Field-based mesocosm studies may be used as conceptual experiments to examine theoretical questions using the generated empirical data. A field-based Drosophilidae-nectarine mesocosm, comprising sun and shaded microclimate treatments arranged in a checkerboard design, was used in this thesis to examine four theoretical objectives. First, the efficacy of spatial analysis for detecting empirical pattern was examined. Natural variation weakened spatial structuring. However, hypothesis generation was shown not to be affected by this inclusion. Second, enhancing the hypothesis generating capacity of spatial methods was assessed, and confirmed to be possible, through the use of a sensitivity analysis method developed here. The method ( distinguished between mechanism categories (intrinsic, extrinsic and natural variation) and assessed the relative strength of each category. Next, an empirical test of the He and Gaston (2000a) parameterisation method and model to predict abundance from occupancy was conducted. Abundance estimates derived using the parameterisation method were underestimated because individuals were highly aggregated within fruit. This model and method require further exploration at fine scales for highly aggregated species. The incorporation of spatially explicit information may improve abundance predictions. Finally, the influence of spatial variation in temperature on adult body size in Drosophila simulans Sturtevant was investigated. The simple developmental effects of temperature differences, or the simple effects of stressful temperatures on thorax length, were overridden by interactive effects between temperature and larval density. As a result, flies attained the same final sizes in the shade and sun. Under natural conditions both mortality and non-lethal effects of temperature and/or crowding are likely to playa role in the evolution of body size. The results of this thesis provide i) an improved understanding of the influence of natural variation on spatial pattern, ii) an additional tool for spatial hypothesis generation, iii) an empirical test of an abundance-prediction model and iv) an understanding of interactive and non-lethal effects on body size under field conditions. The thesis therefore provides empirical support for the usefulness of field-based mesocosms to examine theoretical objectives. / Thesis (PhD (Entomology))--University of Pretoria, 2007. / Zoology and Entomology / unrestricted

Amphibians are influenced by climate change, but we do not have a clear understanding of how changes in temperature, precipitation, or both, may influence amphibian larvae in temperate regions. Do amphibian larvae have similar developmental responses to increased temperature and increased drying rates of wetlands - both plausible effects of climate change? What influence do the interactive effects of temperature and drying have on the relationships between the larval responses themselves (e.g., survival, body size, and time to metamorphosis)? To address these questions, we studied larval responses of two amphibian species, wood frogs (<em>Lithobates sylvaticus</em>) and spring peepers (<em>Pseudacris crucifer</em>), to simulated warming and drying in experimental ponds. Over 13 weeks, we manipulated temperature and water levels in ponds to produce 4 treatments: control, drying, warming, and drying + warming. Our manipulations created warming treatments that were on average 2 ° C higher than controls, and our drying treatments decreased in water depth by 2.5 cm each week compared to warming and control treatments that held a consistent amount of water. In both species, warming treatments resulted in significantly earlier timing of metamorphosis, and drying treatments resulted in significantly reduced body size. We saw a negative relationship between body size and time to metamorphosis (i.e., individuals that metamorphosed faster generally had larger body sizes), indicating an unexpected decoupling of the typical positive relationship between time to- and size at metamorphosis. The strength of the relationship between responses also varied by treatment for wood frogs but not spring peepers, indicating that the responses of larval amphibians to climate change may vary among species. Our study reveals complex relationships among larval survival, body size, and time to metamorphosis and highlights the need for considering not only the role of interacting climate-related pressures on amphibians but also the mechanisms underlying coupling of larval responses to these pressures. We encourage future research and discussion on a better understanding of why different climate pressures caused different responses, and if these patterns may be consistent in other aquatic species. / Master of Science / Across the globe, shifts in temperatures and the availability of freshwater habitats due to climate change are presenting challenges as well as opportunities for many species, particularly those that rely on freshwater habitats to complete their life cycle. Climate change is leading to warmer water temperature and accelerated drying of wetlands and ponds. Warming and drying often occur simultaneously, yet our understanding of how warming and drying may interact and affect sensitive aquatic species is limited. Amphibians with an aquatic life stage (for example, frog tadpoles) are particularly vulnerable to the effects of climate change on wetlands and ponds because they must transform from swimming larvae to land-dwelling adults before aquatic habitats dry out. Warming and drying help amphibian larvae determine when to start that process, called metamorphosis. For this reason, amphibian larvae in aquatic habitats are especially vulnerable to shifts in water temperature and the timing of drying. In this thesis, I explore how warming and drying influence amphibian survival, body size, and time to metamorphosis. To better understand the responses of amphibian larvae to warming and drying, I tested the effects of warming and drying on three response variables: amphibian survival, body size, and time to metamorphosis. I used two different species, wood frogs and spring peepers, to determine whether frogs' responses vary among species. I created an artificial pond experiment where I filled large tanks to represent natural ponds in a controlled, outdoor setting. In these artificial ponds, I measured wood frog and spring peeper growth under experimentally increased water temperatures and accelerated drying levels over 13 weeks. I found a negative relationship between body size and time to metamorphosis, suggesting individuals who spent less time in the water as larvae were more likely to be larger than individuals who spent more time in the water as larvae. Additionally, ponds with higher larval survival were associated with larger body size and a shorter time to metamorphosis. Warmer water temperatures led to a shortened time to metamorphosis but did not always lead to higher body sizes. Accelerated drying did not lead to a shortened time to metamorphosis, but it did lead to smaller body sizes in both species compared to control and warming ponds. Overall, I found complex relationships among larval responses with the directions of responses varying between treatments and species. This highlights the need for considering the role of climate-related changes in the environment (warming and drying) as well as the interactions between specific larval responses to those environmental changes. By understanding how warming and drying influence amphibian larval success, we can make a more direct link between climate change and its effects on aquatic larvae. Incorporating the responses between survival, body size, and time to metamorphosis to gain a more complete understanding of amphibian larval responses to the changing climate is an important step toward conserving and protecting freshwater aquatic species.

Evidence of feminising effects, including additional or enlarged female organs, have been reported in the (sub)-tropical freshwater prosobranch Marisa cornuarietis exposed to vertebrate estrogen receptor agonists. The primary symptom is an increase in the number of eggs laid, but this is only observed when exposure occurs at relatively low temperatures. This research project exposed temperate freshwater prosobranchs and a pulmonate to 17β-oestradiol (10-200 ngL-l, nominal) in an outdoor mesocosm subject to natural seasons to determine whether similar effects occur in European native temperate freshwater gastropods. Laboratory exposures to 17β-oestradiol (1-100 ngL-l, nominal) and Bisphenol-A (0.2-20 ngL-l, nominal) were also carried out over a range of different temperatures and photoperiods to simulate natural seasons. In the mesocosm exposures, significant increases in reproduction were measured in Viviparus viviparus, Bithynia tentaculata and, if the mortality rate was not significantly increased, Planorbarius corneus. It was observed that increases only occurred after the onset of autumn. In the laboratory, the oviposition rate in P. corneus was constant at 20oC with a 16h photoperiod, but declined significantly at 15oC with a 12h photoperiod, except at 100 ngL-l 17β-oestradiol, when the rate remained constant. There were no similar effects from Bisphenol-A exposure. Small increases in reproduction were observed in all the prosobranch exposures to both compounds, but the interpretation of the data was confounded by several factors (test chemical degradation, high mortality rates and parasitized organisms) and there were no significant differences. In conclusion, there were indications that all of the assessed species were capable of increased reproduction, and in P. corneus this appears to be a perpetuation of summer oviposition rates in autumnal conditions. The consequences of this effect in annual semelparous pulmonates may not be detrimental at the population level, but the long-term fitness of iteroparous prosobranchs that practice ‘restrained reproduction’ in early breeding seasons may be adversely affected.

The degradation of soil quality due to anthropogenic causes is globally important, both in terms of ecosystem services and ecological biodiversity. Soil quality reduction is stated to be detrimental for population densities and species diversity of soil invertebrates, including the mesofauna (Acari and Collembola). Within the soil food web, mesofauna occupy several trophic levels and as such facilitate nutrient turnover, fulfilling vital ecosystem functions and services. Understanding soil invertebrate population dynamics not only during degradation, but equally upon ecosystem restoration, is vital to identify possible losses or benefits to healthy ecosystem functioning. Prior to this investigation the Highfield site, Rothamsted Research, had been divided and maintained as grassland, arable cropping or bare fallow for 50 years. The latter resulted in a soil that had low soil organic matter levels, poor structure, low bacterial biomass and virtually no invertebrate population. Investigations into the invertebrate population changes, within both the experimental plots and surrounding land, upon alteration of the existing management strategies was completed over a two year period. Changes to mesofaunal populations were detected across all treatments following conversion. Generally, new fallow and arable management strategies produced low density fluctuating populations affected by the physical disturbance of ploughing and lack of soil organic matter as a basal food resource. Grassland management produced increased species diversity and abundance within a more stable soil food web. Each of the new management strategies developed towards its equivalent management strategy within the control treatments. Although it was apparent that the mesofaunal populations were re-establishing under more favourable environmental conditions, there was no definitive conclusion as to the source of the population increases. An attempt to identify the physical mode of invertebrate movement was completed, utilising a prototype mesocosm to act as a physical barrier, this showed promise for future use in such studies.

The tidal-fresh James River experiences recurring blooms of toxin-producing cyanobacteria, including Microcystis aeruginosa. However, cyanobacteria cell densities in the James are relatively low. Our purpose was to identify key factors suppressing cyanobacteria growth in the face of eutrophication. A mesocosm experiment was designed to test the effects of light, mixing and grazing on cyanobacteria abundance, with nutrients held constant. We predicted that toxic cyanobacteria would be most abundant under stagnant conditions, with enhanced light, with no bivalve grazers present. Abundances of indicator gene copies and phytoplankton counts supported this hypothesis. However, chlorophyll-a, phycocyanin, and the toxin microcystin were all found to be most abundant under mixed conditions with ambient light. Statistically, light and mixing were important in controlling toxic cyanobacteria abundance, with little to no effect observed for bivalve grazers. Our findings suggest that toxin production may be regulated by factors independent from those driving algal growth and cyanobacteria abundance.

A intervenção das atividades antrópicas ao meio ambiente tem repercutido na estrutura e funções dos ecossistemas, sendo que o uso de aditivos químicos, como agrotóxicos e fertilizantes, destacam-se pela parcela de responsabilidade que assumem diante desses desequilíbrios. O agrotóxico Vertimec® 18CE, cuja toxicidade para diversas taxóns já é conhecida, é amplamente utilizado em lavouras agrícolas, e têm-se conhecimento a respeito das intensas práticas de manuseio, muitas vezes irregulares, o que pode fazer com que concentrações muito maiores do que as previstas atinjam o ambiente aquático. Um dos grupos que nos últimos anos vem se destacando pelo declínio crescente associado ao uso destes produtos são os anfíbios. Os anfíbios possuem papel central na cadeia alimentar, e muitos estudos relatam o desequilíbrio ecológico causado pelo declínio desse grupo em relação a adição de contaminantes, incluindo os agrotóxicos. No presente estudo foram desenvolvidos testes laboratoriais a fim de determinar o estágio dos girinos de Lithobates catesbeianus mais suscetível à intervenção do agrotóxico e à concentração capaz de causar mortalidade em 50% dos indivíduos (CL50, 96h). A partir desses resultados, experimentos in situ (mesocosmos) com girinos no estágio mais avançado (25 da tabela de Gosner) foram desenvolvidos com o intuito de comparar as diferenças de toxicidade do Vertimec® 18CE quando manipulado em campo e laboratório, e quais os efeitos causados por uma única aplicação do produto e por aplicações múltiplas. Os testes laboratoriais demonstraram que os girinos em estágios mais precoce (21G) foram mais sensíveis ao agrotóxico Vertimec® 18CE do que àqueles mais avançados (25G). O experimento em campo indicou que a CL50, 96h para L. catesbeianus (25G) foi muito mais agressiva quando próxima às condições naturais, causando a mortalidade de todos os indivíduos no mesmo estágio de desenvolvimento em um período inferior a 24 horas. Entretanto, a concentração inferior à CL50, 96h (0,002 ml de Vertimec.L-1) quando ministrada em campo, assim como no laboratório, não causou mortalidade, mas implicou em atraso no desenvolvimento e maior período larval do que àqueles organismos que não estiveram em contato com o agrotóxico, já que atingiu os recursos disponíveis, promovendo um efeito indireto no sucesso dessa espécie. Não foi possível observar diferença entre as aplicações única e múltipla do Vertimec® 18CE, em decorrência da morte dos girinos do tratamento em dosagem múltipla, porém observou-se desequilíbrio das condições limnológicas do sistema ao sofrer nova intervenção do Vertimec® 18CE. Diante dos resultados obtidos é possível concluir que o Vertimec® 18CE é capaz de afetar diretamente (mortalidade, estágios de desenvolvimento e comportamento) e indiretamente (redução de recursos alimentares) a população de Lithobates catesbeianus, contribuindo para o declínio de anfíbios nos sistemas naturais. / The intervention of anthropogenic activities to the environment has reflected in the structure and functions of ecosystems and the use of chemical additives, such as pesticides and fertilizers, has contributed for the disequilibrium. The Vertimec® 18EC, whose toxicity is described to different taxa, is widely used in agricultural crops, and it has been known about the intense handling practices, often irregular, which can reach higher concentrations than those expected in the aquatic environment. One group that has been highlighted in recent years by the increasing decline associated with the use of these products is the amphibians. Amphibians plays a central role in the food chain and several studies have related the ecological disequilibrium caused by the decline of this group due to the addition of contaminants, including pesticides. In this study, laboratory bioassays were developed to determine the more susceptible stage and the LC50,96h of Lithobates catesbeianus to Vertimec® 18EC. From these results, in situ experiments (mesocosms) were conducted with tadpoles in more advanced stage (25 of Gosner table) in order to compare the differences in toxicity of Vertimec® 18EC when manipulated both in field and in laboratory. Also, the effects caused by a single and multiple application of the pesticides were evaluated. The laboratorial results showed that earlier stages (21G) were more sensitive than more developing tadpoles (25G), and the effects of the pesticide were more aggressive under natural conditions (mesocoms), with 100% of mortality before 24 hours, at the same developmental stage. The results of laboratorial and in situ bioassays indicated that the lower concentration (0.002 ml Vertimec.L-1) didn\'t cause mortality, but alterations on development stage and larval period time were observed, indicating indirect effects (available resources) on the success of this species. On the other hand, no difference was found between the single and multiple applications of Vertimec® 18EC because all organisms died in the unique dosage treatment, but it was possible to verify limnological alterations after the second application of the pesticide. Considering the results obtained we conclude that Vertimec® 18EC can affect directly (mortality, development stages and behavior) and indirectly (food reduction) the population of Lithobates catesbeianus, contributing to the decline of amphibians in the natural systems.

The objective of this study was to address the relationship between benthic microalgal communities and the phosphate nutrient dynamics of Florida Bay sediments and how they relate to benthic and water column primary production. In situ phosphate (P) flux between the sediment and the water column was measured in three regions of Florida Bay. Differences in the ratio of inorganic to organic phosphate flux were found between the three regions in relation to the amount of phosphate measured in the water column. Based upon the average sediment flux in my study, more than 1600 metric tons of P would be supplied by the sediment per year in Florida Bay. Based upon my measurements, dissolved nutrient flux from the sediment can be an important contribution to pelagic phytoplankton blooms in Florida Bay, accounting for 6.5 - 41% of demand and TDN accounts for 100% of the N demand. My findings were similar to others for both benthic nutrient flux and benthic microalgal chlorophyll a concentration. Benthic microalgae in Florida Bay contribute 700 kg Chl a per day to the system. Mesocosm experiments demonstrated that benthic microalgae and water column phytoplankton can respond differently to changes in nutrient availability. The dissolved nutrient in least supply in the water column does not necessarily correspond to the limiting nutrient for benthic microalgae. ³³P acted as a tracer between sediment and water column dissolved P pools. The presence of benthic microalgae enhanced the transport of ³³P to the water column as compared to simple Fickian diffusion. This was supported by the positive flux of dissolved P from the sediment to the water column pools in control treatments with a living benthic microalgal layer. Primary production by benthic microalgae were measured using dissolved O2 evolution and PAM fluorometry. Primary production for BMA habitat in Florida Bay was between 400 and 800 tons of C per day, based upon O2 production and PAM fluorometry, respectively.

This project was a part of a study to evaluate natural attenuation (NA) as a viable remedial option for petroleum hydrocarbon (PHC) contamination at upstream oil- and gas-contaminated sites in Alberta, Canada. Laboratory mesocosms were set up using groundwater and sediment materials collected from two PHC contaminated sites (Site 1 and Site 3) in Alberta to investigate the enhancement of anaerobic PHC biodegradation by amendment of terminal electraon acceptors (TEAs, nitrate or sulfate) and/or nutrients (ammonium and phosphate). Multiple lines of evidence, including the removal of benzene, toluene, ethylbenzene and xylenes (BTEX) and CCME F1 fraction hydrocarbons (C6 to C10), rapid depletion of TEAs, the production of biogenic gases, and detection of the metabolites verified that anaerobic PHC biodegradation was occurring in both laboratory mesocosm studies. Selective biodegradation of PHCs under different reducing conditions was observed. However, there was no conclusive evidence that one reducing condition will universally favor the biodegradation of specific PHCs. In both studies, nutrient amendment showed no enhancement effects. The calculated first-order biodegradation rates in Site 1 mesocosm study ranged from 0.0032 to 0.033 d-1 for benzene, 0 to 0.028 d-1 for ethylbenzene, 0.0021 to 0.036 d-1 for m-, p-xylenes, and 0.0006 to 0.0045 d-1 for F1-BEX (F1 hydrocarbons exclduding BEX) under the tested conditions. The laboratory first-order biodegradation rates of BEX were higher than the estimated field rates, indicating the potential of enhanced anaerobic biodegradation in situ. However, when comparing the TEA amended mesocosms with the unamended controls (in which iron reduction might be the predominant process), the enhancement effects were less apparent and inconsistent. The calculated first-order biodegradation rates in Site 3 mesocosm study ranged from 0 to 0.0009 d-1 for benzene, 0 to 0.011 d-1 for ethylbenzene, 0 to 0.0016 d-1 for m- and p-xylenes, and 0 to 0.15 d-1 for o-xylene. Sulfate amendment significantly stimulated biodegradation of all xylenes and CCME F1 hydrocarbons. However, there was no definitive evidence that nitrate or sulfate amendment could enhance benzene or ethylbenzene biodegradation. / Environmental Engineering

No description available.

A intervenção das atividades antrópicas ao meio ambiente tem repercutido na estrutura e funções dos ecossistemas, sendo que o uso de aditivos químicos, como agrotóxicos e fertilizantes, destacam-se pela parcela de responsabilidade que assumem diante desses desequilíbrios. O agrotóxico Vertimec® 18CE, cuja toxicidade para diversas taxóns já é conhecida, é amplamente utilizado em lavouras agrícolas, e têm-se conhecimento a respeito das intensas práticas de manuseio, muitas vezes irregulares, o que pode fazer com que concentrações muito maiores do que as previstas atinjam o ambiente aquático. Um dos grupos que nos últimos anos vem se destacando pelo declínio crescente associado ao uso destes produtos são os anfíbios. Os anfíbios possuem papel central na cadeia alimentar, e muitos estudos relatam o desequilíbrio ecológico causado pelo declínio desse grupo em relação a adição de contaminantes, incluindo os agrotóxicos. No presente estudo foram desenvolvidos testes laboratoriais a fim de determinar o estágio dos girinos de Lithobates catesbeianus mais suscetível à intervenção do agrotóxico e à concentração capaz de causar mortalidade em 50% dos indivíduos (CL50, 96h). A partir desses resultados, experimentos in situ (mesocosmos) com girinos no estágio mais avançado (25 da tabela de Gosner) foram desenvolvidos com o intuito de comparar as diferenças de toxicidade do Vertimec® 18CE quando manipulado em campo e laboratório, e quais os efeitos causados por uma única aplicação do produto e por aplicações múltiplas. Os testes laboratoriais demonstraram que os girinos em estágios mais precoce (21G) foram mais sensíveis ao agrotóxico Vertimec® 18CE do que àqueles mais avançados (25G). O experimento em campo indicou que a CL50, 96h para L. catesbeianus (25G) foi muito mais agressiva quando próxima às condições naturais, causando a mortalidade de todos os indivíduos no mesmo estágio de desenvolvimento em um período inferior a 24 horas. Entretanto, a concentração inferior à CL50, 96h (0,002 ml de Vertimec.L-1) quando ministrada em campo, assim como no laboratório, não causou mortalidade, mas implicou em atraso no desenvolvimento e maior período larval do que àqueles organismos que não estiveram em contato com o agrotóxico, já que atingiu os recursos disponíveis, promovendo um efeito indireto no sucesso dessa espécie. Não foi possível observar diferença entre as aplicações única e múltipla do Vertimec® 18CE, em decorrência da morte dos girinos do tratamento em dosagem múltipla, porém observou-se desequilíbrio das condições limnológicas do sistema ao sofrer nova intervenção do Vertimec® 18CE. Diante dos resultados obtidos é possível concluir que o Vertimec® 18CE é capaz de afetar diretamente (mortalidade, estágios de desenvolvimento e comportamento) e indiretamente (redução de recursos alimentares) a população de Lithobates catesbeianus, contribuindo para o declínio de anfíbios nos sistemas naturais. / The intervention of anthropogenic activities to the environment has reflected in the structure and functions of ecosystems and the use of chemical additives, such as pesticides and fertilizers, has contributed for the disequilibrium. The Vertimec® 18EC, whose toxicity is described to different taxa, is widely used in agricultural crops, and it has been known about the intense handling practices, often irregular, which can reach higher concentrations than those expected in the aquatic environment. One group that has been highlighted in recent years by the increasing decline associated with the use of these products is the amphibians. Amphibians plays a central role in the food chain and several studies have related the ecological disequilibrium caused by the decline of this group due to the addition of contaminants, including pesticides. In this study, laboratory bioassays were developed to determine the more susceptible stage and the LC50,96h of Lithobates catesbeianus to Vertimec® 18EC. From these results, in situ experiments (mesocosms) were conducted with tadpoles in more advanced stage (25 of Gosner table) in order to compare the differences in toxicity of Vertimec® 18EC when manipulated both in field and in laboratory. Also, the effects caused by a single and multiple application of the pesticides were evaluated. The laboratorial results showed that earlier stages (21G) were more sensitive than more developing tadpoles (25G), and the effects of the pesticide were more aggressive under natural conditions (mesocoms), with 100% of mortality before 24 hours, at the same developmental stage. The results of laboratorial and in situ bioassays indicated that the lower concentration (0.002 ml Vertimec.L-1) didn\'t cause mortality, but alterations on development stage and larval period time were observed, indicating indirect effects (available resources) on the success of this species. On the other hand, no difference was found between the single and multiple applications of Vertimec® 18EC because all organisms died in the unique dosage treatment, but it was possible to verify limnological alterations after the second application of the pesticide. Considering the results obtained we conclude that Vertimec® 18EC can affect directly (mortality, development stages and behavior) and indirectly (food reduction) the population of Lithobates catesbeianus, contributing to the decline of amphibians in the natural systems.