Table 2.
Evaluation matrix for ecosystem services, disservices, and management costs in urban forests, adapted from Vaz et al. (2017). The potential governance responses are intended to maximize services while minimizing disservices, and list specific stakeholders involved. Scenarios align with flower diagrams in Fig. 4
Scenario type | Example | Local context | Ecosystem services | Ecosystem disservices | Management costs | Potential governance response |
---|---|---|---|---|---|---|
Positive synergy | Well-maintained roadside green stormwater infrastructure sites with medium-stature trees | Temperate city with combined sewer system, commercial district, neighborhood at moderate risk of gentrification |
Stormwater runoff reduction Aesthetic appeal Walkable streetscapes, promoting pedestrian traffic in commercial area Carbon sequestration Increased real estate values and rental prices |
Minimal disservices, although installation and ongoing maintenance results in a modest amount of greenhouse gas emissions, and some neighbors may perceive trees as promoting gentrification |
High installation costs for highly engineered sites Seasonal maintenance |
Municipal public works dept.: Sustain effective stormwater functions through seasonal maintenance, strategize techniques to lower greenhouse gas emissions from installation and maintenance, foster neighborhood dialogue to understand and counteract gentrification concerns |
Tradeoff | Large non-native invasive residential yard trees | City with a Mediterranean climate, neighborhood near natural area |
Shade for thermal comfort, building energy-use reduction, and emissions avoidance Carbon sequestration from large-stature tree Aesthetic appeal |
Invading nearby natural areas, reducing wildlife habitat Increased wildfire risk Carbon emissions from installation Infrastructure conflicts with overhead wires Nuisance complaints from shedding bark or leaf litter |
Routine risk management inspections to address infrastructure conflicts Potential emergency costs due to storms or wildfires |
Municipal policy-makers, planners: Develop policies, guidelines, and/or outreach to reduce disservices related to invasive trees and wildfire risk, coordinate with municipal foresters about best practices Residents: Carefully weigh when removal and replacement of invasive trees becomes appropriate |
Negative synergy | Recently planted street trees that have died | Subtropical city, working class neighborhood facing gentrification pressure | Minimal services, as trees died soon after planting, although during their brief life the trees may have provided some aesthetic appeal |
Unkempt standing dead trees signify lack of care Residents concerned about green gentrification Residents resist future planting programs Disposal of tree waste into landfills Carbon emissions from installation |
Sunk planting costs for trees that failed to survive |
Municipal park dept.: Provide permits for tree removal if needed, develop program to re-use tree waste Residents, contract arborists: Remove dead trees promptly Planting program: For future plantings, develop close collaborations with community organizations to address gentrification concerns, and hire local youth for maintenance and job training |