In the next century, the world’s ecosystems are going to change dramatically. Within the Mississippi Delta, shrinking swamps, degraded wetlands, and invasive species of current day southern Louisiana will only continue to evolve. Plant distribution and range, weather patterns and storm frequencies, and uncontrollable growth of weeds are expected to have a huge impact on our environment. Weeds, any non-planned plant, are expected to grow more fiercely with rising levels of pollution, a warmer climate, and higher CO2 levels. Some consider weeds as being at the heart of environmental ruination; they must must be eradicated and they must be destroyed. Arguably, human impact plays a more significant role concerning the integrity of the environment. These are constructed and now changing ideas surrounding nature. In many cases, weeds and invasive species are detrimental. But these plants are also perfectly acclimated to their surroundings, offering the opportunities of phytoremediation, erosion control, storm water control, and even habitat creation with no use of resources and at no monetary cost. The Louisiana landscape has been irrevocably changed through geographical and climatic processes as well as human intervention. Its permanent transformation is expected with not only its shifting ecology but rising sea levels, erosion, and saltwater intrusion. Complete submersion is imminent in the next few centuries. Like the act of keeping New Orleans dry, there is tension between releasing human control over larger environmental systems and saving what we know and understand. Rather than working against nature, an architecture of awareness and acknowledgement of present circumstances and an anxious future can be established. This thesis seeks to investigate the evolving landscape of the future Louisiana coast through the design of a mutually beneficial system that is conscious of both the destruction and benefits of invasive plants. How can the existing and expected landscape occupants be productive and useful? How can the elements that make southern Louisiana so special be adapted for our changing ecologies? And what is the role of architecture in an evolving landscape on the brink of collapse? This thesis hopes to illuminate the ways in which something (sometimes seemingly) destructive can be positive, productive, and conscious. Considering shifting ecologies, how can architecture merge with the new landscapes and adapt to our present preservation needs now and environmental concerns in the future? / 0 / SPK / specialcollections@tulane.edu

Knowledge about the spatial dynamics of invasive species is essential to predict, restrict, and prevent their spread to new areas. Invasive Silver Carp (Hypophthalmichthys molitrix) populations are expanding on all fronts and are threatening to establish in the Laurentian Great Lakes. Understanding their movement patterns is vital to prevent their populations from spreading further and to improve management efficiency. This study looked at multiple factors to understand which have an influence on the movement of invasive Silver Carp in two different river systems. Chapter 1 examined the relationship between individual and environmental factors—including length, body condition, temperature, and discharge—and movement in invasive Silver Carp in the Illinois River. Several different movement metrics were examined—including range, upstream and downstream distance per detection, upstream and downstream movement rate, and total movement—to see if they were affected by any of these factors. Chapter 2 examined multiple morphological metrics—including geometric morphometrics, total length, caudal peduncle depth, and caudal fin aspect ratio—related to the movement of Silver Carp in the Wabash River to see if Silver Carp with similar movement have similar morphology. For both chapters, acoustic telemetry was used to track the movement of Silver Carp. For analysis, multiple generalized linear models were used. For Chapter 1, temperature and discharge were the most commonly included predictors across movement metrics. For Chapter 2, no morphological metrics were identified as predictors of movement. Quantifying the effects of individual and environmental factors can aid in the control and containment of this invasive species and may help to manage populations in at-risk environments. This study demonstrated that factors, like temperature and discharge, can be used to determine when individuals are more likely to expand the invasion front of Silver Carp in the Illinois and Wabash rivers. Which specific individuals are the largest threat to the invasion front can be predicted by individual factors like length, but not body shape.

No description available.

Symbiotic relationships display plasticity through time, depending on a variety of factors that include host properties, symbiont densities, and environmental conditions. Invasive species can affect symbiotic relationships by introducing invasive symbionts, reducing the population of native symbionts, or competing for native symbionts as a resource. There is an established symbiotic relationship between crayfish and annelid worms in the order Branchiobdellida. Branchiobdellidan worms can have a mutualistic cleaning symbiosis with crayfish, or at times become parasitic and feed on crayfish gill tissue if nutrients on the host are low. With the introduction of invasive crayfish in the Southern Appalachians in Virginia, branchiobdellidan worm populations have sharply declined due to invasive crayfish being less competent hosts for the symbionts. However, degree of competency as a host may differ among invasive species to, as invasive hosts have their own unique context-dependent symbiotic relationships. To investigate how symbiotic relationships differ between invasive hosts, I encouraged symbiotic relationships between invasive hosts Faxonius virilis and Faxonius cristavarius and native symbionts Cambarincola ingens. In two experiments spanning several months, I observed changes in growth rates of hosts and damage to gill tissues over varying levels of symbiont exposure. One species of invasive host, F. cristavarius, had increased growth rates when exposed to native symbionts at low symbiont densities, while for the other invasive host, F. virilis, growth rates and gill chamber damage was not impacted by the presence of symbionts. I also compared an invasive host F. cristavarius to a native host Cambarus appalachiensis to measure the response of growth rate, symbiont damage to gills, and behavior of worms across a gradient of symbiont exposure. The native host's growth rates increased over time, but not due to an effect of symbionts. However, the invasive host exhibited effects from parasitism when symbiont densities were high. My findings suggest that invasive hosts can have their own unique context-dependent relationship with native symbionts. Because there is no one-size-fits-all rule for invasive hosts, when invasive hosts enter a region, new symbiotic relationships can be formed that are beneficial for invasive hosts and native symbionts. Invasive hosts or native symbionts could also be rejected by the other which may lead to decreases in either of their populations. / Master of Science / Symbiotic relationships are relationships between two or more organisms lasting for long periods of time and are often associated with proximity or touch. In symbiotic relationships there can be a host and a symbiote. The difference between the host and symbiont can be found in their roles such as protection from predators or parasites or by providing nutrients or transportation and the difference in size with the host being larger. Symbiotic relationships are not static and can change over time due to a variety of reasons, such as host size, symbiont abundance, or nutrient availability. The introduction of harmful non-native species, otherwise known as invasive species, can disrupt symbiotic relationships across ecosystems. Invasive species can introduce non-native symbionts, and also can become potential hosts for native symbionts. The relationship between crayfish and Branchiobdellidan worms, an order of small, segmented worms, has been established over decades of research as a useful system for studying symbiosis. Branchiobdellidan worms can provide a beneficial cleaning service by removing harmful symbionts or bacteria from their crayfish host. Alternatively, they can become parasites and feed on crayfish gills if nutrients are not available on the host. Introduced invasive crayfish can decrease the population of brachiobdellidan worms within the Southern Appalachians in Virginia. However, an established relationship between native symbionts and invasive crayfish hosts has not been studied. To investigate the effects of a symbiotic relationship over the time span of several months between invasive hosts and native symbionts, I experimentally reduced the ability of invasive hosts to remove branchiobdellidan symbionts to allow native branchiobdellidan worms time to acclimate on to invasive crayfish and establish a symbiotic relationship. In two experiments over several months, I recorded changes in host growth rates and gill damage. Invasive hosts had an increased growth rate when there was a low abundance of worms. I also compared an invasive host to a native host to see how changes in growth rates, gill chamber damage, and locations of worms on their host may differ. The native host's growth rates increased, but the invasive host had a negative growth rate when worm densities were too high. My findings suggest invasive hosts can have their own unique symbiotic relationship with native symbionts. When invasive hosts are introduced to a region, native symbiont populations may either decrease or native symbionts may find compatible invasive hosts. By examining relationships between native symbionts and invasive hosts, we can understand how invasions may influence symbiotic relationships and how other organisms are affected in the ecosystem.

Buffelgrass (Pennisetum ciliare (L.) Link), a non-native perennial bunchgrass, invades ecologically intact areas of the Sonoran Desert. It competitively excludes native plants and increases fire frequency and intensity. Since the 1990s, whole buffelgrass plants have been manually uprooted and removed to control the invasion in southern Arizona. Uprooting plants results in bare, disturbed soil which promotes buffelgrass seed germination. This study examined whether leaving entire uprooted buffelgrass plants (thatch) on a field site reduces future buffelgrass establishment compared to removing uprooted plants from the site. A secondary goal was to determine whether light reduction and autoallelopathy were major factors in the negative effect of thatch on buffelgrass seedling density. Field plots with an average of 8,095 kg/ha thatch had 1.9 buffelgrass seedlings/m(2) which was significantly fewer than the 2.9 seedlings/m(2) in plots without thatch. Thatched portions of thatch plots (50% of their total area) had only 0.7 seedlings/m(2). In the greenhouse, which reduced outdoor light intensity by 35.2%, buffelgrass seeds sown in bare soil resulted in significantly higher seedling density than beneath buffelgrass thatch. Potential autoallelopathic chemicals leached from partially decomposed buffelgrass thatch and leached thatch had an intermediate but not significant (p = 0.09) effect on seedling numbers. Results suggest that leaving uprooted buffelgrass plants has the benefit of reducing seedling establishment in the area disturbed by uprooting.

From all the species that arrive to a novel environment, very few manage to form a viable population. The guppy, a very successful invader, is a highly social species that performs some of its vital tasks (e.g., foraging, avoiding predators) in groups. This thesis aimed to quantify heterospecific association benefits that enhance invasion success. Interactions between invaders and natives could be one of the environmental characteristics of a place that increase its risk of invasion. I evaluated the tendency of an invasive species to associate with native individuals with similar ecological requirements. I tested the hypothesis that invaders gain exploring, acquisition of information and foraging benefits when socializing with natives. In these experiments I used the guppy as the invasive model species and endangered native Mexican topminnows (Poeciliopsis infans, Skiffia bilineata, Ameca splendens, Zoogoneticus tequila, Xenotoca eiseni and Girardinichthys viviparous). I found that guppies shoal with other species in Trinidad (Poecilia picta and Poecilia sphenops), where they are native (Chapter 2) and that this trait remains when they are invasive (Chapter 3). Guppies are equally willing to explore novel environments when accompanied by heterospecifics or conspecifics. Guppies are more willing to explore complex environments than simple ones. Moreover, when exploring simple environments they have a higher association tendency, regardless of the partner' species (Chapter 4), which could lead them to acquire the benefits of grouping behaviour and avoid Allee effects - the disadvantages of being part of a small group. In the contexts in which they were tested guppies gained as much information by associating with heterospecifics as with conspecifics (Chapter 5). Finally, I found that when shoaling in bigger shoals guppies are able to locate food faster and spent more time foraging. The benefits of increased shoal size were maintained when the additional guppies were replaced with heterospecifics. However, they derive more benefits from the species they are more willing to associate with (Chapter 6). These results uncover a mechanism enabling founding individuals to survive during the most vulnerable phase of an invasion and help explain why guppies have established viable populations in many parts of Mexico as well as in every continent except Antarctica.

No description available.

Nos recherches abordent, par une approche multidisciplinaire, l’écologie spatiale et la dynamique d’invasion du ravageur de l’épicéa Ips typographus (Coleoptera : Scolytinae) en Belgique. Bien que cette espèce ne puisse pas être considérée au sens strict comme invasive en Belgique où elle est implantée depuis le milieu du 19ème siècle, de très vraisemblables introductions de souches exotiques en provenance de Russie et des Pays baltes, en font un modèle exceptionnel pour l’étude de ces processus. Une analyse en milieu urbain, suivant des transects centre-périphérie, a d’une part suggéré l’introduction probable de ces souches exotiques et d’autre part permis d’étudier ce ravageur forestier dans un milieu qui lui est a priori défavorable. Il en résulte que, malgré un effet de la structure urbaine sur l’abondance du scolyte, sa présence a été observée partout, y compris dans les zones densément bâties du centre de Bruxelles. Cela suggère, en terme de dispersion, que cette espèce est capable d’atteindre des arbres isolés, et en terme d’infestation, que tout épicéa constitue un hôte potentiel tant en milieu forestier qu’en milieu ouvert ou urbain. Une étape préliminaire dans l’estimation des risques liés aux invasions biologiques est d’effectuer une analyse de filière, afin d’analyser les différentes voies d’introduction et les risques liés aux pays d’origine des marchandises importées. Sur base de l’analyse de l’ensemble des sources de données statistiques disponibles, nous avons déterminé l’ampleur du commerce de grumes d’épicéa entre l’est de l’Europe et la Belgique, les modes de transport utilisés, les origines et destinations des grumes, ainsi que la variabilité de la localisation et du nombre des différents points d’entrée de ces marchandises sur le territoire belge d’une année à l’autre, depuis le début des importations en 1996. Notre analyse illustre les difficultés inhérentes à ce genre d’étude, particulièrement au niveau de la disponibilité des données à une échelle appropriée. Par une approche de modélisation, nous avons envisagé différents scénarios de dispersion de souches introduites d’Ips typographus afin d’estimer l’expansion de celles-ci en Belgique. Notre modèle a permis de mettre en évidence l’importance de la bonne connaissance de certains paramètres biologiques caractétistiques de l’espèce étudiée (phénologie, capacité de dispersion, taux de croissance). Par ailleurs, les volumes d’importation et la localisation des points d’entrée des marchandises semblent jouer un rôle secondaire. Enfin, nous avons utilisé des marqueurs génétiques afin d’essayer de prouver l’introduction de souches russes et baltes du scolyte de l’épicéa en Belgique. Des échantillons ont été collectés dans neuf pays européens ainsi que sur l’ensemble du territoire wallon. La structure génétique observée n’a pas permis de mettre en évidence une différenciation entre les populations de l’est et de l’ouest de l’Europe. La présence d’haplotypes communs à l’est et à l’ouest rejoint l’hypothèse d’une homogénéisation des populations en relation avec le large pouvoir de dispersion du typographe. Cependant, un grand nombre de mutations a été observé entre 2 haplotypes. Des introductions d’origines lointaines telles que la Sibérie ne sont donc pas improbables. Les résultats détaillés de chacune de ces études sont développés dans les différents articles constituant cette thèse. La discussion générale met ceux-ci en relation et aborde les perspectives découlant de nos recherches.

This thesis investigates the impact of two invasive ecosystem engineers on the river banks. Invasive species generate significant global environmental and economic costs and represent a particularly potent threat to freshwater ecosystems. Ecosystem engineers are organisms that modify their physical habitat. Therefore this thesis will explore the interaction of these two types of species and their impacts on the example of the impact of signal crayfish and Himalayan balsam The obtained results indicate that there are few avenues through which invasive ecosystem engineers can influence river bank processes. While many uncertainties remain, due to the intrinsic complexity of river ecosystems, a multitude of anthropogenic stressors that they are increasingly subjected to and a wide array of ecosystem services that rivers provide to people, it is important to consider the role of invasive ecosystem engineers in river management practices. on river banks. The work included analyses and development of conceptual models for the understanding of invasive ecosystem engineers, followed by four research chapters aimed at answering specific questions. A study of signal crayfish impact is primarily focused on the impact of burrows that crayfish dig as shelter and their influence on riverbank erosion. The interaction between habitat characteristics, the occurrence of burrows and erosion is analysed on three different levels of spatial scale: bank section in reach, reach in the catchment and bank section in the catchment. Bank section in reach survey (Chapter 4) focused on a reach heavily impacted by crayfish burrowing on the River Windrush, UK, in order to study the maximum effect of burrowing. Also, smaller spatial extent enabled detailed study of three sets of variables as well as an assessment of the impact that signal crayfish population density has on burrowing. Reach in catchment spatial scale expanded the survey to cover 103 river reaches in the Thames catchment and was based on a combination of habitat information from publicly available online data sets, primarily the River Habitat Survey database and rapid field surveys that recorded burrows and erosion. Bank section in catchment-scale was based on the same 103 sites, but the main focus of field observations were ten metres long bank sections for which habitat, burrows and erosion information were collected. Overall, burrowed banks were more likely to be characterised by cohesive bank material, steeper bank profiles with large areas of bare bank face, often on outer bend locations and were associated with bank profiles with signs of erosion. There were indications that signal crayfish burrowing is contributing to the river bank erosion, but no conclusive results have been made. Study of the impact of the Himalayan balsam was undertaken on eight sites at the River Brenta in Italy and it was focused on three main aspects. Firstly it was established that extent of Himalayan balsam domination over native vegetation varies widely depending on the habitat conditions and native plants encountered. Secondly, it was established that there are no conclusive differences in the extent of erosion and deposition on transects covered by native vegetation and Himalayan balsam. Thirdly, measurement of traits of individual plants showed significant differences in traits of individual plants that are known to have consequences for river bank erosion and deposition.

Invasive organisms are one of the major threats to the ecological integrity of aquatic systems in the 21st century. Among the most notorious and important aquatic invasive organisms are the dreissenid mussels, Dreissena polymorpha and D. rostriformis bugensis, which having originated in the Ponto-Caspian region are now common in many parts of Europe and North America. Dreissenids have large impacts on many aspects of lentic ecosystem functioning, the sum of which is thought to lead to the translocation of biological production from the pelagic to the littoral zones of lakes. In this thesis I explore the effects of dreissenids on the nearshore zones of large lakes, investigate the mechanisms by which dreissenids couple the pelagic and nearshore zones of lakes and attempt to elucidate the factors affecting the strength of the dreissenid-mediated connection between the pelagic and littoral zones. The effects of invasive organisms on an aquatic ecosystem will depend, in part, on the distribution and biomass of the invasive organisms in the system. In chapter 2 I present the results of a lake-wide survey of the distribution of invasive dreissenid mussels in Lake Simcoe, Ontario and discuss some of the factors that shape their distribution pattern in the lake. Dreissenid biomass averaged 27.2 (±24.3 SD) g shell-free dry mass (SFDM)/m2 in the main basin of Lake Simcoe and 12.4 (±16.9 SD) g SFDM/m2 in macrophyte-dominated Cook’s Bay. I argue that water movement is an important determinant of dreissenid distribution, both through catastrophic disturbance in shallow water and through non-catastrophic effects on substrate distribution and possibly food supply rates. In areas of dense macrophyte growth, mussel abundance was shown to be associated with that of preferred macrophyte taxa, in particular with that of Ceratophyllum demersum. I used the results of my survey and the relationships between environmental variables and dreissenid biomass to estimate the total biomass of dreissenids in Lake Simcoe: 12,000 tonnes SFDM. Most of the dreissenid biomass in Lake Simcoe was concentrated in the nearshore zone, where dreissenids would have maximal impacts on littoral biological production. One of the effects of the dreissenid invasion into the Laurentian Great Lakes appears to be a resurgence in the abundance of the nuisance alga Cladophora glomerata which experienced a marked decline following phosphorus abatement in the late 1970s and early 1980s. A subsidy of bioavailable phosphorus excreted by dreissenid mussels could be an important mechanism facilitating the growth of C. glomerata. In chapter 3, I describe a survey of dreissenid distribution and abundance followed by in situ experiments designed to measure dreissenid phosphorus excretion rates. Average dreissenid mussel abundance in our study area was 3674 (±2233 SD) individuals/m2, with an average biomass of 52.2 (±29.0 SD) g of shell free dry mass/m2. The mussels excreted bioavailable soluble reactive phosphorus (SRP) at an average rate of 7.0 μg SRP/g shell free dry mass/hour, contributing about 11 tonnes of SRP to the study area over the C. glomerata growing season. Dreissenids appear to be an important source of recycled bioavailable phosphorus to the littoral zone, potentially supplying more soluble reactive phosphorus to the study area than local watercourses and waste water treatment plants, and more phosphorus than is required to sustain local C. glomerata growth. Dreissenid establishment in many systems coincides with increases in the abundance and diversity of littoral benthic invertebrates and with changes to community composition of the benthos. Currently, there is a lack of long-term studies of the impact of dreissenid mussels on hard-substrate inhabiting littoral benthos. In chapter 4 I compare the littoral benthos of Lake Simcoe, Ontario just prior, and 14 years following the establishment of dreissenids in the lake. Densities of non-dreissenid invertebrates on hard substrata increased by nearly 50 times, from an average of 367.9 (±460.8 SD) individuals/m2 in 1993 to an average of 16,706.4 (±10,204.5 SD) individuals/m2 in 2008. The taxonomic diversity of the benthos increased significantly. The distribution of benthic organisms also changed; the numerical abundance of benthos has become more even across depths and sites, as has community composition. I suggest that in addition to increasing resource availability to benthic organisms dreissenids have also caused a homogenization of the littoral habitat by increasing the evenness of the distribution of food and habitat resources. The changes in the littoral benthic community in Lake Simcoe likely have wide-ranging implications to higher trophic levels and the cycling of energy in the lake. In addition to impacting nutrient cycling and the benthic invertebrate communities of littoral zones, dreissenid mussels can have large effects on food webs and energy cycling. In chapter 5 I used stable isotope analysis of pre- and post-dreissenid components of the nearshore food web of Lake Simcoe, Ontario to determine how dreissenids affected food sources and energy flow in the littoral zone of Lake Simcoe. Results suggest that the post-dreissenid food web relies about equally on two energy sources: dreissenid biodeposits (redirected pelagic primary production) and littoral benthic primary producers. Although the relative importance of pelagic and benthic primary production to benthic organisms has not changed much following dreissenid establishment, the absolute importance of both increased considerably in the post-dreissenid littoral zone: the large increase in invertebrate biomass that followed dreissenid establishment means that the amount of both pelagic and benthic primary production needed to sustain post-dreissenid organisms had to increase considerably. The results of this chapter suggest that dreissenids increase the availability to food to littoral organisms by redirecting pelagic primary production to the benthos and by stimulating littoral benthic primary production. The impacts of dreissenids on littoral benthic organisms probably have large effects on littoral and pelagic fish communities of lakes. Dreissenid mussels translocate biological production to the benthos by stimulating benthic primary production through nutrient excretion and increases in water clarity, by increasing habitat availability for benthic organisms and by biodepositing pelagic material that becomes available to benthic organisms and the fish that feed on them. I argue that hydrodynamic factors are important in controlling the strength of the dreissenid-mediated pelagic-littoral connection in lakes. Because hydrodynamics relate to lake size, a relationship between lake size and the ability of dreissenids to translocate production the littoral zone can be postulated, where dreissenid effects are maximal in intermediate-sized lakes.