Plant communities – Characters, Ecotone and edge effect, Succession, Processes and types

What are Plant communities?

  • A plant community refers to a specific assembly of plant species within a defined geographical area, forming a relatively uniform patch that stands apart from adjacent patches with different vegetation types. The characteristics of a plant community are influenced by various factors, including soil type, topography, climate, and human activities. These factors interact to create diverse plant communities across different environments.
  • Soil type plays a crucial role in shaping plant communities. Variations in soil properties, such as moisture levels and organic matter content, affect the types of plants that can thrive in an area. Soil moisture is determined by the rate of water infiltration and evapotranspiration, while organic matter dynamics are influenced by decomposition processes and organic input.
  • Ecologists study plant communities to understand how plant species interact with their environment. These studies provide insights into species dispersal patterns, environmental tolerance, and responses to disturbances. This information is essential for comprehending the dynamics of various plant communities.
  • Plant communities can be described both floristically and phytophysiognomically. Floristic descriptions focus on the species present within the community, while phytophysiognomic descriptions emphasize the physical structure and appearance. For instance, a forest community includes various layers such as the overstory, consisting of tall trees; the understory, which includes shrubs and smaller trees; the herbaceous layer, composed of small vascular plants; and sometimes the moss layer, consisting of non-vascular plants close to the ground.
  • The concept of a plant community is similar to that of a vegetation type but with a greater emphasis on the ecological interactions among species. Vegetation types are often characterized by their general appearance, whereas plant communities focus on the specific associations of species and their ecological relationships.
  • Interestingly, a plant community can be considered rare even if its constituent species are not. This rarity can stem from the unique combination of species and their specific environmental conditions. For example, the sycamore alluvial woodland in California, dominated by the California sycamore (Platanus racemosa), is a rare community despite the California sycamore being relatively common in the region. The rarity is attributed to the unique association and localized nature of the plant community rather than the rarity of the individual species.

Definition of Plant community

A plant community is a group of plant species that coexist and interact within a specific geographical area, forming a distinct and relatively uniform vegetation patch.

Examples of Plant community

  1. Northern Caucasus Steppes
    • Grassland: This plant community features a diverse mix of grass and herbaceous species. Key grasses include Festuca sulcata and Poa bulbosa. The dominant species is Carex shreberi, which characterizes the grassland phytocoenosis. Additionally, forbs such as Artemisia austriaca and Polygonum aviculare are common in these steppe grasslands.
  2. Huangshan Mountains, Eastern China
    • Deciduous Broad-Leaved Forest: Located at elevations above 1,100 meters, this forest community includes trees like Pinus hwangshanensis (Huangshan pine).
    • Evergreen Broad-Leaved Forest: Found at various elevations on the Huangshan Mountains, this community is rich in shrubs and small trees. Notable species include Castanopsis eyrei, Eurya nitidia, Rhododendron ovatum, Pinus massoniana, and Loropetalum chinense.
  3. Central Westland, South Island, New Zealand
    • Podocarp/Broadleaf Forests: This extensive plant community features three distinct layers:
      • Canopy: Includes large trees such as Prumnopitys ferruginea, rimu, and mountain totara.
      • Mid-Story: Dominated by tree ferns like Cyathea smithii and Dicksonia squarrosa.
      • Lowest Tier and Epiphytes: Includes species such as Asplenium polyodon, Tmesipteris tannensis, Astelia solandri, and Lomaria discolor.

Characteristics of Plant Communities

Plant communities exhibit various characteristics that can be broadly categorized into analytic and synthetic types. Understanding these characteristics is essential for analyzing plant community structure and dynamics.

1. Analytic Characters

These are directly observed or measured in sample plots and include the following:

  • Qualitative Characters: These are non-quantitative observations and include aspects such as species composition and vegetation stratification. They describe the types and arrangements of plant species without numerical values.
  • Quantitative Characters: These involve numerical measurements and include several key attributes:
    • Frequency: The percentage of sample plots where a species is present, indicating its spatial distribution. It is calculated using the formula:
Frequency
    • Diversity: This reflects the number of individuals per unit area, indicating species richness and relative abundance.
    • Cover and Basal Area: Cover refers to the percentage of land area occupied by a species, usually above ground. Basal area, measured at 2.5 cm above ground or at ground level, helps determine species dominance.
    • Biomass: Represents the weight of living material per unit area, indicating the growth and productivity of species.
    • Leaf Area: Describes the distribution of leaf sizes among species, reflecting adaptations to environmental conditions.
    • Density: The number of individuals of a species per unit area, providing insight into competition. Calculated as:
Plant Communities
    • Abundance: The number of individuals per sampling unit, calculated as:
Plant Communities

2. Synthetic Characters

These are derived from the analysis of analytic characters and provide a comprehensive view of the plant community. They include:

  • Presence and Constance: Measures the extent to which a species is present throughout the community.
  • Fidelity: Indicates the degree to which a species is restricted to a specific type of community. Such species are known as indicators.
  • Dominance: Expressed in a synthetic form, often through the Importance Value Index (IVI). The IVI integrates relative density, frequency, and dominance (cover) to reflect a species’ overall significance in the community. The IVI is calculated as:
Plant Communities

These characteristics collectively help in understanding the structure, dynamics, and ecological roles of plant communities.

What is Ecotone?

An ecotone is a transition zone between two distinct ecosystems or biomes. This area serves as a boundary where different biological communities meet and interact. For instance, a marshland between a river and its bank is an ecotone, blending characteristics from both the aquatic and terrestrial environments.

Ecotones are significant due to their high biodiversity. They often support a wide array of species from the adjacent ecosystems, as they are influenced by the environmental conditions of both. Examples include marshlands (between dry and wet environments), mangrove forests (linking terrestrial and marine systems), and estuaries (where saltwater meets freshwater).

The structure of an ecotone can vary. It may be a narrow strip or a broader region, with boundaries that are either gradual or distinct. For instance, the transition between a field and a forest can be a local ecotone, while the shift from forest to grassland represents a regional ecotone. Ecotones can also form in mountain ranges due to climatic variations across different elevations.

The term “ecotone” was first coined in 1904 by Frederic E. Clements, combining “ecology” with the Greek word “tonos,” meaning tension. This term reflects the dynamic interaction and integration occurring at these transitional zones.

Characteristics of Ecotone

  • Width Variability: Ecotones can vary greatly in width. They may be narrow, such as the transition zone between a grassland and a forest, or wide, such as the area between a forest and a desert. The width depends on the scale of the ecosystems they connect.
  • Intermediate Conditions: Ecotones exhibit conditions that are intermediate between the adjacent ecosystems. This results in a “zone of tension,” where the environmental conditions are not typical of either adjoining ecosystem but instead represent a blend.
  • Species Composition: The species composition within an ecotone can be unique compared to the adjacent communities. As one moves away from the core of a community or ecosystem, the number and density of its species generally decrease. However, a well-developed ecotone may host organisms that are distinct from those in the bordering systems.
  • Distinct Flora and Fauna: Ecotones often contain species that are not found in the adjoining ecosystems. This diversity arises due to the blending of environmental conditions and the ecological interactions that occur at the boundary.
  • Natural and Man-Made Examples: Ecotones can be natural, such as those formed by the transition between a wetland and a forest, or man-made, like the area between an agricultural field and a forest. Both types serve similar ecological functions but differ in their origins and impacts.

Importance of Ecotone

  • Biodiversity Hotspots: Ecotones are rich in biodiversity. They often host a greater variety of organisms compared to the adjacent ecosystems. This increased diversity arises from the merging of species from both bordering ecosystems and the unique conditions present in the transition zone.
  • Habitat and Nesting Sites: These transitional areas provide valuable habitats for various species. They offer suitable nesting places and resources for animals that move between different ecosystems. This makes ecotones crucial for the survival and reproductive success of many species.
  • Gene Flow and Genetic Diversity: Ecotones facilitate gene flow between populations. The diverse array of species in these areas promotes genetic exchange, which enhances the genetic diversity of populations. This increased genetic variation is vital for the adaptability and resilience of species.
  • Buffer Zones: Ecotones can serve as natural buffer zones. For instance, wetlands within an ecotone can absorb pollutants, preventing them from contaminating adjacent rivers. This buffering function helps protect the health of bordering ecosystems from environmental stressors.
  • Indicators of Climate Change: Ecotones are sensitive to environmental changes and serve as indicators of global climate change. Shifts in the boundaries of ecosystems can reflect changes in climate conditions. Scientists closely monitor these transitions to understand and predict the impacts of climate change on various ecosystems.

What is Edge Effect

Edge effect refers to the alterations in population dynamics and community structures that occur at the interface of two different habitats, known as ecotones. This phenomenon is characterized by an increased abundance and diversity of species within these transitional zones compared to the interior of the adjacent habitats. The edge effect is a significant ecological concept because it highlights how habitat boundaries can influence biological communities.

Characteristics of Edge Effect

  1. Increased Species Richness: At the boundaries of different habitats, the number of species often exceeds that found within either of the individual ecosystems. This occurs because the edge provides a range of resources and conditions from both adjoining habitats. Therefore, the variety of species is often higher in these areas than within the core of either habitat.
  2. Higher Population Density: The population density of some species can be significantly greater in the ecotone than in the surrounding habitats. This is due to the availability of diverse resources and niches that attract a larger number of individuals.
  3. Presence of Edge Species: Certain species thrive primarily in the ecotone or are most abundant in these transitional areas. These species, known as edge species, are adapted to exploit the unique conditions found at habitat boundaries. For instance, in terrestrial ecosystems, birds are commonly found in higher densities at the edges between forests and open areas like deserts.

Examples and Implications

  • Bird Species: The density of bird species often increases in ecotones, such as those between forests and agricultural fields. These areas provide varied nesting sites and food resources not found in the interior of the respective habitats.
  • Ecological Interactions: Edge effects can influence ecological interactions, such as predation and competition, by providing diverse environmental conditions. This can lead to the establishment of new ecological dynamics not present in the core habitats.

What is Ecological Succession?

Ecological succession is a natural process through which an ecological community undergoes gradual changes over time. This process occurs as species in a given area adapt to environmental changes. Succession is an inevitable and predictable phenomenon, driven by the need for biotic components to align with environmental shifts.

The goal of ecological succession is to achieve a stable and balanced ecosystem, known as a climax community. During this process, certain species increase in abundance while others diminish. This dynamic progression is characterized by a series of changes in the species composition of a community.

The sequence of these changes is referred to as a sere. Each stage within this sequence is called a seral stage or seral community. Over time, all observed communities have undergone succession, reflecting the intertwined evolution of species and their environments.

Ecological succession can be categorized into two types: primary and secondary. Primary succession occurs in areas where life begins from a completely barren state, such as on newly formed volcanic islands or exposed glacial landscapes. This process is slow, as it starts from a lack of soil and biological matter. Pioneer species are the first to colonize these new habitats, initiating the development of a new ecosystem.

Secondary succession, on the other hand, happens in areas where an existing ecosystem has been disturbed but not entirely destroyed. This type of succession occurs more rapidly than primary succession because the soil and some biological remnants are still present. Examples of secondary succession include areas recovering from fires, windstorms, or human activities such as logging.

Overall, ecological succession reflects the ongoing process of environmental and biological adaptation, leading to increasingly complex and stable ecosystems.

Types of Ecological Succession

Ecological succession encompasses various types, each defined by the conditions and processes driving the change in species composition over time. The main types of ecological succession include:

  1. Primary Succession
    • Primary succession occurs in environments that are initially barren or devoid of life, such as newly formed volcanic islands or exposed glacial moraines. This process starts from a sterile substrate, where pioneer species first colonize. Over time, these initial species are replaced by more complex communities.
  2. Secondary Succession
    • Secondary succession takes place in areas where a community has been disturbed but not entirely removed, such as after a forest fire or agricultural abandonment. The soil and some remnants of the previous community remain, facilitating faster recovery and re-colonization by new species.
  3. Autotrophic Succession
    • In autotrophic succession, the population of autotrophs (primarily plants) dominates the community, surpassing the heterotrophs (organisms that rely on others for food). This type of succession is characterized by the gradual buildup of plant biomass, leading to a more complex and stable community.
  4. Heterotrophic Succession
    • Heterotrophic succession is marked by the early dominance of heterotrophs such as bacteria, fungi, and some animals. This type of succession typically occurs in organic environments where decomposers and other heterotrophic organisms are the first to establish.
  5. Autogenic Succession
    • Autogenic succession involves changes within a community driven by the interactions of the organisms with their environment. These internal modifications lead to the replacement of the existing community by a new one, reflecting the dynamic relationship between organisms and their habitat.
  6. Allogeneic Succession
    • Allogeneic succession occurs when external factors, rather than internal community interactions, drive the changes in the community structure. These external influences might include changes in climate, soil composition, or other environmental conditions.
  7. Habitat-Specific Succession
    • Succession can also be categorized based on the type of habitat:
    • Hydrosere: Succession that begins in aquatic environments, such as ponds or lakes, leading to the gradual formation of terrestrial habitats.
    • Mesarch: Succession occurring in habitats with adequate moisture conditions, such as wetlands or floodplains.
    • Halosere: Succession in saline environments, including coastal areas with high salt concentrations.
    • Xerosere: Succession in dry, xeric habitats like sand dunes or rocky surfaces, where moisture is minimal. Xeroseres can be further divided into:
      • Psammosere: Succession on sandy substrates.
      • Lithosere: Succession on bare rock surfaces.
    • Oxylosere: Succession in acidic soils, where the environment is characterized by low pH levels.

Causes of succession

Ecological succession is driven by a variety of factors that collectively influence the transition from one community to another. The main causes of succession include:

  1. Climatic Causes
    • Climate plays a significant role in succession. Factors such as temperature, rainfall, light intensity, and wind patterns directly impact the development and composition of ecological communities. Variations in these climatic elements can create conditions that favor certain species over others, thereby influencing the direction and pace of succession.
  2. Biotic Causes
    • Biotic interactions among organisms are crucial in succession. Competition for resources, such as nutrients, light, and space, leads to changes in community structure. As species compete, some may become less dominant and eventually be replaced by others better adapted to the changing conditions. This dynamic process of competition and replacement drives the progression of succession.
  3. Ecesis Causes
    • Ecesis refers to the establishment and adaptation of species within a community. Changes in soil conditions due to processes like invasion, migration, and competition affect the ability of species to establish and thrive. The alteration of soil properties, such as nutrient availability and pH, can create a more favorable environment for certain species, influencing the course of succession.
  4. Stabilizing Causes
    • The ultimate goal of succession is to achieve a climax community, a stable and self-sustaining ecosystem. Succession progresses towards this equilibrium state, where species composition becomes relatively stable and resilient to disturbances. This stabilization process reflects the community’s adaptation to the environmental conditions and interactions among its members.

These causes collectively shape the patterns of ecological succession, driving the changes in species composition and community structure over time.

Stages of ecological succession

Ecological succession progresses through a series of sequential stages, each contributing to the establishment and stabilization of an ecological community. These stages include:

  1. Nudation
    • Nudation marks the initial stage of ecological succession. It involves the formation of a bare or lifeless area. This area may result from natural disturbances or abiotic factors, creating a site devoid of living organisms.
  2. Invasion
    • Invasion follows nudation and involves the arrival and establishment of new species in the bare area. Species that can colonize the new habitat begin to settle and reproduce. This step is crucial as it initiates the process of community development.
  3. Competition and Co-action
    • As species establish themselves, they compete for limited resources such as nutrients, space, and light. Competition can be intra-specific (among individuals of the same species) or inter-specific (between different species). Co-action refers to the interactions among species, which can influence each other’s survival. This stage results in the survival of the most adapted species and the elimination of less suited ones.
  4. Reaction
    • Reaction is a pivotal stage in succession. It involves the modification of the environment by the organisms present. These modifications can alter soil composition, water availability, light intensity, and temperature. The changes in environmental conditions can render the habitat less suitable for the existing community, leading to its replacement by a new one. The sequence of these community replacements is known as a sere, with each community termed as a seral stage.
  5. Stabilization (Climax)
    • Stabilization represents the final stage of ecological succession. In this stage, the community reaches a state of equilibrium, known as the climax community. This community is well-adapted to the local climate and remains stable over long periods. It is characterized by a balanced interaction among species and a relatively constant composition. Examples of climax communities include mature forests, grasslands, and coral reefs.

These stages collectively describe the dynamic process of ecological succession, from the formation of bare areas to the establishment of stable, mature ecosystems.

References

  1. Whittaker, R. H. (1975). Communities and Ecosystems. Macmillan Publishing Co., Inc.
  2. Begon, M., Harper, J. L., & Townsend, C. R. (1996). Ecology: Individuals, Populations, and Communities. Blackwell Science.
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  4. Gosz, J. R. (1993). Ecotone hierarchies. Ecological Applications, 3(3), 369-376.
  5. Hansen, A. J., & di Castri, F. (1992). Landscape boundaries: Consequences for biotic diversity and ecological flows. Springer-Verlag.
  6. Ries, L., & Sisk, T. D. (2004). A predictive model of edge effects. Ecology, 85(11), 2917-2926.
  7. Clements, F. E. (1916). Plant Succession: An Analysis of the Development of Vegetation. Carnegie Institution of Washington.
  8. Odum, E. P. (1969). The strategy of ecosystem development. Science, 164(3877), 262-270.
  9. Pickett, S. T. A., & McDonnell, M. J. (1989). Changing perspectives in community dynamics: A theory of successional forces. Trends in Ecology & Evolution, 4(8), 241-245.
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