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Formulating Your Research: Part II

Formulating Your Research: Part II. Barron J. Orr, PhD University of Arizona March 23, 2014. For: Dissertation Writing and Research Series National Graduate Institute for Policy Studies (GRIPS ) Tokyo, Japan. Formulating Your Research (Part II). Conceptual scientific frameworks

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Formulating Your Research: Part II

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  1. Formulating Your Research: Part II Barron J. Orr, PhD University of Arizona March 23, 2014 For: Dissertation Writing and Research Series National Graduate Institute for Policy Studies (GRIPS)Tokyo, Japan

  2. Formulating Your Research (Part II) Conceptual scientific frameworks Knowledge transfer Diffusion of innovation Local vs. scientific knowledge Informal & problem-based learning Participatory research methods

  3. The Value of Frameworks An example of a conceptual framework adapted from Tushman and O'Reilly's Congruence Model, 2002 by Harvard’s Public Education Leadership Project (PELP)http://www.hbs.edu/pelp/framework.html

  4. The value of a conceptual framework • A defined protocol for identifying, developing and refining indicators can provide scientific rigor to the process and help ensure the indicators capture the complexities of the system and provide the information needed for decision making, ideally so that when they are taken together, they can capture the causality in the system among driving forces, state of the environment, and impacts of changes. • This in turn can help decision makers connect the underlying processes with impacts, make linkages to related assessment areas, and ultimately more directly support decision making. • This approach suggests the need for a causality-based conceptual framework as a foundation for monitoring and assessment and the development, refinement and selection of associated indicators.

  5. Conceptual frameworks based on Stress-Response & Demand-Supply • Environmental statistics, or indicators , information categories based on system components help, but are not enough. • The framework should emphasize the causal relationships between forces acting on the environment, associated consequences, and societal response through a set of interlinked indicators • The MA describes desertification as being “…a result of a long-term failure to balance demand for and supply of ecosystem services in drylands.” • Thus, a “balance-sheet” framework tracking changes in ecosystems services is warranted, linking environmental change and human well-being.

  6. Driving Force-Pressure-State-Impact-Response (DPSIR) Source: Niemeijer and de Groot 2008 A number of pressure-response frameworks are similar in that each addresses both the origins and consequences of whatever issue is being conceptualized, but differ in how each subdivides the causal chain. DPSIR is a very commonly used framework.

  7. Driving Force-Pressure-State-Impact-Response (DPSIR) • Driving forces are indirect or underlying factors that result in pressures that in turn cause changes in the quality and quantity or state of the resources. • Pressuresare indirect drivers (stresses) that human activities place on the environment. • State variables are indicators of the condition of the system (including bio-physical and socio-economic factors). • Impacts are the measure of the effects on human well-being induced by state changes. • Responses are the actions or interventions (regulatory and otherwise) that are taken in response to predicted impacts.

  8. Ecosystem Services:An ecologist’s definition “…the conditions and processes through which natural ecosystems, and the species that make them up, sustain and fulfill human life.” Gretchen Daily Nature’s Services 1997 Island Press

  9. Millennium Ecosystem Assessment Categories Protecting Provisioning Cultural Supporting

  10. Dryland ecosystem services Source: Millennium Ecosystem Assessment (2005) Ecosystems and Human Well-Being Desertification Synthesis

  11. MA conceptual framework Source: MA 2005

  12. Panarchy Framework to account for the dual (and seemingly contradictory) characteristics of all complex systems: stability & change Came (in part) from the observation that when systems were managed for a single variable, changes went unnoticed until they triggered an abrupt change (e.g., fisheries collapse)

  13. 4 key characteristics of Panarchy Change is not continuous or gradual, nor continuously chaotic. It is episodic, regulated by interactions b/w fast & slow variables Non-linear processes reorganize resources across levels Multiple equilibriaare common. Management systems must be flexible and adaptive at the appropriate scale levels

  14. Stages of the Adaptive Cycle r: birth/growth/exploitation K: growth/maturation/conservation Ω: destruction/release α: renewal/re-organization -Ω-phase & α-phase allow a system’s structures and processes to be re-organized. This reshuffling allows for the establishment of new system configurations & opportunities for the incorporation of new entrants into the system. The adaptive cycle explicitly introduces mutations & re-arrangements as a periodic process.

  15. Properties of Adaptive Cycles Potential: sets the limits to what it possible Connectedness: amount of internal control, as distinct from external variables Resilience: how vulnerable a system is to unexpected disturbances that can exceed control

  16. Interconnectedness of Levels Revolt: fast variables overwhelm slow ones Remember: potential stored in slow levels influences re-organization

  17. How is Panarchy different? Importance of the adaptive cycle, esp. the α-phase as the engine of variety Connections b/w levels. There are potentially multiple connections b/w phases at 1 level and phases at another level Hierarchies become dynamic structures Attempts to connect ecosystem function w/ economic activities & human institutions Panarchy is both creative and conserving

  18. From Panarchy to Social-Ecological Systems NB: If Panarchyis more of a conceptual framework, the SES framework is more tangible “The answers are not simple because we have just begun to develop the concepts, technology and methods that can address the generic nature of the problems. Characteristically, these problems tend to be systems problems, where aspects of behaviour are complex and unpredictable and where causes, while at times simple (when finally understood) are always multiple. They are non-linear in nature, cross-scale in time and in space. And have an evolutionary character. This is true for both natural and social systems. In fact, they are one system, with critical feedbacks across temporal and spatial scales.” -Holling et al. 1998

  19. Ostrom’s Social-Ecological Systems (SES) Framework • Framework to promote building of knowledge • Organize information to understand structure • Nested, multi-tier framework • Cumulative capacities to diagnose the problems of linked SESs • Ostrom’s background • interest in common property systems • taking traditional economics to task…

  20. Second-tier variable for analyzing an SES Unpacking the SES framework into multiple levels

  21. A Decomposable System Key characteristic that allows scientific progress Conceptual partitioning of variables into classes & subclasses Relatively separate subsystems that are independent in many ways, but eventually affect each other’s performance Complex systems are greater than the sum of their parts Nested systems w/ larger & smaller SESs

  22. Dryland Development Paradigm • The DDP addresses the livelihoods of human populations in drylands, via the study of coupled human-environmental (H-E) systems. • It is a product of a diverse array of research in desertification, vulnerability, poverty alleviation, and community development From Reynolds et al. (2007) based on Stafford Smith and Reynolds (2002).

  23. The DDP is based on 5 principles • H-E systems are coupled, dynamic and co-adapting, so that their structure, function and interrelationships change over time. • A limited suite of ‘slow’ variables are critical determinants of H-E system dynamics

  24. The DDP is based on 5 principles • Thresholds in key slow variables define different states of H-E systems, often with different controlling processes; thresholds may change over time. • Coupled H-E systems are hierarchical, nested and networked across multiple scales • The maintenance of a body of up-to-date local environmental knowledge (LEK) is key to functional co-adaptation of H-E systems

  25. Conceptual representation of degradation framework

  26. Why does it matter?

  27. The Delicate H-E Balance

  28. The key systems of interest are hierarchically structured

  29. If the systems are nested hierarchies, why not the solutions? • At present, mechanisms for feeding influences upwards are usually much more poorly developed than the reverse. • Leads to management decision often disconnected from local realities • Leads to decisions in “silos” • Leads to feelings of powerlessness and policy remoteness, particularly in drylands

  30. Knowledge Transfer

  31. The traditional approach to scientificknowledge transfer S C I E N C E F A C T O R Y The “Loading Dock” Model SocietyPick-Up Source: http://en.wikipedia.org/wiki/File:Warehouse_Loading_Dock.JPG

  32. The traditional approach to technology transfer The “Build it and They Will Come” Model http://www.webspecks.com/Blog_Continue_Aug_Sept_10.htm

  33. Is technology/knowledge transfer a field of dreams?

  34. Typical Environmental Assessment Vision that is, ideally, based on monitoring & evaluation Experts give vision Actions, ideally, based on “best” practices Practitioners/Managers plan and facilitate actions Ideally,both obtain benefit Community/Individuals (Stakeholders) … and the Environment respond

  35. Typical Environmental Assessment Vision that is, ideally, based on monitoring & evaluation Experts give vision Actions, ideally, based on “best” practices Practitioners/Managers plan and facilitate actions Ideally,both obtain benefit Community/Individuals (Stakeholders) … and the Environment respond

  36. Adding science to community engagement… • …however…. is the top-down problem actually solved? Adapted from USDA Forest Service FireScience Application Cycle (2004) http://www.firescience.gov/projects/04-4-2-01/project/04-4-2-01_vw_jfsp_final_report.pdf

  37. Expert-led, top-down approaches • …may be useful biophysically…however… • They also result in a uni-directional flow of knowledge, • which is less likely to result in: • adoption • trustworthy relations • a supportive and well-informed constituency • retention

  38. The technology transfer challenge “Crossing the Valley of Death” is sometimes used in industry to describe the fundamental challenge of transitioning from research to implementation. National Research Council 2000

  39. Successful crossings • Require: • An understanding of the importance (and risks) of the transition • Development and maintenance of appropriate transition plans • Adequate resource provision • Continuous feedback (in both directions) between R&D and operational activities • Making outreach bidirectional: “Inreach” National Research Council, 2000

  40. Formative R&DApproach If research anddevelopmentare adaptive,can allow for midstream adjustment in research plans through continual evaluation and user feedback.

  41. What might theory offer?

  42. Theoretical Framework • Constructivism vs. Positivism • Science in Service for Society (Translational Science) • “High Tech, High Touch” • Two-way Knowledge Exchange • Positive Deviance • Diffusion of Innovations • Local Knowledge • Active Learning • Informal Learning

  43. Positivism vs. Constructivism • The Positivist View • The Constructivist View

  44. Positivism vs. Constructivism • The Positivist View • The nature of reality is regarded as independent of consciousness and objective, and thus can be studied independently of the inquirer. Thus, different observers should arrive at the same conclusions. • The Constructivist View • Reality is essentially subjective, and "truth" is a construction which is located within our experience (historically, culturally, experientially).

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