| Article of the Month - 
	  January 2008 | 
  	    
      Developing Cost-effective and Resilient Land Administration Systems in 
	  Latin America
	
      Grenville Barnes; USA
	
       This article 
	  in .pdf-format.
      This article 
	  in .pdf-format.
    SUMMARY 
	In this paper I briefly review the wealth of experience in Latin America 
	with initiatives to strengthen and modernize land administration systems. 
	The review shows that there is more experience with land administration 
	projects in this region than in any other. I go on to focus on the question 
	of costs associated with formalizing property in an attempt to find an 
	effective means of comparing costs across countries. I approach this by 
	looking at different ‘levels’ – starting with global budget figures, then 
	narrowing down to specific components and finally by examining the cost of 
	individual tasks required to formalize a parcel. A comparative study of 
	costs in 4 different regions of the world is described together with 
	preliminary conclusions at the global level. The issue of property 
	‘deformalization’ is also discussed with respect to transaction costs. 
	Recognizing that land administration systems, and the economic, social 
	and natural environments within which they operate, are continually 
	changing, I introduce Resilience as an appropriate analytical framework 
	through which to examine changing systems.
	Resilience has evolved as a more nuanced framework for understanding the 
	sustainability of socio-ecological systems. Unlike previous approaches, it 
	accepts that a system will always be subject to disturbances, whether they 
	are due to climate (hurricanes), policy and political administration 
	changes, or demographic shifts due to urbanization or migrant labor markets.
	
	
	RESUMEN
	
	Esta exposición revisa la gran experiencia en América Latina 
	sobre las iniciativas para fortalecer y modernizar los sistemas de 
	administración de tierras. El repaso indica que hay mas experiencia en este 
	region con pryetos de adminsitracion de tierras que en cualquier otra region 
	del mundo. El primer parte enfoque en la cuestion de costos vinculado a la 
	formalización de la propiedad con el motivo de identificar medios aptos para 
	comparar costos entre diferentes paises. Esta analisis incorpora el estudio 
	de costos en diferentes niveles – empezando con costos presupuestos 
	globales, despues enfocando el nivel de componentes individuales y 
	finalmente se examina los costos para diferentes actividades en el proceso 
	de formaliza una propiedad. Se discutir un estudio de costos en cuatro 
	diferentes regiones del mundo y ciertos conclusiones preliminares al nivel 
	global. Esta discusión incluya tambien la cuestion de ‘deformalización’ de 
	propiedad con respeto a los costos transaccionales.
	
	Reconozco que sistemas de administración de tierras, y el 
	ambiente económico, social e ecológico en que el sistema opera, siempre esta 
	cambiando, se introduzca el Resiliencia como una rama analítica apropiada 
	para analizar los dinámicos del sistema.
	
	Finalmente, examinaré los sistemas de administración de 
	tierras a través del lente de ‘resilencia.’ La resilencia se ha desarrollado 
	como un marco matiz para examinar la sostenabilidad de sistemas 
	socio-ecologico. A diferencia de previos acercamientos, éste acepta que el 
	sistema siempre esté sujeto a disturbios, sea a consecuencia del clima 
	(huracanes), cambios políticos o administrativos, o a desplazamientos 
	demográficos a causa de la urbanización o migración de mercados laborales.
	
	1. INTRODUCTION 
	It was appropriate to hold the recent regional FIG conference in Costa 
	Rica as this country was one of the first countries in the region to 
	implement what today would be regarded as a land administration project. The 
	1964 USAID-funded “cadastral survey project” was the pioneer land project in 
	Central America (Goldstein 1974). The focus of that project was to improve 
	the property tax system and complete a topographical mapping project which 
	would provide information for tax, land planning and development purposes. 
	Similar projects followed soon afterwards in Panama, Nicaragua and 
	Guatemala, all focused strongly on property taxes, with additional 
	components addressing natural resource management and land titling in some 
	cases. 
	During the 1980s the World Bank began to fund several large land projects 
	in Latin America and elsewhere. The first two to be completed were the 
	projects in Thailand and NE Brazil (Holstein 1993). The Thailand “land 
	titling project,” the ‘mother’ of all land titling projects, started in 
	1985. This has been a significant project for two reasons. Firstly, it is 
	regarded as a highly successful project. Secondly, it has been the proving 
	grounds for the evolutionary theory of land rights (ETLR) which served as 
	the underlying rationale for many of the subsequent land projects that 
	followed in the next two decades. Many of the assertions or hypotheses 
	internal to the ETLR have been empirically proven using the experience of 
	Thailand (Feder et al 1988). Data was gathered and analyzed to demonstrate 
	the correlation between titling and access to credit, reduction in property 
	disputes, facilitation of the land market, and increasing land values (Feder 
	and Nishio 1996). Based partly on these positive outcomes in Thailand, land 
	administration projects proliferated throughout the developing world. 
	Within Latin American the North East Brazil “national land administration 
	project” was the forerunner of a series of land administration projects in 
	the region (World Bank 1985). USAID continued to fund land titling projects 
	throughout the 1980s, including the “land titling projects” in Honduras and 
	Ecuador (USAID 1985). However, the most successful of the USAID-funded 
	projects may have been the “Land Titling and Registration Project” in St. 
	Lucia (USAID 1983). The island-wide land adjudication process was completed 
	within the originally scheduled time – this by itself may be a unique 
	achievement amongst land administration projects which invariably stretch 
	beyond the time frame set out in the project design. 
	The World Bank has funded land administration projects throughout Latin 
	America, and even by 1998 a study of World Bank projects revealed that there 
	were “..115 projects with land-related activities in the Bank’s 
	portfolio…[and] ..of those, about 40% are in Latin America.” (World Bank 
	1998, p. 10). Subsequent land administration projects ensued in Bolivia 
	(1995, 2001), Brazil (1995), Guatemala (1996, 1997), Honduras (2000), Panama 
	(2000), Nicaragua (2002), Honduras (2003), and El Salvador (2005). 
	The Inter-American Development Bank has also played a lead role in 
	funding land administration projects in Latin America and the Caribbean 
	especially over the past decade – including Trinidad and Tobago (1995), 
	Nicaragua (1995), Dominican Republic (1997), Belize (1997), Colombia (1997), 
	Honduras (1998), Jamaica (1999), Costa Rica (2000), Ecuador (2001), Panama 
	(2002), Brazil (2002), Mexico (2003), Bolivia (2003), Paraguay (2003), and 
	the Bahamas (2004). 
	While this is not a complete list of projects it does illustrate the huge 
	amount of investment that has gone into land administration and property 
	formalization and therefore the wealth of experience in the region. In the 
	following section of this paper I bring this experience to bear on certain 
	key land administration issues, namely the question of costs. 
	2. COMPARATIVE ANALYSIS OF COSTS 
	While significant resources have been invested by the donor community in 
	modernizing land administration infrastructure around the globe, there has 
	been little systematic discussion and documentation of actual costs. Better 
	understanding of the underlying issues and the trade-offs involved in 
	choosing among different technical, legal and institutional options of 
	providing land administration services is needed. Even though the World 
	Bank, IDB and other donors have long supported titling interventions all 
	over the world, surprisingly little is known about the actual costs of such 
	interventions, both in terms of project implementation and comparative 
	transaction costs once the new systems are in place. Until recently, little 
	effort has been made to disaggregate costs into the specific activities 
	required to formalize a piece of land. 
	 
	In reviewing previous studies that dealt with costs, there are several 
	worth mentioning. In 1985 Janice Bernstein at the World Bank documented a 
	study she carried out entitled “The costs of land information systems.” 
	(Bernstein 1985) She compiled information on the topic through “a review of 
	the literature and illustrative programs as well as discussion with experts 
	in the field…” (p. 5) She concluded early on that “..there is a great need 
	for coordinated research among international organizations and training 
	institutions focusing on the economics of land information..” (p. 11) The 
	report focused largely on the potential for lowering the cost of cadastral 
	surveys through inertial surveying and GPS, which were just becoming 
	operational at that time. It also focused on methods for estimating the cost 
	of photogrammetric mapping. A fully operational GPS/GNSS system, the higher 
	precision of today’s satellite imagery, and airborne GPS have essentially 
	reduced the value of this information to one of historical interest. The 
	study also contributes little towards the development of a comparative 
	methodology.
	Two years later in 1987 a symposium entitled “The Economics of Land 
	Information” was held in Baltimore, MD, under the auspices of the Institute 
	of Land Information (ILI 1987). This issue was topical in the US at that 
	time as GIS was becoming mainstream and county offices were in the process 
	of digitizing their land information. Approaches discussed at the ILI and 
	other forums at that time included: (i) an avoided cost approach, where 
	benefits are construed as the avoidance of downstream costs by making 
	upstream (often public) investments in, for example, geodetic infrastructure1 
	– creating the information now means that it does not have to be repeated at 
	a later time; (ii) a ‘use and value’ approach whereby benefits are gauged 
	relative to frequency of use – information that is used more often has more 
	value even though it may have cost the same to produce. The ‘avoided cost’ 
	approach may have some value, but it focuses more on future costs than more 
	defensible present or past costs. However, both approaches are not that 
	useful for developing a comparative methodology as they focus more on 
	benefits than costs. 
	Other cross-country studies include work done by Dale and McLaughlin 
	(1988) and Holstein (1993). Their breakdown of costs by activity is compared 
	with that given by Bernstein (1985) in Table I below.
	TABLE I. Percentage Distribution of Costs by 
	Activity
	
		
			| 
			Source | 
			Mapping | 
			Adjudication | 
			Surveying | 
			Registration | 
			Institutional 
			Strengthening | 
		
			| 
			Bernstein2 | 
			38% | 
			29%3 | 
			  | 
			6%4 | 
			13% | 
		
			| 
			Dale/McLaughlin | 
			20-25 % | 
			30-50 % | 
			20-25% | 
			10-15% | 
		
			| 
			Holstein  | 
			24% | 
			18% | 
			22% | 
			23% | 
			13% | 
	
	
		
			1 See Epstein 
			and Duchesneau 1984
			2 
			Based on the NE Brazil Project Costs. Other components included 
			Support for Land Restructuring” (9%), Project Administration (4%) 
			and Studies (1%)
			3 Land Tenure Identification
			4
			Cadastre Implementation and Titling
 
	 
	None of these three studies provide a robust comparative analysis 
	methodology, although they do suggest focusing on activities such as 
	mapping, adjudication, surveying, etc. Even this can be problematic as 
	surveying may sometimes be included as a sub-component of adjudication (Dale 
	and McLaughlin 1990). 
	Gross unit costs are typically used to compare costs across different 
	projects, without taking into account the significantly different contexts 
	and approaches. As a result, cadastral and land registration interventions 
	are often viewed as expensive activities that do not generate sufficient 
	benefits to justify their costs. Furthermore, no systematic template exists 
	for collecting data across different countries. The cost issue came to a 
	head in a 2001 e-conference on “Lessons Learned in Land Administration” 
	organized by the World Bank (Deininger 2003; Barnes 2003). One participant 
	shared information on the Peruvian Titling Project (PETT) which had reduced 
	the cost of formalizing a parcel to approximately $47 per parcel. In 
	response to this, another participant countered that in Eastern Europe they 
	were titling at the cost of $1.05 per parcel! Either these two participants 
	were talking about two completely different processes and products or else 
	the contextual setting of these two cases was incomparably different. 
	Clearly there was a need to ‘unpack’ these numbers and develop a framework 
	for comparing the same process or product. 
	Following this conference we developed a template of questions and tables 
	that could be administered at the country level. We approached this by 
	identifying costs at three different levels – starting from global project 
	figures and then considering costs at the level of project components, and 
	finally examining specific costs entailed in converting a parcel of land 
	into a formal registered property. We also recognized the need to 
	contextualize these studies so that the cost figures could be considered 
	against the specific context within which the project was being implemented. 
	Subsequently, the template was expanded to include an analysis of the 
	effectiveness of the land administration system. This ‘template’ was then 
	applied in seventeen countries in four different regions - Latin America and 
	the Caribbean (El Salvador, Peru, Bolivia, Trinidad and Tobago), E. Europe 
	and Central Asia (Armenia, Kyrgyzstan, Moldova, Latvia), Asia (Indonesia, 
	Karnataka, Philippines, Thailand) and Africa (Ghana, Mozambique, Namibia, 
	South Africa, Uganda). Subsequently, four regional reports were prepared 
	that summarized the country-level reports (Barnes 2002; Adlington 2002; Land 
	Equity 2003; Augustinus 2003). Finally a global report was prepared 
	comparing all countries across the four regions (Land Equity 2007).
	
	Instead of drawing on the general data for the global comparison, I have 
	widened the LAC scope by considering 11 projects within the region. The data 
	are drawn from the many project documents I have in my own library as well 
	as others which are listed on the LandNet Americas portal.5
	
	 TABLE 
	II. 
	Global Comparison of per parcel Costs - Total Project Costs/Total Parcels 
	6 
	
		
			
				
					| 
					Project | 
					Total Budget 
					US$M | 
					# Parcels | 
					Dates | 
					$/parcel | 
					Area (MHa) | 
					$/ha | 
			
			
				| 
				Peru (PETT1) | 
				36.5 | 
				1,000,000 | 
				1997-2002 | 
				37 | 
				na | 
				na | 
			
				| 
				El Salvador
				 | 
				70 | 
				1,700,000 | 
				1996-2005 | 
				41 | 
				1.9 | 
				37 | 
			
				| 
				Peru (PETT2) | 
				46.7 | 
				170,000 | 
				2003-2007 | 
				62 | 
				3.6 | 
				13 | 
			
				| 
				Costa Rica (IDB) | 
				92 | 
				520,000 | 
				2002-2007 | 
				177 | 
				na | 
				na | 
			
				| 
				Bolivia (PNAT) | 
				28 | 
				10,000 | 
				1995-2003 | 
				2800 | 
				3.7 | 
				8 | 
			
				| 
				Bolivia (St. 
				Cruz) | 
				15 | 
				140,000 | 
				2006-2010 | 
				107 | 
				na | 
				na | 
			
				| 
				Ecuador (PRAT) | 
				16 | 
				135,000 | 
				2003-2007 | 
				119 | 
				0.6 | 
				27 | 
			
				| 
				Nicaragua 
				(PRODEP) | 
				2.4 | 
				90,000 | 
				2003-2010 | 
				27 | 
				1.4 | 
				2 | 
			
				| 
				Belize (LMP) | 
				8.9 | 
				40,000 | 
				2003-2006 | 
				223 | 
				na | 
				na | 
			
				| 
				Panama (LARP-IDB) | 
				72.3 | 
				120,000 | 
				2003-2008 | 
				603 | 
				0.75 | 
				96 | 
			
				| 
				Panama (ProNAT) | 
				47.9 | 
				80,000 | 
				2001-2007 | 
				599 | 
				1.1 | 
				44 | 
			
				| 
				Average | 
				40 | 
				420,000 | 
				  | 
				436 | 
				1.9 | 
				21 | 
			
				| 
				Average (without 
				PNAT) | 
				41 | 
				  | 
				  | 
				200 | 
				  | 
				  |   | 
		
	 
	
	
	This kind of comparison is of minimal use partly because 
	it assumes that the total budget can be associated with the number of 
	parcels that are either titled or regularized in some way. Costs associated 
	with legal reform, institutional strengthening, equipment purchases, etc. 
	are examples of costs that have no relation to parcels, but are still 
	included in the comparative figures given in Table I. Although the parcel is 
	the unit of choice when assessing the extent and cost of surveying and 
	regularization, its cross-scalar nature produces unwelcome complexities. A 
	‘parcel’ may include any of the following tenure units:
	
		- 
		
		small urban lots (e.g. 20m x 30m) 
- 
		
		peri-urban lots 
- 
		
		small agricultural parcels (minifundias) 
- 
		
		medium rural parcels 
- 
		
		large rural parcels 
- 
		
		large communally-held parcels (e.g. indigenous 
		communities) 
	The scale of a parcel may therefore vary from a small 
	urban lot to a communal property that may approximate the size of a 
	municipality. Additionally, at the project design stage the number of 
	parcels in a jurisdiction or area is often the weakest data available. The 
	whole motivation for adjudication and titling stems from the fact that there 
	is no reliable formal parcel information in the registry or cadastre. 
	Therefore parcel information may be available at the end of the project, but 
	during design it can only be inferred through estimating average parcel 
	sizes or consulting census data. 
	
	Costs are also estimated on an area (per hectare) basis? 
	Using the project documents as a source again, those costs that are 
	available are shown in Table I. Four out of the eleven projects in Table I 
	do not list area to be titled or regularized in the project document. In the 
	remainder, the per hectare costs range from $2/ha in Nicaragua to $96/ha in 
	Panama with an average of $21/ha. This approach to unit costs suffers from 
	the same problem as mentioned above – it assumes that the cost per unit area 
	is uniform, ignoring the fact that the multiple scales of parcels contradict 
	this especially in the fieldwork component. Those projects that contain 
	several large parcels, such as indigenous communities, skew the cost per 
	hectare numbers (such as in Nicaragua). It is therefore necessary to look 
	deeper than these global figures if we are to effectively compare these 
	projects. It may be more productive to consider the costs of an average size 
	parcel.
	
	At a more specific level we can examine costs by focusing 
	on procurement type. Once again, this data is easily available in project 
	documents, and the results for a small sample of countries is given in Table 
	III below
	TABLE III. Breakdown of Budgeted Costs by Procurement 
	for Five Countries
		
		
		 
	
	
	FIGURE 1. 
	 Percentage of Budget by Procurement Method
	
	Figure 1 shows that two crucial elements underlying the 
	success of land administration initiatives – training and 
	information/communication – rank last in terms of “procurement type.” 
	However, it is risky to draw any conclusions from these data partly because 
	several categories in Figure 1 overlap. Training, for example, may be 
	treated under a separate category in some projects, while in others it will 
	be included under institutional strengthening. Adding to the complexity of 
	comparative costs are differences in technologies, variations in 
	implementation strategies (in-country or through international bid), and 
	differences in the quality of existing cadastral and registration data, 
	access and boundary complexity. 
	
	Finally, the third level that we examined in the 
	comparative cost study was the cost for each task required to convert a 
	parcel from informality into a fully registered property (see Table IV).
	
	TABLE IV Breakdown of Costs to Formalize a Parcel (Land Equity 2007, p. 
	94)
	
	The number of gaps in the above table shows either that 
	countries are using different approaches that do not include all of the 19 
	tasks listed in Table IV above and/or costs are not always reported at this 
	fine a resolution. It is also important to distinguish between urban and 
	rural as the Peruvian case indicates rural parcels can cost almost five 
	times as much as urban parcels. 
	
	Looking through even a finer lens at a single cost 
	sub-component – cadastral survey (#7 in Table IV) – reveals the extent to 
	which cost can vary at this micro level. Cadastral survey costs for a single 
	parcel can vary considerably depending largely on four factors: the quality 
	and scope of the recorded cadastral information, the nature of the terrain, 
	land value, cadastral evidence (e.g. original monuments/markers, fences) 
	encountered in the field. In Figure 2 below I have related how these factors 
	combine to either increase or decrease the survey costs.
	
	FIGURE 2. Four Factors affecting 
	Cadastral Survey Costs
	If land 
	adjudication (saneamiento) is to be done systematically (barrido) across an 
	area then the expectation is that this will generate economies of scale, 
	thereby dropping the per parcel costs. Furthermore, additional efficiencies 
	can be gained by using methodologies based on GPS which, unlike conventional 
	approaches, does not require line of sight between all surveyed points. To 
	what extent do these two factors – economies of scale and the use of GPS – 
	reduce the survey costs. We were faced with this question in designing the 
	IDB land administration project in Belize in the mid-1990s. At that time 
	private surveyors estimated their survey fees on the basis of this simple 
	formula: US$200 √ area of parcel in acres. In other words, the survey fees 
	for a parcel of 20 acres would be approximately $900. 
	
	Drawing on the experience of the South African cadastral surveying system, 
	which for more than 60 years had a tariff of fees that incorporated a factor 
	to account for increasing economies of scale as more parcels were surveyed, 
	the following figures can be computed in the context of Belize.
	
	TABLE V. Cadastral Survey Fee Structure 
	accounting for Economies of Scale
	
		
			
				
					| 
					Number of 
					Parcels | 
					Scale Factor | 
					Factor applied 
					to Belize Survey Costs7
					 | 
			
			
				| 
				1 | 
				1 | 
				$900 | 
			
				| 
				2 | 
				0.7 | 
				630 | 
			
				| 
				3 | 
				0.6 | 
				540 | 
			
				| 
				4 | 
				0.5 | 
				450 | 
			
				| 
				5 | 
				0.4 | 
				360 | 
			
				| 
				10 | 
				0.4 | 
				360 | 
			
				| 
				20 | 
				0.3 | 
				270 | 
			
				| 
				100 | 
				0.3 | 
				270 | 
			
				| 
				200 | 
				0.2 | 
				180 | 
			
				| 
				400 | 
				0.2 | 
				180 | 
			
				| 
				1000 | 
				0.2 | 
				180 | 
		
	 
	
		
		
			
			
			7
			Assuming an average cost of 
			US$900 for an individual 20 acre parcel
			The scaling factors therefore bring the per parcel costs down to 
			$180 per parcel assuming that a surveyor is contracted to survey at 
			least 200 parcels. In addition to these economies of scale, 
			efficiencies through the use of GPS were estimated to further reduce 
			the measurement and mapping time by a factor of four. We therefore 
			concluded that the combination of scale economies and technological 
			efficiency could reduce the per parcel costs down to as little as 
			$90 per parcel (Barnes 1995). 
			 
			Given the large number of variables in just the cadastral 
			surveying, adjudication, land titling and land registration costs 
			for formalizing a parcel of land, it is not surprising that we are 
			faced with an “apples and oranges” type of comparison of costs. I 
			have just considered initial registration costs in this section, but 
			there are other costs – especially those relating to subsequent 
			transactions – that may be even more crucial to the success and 
			sustainability of a land administration system.
			3. TRANSACTION COSTS
			Informality results when landholders perceive that the costs and 
			benefits of the formal system do not match those of the informal 
			system. In other words, landholders who believe that the costs of 
			formalizing transactions outweigh the perceived benefits that flow 
			from such formalization will conduct their transactions outside the 
			formal system. This is particularly true when informal transaction 
			costs are further reduced because the parties to the transaction are 
			members of the same family. 
			 
			Douglass North’s work on transaction costs, property rights and 
			institutions has perhaps been the most influential work in terms of 
			providing a comprehensive approach towards analyzing this area. 
			North distinguishes between transformation and transaction costs:
			The total costs of production consist of the resource inputs of 
			land, labor and capital involved both in transforming the physical 
			attributes of a good … and in transacting – defining, protecting and 
			enforcing the property rights to goods.. (North 1990, p. 28)
			 
			When entering into a transaction, such as purchasing a parcel of 
			land, costs are incurred in the search for information about the 
			land (quality, value, history, etc.) and the seller’s valid claim to 
			the land (title, transaction history, third-party claims, etc.). As 
			North explains:
			The costliness of information is the key to the costs of 
			transacting, which consists of the costs of measuring the valuable 
			attributes of what is being exchanged and the costs of protecting 
			rights and policing and enforcing agreements. (p.27)
			I
			 believe that high transaction costs following subsidized titling 
			efforts are causing substantial ‘de-formalization’ of titled 
			property. Based on research in St. Lucia and key informant 
			interviews in the field in numerous countries, we have observed a 
			tendency for titleholders not to register transactions after they 
			have received title. Our research in St. Lucia revealed that 
			approximately 28% of the register was out of date some two decades 
			after an island-wide titling project, mainly due to informal 
			generational transfers within families (Griffith-Charles 2004; 
			Barnes and Griffith-Charles 2006). We believe that the situation in 
			many other countries will be substantially worse than this.
			 
			Comparing the de facto and the de jure situation of land parcels 
			is also problematic. Collecting de jure data may simply entail a 
			visit to the registry to extract data on the formal situation. 
			However, even though most registries in Latin America are ‘registros 
			publicos’ they most often restrict public access. Access to property 
			registries may be limited only to those individuals with a valid 
			interest in a transaction. There is often a fear that documents will 
			be defiled unless they are handled by competent public officials. On 
			the other hand, if one does gain entry into the registry large 
			amounts of data on transactions can be obtained in a relatively 
			short period of time. Not so with de facto data. This requires more 
			research and a well-designed sampling strategy that allows 
			researchers to not only select a representative sample of the total 
			parcel population but also to be able to link that parcel with the 
			relevant information in the registry and/or cadastre. Without 
			reliable geographic information for the registered parcels this can 
			become extremely challenging.
			 
			We can also conclude that institutional differences amongst 
			countries, including rapid changes in political administration, 
			levels of decentralization, etc all need to be contemplated when 
			examining costs. The recent focus on land for the poor also raises 
			the issue of affordability. We currently do not have a good idea of 
			what poorer landholders can afford to pay for formalizing subsequent 
			transactions. Finally, in order to come to grips with land 
			administration dynamics we need to understand the processes of 
			change that are occurring in the surrounding environment, in the 
			landholding population and in the infrastructure and services that 
			meld together the social-ecological system. Resilience has emerged 
			as a useful approach towards understanding system change. 
			4. A RESILIENCE APPROACH 
			Phenomena such as global warming, increases in natural disasters 
			such as hurricanes and unpredictable market dynamics remind us daily 
			that our planet is a highly complex system. Through drawing 
			disciplinary boundaries – defining social sciences, natural 
			sciences, etc. - we have in effect parsed our world into more 
			manageable pieces. However, in the process we have disassociated 
			social systems from ecological systems and made it more difficult to 
			understand complex human-environmental interactions. 
			Over the past decade ecologists and others have defined a 
			resilience approach to study complex dynamic human-environment 
			interactions (see, for example, Gunderson and Holling 2002; 
			Carpenter et al 2004; Anderies et al 2006; Walker and Salt 2006). 
			Resilience “stresses the importance of assuming change and 
			explaining stability, instead of assuming stability and explaining 
			change.” (Folke et al 2003, p. 352) A resilience approach recognizes 
			that there is no single stable state in a social-ecological system 
			(SES), but that the system is exposed to different ‘shocks’ that 
			challenge its fundamental identity and make it dynamic. A resilient 
			system is able to absorb shocks and adapt without changing its 
			fundamental structure and function (Gunderson and Holling 2002). 
			Shocks may be stochastic (e.g. tsunami, land policy reform, major 
			macro-economic changes), cyclical (flooding), or occur at different 
			temporal scales – decadal (e.g. drought), annual (e.g. hurricanes, 
			labor migration) or at smaller time scales. 
			Through funding from the National Science Foundation, we are 
			investigating the resilience of social-ecological systems in the SW 
			Amazon. We focus on connectivity as the primary agent of change, 
			specifically the trans-oceanic highway that is being paved and will 
			eventually link the Pacific and Atlantic Oceans. The highway will 
			radically change the connectivity in the region of our research, 
			which includes the states/departments of Made de Dios (Peru), Acre 
			(Brazil), and Pando (Bolivia) and is commonly known as the MAP 
			region. We hypothesize that resilience will increase as connectivity 
			improves; however, at some level of connectivity it will begin to 
			become less resilient due to its over-connectedness and consequent 
			over-dependence on external factors. In short, a graph of resilience 
			(Y axis) and Connectivity (X axis) will reveal an inverted U shape.
			
			One of the many challenges of operationalizing resilience 
			analyses is defining what constitutes the ‘fundamental structure and 
			function’ of a system. In our own research at the University of 
			Florida we have attempted to do this by examining social, ecological 
			and social-ecological measures of this identity. Within the context 
			of land tenure this may be construed as the land administration 
			framework and the decisionmaking with respect to land and its 
			associated resources. What does it mean to focus on change within a 
			land administration system? At a basic level, cadastral and 
			registration systems are constantly changing as the land market 
			operates and property is sold and new parcels are created through 
			subdivision. All successful land administration systems should be 
			designed to accommodate this constant change, otherwise they will 
			quickly become out of date. This suggests that the focus in land 
			administration should be on those parcels that are undergoing the 
			most change (parcels changing hands or being subdivided) or which 
			may be susceptible to change (parcels on the frontier). There is one 
			change that we know will occur in all systems and that is the 
			eventual death of the landholders. The mechanism for dealing with 
			this change, namely inheritance, is presenting a key challenge to 
			the maintenance of land administration systems in the developing 
			world. 
			Resilience is best measured when a system has been subjected to 
			some shock which challenges its continued existence. Extreme shocks 
			that impact land administration may include natural disasters (e.g. 
			hurricanes, floods) or anthropogenic fire. A resilient land 
			administration system is one that can most quickly return to 
			‘normal’ operation after a shock. If the shock pushes the system 
			beyond a certain threshold, it will “flip” into a fundamentally 
			different system. Within the Amazon region, for example, we can 
			observe indigenous forest areas flipping into treeless ranches which 
			are composed of entirely different structures (owners, resources) 
			and processes (land uses). Within the land administration context 
			this may not be as dramatic, with, for example, a flip from 
			registration of deeds to registration of title. 
			There is a recent but growing interest in the resilience of land 
			administration systems in the face of natural disasters such as 
			hurricanes and tsunamis. UN Habitat and others are realizing that 
			the resilience of land administration system and how it is governed 
			play a key role in recovery and reconstruction efforts following 
			natural disasters. The resilience framework is highly appropriate 
			for trying to not only understand the role that land administration 
			systems have played in past disasters, but more importantly how we 
			can strengthen these systems to better support recovery and 
			reconstruction in future disasters. 
 
	 
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CONTACTS 
	Greenville Barnes
	Associate Professor
	University of Florida
	406B Reed Lab
	Gainesville FL 32611
	USA 
	Tel + 1 352 392 4998 
	E-mail: gbarnes@ufl.edu 
	
    