HR: 0800h
AN: C21A-1072 [Abstracts]
TI: Interaction between snowcover and climate, topography and vegetation in semi-arid mountain
catchments
AU: * Marks, D
EM: danny@nwrc.ars.usda.gov
AF: USDA Agricultural Research Service
Northwest Watershed Research Center, 800 Park Blvd
Suite 105, Boise, ID 83712-7716
United States
AU: Pomeroy, J
EM: pomeroy@usask.ca
AF: Centre for Hydrology
Dept. of Geography
University of Saskatchewan, 117 Science Place, Saskatoon, Sas S7N 5C8
Canada
AU: Winstral, A
EM: awinstra@nwrc.ars.usda.gov
AF: USDA Agricultural Research Service
Northwest Watershed Research Center, 800 Park Blvd
Suite 105, Boise, ID 83712-7716
United States
AU: Link, T
EM: tlink@uidaho.edu
AF: Department of Forest Resources
University of Idaho, P.O. Box 441133, Moscow, ID 83844-1133
United States
AU: Seyfried, M
EM: mseyfrie@nwrc.ars.usda.gov
AF: USDA Agricultural Research Service
Northwest Watershed Research Center, 800 Park Blvd
Suite 105, Boise, ID 83712-7716
United States
AU: Essery, R
EM: rie@aber.ac.uk
AF: Institute of Geography and Earth Sciences, University of Wales, Aberystwyth, SY23 3DB
United Kingdom
AB:
Mountainous regions in the semi-arid Northwestern US are snow-dominated with sparse summer precipitation. Vegetation at high
altitudes in this environment is dominated by dry grass and sagebrush with small deciduous and evergreen forest patches in
mid-point and lower hillslope locations of north-facing slopes. Wind direction and variations in near-surface wind fields
due to topography and vegetation control snow deposition, causing tremendous spatial heterogeneity in the distribution of the
snowcover and the delivery of melt water. Snow is scoured from exposed areas during and shortly after storms and deposited
in drifts that develop in the lee of exposed ridges, and inward from forest edges. Vegetation cover and soil development is
associated with topography and topographic effects on the wind field, in that only sites with sufficient melt-water delivery
from drifts and soil moisture storage potential can sustain forests. Forests are typically found down slope from the deepest
sections of snowdrifts, where a melt-water supply can replenish soil moisture but where the persistence of snowcover into
summer does not impede forest growth. Forest canopies diminish the energy available for melt by reducing turbulent transfer,
increasing incoming longwave and reducing incoming shortwave. Hence, snowcover persistence is greatly increased by forest
cover - this reduces the growing season and potential evapotranspiration demand over non-forested sites. In contrast,
sparsely-vegetated, exposed areas of mountain catchments accumulate less snow, and that snow melts earlier and faster than in
forested areas. These hydro-ecological characteristics are very dependent on the snow regime, for instance snow transport
is substantial and primarily from one direction resulting in persistent locations for large snow drifts and a relatively
reliable water supply for soil development and plant growth. Transport of snow primarily to the north-facing slopes delivers
melt-water to sites that have lower potential evapotranspiration demand in summer, permitting more luxuriant forest growth.
To better manage forest and water resources in mountain regions, it is important to understand and model the coupling
between forest structure, climate, and snowcover.
DE: 0736 Snow (1827, 1863)
DE: 0740 Snowmelt
DE: 0754 Leads (4540)
DE: 1816 Estimation and forecasting
DE: 1817 Extreme events
SC: Cryosphere [C]
MN: Fall Meeting 2005