1. Introduction
According to the United Nations [
1], the impacts of urbanization can be seen practically all over the world and, by 2050, over 60% of the population is projected to be urban, generating changes in the ways in which territories are occupied worldwide. Thus, beyond their size, territories are faced with remarkable mutations implying powerful advances in urban development in all dimensions, such as infrastructure, housing, services, and others, generating an urban landscape that is easy to perceive but extremely difficult to delimit, plan, and project.
One way to understand and respond to these phenomena is through the so-called “new science of cities”, which has become a benchmark for modeling and analyzing them. For Batty [
2], these new tools allow for representing, analyzing, simulating, forecasting, and creating urban structures. The above is in the context of defining cities as complex objects with different temporal and spatial scales that, despite their difficult characterization, have a certain logic that allows them to be analyzed [
3].
These modeling possibilities are based on the complexity of cities’ internal processes using geo-simulations [
4], in which traditional stochastic models based on cellular automata, Markov chains, and multi-criteria evaluation give a fuller understanding of the effects of human activity on urbanization and environmental deterioration processes [
5,
6]. Geo-simulation is built on expanding computing capacities, geographic information systems, and other spatial programs and statistical packages that have not only allowed understanding cities’ past growth and the changes in adjacent land cover [
7], but also allow for prospecting future changes and speeds, fundamental aspects for developing more effective planning tools, valuing and protecting particularly fragile ecosystems [
8], and in that way contributing to attenuating or mitigating deterioration processes in the natural system, or contributing to disaster risk management in urban areas [
9,
10].
Modeling approaches have allowed different scales of analysis to be addressed, allowing behaviors to be modeled in mega cities [
11] or in countries with greater concern for the processes that take place in their territories. This is the case with European nations, which have developed a wide range of models to understand these phenomena [
12], thus allowing the driving forces that lead urbanization processes as accelerated processes of change in land use/land cover (LULC) to be analyzed [
13]. Indeed, urban area simulation models are based on predictive variables such as historical LULC trends, the configuration of transport networks, or access to a city’s work center [
14].
In terms of the applicability of spatially explicit models or geo-simulation processes, metropolitan areas and developed countries are not the only ones facing constant changes from the dizzying speed of urbanization that need to be measured [
15], but other smaller cities located in Latin America, for example, are also undergoing significant change that affects and determines their spaces and surroundings, and it is in this context that medium-sized urban entities or intermediate cities emerge [
16]. They have direct links with their rural areas, configuring different degrees of centrality in their regional spaces and acting as important centers in terms of politics, services, social interaction, and connectivity, and administrative infrastructure [
17,
18].
Thus, as is the case with metropolitan areas, medium-sized cities have been under real estate development pressures and show similar complexities as large cities, both in terms of their virtues—such as better access to specialized services and the infrastructure produced by agglomeration economies—as well as the problems, such as pollution, congestion, and uncontrolled expansion, among others. This is why it is important to study them, considering the contributions that urban science models can make to territorial planning or management processes.
Background
Chile is a paradigmatic case in Latin America, with an urban population of over 87% [
19], an economic model with a powerfully neoliberal hallmark, a real estate market with weak regulation, and where intermediate cities and regional capitals have played a role as spaces that catalyze the needs of the territories closest to them [
20].
The city of Temuco is an interesting case study due to its rapid process of metropolization and its high natural and cultural value [
21]. It is located in the Araucanía Region (see location in
Figure 1) and, according to the INE (2017), contains practically 40% of the total regional population, surpassing the city that follows closest threefold and fostering a high dependence on services and infrastructure [
22]. At the same time, in Temuco, there are phenomena such as segregation and impoverished areas [
23] and a large indigenous population of Mapuche origin. In fact, the Araucanía Region concentrates the second-largest population of this people after the national capital and 11% of Temuco’s inhabitants declare themselves as belonging to the Mapuche people.
The presence of the Mapuche population is relevant given its rising demands to recover lands, recognition as a nation, and other historical claims arising from the depletion of their property dating back to the process of consolidating the Chilean nation-state in the late 19th century with the so-called ‘pacification of Araucanía’, a military campaign that killed and reduced Mapuche communities so the Chilean state could annex the current territories in Araucanía, among others [
24].
In addition, in terms of planning, Temuco underwent unsuccessful processes of updating both the Municipal Zoning Plan (PRC, Spanish acronym for Plan Regulador Comunal) as well as the Intermunicipal Zoning Plan (PRI, Spanish acronym for Plan Regulador Intercomunal), regulatory urban land use and regulation tools that were developed in a context of strong real estate development pressure and one in which lands whose owners are Indigenous Communities under Law 19,253 cannot be rented, provided in gratuitous bailment, or assigned to third parties for their use, enjoyment, or administration. This is a restriction that has not been fully respected, as often there is no real record of domain or registration of such lands, creating conflicts over the use of space.
In addition to the elements mentioned are other aspects that also entail tremendous planning challenges in terms of population dynamics and a growing vehicle fleet. Regarding the former, it had 189,994 inhabitants in 1998 and 358,541 in the 2017 census (including the agglomerated municipalities of Temuco and Padre Las Casas). That is, it practically doubled its population in the last 35 years. As far as the latter is concerned, it had 42,548 vehicles in 2001 and 98,430 in 2018, thus more than doubling the number in less than 20 years. Both situations pose challenges in terms of infrastructure, services, quality of life, and environmental quality in the city.
Given this background, there is a need to reflect on the dynamics of this city and its not entirely planned urban expansion, which has revealed the urgent need for studies on the territory to achieve more sustainable urban development, understanding this in its broadest sense by incorporating the different dynamics and stakeholders immersed in it.
For this reason, this article explores changes in LULC in the city of Temuco to generate a simulation of built surface through to 2049 and in that way contribute to the debate on the areas that should be incorporated in the city’s future planning, at least in terms of urban limits. To this end, the land cover between 1985 and 2017 was characterized, after which future urban growth in the city was simulated between 2017 and 2049 by analyzing the resulting spatial patterns in addition to the projected changes.
3. Results
The results were structured in three points. The first concerns validation of the model. The second analyzes the trends in land use and cover between 1985 and 2017, and the last simulates changes in land use and cover for the city of Temuco.
3.1. Validation of the Simulation Model for the City of Temuco
The 2017 LULC map was validated with the 2017 map simulated using the CA_Markov model.
Table 3 shows an analysis based on the discrepancy between a reference map and one that was simulated using the chi-square test, where our hypothesis is that the observed LULC map is the same as the simulated LULC map.
However, the chi-square analysis only allows an overall view of the statistically significant correspondence between the land uses and covers observed and simulated for 2017. For this, the KIA analysis allows the level of agreement/disagreement between the observed LULC and the simulated LULC to be assessed, and
Table 4 shows that there is an overall Kappa (Kno) of 0.69, which reflects a moderate level of aggregation.
In this regard, according to the criteria established by Nath et al. [
9], the Klocation statistics are the measure to be considered to validate the LULC simulation, and in that way predict location, which in this case study is 0.77, considered moderate aggregation (see
Table 4).
The results of the validation carried out through KIA provide information on the agreement/disagreement components of the CA_Markov model, with error due to the 16.9% quantity (DisagreeQuantity) and error due to the 0.8 assignment (DisagreeGridcell) (see
Table 5). In addition, the agreement level based on the specification of the level of the grid cell for each LULC category (AgreementGridcell) is 28%, which is consistent with the moderate levels observed in Kno and Klocation (see
Table 5).
Thus, the chi-square test shows that the statistical value is lower than the critical value. Hence, the null hypothesis is rejected, and it is possible to observe that there are differences between the simulated and reference LULC maps in 2017. However, this is consistent with the results of the analysis of KIA values, which range between the values 0 (zero agreement) and 1 (perfect agreement) [
27], where one can see that there are moderate levels of accuracy between the reference map and the simulated map.
3.2. Trends in Land Use and Cover Between 1985 and 2017
Figure 1 and
Figure 3 express the process of urban expansion and land cover changes between 1985 and 2017. As can be seen, both forest as well as urban surface areas expanded, by 50.2% and 96.1%, respectively. However, the areas assigned to pasture-agricultural land zones, water bodies, and bare soil decreased, with the latter falling by 85.9% (see
Figure 3).
Regarding the areas that expanded, and considering the first period from 1985 to 2001, the most significant was urban land use, which grew by 921 ha, or a 41.6% increase in land cover compared to 1985 (see
Figure 3). For its part, forest land cover increased by 11.3%. In addition, it is important to mention the emergence of Labranza as an urban center, which despite not being contiguous with the city of Temuco, became a new spatial reference in the vicinity of the city, something that did not exist in 1985. As far as decreases in this same period are concerned, bare soil experienced a 38.7% reduction compared to the surface area in the initial year. While the other two covers were diminished (pasture-agricultural land and water bodies), their changes were marginal: 0.6 and 1.7%, respectively.
In the period spanning 2001 to 2017 (see
Figure 3), the most significant change was the drop in the pace of urban land growth, which expanded by 38.5%, or an additional 1206 hectares. For its part, forest land cover increased by 35%, thus expanding its spatial influence by 3130 hectares. Regarding LULC that declined, pasture-agricultural lands, bare soils, and water bodies were the most affected by the transition in LULC. Of these, bare soil was the one that saw its surface area drop the most, 77%, while pasture-agricultural land and water bodies were down by 5.1% and 8.4%, respectively.
In sum, the change in bare soil stands out in the evolution over time between 1985 and 2017. It declined by a total of 85.9% since 1985 (3355 ha), which, beyond its disappearance in terms of cover, indicates significant dynamism in terms of change from one cover to another. For their part, water bodies and pasture-agricultural cover showed less than 10% change. Urban cover stands out among those which increased, growing by almost twice what it represented in 1985 (96.1%), or an increase of 2127 hectares.
In particular, urban land use corresponding to the physical area of Temuco mainly expanded toward the northeast (Vilcún sector) and south-west (Labranza sector) between 1985 and 2017. It is important to highlight the emergence of Labranza as a hub in the urban network without being a direct branch of it. It grew from 33 ha in 2001 to 204 ha in 2017, which shows the sector’s dynamism in just 16 years. However, this situation was predictable, to a great extent thanks to the construction of a dual carriageway road that began in 2011, in addition to the fact that Labranza is a sector that was chosen for the construction of social housing for people who could not find housing solutions near Temuco due to high property prices [
37]. This is a classic way of providing housing solutions in Latin American countries and especially in Chile, causing high levels of segregation and precarious living conditions under the auspices of the state itself [
38].
3.3. Simulation of Changes in Land Use and Cover for the City of Temuco
The results of the Markov chains and the Multi-criteria/multi-objective evaluation were used to simulate land use and cover for 2033 and 2049, with the transitions obtained between 2001 and 2017 used for the former and the transitions between 1985 and 2017 for the latter.
Figure 4 shows the suitability maps for each objective evaluated, which correspond to each land use and land cover and where one can observe that, for the objective of urban suitability, the paired comparison matrix from the AHP allowed the weights or eigenvector for each factor analyzed to be obtained, with the distance from the main urban center and distance to the secondary urban center having a 74.5% impact (see
Table 6).
Considering the scenarios in 2033 and 2049, one can observe sustained growth in the urban area, expanding by an average of 44% between the two periods compared to 2017, equivalent to an average of 2328 hectares that are to be incorporated into the urban area of Temuco. Furthermore, one can see that there is a 59.2% average increase in forest cover compared to 2017 (see
Figure 3).
According to the data contained in
Figure 3, the city of Temuco will grow physically by around 1989 ha and reach a total of 6328 hectares by 2033, of which 293.9 hectares will be in Labranza, which in turn will represent 4.5% of the total urban area of the city of Temuco (see
Figure 4 and
Figure 5). As was the case with the trend observed between 1985, 2001, and 2017, growth toward the northeast, in the Cajón sector (municipality of Vilcún) and southwest (Labranza sector) of the municipality of Temuco is maintained.
For the second scenario simulated to 2049, one can see how urban cover will have increased by 2667 hectares from what it was in 2017, a 42.2% change, whose differential is 54% less than the observed growth rate between 1985 and 2017. Thus, the model simulated through to 2049 shows a slower growth rate than the comparative one with the LULC, but it begins to incorporate new areas in the sectors of Padre Las Casas (712.5 hectares) and Labranza (601.7 hectares).
The Urban Expansion Intensity (EI) Index calculated for Temuco reveals an uneven situation in the pace of urban growth through to 2049. When considering changes in urban areas between 2033 and 2049 compared to 2017, one can see that the urban areas of Vilcún (Cajón sector), Padre Las Casas, and Labranza show growth rates of 0.009%, which is considered low. However, the urban area of the municipality of Temuco shows an average growth rate of 0.13%, which is considered a medium expansion rate. This last expansion trend is consistent when evaluating the sum of all urban areas that comprise the city of Temuco (see
Table 7).
The simulation model proposed for the years 2033 and 2049 shows that urban growth will tend to grow more strongly toward the periphery, with an emphasis on the Labranza sector, which is consistent with the development of the dual carriageway road parallel to the street 1 Norte with the new street 1 Sur. Thus, connectivity between the regional capital and the coastal sector (Temuco–Nueva Imperial–Carahue) is being improved and the passage through Labranza has benefited it greatly.
This is not a random phenomenon, as the social housing construction policy has focused heavily on the area, as noted earlier, in addition to new real estate development projects aimed at middle class sectors and the future construction that is sure to be promoted along the road. According to the 2002 and 2012 censuses, 16% of total regional mobility to Temuco came from these territories, a process that is sustained on the dual carriageway to stimulate urban growth and expansion.
4. Discussion
The results presented in the previous section show some trends that need to be considered in current and future planning of the city and which are summarized in
Figure 6. In the case of Labranza, one way to highlight its growth is through its increase in surface area. If we take 2049 as the reference year, Temuco alone does not manage to double its area, but Labranza will increase its surface area by about four times, with what was observed in 2017 representing 26% of what it will be in 2049, when it will be built as a compact unit. The city of Temuco is expected to grow by 2667.2 ha by 2049, from which we can conclude that it is currently at around 61.9% of what it will be in 2049.
A second sector that will experience significant growth is the sector of Cerro Mariposa, or the road to “Las Vegas de Chivilcán” toward the north of the city, near Cerro Ñielol. There is currently a dynamic property market aimed at leisure plots, but this will change in the future. Indeed, if through to 2033 only Labranza can be considered as a non-contiguous hub of the Temuco system, in 2049 new signs of urbanization will appear in the areas already mentioned, which would exert pressure not only in terms of diffuse real estate development, but also in environmental terms, being located near one of the city’s main wetlands, whose recognition the municipality requested in the framework of the Urban Wetlands Act that has been approved in the country.
In addition, continuing along Route S-258, which is the extension of Pedro de Valdivia Avenue (see
Figure 1), the social housing developments built as a sort of archipelago will also contribute to these dynamics. If the growth trend is projected in the way that the model indicates (see
Figure 6), Temuco will be faced with a scenario of increasingly discontinuous growth, in an amoeba shape and not in a compact form, something already seen in other intermediate cities in Chile [
27,
30] and, while perhaps to be expected, something that goes against all sustainability aspects contained in the National Urban Development Policy released in 2014. In terms of planning urban space, the need to create a new municipality has even been considered, a matter that political circles have taken into account by submitting a request to this effect. In fact, since 2012 a social movement in favor of creating the municipality of Labranza has emerged and has organized different activities aimed at becoming an autonomous unit. However, the cost of the public apparatus and scant political capital could be some of the elements holding back these aspirations.
The above analysis could be further based on the distances and the growth that will be experienced, which can be seen in
Figure 6. It clearly shows where Labranza and Temuco would have a presence on the surface. Regarding the former, we would see it consume land up to 3 km from its center with a clear presence up to the first 2 km, and a slight increase in the third and last kilometer.
For its part, Temuco’s presence, which could reach up to about 14 km from the center, is characterized both by its expansion toward the north side in the direction of the Cajon and Vilcún areas, in addition to its conurbation with Padre Las Casas and the modeled urbanization toward the north of the city parallel to Cerro Ñielol and the forested areas nearby, although due to its current configuration, the greatest presence will be in the first 7 km, as growth will cease to be clearly upward (see
Figure 6).
When this dynamic is analyzed in the context of the status of territorial planning instruments, one can see that the Temuco Zoning Plan has been in force since 2010, with an amendment in 2011 and modifications by means of a sectional plan for the Las Encinas sector in 2012. However, the territory in question does not have a plan in force at the intermunicipal level, a situation that is repeated with Padre Las Casas. In this sense, it is important to observe that limiting factors such as the presence of ‘Mercedes de Tierra’ (indigenous property grants) have not been an obstacle to the expansion and projection simulated. On the contrary, one can see that the communities have remained in the midst of urban expansion [
39], and this is therefore reflected in the inorganic growth of the city.
Notwithstanding the results obtained, the method has certain weaknesses that must be considered, such as the “speckle” or “salt-and-pepper” effect of the modeling. This is characterized by generating a series of patches that appear as part of the simulations distributed in a random and disorganized way, when in practice they should be agglomerated.
Despite this, it mostly presented itself in the projection of the base year (2017) and less so in the others. For this situation, the important thing is not to consider them as was done within the analysis carried out, as they are precisely differentiated from the clusters that the model does manage to determine which are the ones that indicate spatial trends and relations.
In addition to this—as has already been outlined in previous paragraphs—the diffuse planes of the growth hubs are linked to Mapuche enclaves, which are indicated as a constraint in
Table 1 as they cannot be annexed for urban use. In this sense, diffuse and at times discontinuous growth may be a trend in the morphology that the city is taking on.
One of the last aspects to be highlighted is the lack of refinement or reliability of the location vector layers of Mapuche communities or their property. Without doubt there is a need to achieve greater transparency and make more information available to allow more robust results and analyses to be generated. While the country has made progress, it is a far cry from countries with robust, referenced, and reliable information.
Lastly, it should be noted that in Temuco’s case, generating binding urban planning instruments is a priority, as problems have already emerged in terms of diffuse land expansion, and it is projected that growth will not be very harmonious in the next 30 years, together with the presence of indigenous territories whose legal status protects them from intervention, posing a challenge in the matter and raising the need to reduce future conflicts. In this sense, the implementation of Regional Territorial Organization Plans that will regulate rural space through Law 21,070 of 2018 should incorporate this issue as a priority element in their elaboration. Along the same line, strengthening the authority of regional governments in territorial planning is another variable that will allow the complexity of this task to be addressed.