Ground-based hyperspectral analysis of the urban nightscape

https://doi.org/10.1016/j.isprsjprs.2016.12.004Get rights and content

Abstract

Airborne hyperspectral cameras provide the basic information to estimate the energy wasted skywards by outdoor lighting systems, as well as to locate and identify their sources. However, a complete characterization of the urban light pollution levels also requires evaluating these effects from the city dwellers standpoint, e.g. the energy waste associated to the excessive illuminance on walls and pavements, light trespass, or the luminance distributions causing potential glare, to mention but a few. On the other hand, the spectral irradiance at the entrance of the human eye is the primary input to evaluate the possible health effects associated with the exposure to artificial light at night, according to the more recent models available in the literature. In this work we demonstrate the possibility of using a hyperspectral imager (routinely used in airborne campaigns) to measure the ground-level spectral radiance of the urban nightscape and to retrieve several magnitudes of interest for light pollution studies. We also present the preliminary results from a field campaign carried out in the downtown of Barcelona.

Introduction

Light pollution is an issue of growing interest for urban planners, city managers and environmental protection agencies. In its broadest sense, this term encompasses the undesired side-effects associated with the production and use of artificial light, especially at nighttime (Falchi et al., 2011, Bará, 2013, Bará, 2014). Excessive or misdirected light leads to unnecessary energy waste and increased greenhouse gas emissions (Gallaway et al., 2010, Kyba et al., 2014), and poses, according to recent findings, non-negligible threats to the nocturnal environment (Hölker et al., 2010, Gaston et al., 2013, Gaston et al., 2015) as well as potential health hazards (Cho et al., 2015, Haim and Zubidat, 2015, Stevens et al., 2013).

Making strategic decisions on outdoor lighting policy at local and regional levels requires an accurate knowledge of the actual light emissions, ideally with enough spatial and spectral resolution to allow the identification of individual light sources, their directional emission patterns and their detailed spectral composition (Elvidge et al., 2010).

Urban radiance data with moderate spatial resolution are currently available from several instruments on board of space platforms, such as the historical time series of the Operational Linescan System (OLS) of the U.S. Defense Meteorological Satellite Program (DMSP) (Cinzano and Elvidge, 2004, Elvidge et al., 2013, Yang et al., 2014), the Suomi-NPP VIIRS instrument Day-Night Band (DBN) (Miller et al., 2013), and the Earth images taken with commercial grade cameras from the International Space Station (ISS) (Castiglione et al., 2012). The DMSP and Suomi-NPP satellites, located in near polar orbits at altitudes close to 850 km, provide whole Earth coverage with radiance detection limits of order 5 × 10−10 and 2 × 10−11 W cm−2 sr−1, and ground footprint sizes of 5 km and 742 m, respectively. They give no spectrally resolved information, because the detection is performed in a single 0.5–0.9 μm panchromatic band (Elvidge et al., 2013). NightPod-based ISS nighttime imagery (Castiglione et al., 2012), acquired from an orbit at about 400 km altitude with 51.6° inclination and variable footprint pixel size, is restricted in turn to the conventional Bayer matrix RGB bands. Despite this spectral limitation, satellite data are the primary source of information about urban wasted light at planetary scale (Cinzano et al., 2000, Cinzano et al., 2001, Cinzano and Elvidge, 2004, Sánchez de Miguel et al., 2014), correlate well with on-site flux measurements, and are useful tools for monitoring changes in upward light emissions after remodeling urban lighting systems (Estrada-García et al., 2015). The number of spaceborne instruments monitoring the city lights has been, however, comparatively very small until now (Belward and Skøien, 2015). Given the useful information they may provide and the relevance of the study of the anthropogenic emissions of light it is highly desirable that new satellite programs, ideally with nighttime multispectral capabilities, be planned in the near future.

Considerably better spatial and spectral resolution can be achieved with airborne hyperspectral imaging spectrometers, at the expense of a smaller area coverage. Hyperspectral imaging, that has found many applications in Earth imagery (see, e.g., Aasen et al., 2015, Clark and Kilham, 2016) including urban areas (Demarchi et al., 2014, Kotthaus et al., 2014), has also been successfully applied to the study of nighttime artificial lights (Barducci et al., 2003a, Barducci et al., 2003b, Barducci et al., 2003b, Barducci et al., 2006, Kruse and Elvidge, 2011). Airborne hyperspectral measurements combined with photogrammetric imagery allow to obtain reliable estimates of the upward luminance from urban areas with spatial resolutions well below one meter, as we have shown in previous works (Pipia et al., 2014, Corbera et al., 2015).

The overall radiant flux emitted towards the upper hemisphere by urban areas is a measure of the degree of lighting energy waste and is the leading cause of increased skyglow. This flux, however, is only part of the whole light pollution picture. Several detrimental effects of light pollution are essentially ground-level phenomena. They include, among others, light intrusion, disability and discomfort glare, light clutter, and the diverse photobiological effects of light at night. To evaluate the severity of these effects one needs to know the spectral radiance of the urban nightscape, as seen from the city dwellers standpoint. This radiance distribution allows the assessment of glare and light cluttering. It is also instrumental for computing the spectral irradiance in a plane tangent to the human corneal vertex for arbitrary gaze directions, which is the primary input for evaluating the physiological effects of light at night by means of suitable phototransduction models (CIE, 2015, Rea et al., 2005, Rea et al., 2010, Rea et al., 2012). The vertical irradiance on window panes allows, in turn, to quantify the severity of light trespass effects.

As in other areas of remote sensing (Chen et al., 2016), a comprehensive assessment of the overall levels of light pollution can only be achieved if the airborne and satellite data are complemented with ground based measurements acquired from within the town. In this work we describe the adaptation and operation of a hyperspectral imaging sensor routinely used for airborne surveys to acquire these additional datasets from the city streets. Hyperspectral light pollution measurements require dealing with spatially uneven, high dynamic range radiance distributions, and keeping the noise propagation within admissible levels. In Section 2 we describe the hyperspectral measurement system. The data reduction process implemented to get the desired magnitudes is summarized in Section 3. The results of a proof-of-concept measurement campaign carried out in the city of Barcelona are reported in Section 4. Discussion and conclusions are finally drawn in Sections 5 and 6, respectively.

Section snippets

Site selection

The field campaign was carried out at the city of Barcelona (3 million inh.), capital of Catalonia, in the period around the new Moon in February 19th to 20th, 2015. Its public outdoor lighting is mainly based on high pressure sodium vapor and metal halide lamps, with an increasing presence of phosphor-coated white Light Emitting Diode (LED) streetlights and self-luminous billboards. Several downtown areas were selected for measurements, including Plaça d'Espanya (site 1) and Jardinets de

Methods

In this section it is described on the one hand the theoretical frame of the work, including the products derived from the hyperspectral images, and, on the other hand, some image processing methods to deal with several image artifacts inherent to night images.

Results

The outcomes presented in this section correspond to the Jardinets de Gràcia site, and are based on the data taken in the night of February 19th to 20th, 2015. This date was chosen to minimize the contribution of moonlight to the nightscape radiance. The new Moon occured at 00:49 h of February 19th (local time CET = UTC + 1). Sunset took place at 18:29 of February 19th and the Moon was below the horizon from 19:25 h of this day until 08:20 h of Feb 20th. The measurements were taken in the first part

Discussion

The results presented in this work are affected by several limitations. One of them stems from the fact that the irradiances at vertical planes have been computed from radiance distributions with a vertical swath limited to about 40° (i.e., 20° above and below the horizontal) instead of the nominal 180° angular span extending from zenith to nadir. While in fact these radiance data capture the essential features of the urban nightscape from the viewpoint of pedestrians gazing horizontally, and

Conclusions

We described the use of a hyperspectral camera to characterize the urban emissions of light at night from a ground-based perspective, complementary to airborne or spaceborne remote sensing. Whereas the latter provide valuable data to estimate the amount of energy wasted skywards by public and private outdoor lighting systems, our present approach provides supplementary information from the city dwellers standpoint, allowing to assess other relevant aspects of the light pollution problem, as

Funding

This work has been developed within the framework of the Spanish Network for Light Pollution Studies (AYA2015-71542-REDT).

Conflicts of interests

The Institut Cartogràfic i Geològic de Catalunya (ICGC) is a public body of the Catalonian Government that provides photometric and photogrammetric services to local communities, public administration bodies and private customers, including airborne and ground-based hyperspectral imaging.

Acknowledgments

We acknowledge the useful suggestions and comments made by the anonymous reviewers of this manuscript.

References (53)

  • R.J. Lucas et al.

    Measuring and using light in the melanopsin age

    Trends Neurosci.

    (2014)
  • M.S. Rea et al.

    A model of phototransduction by the human circadian system

    Brain Res. Rev.

    (2005)
  • A. Sánchez de Miguel et al.

    Evolution of the energy consumed by street lighting in Spain estimated with DMSP-OLS data

    J. Quant. Spectrosc. Radiat. Transfer

    (2014)
  • R.G. Stevens et al.

    Adverse health effects of nighttime lighting

    Am. J. Prev. Med.

    (2013)
  • F. Yang et al.

    Mapping the human footprint from satellite measurements in Japan

    ISPRS J. Photogramm. Remote Sens.

    (2014)
  • S. Babey et al.

    Radiometric calibration of the compact airborne spectrographic imager (CASI)

    Can. J. Remote Sens.

    (1992)
  • Bará, S., 2013. Light pollution and solid-state lighting: reducing the carbon dioxide footprint is not enough. In: 8th...
  • Bará, S., 2014. Light pollution: Why should we care? In: Second International Conference on Applications of Optics and...
  • S. Bará

    Anthropogenic disruption of the night sky darkness in urban and rural areas

    Roy. Soc. Open Sci.

    (2016)
  • A. Barducci et al.

    Effects of light pollution revealed during a nocturnal aerial survey by two hyperspectral imagers

    Appl. Opt.

    (2003)
  • A. Barducci et al.

    Light pollution observed by MIVIS and VIRS 200 during a nocturnal remote sensing campaign over Italy

    In Remote Sensing for Environmental Monitoring, GIS Applications, and Geology II, Manfred Ehlers, Editor, Proceedings of SPIE

    (2003)
  • A. Barducci et al.

    Hyperspectral remote sensing for light pollution monitoring

    Ann. Geophys.

    (2006)
  • M.A. Bonmati-Carrion et al.

    Protecting the melatonin rhythm through circadian healthy light exposure

    Int. J. Mol. Sci.

    (2014)
  • H. Cai

    High dynamic range photogrammetry for synchronous luminance and geometry measurement

    Light. Res. Technol.

    (2013)
  • Castiglione, L., Conticello, S.S., Esposito, M., Oldenhuis, R., Moon, S.G., Nicolai, A., Stoltz, S., Dettmann, J.,...
  • Y.M. Cho et al.

    Effects of artificial light at night on human health: a literature review of observational and experimental studies applied to exposure assessment

    Chronobiol. Int.

    (2015)
  • Cited by (33)

    • Quantification of ecosystem services supply-demand and the impact of demographic change on cultural services in Shenzhen, China

      2022, Journal of Environmental Management
      Citation Excerpt :

      Therefore, for areas that show a surplus to deficit from day to night, the forms of night tourism can be enriched and supporting facilities can be added. Secondly, for areas that show a deficit to surplus from day to night, consider reducing unnecessary illumination to achieve the goal of reducing light pollution and energy consumption (Alamús et al., 2017). Finally, sound tourism infrastructure is essential to attract tourists (Kanwal et al., 2020; Mou et al., 2022), however, some scenic spots in Shenzhen are located within the ecological control line (Fig. S4), which restricts infrastructure construction.

    • Remote sensing of night lights: A review and an outlook for the future

      2020, Remote Sensing of Environment
      Citation Excerpt :

      The ideal system would be to use a hyperspectral imaging spectrometer at low altitudes. Few studies with limited spatial coverage exist, such as the first ever performed over 1998 in Las Vegas, USA (Elvidge and Green, 2005; Alamús et al., 2017, see section 2.3 for more). Elvidge et al. (2010) showed that it was in principle possible to discriminate light sources with multispectral sensors, using detailed spectral field measurements and a modeling approach for the pre LED technologies.

    View all citing articles on Scopus
    View full text