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The ecology of Atlantic white cedar wetlands - USGS National ...

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filled swamps, or peatlands partly draind after flood- observed no general relationship between watering, provide satisfactory conditions far <strong>white</strong> <strong>cedar</strong> regime and annual radial growth. Cedar growthreproduction (Korstian and Brush 1931; Liile 1950). seemed more closely linked to ground waterchemistry and forest stand characteristics than to the3.2.3 hydrological regime.Sfsdhgs. Little (1950) determined that -. In natural settings,early growth varies greatly with substrate and light<strong>cedar</strong> sometimes develops lateral or basal shootsconditions, with first year increments ranging fromatter injury. Seedlings repeatedly browsed by deer2.5 cm to as high as 25 cm. <strong>The</strong>reafter, seedlingsdevelop multiple stems through layering (Liile 1950;A. and J. Moore, unpubl. field notes).may grow than 0'3 annual'y On favorablesites. This results inHowever, layering stems appear to grow much more3 m saplings in 7 or 8 years inthe and in about years in southem New Jerslowlythan the original growth, and, unlike <strong>of</strong>tenhardwood sprouts fsey. On unfavorable substrate, growth in 15 yearshese stems never formmay be only 1.2 m.an imponent forest compor;ent (Lime 950).Mature. Korstian and Brush (1931) Almost from the time the species was firstpublished extensive life table data for natural- and described, it was known that <strong>Atlantic</strong> <strong>white</strong> <strong>cedar</strong>field-grown <strong>cedar</strong>s. In the single controlled study <strong>of</strong> propagates well from cuttings (letters <strong>of</strong> J. Bartram inmature <strong>Atlantic</strong> <strong>white</strong> <strong>cedar</strong> growth rates published, Darlington 1857). <strong>The</strong> preparation <strong>of</strong> seedbed, seed,Golet and Lowry (I 987) observed that <strong>cedar</strong>s in and cuttingsfor propagation, as well as the influenceRhode Island swamps grow an average <strong>of</strong> 0.79-1.79 <strong>of</strong> competing vegetation on seedling success are dismmlyrradially, primarily during March through cussed under management (Chapter 6).August (Figure 20). <strong>The</strong>y found that yearly variationsin growth within individual <strong>cedar</strong> swamps may be relatedto water level variations, but this relationship differsmarkedly from wetland to wetland. <strong>The</strong>y <strong>The</strong> <strong>Atlantic</strong> <strong>white</strong> <strong>cedar</strong> reaches its maximumsize in the southernmost part <strong>of</strong> its range. <strong>The</strong>"champion" tree now living is in Escambia County,Alabama, on a tributary <strong>of</strong> the Escambia River. Itmeasures 26.5 m tall and 150 cm dbh and is estimatedto be ca. 268 years old (Hunt 1986[measured in 19611; Hartman 1982; J. Arany, pers.comm. [measured in 19851). Trees approaching theAlabama champion in stature have been recentlyreported in Florida (Wills and Simmons 1984; Wardand Clewell, unpubl.).A M J J A S OMonthFigure 20. Annual radial growth Curves for <strong>Atlantic</strong><strong>white</strong> <strong>cedar</strong> in six Rhode Island swamps. Each pointrepresents the mean <strong>of</strong> three trees; each line representsone site (from Golet and Lowry 1987).Clewell and Ward (1987) report that directcounts <strong>of</strong> the annual rings <strong>of</strong> the largest trees havenot been possible, for increment tools fail topenetrate properly, and no record-sized trees havebeen recently cut. <strong>The</strong> largest trees in Mississippiand Florida are possibly 150 to 190 years old asextrapolated from the minimal data available ongrowth rates.<strong>The</strong> maximum size <strong>of</strong> Chamaecyparisdecreases from its mid-range northward, e.g., themaximum heights reported for North CarolinaNirginiawere 36.6 m; for southern New Jersey 21.3 m;and for New Hampshire only 12.5 m.

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