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Reveal: new ecologies for an urban stream systemMcDowell, Charles January 1900 (has links)
Master of Landscape Architecture / Department of Landscape Architecture/Regional and Community Planning / Lee R. Skabelund / Throughout the history of Kansas City, the Brush Creek Corridor has experienced severe flooding which, on numerous occasions, has resulted in loss of life. This urban stream supports a high profile area of the city. It is located adjacent to what is considered Kansas City’s most elite shopping district, the JC Nichols Country Club Plaza, the University of Missouri - Kansas City urban campus, as well as numerous high density residential units.
The stream corridor has been confined due to the encroachment of the surrounding urban environment which has minimized many opportunities for the future management of Brush Creek. There have been many flood control projects but these solutions have not been effective in reducing along the entire corridor. Previous projects have been done in a way that alienates urban dwellers from Brush Creek and does not allow pedestrians to utilize the stream corridor as an effective urban green space.
The Brush Creek Corridor can be redesigned to revitalize the existing area by embracing natural ecological processes in order to create a more sustainable urban stream system. Brush Creek can be envisioned in a way that will enhance visitor experience by exposing and revealing the ecological processes to the users without inhibiting the functionality of those natural processes.
Four project goals have been identified through research: improve, connect, and educate. In order to achieve the project goals, a set of sites are to be selected from the corridor. A corridor study is done to identify sites by assessing factors related to the site’s ability to improve, connect, and educate. Once the sites have been identified and defined, programming and site design strategies will be implemented to relate to the project goals.
The selected sites within the Brush Creek Corridor will be models for experience oriented urban stream design. The project area will harbor healthy ecosystems with integrated pedestrian oriented spaces that connect the corridor, improve environmental conditions, and support environmental education. These projects will be catalysts for experience oriented ecological design solutions throughout the Brush Creek Corridor in the future.
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Influence of stream corridor geomorphology on large wood jams and associated fish assemblages in mixed deciduous-conifer forest in Upper MichiganMorris, Arthur E. L. 24 August 2005 (has links)
No description available.
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Insights into the social ecological system of the Golden Stream Corridor Preserve in Belize through the assessment of direct use values and benefitsMesh, Salvador Nigel 17 May 2022 (has links)
The designation of state and private protected areas around the world has been increasing over the past years. Belize is not an exception to this reality. To date more than 103 protected areas have been recognized into the National Protected Areas System of Belize (NPAS). Private protected areas (PPA) did not become part of Belize’s NPAS until 2015. But long before its legislation, private protected areas have been contributing to conservation and development in Belize. The Golden Stream Corridor Preserve (GSCP) is one of Belize’s exemplary PPA which advocates for conservation through the promotion of sustainable livelihood development and community empowerment.
Using the co-evolution model by Pretzsch et al. (2014) as a conceptual framework, direct use values and benefits of the GSCP are assessed to gain insight into its social ecological system. A single case (embedded) case study design was used to execute this assessment at three buffering communities: Medina Bank, Golden Stream and Indian Creek. A total of 60 households, representing 10% of household leaders in each community were interviewed using a semi structured questionnaire. Community leaders were also interviewed to discover customary rules relating to resource use and the history of each community.
The direct use value assessment revealed that the GSCP only contributes to values associated with tourism and employment. These values were disproportionately distributed across buffering communities; with Indian Creek perceiving all values associated with tourism, and Golden Stream from employment. Medina Bank saw no direct use values from the GSCP. Community forests and lands were found to be the exclusive source of direct use values associated with the utilization of forest products. Sustainable livelihood development opportunities and community empowerment were the most reported benefits arising from the management of the GSCP. The adoption and contribution of livelihood strategies were however met with positive and negative criticism by community members.
Results from this evaluation epitomizes the importance of SES thinking in protected areas. Customary rules of resource use have contributed positively to the integrity of the GSCP. The impending threat of land use change and population growth at buffering communities calls for the creation of enabling environments for the adoption of sustainable livelihood through community participation, consultation, monitoring and evaluation.:CHAPTER ONE
1. Introduction 1
1.1 Research question and justification 2
CHAPTER TWO
2. Theoretical and conceptual framework 4
2.2 Ecosystem service approach in protected areas 7
2.3 Emergence of private protected areas: global status, definition, benefits and downsides 11
2.4 Social ecological co-evolution: a conceptual Framework 13
CHAPTER THREE
3.1 National Context: protected areas in Belize 17
3.2 Local context: The Golden Stream Corridor Preserve 19
3.3 Case study approach 23
3.4 Data collection 25
3.5 Data analysis 29
3.6 Ethical considerations 32
CHAPTER FOUR
4. Embedded case studies . 34
4.1 Case study 1: Medina Bank Village 46
4.2 Case study 2: Golden Stream Village 48
4.3 Case study 3: Indian Creek Village 62
CHAPTER FIVE
5. Consolidating and comparing the embedded cases
CHAPTER SIX
6. Implications of findings for management 92
CHAPTER SEVEN
7. Conclusions, limitations and outlook 102
Limitation 103
Outlook 104
REFERENCES 108
ANNEXS 115
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