How can succession be stopped




















Bradshaw, A. The reconstruction of ecosystems. Using natural processes. Wong and A. Bradshaw eds. Christensen, N. Convergence during secondary forest succession. Journal of Ecology — Invasions by alien plants in the Czech Republic: A quantitative assessment across habitats.

Preslia — Collins, B. Forest development, wood jams, and restoration of floodplain rivers in the Puget Lowland, Washington. Restoration Ecology — Csecserits, A. Secondary succession on sandy old-fields in Hungary. Davis, M. Fluctuating resources in plant communities: A general theory of invasibility. Vegetation change: A reunifying concept in plant ecology. Perspectives in Plant Ecology, Evolution and Systematics — Davy, A.

Acidifying peat as an aid to the reconstruction of lowland heath on arable soil: Lysimeter experiments. Diemer, M. Abandonment alters community composition and canopy structure of Swiss calcareous fens.

Diemont, W. Effects of removal of organic matter on productivity in heathlands. Journal of Vegetation Science — Dunsford, S. J, Free. Acidifying peat as an aid to the reconstruction of lowland heaths on arable soil: A field experiment. Eschner, D. Kulturtechnik und Landentwicklung — Esselink, P. Nature management of coastal salt marshes: interactions between anthropogenic influences and natural dynamics. PhD-thesis, University of Groningen. The effects of decreased management on plant species distribution patterns in a salt marsh nature reserve in the Wadden Sea.

Falinski, J. Vegetation dynamics and sex structure of the populations of pioneer dioecious woody plants. Vegetatio — Fukami, T. Species divergence and trait convergence in experimental plant community assembly. Ecology Letters — Gibson, C. The use of sheep grazing to create species rich grassland from abandoned arable land. Giller, K. Acidification and succession in a flood-plain mire in the Norfolk Broadland, UK. Gimingham, C. The Lowland Heathland Management Handbook. Peterborough: English Nature.

Greipsson, S. Coastal dunes. Perrow and A. Grime, J. Plant Strategies and Vegetation Processes. Chichester: Wiley. Grootjans, A. Influence of drainage on N-mineralization and vegetation response in wet meadows. I: Calthion palustris stands. Oecologia Plantarum — Hansson, M. Management of a seminatural grassland; results from a year-old experiment in southern Sweden. Harmer, R. Vegetation changes during years of development of two secondary woodlands on abandoned arable land.

Hauschild, J. Hill, M. Environmental consequences of set-aside land. Report of the Institute of Terrestrial Ecology.

Huntingdon, United Kingdom. Multi-criteria decision analysis in spatial decision support: The ASSESS analytical hierarchy process and the role of quantitative methods and spatial explicit analysis. Environmental Modelling and Software — Hobbs, R. Disturbance, diversity and invasion: Implications for conservation. Conservation Biology — Spoil heaps from brown coal mining: technical reclamation vs. Hodder, K. Translocations of native species in the UK: Implications for biodiversity.

Holl, K. Long-term vegetation recovery on reclaimed coal surface mines in the eastern USA. Restoration of a species-rich flood meadow by topsoil removal and diaspore transfer with plant material. Hunt, R. Expert Systems — Huston, M. Management strategies for plant invasions: Manipulating productivity, disturbance, and competition. Diversity and Distributions — Jasnowski, M. Phytocoenosis — Johnstone, I. Plant invasion windows: A time-based classification of invasion potential.

Biological Review — Joosten, J. Telma — Kirmer, A. Spontaneous and initiated succession on unvegetated slopes in the abandoned lignite-mining area of Goitsche, Germany. The effects of mowing and fertilization on carbohydrate reserves and regrowth of grasses: do they promote plant coexistence in species-rich meadows? Evolutionary Ecology — Disturbance in transplanted grasslands and wetlands. In: Disturbance in Grasslands. Bakker, and R. Snaydon eds. Dordrecht, Netherlands: Junk Publishers, pp.

Koerselman, W. Eutrophication of fen systems: external and internal nutrient sources and restoration strategies. Lammerts, E. Key environmental variables determining the occurrence and life span of basiphilous dune slack vegetation. Acta Botanica Neerlandica — Lonsdale, W. Global patterns of plant invasions and the concept of invasibility. Ecology — Lucassen, E. Effects of stagnating sulphate-rich groundwater on the mobility of phosphate in freshwater wetlands: A field experiment.

Luken, J. Directing Ecological Succession. London: Chapman and Hall. Marrs, R. Vegetation change on lowland heaths and its relevance for conservation management. Journal of Environmental Management — Soil fertility and nature conservation in Europe: Theoretical considerations and practical management solutions.

Advances in Ecological Research — Manipulating the chemical environment of the soil. Primary succession on man-made wastes: The importance of resource acquisition. In: Primary Succession on Land. Miles and D. Walton eds. Oxford: Blackwell, pp. Factors controlling vegetation change in long-term experiments designed to restore heathland in Breckland, UK.

Control of bracken and restoration of heathland. The regeneration of the heathland community after 18 years of continued bracken control or six years of control followed by recovery.

Heathland and acid grassland creation on arable soils at Minsmere: Identification of potential problems and a test of cropping to impoverish soils. An attempt to restore a central European mountain grassland through grazing. McKay, J. What is an example of a practise that conserves plants? Plants can be conserved by seed banks. A seed bank is a store of lots of seeds from lots of different plants. What is an example of a practise which conserves fish? Fishing quotas, limits tot he amounts of fish fisherman are allowed to catch.

What is an example of a practise that conserves animals? Captive Breeding programs. How can an organism be conserved by relocation? Give two examples of conservation areas? National parks and Nature reserves. Name two methods that could be used to conserve species from a tropical rainforest. Relocation Making area a conservation area.

What is the difference between primary and secondary succession? Primary succession occurs where there is no living matter bare rock or land no soil is present. Secondary succession begins with a soil base. Name the species that are the first to colonise an area during succession. Pioneer species. What is meant by a climax community. This is the final stage, the ecosystem is at it's largest and most complex.

Succession occurs in natural ecosystems. Describe and explain how succession occurs. Colonisation by pioneer species ; 2. Climax community;. Managed ecosystems such as wheat fields are prone to pest infestations. Describe the advantages and disadvantages of using biological agents to control pests.

Specific to one pest ; 2. Pests do not develop resistance; 5. Can be used in organic farming;. Changes in ecosystems can lead to speciation. In Southern California 10 years ago a number of interconnecting lakes contained a single species of pupfish. Increasing temperatures caused evaporation and the formation of separate, smaller lakes and streams.

This led to the formation of a number of different species of pupfish. Explain how these different species evolved. Geographical isolation; 2. Variation due to mutation; 4. Leads to change in allele frequency; 8. Occurs over a long period of time;. Glaciers are masses of moving ice.

When glaciers shrink, the thick covering of ice gradually disappears to leave behind bare land. Land exposed by a shrinking glacier in Alaska became covered by dense forest in years. Waterlogged soils lack oxygen. Suggest why trees are unable to survive in waterlogged soils. To calculate a diversity index at a given time, it is necessary to know the number of insects in each population.

Name one method that could be used to estimate the total number of insects in a population. During this stage the number of different species in the habitat and the size of each population remain fairly constant. Explain what limits the size of populations in a climax community. Biologists studied the process of succession in an area of wasteland over a period of ten years.

After three years, the index of diversity was 1. After ten years, it had risen to 4. Increase in number of species; Increase in numbers of some species;. The increase in the index of diversity is one indication that a biological succession is taking place in the area.

Describe those features of a succession that would bring about an increase in the index of diversity. Conservation is the protection and management of species and habitats.

Why is conservation important? How can plants be conserved? National park and protection agencies, do not allow areas on land to be altered. Also seed banks, where lots of seeds from different plant species are stored. Seeds must be regularly checked to see if the are still viable which is expensive, however if any plant was to go extinct in the wild it could be regrown.

Plant species adapted to the sunny conditions and the broken soil will rapidly invade the site and will become quickly and densely established. These invading plants are what we call "weeds". Now "weeds" have very important ecological roles and functions see, for example, the "Winter Birds" discussion , but weeds also compete with the garden plants for nutrients, water and physical space.

If left unattended, a garden will quickly become a weed patch in which the weakly competitive garden plants are choked out and destroyed by the robustly productive weeds. A gardener's only course of action is to spend a great deal of time and energy weeding the garden. This energy input is directly proportional to the "energy" inherent in the force of ecological succession.

If you extrapolate this very small scale scenario to all of the agricultural fields and systems on Earth and visualize all of the activities of all of the farmers and gardeners who are growing our foods, you begin to get an idea of the immense cost in terms of time, fuel, herbicides and pesticides that humans pay every growing season because of the force of ecological succession. There is a concept in ecological succession called the "climax" community. The climax community represents a stable end product of the successional sequence.

An established Oak-Poplar Forest will maintain itself for a very long period of time. Its apparent species structure and composition will not appreciably change over observable time. To this degree, we could say that ecological succession has "stopped".

We must recognize, however, that any ecosystem, no matter how inherently stable and persistent, could be subject to massive external disruptive forces like fires and storms that could re-set and re-trigger the successional process. As long as these random and potentially catastrophic events are possible, it is not absolutely accurate to say that succession has stopped. Also, over long periods of time "geological time" the climate conditions and other fundamental aspects of an ecosystem change.

These geological time scale changes are not observable in our "ecological" time, but their fundamental existence and historical reality cannot be disputed. No ecosystem, then, has existed or will exist unchanged or unchanging over a geological time scale. This site is licensed under a Creative Commons License. View Terms of Use. What is "ecological succession"? Why does "ecological succession" occur?

Are there examples of "ecological succession" on the Nature Trail?



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