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First published online February 15, 2006
Journal of Experimental Biology 209, 789-800 (2006)
Published by The Company of Biologists 2006
doi: 10.1242/jeb.02053
Crepuscular and nocturnal illumination and its effects on color perception by the nocturnal hawkmoth Deilephila elpenor
1 Biology Department, Duke University, Durham, NC 27708, USA
2 Department of Cell and Organism Biology, Lund University,
Sweden
3 Marine Science Division, Harbor Branch Oceanographic Institution, Fort
Pierce, FL 34946, USA
4 Mathematics and Science Division, US Naval Academy, Annapolis, MD 21402,
USA
5 Optics Department, University of Granada, Spain
* Author for correspondence (e-mail: sjohnsen{at}duke.edu)
Accepted 20 December 2005
| Summary |
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Key words: hawkmoth, Deilephila elpenor, nocturnal vision, color vision, environmental optics
| Introduction |
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|
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First, what is the selective advantage of color vision in these species
that outweighs its costs? Color vision's detrimental effect on spatial
resolution and the additional structural and neurological complexity required
for color processing makes it a more difficult proposition for all species.
However, color vision presents additional difficulties for nocturnal species.
While the decrease in sensitivity associated with the increase in the number
of visual channels has little effect on species operating during
light-saturated diurnal conditions, this sensitivity loss can potentially
affect the ability of nocturnal species to function in their light-limited
environment. It is primarily for this reason that color vision has generally
been expected to be rare or absent among nocturnal species
(Jacobs, 1993
).
Second, what color are objects when viewed under the night sky? Although
not perceived by humans, the spectrum of the night sky is not neutral, and
depends on multiple factors, including how far the sun is below the horizon,
the presence or absence and phase of the moon and, recently, on the level of
light pollution (e.g. Munz and McFarland,
1977
; Endler,
1991
; Leinert et al.,
1998
; McFarland et al.,
1999
; Cinzano et al.,
2001
;
Hernández-Andrés et al.,
2001
; Lee and
Hernández-Andrés, 2003
). It has long been known that
the variation of daytime spectra, due to cloud cover, solar elevation, forest
canopy and depth (for aquatic species), has a substantial effect on the
appearance and visibility of objects and organisms, which can be at least
partly ameliorated by color vision
(Wyszecki and Stiles, 1982
;
Endler, 1991
;
McFarland et al., 1999
;
Johnsen and Sosik, 2003
;
Lovell et al., 2005
). Less
work, however, has been done on the appearance of objects during twilight
(reviewed by McFarland et al.,
1999
; Rickel and Genin,
2005
), and, to our knowledge, the appearance of objects under
different nocturnal illuminants has received very little attention.
This study measures or models spectral irradiance (300700 nm) during daylight, sunset, twilight, moonlit nights, moonless nights and nights in regions with high light pollution. These spectra, in addition to previously published data, are then used to calculate the relative quantum catches of the three photoreceptors of D. elpenor under different lighting conditions. In addition to the general illuminants, relative quantum catches of five stimuli (green leaves, three flowers and the red hindwing of D. elpenor) are also calculated. Three different types of contrasts of the latter four stimuli viewed against green leaves are then determined: (1) achromatic contrast, (2) chromatic contrast and (3) chromatic contrast assuming von Kries color constancy. Finally, quantum catches of hypothetical photoreceptors with varying wavelengths of peak absorption are compared to the catches of the long wavelength receptor in D. elpenor under the different illuminants.
| Materials and methods |
|---|
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|
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Measurement of twilight spectra
Fourteen sunset and twilight measurements of spectral irradiance under
minimal cloud cover were taken on the beaches of two barrier islands located
off the coast of North Carolina, USA (Atlantic Beach; 34°42'N
76°44'W and Cape Hatteras National Seashore; 35°44'N
75°32'W, both at sea level) on 11 June, 12 June and 17 July, 2004.
The locations were chosen to maximize the view of the sky and minimize the
effects of anthropogenic light. Spectra were taken using a USB2000
spectrometer (Ocean Optics Inc., Dunedin, FL, USA) that had been modified for
increased sensitivity by increasing the width of the entrance slit to 200
µm and focusing light onto the detector array with a collector lens (L2
collector lens, Ocean Optics). The spectrometer was fitted with a 1 mm
diameter fiber optic cable that viewed a horizontal slab of a Lambertian
reflector (Spectralon, Labsphere Inc., North Sutton, NH, USA). Because
Lambertian materials reflect light evenly in all directions, their radiance is
proportional to the irradiance striking them
(Palmer, 1995
). This method of
obtaining the cosine response needed for measuring diffuse irradiance was
chosen because it is more efficient than the typical diffusely transmitting
disk (Doxaran et al.,
2004
).
Spectra were taken at solar elevations ranging from +11° to 11° (elevations determined using tables from the United States Naval Observatory). At lower solar elevations, the integration time of the spectrometer was increased to a maximum of 10 s, with 30 such integrations averaged per measurement. Spectra were taken from 300 to 700 nm and averaged over 5 nm intervals.
Measurement of full moonlight and synthesis of starlight spectra
Spectral irradiance under the full moon was measured using a spectrometer
with a highly sensitive photomultiplier detector (OL-754-PMT, Optronics
Laboratories Inc., Orlando, FL, USA). Spectra were taken on 10 December, 2003
at Harbor Branch Oceanographic Institution (Fort Pierce, FL, USA;
27°26'N 80°19'W, sea level) during the full moon
(elevation 69°, moon 98% full). An integrating sphere was used to ensure a
cosine angular response. Data were taken at 5 nm intervals from 350 to 700
nm.
Preliminary attempts showed that even the OL-754 spectrometer was not
sensitive enough to measure spectral irradiance on a moonless night. Therefore
it was calculated in the following manner. The spectral radiances of small
star-free portions of the moonless night sky were obtained from two
observatories: Kitt Peak National Observatory (Tuscon, AZ, USA;
31°58'N 111°36'W, elevation 2083 m) and the William
Herschel Telescope (La Palma, Canary Islands, Spain; 28°36'N
17°45'W, elevation 2400 m) (Benn
and Ellison, 1998
; Massey and
Foltz, 2000
). Star and moon-free night spectra are composed
primarily of airglow (emission spectra of the various molecular components of
the upper atmosphere) and zodiacal light (sunlight scattered from the dust in
the plane of the solar system) (Leinert et al., 1997;
Benn and Ellison, 1998
).
Because airglow is relatively constant over the entire hemisphere and zodiacal
light is concentrated in a small region near the horizon, the former is the
primary contributor to the diffuse irradiance of a star-free night sky
(
80%) (Benn and Ellison,
1998
). The stars contribute approximately 2333% of the
total irradiance, depending on the solar activity level (which affects the
airglow intensity). The average spectrum of the stars of all spectral types
(weighted by their relative abundances) was taken from Matilla (1980). This
spectrum was combined with the star-free night sky spectra and integrated over
the entire hemisphere of the sky to obtain estimates of the spectral
irradiance on moonless nights. Two spectra were calculated from each
observatory spectrum, one for the solar minimum (when stars contribute 33% of
the total irradiance) and one for the solar maximum, (when stars contribute
23%). Spectra were calculated at 5 nm intervals from 300 to 700 nm.
To determine the effect of anthropogenic light on nocturnal irradiance, a spectrum was obtained from an urban location on a cloudy night (Jamaica Pond, Boston, MA, USA, 42°20'N 71°03'W, sea level) (M. Moore, unpublished data). Cloudy conditions were chosen because they maximize the effects of light pollution by reflecting urban lighting back to the ground. The measurement technique and resolution matched that described above for the North Carolina twilight spectra.
Daylight, civil twilight, and forest spectra
An estimate of the variability of daylight and civil twilight spectra (to
compare with the variability during twilight and night) was obtained from 2395
daylight, 254 civil twilight and 220 forest measurements of spectral
irradiance (Chiao et al., 2000
;
Hernández-Andrés et al.,
2001
; Lee and
Hernández-Andrés, 2003
). All the daylight and 205 of
the civil twilight spectra were measured from the roof of the University of
Granada's Science Faculty (Granada, Spain, 37°11'N 3°35'W,
elevation 680 m) from February 1996 to February 1998 using a LI-1800
spectroradiometer (LI-COR Bioscience, Lincoln, NE, USA) fitted with a
cosine-corrected receptor. Measurements were taken at all solar elevations
greater than 4° and in all weather except for rain or snowfall.
Data were collected at 5 nm intervals from 300 to 1100 nm. Another 49 civil
twilight spectra were measured from three sites: Owings, MA, USA
(38°41'N 76°35'W, elevation 15 m), Annapolis, MA, USA
(38°59'N 76°29'W, elevation 18 m), and Marion Center, PA,
USA (40°49'N 79°05'W, elevation 451 m). Measurements (from
380780 nm) were taken from 1998 to 2001 using PR-650 spectroradiometer
(Photo Research Inc., Chatsworth, CA, USA). Solar elevation ranged from 0°
to 5.6°.
The 220 forest spectra were measured from sunrise to sunset during July and August 1999 in several temperate forests in Maryland, USA. Measurement locations included both full shade and under gaps in the canopy, and atmospheric conditions ranged from clear to overcast. Data were collected at 3 nm intervals from 400 to 700 nm using an S2000 spectroradiometer (Ocean Optics) fitted with a cosine corrector.
UV and visible reflectance curves
The spectral reflectance of the white flower of the hawkmoth-pollinated
evening primrose Oenothera neomexicana Munz
(Raguso and Willis, 2002
) and
of the blue flower of the unspotted lungwort Pulmonaria obscura L.
and the yellow flower of the birdsfoot trefoil Lotus corniculatus L.
(Chittka et al., 1994
) were
used and are typical for white, yellow and blue flowers, respectively
(although the flowers of certain species have higher reflectance at UV
wavelengths). Reflections from a green leaf and the red area on the wings of
the nocturnal hawkmoth Deilephila elpenor were measured using an
S2000 Spectrometer (Ocean Optics) calibrated with a diffuse reflectance
standard (WS1, Ocean Optics). All five spectra are shown in
Fig. 1A.
|
![]() | (1) |
) is the stimulus radiance in photons m2
s1 nm1 sr1.
Ri(
) (i=1,2,3) are the absorbance spectra
of the three visual pigments of D. elpenor, calculated from their
recorded sensitivity maxima (350 nm, 440 nm and 525 nm)
(Schwemer and Paulsen, 1973
|
For the calculation of the relative quantum catches, we assumed that the
eyes of D. elpenor have fused rhabdoms with all three receptor types.
This is a simplification because it is likely that there are two additional
ommatidial types, one with blue and green receptors only, and one with UV and
green receptors only (Kelber et al.,
2002
). However, because it is not known whether and how color
processing involves inter-ommatidial connections, the ommatidial type
containing all three receptors was the most general to model. Quantum catches
were calculated assuming lateral screening
(Snyder et al., 1973
) (see
Appendix for complete derivation). The receptor sensitivities were all
normalized so that their integrals equalled 1. Thus, a stimulus that induces
the same response in each photoreceptor type has its color locus in the centre
of the color triangle (for details, see
Kelber et al., 2003b
).
Independent receptor adaptation was used as a model of chromatic adaptation
(von Kries, 1904
;
Kelber et al., 2003b
). This
assumes that receptors adapt to the background intensity by keeping the
response at approximately 50% of their maximal response
(Laughlin and Hardie, 1978
).
The adapted receptor signal q is then:
![]() | (2) |
For calculating achromatic contrast, we assumed that green receptors extend
over the entire length and width of the rhabdom and no lateral screening takes
place (Fig. 1B, broken line).
The achromatic contrast C was then calculated as:
![]() | (3) |
Because the spectra of nocturnal illumination are generally long-shifted (see Results), the 525 nm green pigment of D. elpenor may not be efficient at capturing this light. This possibility was examined by calculating the absolute photon catch of the long-wavelength pigment as a function of its peak wavelength. As was done for the achromatic contrast calculations, we assumed that green receptors extended over the entire length and width of the rhabdom and no lateral screening took place.
| Results |
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450 nm, which became
increasingly prominent as twilight progressed.
|
Human-based chromaticity and relative quantum catches in D. elpenor
Mapping the twilight and nocturnal spectra into the perceptually uniform,
human-based u'v' chromaticity space showed that nautical twilight
(solar elevation between 6° and 12°), moonless nights,
and regions with high light pollution, had chromaticities well outside the
envelope of those of the daylight, forest and early twilight illuminants
(Fig. 3A). The same was also
true for the relative quantum catches of D. elpenor, although the
relative positions of starlight vs daylight vs twilight were
different (Fig. 3B). The
illumination of the full moon mapped to the long-wavelength border of the
Granada daylight coordinates in both color spaces.
|
Relative quantum catches of flowers, leaves and wings
The relative quantum catches of the five examined stimuli (blue, white and
yellow flowers; green leaves; red hindwings of D. elpenor) depended
strongly on the source of illumination
(Fig. 4A,B). In general, the
variation was primarily in the relative quantum catch of the green
photoreceptor (i.e. along a line connecting the green vertex to the
UVblue side). Decreasing solar elevation lowered the relative catch of
the green receptor, with a slight increase in the relative catch of the UV
receptor in nautical twilight. The type of nocturnal illumination affected the
relative quantum catches to a similar degree, with all three illuminants
(moonlight, starlight, light pollution) resulting in higher relative quantum
catches in the green receptor. In general, the stimuli viewed under
light-polluted skies had relative quantum catches substantially different from
those under all natural illuminants, both crepuscular and nocturnal.
|
When von Kries color constancy was assumed, the variation of all five stimuli under the various illuminants was substantially less (Fig. 4C). The largest variation was found in the blue and yellow flower stimuli. The smallest variation was found in the red wing stimulus.
Achromatic and chromatic contrasts
The variation in achromatic contrast of the stimuli against the leaves
under twilight, moonlight and starlight was strongly dependent on the stimulus
(Fig. 5A,D). The achromatic
contrast of the white flower stimulus was fairly independent of illuminant,
with a coefficient of variation (i.e. standard deviation divided by the mean)
of about 5%. In contrast, the achromatic contrasts of the yellow and blue
flower stimuli had coefficients of variation higher than 100%. In addition,
under full moon and starlight, their achromatic contrasts against the leaf
were nearly zero. When the contrast of the two flowers under light polluted
skies were also considered, the variation was even larger, with the contrasts
switching polarities. The coefficient of variation of the red wing against the
green leaves had an intermediate value of 27%.
|
Photon catches as a function of the
max of the long wavelength photoreceptor
Under nautical twilight, the photon catch of a receptor containing only one
photopigment was relatively independent of the pigment's wavelength of peak
absorption (
max), regardless of whether the stimulus was
white, green or red (Fig.
6AC). However, there was a gradual decrease for
hypothetical receptors with
max at low visible and
ultraviolet wavelengths. Under full moon and starlight though, the photon
catch was strongly and positively correlated with
max, with
catches of hypothetical photoreceptors with 650 nm pigments being 23
times greater than those for the actual 525 nm long wavelength photopigment.
This correlation was particularly strong for photoreceptors viewing the red
wings of D. elpenor (Fig.
6C). The source of nocturnal illumination (starlight or moonlight)
had little effect on this correlation for all three stimuli.
|
| Discussion |
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While cloud cover, solar elevation and the presence of a forest canopy also
affect the spectral quality of daylight, the effect is smaller than what is
observed during crepuscular periods and comparable to what is seen during the
night. This is due partially to the fact that solar elevation has little
effect on spectrum for elevations greater than 20°, and that clouds
primarily scatter rather than absorb light, and thus have little effect on
spectral quality. More important, however, is that the only two significant
sources of daytime illumination are the sun and scattered sunlight, whose
spectral characteristics and relative contributions both remain fairly
constant at solar elevations greater than 20°. In contrast, crepuscular
and nocturnal environments are lit by multiple sources with different spectra
including a low-elevation sun or moon, high elevation moon, starlight, airglow
emissions, and scattered sun or moonlight
(Leinert et al., 1998
).
Because both the intensities and spatial extents of these sources vary by many
orders of magnitude (Fig. 2C),
spectral quality can change rapidly and significantly, particularly during the
rising and setting of the sun or moon (Fig.
7). For example, near sunset the small, but intense and
long-wavelength dominated solar disk balances the relatively dim
short-wavelength dominated skylight until the sun nearly reaches the horizon,
after which the general illumination changes rapidly from spectrally neutral
to short-wavelength dominated.
|
Changing crepuscular and nocturnal illumination and monochromatic visual systems
Although the exact achromatic contrasts depend on the spectral sensitivity
of the viewer and the spectral reflectances of the targets and backgrounds,
the examples given in this study show that they can vary significantly under
the different crepuscular and nocturnal illuminants. With the exception of the
white flower, the achromatic contrasts of the stimuli against the leaf
background were quite variable. In certain cases, the contrast changed
polarity. For example, the blue flower was brighter than the leaves during
nautical twilight, but darker than the leaves during night. In addition, two
of the stimuli (the blue and yellow flowers) had low contrasts under moonlight
and starlight, likely rendering them undetectable via achromatic
cues.
In contrast, the white flower, whose reflectance is high but relatively
similar in spectrum to the leaves, had a high and stable contrast under all
light conditions (Fig. 5A).
D. elpenor and other nocturnal hawkmoths are thought to primarily
visit white flowers with exceptionally high reflectance (reviewed by
Raguso and Willis, 2002
;
Kelber et al., 2003a
). In
addition, crepuscular hawkmoths (e.g. Manduca sexta), and those that
are active both during day and night (e.g. Hyles sp.), tend to visit
blue and yellow flowers in bright light but white flowers in dim light
(reviewed by Raguso and Willis,
2002
).
The need for stability of achromatic contrast may also explain why the
nocturnal flowers of many bat-pollinated species tend to be red or white.
Flower-visiting bats are color-blind at night
(Winter et al., 2003
) and thus
rely on achromatic contrast. Because the illumination during moonlit and
starlit nights is long-wavelength shifted, red flowers are bright relative to
green leaves, resulting in a high and more stable contrast. However, because
the peak wavelength of the long-wavelength pigments of some of these bats is
relatively low (
510 nm), they may not be able to exploit this
contrast.
In general, however, achromatic contrast depends strongly on the illuminant, which varies significantly during crepuscular and nocturnal periods. This variation, which occurs whenever spectrally different stimuli and backgrounds are viewed under highly variable illuminants, makes monochromatic vision unreliable during these periods.
Chromatic contrasts and color constancy
While chromatic contrasts varied less than achromatic contrasts
(Fig. 5D), the addition of
color constancy, which has recently been demonstrated for D. elpenor
(Balkenius and Kelber, 2004
),
reduces the variation further. Chromatic contrasts without constancy are
affected by the fact that the different lighting conditions changed the
relative quantum catches from different colored stimuli in different ways. For
example, relative quantum catches from the yellow flower Lotus
corniculatus viewed under moonlight and nautical twilight changed less
than did the relative quantum catches from the green leaf background
(Fig. 4B). This is due to the
fact that the relative contribution of the long-wavelength light that the
yellow flower reflects changes less than the relative contribution of the
middle wavelength light that the leaf reflects (Figs
1A,
2A,B). The result is not only a
shift in the color of the scene, but also of the chromatic contrast between
the flower and the leaf background. Color constancy, which can be explained as
the result of receptor adaptation, reduces the variation for all four stimuli.
In the case of the white flower, whose variation in chromatic contrast is
greater than its variation in achromatic contrast, color constancy removes
nearly all the variation.
The function of nocturnal color vision in D. elpenor is poorly understood. As mentioned above, nocturnal hawkmoths are thought to visit white flowers at night, which can reliably be detected without color vision. However, given that other hawkmoths visit blue and yellow flowers during the day, it is possible that flowers of these colors are also visited at night. Given their unreliable appearance to monochromatic visual systems, blue and yellow flowers may remain undetected by competitors of D. elpenor, allowing them to exploit an additional source of nectar.
The general long-wavelength shift of nocturnal illumination and the red
coloration of D. elpenor render this species quite visible at night.
Also, it has relatively stable achromatic and chromatic contrasts
(Fig. 5). While many hawkmoths
have some red coloration, particularly on their hindwings (which is thought to
function as a startle display), the more extensive red coloration of D.
elpenor is less common (Kitching and
Cadiou, 2000
). This raises the possibility that color vision may
enhance recognition of conspecifics or be used in mating. While mating in
moths is thought to be entirely mediated by olfaction, most tasks are
eventually found to involve multiple sensory modalities. For example,
nocturnal foraging in hawkmoths is known to involve both visual and olfactory
cues (Raguso and Willis,
2002
).
Absolute numbers of captured photons as a function of
max
While the relationship between visual pigment maxima and illuminant spectra
under diurnal conditions is complex, research on deep-sea fish has shown that,
at least in that particular light-limited environment, visual sensitivity
peaks close to the wavelength of peak illumination (reviewed by
Partridge and Cummings, 1999
).
This characteristic, which maximizes photon catch, does not appear to operate
in D. elpenor. The peak wavelength is similar to those found in the
long wavelength receptors of diurnal moths
(Briscoe and Chittka, 2001
),
and differs substantially from that leading to maximal photon catch
(Fig. 6AC). This is
intriguing, given the extreme light limitation present during color vision
under starlight (Kelber et al.,
2002
), and the presence of longer wavelength pigments in the
Lepidoptera (Briscoe and Chittka,
2001
). In vertebrates, the higher noise levels in long-wavelength
ciliary receptors (dark noise) (Barlow,
1957
; Donner et al.,
1990
; Firsov and Govardovskii,
1990
; Ala-Laurila et al.,
2004
) may account for this. However, dark noise appears to play a
minor role in invertebrates due to different transduction mechanisms in
rhabdomeric receptors (Laughlin,
1990
; Warrant,
2004
). Because relative quantum catches in the fused rhabdoms of
D. elpenor vary more with changing illuminant as the peak wavelength
of the long-wavelength receptor increases
(Fig. 6C), the 525 nm peak may
be a compromise between sensitivity and color stability. The peak wavelengths
of the photoreceptors may also be constrained by their function during diurnal
periods.
It is also possible that the sub-optimal
max of the long
wavelength pigment is due to a phylogenetic or other constraint. Indeed, a
survey of visual pigment maxima in insects by Briscoe and Chittka
(2001
) found little correlation
with environment or behavior. However, at least two nocturnal species in the
moth family Noctuidae have a fourth visual pigment
(
max=560, 580 nm)
(Langer et al., 1979
;
Ichikawa and Tateda, 1982
),
which phylogenetic analyses suggest are independently evolved within the
Lepidoptera (Briscoe and Chittka,
2001
). The function of these pigments at nocturnal light levels is
doubtful given the limited optical sensitivity of noctuid eyes (A. Kelber,
unpublished data), but their existence casts some doubt on a phylogenetic
constraints argument.
Light pollution
Anthropogenic light sources (`light pollution') are an increasingly
dominant factor in nocturnal illumination (e.g.
Cinzano et al., 2001
;
Garstang, 2004
). In addition
to reaching intensities comparable to the light during nautical twilight or
under the full moon, spectral irradiance under light polluted skies is
substantially different from that found under any natural illumination
(Fig. 3). While light pollution
spectra have many peaks (primarily due to mercury and sodium emission lamps),
the primary spectral difference is a large increase in the relative
contribution of long-wavelength light. This significantly changed both the
achromatic and chromatic contrasts of the considered stimuli. The achromatic
contrasts of the blue and yellow flowers in particular were significantly
altered.
Light pollution can rival the intensity of the blue sky during nautical twilight and essentially has an opposite spectrum: the former being strongly long-wavelength shifted, the latter strongly short-wavelength shifted. Therefore the color of twilight illumination in urban and other light-polluted regions will vary rapidly over an unnaturally large range, potentially presenting significant difficulties for both monochromatic and color-visual species operating during this period.
Recent research on the ecological effects of light pollution (reviewed by
Longcore and Rich, 2004
) has
generally focused on its intensity. To our knowledge, however, no studies have
examined the effect of the color of light pollution. Given its unusual
spectrum, it may have a significant effect on the foraging and mating of
crepuscular and nocturnal species.
Conclusions
The spectral quality of crepuscular and nocturnal illumination varies over
a larger range than does that of diurnal illumination, even when a wide range
of atmospheric and forest conditions are considered. This variation makes
monochromatic visual systems unreliable during these periods. We propose, for
species that forage during twilight and night, that the increased signal
reliability afforded by color constant color vision offsets the decreased
sensitivity and provides an explanation for this unusual trait. However, the
preference of D. elpenor for white flowers, which have stable
achromatic contrasts, complicate the picture for this species. The mismatch of
the long-wavelength pigment to the spectra of nocturnal illumination results
in a less than optimal photon catch, but may lead to higher color stability.
Light polluted night skies are strongly long-wavelength shifted and
substantially alter the appearance of objects. Future research into nocturnal
vision will need to consider the large natural and anthropogenic variability
of this optical environment.
| Appendix |
|---|
|
|
|---|
) is the stimulus strength (in quanta) at distal surface
of the rhabdom; Ri(
) is the absorbance curve of
ith pigment, where i=UV, B or G, normalized to a peak of 1;
(
) is the un-normalized
average of the three absorbance curves; and k and l are
absorption coefficient and length of the rhabdom, respectively.
The number of photons of wavelength
that penetrate a distance
x into the rhabdom equals:
![]() | (A1) |
![]() | (A2) |
Thus, the total number of photons absorbed by the ith photopigment
at wavelength
by the entire rhabdom equals:
![]() | (A3) |
![]() | (A4) |
![]() | (A5) |
) is
(X1,X2), where:
![]() | (A6) |
![]() | (A7) |
![]() | (A8) |
| Acknowledgments |
|---|
| References |
|---|
|
|
|---|
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