Dark infrastructure

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Areas of light across Earth at night Earth's City Lights by DMSP, 1994-1995 (large).jpg
Areas of light across Earth at night

Dark infrastructure refers to interconnected networks of natural, semi-natural and urbanized spaces, characterized by low levels of artificial light at night (ALAN), that create ecological continuities in order to provide benefits such as ecological restoration, wildlife conservation, and human health. Dark infrastructure aims to recognize the need for natural periods of darkness for life on Earth. [1]

Contents

In practice, different levels of administrative agencies assess, upgrade and monitor existing areas where the environment remains sufficiently undisturbed light-wise for biodiversity to prosper. Modeled on and complementary to ecological infrastructure networks, dark infrastructure most often consists of cores of darkness connected through corridors. They are expected to sustain human and wildlife health as well as maintain ecosystem services in urban areas. [1]

Some cities and regions (e.g. Trame noire, Eurométropole Metz [2] ) in France, Switzerland (e.g. Trame noire and Plan Lumière, Geneva [3] ) and the United States have adopted this approach. Some cities in Normandie have since rescinded their plan.

Several western countries have seen the emergence of dark-sky movements, which focus on the human benefits of experiencing starry night skies.

The rationale is that since the industrial revolution, the intensity and area of artificially lit outdoor spaces has increased dramatically worldwide, disrupting natural cycles and circadian rhythms of humans and animals alike. The effects of ALAN on wildlife, human health, ecosystem services and biodiversity are widespread and severe. Through the Avoiding Barrier effect for terrestrial mammals and amphibians and the Sink/Crash barrier effect for insects and possibly birds, ALAN can further amplify habitat loss and fragmentation for many organisms.

Adverse effects of light pollution

Light Pollution or ALAN is known to cause harm to humans, flora and fauna alike. [4] [1] [5]

Humans

For humans, this includes adverse effects on the visual system and sleep quality (e.g., by an impaired melatonin secretion, disruption of the circadian rhythm). Early-stage research also links ALAN to a higher risk of chronic diseases. [5]

Fauna

Illustration of artificial light corridor effect on the behavior of different taxons. 1-s2.0-S0169204621002954-gr2 lrg.jpg
Illustration of artificial light corridor effect on the behavior of different taxons.

ALAN has been linked as one of the causes of the collapse of insect populations which is happening around the world. [1] The skyglow caused by ALAN can sometimes cover areas of over ten to hundreds of kilometers, even affecting animals in unpopulated areas and protected habitats. [6] [7] One problem of the additional light exposure during the night is the disruption of the circadian rhythm and associated risks similar to humans. Another issue arising from ALAN for animals in the sense that lit areas act as barriers that some animals cannot cross. They either avoid the light barrier altogether (bats, some mammals) (see Image, left) or are attracted by the light and enter the lit area, leading to entrapment inside and possibly death (see Image, right). This can subsequently lead to habitat loss and segmentation, reduces available resources, increases competition and can change predation. All artificial light at night that exceeds the equivalent of that of naturally occurring moonlight lunar phase has negative effects on physiology, behavior, and life-history traits.

Flora

The impact of ALAN on plants has been studied less than on animals. Plant leaf functions and resource-management strategies can be affected negatively as well as resource acquisition rate and disrupt the circadian rhythm and circannual cycle. [4] [8] [9] Aquatic ecosystems close to the coast/shoreline are particularly exposed, since lit infrastructure/urban development are located along rivers, lakes, and sea shores. [4]

Overall, ALAN acts as a pressure for biodiversity, especially contributing to habitat loss and landscape fragmentation.

Implementation and methods

In a notable article published in 2022, an international group of scientists have called to "promote the integration of darkness quality within the 'green and blue infrastructure', to implement a 'dark infrastructure'" and proposed a 4 step-process. [1] They proposed that first the light pollution of the given territory must be quantified and mapped. Second, existing dark infrastructure, or areas where nighttime darkness is already maintained at an optimal level for wildlife, must be identified. Third, this dark infrastructure is to be preserved to prevent further light pollution and restored or expanded upon in areas where the lighting can be modified to increase darkness. Fourth, the infrastructure must be monitored and assessed for effectiveness. [1]

Sources of artificial light at night in Atlanta. Downtown Atlanta at night (39500731114).jpg
Sources of artificial light at night in Atlanta.

The restoration or expansion of dark infrastructure can be carried out via the reduction of artificial lighting across several parameters, including the strength of the illumination, the timing of the lighting period, and the direction and area of the illumination, in order to maintain these cores and corridors of nighttime darkness. [1] [10] Light sources include street lamps, billboards, illuminated signs, car headlights, and indoor lighting that is visible through windows.

Methods to increase darkness include:

Known projects:

Benefits and challenges

Dark infrastructures have numerous ecological and human health benefits, including reduced light pollution and the preservation of nocturnal biodiversity by functioning as sanctuaries for light-sensitive species. [18] [1] Many species, including bats, moths, amphibians, and migratory birds, rely on darkness for critical behaviors such as foraging, mating, and navigation. [18] Dark infrastructure helps reduce habitat fragmentation [19] and protect pollination networks that rely on nocturnal insects. [20] Furthermore, these corridors benefit human health by increasing sleep quality and lowering the risks associated with artificial light exposure, such as sleep disorders. [21] Aside from health benefits, they can help lower energy consumption by reducing unnecessary lighting. [18] [22]

However, implementing dark infrastructure also presents numerous challenges and risks that must be carefully managed. The opinions of various stakeholders, such as society, ecology, the economy, authorities, and private interests, must be considered. [22] One major concern is public safety, as reduced lighting may increase feelings of insecurity, potentially limiting public support for these initiatives. [23] Insufficient lighting along roads and pedestrian paths can also increase the risk of traffic accidents, necessitating the use of adaptive lighting solutions. [24]

From an ecological point of view, dark infrastructure may unintentionally aid in the spread of invasive species or disrupt predator-prey relationships, thereby affecting conservation objectives. [25] [18]

Furthermore, businesses that rely on outdoor lighting (e.g., private and commercial lighting installations) may oppose stricter regulations, [18] and urban planning initiatives may clash with existing zoning laws.

High initial costs and the need for continuous monitoring further complicate their implementation. [22] [19] They require thoughtful design strategies that balance ecological preservation with urban functionality. [19]

References

  1. 1 2 3 4 5 6 7 8 9 10 11 12 13 Sordello, Romain; Busson, Samuel; Cornuau, Jérémie H.; Deverchère, Philippe; Faure, Baptiste; Guetté, Adrien; Hölker, Franz; Kerbiriou, Christian; Lengagne, Thierry; Le Viol, Isabelle; Longcore, Travis; Moeschler, Pascal; Ranzoni, Jessica; Ray, Nicolas; Reyjol, Yorick (March 2022). "A plea for a worldwide development of dark infrastructure for biodiversity – Practical examples and ways to go forward". Landscape and Urban Planning. 219: 104332. Bibcode:2022LUrbP.21904332S. doi:10.1016/j.landurbplan.2021.104332.
  2. "La trame noire". www.eurometropolemetz.eu. Retrieved 2025-02-04.
  3. vCard, Télécharger la. "Plan lumière de la Ville de Genève | Ville de Genève - Site officiel". www.geneve.ch (in French). Retrieved 2025-02-04.
  4. 1 2 3 Segrestin, Jules; Mondy, Nathalie; Boisselet, Christelle; Guigard, Ludivine; Lengagne, Thierry; Poussineau, Sophie; Secondi, Jean; Puijalon, Sara (December 2021). "Effects of artificial light at night on the leaf functional traits of freshwater plants". Freshwater Biology. 66 (12): 2264–2271. Bibcode:2021FrBio..66.2264S. doi:10.1111/fwb.13830. ISSN   0046-5070.
  5. 1 2 Zielinska-Dabkowska, K. M.; Schernhammer, E. S.; Hanifin, J. P.; Brainard, G. C. (2023-06-16). "Reducing nighttime light exposure in the urban environment to benefit human health and society". Science. 380 (6650): 1130–1135. Bibcode:2023Sci...380.1130Z. doi:10.1126/science.adg5277. PMID   37319219.
  6. Davies, Thomas W.; Duffy, James P.; Bennie, Jon; Gaston, Kevin J. (2016). "Stemming the Tide of Light Pollution Encroaching into Marine Protected Areas". Conservation Letters. 9 (3): 164–171. Bibcode:2016ConL....9..164D. doi:10.1111/conl.12191. hdl: 10871/17713 . ISSN   1755-263X.
  7. Gaston, Kevin J.; Duffy, James P.; Bennie, Jonathan (2015). "Quantifying the erosion of natural darkness in the global protected area system". Conservation Biology (in Spanish). 29 (4): 1132–1141. Bibcode:2015ConBi..29.1132G. doi:10.1111/cobi.12462. ISSN   1523-1739.
  8. UFAM, Bundesamt für Umwelt BAFU | Office fédéral de l'environnement OFEV | Ufficio federale dell'ambiente. "Dunkelheit und Licht: von beidem genug und am richtigen Ort". www.bafu.admin.ch (in German). Retrieved 2025-02-03.
  9. Falcón, Jack; Torriglia, Alicia; Attia, Dina; Viénot, Françoise; Gronfier, Claude; Behar-Cohen, Francine; Martinsons, Christophe; Hicks, David (2020-11-16). "Exposure to Artificial Light at Night and the Consequences for Flora, Fauna, and Ecosystems". Frontiers in Neuroscience. 14. doi: 10.3389/fnins.2020.602796 . ISSN   1662-453X. PMC   7701298 . PMID   33304237.
  10. 1 2 3 4 5 6 7 Pollutec (2024-05-06). "THE BLACK INFRASTRUCTURE - EXPLORING IMPACTS, ISSUES, METHODS AND TOOLS". Pollutec Learn & Connect | English. Retrieved 2025-01-31.
  11. 1 2 3 4 5 6 7 "Urban lighting: 6 ways to create local dark infrastructures | Paysalia 2025". www.paysalia.com. Retrieved 2025-01-31.
  12. Sierro, Antoine (January 2019). La lumière nuit! LA NATURE FACE À LA POLLUTION LUMINEUSE (in French). Canton du Valais: Departement de l'economie et de la formation.
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  15. "Éteindre l'éclairage public dans la métropole de Rouen : pourquoi certains reviennent sur leur décision". actu.fr (in French). 2024-12-09. Retrieved 2025-02-03.
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  18. 1 2 3 4 5 "ETC HE Report 2022/8: Review and Assessment of Available Information on Light Pollution in Europe". Eionet Portal. Retrieved 2025-02-05.
  19. 1 2 3 Sordello, Romain; Busson, Samuel; Cornuau, Jérémie H.; Deverchère, Philippe; Faure, Baptiste; Guetté, Adrien; Hölker, Franz; Kerbiriou, Christian; Lengagne, Thierry; Le Viol, Isabelle; Longcore, Travis; Moeschler, Pascal; Ranzoni, Jessica; Ray, Nicolas; Reyjol, Yorick (2022-03-01). "A plea for a worldwide development of dark infrastructure for biodiversity – Practical examples and ways to go forward". Landscape and Urban Planning. 219: 104332. Bibcode:2022LUrbP.21904332S. doi:10.1016/j.landurbplan.2021.104332. ISSN   0169-2046.
  20. Knop, Eva; Zoller, Leana; Ryser, Remo; Gerpe, Christopher; Hörler, Maurin; Fontaine, Colin (2017). "Artificial light at night as a new threat to pollination". Nature. 548 (7666): 206–209. Bibcode:2017Natur.548..206K. doi:10.1038/nature23288. ISSN   1476-4687.
  21. Cho, YongMin; Ryu, Seung-Hun; Lee, Byeo Ri; Kim, Kyung Hee; Lee, Eunil; Choi, Jaewook (2015-10-21). "Effects of artificial light at night on human health: A literature review of observational and experimental studies applied to exposure assessment". Chronobiology International. 32 (9): 1294–1310. doi:10.3109/07420528.2015.1073158. ISSN   0742-0528. PMID   26375320.
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  23. Beaudet, Chloé; Tardieu, Léa; David, Maia (2022-10-01). "Are citizens willing to accept changes in public lighting for biodiversity conservation?". Ecological Economics. 200: 107527. Bibcode:2022EcoEc.20007527B. doi:10.1016/j.ecolecon.2022.107527. ISSN   0921-8009.
  24. Jackett, Michael; Frith, William (2013-03-01). "Quantifying the impact of road lighting on road safety — A New Zealand Study". IATSS Research. 36 (2): 139–145. doi: 10.1016/j.iatssr.2012.09.001 . ISSN   0386-1112.
  25. Maurer, Andrew S.; Cove, Michael V.; Siegal, Olivia M.; Lashley, Marcus A. (2022-06-01). "Urbanization affects the behavior of a predator-free ungulate in protected lands". Landscape and Urban Planning. 222: 104391. Bibcode:2022LUrbP.22204391M. doi:10.1016/j.landurbplan.2022.104391. ISSN   0169-2046.

Further readings