This diploma thesis deals with a new approach to the rural development in the EU, which is the LEADER initiative. This initiative is significative by involving of local actors to the rural development, elaboration of coherent strategy of development and the bottom-up approach. First part of this thesis deals with the level of exercise of this principle in two concrete member states. I choosed two very different states for my comparaison: Czech republic as a new member state (2004), which has never used LEADER initiative and France as one of six founders of the EC, a country, where the LEADER initiative has been exercised since it's begginings in 1991. I've concluded my analyse of the implementation of this initiative (or sub-measure of LEADER+ type) by finding, that the bottom-up principle is exercited better in France than in the Czech republic. The selection of projects to be financed by LEADER initiative had to be approved directly by the Ministry of Agriculture of the Czech Republic. The selection in France was done only by local action groups. I've realised a comparative case study of two concrete local action groups LAG Posázaví, o.p.s. (Czech Republic, Středočeský kraj) and LAG Pays d'Albret (France, Aquitane region) in the second part of my thesis. My target was to ratify or disprove a...

This paper uses an exploratory multiple case study research approach to investigate three bottom-up temporary use projects in Malmö. The aim is to provide an understanding of starting processes of temporary use through a project lens with a focus on phases and activities; key stakeholders and motivations; and project key enablers. Regarding temporary use project phases and activities, this study found that there are five steps/phases among the three cases: (1) inspiration; (2) ideation and feasibility; (3) preparation; (4) implementation; and (5) on-going operation. Furthermore, the common key stakeholders found in the projects are founders; landowner; intermediary; authority; temporary user (participant, volunteer, or tenant); researcher; local community; and funding body. Although the stakeholder groups were pretty similar, they engaged in different intensities in different projects. Their different motivations can be grouped in three different groups: personal interest; assigned task; or monetary incentive. Some stakeholders had mixed motivation. Moreover, this paper discovers 14 key project enablers: (1) municipality support; (2) landowner support; (3) intermediary support; (4) financial support; (5) communication & expectation management; (6) network; (7) good planning; (8) community support; (9) openness and engagement; (10) partnership; (11) space and location advantage; (12) project team and entrepreneurial mindset; (13) luck; and (14) influence from the neighbor city. The study recommends creating a municipal temporary use activating unit in order to grow this type of bottom-up movement in the city. This recommendation is in line with the discourse of the researchers in integrating bottom-up temporary use into the strategy and planning level of top-down activities. This research might allow future project leaders to get reference points and guidance for their own bottom-up temporary use projects, as well as provides understanding to researchers who are interested in temporary use and other bottom-up urban development fields.

To lead an organization in change is complex. Leaders today struggle with how to adapt to the digital transformational change organizations are being exposed to. Digitalization forces leaders to go beyond the traditional way of leading when professions are getting automated. This requires leaders to engage subordinates in the leadership to handle a transformational change since both subordinates and leaders are expected to adapt to technological development. Here is when the role of shared leadership becomes preferable. To investigate this complexity in the banking industry, a case study has been done. A qualitative method was used to collect and analyze the data needed to understand what leaders do to engage subordinates in the transformational change the banks are being exposed to. The results indicate that the leaders to some extent take advantage of shared leadership to involve subordinates. The findings could be applied to the shared leadership model, and the analysis shows that leaders tend to use all components to engage their subordinates, and all components are proven to be equally important. But, the analysis also shows that the banks still face challenges with being hierarchical, which inhibits the subordinates to be completely involved and engaged in the leadership. Conclusions have been made that the leaders believe they engage subordinates in transformational change, whereas not all subordinates perceive it that way.

Die vorliegende Ausgabe beschäftigt sich mit dem Thema Umweltkennzahlensysteme für die Umweltleistungsmessung. Ziel der Arbeit ist es, Unternehmen ein Hilfsmittel zur Integration von Umweltaspekten ins allgemeine Unternehmensgeschehen an die Hand zu geben. Angestrebt ist die Konzeption eines Umweltkennzahlensystems zur Umweltleistungsmessung für Prozesse. Im ersten Schritt wird ein Öko-Controlling-Modell vorgestellt und Umweltkennzahlensysteme in dieses eingeordnet. Umweltkennzahlensysteme sind der Informationsversorgung zuzurechnen. Sie dienen der Information der Informationsverwender, die mit ihrer Hilfe Planen, Steuern und Kontrollieren sollen. Es wird ein Anforderungsprofil für Umweltkennzahlensysteme erstellt, dieses Anforderungsprofil beinhaltet allgemeine Anforderungen, wie die ?Anforderungen der Informationsverwender? und ?formale und logische Anforderungen? und spezielle Anforderungen. Vorhandene Ansätze zu Umweltkennzahlensystemen werden vorgestellt und hinsichtlich des Anforderungsprofils analysiert. Aus dieser Analyse ergibt sich der Schluss, dass es kein Umweltkennzahlensystem gibt, das alle Anforderungen erfüllt. Die Auswertung der an ausgewählte Führungskräfte der SIEMENS AG verschickten Fragebögen zu Umweltkennzahlen bestätigt die gewonnene Aussage der Nicht-Existenz einer first-best-Lösung hinsichtlich eines Umweltkennzahlensystems für alle Unternehmen, da sie verdeutlicht, dass schon die Kennzahlensysteme innerhalb eines Unternehmens stark (aufgrund zu unterschiedlicher Strukturen, Ziele und Strategien) differieren. An die Auswertung der Analyse der vorhandenen Ansätze und der Fragebögen schließt sich die Entwicklung einer Vorgehensweise zur Konzeption von Umweltkennzahlensystemen in Unternehmen an, die in den Schritten Festlegung der Umweltleistung von Unternehmen, Definition der Zielebene, Festlegung und Auswahl von Kennzahlen abläuft.

Increasing storage for energy is one of the most important challenges today to overcome in order to enable higher penetration of renewable energy in the existing energy systems. Thermal storage is one category of energy storage that has been successfully demonstrated in a number of engineering projects and is showing promising potential in the future. However, a technology cannot be widespread if it is not economically feasible and sustainable in the long run. Bottom up cost analysis can be used to assess economic viability of a technology. For newer technologies, the top-down cost calculation is not always possible due to the limited amount of data. The aim of this thesis is to investigate the best practices in performing bottom up cost calculation and to propose a methodology with the purpose of enabling it to be implemented over thermal energy storage bottom up economic evaluations. To achieve this, two proven applications, molten salt storage for concentrated solar power and ice thermal storage for building cooling, were examined as the basis of the bottom up state of the art calculation models. It was found that in the ice storage case, the models were often done in a hybrid bottom up-top down approach which limits a fully detailed cost analysis. Instead these are referred as case studies instead because of the few elements needed in their calculation. The constructed specialized models and case studies are then compared against other external sources to validate the proposed economic analysis procedure. The numerical results showed some discrepancies when compared to external resources. A compilation of a general bottom up cost model with detailed step by step model to perform a bottom up calculation for thermal storages is finally proposed in this work. / Att förbättra möjligheterna att lagra energi är en av dagens viktigaste utmaningar för att kunna öka andelen förnybar energi i vårt energisystem. Termisk energilagring eller värmelagring är en typ av energilagring som använts framgångsrikt i flera områden och visar hög potential i ett flertal ytterligare teknologier. En teknologi kan dock inte få en omfattande påverkan om den inte är ekonomiskt hållbar. En bottom-up kostnadsanalys kan användas för att uppskatta genomförbarheten för teknologin. För nya teknologier är en top-down kostnadsanalys inte alltid möjlig, vilket är beroende på den begränsade tillgången till data. Syftet med den här uppsatsen är att undersöka de vanligaste tillvägagångssätten i att utföra en bottom-up kostnadsanalys och föreslå en metodologi som har ändamålet att användas i bottom-up kostnadsanalyser för värmelagringstekniker. För att uppnå detta har två beprövade tekniker, smält saltlagring i koncentrerad solkraft och islagring för kylning av byggnader, undersökts som modeller för moderna bottom-up kostnadsanalyser. Efter undersökning fann man att i islagringsteknologi genomförs kostnadsanalysen vanligen i ett hybrid bottom up-top down upplägg, vilket begränsar möjligheten att rekonstruera en fullt detaljerad bottom-up kostnadsanalys. Dessa kommer istället att refereras som fallstudier eftersom endast ett fåtal objekt behövdes i en kostnadsberäkning. Specialiserade kostnadsmodeller som konstruerats och fallstudier jämförs med externa källor för att bekräfta den föreslagna analysproceduren för kostnadsberäkningar. Jämförelsen med externa källor visade viss spridning i numeriska resultat. En sammanställning av en generell bottom-up kostnadsmodell med detaljerad steg för steg-beskrivning för att genomföra en bottom-up kostnadsanalys är dessutom föreslagen i detta arbete.

The introduction and establishment of exotic species can profoundly alter ecosystems. Two exotic species drastically changing the landscape of deserts in western North America are Bromus tectorum L. and Bromus rubens L. Through the buildup of biomass and slow decomposition rates in deserts these two exotic annual grasses can alter fire regimes that change the plant and animal community dynamics in the ecosystems. To better understand the ecological mechanisms that could restrict or alter the patterns of invasive plant establishment we established a replicated full factorial experiment in the Great Basin and Mojave Desert. The combinations of factors being manipulated are burned or intact plant communities, and presence or exclusion of small mammals. Generally invasive species establishment is thought to be a result of competitive superiority or lack of natural enemies, but if that is the case then why do not all invasive species establish and become highly abundant in their new ecosystems? To understand why some invasive species establish and others do not we monitored three dominant exotic species from the Great Basin and the Mojave Desert, B. tectorum, Halogeton glomeratus (M. Bieb.) C.A. Mey., and B. rubens. We observed that the presence of small mammals create a biotic resistance to B. tectorum, H. glomeratus, and B. rubens. This pattern was observed in both intact and burned plant communities; however, it was most prevalent in the burned plant communities. The strength of the biotic resistance on these invasive species varied between species and the years sampled. In deserts both plant and small mammal communities are tightly tied to precipitation. We wanted to understand how invasive species establishment is affected by small mammal presence after a fire disturbance, and manipulating total precipitation. Total precipitation was manipulated through three different treatments: 1) drought or 30% reduction of ambient precipitation; 2) ambient precipitation; 3) water addition or an increase of 30% ambient precipitation. We focused on B. rubens establishment in the Mojave Desert as our model organism by monitoring it beneath rain manipulation shelters nested in burned/intact and small mammal presence/absence full factorial plots. What we observed was that again small mammals created a biotic resistance on the density of B. rubens regardless of the burn or precipitation treatments. This biotic resistance also translated into decreasing B. rubens biomass and seed density. Under the drought and ambient precipitation treatments we found that small mammals kept the density and biomass equal but under increased precipitation the efficacy of biotic resistance on B. rubens density and biomass was lessened by the availability of the added water.

There is a plethora of methods and tools that can be used for the assessment of Urban Metabolism. Nevertheless, there is no standardized method for accounting of material flows within and across the boundaries of urban systems. This thesis aims to provide a physical accounting model for monitoring material flows in urban areas that could potentially become the basis for the development of a standardized accounting method in the long term. The model is based on a Physical Input Output Table framework and builds upon the strengths of existing accounting methods but at the same time it demonstrates new features that can address their limitations. The functions of the model were explored and evaluated through its application to an urban neighbourhood in the Stockholm Royal Seaport. Bottom-up data were used for the application of the model in the case study. The application of the model provided a preliminary description of the material flows in the neighbourhood and most importantly provided information that underpinned the assessment of the strengths and limitations of the model. It was deduced, that on the one hand the model can describe successfully the physical interactions between the urban socioeconomic system and the environment or other socioeconomic systems and at the same it has the potentials to illustrate the intersectoral flows within the boundaries of the system. In addition, it can be used to structure available data on material flows and promote the study of an urban system with a life cycle perspective. On the other hand, the process of compiling the tables of the model can be considered as complex and moreover the data requirements for the compilation of the tables are significant. Especially, the compilation of the tables of the model with bottom-up data may require a laborious data collection and analysis process, which however may not address all data gaps. Thus, the combination of bottom-up data with top-down data is recommended. Moreover, it is recommended the development of integrated databases for data collection and management at the municipal level and the fostering of collaboration between stakeholders within the municipalities to facilitate dissemination of data and information. / Mer än hälften av den globala befolkningen bor numera i urbana områden och denna andel uppskattas öka under de kommande årtiondena. Urbana system förbrukar fysiska resurser och genererar stora mängder av rester vilket innebär påfrestningar på miljön samt hindrar en hållbar utveckling. Således kan förståelse av Urban Metabolism (UM) stödja insatserna för att effektivisera resursförbrukningen och avfallshanteringen. I detta sammanhang har en stor mängd av metoder och verktyg utvecklats och tillämpats i UM-studier, såsom Materialflödeanalys (Material Flow Analysis - MFA) och Input-output Analys (Input Output - IOA) baserat på fysiska input-output tabeller (Input Output Tables – PIOTs). Ändå saknas en standardiserad metod för redovisning av materialflöden inom och över gränserna av urbana system. I samband med detta examensarbete utvecklades en fysisk räkenskapsmodell för övervakning av materialflöden i urbana områden. Denna modell kan potentiellt bli grunden för en enhetlig metod för beräkning av materialflöden i urbana system. Modellen utvecklades i en stegvis process och baserades på litteraturgranskning. Grunden för modellen är ett omfattande PIOT ramverk som kan användas för registrering av materialflöden i urbana system. PIOT ramverket är annorlunda än de typiska PIOT-systemen. Det ger en tydligare avgränsning av systemgränserna, det visar tydligt ursprung och destination för materialflöden, och dessutom kan det erbjuda ett livscykelperspektiv på materialflödena. Modellen består av en uppsättning identiska PIOT. Varje deltabell innehåller materialflöden som tillhör i en specifik klass, medan huvudtabellen aggregerar materialet som strömmar för alla material från deltabellerna. Därigenom kan modellen avbilda materialflödena i ett aggregat-perspektiv och samtidigt ge fysiska räkenskaper för specifika materialtyper. Modellen användes i en nybyggd stadsdel i Norra Djurgårdsstaden (NDS), för att utforska och bedöma dess funktioner. För att kartlägga och kvantifiera flödena i stadsdelen genomfördes en MFA baserad på “bottom-up-data”. Insamlingen och analysen av data var emellertid en besvärlig process och dessutom kunde flera materialflöden inte kvantifieras på grund av databrister. Därför kunde modellens tabeller inte fyllas fullständigt och ett flödesdiagram skapades med både kvantitativa och kvalitativa flöden. Trots att det fanns databrister lyckades tillämpningen av modellen att avbilda UM i det avgränsade urbana systemet på ett adekvat sätt. Det visade tydligt att nästan 96% av de materiella insatserna är ackumulerade i lager. Dessutom fastställde modellen kvalitativt den fysiska växelverkan mellan det urbana systemet och den naturliga miljön, det nationella socioekonomiska och det globala socioekonomiska systemet. Emellertid var det inte möjligt att bedöma modellens fullständiga potential eftersom det inte var möjligt att upprätta intersektorala kopplingar. Dessutom beräknades indirekta flöden av flera importerade material baserat på koefficienterna för materialintensitet. Detta tillvägagångssätt kan erbjuda insikt om de uppströms påfrestningar som orsakas av materialproduktionen. Dock finns det endast koefficienter för specifika material. Därför kan de inte användas för att uppskatta de indirekta flödena för varje materialinflöde. Dock framhöll deras partiella tillämpning att indirekta flödena var 38% högre än direktflödena, vilket indikerar att påfrestningar som utövas till miljön på grund av produktion av importerade material är betydande. Tillämpningen av modellen möjliggjorde en bedömning av både styrkor och svagheter hos modellen. Å ena sidan kan modellen fastställa fysiska interaktioner mellan det urbana socioekonomiska systemet och naturmiljön, det nationella socioekonomiska systemet och det globala socioekonomiska systemet. Dessutom har det potential att beskriva intersektorala flöden inom gränserna för det urbana systemet och det kan erbjuda insikt om materialinflödenas ursprung och materialutflödenas destination. En annan styrka i modellen är att den erbjuder livscykelperspektiv genom att ta hänsyn till indirekta flöden av importerade material. Å andra sidan demonstrerades att sammanställningenav modellens tabeller kräver en stor mängd data, speciellt när data erhålls med ett ”bottom-up” tillvägagångssätt. Ändå är bottom-up data inte alltid tillgängliga för urbana områden. En annan svaghet är att sammanställningenav tabellerna i modellen med bottom-up-data kräver en mödosam process för datainsamling och analys. Dessutom kräver analysen av data många antaganden som ökar osäkerheten i resultaten. Ovanstående svagheter i modellen kan hindra tillämpningen av modellen för räkenskap av materialflöden på urbana områden. Således rekommenderas kombinationen av bottom-up-data med top-down data för tillämpning av modellen. Dessutom föreslås utvecklingen av integrerade databaser för datainsamling om materialflöden i urbana områden.

A quantitative assessment of food-water-energy interactions is important to assess pathways and scenarios towards a holistically sustainable regional development. While a range of tools and methods exist that assess energetic demands and potentials on a regional scale, the same is not true for assessments of regional food demand and potential. This work introduces a new food simulation workflow to address local food potential and demand at the regional level, by extending an existing regional energy-water simulation platform. The goal of this work is to develop a GIS-based bottom-up approach to simulate regional food demand that can be linked to similarly GIS-based workflows assessing regional water demands and energetic demands and potentials. This allows us to study food-water-energy issues on a local scale. For this, a CityGML land use data model is extended with a feed and animal potential raster map as well as a soil type map to serve as the main inputs. The workflow simulates: (1) the vegetal and animal product food potentials by taking climate, crop type, soil type, organic farming, and food waste parameters into account; (2) the food demand of vegetal and animal products influenced by population change, body weight, age, human development index, and other indicators. The method is tested and validated in three German counties with various land use coverages. The results show that restricting land used exclusively for energy crop production is the most effective way to increase annual food production potential. Climate change by 2050 is expected to result in annual biomass yield changes between −4% and 2% depending on the region. The amount of animal product consumption is expected to rise by 16% by 2050, while 4% fewer vegetal products are excepted to be consumed.

Structurally precision graphene nanoribbons (GNRs) have attracted great interest considering their prospective applications as organic carbon materials for nanoelectronics. The electronic properties of GNRs not only critically depend on the edge structure and width but also on the heteroatom type, doping position, and concentration. Motivated by the recent undisputable progress in the synthesis of stable boron-doped polycyclic aromatic hydrocarbons (B-PAHs), considerable efforts have been devoted to the precision synthesis of the corresponding boron-doped GNRs (B-GNRs) via bottom-up synthesis approach in recent years in view of the extraordinary ability of boron doping on modulating their physiochemical properties. In this review, an overview of the bottom-up organic synthesis of B-GNRs, including the precursor design and synthesis, structure characterization of the resulting B-GNRs, and investigation of their electronic properties is provided. Moreover, the future challenges and perspectives regarding the bottom-up synthesis of B-GNRs are also discussed. The authors hope that this review will further stimulate the synthesis and device integrations of B-GNRs with a combined effort from different disciplines.

Thèse numérisée par la Direction des bibliothèques de l'Université de Montréal. / Un des défis actuels en écologie du plancton est de déterminer la contribution relative des processus abiotiques et biotiques dans le contrôle environnemental des communautés planctoniques selon différentes échelles spatiales et suivant un continuum d'hétérogénéité environnementale. Cette thèse répond à ces attentes et vise deux principaux objectifs: (1) déterminer l'hétérogénéité spatiale de la biomasse et de la structure en taille des communautés planctoniques aux échelles intra- et inter-lacs; (2) évaluer la contribution relative des facteurs environnementaux ascendants "Bottom-Up" et/ou descendants "Top-Down" à l'origine de cette hétérogénéité. Afin de répondre à ces objectifs, quatre études ont été réalisées à différentes échelles spatiales intra-lac et inter-lacs. A l'échelle intra-lac, nous avons déterminé dans un lac de tourbière l'influence de la prédation par les invertébrés (Chaoboridae) et de la physico-chimie des eaux sur la distribution horizontale et verticale de la biomasse zooplanctonique et sur sa structure en taille (Chapitre 1). Dans le lac Geai, l'hétérogénéité du zooplancton était aussi importante sur l'axe horizontal que vertical. La prédation était le facteur le plus important influençant la répartition horizontale et verticale du zooplancton. La taille et la densité des Chaoboridae, ainsi que la conductivité des eaux influençaient la répartition horizontale du zooplancton dans le lac. Sur l'axe vertical, la biomasse zooplanctonique diminuait avec la profondeur. Le zooplancton évitait les eaux hypolimnétiques froides et anoxiques où se retrouvaient de fortes densités de gros prédateurs Chaoboridae. La seconde étude à l'échelle intra-lac avait pour objectif d'évaluer dans un lac subalpin les effets de la prédation par les juvéniles de perche (Perca fluviatilis) sur la distribution horizontale et verticale des daphnies et des copépodes cyclopoïdes au cours d'un cycle jour-nuit (Chapitre 2). La répartition horizontale et verticale du zooplancton était inverse à celle des poissons. Sur l'axe vertical, le zooplancton était situé de jour dans l'hypolimnion évitant ainsi la prédation par les juvéniles de perche situés dans les eaux épilimnétiques. Une forte opposition horizontale a été identifiée autant de jour que de nuit. La majorité de la densité zooplanctonique a été enregistrée en zone littorale, tandis que la biomasse de perche était principalement pélagique. Nous avons proposé l'hypothèse que la répartition inverse horizontale et verticale du zooplancton face à leur prédateur était due à la prédation des poissons, ainsi que par leur comportement d'anti-prédation (migrations horizontale et verticale). Au cours de la nuit, les cyclopoïdes qui constituaient le principal item du régime alimentaire des perches, étaient plus abondants dans les eaux métalimnétiques plus froides qui étaient évitées par les jeunes perches. A l'échelle inter-lacs, nous avons testé l'influence de la géologie sur la relation phosphore-chlorophylle a (Chapitre 3). Des modèles phosphore-chlorophylle a déterminant la réponse quantitative de la biomasse algale totale et pour 4 classes de taille (< 3 pin, 3 - 20 pm, < 20 pm, et> 20 pm) face aux gradients de TP ont été établis pour les lacs du sud du Québec. Nous avons finalement évalué l'influence d'autres paramètres physicochimiques sur ces relations. Les lacs étudiés reposait sur un socle granitique caractéristique du bouclier canadien. Ces lacs présentaient des concentrations en chlorophylle a plus faible par unité de phosphore que les lacs retrouvés sur des socles sédimentaires. Les lacs les plus productifs étaient dominés par des algues de grandes tailles (>20 pm), tandis que les algues de petites tailles (< 20 pm) étaient plus abondantes dans les lacs de type oligotrophe. L'identification de l'alcalinité comme variable complémentaire à nos modèles de prédiction a permis de proposer l'hypothèse d'un contrôle algal par broutage par le gros zooplancton herbivore dans les lacs plus productifs et alcalins. Les sources de variations spatiales de la biomasse zooplanctonique ont été quantifiées aux échelles intra- (entre les strates) et inter-lacs (entre les lacs) (Chapitre 4). L'influence des facteurs environnementaux abiotiques et biotiques "Bottom-Up" et "TopDown" sur les variations de la biomasse et de la structure en taille du zooplancton (53-100 pm, 100-202 pm, 202-500 pm, > 500 pm) ont été évalués dans les 3 strates limnétiques des lacs du sud du Québec. La variation de la biomasse zooplanctonique était plus importante entre les lacs qu'entre les strates d'un même lac. Cependant, les variations entre les strates n'étaient pas constantes d'un lac à l'autre. Les facteurs "Bottorn-Up" ont été identifiés comme la plus importante source de variation épilimnétique de la biomasse zooplanctonique entre les lacs. Les facteurs "Top-Down", soit la présence ou l'absence de piscivore dans les lacs, expliquaient la structure en taille des communautés zooplanctoniques ainsi que leur variation verticale (entre les strates). Les lacs où les piscivores étaient absents (dominance des planctivores) présentaient des communautés zooplanctoniques dominées par des petits individus. L'ensemble de ces résultats permet de conclure que l'hétérogénéité des communautés planctoniques augmentent avec l'échelle d'observation. A petites échelles (intra-lac, inter-strates), les facteurs biotiques (prédation) exercent un contrôle sur les communautés planctoniques, tandis qu'à plus grandes échelles (inter-lacs), ce sont les facteurs abiotiques (physico-chimie et morphométrie) qui expliquent en premier lieu la variabilité du plancton. La complémentarité des facteurs abiotiques et biotiques "BottomUp" et biotiques "Top-Down" dans le contrôle des communautés planctoniques est omniprésente quel que soit l'échelle d'observation.