Ecological Archives E086-055-A3

Colleen K. Kelly and Michael G. Bowler. 2005. A new application of storage dynamics: differential sensitivity, diffuse competition, and temporal niches. Ecology 86:1012–1022.

Appendix C. Lack of evidence for gap dependence.

Genus

Species

Abundance (stems/ha)

Size difference between nearest neighbors (mm dbh) – observed

N

Size difference between nearest neighbors (mm dbh) – simulated

Estimated gap dependence (P value)

Bursera

instabilis

42.594

7.167 (6.27)

58

8.653 (0.88)

0.141

 

arborea

19.956

5.716 (4.944)

50

6.767 (0.80)

0.187

 

excelsa

8.638

5.914 (3.52)

25

5.643 (0.81)

0.658

Caesalpina

eriostachys

36.339

9.97 (8.49)

60

10.406 (1.13)

0.700

 

sclerocarpa

5.064

6.38 (5.67)

21

8.063 (1.36)

0.217

 

coriaria

2.383

9.136 (7.77)

31

9.089 (1.29)

0.971

Cordia

alliodora

39.019

11.73 (8.07)

52

11.01 (1.14)

0.405

 

eleaegnoides

2.085

20.04 (21.47)

14

42.56 (10.48)

0.197

Jatropha

chamelensis

6.255

2.20 (4.23)

14

2.44 (1.04)

0.815

 

standleyi

5.064

6.35 (3.86)

17

5.36 (1.11)

0.372

   Notes: Gap dependence was estimated by comparing observed mean dbh difference between conspecific nearest neighbor pairs with mean nearest neighbor dbh difference of 10,000 simulated communities of the same size (N).  Simulated communities were constructed by random selection without replacement from the pool of diameters present in the real community.  The P value of this comparison indicates whether a hypothesis of gap dependence may be accepted (P < 0.05); P values are sometimes also used to signify degree of gap dependence (Lusk and Smith 1998).  None of the species examined showed evidence of significant dependence on gaps, nor is there evidence of correlation between species abundance and degree of gap dependence.  NB: Although not used in analyses of recruitment fluctuations due to lack of growth rate data, Caesalpinia coriaria was included here because it had been selected for the study of Kelly et al. (2001) using the same criteria of ecological similarity as that applied to the other nine species.

 † N = number of pairs.

LITERATURE CITED

Kelly, C. K., H. Banyard Smith, Y. M. Buckley, R. Carter, M. Franco, W. Johnson, T. Jones, B. May, R. Perez Ishiwara, A. Perez-Jimenez, A. Solis Magallanes, H. Steers, and C. Waterman. 2001. Investigations in commonness and rarity: a comparative analysis of co-occuring, congeneric Mexican trees. Ecology Letters 4:618–627.

Lusk, C. H., and B. Smith. 1998. Life history differences and tree species coexistence in an old-growth New Zealand rain forest. Ecology 79:795–806.



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