Jump to: Page Content, Section Navigation, Site Navigation, Site Search, Account Information, or Site Tools.
|
|
Technical Comments
|
| 1. |
B. J. Enquist and
K. J. Niklas,
Science
295,
1517
(2002)
|
| 2. | G. C. Evans, The Quantitative Analysis of Plant Growth (Blackwell, Oxford, 1972). |
| 3. | E. J. Veneklaas, L. Poorter, in Inherent Variation in Plant Growth: Physiological Mechanisms and Ecological Consequences, H. Lambers, H. Poorter, M. M. I. Van Vuuren, Eds. (Backhuys, Leiden, Netherlands, 1998), pp. 337-361. |
| 4. | For seven species of woody broad-leaved evergreens, we
excavated plants in a range of sizes in the understories of three
forests in southern Spain (for six of the species, n = 20 to 40; for the seventh, n = 10). We determined
allometries relating variables x and y (i.e., log
y = log x + ), with calculated as the reduced major axis slope (16). For each
allometry, different species typically had the same slope with
different intercepts; we calculated common slopes. 95% confidence
intervals and R2 values were determined as for
least-squares regression (16). SLA scaled with
MT, = -0.22 ± 0.024 (R2 = 0.66); shoot dry mass scaled with root dry
mass, = 1.02 ± 0.078 (R2 = 0.83);
MS scaled with MR, = 1.10 ± 0.085 (R2 = 0.83);
ML scaled with MT, = 0.97± 0.052 (R2 = 0.92) (17). |
| 5. | S. C. Thomas and F. A. Bazzaz, Ecology 80, 1607 (1999) [CrossRef] [ISI]. |
| 6. | J. Cavender-Bares and F. A. Bazzaz, Oecologia 124, 8 (2000) [CrossRef] [ISI]. |
| 7. | W. H. Pearsall, Ann. Bot. 41, 549 (1927) . |
| 8. | C. Monk, Bull. Torrey Bot. Club 93, 402 (1966) [CrossRef]. |
| 9. | G. I. Ågren and T. Ingestad, Plant Cell Environ. 10, 579 (1987) . |
| 10. | M. B. Walters, E. L. Kruger, P. B. Reich, Oecologia 96, 219 (1993) [CrossRef] [ISI]. |
| 11. | D. R. Causton, J. C. Venus, The Biometry of Plant Growth (Edward Arnold, London, 1981). |
| 12. | T. C. Vogelmann, J. N. Nishio, W. K. Smith, Trends Plant Sci. 1, 65 (1996) . |
| 13. | T. Marañón and P. J. Grubb, Funct. Ecol. 7, 591 (1993) [CrossRef]. |
| 14. | B. Shipley and R. H. Peters, Funct. Ecol. 4, 523 (1990) [CrossRef]. |
| 15. | L. Sack and P. J. Grubb, Funct. Ecol. 15, 145 (2001) [CrossRef]. |
| 16. | K. J. Niklas, Plant Allometry (Univ. of Chicago Press, Chicago, 1994). |
| 17. | L. Sack, P. J. Grubb, T. Marañón, Plant Ecol., in press. |
Response: Sack et al. draw much-needed attention to the difference between the allometry of early plant ontogeny and the allometry of interspecific comparisons using data from mature individuals. Using intraspecific data for a few species from closed canopy forests, where light is likely limiting, Sack et al. claim that leaf properties (specifically SLA) change during early ontogeny, such that our model obtains inaccurate estimates of above-ground biomass.
We agree that SLA is an important factor in plant ecophysiology. However, the scaling differences noted by Sack et al. can be explained in other, equally effective ways. For example, our theory (1, 2) assumes that plants are mature and that leaves are the sole photosynthetic organs. For most of the data we analyzed, that assumption is reasonably accurate; however, it is often violated during early ontogeny, when stem tissues may significantly contribute to photosynthesis. If stems do contribute significantly to photosynthesis, our model predicts that the sum of leaf and stem biomass will scale in a near-isometric way with respect to root biomass, as noted by Sack et al.
Similarly, as we stated (1), our model assumes that maternal effects (such as metabolites stored in endosperm or megagametophytes and used in early plant development) are negligible. If this assumption is violated, as it may be in the case of seedling or juvenile establishment, observed standing biomass relations will differ from those predicted by our model. Therefore, a variety of factors other than changes in SLA can account for the differences in juvenile versus mature plant biomass partitioning patterns observed by Sack et al. That these differences evoke a "tenfold error" in the predictions of our model for extremely small, juvenile plants is hardly surprising, but it is also somewhat misleading. Our model identifies the functional allometric relations among standing leaf, stem, and root biomass (across rather than within species) based on Model Type II regression analyses. Therefore, the magnitude of "error" in one variable must be placed in the context of the magnitude of "error" in the other variable against which it is regressed. In this regard, the "errors" referred to by Sack et al. are comparable across 12 orders of magnitude of body size.
Sack et al. also attribute to us statements that we did not make. We explicitly stated that according to allometric theory, "the surface areas over which resources are exchanged with the environment (e.g., leaf surface area, which correlates with ML) are proportional to the 3/4 power of the total plant biomass" [see also (3)]. It cannot escape attention that the resource exchange "surface areas" of leaves include internalized mesophyll surface areas in contact with the air. Further, as noted above, these exchange surfaces might also include stems during early ontogeny. Thus, total exchange surface areas may not be equivalent to total leaf surface area as defined by Sack et al. Unfortunately, these and other inaccurate statements detract from many of the valuable points that Sack et al. make.
We are nonetheless gratified that Sack et al. agree that the 3/4 scaling relation we proposed for gross photosynthesis and total plant body mass fits "realistic ontogenetic allometries...if the area-based photosynthetic rate...is stable," noting that such rates sometimes increase "ontogenetically with plant size, but only slightly." Clearly, these observations only bolster the predictions of our model. Indeed, our recent data compilations support a 3/4 scaling of whole plant resource use for both adult and juvenile plants (4, 5).
We agree with Sack et al. that allometric relationships for early ontogeny may be very different as a result of a variety of factors, some of which we outlined in (1). Nevertheless, our model accurately predicts the scaling relations among standing leaf, stem, and root biomass across 12 orders of magnitude of body size for monocot, dicot, and conifer species growing under remarkably different environmental conditions. To our knowledge, no other analytically based treatment of vegetative biomass partitioning is as statistically, conceptually, or mechanistically robust.
Brian J. Enquist
Department of Ecology and
Evolutionary
Biology
University of Arizona
Tucson, AZ 85721, USA
Karl J. Niklas
Department of Plant Biology
Cornell University
Ithaca, NY 14853, USA
| 1. | B. J. Enquist and K. J. Niklas, Science 295, 1517 (2002) . |
| 2. | K. J. Niklas, B. J. Enquist, Am. Nat., in press. |
| 3. |
G. B. West,
J. H. Brown,
B. J. Enquist,
Science
284,
1677
(1999)
|
| 4. | B. J. Enquist, G. B. West, E. L. Charnov, J. H. Brown, Nature 401, 907 (1999) [CrossRef] . |
| 5. |
K. J. Niklas and
B. J. Enquist,
Proc. Natl. Acad. Sci. U.S.A.
98,
2922
(2001)
|
Science. ISSN 0036-8075 (print), 1095-9203 (online)