1

Supporting Information

2

Appendix 1. Climate data.

3 4

Table A1.1. Characteristics of the meteorological stations of the Spanish National Institute of

5

Meteorology (AEMET) used to derive the relationship between elevation and mean annual

6

air temperature (see Fig. S1), and to obtain three regional temperature datasets. Temperature

7

data were standardized, checked for homogeneity and finally combined into three regional

8

datasets corresponding to the four study treelines.

9 Treeline site

Station

Latitude (N)

Longitude (W, E)

Elevation (m a.s.l.)

Period with available temperature data

Ordesa

Canfranc-Los Arañones Candanchú Sallent de Gállego Panticosa Refugio de Góriz Torla Pic du Midi Benasque Estany Redó Vielha Caldes de Boí Artiés Tredòs-Baqueira Port de la Bonaigua Cabdella Estany Gento Alp

42º 43’ 42º 47’ 42º 46’ 42º 43’ 42º 40’ 42º 38’ 42º 50’ 42º 36’ 42º 38’ 42º 43’ 42º 33’ 42º 42’ 42º 42’ 42º 39’ 42º 28’ 42º 31’ 42º 22’

0º 52’ W 0º 31’ W 0º 20’ W 0º 17’ W 0º 01’ E 0º 07’ W 0º 08’E 0º 38’ E 0º 46’ E 0º 48’ E 0º 50’ E 0º 53’ E 0º 57’ E 0º 59’ E 1º 00’ E 1º 00’ E 1º 53’ E

1160 1600 1305 1184 2215 1053 2862 1138 2240 940 1280 1185 1880 2263 1422 2174

1910-2012 1951-1969 1953-1969 1940-1969 1982-2012 1964-2012 1910-1984 1935-1969 1950-1997 1964-2012 1962-1995 1964-1991 1968-1987 1935-1968 1934-1969 1935-1969

1158

1942-1951

La Molina

42º 20’

1º 56’ E

Puigcerdà

42º 26’

1º 56’ E

1704 1145

1955-1969 1932-1963

Tessó

E. Pera / Meranges

10 1

11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26

Ordesa

Tessó

Meranges

14

Mean annual temperature (ºC)

Treeline

12 10 8 6 4 2 0 -2 -4 1000

1500

2000

2500

3000

Elevation (m) 10

2

r=0.71 1

9 0

-1

8

-2

-3

6

-4

1780 1800 1820 1840 1860 1880 1900 1920 1940 1960 1980 2000 9

1

r=0.53

Pic du Midi

8

0

7

-1

6 -2 5 -3 4 1900

27 28 29 30 31 32 33 34 35 36 37 38

1910

1920

1930

1940

1950

1960

1970

1980

1990

2000

Pic du Midi mean annual temperature (ºC)

CRU mean annual temperature (ºC)

7

E. Redó mean annual temperature (ºC)

CRU E. Redó

2010

Years

Figure A1.1. Spatial and temporal variability of temperature data. (a) Linear regression showing the changes in mean annual temperature as a function of elevation across the Spanish Pyrenees (excepting the “Pic du Midi” station located at ca. 2800 m in the French Pyrenees). The elevation range (2100-2400 m) where most Pyrenean mountain pine (Pinus uncinata) treelines are located is indicated as a grey box. The regression line (continuous black line (equation y = 16.10-0.0059x, r² = 0.92) is shown with 95% confidence intervals (dashed lines) and prediction intervals (continuous grey lines). The uppermost images show three Pyrenean treelines. (b) Correlations obtained by relating the mean annual air temperatures reconstructed in a Pyrenean alpine lake (Estany Redó) or recorded at the highelevation Pic du Midi observatory (Bücher and Dessens, 1991) as compared with gridded interpolated data from the CRU dataset (Harris et al. 2014). 2

39

Appendix 2. Reproductive size threshold at treeline.

40 41

Table A2.1. Parameters and statistics (R2, explained variance; n, number of trees) of the

42

binary logistic equations fitted to cone presence or absence as a function of diameter at breast

43

height (dbh) to estimate the reproductive size threshold in four Pyrenean treelines. Equations

44

estimate the probability of cone production (Pc) as: ln(Pc / 1 − Pc) = a + b dbh, where a and

45

b are the fitted parameters.

46 Treeline site

Parameters

R2 (%)

n

a

b

Ordesa

-2.16

0.44

46.26

636

Tessó del Son

-1.30

0.15

53.04

196

Estanys de la Pera

-0.99

0.18

25.60

170

Meranges

-2.06

0.63

73.13

225

47 48 49

3

50

Appendix 3. Reconstructions of tree establishment.

400 300

O

200 100 0

Density (individuals ha-1)

400

T

300 200 100 0

400

E

300 200 100 0

400

M

300 200 100 0 1700

1750

1800

1850

1900

1950

2000

Year of establishment

51 52

Figure A3.1. Reconstructions of tree establishment for the four studied Pyrenean treelines

53

(O, Ordesa; T, Tessó; E, Estanys de la Pera; M. Meranges). The tick of each bar indicates the

54

last year of the decadal age class considered. For instance, the bar located over the 2000 tick

55

shows the number of individuals recruited between the years 1991 and 2000. 4

56

Appendix 4. Mortality model. 1000

M = 2.02 * (BA) - 7.06 R2 = 0.21; p<0.001

(a) -1 Mortality (trees ha )

800

600

400

200

0 0

20

60

Stand Basal Area (m2ha-1)

(b)

57

40

300

Young stand‐living trees (disturbed treeline recolonizing grassland) Young stand ‐dead trees Middle‐aged stand ‐living trees (densifying undisturbed treeline)

250

Density (stems / ha)

Middle‐aged stand ‐dead trees Old stand ‐living trees (static undisturbed treeline)

200

Old stand ‐dead trees  150

100

50

0 10

15

20

58

25

30

35

40

45

50

55

60

65

70

Dbh (cm)

59

Figure A4.1. Relationships observed between Pinus uncinata total stand basal area and the

60

number of dead trees (A). Frequency distribution of P. uncinata living and dead trees in

61

different size class (B). Data were obtained from 810 Pinus uncinata field plots. We used

62

data of mountain pine forests located in Catalonia (NE Spain), where 65% of the Iberian

63

distribution area of this species is located (Villaescusa and Diaz 1998, Villanueva 2004;

64

Martín-Alcón et al. 2012). 5

65

Appendix 5. Growth models and tree populations forecast.

25 BAI raw Age effect model (variance explained 28.35%)

Ordesa

-1

BAI (cm year )

20

2

15

10

5

0 0

20

40

60

80

100

120

Age at coring height (years)

66 67

Figure A5.1. Changes of basal area increment (BAI) as a function of tree age at coring height

68

(1.3 m) in Ordesa site.

69 70

Table A5.1. Linear mixed-effects models of the annual basal area increment (BAI) residuals

71

from the age model as a function of different monthly temperatures in Ordesa. Abbreviations:

72

K, number of parameters included in the model, including the fixed effect variables, i.e.

73

number of monthly temperature with significant support, plus the constant term, plus the

74

error (see also equation 1 in the main text); Δi, difference of Akaike information criterion

75

with respect to the best model; Wi, relative probability that the model i is the best model

76

given the observed data. Values in bold correspond to models with substantial support.

77

Months abbreviated with a “p” subscript correspond to the previous year.

Ordesa 52 trees n= 2949 Random: tree

Fixed effects sepp+novp+may sepp+novp+may+jul sepp+octp+novp+may+jul sepp+ octp+novp+may+jul+sep sepp+ octp+novp+may+jun+jul+sep sepp+ octp+novp+may+jun+jul+aug+sep sepp+octp+novp+may+jun+jul+aug+sep+oct null model

K 5 6 7 8 9 10 11 2

Δi 0.0 3.0 5.1 9.0 14.8 21.6 30.0 37.8

Wi 75.9 17.2 6.0 0.9 0.0 0.0 0.0 0.0

6

78 79

Table A5.2. Statistical parameters obtained by linear mixed-effects models of basal area

80

increment (BAI) residuals from the age model and monthly temperature for Ordesa. Linear

81

regression coefficients of the fixed factors, standard error of the regression and partial

82

explained variance for each selected variable are noted. Months abbreviated with a “p”

83

subscript correspond to the previous year. Variable

Value

Std.Error

Explained variance (%)

sepp

-0.089

0.0173

13.68

novp

0.074

0.0168

11.38

may

0.094

0.0167

14.42

84 85 86

Table A5.3. Explained variance by the full growth model used for Ordesa. Model includes

87

the effect of three components of tree growth: (i) cambial age at coring height, (ii) monthly

88

temperature time series and (iii) autocorrelation structure of tree growth. Explained variance by age model (%) Explained variance by climate model (%) Explained variance by auto-correlation model* (%) Total explained variance (%)

89

28.35 39.47 11.20 79.02

*The autocorrelation model value for BAI of the previous year was 0.45.

90

7

30

Tessó

BAI raw Age effect model (variance explained 36.61%)

-1

20

2

BAI (cm year )

25

15 10 5 0 0

50

100

150

200

Age at coring height (years)

91 92

Figure A5.2. Changes of basal area increment (BAI) as a function of tree age at coring height

93

(1.3 m) in Tessó site.

94 95

Table A5.4. Linear mixed-effects models of the annual basal area increment (BAI) residuals

96

from the age model as a function of different monthly temperature variables in Tessó del Son

97

Abbreviations: K, number of parameters included in the model, including the fixed effect

98

variables, i.e. number of monthly temperature with significant support, plus the constant

99

term, plus the error (see also equation 1 in the main text); Δi, difference of Akaike

100

information criterion with respect to the best model; Wi, relative probability that the model i

101

is the best model given the observed data. Values in bold correspond to models with

102

substantial support. Months abbreviated with a “p” subscript correspond to the previous year.

Tesso 107 trees n=5587 Random effect: tree

Fixed effects sepp+novp+jun+aug sepp+novp+may+jun+aug sepp+jun+aug sepp+octp+novp+may+jun+aug sepp+octp+novp+may+jun+jul+aug sepp+octp+novp+may+jun+jul+aug+oct sepp+octp+novp+may+jun+jul+aug+oct+nov sepp+octp+novp+may+jun+jul+aug+sep+oct+nov

K 6 7 5 8 9 10 11 12

Δi 0.0 3.6 8.4 10.4 15.9 23.2 30.3 38.1

Wi 84.2 14.1 1.2 0.5 0.0 0.0 0.0 0.0

103

8

104 105

Table A5.5. Statistical parameters obtained by linear mixed effect model of basal area

106

increment (BAI) residuals from the age model and monthly temperature for Tessó del Son.

107

Linear regression coefficients of the fixed factors, standard error of the regression and partial

108

explained variance for each selected variable are noted. Months abbreviated with a “p”

109

subscript correspond to the previous year. Variable

Value

Std.Error

Explained variance (%)

sepp

-0.087

0.020

7.17

novp

0.079

0.019

6.49

jun

0.117

0.025

9.66

aug

0.165

0.024

13.59

110 111 112

Table A5.6. Explained variance by the full growth model used for Tessó del Son. Model

113

includes the effect of three components of tree growth: (i) cambial age at coring height, (ii)

114

monthly temperature time series and (iii) autocorrelation structure of tree growth. Explained variance by age model (%) Explained variance by climate model (%) Explained variance by auto-correlation model* (%) Total explained variance (%)

115

36.61 36.90 9.49 83.00

*The autocorrelation model value for BAI of the previous year was 0.47.

116

9

20

E. Pera

15

2

-1

BAI (cm year )

BAI raw Age effect model (variance explained 28.55%)

10

5

0 0

50

100

150

200

250

Age at coring height (years)

117 118

Figure A5.3 Changes of basal area increment (BAI) as a function of tree age at coring height

119

(1.3 m) in Estanys de la Pera site.

120 121

Table A5.7. Linear mixed-effects models of the annual basal area increment (BAI) residuals

122

from the age model as a function of different monthly temperature variables in Estanys de la

123

Pera. Abbreviations: K, number of parameters included in the model, including the fixed

124

effect variables, i.e. number of monthly temperature with significant support, plus the

125

constant term, plus the error (see also equation 1 in the main text); Δi, difference of Akaike

126

information criterion with respect to the best model; Wi, relative probability that the model i

127

is the best model given the observed data. Values in bold correspond to models with

128

substantial support. Months abbreviated with a “p” subscript correspond to the previous year.

E Pera 80 trees n=2847 Random effect: tree

Fixed effects sepp+novp+may+aug+sep+oct sepp+octp+novp+may+jun+jul+aug+sep+oct sepp+novp+may+aug+oct sepp+octp+novp+may+aug+sep+oct novp+may+aug+oct sepp+octp+novp+may+jun+aug+sep+oct novp+may+aug null model

K 8 11 7 9 6 10 5 2

Δi 0.0 0.0 1.0 2.8 5.0 9.7 24.5 169.4

Wi 34.1 33.9 20.6 8.4 2.7 0.3 0.0 0.0

129

10

130 131

Table A5.8. Statistical parameters obtained by linear mixed effect model of basal area

132

increment (BAI) residuals from the age model and monthly temperature for Estanys de la

133

Pera. Linear regression coefficients of the fixed factors, standard error of the regression and

134

partial explained variance for each selected variable are noted. Months abbreviated with a “p”

135

subscript correspond to the previous year. Variable

Value

Std.Error

Explained variance (%)

sepp

-0.078

0.022

5.16

novp

0.158

0.021

9.67

may

0.091

0.023

5.91

aug

0.215

0.027

12.86

oct

0.100

0.018

6.39

136 137 138

Table A5.9. Explained variance by the full growth model used for Estanys de la Pera. Model

139

includes the effect of three components of tree growth: (i) cambial age at coring height, (ii)

140

monthly temperature time series and (iii) autocorrelation structure of tree growth. Explained variance by age model (%) Explained variance by climate model (%) Explained variance by auto-correlation model* (%) Total explained variance (%)

141

28.54 39.98 17.11 85.63

*The autocorrelation model value for BAI of the previous year was 0.55.

142

11

20

Meranges

15

2

1

BAI (cm year- )

BAI raw Age effect model (variance explained 13.97%)

10

5

0 0

20

40

60

80

100

120

140

Age at coring height (years)

143 144

Figure A5.4. Changes of basal area increment (BAI) as a function of tree age at coring height

145

(1.3 m) in Meranges site.

146 147

Table A5.10. Linear mixed-effects models of the annual basal area increment (BAI) residuals

148

from the age model as a function of different monthly temperature variables in Meranges

149

Abbreviations: K, number of parameters included in the model, including the fixed effect

150

variables, i.e. number of monthly temperature with significant support, plus the constant

151

term, plus the error (see also equation 1 in the main text); Δi, difference of Akaike

152

information criterion with respect to the best model; Wi, relative probability that the model i

153

is the best model given the observed data. Values in bold correspond to models with

154

substantial support. Months abbreviated with a “p” subscript correspond to the previous year.

Meranges 62 trees n=2865 Random effect: tree

Fixed effects octp+novp+may+jun+jul+oct sepp+octp+novp+may+jun+jul+oct octp+novp+may+jun+jul sepp+octp+novp+may+jun+jul octp+may+jun+jul sepp+octp+novp+may+jun+jul+aug+ oct sepp+octp+novp+may+jun+jul+aug+sep+oct null model

K 7 9 6 8 5 10 11 2

Δi 0.0 0.4 1.6 1.6 4.1 5.8 13.3 102.8

Wi 34.6 27.7 15.7 15.5 4.4 1.9 0.0 0.0

155 12

156

Table A5.11. Statistical parameters obtained by linear mixed effect model of basal area

157

increment (BAI) residuals from the age model and monthly temperature for Meranges. Linear

158

regression coefficients of the fixed factors, standard error of the regression and partial

159

explained variance for each selected variable are noted. Months abbreviated with a “p”

160

subscript correspond to the previous year. Variable

Value

Std.Error

Explained variance (%)

octp

0.087

0.018

6.53

novp

0.066

0.020

4.97

may

0.097

0.021

7.28

jun

-0.155

0.028

11.67

jul

0.211

0.030

15.90

161 162 163

Table A5.12. Explained variance by the full growth model used for Meranges. Model

164

includes the effect of three components of tree growth: (i) cambial age at coring height, (ii)

165

monthly temperature time series and (iii) autocorrelation structure of tree growth. Explained variance by age model (%) Explained variance by climate model (%) Explained variance by auto-correlation model* (%) Total explained variance (%)

166

13.97 46.35 23.91 84.23

*The autocorrelation model value for BAI of the previous year was 0.60.

167

13

  20

O

15

15

10

10

5

5

T

2

BAI (cm )

20

0

0

168

1900

1920

1940

1960

1980

2000

2020

2040

2060

2080

2100

1900

1920

1940

1960

1980

2000

2020

2040

2060

2080

2100

1920

1940

1960

1980

2000

2020

2040

2060

2080

2100

  20

E

15

15

10

10

5

5

M

2

BAI (cm )

20

0

169

1900

0 1920

1940

1960

1980

2000

Year

2020

2040

2060

2080

2100

1900

Year

170 171

Figure A5.5. Predicted basal area increment (BAI) of 1000 Mountain pine individuals per in

172

each treeline site based on climate-growth linear mixed effects models. For each study site,

173

we simulated the fate of a population of 1000 individuals, with an age structure of the

174

respective population, as sampled in 2010 (see Fig. A3.1). Note that changes in stand density

175

are only related to density-dependent mortality beyond the year 2040.

176 177 178 179 180 181 182 183 184 185 186 187 188 189

References Bücher, A. and Dessens, J. 1991. Secular trend of surface temperature at an elevated observatory in the Pyrenees. Journal of Climate 4: 859–868. Harris, I., Jones, P.D., Osborn, T.J. & Lister, D.H. 2014. Updated high-resolution grids of monthly climatic observations. International Journal of Climatology 34: 623–642. Martín-Alcón S., Coll L., Aunós A. 2012. A broad-scale analysis of the main factors determining the current structure and understory composition of Catalonian sub-alpine (Pinus uncinata Ram.) forest. Forestry 85: 225–236. Villaescusa, R. & Diaz, R. 1998. Segundo Inventario Forestal Nacional (1986–1996). Ministerio de Medio Ambiente, ICONA, Madrid, Spain. Villanueva, J.A. 2004. Tercer Inventario Forestal Nacional (1997-2007). Comunidad de Madrid, Madrid, Ministerio de Medio Ambiente, Madrid, Spain. 14

190 191

Appendix 6. Seed viability as a function of growth form.

192 193 194 195 196 197 198 199 200 201 202

Figure A6.1. Seed viability (means ± SD) measured as the percentage of germinated seeds

203

from cones taken in Mountain pine (Pinus uncinata) individuals sampled at the Ordesa

204

treeline site. Three growth forms were considered: shrubby individuals (krummholz), adults

205

(arborescent individuals at least 2-m tall presenting vertical or erect stems) and intermediate

206

individuals forming both shrubby and erect stems.

207

15

Ecosystems Supp Info.pdf

Sallent de Gállego 42o 46' 0o 20' W 1305 1953-1969. Panticosa 42o 43' 0o 17' W 1184 1940-1969. Refugio de Góriz 42o 40' 0o 01' E 2215 1982-2012.

5MB Sizes 2 Downloads 278 Views

Recommend Documents

Supp sheet.pdf
Sign in. Page. 1. /. 2. Loading… Page 1 of 2. Page 1 of 2. Page 2 of 2. Page 2 of 2. Supp sheet.pdf. Supp sheet.pdf. Open. Extract. Open with. Sign In. Main menu.Missing:

South Florida Ecosystems
citrus farming in South Florida and it is where the. St. Lucie River flows into the Indian River La- goon, an estuary that empties into the Atlantic. Ocean. The Indian ...

Human Domination of Earth's Ecosystems
The use of land to yield goods and services represents the most substantial human al- teration of the Earth system. Human ... and forests and woodlands from which global environmental change. ..... becomes successful there, calling it back is.

CISS Infos 25_ Supp Europe_web.pdf
Les contributions du public seront directement prises en. compte dans l'agenda politique de la Commission. Représentation des patients au sein de. l'Agence ...

KRA-Supp Sheet-Apr18.pdf
FALL COWS & CALVES EPD'S. LOT TAG NAME HERD GRID CED BW WW Y W MLK MARB RE FAT. 95 589C KLEIN LARKABA 357A-589C 71 52 1 -1.5 72 112 15 0.58 -0.18 0.02. 95A 778E KLEIN LARKABA 589C-778E 81 50 6 -2 62 95 18 0.32 0 0.01. 96 588C KLEIN ABBY 070X-588C 109

Business and Ecosystems
New markets – such as water quality trading, certified sustainable products, wetland banking and threatened ... operations and those of suppliers and customers.

Tapfury MOL in Supp MDismiss.pdf
There was a problem previewing this document. Retrying... Download. Connect more apps... Try one of the apps below to open or edit this item. Tapfury MOL in ...

Hawkeye Supp 2017.pub.pdf
There was a problem previewing this document. Retrying... Download. Connect more apps... Try one of the apps below to open or edit this item. Hawkeye Supp ...

18 Elizabeth Supp 8 Clean.pdf
Whoops! There was a problem loading more pages. 18 Elizabeth Supp 8 Clean.pdf. 18 Elizabeth Supp 8 Clean.pdf. Open. Extract. Open with. Sign In. Details.

2018 Bull Sale supp sheet.pdf
Page 1 of 2. ϮϬϭΘ^ŽŶƐƚĞŐĂƌĚƵůů^ĂůĞ^ƵƉƉůĞŵĞŶƚ^ŚĞĞƚ. ^ĐƌŽƚĂůƚĂŬĞŶκͬϮͬϮϬϭΘ ĂƌĐĂƐƐ^ĐĂŶĂƚĂƚĂŬĞŶκͬκͬϮϬϭΘ hƉĚĂƚĞĚĂƌĐĂƐƐWƐ. >Žƚη / ^ĐƌŽƚĂů tĞŝŐŚƚ /D&ĂĚũ

Terrestrial and Subsurface Ecosystems Postdoctoral Opportunity The ...
Dec 8, 2014 - The U.S. Department of Energy's Environmental Molecular Sciences Laboratory (EMSL) is now accepting applications for its 2015 Terrestrial ...

Platform Ecosystems: Aligning Architecture ...
Books Synopsis : Platform Ecosystems is a hands-on guide that offers a complete roadmap for designing and orchestrating vibrant software platform ecosystems ...

UNIT 06.- ECOSYSTEMS (Worksheet).pdf
There was a problem previewing this document. Retrying... Download. Connect more apps... Try one of the apps below to open or edit this item. UNIT 06.

2018 KBE Supp Sheet.pdf
Page 1 of 1. 2018 Kentucky Farm Bureau Beef Expo. Supplement Sheet. Lot 19. Sells open. Lot 35. AI'd 2/24/18 to Andras New Direction R240, Reg#1506922. Lot 36. Sells with a Heifer Calf on her side; Born 2/16/18,. Birth Weight 68#, Tattoo 818F. Lot 37

13 Elizabeth Supp 7 Clean.pdf
No aboveground utility, telephone, cable TV or other lines or. the poles on which to hang the lines, wires or cables shall be constructed above ground except as. provided in Subsection (b) below. (b) Variances. In the event of severe hardship an appl

Preserving Biodiversity and Ecosystems: Catalyzing Conservation ...
species-rich landscapes, assisting them to form networks with one another, with ... list of 23 projects that Community Conservation, Inc. has either initiated or .... Terborgh, 1999), social scientists have also criticized these projects (Belsky, 199

Updated Energy In Ecosystems Webquest.pdf
and answer these questions. a. List some of the organism(s) that are producers. b. List some of the organism(s) that are consumers. d. ... Do a print screen and e-mail. me your completed food web. Page 2 of 2. Updated Energy In Ecosystems Webquest.pd

Preserving Biodiversity and Ecosystems: Catalyzing Conservation ...
communities from the programs and their management (Brandon et al., 1998; Inamdar et al., .... (see Horwich & Lyon, 2007) not withstanding published accounts of .... ecotourism, classes on ethnobotany, or small businesses (e.g., restaurants ...... an

Digital Ecosystems for Collaborative Learning
1School of Information Technologies, 2Faculty of Education and Social Work ... 3 Ontario Institute for Studies in Education, University of Toronto, Ontario, ...

Human Domination of Earth's Ecosystems
Aug 15, 2013 - or dominated) fall in the range of 39 to 50%. (5) (Fig. .... enhancement to the greenhouse effect; the .... coveries is the best extant illustration that.

Human Domination of Earth's Ecosystems
centration in the atmosphere has increased by nearly 30 percent since the beginning of the Industrial ..... enhancement to the greenhouse effect; the consensus ...