Top Banner
Water Vapor Fluxes from Snow Covered Landscapes: The Importance of Biotic and Abiotic-Mediated Processes Adrian A. Harpold Natural Resources and Environmental Science University of Nevada, Reno CUAHSI Cyberseminar 4/17/2015
46

2015 CUAHSI Spring Cyberseminar Series - Adrian Harpold

Sep 29, 2015

Download

Documents

"Water vapor fluxes from snow covered landscapes: the importance of biotic and abiotic-mediated processes". A discussion of emerging understanding of abiotic vapor fluxes (interception, snowpack sublimation, etc.) and the role of snow water in sustaining transpiration will be discussed in the context of changing snowpack dynamics from climate change and forest disturbance. Dr. Harpold is an Assistant Professor of Natural Resources and Environmental Sciences at the University of Nevada, Reno.
Welcome message from author
This document is posted to help you gain knowledge. Please leave a comment to let me know what you think about it! Share it to your friends and learn new things together.
Transcript
  • Water Vapor Fluxes from Snow Covered Landscapes: The Importance of Biotic

    and Abiotic-Mediated Processes

    Adrian A. Harpold Natural Resources and Environmental Science

    University of Nevada, Reno CUAHSI Cyberseminar 4/17/2015

  • Ecohydrological Paradoxes and Tradeoffs of Water Vapor Fluxes in Snowy Systems

    How can snowmelt be both an efficient irrigator of vegetation and streamflow generation?

    Will warming temperatures generate more/less vapor loss?

    What are the tradeoffs between canopy interception and snowpack sublimation?

    What are the tradeoffs between abiotic and biotic vapor losses on overall water budgets?

    What can we learn from natural experiments (i.e. forest disturbance) to answer these questions?

  • Acknowledgements

    Paul Brooks, University of Utah

    Joel Biederman, USDA ARS

    Patrick Broxton, University of Arizona

    John Knowles, University of Colorado

    Theo Barnhart, University of Colorado

    Noah Molotch, University of Colorado, JPL

  • 1981-2010 Mean Precipitation

    Topography, Water, and Carbon Co-vary

    Sierra Nevada

    S. Rockies Appalachians

  • 1981-2010 Mean Precipitation

    5

    1981-2010 Min Temperature

    Topography, Water, and Carbon Co-vary

    Sierra Nevada

    S. Rockies Appalachians

  • 1981-2010 Mean Precipitation

    6

    1981-2010 Min Temperature

    Topography, Water, and Carbon Co-vary

    Kellendorfer et al., 2011, RSE

    Sierra Nevada

    S. Rockies Appalachians

  • Dry Year P=73 cm

    ET Q

    The Water Balance of Snow-Dominated Systems

    Water balance is dynamic Example: Upper Truckee, CA

    Simplified equation P=ET+Q

    Wet Year P=155 cm

    ET Q

    From USFS

    30-Year Average

    ET Q

  • Interception

    Snow sublimation

    Soil evap Transpiration

    Storage

    Streamflow

    Dry Year P=73 cm

    ET Q

    The Water Balance of Snow-Dominated Systems

    Water balance is dynamic Example: Upper Truckee, CA

    More resolved equation:

    How do we partition P into various stores and fluxes?

    P=Esoil+Vinterception+Vsublimation+T+Q+S

  • Snowmelt Timing Westerling et al., 2006

    Biotic Water Demand is Changing: Effects of Forest Fire

    Year 2000 Fire Regime

    Schmidt et al., 2002

    Beetle Outbreaks (Meddens et al., 2012)

    Large departure from historical means Small departure from historical means

  • Snowpack Dynamics Are Changing: Changes in AccumulaIon

    Change in snow to rain Nov to March 1949-2004

    Knowles, 2006, Journal of Climate

    Change SWE 1950-2000

    Mote et al., 2009

    More rain, less

    snow

    Smaller April 1 snowpacks

  • Snowpack Dynamics Are Changing: Changes in AblaIon

    Trends over the last 30 years (1980-2010) Shorter snowmelts (SM50=Ime 50% melt occurs) Increased sublimaIon (SWE: Winter P raIo)

    Harpold et al., 2012, WRR

  • Paradox/Tradeoff 1: How can snowmelt be both an efficient

    irrigator of vegetation and streamflow generation?

  • Snow is a More Efficient Streamflow Generator Than Rain

    Snowy watersheds show a range of ET/P Snowy watersheds generate more

    streamflow when normalized to climate

    Berghuijs et al., 2014, Nature CC

    Long-term average for one watershed (red=snowy, green=rainy)

    Over generates streamflow

    Under generates streamflow

  • Snow is a More Efficient Streamflow Generator Than Rain. Why?

    259 sites, 2100+ station years

    Snowmelt is responsible for peak soil moisture (PSM) response across varying stations

    Consequently, soil field capacity most likely to be exceeded during snowmelt

    Harpold and Molotch, in prep

    1:1 relationship between peak soil moisture and snow

    disappearance

  • Snow is a More Efficient Streamflow Generator Than Rain. Why?

    Model results suggest that more rapid snowmelt generates more streamflow (less vapor losses)

    1100'0"W1200'0"W

    450'0"N

    400'0"N

    350'0"N

    350Kilometers

    Barnhart et al., in prep

    High snowmelt rates efficiently generate streamflow

    High snow fractions show range of response

    Study Area

  • Snowmelt is an Efficient Irrigator

    Niwot Ridge Ameriflux carbon measurements

    Corresponding snow depth

    Synchronicity between carbon uptake and snow water availability

    0 50 100 150 200 2500

    100

    200Sn

    ow d

    epth

    cm

    2007

    Ordinal Day0 50 100 150 200 250

    5

    0

    NEE

    umol/

    m2 /s

    Snow

    Dep

    th (c

    m) NEE (um

    ol/m2/s)

    Snowmelt begins & NEE increases

    Maximum annual NEE occurs at snow disappearance

  • Snowmelt is an Efficient Irrigator Longer growing season

    lead to less net ecosystem productivity (NEP)

    Snow water used for transpiration throughout the year

    GPP

    (g C

    m-2

    wee

    k-1 )

    Hu et al., 2010, GCB

    Snow derived Rain derived

    Less SWE, less NEP

  • Paradox/Tradeoff 2: Will warming temperatures generate more/less

    biotic vapor losses?

  • BioIc Controls: LimitaIons

    Most of the snow-dominated Western U.S. has both temperature and water limitaIons on transpiraIon

    Boisvenue and Running, 2006; GCB

  • Biotic Controls: Changes in Temperature Limitations

    Most runoff is generated at high elevations

    Reduced temperature limitations can increase ET and decrease runoff

    Assumes forests move up in elevation

    Goulden and Bales, 2014, PNAS

    Most runoff comes from high elevations

    Increased ET w/ warming

  • Biotic Controls: Importance of Alpine and Subalpine Area

    Knowles, Harpold, et al., (in review), Hydro. Proc.

    Spatial distributions matter! 35% of catchment area generates 60% of streamflow Catchment water balance will depend on how these

    ecosystems respond and adapt to warming temperatures

    From niwot.colorado.edu

  • Paradox/Tradeoff 3: What are the tradeoffs between canopy interception and snowpack

    sublimation?

  • Abiotic Controls: Tradeoffs Between Interception and Snowpack Ablation

    Distribution of snow in healthy forests reflects interception and sublimation losses

    Pea

    k S

    WE

    to P

    Rat

    io

    (SW

    E/P

    )

    Canopy sublimation

    Snowpack sublimation

    Distance (m)

    Canopy cover

    Canopy cover

  • Forest Structure Influences on Abiotic Vapor Losses

    Lidar shows impacts of interception and ablation across mosaic of canopy structure and topography

    Canopy position matters!

    Snow%Depth%(cm)%

    0.4%

    0.3%

    0.2%

    0.1%

    %%%0%20%%%%%%%40%%%%%%%60%%%%%%%%80%%%%%%%100%%%%%%120%%%%%140%Pr

    obab

    ility%of%O

    ccurrence%

    Under%Canopy%Near%Canopy%Distant%Canopy%

    Observed:%Solid%Line%Modeled:%Dashed%Line%

    1000 m

    100 m

    Broxton et al., Ecohydrology, 2015 0"

    100"

    200"

    Snow"Depth"(cm)"

    Near canopy Distant NUnder canopy

  • Predicting Abiotic Vapor Losses: Snow Physics and Laser Mapping (SnowPALM)

    Broxton et al., Ecohydrology, 2015

    Topography and canopy structure parameterized at 1-m resolution

    Forced by tower micrometeorology

    Verified with snow depth at 1-m scale

  • 0%

    10%

    20%

    30%

    40%

    50%

    Snow sublimation Interception Total vapor losses

    Frac

    tion

    of W

    inte

    r P

    Jemez, NM Boulder, CO

    PredicIng AbioIc Vapor Losses: Site-Level Controls

    Climate and forest structure lead to differing tradeoffs between interception and snow sublimation at each site

    Snowpack Vapor Loss (mm)

    39 65 92

    Snowpack Vapor Loss (mm)

    119 166 212

    Broxton et al., Ecohydrology, 2015

    Boulder, CO Jemez, NM

  • 50%

    55%

    60%

    65%

    70%

    75%

    1 meter 3 meter 10 meter 30 meter 100 meter

    Frac

    tion

    of to

    tal V

    fr

    om s

    ublim

    atio

    n

    Jemez, NM Boulder, CO

    Smart Forest Management: Fine-Scale Canopy Matters For Water Partitioning Higher resolution leads to different

    estimates using the same physics Characterizing canopy as under or

    open is insufficient

    1000 m

    100 m

    Sublimation increases 15%

    Jemez River

    Boulder Creek

    Broxton et al., Ecohydrology, 2015

  • Paradox/Tradeoff 4: What are the tradeoffs between abiotic and biotic

    vapor losses in snow dominated systems?

  • Tradeoffs In Abiotic and Biotic Vapor Losses: Forests and Alpine

    Response of water budgets depend strongly on distribution of abiotic and biotic-mediated processes

    Changes in runoff generation in alpine areas from warming could overwhelm changes in subalpine forests

    !

    !

    From niwot.colorado.edu

    Knowles, Harpold, et al., (in review), Hydro. Proc.

    Abiotic: more efficient streamflow generator, less sensitive to climate

    Biotic: less efficient streamflow generator, more sensitive to climate

  • What can we learn from natural experiments to answer understand paradoxes and tradeoffs in vapor

    losses from snow-dominated systems?

  • Forest Disturbance in the Southern Rockies: A Natural Experiment

    Can we use forest disturbance to learn about: Tradeoffs between

    interception and snowpack sublimation?

    Tradeoffs between abiotic and biotic vapor losses?

    Denver, CO

    MPB impacts Chimney Park, WY

    Heavy fire impacts Las Conchas, NM

    Impacted study catchments

  • Effects of Disturbance: Expectations from Mountain Pine Beetle (MPB)

    (weeks)

    Gray Attack

    Interception

    (months) (years)

    Hyd

    rolo

    gic

    Par

    titio

    ning

    Ano

    mal

    y E

    nerg

    y A

    nom

    aly Radiationsw

    Wind

    Courtesy: J. Biederman

    Transpiration

    Hypothesis 1: Larger Snowpacks

    Hypothesis 2: Increased Streamflow

  • CanEvap Soil Evap

    Total ET

    0

    200

    400

    600

    CLM4 Noah CLM4 Noah

    Sensi&vity to Vegeta&on Change Chimney Park, WY

    Impacted LAI=1

    Healthy LAI=4

    Water (cm)

    Courtesy of D. Gochis, NCAR

    LAI=1

    LAI=4

    Eects of Disturbance: Model Fidelity Model experiment using two land-surface models

    CLM Noah

    Different total partitioning of vapor losses between models

  • 0

    5

    10

    15

    20

    New

    sno

    w e

    vent

    (cm

    )

    Healthy Post-fire

    Eects of Disturbance: Tradeos Between IntercepIon and Snowpack SublimaIon

    Individual snow event shows evidence of interception changes following disturbance

  • 0

    10

    20

    30

    40

    Healthy Pre-Fire

    Wat

    er (c

    m)

    Winter P Maximum SWE

    SWE:P = 68% SWE:P = 67%

    0

    5

    10

    15

    20

    25

    Healthy Post-fire

    Wat

    er (c

    m)

    Winter P Maximum SWE

    Eects of Disturbance: Tradeos Between IntercepIon and Snowpack SublimaIon

    0"

    10"

    20"

    30"

    40"

    50"

    Healthy" MPB"Die4O"

    Water"(cm)"

    April"2011"Snow"Survey"

    SWE:P"="74%""

    SWE:P"="69%""

    Winter precipita&on (cm)

    0"

    10"

    20"

    30"

    40"

    50"

    Healthy"MPB"Die4O

    "

    Water"(cm)"

    April"2011"Snow"Survey"

    SWE:P"="74%

    ""

    SWE:P"="69%

    ""

    Peak SWE (cm)

    Surprisingly, peak snowpacks did not change after disturbance

    SWE:P = 56% SWE:P = 62%

    2012 POST-FIRE (survey) 2011 POST MPB (survey) Biederman et al., 2015, Ecohydro. Harpold et al., 2015, Ecohydro.

  • MPB below/above 12% 20% Healthy below/above 9% 11%

    Site

    Wind Speed (m/s)

    Rsw (W/m2)

    NWT Above Canopy Sub-canopy

    CP Above Canopy

    Sub-canopy

    4.1 (2.4) 0.38 (0.15)

    3.6 (1.3) 0.43 (0.30)

    131 (65) 14 (9)

    126 (65) 25 (15)

    Change from sublimation in canopy (Healthy) to sublimation of the snowpack (Disturbed)

    Energy to snowpack increased following disturbance

    Biederman, Harpold, et al., WRR

    0%

    10%

    20%

    30%

    40%

    50%

    2010 2011 2012

    Win

    ter V

    apor

    Flu

    x/Pr

    ecip

    itatio

    n (c

    m/c

    m)

    Healthy MPB die-off

    Eects of Disturbance: Tradeos Between IntercepIon and Snowpack SublimaIon

  • Larger snowpack sublimation post-disturbance

    Snowpack sublimation compensates for lower interception (total vapor losses still 30-45%)

    Canopy sublimation

    Snowpack sublimation

    Healthy Forest

    Canopy sublimation

    Post-Fire Forest

    Snowpack sublimation

    Eects of Disturbance: Tradeos Between IntercepIon and Snowpack SublimaIon

  • Eects of Disturbance: Tradeos Between AbioIc and BioIc Vapor Losses

    ~50% of water budget to summer vapor loss

    Similar cumulative vapor losses in post-disturbance forest

    Biederman, Harpold, et al., 2014, WRR

    0%

    10%

    20%

    30%

    40%

    50%

    60%

    70%

    80%

    2010 2011 2012

    Sum

    mer

    Vap

    or F

    lux/

    Prec

    ipita

    tion

    (cm

    /cm

    )

    Healthy MPB die-off

  • Effects of Disturbance: Tradeoffs Between Abiotic and Biotic Vapor Losses

    Evidence of kinetic fractionation indicative of evaporation ONLY in disturbed sites

    Biederman, Harpold, et al., 2014, WRR

  • 0%

    10%

    20%

    30%

    40%

    50%

    2010 2011 2012

    Run

    off E

    ffici

    ency

    (cm

    /cm

    )

    Healthy Q* MPB die-off Q* MPB die-off Q

    Eects of Disturbance: Tradeos Between AbioIc and BioIc Vapor Losses

    No evidence for increased streamflow using both measured streamflow (Q) and water balance approach (Q*=P-ET)

    Biederman, Harpold, et al., 2014, WRR

  • Eects of Disturbance: Tradeos Between AbioIc and BioIc Vapor Losses

    Tradeoffs between interception and snowpack sublimation Increased energy inputs to

    under canopy snowpacks

    Potential sources of growing season vapor losses: Greater soil evaporation Compensation by trees Recovering vegetation

    Soil evaporation

    Remaining forest

    Regrowth

  • Tradeoffs in Abiotic and Biotic Vapor Losses: Disturbed Forests

    Eight watersheds in Colorado were investigated following severe MPB disturbance

    Biederman, Harpold, et al., (in review, WRR)

  • Tradeoffs in Abiotic and Biotic Vapor Losses: Disturbed Forests

    We infer abiotic-mediated vapor losses mediate decreases in transpiration using three different methods

    Biederman, Harpold, et al., (in review)

    Only significant changes were towards less runoff

    following disturbance

  • Take Home Points Snowmelt effectively infiltrates the soil profile

    thus maximizing storage (for transpiration) and water subsidies (for runoff)

    Tradeoffs between interception and snowpack sublimation depend strongly on climate and vegetation structure

    In semi-arid climates (i.e. Rocky Mountains) abiotic-mediated vapor losses are likely compensating for changes in biotic-mediated vapor losses following disturbance

  • Questions and Comments

  • References Berghuijs, W. R., Woods, R. A., & Hrachowitz, M. (2014). A precipitation shift from snow towards rain

    leads to a decrease in streamflow. Nature Climate Change, 4(7), 583-586. Hu, J. I. A., Moore, D. J., Burns, S. P., & Monson, R. K. (2010). Longer growing seasons lead to less

    carbon sequestration by a subalpine forest. Global Change Biology, 16(2), 771-783. Goulden, M. L., & Bales, R. C. (2014). Mountain runoff vulnerability to increased evapotranspiration with

    vegetation expansion. Proceedings of the National Academy of Sciences, 111(39), 14071-14075. Harpold, A.A. and N.P. Molotch. Timing of snowmelt differentially influences soil moisture response in

    Western U.S. mountain ecosystems. Knowles, J., A.A. Harpold, et al. The relative contributions of alpine and subalpine ecosystems to the

    water balance of a mountainous, headwater catchment in Colorado, USA

    Broxton, P., A.A. Harpold, J. Biederman, P.D. Brooks, P.A. Troch, &N.P. Molotch. (2015) Quantifying the effects of vegetation structure on wintertime vapor losses from snow in mixed-conifer forests. Ecohydrology. doi: 10.1002/eco.1565

    Harpold, A.A., J. Biederman, K. Condon, M. Merino, Y. Korganokar, T. Nan, L.L. Sloat, M. Ross, and P.D. Brooks. (2014) Changes in winter season snowpack accumulation and ablation following the Las Conchas Forest Fire. Ecohydrology. 7: 440-452. doi: 10.1002/eco.1363.

    Biederman, J.A., A.A. Harpold, D. Reed, D. Gochis, B. Ewers, E. Gutmann, & P.D. Brooks. (2014) Increased evaporation following widespread tree mortality limits streamflow response. Water Resources Research. 50, 53955409, doi:10.1002/2013WR014994.

    Biederman, J., P.D. Brooks, A.A. Harpold, D. Gochis, E. Gutman, D. Reed, E. Pendall, & B. Ewers. (2014) Multi-scale Observations of Snow Accumulation and Peak Snowpack Following Widespread, Insect-induced Lodgepole Pine Mortality. Ecohydrology. doi:10.1002/eco.1342.

    Biederman, J., Somor, A., A.A. Harpold, et al. Streamflow response to insect-driven tree mortality in subalpine catchments.