Na. Auerbach et al., EFFECTS OF ROADSIDE DISTURBANCE ON SUBSTRATE AND VEGETATION PROPERTIES IN ARCTIC TUNDRA, Ecological applications, 7(1), 1997, pp. 218-235
Tundra adjacent to the gravel Dalton Highway in northern Alaska was ex
amined for effects of 15 yr of chronic road and road dust disturbance.
Road effects at a nonacidic site (soil pH greater than or equal to 5.
0) and an acidic site (soil pH < 5.0) were compared to examine differe
ntial susceptibility. Overall, effects on vegetation were more pronoun
ced in acidic tundra. Initial substrate pH appears to control the degr
ee of response to disturbance by road and calcareous road dust. Soil a
t the acidic site is normally pH 4.0, whereas in the disturbed area ne
xt to the road soil pH was as high as 7.3 +/- 0.07 (at 2 m from the ro
ad edge). Soils next to the road had lower nutrient levels, altered or
ganic horizon depth, higher bulk density, and lower moisture. Effects
on snowpack include both increased drifting in the lee of the road and
earlier meltout near the road due to dust-induced change in albedo. P
ermafrost thaw was deeper next to the road at both sites, and potentia
lly could affect road structure detrimentally. Vegetation biomass of m
ost taxa was reduced near the road at both sites. Total aboveground bi
omass of nonacidic tundra ranged from 330.0 +/- 34.72 g/m(2) (mean +/-
1 SE) at 2 m from the road to 690.7 +/- 94.52 g/m(2) at 100 m away fr
om the road. Total biomass of acidic tundra ranged from 150.5 +/- 16.6
0 g/m(2) at 5 m from the road to 743.1 +/- 168.98 g/m(2) at 100 m from
the road. Species richness in acidic tundra next to the road was less
than half of that at 100 m away from the road. Community composition
was altered most noticeably in acidic tundra. The moss Tomentypnum nit
ens, dominant in nonacidic arctic tussock tundra, was nearly equally a
bundant at all distances from the road at the nonacidic tundra site, w
hereas Sphagnum mosses, dominant in acidic low arctic tussock tundra,
were virtually eliminated near the road at the acidic tundra site. Sal
ix lanata was more abundant next to the road at the nonacidic site. Or
dinations indicate that variation in vegetation cover is explained by
distance from the road. Knowledge of differential effects of road cons
truction and use, including the long-term effects of hydrological alte
rations and dust mobilization on focal corridors, is key information f
or planning development in areas of arctic tundra. Planned placement o
f roads in the future should consider the impact of such changes to se
nsitive (acidic) tundra areas in the Arctic.