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Landscape Limnology: Nutrient Fluxes &
Biotic Stability in Complex Mountain Watersheds Wayne Wurtsbaugh, Michelle Kang & Dave Epstein Watershed Sciences Department & Ecology Center Utah State University IALS Meeting, Snowbird, 14 April 2009
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Landscape Ecology ≠ Lakes
} Kratz, Soranno et al. 1991, 1999 Hershey et al. 1999 Riera et al. 2000 Lake placement in watersheds Synchrony of lake processes } Chemical interactions across stream-lake landscapes Baron and Campbell 1997 Hillbricht-Ilkowska 1999 Kling et al { Insect communities & processes at lake outlets Richardson & Mackay 1991 Fisher (1997) Wiens (2002) { Landscape ecology of streams
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Stream–Lake Interaction Project
How do lakes and streams interact in mountain watersheds? Utah State University Univ. of Wyoming Montana State Univ.
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An important question: How do complex patterns of lakes and streams influence ecosystem function?
Boulder Chain Lakes Watershed, White Cloud Mountains, Idaho A B E C D
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Sawtooth Mountains, ID Study site
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Characteristics: Twin Lakes
Watershed Characteristics Elevations m Granitic, glaciated Pristine Precipitation: 80 cm yr -1 1.8 kg NO3- ha-1 yr -1 (N and P limitation of algae) Characteristics: Twin Lakes
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Lower reaches vegetated with lodgepole pine
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Like many montane watersheds, nutrient transport is closely tied to spring snowmelt
~85% of N flux during 2-month runoff period J F M A M J J A S O N D
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Size-frequency Distribution of Lakes in Sawtooths
Of the 220 lakes analyzed, most are quite small (modal size ca m2) Only 0–4% of watershed areas are covered by lakes
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Streams are tiny features in the landscape
Only 0.3% of watershed area Sawtooth stream lengths_WS areas_Decker Dec 03B
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Watershed differences: the have and have nots
Yellow Belly Creek Watershed “Lake-less” South Alturas Ck.
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Watershed Streams Lakes % Stream Lakes %
Area (ha) Perimeter (km) Watershed Streams Lakes % Stream Lakes % Lake Lake “Lakeless” % % ..(N.Alturas) Yellow Belly % %
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PHYSICAL COMPARISONS OF WATERSHEDS WITH AND WITHOUT MAJOR LAKES
Watershed Volumes Residence Time (1000 m3) @ mean discharge (days) Stream Lakes % lake “Lakeless” (N. Alturas) % Yellow Belly %
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How Does Having Lakes High in the Watershed Influence the Function of the Final Lake? Do high lakes starve lower ones of nutrients? Do high lakes “buffer” the flux of nutrients making algal populations more stable in lakes below? “Lakeless” Stanley Lake Yellow Belly Creek Watershed
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Yellow Belly Creek Watershed
Lakes are dissolved nutrient traps whereas streams are “sources” of dissolved nutrients 16 2.5 2.0 12 Temp 1.5 Temperature (°C) NO3 (µM) ± S.E. 8 1.0 4 NO3 0.5 Yellow Belly Creek Watershed Lake Lake Lake 2 4 6 8 10 12 Distance from inflow of headwater lake (km) Yellow Belly Watershed
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Increasing Lake Area Higher in Watershed Decreases Nutrients in Lowest Lakes (5 watersheds compared)
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Increasing Lake Area Higher in Watershed Decreases Mean Annual Phytoplankton (Chl a) in Lowest Lakes
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Increasing Lake Area Higher in Watershed Decreases Phytoplankton Seasonal Variability of Lakes Low in Watershed Few upstream lakes Large upstream lakes
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Increasing Lake Area Higher in Watershed Decreases Phytoplankton Seasonal Variability of Lakes Low in Watershed Few upstream lakes Large upstream lakes
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Summary When lakes are present in watersheds, they dominate water area & volume of the channalized flow, and thus interactions with radiation & gas exchange. The large volumes greatly increase water & nutrient residence times.
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Summary Many ecological functions are dependent on lake-stream interactions Upstream lakes trap nutrients, lowering nutrient levels in down-valley lakes (and streams) Algal populations in down-valley lakes are lowered when upstream lakes trap nutrients However, algal populations are more stable if upstream lakes buffer the flux of nutrients The spatial patterning of streams and lakes is thus a crucial factor influencing watershed function
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Closing photo FIN
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