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2002-07-08_GENERAL DOCUMENTS - M2002004 (4)
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2002-07-08_GENERAL DOCUMENTS - M2002004 (4)
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8/24/2016 2:18:41 PM
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DRMS Permit Index
Permit No
M2002004
IBM Index Class Name
GENERAL DOCUMENTS
Doc Date
7/8/2002
Doc Name
ATTACHMENT, PART 3
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HABITAT MGMT
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DRMS
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D
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STRATEGIES FOR INCREASED DIVERSITY WITHIN PLANT COMMUNITIES <br />Direct Place Topsoiling <br />The role of topsoil as a "reservoir" /source of seeds and vegetative <br />propagules of indigenous plant species on mined lands has been long <br />recognized and often demonstrated (3, 19, 20). The desirability of <br />volunteer growth from plant propagules in topsoil obviously depends <br />upon the species composition of the propagule reservoir, which may be <br />strongly influenced by both vegetation conditions and management of a <br />site prior to topsoil salvage (20, 13). If seed /propagule composition <br />in topsoil is acceptable, any topsoiling practice favoring volunteer <br />growth may increase ultimate diversity within the plant community. For <br />many indigenous plant species with limited commercial availability and/ <br />or exceptional difficulty in initial establishment via conventional <br />revegetation techniques, topsoiling may comprise the only realistic <br />means of introduction (5). <br />Immediate respreading of salvaged topsoil (i.e., direct place <br />topsoiling) is commonly recognized as one means of encouraging volunteer <br />plant growth, since it will minimize any losses of seed or vegetative <br />propagule viability. If topsoil stockpiling is unavoidable, duration <br />of storage should be kept as short as possible; Iverson and Wali (20), <br />for example, found no significant differences in germinable seed concen- <br />trations between fresh and one year stockpiled topsoil in a North Dakota <br />study. However, more prolonged storage of topsoil may significantly <br />reduce capacity for volunteering. In southwestern Wyoming, Green et al. <br />(15) noted significantly greater establishment of non - seeded native <br />shrubs with fresh than with long- stored applied topsoil. In south- <br />eastern Montana, King (21) reported similar results, in which direct <br />place topsoiling promoted greater numbers and frequency of non - seeded <br />grasses and forbs than did stockpiled topsoiling. <br />Direct place topsoiling may benefit intra - community diversity by <br />other means than simply increasing volunteer plant establishment. The <br />importance of reestablishing soil microorganisms to proper ecosystem <br />function on disturbed lands is becoming increasingly apparent (6). A <br />number of studies have demonstrated general declines in soil microbio- <br />logical activity associated with extended topsoil storage (26 and others). <br />Such declines in general microbiological activity will retard development <br />and functioning of "new" minesoils, thereby directly affecting plant <br />growth and, possibly, indirectly influencing plant community development <br />and diversity. Also, reductions in symbiotic microorganisms with <br />extended topsoil coverage, such as mycorrhizal fungi (39), may specifi- <br />cally retard establishment of many symbiant- dependent plant species <br />whose presence in reclaimed plant communities is beneficial from a <br />diversity standpoint. Research has demonstrated many important, desir- <br />able plant species for mined land revegetation (especially shrubs) to <br />be mycorrhizal, and has suggested a potentially important role of <br />mycorrhizae in mined land plant community succession and diversity (25, <br />37). Direct haul topsoiling or, if such proves impossible, at least <br />minimized time of topsoil storage have often been suggested as means of <br />reducing adverse impacts on mycorrhizae and other essential soil micro- <br />organisms. <br />260 <br />
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