SCALING IMPLICATIONS OF VARIABLE FROZEN SOIL INFILTRATION ON RUNOFF GENERATION JR Janowicz1, JW Pomeroy2 and DM Gray 1 Water Resources Branch, Environment Yukon Whitehorse, YT 2 Centre for Hydrology, University of Saskatchewan Saskatoon, Saskatchewan U OF S LOGO HERE C OF HYD LOGO HERE STUDY OBJECTIVES • To quantify the spatial variability of parameters governing infiltration to frozen soil and infiltration excess (runoff) in cold regions • To examine whether point scale relationships for infiltration and runoff associated with frozen soils can be upscaled using mean parameters • To propose a method for calculating cold regions runoff generation from basins with complex physiography INFILTRATION TO FROZEN SOILS unlimited measured 120 Infiltration (mm) 100 1:1 80 0.3 0.4 0.5 0.6 0.7 60 40 20 0.9 0 0 30 60 90 120 150 180 Snow Water Equivalent (mm) restricted •Early work by U of S came up with 3 classes of infiltrability •Unlimited •Restricted •Limited PARAMETRIC RELATIONSHIP Zhao & Gray (1999) INF = CS 2.92 0 (1 − S I ) 1.64 273.15 − TI 273.15 −0.45 t 0.44 • INF = Infiltration (cm) • SI = initial soil saturation (mm3/mm3) (water + ice; 0-40 cm) • C = bulk coefficient • S0 = surface saturation (mm3/mm3) • TI = initial soil temp (0K) (vol soil moisture / porosity) • t = time (hrs) SCALING PRINCIPLES •Consider Interrelationships Between Parameters INF = CS 2.92 0 (1 − S I ) •INF = f (SWE, SI) •S0, TI, t = f (SWE) •S0, TI = f (SI) 1.64 273.15 − TI 273.15 −0.45 t 0.44 DURATION OF SNOWMELT • Controls infiltration opportunity time, runoff generation, streamflow • Can be simply described as a function of SWE and melt rate, M. • Approximates the infiltration opportunity time, t0, when melt is continuous at high latitudes • Spatially variable because SWE and M are spatially variable. SWE t0 ≈ T = M WATER STORAGE POTENTIAL •Northern mineral soils often overlain by organic layer •Organic layers will hold water to water storage potential 5 – 25 cm Wsp = 0.6φ (1 − S I ) z w Wsp = water storage potential (mm) Φ = porosity SI = initial soil saturation, θ/Φ θ = average volumetric moisture content zw = depth of organic layer (mm) •drain rapidly down slopes •ponds on poorly drained sites NORTHERN RUNOFF GENERATION • • • Occurs through organic matter layers and over frozen mineral soils Primarily snowmelt driven (mineral soils thawed during major rain events) Complex process Subarctic mountainous terrain has highly variable: – – – – – • snow accumulation, melt rate, organic layer thickness, degree of saturation, ice layers Runoff is further complicated by – variable contributing area, – poorly defined drainages, – large storage terms. WOLF CREEK ECOSYSTEMS 2200 2000 Elevation (m) 1800 Alpine Granger 1600 1400 1200 Buckbrush 1000 800 Forest 600 0 20 40 60 % Area Below 80 100 FOREST •Thick Spruce Canopy (20 m) •Level Undulating Terrain SUBALPINE TAIGA •Shrub Alder & Willow (2 m) •Moderate (150) Undulating Hillslope ALPINE TUNDRA •Moss, Grass, Lichen •50 % Level; 50% Shallow Slope (100) GRANGER SUB-BASIN - NORTH FACING Drift •Shrub Alder & Willow (2 m) •Steep Undulating Slope ( 250) GRANGER SUB-BASIN - SOUTH FACING •Shrub Alder & Willow •Steep Undulating Slope ( 250) GRID SURVEY 100 m 5 X 5 m grid 441 points Met Station GRID SURVEY - GRANGER SUB-BASIN 10 X 20 m grid 258 points 420 m 100 m GRID DATA COLLECTION •Soil moisture - TDR – fall (prior to freeze-up) •SWE – Mount Rose – spring (max snowpack) •Porosity - soil particle size VARIATION IN RUNOFF COMPONENTS Snow Accumulation (SWE) 1200 200 1000 150 800 hours mm 250 100 Infiltration Opportunity Time 600 400 50 200 0 0 Granger 40 Shrub Tundra Sparse Tundra Spruce Forest Granger 200 Infiltration 35 140 120 20 mm mm 25 15 Sparse Tundra Spruce Forest Infiltration Excess (Potential Runoff) 180 160 30 Shrub Tundra R = SWE - Inf 100 80 60 40 10 5 20 0 0 Granger Shrub Tundra Sparse Tundra Spruce Forest Granger Shrub Tundra Sparse Tundra Spruce Forest GRANGER FALL SOIL MOISTURE AND SPRING SWE Volumetric Water Content % 100 5 0 4 0 50 3 0 2 0 1 0 0 0 50 100 North Face 150 200 250 300 Valley Bottom 35 0 1 400 South Face 0 100 5 0 0 50 3 0 0 1 0 0 0 0 50 100 150 200 25 0 300 350 400 Snow Water Equivalent mm 0 ORGANIC STORAGE & SOIL INFILTRATION Water Storage Potential mm 100 9 0 7 0 5 0 50 4 0 3 0 2 0 0 1 0 0 50 North Face 100 150 200 250 Valley Bottom 300 3 50 400 South Face 1 0 100 9 0 7 0 5 0 50 4 0 3 0 2 0 0 0 5 0 100 150 200 25 0 300 350 400 Frozen Soil Infiltration mm 1 0 1 0 INFILRATION EXCESS (SNOWMELT RUNOFF) 5 0 0 100 4 0 0 3 0 0 50 2 0 0 1 5 0 1 0 0 0 0 50 100 150 North Face 200 250 300 350 Valley Bottom South Face 100 50 0 0 50 100 150 200 250 300 400 350 400 1 0 CONCLUSIONS • Infiltration and runoff can be calculated from mean parameters (SWE, θ, Φ, M) within a landscape type – no ‘scaling problem’ evident. • Substantial difference in infiltration and runoff with landscape type – SWE determined by windflow change – Melt rate determined by slope and aspect – Soil moisture determined by drainage – Organic layer thickness determined by slope and aspect • Water storage potential in organic layer and infiltration to frozen mineral soils are not primarily drainage controlled but are controlled by slope and aspect through their influence on melt energy and soil and organic layer properties • Snowmelt runoff is not primarily topographically controlled but is controlled primarily by accumulation of wind-blown snow and melt energetics and secondarily by soil moisture. WOLF CREEK – 15 YEARS 1993 - 2008 Thank You