Green spaces are not all the same for the provision of air purification and climate regulation services: The case of urban parks

Abstract The growing human population concentrated in urban areas lead to the increase of road traffic and artificial areas, consequently enhancing air pollution and urban heat island effects, among others. These environmental changes affect citizen's health, causing a high number of premature deaths, with considerable social and economic costs. Nature‐based solutions are essential to ameliorate those impacts in urban areas. While the mere presence of urban green spaces is pointed as an overarching solution, the relative importance of specific vegetation structure, composition and management to improve the ecosystem services of air purification and climate regulation are overlooked. This avoids the establishment of optimized planning and management procedures for urban green spaces with high spatial resolution and detail. Our aim was to understand the relative contribution of vegetation structure, composition and management for the provision of ecosystem services of air purification and climate regulation in urban green spaces, in particular the case of urban parks. This work was done in a large urban park with different types of vegetation surrounded by urban areas. As indicators of microclimatic effects and of air pollution levels we selected different metrics: lichen diversity and pollutants accumulation in lichens. Among lichen diversity, functional traits related to nutrient and water requirements were used as surrogates of the capacity of vegetation to filter air pollution and to regulate climate, and provide air purification and climate regulation ecosystem services, respectively. This was also obtained with very high spatial resolution which allows detailed spatial planning for optimization of ecosystem services. We found that vegetation type characterized by a more complex structure (trees, shrubs and herbaceous layers) and by the absence of management (pruning, irrigation and fertilization) had a higher capacity to provide the ecosystems services of air purification and climate regulation. By contrast, lawns, which have a less complex structure and are highly managed, were associated to a lower capacity to provide these services. Tree plantations showed an intermediate effect between the other two types of vegetation. Thus, vegetation structure, composition and management are important to optimize green spaces capacity to purify air and regulate climate. Taking this into account green spaces can be managed at high spatial resolutions to optimize these ecosystem services in urban areas and contribute to improve human well‐being. Graphical abstract Figure. No Caption available. HighlightsAir purification and climate regulation were quantified in an urban green space.Different vegetation types shown different capacities to provide these services.Original woodland presented the higher ecosystem services provision.Vegetation structure, composition and management matter to services provision.Nature‐based solutions in urban areas can optimize local climate and air quality.

[1]  P. Pinho,et al.  Lichens as ecological indicators in urban areas: beyond the effects of pollutants , 2014 .

[2]  M. J. Pereira,et al.  Disentangling natural and anthropogenic sources of atmospheric sulfur in an industrial region using biomonitors. , 2015, Environmental science & technology.

[3]  C. Branquinho,et al.  Guidelines for biomonitoring persistent organic pollutants (POPs), using lichens and aquatic mosses--a review. , 2013, Environmental pollution.

[4]  I. R. Noble,et al.  What are functional types and how should we seek them , 1997 .

[5]  O. W. Purvis,et al.  Diversity and sensitivity of epiphytes to oxides of nitrogen in London. , 2007, Environmental pollution.

[6]  Virginia H. Dale,et al.  Challenges in the development and use of ecological indicators , 2001 .

[7]  Hsiao-Lan Liu,et al.  The Impact of Green Space Changes on Air Pollution and Microclimates: A Case Study of the Taipei Metropolitan Area , 2014 .

[8]  Ágnes Gulyás,et al.  Microclimate Modification by Urban Shade Trees – An Integrated Approach to Aid Ecosystem Service Based Decision-making , 2016 .

[9]  J. C. Stevens,et al.  Air pollution removal by urban trees and shrubs in the United States , 2006 .

[10]  P. Pinho,et al.  Lichen functional groups as ecological indicators of the effects of land-use in Mediterranean ecosystems , 2012 .

[11]  P. Pinho,et al.  The role of forest in mitigating the impact of atmospheric dust pollution in a mixed landscape , 2017, Environmental Science and Pollution Research.

[12]  A. Kaźmierczak,et al.  Promoting ecosystem and human health in urban areas using Green Infrastructure: A literature review , 2007 .

[13]  Ü. Niinemets,et al.  Bidirectional exchange of biogenic volatiles with vegetation: emission sources, reactions, breakdown and deposition. , 2014, Plant, cell & environment.

[14]  P. Pinho,et al.  Mapping Lichen Diversity as a First Step for Air Quality Assessment , 2004 .

[15]  Mark A. Sutton,et al.  Using lichen functional diversity to assess the effects of atmospheric ammonia in Mediterranean woodlands , 2011 .

[16]  P. Pinho,et al.  Impact of neighbourhood land-cover in epiphytic lichen diversity: analysis of multiple factors working at different spatial scales. , 2008, Environmental pollution.

[17]  P. Pinho,et al.  Causes of change in nitrophytic and oligotrophic lichen species in a Mediterranean climate: impact of land cover and atmospheric pollutants. , 2008, Environmental pollution.

[18]  L. Fahrig,et al.  Relative effects of vehicle pollution, moisture and colonization sources on urban lichens , 2012 .

[19]  D. Nowak,et al.  Tree and forest effects on air quality and human health in the United States. , 2014, Environmental pollution.

[20]  P. Matos,et al.  The application of lichens as ecological surrogates of air pollution in the subtropics: a case study in South Brazil , 2016, Environmental Science and Pollution Research.

[21]  Thomas Elmqvist,et al.  Towards an EU research and innovation policy agenda for nature-based solutions & re-naturing cities. Final report of the Horizon 2020 expert group on nature-based solutions and re-naturing cities. , 2015 .

[22]  A. Brazel,et al.  The urban physical environment: temperature and urban heat islands. Chapter 2 , 2015 .

[23]  Martin J. Westgate,et al.  A new framework for selecting environmental surrogates. , 2015, The Science of the total environment.

[24]  P. Matos,et al.  Lichen traits responding to aridity , 2015 .

[25]  Clifford W. Smith The Lichens of Great Britain and Ireland , 2009 .

[26]  P. Nimis,et al.  The lichens of Italy. A phytoclimatic outline , 1995 .

[27]  Li-wei Lai,et al.  Urban heat island and air pollution--an emerging role for hospital respiratory admissions in an urban area. , 2010, Journal of environmental health.

[28]  Markus Amann,et al.  Contributions to cities' ambient particulate matter (PM): a systematic review of local source contributions at global level , 2015 .

[29]  Catarina Freitas,et al.  Evaluating green infrastructure in urban environments using a multi-taxa and functional diversity approach. , 2016, Environmental research.

[30]  M. Jansson Green space in compact cities: The benefits and values of urban ecosystem services in planning , 2014 .

[31]  R. D. Groot,et al.  Effects of urban trees on local outdoor microclimate: synthesizing field measurements by numerical modelling , 2015, Urban Ecosystems.

[32]  M. Prasad Metals in the environment : analysis by biodiversity , 2001 .

[33]  J. Lelieveld,et al.  The contribution of outdoor air pollution sources to premature mortality on a global scale , 2015, Nature.

[34]  P. Pinho,et al.  Tracking the Spatial Fate of PCDD/F Emissions from a Cement Plant by Using Lichens as Environmental Biomonitors. , 2016, Environmental science & technology.

[35]  P. Pinho,et al.  Modeling the long-term natural regeneration potential of woodlands in semi-arid regions to guide restoration efforts , 2014, European Journal of Forest Research.

[36]  B. McCune,et al.  Analysis of Ecological Communities , 2002 .

[37]  B. Demmig‐Adams,et al.  The effect of atmospheric desiccation and osmotic water stress on photosynthesis and dark respiration of lichens , 1990 .

[38]  R. McDonald,et al.  Planting healthy air: a global analysis of the role of urban trees in addressing particulate matter pollution and extreme heat. , 2016 .

[39]  M. J. Pereira,et al.  Traffic represents the main source of pollution in small Mediterranean urban areas as seen by lichen functional groups , 2017, Environmental Science and Pollution Research.

[40]  C. N. Hewitt,et al.  Quantifying the effect of urban tree planting on concentrations and depositions of PM10 in two UK conurbations , 2007 .

[41]  M. J. Pereira,et al.  The use of lichen functional groups as indicators of air quality in a Mediterranean urban environment , 2012 .

[42]  Helga Jordão,et al.  Floristic changes of epiphytic flora in the Metropolitan Lisbon area between 1980–1981 and 2010–2011 related to urban air quality , 2016 .