My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
PERMFILE108925
DRMS
>
Back File Migration
>
Permit File
>
100000
>
PERMFILE108925
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
8/24/2016 10:01:24 PM
Creation date
11/24/2007 5:31:53 PM
Metadata
Fields
Template:
DRMS Permit Index
Permit No
C1981008
IBM Index Class Name
Permit File
Doc Date
7/30/2007
Doc Name
Vegetation Baseline Studies Nucla Mine 1979
Section_Exhibit Name
Section 2.05.6(2) Attachment 2.05.6(2)-1
Media Type
D
Archive
No
There are no annotations on this page.
Document management portal powered by Laserfiche WebLink 9 © 1998-2015
Laserfiche.
All rights reserved.
/
43
PDF
Print
Pages to print
Enter page numbers and/or page ranges separated by commas. For example, 1,3,5-12.
After downloading, print the document using a PDF reader (e.g. Adobe Reader).
View images
View plain text
<br />-6- <br />i! <br />. VIJ(~TATiOf] PRODOCPICN, COVFdi, FRE~(kNCY. AND SIOt[IB HEIGHTS <br />Sample Site location. Areas to be affected by mining activities were <br />delineated on aerial photographs (1" = 400'). Because of the small areal <br />etct~t of the two vegetation types subjected to quantitative sailing on <br />the affected area, a systenatic tectuuque was used for san~le site loca- <br />tion. This entailed estalzlistmm~t of production exclosures aid cover quad- <br />rats at predetermined paced intervals within the type in a manner m <br />ensure complete coverage of the type. The diirensions of each such type <br />were carefully measured on the topographic Lase map. Sanq~le points were ,~ <br />then e3ually spaced within the type det;.+ motion on the map. Farb point sys- <br />temstically located in this manner was placed in the field by pacing first <br />from a reoogiuzable landmazk to locate the first point and then from located <br />points to place the rams;*rtor of sample locations. The control sites <br />were sled in the same fashion. Fade located sample point was marke3 <br />with a Mooderi stake which identified the sai~le number and vegetation type. <br />All points ce>.,; flagged above the vegetation to allow easy relocation. <br />One rover quadrat and one production exclosure were situated at each <br />• - sanq>le point. Nver quadrats were paced in a wnsistent manner with ore <br />corner touclting-the south side of the sample location stake. Production <br />exclosures arse situated Sm north of each samq~le location stake. This <br />tectuiique ensured the unbiased positioning of both rover quadrats and pro- <br />duction exclosures around the san~le point. . <br />Data Collection. Cover was estimated using a 20x5Oan (1/l0m2) steel frame <br />quadrat at each sample point in each vegetation type. A total of 159 <br />quadrats wrie sampled for rover during this study as shown in Table 1. <br />This sanple size and all production and rover sample sizes were deter- <br />mined on the basis of several criteria: <br />1. Wyani.ri9 DF7) Guideline $2 (March, 1979) suggested that sample size be <br />established on the basis of pre-sample data. That is, a sm311 numd~er <br />of pzduction and Dover samples are taken during the growi.rg season <br />- Prior to actual baseline data collection. Sone idea of natural vari- <br />ation in the vegetation types to be studied is obtained fmn the pre- <br />sanq~le data and this infornetion faci t.i rates the establishmnt of <br /> <br />• <br />(Revised March 2006) Attachment 2.05.6(2)-1-11 <br />
The URL can be used to link to this page
Your browser does not support the video tag.