Ms&gua As early as 1923, Akermandescribed in detail the importance <strong>of</strong> swampmicrorelief in providing suitable <strong>cedar</strong> seedbed. Heobserved that only the logs, stumps, or hummocksthat are above water during the spring high-waterperiods form favorable seedbeds, but seediingsstarting there may die from lack <strong>of</strong> moisture duringlater dry periods. However, seedlings growing inlower places frequently drown during subsequenthigh-water periods. Akerman concluded that seedlingssprouting at intermediate positions had bettersurvival than those starting either at the highest orlowest spots. He found that root development by theend <strong>of</strong> the first growing season began to make seedlingsdrought-resistant, but they remained susceptibleto drowning until after the second growingseason, when many were more than 30 cm tall.<strong>The</strong>se observations have been repeatedly corroborated(e.g., Korstian and Brush 1931 ; Little 1950). Little(1950) determined experimentally that seedlingssurvive in hollows only when they are above the watertable.Suitable substrates include rottenwood, peat, and Sphagnum moss. Hardwood andshrub leaf littea and pine needles inhibit <strong>cedar</strong> germinationto less than one per cent. Seeds may germinatein mineral soil, but non-organic soil is not asfavorable as hardwood swamp peat, where rates areas high as 49% and dominant first-year seedlingsaremore than three times talier than on mineral substrate.<strong>The</strong> floor <strong>of</strong> a wetland previously supporting<strong>Atlantic</strong> <strong>white</strong> <strong>cedar</strong> is the most favorable substrate,Ligbi. Reiatively open conditions are necessaryfor healthy growth <strong>of</strong> C. thyoides seedlings, aCthough they may survive for 1 to 3 years under amature <strong>cedar</strong> canopy, where light intensew averages4% to 6% <strong>of</strong> full sunlight. Canopy thinning enables<strong>white</strong> <strong>cedar</strong> seedlings to live longer, but they are stillout-competed by shrubs and other trees. At a lightintensity <strong>of</strong> 77%, initial growth <strong>of</strong> seedlings wasdouble that at 16% light, and almost quadruple thatat 2% intensity (Little and Garrett, in press). Warmopen areas, such as cleaned clearcut <strong>cedar</strong> stands,abandoned cranberry bogs, recent burns over water-Figure 19. Morphology <strong>of</strong> Chamaecyparis thyoides. A, B, H, and Qare reduced in size; all others are ma(from Korstian and Brush 1931).A-C. Branchlet with pistillate flowers.D-G. Pistillate flowers (longitudinal and cross sections).H. Branchlet wrth staminate flowers.1. Tip <strong>of</strong> H, magnified.J-0. Anthers bearlng pollen sacs (surface and section views).I? Cross sect~on <strong>of</strong> stamen attached to filament.Q. Branchlet with mature fruit.R-X. Branchlet showing arrangement <strong>of</strong> leaves, glands on scales.Y Mature cones (top, side, and dissected views) with seeds intact and discharged.28
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.
- Page 1: Biological Report 85(7.21)July 1989
- Page 5 and 6: PREFACEThis monograph on the ecolog
- Page 7 and 8: CONTENTSea9tl.PREFACE .............
- Page 9 and 10: NumberTABLESEarliest records of Atl
- Page 11 and 12: - CHAPTER 1 -INTRODUCTION1 .I GENER
- Page 13 and 14: TEMPORARLYSEASONALLY1I SATURATED1Fi
- Page 15 and 16: Stagnant,,- melting Icel Block d~ag
- Page 17: Table I. Earliest records of Atlant
- Page 20 and 21: CHAPTER 2 -REGIONAL OVERVIEW2.1 INT
- Page 22 and 23: stands are scattered north and west
- Page 24 and 25: state and is gathering data hithert
- Page 26 and 27: corner of the state, and Uttertown
- Page 28 and 29: hardwood stands, or as isolated tre
- Page 30 and 31: cedar have comprised 40%-60% of the
- Page 32 and 33: tablished. Drainage from 224 krn of
- Page 34 and 35: perennial streams (Figure 18) and i
- Page 36 and 37: - CHAPTER 3 -CHAMAECYPARIS THYOIDES
- Page 40 and 41: - CHAPTER 4 -STRUCTURE AND FUNCTION
- Page 42 and 43: ottomland-isolatedtill & bedrockupl
- Page 44 and 45: Table 5. Mean August tissue nutrien
- Page 46 and 47: - CHAPTER 5 -BIOLOGICAL COMPONENTS
- Page 48 and 49: Figure 24a. Companions: plants freq
- Page 50 and 51: Figure 24c. Companions: Plants freq
- Page 52 and 53: ?able 7. Comparison of bird species
- Page 54 and 55: Meanley (1979) emphasized the impor
- Page 56 and 57: - CHAPTER 6 -MANAGEMENT AND HARVEST
- Page 58 and 59: FireBurnedtreesPeatGlacialrubble-Tr
- Page 60 and 61: Mixedhardwood& shrubsPeatGlacialrub
- Page 62 and 63: acidity is reduced, and ammonia, ph
- Page 64 and 65: and condition of the soil surface a
- Page 66 and 67: sprouts and shade-tolerant shrubs g
- Page 68 and 69: Figure 32. Atlantic white cedar reg
- Page 70 and 71: sedhflings, conversely, canopy open
- Page 72 and 73: FORESTMANAGEMENTSCHEMAT I CLEGEND-
- Page 74 and 75: -.- Rsfupe BoundaryState BoundaryRo
- Page 76 and 77: NATIONAL WILDLIFE RERX;EVirginia an
- Page 78 and 79: Figure 38. Alligator River (North C
- Page 80 and 81: Mainland Dare County is located on
- Page 82 and 83: The cedar swamp forests along the A
- Page 84 and 85: IPure Atlanticwhite cedar standsy-J
- Page 86 and 87: Generally, the mixed swamp forest s
- Page 88 and 89:
species of mammals are recorded by
- Page 90 and 91:
Braun-Blanquet, J. [I 9321 1983. Pl
- Page 92 and 93:
Ferguson, R.H., and C.E. Meyer. 197
- Page 94 and 95:
Littte, S. 1953. Prescribed burning
- Page 96 and 97:
Porter, D.M. 1979. Rare and endange
- Page 98 and 99:
Gov. Print. Off., Washington, DC. (
- Page 101 and 102:
APPENDIX A. Flora Associated with C
- Page 103 and 104:
APPENDIX A. Flora: Trees (6ontin~ed
- Page 106 and 107:
APPENDIX A. Flora: Shrubs (Continue
- Page 108 and 109:
APPENDIX A. Fiora: Herbs (Continud)
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APPENDIX A. Flora: Herbs (Continued
- Page 112 and 113:
APPENDIX A. flora: Herbs (Continued
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APPENDIX A. Flora: Herbs (Continued
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APPENDIX A. Flora: Herbs (Continued
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APPENDIX B. FAUNA OF ATLANTIC WHITE
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APPENDIX C. Hydric Soilsis a soil t
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Frost, CecilFuller, ManleyFunk, Dav
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Ward, Daniel B.Whigham, DennisWidof