Ecological Archives C006-105-A4

Ekananda Paudel, Gbadamassi G. O. Dossa, Marleen D. de Blécourt, Philip Beckschäfer, Jianchu Xu, and Rhett D. Harrison. 2015. Quantifying the factors affecting leaf litter decomposition across a tropical forest disturbance gradient. Ecosphere 6:267. http://dx.doi.org/10.1890/es15-00112.1

Appendix D. Model summaries.

Table D1. Summary of linear mixed-effects model for percent mass loss (log transformed) from leaf litter bags installed across a tropical forest disturbance gradient. Independent variables included, installation season (SEASON), disturbance category (FOR_TYPE), litter type (LIT_TYPE), bag type (BAG_TYPE) and all two-way interactions. Installment season (SEASON) had 2 levels: Dry = dry season (baseline) and Wet = wet season. Forest type (FOR_TYPE) had 3 levels: CC = mature forest (baseline), OC = regenerating forest and OL = open land. Litter type had 2 levels: Dipterocarpus (baseline) and Parashorea. Bag type (BAG_TYPE) had 2 levels: C_Mesh = coarse mesh (baseline, fauna access) and F_Mesh = fine mesh (fauna exclusion). The number of days since installation (DAYS) was modeled as a second order polynomial for the fixed time effect, as this was a repeated measures design, and we included a DAYS:SEASON interaction. Random effects included a random intercept for PLOT/SUBPLOT, as the subject level term, and a random slope for installment season to account for the heteroscedasticity of variance.

Random effects:

Groups

Name

Variance

Std. Dev.

SUB_PLOT.PLOT

SEASON.Wet

0.02629

0.1621

SUB_PLOT.PLOT.1

(Intercept)

0.01091

0.1044

PLOT

SEASON.Wet

0.02319

0.1523

PLOT.1

(Intercept)

0.02151

0.1467

Residual

 

0.05205

0.2281

Fixed effects:

 

Estimate

Std. Error

t value

Intercept

2.6489

0.051

51.94

SEASONWet

0.98773

0.05621

17.57

FOR_TYPEOC

-0.0543

0.06836

-0.79

FOR_TYPEOL

-0.10801

0.08445

-1.28

LIT_TYPEParashorea

0.47255

0.01771

26.69

BAG_TYPEF_Mesh

-0.13562

0.01773

-7.65

poly(DAYS, 2)1

37.10402

0.3625

102.36

poly(DAYS, 2)2

2.94047

0.3475

8.46

SEASONWet:FOR_TYPEOC

-0.02615

0.07449

-0.35

SEASONWet:FOR_TYPEOL

-0.62543

0.09184

-6.81

SEASONWet:LIT_TYPEParashorea

-0.02699

0.01639

-1.65

SEASONWet:BAG_TYPEF_Mesh

-0.03749

0.01641

-2.28

SEASONWet:poly(DAYS, 2)1

-24.9217

0.4973

-50.11

SEASONWet:poly(DAYS, 2)2

-11.2644

0.4946

-22.77

FOR_TYPEOC:LIT_TYPEParashorea

0.02194

0.01816

1.21

FOR_TYPEOL:LIT_TYPEParashorea

-0.09181

0.02344

-3.92

FOR_TYPEOC:BAG_TYPEF_Mesh

-0.07279

0.01816

-4.01

FOR_TYPEOL:BAG_TYPEF_Mesh

-0.18194

0.02347

-7.75

LIT_TYPEParashorea:BAG_TYPEF_Mesh

0.10298

0.01637

6.29

 

Table D2. Summary of linear mixed-effects model for percent mass loss (log transformed) from leaf litter bags installed in a shade-house mesocosm experiment, with three levels of simulated canopy cover and three litter-bed treatments. Independent variables included, installation season (SEASON), simulated canopy cover (SIM_CC), litter-bed disturbance category (FOR_TYPE), litter type (LIT_TYPE) and all two-way interactions. Installment season (SEASON) had 2 levels: Dry = dry season (baseline) and Wet = wet season. Simulated canopy cover had three levels: full-shade (baseline, two layers of shade-cloth), half-shade (HS, one layer of shade-cloth) and open-canopy (OP, no shade-cloth). Liter-bed forest type (FOR_TYPE) had 3 levels: CC = mature forest (baseline), OC = regenerating forest and OL = open land. Litter type had 2 levels: Dipterocarpus (baseline) and Parashorea. The number of days since installation (DAYS) was modeled as a second order polynomial for the fixed time effect, as this was a repeated measures design, and we included a DAYS:SEASON interaction. Random effects included a random intercept for ROW:COL/PLOT, as the subject level term, and a random slope for installment season to account for the heteroscedasticity of variance.

Random effects:

Groups

Name

Variance

Std. Dev.

ROW:COL:PLOT

SEASON.Wet

0.002686

0.051822

ROW:COL

(Intercept)

0.000053

0.007281

Residual

0.07912

0.077450

0.278306

Fixed effects:

 

Estimate

Std. Error

t value

(Intercept)

1.869071

0.043936

42.54

SEASONWet

1.36706

0.055837

24.48

poly(DAYS, 2)1

23.761881

0.393399

60.4

poly(DAYS, 2)2

-2.263696

0.376596

-6.01

SIM_CCHS

-0.005886

0.046764

-0.13

SIM_CCOP

0.25303

0.046764

5.41

LIT_TYPEParashorea

0.575858

0.05356

10.75

FOR_TYPEOC

0.016536

0.046384

0.36

FOR_TYPEOL

-0.032373

0.046384

-0.7

SEASONWet:poly(DAYS, 2)1

-14.436745

0.556955

-25.92

SEASONWet:poly(DAYS, 2)2

-0.487704

0.559238

-0.87

SEASONWet:SIM_CCHS

-0.448089

0.056277

-7.96

SEASONWet:SIM_CCOP

-0.948146

0.056277

-16.85

SEASONWet:LIT_TYPEParashorea

0.098336

0.043732

2.25

SEASONWet:FOR_TYPEOC

-0.083887

0.056277

-1.49

SEASONWet:FOR_TYPEOL

-0.056509

0.056277

-1

SIM_CCHS:LIT_TYPEParashorea

-0.067359

0.05356

-1.26

SIM_CCOP:LIT_TYPEParashorea

-0.207467

0.05356

-3.87

LIT_TYPEParashorea:FOR_TYPEOC

0.02027

0.05356

0.38

LIT_TYPEParashorea:FOR_TYPEOL

-0.008388

0.05356

-0.16

 

Table D3. Summary of linear mixed-effects model for percent mass loss (log transformed) from leaf litter bags installed across a tropical forest disturbance gradient. Independent variables included, installation season (SEASON), plant species composition (NMDS1 and NMDS2), litter type (LIT_TYPE), bag type (BAG_TYPE) and all two-way interactions. Installment season (SEASON) had 2 levels: Dry = dry season (baseline) and Wet = wet season. Plant species composition (trees, herbs, lianas) was represented by the first two axes of an NMDS ordination (see Fig. 5). Litter type had 2 levels: Dipterocarpus (baseline) and Parashorea. Bag type (BAG_TYPE) had 2 levels: C_Mesh = coarse mesh (baseline, fauna access) and F_Mesh = fine mesh (fauna exclusion). The number of days since installation (DAYS) was modeled as a second order polynomial for the fixed time effect, as this was a repeated measures design, and we included a DAYS:SEASON interaction. Random effects included a random intercept for PLOT/SUBPLOT, as the subject level term, and a random slope for installment season to account for the heteroscedasticity of variance. Note response data were the same as in Table A3 but the analysis replaced FOR_TYPE with plant species composition data.

Random effects:

Groups

Name

Variance

Std. Dev.

SUB_PLOT.PLOT

SEASON.Wet

0.02602

0.1613

SUB_PLOT.PLOT.1

(Intercept)

0.01108

0.1052

PLOT

SEASON.Wet

0.02236

0.1495

PLOT.1

(Intercept)

0.01549

0.1244

Residual

 

0.05241

0.2289

Fixed effects:

 

Estimate

Std. Error

t value

Intercept

2.61389

0.02704

96.66

SEASONWet

0.81562

0.03271

24.93

poly(DAYS, 2)1

36.93878

0.36358

101.60

poly(DAYS, 2)2

2.89596

0.3486

8.31

LIT_TYPEParashorea

0.45145

0.01154

39.10

BAG_TYPEF_Mesh

-0.22481

0.01165

-19.30

NMDS1

0.14647

0.06861

2.13

NMDS2

-0.29127

0.11214

-2.60

SEASONWet:NMDS1

0.5841

0.08353

6.99

SEASONWet:NMDS2

0.36838

0.13662

2.70

SEASONWet:poly(DAYS, 2)1

-24.7967

0.49879

-49.71

SEASONWet:poly(DAYS, 2)2

-11.2242

0.49607

-22.63

LIT_TYPEParashorea:BAG_TYPEF_Mesh

0.1

0.01649

6.07

NMDS1:LIT_TYPEParashorea

0.06576

0.02205

2.98

NMDS2:LIT_TYPEParashorea

0.09477

0.03516

2.70

NMDS1:BAG_TYPEF_Mesh

0.1741

0.02207

7.89

NMDS2:BAG_TYPEF_Mesh

-0.0822

0.03519

-2.34

 

Table D4. Summary of linear mixed-effects model for percent mass loss (log transformed) from leaf litter bags installed across a tropical forest disturbance gradient. Independent variables included, installation season (SEASON), soil/topography (PCA1 and PCA2), litter type (LIT_TYPE), bag type (BAG_TYPE) and all two-way interactions. Installment season (SEASON) had 2 levels: Dry = dry season (baseline) and Wet = wet season. Soil (see Appendix C: Table A2) /topographic data was represented by the first two axes of a principal components ordination (see Fig. 7). Litter type had 2 levels: Dipterocarpus (baseline) and Parashorea. Bag type (BAG_TYPE) had 2 levels: C_Mesh = coarse mesh (baseline, fauna access) and F_Mesh = fine mesh (fauna exclusion). The number of days since installation (DAYS) was modeled as a second order polynomial for the fixed time effect, as this was a repeated measures design, and we included a DAYS:SEASON interaction. Random effects included a random intercept for PLOT/SUBPLOT, as the subject level term, and a random slope for installment season to account for the heteroscedasticity of variance. Note response data were the same as in Table A3 but the analysis replaced FOR_TYPE with soil/topographic data.

Random effects:

Groups

Name

Variance

Std. Dev.

SUB_PLOT.PLOT

SEASON.Wet

0.025072

0.15834

SUB_PLOT.PLOT.1

(Intercept)

0.009304

0.09646

PLOT

SEASON.Wet

0.091065

0.30177

PLOT.1

(Intercept)

0.031865

0.17851

Residual

 

0.053635

0.23159

Fixed effects:

 

Estimate

Std. Error

t value

Intercept

2.61216

0.036137

72.29

SEASONWet

0.813478

0.059324

13.71

poly(DAYS, 2)1

36.95171

0.368167

100.37

poly(DAYS, 2)2

2.882306

0.353112

8.16

LIT_TYPEParashorea

0.452623

0.011652

38.85

BAG_TYPEF_Mesh

-0.21841

0.011754

-18.58

PCA1

-0.01583

0.009679

-1.64

PCA2

0.036771

0.011865

3.1

SEASONWet:PCA1

-0.01078

0.014535

-0.74

SEASONWet:PCA2

0.008874

0.018142

0.49

SEASONWet:poly(DAYS, 2)1

-24.8

0.504946

-49.11

SEASONWet:poly(DAYS, 2)2

-11.2003

0.502153

-22.3

LIT_TYPEParashorea:BAG_TYPEF_Mesh

0.099707

0.01668

5.98

PCA1:LIT_TYPEParashorea

0.004785

0.004262

1.12

PCA2:LIT_TYPEParashorea

0.003213

0.004735

0.68

PCA1:BAG_TYPEF_Mesh

0.008834

0.004263

2.07

PCA2:BAG_TYPEF_Mesh

-0.01578

0.004749

-3.32


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