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Student: Paul Welle
Collaborators:Ines AzevedoMitchell SmallSarah CooleyScott Doney
THE IMPACT OF CLIMATE STRESSORS
ON CORAL BLEACHING AND MORTALITY:
A CASE STUDY OF THE 2005 CARIBBEAN SUMMER
2
Eakin et al. (2010) Caribbean summer 2005 Bleaching, Mortality (dependent variables) Temperature (independent variable)
BACKGROUND
Reproduced from Eakin (2010)
5
(1) Limited by the functional form of OLS
We expand to a non-linear model.
(2) Uncontrolled spatial correlation
We add in fixed eff ects.
(3) Limited number of explanatory variables
We extend the dataset to include photosynthetically active radiation (PAR) and pH. We also recalculate
DHW.
ANALYSIS CAN BE IMPROVED
6
DHW correlates well with bleaching and mortality, although there are indications that the 12-week interval should be lengthened.
PAR Anomaly correlates well with bleaching and mortality (PAR does not), but seems to be of less importance than DHW.
In predicting mortality, it is best to use the maximum value of a stressor, while predicting bleaching the recent (observed) temperatures are more important.
Depth is very protective against PAR. For deep corals (13.5m, or 80 th percentile), PAR plays almost no part in predicting bleaching. For shallow corals (5m, or 20 th percentile), PAR is roughly as important a stressor as DHW.
WHAT WE LEARNED
9
METHOD(VARIABLES)
Four stressor formulations Temperature - Degree Heating Weeks (DHW) – 12 week Photosynthetically Active Radiation – PAR 12 week average Photosynthetically Active Radiation – PAR Anomaly Simulated pH – Monthly average
Each formulation has 2 forms “Maximum” – Hypothesized to be important for mortality “Observed” – Hypothesized to be important for bleaching
Bleaching-and-
Mortality=
MaxDHW, ObsDHW, MaxPAR, MaxPAR Anomaly, ObsPAR,
ObsPAR Anomaly, MaxPH, ObsPHf( )
10
RESULTS
General Model:
Mortality Model
Bleaching Model
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� �� ܦܪ� ൌ��� �ఈభή�ௗ�௧ ήܦܪ�� ݔܯ� ͳൌ�� �ఈభή�ௗ�௧ ή� �� ݏܦܪ�� �� ܣ� ൌ��� �ఈమή�ௗ�௧ ή� ܣ� ݔݔݔݔݔݔݔݔݔݔݔݔݔܯ� ݔ ݕ�� � ܣ ͳൌ�� �ఈమήݐ�� � ή� �� ܣ� ݏ ݕ�� � ܣ
16
DHW correlates well with bleaching and mortality, although there are indications that the 12-week interval should be lengthened.
PAR Anomaly correlates well with bleaching and mortality (PAR does not), but seems to be of less importance than DHW.
In predicting mortality, it is best to use the maximum value of a stressor, while predicting bleaching the recent (observed) temperatures are more important.
Depth is very protective against PAR. For deep corals (13.5m, or 80 th percentile), PAR plays almost no part in predicting bleaching. For shallow corals (5m, or 20 th percentile), PAR is roughly as important a stressor as DHW.
WHAT WE LEARNED
17
Eakin, C . M. , Morgan, J . a , Heron, S. F. , Smith, T. B. , L iu , G. , A lvarez-Fi l ip , L . , … Bouchon, C. (2010). Car ibbean cora ls in cr is is : record thermal s t ress , b leaching, and morta l i ty in 2005. PloS one , 5 (11) , e13969.
Hoegh- Guldberg, O. , Mumby, P. J . , Hooten, a J . , Steneck, R. S . , Greenfi eld, P. , Gomez, E . , … Hatz io los , M. E . (2007). Cora l reefs under rapid c l imate change and ocean ac id ifi cat ion. Science (New York, N.Y. ) , 318 (5857), 1737–42.
McWil l iams, J . , Côté, I . , & Gi l l , J . (2005). Accelerat ing impacts of temperature-induced cora l b leaching in the Car ibbean. Ecology , 86 (8) , 2055–2060.
Wilkinson, C. "Cora l b leaching and morta l i ty–The 1998 event 4 years later and b leaching to 2002." Status of cora l reefs of the wor ld (2002): 33-44.
Wilkinson, C l ive R. , and David Souter , eds. Status of Car ibbean cora l reefs af ter b leaching and hurr icanes in 2005 . Global Cora l Reef Monitor ing Network, 2008.
Yee, S. H. , Santavy, D. L . , & Barron, M. G. (2008). Compar ing environmental infl uences on cora l b leaching across and with in spec ies us ing c lustered b inomial regress ion. Ecologica l Model l ing , 218 (1-2) , 162–174.
Yee, S. H. , & Barron, M. G. (2010). Predict ing cora l b leaching in response to environmental s t ressors us ing 8 years of g lobal -scale data. Environmental monitor ing and assessment , 161 (1-4) , 423–38.
REFERENCES
22
DESCRIPTIVE STATISTICS
Variable [units] Min Median Mean Max
Dependent Variables:
Bleaching [%] 0.0 26.3 33.2 100 Mortality [%] 0.0 0.0 2.0 68.3
Candidate Explanatory Variables:
Depth [m] 0.9 9.2 10.0 42.7 Maximum DHW [°C] 0.0 3.7 4.6 17.2 Observed DHW [°C] 0.0 0.5 2.8 16.6 Maximum PAR [Einsteins/m2] 35.6 47.7 47.9 53.7 Maximum PAR Anomaly [Einsteins/m2]
1.6 16.0 17.9 56.0
Observed PAR [Einsteins/m2] 26.3 39.8 40.4 52.4 Observed PAR Anomaly [Einsteins/m2]
0.0 0.75 4.67 36.5
Simulated Maximum pH [-] 8.07 8.10 8.10 8.20 Simulated Observed pH [-] 8.03 8.07 8.07 8.13 Base PAR [Einsteins /m2] 42.3 51.1 50.4 54.2
26
CORRELATIONS
Max DHW
Obs DHW
Max PAR
Obs PAR
Max PAR Anomaly
Obs PAR Anomaly
Max pH Obs pH Base PAR
Depth
Max DHW ---- 0.67*** -0.02 -0.09*** 0.19*** 0.11*** 0.00 0.41*** -0.39*** 0.15***
Obs DHW *** ---- -0.11*** -0.39*** -0.06*** -0.33*** -0.05** 0.51*** -0.26*** 0.15***
Max PAR *** ---- 0.33*** 0.21*** 0.21*** 0.15*** -0.15*** 0.59*** -0.01
Obs PAR *** *** *** ---- 0.03* 0.70*** -0.12*** -0.71*** 0.27*** 0.06***
Max PAR Anomaly
*** *** *** * ---- 0.36*** 0.22*** 0.02 -0.46*** -0.10***
Obs PAR Anomaly
*** *** *** *** *** ---- -0.06*** -0.51*** -0.09*** 0.00
Max pH ** *** *** *** *** ---- 0.23*** 0.11*** -0.11***
Obs pH *** *** *** *** *** *** ---- -0.18*** 0.06***
Base PAR *** *** *** *** *** *** *** *** ---- 0.05***
Depth *** *** *** *** *** *** *** ----
27
Questions:Which stressor form fi ts best- maximum, observed, or
weighted average?Bleaching – Weighted AverageMortality – Maximum
Does PAR or PAR anomaly fi t the data better?Bleaching – PAR AnomalyMortality – PAR Anomaly
Does measuring independent maximums of temperature and radiation suffi ce, or must one account for simultaneously high peaks?
Bleaching – IndependentMortality – Independent
Is there evidence for a depth-stressor interaction?Bleaching – YesMortality - No
SUMMARY
28
MORTALITY MODELS
Model 4
Model 5
General Model:
Model 1
Model 2
Model 3
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29
MORTALITY MODELS
(1) (2) (3) (4) (5) VARIABLES Model Model Model Model Model
Maximum DHW 0.164*** 0.166*** 0.188*** 0.176*** 0.187***
(0.0279) (0.0295) (0.0286) (0.0628) (0.0289) Maximum PAR 0.0452 0.156***
(0.0352) (0.0576) Depth -0.0535*** -0.0501*** -0.0479*** -0.173*** -0.0477***
(0.0112) (0.0121) (0.0118) (0.0670) (0.0117) Base PAR -0.167***
(0.0641) Maximum PAR 0.0283*** -0.0276* 0.0261***
Anomaly (0.00851) (0.0149) (0.00939)
Depth x 0.000333 Maximum DHW (0.00486)
Depth x 0.00551**
*
Maximum PAR (0.00125)
Maximum DHW 0.00109 x Maximum PAR Anomaly Follow
(0.00215)
Maximum PAR
Anomaly x Max DHW Follow
-0.00449 (0.00595)
Constant -6.648*** -3.823** -5.496*** -4.068*** -5.515***
(1.547) (1.845) (0.430) (0.784) (0.468)
Log-Likelihood -62.4294 -62.0861 -62.0672 -61.4354 -62.0358
AIC 0.163501 0.164758 0.162808 0.165427 0.166576
Observations 1,045 1,045 1,045 1,045 1,045
30
BLEACHING MODELS
Model 5
Model 6
General Model:
Model 1
Model 2
Model 3
Model 4
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ݖ ൌߚ�� ଵߚ �� ܦܪ� ݏ ଶߚ �� ܣ� ݏ ଷߚ ݐݐܦ ସߚ ݏ ܤ� � ܣ� ߚ � K
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31
BLEACHING MODELS
(1) (2) (3) (4) (5) (6) VARIABLES Model Model Model Model Model Model
Observed DHW 0.145*** 0.148*** 0.138*** 0.170*** 0.204***
(0.00982) (0.00974) (0.00982) (0.00924) (0.0155) Observed PAR -0.0273*** -0.0245***
(0.00601) (0.00601) Depth 0.00962** 0.0103** 0.00863* 0.0106** 0.0731*** 0.0739***
(0.00464) (0.00461) (0.00463) (0.00463) (0.0113) (0.0115) Base PAR -0.0364**
(0.0179) Observed PAR
Anomaly -0.0213***
(0.00377)
Maximum PAR
Anomaly 0.00909**
(0.00359) 0.0340*** (0.00593)
Depth x Observed
DHW -0.00333***
(0.000999)
Depth x Observed
PAR -0.00269***
(0.000492)
Weighted Average DHW (α=0.0282)
0.213*** (0.0152)
Weighted Average PAR (α=0.0034)
0.0416*** (0.00662)
Depth x Weighted
Average DHW -0.00322***
(0.000967)
Depth x Weighted Average PAR
-0.00301*** (0.000559)
Constant -0.332 1.329 -1.264*** -1.680*** -2.258*** -2.452***
(0.266) (0.894) (0.107) (0.144) (0.175) (0.173)
Log-Likelihood -1267.13 -1266.48 -1265.58 -1268.99 -1263.85 -1260.05 AIC 0.87683 0.877067 0.875777 0.878091 0.875961 0.87472
Observations 2,945 2,945 2,945 2,945 2,945 2,945
32
Fixed Eff ects Fractional Logit Model Logit – Used for binary dependent variables Fractional Logit – Repurposed for bounded dependent
variable Fixed Effects – Used to control for homogeneity within
groupsMaximize quasi-likelihood function:
Returns sigmoid in range (0,1)
MODEL
𝑦𝑖 = 11+ 𝑒−(𝛽0+σ 𝛽𝑗𝑥𝑖𝑗+ σ 𝛽𝑘𝑑𝑖𝑘 + 𝜖𝑖)𝑘𝑗