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Rural Development Policies and Sustainable Land Use in the ...

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26 CHAPTER 3<br />

decide <strong>the</strong> number of clusters to consider.<br />

However, hierarchical cluster<strong>in</strong>g can give<br />

rise to misclassification of observations at<br />

<strong>the</strong> boundaries between clusters (Wishart<br />

1999). Us<strong>in</strong>g k-means analysis corrects for<br />

this problem. The k-means cluster analysis<br />

is an iterative process that allows for start<strong>in</strong>g<br />

po<strong>in</strong>ts <strong>and</strong> <strong>the</strong>ir means to be set at <strong>the</strong><br />

beg<strong>in</strong>n<strong>in</strong>g of <strong>the</strong> process. We used <strong>the</strong> number<br />

of clusters <strong>and</strong> <strong>the</strong> means of each factor<br />

<strong>in</strong> <strong>the</strong>se clusters as start<strong>in</strong>g centers for <strong>the</strong><br />

k-means analysis. Observations were <strong>the</strong>n<br />

assigned to groups that <strong>the</strong>y are “closest” to.<br />

Based on <strong>the</strong> addition of each subsequent<br />

observation, cluster centers were recalculated<br />

<strong>and</strong> progressively calibrated through<br />

successive iterations. This process was repeated<br />

until all observations were assigned<br />

across groups.<br />

Empirical Model<br />

<strong>Rural</strong> people <strong>and</strong> policymakers are most<br />

<strong>in</strong>terested <strong>in</strong> what drives outcome variables<br />

such as agricultural production, household<br />

<strong>in</strong>come, <strong>and</strong> resource conditions. Once we<br />

have clustered <strong>the</strong> household sample <strong>in</strong>to<br />

livelihood strategy groups, <strong>the</strong> household’s<br />

livelihood choice can be expla<strong>in</strong>ed based on<br />

a set of predeterm<strong>in</strong>ed asset-based variables<br />

that <strong>in</strong>clude natural <strong>and</strong> human capital <strong>and</strong><br />

geographic determ<strong>in</strong>ants of comparative<br />

advantage. Livelihood strategies are an important<br />

part of a wider set of explanatory<br />

asset-based variables that determ<strong>in</strong>es household<br />

<strong>in</strong>come <strong>and</strong> besides exogenous assetbased<br />

variables also <strong>in</strong>clude physical, f<strong>in</strong>ancial,<br />

<strong>and</strong> social capital. In this way a<br />

household’s asset hold<strong>in</strong>gs has both a direct<br />

<strong>and</strong> <strong>in</strong>direct (via <strong>the</strong>ir impact on <strong>the</strong> livelihood<br />

strategy choice) <strong>in</strong>fluence on <strong>in</strong>come.<br />

Of <strong>the</strong> wider set of asset-based variables, we<br />

consider social capital assets (measured by<br />

<strong>the</strong> household’s participation <strong>in</strong> programs<br />

<strong>and</strong> organizations) as endogenous <strong>and</strong> <strong>in</strong>fluenced<br />

by <strong>the</strong> same factors determ<strong>in</strong><strong>in</strong>g <strong>the</strong><br />

household’s livelihood strategy. Resource<br />

conditions are l<strong>in</strong>ked to l<strong>and</strong> management<br />

decisions which are <strong>in</strong>fluenced by <strong>the</strong> same<br />

set of variables as household <strong>in</strong>come plus<br />

o<strong>the</strong>r variables that reflect field-specific<br />

characteristics. F<strong>in</strong>ally, agricultural production<br />

can be expla<strong>in</strong>ed by <strong>the</strong> same set of<br />

variables as l<strong>and</strong> management decisions,<br />

<strong>the</strong> use of labor <strong>and</strong> external <strong>in</strong>puts, <strong>and</strong> l<strong>and</strong><br />

management decisions <strong>the</strong>mselves. Labor<br />

<strong>and</strong> external <strong>in</strong>put use, <strong>in</strong> turn, are determ<strong>in</strong>ed<br />

by a set of factors similar to that for<br />

l<strong>and</strong> management decisions.<br />

Based on <strong>the</strong> preced<strong>in</strong>g discussion, <strong>the</strong><br />

variables of <strong>in</strong>terest for our econometric<br />

model are agricultural production; use of<br />

labor, external <strong>in</strong>puts, <strong>and</strong> l<strong>and</strong> management<br />

practices; choice of livelihood strategy <strong>and</strong><br />

participation <strong>in</strong> programs <strong>and</strong> organizations;<br />

<strong>and</strong> household <strong>in</strong>come per capita. In <strong>the</strong><br />

follow<strong>in</strong>g subsections we summarize <strong>the</strong> empirical<br />

model for each of <strong>the</strong>se variables.<br />

Value of Crop Production<br />

For agricultural production, we focus on <strong>the</strong><br />

value of crop production, <strong>in</strong> order to avoid<br />

estimation of large numbers of <strong>in</strong>dividual<br />

production functions for s<strong>in</strong>gle crops <strong>in</strong> different<br />

seasons. We assume that <strong>the</strong> value of<br />

production of crop type i (i <strong>in</strong>dexes annuals<br />

or perennials) by household h on plot p <strong>in</strong><br />

season t (y i<br />

hpt<br />

) is determ<strong>in</strong>ed by <strong>the</strong> labor<br />

<strong>in</strong>puts applied to <strong>the</strong> plot (family labor,<br />

hired wage labor, piece labor) (L hpt<br />

); <strong>the</strong><br />

l<strong>and</strong> management practices used (no burn<strong>in</strong>g,<br />

m<strong>in</strong>imum or zero tillage, <strong>in</strong>corporation of<br />

crop residues, use of mulch, use of manure)<br />

(LM hpt<br />

); <strong>the</strong> external <strong>in</strong>puts applied to <strong>the</strong><br />

plot (<strong>in</strong>organic fertilizer, herbicide, <strong>in</strong>secticide,<br />

o<strong>the</strong>r purchased <strong>in</strong>puts) (IN hpt<br />

); <strong>the</strong><br />

“natural capital” of <strong>the</strong> plot (NC hpt<br />

) (biophysical<br />

characteristics such as size, altitude,<br />

slope, position on <strong>the</strong> slope, <strong>and</strong> <strong>in</strong>herent soil<br />

fertility, <strong>and</strong> presence of l<strong>and</strong> <strong>in</strong>vestments<br />

such as stone walls, live barriers, <strong>and</strong> planted<br />

trees at <strong>the</strong> beg<strong>in</strong>n<strong>in</strong>g of <strong>the</strong> period); 26 <strong>the</strong><br />

26<br />

NC hpt<br />

<strong>in</strong>cludes ra<strong>in</strong>fall s<strong>in</strong>ce we used a GIS to “assign” ra<strong>in</strong>fall data to each plot.

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