Abstract
Cities are concentrations of sociopolitical power and prime architects of land transformation, while also serving as consumption hubs of “hard” water and energy infrastructures. These infrastructures extend well outside metropolitan boundaries and impact distal river ecosystems. We used a comprehensive model to quantify the roles of anthropogenic stressors on hydrologic alteration and biodiversity in US streams and isolate the impacts stemming from hard infrastructure developments in cities. Across the contiguous United States, cities’ hard infrastructures have significantly altered at least 7% of streams, which influence habitats for over 60% of North America’s fish, mussel, and crayfish species. Additionally, city infrastructures have contributed to local extinctions in 260 species and currently influence 970 indigenous species, 27% of which are in jeopardy. We find that ecosystem impacts do not scale with city size but are instead proportionate to infrastructure decisions. For example, Atlanta’s impacts by hard infrastructures extend across four major river basins, 12,500 stream km, and contribute to 100 local extinctions of aquatic species. In contrast, Las Vegas, a similar size city, impacts <1,000 stream km, leading to only seven local extinctions. So, cities have local policy choices that can reduce future impacts to regional aquatic ecosystems as they grow. By coordinating policy and communication between hard infrastructure sectors, local city governments and utilities can directly improve environmental quality in a significant fraction of the nation’s streams reaching far beyond their city boundaries.
Original language | English |
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Pages (from-to) | 9581-9586 |
Number of pages | 6 |
Journal | Proceedings of the National Academy of Sciences of the United States of America |
Volume | 114 |
Issue number | 36 |
DOIs | |
State | Published - Sep 5 2017 |
Funding
indigenous or nonindigenous species currently present but historically undetected (Uc and NUc, respectively), and the number of indigenous species historically present but currently undetected (Uh). For each taxon, we calculated detection probabilities for indigenous species (pi) and nonindigenous species (pn), where pi = Uc/Rc and pn = NUc/NRc. We then corrected for false absences by inflating species richness estimates for current indigenous species (Rbc) and nonindigenous species (NRdc), but deflating locally extinct indigenous species richness (Uhc) using the following: Rcb = Uc/pi + (Rc − Uc), NRcd = NUc/pn + (NRc − NUc), and Uhc=Uh×pi. ACKNOWLEDGMENTS. We thank Mark Peterson, Jay Gulledge, Shih-Chieh Kao, Brennan Smith, and John Neal for support of the research concept; Jesse Piburn for assistance with residential energy demand estimates; and Brenda Pracheil and Mike Goodchild for providing comments and editorial suggestions on earlier versions of this manuscript. Funding was provided by the Oak Ridge National Laboratory Directed Research and Development Program. B.L.R. was supported by National Science Foundation Grant ACI-1639529. This manuscript has been authored by UT-Battelle, LLC, under contract DE-AC05-00OR22725 with the US Department of Energy (DOE). The US Government retains and the publisher, by accepting the article for publication, acknowledges that the US Government retains a nonexclusive, paid-up, irrevocable, worldwide license to publish or reproduce the published form of this manuscript, or allow others to do so, for US Government purposes. The DOE will provide public access to these results of federally sponsored research in accordance with the DOE Public Access Plan (https://energy.gov/ downloads/doe-public-access-plan).
Funders | Funder number |
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US Department of Energy | |
National Science Foundation | 1639529, DE-AC05-00OR22725, ACI-1639529 |
National Science Foundation | |
U.S. Department of Energy | |
Oak Ridge National Laboratory |
Keywords
- Electricity
- Energy–water nexus
- Hydrologic alteration
- Urban ecology
- Urban sustainability