2014-AGU_poster_ver9

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How does increasing deciduous shrub dominance influence: 1. canopy phenology? 2. Growing and peak season length? 3. vegetation-atmosphere carbon exchange? Results References Modeled LAI and CO 2 Flux We thank Rick Shory and Geneva Chong for help in deploying equipment and with data analysis. We thank Gus Shaver for advisement during the preparation of the manuscript, and Jesse Krause, Jessica Gersony, Heather Greaves, and TeamBird 2013 for field assistance. We also thank the Institute of Arctic Biology and Toolik Field Station (University of Alaska, Fairbanks) for support and logistics. This project has been funded by collaborative NSF grants from NSF’s Office of Polar Programs (ARC 0908444 to N.T. Boelman, 0908602 to L. Gough, and ARC 0902030 to H. Steltzer) and a Climate Center grant from Columbia University (UR00801-07 60437 to K.L. Griffin). Phenology and Season Length AMAP (Arctic Monitoring and Assessment Programme) (2012) SWIPA Overview Report. In: Arctic climate issues 2011: Changes in Arctic snow, water, ice and permafrost. 97pp. Oslo, Norway. Euskirchen ES et al. (2006) Importance of recent shifts in soil thermal dynamics on growing season length, productivity, and carbon sequestration in terrestrial high-latitude ecosystems. Glob Change Biol, 12:731–750. Jia GJ et al. (2009) Vegetation greening in the Canadian arctic related to decadal warming. J Environ Monitor, 11:2231-2238. Myers-Smith IH et al. (2011) Shrub expansion in tundra ecosystems: dynamics, impacts and research priorities. Environ Res Lett, 6:045509. Shaver GR et al. (2013) Pan-Arctic modeling of net ecosystem exchange of CO 2 . Phil Trans R Soc B, 368: 20120485. Street LE et al. (2007) What is the relationship between changes in leaf area and changes in photosynthetic CO 2 flux in arctic ecosystems? J Ecol, 95:135-150. Zeng H et al. (2011) Recent changes in phenology over the northern high latitudes detected from multi-satellite data. Environ Res Lett, 6:045508 Canopy Phenology (Fig. 5) Compared to EG canopies, DS canopies reached: onset of greening 2 days later onset of peak green 13 days earlier (P < 0.001) onset of senescence 3 days earlier Compare to EG canopies, DS canopies’: green season was 5 days shorter peak season was 10 days longer (P < 0.01) Deciduous Shrub Dominance (Fig. 6) greater deciduous shrub cover = faster green-up (P < 0.001) earlier peak onset (P < 0.001) longer peak season (P < 0.001) Comparing Community Type (Fig. 7) Based on model estimates, DS canopies had: higher LAI greater net CO 2 uptake greater CO 2 loss from R E (P < 0.001) greater CO 2 uptake from GPP (P < 0.001) During green season , DS canopies took up ~ 2x more carbon (an estimated 113 g C m -2 season -1 ) compared to EG canopies (P < 0.001) During peak season , DS canopies took up ~ 3x more carbon (an estimated 100 g C m -2 season -1 ) compared to EG canopies (P < 0.001) Deciduous Shrub Dominance greater deciduous shrub cover = greater NEE during the green season (R 2 = 0.8; P < 0.001) and the peak season (R 2 = 0.9; P < 0.001) Changing Season Length (Table 1) Extending seasons increased C uptake, but more significantly for peak season & more for DS ~ 29% of additional C uptake by deciduous shrub communities during the peak season was due to greater leaf area ~ 71% of additional C uptake was due to the longer peak season of deciduous shrub communities compared to evergreen/graminoid communities Shannan K. Sweet 1 , Natalie T. Boelman 1 , Kevin L. Griffin 1 , Heidi Steltzer 2 , Laura Gough 3 1 Lamont-Doherty Earth Observatory, Department of Earth and Environmental Sciences, Columbia University; 2 Department of Biology, Fort Lewis College, Colorado; 3 Department of Biology, University of Texas, Arlington Introduction Greater deciduous shrub abundance extends tundra peak season and increases modeled net CO 2 uptake * accepted at Global Change Biology Acknowledgements Fig. 5. Seasonal canopy greenness for deciduous shrub (DS) and evergreen/graminoid (EG) canopies. On the respective NDVI curves, dates when canopy phenology metrics were reached are marked with red (DS) and blue (EG) points, with arrows of matching colors extended to the x-axis. Canopy phenology parameters are indicated by number boxes on the x-axis: [1] onset of greening; [2] onset of peak green; and [3] onset of senescence. Green-up rate (slope) Onset peak green (DOY) Peak season length (# days) Deciduous shrub cover (%) Fig. 6. Relationship between deciduous shrub cover in all 18 (9 DS + 9 EG) quadrats and the (a) rate of green-up, (b) onset of peak green, and (c) peak green season length. 175 185 195 R! = 0.8 175 185 195 30 40 50 60 R! = 0.7 30 40 50 60 0.005 0.015 0.025 R! = 0.7 0.005 0.015 0.025 Satellite studies suggest longer growing seasons and earlier peak seasons due to increasing air temperature & earlier spring snowmelt in some Arctic regions Longer growing season enhance carbon (C) uptake by tundra vegetation, especially during peak season when C uptake is at its maximum (c) (b) (a) Change in spring snow-cover duration (1973 – 2009), days Fig. 7. Seasonal (a) leaf area index and (b) net ecosystem exchange of deciduous shrub-dominated (DS) and evergreen/graminoid-dominated (EG) canopies. Dates when phenology metrics were reached are marked with red (DS) and blue (EG) symbols {see Fig. 5} Table 1. Seasonal average NEE (+/- 1 SEM) for deciduous shrub (DS) and evergreen/ graminoid (EG) canopies calculated under modeled season length scenarios: (a) DS green season (63 days); EG green season (68 days); (b) DS peak season (44 days); and EG peak season (34 days). Percentages indicate additional carbon uptake during the longer seasons (i.e. 5-day longer green & 10-day longer peak season). {See Fig. 5 for phenology dates} (a) DS Green Season (63 d) EG Green Season (68 d) % Change P DS NEE (grams C m -2 season -1 ) 221 ± 10 228 ± 10 3% ns EG NEE (grams C m -2 season -1 ) 103 ± 16 107 ± 16 4% ns (b) DS Peak Season (44 d) EG Peak Season (34 d) DS NEE (grams C m -2 season -1 ) 156 ± 5 85 ± 4 84% < 0.01 EG NEE (grams C m -2 season -1 ) 77 ± 12 47 ± 7 64% < 0.05 Change in air T (2005 – 2009, baseline 1951 – 2000), deg-C Change in deciduous shrub cover (~ 1990s – 2010) AMAP 2012 Increases No change each day the growing season is extended in the arctic tundra net carbon uptake increases by 5.3 g C m -2 yr -1 Euskirchen et al. 2006 AMAP 2012 Zeng et al. 2011 Change in start of growing season (2000-2010), days Myers-Smith et al. 2010 Peak season phenology (i.e. peak season length) & how indirect impacts of arctic warming (i.e. increasing deciduous shrub cover) may be contributing to satellite signals of changing regional phenology are less well understood Our Questions We are interested in this length VS. this length 10 20 30 40 50 60 SITES: Data collected 1 Jun to 6 Sep 2013 at two sites, North Slope of Alaska (Fig. 1) Each site had two plots (each plot had two 100-m transects): EG (dominated by evergreens & graminoids) DS (dominated by deciduous shrubs) Chose 18 1-m 2 quadrats along transects (n = 9 DS & 9 EG) based on functional group dominance (Fig. 2) & because 18 equipment assemblages were available (Fig. 3) Fig. 1. Map of Alaska & North Slope of Brooks Range (inset). Field sites are stars. 1 3 2 Day of year NDVI Fig. 4. Model of seasonal canopy phenology B A m Fig. 3. Equipment assemblage; collected reflectance and temperature data used to calculate NDVI and NEE (n = 18) Fig. 2. Mean percent cover (%) of deciduous shrubs and evergreens + graminoids at each site & canopy type. Different letters = significantly different (P < 0.05). Methods NET ECOSYSTEM EXCHANGE MODEL: Modeled: 1) Leaf area index (LAI) {Eq. 2} using tundra specific model from Street et al. (2007) 2) Net ecosystem exchange (NEE) {Eq. 3}, using model from Shaver et al. (2013) & low Arctic site parameters for respiration (R E ) and gross primary production (GPP) Examined effect of changing LAI & season length across DS & EG canopies by integrating NEE for green and peak seasons: 1) Using respective season lengths of each canopy 2) Imposing average season lengths of each canopy type on one another CANOPY PHENOLOGY: Calculated normalized difference vegetation index (NDVI) {Eq. 1} Used piecewise regressions to determine canopy phenology (Fig. 4-circles): onset of greening (start rapid increase in NDVI) onset of peak green (level out of NDVI) onset of senescence (start rapid decrease of NDVI) Calculated season lengths (Fig. 4-squares): A peak season = onset peak green to onset senescence B green season = onset greening to onset senescence Calculated green-up rates (Fig. 4-diamond): m = slope daily rate of change in NDVI Satellite studies of the Arctic report longer growing and peak seasons since the 1980s, which lengthens the period of carbon uptake. These trends are attributed to increasing air temperatures and reduced snow cover duration in spring and fall. Concurrently, deciduous shrubs are becoming increasingly abundant in tundra landscapes, which may also impact canopy phenology and productivity. To examine the impact of increasing deciduous shrub dominance on growing season phenology, season length, and carbon (C) flux we monitored canopy phenology using the normalized difference vegetation index (NDVI) and modeled leaf area (LAI) and net ecosystem C exchange (NEE) across a gradient of deciduous shrub- and evergreen/graminoid-dominated tundra . We found that deciduous shrub canopies reached the onset of peak greenness 13 days earlier and the onset of senescence 3 days earlier compared to evergreen/graminoid canopies, resulting in a 10-day extension of the peak season. The combined effect of the longer peak season and greater leaf area of deciduous shrub canopies almost tripled C uptake of deciduous shrub communities compared to evergreen/graminoid communities, while the longer peak season alone resulted in 84% greater C uptake in deciduous shrub communities. These results suggest that greater deciduous shrub abundance increases C uptake not only due to greater leaf area, but also due to an extension of the period of peak greenness, which extends the period of maximum C uptake. Jia et al. 2009 Peak green date in two common arctic subzones Key Findings Abstract {Eq. 1} NDVI = (NIR - R) / (NIR + R) {Eq. 2} LAI = a * e b*NDVI {Eq. 3} NEE = R E – GPP

Transcript of 2014-AGU_poster_ver9

Page 1: 2014-AGU_poster_ver9

How does increasing deciduous shrub dominance influence:

1. canopy phenology? 2. Growing and peak season

length? 3. vegetation-atmosphere carbon

exchange?

Results

References

Modeled LAI and CO2 Flux

We thank Rick Shory and Geneva Chong for help in deploying equipment and with data analysis. We thank Gus Shaver for advisement during the preparation of the manuscript, and Jesse Krause, Jessica Gersony, Heather Greaves, and TeamBird 2013 for field assistance. We also thank the Institute of Arctic Biology and Toolik Field Station (University of Alaska, Fairbanks) for support and logistics. This project has been funded by collaborative NSF grants from NSF’s Office of Polar Programs (ARC 0908444 to N.T. Boelman, 0908602 to L. Gough, and ARC 0902030 to H. Steltzer) and a Climate Center grant from Columbia University (UR00801-07 60437 to K.L. Griffin).

Phenology and Season Length

AMAP (Arctic Monitoring and Assessment Programme) (2012) SWIPA Overview Report. In: Arctic climate issues 2011: Changes in Arctic snow, water, ice and permafrost. 97pp. Oslo, Norway.

Euskirchen ES et al. (2006) Importance of recent shifts in soil thermal dynamics on growing season length, productivity, and carbon sequestration in terrestrial high-latitude ecosystems. Glob Change Biol, 12:731–750.

Jia GJ et al. (2009) Vegetation greening in the Canadian arctic related to decadal warming. J Environ Monitor, 11:2231-2238.

Myers-Smith IH et al. (2011) Shrub expansion in tundra ecosystems: dynamics, impacts and research priorities. Environ Res Lett, 6:045509.

Shaver GR et al. (2013) Pan-Arctic modeling of net ecosystem exchange of CO2. Phil Trans R Soc B, 368: 20120485.

Street LE et al. (2007) What is the relationship between changes in leaf area and changes in photosynthetic CO2 flux in arctic ecosystems? J Ecol, 95:135-150.

Zeng H et al. (2011) Recent changes in phenology over the northern high latitudes detected from multi-satellite data. Environ Res Lett, 6:045508

Canopy Phenology (Fig. 5) u  Compared to EG canopies, DS

canopies reached: •  onset of greening 2 days later • onset of peak green 13 days earlier (P < 0.001)

•  onset of senescence 3 days earlier u  Compare to EG canopies, DS

canopies’: •  green season was 5 days shorter • peak season was 10 days longer (P < 0.01)

Deciduous Shrub Dominance (Fig. 6) u  greater deciduous shrub cover =

•  faster green-up (P < 0.001) •  earlier peak onset (P < 0.001) •  longer peak season (P < 0.001)

Comparing Community Type (Fig. 7) u  Based on model estimates, DS canopies had:

•  higher LAI • greater net CO2 uptake

ü greater CO2 loss from RE

(P < 0.001)

ü greater CO2 uptake from GPP (P < 0.001)

u  During green season, DS canopies took up

~ 2x more carbon (an estimated 113 g C m-2 season-1) compared to EG canopies

(P < 0.001)

u  During peak season, DS canopies took up ~ 3x more carbon (an estimated 100 g C m-2 season-1) compared to EG canopies

(P < 0.001)

Deciduous Shrub Dominance u  greater deciduous shrub cover = greater NEE

during the green season (R2 = 0.8; P < 0.001) and the peak season (R2 = 0.9; P < 0.001)

Changing Season Length (Table 1) u  Extending seasons increased C uptake, but

more significantly for peak season & more for DS

~ 29% of additional C uptake by deciduous shrub communities during the peak season was due to greater leaf area

~ 71% of additional C uptake was due to the longer peak season of deciduous

shrub communities compared to evergreen/graminoid communities

Shannan K. Sweet1, Natalie T. Boelman1, Kevin L. Griffin1, Heidi Steltzer2, Laura Gough3 1 Lamont-Doherty Earth Observatory, Department of Earth and Environmental Sciences, Columbia University; 2 Department of Biology, Fort Lewis College, Colorado; 3 Department of Biology, University of Texas, Arlington

Introduction

Greater deciduous shrub abundance extends tundra peak season and increases modeled net CO2 uptake * accepted at Global Change Biology

Acknowledgements

Fig. 5. Seasonal canopy greenness for deciduous shrub (DS) and evergreen/graminoid (EG) canopies. On the respective NDVI curves, dates when canopy phenology metrics were reached are marked with red (DS) and blue (EG) points, with arrows of matching colors extended to the x-axis. Canopy phenology parameters are indicated by number boxes on the x-axis: [1] onset of greening; [2] onset of peak green; and [3] onset of senescence.

Gre

en-u

p ra

te

(slo

pe)

Ons

et p

eak

gree

n (D

OY

) P

eak

seas

on le

ngth

(#

day

s)

Deciduous shrub cover (%)

Fig. 6. Relationship between deciduous shrub cover in all 18 (9 DS + 9 EG) quadrats and the (a) rate of green-up, (b) onset of peak green, and (c) peak green season length.  

175

185

195

R! = 0.8

175

185

195

3040

5060

R! = 0.73040

5060

0.005

0.015

0.025

R! = 0.7

0.005

0.015

0.025

•  Satellite studies suggest longer growing seasons and earlier peak seasons due to increasing air temperature & earlier spring snowmelt in some Arctic regions

•  Longer growing season enhance carbon (C) uptake by tundra vegetation, especially during peak season when C uptake is at its maximum

(c)

(b)

(a)

Change in spring snow-cover duration (1973 – 2009), days

Fig. 7. Seasonal (a) leaf area index and (b) net ecosystem exchange of deciduous shrub-dominated (DS) and evergreen/graminoid-dominated (EG) canopies. Dates when phenology metrics were reached are marked with red (DS) and blue (EG) symbols {see Fig. 5}

Table 1. Seasonal average NEE (+/- 1 SEM) for deciduous shrub (DS) and evergreen/graminoid (EG) canopies calculated under modeled season length scenarios: (a) DS green season (63 days); EG green season (68 days); (b) DS peak season (44 days); and EG peak season (34 days). Percentages indicate additional carbon uptake during the longer seasons (i.e. 5-day longer green & 10-day longer peak season). {See Fig. 5 for phenology dates}

(a) DS Green Season (63 d)

EG Green Season (68 d)

% Change P

DS NEE (grams C m-2 season-1) − 221 ± 10 − 228 ± 10 3% ns

EG NEE (grams C m-2 season-1) − 103 ± 16 − 107 ± 16 4% ns

(b) DS Peak Season (44 d)

EG Peak Season (34 d)

DS NEE (grams C m-2 season-1) − 156 ± 5 − 85 ± 4 84% < 0.01

EG NEE (grams C m-2 season-1) − 77 ± 12 − 47 ± 7 64% < 0.05

Change in air T (2005 – 2009, baseline 1951 – 2000), deg-C

Change in deciduous shrub cover (~ 1990s – 2010)

AMAP 2012

Increases No change

each day the growing season is extended in

the arctic tundra

net carbon uptake increases by

5.3 g C m-2 yr-1

Euskirchen et al. 2006

AMAP 2012

Zeng et al. 2011

Change in start of growing season (2000-2010), days

Myers-Smith et al. 2010

•  Peak season phenology (i.e. peak season length) & how indirect impacts of arctic warming (i.e. increasing deciduous shrub cover) may be contributing to satellite signals of changing regional phenology are less well understood

Our Questions

We are interested in this length VS. this length

10 20 30 40 50 60

SITES: u  Data collected 1 Jun to 6 Sep 2013 at two

sites, North Slope of Alaska (Fig. 1) u  Each site had two plots (each plot had two

100-m transects): •  EG (dominated by evergreens &

graminoids) •  DS (dominated by deciduous shrubs)

•  Chose 18 1-m2 quadrats along transects (n = 9 DS & 9 EG) based on functional group dominance (Fig. 2) & because 18 equipment assemblages were available (Fig. 3)

Fig. 1. Map of Alaska & North Slope of Brooks Range (inset). Field sites are stars.

1

3 2

Day of year

ND

VI

Fig. 4. Model of seasonal canopy phenology

B

A m

Fig. 3. Equipment assemblage; collected reflectance and temperature data used to calculate NDVI and NEE (n = 18)

Fig. 2. Mean percent cover (%) of deciduous shrubs and evergreens + graminoids at each site & canopy type. Different letters = significantly different (P < 0.05).

Methods

NET ECOSYSTEM EXCHANGE MODEL: u  Modeled:

1)  Leaf area index (LAI) {Eq. 2} using tundra specific model from Street et al. (2007) 2)  Net ecosystem exchange (NEE) {Eq. 3}, using model from Shaver et al. (2013) &

low Arctic site parameters for respiration (RE) and gross primary production (GPP) u Examined effect of changing LAI & season length across DS & EG canopies by

integrating NEE for green and peak seasons: 1) Using respective season lengths of each canopy 2)  Imposing average season lengths of each canopy type on one another

CANOPY PHENOLOGY: u  Calculated normalized difference vegetation index (NDVI) {Eq. 1} u  Used piecewise regressions to determine canopy phenology (Fig. 4-circles):

①  onset of greening (start rapid increase in NDVI) ②  onset of peak green (level out of NDVI) ③  onset of senescence (start rapid decrease of NDVI)

u  Calculated season lengths (Fig. 4-squares): A peak season = onset peak green to onset senescence B green season = onset greening to onset senescence

u Calculated green-up rates (Fig. 4-diamond): m = slope à daily rate of change in NDVI

Satellite studies of the Arctic report longer growing and peak seasons since the 1980s, which lengthens the period of carbon uptake. These trends are attributed to increasing air temperatures and reduced snow cover duration in spring and fall. Concurrently, deciduous shrubs are becoming increasingly abundant in tundra landscapes, which may also impact canopy phenology and productivity. To examine the impact of increasing deciduous shrub dominance on growing season phenology, season length, and carbon (C) flux we monitored canopy phenology using the normalized difference vegetation index (NDVI) and modeled leaf area (LAI) and net ecosystem C exchange (NEE) across a gradient of deciduous shrub- and evergreen/graminoid-dominated tundra . We found that deciduous shrub canopies reached the onset of peak greenness 13 days earlier and the onset of senescence 3 days earlier compared to evergreen/graminoid canopies, resulting in a 10-day extension of the peak season. The combined effect of the longer peak season and greater leaf area of deciduous shrub canopies almost tripled C uptake of deciduous shrub communities compared to evergreen/graminoid communities, while the longer peak season alone resulted in 84% greater C uptake in deciduous shrub communities. These results suggest that greater deciduous shrub abundance increases C uptake not only due to greater leaf area, but also due to an extension of the period of peak greenness, which extends the period of maximum C uptake.

Jia et al. 2009

Peak green date in two common arctic subzones

Key Findings

Abstract

{Eq. 1} NDVI = (NIR - R) / (NIR + R) {Eq. 2} LAI = a * eb*NDVI

{Eq. 3} NEE = RE – GPP