Thesis (Ph.D.) - University of Queensland, 2003. / Includes bibliography.

Yeung, Chung Wing. / Thesis (M.Phil.)--Chinese University of Hong Kong, 2010. / Includes bibliographical references (leaves 143-156). / Abstracts in English and Chinese. / Acknowledgements --- p.i / Abstract (English) --- p.iii / Abstract (Chinese) --- p.vi / Contents --- p.vii / List of Tables --- p.xii / List of Figures --- p.xii / Chapter Chapter 1 --- Introduction / Chapter 1.1 --- Ecological and economic importance of coral reef habitats --- p.1 / Chapter 1.2 --- D egradation of coral reefs --- p.2 / Chapter 1.2.1 --- Natural recovery --- p.3 / Chapter 1.2.2 --- Restoration of disturbed reefs --- p.3 / Chapter 1.2.2.1 --- Whole colony transplantation --- p.4 / Chapter 1.2.2.2 --- Fragment transplantation --- p.4 / Chapter 1.2.2.3 --- Coral nursery --- p.5 / Chapter 1.3 --- Studies on octocorals --- p.6 / Chapter 1.3.1 --- Functional ecology of octocorals --- p.7 / Chapter 1.3.2 --- Biodiversity of octocorals in Hong Kong --- p.9 / Chapter 1.3.3 --- Threats on octocorals in Hong Kong --- p.10 / Chapter 1.4 --- The focus and significance of the present study --- p.12 / Chapter 1.4.1 --- "Lobophytum sarcophytoides, the study organism" --- p.14 / Chapter 1.4.2 --- Objectives --- p.15 / Chapter 1.5 --- Thesis Outline --- p.16 / Chapter Chapter 2 --- Seasonal Variation and Size-dependent Eco-physiological Performances of the Soft Coral Lobophytum sarcophytoides / Chapter 2.1 --- Introduction --- p.19 / Chapter 2.1.1 --- Damage recovery --- p.20 / Chapter 2.1.2 --- Photosynthetic activity --- p.21 / Chapter 2.1.3 --- Reproductive biology --- p.22 / Chapter 2.1.4 --- Growth rate --- p.23 / Chapter 2.1.5 --- Significance and objectives --- p.23 / Chapter 2.2 --- Study Sites --- p.24 / Chapter 2.2.1 --- Lan Guo Shui (LGS) --- p.24 / Chapter 2.2.2 --- Tolo Harbour (MSL) --- p.25 / Chapter 2.3 --- Methodologies --- p.27 / Chapter 2.3.1 --- Sample collection --- p.27 / Chapter 2.3.2 --- Treatment of samples --- p.27 / Chapter 2.3.3 --- Health condition --- p.28 / Chapter 2.3.4 --- Damage recovery --- p.29 / Chapter 2.3.5 --- Growth rate --- p.29 / Chapter 2.3.6 --- Photosynthetic activity --- p.30 / Chapter 2.3.7 --- Reproductive biology --- p.30 / Chapter 2.3.8 --- Statistical Analysis --- p.31 / Chapter 2.4 --- Results --- p.32 / Chapter 2.4.1 --- Acclimation of transplanted corals --- p.32 / Chapter 2.4.2 --- Health condition --- p.33 / Chapter 2.4.3 --- Growth rate --- p.34 / Chapter 2.4.4 --- Photosynthetic activity --- p.38 / Chapter 2.4.5 --- Damage recovery --- p.39 / Chapter 2.4.6 --- Reproductive biology --- p.40 / Chapter 2.5 --- Discussion --- p.41 / Chapter 2.5.1 --- Diurnal expansion and contraction of colonies --- p.41 / Chapter 2.5.2 --- Size fluctuation of the colonies --- p.42 / Chapter 2.5.3 --- Possible factors for the high initial mortality of corals --- p.43 / Chapter 2.5.4 --- Causes of bleaching and the harmful effects --- p.44 / Chapter 2.5.5 --- Energy allocation between reproduction and growth --- p.47 / Chapter 2.5.6 --- Quick healing of cut fragments and its ecological implication --- p.48 / Chapter 2.5.7 --- Choice of suitable fragment size for nursery use --- p.49 / Chapter 2.5.8 --- Suitable season for conducting the experiment --- p.50 / Chapter 2.6 --- Summary --- p.51 / Chapter Chapter 3 --- Effects of Temperature on the Health Condition and Photosytnthetic Activity of the Soft Coral Lobophytum sarcophytoides / Chapter 3.1 --- Introduction --- p.69 / Chapter 3.2 --- Methodologies --- p.73 / Chapter 3.2.1 --- Sample collection --- p.73 / Chapter 3.2.2 --- Experimental set-up of aquaria for growing corals --- p.73 / Chapter 3.2.2.1 --- Temperature experiment I --- p.74 / Chapter 3.2.2.2 --- Temperature experiment II --- p.74 / Chapter 3.2.2.3 --- Temperature experiment III --- p.76 / Chapter 3.2.3 --- Health condition --- p.76 / Chapter 3.2.4 --- Photosynthetic activity --- p.77 / Chapter 3.2.5 --- Statistical analysis --- p.78 / Chapter 3.3 --- Results --- p.79 / Chapter 3.3.1 --- Temperature experiment I --- p.79 / Chapter 3.3.1.1 --- Health condition --- p.79 / Chapter 3.3.1.2 --- Photosynthetic activity --- p.80 / Chapter 3.3.2 --- Temperature experiment IIA --- p.81 / Chapter 3.3.2.1 --- Health condition --- p.81 / Chapter 3.3.2.2 --- Photosynthetic activity --- p.83 / Chapter 3.3.3 --- Temperature experiment IIB --- p.84 / Chapter 3.3.3.1 --- Health condition --- p.84 / Chapter 3.3.3.2 --- Photosynthetic activity --- p.85 / Chapter 3.3.4 --- Temperature experiment III --- p.85 / Chapter 3.3.4.1 --- Health condition --- p.85 / Chapter 3.3.4.2 --- Photosynthetic activity --- p.86 / Chapter 3.4 --- Discussion --- p.87 / Chapter 3.4.1 --- The effect of acclimation --- p.87 / Chapter 3.4.2 --- Temperature tolerance range of L. sarcophytoides --- p.90 / Chapter 3.4.3 --- Indicators of coral health --- p.92 / Chapter 3.4.3.1 --- Photosynthetic activity --- p.92 / Chapter 3.4.3.2 --- Colony contraction --- p.94 / Chapter 3.4.3.3 --- Bleaching --- p.95 / Chapter 3.4.3.4 --- Algal overgrowth --- p.97 / Chapter 3.4.3.5 --- Attachment of transplanted corals --- p.99 / Chapter 3.5 --- Summary --- p.100 / Chapter Chapter 4 --- Reproductive Biology of Lobophytum sarcophytoides / Chapter 4.1 --- Introduction --- p.114 / Chapter 4.2 --- Methodologies --- p.117 / Chapter 4.2.1 --- Study site --- p.117 / Chapter 4.2.2 --- Sample collection and treatments --- p.117 / Chapter 4.3 --- Results --- p.119 / Chapter 4.3.1 --- Gametogenic development: Size changes --- p.119 / Chapter 4.3.2 --- Gametogenic development: Developmental stages --- p.120 / Chapter 4.3.2.1 --- Oogenesis --- p.120 / Chapter 4.3.2.2 --- Spermatogenesis --- p.121 / Chapter 4.4 --- Discussion --- p.122 / Chapter 4.4.1 --- Unusual oogenic development pattern in L sarcophytoides --- p.122 / Chapter 4.4.2 --- Possible effect of lack of a temperature cue on gametogenic development --- p.123 / Chapter 4.4.3 --- Alternative explanation: Energy allocation --- p.126 / Chapter 4.5 --- Summary --- p.128 / Chapter Chapter 5 --- Summary and Perspectives --- p.137 / References --- p.143

Thesis (Ph. D.)--University of Texas at Austin, 2001. / Vita. Includes bibliographical references (leaves 173-201). Available also in a digital version from Dissertation Abstracts.

Mesophotic reefs represent biodiverse ecosystems that may act as a refuge for depth-generalist coral species threatened in shallow habitats. Despite the importance of coral-algal symbioses, few studies focus on mesophotic zooxanthellae assemblages and their influence on connectivity. This study compared zooxanthellae in Montastraea cavernosa at shallow and mesophotic depths at Flower Garden Banks National Marine Sanctuary and McGrail Bank. Mesophotic corals contained more zooxanthellae and more chlorophyll a and c2 per unit area coral. Increased zooxanthellae within mesophotic corals may represent an adaptive strategy to optimize light capture in low-light environments. Genetic profiles for zooxanthellae assemblages from shallow and mesophotic corals showed similar diversity across banks and between depths. The dominant sequence making up assemblages was identified as Symbiodinium type C1. Similar assemblage diversity suggests that zooxanthellae assemblages will not limit connectivity potential between shallow and mesophotic corals at these reefs. / Includes bibliography. / Thesis (M.S.)--Florida Atlantic University, 2016. / FAU Electronic Theses and Dissertations Collection

Nitrogen (N) has traditionally been regarded as the primary limiting nutrient to algal growth in marine coastal waters, but recent studies suggest that phosphorus (P) can be limiting in carbonate-rich environments. To better understand the importance of P. alkaline phosphatase activity (APA) was measured in reef macroalgae in seven counties of south Florida ; several significant trends emerged : 1) APA decreased geographically from the highest values in Dada>Monroe>Palm Beach>St. Lucie>Broward>Martin>Lee counties 2) APA varied temporally with increasing nutrient-rich runoff in the wet season 3) APA varied due to taxonomic division Phaeophyta>Rhodophyta>Chlorophyta 4) Nutrient enrichment experiments demonstrated that increased N-enrichment enhanced P-limitation while increased P decreased P-limitation. These results suggest that high APA observed in carbonate-rich waters of Dade County and low APA in Broward County resulted from high nutrient inputs associated with anthropogenic nutrient pollution. / by Courtney Kehler. / Thesis (M.S.)--Florida Atlantic University, 2012. / Includes bibliography. / Mode of access: World Wide Web. / System requirements: Adobe Reader.

The unique coral reef at St. Lucie Reef (Stuart, FL) persists despite environmental variability from extensive freshwater discharges, summer upwelling, and thermal instability. By examining the symbiotic zooxanthellae, or Symbiodinium, that reside in corals, we can gain insight to coral physiology impacted by local stressors. Two scleractinian corals, Montastraea cavernosa and Pseudodiploria clivosa were sampled over 1.5 years, including both wet and dry seasons. Zooxanthellae were isolated and quantitatively characterized using standard measurements and molecular techniques. Both coral species varied in zooxanthellae biomass, where Pseudodiploria clivosa had Higher cell densities and chlorophyll concentrations than Montastraea cavernosa. Over time, these parameters varied, but were not significantly altered by fresh water discharge events. Symbiodinium diversity and abundance were identified by ITS2 region amplification and next-generation sequencing .Novel associations between Symbiodinium and each coral explained the observed physiological differences. The symbioses remained stable throughout and could indicate local adaptation for St. Lucie Reef corals. / Includes bibliography. / Thesis (M.S.)--Florida Atlantic University, 2014. / FAU Electronic Theses and Dissertations Collection

Corals, the foundation species of tropical reefs, are in rapid global decline as a result of anthropogenic disturbance. On many reefs, losses of coral have coincided with the over-harvesting of reef herbivores, resulting in ecosystem phase-shifts from coral to macroalgal dominance. It is hypothesized that abundant macroalgae inhibit coral recovery and recruitment, thereby generating ecological feedback processes that reinforce phase-shifts to macroalgae and further diminish reef function. Notwithstanding, the extent to which macroalgae directly outcompete coral, the mechanisms involved, and the species-specificity of algal-coral competition remains debated. Moreover the capacity for herbivores to prevent vs. reverse ecosystem phase-shifts to macroalgae and the roles of herbivore diversity in such phenomena remain poorly understood. Here I demonstrate with a series of field experiments in the tropical Pacific and Caribbean Sea that multiple macroalgae common to degraded reefs directly outcompete coral using chemical warfare, that these interactions are mediated by hydrophobic secondary metabolites transferred from algal to coral surfaces by direct contact, and that the outcomes of these allelopathic interactions are highly species-specific. Using field observations and experiments in the tropical Pacific, I also demonstrate that the process of herbivory attenuates the competitive effects of allelopathic algae on corals by controlling succession of algal communities, and that the herbivore species responsible for macroalgal removal possess complementary tolerances to the diversity of chemical defenses deployed among algae, creating an essential role for herbivore diversity in reversing ecosystem phase-shifts to macroalgae. Lastly, I demonstrate with field experiments in the tropical Pacific that algal-coral competition simultaneously induces allelochemicals and suppresses anti-herbivore deterrents in some algae, likely due to trade-offs in the productions of defense metabolites with differing ecological functions. Together, these studies provide strong evidence that chemically mediated competitive and consumer-prey interactions play principal roles in coral reef degradation and recovery, and should provide resource managers with vital information needed for effective management of these ecologically and economically important but threatened ecosystems.

Herbivory is a key process that mediates the abundance of primary producers and community composition in both terrestrial and aquatic ecosystems. On tropical coral reefs, changes in herbivory are often related to phase shifts between coral-dominance and dominance by seaweeds, or foliose macroalgae. Resilience or capacity to resist and reverse such phase shifts is, therefore, viewed as a critical function on coral reefs. This thesis used grazer exclusion and assay experiments at six sites within three different fisheries management regimes in Kenya to identify the impacts of herbivores (sea urchins and fishes) on algal dynamics in the context of coral reef resilience. First, I examined the grazing rates necessary to prevent phase shifts by quantifying consumption and algal production. Here, I found that, over a 390-day experiment, at least 50 percent of algal production must be consumed to avoid accumulation of algal biomass. Using video observations, I also showed that scraping parrotfishes remove more algae (per unit of fish biomass) than previously assumed, and that sea urchins, if released from predation, have similar impacts to fishes. Then I focused on algal succession, and found that sea urchins and fishes have different effects that are mediated by their abundances and species composition. Where sea urchins were less abundant and parrotfishes absent (e.g. young fisheries closures), progression of algae from turfs to early and then late successional macroalgae occurred rapidly and within 100 days. I then turned my focus to the removal of already established macroalgae (grown for > 1 yr in the absence of herbivores) and showed that sea urchins and browsing fishes were able to remove significant amounts of macroalgae where either herbivore was abundant. However, using multiple-choice selectivity assays and in situ video recordings, I found that browsing fishes fed very selectively with low overlap in diet among species, leading to low functional redundancy within a high diversity system. Finally, using long-term survey data (from 28 sites) to build a 43-year chronosequence, I showed that it is possible that the effects of herbivory will not be constant across transitions from open fishing to fishery closures through non-linear grazing intensity. Therefore, increases in herbivory within fisheries closures may not be immediate and may allow a window of opportunity for algae to go from turf to unpalatable macroalgae until scraping and browsing fishes fully recover from fishing (~ 20 years). The findings in this thesis are novel and raise concern over the potential implications of the slow recovery of parrotfishes or, given lower than expected functional redundancy in grazing effects, the absence of even one browsing fish species in fisheries closures. Overall, this thesis highlights the importance of herbivore community dynamics in mediating interactions among algae, and provides new insights for conservation and management actions that attempt to bolster the resilience of coral reefs.