Study Number: 

1001

Project Title:

Diversity of macroinvertebrates in water-filled containers: the role of scale on productivity.

Investigator(s):

Donald A. Yee  Tel. 309.438.5278
Steven A. Juliano  Tel. 309.438.5278
Affiliated Institution(s): Illinois State University            
Address: Program in Behavior, Ecology, Evolution, and Systematics
Department of Biological Sciences
Illinois State University
Normal, Illinois 61790-4120
USA
Study Type: Terrestrial
Project Type: Visiting Researcher(s)
Study Period:

06/2000 - 08/2000

Status/Notes:

Project Cancelled.  Project file closed, edits are complete.

Funding Sources:

Scholar-Educator/G.A.A.N.N. funds to D. Yee (internal IUS grant and Department of Education).

Abstract: A considerable void exists in the understanding of how ecological processes affect patterns in nature. In order to fill this gap in understanding, ecologists have proposed a number of seemingly broad ranging explanations for the distribution and abundances of individuals in nature. One of the most debated explanations for broad patterns of species diversity is productivity of the system (1, 2, 3). Productivity may be defined as the rate at which energy flows in an ecosystem. Three patterns of diversity with increasing productivity of a system are pervasive in nature: diversity increases, diversity first increases then decreases beyond some threshold, or diversity decreases. The middle pattern, referred to as ?humped? shaped appears commonly at larger scales (2, 3). Rarely encountered is an increase in diversity with increasing productivity. This pattern may simply represent the first part of a humped-shaped curve where higher productivities have not been examined. The last pattern is commonly found for small-scale (< 1m2) plots (3) and is has been explained by the presence of a superior competitor whose effects are felt at higher productivities (3), underlying environmental heterogeneity, disturbance, or area (2). Although the initial increase in diversity with increasing productivity is intuitive, a decrease in diversity beyond some threshold remains one of the disconcerting holes in ecology. Clouding the issue of process investigation is the issue of scale. It has proven difficult to make the connection between the spatial and temporal scale at which a process is measured, and the scale at which it may operate to produce a particular pattern (4). Organisms themselves perceive their world at scales that may be quite different than the one proposed for investigation. Spatial scale as a factor driving our perceptions of pattern and process has been investigated for few animal communities.

Although no consensus has been reached, it is evident that the spatial scale of investigation can have significant effects on productivity-diversity relationships (5, 6, 7). Microcosms, both natural or artificial, are single bounded representations of larger or more complex systems. Microcosms have been used to bridge the gap between theory and nature (8) and the history of their use in testing ecological theory is long (9, 10, 11). Microcosms may lead to mechanistic insights into the structure of natural communities (12, 8), and may provide a way to reduce extraneous variability in seeking answers to questions of general interest. Tree holes are a commonly used natural microcosms for the investigation of community and population level questions in ecology (e.g., 13, 14, 15). Tree holes are found in virtually all forests, and thus they have a wide distribution throughout temperate and tropical regions. Recently, the relationship of productivity and diversity was examined in tree holes in England (15). The authors of this work found an increase in diversity with increasing productivity but their work failed in several crucial ways to assess adequately their hypotheses. First, although productivity was the ecosystem process of interest, initial nutrient conditions were used as a surrogate for productivity. Second, a rather narrow gradient of initial conditions was used and this fact may help to explain why only an increase in diversity with increasing nutrients was found. If a longer gradient of concentration of nutrients were used, the unimodal pattern may appear. In fact, although regional patterns of productivity and diversity appear to be unimodal, monotonic patterns may potentially result at larger scales of observation (16). Third, because tree holes in England are considered depauperate in species, the productivity-diversity relationship may be hard to elucidate and mechanisms that explain it may be harder to address. Tropical systems contain a higher diversity of organisms and also contain more trophic levels. These characteristics may better allow tropical systems to be used to examine the mechanisms underlying the productivity-diversity relationship, especially for those hypotheses concerned with the total species found in a location and hypotheses based on the geological age of habitats (2). Finally, scale was not considered in their investigation. Scale, as mentioned, may affect the pattern that is observed. Thus, a more through examination of the productivity diversity relationship is needed in order to determine if patterns are consistent with theory and to fully test mechanisms hypothesized to cause them. In order to examine the effect of productivity on species diversity across multiple spatial scale, it will be necessary to collect data from as many locations as possible.

Four levels of spatial scale (i.e., cluster, location, region, and geographic area) will be used to assess questions of productivity on patterns of diversity of macroinvertebrates in tree holes. Two geographic areas of interest are temperate (north of the Tropic of Cancer and south of the Tropic of Capricorn) and tropical (all remaining area). Geographic area will be further subdivided into 2 regions each, north and south. Locations will subdivide regions into multiple sites (? 2 per location). Finally, each location will contain a number of clusters (? 3), representing an aggregation of tree holes which are bounded by artificial barriers (e.g., agricultural lands) and exist within the same forest type. Objectives I believe that tree holes should display the same unimodal productivity-diversity relationship common for other systems. This relationship should change depending on the scale of observation. For instance, at small scales we may expect a tight relationship between diversity and productivity. As scale increases towards the regional level, the relationship may become more variable as other factors such as environmental variation impact the relationship. At larger spatial scales, the pattern may change to a linear relationship. A critical objective in all research is first to quantify patterns before investigating processes hypothesized to structure them. With this in mind, the collection of baseline data is essential to allow for the development of testable hypotheses. I plan to collect baseline data during the summer of 2000 from as many potential sites as possible before designing experiments to address hypotheses for subsequent years. My overall goals are to visit potential collecting locations and for each site to determine it?s accessibility, the abundance and diversity of useable tree holes, and to gather preliminary data on taxonomic and functional diversity of macroinvertebrates at each site.

Location(s), Described: Project Cancelled. Undetermined. This summer's work involves finding potential tree holes for future work. Tree holes would be located in hardwoods in secondary growth.
Location(s), Download GPS: Project Cancelled. None Generated.
Location(s), Online Maps: Project Cancelled. None Generated.
Methods/Experimental Design: Tree holes from sites will be sampled during summer 2000. At collection time, all individuals will be removed and identified to the lowest taxonomic level possible. These data will form the basis for future investigations. In addition to macroinvertebrates, a number of environmental readings will be taken for each tree hole so as to allow for and examination of the surrounding matrix and tree hole environment and how it potentially affects diversity. This will include: GPS coordinates, canopy openness, tree diameter, height, and species, distance to nearest tree hole, tree hole volume (area surrogate), hole opening, height, type (rot vs. pan forms), and opening direction. Where possible, detritus and fluid will be returned to each tree hole in order to decrease the potential impacts on future macroinvertebrate diversity. Macroinvertebrates collected from tree holes will be returned to the ISU campus for identification. Sampling apparatus will include plastic containers, strainers, funnels, and turkey basters (for fluid removal). No hazardous chemicals will be utilized.
Sampling Frequency: Once a year.
Data Columns: Project Cancelled.
N
oteThe tree species that are endemic to Coweeta LTER do not naturally develop the type of tree holes that were required for the proposed macroinvertebrate study, thus no data was collected, and the project was closed.

plot - permanent vegetation plot 
year - year sampled 
sample_No - 86 quadrats 
x location - x coordinate within 80 x 80 meter plot 
y location - y coordinate within 80 x 80 meter plot 
beun - Betula lenta/lutea seedlings within quadrat 
nysy - Nyssa sylvatica seedlings within quadrat 
fram - Fraxinus americana seedlings within quadrat 
tsca - Tsuga canadensis seedlings within quadrat 
litu -  Liriodendron tulipifera seedlings within quadrat 
rhma - Rhododendron maximum seedlings within quadrat 
visp - Vitis spp seedlings within quadrat 
acru - Acer rubrum seedlings within quadrat 
acpe - Acer pennsylvannicum seedlings within quadrat 
acsa -  Acer saccharum seedlings within quadrat 
casp - Carya spp. seedlings within quadrat 
quve - Quercus velutina seedlings within quadrat 
amun - Amalanchier canadensis/laevis seedlings within quadrat 
rops - Robinia pseudoacacia seedlings within quadrat 
quru -  Quercus rubra seedlings within quadrat 
havi - Hamamelis virginiana seedlings within quadrat 
saal - Sassafras albidum seedlings within quadrat 
qupr - Quercus prinus seedlings within quadrat 
mafr - Magnolia frasierii seedlings within quadrat
maac -  Magnolia acuminata seedlings within quadrat

Missing Data Codes:  None

Publications:

1. P.A. Abrams, Ecology 76, 2019 (1995).
2. M. L. Rosenzweig, Species Diversity in Space and Time (Cambridge Univ. Press,
Cambridge, 1995).
3. M. L. Rosenzweig, Science 171, 385 (1971).
4. S. A. Levin, Ecology 73, (1943).
5. R. J. Moore, P. Keddy, Vegetation 79, 99 (1989).
6. J. Oksanen, Ecology 84, 293 (1996).
7. E. Weiher, J. Ecology 87, 1005 (1999).
8. L. H. Fraser, P. Keddy, Trends in Ecology and Evolution 12, 478 (1997).
9. G. F.Gause, J. Exp. Bio. 12, 44 (1935).
10. Thomas Park, Ecological Monographs 18, 267 (1948).
11. C. B.Huffaker, Hilgardia 27, 343 (1958).
12. S. R.Carpenter, Ecology 77, 677 (1996).
13. B. Jenkins, R. L. Kitching, Australian Journal of Ecology 15, 199 (1990).
14. R. L. Kitching, C. Callaghan, Australian Ent. Magazine 8, 61 (1982).
15. D. S. Srivastava, J. H. Lawton, American Naturalist 152,
510 (1988).
16. D. H. Wright, Oikos 41: 496-506 (1983).

Data Restrictions: Users must adhere to the Coweeta LTER Data Policy.
Metadata: EML Format (XML Schema) | Information about EML
Data Downloads: Project Cancelled.  None generated.