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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$able 2+4. Soil dnz<strong>in</strong>uge classes jafier Wright and Sautter 2 979).<br />
-- -- --.- - - ----<br />
bmage class<br />
Characteristics<br />
--- -- - - -------- --<br />
Excessively dra<strong>in</strong>ed<br />
BrightIy colored; usually coarse-textured; rapid permeability; very low<br />
water-hold<strong>in</strong>g capacity; subsoil free <strong>of</strong> mottlesa<br />
Somewhat excessively dra<strong>in</strong>ed Brightly colored; ra<strong>the</strong>r sandy; rapid permeability; low water-hold<strong>in</strong>g<br />
capacity; subsoil free <strong>of</strong> mottles<br />
Well dra<strong>in</strong>ed<br />
Color usually bright yellow, red, or brown; dra<strong>in</strong> excess water readily,<br />
but conta<strong>in</strong> sufficient f<strong>in</strong>e material to provide adequate moisture for<br />
plant growth; subsoil free <strong>of</strong> mottles to a depth <strong>of</strong> at least 91 cm<br />
Moderately well dra<strong>in</strong>ed<br />
Generally any texture, but <strong>in</strong>ternal dra<strong>in</strong>age is restricted to some degree;<br />
mottles common <strong>in</strong> <strong>the</strong> lower part <strong>of</strong> <strong>the</strong> subsoil, generally at a depth <strong>of</strong><br />
46-91 cm; may rema<strong>in</strong> wet and cold later <strong>in</strong> spr<strong>in</strong>g; generally suited for<br />
agricultural use<br />
Somewhat poorly dra<strong>in</strong>ed Rema<strong>in</strong> wet for long periods <strong>of</strong> time due to slow removal <strong>of</strong> water;<br />
generally have a slowly permeable layer with<strong>in</strong> <strong>the</strong> pr<strong>of</strong>ile or a high<br />
water table; mottles common <strong>in</strong> <strong>the</strong> subsoil at a depth <strong>of</strong> 20-46 cm<br />
brly dra<strong>in</strong>ed<br />
Dark, thick surface horizons commonly; gray colors usuilly dom<strong>in</strong>ate<br />
subsoil; water table at or near <strong>the</strong> surface dur<strong>in</strong>g a considerable part <strong>of</strong><br />
<strong>the</strong> year; mottles frequently found with<strong>in</strong> 20 cm <strong>of</strong> <strong>the</strong> soil surface<br />
Very poorly dra<strong>in</strong>ed<br />
Generally thick black surface horizons and gray subsoil; saturated by<br />
high water table most <strong>of</strong> <strong>the</strong> year; usually occur <strong>in</strong> level or depressed<br />
sites and are frequently ponded with water<br />
"See <strong>the</strong> section on soils <strong>in</strong> this chapter for a discussion <strong>of</strong> <strong>the</strong> significance <strong>of</strong> mottlcs.<br />
detailed account <strong>of</strong> water level activity <strong>in</strong> seasonally<br />
flooded and seasonally saturated red maple<br />
swamps. The follow<strong>in</strong>g discussion <strong>of</strong> water levels<br />
is based on <strong>the</strong>ir f<strong>in</strong>d<strong>in</strong>gs.<br />
General Patterns<br />
Water levels <strong>in</strong> red maple swamps are highly<br />
dynamic; marked variations among seasons,<br />
years, and swamps are typical. Figure 2.7 shows<br />
<strong>the</strong> general pattern <strong>of</strong> water level activity <strong>in</strong> seasonally<br />
flooded red maple swamps, based on<br />
Lowry's (1984) study. From an annual high <strong>in</strong> <strong>the</strong><br />
spr<strong>in</strong>g (April-May), water levels at all six sites<br />
decl<strong>in</strong>ed to <strong>the</strong>ir lowest po<strong>in</strong>ts <strong>in</strong> late summer or<br />
early fall. The low po<strong>in</strong>t commonly occurred <strong>in</strong><br />
September, but ranged from July to October, depend<strong>in</strong>g<br />
on <strong>the</strong> amount and distribution <strong>of</strong> precipitation<br />
<strong>in</strong> <strong>the</strong> particular year. High water levels<br />
ranged from 20 cm above <strong>the</strong> surface to 20 cm<br />
below <strong>in</strong> most years, but low water levels were far<br />
more variable. In <strong>the</strong> wettest year <strong>of</strong> <strong>the</strong> study<br />
(1979), three <strong>of</strong> <strong>the</strong> swamps had water at or above<br />
<strong>the</strong> surface dur<strong>in</strong>g <strong>the</strong> entire measurement period<br />
(mid-April to mid-December); water levels at <strong>the</strong><br />
o<strong>the</strong>r sites rema<strong>in</strong>ed with<strong>in</strong> 30 cm below <strong>the</strong> surface<br />
<strong>in</strong> that year. In <strong>the</strong> driest years <strong>of</strong> <strong>the</strong> study<br />
(1980,1981), water levels at all sites dropped more<br />
than 50 cm below <strong>the</strong> surface, and at some sites a<br />
subsurface depth <strong>of</strong> 1 m was exceeded.<br />
Differences <strong>in</strong> water levels among sites were<br />
greatest at <strong>the</strong> end <strong>of</strong> <strong>the</strong> summer, when water<br />
levels were lowest (Fig. 2.7). The greatest differences<br />
were observed <strong>in</strong> <strong>the</strong> driest years. Lowry<br />
(1984) concluded that <strong>the</strong>se differences <strong>in</strong> low<br />
water levels resulted from differ<strong>in</strong>g amounts <strong>of</strong><br />
groundwater <strong>in</strong>flow at <strong>the</strong> various sites, a factor<br />
determ<strong>in</strong>ed by hydrogeologic sett<strong>in</strong>g and soil type<br />
(Bay 1967; OBrien 1977). In nearly every year,<br />
water levels were clearly <strong>in</strong>fluenced not only by<br />
total precipitation, but also by dist<strong>in</strong>ct wea<strong>the</strong>r<br />
patterns or unusual events (e.g., heavy ra<strong>in</strong>s associated<br />
with Hurricane Belle <strong>in</strong> August <strong>of</strong> 1976;<br />
exceptionally high ra<strong>in</strong>fall <strong>in</strong> May <strong>of</strong> 1978 and<br />
June <strong>of</strong> 1982; abnormally high, well-distributed<br />
ra<strong>in</strong>fall <strong>in</strong> 1979; and consistently low ra<strong>in</strong>fall<br />
throughout 1980 and 1981).<br />
Inspection <strong>of</strong> <strong>the</strong> water level hydrographs<br />
(Fig. 2.7) revealed that most <strong>of</strong> <strong>the</strong> sites studied by<br />
Lowry (1984) met <strong>the</strong> def<strong>in</strong>ition <strong>of</strong> seasonally<br />
flooded (Table 2.3), while <strong>the</strong> o<strong>the</strong>rs were seasonally<br />
saturated. The soils at all <strong>of</strong> those sites were<br />
very poorly dra<strong>in</strong>ed. In <strong>the</strong> transition-zone stud%<br />
all <strong>of</strong> <strong>the</strong> wetland stations-poorly dra<strong>in</strong>ed and<br />
very poorly dra<strong>in</strong>ed-were seasonally saturated;<br />
except for brief ra<strong>in</strong>fall events, surface water was<br />
absent dur<strong>in</strong>g <strong>the</strong> grow<strong>in</strong>g season <strong>in</strong> most years.<br />
Figure 2.8 provides a 3-year record <strong>of</strong> water<br />
levels at 2 <strong>of</strong> <strong>the</strong> 54 wetland stations monitored