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<document xmlns="http://cnx.rice.edu/cnxml" xmlns:md="http://cnx.rice.edu/mdml/0.4" xmlns:bib="http://bibtexml.sf.net/" id="new21">
  <name>Spatial Gradients in Biodiversity</name>
  <metadata>
  <md:version>1.1</md:version>
  <md:created>2003/07/28 12:12:37 GMT-5</md:created>
  <md:revised>2004/07/13 14:24:58.879 GMT-5</md:revised>
  <md:authorlist>
      <md:author id="harrison">
      <md:firstname>Ian</md:firstname>
      
      <md:surname>Harrison</md:surname>
      <md:email>harrison@amnh.org</md:email>
    </md:author>
      <md:author id="laverty">
      <md:firstname>Melina</md:firstname>
      
      <md:surname>Laverty</md:surname>
      <md:email>laverty@amnh.org</md:email>
    </md:author>
      <md:author id="sterling">
      <md:firstname>Eleanor</md:firstname>
      
      <md:surname>Sterling</md:surname>
      <md:email>sterling@amnh.org</md:email>
    </md:author>
  </md:authorlist>

  <md:maintainerlist>
    <md:maintainer id="harrison">
      <md:firstname>Ian</md:firstname>
      
      <md:surname>Harrison</md:surname>
      <md:email>harrison@amnh.org</md:email>
    </md:maintainer>
    <md:maintainer id="nbynum">
      <md:firstname>Nora</md:firstname>
      
      <md:surname>Bynum</md:surname>
      <md:email>nbynum@amnh.org</md:email>
    </md:maintainer>
    <md:maintainer id="charlet">
      <md:firstname>Charlet</md:firstname>
      
      <md:surname>Reedstrom</md:surname>
      <md:email>charlet@rice.edu</md:email>
    </md:maintainer>
    <md:maintainer id="laverty">
      <md:firstname>Melina</md:firstname>
      
      <md:surname>Laverty</md:surname>
      <md:email>laverty@amnh.org</md:email>
    </md:maintainer>
    <md:maintainer id="sterling">
      <md:firstname>Eleanor</md:firstname>
      
      <md:surname>Sterling</md:surname>
      <md:email>sterling@amnh.org</md:email>
    </md:maintainer>
  </md:maintainerlist>
  
  <md:keywordlist>
    <md:keyword>biodiversity</md:keyword>
  </md:keywordlist>

  <md:abstract/>
</metadata>

  <content>
    <para id="para1">
      Generally speaking, warm tropical ecosystems are richer in
      species than cold temperate ecosystems at high latitudes (see
      <cite src="#gastonandwilliams">Gaston and Williams, 1996</cite>,
      for general discussion). A similar pattern is seen for higher
      taxonomic groups (genera, families). Various hypotheses
      (<foreign>e.g.</foreign>, environmental patchiness, solar
      energy, productivity; see <cite src="#blackburnandgaston">Blackburn and Gaston, 1996</cite>)
      have been raised to explain these patterns.  For example, it is
      assumed that warm, moist, tropical environments, with long
      day-lengths provide organisms with more resources for growth and
      reproduction than harsh environments with low energy resources
      (<cite src="#hunter">Hunter, 2002</cite>). When environmental
      conditions favor the growth and reproduction of primary
      producers (<foreign>e.g.</foreign>, aquatic algae, corals,
      terrestrial flora) then these may support large numbers of
      secondary consumers, such as small herbivores, which also
      support a more numerous and diverse fauna of predators. In
      contrast, the development of primary producers in colder
      temperate ecosystems is constrained by seasonal changes in
      sunlight and temperature. Consequently, these ecosystems may
      support a less diverse biota of secondary consumers and
      predators.</para>


    <para id="paradf">
      Recently, (<cite src="#allen">Allen <foreign>et al.</foreign>
      2002</cite>) developed a model for the effect of ambient
      temperature on metabolism, and hence generation time and
      speciation rates, and used this model to explain the latitudinal
      gradient in biodiversity. However, these authors also noted that
      the principles that underlie these spatial pattern of
      biodiversity are still not well understood. </para>
    
    <para id="para4">
      Species and ecosystem diversity is also known to vary with
      altitude <cite src="#walter">Walter (1985)</cite> and <cite src="#gastonandwilliams">Gaston and Williams (1996:
      214-215)</cite>. Mountainous environments, also called <term src="#orobiome">orobiomes</term>, are subdivided vertically into
      altitudinal belts, such as montane, alpine and nival, that have
      quite different <term src="#ecosystem">ecosystems</term>.
      Climatic conditions at higher elevations
      (<foreign>e.g.</foreign>, low temperatures, high aridity) can
      create environments where relatively few species can
      survive. Similarly, in oceans and freshwaters there are usually
      fewer species as one moves to increasing depths below the
      surface. However, in the oceans there may be a rise in species
      richness close to the seabed, which is associated with an
      increase in ecosystem heterogeneity.</para>

    <para id="para5">
      By mapping spatial gradients in biodiversity we can also
      identify areas of special conservation interest. Conservation
      biologists are interested in areas that have a high proportion
      of <term src="#endemicspecies">endemic species</term>,
      <foreign>i.e.</foreign>, species whose distributions are
      naturally restricted to a limited area. It is obviously
      important to conserve these areas because much of their flora
      and fauna, and therefore the ecosystems so-formed, are found
      nowhere else. Areas of high endemism are also often associated
      with high <term src="#spec">species richness</term> (see <cite src="#gastonandspicer">Gaston and Spicer, 1998</cite> for
      references).
    </para>

    <para id="paraa">
      Some conservation biologists have focused their attention on
      areas that have high levels of endemism (and hence diversity)
      that are also experiencing a high rate of loss of ecosystems;
      these regions are <term src="#biodhs">biodiversity
      hotspots</term>.  Because biodiversity hotspots are
      characterized by localized concentrations of biodiversity under
      threat, they represent priorities for conservation action (<cite src="#sechrestplus">Sechrest <foreign>et al.</foreign>,
      2002</cite>). A <term src="#tbiodivhot">terrestrial biodiversity
      hotspot</term> is defined quantitatively as an area that has at
      least 0.5%, or 1,500 of the world's ca. 300,000 species of green
      plants (<foreign>Viridiplantae</foreign>), and that has lost at
      least 70% of its primary vegetation (<cite src="#myers">Myers
      <foreign>et al.</foreign>, 2000</cite>; <cite src="#conservationintl">Conservation International,
      2002</cite>). <term src="#mbiodivhot">Marine biodiversity
      hotspots</term> are quantitatively defined based on measurements
      of relative endemism of multiple taxa (species of corals,
      snails, lobsters, fishes) within a region and the relative level
      of threat to that region (<cite src="#robertsplus">Roberts
      <foreign>et al.</foreign>, 2002</cite>). According to this
      approach, the Philippine archipelago and the islands of Bioko,
      Sao Tome, Principe and Annobon in the eastern Atlantic Gulf of
      Guinea are ranked as two of the most threatened marine
      biodiversity hotspot regions.</para>


    <para id="para7">
      Conservation biologists may also be interested in <term src="#biodivcold">biodiversity coldspots</term>; these are
	areas that have relatively low biological diversity but also
	include threatened ecosystems (<cite src="#karandmar">Kareiva
	and Marvier, 2003</cite>). Although a biodiversity coldspot is
	low in species richness, it can also be important to conserve,
	as it may be the only location where a rare species is found.
	Extreme physical environments (low or high temperatures or
	pressures, or unusual chemical composition) inhabited by just
	one or two specially adapted species are coldspots that
	warrant conservation because they represent unique
	environments that are biologically and physically
	interesting. For further discussion on spatial gradients in
	biodiversity and associated conservation practices see the
	related modules on <cnxn document="">"Where is the world's
	biodiversity?"</cnxn> and <cnxn document="">"Conservation
	Planning at a Regional Scale."</cnxn><!-- fix cnxns; future
	topics -->
    </para>

  </content>

  <glossary>
    <definition id="biodhs">
      <term>Biodiversity hotspots</term>
      <meaning>
	in general terms these are areas that have high levels of
	endemism (and hence diversity) but which are also experiencing
	a high rate of loss of habitat. This concept was originally
	developed for terrestrial ecosystems. A terrestrial
	biodiversity hotspot is an area that has at least 0.5%, or
	1,500 of the worlds ca. 300,000 species of green plants
	(<foreign>Viridiplantae</foreign>), and that has lost at least
	70% of its primary vegetation (<cite src="#myers">Myers
	<foreign>et al.</foreign>, 2000</cite>). Marine biodiversity
	hotspots have been defined for coral reefs, based on
	measurements of relative endemism of multiple taxa (species of
	corals, snails, lobsters, fishes) within a region and the
	relative level of threat to that region (<cite src="#robertsplus">Roberts <foreign>et al.</foreign>,
	2002</cite>)
      </meaning>
    </definition>
    <definition id="orobiome">
      <term>Orobiome</term>
      <meaning>
	a mountainous environment or landscape with its constituent
	ecosystems
      </meaning>
    </definition>
    <definition id="spec">
      <term>Species richness</term>
      <meaning>the number of different species in a particular area.</meaning>
    </definition>
    <definition id="ecosystem">
      <term>ecosystem</term>
      <meaning>
	a community plus the physical environment that it occupies at
	a given time.
      </meaning>
    </definition>
    <definition id="endemism">
      <term>Area of endemism</term>
      <meaning>
	an areas which has a high proportion of endemic species
	(<foreign>i.e.</foreign>, species with distributions that are
	naturally restricted to that region)
      </meaning>
    </definition>

    <definition id="endemicspecies">
      <term>Endemic species</term>
      <meaning>
	those species whose distributions are naturally restricted to
	a defined region
      </meaning>
    </definition>

    <definition id="tbiodivhot">
      <term>Terrestrial Biodiversity hotspots</term>
      <meaning>
      </meaning>
    </definition>

    <definition id="mbiodivhot">
      <term>Marine Biodiversity hotspots</term>
      <meaning>
      </meaning>
    </definition>

    <definition id="biodivcold">
      <term>Biodiversity coldspots</term>
      <meaning>
	areas that have relatively low biological diversity but are
	also experiencing a high rate of habitat loss
      </meaning>
    </definition>
  </glossary>

  <bib:file>
    <bib:entry id="gastonandwilliams">
      <bib:incollection>
	<bib:author>Gaston, K.J. and P.H. Williams</bib:author>
	<bib:title>Spatial patterns in taxonomic diversity</bib:title>
	<bib:booktitle>
	  Biodiversity: a biology of numbers and difference
	</bib:booktitle>
	<bib:publisher>Blackwell Science Ltd.</bib:publisher>
	<bib:year>1996</bib:year>
	<bib:editor>K.J. Gaston</bib:editor>
	<bib:pages>202-229</bib:pages>
	<bib:address>Oxford, U.K.</bib:address>
      </bib:incollection>
    </bib:entry>

    <bib:entry id="blackburnandgaston">
      <bib:article>
	<bib:author>Blackburn, T.M. and K.J. Gaston</bib:author>
	<bib:title>
	  A sideways look at patterns in species richness, or why
	  there are so few species outside the tropics
	</bib:title>
	<bib:journal>Biodiversity Letters</bib:journal>
	<bib:year>1996</bib:year>
	<bib:volume>3</bib:volume>
	<bib:pages>44-53</bib:pages>
      </bib:article>
    </bib:entry>

    <bib:entry id="allen">
      <bib:article>
	<bib:author>Allen, A.P., J.H. Brown and J.F. Gillooly</bib:author>
	<bib:title>
	  Global biodiversity, biochemical kinetics, and the
	  energetic-equivalence rule
	</bib:title>
	<bib:journal>Science</bib:journal>
	<bib:year>2002</bib:year>
	<bib:volume>297</bib:volume>
	<bib:pages>1545-1548</bib:pages>
      </bib:article>
    </bib:entry>

    <bib:entry id="gastonandspicer">
      <bib:incollection>
	<bib:author>Gaston, K.J. and J.I. Spicer</bib:author>
	<bib:title>Mapping biodiversity</bib:title>
	<bib:booktitle>
	  Biodiversity: an Introduction
	</bib:booktitle>
	<bib:publisher>Blackwell Science Ltd.</bib:publisher>
	<bib:year>1998</bib:year>
	<bib:editor>K.J. Gaston and J.I. Spicer</bib:editor>
	<bib:pages>43-75</bib:pages>
	<bib:address>Oxford, U.K.</bib:address>
      </bib:incollection>
    </bib:entry>
    <bib:entry id="hunter">
      <bib:book>
	<bib:author>Hunter, M. Jnr</bib:author>
	<bib:title>Fundamentals of Conservation Biology</bib:title>
	<bib:publisher>Blackwell Science</bib:publisher>
	<bib:year>2002</bib:year>
	<bib:address>Massachusetts, U.S.A</bib:address>
	<bib:edition>Second Edition</bib:edition>
      </bib:book>
    </bib:entry>
    <bib:entry id="myers">
      <bib:article>
	<bib:author>
	  Myers, N., R.A. Mittermeier, C.G. Mittermeier, G.A.B. da
	  Fonseca and J. Kent
	</bib:author>
	<bib:title>
	  Biodiversity hotspots for conservation priorities
	</bib:title>
	<bib:journal>Nature</bib:journal>
	<bib:year>2000</bib:year>
	<bib:volume>403</bib:volume>
	<bib:pages>853-858</bib:pages>
      </bib:article>
    </bib:entry>

    <bib:entry id="conservationintl">
      <bib:misc>
	<bib:author>Conservation International</bib:author>
	<bib:title>Biodiversity Hotspots</bib:title>
	<bib:year>2002</bib:year>
	<bib:note>
	  Available from:
	  http://www.biodiversityhotspots.org/xp/Hotspots (accessed
	  May 11, 2003)
	</bib:note>
      </bib:misc>
    </bib:entry>

    <bib:entry id="robertsplus">
      <bib:article>
	<bib:author>
	  Roberts, C.M., C.J. McClean, J.E.N. Veron, J.P. Hawkins,
	  G.R. Allen, D.E. McAllister, C.G. Mittermeier,
	  F.W. Schueler, M. Spalding, F. Wells, C. Vynne, and
	  T.B. Werner
	</bib:author>
	<bib:title>
	  Marine biodiversity hotspots and conservation priorities for
	  tropical reefs
	</bib:title>
	<bib:journal>Science</bib:journal>
	<bib:year>2002</bib:year>
	<bib:volume>295</bib:volume>
	<bib:pages>1280-1284</bib:pages>
      </bib:article>
    </bib:entry>

    <bib:entry id="sechrestplus">
      <bib:article>
	<bib:author>
	  Sechrest, W., T.M. Brooks, G.A.B. da Fonseca, W.R. Konstant,
	  R.A. Mittermeier, A. Purvis, A.B. Rylands, and
	  J.L. Gittleman
	</bib:author>
	<bib:title>
	  Hotspots and the conservation of evolutionary history
	</bib:title>
	<bib:journal>
	  Proceedings of the National Academy of Sciences
	</bib:journal>
	<bib:year>2002</bib:year>
	<bib:volume>99</bib:volume>
	<bib:number>4</bib:number>
	<bib:pages>2067-2071</bib:pages>
      </bib:article>
    </bib:entry>

    <bib:entry id="karandmar">
      <bib:article>
	<bib:author>Kareiva, P. and M. Marvier</bib:author>
	<bib:title>
	  Conserving biodiversity coldspots
	</bib:title>
	<bib:journal>American Scientist</bib:journal>
	<bib:year>2003</bib:year>
	<bib:volume>91</bib:volume>
	<bib:pages>344-351</bib:pages>
      </bib:article>
    </bib:entry>

    <bib:entry id="walter">
      <bib:book>
	<bib:author>Walter, H.</bib:author>
	<bib:title>
	  Vegetation of the Earth and ecological systems of the
	  geo-biosphere
	</bib:title>
	<bib:publisher>Springer-Verlag</bib:publisher>
	<bib:year>1985</bib:year>
	<bib:address>New York, New York, U.S.A.</bib:address>
	<bib:edition>Third, revised and enlarged edition</bib:edition>
	<bib:note>
	  translated from the fifth, revised German edition by Owen
	  Muise
	</bib:note>
      </bib:book>
    </bib:entry>
  </bib:file>

</document>
