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Procedia Environmental Sciences 32 ( 2016 ) 124 – 137

International Conference – The Environment at a Crossroads: SMART approaches for a sustainable future Peri-urban Areas and Land Use Structure in at LAU2 Level: An Exploratory Spatial Data Analysis

Cristina Lincarua*, Draga Atanasiub, Vasilica Ciucăc, Spera nţa Pirciogd

abcdLabour Market Department, National Scientific Research Institute for Labor and Social Protection - INCSMPS, 6-8 Povernei Street,, 010643, Romania

Abstract

The smart, sustainable and inclusive growth adopted by Europe 2020 demands new types of information as it is the land use data as an indicator of the land (a primary production factor) - the building block of any economy. Our method is based the article of Salvati & Carlucci (2014) regarding the Urban Growth and Land Use Structure, we develop an Exploratory Spatial Data Analysis ESDA (Method of Choropleth Maps and LISA, Anselin 2003, 2005) for identification of peri-urban areas in Romania at LAU2 level as lattice data (in Arc Gis, GeoDa) and statistical analysis (in SPSS). The main results of this paper consists in suggesting that the indicator land us changes towards covering with buildings could be used as a synthesis monitoring indicator for the divergent growth effects, allowing the identification of the peri-urban areas, as a result of positive agglomeration process formation based on New Economic Geography theory background. The shapes and locations identified offer a quantitative imagine complementary characterized in a qualitative manner by their higher propensity to be with the highest global competitive performance among the national landscape, in the context of free market main driving force expression.

©© 20162016 The The Authors. Authors. Published Published by Elsevierby Elsevier B.V B.V.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 ECOSMART 2015. Peer-review under responsibility of the organizing committee of ECOSMART 2015 Keywords: peri-urban areas; land use; ESDA, agglomeration, FOB exports;

1. Introduction

The smart, sustainable and inclusive growth adopted by Europe 2020 [1] demands new types of information and requests spatial integrated approaches of social and economic dimensions. In this context, it is increasing the interest for better profiling the rapidly urbanizing landscapes [2] as periurban “fresh” areas or the “arena” where interaction

* Corresponding author. Tel.: +4-021-312-4069/24; fax: +4-021-311-7595. E-mail address: [email protected]

1878-0296 © 2016 The Authors. Published by Elsevier B.V. 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 ECOSMART 2015 doi: 10.1016/j.proenv.2016.03.017 Cristina Lincaru et al. / Procedia Environmental Sciences 32 ( 2016 ) 124 – 137 125 between the natural and human components based on the synergy of ecological and social;-economic factors unfolds its dynamics. The reference to a peri-ruban space as main concept is quite old but knows many “shapes”. In the urbanism theory of Burgess (1925) [3] it is used the growth of the city and since 1937 Smith [4] termed as urban geography concept the “urban fringe” so as “to include the buildup area just outside the corporate limits of the city”, but at first mainly with demographic characteristics of the analyzed area. It is also remarkable that Carter [5] defined the concept of “rural-urban fringe” in 1972 as “the space into which the extends as the process of dispersion operates”. In 1994, Khan [6], draws the attention to the “scholars from various disciplines like Geography, Sociology, Economics, Political Science and Planning” as regards the multidisciplinary academic interest of the “rural-urban fringe”. This vast interest for peri-urban area reflects the huge diversity [6] of applications, each term is correct in a specific framework defined in a specific school, by country. In USA, expressions like exurbia are used by Joseph and Smith 1981 [7], exurban areal by Lessinger 1986 [8], technoburb by Fishman 1990 [9],t pos -urban surface by Garreau 1991 [10], rural – urban interface by Sharp & Clark 2008 [11], etc. In UK, there are differentiated concepts like hinterland by Hoggart 2005 [12], the edgeland, suburbs, vorort by Gallent et al. 2006 [13] , where the team realised 11 systemised in 13 categorised methods for determining the rural – urban limits: Margin of built-up zones, Land use, Transition zones, Metropolitan zones, Inside the rural, Urban meets rural, pressure zones, population, Territorial – administrative policy, economy, accessibility, landscape, way of life. In China, urban fringe is used by Xu 2004 [14]. In France, there are used terms like periurban, banlieu by David [15] in 1997, PLURIEL [16] in 2008 recommended a typology of 4 classes for all Europe rural-urban regions (RURs): Rural, Dispersed polycentric, Urban polycentric metropolitan, Urban monocentric, couronne [17]. In Romania, it is registered an equivalent expression defined in relation to the distance as the „edge of the urban areas - up from where the built surface ends - and carried to where there is direct and effective influence of the city", here the term is synonymous with the suburban area (zonă preorăşenească / suburban area) used by Iordan (1973, p 8) [18]; Urban influenced area byo Ian ş in 1987 [19],r- ru urban fringe by Avram 2009 [20], other: urban basin surrounding urban environment.

1.1. Land use structure main concepts approach at international level

Europe 2020 is focused on implementing the “Smart Growth” goal under consideration that “Smart Growth is an attempt to rethink the consumption of land and natural resources through community planning and transportation policies to counteract leapfrog development (or sprawl). Smart Growth is a policy-driven movement within the larger framework of growth management” [21]. Smart growth was identified by Porter [22] as adopted in some communities before 1997 concerning economic growth coupled with improvement and greater social inclusion and already implemented in the legislation of Maryland USA since 1997 by Daniels and Lapping [23]. “Dumb Growth” is the opposite concept to “Smart Growth”, broadly defined by Libby & Bradley [24] as “sprawling, haphazardous and poorly planned development in the outer suburbs and ex suburbs”. Mere development focused to serve only the economy and the community could be toxic and might damage the environment [25]. Land-use policy and growth management at the rural-urban fringe represents a huge interest in literature [26], [27], [28], [29], [30], [31], [32]. The integrated approach of economy and geography is reflected under the modern economic theories that explain the economic convergence. Among the economic growth models, there are included the economic divergence family of imperfect competition models which include: Geography, Agglomeration and Trade in the New Trade Theory (NTT) [33], followed by the theory of The New Economic Geography (NEG) [34] and developed by The New Geography of Jobs NEGJ [35]. Geographical Agglomeration plays a central role in all mentioned theories. In NTT and NEG, agglomeration appears "as the outcome of the interaction of increasing returns, trade costs and factor price differences." [36] Against this theory background, the driving factor of modeling agglomeration (including urban area) is the trade economy of scale. This factor explains the divergence among regions, in a “self-sustainable way”, while the „economic regions with most production will be more profitable and will therefore attract even more production. That is, NTT implies that instead of spreading out evenly around the world, production will tend to concentrate in a few countries, regions, or cities, which will become densely populated, but will also have higher levels of income [37, 38]. Expanding the theory, the NEGJ sees that among knowledge economies and geography, 126 Cristina Lincaru et al. / Procedia Environmental Sciences 32 ( 2016 ) 124 – 137

the links is growing, creating the Great Divergence. Under NEGJ theory, the driving factor is represented by the presence of more educated workers in the geographic agglomeration called Brain Hub Cities, a source of creativity that produces added value, explaining finally the widening of the economic disparities among individuals and cities.

1.2. Spatial modeling of peri-urban areas

The spatial models are among the specialized tools important to evaluate the policy options, to asses’ ex-ante and post impact on different time horizon of the policies. Conversion of Land Use and its Effects (CLUE) [39], [40]) is a spatial planning and growth management tool that could be applied at national and continental level. CLUE model was created to analyze the possible trajectories of land use changes in short time, “it was developed to simulate land use change using empirically quantified relations between land use and its driving factors in combination with dynamic modeling of competition between land use types.” [14, p.13]. China is a huge emergent economy (the second World Economy by IMF [41] ranking in 2014) with very high economic growth rates offering the best model for study of the rapid land use changes in “transitional and semi-urban systems” like the urban fringe or the foreland of “urban sprawl” [14] applied the explicit model named CLUE (Conversion of Land Use and its Effects) to explore the spatial and temporal dynamics of land use in a developing country, far away from the classical models provided by the huge literature offered for developed countries. Modeling the spatial pattern of urban fringe, seen at the foreland in the process of “urban sprawl” was done in a integrated approach including the significant driving factors. Xu Feng emphasized the huge difference among the driving factors of urbane fringe’s development in Western countries and in developing countries. In Western countries, the transport technology is the essential force, followed by the high technology that creates new jobs, the government policy and urban planning are only in the 3rd rank,, the demographic boom ranks 4th and on 5th the love for nature as a cultural value. On the other side, in development locations (i.e. China Hongshan, Wuhan) the driving forces are: topology conditions with government policy and controls, lower costs of exploring land, economic growth, transportation and communication. Another model is Driving forces, Pressures, States, Impact and Responses (DPSIR) model (Sharifi et al., 2003) [42] a simple and good tool to identify the possible factor of the land use change [14, p.19]. Changes in land use can be classified into random and systematic transitions [43], The dynamics of land use and occupation in Portugal between 1958- 2007 prove deep changes involving an increase in pattern complexity, presenting different trajectories for different sectors and also indicating a transfer taking place in small steps, underlining the evolution from rural characteristics to an intensive process of peri-urbanisation, and ending in urban consolidation [44]. In Romania, there is also a rich literature regarding peri- urban as highly conflict area for a high land use change structure. Cocheci et.al [45] describes a peri-urban area as the effect of land use change under high anthropic pressure (Anthropic interventions with a high ecological footprint: land use and land cover (LULC), demographic pressure, mining operations), where ‘land use and land cover changes can be considered an important indicator of anthropic pressure” [46]. Land conversion led to changes of ecosystem services [47]. Following the logic presented by Grădinaru [48], in the absence of a market for evaluating the environment benefits, it could be used the availability to pay as substituting goods sold on the market, respectively the land conversion could be estimated quantitatively and economically. The functional incompatibilities inside the settlements represent a source of territorial conflicts, especially in spaces with high spatial and temporal dynamic, especially areas in the proximity of large cities [49]. In Romania, the lack of statistic data about the distribution of conflicts, diminishes the impact of sustainable planning and the chaotic development of constructions determined the inclusion of numerous areas with functional incompatibilities inside the settlements, highlighting the dimension of territorial conflicts [50]. Hersperger et. al [51] emphasizing that “land-use conflicts and tensions are especially prevalent in peri-urban and multifunctional landscapes” [52]; [13]; [53], and concluding that “more research is needed to develop tools to support conflict anticipation” [50, p. 11]. Grădinaru et. al. [54] depict the new model of Romanian urban areas. It emphasizes that the planning system decreased its importance and the economic development became the most important driving factor. The shape of the urban areas changed from a compact city towards the city with “more dispersed patterns, or expanded in a compact manner. Although specific processes of urban expansion, such as sub-urbanization or peri-urbanization, affect the vast majority of the analyzed cities that are influenced by the development level of the urban area”. Peri- urbanization is accentuated in Romanian urban areas, as shown by the decrease of Centrality Index (higher Cristina Lincaru et al. / Procedia Environmental Sciences 32 ( 2016 ) 124 – 137 127 decreases were recorded by development level DL1: Cluj Napoca, , Bacău and DL2: , Brăila) and Compactness values () [54, p.136]. In these areas, there are identified as driving force the lower taxes and land prices, on a background with still a rural character developing strong dynamics by some functions only (specific to high degree of urbanization). Iojă et.al. [55] made a complex environmental quality profile of Bucharest and its Metropolitan area based on a broad-indicators system and specialized methods. Among the main conclusions of this book the author predicted that in the absence of coherent, democratic, responsible regional development policy implementation that includes the environmental conservation as a priority “the Bucharest metropolitan area will became a victim of globalization, a space with a reduced competitiveness”.[55, p.242] Grădinaru et. al. [56] estimate the impact of landfill proximity on the value of real estate goods in the Bucharest periphery using the method of hedonic pricing. The landfill proximity in Bucharest where “periphery has a negative impact on the value of real estate goods that is manifested by a price variation of 15,335 Euros per kilometre, and 13,000 Euros per kilometre if the area around the house is considered too” [56, p.49]. Niţă [57] promotes an instrument for the identification of areas with favourability and restrictiveness in the development of residential surfaces using “a series of attributes extracted from topographical maps (1977-1978) and aerial images (2005 and 2008), and considered to be of major impact upon residential surfaces, such as: public services, incompatible functions, road infrastructure, existent residential surfaces, forest, and water surfaces and soils characteristics [57, p.59]. Iojă et al [58] used a multi-criteria analysis applied in the Bucharest Metropolitan Area at LAU level to create a tool for integrating land-use conflicts into the strategies for territory planning at the metropolitan level. According to Ion et.al. [59], the dynamics of the spatial patterns of land use types in the post-Socialist period at the level of first tier of administrative-territorial units ( and rural communes) from the viewpoint of the rural-urban fringe approach. There were applied methods of multivariate statistics and hierarchical agglomerative clustering. The analysed LAU passes from rural features into suburban and urban ones, “changed their dominant land use type from agricultural to non-agricultural, mainly, residential. A combined approach to planning is required” [59, p.65]. Onose et al. [60] use “Bucharest as a case study in developing a methodology for mapping critical areas of exposure to environmental conflicts” related with “changes in the consumption models and the desire for an increased quality of life”. Grădinaru S. R. et. al. [61] analysed the periphery of Bucharest over a period of 11 years (2002-2013) based on data of aerial images validating the model of expanding the cities of the former Socialist countries into nearby agricultural areas, in a mosaic of built-up and agricultural parches shapes. The results “confirmed that land abandonment is a valid precursor of built-up development” [61, p, 312]. In this study the driving forces were considered the economic transformations and changes in urban regulations. Our approach starts with land use under the definition (FAO) [63] of “what” is the purpose of activities undertaken to reflect how people use the land, in a holistic manner, under the consideration that the space integrates the society, economy and environment. The land use reflects both the economic interactions between humans and environment describing the way of exploiting the primary production factor “the land” - the building block of any economy but also the social interactions (habitation, leisure, etc.). On this background we focus in this article for the definition of the peri-urban areas as the fringes that registered land use changes from other activity (economic and non-economic activity) towards habitation land use (social use), in a significant share. Starting from the article of Salvati & Carlucci (2014) [64] regarding the Urban Growth and Land Use Structure we develop an Exploratory Spatial Data Analysis (ESDA) for peri-urban areas in Romania at LAU2 level based on Land use categories provided by TEMPO INS’ indicator AGR101B, modelled for 2 years (2010 and 2014). The ESDA tools (Method of Choropleth Maps and LISA) allow to evaluate, monitor and asses the land use dynamic in spatial and temporal dimension, proving some useful results for academics [6], but mainly for applied policies. Identifying the agglomeration of LAU2 considered as lattice data this approach offers valuable inputs (maps as intuitive synthetic imagines) also for the applicative field of Policies with high dependence of space: R&D&I Policy, Competitiveness Policy, Regional Development, Employment Policy, Cohesion Policy, Educational Policy, Poverty Alleviation Policy, etc. The results could offer a fresh insight regarding the dimensions of exurbanisation, in a dynamic manner [32] (in both positive and negative externalizations). The general objective of this study is to exploit the agglomeration process formation based on NEG theory background, in a global economy, as the main driver of peri-urban area formation, in an integrated manner (economic, social, environment [1]). The specific research questions are: (a) Which are the positive and negative 128 Cristina Lincaru et al. / Procedia Environmental Sciences 32 ( 2016 ) 124 – 137

modifications during 2010-2014 at national level; (b) Which are the locations with positive changes of land use for buildings as a measure of peri-urban area identification at national level? This research is new in applying spatial analysis (LISA) in order to study the agglomeration dynamics formations and retrieve.

2. Data and Method

The variates methods and data sources used to analyse the land use pattern mentioned in Romanian literature are: The Method of Data sources analysis of statistical data; - interpretation of Urban Planning Plans, GIS modeling - topographic maps satellite imagery aero photograms, Corine Land Cover maps, Multivariate analysis - statistical evidence Statistical analysis [59] [65] using as reference the OECD [66] definition that “a commune is classified as rural if the population density is below 150 inhabitants per km²”, than there could be determined also the minimum threshold estimation of the LAU 2 land covered with buildings positive modification in a significant share. Our method is based the article of Salvati & Carlucci (2014) regarding the Urban Growth and Land Use Structure, we develop an ESDA for peri-urban areas in Romania at LAU2 level / NUTS 5 level. applying the ESDA tools (Method of Choropleth Maps and LISA) and statistical analysis. Statistical (spatial) analysis made Arc Gis and GeoDa softwares is easy to be applied and the repetitive potential of algorithm building. Data with spatial link is more accessible [58][59]. The background of increasing the offer of social-economic-environment offer of indicators provided by Official Statistics in the smallest administrative unit LAU2 increases the return of geography connection with different domains under the conditions of smart growth and provides results accessible at lowest executive unit. The spatial integration of quality data at micro level increases the potential to increase the responsibility and conscience of any trade off, including also the environmental costs next to economic and social cost. The microaggregate data are accessible from TEMPO INS in a full format since 2010 in annual frequency until 2014, time span associated to a strategical cycle nationally, but also at European level. This method could offer a tool for the evaluation and assessment of some policies applied during the latest strategical cycle.

2.1. Data

In the context of the software tools designed to implement techniques for ESDA on lattice data [67] like GeoDa and GIS, we explore the land use dynamics focused on buildings covered utility at Local Administrative Unit - LAU2 level. In consequence LAU2 formerly Nomenclature of Units for Territorial Statistics – NUTS5 [68] level represent the “smallest” statistical unit counting 3181units (42 Counties NUTS3 level units, 8 Regions NUTS 2 level units, 4 Macro regions NUTS1 level). Administrative and geographical data: Area data are provided by Romania ESRI shape polygons that reflect territorial description of LAU2 and are regulated according to Law 351/6th July 2001 regarding the National Territory Arrangement Plan - spatially geocoded using the polygons areas for LAU2 described by ESRI Romania using Arc GIS Software. The territorial administrative units LAU2 level are represented in SIRUTA (Romania’s National Institute of Statistic (INS) – The National Interest Nomenclature Server – SENIN, the SIRUTA Methodology – General Presentation) code by , town, commune and County residence and are equivalent with NUTS5 (Nomenclature of Territorial Units for Statistics) level (Lincaru et.al., 2014) [69]. Attribute data - economic and social describing of administrative and geographical date: Variable on which the ESDA analysis is made including LISA spatial analysis, on which we calculated “high-high” (H-H), “low-low” (L- L), “low-high” (L-H), and “high-low” (H-L) clusters in GeoDA (Anselin) for: AGR101B - Land fund area by usage, counties and localities provided by TEMPO INS Romania [70]. This indicator is the statistical tool for implementing and monitoring the Law no. 215/2001 - the main law that regulates the general regime of local autonomy, as well as the organisation and functioning of the local public administration authorities [71] allowing to form a precise insight at LAU2 level. AGR101B results from an Exhaustive statistical survey based on administrative data having the following Statistical Activity Objective: Evaluating the land use - farm lands, pastures, meadows, vineyards and orchards, and nonagricultural land - forests, water, roads and railways, and other nonproductive land, depending on the type of tenure, from cadastral data sources [70]. This indicator provides 12 Categories of land by its Economic (Agricultural) area usage, as follows: Agricultural area; Farm land; Pastures; Meadows; Vineyards and vine nurseries; Orchards and fruit tree nurseries; Non-agricultural land, total; Forests and other forest vegetation; Land Cristina Lincaru et al. / Procedia Environmental Sciences 32 ( 2016 ) 124 – 137 129 covered with waters, ponds; Land covered with buildings; Ways of communication and railways; Degraded and unproductive land; Total and private type of ownership. Even if the AGR101B is higher, we use only the total category by type of ownership while the private type of ownership category will be used in the future. These data provided important limits given by the complexity of the land use classification system in the sense that in Romania it is not possible to distinct among the social and economic destination of the Land covered with buildings as is already available in USA [72]. The economic performance and competitiveness of counties that included LAU2 identified as peri-urban is characterized by the indicator EXP101J - Exports (FOB) by counties and by sections/ chapters of the Combined Nomenclature (CN) - monthly data provided also by TEMPO INS [73]. We mention that in this indicator the exports of goods include all goods which by onerous title or free of charge leave the economic territory of the country to the rest of the world destination.

2.2. Variables characteristics

Based on the definition of peri-urban area (stated in Introduction) among the 12 characteristics provided by the indicator, the only one characteristic that reflects the habitation land use is the land covered with building characteristic. At this moment, as we mentioned before, we are not able to make a distinction regarding the economic use of buildings (next to residential, there could be industrial, commercial and agricultural) towards the habitation use, but we consider a good proxy for our research question: “Which are the locations with positive changes of land use for buildings as a measure of peri-urban area identification?” In order to compensate the lack of data regarding the habitation land use we explore in a first stage the indirect measure for rural – urban interaction given by the habitation land use confirmed in the urban area characteristics. The indication of change of land use toward peri-urban area could be validated by the land fund usage structural change towards habitation when the share of land usage to buildings increases in a significant manner. In Table 1 we present the average profile of the structure by land fund usage at LAU2 level by administrative type. The average share of land fund area by usage at LAU 2 in 2014 is 3.2% for rural LAU2 and for urban LAU2: 6% for town, 13.3% for the Municipality and 23.8% for County Residence.

Table 1. The average share of land fund area by usage at LAU 2 in 2014 (%, calculated by authors). LAU2 type pAg pAr pFin pPAs pVii pLiv pNag pPAd pApe pCons pCAiF pTrDg pTot Mean 67.8 45.3 8.8 14.0 1.6 1.6 32.2 23.9 2.4 3.2 1.8 2.2 100.0 Commune SEM 0.4 0.5 0.2 0.2 0.1 0.1 0.4 0.4 0.1 0.1 0.0 0.1 0.0 Mean 58.5 35.9 9.0 12.8 1.9 1.7 41.5 19.6 3.0 13.3 3.2 2.8 100.0 Municipality SEM 2.4 3.1 1.1 1.1 0.5 0.5 2.4 2.5 0.5 1.5 0.3 0.4 0.0 Mean 58.5 38.7 7.8 12.4 2.2 1.4 41.5 28.8 3.2 6.0 2.1 2.5 100.0 City SEM 1.6 1.9 0.6 0.5 0.5 0.2 1.6 1.8 0.5 0.5 0.1 0.3 0.0 County Mean 46.0 33.5 3.7 7.2 0.9 2.0 54.0 19.0 4.1 23.8 4.6 2.7 100.0 residence SEM 3.1 3.0 0.8 0.9 0.3 0.5 3.1 2.9 0.8 2.6 0.6 0.6 0.0 Mean 66.7 44.5 8.6 13.8 1.7 1.6 33.3 24.0 2.5 3.9 1.9 2.2 100.0 Total SEM 0.4 0.5 0.2 0.2 0.1 0.1 0.4 0.4 0.1 0.1 0.0 0.1 0.0 Where the average share of land by usage at LAU 2 in 2014 is: pAg Agricultural area (%); pAr Farm land (%); pFin Pastures (%); pPAs Meadows (%); pVii Vineyards and vine nurseries (%); pLiv Orchards and fruit tree nurseries (%); pNag Non-agricultural land, total (%); pPAd Forests and other forest vegetation (%); pApe Land covered with waters, ponds (%); pCons Land covered with buildings (%); pCAiF Ways of communication and railways (%); TrDg Degraded and unproductive land (%); pTot LAU2 area (%), SEM Standard Error of Mean

In 2014 the average share of land fund area by usage type at LAU 2 at county level is strongly differentiated by administrative type unit. Among rural LAU2 type, ranks the first place from 42 with a share of average land covered with construction of 14.4%, followed at a distance by Brasov with 6.3%, almost double than the national average of 3.2%, while only 17 counties present values above average. The empirical distribution of the data (based on the histograms) is positively skewed (the mean is larger than the median, the smallest values are much closer to the mean than the largest values), showing after a visual check a Log Normal or Gamma Left 130 Cristina Lincaru et al. / Procedia Environmental Sciences 32 ( 2016 ) 124 – 137

probability distribution shape, indicating the rejection of null hypothesis that it is normally distributed. At this point (while the structure of land use is specified only for one year – 2014) we can analyze the dynamic of land covered with buildings without specifying the sources of this change (agricultural area use or non-agricultural land use) [14, 42, 44]. From this point forward we focus only on Land covered with building characteristics and dynamics in 2010 and 2014 in both relative and absolute dynamics in order to choose the best indicator for spatial analysis. Based on the Table 2 results (presenting higher variation) we prefer the absolute indicator: the average differences for land covered with buildings in 2014 as compared with 2010 by LAU2 type (Ha, calculated by authors).

Table 2. Land covered with building characteristics and dynamics in 2010 and 2014. The share of land covered The share of land covered The average differences for land with buildings by LAU 2 in with buildings by LAU 2 in covered with buildings in 2014 2010 (%, calculated by 2014 (%, calculated by comparing with 2010 by LAU2 LAU2 type authors) authors) type (Ha, calculated by authors) Mean 3.1 3.2 6.9 Minimum 0.0 0.0 -855.0 Comuna/ Maximum 68.1 87.9 2860.0 Commune Sum 19751.0 (rural area) Std. Deviation 3.5 4.1 95.4 Variance 12.3 16.8 9102.4 Std. Error of Mean 0.1 0.1 1.8 Mean 12.6 13.3 46.0 Minimum 0.9 0.9 -138.0 / Maximum 66.3 66.5 579.0 Municipality Sum 2895.0 (urban Std. Deviation 11.9 12.2 122.0 area) Variance 142.8 147.8 14894.3 Std. Error of Mean 1.5 1.5 15.4 Mean 5.7 6.0 20.9 Minimum 0.1 0.2 -174.0 Oras / Maximum 54.4 56.0 887.0 Town Sum 4410.0 (urban Std. Deviation 6.9 7.2 100.2 area) Variance 48.0 52.1 10047.1 Std. Error of Mean 0.5 0.5 6.9 Mean 23.1 23.8 62.9 Resedinta Minimum 2.5 2.6 -691.0 de judet / Maximum 58.7 65.0 724.0 County Sum 2515.0 Residence Std. Deviation 16.1 16.5 206.2 (urban Variance 260.1 271.7 42530.4 area) Std. Error of Mean 2.5 2.6 32.6 Mean 3.7 3.9 9.3 Minimum 0.0 0.0 -855.0 Maximum 68.1 87.9 2860.0 Total Sum 29571.0 Std. Deviation 5.2 5.7 98.8 Variance 27.1 32.3 9756.8 Std. Error of Mean 0.1 0.1 1.8

2.3. ESDA methods applied In order to respond to the question: ‘Which are the locations that record positive changes for land covered with building’, we apply first the Exploratory Spatial Data Analysis (ESDA) Method of Choropleth Maps (Anselin, 2005)74 5 classes - manual selection (Class 1: -855Ha -100 Ha; Class 2: -99 Ha - -1 Ha, Class 3: 0, Class 4: 1 Ha - 100 Ha, Class 5: 101 Ha -2860 Ha) so as to make a simple map and select locations with large positive variations regarding the modifications of land use for buildings. The interval classes were set based on variable land use for building at LAU2 level based on Histogram for land covered with building changes used between 2010-2014 (having a normal distribution shape). Secondly, in order to Cristina Lincaru et al. / Procedia Environmental Sciences 32 ( 2016 ) 124 – 137 131 validate the first sets of results, we identify the clusters of LAU2 using the uni-variate Local Indicators of Spatial Association (LISA) in GeoDA software [74] going at the following steps: 1. Neighborhood analysis / contiguity and spatial weighting technique used is founded on [67] [74]. Spatial relation conceptualization spatial LAG modeling is based on rook contiguity, first order type. Among the 3189 LAU2 with data there are 805 locations with 5 neighbors, 799 locations with 6 neighbors, 577 locations with 7 neighbors, 408 with 4 neighbors and 282 with 8 neighbors, summing a cumulative percent of 90.1%. The maximum number of neighbors is 16 and the minimum 1 in 4 locations; 2. Global Analysis is performed through the Moran‘s I [67] [74]. The observed values of Moran I index is positive but very low 0.0048, higher than the theoretical mean of E(I) = -0.0003, Sd 0.01

3. Results

In Fig. 1 (a) and (b) there are visible, both positive and negative modifications during the 2010-2014 period, of the changing land use for construction in the period 2010-2014, irrespective of the UAT2 administrative type. More than 75% of the locations with positive modifications in the total locations with positive modifications are LAU2 of commune type. These rural locations with peri-urban characteristics gravitate around some powerful urban centres like: Braşov; Piteşti; Ploieşti; Nord West Region – with two nucleus of peri-urban area at Oradea and Pietroasa and Bucharest. Following the ESDA results presented in Fig.1 (a and b), we apply the ranking analysis by land covered with buildings change between 2010-2014 at LAU2 level to peri-urban locations identified with the Method of Choropleth Maps 5 classes’ manual selection and validated by the local autocorrelation LISA and presented by county. A common issue of the counties with highest positive dynamic resulted from both applied methods is that for a 4- year period, the minimum threshold of the land covered with buildings positive modification in a significant share, is higher than 10Ha in absolute terms or higher than 3% of the share of land covered with buildings by LAU 2 in relative terms (except Buneşti from Braşov with 2.7%), for the minimum threshold of the share of land covered with buildings, regardless the LAU2 type. In order to explain the spatial heterogeneity of land use positive modification in post-crisis context, we made an independent benchmark analysis at the national level by Exports (FOB) by counties and by sections/ chapters of the Combined Nomenclature (CN). It was visible that the identified counties present high performance in terms of export share indicating that the land covered with buildings is highly correlated with industrial activities: Counties with peri-urban location were identified and higher than the national average for the share in total exports (FOB) of 4.8% in January 2015 – ranking on the 6th place: Arge ş (, Ratesti, , Suseni, Piteşti) the county with the highest number of HH locations - ranks on the 2nd place by counties with 9% for the share in total exports (FOB) in January 2015, slightly decreasing with 1.2pp since January 2011. We mention that Piteşti is an Urban Development Pole (Ianoș et.al., 2012)76. Arad (Arad, Sagu – presented in Nord - West map) ranks on the 4th place by counties with 5.3% for the share in total exports (FOB) in January 2015, slightly decreasing with 1.2pp since January 2011. We mention that Arad is an Urban Development Pole77.

132 Cristina Lincaru et al. / Procedia Environmental Sciences 32 ( 2016 ) 124 – 137

a

b

Fig. 1. Land covered with buildings change between 2010-2014 at LAU2 level identification of locations with peri-urban development using: (a) Representation by Cloropleth 5 classes Manual Selection; (b) Representation LISA clusters calculated in GeoDA. Cristina Lincaru et al. / Procedia Environmental Sciences 32 ( 2016 ) 124 – 137 133

Braşov (Râşnov, ) ranks on the 5th place by counties with 4.9% for the share in total exports (FOB) in January 2015, increasing with 0.9pp since January 2011. We mention that Braşov is a Growth Pole.[76] Counties with peri-urban location identified and lower than the national average for the share in total exports (FOB) of 4.8% in January 2015: Bihor (Pietroasa, , ) ranks on the 8th place by counties with 3.3% for the share in total exports (FOB) in January 2015, decreasing sharply with -5.2pp since January 2011. We mention that Oradea is an Urban Development Pole [68]. Ilfov (Ciorogârla) ranks on the 9th place by counties with 3.2% for the share in total exports (FOB) in January 2015, increasing with 5.8pp since January 2011, shaping the metropolitan area for Bucharest. Prahova (Băicoi) ranks on the 10th place by counties with 3.1% for the share in total exports (FOB) in January 2015, very slightly decreasing with 0.2pp since January 2011. We mention that Ploieşti is a Growth Pole.[76] Counties without peri-urban location identified and higher than the national average for the share in total exports (FOB) of 4.8% in January 2015 – ranks on the 6th place: Special case Bucharest presents a low level of land covered with buildings dynamics, but ranking 1st by counties with 18.3% for the share in total exports (FOB) in January 2015 Timiș ranks on the 3rd place by counties with 7.9% for the share in total exports (FOB) in January 2015, slightly decreasing with 0.4pp since January 2011. We mention that Timişoara is a Growth Pole [76]. At the beginning of crisis of 2010 for Banat region and especially at Timiş county level some important spatial gatherings of firms have been identified operatting in certain fields which could represent potential clusters (following the Porter definition 1998) in areas: “in the following domains: wood industry, textiles, shoes and software and electronics”[69] According to the Government Decisions 998 and 1948 of the year 2008, there are 7 national growth poles and 12 urban growth poles [76], of which there are 2 Growth Poles and 3 Urban Development Poles with peri-urban areas. The presence of peri-urban locations could be an indicator of success of these structures government. Another common issue for peri-urban areas identified based on land use change toward coverage with buildings is illustrated by Argeş (2nd rank), Arad (4th rank), Brașov (5th rank), Bihor (8th rank) and Prahova (10th rank) that are counties with good economic performance and competitiveness expressed through important share in total exports (FOB) in similar sections and chapter of Combined Nomenclature (CN) in January 2015: Gathering everything at this point, we can conclude that the land use change towards land coverage with buildings indicates a major structural change from rural to urban, where the main change of land use is from agricultural toward land covered with buildings, where those buildings could be both for industrial use and for residential use. On the background of crisis, the spatial agglomerations able to sprawl in space only in the neighbourhood of locations with global competitive activities like vehicles and machineries and mechanical appliance, in conditions of high level of specialisation. This model indicates that economic growth leads to development, but not certain to demographic growth.

4. Discussions

The smart, sustainable and inclusive growth adopted by Europe 2020 [1] demands an integrated approach in all policies fields. On the background of NTT [33], NEG [34] and NEJ [35], it becomes possible to integrate the simultaneous action of all production factors: land, work, knowledge, capital so as to produce a sustainable smart growth. [21], [22]. The modeling agglomeration (including urban area) as a trade economy of scale presents a huge potential to integrate the environment in social-economic analysis [47], from both quantitative and qualitative perspectives. Romania’s dynamics of the land using it covered with buildings as a measure of peri-urban area development indicates that more than 75% of the locations with positive modifications of the total locations with positive modifications are LAU2 of commune type that gravitate around some powerful urban centers. A common issue of the counties with highest positive dynamic resulted from both applied methods is that for a 4-year period the minimum threshold of the land covered with buildings records positive modification in a significant share, higher than 10Ha in absolute terms or higher than approximately 3% the share of land covered with buildings change by LAU 2 in relative terms (for the minimum threshold the share of land covered with buildings, regardless the LAU2 type). 134 Cristina Lincaru et al. / Procedia Environmental Sciences 32 ( 2016 ) 124 – 137

In order to explain the spatial heterogeneity of land use positive modification in post-crisis context we made an independent benchmarking analysis at national level by Exports (FOB) by counties and by sections/ chapters of the Combined Nomenclature (CN). It was visible that the identified counties present high performance in terms of export share indicating that the land covered with buildings is highly correlated with industrial activities. This result is coherent with a low level of competitiveness, Romania is still an efficiency-driven economy, next to Bulgaria, while all the other Eu26 countries are included by the Global Competitiveness Report (2014)78 among innovation- driven economies. In a free economic market system, the planned development in a systematic way is highly requested as rational alternative to random transition [43], calling for combined approaches of planning with participatory mechanism [59]. In Romania in the last strategical cycle, our results reflect more the tendency of random transition of urban dynamics – peri-urban areas (the Pole Policies result is only partially correlated with peri-urban areas development, but more with economic competitive performance). Romania as emergent economy presents some specific characteristics: high growth rates coupled with relatively low level of the quality of life, inefficient institutions still functioning decrease the success of main Policies implementation and finally diminish the resources return. It is coherent with the conclusion of [14], the economic competitive growth is realised in manufacturing (some technological sectors), but not in high tech sectors. The detailed analysis of Bucharest and its surrounding area is coherent with [55]. Accepting the LAU2 limit of comparability for this location, an asymmetric shape development area is emphasized especially in the South East, confirming [56] and the lack of a successful planning implementation. Looking on the cohesion policy evaluation at the new cycle start, we have to emphasize the fact that Bucharest – Ilfov area is a more developed region that derives from the cohesion policy eligibility mechanism and there for is not comparable in terms of regional policy demands with all other Romanian regions. The result for Ploieşti is complementary, with the main conclusion from [62] indicating that the main driver of success is given by machinery industry and not by oil industry. There is a lot of space in peri-urban research to make a clear distinction between cause and effect. Our study points out that agglomerations driven by economic and competitive performance have a positive dynamics, which could provide better convergence towards the smart-growth objectives. [1] The land use covered with buildings is an effect factor available at LAUT 2 – as a powerful synthetic indicator, and the exports here is a causal economic performance in a global competitive economy indicator. This simplified method could be improved through better connecting competitiveness as source of development that works as lawfulness for social – economic systems development in time and space. In order to increase the growth convergence, in a dispersed growing model driven by highly technological global competitivity, the process of Community decision becomes vital for the success of a location and its community. In an open economy (at least in EU common market) is more and more requested to be innovative, responsible and highly participative. In the divergent model, there are no unique solutions, it is impossible to develop only homogenous Planning policy (e.g. Convergence Policy, Agricultural Policy, and Research Policy at European level). The solution is to unleash the creativity and to develop also appropriate solutions at territorial level. The advantage of looking at LAU2 level “resolution” is limited by the lack of detail, our reference is only to the structure of land use covered with buildings. Other limits are the absence of some determining dimension for urban dynamics (centrality, compactness, etc.) [54] This instrument allows to be highly standardized [72] by economic use of buildings, next to be completed and finally used in the public administration through the Structural funds oriented toward increasing the institutional capacity. The high level of relatively novelty represents a barrier towards internalization of using mixed tools in public management decision, regardless of the level of responsibility. Our approach is only an attempt to integrate at least at some point the common spring – the growth model chosen to be implemented on long term - especially for public policies, in a coherent, coordinated and participative manner.

5. Conclusion

Land use approaches ESDA models focused on the dynamic given by land covered with buildings change during 2010-2014 period at LAU2 level is not entirely convergent with the results obtained previous using the population Cristina Lincaru et al. / Procedia Environmental Sciences 32 ( 2016 ) 124 – 137 135 density [69]. Only Argeş (could be a good practice example) and Prahova (slightly Ilfov) are counties confirmed with peri-urban development units in a large spectrum of definitions background (both density of population and habitation (social) land use criteria). One explanation of this lack of consistency is provided by Popa [79]] proving that the Romania’s demographic profile is decoupled by the economic development profile. The geographic model of this profile is a V shape indicating the demographic grow on the North-West descending to the South and the economic growth from the West – Center descending to the South. The main results of this paper consists in suggesting that the indicator land us changes towards covering with buildings could be used as a synthesis monitoring indicator for the divergent growth effects, allowing the identification of the presence of the periurban areas with LAU2 level “resolution”, as a result of an spatial statistic “scanning of the full national framework (LAU2 areas are seen as lattice data and comparing with an minimum relative and absolute threshold of the change in 4 years). The shapes and locations identified offer a quantitative imagine (as response to [50] complementary characterized in a qualitative manner by their higher propensity to be with the highest global competitive performance among the national landscape, in the context of free market main driving force expression. Our methodology could improve the integrated management of development processes, if there should be spatial planning harmonized with the positive externalities of the agglomeration with performance in national economy measured in global competitive terms. We consider crucially important this holistic approach – when the spatial planning (anticipating the functional incompatibilities [49] anthropic management pressure [46], conflict management) should become effectively an instrument [47] of improving and supporting the Romanian’s economy competitivitiy [50]) in a world wide open economy. The next step in this research series could be improved integrating both the economic and the social / demographic elements simultaneously in space so as to better practice the diverse peri-urban definitions richer shaded by its context already announced in literature as “different types” of peri-urban areas [2].

Acknowledgements This work was supported by a grant of the Romanian National Authority for Scientific Research, CNDI– UEFISCDI, DYNAHU project number PN-II-PT-PCCA-2011-3.2-0084.

References

1. EUROPE 2020 A strategy for smart, sustainable and inclusive growth. Communication from the Commission. Brussels, 3.3.2010 COM(2010); 2020. 2. Iaquinta D.L., Drescher A.W., Defining Periurban: Understanding Rural-Urban Linkages and Their Connection to Institutional Contexts. Papers of the the Tenth World Congress of the International Rural Sociology Association. Rio de Janeiro; August 1, 2000. pp. 2-26. 3. Burgess, E.W. The Growth of the city. In The City, ed. R.E. Park, E.W. Burgess, and R.A. McKenzie, Chicago: University of Chicago Press. 1925. 4. T.L. Smith, The Population of Louisiana: its Composition and change. Louisian Bulle. No.293, 1937, p. 24 5. H. Carter, The Study of Urban Geography, Arnold London, 1972, p.288. 6. Khan Z.T., Bilaspur: A Study in Urban G eography, Northern Book Centre New Delhi, 1994, p. 166. 7. Joseph, A., B. Smite. Implications of exurban residential development: A review. The Canadian Journal of Regional Science 4(2). 1981, 207- 224. 8. Lessinger, J. Regions of opportunity. New York: Timesbooks, 1996. 9. Fishman, R., Megapolis unboind, Wilson Quarterly, 14, 1990, pp.25-48. 10. Garreau, J., Edge City: Life on the New Frontier, New York: Doubleday, 1991. 11. Sharp, J.S., Clark JK, Between the country and the concrete: Rediscovering the RuralǦ Urban fringe, City & Community, 2008. 12. Hoggart, K., editor, The City's Hinterland. Dynamism and Divergence in Europe's Peri-Urban Territories., King's College London, UK, 2005. 13. Gallent N., Andersson J., Bianconi M., Planning on the edge: The context for Planning at the rural –urban Fringe, London: Routledge, 2006. 14. Xu Feng, Modelling the spatial pattern of urban fringe. Case study Hongshan, Wuhan, International Institute for Geo-Information Science and Earth Observation Enschede, The Netherlands, 2004. 15. David.L. Coeur de banlieue: codes, rites, et langages. Odile Jacob, 1997. 16. ***, PLURIEL, NEWSLETTER, September 2008 17. INSEE 20106, http://www.insee.fr/fr/methodes/default.asp?page=definitions/couronne-periurbaine.htm. 18. Ianoş, I., Oraşele şi organizarea spaţiului geografic, 1987, quoted by Drăghici, C.C, Activitățile turistice și dezvoltarea integrată în zona de influență a orașul ui Râmnicu Vâlcea, Rezumat Teză de Doctorat, p. 2, 19. Iordan, I., Zona periurbană a Bucureştilor, 1973, quoted by Drăghici, C.C, Activitățile turistice și dezvoltarea integrată în zona de influență a orașului Râmnicu Vâlcea, Rezumat Teză de Doctorat, p. 3, 136 Cristina Lincaru et al. / Procedia Environmental Sciences 32 ( 2016 ) 124 – 137

20. Avram, S. The position of rural-urban fringe in the framework of human settlement system. Forum Geografic. Studii şi cercetări de geografie şi protecţia mediului, Vol. 8, No. 8/ 2009, pp. 139- 145. 21.Wuerzer, T. Encyclopedia of Quality of Life and Well-Being Research, Smart Growth, Springer Link, http://link.springer.com/referenceworkentry/10.1007%2F978-94-007-0753-5_3569, 2014, pp. 6007-6010. 22. Porter, D.R., Managing Growth in America’s Communities, Washington, DC., Island Press, 1997. 23. Daniels,T., Lapping, M., Chapter 2, Land Preservation: An Essential Ingredient in Smart Growth, Growth Management and Public Land Acquisition, Balancing Conservation and Development, Edited by Chapin, T.S., Christopher, C., Urban Planning and Environment ASGATE, 2011, pp. 7-32. 24. Libby, J.M., Bradley, D., Vermont housing and conservation board: A conspiracy of good will among land trusts and housing trusts, in Geisler, C., Daneker, G. (editors), Property and Values: Alternatives to Public and Privare Ownership, Washingtonm D. C.: Island Press, pp. 259-81. 25.Porter, D.R., Marsh, L.L., Developing Land while Retaining Environmental Values: A Modern Search for the Grail. (Chapter 7) published in Vince, S.W., Duryea M.L., Edward A. Macie, E.A., Hermansen, A. (editors). Forests at the Wildland-Urban Interface: Conservation and Management, C.R.C. Press, 2005, pp. 95-108. 26. Healy, R., James, S. The market for rural land: Trends, issues, policies. Washington, DC: The Conservation Foundation. 1981. 27. Nelson, A.C., Characterizing exurbia, Journal of Planning Literature 6(4), Sage Publications, 1992, pp.350-368. 28. Davies, J.S., The Commuting of Exurban Home Buyers, Urban geography, Volume 14, Issue 1, 1993, pp.7-29. 29. Davis J.S., Nelson A.C., Dueker KJ, The New'Burbs The Exurbs and Their Implications for Planning Policy, Journal of the American Planning Association 60 (1), 1994, pp. 45-59. 30. Nelson, A.C., Sanchez, T.W., Exurban and suburban households: a departure from traditional location theory? Journal of Housing Research 8, 1997, pp.249-276. 31. Daniels, T., When City and Country Collide: Managing Growth in the Metropolitan Fringe. Island Press, Washington, DC, 1999. 32. Esparza, A.X., Carruthers, J.I., Land Use Planning and Exurbanization in the Rural Mountain West, Journal of Planning Education and Research 20, 2000, pp.23-36. 33. Krugman, P.R., Increasing Returns, Monopolistic Competition, and International Trade paper in the Journal of International Economics 9, 469-479, 1979 34. Krugman, P.R., "Increasing Returns and Economic Geography", published in the Journal of Political Economy, volume 99, issue 3(Jun., 1991), 483-499. 35. Moretti, E., The New Geography of Jobs, New York: Houghton Mifflin Harcourt, 2012, p. 252 36. Behrens, K., Robert-Nicoud, F., "Krugman's Papers in Regional Science: The 100 dollar bill on the sidewalk is gone and the 2008 Nobel Prize well-deserved". Papers in Regional Science 88 (2), 2009, pp. 467–489. 37. Nobel Prize Committee, "The Prize in Economic Sciences 2008, 2008. 38. Paul Krugman, Nobel", Forbes, October 13, 2008. 39. Velkamp, A., Fresco, L.O., CLUE-CR: an integrated multi-scale model to simulate changes scenarious in Costa Rica. Ecological Modelling 91, 1996: 231-248. 40. Verburge, P.H.V., A., de Koning, G.H.J., Kok, K., Bouma, J., A spatial explicit allocation procedure for modelling the pattern of land use change based upon actual land use. Ecological Modelling 116, 1999, pp. 45-61. 41. World Economic Outlook. International Monetary Fund. April 2015. 42. Sharifi, M.A., van Herwijnen, M., van den Toorn, W. Spatial decision support systems. ITC Lecture Series, 2003. 43. Braimoh, A. K. (2006). Random and systematic land-cover transitions in northern Ghana. Agriculture, Ecosystems and Environment, 113, 2006, pp. 254-263. 44. Tavares, A. O., Pato, R. L., & Magalhães, M. C.. Spatial and temporal land use change and occupation over the last half century in a peri- urban area. Applied Geography, 34, 2012, pp. 432-444. 45.Cocheci R-M., Dorobanţu R-M, Sârbu C.S., Environmental Degradation In Rural Areas With High Anthropic Pressure – Impact And Planning Models, Carpathian Journal of Earth and Environmental Sciences, August 2015, Vol. 10, No 3, pp. 25 – 36. 46. Popovici, E.A., Balteanu, D. & Kucsicsa, G., 2013. Assessment of changes in land-use and land-cover pattern in Romania using CORINE Land Cover database. Carpathian Journal of Earth and Environmental Sciences, 8, 4, 2013. pp. 195-208. 47. Grădinaru G., “Ecosystem Services” Concept - Economic Approach, Revista Română de Statistică nr. 8 / 2012. 48. Grădinaru G.(Chapter author), The Chapter: Environment Benefits Quantification Through Statistical Indicators, Armon R.H., Hänninen O., (Editors), Environmental Indicators, Editura Springer Netherlands, 2015, pp. 225-236. 49. Ianos, I., Dinamica urbană, I Ianoş - Editura Tehnică, Bucureşti, 2004. 50.j Io ă C.I., Modeling of environmental impact induced by the typologies of incompatible land uses in human settlements, Final report, Program: Human Resources – Young Research Teams, PN-II-RU-TE-2011-3 –PN II Human resources - TE 2011, Contract 65/2011, Universitatea din Bucuresti, Centrul de Cercetare a Mediului şi Efectuare a Studiilor De Impact, 2014. 51. Hersperger A.M., Iojă C., Steiner F., Tudor C.A., Comprehensive Consideration Of Conflicts In The Land-Use Planning Process: A Conceptual Contribution, Carpathian Journal of Earth and Environmental Sciences, November 2015, Vol. 10, No 4, pp. 5 – 13. 52. Cadieux, K. V., Political ecology of exurban "lifestyle" landscapes at Christchurch`s contested urban fence. Urban Forestry and urban greening, 7, 2008., pp. 183-194. 53. von der Dunk, A., Spatially explicit analysis of land-use conflicts in Northern Switzerland: new approaches for investigating a complex phenomenon. In: Diss. ETH No 20099, ETH Zurich – Zurich, 2011. 54. Grădinaru S. R., Iojă C.I., Gavrilidis A.A., Pătru-Stupariu I., Do Post-Socialist Urban Areas Maintain their Sustainable Compact Form? Romanian Urban Areas as Case Study, Journal of Urban and Regional Analysis, vol. VII, 2, 2015a, pp. 129 – 144 55. Iojă, I.C., Methods and techniques of assessing environmental quality in the Bucharest metropolitan area (in Romanian), Bucharest University Publishing House, Bucharest, 2008, p. 232 56. Grădinaru G.I., Ioan I., Estimating the Impact of Landfill Proximity on the Value of Real Estate Goods, Amfiteatrul economic, Vol. XIV • No. 31, February 2012, pp. 38-49 Cristina Lincaru et al. / Procedia Environmental Sciences 32 ( 2016 ) 124 – 137 137

57. Nita M.R., Mapping favorability for residential development. Case study: Bucharest Metropolitan Area. Procedia Environmental Sciences no. 14 Landscape, Environment, European Identity, 2012, pp. 59-70; 58. Iojă C.I., Nita, M.R., Vanau G.O., Onose, D.A., Gavrilidis A.A., Using multi-criteria analysis in identifying spatial land-use conflicts in the Bucharest Metropolitan Area, Ecological Indicators, 2013, pp. 1-10. 59. Ion, F., Change of land-use patterns in a suburbanized area: The Bucharest municipality as case study, Forum geografic. Studii și cercetări de geografie și protecția mediului, Volume XIV, Issue 1 (June 2015), pp. 64-74 60. Onose D-A, Niţă M.R., Ciocănea C.M., Pătroescu M., Vȃn ău G.O., Bodescu F., Identifying Critical Areas Of Exposure To Environmental Conflicts Using Expert Opinion And Multi-Criteria Analysis, Carpathian Journal of Earth and Environmental Sciences, November 2015, Vol. 10, No 4, pp. 15 – 28. 61. Grădinaru S. R., Iojă C.I., Onose D.A., Gavrilidis A.A., Pătru-Stupariu I., Kienast F., Hersperger A.M., Land abandonment as a precursor of built-up development at the sprawling periphery of former socialist cities. Ecological Indicators 57, 2015a, pp. 305–313. 62. Gavrilidis A.A, Grădinaru S.R., Iojă I.C., Cârstea E.M., Pătru-Stupariu I., Land Use And Land Cover Dynamics In The Periurban Area Of An Industrialized East-European City An Overview Of The Last 100 Years, Carpathian Journal of Earth and Environmental Sciences, November 2015, Vol. 10, No 4, pp. 29 – 38. 63. http://www.fao.org/nr/land/use/en/ 64. Salvati L., Carlucci M., Urban Growth and Land-Use Structure in Two Mediterranean Regions: An Exploratory Spatial Data Analysis. SAGE Open ; October-December 2014. pp. 1–13. 65. Samat N., Hasni R., Elhadary YAE. Modelling Land Use Changes at the Peri-Urban Areas Using Geographic Information Systems and Cellular Automata Model. Journal of Sustainable Development Vol. 4, No. 6; December 2011. pp 72-84. 66. OECD, Creating rural indicators for shaping territorial policy, Paris, 1994 67. Anselin, L., GeoDa™ 0.9 User’s Guide, Spatial Analysis Laboratory, Department of Agricultural and Consumer Economics University of Illinois, Urbana-Champaign, Urbana, IL 61801, and Center for Spatially Integrated Social Science, Revised; June 15, 2003. 68. Regulation (EC) No 1059/2003. 69. Lincaru C., Atanasiu D., Periurban Areas and Population Density Clustering Model. Romanian Journal of Regional Science RJRS – The Journal of the Romanian Regional Science Association, Vol. 8. No.2; Winter 2014. pp. 29-44. 70. http://statistici.insse.ro/shop/index.jsp?page=tempo3&lang=en&ind=AGR101B 71. http://colectaredate.insse.ro/metadata/viewStatisticalResearch.htm?locale=en&researchId=2482 72. Anderson JR., Hardy EE., Roach JT., Witmer RE. A Land Use And Land Cover Classification System For Use With Remote Sensor Data. Geological Survey Professional Paper 964. A revision of the land use classification system as presented in U.S. Geological Survey Circular 671. United States Government Printing Office, Washington; 1976. Conversion to Digital 2001. 73. http://statistici.insse.ro/shop/?page=tempo3&lang=en&ind=EXP101J 74. Anselin L. Exploring Spatial Data with GeoDaTM : A Workbook, Center for Spatially Integrated Social Science, Illinois, U.S.A; 2005. 75. Chen XW., Pei ZY., Chen AL., Wang F., Shen KJ, Zhou QF., Sun L. Spatial distribution patterns and influencing factors of poverty – a case study on key country from national contiguous special poverty stricken areas in China. Procedia Environmental Sciences 26; 2015. pp. 82 – 90. 76. Ianoş I., Peptenatu D., Drăghici C., Pintilii RD. Management Elements of the Emergent Metropolitan Areas in a Transition Country. Romania, As Case Study. Journal of Urban and Regional Analysis, vol. IV 2, 2012, pp. 149 – 172. 77. Işfănescu R. Potential Clusters in Banat and their Role in Regional Economic Development. Journal of Urban and Regional Analysis, vol. II, 1, 2010; pp. 15-24. 78. Research and Innovation performance in the EU 2014, Innovation Union progress at country level edited by Directorate-General for Research and Innovation, EUROPEAN COMMISSION, EUR 26334 EN, 236. 79. Popa N. Mutations in the evolution of the growth poles and in setting up regional balances from Romania. PROCEEDINGS of the International Conference Environment at a CrossrOads: SMART approaches for a sustainable future 2015 Annual Meeting of the Faculty of Geography Bucharest, Romania. Edited by University of Bucharest Faculty of Geography, Department of Regional Geography and Environment. November 12-15, 2015. p. 217.