Group 1 Flashcards

1
Q

Riddle and Haffner 1999

A
  • 15 ESU within a well studied cactus mouse

- traditional concept of species failed to delineate monophyletic set of population

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2
Q

Groom & Palmer 2012

A
  • 2 pilot projects, china and Mozambique of REDD
  • Mozambique: N’hambita Community Carbon Project promotes agroforestry project. Financial benefit to the farmers may be limited but potentially create off-farm employment
  • Pro REDD
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3
Q

Winkel 2012

A
  • Connecting Foucault and forests
  • Review paper of Foucaltalian criticisms/papers of environmental governance
  • Common motivation: how the so-called mainstream knowledge is created
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4
Q

Berglund 2001

A
  • Finnish Forest War
  • Conflict between two powers (Forestry and Conservation) using the same science to fight against each other
  • Example of science as a discursive strategy
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5
Q

Balmford &Cowling 2006

A
  • 10 challenges of conservation
  • Better monitoring and communicating the changing state of nature
  • Assessing and improving the success of conservation interventions
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6
Q

Moyle 2003

A
  • Unexpected consequence of oversimplification in CITES principles
  • E.g. New Zealand blindly proposed to list all the kiwi species on Appendix I thought trades are not the main cause to the vulnerability
  • E.g. Australian parrots sales legal domestically but internationally banned by CITESàthe price skyrocketed in the black market and created incentives to capture/smuggle them
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7
Q

Khanna and Harford 1996

A
  • CITES Critiques
  • Trends in African elephant population vary depending on the country
  • Countries with stable populations were against banning
  • Countries with declining populations and income from tourism wanted banning
  • In Zimbabwe, illegal killing of elephants increased by ten-folds after a total ban in 1990 within a year
  • International regulations should be supplemented by incentives
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8
Q

Gomez-Boggethun et al. 2010

A
  • Different values of ecosystem services
  • Intrinsic value (economic): use value
  • Intrinsic value (biophysical): non-use value
  • Subjective value: exchange value
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9
Q

Hall 1952

A
  • Values don’t exist intrinsically

- Values are independent from facts

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10
Q

Salamon 2002

A

-Tools of governance: regulations, grants, taxes and loans

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11
Q

Goldstein et al. 2012

A
  • Gap between ecological and financial values when ecosystem services fail to be part of the market
  • Incorporating ES values to Land-use Planning
  • E.g. Kamehameha schools in Hawaii
  • Seven scenarios
  • Tradeoffs between environment and financial benefits
  • Tradeoffs between carbon storage and water quality
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12
Q

Costanza et al. 1997

A

-Willingness to pay

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13
Q

Benton et al. 2003

A
  • Heterogeneous landscapes and biodiversity

- Spacial variability acts as a buffer to temporal variability

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14
Q

Dutton et al. 2008

A
  • Modeling farmers’ willingness to practice agroforestry
  • Integrate social and ecological modelling to predict outcomes
  • > 70% of species overlapping in forest and agroforest
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15
Q

Bhagwat et al. 2005

A
  • Quality of matrix is important of habitat islands existing within the matrix
  • Sacred sites
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16
Q

Rodda 1999

A
  • Guam’s tree snakes

- 1/3 of mammals, 50% of reptiles and 90% of birds (decline or extinction?)

17
Q

Doughty et al. 2010

A
  • Climate change and extinction of mammas

- Albedo

18
Q

Moyle 2003

A
  • CITES criticized for its simplicity
  • Differentiating regulation level among member states does not change the demand but provide cheaper routes for smugglers (e.g. Ivory)
  • E.g. New Zealand government’s proposal to list all the kiwi species in Appendix I in 1994 (kiwis are threatened by exotic predictors, not trades)
  • E.g. Australian parrot trade: domestically legal, internationally illegal. Prices skyrocketed in the international market and created additional demand that didn’t exist in the domestic market
19
Q

Kunin 1998

A
  • Two plant species in England
  • Land occupancy change as focal scale changes
    cf. Whittaker lecture 4
20
Q

Joppa and Pfaff 2009

A
  • GIS analysis of existing PA locations
  • Layered PA locations, elevation, slope, and distance from major roads
  • Higher, steeper and far areas from roads: tend to be protected
  • PA protect already remote areas
21
Q

Dudley et al. 2008

A

-Explain IUCN PA categories

22
Q

Boitani et al. 2008

A
  • Criticized IUCN PA categories for being goal-based

- Suggested changing the focus from why protected to what to be protected

23
Q

Riddle and Haffner 1999

A
  • 15 ESU within a well studied cactus mouse

- traditional concept of species failed to delineate monophyletic set of population