Ecology of Red Maple Swamps in the Glaciated Northeast: A ...
Ecology of Red Maple Swamps in the Glaciated Northeast: A ...
Ecology of Red Maple Swamps in the Glaciated Northeast: A ...
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dw<strong>in</strong>g <strong>the</strong> transition-zone study. The stations are<br />
<strong>of</strong> average water level activity <strong>in</strong> a<br />
very poorly dra<strong>in</strong>ed m<strong>in</strong>eral soil (Scarboro series,<br />
a Histic Wumaquept) and a poorly dra<strong>in</strong>ed m<strong>in</strong>eral<br />
soil (Walpole series, an Aeric Haplaquept). Although<br />
water levels at <strong>the</strong> two stations differed by<br />
30-60 cm, seasonal and annual patterns were<br />
similar. At both stations, <strong>the</strong>re were large variations<br />
between years <strong>in</strong> grow<strong>in</strong>g-season water levels;<br />
however, dormant-season water levels at each<br />
station were similar <strong>in</strong> <strong>the</strong> 3 years <strong>of</strong> observations.<br />
Mean monthly precipitation <strong>in</strong> sou<strong>the</strong>rn Rhode<br />
Island ranges from about 7.5 cm <strong>in</strong> June and July<br />
to 11.8 cm <strong>in</strong> March and November, while evapotranspiration<br />
ranges from 16.5 cm <strong>in</strong> July to<br />
essentially zero dur<strong>in</strong>g <strong>the</strong> dormant season Wniversity<br />
<strong>of</strong> Rhode Island Wea<strong>the</strong>r Station, K<strong>in</strong>gston).<br />
Monthly evapotranspiration is relatively<br />
constant from year to year. Thus, water level<br />
fluctuation with<strong>in</strong> each year is due primarily to<br />
seasonal variations <strong>in</strong> evapotranspiration rates,<br />
whereas yearly differences <strong>in</strong> water levels are<br />
caused by annual variations <strong>in</strong> precipitation. The<br />
response <strong>of</strong> water levels to annual variations <strong>in</strong><br />
precipitation <strong>in</strong> seasonally saturated swamps<br />
(Fig. 2.8) closely mirrored <strong>the</strong> response <strong>of</strong> water<br />
levels <strong>in</strong> <strong>the</strong> seasonally flooded swamps (Fig. 2.7).<br />
Grow<strong>in</strong>g-season precipitation was 41% above <strong>the</strong><br />
30-year mean <strong>in</strong> 1985, roughly equal to <strong>the</strong> mean<br />
<strong>in</strong> 1986, and 20% below <strong>the</strong> mean <strong>in</strong> 1987.<br />
S pecificc IFydrologic At tributes<br />
A comparison <strong>of</strong> data ga<strong>the</strong>red by Lowry (1984)<br />
and values generated by <strong>the</strong> Rhode Island transition-zone<br />
project (Table 2.5) <strong>in</strong>dicates that, dur<strong>in</strong>g<br />
a period <strong>of</strong> several years, grow<strong>in</strong>g-season water<br />
levels <strong>in</strong> Rhode Island red maple swamps averaged<br />
about 15-25 cm below <strong>the</strong> surface for very poorly<br />
dra<strong>in</strong>ed soils and 60 cm below <strong>the</strong> surface for<br />
poorly dra<strong>in</strong>ed soils. The extent <strong>of</strong> annual water<br />
level fluctuation varied widely among years, but<br />
was remarkably similar from one swamp to ano<strong>the</strong>r,<br />
particularly at Lowry's sites (Fig. 2.7). In<br />
both studies, water level fluctuation at <strong>in</strong>dividual<br />
sites ranged from less than 10 cm <strong>in</strong> wet years to<br />
more than 1.2 m <strong>in</strong> dry years. On <strong>the</strong> average,<br />
water levels fluctuated 35-50 cm each year <strong>in</strong> very<br />
poorly dra<strong>in</strong>ed soils and about 70 cm <strong>in</strong> poorly<br />
dra<strong>in</strong>ed soils. Water levels dropped more than<br />
80 cm below <strong>the</strong> surface at <strong>the</strong> majority <strong>of</strong> <strong>the</strong><br />
poorly dra<strong>in</strong>ed stations at some time each year.<br />
The duration <strong>of</strong> surface flood<strong>in</strong>g varied widely as<br />
well. At <strong>the</strong> seasonally flooded sites, surface water<br />
was present from late November or December <strong>in</strong>to<br />
June <strong>in</strong> most years. The ?-year mean hydroperiod<br />
at <strong>the</strong>se sites ranged from less than 1P/o to about<br />
50% <strong>of</strong> <strong>the</strong> grow<strong>in</strong>g season (Lowry 1984). At <strong>the</strong><br />
transition-zone sites, very poorly dra<strong>in</strong>ed soils had<br />
surface water less than 2% <strong>of</strong> <strong>the</strong> grow<strong>in</strong>g season,<br />
on <strong>the</strong> average, while poorly dra<strong>in</strong>ed soils were<br />
never flooded dur<strong>in</strong>g <strong>the</strong> 3-year study (Table 2.5).<br />
Table 2.5. Hydrologic characteristics <strong>of</strong> seasonally saturated soils from Rhode Isktnd red maple swamps<br />
dur<strong>in</strong>g <strong>the</strong> grow<strong>in</strong>g season (15 April-30 November) (data from Allen et al. 1989 and Department <strong>of</strong><br />
Natural Resources Science, University <strong>of</strong> Rhode Island, K<strong>in</strong>gston, unpublished data).<br />
POOL"!Y__~~.~~E~L~O~~<br />
Organic<br />
M<strong>in</strong>eral<br />
(n = 6)b (n = 19)~<br />
Poorly<br />
dra<strong>in</strong>ed soil<br />
(n = 141b<br />
Mean water level (em)<br />
(Range)<br />
Water level fluctuation (cm)<br />
(Range)<br />
Hydroperiod (To <strong>of</strong> grow<strong>in</strong>g season)<br />
Otange)<br />
Water level duration with<strong>in</strong><br />
30 cm <strong>of</strong> surface (To <strong>of</strong><br />
grow<strong>in</strong>g season)<br />
(Range)<br />
-22.4<br />
(-4.6 to -45.6)<br />
47.5<br />
(9 to 98)<br />
1.4<br />
(Oto 11.1)<br />
'~nsed on weekly measurements at three swa<strong>in</strong>ps dur<strong>in</strong>g 3 years.<br />
bn = total number <strong>of</strong> monitor<strong>in</strong>g stations st three study sites.