<?xml version="1.0"?>
<feed xmlns="http://www.w3.org/2005/Atom" xml:lang="en">
	<id>https://www.iamcdocumentation.eu/history/Land-use_-_AIM-Hub?feed=atom</id>
	<title>Land-use - AIM-Hub - Revision history</title>
	<link rel="self" type="application/atom+xml" href="https://www.iamcdocumentation.eu/history/Land-use_-_AIM-Hub?feed=atom"/>
	<link rel="alternate" type="text/html" href="https://www.iamcdocumentation.eu/history/Land-use_-_AIM-Hub"/>
	<updated>2026-05-04T14:47:27Z</updated>
	<subtitle>Revision history for this page on the wiki</subtitle>
	<generator>MediaWiki 1.39.15</generator>
	<entry>
		<id>https://www.iamcdocumentation.eu/index.php?title=Land-use_-_AIM-Hub&amp;diff=13026&amp;oldid=prev</id>
		<title>Rineke Oostenrijk: Text replacement - &quot;IsDocumentationOf=AIM-CGE&quot; to &quot;IsDocumentationOf=AIM-Hub&quot;</title>
		<link rel="alternate" type="text/html" href="https://www.iamcdocumentation.eu/index.php?title=Land-use_-_AIM-Hub&amp;diff=13026&amp;oldid=prev"/>
		<updated>2020-06-15T13:18:50Z</updated>

		<summary type="html">&lt;p&gt;Text replacement - &amp;quot;IsDocumentationOf=AIM-CGE&amp;quot; to &amp;quot;IsDocumentationOf=AIM-Hub&amp;quot;&lt;/p&gt;
&lt;table style=&quot;background-color: #fff; color: #202122;&quot; data-mw=&quot;interface&quot;&gt;
				&lt;col class=&quot;diff-marker&quot; /&gt;
				&lt;col class=&quot;diff-content&quot; /&gt;
				&lt;col class=&quot;diff-marker&quot; /&gt;
				&lt;col class=&quot;diff-content&quot; /&gt;
				&lt;tr class=&quot;diff-title&quot; lang=&quot;en&quot;&gt;
				&lt;td colspan=&quot;2&quot; style=&quot;background-color: #fff; color: #202122; text-align: center;&quot;&gt;← Older revision&lt;/td&gt;
				&lt;td colspan=&quot;2&quot; style=&quot;background-color: #fff; color: #202122; text-align: center;&quot;&gt;Revision as of 15:18, 15 June 2020&lt;/td&gt;
				&lt;/tr&gt;&lt;tr&gt;&lt;td colspan=&quot;2&quot; class=&quot;diff-lineno&quot; id=&quot;mw-diff-left-l1&quot;&gt;Line 1:&lt;/td&gt;
&lt;td colspan=&quot;2&quot; class=&quot;diff-lineno&quot;&gt;Line 1:&lt;/td&gt;&lt;/tr&gt;
&lt;tr&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;{{ModelDocumentationTemplate&lt;/div&gt;&lt;/td&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;{{ModelDocumentationTemplate&lt;/div&gt;&lt;/td&gt;&lt;/tr&gt;
&lt;tr&gt;&lt;td class=&quot;diff-marker&quot; data-marker=&quot;−&quot;&gt;&lt;/td&gt;&lt;td style=&quot;color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #ffe49c; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;|IsDocumentationOf=AIM-&lt;del style=&quot;font-weight: bold; text-decoration: none;&quot;&gt;CGE&lt;/del&gt;&lt;/div&gt;&lt;/td&gt;&lt;td class=&quot;diff-marker&quot; data-marker=&quot;+&quot;&gt;&lt;/td&gt;&lt;td style=&quot;color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #a3d3ff; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;|IsDocumentationOf=AIM-&lt;ins style=&quot;font-weight: bold; text-decoration: none;&quot;&gt;Hub&lt;/ins&gt;&lt;/div&gt;&lt;/td&gt;&lt;/tr&gt;
&lt;tr&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;|DocumentationCategory=Land-use&lt;/div&gt;&lt;/td&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;|DocumentationCategory=Land-use&lt;/div&gt;&lt;/td&gt;&lt;/tr&gt;
&lt;tr&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;}}&lt;/div&gt;&lt;/td&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;}}&lt;/div&gt;&lt;/td&gt;&lt;/tr&gt;

&lt;!-- diff cache key iamcdb:diff::1.12:old-12937:rev-13026 --&gt;
&lt;/table&gt;</summary>
		<author><name>Rineke Oostenrijk</name></author>
	</entry>
	<entry>
		<id>https://www.iamcdocumentation.eu/index.php?title=Land-use_-_AIM-Hub&amp;diff=12937&amp;oldid=prev</id>
		<title>Rineke Oostenrijk: Rineke Oostenrijk moved page Land-use - AIM-CGE to Land-use - AIM-Hub without leaving a redirect: Text replacement - &quot;AIM-CGE&quot; to &quot;AIM-Hub&quot;</title>
		<link rel="alternate" type="text/html" href="https://www.iamcdocumentation.eu/index.php?title=Land-use_-_AIM-Hub&amp;diff=12937&amp;oldid=prev"/>
		<updated>2020-06-15T12:52:59Z</updated>

		<summary type="html">&lt;p&gt;Rineke Oostenrijk moved page &lt;a href=&quot;/edit/Land-use_-_AIM-CGE?redlink=1&quot; class=&quot;new&quot; title=&quot;Land-use - AIM-CGE (page does not exist)&quot;&gt;Land-use - AIM-CGE&lt;/a&gt; to &lt;a href=&quot;/Land-use_-_AIM-Hub&quot; title=&quot;Land-use - AIM-Hub&quot;&gt;Land-use - AIM-Hub&lt;/a&gt; without leaving a redirect: Text replacement - &amp;quot;AIM-CGE&amp;quot; to &amp;quot;AIM-Hub&amp;quot;&lt;/p&gt;
&lt;table style=&quot;background-color: #fff; color: #202122;&quot; data-mw=&quot;interface&quot;&gt;
				&lt;col class=&quot;diff-marker&quot; /&gt;
				&lt;col class=&quot;diff-content&quot; /&gt;
				&lt;col class=&quot;diff-marker&quot; /&gt;
				&lt;col class=&quot;diff-content&quot; /&gt;
				&lt;tr class=&quot;diff-title&quot; lang=&quot;en&quot;&gt;
				&lt;td colspan=&quot;2&quot; style=&quot;background-color: #fff; color: #202122; text-align: center;&quot;&gt;← Older revision&lt;/td&gt;
				&lt;td colspan=&quot;2&quot; style=&quot;background-color: #fff; color: #202122; text-align: center;&quot;&gt;Revision as of 14:52, 15 June 2020&lt;/td&gt;
				&lt;/tr&gt;
&lt;!-- diff cache key iamcdb:diff::1.12:old-6317:rev-12937 --&gt;
&lt;/table&gt;</summary>
		<author><name>Rineke Oostenrijk</name></author>
	</entry>
	<entry>
		<id>https://www.iamcdocumentation.eu/index.php?title=Land-use_-_AIM-Hub&amp;diff=6317&amp;oldid=prev</id>
		<title>Shinichiro Fujimori at 03:35, 7 December 2016</title>
		<link rel="alternate" type="text/html" href="https://www.iamcdocumentation.eu/index.php?title=Land-use_-_AIM-Hub&amp;diff=6317&amp;oldid=prev"/>
		<updated>2016-12-07T03:35:28Z</updated>

		<summary type="html">&lt;p&gt;&lt;/p&gt;
&lt;table style=&quot;background-color: #fff; color: #202122;&quot; data-mw=&quot;interface&quot;&gt;
				&lt;col class=&quot;diff-marker&quot; /&gt;
				&lt;col class=&quot;diff-content&quot; /&gt;
				&lt;col class=&quot;diff-marker&quot; /&gt;
				&lt;col class=&quot;diff-content&quot; /&gt;
				&lt;tr class=&quot;diff-title&quot; lang=&quot;en&quot;&gt;
				&lt;td colspan=&quot;2&quot; style=&quot;background-color: #fff; color: #202122; text-align: center;&quot;&gt;← Older revision&lt;/td&gt;
				&lt;td colspan=&quot;2&quot; style=&quot;background-color: #fff; color: #202122; text-align: center;&quot;&gt;Revision as of 05:35, 7 December 2016&lt;/td&gt;
				&lt;/tr&gt;&lt;tr&gt;&lt;td colspan=&quot;2&quot; class=&quot;diff-lineno&quot; id=&quot;mw-diff-left-l3&quot;&gt;Line 3:&lt;/td&gt;
&lt;td colspan=&quot;2&quot; class=&quot;diff-lineno&quot;&gt;Line 3:&lt;/td&gt;&lt;/tr&gt;
&lt;tr&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;|DocumentationCategory=Land-use&lt;/div&gt;&lt;/td&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;|DocumentationCategory=Land-use&lt;/div&gt;&lt;/td&gt;&lt;/tr&gt;
&lt;tr&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;}}&lt;/div&gt;&lt;/td&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;}}&lt;/div&gt;&lt;/td&gt;&lt;/tr&gt;
&lt;tr&gt;&lt;td class=&quot;diff-marker&quot; data-marker=&quot;−&quot;&gt;&lt;/td&gt;&lt;td style=&quot;color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #ffe49c; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;A function is used whereby land is an input for the production of crops and livestock products, and landowners change its use in accordance with the prices of goods produced on cropland, pastureland, and in forests. The model has a land nesting strategy, which is similar to the treatment in Sands and Edmonds (2005) and Wise and Calvin (2011). Land is categorized as one of &lt;del style=&quot;font-weight: bold; text-decoration: none;&quot;&gt;three &lt;/del&gt;ecological zones, and there is a land market for each zone. Allocation of land by sector is formulated as a multinominal logit function to reflect the differences in substitutability across land categories with land rent. The function assumes that the landowner of each region and Agro-Ecological Zone (AEZ) decides on the land distribution among the possible options, with the land rent dependent on the production of each land type (i.e., crops, livestock, and wood products). We deal with all land excluding desert, rock, ice, tundra, and built-up land. The &lt;del style=&quot;font-weight: bold; text-decoration: none;&quot;&gt;model &lt;/del&gt;has 18 AEZ classifications.&lt;/div&gt;&lt;/td&gt;&lt;td class=&quot;diff-marker&quot; data-marker=&quot;+&quot;&gt;&lt;/td&gt;&lt;td style=&quot;color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #a3d3ff; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;A function is used whereby land is an input for the production of crops and livestock products, and landowners change its use in accordance with the prices of goods produced on cropland, pastureland, and in forests. The model has a land nesting strategy, which is similar to the treatment in Sands and Edmonds (2005) and Wise and Calvin (2011). Land is categorized as one of &lt;ins style=&quot;font-weight: bold; text-decoration: none;&quot;&gt;nine &lt;/ins&gt;ecological zones, and there is a land market for each zone. Allocation of land by sector is formulated as a multinominal logit function to reflect the differences in substitutability across land categories with land rent&lt;ins style=&quot;font-weight: bold; text-decoration: none;&quot;&gt;. Multinominal logit function allows us multi level nesting structure in logit selection&lt;/ins&gt;. The function assumes that the landowner of each region and Agro-Ecological Zone (AEZ) decides on the land distribution among the possible options, with the land rent dependent on the production of each land type (i.e., crops, livestock, and wood products). We deal with all land excluding desert, rock, ice, tundra, and built-up land. The &lt;ins style=&quot;font-weight: bold; text-decoration: none;&quot;&gt;original social accounting matrix data &lt;/ins&gt;has 18 AEZ classifications &lt;ins style=&quot;font-weight: bold; text-decoration: none;&quot;&gt;but the model deals with aggregated 9 classification&lt;/ins&gt;.&lt;/div&gt;&lt;/td&gt;&lt;/tr&gt;
&lt;tr&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;br/&gt;&lt;/td&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;br/&gt;&lt;/td&gt;&lt;/tr&gt;
&lt;tr&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;[[File:38469888.png|thumb|500px|left]]&lt;/div&gt;&lt;/td&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;[[File:38469888.png|thumb|500px|left]]&lt;/div&gt;&lt;/td&gt;&lt;/tr&gt;
&lt;tr&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;br/&gt;&lt;/td&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;br/&gt;&lt;/td&gt;&lt;/tr&gt;
&lt;tr&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;The figure shows the nesting diagram for land using AEZ classification. We consider all land excluding desert, rock, ice, tundra, and built-up land. There are 18 AEZ classifications. At the top is all land, which is divided into two main nodes: forestry land and non-forest land. The forestry-land node contains two competing uses: primary forest (unmanaged forest) and secondary forest (managed forest). The non-forested land can be divided into grassland and cropland. The grassland can be further divided into primary grassland (unmanaged pasture) and grazing grassland (managed pasture that feeds marketed livestock); the latter is further divided into livestock types (1 to n). The cropland could be divided further into cropland for each crop type (1 to n) and fallow land. The nesting strategy is based on the assumption that the land regions are small enough that all competing options are equally substitutable. This assumption implies that it is as easy to switch from forest to wheat as it is to switch from corn to wheat. However, this conversion would not happen unless wheat was more profitable than forest or corn. The function assumes that the landowner of each region and AEZ subregion decides on the land distribution among the possible options depending on the land rent obtained from production with each land use (i.e., crops, livestock, and wood products). To calibrate the function for both the managed and unmanaged land in the base year, we took the mean base-year land rent of the managed land to be that of the unmanaged land because data for the unmanaged land were lacking. The carbon stock on forest land was evaluated by the price in the case of the climate mitigation scenario. The land rent of forest areas includes both the revenue from wood products and the price of the carbon stock.&lt;/div&gt;&lt;/td&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;The figure shows the nesting diagram for land using AEZ classification. We consider all land excluding desert, rock, ice, tundra, and built-up land. There are 18 AEZ classifications. At the top is all land, which is divided into two main nodes: forestry land and non-forest land. The forestry-land node contains two competing uses: primary forest (unmanaged forest) and secondary forest (managed forest). The non-forested land can be divided into grassland and cropland. The grassland can be further divided into primary grassland (unmanaged pasture) and grazing grassland (managed pasture that feeds marketed livestock); the latter is further divided into livestock types (1 to n). The cropland could be divided further into cropland for each crop type (1 to n) and fallow land. The nesting strategy is based on the assumption that the land regions are small enough that all competing options are equally substitutable. This assumption implies that it is as easy to switch from forest to wheat as it is to switch from corn to wheat. However, this conversion would not happen unless wheat was more profitable than forest or corn. The function assumes that the landowner of each region and AEZ subregion decides on the land distribution among the possible options depending on the land rent obtained from production with each land use (i.e., crops, livestock, and wood products). To calibrate the function for both the managed and unmanaged land in the base year, we took the mean base-year land rent of the managed land to be that of the unmanaged land because data for the unmanaged land were lacking. The carbon stock on forest land was evaluated by the price in the case of the climate mitigation scenario. The land rent of forest areas includes both the revenue from wood products and the price of the carbon stock.&lt;/div&gt;&lt;/td&gt;&lt;/tr&gt;
&lt;/table&gt;</summary>
		<author><name>Shinichiro Fujimori</name></author>
	</entry>
	<entry>
		<id>https://www.iamcdocumentation.eu/index.php?title=Land-use_-_AIM-Hub&amp;diff=4129&amp;oldid=prev</id>
		<title>Rineke Oostenrijk at 06:00, 24 August 2016</title>
		<link rel="alternate" type="text/html" href="https://www.iamcdocumentation.eu/index.php?title=Land-use_-_AIM-Hub&amp;diff=4129&amp;oldid=prev"/>
		<updated>2016-08-24T06:00:00Z</updated>

		<summary type="html">&lt;p&gt;&lt;/p&gt;
&lt;table style=&quot;background-color: #fff; color: #202122;&quot; data-mw=&quot;interface&quot;&gt;
				&lt;col class=&quot;diff-marker&quot; /&gt;
				&lt;col class=&quot;diff-content&quot; /&gt;
				&lt;col class=&quot;diff-marker&quot; /&gt;
				&lt;col class=&quot;diff-content&quot; /&gt;
				&lt;tr class=&quot;diff-title&quot; lang=&quot;en&quot;&gt;
				&lt;td colspan=&quot;2&quot; style=&quot;background-color: #fff; color: #202122; text-align: center;&quot;&gt;← Older revision&lt;/td&gt;
				&lt;td colspan=&quot;2&quot; style=&quot;background-color: #fff; color: #202122; text-align: center;&quot;&gt;Revision as of 08:00, 24 August 2016&lt;/td&gt;
				&lt;/tr&gt;&lt;tr&gt;&lt;td colspan=&quot;2&quot; class=&quot;diff-lineno&quot; id=&quot;mw-diff-left-l5&quot;&gt;Line 5:&lt;/td&gt;
&lt;td colspan=&quot;2&quot; class=&quot;diff-lineno&quot;&gt;Line 5:&lt;/td&gt;&lt;/tr&gt;
&lt;tr&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;A function is used whereby land is an input for the production of crops and livestock products, and landowners change its use in accordance with the prices of goods produced on cropland, pastureland, and in forests. The model has a land nesting strategy, which is similar to the treatment in Sands and Edmonds (2005) and Wise and Calvin (2011). Land is categorized as one of three ecological zones, and there is a land market for each zone. Allocation of land by sector is formulated as a multinominal logit function to reflect the differences in substitutability across land categories with land rent. The function assumes that the landowner of each region and Agro-Ecological Zone (AEZ) decides on the land distribution among the possible options, with the land rent dependent on the production of each land type (i.e., crops, livestock, and wood products). We deal with all land excluding desert, rock, ice, tundra, and built-up land. The model has 18 AEZ classifications.&lt;/div&gt;&lt;/td&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;A function is used whereby land is an input for the production of crops and livestock products, and landowners change its use in accordance with the prices of goods produced on cropland, pastureland, and in forests. The model has a land nesting strategy, which is similar to the treatment in Sands and Edmonds (2005) and Wise and Calvin (2011). Land is categorized as one of three ecological zones, and there is a land market for each zone. Allocation of land by sector is formulated as a multinominal logit function to reflect the differences in substitutability across land categories with land rent. The function assumes that the landowner of each region and Agro-Ecological Zone (AEZ) decides on the land distribution among the possible options, with the land rent dependent on the production of each land type (i.e., crops, livestock, and wood products). We deal with all land excluding desert, rock, ice, tundra, and built-up land. The model has 18 AEZ classifications.&lt;/div&gt;&lt;/td&gt;&lt;/tr&gt;
&lt;tr&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;br/&gt;&lt;/td&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;br/&gt;&lt;/td&gt;&lt;/tr&gt;
&lt;tr&gt;&lt;td class=&quot;diff-marker&quot; data-marker=&quot;−&quot;&gt;&lt;/td&gt;&lt;td style=&quot;color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #ffe49c; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;[[File:38469888.png|thumb|500px]]&lt;/div&gt;&lt;/td&gt;&lt;td class=&quot;diff-marker&quot; data-marker=&quot;+&quot;&gt;&lt;/td&gt;&lt;td style=&quot;color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #a3d3ff; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;[[File:38469888.png|thumb|500px&lt;ins style=&quot;font-weight: bold; text-decoration: none;&quot;&gt;|left&lt;/ins&gt;]]&lt;/div&gt;&lt;/td&gt;&lt;/tr&gt;
&lt;tr&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;br/&gt;&lt;/td&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;br/&gt;&lt;/td&gt;&lt;/tr&gt;
&lt;tr&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;The figure shows the nesting diagram for land using AEZ classification. We consider all land excluding desert, rock, ice, tundra, and built-up land. There are 18 AEZ classifications. At the top is all land, which is divided into two main nodes: forestry land and non-forest land. The forestry-land node contains two competing uses: primary forest (unmanaged forest) and secondary forest (managed forest). The non-forested land can be divided into grassland and cropland. The grassland can be further divided into primary grassland (unmanaged pasture) and grazing grassland (managed pasture that feeds marketed livestock); the latter is further divided into livestock types (1 to n). The cropland could be divided further into cropland for each crop type (1 to n) and fallow land. The nesting strategy is based on the assumption that the land regions are small enough that all competing options are equally substitutable. This assumption implies that it is as easy to switch from forest to wheat as it is to switch from corn to wheat. However, this conversion would not happen unless wheat was more profitable than forest or corn. The function assumes that the landowner of each region and AEZ subregion decides on the land distribution among the possible options depending on the land rent obtained from production with each land use (i.e., crops, livestock, and wood products). To calibrate the function for both the managed and unmanaged land in the base year, we took the mean base-year land rent of the managed land to be that of the unmanaged land because data for the unmanaged land were lacking. The carbon stock on forest land was evaluated by the price in the case of the climate mitigation scenario. The land rent of forest areas includes both the revenue from wood products and the price of the carbon stock.&lt;/div&gt;&lt;/td&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;The figure shows the nesting diagram for land using AEZ classification. We consider all land excluding desert, rock, ice, tundra, and built-up land. There are 18 AEZ classifications. At the top is all land, which is divided into two main nodes: forestry land and non-forest land. The forestry-land node contains two competing uses: primary forest (unmanaged forest) and secondary forest (managed forest). The non-forested land can be divided into grassland and cropland. The grassland can be further divided into primary grassland (unmanaged pasture) and grazing grassland (managed pasture that feeds marketed livestock); the latter is further divided into livestock types (1 to n). The cropland could be divided further into cropland for each crop type (1 to n) and fallow land. The nesting strategy is based on the assumption that the land regions are small enough that all competing options are equally substitutable. This assumption implies that it is as easy to switch from forest to wheat as it is to switch from corn to wheat. However, this conversion would not happen unless wheat was more profitable than forest or corn. The function assumes that the landowner of each region and AEZ subregion decides on the land distribution among the possible options depending on the land rent obtained from production with each land use (i.e., crops, livestock, and wood products). To calibrate the function for both the managed and unmanaged land in the base year, we took the mean base-year land rent of the managed land to be that of the unmanaged land because data for the unmanaged land were lacking. The carbon stock on forest land was evaluated by the price in the case of the climate mitigation scenario. The land rent of forest areas includes both the revenue from wood products and the price of the carbon stock.&lt;/div&gt;&lt;/td&gt;&lt;/tr&gt;

&lt;!-- diff cache key iamcdb:diff::1.12:old-4128:rev-4129 --&gt;
&lt;/table&gt;</summary>
		<author><name>Rineke Oostenrijk</name></author>
	</entry>
	<entry>
		<id>https://www.iamcdocumentation.eu/index.php?title=Land-use_-_AIM-Hub&amp;diff=4128&amp;oldid=prev</id>
		<title>Rineke Oostenrijk at 05:54, 24 August 2016</title>
		<link rel="alternate" type="text/html" href="https://www.iamcdocumentation.eu/index.php?title=Land-use_-_AIM-Hub&amp;diff=4128&amp;oldid=prev"/>
		<updated>2016-08-24T05:54:55Z</updated>

		<summary type="html">&lt;p&gt;&lt;/p&gt;
&lt;table style=&quot;background-color: #fff; color: #202122;&quot; data-mw=&quot;interface&quot;&gt;
				&lt;col class=&quot;diff-marker&quot; /&gt;
				&lt;col class=&quot;diff-content&quot; /&gt;
				&lt;col class=&quot;diff-marker&quot; /&gt;
				&lt;col class=&quot;diff-content&quot; /&gt;
				&lt;tr class=&quot;diff-title&quot; lang=&quot;en&quot;&gt;
				&lt;td colspan=&quot;2&quot; style=&quot;background-color: #fff; color: #202122; text-align: center;&quot;&gt;← Older revision&lt;/td&gt;
				&lt;td colspan=&quot;2&quot; style=&quot;background-color: #fff; color: #202122; text-align: center;&quot;&gt;Revision as of 07:54, 24 August 2016&lt;/td&gt;
				&lt;/tr&gt;&lt;tr&gt;&lt;td colspan=&quot;2&quot; class=&quot;diff-lineno&quot; id=&quot;mw-diff-left-l5&quot;&gt;Line 5:&lt;/td&gt;
&lt;td colspan=&quot;2&quot; class=&quot;diff-lineno&quot;&gt;Line 5:&lt;/td&gt;&lt;/tr&gt;
&lt;tr&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;A function is used whereby land is an input for the production of crops and livestock products, and landowners change its use in accordance with the prices of goods produced on cropland, pastureland, and in forests. The model has a land nesting strategy, which is similar to the treatment in Sands and Edmonds (2005) and Wise and Calvin (2011). Land is categorized as one of three ecological zones, and there is a land market for each zone. Allocation of land by sector is formulated as a multinominal logit function to reflect the differences in substitutability across land categories with land rent. The function assumes that the landowner of each region and Agro-Ecological Zone (AEZ) decides on the land distribution among the possible options, with the land rent dependent on the production of each land type (i.e., crops, livestock, and wood products). We deal with all land excluding desert, rock, ice, tundra, and built-up land. The model has 18 AEZ classifications.&lt;/div&gt;&lt;/td&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;A function is used whereby land is an input for the production of crops and livestock products, and landowners change its use in accordance with the prices of goods produced on cropland, pastureland, and in forests. The model has a land nesting strategy, which is similar to the treatment in Sands and Edmonds (2005) and Wise and Calvin (2011). Land is categorized as one of three ecological zones, and there is a land market for each zone. Allocation of land by sector is formulated as a multinominal logit function to reflect the differences in substitutability across land categories with land rent. The function assumes that the landowner of each region and Agro-Ecological Zone (AEZ) decides on the land distribution among the possible options, with the land rent dependent on the production of each land type (i.e., crops, livestock, and wood products). We deal with all land excluding desert, rock, ice, tundra, and built-up land. The model has 18 AEZ classifications.&lt;/div&gt;&lt;/td&gt;&lt;/tr&gt;
&lt;tr&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;br/&gt;&lt;/td&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;br/&gt;&lt;/td&gt;&lt;/tr&gt;
&lt;tr&gt;&lt;td class=&quot;diff-marker&quot; data-marker=&quot;−&quot;&gt;&lt;/td&gt;&lt;td style=&quot;color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #ffe49c; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;[[File:38469888.png|thumb|500px&lt;del style=&quot;font-weight: bold; text-decoration: none;&quot;&gt;|left&lt;/del&gt;]]&lt;/div&gt;&lt;/td&gt;&lt;td class=&quot;diff-marker&quot; data-marker=&quot;+&quot;&gt;&lt;/td&gt;&lt;td style=&quot;color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #a3d3ff; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;[[File:38469888.png|thumb|500px]]&lt;/div&gt;&lt;/td&gt;&lt;/tr&gt;
&lt;tr&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;br/&gt;&lt;/td&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;br/&gt;&lt;/td&gt;&lt;/tr&gt;
&lt;tr&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;The figure shows the nesting diagram for land using AEZ classification. We consider all land excluding desert, rock, ice, tundra, and built-up land. There are 18 AEZ classifications. At the top is all land, which is divided into two main nodes: forestry land and non-forest land. The forestry-land node contains two competing uses: primary forest (unmanaged forest) and secondary forest (managed forest). The non-forested land can be divided into grassland and cropland. The grassland can be further divided into primary grassland (unmanaged pasture) and grazing grassland (managed pasture that feeds marketed livestock); the latter is further divided into livestock types (1 to n). The cropland could be divided further into cropland for each crop type (1 to n) and fallow land. The nesting strategy is based on the assumption that the land regions are small enough that all competing options are equally substitutable. This assumption implies that it is as easy to switch from forest to wheat as it is to switch from corn to wheat. However, this conversion would not happen unless wheat was more profitable than forest or corn. The function assumes that the landowner of each region and AEZ subregion decides on the land distribution among the possible options depending on the land rent obtained from production with each land use (i.e., crops, livestock, and wood products). To calibrate the function for both the managed and unmanaged land in the base year, we took the mean base-year land rent of the managed land to be that of the unmanaged land because data for the unmanaged land were lacking. The carbon stock on forest land was evaluated by the price in the case of the climate mitigation scenario. The land rent of forest areas includes both the revenue from wood products and the price of the carbon stock.&lt;/div&gt;&lt;/td&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;The figure shows the nesting diagram for land using AEZ classification. We consider all land excluding desert, rock, ice, tundra, and built-up land. There are 18 AEZ classifications. At the top is all land, which is divided into two main nodes: forestry land and non-forest land. The forestry-land node contains two competing uses: primary forest (unmanaged forest) and secondary forest (managed forest). The non-forested land can be divided into grassland and cropland. The grassland can be further divided into primary grassland (unmanaged pasture) and grazing grassland (managed pasture that feeds marketed livestock); the latter is further divided into livestock types (1 to n). The cropland could be divided further into cropland for each crop type (1 to n) and fallow land. The nesting strategy is based on the assumption that the land regions are small enough that all competing options are equally substitutable. This assumption implies that it is as easy to switch from forest to wheat as it is to switch from corn to wheat. However, this conversion would not happen unless wheat was more profitable than forest or corn. The function assumes that the landowner of each region and AEZ subregion decides on the land distribution among the possible options depending on the land rent obtained from production with each land use (i.e., crops, livestock, and wood products). To calibrate the function for both the managed and unmanaged land in the base year, we took the mean base-year land rent of the managed land to be that of the unmanaged land because data for the unmanaged land were lacking. The carbon stock on forest land was evaluated by the price in the case of the climate mitigation scenario. The land rent of forest areas includes both the revenue from wood products and the price of the carbon stock.&lt;/div&gt;&lt;/td&gt;&lt;/tr&gt;

&lt;!-- diff cache key iamcdb:diff::1.12:old-4127:rev-4128 --&gt;
&lt;/table&gt;</summary>
		<author><name>Rineke Oostenrijk</name></author>
	</entry>
	<entry>
		<id>https://www.iamcdocumentation.eu/index.php?title=Land-use_-_AIM-Hub&amp;diff=4127&amp;oldid=prev</id>
		<title>Rineke Oostenrijk at 05:54, 24 August 2016</title>
		<link rel="alternate" type="text/html" href="https://www.iamcdocumentation.eu/index.php?title=Land-use_-_AIM-Hub&amp;diff=4127&amp;oldid=prev"/>
		<updated>2016-08-24T05:54:16Z</updated>

		<summary type="html">&lt;p&gt;&lt;/p&gt;
&lt;table style=&quot;background-color: #fff; color: #202122;&quot; data-mw=&quot;interface&quot;&gt;
				&lt;col class=&quot;diff-marker&quot; /&gt;
				&lt;col class=&quot;diff-content&quot; /&gt;
				&lt;col class=&quot;diff-marker&quot; /&gt;
				&lt;col class=&quot;diff-content&quot; /&gt;
				&lt;tr class=&quot;diff-title&quot; lang=&quot;en&quot;&gt;
				&lt;td colspan=&quot;2&quot; style=&quot;background-color: #fff; color: #202122; text-align: center;&quot;&gt;← Older revision&lt;/td&gt;
				&lt;td colspan=&quot;2&quot; style=&quot;background-color: #fff; color: #202122; text-align: center;&quot;&gt;Revision as of 07:54, 24 August 2016&lt;/td&gt;
				&lt;/tr&gt;&lt;tr&gt;&lt;td colspan=&quot;2&quot; class=&quot;diff-lineno&quot; id=&quot;mw-diff-left-l4&quot;&gt;Line 4:&lt;/td&gt;
&lt;td colspan=&quot;2&quot; class=&quot;diff-lineno&quot;&gt;Line 4:&lt;/td&gt;&lt;/tr&gt;
&lt;tr&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;}}&lt;/div&gt;&lt;/td&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;}}&lt;/div&gt;&lt;/td&gt;&lt;/tr&gt;
&lt;tr&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;A function is used whereby land is an input for the production of crops and livestock products, and landowners change its use in accordance with the prices of goods produced on cropland, pastureland, and in forests. The model has a land nesting strategy, which is similar to the treatment in Sands and Edmonds (2005) and Wise and Calvin (2011). Land is categorized as one of three ecological zones, and there is a land market for each zone. Allocation of land by sector is formulated as a multinominal logit function to reflect the differences in substitutability across land categories with land rent. The function assumes that the landowner of each region and Agro-Ecological Zone (AEZ) decides on the land distribution among the possible options, with the land rent dependent on the production of each land type (i.e., crops, livestock, and wood products). We deal with all land excluding desert, rock, ice, tundra, and built-up land. The model has 18 AEZ classifications.&lt;/div&gt;&lt;/td&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;A function is used whereby land is an input for the production of crops and livestock products, and landowners change its use in accordance with the prices of goods produced on cropland, pastureland, and in forests. The model has a land nesting strategy, which is similar to the treatment in Sands and Edmonds (2005) and Wise and Calvin (2011). Land is categorized as one of three ecological zones, and there is a land market for each zone. Allocation of land by sector is formulated as a multinominal logit function to reflect the differences in substitutability across land categories with land rent. The function assumes that the landowner of each region and Agro-Ecological Zone (AEZ) decides on the land distribution among the possible options, with the land rent dependent on the production of each land type (i.e., crops, livestock, and wood products). We deal with all land excluding desert, rock, ice, tundra, and built-up land. The model has 18 AEZ classifications.&lt;/div&gt;&lt;/td&gt;&lt;/tr&gt;
&lt;tr&gt;&lt;td class=&quot;diff-marker&quot; data-marker=&quot;−&quot;&gt;&lt;/td&gt;&lt;td style=&quot;color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #ffe49c; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;&lt;del style=&quot;font-weight: bold; text-decoration: none;&quot;&gt;&amp;lt;div style=&amp;quot;clear:both&amp;quot;&amp;gt;&amp;lt;/div&amp;gt;&lt;/del&gt;&lt;/div&gt;&lt;/td&gt;&lt;td class=&quot;diff-marker&quot; data-marker=&quot;+&quot;&gt;&lt;/td&gt;&lt;td style=&quot;color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #a3d3ff; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt; &lt;/div&gt;&lt;/td&gt;&lt;/tr&gt;
&lt;tr&gt;&lt;td class=&quot;diff-marker&quot; data-marker=&quot;−&quot;&gt;&lt;/td&gt;&lt;td style=&quot;color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #ffe49c; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;[[File:38469888.png|thumb|&lt;del style=&quot;font-weight: bold; text-decoration: none;&quot;&gt;450px&lt;/del&gt;|left]]&lt;/div&gt;&lt;/td&gt;&lt;td class=&quot;diff-marker&quot; data-marker=&quot;+&quot;&gt;&lt;/td&gt;&lt;td style=&quot;color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #a3d3ff; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;[[File:38469888.png|thumb|&lt;ins style=&quot;font-weight: bold; text-decoration: none;&quot;&gt;500px&lt;/ins&gt;|left]]&lt;/div&gt;&lt;/td&gt;&lt;/tr&gt;
&lt;tr&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;br/&gt;&lt;/td&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;br/&gt;&lt;/td&gt;&lt;/tr&gt;
&lt;tr&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;The figure shows the nesting diagram for land using AEZ classification. We consider all land excluding desert, rock, ice, tundra, and built-up land. There are 18 AEZ classifications. At the top is all land, which is divided into two main nodes: forestry land and non-forest land. The forestry-land node contains two competing uses: primary forest (unmanaged forest) and secondary forest (managed forest). The non-forested land can be divided into grassland and cropland. The grassland can be further divided into primary grassland (unmanaged pasture) and grazing grassland (managed pasture that feeds marketed livestock); the latter is further divided into livestock types (1 to n). The cropland could be divided further into cropland for each crop type (1 to n) and fallow land. The nesting strategy is based on the assumption that the land regions are small enough that all competing options are equally substitutable. This assumption implies that it is as easy to switch from forest to wheat as it is to switch from corn to wheat. However, this conversion would not happen unless wheat was more profitable than forest or corn. The function assumes that the landowner of each region and AEZ subregion decides on the land distribution among the possible options depending on the land rent obtained from production with each land use (i.e., crops, livestock, and wood products). To calibrate the function for both the managed and unmanaged land in the base year, we took the mean base-year land rent of the managed land to be that of the unmanaged land because data for the unmanaged land were lacking. The carbon stock on forest land was evaluated by the price in the case of the climate mitigation scenario. The land rent of forest areas includes both the revenue from wood products and the price of the carbon stock.&lt;/div&gt;&lt;/td&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;The figure shows the nesting diagram for land using AEZ classification. We consider all land excluding desert, rock, ice, tundra, and built-up land. There are 18 AEZ classifications. At the top is all land, which is divided into two main nodes: forestry land and non-forest land. The forestry-land node contains two competing uses: primary forest (unmanaged forest) and secondary forest (managed forest). The non-forested land can be divided into grassland and cropland. The grassland can be further divided into primary grassland (unmanaged pasture) and grazing grassland (managed pasture that feeds marketed livestock); the latter is further divided into livestock types (1 to n). The cropland could be divided further into cropland for each crop type (1 to n) and fallow land. The nesting strategy is based on the assumption that the land regions are small enough that all competing options are equally substitutable. This assumption implies that it is as easy to switch from forest to wheat as it is to switch from corn to wheat. However, this conversion would not happen unless wheat was more profitable than forest or corn. The function assumes that the landowner of each region and AEZ subregion decides on the land distribution among the possible options depending on the land rent obtained from production with each land use (i.e., crops, livestock, and wood products). To calibrate the function for both the managed and unmanaged land in the base year, we took the mean base-year land rent of the managed land to be that of the unmanaged land because data for the unmanaged land were lacking. The carbon stock on forest land was evaluated by the price in the case of the climate mitigation scenario. The land rent of forest areas includes both the revenue from wood products and the price of the carbon stock.&lt;/div&gt;&lt;/td&gt;&lt;/tr&gt;

&lt;!-- diff cache key iamcdb:diff::1.12:old-4126:rev-4127 --&gt;
&lt;/table&gt;</summary>
		<author><name>Rineke Oostenrijk</name></author>
	</entry>
	<entry>
		<id>https://www.iamcdocumentation.eu/index.php?title=Land-use_-_AIM-Hub&amp;diff=4126&amp;oldid=prev</id>
		<title>Rineke Oostenrijk at 05:53, 24 August 2016</title>
		<link rel="alternate" type="text/html" href="https://www.iamcdocumentation.eu/index.php?title=Land-use_-_AIM-Hub&amp;diff=4126&amp;oldid=prev"/>
		<updated>2016-08-24T05:53:45Z</updated>

		<summary type="html">&lt;p&gt;&lt;/p&gt;
&lt;table style=&quot;background-color: #fff; color: #202122;&quot; data-mw=&quot;interface&quot;&gt;
				&lt;col class=&quot;diff-marker&quot; /&gt;
				&lt;col class=&quot;diff-content&quot; /&gt;
				&lt;col class=&quot;diff-marker&quot; /&gt;
				&lt;col class=&quot;diff-content&quot; /&gt;
				&lt;tr class=&quot;diff-title&quot; lang=&quot;en&quot;&gt;
				&lt;td colspan=&quot;2&quot; style=&quot;background-color: #fff; color: #202122; text-align: center;&quot;&gt;← Older revision&lt;/td&gt;
				&lt;td colspan=&quot;2&quot; style=&quot;background-color: #fff; color: #202122; text-align: center;&quot;&gt;Revision as of 07:53, 24 August 2016&lt;/td&gt;
				&lt;/tr&gt;&lt;tr&gt;&lt;td colspan=&quot;2&quot; class=&quot;diff-lineno&quot; id=&quot;mw-diff-left-l5&quot;&gt;Line 5:&lt;/td&gt;
&lt;td colspan=&quot;2&quot; class=&quot;diff-lineno&quot;&gt;Line 5:&lt;/td&gt;&lt;/tr&gt;
&lt;tr&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;A function is used whereby land is an input for the production of crops and livestock products, and landowners change its use in accordance with the prices of goods produced on cropland, pastureland, and in forests. The model has a land nesting strategy, which is similar to the treatment in Sands and Edmonds (2005) and Wise and Calvin (2011). Land is categorized as one of three ecological zones, and there is a land market for each zone. Allocation of land by sector is formulated as a multinominal logit function to reflect the differences in substitutability across land categories with land rent. The function assumes that the landowner of each region and Agro-Ecological Zone (AEZ) decides on the land distribution among the possible options, with the land rent dependent on the production of each land type (i.e., crops, livestock, and wood products). We deal with all land excluding desert, rock, ice, tundra, and built-up land. The model has 18 AEZ classifications.&lt;/div&gt;&lt;/td&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;A function is used whereby land is an input for the production of crops and livestock products, and landowners change its use in accordance with the prices of goods produced on cropland, pastureland, and in forests. The model has a land nesting strategy, which is similar to the treatment in Sands and Edmonds (2005) and Wise and Calvin (2011). Land is categorized as one of three ecological zones, and there is a land market for each zone. Allocation of land by sector is formulated as a multinominal logit function to reflect the differences in substitutability across land categories with land rent. The function assumes that the landowner of each region and Agro-Ecological Zone (AEZ) decides on the land distribution among the possible options, with the land rent dependent on the production of each land type (i.e., crops, livestock, and wood products). We deal with all land excluding desert, rock, ice, tundra, and built-up land. The model has 18 AEZ classifications.&lt;/div&gt;&lt;/td&gt;&lt;/tr&gt;
&lt;tr&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;&amp;lt;div style=&amp;quot;clear:both&amp;quot;&amp;gt;&amp;lt;/div&amp;gt;&lt;/div&gt;&lt;/td&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;&amp;lt;div style=&amp;quot;clear:both&amp;quot;&amp;gt;&amp;lt;/div&amp;gt;&lt;/div&gt;&lt;/td&gt;&lt;/tr&gt;
&lt;tr&gt;&lt;td class=&quot;diff-marker&quot; data-marker=&quot;−&quot;&gt;&lt;/td&gt;&lt;td style=&quot;color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #ffe49c; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;[[File:38469888.png|thumb|&lt;del style=&quot;font-weight: bold; text-decoration: none;&quot;&gt;4500px&lt;/del&gt;|left]]&lt;/div&gt;&lt;/td&gt;&lt;td class=&quot;diff-marker&quot; data-marker=&quot;+&quot;&gt;&lt;/td&gt;&lt;td style=&quot;color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #a3d3ff; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;[[File:38469888.png|thumb|&lt;ins style=&quot;font-weight: bold; text-decoration: none;&quot;&gt;450px&lt;/ins&gt;|left]]&lt;/div&gt;&lt;/td&gt;&lt;/tr&gt;
&lt;tr&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;br/&gt;&lt;/td&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;br/&gt;&lt;/td&gt;&lt;/tr&gt;
&lt;tr&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;The figure shows the nesting diagram for land using AEZ classification. We consider all land excluding desert, rock, ice, tundra, and built-up land. There are 18 AEZ classifications. At the top is all land, which is divided into two main nodes: forestry land and non-forest land. The forestry-land node contains two competing uses: primary forest (unmanaged forest) and secondary forest (managed forest). The non-forested land can be divided into grassland and cropland. The grassland can be further divided into primary grassland (unmanaged pasture) and grazing grassland (managed pasture that feeds marketed livestock); the latter is further divided into livestock types (1 to n). The cropland could be divided further into cropland for each crop type (1 to n) and fallow land. The nesting strategy is based on the assumption that the land regions are small enough that all competing options are equally substitutable. This assumption implies that it is as easy to switch from forest to wheat as it is to switch from corn to wheat. However, this conversion would not happen unless wheat was more profitable than forest or corn. The function assumes that the landowner of each region and AEZ subregion decides on the land distribution among the possible options depending on the land rent obtained from production with each land use (i.e., crops, livestock, and wood products). To calibrate the function for both the managed and unmanaged land in the base year, we took the mean base-year land rent of the managed land to be that of the unmanaged land because data for the unmanaged land were lacking. The carbon stock on forest land was evaluated by the price in the case of the climate mitigation scenario. The land rent of forest areas includes both the revenue from wood products and the price of the carbon stock.&lt;/div&gt;&lt;/td&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;The figure shows the nesting diagram for land using AEZ classification. We consider all land excluding desert, rock, ice, tundra, and built-up land. There are 18 AEZ classifications. At the top is all land, which is divided into two main nodes: forestry land and non-forest land. The forestry-land node contains two competing uses: primary forest (unmanaged forest) and secondary forest (managed forest). The non-forested land can be divided into grassland and cropland. The grassland can be further divided into primary grassland (unmanaged pasture) and grazing grassland (managed pasture that feeds marketed livestock); the latter is further divided into livestock types (1 to n). The cropland could be divided further into cropland for each crop type (1 to n) and fallow land. The nesting strategy is based on the assumption that the land regions are small enough that all competing options are equally substitutable. This assumption implies that it is as easy to switch from forest to wheat as it is to switch from corn to wheat. However, this conversion would not happen unless wheat was more profitable than forest or corn. The function assumes that the landowner of each region and AEZ subregion decides on the land distribution among the possible options depending on the land rent obtained from production with each land use (i.e., crops, livestock, and wood products). To calibrate the function for both the managed and unmanaged land in the base year, we took the mean base-year land rent of the managed land to be that of the unmanaged land because data for the unmanaged land were lacking. The carbon stock on forest land was evaluated by the price in the case of the climate mitigation scenario. The land rent of forest areas includes both the revenue from wood products and the price of the carbon stock.&lt;/div&gt;&lt;/td&gt;&lt;/tr&gt;

&lt;!-- diff cache key iamcdb:diff::1.12:old-4125:rev-4126 --&gt;
&lt;/table&gt;</summary>
		<author><name>Rineke Oostenrijk</name></author>
	</entry>
	<entry>
		<id>https://www.iamcdocumentation.eu/index.php?title=Land-use_-_AIM-Hub&amp;diff=4125&amp;oldid=prev</id>
		<title>Rineke Oostenrijk at 05:53, 24 August 2016</title>
		<link rel="alternate" type="text/html" href="https://www.iamcdocumentation.eu/index.php?title=Land-use_-_AIM-Hub&amp;diff=4125&amp;oldid=prev"/>
		<updated>2016-08-24T05:53:39Z</updated>

		<summary type="html">&lt;p&gt;&lt;/p&gt;
&lt;table style=&quot;background-color: #fff; color: #202122;&quot; data-mw=&quot;interface&quot;&gt;
				&lt;col class=&quot;diff-marker&quot; /&gt;
				&lt;col class=&quot;diff-content&quot; /&gt;
				&lt;col class=&quot;diff-marker&quot; /&gt;
				&lt;col class=&quot;diff-content&quot; /&gt;
				&lt;tr class=&quot;diff-title&quot; lang=&quot;en&quot;&gt;
				&lt;td colspan=&quot;2&quot; style=&quot;background-color: #fff; color: #202122; text-align: center;&quot;&gt;← Older revision&lt;/td&gt;
				&lt;td colspan=&quot;2&quot; style=&quot;background-color: #fff; color: #202122; text-align: center;&quot;&gt;Revision as of 07:53, 24 August 2016&lt;/td&gt;
				&lt;/tr&gt;&lt;tr&gt;&lt;td colspan=&quot;2&quot; class=&quot;diff-lineno&quot; id=&quot;mw-diff-left-l5&quot;&gt;Line 5:&lt;/td&gt;
&lt;td colspan=&quot;2&quot; class=&quot;diff-lineno&quot;&gt;Line 5:&lt;/td&gt;&lt;/tr&gt;
&lt;tr&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;A function is used whereby land is an input for the production of crops and livestock products, and landowners change its use in accordance with the prices of goods produced on cropland, pastureland, and in forests. The model has a land nesting strategy, which is similar to the treatment in Sands and Edmonds (2005) and Wise and Calvin (2011). Land is categorized as one of three ecological zones, and there is a land market for each zone. Allocation of land by sector is formulated as a multinominal logit function to reflect the differences in substitutability across land categories with land rent. The function assumes that the landowner of each region and Agro-Ecological Zone (AEZ) decides on the land distribution among the possible options, with the land rent dependent on the production of each land type (i.e., crops, livestock, and wood products). We deal with all land excluding desert, rock, ice, tundra, and built-up land. The model has 18 AEZ classifications.&lt;/div&gt;&lt;/td&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;A function is used whereby land is an input for the production of crops and livestock products, and landowners change its use in accordance with the prices of goods produced on cropland, pastureland, and in forests. The model has a land nesting strategy, which is similar to the treatment in Sands and Edmonds (2005) and Wise and Calvin (2011). Land is categorized as one of three ecological zones, and there is a land market for each zone. Allocation of land by sector is formulated as a multinominal logit function to reflect the differences in substitutability across land categories with land rent. The function assumes that the landowner of each region and Agro-Ecological Zone (AEZ) decides on the land distribution among the possible options, with the land rent dependent on the production of each land type (i.e., crops, livestock, and wood products). We deal with all land excluding desert, rock, ice, tundra, and built-up land. The model has 18 AEZ classifications.&lt;/div&gt;&lt;/td&gt;&lt;/tr&gt;
&lt;tr&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;&amp;lt;div style=&amp;quot;clear:both&amp;quot;&amp;gt;&amp;lt;/div&amp;gt;&lt;/div&gt;&lt;/td&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;&amp;lt;div style=&amp;quot;clear:both&amp;quot;&amp;gt;&amp;lt;/div&amp;gt;&lt;/div&gt;&lt;/td&gt;&lt;/tr&gt;
&lt;tr&gt;&lt;td class=&quot;diff-marker&quot; data-marker=&quot;−&quot;&gt;&lt;/td&gt;&lt;td style=&quot;color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #ffe49c; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;[[File:38469888.png|thumb|&lt;del style=&quot;font-weight: bold; text-decoration: none;&quot;&gt;500px&lt;/del&gt;|left]]&lt;/div&gt;&lt;/td&gt;&lt;td class=&quot;diff-marker&quot; data-marker=&quot;+&quot;&gt;&lt;/td&gt;&lt;td style=&quot;color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #a3d3ff; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;[[File:38469888.png|thumb|&lt;ins style=&quot;font-weight: bold; text-decoration: none;&quot;&gt;4500px&lt;/ins&gt;|left]]&lt;/div&gt;&lt;/td&gt;&lt;/tr&gt;
&lt;tr&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;br/&gt;&lt;/td&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;br/&gt;&lt;/td&gt;&lt;/tr&gt;
&lt;tr&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;The figure shows the nesting diagram for land using AEZ classification. We consider all land excluding desert, rock, ice, tundra, and built-up land. There are 18 AEZ classifications. At the top is all land, which is divided into two main nodes: forestry land and non-forest land. The forestry-land node contains two competing uses: primary forest (unmanaged forest) and secondary forest (managed forest). The non-forested land can be divided into grassland and cropland. The grassland can be further divided into primary grassland (unmanaged pasture) and grazing grassland (managed pasture that feeds marketed livestock); the latter is further divided into livestock types (1 to n). The cropland could be divided further into cropland for each crop type (1 to n) and fallow land. The nesting strategy is based on the assumption that the land regions are small enough that all competing options are equally substitutable. This assumption implies that it is as easy to switch from forest to wheat as it is to switch from corn to wheat. However, this conversion would not happen unless wheat was more profitable than forest or corn. The function assumes that the landowner of each region and AEZ subregion decides on the land distribution among the possible options depending on the land rent obtained from production with each land use (i.e., crops, livestock, and wood products). To calibrate the function for both the managed and unmanaged land in the base year, we took the mean base-year land rent of the managed land to be that of the unmanaged land because data for the unmanaged land were lacking. The carbon stock on forest land was evaluated by the price in the case of the climate mitigation scenario. The land rent of forest areas includes both the revenue from wood products and the price of the carbon stock.&lt;/div&gt;&lt;/td&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;The figure shows the nesting diagram for land using AEZ classification. We consider all land excluding desert, rock, ice, tundra, and built-up land. There are 18 AEZ classifications. At the top is all land, which is divided into two main nodes: forestry land and non-forest land. The forestry-land node contains two competing uses: primary forest (unmanaged forest) and secondary forest (managed forest). The non-forested land can be divided into grassland and cropland. The grassland can be further divided into primary grassland (unmanaged pasture) and grazing grassland (managed pasture that feeds marketed livestock); the latter is further divided into livestock types (1 to n). The cropland could be divided further into cropland for each crop type (1 to n) and fallow land. The nesting strategy is based on the assumption that the land regions are small enough that all competing options are equally substitutable. This assumption implies that it is as easy to switch from forest to wheat as it is to switch from corn to wheat. However, this conversion would not happen unless wheat was more profitable than forest or corn. The function assumes that the landowner of each region and AEZ subregion decides on the land distribution among the possible options depending on the land rent obtained from production with each land use (i.e., crops, livestock, and wood products). To calibrate the function for both the managed and unmanaged land in the base year, we took the mean base-year land rent of the managed land to be that of the unmanaged land because data for the unmanaged land were lacking. The carbon stock on forest land was evaluated by the price in the case of the climate mitigation scenario. The land rent of forest areas includes both the revenue from wood products and the price of the carbon stock.&lt;/div&gt;&lt;/td&gt;&lt;/tr&gt;
&lt;/table&gt;</summary>
		<author><name>Rineke Oostenrijk</name></author>
	</entry>
	<entry>
		<id>https://www.iamcdocumentation.eu/index.php?title=Land-use_-_AIM-Hub&amp;diff=4124&amp;oldid=prev</id>
		<title>Rineke Oostenrijk at 05:52, 24 August 2016</title>
		<link rel="alternate" type="text/html" href="https://www.iamcdocumentation.eu/index.php?title=Land-use_-_AIM-Hub&amp;diff=4124&amp;oldid=prev"/>
		<updated>2016-08-24T05:52:46Z</updated>

		<summary type="html">&lt;p&gt;&lt;/p&gt;
&lt;table style=&quot;background-color: #fff; color: #202122;&quot; data-mw=&quot;interface&quot;&gt;
				&lt;col class=&quot;diff-marker&quot; /&gt;
				&lt;col class=&quot;diff-content&quot; /&gt;
				&lt;col class=&quot;diff-marker&quot; /&gt;
				&lt;col class=&quot;diff-content&quot; /&gt;
				&lt;tr class=&quot;diff-title&quot; lang=&quot;en&quot;&gt;
				&lt;td colspan=&quot;2&quot; style=&quot;background-color: #fff; color: #202122; text-align: center;&quot;&gt;← Older revision&lt;/td&gt;
				&lt;td colspan=&quot;2&quot; style=&quot;background-color: #fff; color: #202122; text-align: center;&quot;&gt;Revision as of 07:52, 24 August 2016&lt;/td&gt;
				&lt;/tr&gt;&lt;tr&gt;&lt;td colspan=&quot;2&quot; class=&quot;diff-lineno&quot; id=&quot;mw-diff-left-l5&quot;&gt;Line 5:&lt;/td&gt;
&lt;td colspan=&quot;2&quot; class=&quot;diff-lineno&quot;&gt;Line 5:&lt;/td&gt;&lt;/tr&gt;
&lt;tr&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;A function is used whereby land is an input for the production of crops and livestock products, and landowners change its use in accordance with the prices of goods produced on cropland, pastureland, and in forests. The model has a land nesting strategy, which is similar to the treatment in Sands and Edmonds (2005) and Wise and Calvin (2011). Land is categorized as one of three ecological zones, and there is a land market for each zone. Allocation of land by sector is formulated as a multinominal logit function to reflect the differences in substitutability across land categories with land rent. The function assumes that the landowner of each region and Agro-Ecological Zone (AEZ) decides on the land distribution among the possible options, with the land rent dependent on the production of each land type (i.e., crops, livestock, and wood products). We deal with all land excluding desert, rock, ice, tundra, and built-up land. The model has 18 AEZ classifications.&lt;/div&gt;&lt;/td&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;A function is used whereby land is an input for the production of crops and livestock products, and landowners change its use in accordance with the prices of goods produced on cropland, pastureland, and in forests. The model has a land nesting strategy, which is similar to the treatment in Sands and Edmonds (2005) and Wise and Calvin (2011). Land is categorized as one of three ecological zones, and there is a land market for each zone. Allocation of land by sector is formulated as a multinominal logit function to reflect the differences in substitutability across land categories with land rent. The function assumes that the landowner of each region and Agro-Ecological Zone (AEZ) decides on the land distribution among the possible options, with the land rent dependent on the production of each land type (i.e., crops, livestock, and wood products). We deal with all land excluding desert, rock, ice, tundra, and built-up land. The model has 18 AEZ classifications.&lt;/div&gt;&lt;/td&gt;&lt;/tr&gt;
&lt;tr&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;&amp;lt;div style=&amp;quot;clear:both&amp;quot;&amp;gt;&amp;lt;/div&amp;gt;&lt;/div&gt;&lt;/td&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;&amp;lt;div style=&amp;quot;clear:both&amp;quot;&amp;gt;&amp;lt;/div&amp;gt;&lt;/div&gt;&lt;/td&gt;&lt;/tr&gt;
&lt;tr&gt;&lt;td class=&quot;diff-marker&quot; data-marker=&quot;−&quot;&gt;&lt;/td&gt;&lt;td style=&quot;color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #ffe49c; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;[[File:38469888.png|thumb|&lt;del style=&quot;font-weight: bold; text-decoration: none;&quot;&gt;600px&lt;/del&gt;|left]]&lt;/div&gt;&lt;/td&gt;&lt;td class=&quot;diff-marker&quot; data-marker=&quot;+&quot;&gt;&lt;/td&gt;&lt;td style=&quot;color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #a3d3ff; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;[[File:38469888.png|thumb|&lt;ins style=&quot;font-weight: bold; text-decoration: none;&quot;&gt;500px&lt;/ins&gt;|left]]&lt;/div&gt;&lt;/td&gt;&lt;/tr&gt;
&lt;tr&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;br/&gt;&lt;/td&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;br/&gt;&lt;/td&gt;&lt;/tr&gt;
&lt;tr&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;The figure shows the nesting diagram for land using AEZ classification. We consider all land excluding desert, rock, ice, tundra, and built-up land. There are 18 AEZ classifications. At the top is all land, which is divided into two main nodes: forestry land and non-forest land. The forestry-land node contains two competing uses: primary forest (unmanaged forest) and secondary forest (managed forest). The non-forested land can be divided into grassland and cropland. The grassland can be further divided into primary grassland (unmanaged pasture) and grazing grassland (managed pasture that feeds marketed livestock); the latter is further divided into livestock types (1 to n). The cropland could be divided further into cropland for each crop type (1 to n) and fallow land. The nesting strategy is based on the assumption that the land regions are small enough that all competing options are equally substitutable. This assumption implies that it is as easy to switch from forest to wheat as it is to switch from corn to wheat. However, this conversion would not happen unless wheat was more profitable than forest or corn. The function assumes that the landowner of each region and AEZ subregion decides on the land distribution among the possible options depending on the land rent obtained from production with each land use (i.e., crops, livestock, and wood products). To calibrate the function for both the managed and unmanaged land in the base year, we took the mean base-year land rent of the managed land to be that of the unmanaged land because data for the unmanaged land were lacking. The carbon stock on forest land was evaluated by the price in the case of the climate mitigation scenario. The land rent of forest areas includes both the revenue from wood products and the price of the carbon stock.&lt;/div&gt;&lt;/td&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;The figure shows the nesting diagram for land using AEZ classification. We consider all land excluding desert, rock, ice, tundra, and built-up land. There are 18 AEZ classifications. At the top is all land, which is divided into two main nodes: forestry land and non-forest land. The forestry-land node contains two competing uses: primary forest (unmanaged forest) and secondary forest (managed forest). The non-forested land can be divided into grassland and cropland. The grassland can be further divided into primary grassland (unmanaged pasture) and grazing grassland (managed pasture that feeds marketed livestock); the latter is further divided into livestock types (1 to n). The cropland could be divided further into cropland for each crop type (1 to n) and fallow land. The nesting strategy is based on the assumption that the land regions are small enough that all competing options are equally substitutable. This assumption implies that it is as easy to switch from forest to wheat as it is to switch from corn to wheat. However, this conversion would not happen unless wheat was more profitable than forest or corn. The function assumes that the landowner of each region and AEZ subregion decides on the land distribution among the possible options depending on the land rent obtained from production with each land use (i.e., crops, livestock, and wood products). To calibrate the function for both the managed and unmanaged land in the base year, we took the mean base-year land rent of the managed land to be that of the unmanaged land because data for the unmanaged land were lacking. The carbon stock on forest land was evaluated by the price in the case of the climate mitigation scenario. The land rent of forest areas includes both the revenue from wood products and the price of the carbon stock.&lt;/div&gt;&lt;/td&gt;&lt;/tr&gt;

&lt;!-- diff cache key iamcdb:diff::1.12:old-4123:rev-4124 --&gt;
&lt;/table&gt;</summary>
		<author><name>Rineke Oostenrijk</name></author>
	</entry>
	<entry>
		<id>https://www.iamcdocumentation.eu/index.php?title=Land-use_-_AIM-Hub&amp;diff=4123&amp;oldid=prev</id>
		<title>Rineke Oostenrijk at 05:52, 24 August 2016</title>
		<link rel="alternate" type="text/html" href="https://www.iamcdocumentation.eu/index.php?title=Land-use_-_AIM-Hub&amp;diff=4123&amp;oldid=prev"/>
		<updated>2016-08-24T05:52:12Z</updated>

		<summary type="html">&lt;p&gt;&lt;/p&gt;
&lt;table style=&quot;background-color: #fff; color: #202122;&quot; data-mw=&quot;interface&quot;&gt;
				&lt;col class=&quot;diff-marker&quot; /&gt;
				&lt;col class=&quot;diff-content&quot; /&gt;
				&lt;col class=&quot;diff-marker&quot; /&gt;
				&lt;col class=&quot;diff-content&quot; /&gt;
				&lt;tr class=&quot;diff-title&quot; lang=&quot;en&quot;&gt;
				&lt;td colspan=&quot;2&quot; style=&quot;background-color: #fff; color: #202122; text-align: center;&quot;&gt;← Older revision&lt;/td&gt;
				&lt;td colspan=&quot;2&quot; style=&quot;background-color: #fff; color: #202122; text-align: center;&quot;&gt;Revision as of 07:52, 24 August 2016&lt;/td&gt;
				&lt;/tr&gt;&lt;tr&gt;&lt;td colspan=&quot;2&quot; class=&quot;diff-lineno&quot; id=&quot;mw-diff-left-l4&quot;&gt;Line 4:&lt;/td&gt;
&lt;td colspan=&quot;2&quot; class=&quot;diff-lineno&quot;&gt;Line 4:&lt;/td&gt;&lt;/tr&gt;
&lt;tr&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;}}&lt;/div&gt;&lt;/td&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;}}&lt;/div&gt;&lt;/td&gt;&lt;/tr&gt;
&lt;tr&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;A function is used whereby land is an input for the production of crops and livestock products, and landowners change its use in accordance with the prices of goods produced on cropland, pastureland, and in forests. The model has a land nesting strategy, which is similar to the treatment in Sands and Edmonds (2005) and Wise and Calvin (2011). Land is categorized as one of three ecological zones, and there is a land market for each zone. Allocation of land by sector is formulated as a multinominal logit function to reflect the differences in substitutability across land categories with land rent. The function assumes that the landowner of each region and Agro-Ecological Zone (AEZ) decides on the land distribution among the possible options, with the land rent dependent on the production of each land type (i.e., crops, livestock, and wood products). We deal with all land excluding desert, rock, ice, tundra, and built-up land. The model has 18 AEZ classifications.&lt;/div&gt;&lt;/td&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;A function is used whereby land is an input for the production of crops and livestock products, and landowners change its use in accordance with the prices of goods produced on cropland, pastureland, and in forests. The model has a land nesting strategy, which is similar to the treatment in Sands and Edmonds (2005) and Wise and Calvin (2011). Land is categorized as one of three ecological zones, and there is a land market for each zone. Allocation of land by sector is formulated as a multinominal logit function to reflect the differences in substitutability across land categories with land rent. The function assumes that the landowner of each region and Agro-Ecological Zone (AEZ) decides on the land distribution among the possible options, with the land rent dependent on the production of each land type (i.e., crops, livestock, and wood products). We deal with all land excluding desert, rock, ice, tundra, and built-up land. The model has 18 AEZ classifications.&lt;/div&gt;&lt;/td&gt;&lt;/tr&gt;
&lt;tr&gt;&lt;td class=&quot;diff-marker&quot; data-marker=&quot;−&quot;&gt;&lt;/td&gt;&lt;td style=&quot;color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #ffe49c; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;&amp;lt;div style=&amp;quot;clear:both&amp;gt;&amp;lt;/div&amp;gt;&lt;/div&gt;&lt;/td&gt;&lt;td class=&quot;diff-marker&quot; data-marker=&quot;+&quot;&gt;&lt;/td&gt;&lt;td style=&quot;color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #a3d3ff; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;&amp;lt;div style=&amp;quot;clear:both&lt;ins style=&quot;font-weight: bold; text-decoration: none;&quot;&gt;&amp;quot;&lt;/ins&gt;&amp;gt;&amp;lt;/div&amp;gt;&lt;/div&gt;&lt;/td&gt;&lt;/tr&gt;
&lt;tr&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;[[File:38469888.png|thumb|600px|left]]&lt;/div&gt;&lt;/td&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;[[File:38469888.png|thumb|600px|left]]&lt;/div&gt;&lt;/td&gt;&lt;/tr&gt;
&lt;tr&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;br/&gt;&lt;/td&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;br/&gt;&lt;/td&gt;&lt;/tr&gt;
&lt;tr&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;The figure shows the nesting diagram for land using AEZ classification. We consider all land excluding desert, rock, ice, tundra, and built-up land. There are 18 AEZ classifications. At the top is all land, which is divided into two main nodes: forestry land and non-forest land. The forestry-land node contains two competing uses: primary forest (unmanaged forest) and secondary forest (managed forest). The non-forested land can be divided into grassland and cropland. The grassland can be further divided into primary grassland (unmanaged pasture) and grazing grassland (managed pasture that feeds marketed livestock); the latter is further divided into livestock types (1 to n). The cropland could be divided further into cropland for each crop type (1 to n) and fallow land. The nesting strategy is based on the assumption that the land regions are small enough that all competing options are equally substitutable. This assumption implies that it is as easy to switch from forest to wheat as it is to switch from corn to wheat. However, this conversion would not happen unless wheat was more profitable than forest or corn. The function assumes that the landowner of each region and AEZ subregion decides on the land distribution among the possible options depending on the land rent obtained from production with each land use (i.e., crops, livestock, and wood products). To calibrate the function for both the managed and unmanaged land in the base year, we took the mean base-year land rent of the managed land to be that of the unmanaged land because data for the unmanaged land were lacking. The carbon stock on forest land was evaluated by the price in the case of the climate mitigation scenario. The land rent of forest areas includes both the revenue from wood products and the price of the carbon stock.&lt;/div&gt;&lt;/td&gt;&lt;td class=&quot;diff-marker&quot;&gt;&lt;/td&gt;&lt;td style=&quot;background-color: #f8f9fa; color: #202122; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #eaecf0; vertical-align: top; white-space: pre-wrap;&quot;&gt;&lt;div&gt;The figure shows the nesting diagram for land using AEZ classification. We consider all land excluding desert, rock, ice, tundra, and built-up land. There are 18 AEZ classifications. At the top is all land, which is divided into two main nodes: forestry land and non-forest land. The forestry-land node contains two competing uses: primary forest (unmanaged forest) and secondary forest (managed forest). The non-forested land can be divided into grassland and cropland. The grassland can be further divided into primary grassland (unmanaged pasture) and grazing grassland (managed pasture that feeds marketed livestock); the latter is further divided into livestock types (1 to n). The cropland could be divided further into cropland for each crop type (1 to n) and fallow land. The nesting strategy is based on the assumption that the land regions are small enough that all competing options are equally substitutable. This assumption implies that it is as easy to switch from forest to wheat as it is to switch from corn to wheat. However, this conversion would not happen unless wheat was more profitable than forest or corn. The function assumes that the landowner of each region and AEZ subregion decides on the land distribution among the possible options depending on the land rent obtained from production with each land use (i.e., crops, livestock, and wood products). To calibrate the function for both the managed and unmanaged land in the base year, we took the mean base-year land rent of the managed land to be that of the unmanaged land because data for the unmanaged land were lacking. The carbon stock on forest land was evaluated by the price in the case of the climate mitigation scenario. The land rent of forest areas includes both the revenue from wood products and the price of the carbon stock.&lt;/div&gt;&lt;/td&gt;&lt;/tr&gt;

&lt;!-- diff cache key iamcdb:diff::1.12:old-4122:rev-4123 --&gt;
&lt;/table&gt;</summary>
		<author><name>Rineke Oostenrijk</name></author>
	</entry>
</feed>