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TESTING ENERGETIC THEORY WITH 
EXPERIMENTAL DEEP-SEA WOOD FALLS 
CRAIG R MCCLAIN 
National Evolutionary Synthesis Center
WOOD FALL 
Dead Wood Tell Tales 
@DrCraigMc 
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Copy, share, adapt, or re-mix; 
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#woodfall 
@DrCraigMc
Biodiversity 
Productivity Diversity Relationship 
Productivity
THEORIES 
OF 
COMMUNITY 
ASSEMBLY AND 
ENERGETIC 
THEORY
The Species Energy Theory (More Individuals Hypothesis) 
(Srivastava & Lawton 1998), originally 
proposed by Wright (1983) 
! 
As productivity decreases, abundances 
of species also decrease. 
! 
Rare species at low productivities are 
thus at increased risk of stochastic 
extinction, i.e. Allee effects. 
! 
With increased productivity Allee 
effects are diminished and coexistence 
increases (Wright et al. 1993). 
Abundance 
Productivity
Additional energy may elevate the 
amount of rare resources, allowing 
rare or absent niche-specialists to 
become abundant and raise overall 
community diversity, e.g. Niche 
Position Hypothesis (Evans et al. 1999; 
Evans et al. 2005). 
! 
At high productivities, this theory also 
predicts that greater specialization is 
allowable and prevents competitive 
exclusion (Schoener 1976; DeAngelis 
1994). 
Niche Position Hypothesis 
Productivity 
Species 
Unique Traits
Increased energy may increase the 
amount of preferred resource, and 
species may decrease their 
consumption of less optimal 
resources. This would reduce niche 
breadth in high energy areas and 
allow for greater coexistence, e.g. 
Niche Width Hypothesis (Evans et al. 
1999). 
Niche Width Hypothesis 
Productivity 
Niche Breadth
The food web is predicted 
to become more complex 
with increased energy; 
sustenance to higher trophic 
levels results in longer food 
chains (Post 2002a; Takimoto 
& Post 2012). 
One More Trophic Level Hypothesis 
Productivity 
Trophic Level
Nonequitable Distribution of Energy Hypothesis 
An energetic optimum size exists for a 
community that maximizes multiple 
energetic constraints that correlate with 
body size, e.g. metabolism, life history, 
foraging efficiency, starvation resistance 
(Rex & Etter 1998; Sebens 2002). Species 
of this optimum size are more efficient in 
procuring resources and translating them 
into growth and reproduction. 
! 
More energy allows decreases 
competitive interactions based on size, 
i.e. species don’t have to be the perfect 
size 
Productivity 
Body Size
WOOD FALLS 
are an IDEAL 
test system 
for theories about 
COMMUNITY ASSEMBLY 
AND ENERGETIC THEORY
During the Typhoon Morakot in 2009, 
a total of 8.4*1012 g of total woody debris 
was transported to the oceans of Asia
The total amount of energy 
can be precisely controlled 
to the wood fall community.
Discrete habitat boundaries allow for the easy quantification 
of standing stock, trophic structure, and diversity. 
! 
Easily collected allowing for the whole community to be quantified as 
opposed to just the collection of a subset.
39/43 of the species found on the wood fall were endemic 
of these endemic species all were represented by ~10-10,000 
individuals, non-endemics have 1-4 individuals 
Deep-sea wood falls host an almost 
completely endemic fauna 
covering a broad taxonomic composition.
Accurate tracking of energy through the community via stable isotope analysis. 
! 
Stable isotope compositions of animals that rely energetically on wood 
are isotopically distinct from animals that rely energetically on phytodetritus.
Wood falls in deep sea, especially at the depths investigated here, 
are also energetically isolated from the surrounding deep sea.
WOOD 
FALLS 
the IDEAL 
EXPERIMENT
WOOD FALLS 
the 
RESULTS
Xylophaga
-1.0 -0.5 0.0 0.5 
-0.8 -0.6 -0.4 -0.2 0.0 0.2 0.4 0.6 
NMDS1 
NMDS2 
Absent 
Light 
Present 
Weight (kg) 
0 
5 
10 
15 
MDS: a matrix of item–item 
similarities, then assigns a 
location to each item in N-dimensional 
space. Distance in 
plot correlates with differences in 
communities! 
! 
1. Abundance! 
2. Composition 
McClain & Barry, Biology Letters, 2014
Xyloskenea sp. nov. 
32 
30 
Xyloskenea sp. nov. 
large medium small 
Absent Light Present 
-30 -20 -10 0 10 
0 10 20 30 40 
CAP1 
CAP2 
Provanna sp. 1 
Hyalogyra sp. 1 
Polynoidae sp. A. 
Protanais sp. nov. 
3 
65 
7 
10 
1113 
18 
19 
21 
22 
26 27 
35 
Weight 
Absent 
Present 
Light 
Occurence of Halo 
200 
100 
400 
200 
200 
100 
500 
400 
300 
200 
100 
0 
Abundance Per Wood Fall 
Protanais sp. nov. 
0 
0 
0 
Abundance Per Wood Fall 
Wood Weight Group 
Hyalogyra sp. 1 
Provanna sp. 1 
McClain & Barry, Biology Letters, 2014
Protanais sp. nov. 
Dillwynella (Ganesa) panamesis
Set 1 
Set 2 
November 2006-October 2011 (5 years) 
multiple successional stages 
November 2006-October 2013 (7 years) 
post halo stage
Species are targeted to a specific log size and successional state 
Species Energy/Niche Position 
P 
−1.5 −1.0 −0.5 0.0 0.5 1.0 
−1.0 −0.5 0.0 0.5 
NMDS1 
NMDS2 
1 
2 
Log Size 
MDS: a matrix of item–item 
similarities, then assigns a 
location to each item in N-dimensional 
space. Distance in 
plot correlates with differences in 
communities! 
! 
1. Abundance! 
2. Composition
Presence/Absence 
−1.5 −1.0 −0.5 0.0 0.5 
Species are targeted to a specific log size and successional state 
Niche Position Hypothesis 
−0.8 −0.6 −0.4 −0.2 0.0 0.2 0.4 
NMDS1 
NMDS2 
1 
2 
MDS: a matrix of item–item 
similarities, then assigns a 
location to each item in N-dimensional 
space. Distance in 
plot correlates with differences in 
communities! 
! 
1. Composition
Biodiversity 
Productivity Diversity Relationship 
Productivity
1 
2 
3 
4 
5 
6 
7 
8 
9 
10 
11 
12 
13 
14 
15 
16 
17 
24 
18 
19 
20 
21 
22 
23 
26 
27 
28 
29 
30 
31 
32 
35 
20 
15 
10 
5 
0.0 0.5 1.0 
Log10 Weight (kg) 
Richess 
Set 
a 
a 
1 
2 
Species Richness Increases With Wood Fall Size 
Wood Fall Size and Richness Weaker In Second Set 
Smaller Wood Falls Become More Diverse
Hyalogyra sp. 1 Dillwynella (Ganesa) panamesis Xyloskena sp. nov 
Provanna pacifica Provanna sp. 1 Provanna sp. 1 
Hyalogyra sp. 1 
Cephalaspidea sp.???
1 
2 
3 
4 
5 6 
7 
8 
9 
10 
11 
12 
13 
14 
15 
16 
17 
24 
18 
19 
20 
21 
22 
23 
26 
27 
28 
29 
31 30 
32 35 
2500 
2000 
1500 
1000 
500 
0 
0.0 0.5 1.0 
Log10 Weight (kg) 
Abundance 
Set 
a 
a 
1 
2 
743 
1078 
Abundance Increases with Wood Fall Size
1 
2 
3 
4 
5 
6 
7 
8 
9 
10 
11 
12 
13 
14 
15 
35 
16 
17 
18 
19 
20 
21 
22 
24 
23 
26 
27 
28 
29 
30 
31 
32 
20 
15 
10 
5 
1.5 2.0 2.5 3.0 
Log10 Abundance 
Richess 
Set 
a 
a 
1 
2 
Richness of Wood Falls Correlated With Abundance 
More Individual Hypothesis
1 
2 
3 
4 
5 
6 
7 
8 
12 
13 
11 9 10 
14 
15 
16 
17 
18 
19 
20 
21 
22 23 24 26 
27 
28 
2930 
31 
32 
35 
8 
6 
4 
2 
0.0 0.5 1.0 
Log10 Weight (kg) 
Singletons 
Set 
a 
a 
1 
2 
1 
2 
3 
4 
16 
5 
6 
7 
8 
9 
10 
11 
12 
13 
14 
15 
17 
18 
19 
20 
21 
22 
23 24 
26 
27 
28 
29 
30 
31 
32 
35 
15 
10 
5 
0 
0.0 0.5 1.0 
Log10 Weight (kg) 
No. of Species w/ Abundance Less Than 5 
Set 
a 
a 
1 
2 
Number of Rare Species Increases With Wood Fall Size 
More Individual Hypothesis/Niche Position
Gastropod.1 Gastropod.2 Gastropod.3 Gastropod.4 Gastropod.5 Gastropod.7 Gastropod.8 
1.5 
1.0 
2.0 
1.5 
1.0 
0.5 
1.5 
1.0 
0.5 
1.50 
1.25 
1.00 
0.3 
0.2 
0.1 
0.10 
0.05 
0.00 
0.0 0.5 1.0 0.0 0.5 1.0 0.0 0.5 1.0 0.0 0.5 1.0 0.0 0.5 1.0 0.0 0.5 1.0 0.0 0.5 1.0 
Gastropod.9 Gastropod.10 Anemone1 Anemone2 Crinoid Ophiuroid.1 Ophiuroid.2 
0.9 
0.6 
0.3 
0.6 
0.4 
0.2 
0.05 
0.04 
0.03 
0.02 
0.01 
0.9 
0.6 
0.3 
0.6 
0.4 
0.2 
0.06 
0.04 
0.02 
0.0 0.5 1.0 0.0 0.5 1.0 0.0 0.5 1.0 0.0 0.5 1.0 0.0 0.5 1.0 0.0 0.5 1.0 0.0 0.5 1.0 
Ophiuroid.3 Bivalve.4 Bivalve.1 Bivalve.2 Bivalve.3 Polychaete.1 Polychaete.2 
0.050 
0.025 
0.000 
0.4 
0.3 
0.2 
0.1 
0.3 
0.2 
0.1 
0.06 
0.04 
0.02 
1.2 
0.8 
0.4 
1.5 
1.0 
0.5 
0.0 0.5 1.0 0.0 0.5 1.0 0.0 0.5 1.0 0.0 0.5 1.0 0.0 0.5 1.0 0.0 0.5 1.0 0.0 0.5 1.0 
Polychaete.3 Polychaete.4 Polychaete.6 Polychaete.7 Polychaete.8 Polychaete.9 Polychaete.10 
1.2 
0.8 
0.4 
0.6 
0.4 
0.2 
0.3 
0.2 
0.1 
0.12 
0.08 
0.04 
0.20 
0.15 
0.10 
0.05 
0.100 
0.075 
0.050 
0.025 
0.0 0.5 1.0 0.0 0.5 1.0 0.0 0.5 1.0 0.0 0.5 1.0 0.0 0.5 1.0 0.0 0.5 1.0 0.0 0.5 1.0 
Polychaete.11 Polychaete.16 Polychaete.17 Tanaid.1 Galatheid.1 Galatheid.2 Chiton 
0.15 
0.10 
0.05 
0.04 
0.02 
2.0 
1.6 
1.2 
0.8 
0.6 
0.4 
0.2 
0.3 
0.2 
0.1 
0.100 
0.075 
0.050 
0.025 
0.0 0.5 1.0 0.0 0.5 1.0 0.0 0.5 1.0 0.0 0.5 1.0 0.0 0.5 1.0 0.0 0.5 1.0 0.0 0.5 1.0 
Asteroid.1 WTF.1 WTF.2 Amphipod1 Amphipod2 Amphipod3 Pycno1 
0.075 
0.050 
0.025 
0.05 
0.0 0.5 1.0 0.0 0.5 1.0 0.0 0.5 1.0 0.0 0.5 1.0 0.0 0.5 1.0 0.0 0.5 1.0 0.0 0.5 1.0 
Iso1 Limpet1 Limpet2 
2.0 
1.5 
1.0 
0.5 
0.0 
0.5 
0.0 
0.0 
0.75 
0.0 
−0.05 
0.15 
0.10 
0.05 
0.00 
0.0 
0.0 
0.00 
0.0 
0.0 
0.00 
0.100 
0.075 
0.050 
0.025 
0.000 
−0.025 
0.0 
0.0 
0.00 
0.0 
0.0 
0.75 
0.50 
0.25 
0.00 
0.0 
0.0 
0.0 
0.00 
0.00 
0.000 
0.100 
0.075 
0.050 
0.025 
0.000 
0.00 
0.00 
0.8 
0.0 
0.0 
0.000 
0.06 
0.04 
0.02 
0.00 
0.000 
0.00 
1.2 
0.9 
0.6 
0.3 
0.0 
1.00 
0.75 
0.50 
0.25 
0.00 
0.5 
0.4 
0.3 
0.2 
0.1 
0.0 
0.075 
0.050 
0.025 
0.000 
0.100 
0.075 
0.050 
0.025 
0.000 
1.0 
0.5 
0.0 
1.00 
0.75 
0.50 
0.25 
0.00 
0.0 0.5 1.0 0.0 0.5 1.0 0.0 0.5 1.0 
Log10 Weight (kg) 
Abundance 
Set 
1 
2 
Responses of Individual Species Vary
The food web is predicted 
to become more complex 
with increased energy; 
sustenance to higher trophic 
levels results in longer food 
chains (Post 2002a; Takimoto 
& Post 2012). 
One More Trophic Level Hypothesis 
Productivity 
Trophic Level
Conclusions 
• Species richness increases with increasing wood fall size 
• With greater time the relationship becomes weaker 
• With time, smaller logs add species with greater magnitude that larger logs 
• Abundance increases with increasing log size and in second set (more time) 
• Richness is a function of abundance among wood falls (Species Energy) 
• But more species for same abundance in second set 
• Second set is more even (adding more species without increasing abundance) 
• Addition of rare species (Island biogeography, Niche Position) 
• Number of singletons more pronounced in smaller logs (Allee Efffects, Species 
Energy) 
• However, rare species seem to contribute to overall all richness in both sets with 
increasing wood size (Niche Position) 
• Abundance of all species do not increase at the same rate (Niche Position)
Acknowledgments 
Jim Barry (MBARI), Jenna Judge (UC 
Berkeley), David Honig (Duke U), 
Janet Voight (Field Museum), Tammy 
Horton (NOC), Doug Eernisse (UC 
Fullerton), Keiichi Kakue (Hokkaido U) 
! 
Funding: National Evolutionary 
Synthesis Center (NSF Grant 
#EF-0905606) 
! 
Funding and Ship Support: Monterey 
Bay Aquarium Research Institute 
(Packard Foundation) 
! 
Artwork by Immy Smith 
Visiting Artist, Herbarium RNG
Deep Sea News 
http://deepseanews.com 
@DrCraigMc 
Deep Sea 
News 
DSN 
http://craigmcclain.com
More Individuals Hypothesis 
Abundance of all species is expected to increase with increasing wood-fall size. 
! 
Wood-fall size is predicted to be a significant predictor of abundance. 
The size*species interaction term should not be statistically significant, i.e. different relationships— 
negative and positive—between size and abundance for each species 
Df Sum Sq Mean Sq F value Pr(>F) 
Weight 1 46950 46950 26.0946 3.717e-07 *** 
Species 44 815908 18543 10.3063 < 2.2e-16 *** 
Set 1 10825 10825 6.0162 0.0143 * 
Weight*Species 44 432523 9830 5.4635 < 2.2e-16 *** 
Residuals 1349 2427164 1799
Niche Position Hypothesis 
Additional energy may elevate the amount of rare resources, allowing rare or absent niche-specialists 
to become abundant and raise overall community diversity 
! 
Abundance of rare species only increases with increasing wood-fall size. 
! 
The abundance rank order, a metric of dominance/rarity, is expected to show a significant 
interaction effect with size, i.e. high rank order species have slopes near zero and low rank order 
species have positive slopes. 
Df Sum Sq Mean Sq F value Pr(>F) 
Weight 1 46950 46950 21.3099 4.256e-06 *** 
Set 1 10825 10825 4.9131 0.02681 * 
Rank 1 414815 414815 188.2776 < 2.2e-16 *** 
Weight:Rank 1 99176 99176 45.0142 2.807e-11 *** 
Residuals 1435 3161605 2203
Species Rank 
Species Abundance 
1 2 5 10 20 50 100 
1 2 3 4 5 6 7 8 9 10 11 12 
Species Rank 
Species Abundance 
1 2 5 10 20 50 
2 4 6 8 10 12 14 16 
3 
5 
26 
24 
21 19 
6 
7 
10 
18 
22 
11 13 
27 
30 
32 
35 
1 
2 
4 
8 
9 
12 
14 
15 
16 
17 
20 
23 
28 
29 
3.0 
2.5 
2.0 
1.5 
1.0 31 
0.0 0.5 1.0 
Log10 Weight (kg) 
Coefficient from Zipf Fit 
Set 
a 
a 
1 
2 
3 
5 
27 26 
6 
7 
10 
11 
13 
18 
19 
21 
22 
30 
32 
35 
24 
1 
2 
4 
8 
9 
12 
14 
15 
16 
17 
20 
23 
29 28 
31 
0.8 
0.6 
0.4 
0.2 
0.0 0.5 1.0 
Log10 Weight (kg) 
K from Geometric Series 
Set 
a 
a 
1 
2 
Log 32 
Log 35

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Testing energetic theory with experimental deep-sea food falls

  • 1. TESTING ENERGETIC THEORY WITH EXPERIMENTAL DEEP-SEA WOOD FALLS CRAIG R MCCLAIN National Evolutionary Synthesis Center
  • 2. WOOD FALL Dead Wood Tell Tales @DrCraigMc You are free to:! ! Copy, share, adapt, or re-mix; Photograph, film, or broadcast; Blog, Tweet, or post video of; ! Provide that:! ! You attribute the work to its author ! #woodfall @DrCraigMc
  • 3. Biodiversity Productivity Diversity Relationship Productivity
  • 4. THEORIES OF COMMUNITY ASSEMBLY AND ENERGETIC THEORY
  • 5. The Species Energy Theory (More Individuals Hypothesis) (Srivastava & Lawton 1998), originally proposed by Wright (1983) ! As productivity decreases, abundances of species also decrease. ! Rare species at low productivities are thus at increased risk of stochastic extinction, i.e. Allee effects. ! With increased productivity Allee effects are diminished and coexistence increases (Wright et al. 1993). Abundance Productivity
  • 6. Additional energy may elevate the amount of rare resources, allowing rare or absent niche-specialists to become abundant and raise overall community diversity, e.g. Niche Position Hypothesis (Evans et al. 1999; Evans et al. 2005). ! At high productivities, this theory also predicts that greater specialization is allowable and prevents competitive exclusion (Schoener 1976; DeAngelis 1994). Niche Position Hypothesis Productivity Species Unique Traits
  • 7. Increased energy may increase the amount of preferred resource, and species may decrease their consumption of less optimal resources. This would reduce niche breadth in high energy areas and allow for greater coexistence, e.g. Niche Width Hypothesis (Evans et al. 1999). Niche Width Hypothesis Productivity Niche Breadth
  • 8. The food web is predicted to become more complex with increased energy; sustenance to higher trophic levels results in longer food chains (Post 2002a; Takimoto & Post 2012). One More Trophic Level Hypothesis Productivity Trophic Level
  • 9. Nonequitable Distribution of Energy Hypothesis An energetic optimum size exists for a community that maximizes multiple energetic constraints that correlate with body size, e.g. metabolism, life history, foraging efficiency, starvation resistance (Rex & Etter 1998; Sebens 2002). Species of this optimum size are more efficient in procuring resources and translating them into growth and reproduction. ! More energy allows decreases competitive interactions based on size, i.e. species don’t have to be the perfect size Productivity Body Size
  • 10. WOOD FALLS are an IDEAL test system for theories about COMMUNITY ASSEMBLY AND ENERGETIC THEORY
  • 11. During the Typhoon Morakot in 2009, a total of 8.4*1012 g of total woody debris was transported to the oceans of Asia
  • 12.
  • 13. The total amount of energy can be precisely controlled to the wood fall community.
  • 14. Discrete habitat boundaries allow for the easy quantification of standing stock, trophic structure, and diversity. ! Easily collected allowing for the whole community to be quantified as opposed to just the collection of a subset.
  • 15. 39/43 of the species found on the wood fall were endemic of these endemic species all were represented by ~10-10,000 individuals, non-endemics have 1-4 individuals Deep-sea wood falls host an almost completely endemic fauna covering a broad taxonomic composition.
  • 16. Accurate tracking of energy through the community via stable isotope analysis. ! Stable isotope compositions of animals that rely energetically on wood are isotopically distinct from animals that rely energetically on phytodetritus.
  • 17. Wood falls in deep sea, especially at the depths investigated here, are also energetically isolated from the surrounding deep sea.
  • 18. WOOD FALLS the IDEAL EXPERIMENT
  • 19.
  • 20.
  • 21.
  • 22.
  • 23.
  • 24.
  • 25.
  • 26. WOOD FALLS the RESULTS
  • 27.
  • 29.
  • 30.
  • 31.
  • 32.
  • 33. -1.0 -0.5 0.0 0.5 -0.8 -0.6 -0.4 -0.2 0.0 0.2 0.4 0.6 NMDS1 NMDS2 Absent Light Present Weight (kg) 0 5 10 15 MDS: a matrix of item–item similarities, then assigns a location to each item in N-dimensional space. Distance in plot correlates with differences in communities! ! 1. Abundance! 2. Composition McClain & Barry, Biology Letters, 2014
  • 34. Xyloskenea sp. nov. 32 30 Xyloskenea sp. nov. large medium small Absent Light Present -30 -20 -10 0 10 0 10 20 30 40 CAP1 CAP2 Provanna sp. 1 Hyalogyra sp. 1 Polynoidae sp. A. Protanais sp. nov. 3 65 7 10 1113 18 19 21 22 26 27 35 Weight Absent Present Light Occurence of Halo 200 100 400 200 200 100 500 400 300 200 100 0 Abundance Per Wood Fall Protanais sp. nov. 0 0 0 Abundance Per Wood Fall Wood Weight Group Hyalogyra sp. 1 Provanna sp. 1 McClain & Barry, Biology Letters, 2014
  • 35. Protanais sp. nov. Dillwynella (Ganesa) panamesis
  • 36. Set 1 Set 2 November 2006-October 2011 (5 years) multiple successional stages November 2006-October 2013 (7 years) post halo stage
  • 37. Species are targeted to a specific log size and successional state Species Energy/Niche Position P −1.5 −1.0 −0.5 0.0 0.5 1.0 −1.0 −0.5 0.0 0.5 NMDS1 NMDS2 1 2 Log Size MDS: a matrix of item–item similarities, then assigns a location to each item in N-dimensional space. Distance in plot correlates with differences in communities! ! 1. Abundance! 2. Composition
  • 38. Presence/Absence −1.5 −1.0 −0.5 0.0 0.5 Species are targeted to a specific log size and successional state Niche Position Hypothesis −0.8 −0.6 −0.4 −0.2 0.0 0.2 0.4 NMDS1 NMDS2 1 2 MDS: a matrix of item–item similarities, then assigns a location to each item in N-dimensional space. Distance in plot correlates with differences in communities! ! 1. Composition
  • 39. Biodiversity Productivity Diversity Relationship Productivity
  • 40. 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 24 18 19 20 21 22 23 26 27 28 29 30 31 32 35 20 15 10 5 0.0 0.5 1.0 Log10 Weight (kg) Richess Set a a 1 2 Species Richness Increases With Wood Fall Size Wood Fall Size and Richness Weaker In Second Set Smaller Wood Falls Become More Diverse
  • 41. Hyalogyra sp. 1 Dillwynella (Ganesa) panamesis Xyloskena sp. nov Provanna pacifica Provanna sp. 1 Provanna sp. 1 Hyalogyra sp. 1 Cephalaspidea sp.???
  • 42. 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 24 18 19 20 21 22 23 26 27 28 29 31 30 32 35 2500 2000 1500 1000 500 0 0.0 0.5 1.0 Log10 Weight (kg) Abundance Set a a 1 2 743 1078 Abundance Increases with Wood Fall Size
  • 43. 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 35 16 17 18 19 20 21 22 24 23 26 27 28 29 30 31 32 20 15 10 5 1.5 2.0 2.5 3.0 Log10 Abundance Richess Set a a 1 2 Richness of Wood Falls Correlated With Abundance More Individual Hypothesis
  • 44. 1 2 3 4 5 6 7 8 12 13 11 9 10 14 15 16 17 18 19 20 21 22 23 24 26 27 28 2930 31 32 35 8 6 4 2 0.0 0.5 1.0 Log10 Weight (kg) Singletons Set a a 1 2 1 2 3 4 16 5 6 7 8 9 10 11 12 13 14 15 17 18 19 20 21 22 23 24 26 27 28 29 30 31 32 35 15 10 5 0 0.0 0.5 1.0 Log10 Weight (kg) No. of Species w/ Abundance Less Than 5 Set a a 1 2 Number of Rare Species Increases With Wood Fall Size More Individual Hypothesis/Niche Position
  • 45. Gastropod.1 Gastropod.2 Gastropod.3 Gastropod.4 Gastropod.5 Gastropod.7 Gastropod.8 1.5 1.0 2.0 1.5 1.0 0.5 1.5 1.0 0.5 1.50 1.25 1.00 0.3 0.2 0.1 0.10 0.05 0.00 0.0 0.5 1.0 0.0 0.5 1.0 0.0 0.5 1.0 0.0 0.5 1.0 0.0 0.5 1.0 0.0 0.5 1.0 0.0 0.5 1.0 Gastropod.9 Gastropod.10 Anemone1 Anemone2 Crinoid Ophiuroid.1 Ophiuroid.2 0.9 0.6 0.3 0.6 0.4 0.2 0.05 0.04 0.03 0.02 0.01 0.9 0.6 0.3 0.6 0.4 0.2 0.06 0.04 0.02 0.0 0.5 1.0 0.0 0.5 1.0 0.0 0.5 1.0 0.0 0.5 1.0 0.0 0.5 1.0 0.0 0.5 1.0 0.0 0.5 1.0 Ophiuroid.3 Bivalve.4 Bivalve.1 Bivalve.2 Bivalve.3 Polychaete.1 Polychaete.2 0.050 0.025 0.000 0.4 0.3 0.2 0.1 0.3 0.2 0.1 0.06 0.04 0.02 1.2 0.8 0.4 1.5 1.0 0.5 0.0 0.5 1.0 0.0 0.5 1.0 0.0 0.5 1.0 0.0 0.5 1.0 0.0 0.5 1.0 0.0 0.5 1.0 0.0 0.5 1.0 Polychaete.3 Polychaete.4 Polychaete.6 Polychaete.7 Polychaete.8 Polychaete.9 Polychaete.10 1.2 0.8 0.4 0.6 0.4 0.2 0.3 0.2 0.1 0.12 0.08 0.04 0.20 0.15 0.10 0.05 0.100 0.075 0.050 0.025 0.0 0.5 1.0 0.0 0.5 1.0 0.0 0.5 1.0 0.0 0.5 1.0 0.0 0.5 1.0 0.0 0.5 1.0 0.0 0.5 1.0 Polychaete.11 Polychaete.16 Polychaete.17 Tanaid.1 Galatheid.1 Galatheid.2 Chiton 0.15 0.10 0.05 0.04 0.02 2.0 1.6 1.2 0.8 0.6 0.4 0.2 0.3 0.2 0.1 0.100 0.075 0.050 0.025 0.0 0.5 1.0 0.0 0.5 1.0 0.0 0.5 1.0 0.0 0.5 1.0 0.0 0.5 1.0 0.0 0.5 1.0 0.0 0.5 1.0 Asteroid.1 WTF.1 WTF.2 Amphipod1 Amphipod2 Amphipod3 Pycno1 0.075 0.050 0.025 0.05 0.0 0.5 1.0 0.0 0.5 1.0 0.0 0.5 1.0 0.0 0.5 1.0 0.0 0.5 1.0 0.0 0.5 1.0 0.0 0.5 1.0 Iso1 Limpet1 Limpet2 2.0 1.5 1.0 0.5 0.0 0.5 0.0 0.0 0.75 0.0 −0.05 0.15 0.10 0.05 0.00 0.0 0.0 0.00 0.0 0.0 0.00 0.100 0.075 0.050 0.025 0.000 −0.025 0.0 0.0 0.00 0.0 0.0 0.75 0.50 0.25 0.00 0.0 0.0 0.0 0.00 0.00 0.000 0.100 0.075 0.050 0.025 0.000 0.00 0.00 0.8 0.0 0.0 0.000 0.06 0.04 0.02 0.00 0.000 0.00 1.2 0.9 0.6 0.3 0.0 1.00 0.75 0.50 0.25 0.00 0.5 0.4 0.3 0.2 0.1 0.0 0.075 0.050 0.025 0.000 0.100 0.075 0.050 0.025 0.000 1.0 0.5 0.0 1.00 0.75 0.50 0.25 0.00 0.0 0.5 1.0 0.0 0.5 1.0 0.0 0.5 1.0 Log10 Weight (kg) Abundance Set 1 2 Responses of Individual Species Vary
  • 46. The food web is predicted to become more complex with increased energy; sustenance to higher trophic levels results in longer food chains (Post 2002a; Takimoto & Post 2012). One More Trophic Level Hypothesis Productivity Trophic Level
  • 47.
  • 48.
  • 49. Conclusions • Species richness increases with increasing wood fall size • With greater time the relationship becomes weaker • With time, smaller logs add species with greater magnitude that larger logs • Abundance increases with increasing log size and in second set (more time) • Richness is a function of abundance among wood falls (Species Energy) • But more species for same abundance in second set • Second set is more even (adding more species without increasing abundance) • Addition of rare species (Island biogeography, Niche Position) • Number of singletons more pronounced in smaller logs (Allee Efffects, Species Energy) • However, rare species seem to contribute to overall all richness in both sets with increasing wood size (Niche Position) • Abundance of all species do not increase at the same rate (Niche Position)
  • 50. Acknowledgments Jim Barry (MBARI), Jenna Judge (UC Berkeley), David Honig (Duke U), Janet Voight (Field Museum), Tammy Horton (NOC), Doug Eernisse (UC Fullerton), Keiichi Kakue (Hokkaido U) ! Funding: National Evolutionary Synthesis Center (NSF Grant #EF-0905606) ! Funding and Ship Support: Monterey Bay Aquarium Research Institute (Packard Foundation) ! Artwork by Immy Smith Visiting Artist, Herbarium RNG
  • 51. Deep Sea News http://deepseanews.com @DrCraigMc Deep Sea News DSN http://craigmcclain.com
  • 52. More Individuals Hypothesis Abundance of all species is expected to increase with increasing wood-fall size. ! Wood-fall size is predicted to be a significant predictor of abundance. The size*species interaction term should not be statistically significant, i.e. different relationships— negative and positive—between size and abundance for each species Df Sum Sq Mean Sq F value Pr(>F) Weight 1 46950 46950 26.0946 3.717e-07 *** Species 44 815908 18543 10.3063 < 2.2e-16 *** Set 1 10825 10825 6.0162 0.0143 * Weight*Species 44 432523 9830 5.4635 < 2.2e-16 *** Residuals 1349 2427164 1799
  • 53. Niche Position Hypothesis Additional energy may elevate the amount of rare resources, allowing rare or absent niche-specialists to become abundant and raise overall community diversity ! Abundance of rare species only increases with increasing wood-fall size. ! The abundance rank order, a metric of dominance/rarity, is expected to show a significant interaction effect with size, i.e. high rank order species have slopes near zero and low rank order species have positive slopes. Df Sum Sq Mean Sq F value Pr(>F) Weight 1 46950 46950 21.3099 4.256e-06 *** Set 1 10825 10825 4.9131 0.02681 * Rank 1 414815 414815 188.2776 < 2.2e-16 *** Weight:Rank 1 99176 99176 45.0142 2.807e-11 *** Residuals 1435 3161605 2203
  • 54. Species Rank Species Abundance 1 2 5 10 20 50 100 1 2 3 4 5 6 7 8 9 10 11 12 Species Rank Species Abundance 1 2 5 10 20 50 2 4 6 8 10 12 14 16 3 5 26 24 21 19 6 7 10 18 22 11 13 27 30 32 35 1 2 4 8 9 12 14 15 16 17 20 23 28 29 3.0 2.5 2.0 1.5 1.0 31 0.0 0.5 1.0 Log10 Weight (kg) Coefficient from Zipf Fit Set a a 1 2 3 5 27 26 6 7 10 11 13 18 19 21 22 30 32 35 24 1 2 4 8 9 12 14 15 16 17 20 23 29 28 31 0.8 0.6 0.4 0.2 0.0 0.5 1.0 Log10 Weight (kg) K from Geometric Series Set a a 1 2 Log 32 Log 35