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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

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