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REV05290
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REV05290
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Last modified
8/25/2016 1:03:47 AM
Creation date
11/21/2007 9:24:38 AM
Metadata
Fields
Template:
DRMS Permit Index
Permit No
M1977210
IBM Index Class Name
Revision
Doc Date
5/22/1989
Doc Name
RESPONSES TO ADEQUACY LETTER FOR SNYDER QUARRY AMENDMENT FN 77-210
From
MARK A HEIFNER
To
MLR
Type & Sequence
AM3
Media Type
D
Archive
No
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<br />We have previously tried alfalfa and have found summer drought periods reduces <br />its presence to a very minor component in the vegetation. After about two years it <br />is gone. It never becomes large enough to do any good for nitrogen incorporation <br />into the soil or for forage. We have dropped alfalfa from consideration until sane <br />variety is produced which is more drought resistant. <br />Mountain Mahogany can only be seeded with commercial seed if the seed is <br />drilled. In this rocky soil medium drilling is out of the question. Native <br />collections of seed and planting of uncleared seed is possible, but is only <br />beneficial where soil is not being replaced. Where the native soil is replaced, <br />this shrub appears as seedlings in the second season. Its source is undoubtedly <br />from seeds in the soil rather than root sprouts as this species does not exhibit <br />suckering. In general, we feel that planting a shrub species which is going to <br />invade quite readily is rather pointless and can actually be harmful. It could <br />easily increase shrub seedling density far beyond the ability of the environment to <br />support them. <br />Oak Hrush does not appear to be capable of very successful seeding and we have <br />never found a source for Gambel Oak seed. This species seems to be quite particular <br />about where it lives and seems to invade much later in the successional sequence. <br />It can be transplanted, provided the soil it grew in goes with it. Otherwise, <br />transplants seem to generally fail. Also, when transplanted it seems to need <br />prodigious quantities of water to become established. <br />ITF]M 8 - In the same letter, the DW also recalculated placement of fill along the <br />backwalls every 20C`300 feet to provide escape routes for deer and bighorn sheep <br />from coyotes, bears, and mountain lions. The DOW recamerided the escape routes be <br />staggered between terraces for maximum effectiveness. Please incorporate these in <br />the final land use configuration or discuss why they should not be. <br />RESPQ~6E: We are aware of this approach. In this amendment that approach was <br />not recommended by the DOW. This is because the bench lengths will be so short <br />escape ramps are unnecessary. <br />ITEM 9 - Dn page 34, it is discussed that in lieu of fertilizer application on test <br />plots, "the greatest benefit came from a secondary seeding at a rate of about one- <br />half the normal rate." Does the operator commit to this reseeding for revegetation <br />success? <br />RESPOND: Secondary seedings are highly beneficial where the first year <br />seeding success is below expectatim. A5 a rule, in semi-arid lands, if the seeding <br />produces about 4 to 6 plants per square foot (or more) secondary seeding will not be <br />beneficial and can induce excess moisture competition. Where the seeding success is <br />below about 4 plants per square foot then a secondary seeding can be helpful, unless <br />the environment cannot sustain more than 3 to 5 plants per square foot in the first <br />place. In most situations at this quarry, the environment should ultimately be <br />capable of supporting 6 to 12 mature grass plants per square foot, so if a <br />particular seeding only produces about 3 or fewer plants per square foot a secondary <br />seeding would be done. <br />SNYDER NW ANQmhETfl ADE(aIIACY RESPQJSES MAY 22, 1989 PACE 9 <br />
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