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Chapter 4: Plant Succession and Disturbances in the Urban Forest ...

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<strong>Chapter</strong> 4: <strong>Plant</strong> <strong>Succession</strong> <strong>and</strong> <strong>Disturbances</strong> <strong>in</strong> <strong>the</strong> <strong>Urban</strong> <strong>Forest</strong> Ecosystem 16<br />

Information should be regularly collected to<br />

document patterns <strong>and</strong> effects of management,<br />

<strong>in</strong>clud<strong>in</strong>g current <strong>and</strong> historical site conditions, such<br />

as soils, vegetation <strong>and</strong> disturbances. A site<br />

<strong>in</strong>ventory should be conducted to determ<strong>in</strong>e <strong>the</strong><br />

potential of <strong>the</strong> site (see also <strong>Chapter</strong> 7 - Soil <strong>and</strong><br />

Site Factors). If a location is too degraded (due to<br />

pollution, nutrient load<strong>in</strong>g, or heavy pesticide use), it<br />

may not be possible to restore it to a desired<br />

historical successional stage. Realistic <strong>and</strong> feasible<br />

restoration goals will ultimately determ<strong>in</strong>e a project's<br />

success.<br />

<strong>in</strong>dustrial l<strong>and</strong>s with four native plant ecosystems,<br />

<strong>in</strong>clud<strong>in</strong>g forests <strong>and</strong> prairies. For example, a 35-acre<br />

project will restore a natural prairie ecosystem close<br />

to downtown St. Paul (Figure 20). Prairies will be<br />

ma<strong>in</strong>ta<strong>in</strong>ed <strong>in</strong> a grassy successional stage by us<strong>in</strong>g<br />

frequent low <strong>in</strong>tensity fires. "Prescribed fire" <strong>and</strong>/or<br />

shrub/tree cutt<strong>in</strong>g will be used to ma<strong>in</strong>ta<strong>in</strong> this<br />

grass-like stage <strong>and</strong> keep weeds under control. Such<br />

strategy will provide, <strong>in</strong> <strong>the</strong> long run, an important<br />

successional stage that was miss<strong>in</strong>g from this<br />

urbanized l<strong>and</strong>scape.<br />

A particular stage, or a mosaic of different<br />

successional stages, may be chosen as <strong>the</strong> objective<br />

of restoration, based on <strong>the</strong> <strong>in</strong>formation collected<br />

from <strong>the</strong> site <strong>in</strong>ventory. The plant species to be<br />

established should be those characteristic of <strong>the</strong><br />

correspond<strong>in</strong>g natural successional stages. For<br />

<strong>in</strong>stance, plant<strong>in</strong>g trees <strong>and</strong> shrubs to attract as many<br />

bird species as possible, many of which are not<br />

typical of <strong>the</strong> desired successional stage, may not<br />

lead to a susta<strong>in</strong>able objective.<br />

Incorporat<strong>in</strong>g disturbances <strong>and</strong> succession<br />

<strong>in</strong>to small scale projects<br />

Restoration projects <strong>in</strong> small areas may <strong>in</strong>clude<br />

ecosystem(s) <strong>in</strong> which succession can be effectively<br />

managed. These situations may <strong>in</strong>clude <strong>the</strong><br />

restoration of a bare site, elim<strong>in</strong>ation of <strong>in</strong>vasive<br />

species or re-<strong>in</strong>troduction of more natural<br />

disturbances.<br />

Restor<strong>in</strong>g bare sites<br />

On a bare site, one stage of succession could be<br />

chosen <strong>and</strong> a first effort to restore it could be by<br />

plant<strong>in</strong>g a mix of all species typical of that<br />

successional stage. However, it may take decades for<br />

<strong>the</strong> trees to become mature, <strong>and</strong> litterfall <strong>and</strong> logs<br />

may need to be imported if a late successional stage<br />

is to be approximated. Introduction of natural<br />

disturbance regimes, such as frequent ground fire,<br />

may be desirable or necessary <strong>in</strong> some cases.<br />

The Green<strong>in</strong>g <strong>the</strong> Great River Park Program,<br />

established <strong>in</strong> 1995, seeks to restore native<br />

ecosystems along <strong>the</strong> Mississippi River <strong>in</strong> St. Paul,<br />

MN. The project <strong>in</strong>volves <strong>the</strong> l<strong>and</strong>scap<strong>in</strong>g of<br />

Figure 20.1 Photo courtesy of Chicago Wilderness<br />

Elim<strong>in</strong>at<strong>in</strong>g <strong>in</strong>vasive species<br />

In some sites, removal of <strong>in</strong>vasive plants may be<br />

sufficient to release native species from competition<br />

<strong>and</strong> restore natural succession. In <strong>the</strong> Ivy Removal<br />

Project <strong>in</strong> <strong>Forest</strong> Park, Portl<strong>and</strong>, removal of English<br />

ivy (Hedera helix) has renewed <strong>the</strong> health of <strong>the</strong><br />

exist<strong>in</strong>g vegetation (Figure 21). English ivy is an<br />

aggressive exotic v<strong>in</strong>e, extensively planted <strong>in</strong> <strong>the</strong><br />

surround<strong>in</strong>g neighborhoods, that has <strong>in</strong>vaded <strong>the</strong><br />

park <strong>and</strong> suppressed its native vegetation. Regular

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