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REP21701
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Last modified
8/24/2016 11:54:55 PM
Creation date
11/27/2007 3:14:35 AM
Metadata
Fields
Template:
DRMS Permit Index
Permit No
C1980005
IBM Index Class Name
Report
Doc Date
1/19/1999
Doc Name
1998 Reclamation & Shrub Establishment Studies at Seneca II & Seneca IIW Mines
Permit Index Doc Type
Reveg Monitoring Report
Media Type
D
Archive
No
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<br /> <br />I~ <br />I' <br />I' <br />iJ <br />I <br />SECTION B: TOPSOIL DEPTH & SHRUB ESTABLISHMENT STUDY <br />Introduction <br />The purpose of this study was to determine the effect of topsoil application on the re- <br />establishment of native woody plants at Seneca II Mine. Topsoil application has been <br />demonstrated to be vital to the establishment of grass and forb species which require the textural, <br />chemical and biological properties of topsoil for seed germination. Woody species, however, <br />have a greater adaptation to coarse, rocky and shallow soils. Establishment of serviceberry <br />(Amelanchier alnifo[ia), chokecherry (Prunus virginiana), and Gambel's oak (Quercus gambelii) <br />is potentially limited by both plant competition resulting from topsoil application and <br />inappropriate soil texture. This study addresses the following hypothesis: <br />"Application of topsoil adversely affects shrub establishment within shrub areas <br />at Seneca II Mine." <br />Questions investigated by this study are: <br />1. Does topsoil application affect shrub survival? <br />2. Does topsoil application affect vigor of planted shrubs? <br />3. Does topsoil application affect herbaceous plant density and percent cover? <br />4. Is there a direct relationship between topsoil application, herbaceous plant growth and <br />shrub survival with shrub azeas? <br />Me h s <br />Study Design. The study site is located within the planting unit designated 95-4 at Seneca II <br />Mine. The two treatments investigated in this study aze: 1) "Control" in which the topsoil depth <br />averages 20.9 centimeters; and 2) "No-Topsoil" in which topsoil was not applied to the final <br />graded spoils. Prior to study establishment, both sites were planted in a common fashion by a <br />commercial tree planting crew. The experimental design consists of a series of belt transects <br />randomly placed along baselines within the two treatment areas. Two baselines were <br />subjectively placed along the lower slope boundary of each treatment plot. A total often <br />permanent belt transects, 2 meters by 25 meters, were randomly placed along each baseline. Belt <br />transects were not allowed to overlap. Data was collected during late August or early September <br />annually for three yeazs. Variables measured on the site were presence/absence, herbaceous <br />cover, damage, height, and mycorrhizal colonization. <br />Woody species were examined for presence/absence, browse damage, and height on an annual <br />basis. The initial data was collected under conditions of snow cover, thus, baseline data was <br />recollected during spring 1996 after snow melt. Browse was determined by examining the main <br />shoot of the plant for signs of damage. Height was determined in centimeters for the first five <br />plants of a species located within each transect. <br />11 <br />
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