5. Conclusion
In this study, we evaluated participatory mapping methods for assessing urban park benefits. The scaling-up of these methods from the suburb-level to a large urban-park system introduced greater variability in the results but multiple urban park benefits by park type associations were confirmed at the larger urban scale. Participatory mapping, with a focus on the distribution of park benefits in addition to physical design standards, can provide supplemental information to refine and adjust physical park standards.
There is contemporary academic interest in the assessment and analysis of urban areas for ecosystem services (e.g., Gómez-Baggethun & Barton, 2013; Rall et al., 2017; Woodruff & BenDor, 2016). The participatory mapping methods described in this study provide a means to assess cultural ecosystem services associated with urban parks and greenspaces. However, as noted by Ahearn et al. (2014), the assessment of urban ecosystem services alone does not provide the innovation required to inform routine urban and infrastructure development activity (Ahern, Cilliers, & Niemelä, 2014). And yet, participatory mapping offers the potential to better inform urban green infrastructure because of its spatially-explicit, systems approach to assessment focused on a range of benefits. Future research could analyze the spatial distribution of park benefits by suburb or neighborhood (spatial disaggregation) to identify social inequities in park benefits that could be addressed through further development of green infrastructure.