<?xml version="1.0" encoding="UTF-8"?><!DOCTYPE article PUBLIC "-//NLM//DTD Journal Publishing DTD v3.0 20080202//EN" "http://dtd.nlm.nih.gov/publishing/3.0/journalpublishing3.dtd">
<article xmlns:mml="http://www.w3.org/1998/Math/MathML" xmlns:xlink="http://www.w3.org/1999/xlink" dtd-version="3.0" xml:lang="en" article-type="research article">
 <front>
  <journal-meta>
   <journal-id journal-id-type="publisher-id">
    ojf
   </journal-id>
   <journal-title-group>
    <journal-title>
     Open Journal of Forestry
    </journal-title>
   </journal-title-group>
   <issn pub-type="epub">
    2163-0429
   </issn>
   <issn publication-format="print">
    2163-0437
   </issn>
   <publisher>
    <publisher-name>
     Scientific Research Publishing
    </publisher-name>
   </publisher>
  </journal-meta>
  <article-meta>
   <article-id pub-id-type="doi">
    10.4236/ojf.2024.144022
   </article-id>
   <article-id pub-id-type="publisher-id">
    ojf-135250
   </article-id>
   <article-categories>
    <subj-group subj-group-type="heading">
     <subject>
      Articles
     </subject>
    </subj-group>
    <subj-group subj-group-type="Discipline-v2">
     <subject>
      Earth 
     </subject>
     <subject>
       Environmental Sciences
     </subject>
    </subj-group>
   </article-categories>
   <title-group>
    How Land Use Policies Are Transforming Shifting Cultivation to Short Fallow Systems and Permanent Cultivation of Annual Crops in Tanzania
   </title-group>
   <contrib-group>
    <contrib contrib-type="author" xlink:type="simple">
     <name name-style="western">
      <surname>
       Charles Joseph
      </surname>
      <given-names>
       Kilawe
      </given-names>
     </name>
    </contrib>
   </contrib-group> 
   <aff id="affnull">
    <addr-line>
     aDepartment of Ecosystems and Conservation, Sokoine University of Agriculture, Morogoro, Tanzania
    </addr-line> 
   </aff> 
   <pub-date pub-type="epub">
    <day>
     15
    </day> 
    <month>
     08
    </month>
    <year>
     2024
    </year>
   </pub-date> 
   <volume>
    14
   </volume> 
   <issue>
    04
   </issue>
   <fpage>
    397
   </fpage>
   <lpage>
    412
   </lpage>
   <history>
    <date date-type="received">
     <day>
      25,
     </day>
     <month>
      April
     </month>
     <year>
      2024
     </year>
    </date>
    <date date-type="published">
     <day>
      12,
     </day>
     <month>
      April
     </month>
     <year>
      2024
     </year> 
    </date> 
    <date date-type="accepted">
     <day>
      12,
     </day>
     <month>
      August
     </month>
     <year>
      2024
     </year> 
    </date>
   </history>
   <permissions>
    <copyright-statement>
     © Copyright 2014 by authors and Scientific Research Publishing Inc. 
    </copyright-statement>
    <copyright-year>
     2014
    </copyright-year>
    <license>
     <license-p>
      This work is licensed under the Creative Commons Attribution International License (CC BY). http://creativecommons.org/licenses/by/4.0/
     </license-p>
    </license>
   </permissions>
   <abstract>
    Recent studies show that shifting cultivation in Tanzania has transformed into more intensive farming practices. One of the drivers of this shift is the implementation of policies that favor sedentary farming. However, there is inadequate information on how this transformation operates at the village level. Based on a case study of one village in Central Tanzania, this study demonstrates that the village land use plan is the primary policy tool for the transformation and intensification of shifting cultivation at the village level. Through the land use planning process, land is allocated only for lawful uses such as settlement, permanent cultivation, and the village forest reserve. No land is designated for shifting cultivation. Additionally, the land use plans are accompanied by by-laws that restrict shifting cultivation practices, such as the use of fire during land preparation and leaving the land fallow for more than 3 years. The intensification of shifting cultivation was not associated with an increase in the use of farm inputs such as improved seeds, fertilizer, or irrigation, as is commonly practiced in sustainable intensive agriculture. Instead, it was associated with the adoption of short fallow farming systems and labor-intensive land preparation methods, such as deep plowing to loosen the soil and sub-soiling vegetation.
   </abstract>
   <kwd-group> 
    <kwd>
     Land Use Planning
    </kwd> 
    <kwd>
      Land Use Change
    </kwd> 
    <kwd>
      Short Fallow Systems
    </kwd> 
    <kwd>
      Slash-and-Burn
    </kwd>
   </kwd-group>
  </article-meta>
 </front>
 <body>
  <sec id="s1">
   <title>1. Introduction</title>
   <p>Traditional shifting cultivation in Tanzania, also known in Kiswahili as “mahame” (shifted land) or “malale” (fallow land), has been practiced for many years in semi-humid areas. During the pre-colonial and colonial periods, it served as the primary farming strategy as farmers lived in scattered settlements to avoid slavery and tribal wars. It was also employed as a strategy to evade tsetse flies and dangerous wild animals prevalent in sedentary settlements (<xref ref-type="bibr" rid="scirp.135250-11">
     Kikula, 1997
    </xref>; <xref ref-type="bibr" rid="scirp.135250-15">
     Kjekshus, 2022
    </xref>). The farming system was additionally utilized to control the prevalence of weeds, pests, and diseases, while also contributing to the restoration of soil fertility and productivity (<xref ref-type="bibr" rid="scirp.135250-13">
     Kilawe, Mertz et al., 2018
    </xref>; <xref ref-type="bibr" rid="scirp.135250-12">
     Kilawe et al., 2022
    </xref>).</p>
   <p>Recent studies have shown that traditional long fallow shifting cultivation has been intensified into short fallow systems and continuous annual cropping (<xref ref-type="bibr" rid="scirp.135250-1">
     Birch-Thomsen &amp; Fog, 1996
    </xref>; <xref ref-type="bibr" rid="scirp.135250-5">
     Grogan et al., 2013
    </xref>; <xref ref-type="bibr" rid="scirp.135250-8">
     Itani, 2007
    </xref>; <xref ref-type="bibr" rid="scirp.135250-13">
     Kilawe, Mertz et al., 2018
    </xref>; <xref ref-type="bibr" rid="scirp.135250-17">
     Luoga et al., 2000
    </xref>). Population pressure, market access, technological advancement and policies have been cited as the major drivers of land-use intensification in East Africa (<xref ref-type="bibr" rid="scirp.135250-2">
     Birch-Thomsen, 1999
    </xref>; <xref ref-type="bibr" rid="scirp.135250-1">
     Birch-Thomsen &amp; Fog, 1996
    </xref>; <xref ref-type="bibr" rid="scirp.135250-3">
     Chidumayo, 1987
    </xref>; <xref ref-type="bibr" rid="scirp.135250-5">
     Grogan et al., 2013
    </xref>; <xref ref-type="bibr" rid="scirp.135250-8">
     Itani, 2007
    </xref>; <xref ref-type="bibr" rid="scirp.135250-13">
     Kilawe, Mertz et al., 2018
    </xref>; <xref ref-type="bibr" rid="scirp.135250-17">
     Luoga et al., 2000
    </xref>; <xref ref-type="bibr" rid="scirp.135250-35">
     Van Vliet et al., 2012
    </xref>). Most studies such as those of (<xref ref-type="bibr" rid="scirp.135250-2">
     Birch-Thomsen, 1999
    </xref>; <xref ref-type="bibr" rid="scirp.135250-3">
     Chidumayo, 1987
    </xref>; <xref ref-type="bibr" rid="scirp.135250-5">
     Grogan et al., 2013
    </xref>; <xref ref-type="bibr" rid="scirp.135250-26">
     Stromgaard, 1989
    </xref>) have analyzed the role of population growth, technology and market in intensification of shifting cultivation in the region. There are few studies that show the role of policies on small-scale farming and how the farmers have reacted to these policies to change their farming systems (<xref ref-type="bibr" rid="scirp.135250-28">
     Sunseri, 2003
    </xref>).</p>
   <p>Consequently, this case study explores the role of land-tenure, agriculture, and forestry policies on intensification of shifting cultivation at a village level in Tanzania. The study is based on data acquired through intensive review of the policy documents, individual and group farmer interview and field observation. The paper starts with a literature review on how policies developed over the past 100 years have contributed to the transformation of shifting cultivation in Tanzania. Thereafter, I present a case study showing the role of policies in intensification of shifting cultivation at village level.</p>
  </sec><sec id="s2">
   <title>2. Literature Review on Historical Impacts of Land Use Policies on Shifting Cultivation</title>
   <p>Tanzania-previously known as Tanganyika, was colonized by German between 1885 and 1918. Ten years after German successful invasion, they passed a land-tenure Act called “Regarding creations, Acquisition and Conveyance of Crown land” of 1895. The Act declared all lands in Tanganyika as crown land vested in German empire (<xref ref-type="bibr" rid="scirp.135250-7">
     Iliffe, 1969
    </xref>; <xref ref-type="bibr" rid="scirp.135250-27">
     Sundet, 1997
    </xref>; <xref ref-type="bibr" rid="scirp.135250-29">
     United Republic of Tanzania, 1995
    </xref>). This Act recognized two types of land ownership: public land managed and administered by Governor on behalf of German Empire and the freehold land owned and managed by settlers. The Africans could only access and use reserved land for the Natives on condition that it should be physically occupied (<xref ref-type="bibr" rid="scirp.135250-6">
     Hamilton &amp; Mwasha, 1989
    </xref>; <xref ref-type="bibr" rid="scirp.135250-7">
     Iliffe, 1969
    </xref>). The colonial administration introduced and promoted intensive agriculture that was based on well managed plantations of cotton, coffee, peanut, sisal and rubber (<xref ref-type="bibr" rid="scirp.135250-7">
     Iliffe, 1969
    </xref>; <xref ref-type="bibr" rid="scirp.135250-11">
     Kikula, 1997
    </xref>; <xref ref-type="bibr" rid="scirp.135250-28">
     Sunseri, 2003
    </xref>). They prohibited and discouraged traditional agriculture characterized with shifting cultivation, even though it continued to be practiced secretly (<xref ref-type="bibr" rid="scirp.135250-11">
     Kikula, 1997
    </xref>; <xref ref-type="bibr" rid="scirp.135250-24">
     Raikes, 1986
    </xref>). The intensive agriculture promoted and established by the colonialist proved failure during the two decades of their administration in Tanganyika (<xref ref-type="bibr" rid="scirp.135250-7">
     Iliffe, 1969
    </xref>). The farming system failed largely due to poor climatic conditions and soils, pests and endless wars from locals who protested against land alienation, land-use restrictions and forced labor (<xref ref-type="bibr" rid="scirp.135250-6">
     Hamilton &amp; Mwasha, 1989
    </xref>; <xref ref-type="bibr" rid="scirp.135250-7">
     Iliffe, 1969
    </xref>; <xref ref-type="bibr" rid="scirp.135250-28">
     Sunseri, 2003
    </xref>). The colonialists reviewed their land and agricultural policies to give the natives more access to land and freedom to labor. Albrecht von Rechenberg, the German East Africa governor of the time wrote: “It serves the public interest to promote native settlement and their attachment to the soil, not to diminish it” (<xref ref-type="bibr" rid="scirp.135250-7">
     Iliffe, 1969
    </xref>). The Germans then introduced a “Nyamwezi and Peanut Policy” in the Central and “Peasant Cotton Policy” in the Lake zone and Southeast Tanzania (<xref ref-type="bibr" rid="scirp.135250-7">
     Iliffe, 1969
    </xref>; <xref ref-type="bibr" rid="scirp.135250-28">
     Sunseri, 2003
    </xref>). The context of the policies was to promote local farming systems on the view that it was more adapted to local environmental conditions. It was assumed that the local farming systems would naturally intensify due to attractions from the market demand and the German government would benefit from collection of tax (<xref ref-type="bibr" rid="scirp.135250-7">
     Iliffe, 1969
    </xref>). They consigned intensive cultivation of managed crop plantations to settlers confined in the Northern Zone of Tanganyika (<xref ref-type="bibr" rid="scirp.135250-6">
     Hamilton &amp; Mwasha, 1989
    </xref>; <xref ref-type="bibr" rid="scirp.135250-7">
     Iliffe, 1969
    </xref>). The German agricultural reform model performed very well with massive increase in tax collection and decline in conflicts in a very short time (<xref ref-type="bibr" rid="scirp.135250-7">
     Iliffe, 1969
    </xref>). Besides agriculture, the colonialist promoted forest protection for production purposes-establishment of crop plantations and timber for export (<xref ref-type="bibr" rid="scirp.135250-6">
     Hamilton &amp; Mwasha, 1989
    </xref>; <xref ref-type="bibr" rid="scirp.135250-7">
     Iliffe, 1969
    </xref>). They created and gazetted several forest reserves and enforced stringent rules and regulations, but the rules only applied to gazetted or reserved forests (<xref ref-type="bibr" rid="scirp.135250-6">
     Hamilton &amp; Mwasha, 1989
    </xref>; <xref ref-type="bibr" rid="scirp.135250-7">
     Iliffe, 1969
    </xref>; <xref ref-type="bibr" rid="scirp.135250-28">
     Sunseri, 2003
    </xref>; <xref ref-type="bibr" rid="scirp.135250-36">
     Zahabu et al., 2009
    </xref>).</p>
   <p>The German colonial administration in Tanganyika was overthrown by British during the First World War (1914-1918). The British ruled Tanganyika between 1919 and 1961, when Tanganyika gained her independence. The British continued with the land-tenure Act enacted by Germans until 1923, when they enacted the Land Tenure Ordinance No.3-also known as Land Ordinance Chapter 113. This Act declared all lands in Tanzania as public lands and the right over or in land were vested under the British Governor in Tanganyika (<xref ref-type="bibr" rid="scirp.135250-29">
     United Republic of Tanzania, 1995
    </xref>). Like German era, under British, the Natives could only access and use land approved by the Governor (<xref ref-type="bibr" rid="scirp.135250-11">
     Kikula, 1997
    </xref>; <xref ref-type="bibr" rid="scirp.135250-25">
     Reed, 1979
    </xref>; <xref ref-type="bibr" rid="scirp.135250-27">
     Sundet, 1997
    </xref>). However, in 1928, the Land Tenure Ordinance was amended and customary right of occupancy for the Natives introduced. The new Act vested the powers on land (held and used by local communities) to local Chiefs and the Chiefs could exercise the powers to the locals based on traditional norms and regulations (<xref ref-type="bibr" rid="scirp.135250-25">
     Reed, 1979
    </xref>). The aims of this approach were described as: “first to provide a form of local government, close to the people, which the people themselves understood, using traditional leaders of the people as administrator, and second to initiate participation by the indigenous people in the Government of the country, such as could be expanded with their increasing education and experience into full integration” (<xref ref-type="bibr" rid="scirp.135250-25">
     Reed, 1979
    </xref>). The British continued the agricultural policies implemented by the Germans (<xref ref-type="bibr" rid="scirp.135250-25">
     Reed, 1979
    </xref>). They promoted intensive agriculture such as managed groundnuts, coffee, tobacco, tea, oil palms, rubber, and sisal. However, intensive agriculture did not deliver the desired results due to high crop failure caused by pests and diseases, drought and poor soils (<xref ref-type="bibr" rid="scirp.135250-6">
     Hamilton &amp; Mwasha, 1989
    </xref>; <xref ref-type="bibr" rid="scirp.135250-27">
     Sundet, 1997
    </xref>). The British administration also continued the establishment of forest reserves, but unlike the Germans, their motives for establishment of forest reserves were to conserve soil, water and biodiversity (<xref ref-type="bibr" rid="scirp.135250-6">
     Hamilton &amp; Mwasha, 1989
    </xref>). During the late years of British administration in Tanganyika, they enacted the Forest Ordinance Chapter 389 of 1959. This Act imposed restriction on local access to protected forests, but the rules and regulations were only applicable to gazetted or declared forest reserves (<xref ref-type="bibr" rid="scirp.135250-36">
     Zahabu et al., 2009
    </xref>)</p>
   <p>Tanganyika gained independence from British in 1961 and in 1964 it became the United Republic of Tanzania after a merge with Zanzibar Archipelago. The first phase of government was led by the President Mwalimu Julius Kambarage Nyerere between 1961 and 1985. Tanzania continued with the Land Tenure Ordinance Act of 1923 enacted by the British administration. However, in 1963 the government enacted African Chiefs Ordinance Act No.13 which made absolute the powers of Chiefs in allocation and distribution of lands to individuals under customary laws (<xref ref-type="bibr" rid="scirp.135250-29">
     United Republic of Tanzania, 1995
    </xref>). In 1965, the government enacted another act, The Land Tenure Act. The Act granted the government settlement authority, the powers of allocation and distribution of community land to individuals. Further, the Act converted the freehold tenure to Government Leasehold not exceeding 99 years (<xref ref-type="bibr" rid="scirp.135250-27">
     Sundet, 1997
    </xref>; <xref ref-type="bibr" rid="scirp.135250-29">
     United Republic of Tanzania, 1995
    </xref>). In 1967, the government introduced a voluntary re-settlement programme called Ujamaa (familyhood) which required rural people to move to a concentrated area called Ujamaa village. The aim was to change traditional settlement characterized with isolated pockets, shifting cultivation, small farms, poor implements, and low yields to larger permanent settlement characterized with modern permanent cultivation, higher yield and with easy provision of development facilities (<xref ref-type="bibr" rid="scirp.135250-4">
     Daley, 2005
    </xref>; <xref ref-type="bibr" rid="scirp.135250-11">
     Kikula, 1997
    </xref>; <xref ref-type="bibr" rid="scirp.135250-16">
     Limbu, 1995
    </xref>). However, rural communities did not respond to the call since by the end of 1969 only 2.5% of the country’s population had voluntarily resettled into the villages (<xref ref-type="bibr" rid="scirp.135250-4">
     Daley, 2005
    </xref>; <xref ref-type="bibr" rid="scirp.135250-11">
     Kikula, 1997
    </xref>). Between 1970 and 1976, the government introduced and implemented a forceful re-settlement of rural communities from traditional settlement to Ujamaa villages—this programme is also known as “villagisation” (Operation Vijiji in Swahili). The Ujamaa village consisted between 250 - 600 families and the land was allocated to the household by the Village Council (<xref ref-type="bibr" rid="scirp.135250-11">
     Kikula, 1997
    </xref>; <xref ref-type="bibr" rid="scirp.135250-27">
     Sundet, 1997
    </xref>). The villagisation programme was accompanied by several agricultural policies such as Siasa ni Kilimo (Politics is Agriculture) of 1972 and Kilimo cha Kufa na Kupona (Do or die agriculture) of 1974 all of which promoted intensive and permanent cultivation. Farmers were supplied with subsidized improved hybrid maize seeds and fertilizers, Tri-Super Phosphate (TSP) and Calcium-Ammonium Nitrate (CAN) (<xref ref-type="bibr" rid="scirp.135250-2">
     Birch-Thomsen, 1999
    </xref>; <xref ref-type="bibr" rid="scirp.135250-11">
     Kikula, 1997
    </xref>). Further, in Ujamaa village, only two type of farming systems were allowed: Communal farming system (Ujamaa farming), where crop production was performed on village field(s) on a cooperative basis and a block farming system (bega kwa bega), whereby individuals were allocated small private fields, but the fields were located adjacent to each other in a block form for easy supervision and supply of agriculture inputs (<xref ref-type="bibr" rid="scirp.135250-4">
     Daley, 2005
    </xref>; <xref ref-type="bibr" rid="scirp.135250-11">
     Kikula, 1997
    </xref>). Despite all the efforts to modernize traditional agriculture, productivity declined significantly during villagisation leading to severe hunger and poverty in the early 1980s (<xref ref-type="bibr" rid="scirp.135250-4">
     Daley, 2005
    </xref>; <xref ref-type="bibr" rid="scirp.135250-11">
     Kikula, 1997
    </xref>). Decline in productivity was associated with inadequate knowledge on fertilizer application, poor climate condition; cultivation of one site for long period and state monopoly of crop market and poor infrastructure (<xref ref-type="bibr" rid="scirp.135250-11">
     Kikula, 1997
    </xref>; <xref ref-type="bibr" rid="scirp.135250-16">
     Limbu, 1995
    </xref>; <xref ref-type="bibr" rid="scirp.135250-24">
     Raikes, 1986
    </xref>; <xref ref-type="bibr" rid="scirp.135250-27">
     Sundet, 1997
    </xref>). In 1983, the government developed the National Agricultural Policy to prevent the breakdown of the sector. The policy among many encouraged commercial agriculture, and relaxed land-use restrictions (<xref ref-type="bibr" rid="scirp.135250-1">
     Birch-Thomsen &amp; Fog, 1996
    </xref>; <xref ref-type="bibr" rid="scirp.135250-4">
     Daley, 2005
    </xref>; <xref ref-type="bibr" rid="scirp.135250-27">
     Sundet, 1997
    </xref>). Some villagers reacted to these changes by going back to their old traditional settlement and cultivation methods (<xref ref-type="bibr" rid="scirp.135250-4">
     Daley, 2005
    </xref>; <xref ref-type="bibr" rid="scirp.135250-27">
     Sundet, 1997
    </xref>). Shifting cultivation of maize and finger millet was once again on course and this time saw large forest area opened for cultivation, expanding radially outward from village core (<xref ref-type="bibr" rid="scirp.135250-2">
     Birch-Thomsen, 1999
    </xref>; <xref ref-type="bibr" rid="scirp.135250-4">
     Daley, 2005
    </xref>; <xref ref-type="bibr" rid="scirp.135250-11">
     Kikula, 1997
    </xref>; <xref ref-type="bibr" rid="scirp.135250-24">
     Raikes, 1986
    </xref>). In 1984, the government introduced land use planning in villages in attempt to control land degradation caused by poor farming methods (<xref ref-type="bibr" rid="scirp.135250-27">
     Sundet, 1997
    </xref>). However, village land use planning failed to make an impact largely due to its top-down approach, poor quality and inability to solve land-tittle issues (<xref ref-type="bibr" rid="scirp.135250-27">
     Sundet, 1997
    </xref>). During the first government phase, the government adopted the Forest Ordinance of 1959 enacted during the British administration.</p>
   <p>The second phase government was elected and governed between 1985 and 1995. This phase is known as a period of economic liberalization and recovery from the economic downturn of the first government phase. Contrary to the first phase, this phase agricultural subsidies were removed, the government withdrew from physical agriculture and private sector allowed to process and trade on agricultural products (<xref ref-type="bibr" rid="scirp.135250-2">
     Birch-Thomsen, 1999
    </xref>; <xref ref-type="bibr" rid="scirp.135250-4">
     Daley, 2005
    </xref>; <xref ref-type="bibr" rid="scirp.135250-5">
     Grogan et al., 2013
    </xref>; <xref ref-type="bibr" rid="scirp.135250-16">
     Limbu, 1995
    </xref>). There were few restrictions imposed on agriculture development in this phase, thus the small scale, medium and commercial agriculture increased (<xref ref-type="bibr" rid="scirp.135250-27">
     Sundet, 1997
    </xref>). Toward the end of this phase, the government approved the National Land Policy of 1995. The Policy recognized two types of land-tenure: the granted right of occupancy in reserved National lands and customary right of occupancy in Village lands. The village council was granted the power to administer the customary right of occupancy on village lands on conditions that the village should: 1) have a land use plan, 2) village land certificate and 3) village land registry. In this Policy, the top-down approach of the 1984 land-use plans was replaced with introduction of participatory approach in land-use planning, however some land-uses such as shifting cultivation and nomadism were prohibited (<xref ref-type="bibr" rid="scirp.135250-27">
     Sundet, 1997
    </xref>; <xref ref-type="bibr" rid="scirp.135250-29">
     United Republic of Tanzania, 1995
    </xref>). In this phase, the Forest Ordinance of 1959 continued to be used in management of forest resources. However, in 1992 the concept of Participatory Forest Management was introduced whereby involvement of local communities in forest management was sought (<xref ref-type="bibr" rid="scirp.135250-36">
     Zahabu et al., 2009
    </xref>).</p>
   <p>The third phase government governed between 1995 and 2005. This government phase witnessed a sharp increase in interest in formal settlement and nature conservation. In this phase, the National Land Policy of 1995 was translated into the National Land Act No. 4 of 1999 and the Village Land Act No. 5 of 1999. The National Land Act declares all land in Tanzania as public land, held in trust by the Head of State. Land tenure is in-form of a right of occupancy for Tanzanians and leasehold for foreigners. The Act categorizes lands into three: The reserved land, village land and general land. The reserved lands encompass all lands set aside for special purpose, including forest reserves, game parks, game reserves, land reserved for public utilities and highways, hazardous land and land reserved for settlement. Reserved land is managed by the sector under which it was reserved. The land tenure for this land category is granted right of occupancy or derivative right of occupancy granted by the Commissioner of lands on behalf of the President of United Republic of Tanzania. General lands denote all lands which are not reserved land or village land, including unused or unoccupied village land. The management, administration and land tenure in general land is similar to reserved lands (<xref ref-type="bibr" rid="scirp.135250-31">
     URT, 1999a
    </xref>). The village land encompasses all lands within the boundaries of the village. The land is managed by the village assembly. The land tenure in village land is customary right of occupancy administered by the Village Council on behalf of Village Assembly (<xref ref-type="bibr" rid="scirp.135250-31">
     URT, 1999a
    </xref>, <xref ref-type="bibr" rid="scirp.135250-32">
     1999b
    </xref>). The Village Land Act made land-use plans a requirement for a village to be registered and granted Village Land Certificate (<xref ref-type="bibr" rid="scirp.135250-32">
     URT, 1999b
    </xref>). In other words, villages that have not conducted land use planning, do not have village land certificate or village boundaries, and are thus considered to be in general land category. Further, the Act identifies the lawful land-uses that a village land-use plan should contain. It prohibits leaving a piece of land to fallow for a period of more than five years, otherwise the land is declared abandoned, and the Act directs village council to revoke the ownership and transfer it back to the village council or to another villager (<xref ref-type="bibr" rid="scirp.135250-32">
     URT, 1999b
    </xref>). In the context, ownership of a village land is not real customary as claimed in the Act since the central government has already decided the uses the land should be put to. During the third government phase, the government passed the National Agricultural and Livestock Policy of 1997. The Policy supports land-use planning for efficient delivery of agricultural education and extension services. The policy condemns shifting cultivation and directs that it should be discouraged, and intensive permanent agriculture promoted (<xref ref-type="bibr" rid="scirp.135250-34">
     URT, 2007
    </xref>). In this government phase, the government also passed the National Forestry Policy of 1998 and enacted the National Forest Act No.14 of 2002. The Policy defines forest in a broader way that also includes agricultural fields under fallow. Forest is defined as: “all land bearing vegetation association dominated by trees of any size, exploitable or not, and capable of producing wood or other products of exerting influence on the climate or water regime or providing shelter to livestock and wildlife (<xref ref-type="bibr" rid="scirp.135250-30">
     URT, 1998
    </xref>). The Policy categories forest tenure into: Central and local authority forest reserve, community forest reserves, private forests, and forest on public land (non-reserved forest land). The implication of this categorization is that agricultural fields under fallow fall under private forest if the farmer has the certificate of customary right of occupancy (CCRO) or forest on public land if the villager does not have the CCRO. The Policy identifies shifting cultivation as a threat to forest cover and biodiversity in reserved forests and non-reserved forest in public lands thus direct the conversion of later to forest reserves and ensure intensive survey in forest reserves (<xref ref-type="bibr" rid="scirp.135250-30">
     URT, 1998
    </xref>). The Forest Act requires all forests (including fields under fallows) to be managed according to forest management plan approved by the Director of Forest. The Act also prohibit the extraction of forest products without authorized license or permit (<xref ref-type="bibr" rid="scirp.135250-33">
     URT, 2002
    </xref>). In other words, it is illegal for a farmer to clear his/her fallow without permit.</p>
   <p>The fourth phase government governed between 2005 and 2015. In this phase, the land tenure policies developed in the previous phase were adopted. However, the land-use planning was given a particular emphasis through development of Guidelines of Participatory Land Use Management (PLUM) in 2006 and enactment of the National Land Use Planning Act in 2007. PLUM provided six main steps on how to conduct participatory village land-use planning (NLUPC 2006). The guide suggested the potential land-use for villages in Tanzania but gave the flexibility to include the already established land-uses in the villages. The Land Use Planning Act approved the village council to be the planning authority in village land-use planning. The Act called on the village council to follow the procedures outlined in Village Land Act of 1999 and PLUM of 2006 to conduct land-use plans that involves participation of all land beneficiaries and based on land suitability assessment (<xref ref-type="bibr" rid="scirp.135250-34">
     URT, 2007
    </xref>). Regarding agriculture, this government phase was seen as a period of agriculture revolution due to large investment and focus on intensive agriculture. The government launched big and ambitious agricultural programmes such as Agriculture Sector Development Strategy (ASDS) of 2006, Agricultural Sector Development Programme (ASDP) of 2008, Kilimo Kwanza (Agriculture First) of 2009 and Private Public Partnership (PPP) of 2012. The programs aimed to modernize and commercialize agriculture through involvement of private sector (<xref ref-type="bibr" rid="scirp.135250-22">
     Ngaiza, 2012
    </xref>). Ideally, private investors are granted large piece of village land for large scale commercial cultivation. The programmes provide guidelines on how to increase agriculture productivity in small scale agriculture through provision of subsidies such as fertilizer, improved seeds, irrigation and mechanization (<xref ref-type="bibr" rid="scirp.135250-22">
     Ngaiza, 2012
    </xref>). Further, the programmes provide a guideline on how to avoid degradation due to shifting cultivation through adoption of climate resilient agriculture (<xref ref-type="bibr" rid="scirp.135250-21">
     Mshale et al., 2012
    </xref>). Under this concept, “intensive” agriculture demonstration gardens (Shamba Darasa), were developed in almost every village or wards. The villagers were advised to follow the Shamba darasa model in their own gardens. A survey of two villages in Kilosa District revealed that this model has not been voluntarily accepted by the farmers. Less than 5% of the famers use fertilizers, pesticides, even when those were provided for free (<xref ref-type="bibr" rid="scirp.135250-13">
     Kilawe, Mertz et al., 2018
    </xref>). Regarding forestry, in this phase, the government continued to implement the Forest Policy of 1998 and enforce the Forest Act of 2002. In 2007, the government ratified the Kyoto protocol. The international agreement allows the member countries to reduce their greenhouse gas emissions through market-based mechanisms. The mechanisms through which the emissions can be traded are the Clean Development Mechanism (CDM) and the proposed Reduced Emission from Deforestation and Forest Degradation plus (REDD+). The later mechanism is seen as a threat to shifting cultivation since it targets the restoration of deforested and degraded landscape. In Tanzania the National Forest Policy of 1998 and the National REDD Strategy of 2013 identify the fallows as degraded “forest” (<xref ref-type="bibr" rid="scirp.135250-34">
     URT, 2007
    </xref>). There is considerable risk that shifting cultivators may lose their land in expense of establishment of forest reserves for carbon sequestration and storage.</p>
   <p>Shifting cultivation in Tanzania has survived despite the effort to convert it to intensive permanent cultivation. The recent official figures show that the farming system occupies 7.6% of the total country land area and 33% of area classified as woodlands in Tanzania (<xref ref-type="bibr" rid="scirp.135250-18">
     Malimbwi &amp; Zahabu, 2014
    </xref>). There are no country level estimates of the number of people relying on this land-use. However, local level estimates are: 5% in Sumbawanga (<xref ref-type="bibr" rid="scirp.135250-5">
     Grogan et al., 2013
    </xref>); 20% - 50% in Kilosa (<xref ref-type="bibr" rid="scirp.135250-13">
     Kilawe, Mertz et al., 2018
    </xref>; <xref ref-type="bibr" rid="scirp.135250-23">
     Norrlund &amp; Brus, 2004
    </xref>); 68% in Kitulanghalo (<xref ref-type="bibr" rid="scirp.135250-17">
     Luoga et al., 2000
    </xref>); 90% in Urambo (<xref ref-type="bibr" rid="scirp.135250-19">
     Mangora, 2012
    </xref>) and 70% - 100% in Lindi rural district (<xref ref-type="bibr" rid="scirp.135250-21">
     Mshale et al., 2012
    </xref>). The practices and techniques in shifting cultivation have however been transformed into intensive short fallows and grass composite systems (<xref ref-type="bibr" rid="scirp.135250-5">
     Grogan et al., 2013
    </xref>; <xref ref-type="bibr" rid="scirp.135250-13">
     Kilawe, Mertz et al., 2018
    </xref>).</p>
  </sec><sec id="s3">
   <title>3. Methodology</title>
   <sec id="s3_1">
    <title>3.1. The Case Study Area</title>
    <p>This study was conducted in Ulaya Mbuyuni Village in Kilosa District. The village was selected randomly from the list of eight other villages with a history of shifting cultivation and had performed land-use planning.</p>
    <p>Ulaya Mbuyuni village is situated 30 km along the rough road from Kilosa to Mikumi Township and is bounded by latitude 7˚01'29" and 7˚01'55" South and longitudes 36˚57'07" and 36˚58'01" East (<xref ref-type="fig" rid="fig1">
      Figure 1
     </xref>). The village has a total village area of 57.22 km<sup>2</sup> and with the total population of 3474 people, resulting in a population density of 60 persons per km<sup>2</sup>. The village had 354 households divided into six sub-villages (<xref ref-type="bibr" rid="scirp.135250-9">
      KDC, 2012a
     </xref>). The traditional ethnic group in the village is Wasagala, but many other ethnic groups such as Wagogo, Wasukuma, Waha, Wanyamwezi, Wangoni, Wahehe and Wakwiva have moved in over time. Most of the immigrants were laborers in the failed sisal plantations in the district. According to Kilosa District Council, the village falls under central and southern agro-climatic zone (<xref ref-type="bibr" rid="scirp.135250-9">
      KDC, 2012a
     </xref>). The mean annual rainfall is estimated to range between 1000 and 1400 mm falling in two seasons (“long” rains between March and May and “short” rains between October and December). Mean annual</p>
    <fig id="fig1" position="float">
     <label>Figure 1</label>
     <caption>
      <title>Figure 1. Map of study area. The map was created by Mr. Thadei Rugambwa.</title>
     </caption>
     <graphic mimetype="image" position="float" xlink:type="simple" xlink:href="https://html.scirp.org/file/1621032-rId13.jpeg?20240815093421" />
    </fig>
    <p>temperature ranges between 25˚C - 27˚C. The natural vegetation is Miombo woodland dominated by Brachystegia microphylla, Brachystegia boehmii, Diplorhynchus condylocarpon and Combretum collinum. The soils of Ulaya Mbuyuni village are typically an association of very deep, well drained, dark gray, very friable, clays with thick reddish-brown clay top soils on ridge summits (Rhodi-Ferric Ferralsols) and very deep, well drained, dark brown to strong brown, sandy clay loams with thin brown sandy loam top soils on ridge slopes (Ferri-Profondic Luvisols and Acrisols) (<xref ref-type="bibr" rid="scirp.135250-14">
      Kimaro et al., 2008
     </xref>).</p>
    <p>The main economic activity in this village is small-scale farming, comprising 81% of the households. The main crops are Maize, sorghum, rice, pigeon pea, sesame, cowpea, and sunflower. Farming takes two forms: 1) Permanent and continuous cultivation around the village and valleys or nearby the rivers. This involves cultivation of rice, maize, sunflower, beans, bananas and most vegetables and 2) shifting cultivation is practiced far (around 4 km) from the village core, scattering all over the woodland. The crops grown under shifting cultivation are sesame, cowpea and pigeion pea.</p>
   </sec>
   <sec id="s3_2">
    <title>3.2. Field Method and Data</title>
    <p>This study is based on data acquired through review of the land use plan, individual and group farmer interview and field observation. Land use plan was selected because it is a tool framed for implementation of land tenure and resource use policies at village level (<xref ref-type="bibr" rid="scirp.135250-34">
      URT, 2007
     </xref>). The steps provided in the guidelines for participatory land-use management (PLUM) of 2006 were evaluated against actual procedures in the villages. The actual procedures in the villages are documented in the village land use plan of 2012 (<xref ref-type="bibr" rid="scirp.135250-10">
      KDC, 2012b
     </xref>). The interview of village land use management committee (VLUMC) was conducted in 2013 to determine the official perception of the land-use plan and their effects on shifting cultivation. The VLUM were particularly important because they are the ones responsible for land demarcation during land use plan, allocation of land to individuals in the village and enforcement of by-laws attached to each land-use. Semi-structured interviews were administered to seven shifting cultivators, firstly individually and finally in groups. The first shifting cultivator was selected with the assistance of the Village Executive Officer. Through snow bowling technique, the other six shifting cultivators were selected and interviewed. The questions aimed to get the farmers’ view on land use planning and how this has or would affect their farming system currently and the future.</p>
   </sec>
  </sec><sec id="s4">
   <title>4. Results</title>
   <sec id="s4_1">
    <title>4.1. Shifting Cultivation before Land-Use Planning.</title>
    <p>According to the Village Land Use Management Committee (VLUMC), shifting cultivation was practiced by 30% - 35% of all households in the village before the land use planning. VLUMC described the areas where shifting cultivation was practiced as “msituni” (in the forest), implying that the area was dominated by trees. Interviews with shifting cultivators revealed that all of them had permanent fields around their homes or in the valleys. Shifting cultivators mentioned several reasons for practicing shifting cultivation, including controlling weeds and pests, optimizing labor, restoring fertility, controlling soil erosion, and using the fallow phase as a “small bank”. In times of hardship, they could produce timber, poles, or charcoal to sustain the household. They emphasized that weeding was performed only once in a newly opened area but at least three times in an area cultivated continuously for more than three years. The farmers described the practice of shifting cultivation in the following steps: 1) Land clearing was performed between July and September, involving clearing of vegetation and collecting it into several small heaps. 2) Burning of the plant residue (collected in heaps) was done between late September and early October. 3) Post-fire land preparation is performed between October and November. It involves deep plowing to loosen the soil and burry undecomposed vegetation (known as Kukwatua in Kiswahili Language) or scratching of the soil surface and spreading the undecomposed vegetation on the soil surface (Kuberega). 4) Planting was performed between late November and Early January. The crops planted are mostly sesame and pigeon pea if the farms are located far from settlement but otherwise include a mix of different crops such as cowpea, maize, sunflower, millet, sorghum, cassava, beans, and groundnuts. 5) Fallowing and shifting to another field. Cropping continues until the increase in weed and pest infestation becomes too high or yields declines, usually three years for field under sesame or sorghum and five years for field under pigeon pea, maize, or mixture of both. Then farmers shift to another field and leave the current farm to rest as fallow.</p>
   </sec>
   <sec id="s4_2">
    <title>4.2. The Land Use Planning Process</title>
    <p>Land-use planning in this village was conducted in 2012. It was facilitated by two local NGOs. The local NGOs were the initiators of the land-use plan since they were interested in establishing forest reserves for a charcoal project. Land-use planning becomes important here because through it, the village land certificate is granted, land category changes from general land managed and administered by commissioner of lands to village land managed and administered by village council. Further, the land-tenure for individual ownership of land changed from granted right of occupancy to customary right of occupancy. This land-use plan was developed following four steps identified in the Guidelines of Village Land Use Planning of 1998, instead of the six steps identified in 2006 guideline (<xref ref-type="bibr" rid="scirp.135250-10">
      KDC, 2012b
     </xref>). According to the land use plan report and the interview with VLUMC, all villagers were involved in land use planning exercise. However, all (7) interviewed shifting cultivators claimed that they were only involved in village seminars and workshops during awareness creation. They claimed that they were not involved in boundary demarcation and development of by-laws. The village land use planning exercises led to a Land Use Plan that includes five land use categories summarized in <xref ref-type="table" rid="table1">
      Table 1
     </xref>. The table shows dramatic change in areas allocated to some of land uses, the most being agriculture declining from 70.5% to 35.5%, shifting cultivation declining from 28.3% to 0.5% and area allocated for forest reserve increasing from 0 to 61%.</p>
    <table-wrap id="table1">
     <label>
      <xref ref-type="table" rid="table1">
       Table 1
      </xref></label>
     <caption>
      <title>
       <xref ref-type="bibr" rid="scirp.135250-"></xref>Table 1. The area under different land uses before and after land use planning in Ulaya Mbuyuni Village.</title>
     </caption>
     <table class="MsoTableGrid custom-table" border="0" cellspacing="0" cellpadding="0"> 
      <tr> 
       <td class="custom-bottom-td acenter" width="30.26%"><p style="text-align:center">Land Use</p></td> 
       <td class="custom-bottom-td acenter" width="19.40%"><p style="text-align:center">Area before land-use planning (Acre)</p></td> 
       <td class="custom-bottom-td acenter" width="15.46%"><p style="text-align:center">Percentage of total area</p></td> 
       <td class="custom-bottom-td acenter" width="19.57%"><p style="text-align:center">Area after land-use planning (Acre)</p></td> 
       <td class="custom-bottom-td acenter" width="15.31%"><p style="text-align:center">Percentage of total area</p></td> 
      </tr> 
      <tr> 
       <td class="custom-top-td acenter" width="30.26%"><p style="text-align:center">Concentrated settlement</p></td> 
       <td class="custom-top-td acenter" width="19.40%"><p style="text-align:center">164.4</p></td> 
       <td class="custom-top-td acenter" width="15.46%"><p style="text-align:center">1.1</p></td> 
       <td class="custom-top-td acenter" width="19.57%"><p style="text-align:center">231.82</p></td> 
       <td class="custom-top-td acenter" width="15.31%"><p style="text-align:center">1.6</p></td> 
      </tr> 
      <tr> 
       <td class="acenter" width="30.26%"><p style="text-align:center">Agriculture</p></td> 
       <td class="acenter" width="19.40%"><p style="text-align:center">10,093</p></td> 
       <td class="acenter" width="15.46%"><p style="text-align:center">70.5</p></td> 
       <td class="acenter" width="19.57%"><p style="text-align:center">5102.5</p></td> 
       <td class="acenter" width="15.31%"><p style="text-align:center">35.6</p></td> 
      </tr> 
      <tr> 
       <td class="acenter" width="30.26%"><p style="text-align:center">Scattered settlement and farms/shifting cultivation</p></td> 
       <td class="acenter" width="19.40%"><p style="text-align:center">4057</p></td> 
       <td class="acenter" width="15.46%"><p style="text-align:center">28.3</p></td> 
       <td class="acenter" width="19.57%"><p style="text-align:center">79</p></td> 
       <td class="acenter" width="15.31%"><p style="text-align:center">0.6</p></td> 
      </tr> 
      <tr> 
       <td class="acenter" width="30.26%"><p style="text-align:center">Grazing</p></td> 
       <td class="acenter" width="19.40%"><p style="text-align:center">0</p></td> 
       <td class="acenter" width="15.46%"><p style="text-align:center">0.0</p></td> 
       <td class="acenter" width="19.57%"><p style="text-align:center">44.5</p></td> 
       <td class="acenter" width="15.31%"><p style="text-align:center">0.3</p></td> 
      </tr> 
      <tr> 
       <td class="acenter" width="30.26%"><p style="text-align:center">Village forest reserve</p></td> 
       <td class="acenter" width="19.40%"><p style="text-align:center">0</p></td> 
       <td class="acenter" width="15.46%"><p style="text-align:center">0.0</p></td> 
       <td class="acenter" width="19.57%"><p style="text-align:center">8743</p></td> 
       <td class="acenter" width="15.31%"><p style="text-align:center">61.1</p></td> 
      </tr> 
      <tr> 
       <td class="acenter" width="30.26%"><p style="text-align:center">Community service</p></td> 
       <td class="acenter" width="19.40%"><p style="text-align:center">0</p></td> 
       <td class="acenter" width="15.46%"><p style="text-align:center">0.0</p></td> 
       <td class="acenter" width="19.57%"><p style="text-align:center">113.58</p></td> 
       <td class="acenter" width="15.31%"><p style="text-align:center">0.8</p></td> 
      </tr> 
      <tr> 
       <td class="acenter" width="30.26%"><p style="text-align:center">Total</p></td> 
       <td class="acenter" width="19.40%"><p style="text-align:center">14,314.4</p></td> 
       <td class="acenter" width="15.46%"><p style="text-align:center">100.0</p></td> 
       <td class="acenter" width="19.57%"><p style="text-align:center">14,314.4</p></td> 
       <td class="acenter" width="15.31%"><p style="text-align:center">100.0</p></td> 
      </tr> 
     </table>
    </table-wrap>
    <p>Source: Extracted from (<xref ref-type="bibr" rid="scirp.135250-10">
      KDC, 2012b
     </xref>).</p>
    <p>By-laws were enacted to discourage/stop shifting cultivation in areas allocated for agriculture or village forest reserves. The by-laws prohibit any sort of slash-and-burn during land preparation and fallowing for duration longer than 3 years. The by-laws also prohibited extraction of trees for charcoal or timber in these land-uses. Failure to comply with the law could lead to a punishment of TZS50,000 (25USD) or dispossession of the land holding (<xref ref-type="bibr" rid="scirp.135250-10">
      KDC, 2012b
     </xref>). According to VLUM, the fields of more than 30 farms were reclassified as forest reserve and thus they were supposed to be re-allocated other area in the village. The Land Use Planning Team (PLUM) commented on the agriculture practiced in the village as “poor” caused by lack of knowledge on good agriculture practice. They introduced new farming system called “conservation agriculture” for maize and cowpea. The new farming practice involved scratching a piece of land, marking it into lines and plots. The distance between line was 75 cm and between plots 30 cm. In each plot four maize seed were planted and between the lines, green gram was planted. This farming method was demonstrated in the demonstration garden (Shamba darasa) and the farmers were asked to adopt in their farming system.</p>
   </sec>
   <sec id="s4_3">
    <title>4.3. Shifting Cultivation after the Land Use Planning</title>
    <p>According to the VLUM, shifting cultivators in the village declined from 30% - 35% to 25% between 2012 and 2015. However, admitted that it was difficult to enforce the by-laws since the shifting cultivators were returned to their former fields. Interview with shifting cultivators and field observations reveals that the shifting cultivation methods were still widely practiced in 2015. Slash-and-burn and fallowing were still practiced despite being restricted. An important change, however, was that the fallows were managed to look like they were 3 - 4 years as required by the by-law (<xref ref-type="table" rid="table2">
      Table 2
     </xref>). Field observation in the village found the oldest fallow to be 7 years, and even this one, the farmer had already chopped all big trees. Additionally, charcoaling was not being performed in the fields under fallow. Shifting cultivators complained about this one as to why they should not be allowed to do so in their private field. The introduced conservation farming system model was not successful since only 1/7 farmers adopted it. The farmers who tried and abandoned this farming system claimed that it was laborious, due to difficulty in marking and digging the holes. Also, the system required the use of improved maize seeds and fertilizer. The farmers insist that the farming system was not flexible, to include the crops that they wanted. Further, they claimed that the introduced maize seeds required special handling such as fertilizer and pesticides and these should be bought in every season which they cannot afford.</p>
    <table-wrap id="table2">
     <label>
      <xref ref-type="table" rid="table2">
       Table 2
      </xref></label>
     <caption>
      <title>
       <xref ref-type="bibr" rid="scirp.135250-"></xref>Table 2. Farming practices among shifting cultivators before and after land use planning in Ulaya Mbuyuni Village.</title>
     </caption>
     <table class="MsoTableGrid custom-table" border="0" cellspacing="0" cellpadding="0"> 
      <tr> 
       <td class="custom-bottom-td acenter" width="50.92%" colspan="2"><p style="text-align:center">Land use practices</p></td> 
       <td class="custom-bottom-td acenter" width="21.69%" colspan="2"><p style="text-align:center">Before land use planning</p></td> 
       <td class="custom-bottom-td acenter" width="27.39%" colspan="2"><p style="text-align:center">After land use planning</p></td> 
      </tr> 
      <tr> 
       <td class="custom-top-td acenter" width="50.92%" colspan="2"><p style="text-align:center">Fallow duration (years)</p></td> 
       <td class="custom-top-td acenter" width="21.69%" colspan="2"><p style="text-align:center">4 - 7</p></td> 
       <td class="custom-top-td acenter" width="27.39%" colspan="2"><p style="text-align:center">3</p></td> 
      </tr> 
      <tr> 
       <td class="acenter" width="50.78%"><p style="text-align:center">Burning of vegetation</p></td> 
       <td class="acenter" width="21.63%" colspan="2"><p style="text-align:center">√</p></td> 
       <td class="acenter" width="27.31%" colspan="2"><p style="text-align:center">×</p></td> 
      </tr> 
      <tr> 
       <td class="acenter" width="50.78%"><p style="text-align:center">No-till (kuberega)</p></td> 
       <td class="acenter" width="21.63%" colspan="2"><p style="text-align:center">√</p></td> 
       <td class="acenter" width="27.31%" colspan="2"><p style="text-align:center">√</p></td> 
      </tr> 
      <tr> 
       <td class="acenter" width="50.78%"><p style="text-align:center">Deep till (kukwatua)</p></td> 
       <td class="acenter" width="21.63%" colspan="2"><p style="text-align:center">×</p></td> 
       <td class="acenter" width="27.31%" colspan="2"><p style="text-align:center">√</p></td> 
      </tr> 
      <tr> 
       <td class="acenter" width="50.78%"><p style="text-align:center">Mechanization and use of farm input-ox or tractor land preparation, use of improved seeds, fertilizer, pesticides, or irrigation (%)</p></td> 
       <td class="acenter" width="21.63%" colspan="2"><p style="text-align:center">0</p></td> 
       <td class="acenter" width="27.31%" colspan="2"><p style="text-align:center">0</p></td> 
      </tr> 
      <tr> 
       <td class="acenter" width="50.78%"><p style="text-align:center">Use of tree resources in the fallow for firewood, timber, or charcoal</p></td> 
       <td class="acenter" width="21.63%" colspan="2"><p style="text-align:center">√</p></td> 
       <td class="acenter" width="27.31%" colspan="2"><p style="text-align:center">×</p></td> 
      </tr> 
     </table>
    </table-wrap>
    <p>Where: √: practiced ×: not practiced.</p>
   </sec>
  </sec><sec id="s5">
   <title>5. Discussion</title>
   <p>This case study shows how policy instruments have been used to drive the intensification of shifting cultivation at the village level. Through land use planning, no land was allocated to shifting cultivation, and many restrictions were imposed on shifting cultivation practices, such as the use of fire during land preparation and the restriction on fallow periods longer than three years. It was also found that some shifting cultivators were returning to their former fields (from which they were evicted after land use planning). This can partly be attributed to difficulties in implementing the alternative livelihood strategies imposed on them, leading to periods of food insecurity (<xref ref-type="bibr" rid="scirp.135250-13">
     Kilawe, Mertz et al., 2018
    </xref>). Alternative farming technologies, such as conservation agriculture, were introduced, but the adoption rate was very low because they were labor-intensive and there was a general lack of farm inputs such as pesticides and fertilizer.</p>
   <p>The additional restrictions, such as not allowing farmers to leave the land fallow for more than three years, might lead to a degraded shifting cultivation landscape. Low tree cover in agricultural fields could lead to a shortage of firewood, charcoal, medicine, and timber, which will attract people to encroach on reserved forests. Furthermore, the restriction on using trees during the fallow period could result in low motivation for maintaining trees in agricultural landscapes. It has been argued that the benefits associated with smallholder farming systems must be given to the farmers involved (<xref ref-type="bibr" rid="scirp.135250-20">
     Mertz &amp; Bruun, 2017
    </xref>).</p>
   <p>It has been suggested that sustainable intensification of traditional farming practices should come through agricultural technologies developed, tested, and adopted by farmers themselves. This kind of intensification, described as autonomous intensification, occurs gradually over time and is shaped by an increase in population and innovation of new technologies (<xref ref-type="bibr" rid="scirp.135250-2">
     Birch-Thomsen, 1999
    </xref>; <xref ref-type="bibr" rid="scirp.135250-20">
     Mertz &amp; Bruun, 2017
    </xref>). Market opportunities, for example, have been shown to lead to the adoption of animal traction in Southern Tanzania (<xref ref-type="bibr" rid="scirp.135250-2">
     Birch-Thomsen, 1999
    </xref>). Forceful intensification of shifting cultivation can negatively affect the livelihoods of the farmers involved (<xref ref-type="bibr" rid="scirp.135250-13">
     Kilawe, Mertz et al., 2018
    </xref>)</p>
  </sec><sec id="s6">
   <title>Acknowledgements</title>
   <p>This study was funded by the Danish Ministry of Foreign Affairs (Danida) through the Building Stronger Universities Programme (BSU). We are grateful to the local people of Ulaya Mbuyuni for providing information. Our thanks also go to Abdalah Mazingira for his valuable support during fieldwork.</p>
  </sec><sec id="s7">
   <title>Data Availability</title>
   <p>The datasets generated during and/or analyzed during the current study are available from the corresponding author on reasonable request.</p>
  </sec>
 </body><back>
  <ref-list>
   <title>References</title>
   <ref id="scirp.135250-ref1">
    <label>1</label>
    <mixed-citation publication-type="other" xlink:type="simple">
     Birch-Thomsen, T.,&amp;Fog, B. (1996). Changes within Small-Scale Agriculture. A Case-Study from the Southwestern Tanzania. Geografisk Tidsskrift-Danish Journal of Geography, 96, 60-69. &gt;https://doi.org/10.1080/00167223.1996.10649377
    </mixed-citation>
   </ref>
   <ref id="scirp.135250-ref2">
    <label>2</label>
    <mixed-citation publication-type="other" xlink:type="simple">
     Birch-Thomsen, T., Karim-Sesay, J. A.,&amp;Croxton, S. (1999). 2. Animal Traction and Market Conditions: A Case Study from South-Western Tanzania and Northern Zambia; Draft Animal Power Potential and Utilisation in the Tonota District of Botswana; Users in Control: Farmer Participation in Technology Research and Development. In P. Starkey,&amp;P. Kaumbutho (Eds.), Meeting the Challenges of Animal Traction (pp. 33-50). Practical Action Publishing.
    </mixed-citation>
   </ref>
   <ref id="scirp.135250-ref3">
    <label>3</label>
    <mixed-citation publication-type="other" xlink:type="simple">
     Chidumayo, E. N. (1987). A Shifting Cultivation Land Use System under Population Pressure in Zambia. Agroforestry Systems, 5, 15-25. &gt;https://doi.org/10.1007/bf00046411
    </mixed-citation>
   </ref>
   <ref id="scirp.135250-ref4">
    <label>4</label>
    <mixed-citation publication-type="other" xlink:type="simple">
     Daley, E. (2005). Land and Social Change in a Tanzanian Village 1: Kinyanambo, 1920s-1990. Journal of Agrarian Change, 5, 363-404. &gt;https://doi.org/10.1111/j.1471-0366.2005.00105.x
    </mixed-citation>
   </ref>
   <ref id="scirp.135250-ref5">
    <label>5</label>
    <mixed-citation publication-type="other" xlink:type="simple">
     Grogan, K., Birch-Thomsen, T.,&amp;Lyimo, J. (2013). Transition of Shifting Cultivation and Its Impact on People’s Livelihoods in the Miombo Woodlands of Northern Zambia and South-Western Tanzania. Human Ecology, 41, 77-92. &gt;https://doi.org/10.1007/s10745-012-9537-9
    </mixed-citation>
   </ref>
   <ref id="scirp.135250-ref6">
    <label>6</label>
    <mixed-citation publication-type="other" xlink:type="simple">
     Hamilton, A. C.,&amp;Mwasha, I. V. (1989). History of Resource Utilization and Management. In A. C. Hamilton,&amp;R. Bensted-Smith (Eds.), Forest Conservation in the East Usambara Mountains Tanzania (pp. 45-56). IUCN.
    </mixed-citation>
   </ref>
   <ref id="scirp.135250-ref7">
    <label>7</label>
    <mixed-citation publication-type="other" xlink:type="simple">
     Iliffe, J. (1969). Tanganyika under German Rule 1905-1912. Cambridge University Press. &gt;https://doi.org/10.1017/cbo9780511759635
    </mixed-citation>
   </ref>
   <ref id="scirp.135250-ref8">
    <label>8</label>
    <mixed-citation publication-type="other" xlink:type="simple">
     Itani, J. (2007). Effects of Socio-Economic Changes on Cultivation Systems under Customary Land Tenure in MBozi District, Southerzania. African Study Monographs, No. 34, 57-74.
    </mixed-citation>
   </ref>
   <ref id="scirp.135250-ref9">
    <label>9</label>
    <mixed-citation publication-type="other" xlink:type="simple">
     KDC (2012a). Kilosa District Socio-Economic Profile. Kilosa District Council.
    </mixed-citation>
   </ref>
   <ref id="scirp.135250-ref10">
    <label>10</label>
    <mixed-citation publication-type="other" xlink:type="simple">
     KDC (2012b). Mpango wa Matumizi Bora ya Ardhi ya Kijiji cha Ulaya Mbuyuni. Kilosa District Council. 
    </mixed-citation>
   </ref>
   <ref id="scirp.135250-ref11">
    <label>11</label>
    <mixed-citation publication-type="other" xlink:type="simple">
     Kikula, I. S. (1997). Policy Implications on Environment: The Case of Villagisation in Tanzania. Nordic Africa Institute.
    </mixed-citation>
   </ref>
   <ref id="scirp.135250-ref12">
    <label>12</label>
    <mixed-citation publication-type="other" xlink:type="simple">
     Kilawe, C. J., Maliondo, S. M., Bruun, T. B., Birch-Thomsen, T., Silayo, D. S. A.,&amp;Mertz, O. (2022). The Intensification of Shifting Cultivation in Tanzania: Effects on Soil and Vegetation. In A. A. Rukhsana (Ed.), Agriculture, Environment and Sustainable Development: Experiences and Case Studies (pp. 21-42). Springer International Publishing. &gt;https://doi.org/10.1007/978-3-031-10406-0_3
    </mixed-citation>
   </ref>
   <ref id="scirp.135250-ref13">
    <label>13</label>
    <mixed-citation publication-type="other" xlink:type="simple">
     Kilawe, C. J., Mertz, O., Silayo, D. S. A., Birch-Thomsen, T.,&amp;Maliondo, S. M. (2018). Transformation of Shifting Cultivation: Extent, Driving Forces and Impacts on Livelihoods in Tanzania. Applied Geography, 94, 84-94. &gt;https://doi.org/10.1016/j.apgeog.2018.03.002
    </mixed-citation>
   </ref>
   <ref id="scirp.135250-ref14">
    <label>14</label>
    <mixed-citation publication-type="other" xlink:type="simple">
     Kimaro, D. N., Msanya, B. M., Ashimogo, G., Mbilinyi, B. P.,&amp;Kadigi, R. (2008). Development of Land Suitability Maps with Environmental Overlays for Kilosa District, Tanzania. United Republic of Tanzania.
    </mixed-citation>
   </ref>
   <ref id="scirp.135250-ref15">
    <label>15</label>
    <mixed-citation publication-type="other" xlink:type="simple">
     Kjekshus, H. (2022). Ecology Control and Economic Development in East African History: The Case of Tanganyika 1850-1950. Ohio U Press.
    </mixed-citation>
   </ref>
   <ref id="scirp.135250-ref16">
    <label>16</label>
    <mixed-citation publication-type="other" xlink:type="simple">
     Limbu, F. (1995). Agriculture and Rural Development in Tanzania: A Survey of the 1980-1985 Literature (Issue 7). Economic and Social Research Foundation.
    </mixed-citation>
   </ref>
   <ref id="scirp.135250-ref17">
    <label>17</label>
    <mixed-citation publication-type="other" xlink:type="simple">
     Luoga, E. J., Witkowski, E. T. F.,&amp;Balkwill, K. (2000). Subsistence Use of Wood Products and Shifting Cultivation within a Miombo Woodland of Eastern Tanzania, with Some Notes on Commercial Uses. South African Journal of Botany, 66, 72-85. &gt;https://doi.org/10.1016/s0254-6299(15)31053-x
    </mixed-citation>
   </ref>
   <ref id="scirp.135250-ref18">
    <label>18</label>
    <mixed-citation publication-type="other" xlink:type="simple">
     Malimbwi, R. E.,&amp;Zahabu, E. (2014). NAFORMA Process and Biophysical Results.
    </mixed-citation>
   </ref>
   <ref id="scirp.135250-ref19">
    <label>19</label>
    <mixed-citation publication-type="other" xlink:type="simple">
     Mangora, M. M. (2012). Shifting Cultivation, Wood Use and Deforestation Attributes of Tobacco Farming in Urambo District, Tanzania. Current Research Journal of Social Sciences, 4, 135-140.
    </mixed-citation>
   </ref>
   <ref id="scirp.135250-ref20">
    <label>20</label>
    <mixed-citation publication-type="other" xlink:type="simple">
     Mertz, O.,&amp;Bruun, T. B. (2017). Shifting Cultivation Policies in Southeast Asia: A Need to Work with, Rather than against, Smallholder Farmers. In M. Cairns (Ed.), Shifting Cultivation Policies: Balancing Environmental and Social Sustainability (pp. 27-42). CABI. &gt;https://doi.org/10.1079/9781786391797.0027
    </mixed-citation>
   </ref>
   <ref id="scirp.135250-ref21">
    <label>21</label>
    <mixed-citation publication-type="other" xlink:type="simple">
     Mshale, B., Mshana, D.,&amp;Yared, P. (2012). Improving Agricultural Practices in the Context of REDD Readiness in Lindi Rural District, Tanzania: A Review of Current Agricultural Practices and Recommendations for Project Interventions, Tanzania. Tanzania Forest Conservation Group.
    </mixed-citation>
   </ref>
   <ref id="scirp.135250-ref22">
    <label>22</label>
    <mixed-citation publication-type="other" xlink:type="simple">
     Ngaiza, R. S. (2012). Kilimo Kwanza: The Declaration of Tanzania’s Agricultural Transformation. In FAO Regional Workshop on an Integrated Policy Approach to Commercializing Smallholder Maize Production (p. 63). University of Nairobi.
    </mixed-citation>
   </ref>
   <ref id="scirp.135250-ref23">
    <label>23</label>
    <mixed-citation publication-type="other" xlink:type="simple">
     Norrlund, L.,&amp;Brus, L. (2004). Agricultural Practices in Relation to Soil Properties and Water Supply in a Miombo Forest Village (p. 107). Minor Field Study, Committee of Tropical Ecology, Uppsala University.
    </mixed-citation>
   </ref>
   <ref id="scirp.135250-ref24">
    <label>24</label>
    <mixed-citation publication-type="other" xlink:type="simple">
     Raikes, P. (1986). Eating the Carrot and Wielding the Stick: The Agricultural Sector in Tanzania. In J. Boesen, et al. (Eds.), Tanzania: Crisis and Struggle for Survival (pp. 105-141). Scandinavian Institute of African Studies.
    </mixed-citation>
   </ref>
   <ref id="scirp.135250-ref25">
    <label>25</label>
    <mixed-citation publication-type="other" xlink:type="simple">
     Reed, J. S. (1979). Government Publications Relating to Tanganyika, 1919-1961. EP Microform Limited.
    </mixed-citation>
   </ref>
   <ref id="scirp.135250-ref26">
    <label>26</label>
    <mixed-citation publication-type="other" xlink:type="simple">
     Stromgaard, P. (1989). Adaptive Strategies in the Breakdown of Shifting Cultivation: The Case of Mambwe, Lamha, and Lala of Northern Zambia. Human Ecology, 17, 427-444. &gt;https://doi.org/10.1007/bf00889499
    </mixed-citation>
   </ref>
   <ref id="scirp.135250-ref27">
    <label>27</label>
    <mixed-citation publication-type="other" xlink:type="simple">
     Sundet, G. (1997). The Politics of Land in Tanzania. University of Oxford.
    </mixed-citation>
   </ref>
   <ref id="scirp.135250-ref28">
    <label>28</label>
    <mixed-citation publication-type="other" xlink:type="simple">
     Sunseri, T. (2003). Reinterpreting a Colonial Rebellion: Forestry and Social Control in German East Africa, 1874-1915. Environmental History, 8, 430-451. &gt;https://doi.org/10.2307/3986203
    </mixed-citation>
   </ref>
   <ref id="scirp.135250-ref29">
    <label>29</label>
    <mixed-citation publication-type="other" xlink:type="simple">
     United Republic of Tanzania (1995). National Land Policy. Government Printer.
    </mixed-citation>
   </ref>
   <ref id="scirp.135250-ref30">
    <label>30</label>
    <mixed-citation publication-type="other" xlink:type="simple">
     URT (1998). National Forest Policy. Government Printers.
    </mixed-citation>
   </ref>
   <ref id="scirp.135250-ref31">
    <label>31</label>
    <mixed-citation publication-type="other" xlink:type="simple">
     URT (1999a). National Land Act (and Regulations) No. 4 of 1999. Ministry of Lands and Human Settlements Development.
    </mixed-citation>
   </ref>
   <ref id="scirp.135250-ref32">
    <label>32</label>
    <mixed-citation publication-type="other" xlink:type="simple">
     URT (1999b). Village Land Act (and Regulations) No. 5 of 1999. Ministry of Lands and Human Settlements Development.
    </mixed-citation>
   </ref>
   <ref id="scirp.135250-ref33">
    <label>33</label>
    <mixed-citation publication-type="other" xlink:type="simple">
     URT (2002). Forest Act No. 14 of 2002. Tanzania Government Printers.
    </mixed-citation>
   </ref>
   <ref id="scirp.135250-ref34">
    <label>34</label>
    <mixed-citation publication-type="other" xlink:type="simple">
     URT (2007). Land Use Planning Act No. 6 of 2007. Ministry of Lands and Human Settlements Development.
    </mixed-citation>
   </ref>
   <ref id="scirp.135250-ref35">
    <label>35</label>
    <mixed-citation publication-type="other" xlink:type="simple">
     van Vliet, N., Mertz, O., Heinimann, A., Langanke, T., Pascual, U., Schmook, B. et al. (2012). Trends, Drivers and Impacts of Changes in Swidden Cultivation in Tropical Forest-Agriculture Frontiers: A Global Assessment. Global Environmental Change, 22, 418-429. &gt;https://doi.org/10.1016/j.gloenvcha.2011.10.009
    </mixed-citation>
   </ref>
   <ref id="scirp.135250-ref36">
    <label>36</label>
    <mixed-citation publication-type="other" xlink:type="simple">
     Zahabu, E., Eid, T., Kajembe, G., Mbwambo, L., Mongo, C., Sangeda, A., Malimbwi, R., Katani, J., Kashaigili, J.,&amp;Luoga, E. (2009). Forestland Tenure Systems in Tanzania: An Overview of Policy Changes in Relation to Forest Management. Department of Ecology and Natural Resource Management Norwegian University of Life Sciences.
    </mixed-citation>
   </ref>
  </ref-list>
 </back>
</article>