SherbyNet - /page/wikibook/entry.mu

Micron Document

<!DOCTYPE html>

<title>Land imprinter</title>

</head>

Land imprinter

</h1>

</header>

The land imprinter<a href="#cite_note-rfPatent-1">[1]</a> is a <a href="No-till_farming" title="No-till farming">no-till</a> device for establishing <a href="Grass" title="Grass">grass</a> <a href="Vegetation_cover" class="mw-redirect" title="Vegetation cover">cover</a> in <a href="Arid" class="mw-redirect" title="Arid">arid</a> environments and <a href="Desert" title="Desert">deserts</a>.

The imprinter consists of a metal roller, with steel angles welded to the surface in various configurations.<a href="#cite_note-rfForestService2004-2">[2]</a> The angled teeth of the imprinter cut through weeds and brush to form a <a href="Mulch" title="Mulch">mulch</a>, while the teeth press seeds of grasses and other plants into the soil. The imprints remain stable for approximately two years.<a href="#cite_note-rfArmyCorps1986-3">[3]</a> During that time, imprints funnel water toward seedlings, protect them from wind, and concentrate nutrients for plant growth.

<div class="mw-heading mw-heading2"><h2 id="Desertification">Desertification</h2></div>

Much of the world depends on grassland for the grazing of domestic livestock.<a href="#cite_note-rfWrobelRedford-4">[4]</a> Due to <a href="Overgrazing" title="Overgrazing">overgrazing</a>, erosion, and other environmental factors, half of the world's rangeland is now lightly to moderately degraded, and 5% is severely degraded.<a href="#cite_note-rfBrown-5">[5]</a> <a href="Desertification" title="Desertification">Desertification</a> is expanding and threatens one-third of the world's dry land.<a href="#cite_note-rfMontgomery-6">[6]</a>

Plants and their root systems increase the quantity and size of <a href="Macropore" title="Macropore">macropores</a> in <a href="Soil" title="Soil">soil</a>, allowing rainwater to infiltrate.<a href="#cite_note-rfDixon1995-7">[7]</a> When ranges and grassland are overgrazed, soil becomes stripped of cover plants. <a href="Denudation" title="Denudation">Denuded</a> soil has reduced macroporosity, reducing water infiltration and leading to <a href="Surface_runoff" title="Surface runoff">runoff</a>.<a href="#cite_note-rfDixon1990-8">[8]</a>

<div class="mw-heading mw-heading2"><h2 id="Infiltration">Infiltration</h2></div>

The natural state of <a href="Grassland" title="Grassland">grassland</a> is rough and open. Plants create small crests and troughs in the soil surface, making it rough. Root systems create macroports at the bottom of the troughs, into which water can infiltrate. At the same time, the small ridges allow air to escape.<a href="#cite_note-DixonPeterson1971-9">[9]</a>

Desertification causes the soil surface to be smooth and closed.<a href="#cite_note-rfDixon1995-7">[7]</a> Reduced soil macroporosity inhibits infiltration. Rainfall cannot infiltrate through macroports, and air becomes trapped.<a href="#cite_note-DixonPeterson1971-9">[9]</a> A sealed soil surface prevents rainwater infiltration, partly because air contained within soil macropores cannot escape, and water is unable to displace the air.<a href="#cite_note-rfDixon1989-10">[10]</a>

<div class="mw-heading mw-heading2"><h2 id="Imprinting">Imprinting</h2></div>

Imprinting reverses the <a href="Desertification" title="Desertification">desertification</a> process by pressing V-shape imprints into the soil with steel angles on a heavy roller.<a href="#cite_note-rfDixonCarr2004-11">[11]</a> Rainwater then funnels into the troughs of the imprints, where the water infiltrates into the indentation and air exhausts from the crests.<a href="#cite_note-rfDixon1995-7">[7]</a> Seedlings are protected from wind, and organic material is concentrated at the base of the troughs to provide nutrients to the seedling.<a href="#cite_note-rfDixon1995-7">[7]</a> Wind protection attenuates evaporation at the base of the seedling, maximizing water availability to the plant during the rainy season. The seedbed may remain dry for some time before water infiltrates and germination occurs. In the meantime, the stable imprint protects the seed from <a href="Wind_erosion" class="mw-redirect" title="Wind erosion">wind erosion</a> and desiccation from exposure to the sun.<a href="#cite_note-rfRoundy_etAl1992-12">[12]</a>

<a href="Broadcast_seeder" class="mw-redirect" title="Broadcast seeder">Broadcast seeders</a> can be attached to the frame assembly or grain boxes mounted in front of the imprinting roller, so that seed is dropped in front of the roller which presses the seed into the soil.<a href="#cite_note-rfForestService2004-2">[2]</a> The weight of the imprinter can be adjusted to be appropriate for various soils and planting conditions by filling the roller and ballast tanks with water.<a href="#cite_note-rfForestService2004-2">[2]</a>

<div class="mw-heading mw-heading2"><h2 id="Uses_and_limitations">Uses and limitations</h2></div>

The land imprinter was initially developed to <a href="Revegetation" title="Revegetation">revegetate</a> desertified land in the southwestern United States and has been used to plant 20,000 hectares of land with grasses and other plant species in <a href="Arizona" title="Arizona">Arizona</a>.<a href="#cite_note-rfDixonCarr2004-11">[11]</a> Imprinting is most effective on <a href="Loam" title="Loam">loam</a> soils that have some moisture but are not wet, which can cause soil to become compacted into the imprinter teeth.<a href="#cite_note-rfArmyCorps1986-3">[3]</a> Imprinting has been conducted on slopes of up to 45% grade. For those applications cables can be used to tow the imprinter up the incline.<a href="#cite_note-rfArmyCorps1986-3">[3]</a> The land imprinter is not well adapted for shallow soil or extremely rocky soil and is not well suited to mulching large stands of brush.<a href="#cite_note-rfArmyCorps1986-3">[3]</a> Large shrubs must be chopped or removed prior to imprinting.<a href="#cite_note-rfDixon1990-8">[8]</a>

The land imprinter is typically used directly on unprepared soils, without initial <a href="Tillage" title="Tillage">tilling</a>. The heavy roller and angled teeth crush weeds and brush into mulch, which remain as a nutrient base for new seedlings. Accordingly, it can be used on land that has been burned either intentionally or in <a href="Wildfire" title="Wildfire">wildfires</a>, where remnant vegetation should be retained.<a href="#cite_note-rfForestService2004-2">[2]</a>

Imprinting is best suited for seeding on loose soils, and where there is either no existing <a href="Plant_cover" title="Plant cover">plant cover</a>—or light to moderate brush cover—before planting.<a href="#cite_note-rfForestService2004-2">[2]</a> Haferkamp and colleagues compared <a href="Seed_drill" title="Seed drill">seed drill</a> planting to imprinting on loose and firm seedbeds on a <a href="Wyoming" title="Wyoming">Wyoming</a> big <a href="Sagebrush" title="Sagebrush">sagebrush</a> and <a href="Needlegrass" title="Needlegrass">needlegrass</a> habitat. Drilling produced more seedlings on firm seedbeds, whereas imprinting produced two times more seedlings on loose soils, compared to drilling.<a href="#cite_note-rfHaferkamp_etAl_1987-13">[13]</a> Haferkamp and colleagues used brushbeating plus disking to create the loosened soil treatment in that study.<a href="#cite_note-rfHaferkamp_etAl_1987-13">[13]</a> Ripping or chisel plowing can be used as alternatives to disking when soil is deeply compacted, as they are less destructive to soil components than disking.<a href="#cite_note-rfDixon1990-8">[8]</a>

The land imprinter creates microdepressions in the soil that effectively reduce erosion and runoff.<a href="#cite_note-rfAnderson1981-14">[14]</a> Imprinting has been found to be superior to drilling at research sites in <a href="Utah" title="Utah">Utah</a>,<a href="#cite_note-rfClary_etAl_1983-15">[15]</a> and superior to chaining after aerial broadcasting on burned seedbeds in <a href="Oregon" title="Oregon">Oregon</a>.<a href="#cite_note-rfGanskopp1985-16">[16]</a>

<div class="mw-heading mw-heading2"><h2 id="References">References</h2></div>

/* start https://en.wikipedia.org/ */

.mw-parser-output .reflist{margin-bottom:0.5em;list-style-type:decimal}@media screen{.mw-parser-output .reflist{font-size:90%}}.mw-parser-output .reflist .references{font-size:100%;margin-bottom:0;list-style-type:inherit}.mw-parser-output .reflist-columns-2{column-width:30em}.mw-parser-output .reflist-columns-3{column-width:25em}.mw-parser-output .reflist-columns{margin-top:0.3em}.mw-parser-output .reflist-columns ol{margin-top:0}.mw-parser-output .reflist-columns li{page-break-inside:avoid;break-inside:avoid-column}.mw-parser-output .reflist-upper-alpha{list-style-type:upper-alpha}.mw-parser-output .reflist-upper-roman{list-style-type:upper-roman}.mw-parser-output .reflist-lower-alpha{list-style-type:lower-alpha}.mw-parser-output .reflist-lower-greek{list-style-type:lower-greek}.mw-parser-output .reflist-lower-roman{list-style-type:lower-roman}

/* end https://en.wikipedia.org/ */

</style><div class="reflist">

<li id="cite_note-rfPatent-1"><a href="#cite_ref-rfPatent_1-0">^</a> <a rel="nofollow" class="external text" href="http://www.google.com/patents?hl=en&lr=&vid=USPAT4195695&id=pxQ0AAAAEBAJ&oi=fnd&dq=%22land+imprinter%22&printsec=abstract#v=onepage&q&f=false">US Patent 4,195,695.</a> (1980).

</li>

<li id="cite_note-rfForestService2004-2">^ <a href="#cite_ref-rfForestService2004_2-0">a</a> <a href="#cite_ref-rfForestService2004_2-1">b</a> <a href="#cite_ref-rfForestService2004_2-2">c</a> <a href="#cite_ref-rfForestService2004_2-3">d</a> <a href="#cite_ref-rfForestService2004_2-4">e</a> Stevens, R. and Monsen, S. B. (2004). <a rel="nofollow" class="external text" href="http://www.fs.fed.us/rm/pubs/rmrs_gtr136_1/rmrs_gtr136_1_065_088.pdf">Mechanical plant control</a> in Restoring western ranges and wildlands, vol. 1. Gen. Tech. Rep. RMRS-GTR-136-vol-1, 65-88. U.S. Department of Agriculture, Forest Service: Fort Collins, CO.

</li>

<li id="cite_note-rfArmyCorps1986-3">^ <a href="#cite_ref-rfArmyCorps1986_3-0">a</a> <a href="#cite_ref-rfArmyCorps1986_3-1">b</a> <a href="#cite_ref-rfArmyCorps1986_3-2">c</a> <a href="#cite_ref-rfArmyCorps1986_3-3">d</a> Doer, B. D. (1986). <a rel="nofollow" class="external text" href="https://web.archive.org/web/20121008175832/http://www.dtic.mil/cgi-bin/GetTRDoc?AD=ADA257377&Location=U2&doc=GetTRDoc.pdf">Technical report EL-86-43: Land imprinters</a> Section 8.2.7., US Army Corps of Engineers Wildlife Resources Management Manual, July 1986 Final Report, Department of the Army, <a href="United_States_Army_Corps_of_Engineers" title="United States Army Corps of Engineers">US Army Corps of Engineers</a>: Washington, DC.

</li>

<li id="cite_note-rfWrobelRedford-4"><a href="#cite_ref-rfWrobelRedford_4-0">^</a> Wrobel, M. L. and Redford, K. H. (2010). "Introduction: A review of rangeland conservation issues in an uncertain future," in Wild Rangelands: Conserving Wildlife While Maintaining Livestock in Semi-Arid Ecosystems (eds J. T. du Toit, R. Kock and J. C. Deutsch), John Wiley & Sons, Ltd: Chichester, UK.

</li>

<li id="cite_note-rfBrown-5"><a href="#cite_ref-rfBrown_5-0">^</a> Brown, L.R. (2008). Plan B 3.0: Mobilizing to Save Civilization. W.W. Norton & Company, Inc.: New York.

</li>

<li id="cite_note-rfMontgomery-6"><a href="#cite_ref-rfMontgomery_6-0">^</a> Montgomery, D.R. (2007). Dirt: The Erosion of Civilizations, University of California Press: Berkeley and Los Angeles.

</li>

<li id="cite_note-rfDixon1995-7">^ <a href="#cite_ref-rfDixon1995_7-0">a</a> <a href="#cite_ref-rfDixon1995_7-1">b</a> <a href="#cite_ref-rfDixon1995_7-2">c</a> <a href="#cite_ref-rfDixon1995_7-3">d</a> Dixon, R. M. (1995). "Water infiltration control at the soil surface: Theory and practice." Journal of Soil and Water Conservation 50 (5), 450-453.

</li>

<li id="cite_note-rfDixon1990-8">^ <a href="#cite_ref-rfDixon1990_8-0">a</a> <a href="#cite_ref-rfDixon1990_8-1">b</a> <a href="#cite_ref-rfDixon1990_8-2">c</a> Dixon, R. M. (1990). <a rel="nofollow" class="external text" href="https://books.google.com/books?id=H0ZZnTdkt5cC&pg=PA14">Land imprinting for dryland revegetation and restoration</a> in Environmental restoration: Science and strategies for restoring the Earth (ed J. J. Berger), Island Press: Washington, DC.

</li>

<li id="cite_note-DixonPeterson1971-9">^ <a href="#cite_ref-DixonPeterson1971_9-0">a</a> <a href="#cite_ref-DixonPeterson1971_9-1">b</a> Dixon, R. M. and Peterson, A. E. (1971). "Water infiltration control: A channel system concept." Soil Science Society of America Proceedings 35, 968-973.

</li>

<li id="cite_note-rfDixon1989-10"><a href="#cite_ref-rfDixon1989_10-0">^</a> Dixon, R. M. (1989). <a rel="nofollow" class="external text" href="http://www.fs.fed.us/psw/publications/documents/psw_gtr110/psw_gtr110_i_dixon.pdf">Air-earth interface model for restoring riparian habitats</a>, Proceedings of the California Riparian Systems Conference, September 22–24, 1988, Davis, CA.

</li>

<li id="cite_note-rfDixonCarr2004-11">^ <a href="#cite_ref-rfDixonCarr2004_11-0">a</a> <a href="#cite_ref-rfDixonCarr2004_11-1">b</a> Dixon, R. M. and Carr, A. B. (2004). "Land imprinting standards for accelerating succession past the exotic weed stage." Proceedings of the 16th International Conference of the <a href="Society_for_Ecological_Restoration" title="Society for Ecological Restoration">Society for Ecological Restoration</a>, August 24–26, 2004, Victoria, Canada.

</li>

<li id="cite_note-rfRoundy_etAl1992-12"><a href="#cite_ref-rfRoundy_etAl1992_12-0">^</a> Roundy, B. A., Winkelb, V. K., Khalifab, H., and Matthias, A. D. (1992). "Soil water availability and temperature dynamics after one-time heavy cattle trampling and land imprinting," Arid Land Research and Management 6 (1), 53-69.

</li>

<li id="cite_note-rfHaferkamp_etAl_1987-13">^ <a href="#cite_ref-rfHaferkamp_etAl_1987_13-0">a</a> <a href="#cite_ref-rfHaferkamp_etAl_1987_13-1">b</a> Haferkamp, M.R., Ganskopp, D., Miller, R.F., and Sneva, F.A. (1987). <a rel="nofollow" class="external text" href="http://oregonstate.edu/dept/eoarc/sites/default/files/researchhome/documents/326.pdf">Drilling versus imprinting for establishing crested wheatgrass in the sagebrush - bunchgrass steppe</a> Journal of Range Management 40 (6), 524-530.

</li>

<li id="cite_note-rfAnderson1981-14"><a href="#cite_ref-rfAnderson1981_14-0">^</a> Anderson, R. (1981). "A story in two parts: Advance of the barren earth, technology for reversing desertification," Rangelands 3, 47-50.

</li>

<li id="cite_note-rfClary_etAl_1983-15"><a href="#cite_ref-rfClary_etAl_1983_15-0">^</a> Clary, W. C. and Johnson, T. J. (1983). "Land imprinter results in Utah," in 37th Annual Report, Vegetative Rehabilitation & Equipment Workshop, Albuquerque, NM, pg. 23-24, USDA Forest Service, Equipment Development Center: Missoula, MT.

</li>

<li id="cite_note-rfGanskopp1985-16"><a href="#cite_ref-rfGanskopp1985_16-0">^</a> Ganskopp, D. C. (1985). "Success of broadcast seeding on untreated, imprinted and chained rangelands," in Special report - Oregon State University, Agricultural Experiment Station 743, pg. 4-6. <a href="Oregon_State_University" title="Oregon State University">Oregon State University</a>: Corvallis, OR.

</li>

</ol></div></div></div><div><div class="zim-footer">

This article is issued from <a class="external text" title="Last edited on 2024-06-08" href="https://en.wikipedia.org/wiki/?title=Land_imprinter&oldid=1227945373">Wikipedia</a>. The text is available under <a class="external text" href="https://creativecommons.org/licenses/by-sa/4.0/deed.en">Creative Commons Attribution-Share Alike 4.0</a> unless otherwise noted. Additional terms may apply for the media files.

</div>

</div></div>

</div>

</main>

</div>

</body></html>