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  Landscape Characterization / Impervious Surfaces / What are the effects? / Habitat degradation and destruction

What are the effects?

Habitat Degradation, Loss, and Fragmentation

Aquatic and terrestrial habitats are increasingly degraded and lost as greater percentages of watershed areas are made impervious. The following sections focus upon these impacts which include habitat degradation, habitat loss, and habitat fragmentation.

Habitat degradation is the diminishment of habitat quality and its ability to support biological communities. It stems from the adverse effects of urban development, such as increases in impervious surfaces within watersheds. Its adverse effects can be immediate or cumulative.

Habitat loss is the outright destruction of habitat, such as filling a wetland or channelizing a section of stream. Its impacts upon biological communities are immediate and catastrophic.

Habitat fragmentation is the piecemeal disassembly of terrestrial habitats into discontinuous, oftentimes isolated, patches as a consequence of development. Its adverse effects are cumulative and not immediately noticeable. Habitat fragmentation stems from habitat loss.


 

 

 

 

 

 

Effects on aquatic organisms and streams

Aquatic and bay habitats are adversely impacted by the nonpoint pollutants and the higher volumes of runoff issuing from urbanized lands. Observable declines in the biological integrity of streams and the quality of stream habitats occur when watershed imperviousness reaches 10% to 15%.


Source: NEMO after Schueler, 1994


Observable indicators of stream health degradation include:
  • population shifts to aquatic organisms tolerant of poor water quality and poor habitat,
  • less riparian vegetation,
  • reduced macroinvertebrate, fish, and amphibian diversity,
  • lower plant and amphibian density,
  • increased sediment and stormwater runoff,
  • fewer snags in channels to dissipate energy,
  • channel instability.

 

 

 

 

 

 

The biological degradation of streams is manifested more quickly than physical degradation. There is a time lag, often of several years, between both increased runoff and the sedimentation that results from urban development and subsequent stream channel readjustment. Channel readjustments may include bank or bed erosion and channel scour or deposition, depending upon climate and other factors. In contrast, aquatic organisms respond quickly to poor water quality, more frequent peak flows, higher flow velocities and loss of resting areas, habitat loss, higher sediment loads, and the reduced availability of food, all of which are associated with the urbanization of streams.

Stream bank erosion due to rapid stormwater runoff.

Source: Jonson, Baltimore County DEPRM.

In some areas, natural stream channels have been replaced by artificial channels. Artificial channels are hostile to aquatic life and are not aesthetically pleasing.

 

 

Natural Channel

Artificial Channel

Adequate shading:
suitable water temperatures;
good cover for fish
minimal variation in temperatures;
abundant leaf material input.

No shading:
Increased water temperatures;
no cover for fish; rapid
daily and seasonal fluctuations in
temperatures; reduced leaf material input.


Sorted gravels provide diversified
habitats for many stream organisms.
Unsorted gravels result in
reduction in habitats; few organisms.


Pool Environment

Diversity of water velocities:
high in pools, lower in riffles. Resting
areas abundant beneath undercut
banks or behind large rocks, etc.

Low diversities of water velocities:
may have stream velocity higher than some aquatic life can withstand. Few or no resting places.
Sufficient water depth to support fish
and other aquatic life during dry season.
Insufficient depth of flow during dry
seasons to support diversity of fish and
aquatic life. Few if any pools (all riffle)
Source: CGIS after Goudie, 1990

Effects on terrestrial organisms and habitats

Urban and suburban development, particularly spatially dispersed forms such as large-lot single family housing, result not only in greater amounts of impervious surfaces throughout watersheds, but destroy and fragment terrestrial habitats. Urban growth may reduce habitat to residual patches that are too small to meet the ecological requirements of animals, birds, and plants, especially those which require large tracts of uninterrupted habitat or which are sensitive to human intrusion. Organisms in these patches become increasingly isolated by adjacent environments which are inhospitable and difficult or dangerous to cross.

Habitat Before and After Development

One consequence of habitat fragmentation is an increase in the amount of edge (boundaries between different habitats), such as that between a forest and a road or a lawn and a wetland. Some species, such as white-tailed deer and turkeys, benefit from edges. However, increases in edges are generally detrimental to overall biodiversity.

Edge Effects include:
  • Increased plant desiccation and wind-throw hazard,
  • More frequent and more severe wildfires,
  • Increased poaching and hunting,
  • Higher predation rates,
  • Heavier browsing and more disturbances that favor opportunistic species,
  • Increased cowbird parasitism of song bird nests.

 

 

 

 

 

Looking for the tools to protect your local watershed and ideas on how to manage urban development? For factsheets and literature on watershed protection and imperviousness, discussion of land-use planning and management techniques, and model ordinances check out:

Center for Watershed Protection
www.cwp.org/
EPA Office of Water: Watershed Protection
www.epa.gov/owow/watershed

Biological Indicators of Watershed Health
http://www.epa.gov/bioindicators/


Save Our Streams: Curriculum Materials for Environmental Educators Montgomery County Schools, Maryland
mcps.k12.md.us/curriculum/streams/

 



 

 

 

 

 

 

 

 

© CGIS at Towson University