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Reinette (Oonsie) Biggs

Reinette (Oonsie) Biggs

Thursday, 29 November 2012 09:13

Settlement of Iceland

Settlement of Iceland

Brief description

Until the arrival of the Norse in AD 871, at the height of the Viking expansion across the North Atlantic, Iceland was a pristine wilderness. The arrival of humans and the sheep, goats, pigs and cattle they brought with them had a profound - some would say devastating - effect on the ecology of the island. Most notably, tree cover collapsed and soils were widely lost to erosion.

Key References

  1. http://www.geog.leeds.ac.uk/study/phd/ecology-and-global-change/human-settlement-and-its-effects-on-lake-and-wetland-ecosystems-in-northern-iceland/
Tuesday, 27 November 2012 15:16

Chesapeake Bay

Chesapeake Bay

Main Contributors:

Reinette (Oonsie) Biggs

Other Contributors:

Summary

The Chesapeake Bay is the largest estuary in the United States, and lies off the Atlantic Ocean, surrounded by Maryland and Virginia.
The bay is mostly known for its seafood production, especially blue crabs, clams and oysters. In the middle of the twentieth century, the bay supported 9,000 full-time watermen, according to one account. Today, the body of water is less productive than it used to be because of runoff from urban areas (mostly on the Western Shore) and farms (especially on the Eastern Shore and in the Susquehanna River watershed), over-harvesting, and invasion of foreign species.
In contrast to harvesting wild oysters, oyster farming is a growing industry for the bay to help maintain the estuary's productivity as well as a natural effort for filtering impurities from the water in an effort to reduce the effects of man-made pollution. 

Type of regime shift

Ecosystem type

  • Marine & coastal

Land uses

  • Urban
  • Large-scale commercial crop cultivation
  • Tourism

Spatial scale of the case study

  • Local/landscape (e.g. lake, catchment, community)

Continent or Ocean

  • North America

Region

  • East Coast

Countries

  • United States

Locate with Google Map

Key References

  1. Boesch, D.F. 2004. Scientific requirements for ecosystem-based management in the restoration of Chesapeake Bay and Coastal Louisiana. Ecological Engineering. 26 (1) pp 6-26

Citation

Reinette (Oonsie) Biggs. Chesapeake Bay. In: Regime Shifts Database, www.regimeshifts.org. Last revised 2012-11-27 15:27:41 GMT.
Tuesday, 27 November 2012 14:30

Irish Potato Famine

Irish Potato Famine

Brief description

Between 1845 and 1850, a potato blight triggered a famine that killed or displaced 25% of the Irish population.  In Ireland, a host of economic, demographic, and social pressures marked the decades leading to the famine and meant that the Irish peasantry had no food options when the potato crop failed. The agro-ecosystem that developed in Ireland prior to the famine had characteristics typical of vulnerable environments: fields were close together, biodiversity was low, and a large amount of biomass made this ecosystem attractive to opportunistic pests. 

Key References

  1. Fraser, E. D. G. 2003. Social vulnerability and ecological fragility: building bridges between social and natural sciences using the Irish Potato Famine as a case study. Conservation Ecology 7(2): 9. [online] URL: http://www.consecol.org/vol7/iss2/art9/
Wednesday, 14 November 2012 09:19

Everglades

Everglades

Brief description

Nutrient and flow management. Management potentially stuck in a rigidity trap - no new ideas are able to take hold, due to vested capital and power dynamics.

Key References

  1. Potential contact: Lance Gunderson
Wednesday, 14 November 2012 09:17

Glen Canyon Dam

Glen Canyon Dam

Brief description

Grand Canyon/Colorado River - Dam caused a large regime shift in ecology, but over time management has been adapted to try to approximate the original regime through water releases etc. Learnign how to do this has been achieved through experimentation & adaptive management.

Key References

  1. Mentioned by Lance Gunderson
Saturday, 10 November 2012 14:39

Hartbeespoort Dam, South Africa

Hartbeespoort Dam, South Africa

Main Contributors:

Reinette (Oonsie) Biggs

Other Contributors:

Summary

Hartbeespoort Dam is a reservoir in the North West Province of South Africa Coordinates. The dam was originally designed for irrigation which is still its primary use. Hartbeespoort Dam has been renowned for its poor water quality since the mid twentieth century (Allanson & Gieskes 1961). The Dam suffers severe eutrophication, resulting from high concentrations of phosphates and nitrates in the Crocodile River, the major inflow. The primary pollution sources are industrial and domestic effluent from Gauteng . The extreme level of eutrophication is evident in the excessive growth of microscopic algae and cyanobacteria, and macrophytes such as water hyacinth (Eichhornia crassipes). The South African Department of Water Affairs and Forestry launched the Harties metsi a me (English: Harties, My Water) programme to try to find solutions to the water quality problems.

Type of regime shift

Ecosystem type

  • Freshwater lakes & rivers

Land uses

  • Urban
  • Large-scale commercial crop cultivation
  • Extensive livestock production (natural rangelands)
  • Tourism

Spatial scale of the case study

  • Local/landscape (e.g. lake, catchment, community)

Continent or Ocean

  • Africa

Region

  • Northwest Province

Countries

  • South Africa

Locate with Google Map

Key References

  1. Allanson BR, Gieskes JMTM. 1961. Investigations into the ecology of polluted inland waters in the Transvaal, Part II: An introduction to the limnology of Hartbeespoort Dam with special reference to the effect of industrial and domestic pollution. Hydrobiologia, 18(1-2): 77-94.
  2. Harding WR, Thornton JA, Steyn G, Panuska J, Morrison IR. 2004. Hartbeespoort Dam Remediation Project (Phase 1) Action Plan Final Report (Volume II). North West Province DACE. Available from: http://www.dwa.gov.za/harties/
  3. Van Ginkel CE, Silberbauer MJ. 2007. Temporal trends in total phosphorus, temperature, oxygen, chlorophyll a and phytoplankton populations in Hartbeespoort Dam and Roodeplaat Dam, South Africa, between 1980 and 2000. African Journal of Aquatic Science 32 (1): 63-70.

Citation

Reinette (Oonsie) Biggs. Hartbeespoort Dam, South Africa. In: Regime Shifts Database, www.regimeshifts.org. Last revised 2012-11-10 14:55:35 GMT.
Tuesday, 06 November 2012 18:46

Aquaculture-related regime shifts

Aquaculture-related regime shifts

Brief description

Aquaculture growth has led to worries about overfishing and reduction in wild-caught food fish supply because of increased demand for fish meal. As such, the price ratio between fish meal and soybean meal has received much attention as an indicator of changing market conditions. In recent years, the price ratio between these two commodities has become more volatile. Several authors have suggested that the traditional relationship between fish meal and soybean meal has broken down and that this is evidence of increased demand pressure on fish meal. In this article, we investigate the hypothesis that there are two regimes for the relative price between fish meal and soybean meal. The empirical results support this hypothesis, with the low-price regime representing the traditional stable relative price. The continued linkages between the fish meal and the soybean meal markets indicate that aquaculture is reducing its dependency on marine proteins in favour of vegetable proteins.

Key References

  1. Asche, F., Oglend, A. and Tveteras, S. (2012), Regime Shifts in the Fish Meal/Soybean Meal Price Ratio. Journal of Agricultural Economics. doi: 10.1111/j.1477-9552.2012.00357.x
Saturday, 20 October 2012 17:12

Goulburn-Broken Catchment, Australia

Goulburn-Broken Catchment, Australia

Main Contributors:

Reinette (Oonsie) Biggs

Other Contributors:

Summary

Around 85% of the native woodland and forest cover has been removed from the mid catchment of the Goulburn-Broken, and 98% from the lower catchment (GBCMA 2003). Anderies et al. (2006b) estimate that the cover of woody vegetation was reduced to below the threshold level needed to maintain the water table below the surface about a decade after clearing began. This threshold is estimated at about 80% vegetation cover in the mid catchment (groundwater in the upper catchment appears not to be connected to water tables in the mid and lower catchment). As water tables rise in response to the reduced vegetation cover, there is a critical threshold at around 2 m below the surface (depending on soil texture). When the water table rises above this, capillary action draws water to the surface. The height of the water table determines the area salinized because of topographic variation, so area salinized and water-table depth are treated as a single threshold. Because of a strong hysteresis effect (tree roots do not function well in saturated soil, so it takes more trees than in unsaturated soil to achieve the same amount of transpiration), more than 80% of the catchment needs to be revegetated to change the trajectory of the system such that the equilibrium water-table depth is below the root zone. As this would affect large areas of dryland farms, pumping is needed in addition to revegetation—the less revegetation, the more pumping (see Anderies et al. 2006b). A constraint is the large volumes of saline water produced. Almost twice as much saline water needs to be pumped if there is no revegetation, which would violate the current salt discharge cap. Revegetation and pumping are both costly. Extracted from Walker et al 2009.

Type of regime shift

Ecosystem type

  • Agro-ecosystems

Land uses

  • Large-scale commercial crop cultivation
  • Intensive livestock production (eg feedlots, dairies)

Spatial scale of the case study

  • Local/landscape (e.g. lake, catchment, community)

Continent or Ocean

  • Australia & New Zealand

Region

  • Murray-Darling Basin

Countries

  • Australia

Locate with Google Map

Key References

  1. Walker, B. H., N. Abel, J. M. Anderies, and P. Ryan. 2009. Resilience, adaptability, and transformability in the Goulburn-Broken Catchment, Australia. Ecology and Society 14(1): 12. [online] URL: http://www.ecologyandsociety.org/vol14/iss1/art12/

Citation

Reinette (Oonsie) Biggs. Goulburn-Broken Catchment, Australia. In: Regime Shifts Database, www.regimeshifts.org. Last revised 2012-11-10 14:25:51 GMT.
Thursday, 18 October 2012 10:13

Seabird populations

Seabird populations

Brief description

What they found was a remarkable global consistency between access to fish and seabird breeding success. Wherever they occurred in the world the effect of low fish was similar. Österblom and his colleagues found that breeding reaches a plateau and does not change even as food abundance increases. When the amount of fish in the sea was greater than one-third of maximum levels of fish, the number of chicks produced remained pretty much unaffected. But if the fish abundance fell below this one-threshold, the number of chicks produced declined. "The global pattern shows a threshold below which the numerical breeding response declines strongly as food abundance decreases," says Henrik Österblom. Österblom and his colleagues also found that breeding reaches a plateau and does not change even as food abundance increases.

Key References

  1. Philippe M. Cury, Ian L. Boyd, Sylvain Bonhommeau, Tycho Anker-Nilssen, Robert J.M. Crawford, Robert W. Furness, James A. Mills, Eugene J. Murphy, Henrik u00d6sterblom, Michelle Paleczny, John F. Piatt, Jean-Paul Roux, Lynne Shannon and William J. Sydeman. 2011. Global seabird response to forage fish depletion u2014 one-third for the birds. Science 334, Issue 6063.
  2. http://www.stockholmresilience.org/research/researchnews/saveathirdforthebirds.5.3f0adc2c1344ec370d380001569.html
Thursday, 18 October 2012 10:05

Shrimp farming in Thailand

Shrimp farming in Thailand

Brief description

We explain how a shift from culture of the black tiger shrimp (Penaeus monodon) to the Pacific white shrimp (Litopenaeus vannamei) took place during 2002-6 in Thailand. We use system innovation theory to help explain how niche substitution led to a regime change within a Thai aquaculture industry trying to maintain international competitiveness but under pressures from a global landscape in which consumers are increasingly concerned with health and ecological sustainability. Support from a vertically integrated major firm, an extensive foundation of learning networks within the industry, and early profitability made the scaling-up and embedding of the experiment with white shrimp very rapid once the formal ban on import of exotic broodstock was lifted. Disease management with domesticated, specific pathogen-free strains of white shrimp has proven much easier than with black shrimp still dependent on capture of wild broodstock. Moreover relative production costs are lower. The switch in species had significant consequences for the environment and firms. Using life cycle analysis we found that rearing white shrimp requires less resource and produces less waste than black shrimp. The shift in regime, however, also made it more difficult for small farms and hatchery businesses.  

Key References

  1. Louis Lebel, Rattanawan Mungkung, Shabbir H. Gheewala, Phimphakan Lebel, Innovation cycles, niches and sustainability in the shrimp aquaculture industry in Thailand, Environmental Science & Policy, Volume 13, Issue 4, June 2010, Pages 291-302, ISSN 1462-9011, 10.1016/j.envsci.2010.03.005. (http://www.sciencedirect.com/science/article/pii/S1462901110000237)
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