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Thesis (Ph.D.) -- University of Adelaide, Dept. of Botany, 1999. / Bibliography: p. 191-200.

Individuals of Eriogonum abertianum Torr. (Polygonaceae) flower in spring, or following onset of summer rains, or both. Within populations flowering time is mainly environmentally determined: there is little genetic variance for flowering time, and experimental moisture limitation significantly delays flowering. In the field a Sonoran Desert population experienced significantly more mortality during the foresummer droughts, and had a significantly greater proportion of spring-flowering plants, than a Chihuahuan Desert population. Greenhouse experiments suggest a genetic basis for differences in size and time of flowering between these populations. Fossil and biogeographic evidence support an adaptive interpretation of earlier flowering in the Sonoran Desert. A model of selection comparing spring-plus-summer flowering with spring-only flowering suggests that expected summer fecundity may not offset the risk of foresummer mortality in the Sonoran population. Rather than switching to a spring-only habit as predicted by the model, the species' range ends where summer rainfall declines abruptly. The invariance of the spring-plus-summer habit is not explained by the demographic, historical, or genetic data. Plants which live for more than a year in the wild have offspring which, in the greenhouse, live longer than the offspring of the general population. This suggests a genetic basis for the occasional observed perennation. Analysis of a quantitative genetic model suggests that when adult survivorship is low, selection will generally reduce perennation. The annual habit is thus likely to persist even in the presence of genetic variation for perennation. Optimal control models of plant carbon allocation are extended to include within-season mortality and allometric growth constraints. When parameters are varied in numerical experiments, resulting predictions for easily measurable characters (e.g., time to first flower) often vary only slightly; most differences are in fitness, suggesting that satisfactory empirical tests may be difficult to conduct. Arbitrary mortality functions can optimally lead to multiple flowering episodes, and this can depend sensitively on parameter values. Optimal trajectories with allometric constraints are divided into a period of vegetative growth and another period of mixed growth.

Removal experiments were conducted to determine particular spatial and temporal conditions that can influence competitive interactions in several desert winter annual species. During the 1987-88 season, variation in the magnitude of competition at three habitats along a topographic gradient was demonstrated in two co-occurring species of winter annuals, Plantago patagonica and Pectocarya recurvata. Density effects on the survival and reproductive success of either species were weakest at the slope. However, the habitats where the two species experienced the most intense competition differed. Plantago was most affected by competition at the wash while Pectocarya was most affected at the base of the hill. The most striking pattern observed was that, for both species, the habitat with the highest reproductive success for plants that were not experiencing competition tended to be the worst habitat for plants in competition. A comparison of results from two experiments performed on Plantago patagonica during two growing seasons showed that competition occurred despite large seasonal differences in weather and plant performance. When wet and dry conditions of different year types were simulated by artificial irrigation during a dry season, competition was still detected in both rainfed and irrigated plants regardless of the marked differences in plant size as a result of the irrigation treatment. A neighborhood density roughly equivalent to 8 plants/dm² appeared sufficient to create competitive conditions for Plantago. Effects of competition were consistently manifested in reduced plant growth and fecundity. There was no evidence for density-dependent seedling mortality (self-thinning) even with seedling densities as high as 48 plants/dm². In two pairs of species tested, Plantago patagonica-Schismus barbatus and Plantago patagonica-Pectorcarya recurvata, there was no statistically detectable effect of neighbor species identity on target plants of Plantago and Pectocarya suggesting the possible equivalence of competitive effects in these species of desert winter annuals.

Diss. (sammanfattning) Uppsala : Sveriges lantbruksuniv., 2003. / Härtill 4 uppsatser.

Thesis (Ph. D.)--University of Washington, 1986. / Vita. Bibliography: leaves [174]-187.

This study lends strong support to the idea that members of Bromeliaceae have undergone a recent adaptive radiation, and therefore show that, at least in part, diversity in the tropics is due to a fast speciation rate and that the tropics can be a "cradle" for new diversification and exploitation of varying ecological niches through the diversification of ecophysiological traits within a lineage.

Chan Yee-kwan. / Thesis (M.Phil.)--Chinese University of Hong Kong, 2000. / Includes bibliographical references (leaves 108-131). / Abstracts in English and Chinese. / Thesis Committee --- p.i / Abstract --- p.ii / Acknowledgments --- p.v / General Abbreviations --- p.vii / Abbreviation for Chemicals --- p.x / Table of Contents --- p.xi / List of Figures --- p.xiv / List of Tables --- p.xv / Chapter 1. --- Literature Review / Chapter 1.1 --- Salinity as a global problem --- p.1 / Chapter 1.2 --- Salinity and agriculture --- p.2 / Chapter 1.3 --- Plant adaptation to salinity --- p.4 / Chapter 1.3.1 --- Salt secretion --- p.6 / Chapter 1.3.2 --- Ion transport --- p.8 / Chapter 1.3.2.1 --- Role of H+-ATPase in salt tolerance --- p.8 / Chapter 1.3.2.2 --- Potassium and sodium uptake --- p.13 / Chapter 1.3.2.3 --- Sodium efflux --- p.15 / Chapter 1.3.3 --- Osmotic adjustment --- p.20 / Chapter 1.3.3.1 --- Accumulation of mannitol --- p.21 / Chapter 1.3.3.2 --- Accumulation of proline --- p.23 / Chapter 1.3.3.3 --- Accumulation of glycinebetaine --- p.23 / Chapter 2. --- Materials and Methods / Chapter 2.1 --- Plant materials and growth conditions --- p.26 / Chapter 2.1.1 --- Surface sterilization of Arabidopsis seeds --- p.26 / Chapter 2.1.2 --- Determination of sub-lethal inhibitory doses of sodium --- p.27 / Chapter 2.1.3 --- Growth conditions of Arabidopsis seeds for total RNA extraction --- p.27 / Chapter 2.1.4 --- NaCl dosage tests --- p.28 / Chapter 2.1.5 --- Expression kinetic tests --- p.28 / Chapter 2.2 --- Isolation of total RNAs --- p.28 / Chapter 2.3 --- Isolation of genes differentially expressed in NaCl concentration by RAP-PCR --- p.30 / Chapter 2.3.1 --- RNA fingerprinting by RAP-PCR --- p.30 / Chapter 2.3.2 --- PCR reamplificatin of RAP products --- p.31 / Chapter 2.3.3 --- Cloning of differentially expressed genes --- p.33 / Chapter 2.3.3.1 --- Ligation of inserts into pCR-Script vector and transformation --- p.33 / Chapter 2.3.3.2 --- Ligation of inserts into pBluescript II KS (+) T-vector and transformation --- p.36 / Chapter 2.3.3.3 --- Screening of recombinant plasmids --- p.37 / Chapter 2.4 --- Sequencing of differentially expressed genes --- p.39 / Chapter 2.4.1 --- DNA cycle sequencing --- p.39 / Chapter 2.5 --- Northern blot hybridization of NaCl inducible genes --- p.40 / Chapter 2.5.1 --- RNA fractionation by formaldehyde gel electrophoresis --- p.40 / Chapter 2.5.2 --- Northern blotting --- p.41 / Chapter 2.5.3 --- Preparation of single-stranded DIG-labeled PCR probes --- p.41 / Chapter 2.5.3.1 --- Isolation of Total RNA --- p.41 / Chapter 2.5.3.2 --- Primer design --- p.42 / Chapter 2.5.3.3 --- PCR amplification of single-stranded DIG PCR probes --- p.43 / Chapter 2.5.4 --- Hybridization --- p.45 / Chapter 2.5.5 --- Stringency washes --- p.46 / Chapter 2.5.6 --- Chemiluminescent detection --- p.46 / Chapter 3. --- Results / Chapter 3.1 --- Determination of sub-lethal inhibitory doses of sodium --- p.48 / Chapter 3.2 --- Isolation of total RNA from A. thaliana treated with sodium chloride --- p.48 / Chapter 3.3 --- Isolation of genes differentially expressed in sodium concentration by RNA arbitrarily primed polymerase chain reaction RAP-PCR --- p.52 / Chapter 3.3.1 --- Differential cDNA fragments identified by RAP-PCR --- p.52 / Chapter 3.3.2 --- PCR reamplification of RAP products --- p.52 / Chapter 3.3.3 --- Cloning of selected RAP-fragments --- p.62 / Chapter 3.4 --- Nucleotide sequence analysis of selected RAP PCR clones --- p.65 / Chapter 3.5 --- Expression pattern analysis of salt inducible genes by northern blot hybridization --- p.75 / Chapter 3.5.1 --- Preparation of single-stranded digoxigenin (DIG)-labeled probes --- p.75 / Chapter 3.5.2 --- Dosage response of NaCl inducible genes --- p.79 / Chapter 3.5.3 --- Expression kinetics of NaCl inducible genes --- p.80 / Chapter 4. --- Discussion / Chapter 4.1 --- Isolation of RAP-PCR targets --- p.93 / Chapter 4.2 --- Expression of NaCl inducible P450 genes --- p.94 / Chapter 4.2.1 --- Cytochrome P450 CYP73A5 --- p.97 / Chapter 4.2.2 --- Cytochrome P450 CYP83A1 --- p.98 / Chapter 4.3 --- NaCl induction gene related to post-transcriptional activities --- p.99 / Chapter 4.3.1 --- Glycine-rich RNA binding protein (BAC F3F19) --- p.100 / Chapter 4.3.2 --- Chloroplast signal recognition particle (54CP) --- p.103 / Chapter 4.4 --- Conclusion --- p.106 / References --- p.108

Shale barrens are unique habitats located throughout the southern Appalachians. They are characterized by a south or south west aspect, a steep slope, and an exposed rocky surface (Platt, 1951). They have a high total irradiance and can experience temperatures higher than the surrounding deciduous forest. A variety of plant species, several of which are rare or endangered, are endemic to the shale barren habitat. One reason proposed fc)r their endemism is that the plants are obligate heliophytes (Keener, 1983). The purpose of this dissertation is tel examine the acclimation ability of the shale barren endemic Eriogonum alIeni to shade and high temperature. / Ph. D.

[Truncated abstract] In the most common (hydrological) viewpoint, vegetation is a