The Relation Between Road Crack Vegetation and Plant Biodiversity in Urban Landscape

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The Relation Between Road Crack Vegetation and Plant Biodiversity in Urban Landscape Int. J. of GEOMATE, June, 2014, Vol. 6, No. 2 (Sl. No. 12), pp. 885-891 Geotech., Const. Mat. & Env., ISSN:2186-2982(P), 2186-2990(O), Japan THE RELATION BETWEEN ROAD CRACK VEGETATION AND PLANT BIODIVERSITY IN URBAN LANDSCAPE Taizo Uchida1, JunHuan Xue1,2, Daisuke Hayasaka3, Teruo Arase4, William T. Haller5 and Lyn A. Gettys5 1Faculty of Engineering, Kyushu Sangyo University, Japan; 2Suzhou Polytechnic Institute of Agriculture, China; 3Faculty of Agriculture, Kinki University, Japan; 4Faculty of Agriculture, Shinshu University, Japan; 5Center for Aquatic and Invasive Plants, University of Florida, USA ABSTRACT: The objective of this study is to collect basic information on vegetation in road crack, especially in curbside crack of road, for evaluating plant biodiversity in urban landscape. A curbside crack in this study was defined as a linear space (under 20 mm in width) between the asphalt pavement and curbstone. The species composition of plants invading curbside cracks was surveyed in 38 plots along the serial National Route, over a total length of 36.5 km, in Fukuoka City in southern Japan. In total, 113 species including native plants (83 species, 73.5%), perennial herbs (57 species, 50.4%) and woody plants (13 species, 11.5%) were recorded in curbside cracks. Buried seeds were also obtained from soil in curbside cracks, which means the cracks would possess a potential as seed bank. Incidentally, no significant differences were found in the vegetation characteristics of curbside cracks among land-use types (Kolmogorov-Smirnov Test, P > 0.05). From these results, curbside cracks would be likely to play an important role in offering habitat for plants in urban area. Keywords: Biodiversity, Road Crack, Seed Bank, Urban Area, Vegetation 1. INTRODUCTION diversity and ecosystems [12], [19], [20]. And, to evaluate the urban biodiversity and ecosystems, the Roads are important infrastructure components sites where could be habitats for plant, such as that provide critical corridors for transporting goods wetland, riverside, garden, park or shrine in the and humans. Expansion and integration of asphalted cities, have been surveying [12]. road networks would symbolize urbanization. Some In this study, we hypothesize that road cracks, plants, however, become established in curbside especially curbside cracks of road, can be site where cracks of road and cause deterioration of asphalt and some plants establish including ecologically curbs, reducing road surface longevity and safety valuable species, and be evaluated as useful habitat (Fig. 1). Therefore, road managers spend a consider- for plant. To investigate above hypothesis, we able amount of time and money on roadside surveyed plant that invades curbside cracks of road; vegetation management [4]. In this context, several we compared species composition and characteris- ecological traits of plants in curbside cracks of road tics in the curbside cracks among land-use types in have been also shown for effective road manage- urban area. The objective of this study is to collect ment [4], [5], [18]. basic information on vegetation in road crack, On the other hand, there has been growing especially in curbside cracks of road, for evaluating interest in the effect of urbanization on the bio- plant biodiversity in urban area. xxxxxxxx 2. MATERIALS AND METHODS 2.1 Study Area Surveying of vegetation in curbside cracks was conducted in Fukuoka City, southern Japan, in September 2012 along National Route 3, 202 and 263, over a total distance of 36.5 km (Fig. 2). Fukuoka City is one of the biggest cities in Japan besides Tokyo, Osaka and Nagoya, and the population is around one and a half million, the density is 4,392 km-2, as of May 1, 2013 (Fukuoka City Environmental Data System). According to Fig. 1 Some plants established in curbside cracks AMEDAS (Automated Meteorological Data aaaaaaaaof road. Acquisition System) from 2003 to 2012, Fukuoka 885 Int. J. of GEOMATE, June, 2014, Vol. 6, No. 2 (Sl. No. 12), pp. 885-891 City lies in the warm-temperature zone, with values xxxx of Kira’s Warmth Index [9] ranging from 143.4 to 155.5 °C and with annual precipitation of 1,020 to 2,018 mm. 2.2 Species Composition and Characteristics Route 3 The species composition of vegetation in curbside cracks was recorded according to the Route 202 methodology of Braun-Blanquet cover-abundance Route 263 scale [2]. A curbside crack was defined as a linear space (under 20 mm in width) between the asphalt pavement and curbstone [4]. We located 38 survey 0 2 4 km plots along the route at intervals of approximately 1 km. The size of the plots was 50 m (length) × 20 mm (maximum width of the crack). Fig. 2 Location of study sites. Plant nomenclature used in this paper followed Miyawaki et al. (1994), Baba (1999) and Shimizu (2003). All the recorded species were categorized by life form (dormancy form, disseminule form, types [3], [21]. The vegetation characteristics radicoid form and growth form) and invasive status employed were the following: the total number of (native or non-native), in order to characterize the species, average number of species, Sannon- vegetation surveyed. Life form was based on the Wiener’s diversity index (H’) and the percentage of description by Raunkiaer (1934) and Numata (1990), non-native species. and we distinguished non-native from native species Horn’s measurement of overlap [6] was done based on published literature [1], [11], [17]. Using with mean cover data of species in each land-use aerial photographs and field observation, dominant type in order to examine the similarity of species land-use types within a radius of 100 m from each composition among land-use types. According to the survey plot were classified as forest, business area, residential districts, developed land, dry fields and Eq. (1), Summed Dominance Ratio (SDR) of species paddy fields. [14] in each land-use type was also calculated; 2.3 Soil Property SDR = (F’ + C’) / 2 (1) The soil was collected from curbside crack in Where F’ and C’ is the ratio of frequency and each survey plot, using stainless spatula, for mea- cover of each species to the numbers of the most surement of pH and EC. abundant species, respectively. And then, in order to estimate the potential To find out whether the proportion of each life vegetation in curbside crack, the soil obtained from 2 form was different among land-use types, we the crack was spread over 20 cm with thickness of conducted a two-way ANOVA. The differences in 1.5 cm on the vinyl pot filled with expanded vermiculite. Prepared pots were put under the pH and EC of curbside crack soil among land-use constant temperature of 25 °C with 12 hours light of types were also analyzed using an ANOVA. All of 3,300-3,600 lux a day for 3 months, and plant the data for the ANOVAs were used after trans- emerged from the soil was regularly identified. forming to ln(x + 0.5) value. 2.4 Data Analysis 3. RESULTS Braun-Blanquet cover-abundance scale (r, +, I, II, 3.1 Species Composition and Characteristics III, IV and V) was transformed as follows: r and +, 0.1%; I, 5.0%; II, 17.5%; III, 37.5%; IV, 62.5% and In total, 113 species including 83 (73.5%) V, 87.5%. natives were observed in curbside cracks along the To test whether characteristics of vegetation in surveyed routes (Appendix 1), of which 100 (88.5%) curbside cracks were different among land-use types, species were herbaceous and 13 (11.5%) species we conducted a Kolmogorov-Smirnov test, under the were woody plants. In the former, 57 perennials null hypothesis that vegetation characteristics of (50.4%) were recorded. Of the 36 families obtained curbside cracks were equivalent across land-use in this survey (Appendix 1), Poaceae and Asteraceae 886 Int. J. of GEOMATE, June, 2014, Vol. 6, No. 2 (Sl. No. 12), pp. 885-891 Txxable 1 Vegetation characteristics of curbside cracks among land-use types. Vegetation characteristics Number of survey Total number of Average number of Sannon-Wiener's Percentage of non- Land-use types plots species species diversity index (H ') native species Forest 18 63 13.3 1.670 19.0 Business area 12 45 10.6 1.952 35.6 Residential districts 14 41 18.7 1.785 39.0 Developed land 11 20 20.0 2.987 40.0 Dry fields 13 23 10.0 1.675 30.4 Paddy fields 10 - - - - P -value - 0.200ns 0.194ns 0.053ns 0.200ns P > 0.05: ns indicates not significant using Kolmogorov-Smirnov test. Horn's overlap index (Ro) 1.0 0.8 0.6 0.4 accounted for the majority of herbaceous plants (47/100 species), and Ulmaceae was dominant in woody plants recorded (4/13 species). V1 n = 26 No significant differences were found in the vegetation characteristics of curbside cracks across land-use types (P > 0.05) (Table 1). V2 Using Horn’s measurement of overlap three n = 9 vegetation types could be distinguished (Fig. 3). Type V1 contained business area and residential V3 districts (n = 26), and Type V2 included forest and n = 3 developed land (n = 9). Type V3 consisted of dry fields (n = 3). Common species to all vegetation Fig. 3 Classification of 5 land-use types based on types (12/113 species) were Artemisia princeps aaaaaaaamean cover of component species. See xxxxx aaaaaaaaAppendix 1. 10100%0 ( I ) 1001%00 ( III ) P = 0.757ns P = 0.908ns 7157%5 751%75 5105%0 501%50 Th(w) R5 ) 125 25% 251%25 R4 % Th ( s H R3 m r 100 Ch R2 o 0% 01%00 f e 群V1A 群V2B 群V3C V1 V2 V3 f 群A 群B 群C i l f o n o i 10100%0 10100%0 t ( II ) ( IV ) r o ns P = 0.830ns p P = 0.645 o r P 7157%5 7157%5 t-p t,t-p t 150 50% 5105%0 r ps 2152%5 2152%5 pr D4 p-b D3 e 100%0 D1 100%0 b-p 群V1A 群V2B 群V3C 群VA1 群VB2 群V3C Vegetation types Fig.
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