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Land-use patterns in Xiamen City in 1990 (a), 2000 (b), and 2010 (c). These maps were used to compute enrichment factors and verify large neighborhood effects. 

Land-use patterns in Xiamen City in 1990 (a), 2000 (b), and 2010 (c). These maps were used to compute enrichment factors and verify large neighborhood effects. 

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Urban cellular automata (CA) models are broadly used in quantitative analyses and predictions of urban land-use dynamics. However, most urban CA developed with neighborhood rules consider only a small neighborhood scope under a specific spatial resolution. Here, we quantify neighborhood effects in a relatively large cellular space and analyze their...

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... P ij is the total development probability of cell ( i , j ) at moment t in the new urban CA model; ( P l ) ij is the local development suitability of cell ( i , j ), which is calculated with the method proposed in Section 2.1 and has the same inputs and parameters as the Logistic-CA model proposed in Section 2.2; ( P U ) ij is the impact of the 3 Â 3 kernel neighborhood at moment t À 1; con () is the constraints on urban growth at moment t À 1; ( P ln ) ij represents large neighborhood effects at moment t À 1; and P r is the stochastic perturbation term. The model presented here is called Logistic- LNCA, which considers extended neighborhood effects. The Logistic-CA model proposed in Section 2.2 does not have such considerations. The components/procedures of the urban CA considering large neighborhood effects are illustrated in Fig. 2. The simulation experiment was designed to include a model calibration in 1990 e 2000 (Sections 3.4, 3.5, and 3.6) and an independent validation in 2000 e 2010 (Section 3.7). Referring to pre- vious studies on urban CA modeling and testing (Feng and Liu, 2013; Feng et al., 2011; Li et al., 2014; Van Vliet et al., 2013), the generated transitional rules were applied to urban expansion simulations during the same two periods. During the validation stage, observed land-use changes were treated as an independent data set and the transition rules calibrated during the fi rst period were used to predict urban expansion dynamics at the end of second period (Van Vliet et al., 2013). According to Eqs. (2) and (3), urban CA models are mainly characterized by model inputs and parameter settings. From this point of view, the Logistic-CA model is de fi ned by a series of spatial variables and corresponding parameter values used for determining local development suitability. In contrast, the Logistic-LNCA model also includes inputs and parameters for the extended neighborhood rule, except those for the local development suitability component. During the independent validation period (2000 e 2010), the parameter con fi gurations related to the afore- mentioned transition rules in the two urban CA models were all obtained during the calibration period (1990 e 2000), and the model inputs remained unchanged. Xiamen City in southeast China, with an area of 1574 km , was selected as the study area for this research. In 2010, Xiamen City had a total population of 1,802,060 (Tang et al., 2013; XCSB, 2011). Its urban landscape consisted of two urban centers (Siming District and Huli District on Xiamen Island) and four sub-centers outside the island (Jimei, Haicang, Tongan, and Xiangan). Recently, Haicang, Jimei, and Xiangan have gradually become the new industrial centers. Xiamen City is one of the fi rst four special economic zones in China. Its urbanization has accelerated over the past three decades, and its built-up area increased from 34.01 km 2 in 1989 to 197 km 2 in 2008 (Chen and Xu, 2005; XCSB, 2008). Such rapid urban expansion poses serious challenges for the region in terms of sustainable development, environmental loads, and ecosystem ser- vices (Shaker, 2015). Land-use maps of the study area in 1990, 2000, and 2010 were obtained from the Institute of Remote Sensing and Digital Earth of the Chinese Academy of Sciences. Each land-use map has a 30 Â 30 m spatial resolution and includes farmland, woodland, grassland, urban residential land, industrial land, water, and rural areas (Fig. 3). First, the land-use datasets from 1990 to 2000 were used to compute the extended enrichment factors of different land-use types in the neighborhood of residential land during the periods of 1990 e 2000 and 2000 e 2010 and to verify the existence of neighborhood effects. Subsequently, the land-use maps from 1990, 2000, and 2010 were regrouped into three categories (built-up land, non built-up land, and water bodies). Industrial land and residential land were merged into built-up land, and the spatial resolution remained unchanged during the aggregation process. The reclassi fi ed data for 1990 and 2000 were used to calculate the extended enrichment factor and con fi gure the initial states of the Logistic-LNCA model during the simulation periods. When measuring neighborhood effects with the enrichment factor formula, the enrichment factors of all land-use types can be computed for all locations of a speci fi c type or only for locations that have changed their land-use states/types (Van Vliet et al., 2013). We used the second approach to calculate the enrichment factors for each land-use type for locations that changed to industrial or urban residential land during the simulation period. We also determined the average enrichment factor through logistic trans- formation for comparison and curve drawing in the speci fi c neighborhood scope. The extended enrichment factor of urban or industrial land near new residential land was greater than that of agriculture, woodland, grassland, water, or rural land, but its value decreased with distance (Fig. 4), suggesting that new urban and industrial land are more likely to emerge in the neighborhood of urban land use than other land-use types. The depicted enrichment factor curves indicated that the in fl uences of neighboring land-use types decrease with increasing neighborhood radius. However, the measured extended enrichment factors for urban or industrial land in certain large neighborhood scopes (1 e 3 km, equal to 30 e 100 cells in the neighborhood radius) of new urban land still maintained relatively high values. The extended enrichment factor curves presented an undulating pattern. These neighborhood characteristics demonstrated that there was a considerably large neighborhood effect in cellular space. Compared with traditional small neighborhood windows that generally cover several cells (for instance, 1 e 4 cells, up to a 9 Â 9 Moore neighborhood) in the neighborhood radius, it is more appropriate to construct the transition rules of the urban CA model using a large neighborhood. To further estimate the in fl uence of a particular large neighborhood, the values of D r , R min , and R max in Eq. (7) were set to 10, 11, and 81, respectively. Thus, the large neighborhood of the central cell was divided into seven annular bands, and the radius of each annular band was 10 cells. It is worth noting that the window size used here was visually obtained from Fig. 4, and its in fl uence on the model results is still unknown. The large neighborhood module dynamically calculated the extended enrichment factors for the central cell at different annular bands. Similarly, whether the cell was to become built-up land was treated as the dependent variable, and 20% of the sample points were extracted through proportional random-strati fi ed sampling. The obtained sample data were used to perform a binary logistic regression in SPSS. Eq. (9) was used to calibrate the model, and parameter values of the large neighborhood module were obtained. Before executing the logistic regression calibration, the enrichment factor for the large neighborhood was normalized and the standardization was realized ...

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