengths, also the'region of chlorophyll<br />

absorption. Patterns of surface planktonic biomass and<br />

chlorophyll fluorescence can be used to derive estimates of<br />

primary productivity. Patterns of phytoplankton pigment<br />

groups allow further delineation of the phytoplankton<br />

community into some functional group classes (e.g., Carder<br />

and Steward, 1985).<br />

Pollutants (both inorganic sediments<br />

and organic constituents) may affect the reflective or<br />

emissive properties of water bodies. Relative turbidity is<br />

easily detected as tonal changes in remotely sensed imagery<br />

(e.g. , Klemans et al. 1973 ; Strong 1978) . Wavelength bands<br />

in the thermal infrared estimate the surface temperature<br />

(upper few microns) of water bodies, from which plume and<br />

circulation patterns can be depicted (e.g., Schott and<br />

Schimminger 1981). Numerous ocean studies have shown that<br />

at microwave frequencies, where water is opaque to<br />

radiation, surf ace structural features such as currents and<br />

eddies are measurable (e.g. , Kasischke et al. 1984 ; Vesecky<br />

and Steward 1982) .<br />

The task of landscape ecology, as defined by Toth<br />

(1988), is to:<br />

1) discover, by way of analysis, which factors are<br />

operationally significant;<br />

2) determine how these factors bring about change in the<br />

landscape; and<br />

3) describe how these factors define the spatial (form)<br />

characteristics of a landscape.<br />

In light of these objectives and the foregoing discussion,<br />

the synoptic view of the land and seascape as provided by<br />

remote sensing instrumentation is essential to the analysis<br />

of large-scale ecological pattern and process. The<br />

critical issue is how best to interpret the emergent

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