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The purpose of this study was to examine the direct and indirect effects of ultraviolet-B (UV-B) radiation on freshwater protists. Laboratory experiments were conducted in order to determine the importance of photoenzymatic repair (PER) of UVBinduced DNA damage in the heterotrophic nanoflagellate Paraphysomonas sp. Investigations into the combined effects of UV-B and chromophoric dissolved organic matter (CDOM) were conducted in laboratory experiments in which protist cultures were exposed to UV-B radiation in the presence and absence of water amended to a higher CDOM concentration in order to determine the ability of CDOM to act as a UV-B filter and as a potential nutrient source. Field experiments examined the responses of natural communities of protists and bacteria to ultraviolet radiation (UVR) in the presence of high and low concentrations of CDOM. Ultraviolet-B radiation (UV-B; 280 – 320 nm) negatively affects many aquatic organisms, including heterotrophic flagellates, by directly damaging DNA. The quantity of UV-B reaching the surface of a lake varies with atmospheric chemistry, including stratospheric ozone, and the presence of large holes (Alldredge 1977) in this ozone shield during the last decade resulted in historically high UV-B levels. In aquatic systems, the nature of the damage to organisms depends on the intensity and duration of solar radiation, plus its attenuation in the water column. The amount of UV-B damage is highly dependent on the concentration of CDOM in the water column because CDOM strongly absorbs UV-B radiation. This protective role of CDOM is likely to be reduced in areas where warmer, drier climate decreases watershed runoff, which ultimately results in acidification and increased CDOM photodegradation. However, CDOM also may also act as an organic carbon source for bacteria and stimulate growth of the microbial food web, including bacterivores like heterotrophic flagellates. The effect of UV and CDOM interactions on the microbial food web is not well understood, but climate-related increase in CDOM in an oligotrophic lake could increase the heterotrophic microbial food web impact by reducing UV-B damage and increasing available resources. Since aquatic organisms, including protists, are differentially susceptible to UV-B radiation, climate change effects on CDOM and UV-B attenuation are likely to alter the ecology and community structure of aquatic systems. This thesis describes investigations into the direct and indirect effects of UV-B radiation on freshwater protozoa. The role of PER of direct UV-B induced DNA damage was examined in laboratory experiments that compared the survival and population growth of the heterotrophic nanoflagellate Paraphysomonas sp. at two environmentally relevant temperatures. The results from these experiments demonstrated the reliance of Paraphysomonas sp. on PER, with 100% mortality in the absence of the photorepair radiation that activates photoenzymatic repair enzymes. The ability of Paraphysomonas sp. to recover from exposure to UV-B radiation declined in flagellates adapted to 15°C relative to the same exposures at 20°C. Experiments examining the direct and indirect effects of UV-B radiation and CDOM on freshwater protists conducted in the laboratory and in an oligotrophic lake in the Pocono Mountains showed that potential DNA damage resulting from UV exposure is reduced and microbial growth may be enhanced with an increase in CDOM concentration. / Biology

Increasingly higher numbers of people are moving into urbanizing environments, yet our understanding of ecosystem consequences of rapid urbanization is still in its infancy. In this dissertation, I assessed dynamics of residential landscapes during suburban succession and consequences for ecosystem functioning. First, I used a space-for-time approach to quantify more than a century of suburban succession in the Dallas – Fort Worth metroplex (DFW). Attributes of residential landscape plant diversity and habitat complexity were quantified for 232 individual properties nested within 14 neighborhoods constructed between 1906 and 2020. Suburban succession progressed from simple turf lawns with limited habitat complexity to landscapes dominated by deciduous trees and high habitat complexity, but homeowner decisions related to landscape management affect the rate of that transition and the number of plants and taxa present. Next, I used the novel spatial construct of "neighborhoodsheds" to test for effects of suburban succession on carbon export, and found that the proportion of carbon derived from C3 vs. C4 plants was affected by neighborhood plant community structure (i.e. greater proportion of trees and shrubs primarily in later stages of suburban succession). Finally, I conducted a mesocosm experiment to test effects of changes in allochthonous inputs during suburban succession on aquatic ecosystem functioning. The proportion of carbon from C3 vs. C4 sources interacted with time to affect abundance of emergent mosquitoes and chironomids. This work sets the stage for further research on urban ecology in DFW and provides conceptual advances for the study of urban ecosystems more broadly.

Master of Science / Department of Biology / Walter K. Dodds / Human-induced stressors such as increased nitrogen (N) loadings, altered watershed land-use, and biodiversity losses are a few of the numerous threats to aquatic systems. Prairie streams experience natural disturbances, such as flooding and desiccation, which may alter responses to anthropogenic stressors. Denitrification, the dissimilatory reduction of NO3- to N gas (N2O or N2), is the only permanent form of N removal from terrestrial or aquatic ecosystems, and is important in mitigating N pollution to streams and downstream waters. Little is known about the relationships between denitrification and riparian prairie vegetation or large consumers. In the first chapter, I used outdoor mesocosms to determine the impact of a grazing minnow, Campostoma anomalum, on structural and functional responses of prairie streams to a simulated flood, focusing on denitrification. In terrestrial ecosystems, grazing can stimulate denitrification, but this has not been studied in streams. Ammonium (NH4+) enrichments, used to simulate fish excretion, alleviated N limitations on denitrification. Both fish and NH4+ affected algal biomass accrual, but only fish affected algal filament lengths and particulate organic matter. In a second experiment, I examined the impact of woody vegetation expansion, a primary threat to tallgrass prairie, on riparian and benthic denitrification. Expansion of woody vegetation in these grasslands is due primarily to altered fire regimes, which historically inhibited woody vegetation growth. To determine the effect of woody vegetation expansion on benthic and riparian denitrification, woody vegetation was removed from the riparian zone of a grazed and an ungrazed watershed. Both soil and benthic denitrification rates from this removal buffer were compared to rates in grassy or woody riparian zones. Riparian soil denitrification was highly seasonal, with greatest rates occurring during early spring, and rates being low throughout the remainder of the year. Benthic denitrification was also temporally variable but did not exhibit seasonal trends, suggesting benthic denitrification is driven by factors other than water temperature. Removal of woody vegetation stimulated soil and benthic denitrification rates over rates found in naturally vegetated riparian zones. Elevated N loadings will continue to affect aquatic ecosystems, and these effects may be exacerbated by biodiversity losses or changing riparian vegetation.

Nous avons cherché des relations empiriques entre l’abondance des macrophytes submergés et le développement résidentiel du bassin versant, les propriétés du lac et la présence de milieux humides dans 34 lacs de la région des Laurentides et de Lanaudière sélectionnés à travers un gradient de développement résidentiel. Les macrophytes submergés ont été échantillonnés par méthode d’échosondage à l’intérieur de la zone littorale. L’abondance moyenne des macrophytes a ensuite été estimée à l’intérieur de quatre zones de croissance optiquement définies (profondeur maximale = 75 %, 100 %, 125 % et 150 % de la profondeur de Secchi) ainsi qu’à l’intérieur de toute la zone littorale. L’occupation humaine a été considérée selon trois échelles spatiales : celle présente 1- dans un rayon de 100 mètres autour du lac, 2- dans la fraction du bassin versant qui draine directement vers le lac et 3- dans le bassin versant en entier. Nous avons aussi testé, lac par lac, l’effet de la pente locale sur l’abondance des macrophytes. Nous avons observé des corrélations positives et significatives entre l’abondance des macrophytes submergés et l’occupation humaine de l’aire de drainage direct (r > 0.51). Toutefois, il n’y a pas de relation entre l’abondance des macrophytes submergés et l’occupation humaine de la bande de 100 mètres entourant le lac et du bassin versant entier. Les analyses de régression multiple suggèrent que l’abondance des macrophytes submergés est faiblement corrélée avec l’aire du lac (+) et avec la présence de milieux humides dans le bassin versant entier (-). Localement, l’abondance des macrophytes est reliée à la pente et à la profondeur qui expliquent 21% de la variance. Les profondeurs de colonisation maximale et optimale des macrophytes submergés sont corrélées positivement au temps de résidence et à la profondeur de Secchi et négativement à l’occupation humaine et à l’importance des milieux humides. / We searched for empirical relationships between whole-lake submerged macrophyte abundance and residential development, lake properties and wetlands in 34 lakes from the Laurentides-Lanaudière region subjected to a wide range of residential development. Submerged macrophyte abundance was assessed by echosounding of the entire littoral zone. Human encroachment was measured at three spatial scales: Within 1- a 100 m-wide buffer strip circling the lake, 2- the fraction of the watershed that drains directly into the lake and 3- the entire watershed. Single and multiple regression were used to test the effect of residential development on macrophyte abundance in the entire littoral zone and within four optical growth zones defined by Secchi depth. The local effect of slope on local macrophyte abundance was also tested in individual lakes. We found significant positive correlations between submerged macrophyte abundance and dwelling density present within the direct drainage area (r > 0.51). In contrast, there was no significant relation between macrophyte abundance and human occupation of the 100 m-wide buffer circling lake and the entire watersheds. Multiple regression analysis suggest that submerged macrophyte abundance is weakly correlated with lake area (+) and wetland importance within the entire watershed (-). Locally, macrophyte abundance is related to slope and depth which explained together 21% of the variance. Maximum and optimum colonization depths of submerged macrophytes were positively correlated to residence time and Secchi depth and negatively to human occupation and to wetland importance.

I used natural abundances of stable isotopes (δ13C and δ15N) to examine the food web structure of lake zooplankton communities. I focused on modeling isotopic variation with respect to trophic variation (δ15N) and to variation in dietary carbon sources (δ13C). The isotopic patterns suggest that zooplankton food webs have reticulate connections between food chains, and a large diversity of interactions between consumers and their resources. Variation in the δ13C of zooplankton depended on taxonomic identity, body composition, and habitat specialization. In Sooke Lake Reservoir, seasonal variation in the δ13C of zooplankton was mainly related to variation in lipid content and the δ13C of lipids. This has significant consequences for interpreting the pathways of terrestrial carbon through plankton food webs. In Council Lake, variation in the δ13C of zooplankton among taxa was related to habitat specialization, and indicates taxon- specific exploitation of allochthonous resources. Using a cage experiment, I confirmed that δ13C can indicate habitat specialization of zooplankton. Among lakes, my data suggest that zooplankton communities can readily exploit carbon produced below the epilimnion. Large inter- and intra-lake variation in the δ15N of zooplankton suggests significant trophic variation within zooplankton communities. In a year-long study, annual averages of taxa specific δ15N matched our expectations about the feeding ecology of zooplankton. However, short-term variation in the δ15N of herbivorous zooplankton (like Daphnia) was decoupled from seasonal variation in the δ15N of invertebrate predators. This suggests there are multiple food chains within the plankton community (i.e. grazing chain, microbial chain), and that the strength of each food chain may vary among lakes or seasonally within a lake. This seasonal variation in the food web structure of zooplankton has significant consequences for how we model and consider the trophic position of individual fish.

Master of Science / Department of Biology / Keith B. Gido / Nonnative species represent a major threat to the continued persistence of native fishes globally, especially in the Colorado River Basin of western North America, where there are now more nonnative than native fishes. In the upper Gila River, a tributary of the Colorado, numerous nonnative fishes have established populations, and predation by these nonnatives has been linked to extirpation of native fishes under low-flow conditions at some locations. Historically, the upper Gila lacked a top piscivore, and it is unclear what mechanisms have allowed the establishment of nonnative piscivores and resultant extension in food chain length. To investigate the phenomenon of increased food chain length through nonnative introductions we explored the influence of autochthonous energy availability on nonnative predator abundance, food chain length, and abundance of other trophic levels. Predictions were that increased basal energy availability would lead to increased nonnative predator abundance and thus increased food chain length, based upon predictions from food web theory. Annual production and biomass of four trophic levels measured across six longitudinally-positioned sites were calculated between June 2008 and June 2009 to test these predictions. In addition, energy demand of trophic levels relative to energy supply was compared across sites using a quantitative food web approach, to evaluate energy limitation across trophic levels. Primary production was found to vary considerably across the upper Gila (1,677-16,276 kcal m-2 yr-1), but production and biomass of other trophic levels was not related to this gradient as predicted. In addition, food chain length demonstrated a marginally-significant negative relationship with primary production (R[superscript]2=0.42, d.f.=5, p=0.16), which was in contrast with predicted responses. These results suggest that energy availability does not appear to be a limiting factor to the production or biomass of consumers. The influence of other mechanisms on food chain length in the upper Gila River, in particular disturbance frequency and intensity, deserve further investigation.

Les thiols et le sélénium peuvent jouer un rôle important dans la méthylation du mercure des environnements aquatiques. Pour démontrer la présence des thiols et du sélénium et leur relation avec le mercure dans certains écosystèmes d'eau douce québécois, une campagne d’échantillonnage fut réalisée durant l’été 2010, dans le parc national du Mont-Tremblant (Laurentides, Québec). Il existe une corrélation significative entre le sélénium et le mercure total dans l’eau des lacs du parc. Cependant, les concentrations de sélénium sont très faibles dans les lacs, les étangs de castor et les ruisseaux. Par ailleurs, les lacs du parc national du Mont-Tremblant ont des concentrations relativement élevées de méthylmercure avec une moyenne de 0,33 ng L-1 et des maximums allant jusqu’à 3,29 ng L-1. Les étangs de castor peuvent aussi être considérés comme des lieux de contamination au méthylmercure, avec une concentration moyenne de 0,95 ng L-1. Toutefois, la présence d’une colonie de castors sur le bassin versant d’un lac ne semble pas influencer les concentrations de mercure que l’on y retrouve. Deux thiols sont détectables dans l’eau de surface des Laurentides, soit le glutathion et l’acide thioglycolique. La concentration de ce dernier thiol est corrélée significativement avec celle du mercure total et du méthylmercure. Les thiols peuvent jouer un rôle important dans les processus de méthylation en favorisant le transport du mercure inorganique à l’intérieur des bactéries sulfato-réductrices. Afin de mieux comprendre l’action antagoniste entre le sélénium et le mercure, des études devraient être réalisées au niveau des tissus des organismes vivants dans ces zones pauvres en sélénium. / Thiols and selenium may influence mercury methylation in aquatic environments. To demonstrate the occurrence of both elements with mercury in selected aquatic systems of Quebec, a sampling campaign was conducted during the summer of 2010 in Mont-Temblant national park (Laurentians, Quebec). There is a significant correlation between selenium and total mercury in surface water. However, concentrations of selenium are very low in lakes and beavers ponds. In addition, the park’s lakes have a relatively high concentrations of methyl mercury with an average of 0,33 ng L-1 and maximum values up to 3,29 ng L-1. Beaver ponds can also be considered hotspots of methylmercury contamination, with an average concentration of 0,95 ng L-1. However, the presence of a colony of beavers in the watershed of a lake does not appear to influence the levels of mercury in that lake. Two species of thiols are present in the surface water of the Laurentian ecosystems: glutathione and thioglycolic acid. The latter is significantly correlated with total mercury and methyl mercury. Thiols may play an important role in the methylation process by promoting the transport of inorganic mercury within the sulfate-reducing bacteria. To better undestand the antagonistic action between selenium and mercury, more research should be conducted in the tissue of organisms living in areas of low concentration of selenium to know if they are protected against mercury toxicity.

L’effet du développement résidentiel des bassins versants sur l’habitat et la distribution des macrophytes dans le littoral de six lacs des Laurentides a été évalué à l’aide de carottes de sédiments et de quadrats. Le développement augmente la proportion de milieux déboisés ce qui réduit l’apport en débris de bois et augmente l’érosion et les apports de nutriments dans les sédiments du littoral. Les sédiments sont plus fins, plus denses et contiennent moins de matière organique. Ces changements favorisent les macrophytes en augmentant leur couverture dans les lacs développés. La présence d’espèces submergées de macrophytes est également favorisée au détriment des espèces à feuilles flottantes, plus caractéristiques des lacs moins développés. Même si la biomasse des macrophytes est limitée dans certains lacs, celle-ci augmente dans les lacs développés et montre des signes d’un effet tampon sur les apports de nutriments. Des quantités équivalentes à des valeurs entre 35 et 230% des apports annuels de phosphore et entre 79 et 659% des apports d’azote par les résidents ont été accumulées dans les tissus des macrophytes des lacs dont le bassin versant est très déboisé. Les sédiments s’enrichissent à la sénescence des macrophytes et contiennent alors plus de nutriments que la colonne d’eau et ce, pour tous les lacs. Une présence accrue d’espèces submergées et plus de nutriments dans les tissus des macrophytes des lacs développés, jumelés à l’absence de prolifération de phytoplancton malgré un plus grand apport de nutriments, laisse penser que les lacs des Laurentides sont en état d’eutrophisation précoce. / Effects of residential development on macrophyte habitat and distribution in the littoral zone of six lakes of the Laurentian region were assessed with quadrats and small cores. Residential development increases the proportion of open area which reduces coarse woody debris inputs and enhances erosion and nutrient inputs into the sediments. Sediments are then finer, more compact and contain less organic matter. With less important proportion of forested area in developed watersheds, nutrients inputs are then more important in sediment as well. These changes in macrophyte habitats enhance coverage of the littoral by aquatic plants in developed lakes. Submerged species are also favoured at the expense of floating species that are more typical of pristine conditions. Despite the limitation of aquatic plants biomass in some lakes, macrophyte biomass is higher in developed lakes and showed signs of a buffering effect on nutrient inputs, especially for phosphorus. Macrophyte nutrient content represented values between 35 and 230% of annual phosphorus inputs by residents on the shore of developed lakes and between 79 and 659% of the annual nitrogen inputs. Sediments are enriched by macrophytes at their senescence and therefore contain more nutrients than the water column and macrophytes for all lakes. The greater presence of submerged macrophytes, and the higher amount of nutrients in macrophytes of developed lakes combined with absence of phytoplankton blooms in spite of greater nutrient supply, suggests that Laurentian lakes are in an early stage of eutrophication.