Abstract

The green roofs sector is a relatively recent phenomenon in Mediterranean countries, meaning that as yet there is no complete understanding of which plants are suited to this particular environment. Such plants would need to be adaptable to the green roof itself as well as to the drought and intense lighting typical of a Mediterranean summer. Two simulated green roofs were planted with a variety of species and life forms and subjected to two minimal irrigation treatments and one treatment without irrigation. Mainly subshrub species were planted in one simulation, while the other contained a prevalence of groundcover species. The study looked at performance in terms of species, life forms, and simulation. We analysed flowering, mortality, frequency of planted species and of invasive species, and biomass. We took periodic measurements of cover and of the Shannon-Wiener vegetal diversity index. The groundcover species obtained a higher degree of cover, but suffered more from seasonal stresses. Both green roofs saw an increase in the abundance of a few species, leading to a simplification of the original design. Diversity and the ability to host colonising species were influenced mainly by differences in vegetational structure. Of the subshrub species, Centranthus ruber and Helichrysum stoechas performed best, while Frankenia laevis and Thymus serpyllum came top among groundcover species. In order to withstand severe drought stress, a minimal amount of irrigation was found to be necessary. Our study demonstrates that it is possible to obtain good results from a Mediterranean green roof by using an appropriate combination of vegetal species with different structures and development.

Highlights

  • Green roofs represent an ideal opportunity to improve the urban environment

  • There were no significant differences in average mortality rates between the three different irrigation treatments in the subshrub green roof

  • The green roof containing groundcover species obtained a higher level of cover that the green roof with subshrub species, a situation which can be explained by structural differences between the two species groups: the subshrubs tend to develop more in terms of volume while the groundcover species grow horizontally and superficially

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Summary

Introduction

Green roofs represent an ideal opportunity to improve the urban environment. They increase biodiversity in cities (Lundholm, 2006; Oberndorfer et al, 2007; Bass, 2009), lead to reduced energy costs for the buildings on which they are installed (Liu & Baskaran, 2003; Carter & Butler, 2008; Spala et al, 2008), and by absorbing rainwater they reduce stormwater runoff and the consequent overloading of drainage systems (Liu & Minor, 2005; Mentens et al, 2006; Stovin, 2010). The delay in implementing green roofs technology is related to specific climate conditions in the Mediterranean area, including high temperatures and prolonged droughts. In many large cities, including London and Hong Kong, green roofs are seen as an important instrument in the urban planner’s attempts to combat the aforementioned effects (Townshend & Duggie, 2007; Greater London Authority, 2008; Van Lennep & Finn, 2008)

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