Conservation and restoration of quaking aspen in the western United States requires an understanding of how and when aspen clones became established, how clones adapt to environmental challenges, and how individual clones interact within stands. I used molecular tools to identify individual clones in a natural population of aspen in southern Utah and detected high and low levels of clonal diversity within stands. Stands with high clonal diversity were located in areas with a more frequent fire history, indicating that fires may have prepared sites for seed germination and establishment over time. Conversely, areas of low clonal diversity corresponded to areas with less frequent fire. The same molecular tools were then used to investigate clonal interactions/succession over relatively recent time. For this portion of the study I sampled small, medium, and large aspen ramets (stems) at 25 subplots within spatially separated one-hectare plots, and mapped the clonal identities. I found that approximately 25% of the clones appeared to be spreading into adjacent clones, while 75% of the clones had a stationary pattern. In the final portion of the study, I again used molecular tools to identify aspen clones and investigated tradeoffs between growth and defense chemistry in mature, naturally-occurring trees. Growth was estimated using a ten-year basal area increment, and the percent dry weight of salicortin, tremulacin, and condensed tannins was measured in the same trees. Overall I discovered evidence for a tradeoff between growth and salicortin/tremulacin, and a marginally significant but positive relationship between growth and condensed tannins.

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Quaking aspen (Populus tremuloides) clones within close proximity to one another can exhibit drastically different levels of browsing by ungulates. The objectives of this study were to (1) determine interclonal differences in plant chemistry between adjacent clones exhibiting different degrees of herbivory which may influence the browsing behavior and patterns of ungulates, and (2) determine if correlation exists in the levels of salicortin and tremulacin between current year's suckers and current year's growth on older trees. This second objective was meant to indicate a protocol for land managers for identifying clones meriting increased protection from herbivory after treatment and wildfire. In July of 2005, 6 pairs of clones were identified on the Dixie National Forest, Utah, and on Cedar Mountain, east of Cedar City, Utah. Pairs consisted of 2 clones within the same pasture and/or grazing allotment and within a minimal distance from one another; one clone displaying moderate to high levels of ungulate utilization of aspen suckers, and one exhibiting minimal to no ungulate utilization of aspen suckers. Soil samples were taken at each clone and leaf tissues were sampled to determine genet. Aspen suckers were sampled for nutrient content, combined phenolic glycoside concentration (salicortin and tremulacin), condensed tannins, and the presence of extra floral nectaries (EFNs), at intervals throughout the growing season (August 3-6, August 31-September 2, and October 12-14). Current year's growth from representative mature trees was sampled for phenolic glycoside concentration at these times as well. All tests demonstrated high levels of insignificance for both leaves and stems.Sucker nitrogen values may have been elevated during portions of the sampling year in clones displaying moderate to high levels of ungulate utilization, possibility indicating an ungulate preference for nitrogen, but due to missing values, this is far from conclusive. P-values for forest floor factors were also highly non-significant with the exception of forest floor C (0.04) in the regenerating clones. Two post-project hypotheses are postulated in an attempt to explain the differences of forest floor carbon in terms of factors that may be influencing ungulate herbivory.

This thesis includes two studies: The first examined developmental changes that take place in the physiology of aspen (Populus tremuloides Michx.) and to characterize developmental influences on patterns of phenotypic trait variation among different aged ramets within the aspen clones. We surveyed eight clones, each with 8 distinct age classes ranging from 1 to 170 yrs in age. Using regression analysis we examined the relationships between ramet age and expression of functional phenotypes. Eight of the phenotypic traits demonstrated a non-linear relationship in which large changes in phenotype occurred in the early stages of ramet development and stabilized thereafter. Water and nutrient concentration, leaf gas exchange and phenolic glycosides tended to decrease from early to late development, while sucrose and condensed tannin concentrations and water use efficiency increased with ramet age. We hypothesize that ontogenetically derived phenotypic variation leads to fitness differentials among different aged ramets, which may have important implications for clone fitness. Age-related increases in phenotypic diversity may partially underlie aspen's ability as a species to tolerate the large environmental gradients that span its broad geographical range. Fire is an essential component of many forest ecosystems and fire exclusion policies and other anthropogenic factors have significantly altered disturbance regimes, which has lead to increased aspen succession to conifers. The second study examined how post-fire aspen regeneration success is influenced by increasing conifer abundance under longer fire return intervals. 66 sites were selected from the Sanford prescribed fire complex located in the Dixie National Forest. Slope, aspect, sucker regeneration heights, soil samples, and post and prefire stand densities were measured. Results from this study demonstrated that pre-disturbance conifer abundance and aspen densities are good predictors of aspen sucker regeneration success. Results also found that although conifer densities don't change across aspects, aspen densities are different on north facing slopes. We hypothesize the high levels of aspen regeneration came from a large disturbance size which overwhelmed the high levels of herbivores.