were saturated (Teskey and tiinckleyI???).Figure 29. Buttressed roots <strong>of</strong> trees in hydrichammock, including Florida elm (In front) andswamp laurel oak (behind), provide stability inwet soils and perhaps help to aerate the rootsystem.water oak and loblolly pine the shortest(Teskey and Hinckley 1977).Weakly tolerant species include hornbeam,red mulberry, and several oaks--water, live, Shumard, and swamp chestnut.According to McKnight et al.(1981), these species are able to surviveonly short hydroperiods (a fewdays to a few weeks), and they possessno apparent adaptations to inundation.Seedlings <strong>of</strong> hydric hammock trees generallyare more sensitive to floodingthan mature trees, although, as notedabove, mortality rates depend on thedegree <strong>of</strong> submersion. In short-termexperiments, death usually occurredwithin 20-30 days when the seedlingswere compl etel y submersed and within0.5-3 months when they were partiallyflooded; no seed1 ings died when soils<strong>The</strong> damming <strong>of</strong> the Oklawaha River innorth-central Florida provided addi -tional evidence <strong>of</strong> the differences inflood tolerance among hydric-hammockspecies (Harms et a1 . 1980). Probablymost <strong>of</strong> the flooded forest was riverswamp dominated by deciduous hardwoods,but part was hydric hammock(Florida Game and Fresh Water FishLcirnmr ssion 1476 j . Tiir-ee yedt :, dfteidam construction, tree mortal ity wasstrongly correlated with water depth,with essentially 100% mortality at averagedepths <strong>of</strong> 1.2 m or more, decreasingas prevailing water level declined. However, mortal i ty rates significantlyvaried among tree species.Bald cypress, swamp tupelo, and cabbagepalm were the most tolerant <strong>of</strong>flooding. Cabbage palms were scatteredthroughout the forest and fewdied, irrespective <strong>of</strong> water depth.<strong>The</strong>y accounted for most <strong>of</strong> the survivorsin the most deeply flooded section<strong>of</strong> the forest. Two species <strong>of</strong>oaks, water and swamp laurel, wereleast tolerant <strong>of</strong> flooding, survivingonly at the shallowest depths (aboutthe same and 20 cm deeper than controlsites outside <strong>of</strong> the reservoir). Nodoubt water levels in the reservoirfluctuated less thdn in tile undi5-turbed floodplain and long periods <strong>of</strong>continuous flooding occurred. However,data on the water elevation <strong>of</strong>the lake indicate that prolonged drydownsalso took place (Harms et al.1980).<strong>The</strong> placement <strong>of</strong> tree species withinhydric hammocks probably ref1 ects inlarge part their relative tolerancesto flooding. Species abundances a1 onga presumed flooding gradient inSanchez Prairie, San Fel asco HammockState Preserve, are shown in Figure30. At the time <strong>of</strong> sampling, shallowwater stood at the beginning <strong>of</strong> thetransect, in a stand dominated by baldcypress and red maple. <strong>The</strong> transectclimbed a very gentle slope into hydrichammock, ending where live andwater oaks dominated and the groundwas quite dry. Bald cypress was restrictedto the wetter (swamp) end <strong>of</strong>
I ~ U mapleswamp laurel oak 3:1100bald cypress a- swamp tupelo -,100wgreen ash m jo $sweetgum m rn 3:6IO~IOIIY pine 3: !i100live oak- dowater oakI0 40 80 120 160 200DISTANCE (m)Figure 30. Distribution <strong>of</strong> tree species along apresumed flooding gradient in Sanchez Prairie,San Felasco Hammock State Preserve. <strong>The</strong> transectbegins in swamp conditions (left) and endsin drier hydric hammock (right).the gradient, and live oak, water oak,and loblolly pine to the drier(hammock) part. Red maple and swamp1 aurel oak ranged almost throughoutthe swamp/hammock transect. Swamplaurel oak was replaced by 1 ive andwater oaks at the dry end <strong>of</strong> the gradient,their relative positions in accordancewith flooding to1 erances inferredfrom the studies cited above.Another study transected 200 m <strong>of</strong> aSemi no1 e County hydri c hammock (Table5), descending 80 cm to river swampdominated by bald cypress, red maple,and sweetgum (G. R. Best and P. Wallace,pers. comm.). <strong>The</strong> first half <strong>of</strong>the transect probably was slightlyabove average high water, whereas thesecond half was slightly below. Sugarberry'and hornbeam were found onlyin the first 50 m, while swamp laureloak extended to 150 m. Sweetgum andFlorida elm ranged throughout the twohammock sections and into the swamp.Cabbage palm, the dominant tree inthis hydric hammock (Table 5), alsowas ubiquitous, but its abundance declined greatly in the swamp. Redmaple occurred in swamp and hydrichammock, though only as saplings inthe latter. NO 1 ive oaks were sampled,although this species was ob-served in other, generally drier,parts <strong>of</strong> the hydric hammock.Some <strong>of</strong> the differences in composition<strong>of</strong> plant species among hydrichammocks also result from variablepatterns <strong>of</strong> flooding and drydown. <strong>The</strong>Seminole County hammock probablyfloods more <strong>of</strong>ten and for a longer periodthan many others, which was reflectedin the vegetation: Floridaelm was an important species, redmaple and swamp laurel oak sap1 ingswere abundant, no 1 ive oaks were sampled,and bald cypresses were present.Live oak was absent also from theWekiva Springs and Tiger Creek hydrichammocks, both <strong>of</strong> which receive seepageand are almost always moist. Inthe Wekiva Springs hammock, a high watertable is maintained by dischargefrom a deep aquifer (see Figure 9).<strong>The</strong> hydrology <strong>of</strong> the Tiger Creek hammockwas discussed in Chapter 2.4;thi s wet1 and receives up1 and seepagedepending on the season. <strong>The</strong> pr<strong>of</strong>usion<strong>of</strong> shrubs and ground vegetationin these hammocks probably resultsfrom the nearly constant saturation <strong>of</strong>the soils. <strong>The</strong> influence <strong>of</strong> seepageon plant species composition is especial1 y pronounced at Wekiva Springs.Numerous bay trees, needle palm, andcinnamon fern make this forest intermediatein composition between"typical" hydric hammock and bayhead,a community characterized by constantseepage. <strong>The</strong> re1 atively constantmoisture regime <strong>of</strong> the Wekiva Springsand Tiger Creek hammocks contrastswith the extremes <strong>of</strong> drought andflooding experienced by other hydrichammocks. We suggest that hydric hammockslow in species diversity anddominated by cabbage palm and live oakexi st where long, dry periods are interruptedby occasional episodes <strong>of</strong>flooding. Examples are found in theupper St. Johns and Myakka Riverbasins, where river overflow only sporadicallyfloods the hydric hammocks.In Myakka River State Park, hydrichammock has expanded into freshwatermarsh during the past 30 years (Figure31), at the same time as river levelshave declined due to upstream diversions(Robert Dye, Florida Department<strong>of</strong> Natural Resources; pers. comm.).Whereas the old part <strong>of</strong> the hydric
- Page 2 and 3: Copies of this publication may be o
- Page 4 and 5: DISCLAIMERThe opinions and recommen
- Page 6 and 7: CONVERSION TABLEMetric to U.S. Cust
- Page 8 and 9: FIGURESNumber1AL...............Dist
- Page 10 and 11: NumberTABLESPaqeClassifications of
- Page 13 and 14: CHAPTER 1. INTRODUCTION"Hammock, ho
- Page 15 and 16: whereas hydric hammock is a still-w
- Page 17 and 18: CHAPTER 2. PHYSICAL SElTiNG2.3 CLIM
- Page 19 and 20: Recent and PIe~sIoLene sands clay m
- Page 21 and 22: ern vegetation associations formed-
- Page 23 and 24: Table 3. Comparison of surface soil
- Page 25 and 26: throughout the year in Florida, and
- Page 27 and 28: Figure 13. Flooding and drydown of
- Page 29 and 30: +southari:magnolla+-------cabbage p
- Page 31 and 32: frequency may be once per year in f
- Page 33 and 34: Table 4. Plants occurring in hydric
- Page 35 and 36: Table 4. (Continued).Scientific nam
- Page 37 and 38: of the subcanopy and shrub layers i
- Page 39 and 40: sites were not chosen randomly;rath
- Page 41 and 42: When present in a hydric hammock,ca
- Page 43 and 44: hydric harriniock forests. These sp
- Page 45 and 46: was the most frequent shrub in the
- Page 47 and 48: Gulf Hammock is rep1 aced abruptly
- Page 49: A sequence of changes in plantmat a
- Page 53 and 54: The salt concentration of hydricham
- Page 55 and 56: Cabbage palm is the most fire-toler
- Page 57 and 58: frequent fires, a1 though timber ha
- Page 59: Figure 38. Tree blowdowns due to hu
- Page 62 and 63: locally collected litter lost 85% o
- Page 64 and 65: Table 7. Occurrence of reptiles and
- Page 66 and 67: Table 8. Occurrence of reptiles and
- Page 68 and 69: 4.3 BIRDS4.3.1 Community StructureM
- Page 70 and 71: Table 11. (Concluded).- ----Variabl
- Page 72 and 73: and cerambyci d beet1 es) . Unl i k
- Page 74 and 75: no specific habitat preference; it
- Page 76 and 77: not take place in years of mast fai
- Page 78 and 79: Graves 1977). These observations su
- Page 80 and 81: Consumption of fleshy fruits by res
- Page 82 and 83: CHAPTER 6. LINKAGES WITH OTHER ECOS
- Page 84: R Amerlcan swallow-tailed kite b. t
- Page 87: Conner, W.H., and J.W. Day, Jr. 197
- Page 90 and 91: Duck foods in managed tidalimpoundm
- Page 92 and 93: Puri, M,S., 3.W, Yon, and W.R.Ogles
- Page 94 and 95: Wharton, C.H. 1977. The naturalenvi