Next Article in Journal
Severe Drought Monitoring by Remote Sensing Methods and Its Impact on Wetlands Birds Assemblages in Nuntași and Tuzla Lakes (Danube Delta Biosphere Reserve)
Previous Article in Journal
Oil Palm Land Use Change and Rice Sustainability in South Sumatra, Indonesia
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

Understanding Industrial Land Development on Rural-Urban Land Transformation of Jakarta Megacity’s Outer Suburb

1
Regional and Rural Development Planning Science Study Program, Faculty of Economics and Management, IPB University, Bogor 16680, Indonesia
2
Laboratory of Regional Planning, Graduate School of Global Environmental Studies, Kyoto University, Kyoto 606-8501, Japan
3
Regional Development Planning Division, Department of Soil Science and Land Resources, Faculty of Agriculture, IPB University, Bogor 16680, Indonesia
4
Center for Regional System Analysis, Planning, and Development (CRESTPENT), IPB University, Bogor 16680, Indonesia
5
Department of Human Geography and Regional Development, Faculty of Science, University of Ostrava, 710 00 Ostrava, Czech Republic
*
Author to whom correspondence should be addressed.
Land 2022, 11(5), 670; https://doi.org/10.3390/land11050670
Submission received: 25 March 2022 / Revised: 20 April 2022 / Accepted: 25 April 2022 / Published: 30 April 2022
(This article belongs to the Section Urban Contexts and Urban-Rural Interactions)

Abstract

:
After decentralization, there was massive development in Jakarta megacity’s outer suburbs (JMOS), especially in Bekasi and Tangerang regencies, marked by large-scale industrial estate/park (LSIEP) and followed by new town developments. However, this process led to the emergence of “chaotic” urban-rural land patterns. This study sought to identify the extent to which LSIEP development has affected rural-urban land transformation (RULT). The primary data were land use/cover (LUC) data from 2005, 2015, and 2020 and the LSIEP distributions. The methods applied are the Patch-generating Land Use Simulation (PLUS) model for 2025’s LUC prediction and the RULT index approach, RULT index development using the analytical hierarchy process. These combined approaches were novel in Indonesia, which usually relies on Cellular Automata (CA)-Markov, overlay (spatial), and descriptive statistics analyses to describe the RULT phenomenon. It was found that the villages located around the LSIEP close to the Jakarta megacity toll road network and those adjacent to the municipality (city) had been transformed into urban areas, while villages far from those locations were still rural. This study’s results help clarify the rural to urban transformation in Jakarta megacity’s outer suburbs and could be used as input for spatial planning policy.

1. Introduction

Recent spatial expansion of urban land around the Asian megacities is associated with several threats to their sustainability. Intensification of agricultural land conversions, environmental degradation, landscape fragmentation, green space losses, and “chaotic” patterns of urban-rural land are among the most often-cited sustainable issues (see [1,2,3,4,5,6]). In this paper, we focus on Southeast Asian megacities, especially in the suburban area, combining high density with lower land-use diversity (compared with East Asian cities and Western cities) (see [7])—resulting from the existence of large monofunctional residential or commercial areas [8]. Drawing on a case study from the Indonesian capital’s suburban developments, we illustrate the pace of rural-urban transformation (RUT) driven by extensive industrial development. The Jakarta megacity is representative of highly polycentric Asian megacities, which are characterized by rapid population growth, industrialization, and land transformation in their outer rings [3].
The 2020 Indonesian census found that more than thirty-one million people were living in the Jakarta megacity, or Jakarta metropolitan region (JMR), the second-largest global urban agglomeration after the Tokyo megacity [9]. The Jakarta megacity consists of the core region and the suburb/hinterland regions (see Figure 1). Since the regional autonomy/decentralization policy was implemented in 2001, the Bodetabek (Jakarta megacity’s suburb) region, especially in the outer suburbs: Bekasi and Tangerang regencies, has experienced rapid land development [10,11]. Land development in both regencies is also driven by a shift of population and industrial activities from the core/inner suburb area to the outer suburb because land in those areas is already scarce [5,12]; these processes and shifts are called “suburbanization” [13].
Regional autonomy/decentralization policies have given local governments in the Jakarta megacity’s suburbs more authority to regulate their regions, especially development planning and budgeting [14,15]. Besides, regional autonomy/decentralization can also trigger inter-regional competition through increasing local economic capacity [16]. The Bekasi and Tangerang regencies (kabupaten) governments are taking advantage of their regional autonomy to increase their regional income (economic-growth oriented) and competitiveness [11]. This development approach has resulted in the establishment of large-scale industrial estate/park (LSIEP) development, which has had a multiplication effect on the local economy (see [10,17,18]). Moreover, the development of the LSIEP is to support the economic system of the Jakarta megacity [19].
After Industrial park/estate regulation was issued in 1989 [20] and decentralization was implemented in 2001, the number of LSIEPs built by the private sector in Bekasi and Tangerang regencies increased significantly. In both regencies, LSIEP development is mainly carried out by the private sector and financed by foreign direct investment (FDI) or the public-private partnership (PPP) mechanism [11,21]. LSIEP in both regions reached sixteen [22]. The manufacturing sector’s contribution to the Gross Regional Domestic Product (GRDP) is dominant, especially in the Bekasi Regency, reaching 75% of their GRDP in 2019 [23].
The LSIEP developments have triggered significant urban land developments, especially after decentralization was implemented. According to [24], from 1995 to 2012, dry and agricultural land conversion significantly occurred in Jakarta’s suburbs, especially in Bekasi and Tangerang regencies. Most of the agricultural areas in these regencies have been converted into industrial and settlement areas [2]. The rapid land conversion also led to the “chaotic” patterns of urban-rural land and caused imperfections in the RULT [4,5].
Identifying land transformation is necessary for understanding the development process because the land is the primary physical resource for socio-economic development [25,26]. In addition, land and its transformation process indicate urban-rural development and transformation [27,28,29]. Land-use/cover (LUC) transformation results from a region’s dynamic social and economic development [30]. Therefore, research on LUC transformation/change can be the basis for urban-rural development policies, especially to control urbanization [27,28].
Most recent Indonesian rural to urban transformation research has utilized multitemporal land use/cover (LUC) data to identify agricultural land loss, urban expansion, and physical urban growth (see [2,3,5,24,31,32,33]). Specifically, there have been several studies related to spatial LUC change issues in the Jakarta megacity; the latest studies related to this topic are the research of Rustiadi et al. [3,5] and Kurnianti et al. [24]. Most previous studies mainly used overlay (spatial) techniques and descriptive statistical analyses to explain these phenomena. However, most of the latest research measures the rural to urban transformation only by the changes in the agricultural area or non-built-up area into the built-up area, whereas the transformation into urban land is not only a simple shift towards a higher share of the built-up area.
A more comprehensive approach based on a multi-criteria evaluation of the LUC data can be used to assess and identify the land transformation [26]. Moreover, according to bibliometric analysis using the Scopus database, a study related to RULT in Southeast Asian megacity’s suburbs, especially at the microlevel, is hardly ever discussed. Therefore, this study aims to identify the extent of the LSIEP development on the RULT of Jakarta megacity’s outer suburb (JMOS) at the micro-level (village). Additionally, this study compares Bekasi and Tangerang regencies as industrial-dominated suburbs in the Jakarta megacity. Furthermore, using LUC data—as a substitute for challenging-to-obtain socioeconomic data at the village level—this study reveals RUT in the Jakarta megacity’s suburbs at the microlevel.
Our paper develops a RULT index using the analytical hierarchy process (AHP) as a multi-criteria analysis approach to identify the RULT on JMOS. Similar studies are the study of Liu et al. [26] and Liu et al. [34]; Liu et al. [26] discuss land transformation in Xuanhua district on a village scale in North China. The main difference from Liu et al. [26] is that the number of LUC classes used as criteria was adjusted to conditions and LUC data. This paper’s study uses six LUC classes in which the built-up area is separated into settlement area (SA) and industrial, trade, and service (ITS) area. ITS development is the main feature of the urbanization process (rural to urban transformation) in the Jakarta megacity’s suburbs [17,35].
Another main difference is that this research performs RULT prediction, which is not performed in the study of Liu et al. [26]. The LUC prediction method applied in this study is the latest, namely the patch-generating land use simulation (PLUS) model developed by Liang et al. [36]. Besides being described as a method with high accuracy, the PLUS model was developed to improve the weaknesses found in the previous methods, especially the CA model [37,38]; the mainstream method is used for LUC prediction, especially in Indonesia (see [39,40,41,42]). This research also involves some driving factors in prediction models related to industrial and settlement development. LUC model predictions in this study are also equipped with spatial constraints using the regency spatial plan. The spatial plan as a spatial constraint is intended so that this study not only describes the RULT that occurred in detail but also can be an evaluation and input for the spatial planning policy of the Bekasi and Tangerang regencies.

2. Materials and Methods

2.1. Study Area

The core of the Jakarta megacity is Jakarta special capital region (SCR), while the Bodetabek region (an acronym for Bogor-Depok-Tangerang-Bekasi municipalities/regencies) is the suburb/hinterland of this megacity [5,8]. The 2020 Indonesian census found that the population in the Jakarta megacity core was 10.56 million people, and in the Jakarta megacity suburbs was 20.68 million people. In some research, the suburban region of the Jakarta megacity is divided into two regions, namely Jakarta megacity’s inner suburb and outer suburb—the region with “municipality (city)” or “kota” status is the inner suburb, while the region with “regency” or “kabupaten” status is the outer suburb [3]. The core and suburb/hinterland area is a feature of the nodal (functional) region system [43,44].
This study focuses on JMOS, particularly the Bekasi and Tangerang regencies located in the northern part of Java island (see Figure 2). Both regencies have similar topographic characteristics: situated in the coastal area, almost all of the area is lowland and has almost no steep slopes. At the same time, the topographical features of the Bogor Regency are somewhat different from both regencies (see [45]). Therefore, this study compares the level of industrial development and its effect on RULT in the regencies of Jakarta megacity that have similar topographic characteristics.
The Indonesian census in 2020 found that the population in the Bekasi and Tangerang Regencies was more than six million people. The Bekasi and Tangerang Regencies have 52 subdistricts (kecamatan); 29 in the Tangerang Regency and 23 in the Bekasi Regency. The analysis unit used in this study was the village (desa/kelurahan), with the Bekasi Regency comprising 187 villages, and the Tangerang Regency comprising 274 villages.
Based on President Regulation No. 60/2020 [46] concerning Jakarta megacity’s spatial planning policy, there are three urban areas in Bekasi and Tangerang regencies, namely Cikarang, Balaraja, and Tigaraksa region. The Cikarang urban area is directed as the capital and the center of health and social amenities of the Bekasi regency. Tigaraksa urban area is directed as the capital of Tangerang regency, while Balaraja urban area is directed as the ITS area of Tangerang regency. Additionally, the Cikarang, Balaraja, and Tigaraksa regions are also directed as the center of LSIEP development in the JMOS.

2.2. Data Collection

The primary data used in this study were LUC data in 2005 (describes conditions when decentralization was just implemented) and LUC data in 2015. The LUC data were obtained from the Center for Regional System Analysis, Planning, and Development (CRESTPENT), IPB University. The data were processed using the supervised classification method using the maximum likelihood classification technique. Supervised classification is one of the preferred methods used to create LUC data [47], and this classification method can control the separation of spectral values for each LUC class by computer [47]. For LUC prediction validation, this study produces 2020’s LUC data with the same raw data, methods, and techniques as the data obtained by CRESTPENT, IPB University.
For data obtained from CRESTPENT, IPB University, we separated LUC class (Built-up area) into the settlement area (SA) and the ITS because they are not separated yet. Subsequently, there are six LUC classes used in this study, namely: (1) settlement area (SA); (2) industrial, trade, and service (ITS) area; (3) wet-agricultural land (WAL); (4) dry and bare land (DBL), (5) forest and mangrove (FR); and (6) mixed plantation (MP). Furthermore, the other data used in this study are regency spatial plan data as a spatial constraint and some data related to the driving factors of LSIEP and residential development.
In this study, areas planned (according to Bekasi and Tangerang regencies’ spatial plan) as protected forests (including mangrove areas), open green spaces, parks, agricultural land, river borders, coastal borders, and water bodies (rivers and lakes) should not be changed/converted. Areas that can be changed/converted and cannot be changed/converted are presented in Figure 3. This study also involves some driving factors in LUC prediction related to LSIEP and residential area development, namely: (1) proximity to LSIEP locations, (2) proximity to toll road gates, (3) proximity to main roads, and (4) proximity to the commuter railway station; these are the main driving factors of land (rural to urban) transformation/changes in Bekasi and Tangerang regencies (see [3,8,10,13,48,49,50,51,52,53]). All types of data are presented in Table 1.
According to the Ministry of Industry, the Republic of Indonesia, ten LSIEPs are located in the Bekasi regency [22]. Compared with Bekasi Regency, the number of LSIEP in the Tangerang Regency is lower, which is six, with the most expansive being the Millennium Industrial Estate covering an area of 1800 hectares (see Table 2) [22]. Furthermore, Bekasi Regency has five LSIEPs covering more than 500 hectares, while the Tangerang regency only has one. The list of LSIEP was explained in Section 3.1.

2.3. Data Processing

2.3.1. LUC Prediction for Rural-Urban Land Transformation Prediction

This study used the PLUS method for LUC prediction—the latest LUC prediction method; and we tested this method to predict LUC with a dispersed pattern, as happened in Bekasi and Tangerang regencies. The PLUS method improves previous methods, such as the CA-ANN and CA-Markov [36,37,38]. The two weaknesses of the CA model highlighted by scholars are weak at revealing the relationships underlying LUC change [36] and at capturing the patch evolution of LUC types naturally [36,54].
To improve the weakness, The PLUS model has two features, namely: (1) land expansion analysis strategy (LEAS)—a couple of combinations of transition analysis strategy (TAS) and pattern analysis strategy (PAS); and (2) CA based on multitype random patch seeds (CARS) [36]. The LEAS feature in the PLUS model functions as a data mining framework for identifying the rules of LUC change [36]. LEAS is also equipped with a random forest classification (RFC) algorithm to explore the relationships between each LUC type’s growth and multiple driving factors [36,38]. Furthermore, at the fine-scale resolution, CARS could better simulate the patch growth in all LUC classes [36].
The basis for selecting the driving factor used in this study has been explained in Section 2.2. This study does not pay attention to topography factors because both regencies are located in coastal areas, mostly lowlands—there are no striking differences in topography throughout both regencies. An example of the driven factor used in this study is presented in Figure 4. In addition, this study also uses spatial plan data as spatial constraints, as described in Section 2.2. The LUC prediction framework in this study is described in Figure 5.

2.3.2. Rural-Urban Land Transformation (RULT) Index

This study uses the AHP to build a RULT index. AHP is one of the universal methods of multi-criteria decision making (MCDM) that succeeded in breaking the opinion that the measurement of objects/phenomena must be based on a physical scale with a zero and a unit [55]. AHP is a relative scale based on expert preferences [55]—measurement of weight in AHP is based on pairwise comparison inputs [56]. AHP in this study involved eight experts in urban and regional planning, regional development, and urban studies. The eight experts represent the central government (C), local government (L) (representations of Tangerang and Bekasi regency government), developers (D), urban and regional planning consultant (U), and lecturers/academics (A). The list of expert institutions is presented in Table 3.
The primary purpose of the AHP was to determine the priorities for the RULT criteria by giving weights to each land use criterion. Interviews were conducted with the experts on their preferences regarding the priority for each land use criterion. According to the expert preferences and previous studies, the ITS and SA are worth (+), meaning that the LUC criteria align with the transformation from rural to urban areas. In contrast, DBL, WAL, FR, and MP are worth (–), meaning that those LUC criteria are in the opposite direction towards the rural to urban land transformation.
Based on the AHP’s results involving eight experts’ preferences, it was found that wet-agricultural land (WAL) and industrial, trade, and service (ITS) are the leading criteria that can differentiate/determine an area that can be categorized as urban or rural. Additionally, the AHP’s consistency ratio (CR) value acquired in this study is 0.5%. Furthermore, the AHP model used in this study was considered valid because the CR value is below 10% [55,57]. A list of weights for each criterion is presented in Table 4. The weight of each LUC criteria coupled with the direction mark (+/–) forms the RULT index’s equation, the equation of the RULT index (RULTI) is presented in Equation (1).
RULTI   i = ( ( ITS TA × 0.341 ) + ( SA TA × 0.201 ) ( DBL TA × 0.085 ) ( WAL TA × 0.231 ) ( FR TA × 0.061 ) ( MP TA × 0.081 ) × 100 )
The maximum value of the RULTI in this study is 54.2 (total weight of the built-up group), and the minimum value is −45.8 (total weight of the non-built-up group). Subsequently, The RULTI results were then classified based on the value intervals; for example, each village with a RULTI value > 0 was classified as an urban area because the LUC, which reflects its socioeconomic activities, is dominant in the urban. In contrast, the village with a RULTI value < 0 is classified as a rural area because the LUC, which reflects its socioeconomic activities, is dominant in the rural.

2.3.3. Exploration Spatial Data Analysis (ESDA)

This study also analyzed the spatial autocorrelation of the difference in RULTI value (RULTI 2015 value minus (–) RULTI 2005 value). The analysis was to identify which villages experienced high growth in the RULT index and vice versa. The spatial pattern/association analysis in this study uses Local Moran’s I, which utilized the local indicators of spatial association (LISA) developed by Anselin [58]. LISA is a widely used method to explore spatial pattern/association/disparity of multitemporal spatial data [59,60,61,62]; the formula for which is presented in Equation (2) [58,59,60,61].
I i = n   j = 1 n w i j ( x i x   ¯ )   ( x j x   ¯ ) Z x 2 j = 1 n w i j
where: Ii = LISA; x = the difference value of the RULTI for the 2005–2015 period at the village level; i is the village, the index for which was calculated; j is the neighboring village; Wij = is the spatial proximity matrix that represents the spatial proximity value between village i and neighboring village (j); and Z x 2 = variance of RULTI difference value for the 2005–2015 period at the village level.

3. Results

3.1. Land Development and Its Effect on the LUC

The data analysis revealed that in 2005 more than 50% of the land in the Bekasi and Tangerang Regencies was devoted to paddy fields (WAL), with the built-up areas being only around 10% in each regency. However, the pace of urban physical growth in both regencies is relatively high; each year (period 2005–2015), with the built-up areas growing by 4.2 – 6.4 % per year. In 2015, the built-up area covered 15.8% of the Bekasi regency’s total area and 22.8% of the Tangerang regency’s total area (see Table 5).
In 2015, the ITS area covered 18.7% of the total built-up area in both regencies, with the remainder being SAs (including urban and rural settlements). The growth rate of the ITS area is not as big as the SA reaching 6.3% per year, which is 1.6% per year (see Table 6). This significant growth rate made the SA cover 81.3% of the total built-up area in both regencies, only 73.5% in 2005.
Most LSIEP locations are concentrated close to Jakarta megacity’s toll road network (JMTRN); only LSIEP with codes B1, B8, B9, T1, and T6 are not located in those locations (see Figure 6). The LSIEP with codes B1, B8, B9, T1, and T6 are located in areas surrounded by agricultural land that is not built-up area yet. In contrast, the LSIEPs are close to the JMTRN, surrounded by SA (e.g., T3 and B5, see Figure 7).
In 2015, the area (with a radius of 2 km) around LSIEP (B1, B8, B9, T1, and T6) had a low-level ITS and SA coverage (e.g., T1, see Figure 7), with the coverage percentage being below the areas surrounding the LSIEP close to the JMRTN. Interestingly, several villages, such as those in the Kosambi, Balaraja, and Tambun Selatan subdistricts, which are not close to the LSIEP, had high ITS area coverage. Numerous industrial areas in those subdistricts are not listed in the Ministry of Industry’s data or managed or located in LSIEP, particularly in the Kosambi subdistrict (see [63]).
Most LSIEP in both regencies focuses on the manufacturing sector and becomes the backbone of both regencies’ economies, especially the Bekasi regency. The manufacturing sector contributed 78% of the 2019 Bekasi regency’s real GDP [23], while the manufacturing sector in the Tangerang regency contributed 33.6% of the total GRDP [64]. In terms of 2019’s Real GRDP per capita [23,64], the Bekasi regency is superior to the Tangerang Regency, which is IDR 66.81 million (USD 4721) compared with IDR 36.93 million (USD 2610).

3.2. Rural-Urban Land Transformation of JMOS

In 2005, the villages that have been transformed into urban areas were spread over twelve subdistricts: six in the Bekasi regency (B) and six in the Tangerang regency (T) (see Figure 8). For explanation purposes, the urban areas are grouped into six regions: (1) Balaraja (T) region (Balaraja subdistrict); (2) Cikupa-Pasar Kemis (T) region (Cikupa and Pasar Kemis subdistrict); (3) Kosambi (T) region (Kosambi subdistrict); (4) Curug-Kelapa Dua (T) region (Curug and Kelapa Dua subdistrict); (5) Tambun (B) region (Tambun Utara, Cibitung dan Tambun Selatan subdistrict); and (6) Cikarang (B) region (Cikarang Barat, Cikarang Selatan, and Cikarang Utara subdistricts). The group division is considered on a spatial planning policy and contiguity aspect. Most urban areas are close to the JMTRN and adjacent to the municipality (city) (see Figure 8).
The Cikupa–Pasar Kemis region and Cikarang region are the locations most of LSIEP, especially the Cikarang region, which has seven LSIEPs. Meanwhile, the Balaraja, Tambun, and Kosambi regions are supported by industrial areas that are not managed by LSIEP. In 2015, new urban area enclaves emerged, especially in Tangerang Regency (see Figure 8); during this period, development was inclined towards urban settlement (residential) development carrying the new-town concept. Furthermore, the merging of some urban areas needs to be highlighted in this period, for instance, the merging of the Tambun and Cikarang regions and the merging of the Curug-Kelapa Dua and Cikupa-Pasar Kemis regions (see Figure 8).
The LISA results derived from ArcGIS (ESRI, Redlands, CA, USA) showed that from 2005 to 2015, the villages that had significant index value increases tended to be close to the location of LSIEP, the toll road gate, primary and secondary roads, and commuter railway stations; as indicated by high-high clusters (see Figure 9). In contrast, villages far from those locations have a low or almost no change in index value difference, as indicated by the low–low cluster. The proximity to primary/secondary roads and commuter railway station factors are the main driving factors for the rural to the urban transformation process in Bekasi Regency. In comparison, the proximity to LSIEP location and primary/secondary roads have more influence on the transformation from rural to urban regions in the Tangerang regency (see Figure 9).

3.3. JMOS Rural-Urban Land Transformation Prediction

The primary data for RULT index prediction was the 2025 LUC prediction, processed using the PLUS Model. This study’s LUC prediction accuracy results using overall accuracy (OA) and kappa are 0.866 and 0.782, respectively. It can be concluded that the LUC predictions generated in this study are considered valid, exceeding the values of 0.7 and 0.6, respectively [65]. The one thing that causes the OA or Kappa values not to achieve perfect scores is that the PLUS model is not successful in describing new patches of industrial estates that exist in 2020’s LUC map (validation map); many newly formed industrial areas are found in 2020’s LUC map, while in 2015’s LUC map, those locations are not industrial areas. Therefore, the PLUS Model is unsuccessful in perfectly meeting and describing the land demand for industrial area purposes.
The 2025 LUC result indicated that the annual BA growth from 2015 to 2025 was lower than from 2005 to 2015 (see Table 7). Because a spatial plan was used as a spatial constraint, there should have been no BA (ITS and SA) expansion in areas that could not be changed/converted (see Section 2.2). This study also included driving factors that could result in a more natural annual growth that did not necessarily follow the annual growth rate in the previous period. From 2015 to 2025, although there was a positive growth rate, the Tangerang Regency experienced a growth decline compared to the previous period (see Table 7).
The coverage area to total area assessment revealed that the predicted BA coverages in the two regencies in 2025 would still be below 30% and that the BA coverage in Tangerang Regency would be higher than in the Bekasi Regency (see Table 7). From 2015 to 2025, the annual growth rate of the SA still followed the previous period’s pattern, which was still higher than the ITS area’s annual growth rate. Compared to the Bekasi Regency, which had a large gap, there was no significant gap between the annual SA and ITS area growth rates in the Tangerang Regency (see Table 7).
It was predicted that by 2025 there would be expanding urban areas, the merging of urban regions, and the emergence of new urban areas (see Figure 10). It was predicted that the urban regions would be increasingly integrated, such as the merging of the Balaraja and Cikupa-Pasar Kemis-Curug–Kelapa Dua regions. It was also predicted that the urban region would expand to include the Kosambi, Curug–Kelapa Dua, and Tambun-Cikarang regions. Moreover, some villages of the Tarumajaya subdistrict—the location of Marunda Center Industrial Park (B8)—will be transformed into an urban area as a new urban area.
The RULT map produced by this study illustrates the relationship between RULT and the driving factors used in this study (see Figure 10). For example, most urban land in the Bekasi Regency had the following characteristics; close to the commuter railway station, close to primary and secondary roads, and close to the LSIEP locations. However, proximity to the commuter railway station was not the main factor for the rural to urban transformation in the Tangerang Regency (see Figure 10).

4. Discussion

4.1. Industrial Development on the Suburbanization of JMOS

Suburbanization in JMOS, especially in Bekasi and Tangerang regencies, has been strongly encouraged by industrial development [10,13,17,21]. This phenomenon is similar to the suburbanization in many metropolitan areas in China characterized by LSIEP development [66]. Suburbanization that occurred in Bekasi and Tangerang regencies does not resemble the suburbanization process in the Jakarta megacity’s inner suburbs (or even in cities in Western countries that have been primarily driven by residential development (see [8,66])).
LSIEP developments have been designed to support Indonesia’s economy and especially the creation of jobs and the engine of economic growth in the JMOS (see [10,17,21,67]). LSIEP, which focuses on the manufacturing sector, employs more than 500,000 workers in the Bekasi regency [10], the most expansive of which is the Jababeka industrial park [22]. The study results indicate that the LSIEP close to the Jakarta megacity toll road network has become a growth center in the region, as evidenced by the development/expansion of residential areas around those locations.
Manufacturing is a major contributor to the Bekasi and Tangerang regional economies [23,64]. If we compared the manufacturing sector’s contribution with both regency economies, Bekasi regencies are superior to Tangerang regency in terms of the manufacturing sector’s contribution to GRDP. The superiority of the Bekasi regency is also described by the number of LSIEP, which are more than the Tangerang regency.

4.2. LSIEP on Land Development Issues

Urban-biased policies are often the mainstream land development policies in the megacity suburbs of China (East Asia) and Indonesia (Southeast Asia), characterized by industrial and residential development (see [3,26,29,68]). Industrial land development in megacity suburbs of China and Indonesia often raises land development issues: agricultural land conversion and “chaotic” urban-rural land (see [4,5,6,13]). This study found that there had been significant industrial and residential development growth in the Bekasi and Tangerang Regencies from 2005 to 2015, most of which involved agricultural land conversions. The significant growth supports the statement of several studies, which explain that decentralization is one of the starting points for massive development in JMOS (see [18]) and massive agricultural land conversion in both regions (see [2,69,70,71,72]).
New-town development, a by-product of LSIEP development, is one of the main contributors to land development in JMOS, providing housing facilities for rich-urban people, as land in the core area was scarce, thus creating gated communities [8,18]. The Tangerang regency was found to have developed five new towns over more than 500 hectares [18,73]. The annual SA development growth rate and the predicted growth rate revealed that new-town developments will become the main land development characteristic in the JMOS in the future. However, the development in the Jakarta megacity’s suburbs often violates spatial plan regulation – many studies have revealed this, including the studies by Firman [48], Kurnianti, et al. [24], and Santosa et al. [69].

5. Conclusions and Policy Implications

In the concluding section, we aim to discuss our main empirical findings from the viewpoint of spatial planning together with fundamental limitations and possible avenues for future research.

5.1. Rural-Urban Land Transformation toward Spatial Planning Policy

Paying more attention to the spatial plan is essential because the development of settlements and industrial areas in the JMOS is sometimes on land not intended for these development [24,48,69]. Moreover, the development led to agricultural land conversion, especially the paddy field area [2,3,31,48,69,74]. If these things are allowed to continue, then the sustainable development goals listed in the Bekasi and Tangerang regency spatial plan regulation will be difficult to achieve, namely “environmental-friendly industrial and residential development that is in synergy with the agricultural sector development” [75,76].
This study also found that if the development follows spatial plan regulations, the growth rate of built-up area (SA and ITS) would be decreases, and would fall by at least half in the Tangerang Regency. Ultimately, the results of this study could be used as an input or an evaluation for spatial planning policies, particularly for protecting those areas dominated by rural land and characterized by extensive agricultural land/nonBA coverage. Evaluations of the spatial planning implementation are necessary, especially as the development in the Jakarta megacity suburbs is not yet complete. There are still many residential development megaprojects waiting to be built, including the 1000 ha PIK 2 (new-town) development in Kosambi subdistrict for the construction of 3000 landed residential units and 14,000 apartment units [77]. Furthermore, the Pagedangan subdistrict part of the Curug-Kelapa Dua region, which is an expansion and planning area of Bumi Serpong Damai (BSD) new-town (see [51]).
Maintaining the rural land in the JMOS must be a priority in land development policy because rural land is needed to supply food and maintain the ecological balance. Many studies have found that the development in Jakarta’s megacity’s suburbs disrupted food production [2,69] and caused environmental degradation [78]. Furthermore, environmental degradation has caused some areas in the JMOS to experience erosion and flooding [79].

5.2. Limitations and Possible Further Development

The primary limitation of this study was that the LUC dataset that was consulted was less detailed, especially for the built-up areas, as the urban and rural settlements were classified under one LUC class. Although the LUC can provide an overview of the socioeconomic activities of a region, it can only provide a simple description. Further, the LUC used in this study was focused more on land cover data. Nevertheless, this study could be considered an initial study for determining the region classifications in the JMOS and an alternative study for countries that do not have micro-scale area socioeconomic data adequately at the village level.
The criteria/parameters and methodological limitations meant that it was only possible to divide the region into rural and urban regions as it was unable to clearly define the “desakota” regions, which are regions that have mixed urban and rural characteristics [13]. Therefore, further research should use more detailed land-use data on the built-up areas that include the AHP criteria, and it is also necessary to develop an academic method to classify urban, rural, and desakota areas.

Author Contributions

Data collection, conceptualization, field survey conduction, data curation, formal analysis, methodology, validation, visualization, and writing—original draft: A.A.K.; investigation, methodology, supervision, validation, writing—review, and editing: E.R., A.F., A.E.P., J.Ž. and I.S. All authors have read and agreed to the published version of the manuscript.

Funding

This research and the APC were funded by the Ministry of Education, Culture, Research and Technology, the Republic of Indonesia, through the PMDSU scholarship scheme with grant number 1/E1/K.P.PTNBH/2021.

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

Not applicable.

Acknowledgments

We would like to thank the Ministry of Education, Culture, Research and Technology, the Republic of Indonesia, for funding this research and the APC of our article.

Conflicts of Interest

The authors declare no conflict of interest. The funders had no role in the study; in the collection, analyses, or interpretation of data; in the writing of the manuscript, or in the decision to publish the results.

References

  1. Xu, G.; Jiao, L.; Liu, J.; Shi, Z.; Zeng, C.; Liu, Y. Understanding Urban Expansion Combining Macro Patterns and Micro Dynamics in Three Southeast Asian Megacities. Sci. Total Environ. 2019, 660, 375–383. [Google Scholar] [CrossRef] [PubMed]
  2. Pribadi, D.O.; Pauleit, S. The Dynamics of Peri-Urban Agriculture during Rapid Urbanization of Jabodetabek Metropolitan Area. Land Use Policy 2015, 48, 13–24. [Google Scholar] [CrossRef]
  3. Rustiadi, E.; Pravitasari, A.E.; Setiawan, Y.; Mulya, S.P.; Pribadi, D.O.; Tsutsumida, N. Impact of Continuous Jakarta Megacity Urban Expansion on the Formation of the Jakarta-Bandung Conurbation over the Rice Farm Regions. Cities 2021, 111, 103000. [Google Scholar] [CrossRef]
  4. Yokohari, M.; Takeuchi, K.; Watanabe, T.; Yokota, S. Beyond Greenbelts and Zoning: A New Planning Concept for the Environment of Asian Mega-Cities. Landsc. Urban Plan. 2000, 47, 159–171. [Google Scholar] [CrossRef]
  5. Rustiadi, E.; Pribadi, D.O.; Pravitasari, A.E.; Indraprahasta, G.S.; Iman, L.S. Jabodetabek Megacity: From City Development Toward Urban Complex Management System. In Urban Development Challenges, Risks and Resilience in Asian Mega Cities; Springer: Tokyo, Japan, 2015; pp. 421–445. [Google Scholar] [CrossRef]
  6. Yang, R.; Zhang, J.; Xu, Q.; Luo, X. Urban-Rural Spatial Transformation Process and Influences from the Perspective of Land Use: A Case Study of the Pearl River Delta Region. Habitat Int. 2020, 104, 102234. [Google Scholar] [CrossRef]
  7. Chen, T.L.; Chiu, H.W.; Lin, Y.F. How Do East and Southeast Asian Cities Differ from Western Cities? A Systematic Review of the Urban Form Characteristics. Sustainability 2020, 12, 2423. [Google Scholar] [CrossRef] [Green Version]
  8. Zhu, J.; Simarmata, H.A. Formal Land Rights versus Informal Land Rights: Governance for Sustainable Urbanization in the Jakarta Metropolitan Region, Indonesia. Land Use Policy 2015, 43, 63–73. [Google Scholar] [CrossRef]
  9. Martinez, R.; Masron, I.N. Jakarta: A City of Cities. Cities 2020, 106, 102868. [Google Scholar] [CrossRef]
  10. Hudalah, D.; Firman, T. Beyond Property: Industrial Estates and Post-Suburban Transformation in Jakarta Metropolitan Region. Cities 2012, 29, 40–48. [Google Scholar] [CrossRef]
  11. Talitha, T. Rethinking metropolitan governance: An exploration of urban entrepreneurialism in decentralized Indonesia: The case of Jakarta Metropolitan Region (JMR). Governance, Policy and Political Economy (GPPE). Available online: http://hdl.handle.net/2105/37321 (accessed on 20 February 2022).
  12. Rustiadi, E.; Panuju, D.R. Spatial Pattern of Suburb. In Land Use Changes in Comparative Perspective, 1st ed.; Himiyama, Y., Ed.; Taylor&Francis Group: Abingdon, UK, 2002; pp. 33–52. [Google Scholar]
  13. Kurnia, A.; Rustiadi, E.; Pravitasari, A. Characterizing Industrial-Dominated Suburban Formation Using Quantitative Zoning Method: The Case of Bekasi Regency, Indonesia. Sustainability 2020, 12, 8094. [Google Scholar] [CrossRef]
  14. Firman, T. Potential Impacts of Indonesia’s Fiscal Decentralisation Reform on Urban and Regional Development: Towards a New Pattern of Spatial Disparity. Space Polity 2003, 7, 247–271. [Google Scholar] [CrossRef]
  15. Talitha, T.; Firman, T.; Hudalah, D. Welcoming Two Decades of Decentralization in Indonesia: A Regional Development Perspective. Territ. Politics Gov. 2020, 8, 690–708. [Google Scholar] [CrossRef]
  16. Indraprahasta, G.S.; Derudder, B.; Hudalah, D. Local Institutional Actors and Globally Linked Territorial Development in Bekasi District: A Strategic Coupling? Singap. J. Trop. Geogr. 2019, 40, 219–238. [Google Scholar] [CrossRef]
  17. Hudalah, D.; Viantari, D.; Firman, T.; Woltjer, J. Industrial Land Development and Manufacturing Deconcentration in Greater Jakarta. Urban Geogr. 2013, 34, 950–971. [Google Scholar] [CrossRef]
  18. Winarso, H.; Hudalah, D.; Firman, T. Peri-Urban Transformation in the Jakarta Metropolitan Area. Habitat Int. 2015, 49, 221–229. [Google Scholar] [CrossRef]
  19. Firman, T.; Fahmi, F.Z. The Privatization of Metropolitan Jakarta’s (Jabodetabek) Urban Fringes: The Early Stages of “Post-Suburbanization” in Indonesia. J. Am. Plan. Assoc. 2017, 83, 68–79. [Google Scholar] [CrossRef]
  20. Peraturan Pemerintah Republik Indonesia. Kawasan Industri (Industrial Park/Estate) Regulation. Available online: https://jdih.esdm.go.id/peraturan/PP%2010%20Thn%201989.pdf (accessed on 20 February 2022).
  21. Indraprahasta, G.S.; Derudder, B.; Koelemaij, J. Global-Local Dynamics in the Transformation of the Jakarta Metropolitan Area into a Global City-Region. Disp Plan. Rev. 2018, 54, 52–62. [Google Scholar] [CrossRef]
  22. Ministry of Industry of the Republic of Indonesia. List of Large-Scale Industrial Estates in Indonesia. Available online: https://kemenperin.go.id/kawasan (accessed on 13 November 2021).
  23. Bekasi Regency’s Statistical Agency [BPS]. Gross Regional Domestic Product of Bekasi Regency 2016–2020; Bekasi Regency’s Statistical Agency: Bekasi, Indonesia, 2021. [Google Scholar]
  24. Kurnianti, D.N.; Rustiadi, E.; Baskoro, D.P.T. Land Use Projection for Spatial Plan Consistency in Jabodetabek. Indones. J. Geogr. 2015, 47, 124–131. [Google Scholar] [CrossRef] [Green Version]
  25. Hu, Z.; Wang, Y.; Liu, Y.; Long, H.; Peng, J. Spatio-Temporal Patterns of Urban-Rural Development and Transformation in East of the “Hu Huanyong Line”, China. ISPRS Int. J. Geo Inf. 2016, 5, 24. [Google Scholar] [CrossRef] [Green Version]
  26. Liu, J.; Liu, Y.; Yan, M. Spatial and Temporal Change in Urban-Rural Land Use Transformation at Village Scale—A Case Study of Xuanhua District, North China. J. Rural Stud. 2016, 47, 425–434. [Google Scholar] [CrossRef]
  27. Liu, Y.; Yang, R. The Spatial Pattern Measure of Urban-Rural Development Transformation in the Bohai Rim Region in China. Acta Geogr. Sin. 2015, 70, 248–256. [Google Scholar] [CrossRef]
  28. Yang, Y.; Liu, Y.; Li, Y.; Li, J. Measure of Urban-Rural Transformation in Beijing-Tianjin-Hebei Region in the New Millennium: Population-Land-Industry Perspective. Land Use Policy 2018, 79, 595–608. [Google Scholar] [CrossRef]
  29. Wang, Y.; Liu, Y.; Li, Y.; Li, T. The Spatio-Temporal Patterns of Urban-Rural Development Transformation in China since 1990. Habitat Int. 2016, 53, 178–187. [Google Scholar] [CrossRef]
  30. Long, H. Land Use Transition and Rural Transformation Development. Prog. Geogr. 2012, 31, 131–138. [Google Scholar]
  31. Indraprahasta, G.S. The Potential of Urban Agriculture Development in Jakarta. Procedia Environ. Sci. 2013, 17, 11–19. [Google Scholar] [CrossRef] [Green Version]
  32. Gandharum, L.; Hartono, D.M.; Karsidi, A.; Ahmad, M. Monitoring Urban Expansion and Loss of Agriculture on the North Coast of West Java Province, Indonesia, Using Google Earth Engine and Intensity Analysis. Sci. World J. 2022, 2022, 3123788. [Google Scholar] [CrossRef]
  33. Divigalpitiya, P.; Nurul Handayani, K. Measuring the Urban Expansion Process of Yogyakarta City in Indonesia: Urban Expansion Process and Spatial and Temporal Characteristics of Growing Cities. Int. Rev. Spat. Plan. Sustain. Dev. 2015, 3, 18–32. [Google Scholar] [CrossRef] [Green Version]
  34. Liu, Y.; Hu, Z.; Li, Y. Process and Cause of Urban-Rural Development Transformation in the Bohai Rim Region, China. J. Geogr. Sci. 2014, 24, 1147–1160. [Google Scholar] [CrossRef] [Green Version]
  35. Hakim, I.; Parolin, B. Spatial Structure and Spatial Impacts of the Jakarta Metropolitan Area: A Southeast Asian EMR Perspective. Int. J. Civ. Environ. Struct. Constr. Archit. Eng. 2008, 2, 227–235. [Google Scholar]
  36. Liang, X.; Guan, Q.; Clarke, K.C.; Liu, S.; Wang, B.; Yao, Y. Understanding the Drivers of Sustainable Land Expansion Using a Patch-Generating Land Use Simulation (PLUS) Model: A Case Study in Wuhan, China. Comput. Environ. Urban Syst. 2021, 85, 101569. [Google Scholar] [CrossRef]
  37. Liu, Q.; Yang, D.; Cao, L.; Anderson, B. Assessment and Prediction of Carbon Storage Based on Land Use/Land Cover Dynamics in the Tropics: A Case Study of Hainan Island, China. Land 2022, 11, 244. [Google Scholar] [CrossRef]
  38. Zhang, S.; Zhong, Q.; Cheng, D.; Xu, C.; Chang, Y.; Lin, Y.; Li, B. Coupling Coordination Analysis and Prediction of Landscape Ecological Risks and Ecosystem Services in the Min River Basin. Land 2022, 11, 222. [Google Scholar] [CrossRef]
  39. Prayitno, G.; Sari, N.; Hasyim, A.W.; Nyoman Widhi, S.W. Land-Use Prediction in Pandaan District Pasuruan Regency. Int. J. GEOMATE 2020, 18, 64–71. [Google Scholar] [CrossRef]
  40. Yulianto, F.; Maulana, T.; Khomarudin, M.R. Analysis of the Dynamics of Land Use Change and Its Prediction Based on the Integration of Remotely Sensed Data and CA-Markov Model, in the Upstream Citarum Watershed, West Java, Indonesia. Int. J. Digit. Earth 2019, 12, 1151–1176. [Google Scholar] [CrossRef]
  41. Ghani, G.A.; Dimyati, M.; Damayanti, A. Prediction of Land Cover and Land Surface Temperature in Kuta Selatan Sub-District, Bali Province. Int. J. Adv. Sci. Eng. Inf. Technol. 2021, 11, 130–138. [Google Scholar] [CrossRef]
  42. Ricky, E.R.; Barus, B. A Projection of Land Needed for Settlements and Conversion of Paddy Fields in Solok City. J. Reg. City Plan. 2017, 28, 186–203. [Google Scholar] [CrossRef] [Green Version]
  43. Zivanovic, V. The Role of Nodal Centers in Achieving Balanced Regional Development. J. Geogr. Inst. Jovan Cvijic SASA 2017, 67, 69–84. [Google Scholar] [CrossRef]
  44. Liu, K.; Murayama, Y.; Ichinose, T. Exploring the Relationship between Functional Urban Polycentricity and the Regional Characteristics of Human Mobility: A Multi-View Analysis in the Tokyo Metropolitan Area. Cities 2021, 111, 103109. [Google Scholar] [CrossRef]
  45. Henny, C.; Meutia, A.A. Urban Lakes in Megacity Jakarta: Risk and Management Plan for Future Sustainability. Procedia Environ. Sci. 2014, 20, 737–746. [Google Scholar] [CrossRef] [Green Version]
  46. Republic of Indonesia Government. Rencana Tata Ruang Kawasan Perkotaan Jakarta, Bogor, Depok, Tangerang, Bekasi, Puncak, Dan Cianjur “Jakarta Megacity’s Spatial Planning”. Available online: https://jdih.setkab.go.id/PUUdoc/176105/Perpres_60_Tahun_2020.pdf (accessed on 13 November 2021).
  47. Forget, Y.; Linard, C.; Gilbert, M. Supervised Classification of Built-up Areas in Sub-Saharan African Cities Using Landsat Imagery and Openstreetmap. Remote Sens. 2018, 10, 1145. [Google Scholar] [CrossRef] [Green Version]
  48. Firman, T. The Continuity and Change in Mega-Urbanization in Indonesia: A Survey of Jakarta-Bandung Region (JBR) Development. Habitat Int. 2009, 33, 327–339. [Google Scholar] [CrossRef]
  49. Fahmi, F.Z.; Hudalah, D.; Rahayu, P.; Woltjer, J. Extended Urbanization in Small and Medium-Sized Cities: The Case of Cirebon, Indonesia. Habitat Int. 2014, 42, 1–10. [Google Scholar] [CrossRef]
  50. Irawati, M. Agricultural Land Conversion Mechanisms, Internal Migrations, and Housing Policy: Case Studies of Industrial Estates in the Northern Cikarang, West Java Province, Indonesia. In Proceedings of the IOP Conference Series: Earth and Environmental Science, Volume 556, The 6th International Conference of Jabodetabek Study Forum, Bogor, Indonesia, 29–30 August 2018. [Google Scholar]
  51. Herlambang, S.; Leitner, H.; Tjung, L.J.; Sheppard, E.; Anguelov, D. Jakarta’s Great Land Transformation: Hybrid Neoliberalisation and Informality. Urban Stud. 2019, 56, 627–648. [Google Scholar] [CrossRef]
  52. Dorodjatoen, A. The Emergence of Jakarta-Bandung Mega-Urban Region and Its Future Challenges. J. Reg. City Plan. 2009, 20, 15–33. [Google Scholar]
  53. Budi, D.; >Herwindiati, D.E.; Hendryli, J. Land use change using least absolute shrinkage and selection operator regression in jakarta’s buffer cities. In Proceedings of the 2021 IEEE 11th IEEE Symposium on Computer Applications & Industrial Electronics (ISCAIE), Penang, Malaysia, 3–4 April 2021. [Google Scholar]
  54. Yang, J.; Gong, J.; Tang, W.; Liu, C. Patch-Based Cellular Automata Model of Urban Growth Simulation: Integrating Feedback between Quantitative Composition and Spatial Configuration. Comput. Environ. Urban Syst. 2020, 79, 101402. [Google Scholar] [CrossRef]
  55. Saaty, T.L. Decision Making—the Analytic Hierarchy and Network Processes (AHP/ANP). J. Syst. Sci. Syst. Eng. 2004, 13, 1–35. [Google Scholar] [CrossRef]
  56. Goepel, K. Implementation of an Online Software Tool for the Analytic Hierarchy Process (AHP-OS). Int. J. Anal. Hierarchy Process 2018, 10, 469–487. [Google Scholar] [CrossRef] [Green Version]
  57. Saaty, R.W. The Analytic Hierarchy Process-What It Is and How It Is Used. Math. Model. 1987, 9, 161–176. [Google Scholar] [CrossRef] [Green Version]
  58. Anselin, L. Local Indicators of Spatial Association—LISA. Geogr. Anal. 1995, 27, 93–115. [Google Scholar] [CrossRef]
  59. Pravitasari, A.E.; Rustiadi, E.; Mulya, S.P.; Fuadina, L.N. Developing Regional Sustainability Index as a New Approach for Evaluating Sustainability Performance in Indonesia. Environ. Ecol. Res. 2018, 6, 157–168. [Google Scholar] [CrossRef]
  60. Kurnia, A.A.; Rustiadi, E.; Pravitasari, A.E. Cluster Analysis and Spatial Pattern Approaches in Identifying Development Pattern of Bodebek Region, West Java. In Proceedings of the SPIE—The International Society for Optical Engineering, Bogor, Indonesia, 24 December 2019; Volume 11372. [Google Scholar] [CrossRef]
  61. Wei, C.; Wang, Z.; Lan, X.; Zhang, H.; Fan, M. The Spatial-Temporal Characteristics and Dilemmas of Sustainable Urbanization in China: A New Perspective Based on the Concept of Five-in-One. Sustainability 2018, 10, 4733. [Google Scholar] [CrossRef] [Green Version]
  62. Gutiérrez, A.; Delclòs, X. The Uneven Distribution of Evictions as New Evidence of Urban Inequality: A Spatial Analysis Approach in Two Catalan Cities. Cities 2016, 56, 101–108. [Google Scholar] [CrossRef]
  63. Widyastuti, A.Y. Kemenperin: Pabrik Kembang Api Harus di Kawasan Industri Ministry of Industry: Fireworks Factory Must be in Industrial Area. Available online: https://bisnis.tempo.co/read/1031155/kemenperin-pabrik-kembang-api-harus-di-kawasan-industri (accessed on 17 November 2021).
  64. Tangerang Regency’s Statistical Agency [BPS]. Gross Regional Domestic Product of Tangerang Regency 2016–2020; Tangerang: Banten, Indonesia, 2021. [Google Scholar]
  65. Yang, R.; Luo, F.; Ren, F.; Huang, W.; Li, Q.; Du, K.; Yuan, D. Identifying Urban Wetlands through Remote Sensing Scene Classification Using Deep Learning: A Case Study of Shenzhen, China. ISPRS Int. J. Geo-Inf. 2022, 11, 131. [Google Scholar] [CrossRef]
  66. Yan, Y.; Liu, H.; Wang, N.; Yao, S. How Does Low-Density Urbanization Reduce the Financial Sustainability of Chinese Cities? A Debt Perspective. Land 2021, 10, 981. [Google Scholar] [CrossRef]
  67. Indraprahasta, G.S.; Derudder, B. Probing the Position of the Jakarta Metropolitan Area in Global Inter-Urban Networks through the Lens of Manufacturing Firms. Asian Geogr. 2017, 34, 147–167. [Google Scholar] [CrossRef] [Green Version]
  68. Wang, S.; Tan, S.; Yang, S.; Lin, Q.; Zhang, L. Urban-Biased Land Development Policy and the Urban-Rural Income Gap: Evidence from Hubei Province, China. Land Use Policy 2019, 87, 104066. [Google Scholar] [CrossRef]
  69. Santosa, S.; Rustiadi, E.; Mulyanto, B.; Murtilaksono, K.; Rachman, N.F.; Resources, L.; Sciences, C. Modeling on Establishment of Sustainable Paddy Field Zone in Bekasi Regency, Indonesia. J. Environ. Earth Sci. 2015, 5, 79–90. [Google Scholar]
  70. Vollmer, D.; Pribadi, D.O.; Remondi, F.; Rustiadi, E.; Grêt-Regamey, A. Prioritizing ecosystem services in rapidly urbanizing river basins: A spatial multi-criteria analytic approach. Sustain. Cities Soc. 2016, 20, 237–252. [Google Scholar] [CrossRef]
  71. Pribadi, D.O.; Pauleit, S. Peri-Urban Agriculture in Jabodetabek Metropolitan Area and Its Relationship with the Urban Socioeconomic System. Land Use Policy 2016, 55, 265–274. [Google Scholar] [CrossRef]
  72. Pribadi, D.O.; Zasada, I.; Müller, K.; Pauleit, S. Multifunctional Adaption of Farmers as Response to Urban Growth in the Jabodetabek Metropolitan Area, Indonesia. J. Rural Stud. 2017, 55, 100–111. [Google Scholar] [CrossRef]
  73. Firman, T. New Town Development in Jakarta Metropolitan Region: A Perspective of Spatial Segregation. Habitat Int. 2004, 28, 349–368. [Google Scholar] [CrossRef]
  74. Firman, T. Rural to Urban Land Conversion in Indonesia during Boom and Bust Periods. Land Use Policy 2000, 17, 13–20. [Google Scholar] [CrossRef]
  75. Bekasi Regency Government. Bekasi Regency’s Spatial Plan 2011–2031; Bekasi Regency Government: Bekasi, Indonesia, 2011; pp. 1–41.
  76. Tangerang Regency Government. Tangerang Regency’s Spatial Plan 2011–2031 2011, 1–52.
  77. Agung Sedayu Group. PIK 2 Masterplan: 1000 Ha Total Area. Available online: http://pik2-asg.com/wp-content/uploads/2018/05/PRESENTASI-KAVDEV-External-18-02-10.pdf (accessed on 20 February 2022).
  78. Pravitasari, A.E.; Saizen, I.; Rustiadi, E. Towards Resilience of Jabodetabek Megacity: Developing Local Sustainability Index with Considering Local Spatial Interdependency. Int. J. Sustain. Futur. Hum. Secur. 2016, 4, 27–34. [Google Scholar] [CrossRef] [PubMed]
  79. Pribadi, D.O.; Vollmer, D.; Pauleit, S. Impact of Peri-Urban Agriculture on Runoff and Soil Erosion in the Rapidly Developing Metropolitan Area of Jakarta, Indonesia. Reg. Environ. Chang. 2018, 18, 2129–2143. [Google Scholar] [CrossRef]
Figure 1. Jakarta megacity or Jakarta Metropolitan Region.
Figure 1. Jakarta megacity or Jakarta Metropolitan Region.
Land 11 00670 g001
Figure 2. Study area location.
Figure 2. Study area location.
Land 11 00670 g002
Figure 3. Spatial constraint map based on regency spatial plan.
Figure 3. Spatial constraint map based on regency spatial plan.
Land 11 00670 g003
Figure 4. Example of the driven factor used in this study.
Figure 4. Example of the driven factor used in this study.
Land 11 00670 g004
Figure 5. The framework of landcover prediction, modified from Liang et al. [36].
Figure 5. The framework of landcover prediction, modified from Liang et al. [36].
Land 11 00670 g005
Figure 6. The distribution of LSIEP and the built-up area in 2015.
Figure 6. The distribution of LSIEP and the built-up area in 2015.
Land 11 00670 g006
Figure 7. LUC around the selected LSIEP location.
Figure 7. LUC around the selected LSIEP location.
Land 11 00670 g007
Figure 8. Regional typology (2005–2015) based on the RULT index.
Figure 8. Regional typology (2005–2015) based on the RULT index.
Land 11 00670 g008
Figure 9. LISA Map of 2005–2015 RULT Index value difference.
Figure 9. LISA Map of 2005–2015 RULT Index value difference.
Land 11 00670 g009
Figure 10. Regional typology prediction (2025) based on the RULT index.
Figure 10. Regional typology prediction (2025) based on the RULT index.
Land 11 00670 g010
Table 1. A list of data used in this study.
Table 1. A list of data used in this study.
CategoryDataData Resource
Land use/cover (LUC) dataLUC data in 2005, 2015, and 2020CRESTPENT, IPB University for 2005 and 2015 LUC data; Landsat Satellite Imagery (2020 LUC raw data)
Driving Factor
(1)
Proximity to LSIEP locations,
(2)
Proximity to toll road gates,
(3)
Proximity to primary, secondary, and tertiary roads and
(4)
Proximity to the commuter railway station
Ministry of Industry, the Republic of Indonesia, 2021 [22]
OpenStreetMap (https://www.openstreetmap.org/) (accessed on 20 December 2021)
Spatial Constraint
(1)
Bekasi Regency’s spatial plan
(2)
Tangerang Regency’s spatial plan
Bekasi Regency’s Government
Tangerang Regency’s Government
Table 2. List of LSIEP in Bekasi and Tangerang regencies.
Table 2. List of LSIEP in Bekasi and Tangerang regencies.
CodeIndustrial Estate/Park NameTotal Area (ha)Location (Subdistrict)
B1Indonesia–China Integrated Industrial Park/Estate205Serang Baru/Cikarang Pusat
B2Bekasi International Industrial Estate200Cikarang Selatan
B3MM2100 Industrial Town BFIE1700Cikarang Barat
B4MM2100 Industrial Town MMID805Cikarang Barat
B5Jababeka Industrial Park/Estate2267Cikarang Utara
B6East Jakarta Industrial Park/Estate320Cikarang Selatan
B7Gobel Industrial Park/Estate54Cikarang Barat
B8Marunda Center Industrial Park/Estate60Tarumajaya
B9Greenland International Industrial Center (GIIC)1700Cikarang Pusat
B10Lippo Cikarang Industrial Park/Estate1645Cikarang Selatan
T1Millennium Industrial Estate1800Panongan
T2Pasar Kemis Industrial Park74Pasar Kemis
T3Cikupamas Industrial and Warehouse Park/Estate250Cikupa
T4Purati Kencana Alam Industrial Park/Estate70Cikupa
T5Griya Idola Industrial Park99Cikupa
T6Sumber Rezeki Industrial Park/Estate72Tigaraksa
Source: Ministry of Indonesia, the Republic of Indonesia, 2021 [22].
Table 3. List of experts for the AHP.
Table 3. List of experts for the AHP.
CodeExpert’s Institution
A1Regional Development Planning Division, Faculty of Agriculture, IPB University
A2Department of Urban and Regional Planning, University of Trisakti
L1Department of Regional Development Planning (Bappeda), Bekasi Regency
L2Department of Regional Development Planning (Bappeda), Tangerang Regency
C1Ministry of National Development Planning (Bappenas), Republic of Indonesia
C2Ministry of Agrarian Affairs and Spatial Planning, Republic of Indonesia
D1Developer
U1Nusantara Urban Advisory (Urban and Regional Planning Consultant)
Table 4. List of Weight for each Criterion.
Table 4. List of Weight for each Criterion.
CodeLUC CriteriaWeightDirection
ITSIndustrial, Trade, and Service Area0.341+
SASettlement Area0.201+
DBLDry and Bare Land0.085
WALWet-agricultural Land0.231
FRForest (Mangrove)0.061
MPMixed Plantation0.081
Additional information: (+) means that the LUC criterion is in line with the rural to urban land transformation, while (–) means otherwise; TA is the village’s total area; i is the village of i.
Table 5. Built-up Area (BA) coverage and annual growth rate in 2005-2015.
Table 5. Built-up Area (BA) coverage and annual growth rate in 2005-2015.
Regency% BA’s Coverage to Total AreaBA’s Annual
Growth Rate (%)
2005 (%)2015 (%)
Bekasi10.515.84.2
Tangerang12.322.86.4
Table 6. Composition of Built-up (BA) Area and Its annual growth rate.
Table 6. Composition of Built-up (BA) Area and Its annual growth rate.
Regency% Share to Total Area (2015)The Annual Growth Rate
(2005–2015) (%)
ITSSAITSSA
Bekasi19.980.11.25.1
Tangerang 17.682.42.27.6
Both regencies18.781.31.66.3
Table 7. Built-up area (BA) coverage and annual growth rate.
Table 7. Built-up area (BA) coverage and annual growth rate.
Regency% BA’s Coverage to
Total Area in
2025 (%)
BA’s Annual
Growth Rate
Annual Growth Rate
from 2015–2025 (%)
2005–2015 (%)2015–2025 (%)ITSSA
Bekasi23.14.23.91.74.4
Tangerang28.96.43.22.93.2
Publisher’s Note: MDPI stays neutral with regard to jurisdictional claims in published maps and institutional affiliations.

Share and Cite

MDPI and ACS Style

Kurnia, A.A.; Rustiadi, E.; Fauzi, A.; Pravitasari, A.E.; Saizen, I.; Ženka, J. Understanding Industrial Land Development on Rural-Urban Land Transformation of Jakarta Megacity’s Outer Suburb. Land 2022, 11, 670. https://doi.org/10.3390/land11050670

AMA Style

Kurnia AA, Rustiadi E, Fauzi A, Pravitasari AE, Saizen I, Ženka J. Understanding Industrial Land Development on Rural-Urban Land Transformation of Jakarta Megacity’s Outer Suburb. Land. 2022; 11(5):670. https://doi.org/10.3390/land11050670

Chicago/Turabian Style

Kurnia, Adib Ahmad, Ernan Rustiadi, Akhmad Fauzi, Andrea Emma Pravitasari, Izuru Saizen, and Jan Ženka. 2022. "Understanding Industrial Land Development on Rural-Urban Land Transformation of Jakarta Megacity’s Outer Suburb" Land 11, no. 5: 670. https://doi.org/10.3390/land11050670

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop