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Available online at www.sciencedirect.com ScienceDirect Procedia - Social and Behavioral Sciences 227 ( 2016 ) 3 10 CITIES 2015 International Conference, Intelligent Planning Towards Smart Cities, CITIES 2015, 3-4 November 2015, Surabaya, Indonesia Prediction of urban growth using the bucket model I Made IM Brunner a* a Department of Environmental Engineering, Universitas Bakrie, Jl. HR Rasuna Said Kav. C22, Jakarta Selatan 12920, Indonesia Abstract A model has been developed to figure out possible population growth pattern in a city. The model suggests that new inhabitants will first saturate the developed urban area, then the overflow fill the partially developed urban area, and lastly move to the adjacent area outside of those two mentioned zones. The last zone is mostly located in an existing agricultural site, which is converted into urban area after the adjacent areas are developed. This model was generated based on spatial and other datasets from the City and County of Honolulu, Hawaii. Those data were analyzed and manipulated mathematically to create the grid map system, a uniform vector grid cell that is filled with demographic, socio-economic, and land use data. This deterministic model is relatively simple yet powerful enough to help planners in decision making process on projecting infrastructures in the future of a city. 2016 The Authors. Published by Elsevier by Elsevier Ltd. Ltd. This is an open access article under the CC BY-NC-ND license (http://creativecommons.org/licenses/by-nc-nd/4.0/). Peer-review under responsibility of the organizing committee of CITIES 2015. Peer-review under responsibility of the organizing committee of CITIES 2015 Keywords: Urban Growth; Spatial Model; GIS; Honolulu. 1. Introduction This paper attempts to discuss the development of an urban growth model that can be used to assist decision makers, planners, or engineers to look at the possible growth pattern of a city. This Bucket model was created * Corresponding author. Tel.: +62 81317821085; fax: +0-000-000-0000. E-mail address: imade.brunner@gmail.com 1877-0428 2016 The Authors. Published by Elsevier Ltd. This is an open access article under the CC BY-NC-ND license (http://creativecommons.org/licenses/by-nc-nd/4.0/). Peer-review under responsibility of the organizing committee of CITIES 2015 doi:10.1016/j.sbspro.2016.06.036

4 I. Made IM Brunner / Procedia - Social and Behavioral Sciences 227 ( 2016 ) 3 10 based on a uniform 0.1 square-miles or around 25.9 hectares grid (approximately 508.6 x 508.6 square-meters) cells. This checker-board pattern cells were populated with number of population who reside in Honolulu, Hawaii. The population data were derived from the 2000 US Census Data and spatially manipulated by overlying the land use, zoning, and tax-map key (TMK) maps. The cells were also filled with number of possible jobs based on the US Economic Census, County Business Pattern, and TMK data. Land use data consisted of information regarding the allocation of land either for urban, rural, agriculture, or conservation purposes. Although Honolulu is famous for its images of sandy beaches and swaying palm trees, isolated location and extremely centralized government system making it an ideal location for the development of this urban growth model. Honolulu which located on the island of Oahu has an extensive collection of publicly available spatial datasets, as well as other data. Nonetheless, those data come from different sources, which increase level of difficulty in analyzing and comparing them. Creating a grid-based mapping system by spatially converting maps with different size of boundaries into uniform cells could be a possible solution. Data from the original maps were digitally manipulated and stored in vector based cells. The cells hold robust information to assist researchers for various applications. The Bucket model is based on the assumption that growth first occurs in urban areas already being developed. Once density of an urban area becomes saturated, growth moves to partially developed lands adjacent to the urban district, finally spreads into agricultural and open zone areas. The model could provide a broad picture of where growth could arise based on population increase and how rigidly growth management is applied. The growth pattern is determined by set parameters, which can be related to urban policies stipulated by the government or infrastructure development plans. Decision makers, planners, engineers, or other entities could participate in shaping the model by providing the allowable population increase in an area, among others. 2. Methods 2.1. Grid Map The checker-board pattern grid map is believed to be more preferable than the original thematic maps. There are several reasons supporting the idea. Firstly, the shapes and sizes of the grid map are equal whereas those of the original thematic maps are not uniform. Secondly, grid map could provide a way in screening out areas that are not suitable for analysis, such as uninhabited areas within an administrative map. Thirdly, grid map is a solution that can be applied in disaggregating a larger size thematic polygon into smaller size cells. The 25.9 hectares vector type cell is applied because it is within 402.3 meters radius walking distance and about the size of a neighborhood. The distance between centroid of a cell and it adjacent one is between 508.6 to 719.4 meters. This distance is within a comfortable walking distance of 402.3 to 804.7 meters as suggested by the literature (Dittmar & Ohland, 2004; NJTransit, 1994; Regional Plan Association, 1997). The distance between the centroid of a cell and the centroid of second neighbor cells is between 1.1 to 1.5 kilometers. This distance is further than the comfortable walking distance but still within the walking impact zone of 1.2 kilometers as revealed in the study of ridership among housing and commercial developments near 4 rail stations in Canada (TCRP, 1995, p.31). The cell, since it is smaller than the size of a typical census block group, which can provide more detailed information. Another benefit is that the number of population within a cell can be directly compared to other cell to determine their density level. Analysis of population using this grid maps system has been applied in several studies (UH DURP & UHERO, 2015; Brunner, Kim & Yamashita, 2011; Kim, Brunner & Yamashita, 2006). Meanwhile, similar studies using a larger cell of 0.25 square-miles or around 64.75 hectares have been conducted for analysis of transit route in Logan, Utah (Ramirez & Seneviratne, 1996), as well as in south Placer County, California (Milam & Luo, 2008) to find out the correlation between land use development density and intensity with potential Bus Rapid Transit (BRT) stations location. Figure 1, Population Distribution on Oahu in 2000, shows the comparison between population distributions based on the 2000 Census Blockgroups and grid based map. The baseline population grid based map is more realistic than the 2000 Census Blockgroups map. Population on Oahu in reality resides mostly near the main roads, and most of the island interior mountainous areas are unpopulated. The blockgroup map does not have information that could separate populated and uninhabited areas. Hence, populations of a blockgroup are distributed evenly within the

I. Made IM Brunner / Procedia - Social and Behavioral Sciences 227 ( 2016 ) 3 10 5 entity boundary. Meanwhile, in the grid map system, populations are distributed based on the location of residential areas. Population count by blockgroup is also not directly correlated with population density. Population density could not be calculated directly since the size of blockgroup polygons are not equal, and there is possibility that some areas within a blockgroup could not be inhabited. The grid map system, however, shows that number of population automatically indicates level of population density. The transformation from blockgroup to grid level involved some mathematical manipulations. Hence, some level of differences in total number of population by blockgroups and grids is expected. The blockgroup data show that there were 876,156 people lived on Oahu during the 2000 Census. The grid map data show that the baseline population living on Oahu is 875,195 people or 961 less than the blockgroup data. This is a 0.11% difference relative to the census data. a b 2.2. The Bucket Model Fig. 1. Population Distribution on Oahu in 2000 by (a) Blockgroups; and (b) Grid-Based Structure The population of Oahu is projected to grow in the future. The Planning for Sustainable Tourism in Hawaii, Economic and Environmental Assessment Modeling Study (DBEDT, 2005, p.a3-32) projects that in 2030 Honolulu will be inhabited by 961,594 persons. A higher projection was reported in the Honolulu Transit Corridor Project Draft EIS (US FTA & DTS, 2008, p. 1-8), where 1,117,200 people are projected to be living on Oahu in 2030. The later study broke down the projected population distribution into 25 development plan areas. This study attempts to distribute the projected population on Oahu into a finer 25.9 hectare grid level within these 25 development plan zones. By allocating into grid level, the future population concentrations could be identified and transit systems could be aligned to better serve those areas. The distribution analysis was made on each development plan zone, which was more preferable than using an island-wide analysis. This allowed for a more realistic model of uneven population growth. The projected population distribution was done by applying the bucket approach. The logic of this idea is that additional inhabitants of a growth region would first saturate a developed urban area designated as Zone A, then fill a partially developed urban area Zone B, and lastly fill the areas adjacent to A and/or B which is called Zone C. Zone C, presently an agricultural site or undeveloped residential area, can be converted into an urban area after zones A and B are filled. In addition to these zones, there are two more zones in the bucket system Zone P and Zone X. Zone P indicates protected or conservation areas, while Zone X indicates urban areas not assigned for residential use (such as airports, harbors, and industrial zones). These latter zones are excluded from any further residential developments. Table 1, General Guidelines for Allocating the Bucket Zones, explains the general guidelines to allocate the bucket zones.

6 I. Made IM Brunner / Procedia - Social and Behavioral Sciences 227 ( 2016 ) 3 10 Table 1. General Guidelines for Allocating the Bucket Zones Bucket Type of Zoning Baseline Population P (Protected) Protected Any values X (Prohibited) A (Developed Urban Area) Agricultural 0 Military 0 Residential > 10 Military > 0 Business > 0 B (Partially Developed) Residential 0 to 10 C (Undeveloped Area) Residential 0 Agricultural > 0 Each grid cell is also filled with information on Development Plan Region based on its location, as well as bucket type. Type A bucket, based on information from table 1, is assigned to a cell where its zoning is residential area and number of population is greater than 10. If a cell that zoned as residential but has population less than 10, it will be assigned as bucket type B. Although the allocation of bucket type can be assigned using mathematical algorithm, a final touch by a person who familiar with the area should be applied. Once all cells are assigned with proper bucket type, number of additional population in 2030 can be allocated proportionally. For example, additional population for a Development Plan Region is 1000 persons, and within that region there are 10 bucket A cells, 50 bucket B, and no cells assigned for other types. Assume that the baseline population number for each grid within the region is steady. Planners or decision makers should set a number indicating the maximum population can be allocated for cell with type A, B, and C. Let say that the total space available for those 10 bucket A cells is 300, and for B is 2000. Immediately, 300 new populations can be distributed to A and 700 to the B. The 300 should not be equally distributed to those 10 cells, but should be based on the space available on each cell. Cells with more space available which also means has less baseline population, will have more new population in the future. The same ideas should also be applied in allocating population in type B or C. In a case that additional population is larger than the space available, a new maximum number should be set. Let say that the total space available for those 10 bucket A cells is 300, and for B is only 500. If 1000 new population need to be distributed, there are 200 would be excluded. This is actually a signal for planners or decision makers to go back to drawing board and decide of whether or not their population projection is feasible, or they should allow a higher density development in a region. 3. Result and Discussions The comparisons between the baseline with the projected population by development plan region is depicted on Table 2, Population Distributions in 2000 and 2030 by Development Plan Region. The baseline population distribution was calculated by querying the 2000 Census data by cell in the grid-based map. Data for the population in 2030 were gathered from the Honolulu Transit Corridor Project Draft EIS (US FTA & DTS, 2008, p. 1-8). The table also shows number baseline population living within the conservation areas. There are 38,689 persons out of 875,159 total baseline populations living within the conservation area adjacent to several development plan regions. The population of the conservation area is expected to remain steady through 2030. Therefore, the distribution of projected population is only applied to those who lived outside of the conservation area. The table also mentions that there are 34,068 population lived in Wahiawa region in 2000, and 1,366 of them lived in the adjacent conservation areas. The projected population for this region is 36,200, and those who lived in the conservation areas should remain the same as in baseline condition. Hence, 34,834 population need to be distributed in 2030 using the bucket approach. Table 2. Population Distributions in 2000 and 2030 by Development Plan Region

I. Made IM Brunner / Procedia - Social and Behavioral Sciences 227 ( 2016 ) 3 10 7 Development Plan Region Population Number in 2000 Lived outside of Total conservation area Lived inside of conservation area Population Number in 2030 Lived outside of Total conservation area Downtown 6,680 6,680 0 22,900 22,900 Kakaako 4,385 4,385 0 33,200 33,200 Moiliili-Ala Moana 37,572 37,572 0 48,800 48,800 Waikiki 22,331 22,331 0 22,900 22,900 Kaimuki-Waialae 54,532 51,363 3,169 57,800 54,631 Palama-Liliha 66,129 63,171 2,958 67,900 64,942 Kalihi-Iwilei 29,178 29,178 0 34,000 34,000 Airport-Pearl Harbor 12,666 12,666 0 12,500 12,500 Salt Lake-Aliamanu 54,390 49,963 4,427 54,300 49,873 Pearl City-Aiea 77,851 74,074 3,777 79,100 75,323 Ewa 44,447 44,447 0 90,500 90,500 Kapolei 11,382 11,382 0 55,500 55,500 Makakilo 13,823 13,823 0 29,500 29,500 Waipahu-Waikele 51,461 51,461 0 61,300 61,300 Waiawa 12,371 12,371 0 45,500 45,500 Mililani 48,762 48,762 0 53,400 53,400 Wahiawa 34,068 32,702 1,366 36,200 34,834 East Honolulu 46,947 39,937 7,010 51,000 43,990 Kaneohe 54,191 49,594 4,597 54,500 49,903 Kailua 63,812 59,389 4,423 63,600 59,177 Koolauloa 14,546 13,978 568 16,500 15,932 North Shore 18,380 18,219 161 20,500 20,339 Waianae 42,322 41,296 1,026 52,000 50,974 Makiki-Manoa 45,803 40,596 5,207 47,700 42,493 UH Manoa 7,166 7,166 0 6,100 6,100 TOTAL 875,195 836,506 38,689 1,117,200 1,078,511 Table 3, Population Distributions in 2030 by Development Plan Region Based on Calculation and Draft EIS Report, shows distribution of the projected population that was calculated using the bucket approach and the projected population numbers in each development plan from the Draft EIS report. The total population of both calculated and from the EIS Report are meant for those who lived in the development plan region and conservation area adjacent to associated development plan region. Note that the calculated population in all except four development plan regions (i.e. Airport - Pearl Harbor, Salt Lake Aliamanu, Kailua, and UH Manoa) shows relatively similar numbers as the 2030 population based on the Draft EIS. The 2030 population in those regions is higher than the Draft EIS numbers. This happens because the baseline population in those four regions is higher than the 2030 projection. The computation was designed to use the baseline population count if the projected number is lower than the baseline. Result of the computation using the bucket model is shown in Figure 2, Projected Population Distribution on Oahu by Grid in 2030. The Ewa, Kapolei, and Makakilo areas, which are located on the South-West of the island, show very contrast differences with the baseline condition. Denser population in those areas is expected to occur around existing developed locations. Those areas are also set as the new urban development to support the growth of the Downtown and Waikiki areas, which located on the South shore center of the island.

8 I. Made IM Brunner / Procedia - Social and Behavioral Sciences 227 ( 2016 ) 3 10 Table 3. Population Distributions in 2030 by Development Plan Region Based on Calculation and Draft EIS Report Development Plan Region Code Calculation Results Lived inside of conservation area Lived outside of conservation area Total Draft EIS Report Downtown 1 0 22,900 22,900 22,900 Kakaako 2 0 33,199 33,199 33,200 Moiliili - Ala Moana 3 0 48,799 48,799 48,800 Waikiki 4 0 22,900 22,900 22,900 Kaimuki - Waialae 5 3,169 54,629 57,798 57,800 Palama - Liliha 6 2,958 64,943 67,901 67,900 Kalihi - Iwilei 7 0 34,000 34,000 34,000 Airport - Pearl Harbor # 8 0 12,666 12,666 12,500 Salt Lake - Aliamanu # 9 4,427 49,963 54,390 54,300 Pearl City - Aiea 10 3,777 75,325 79,102 79,100 Ewa 11 0 90,513 90,513 90,500 Kapolei 12 0 55,526 55,526 55,500 Makakilo 13 0 29,509 29,509 29,500 Waipahu - Waikele 14 0 61,297 61,297 61,300 Waiawa 15 0 45,507 45,507 45,500 Mililani 16 0 53,398 53,398 53,400 Wahiawa 17 1,366 34,822 36,188 36,200 East Honolulu 18 7,010 43,986 50,996 51,000 Kaneohe 19 4,597 49,895 54,492 54,500 Kailua # 20 4,423 59,389 63,812 63,600 Koolauloa 21 568 15,911 16,479 16,500 North Shore 22 161 20,332 20,493 20,500 Waianae 23 1,026 50,942 51,968 52,000 Makiki Manoa 24 5,207 42,489 47,696 47,700 UH Manoa # 25 0 7,166 7,166 6,100 TOTAL 38,689 1,080,006 1,118,695 1,117,200 # Numbers of 2030 population in those regions are higher than the Draft EIS numbers. Total

I. Made IM Brunner / Procedia - Social and Behavioral Sciences 227 ( 2016 ) 3 10 9 Fig.2. Projected Population Distribution on Oahu by Grid in 2030 4. Conclusions There are several contributions of this study. The grid map used in this study provides several benefits. First, it can be used to overcome problems that exist with thematic maps that have irregular shaped and sized objects. Second, it can be used to screen out areas in the thematic polygon maps not suitable for development. Third, it can be used to disaggregate datasets in a larger area into a smaller grid level. Fourth, with a uniform grid size, data of a grid can be directly compared with other grids. The model allows many share-holders to contribute their thoughts in shaping the future of an urban area. Model simulation using different growth scenarios had been implemented in County of Kauai Important Agricultural Lands (IAL) study (UH DURP & UHERO, 2015). In that study, share-holders assessed three possible growth scenarios (i.e. No urban containment no growth management strategy applied; Limited urban containment such as resulting from bordering IAL and some allowance of urban development in non IAL agricultural areas; and Strict urban containment increased density allowances such as increasing height). Share-holders were involved in deciding the level of development allowed in each region. Planners then interpreted those levels into allowed population growth in the future. The process was done repeatedly until agreeable consensus was reached. The outcomes gave all parties the possible implication of their plans in years to come and the use of GIS map allowed share-holders to have a better understanding about the plans.

10 I. Made IM Brunner / Procedia - Social and Behavioral Sciences 227 ( 2016 ) 3 10 References Brunner, I.M., Kim, K., Yamashita, E. (2011). Identifying optimal transit alignments using AHP (Analytic Hierarchy Process) and GIS (Geographic Information Systems). Transportation Research Record, 2215, 59-66. Dittmar, H. & Ohland, G. (eds.). (2004). The new transit town: best practices in transit-oriented development. Washington, D.C.: Island Press. Kim, K., Brunner, I.M., Yamashita, E. (2006). Influence of land use, population, employment, and economic activity on accidents. Transportation Research Record, 1953, 56-64. Milam, R.T., and T. Luo. Land Use-Based Transit Planning. (2008). In Transportation Research Record: Journal of the Transportation Research Board, No.2063, Transportation Research Board of the National Academies, Washington D.C., pp. 143-148. NJTransit. (1994). Planning for transit-friendly land use a handbook for New Jersey communities. New Jersey: Author. Ramirez, A.I., and P.N. Seneviratne. (1996). Transit Route Design Applications Using Geographic Information Systems. In Transportation Research Record: Journal of the Transportation Research Board, No.1557, Transportation Research Board of the National Academies, Washington D.C., pp. 10-14. Regional Plan Association (RPA). (1997). Building transit-friendly communities a design and development strategy for the Tri-state metropolitan region. Retrieved from: http://www.rpa.org. State of Hawaii, Department of Business, Economic Development and Tourism (DBEDT). (2005). Planning for sustainable tourism in Hawaii: Economic and environmental assessment modeling study, modeling technical report. Honolulu: Author. Retrieved from: http://hawaii.gov/dbedt/info/visitor-stats/sustainable-tourism-project/drafts/modeling-technical-report.pdf Transit Cooperative Research Program (TCRP). (1995). Research results digest: An evaluation of the relationships between transit and urban form. Washington, D.C: Author. Retrieved from: http://onlinepubs.trb.org/onlinepubs/tcrp/tcrp_rrd_07.pdf. U.S. Department of Transportation Federal Transit Administration (US FTA) & City and Couty of Honolulu Department of Transportation Services (DTS). (2008). Honolulu high-capacity transit corridor project, Draft environmental impact statement. Honolulu: Authors University of Hawaii Department of Urban and Regional Planning and The University of Hawaii Economic Research Organization (UH DURP & UHERO). (2015). Kauai County Important Agricultural Lands Study, Final Report. Hawaii, Honolulu. Retrieved from: https://sites.google.com/site/kauaiial12/cok_ialstudy_finaldraft_071315.pdf?attredirects=0