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Kristianstad is a city of 41.000 inhabitants in southern Sweden. Once a fort on an island in the river of Helge Å, parts of the river and surrounding lakes were lowered or removed as the city expanded. This has caused parts of Kristianstad to have the lowest point in Sweden, -2,32 meters below ocean level. The surrounding river has an important role as it creates a wetland ecosystem called Vattenriket that surrounds the city. This area is recognised as a biosphere reserve of international importance. Water is currently held at bay with help of embankments, but the city experiences recurring floods during years of high water levels. The threat that the water poses is expected to increase by the end of the century due to rising sea levels.  How can a city combat flooding through use of urban design in relation to local ecosystems in an era of rising water levels? This project is about how a city in an exposed position could deal with water, ecosystems services and sustainable development in a changing climate with care towards the surrounding wetland, to use it as a major tool in how to tackle the challenges ahead.

Most models for the spread of an invasive species into a new environment are based on Fisher's reaction-diffusion equation. They assume that habitat quality is independent of the presence or absence of the invading population. Ecosystem engineers are species that modify their environment to make it (more) suitable for them. A potentially more appropriate modeling approach for such an invasive species is to adapt the well-known Stefan problem of melting ice. Ahead of the front, the habitat is unsuitable for the species (the ice); behind the front, the habitat is suitable (the open water). The engineering action of the population moves the boundary ahead (the melting). This approach leads to a free boundary problem. In this thesis, we mathematically analyze a novel free-boundary model for the spread of ecosystem engineers that was recently derived from an individual random walk model. The Stefan condition for the moving boundary is replaced by a biologically derived two-sided condition that models the movement behavior of individuals at the boundary as well as the process by which the population moves the boundary to expand their territory. We first consider the model with logistic growth and study its well-posedness. We assign a convex functional to this problem so that the evolution system governed by this convex potential is exactly the system of evolution equations describing the above model. We then apply variational and fixed-point methods to deal with this free boundary problem and prove the existence of local in-time solutions. We next study traveling wave solutions of the model with the strong Allee growth function. We use phase plane analysis to find traveling wave solutions of different types and their corresponding existence range of speed for the model with an imposed speed of the moving boundary. We then find the speeds in those ranges at which the corresponding traveling wave follows the speed of the free boundary.

Abstract: Managing worldwide urbanization and housing shortage in cities through a resilient development isan immense issue of today. This study states the risk with urban densification, at the expense ofgreenspace, which is crucial to maintain vital ecosystem services. The nonlinear response todisturbance in ecosystems, need to be emphasized both in planning and practice, to avoiddegradation and collapse. Despite general promotion of densification as a tool to decrease negativeurban impact on surrounding landscape, as to mitigate climate change, current strategies ofcompacting cities are argued to endanger future resilience. In this work, it is stressed that valuationof greenery in urban areas should include the recognition of uncertainty, safeguarding the availabilityof all forms of ecosystem services in a changing future. Applying a framework of social-ecologicalresilience, a case-study of Stockholm regarding valuation of greenery and ecosystem services inplanning and exploitation, as in continuous management, has been carried out. A wide range ofactors within the fields of green management, planning and exploitation have been interviewed.When compared with expressed visions in comprehensive plans and policies, results from interviewsshow severe gaps between planning and practice. Foresight planning in relation to adaptivegovernance, to enhance social-ecologic interactions, is suggested a tool to improve implementationand acknowledgement of ecosystem services in urban development and design. Further, enhancedcross-learning and knowledge exchange in the social-ecological system, should be improved throughinteraction and recognition of the variety of stakeholders and multi-functional green areas tostrengthen social-ecological resilience in the urban context. / Sammanfattning: Dagens intensiva urbanisering och bostadsbrist, betonar behovet av resilient stadsutveckling. Dennastudie understryker faran med förtätning på bekostnad av grönstrukturer, vilka är avgörande förupprätthållandet av livsnödvändiga ekosystemtjänster. Ekosystems icke lineära respons påstörningar, bör uppmärksamma i både planering och praktik, för att undvika utarmning eller kollaps.Tillskillnad från ofta framhållna fördelar med förtätning, som minskad inverkan på kringliggandegrönstrukturer och motverkande av klimatförändringar, vill den här studien framhålla hurförtätningsprocesser riskerar att försämra städers resiliens. För att säkra en framtida motståndskraftoch anpassningsförmåga till förändrade omständigheter, bör värdering av grönstrukturer i stadsmiljötydliggöra framtida osäkerhetsfaktorer i relation till ekosystemens förmåga att tillhandahålla olikatjänster. Utifrån ett social-ekologiskt ramverk har en fallstudie av hur grönstrukturer värderas iplanering- och exploateringsprocesser, samt inom allmänt underhåll, genomförts i Stockholm. Enbredd av aktörer inom planering, exploatering och grönskötsel intervjuades. I jämförelse meduttryckta visioner i olika översiktsplaner och policydokument, visar resultaten från intervjuerna påflera luckor mellan planering och utförande. En långsiktig planering i samband med ett socialekologisktresilient styrelseskick, som syftar på en större förståelse och interaktion mellan socialaoch ekologiska faktorer, föreslås förbättra såväl implementering som uppmärksammande avekosystemtjänster inom stadsutformning och utveckling. Vidare kan ett utökat lärande ochkunskapsutväxling mellan och inom social-ekologiska system, öka förståelsen för- och förstärkastäders social-ekologiska resiliens.

Disturbance is one of the central concepts explaining how diversity arises and is perpetuated in ecological time. A good model system for testing hypotheses related to disturbance is the longleaf pine ecosystem in the southeastern U.S. because in this ecosystem frequent, low-severity fires acts as a disturbance that maintains a unique vegetation structure and high species richness. Vegetation structure influences animal distributions; in fire-dependent ecosystems many animals rely on open-structured, fire-maintained vegetation but shrubs and trees encroach into fire-dependent ecosystems where fire has been excluded. Prescribed burning and mechanical removal are commonly used as restoration tools to control encroachment. To better assess and compare the restoration potential of these tools, a more thorough understanding of how they change vegetation structure and habitat suitability for animals is necessary. The southeastern U.S. is a diversity hot-spot for amphibians, many of which require ephemeral wetlands embedded in longleaf pine uplands for the aquatic phase of their life cycle. Amphibian diversity has been declining in recent decades and habitat loss/degradation has been cited as one of the leading causes. Although often overlooked in studies of fire ecology, the ephemeral wetlands required by many amphibians are also fire-dependent habitats that have been negatively impacted by lack of fire. To understand how disturbance interacts with wetland vegetation and aquatic-phase amphibians, three disturbance treatments meant to mimic the effects of natural disturbance on vegetation structure were applied randomly to 28 dry ephemeral iii wetlands in the Lower Coastal Plain of South Carolina, U.S. The treatments consisted of early growing-season prescribed fire, mechanical vegetation removal (a proposed fire surrogate), and a combination of mechanical removal plus fire; some sites were left untreated for reference. Vegetation structure was quantified and amphibian assemblages were monitored before and after treatments. In addition, one species of amphibian was used in a tadpole survival experiment to examine differences in performance among treatments. Other factors that could be affected by treatments and in turn influence amphibians were measured, including water chemistry, wetland depth, quantity and quality of epilithon, and leaf litter composition. Amphibian survival was lowest, and species depauperateness highest in untreated wetlands. Depauperateness of species whose range was restricted to the range of longleaf pine was lowest in sites that had mechanical treatment plus fire. The mechanical plus fire treatment created the most open vegetation structure with lowest leaf litter accumulation, especially of hardwood litter, conditions correlated with high amphibian survival and diversity. When data from this study was combined with data from a previous study of similar nearby wetlands, a pattern emerged in which one suite of species was absent from recently burned sites, while an entirely different suite of species was absent from long-unburned sites. This evidence suggests that disturbance is related to a shift in amphibian assemblage possibly due to changes in vegetation structure and perhaps wetland ecology in general, from an algal-based system maintained by frequent fire to a detrital-based system that develops in the absence of fire

Increased salinization of inland freshwater resources is present on a global scale, but is pro- gressing rapidly in the densely populated Mid-Atlantic United States. This phenomenon threatens aquatic health, ecosystem services and functionality, and can alter the percep- tion of potable drinking water. The Occoquan watershed, located in Northern Virginia has experienced rapid urbanization across recent decades and is now confronted with rising salinization. Various stakeholders in the area have focused efforts to quantify the drivers of salinization in order to take corrective action to preserve this resource. To aid these efforts, urbanization's relationship with in-stream salinity was analyzed, where its exerted influence was found to be dependent upon overland hydrologic flowpaths which connect urban areas to stream networks. The analysis was then broadened to Multiple Linear Regression models of urban and climatological drivers to statistically quantify each driver's relative influence on in-stream salinity. The models demonstrated that urbanization is the primary driver, where rainfall and roadway deicer application were also found to be significant. The model was then used to predict the magnitude of salinization in the Occoquan watershed to a time horizon of 2040 based on expected population growth as well as two anticipated climate scenarios. Finally, the analytical framework produced in this research was generated with scalability in mind, such that it can potentially be utilized as a watershed-scale screening tool accross the Mid-Atlantic, to inform proactive, regionally appropriate management decisions. / Master of Science / Increased salinization of inland freshwater resources is present on a global scale, but is progressing rapidly in the densely populated Mid-Atlantic United States. Driven by the engineered systems that define our modern world, this phenomenon threatens aquatic health, ecosystem services and functionality, and can alter the perception of potable drinking water. The Occoquan watershed, located in Northern Virginia has experienced rapid urbanization across recent decades and is now confronted with rising salinization. Various stakeholders in the area have focused efforts to quantify the drivers of salinization in order to take corrective action to preserve this resource. The analyses completed in this body of work act to model and statistically analyze the drivers which foster salinization in the Occoquan. The analyses demonstrated that while climatological factors drive salinity in the Occoquan, urbanization is the primary driver, where its exerted influence is dependent upon overland hydrologic flowpaths which connect urban areas to stream networks. Further analyses were completed to project salinization to a time horizon of 2040 based on expected population growth as well as two anticipated climate scenarios to predict the magnitude of salinization in the Occoquan watershed in decades to come. These results indicated that anticipated levels of in-stream salinity will increase across most sampling stations in coming years. Finally, the analytical framework produced in this research was generated with scalability in mind, such that it can potentially be utilized as a watershed-scale screening tool accross the Mid-Atlantic, to inform proactive, regionally appropriate management decisions.

Understanding spatiotemporal variation in net primary productivity (NPP) continues to be of fundamental importance to basic ecology and to applied conservation and management efforts for human well-being. Diversity is an important driver of NPP variation, but its effect is variable depending on ecosystem context and spatial scale as well as more closely linked to functional traits. Explicitly considering processes of trait-based community assembly and maintenance at relevant scales at which they occur can potentially resolve some of this variation. In my thesis, I address this gap by considering various processes that structure and maintain diversity in communities and analyze NPP as an outcome of these processes. I examine processes in high diversity tropical forests, relatively less explored in the context of biodiversity-ecosystem functioning. In Chapter 1, through a manipulated experiment, I show that diversity effect on biomass gain in seedling communities is modulated by light. This interactive effect holds across different functional groups that are known to respond uniquely to light. In Chapter 2, I expand the spatial scale of inquiry to community assembly processes that maintain diversity at regional spatial scales – dispersal and competition, akin to island biogeographic contexts. Through simulations, I show that dispersal and competition acting on correlated traits explain a range of variation in BEF curves observed in nature. Finally, in Chapter 3, expanding the focus of inquiry to include human aspects, I consider the impact of a biodiversity-driven human intervention, protected areas, in maintaining NPP. I show that at the landscape scale, mean annual NPP and temporal stability are both influenced by protection status, but the effectiveness of protection is contingent on environmental factors. Taken together, my thesis suggests that understanding the combined drivers of diversity and NPP can improve predictions for spatiotemporal variation of this ecosystem function. Further inquiry integrating diversity-gradients at multiple scales can improve process-based understanding of the effect of biodiversity on ecosystem functioning.

With the expansion of underpinning technologies, advanced digital technologies and innovations are transforming many aspects of human daily life, such as education, health, and business productivity. Today, the implementation of digital technologies is considered a characteristic of modern societies. However, while society is becoming increasingly dependent on digital technology and e-innovations in business and trade, the need for paying adequate attention to the societal side of this transformation is also becoming prominent. As a generation setting the future orientation of emerging digital innovations, we hold the ethical responsibility to build an inclusive playground for the current and future generations. Such an ethical responsibility urges attending to societal and humanitarian concerns of the current digital transformation into account. As our perception has evolved over the past decades, we perceive societal consideration as a backbone supporting long-term value creation and equitable welfare. Hence, this PhD thesis investigates the associated societal impact of digital technologies.

To reduce the negative impacts of climate change, electric vehicles (EVs) have emerged as a viable solution in the mobility sector, leading to an increase in battery production and use. For electric vehicle batteries (EVBs) to be sustainable, the total impact of the supply and value chain has to be as low as possible, making the implementation of circular economy (CE) principles a key element in the transition. There is currently limited research regarding circularity implementation in the value chains of EVBs, and especially in developing countries. This thesis explores the key stakeholders in the EVB ecosystem in Nairobi, Kenya, and identifies barriers and enablers for CE implementation. The objective of the thesis is to analyze, based on literature and empirical findings, what activities are deemed necessary to facilitate a circular value chain (CVC) for EVBs in Nairobi. To enable a realistic and thus relatively comprehensive analysis, a case study was conducted involving a literature study, interview study, document review, and workshop. Findings indicate that the Nairobi EVB ecosystem is largely unexplored but that currently, the most important stakeholders can be seen as EV manufacturers and consumers, as well as waste management actors, and second life actors. The key enablers of the ecosystem are government, government agencies, energy providers and suppliers, as well as importers and distributors. The findings indicate the possibility of new essential stakeholders in the future including battery original equipment manufacturers (OEMs), new EV manufacturers and original equipment manufacturers (OEMs), public transport companies, and second life actors. Potential ecosystem enablers include financial actors, research institutions, and insurance companies. Identified barriers and enablers of CE implementation can be divided into five areas, namely technology and infrastructure, supply chain and management, economic, policy and regulation, and social. The findings indicate that barriers identified within the different areas are interconnected, requiring coinciding strategies to be solved and making it difficult to rate them in terms of importance. The findings further suggest that for a CVC for EVBs to be initiated and supported by stakeholders, actors within the ecosystem have to adopt CE strategies to create a closed loop supply and value chain. Battery design needs to enable CE strategies, such as reuse, repair, refurbish, remanufacture, repurpose, and recycle. Furthermore, innovative business models that extend the life cycle of products need to be developed to facilitate the transition to CE. This requires collaboration between the stakeholders in the ecosystem, as well as working with the barriers and enablers identified. To create favorable and enabling system conditions, there is a need for policies and regulations to facilitate the implementation of CE strategies at end-of-life (EoL).

Improved agricultural productivity due to use of fertilizers over the last century has resulted in yield of cash crops, such as corn (Zea mayes L), to be increased on a per hectare basis. Consequently, inadequate fertilizer management such as improper timing or over application has led to infiltration into aquatic environments which can be detrimental to the ecology of such systems. Agricultural systems within the Mississippi River Basin have contributed to large-scale eutrophication in the Gulf of Mexico through surface and dissolved fertilizer loading in upstream tributaries. In response to these concerns, nutrient loss reduction strategies (NLRS), have developed in order to minimize these contributions of eutrophication to aquatic environments. Among adjustments in agricultural practices, one solution is the implementation of cover crops at the end of the cash crop growing season. The primary purpose of cover crops is to increase retention of nutrients during the fall and spring through soil stabilization and nutrient uptake which can prevent erosion and dissolved pathways to fertilizer loading in aquatic environments. Common types of cover crops able to achieve these goals are categorized as winter cereal cover crops (WCCC) and namely, winter cereal rye (Secale cereale) (WCR) is preferred in the state of Illinois. Using WCR has provides addition potential benefits such as cold hardiness establishment, carbon sequestration, weed suppression, and altering hydrological conditions before or during the cash crop. Although there are a variety of benefits from WCR, there are documented tradeoffs due to the presence of WCR, namely, reduced corn yields due to diminished stand population and decreased nitrogen availability through the process of immobilization which results from a carbon to nitrogen ration (C:N) which is greater than 25:1. Our research centered around solutions to maximize benefits of WCR while minimizing negative tradeoffs to the subsequent corn. We hypothesized that reduced seeding rate and higher quality cultivars of WCR would lead to quicker decomposition of biomass (Chapter 1) and would result in corn yields (Chapter 2) that were higher than the alternative treatments of high seeding rates and typical cultivars of WCR. Additionally, we hypothesized that selecting alternative cover crop species such as crimson clover (Trifolium incarnatum), integrating crimson clover with WCR, and reducing seeding rate through precision planting of cover crops off of the corn row would lead to quicker decomposition and result in higher corn yields than the WCR treatment planted normally (Chapter 3). All research was conducted with two site-years for each study. Chapter 1 consisted of two studies (Study A and Study B) where WCR seeding rate was modified and consisted of five treatments of 0, 34, 56, 84, and 112 kg ha-1 of WCR (Study A), and where WCR seeding rate as well as cultivar was modified and consisted of five treatments (Study B). Treatments consisted of an initial no cover crop control and two cultivars, one typical rye considered as “normal” and a hybrid variety (KWS) considered as “hybrid” that were planted at rates of 67 kg ha-1, considered as “low”, and 100 kg ha-1, considered as “high”. The objective of both studies in Chapter 1 was to evaluate the influence of seeding rate (Study A) as well as seeding rate × cultivar had on (i) WCR biomass and nutrient composition, (ii) decomposition and C:N dynamics, and (iii) soil nitrogen dynamics during the growing season in 2021 (Year 1) and 2022 (Year 2). In Study A, it was found that overall biomass was higher as seeding rate increased linearly (R2 = .94) over the two years from 34, 56, 84, to 112 kg ha-1 (2810.43, 3022.14, 3179.89, 3416.52 kg ha-1, respectively). The seeding rate did not influence the rate at which WCR biomass decomposed due to similarities in carbon and nitrogen concentrations within WCR. Fluctuations in C:N ranged from a high of 37:1 at the beginning of the decomposition phase to a minimum of 21:1 by the end of the decomposition phase. Soil NO3-N and NH4-N measured lowest in the 112 kg ha-1 treatment at 15-30 cm in Year 1. Treatments with no cover crop had the highest soil NO3-N from 0-30 cm in Year 2. Overall biomass of WCR was consistently higher during both years in the hybrid WCR treatments at both seeding rates compared to the normal rye of the respective seeding rate. The ratio of carbon to nitrogen was higher in hybrid varieties (42:1) in Year 1 but not in Year 2. The decomposition rate of all WCR in Study B were similar and not influenced by the various treatments. Fluctuations of C:N ranged from a high of 42:1 in the beginning of decomposition to a minimum of 17:1 by the end of the decomposition phase. Estimated N release of all treatments were similar. Both NO3-N and NH4-N were higher in the no cover crop treatment at the end of the season from 0-30 cm during Year 1, while there was no end of year difference in Year 2. In conjunction with the results of Chapter 1, our objectives in Chapter 2 were to see how treatments from Study A and B influenced (i) corn grain yield, (ii) corn stand count, near difference vegetation index (NDVI), leaf area index (LAI), corn N uptake, corn ear composition, as well as end of year N balance, and (iii) to analyze how those components related to overall corn yield. We additionally included how the treatments’ influence on corn could impact soil N dynamics. In Study A, overall corn yield was influenced by WCR seeding rate (p < .05) as the no cover crop and 34 kg ha-1 treatment (11.57, 11.61 Mg ha-1, respectively) were significantly different from the 112 kg ha-1 treatment (10.73 Mg ha-1). Stand count for corn was also influenced by WCR seeding rate (p < .05) as it linearly decreased with increasing seeding rate (R2 = .90) from 70,0009 to 62,552 plants ha-1. The seeding rate influenced the NDVI reading as it was lower in the 84 and 112 kg ha-1 treatments, indicating greater potential soil N immobilization. It was found that yield was most strongly correlated with corn stand count and 1000 kernel weight. In Study B, corn stand count was the only variable influenced by treatment, which was highest in the no cover crop treatment and was lower in the hybrid WCR when compared to the normal WCR at their respective seeding rates. Yield, kernel weight, number, N uptake were all higher in Year 1 and N balance was lower in Year 1. Chapter 3 investigated how cover crop selection, integration, and planting method influenced all of the aforementioned objectives from Chapter 1 and 2. One study made up Chapter 3 (Study C) and consisted of six treatments which were a no cover crop control, WCR monoculture planted at a rate of 67 kg ha-1, crimson clover monoculture planted normally (CNP) at a rate of 28 kg ha-1, crimson clover monoculture precision planted off of the subsequent corn row (CPP) at a rate of 20 kg ha-1, a mixture of the WCR and crimson clover planted normally (RCNP) at a rate of 33 and 22 kg ha-1, respectively, and a mixture of WCR and crimson clover precision planted with crimson clover on the subsequent corn row (RCPP) at a rate of 50 and 7 kg ha-1, respectively. It was observed that overall biomass was driven by presence of WCR but was not significantly different from the mixture treatments in either year. The biomass of crimson clover was not impacted by precision planting, indicating the ability to lower seeding rate. Presence of crimson clover was responsible for the C:N ratio of the treatment as all crimson clover monoculture treatments, aside from Year 1 CNP due to presence of weeds biomass, were lower in C:N (17:1) than all other treatments. Decomposition rate was influenced by cover crop selection as CPP had the highest decay rate of all treatments in both years (-0.00111, -0.00118 in Year 1 and 2, respectively) and RCPP treatment decomposed quicker than WCR in Year 2. The ratio of carbon to nitrogen was lowest for crimson clover monoculture treatments, followed by mixture treatments. By the end of the decomposition phase in Year 1, all treatments had similar C:N ratios indicating biomass decomposition and higher N content in WCR. Year 2 had a lower amount of N concentration in all treatments which influenced C:N ratio of WCR associated treatments. Estimated N release was higher in the mixture treatments as their N content was higher than the WCR monoculture with more biomass than the crimson clover monocultures. Over the two years of the study, crimson clover monoculture treatments resulted in the highest yields (10.16 and 10.11 Mg ha-1 for CNP and CPP, respectively) which were significantly different than the RCPP and WCR treatments, resulting in higher N balances in the RCPP and WCR treatments. Year 2 had lower corn stand count, yield, kernel weight, kernel number, NDVI. Yield was strongly correlated with CSD (.81), diameter (.91) and length (-.91). During both years, soil NO3-N and NH4-N were similar in all treatments by the end of the season indicating uptake by corn. We conclude that in Southern Illinois it may not be fiscally responsible for a grower to use seeding rates over 34 kg ha-1 or hybrid cultivars if their intention is to use WCR as a cover crop before corn in their cropping system. Although the biomass was higher, decomposition was not quicker than lower seeding rate of WCR or typical varieties of WCR. Integrating WCR with crimson clover did not result in lower biomass which may be a practical solution to lowering C:N in the cover crop system, aiding in decomposition so the biomass associated N is able to accessed by corn without being loss to early in the growing season through leaching. Precision planting of cover crops did not impede biomass accumulation which indicates seeding rates and planting design possibilities for WCR, and crimson clover cover cropping systems. Corn stand density was highly impacted by the presence of WCR which indicates the need for adjusting rate and cover crop selection in order to minimize yield reduction in corn.