The environment of Chamae'cyparis lawsoniana (A. Murr.) Parl. was measured at 10 or more sites in Oregon and California which represent six different plant communities. Water is probably the factor most limiting the species' distribution. Most populations have late summer predawn xylem pressure potentials above -11 bars. The eastern range boundary coincides with a rapid decrease in the ratio of precipitation to evaporation. The species is usually confined to wet ultramafic parent materials except at high elevations and in the N. Its southern limit may coincide with absence of consistently wet ultramafics. Success of Chamaecyparis on ultramafics may result from failure of Pseudotsuga and other competitors to cope with the chemical composition and saturation of these substrates. Foliar nutrient concentrations of C. lawsoniana are lower on ultramafics than on other soils, but have a high Ca:Mg ratio. Mycorrhizae show no differences associated with soil type. Despite a large temperature range in the habitat of C. lawsoniana, temperature does not seem to limit the species directly. Mean annual air temperatures range from 4.4-10.9 C. Especially at the northern end of the range, temperatures decrease more slowly in late summer than outside the range. Soils are cool, with little annual variation in areas with seepage. Chamaecyparis lawsoniana seems to be restricted by different aspects of the environment than are most dominant species with which it grows. Variations in temperature and parent material within its range are responsible for large changes in vegetation type without excluding the Chamaecyparis. Yet the changes in water availability which limit C. lawsoniana, often do not produce discontinuities in the other vegetation present. INTRODUCTION Chamaecyparis lawsoniana (A. Murr.) Parl. (Cupressaceae), Port Orford cedar, is endemic to the Klamath Mountain region of Oregon and California. It is of interest because: (1) It has a paradoxical distribution, being restricted to a limited geographic range but occurring on many diverse habitats (Fowells, 1965); (2) exploitation and a nonendemic root rot are rapidly decimating the natural forests; (3) the wood is very valuable; and (4) as Chama,ecyparis also grows in temperate habitats in Japan and Taiwan, comparison with studies of those species may clarify the meaning of our results. The distribution. vegetation, topographic and geologic relationships of Chamaecyp,aris lawsoniana, forests are known in some detail (Whittaker, 1960; Griffin and Critchfield, 1972; Hawk, 1977). Other ecological descriptions of this species (Fowells, 1965). are mostly general. This study sampled several aspects of the environment of C. lawsoniana. Sampling sites included extreme as well as typical conditions for the species. Air and soil temperatures, humidity, depth to water table, degree of shading of tree reproduction, effects of prolonged drought, and xylem pressure potential and foliar nutrient concentrations of the plants 'were measured. Our results cara help define reasons for the range restriction of C. lawsoniana, as well as the environment where it may be best managed. GENERAL ENVIRONMENT OF THE SPECIES' RANGE Chamaecyparis lawsoniana receives moderately high precipitation. In southernmost Oregon, the eastern range boundary coincides approximately with the 1000mm (40-inch) isohyet (U.S. Dep. Agric., 1964), and in California most stands receive at least 1500 mm (Rantz, 1968). East of its range, rainfall is less and evaporative stress is greater, as shown by the flora (Waring, 1969) and by moisture 1 Present address: Forestry Sciences Laboratory, U. S. Forest Service, 3200 Jefferson Way, Corvallis, Oregon 97331.
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