This video has been viewed over 2.85 million times and explains in detail FYRLYT's response to the AMA's report on LED street lighting. There are some people that claim we have it wrong. They are often brands or resellers of LED or HID lights! These people may wish to consider we have had a number of ophthalmologists and academics agreeing that 5000K is NOT IDEAL. Who would you trust? Ask them would they be prepared to debate an opthamologist?

This statement from the AMA refers to 'street lighting' however it is relevant to driving lights in our opinion as this is about light function in an outside night environment and how the human eye/body reacts. 


This information re the light emitted by high intensity led sources has been known for years and was a primary reason why FYRLYT elected to design a high performance halogen light source as having the least downsides re glare and negative effect on visual acuity. 


History has seen, FYRLYT meet fierce opposition and naysayers who believed we had it wrong re halogen. Some media channels will claim they use 'LAB' tests etc and hang their credibility on that. How these same 'experts' will react to this public release by the AMA will be interesting indeed. How does this reflect on their credibility as a technical source of information? Consider, the aftermarket industry and media have and still promote this when the evidence was already in the public domain.

In summary. A light quality has been promoted for years by commercial or 'other' agendas has now seen the AMA publish recommendations concluding the light emitted is problematic for vision and health. 

Who do you trust? A light brand? A store selling what they have on the shelf? Media selling advertising space to these businesses? The 'RA RA' of a racing team or other proclaimed 'CELEBRITY' of the moment being supplied 'SPONSORED' product and the subsequent pretty pictures and hype they are obligated to provide?


We believe FYRLYT offers the discerning customer a driving light that is unsurpassed and exists due to an unwavering focus on innovation and best in class design principles that are easily verified beyond market trends or fashion.


The AMA, American Medical Association on June 14, 2016 released a community guidance report that makes for very interesting reading. 

AMA Adopts Community Guidance to Reduce the Harmful Human and Environmental Effects of High Intensity Street Lighting


For immediate release:
June 14, 2016


CHICAGO - Strong arguments exist for overhauling the lighting systems on U.S. roadways with light emitting diodes (LED), but conversions to improper LED technology can have adverse consequences. In response, physicians at the Annual Meeting of the American Medical Association (AMA) today adopted guidance for communities on selecting among LED lighting options to minimize potential harmful human and environmental effects.

Converting conventional street light to energy efficient LED lighting leads to cost and energy savings, and a lower reliance on fossil-based fuels. Approximately 10 percent of existing U.S. street lighting has been converted to solid state LED technology, with efforts underway to accelerate this conversion.

"Despite the energy efficiency benefits, some LED lights are harmful when used as street lighting," AMA Board Member Maya A. Babu, M.D., M.B.A. "The new AMA guidance encourages proper attention to optimal design and engineering features when converting to LED lighting that minimize detrimental health and environmental effects."

High-intensity LED lighting designs emit a large amount of blue light that appears white to the naked eye and create worse nighttime glare than conventional lighting. Discomfort and disability from intense, blue-rich LED lighting can decrease visual acuity and safety, resulting in concerns and creating a road hazard.

In addition to its impact on drivers, blue-rich LED streetlights operate at a wavelength that most adversely suppresses melatonin during night. It is estimated that white LED lamps have five times greater impact on circadian sleep rhythms than conventional street lamps. Recent large surveys found that brighter residential nighttime lighting is associated with reduced sleep times, dissatisfaction with sleep quality, excessive sleepiness, impaired daytime functioning and obesity.

The detrimental effects of high-intensity LED lighting are not limited to humans. Excessive outdoor lighting disrupts many species that need a dark environment. For instance, poorly designed LED lighting disorients some bird, insect, turtle and fish species, and U.S. national parks have adopted optimal lighting designs and practices that minimize the effects of light pollution on the environment.

Recognizing the detrimental effects of poorly-designed, high-intensity LED lighting, the AMA encourages communities to minimize and control blue-rich environmental lighting by using the lowest emission of blue light possible to reduce glare. The AMA recommends an intensity threshold for optimal LED lighting that minimizes blue-rich light. The AMA also recommends all LED lighting should be properly shielded to minimize glare and detrimental human health and environmental effects, and consideration should be given to utilize the ability of LED lighting to be dimmed for off-peak time periods.

The guidance adopted today by grassroots physicians who comprise the AMA's policy-making body strengthens the AMA's policy stand against light pollution and public awareness of the adverse health and environmental effects of pervasive nighttime lighting.

Media Contact:
AMA Media and Editorial
Pressroom: (312) 239-4991

The REPORT in its entirety line for line is as follows below.


CSAPH Report 2-A-16

Subject: Human and Environmental Effects of Light Emitting Diode (LED) Community Lighting

Presented by: Louis J. Kraus, MD, Chair

Referred to: Reference Committee E (Theodore Zanker, MD, Chair)




3 With the advent of highly efficient and bright light emitting diode (LED) lighting, strong economic

4 arguments exist to overhaul the street lighting of U.S. roadways.1-3 Valid and compelling reasons

5 driving the conversion from conventional lighting include the inherent energy efficiency and longer

6 lamp life of LED lighting, leading to savings in energy use and reduced operating costs, including

7 taxes and maintenance, as well as lower air pollution burden from reduced reliance on fossil-based

8 carbon fuels.


10 Not all LED light is optimal, however, when used as street lighting. Improper design of the lighting

11 fixture can result in glare, creating a road hazard condition.4,5 LED lighting also is available in

12 various color correlated temperatures. Many early designs of white LED lighting generated a color

13 spectrum with excessive blue wavelength. This feature further contributes to disability glare, i.e.,

14 visual impairment due to stray light, as blue wavelengths are associated with more scattering in the

15 human eye, and sufficiently intense blue spectrum damages retinas.6,7 The excessive blue spectrum

16 also is environmentally disruptive for many nocturnal species. Accordingly, significant human and

17 environmental concerns are associated with short wavelength (blue) LED emission. Currently,

18 approximately 10% of existing U.S. street lighting has been converted to solid state LED

19 technology, with efforts underway to accelerate this conversion. The Council is undertaking this

20 report to assist in advising communities on selecting among LED lighting options in order to

21 minimize potentially harmful human health and environmental effects.




25 English language reports published between 2005 and 2016 were selected from a search of the

26 PubMed and Google Scholar databases using the MeSH terms “light,” “lighting methods,”

27 “color,” “photic stimulation,” and “adverse effects,” in combination with “circadian

28 rhythm/physiology/radiation effects,” “radiation dosage/effects,” “sleep/physiology,” “ecosystem,”

29 “environment,” and “environmental monitoring.” Additional searches using the text terms “LED”

30 and “community,” “street,” and “roadway lighting” were conducted. Additional information and

31 perspective were supplied by recognized experts in the field.




35 The main reason for converting to LED street lighting is energy efficiency; LED lighting can

36 reduce energy consumption by up to 50% compared with conventional high pressure sodium


(HPS) CSAPH Rep. 2-A-16 -- page 2 of 8


1 lighting. LED lighting has no warm up requirement with a rapid “turn on and off” at full intensity.

2 In the event of a power outage, LED lights can turn on instantly when power is restored, as

3 opposed to sodium-based lighting requiring prolonged warm up periods. LED lighting also has the

4 inherent capability to be dimmed or tuned, so that during off peak usage times (e.g., 1 to 5 AM),

5 further energy savings can be achieved by reducing illumination levels. LED lighting also has a

6 much longer lifetime (15 to 20 years, or 50,000 hours), reducing maintenance costs by decreasing

7 the frequency of fixture or bulb replacement. That lifespan exceeds that of conventional HPS

8 lighting by 2-4 times. Also, LED lighting has no mercury or lead, and does not release any toxic

9 substances if damaged, unlike mercury or HPS lighting. The light output is very consistent across

10 cold or warm temperature gradients. LED lights also do not require any internal reflectors or glass

11 covers, allowing higher efficiency as well, if designed properly.8,9


13 Despite the benefits of LED lighting, some potential disadvantages are apparent. The initial cost is

14 higher than conventional lighting; several years of energy savings may be required to recoup that

15 initial expense.10 The spectral characteristics of LED lighting also can be problematic. LED

16 lighting is inherently narrow bandwidth, with "white" being obtained by adding phosphor coating

17 layers to a high energy (such as blue) LED. These phosphor layers can wear with time leading to a

18 higher spectral response than was designed or intended. Manufacturers address this problem with

19 more resistant coatings, blocking filters, or use of lower color temperature LEDs. With proper

20 design, higher spectral responses can be minimized. LED lighting does not tend to abruptly “burn

21 out,” rather it dims slowly over many years. An LED fixture generally needs to be replaced after it

22 has dimmed by 30% from initial specifications, usually after about 15 to 20 years.1,11


24 Depending on the design, a large amount blue light is emitted from some LEDs that appear white

25 to the naked eye. The excess blue and green emissions from some LEDs lead to increased light

26 pollution, as these wavelengths scatter more within the eye and have detrimental environmental

27 and glare effects. LED’s light emissions are characterized by their correlated color temperature

28 (CCT) index.12,13  The first generation of LED outdoor lighting and units that are still widely being

29 installed are “4000K” LED units. This nomenclature (Kelvin scale) reflects the equivalent color of

30 a heated metal object to that temperature. The LEDs are cool to the touch and the nomenclature has

31 nothing to do with the operating temperature of the LED itself. By comparison, the CCT associated

32 with daylight light levels is equivalent to 6500K, and high pressure sodium lighting (the current

33 standard) has a CCT of 2100K. Twenty-nine percent of the spectrum of 4000K LED lighting is

34 emitted as blue light, which the human eye perceives as a harsh white color. Due to the point-

35 source nature of LED lighting, studies have shown that this intense blue point source leads to

36 discomfort and disability glare. 14


38 More recently engineered LED lighting is now available at 3000K or lower. At 3000K, the human

39 eye still perceives the light as “white,” but it is slightly warmer in tone, and has about 21% of its

40 emission in the blue-appearing part of the spectrum. This emission is still very blue for the

41 nighttime environment, but is a significant improvement over the 4000K lighting because it

42 reduces discomfort and disability glare. Because of different coatings, the energy efficiency of

43 3000K lighting is only 3% less than 4000K, but the light is more pleasing to humans and has less

44 of an impact on wildlife.


46 Glare


48 Disability glare is defined by the Department of Transportation (DOT) as the following:


50 “Disability glare occurs when the introduction of stray light into the eye reduces the ability to

51 resolve spatial detail. It is an objective impairment in visual performance.”


CSAPH Rep. 2-A-16 -- page 3 of 8


1 Classic models of this type of glare attribute the deleterious effects to intraocular light scatter in the

2 eye. Scattering produces a veiling luminance over the retina, which effectively reduces the contrast

3 of stimulus images formed on the retina. The disabling effect of the veiling luminance has serious

4 implications for nighttime driving visibility. 15


6 Although LED lighting is cost efficient and inherently directional, it paradoxically can lead to

7 worse glare than conventional lighting. This glare can be greatly minimized by proper lighting

8 design and engineering. Glare can be magnified by improper color temperature of the LED, such as

9 blue-rich LED lighting. LEDs are very intense point sources that cause vision discomfort when

10 viewed by the human eye, especially by older drivers. This effect is magnified by higher color

11 temperature LEDs, because blue light scatters more within the human eye, leading to increased disability glare.16



14 In addition to disability glare and its impact on drivers, many residents are unhappy with bright

15 LED lights. In many localities where 4000K and higher lighting has been installed, community

16 complaints of glare and a “prison atmosphere” by the high intensity blue-rich lighting are common.

17 Residents in Seattle, WA have demanded shielding, complaining they need heavy drapes to be

18 comfortable in their own homes at night.17 Residents in Davis, CA demanded and succeeded in

19 getting a complete replacement of the originally installed 4000K LED lights with the 3000K

20 version throughout the town at great expense.18 In Cambridge, MA, 4000K lighting with dimming

21 controls was installed to mitigate the harsh blue-rich lighting late at night. Even in places with a

22 high level of ambient nighttime lighting, such as Queens in New York City, many complaints were

23 made about the harshness and glare from 4000K lighting.19 In contrast, 3000K lighting has been

24 much better received by citizens in general.


26 Unshielded LED Lighting


28 Unshielded LED lighting causes significant discomfort from glare. A French government report

29 published in 2013 stated that due to the point source nature of LED lighting, the luminance level of

30 unshielded LED lighting is sufficiently high to cause visual discomfort regardless of the position,

31 as long as it is in the field of vision. As the emission surfaces of LEDs are highly concentrated

32 point sources, the luminance of each individual source easily exceeds the level of visual

discomfort, in some cases by a factor of 1000. 17



35 Discomfort and disability glare can decrease visual acuity, decreasing safety and creating a road

36 hazard. Various testing measures have been devised to determine and quantify the level of glare

37 and vision impairment by poorly designed LED lighting.20 Lighting installations are typically

38 tested by measuring foot-candles per square meter on the ground. This is useful for determining the

39 efficiency and evenness of lighting installations. This method, however, does not take into account

40 the human biological response to the point source. It is well known that unshielded light sources

41 cause pupillary constriction, leading to worse nighttime vision between lighting fixtures and

42 causing a “veil of illuminance” beyond the lighting fixture. This leads to worse vision than if the

43 light never existed at all, defeating the purpose of the lighting fixture. Ideally LED lighting

44 installations should be tested in real life scenarios with effects on visual acuity evaluated in order to

45 ascertain the best designs for public safety.


47 Proper Shielding


49 With any LED lighting, proper attention should be paid to the design and engineering features.

50 LED lighting is inherently a bright point source and can cause eye fatigue and disability glare if it

51 is allowed to directly shine into human eyes from roadway lighting. This is mitigated by proper


CSAPH Rep. 2-A-16 -- page 4 of 8

1 design, shielding and installation ensuring that no light shines above 80 degrees from the

2 horizontal. Proper shielding also should be used to prevent light trespass into homes alongside the

3 road, a common cause of citizen complaints. Unlike current HPS street lighting, LEDs have the

4 ability to be controlled electronically and dimmed from a central location. Providing this additional

5 control increases the installation cost, but may be worthwhile because it increases long term energy

6 savings and minimizes detrimental human and environmental lighting effects. In environmentally

7 sensitive or rural areas where wildlife can be especially affected (e.g., near national parks or bio-

8 rich zones where nocturnal animals need such protection), strong consideration should be made for

9 lower emission LEDs (e.g., 3000K or lower lighting with effective shielding). Strong consideration

10 also should be given to the use of filters to block blue wavelengths (as used in Hawaii), or to the

11 use of inherent amber LEDs, such as those deployed in Quebec. Blue light scatters more widely

12 (the reason the daytime sky is “blue”), and unshielded blue-rich lighting that travels along the

13 horizontal plane increases glare and dramatically increases the nighttime sky glow caused by

14 excessive light pollution.




18 Much has been learned over the past decade about the potential adverse health effects of electric

19 light exposure, particularly at night.21-25 The core concern is disruption of circadian rhythmicity.

20 With waning ambient light, and in the absence of electric lighting, humans begin the transition to

21 nighttime physiology at about dusk; melatonin blood concentrations rise, body temperature drops,

22 sleepiness grows, and hunger abates, along with several other responses.


24 A number of controlled laboratory studies have shown delays in the normal transition to nighttime

25 physiology from evening exposure to tablet computer screens, backlit e-readers, and room light

26 typical of residential settings.26-28 These effects are wavelength and intensity dependent,

27 implicating bright, short wavelength (blue) electric light sources as disrupting transition. These

28 effects are not seen with dimmer, longer wavelength light (as from wood fires or low wattage

29 incandescent bulbs). In human studies, a short-term detriment in sleep quality has been observed

30 after exposure to short wavelength light before bedtime. Although data are still emerging, some

31 evidence supports a long-term increase in the risk for cancer, diabetes, cardiovascular disease and

32 obesity from chronic sleep disruption or shiftwork and associated with exposure to brighter light

33 sources in the evening or night.25,29


35 Electric lights differ in terms of their circadian impact. 30 Understanding the neuroscience of

36 circadian light perception can help optimize the design of electric lighting to minimize circadian

37 disruption and improve visual effectiveness. White LED streetlights are currently being marketed

38 to cities and towns throughout the country in the name of energy efficiency and long term cost

39 savings, but such lights have a spectrum containing a strong spike at the wavelength that most

40 effectively suppresses melatonin during the night. It is estimated that a “white” LED lamp is at

41 least 5 times more powerful in influencing circadian physiology than a high pressure sodium light

42 based on melatonin suppression.31 Recent large surveys found that brighter residential nighttime

43 lighting is associated with reduced sleep time, dissatisfaction with sleep quality, nighttime

44 awakenings, excessive sleepiness, impaired daytime functioning, and obesity.29,32 Thus, white LED

45 street lighting patterns also could contribute to the risk of chronic disease in the populations of

46 cities in which they have been installed. Measurements at street level from white LED street lamps

47 are needed to more accurately assess the potential circadian impact of evening/nighttime exposure

48 to these lights.


CSAPH Rep. 2-A-16 -- page 5 of 8



3 The detrimental effects of inefficient lighting are not limited to humans; 60% of animals are

4 nocturnal and are potentially adversely affected by exposure to nighttime electrical lighting. Many

5 birds navigate by the moon and star reflections at night; excessive nighttime lighting can lead to

6 reflections on glass high rise towers and other objects, leading to confusion, collisions and death. 33

7 Many insects need a dark environment to procreate, the most obvious example being

8 lightning bugs that cannot “see” each other when light pollution is pronounced. Other

9 environmentally beneficial insects are attracted to blue-rich lighting, circling under them until they

10 are exhausted and die.34,35 Unshielded lighting on beach areas has led to a massive drop in turtle

11 populations as hatchlings are disoriented by electrical light and sky glow, preventing them from

12 reaching the water safely.35-37  Excessive outdoor lighting diverts the hatchlings inland to their

13 demise. Even bridge lighting that is “too blue” has been shown to inhibit upstream migration of

14 certain fish species such as salmon returning to spawn. One such overly lit bridge in Washington

15 State now is shut off during salmon spawning season.


17 Recognizing the detrimental effects of light pollution on nocturnal species, U.S. national parks

18 have adopted best lighting practices and now require minimal and shielded lighting. Light pollution

19 along the borders of national parks leads to detrimental effects on the local bio-environment. For

20 example, the glow of Miami, FL extends throughout the Everglades National Park. Proper

21 shielding and proper color temperature of the lighting installations can greatly minimize these types

22 of harmful effects on our environment.




26 Current AMA Policy supports efforts to reduce light pollution. Specific to street lighting, Policy H-

27 135.932 supports the implementation of technologies to reduce glare from roadway lighting. Thus,

28 the Council recommends that communities considering conversion to energy efficient LED street

29 lighting use lower CCT lights that will minimize potential health and environmental effects. The

30 Council previously reviewed the adverse health effects of nighttime lighting, and concluded that

31 pervasive use of nighttime lighting disrupts various biological processes, creating potentially

32 harmful health effects related to disability glare and sleep disturbance.25




36 The Council on Science and Public Health recommends that the following statements be adopted,

37 and the remainder of the report filed.


39 1. That our American Medical Association (AMA) support the proper conversion to community-

40 based Light Emitting Diode (LED) lighting, which reduces energy consumption and decreases

41 the use of fossil fuels. (New HOD Policy)


43 2. That our AMA encourage minimizing and controlling blue-rich environmental lighting by

44 using the lowest emission of blue light possible to reduce glare. (New HOD Policy)


46 3. That our AMA encourage the use of 3000K or lower lighting for outdoor installations such as

47 roadways. All LED lighting should be properly shielded to minimize glare and detrimental

48 human and environmental effects, and consideration should be given to utilize the ability of

49 LED lighting to be dimmed for off-peak time periods. (New HOD Policy)


Fiscal Note: Less than $500


CSAPH Rep. 2-A-16 -- page 6 of 8



1. Municipal Solid State Street Lighting Consortium. Accessed April 4, 2016.

2. Illuminating Engineering Society RP-8 – Guide to Roadway Lighting. 2014. Accessed April 4, 2016.

3. LED Lighting Facts–A Program of the United States Department of Energy. Accessed April 5, 2016.

4. Lin Y, Liu Y, Sun Y, Zhu X, Lai J, Heynderickz I. Model predicting discomfort glare caused by LED road lights. Opt Express. 2014;22(15):18056-71. 5. Gibbons RB, Edwards CJ. A review of disability and discomfort glare research and future direction. 18th Biennial TRB Visibility Symposium, College Station TX, United States, April 17-19, 2007.

6. Shang YM, Wang GS, Sliney D, Yang CH, Lee LL. White light–emitting diodes (LEDs) at domestic lighting levels and retinal injury in a rat model. Environ Health Perspect. 2014:122(3):269-76.

7. Lougheed T. Hidden blue hazard? LED lighting and retinal damage in rats, Environ Health Perspect. 2014;122(3):A81.

8. A Municipal Guide for Converting to LED Street Lighting, ( 10/13/2013.

9. In depth: Advantages of LED Lighting. Accessed April 5, 2016.

10. Silverman H. How LED Streetlights Work. June 22, 2009. Accessed April 7, 2016.

11. Jin H, Jin S, Chen L, Cen S, Yuan K. Research on the lighting performance of LED street lights with different color temperatures. IEEE Photonics Journal. 2015;24(6):975- 78. Accessed April 7, 2016.

12. Morris N. LED there be light. Nick Morris predicts a bright future for LEDs. Accessed April 7, 2016.

13. Mills MP. The LED illumination revolution. Forbes Magazine. February 27, 2008. Accessed April 5, 2016. CSAPH Rep. 2-A-16 -- page 7 of 8

14. Opinion of the French Agency for Food, Environmental and Occupational Health & Safety, October 19, 2010. 0408EN.pdf

15. U.S. Department of Transportation, Federal Highway Administration, 2005.

16. Sweater-Hickcox K, Narendran N, Bullough JD, Freyssinier JP. Effect of different coloured luminous surrounds on LED discomfort glare perception. Lighting Research Technology. 2013;45(4):464-75. Accessed April 5, 2016.

17. Scigliano E. Seattle’s new LED-lit streets Blinded by the lights. Crosscut. March 18, 2013. Accessed April 6, 2016.

18. Davis will spend $350,000 to replace LED lights after neighbor complaints. CBS Local, Sacramento;October 21, 2014.

19. Chaban M. LED streetlights in Brooklyn are saving energy but exhausting residents. NY Times; March 23, 2015. Accessed April 5, 2016.

20. Vos JJ. On the cause of disability glare and its dependence on glare angle, age and ocular pigmentation. Clin Exp Optom. 2003;86(6):363-70. 21. Stevens RG, Brainard GC, Blask DE, Lockley, SW, Motta, ME. Breast cancer and circadian disruption from electric lighting in the modern world. CA Cancer J Clin. 2014;64:207-18.

22. Evans JA, Davidson AJ. Health consequences of circadian disruption in humans and animal models. Prog Mol Biol Transl Sci. 2013;119:283-323.

23. Wright KP Jr, McHill AW, Birks BR, Griffin BR, Rusterholz T, Chinoy ED. Entrainment of the human circadian clock to the natural light-dark cycle. Curr Biol. 2013;23:1554-8.

24. Energy Savings Estimates of Light Emitting Diodes in Niche Lighting Applications. Building Technologies Program, Office of Energy Efficiency and Renewable Energy, U.S. Department of Energy. January 2011. 1.pdf.Accessed April 7, 2016.

25. Council on Science and Public Health Report 4. Light pollution. Adverse effects of nighttime lighting. American Medical Association, Annual Meeting, Chicago, IL. 2012.

26. Cajochen C, Frey S, Anders D, et al. Evening exposure to a light-emitting diodes (LED)- backlit computer screen affects circadian physiology and cognitive performance. J Appl Physiol. 2011;110:1432-8.

27. Chang AM, Aeschbach D, Duffy JF, Czeisler CA. Evening use of light-emitting eReaders negatively affects sleep, circadian timing, and next-morning alertness. Proc Natl Acad Sci USA. 2015;112:1232-7. CSAPH Rep. 2-A-16 -- page 8 of 8

28. Gooley JJ, Chamberlain K, Smith KA, et al. Exposure to room light before bedtime suppresses melatonin onset and shortens melatonin duration in humans. J Clin Endocrinol Metab. 2011;96:E463-72.

29. Koo YS, Song JY, Joo EY, et al. Outdoor artificial light at night, obesity, and sleep health: Cross-sectional analysis in the KoGES study. Chronobiol Int. 2016;33(3):301-14.

30. Lucas RJ, Peirson SN, Berson DM, et al. Measuring and using light in the melanopsin age. Trends Neurosci. 2014;37:1-9.

31. Falchi F, Cinzano P, Elvidge CD, Keith DM, Haim A. Limiting the impact of light pollution on human health, environment and stellar visibility. J Environ Manage. 2011;92:2714-22.

32. Ohayon M, Milesi C. Sleep deprivation/insomnia and exposure to street lights in the American general population. American Academy of Neurology Annual Meeting. April 15-21, 2016. Vancouver, BC.

33. Pawson SM, Bader MK. Led lighting increases the ecological impact of light pollution irrespective of color temperature. Ecological Applications. 2014;24:1561-68.

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36. Rusenko KW, Mann JL, Albury R, Moriarty JE, Carter HL. Is the wavelength of city glow getting shorter? Parks with no beachfront lights record adult aversion and hatchling disorientations in 2004. Kalb H, Rohde A, Gayheart K, Shanker, K, compilers. 2008. Proceedings of the Twenty-fifth Annual Symposium on Sea Turtle Biology and Conservation, NOAA Technical Memorandum NMFS-SEFSC-582, 204pp.

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Acknowledgement: The Council thanks George Brainard, PhD (Thomas Jefferson University); Richard Stevens, PhD (University Connecticut Health Center); and Mario Motta, MD (CSAPH, Tufts Medical School) for their contributions in preparing the initial draft of this report, and the commentary by Travis Longcore, PhD, on the ecological impact of nighttime electrical lighting.