Tp. Rooney et Dm. Waller, Local and regional variation in hemlock seedling establishment in forests of the upper Great Lakes region, USA, FOREST ECOL, 111(2-3), 1998, pp. 211-224
Successful tree regeneration requires both successful seedling establishmen
t and subsequent survival and growth sufficient to ensure recruitment. We e
xamined patterns of initial seedling establishment in randomly selected sta
nds of eastern hemlock (Tsuga canadensis) distributed across northern Wisco
nsin and eastern Upper Michigan. In 1990, we counted all hemlock seedlings
(defined as 4-29 cm tall) and sampled substrate conditions in two 7x7 m qua
drats of 142 hemlock and hemlock-hardwood stands. In 1996, we resampled 109
of these stands more intensively using six 7x7 m quadrats. In 1997, we als
o intensively surveyed which substrate-supported hemlock seedlings in three
50 m(2) replicate areas from each of five stands. In 1990, we found no hem
lock seedlings at 64 of the 142 stands sampled, and 46% of the stands had m
ore than 100 hemlock seedlings ha(-1) (mean density=480+/-90 ha(-1)). In co
ntrast, only 14 (13%) of the 109 stands resampled in 1996 had no seedlings
and 66% had over 100 seedlings ha(-1) (mean density=840+/-200 ha(-1)). Thes
e results suggest that seedling establishment is patchy, causing the estima
ted frequency of successful establishment to depend strongly on the area sa
mpled. Seedling abundance within sites was correlated between years, sugges
ting that site history may in part account for the abundance of seedlings.
Analysis of variance to mean ratios reveals that seedlings are indeed stron
gly clumped at the 7x7 m scale or smaller. Such clumping probably results f
rom the tendency for hemlock seedlings to occur most frequently on particul
ar substrates (i.e. decaying wood). Hemlock seedlings occur less frequently
in stands with high basal area of sugar maple but do not decline in stands
with greater hemlock basal area, suggesting that maple litter may restrict
local opportunities for seedling establishment. Seedling densities do not
vary among habitat-types, and no other stand or regional variable significa
ntly affected hemlock seedling density. These results suggest that ground s
urveys are needed to assess hemlock seedling abundance, and that such surve
ys should be based on quadrats of at least 100 m(2). Successful hemlock reg
eneration should capitalize on local patches of existing hemlock seedlings
where interference by hardwoods is minimal. Even high initial seedling esta
blishment, however, may not guarantee regeneration in areas where high deer
densities preclude recruitment into larger size classes. (C) 1998 Elsevier
Science B.V.