National Assessment of Beachfront Lighting and its Effect - DukeSpace
Transcript of National Assessment of Beachfront Lighting and its Effect - DukeSpace
IN THE SPOTLIGHT:
AN ASSESSMENT OF BEACHFRONT LIGHTING AT FOUR HOTELS AND RECOMMENDATIONS FOR MITIGATION NECESSARY TO SAFEGUARD SEA
TURTLES NESTING IN BARBADOS, WEST INDIES
by John English Knowles
Dr. Karen L. Eckert, Advisor December 2007
Masters project submitted in partial fulfillment of the requirements for the Master of Environmental Management degree in
the Nicholas School of the Environment and Earth Sciences of Duke University
2007
ABSTRACT
Artificial beachfront lighting is an increasing problem for sea turtle hatchlings and adult
females. Barbados, the easternmost Caribbean island, exhibits particularly acute light pollution on the south and west coasts, which overlap one of the largest hawksbill sea turtle, Eretmochelys imbricata, rookeries in the region. A predominant source of artificial beachfront lighting is from hotels. To address the industry’s impact, and following the recommendations of a 2000 national workshop titled, “Sea Turtles and Beachfront Lighting: An Interactive Workshop for Industry Professionals and Policy-Makers in Barbados,” four leading hotels participated in a six-month voluntary lighting assessment. The lighting assessments followed standard guidelines and a ranking system was developed to objectively evaluate each light fixture based on intensity. The ranking system highlights fixtures most detrimental to sea turtle orientation, and encourages hoteliers to evaluate progress made toward sea turtle friendly lighting regimes over time. The results of the assessment were presented to the four hotels in user friendly assessment reports, which included mitigation recommendations for each fixture type. The assessment reports establish a lighting baseline for future assessments and act as a clearinghouse of recommenda-tions for problematic lighting schemes. The hotel industry bears responsibility for the effects of their properties on sea turtle nesting grounds; therefore, encouraging them to rectify beachfront light pollution is crucial to the management of sea turtle populations in the Caribbean and throughout the world. The study, and the willingness of major beachfront hotels to participate, provides a replicable model for other countries to follow.
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Table of Contents Introduction..................................................................................................................................... 3 Barbados in the Spotlight................................................................................................................ 5 Participating Hotels......................................................................................................................... 7
Fairmont Royal Pavilion............................................................................................................. 9 Sandy Lane.................................................................................................................................. 9 Turtle Beach Resort .................................................................................................................... 9 Southern Palms Beach Club...................................................................................................... 10
Methodology................................................................................................................................. 10 Management Issues....................................................................................................................... 14
Hatchling Arena Assays............................................................................................................ 14 Commonalities among Properties ............................................................................................. 16 Distinct Issues ........................................................................................................................... 19 Lighting and Crime Misconceptions......................................................................................... 22
Next Steps and Broader Recommendations.................................................................................. 25 Literature Cited ............................................................................................................................. 32 Appendix I - Resolutions, pledges, and recommendations emerging the meeting title: Sea Turtles and Beachfront Lighting: An Interactive Workshop for Industry Professionals and Policy-Makers in Barbados held in 2000 .............................................................................................................. 36 Appendix II - Hotel invitation letter to participate in lighting assessment ................................... 38 Appendix III - Original lighting evaluation form ......................................................................... 41 Appendix IV - Modified lighting evaluation form ....................................................................... 42 Appendix V – Fairmont Royal Pavilion property map................................................................. 43 Appendix VI – Fairmont Royal Pavilion assessment report......................................................... 44 Appendix VII – Sandy Lane property map................................................................................... 69 Appendix VIII – Sandy Lane assessment report........................................................................... 70 Appendix IX –Turtle Beach Resort property map...................................................................... 103 Appendix X– Turtle Beach Resort assessment report ................................................................ 104 Appendix XI – Southern Palms Beach Club property map ........................................................ 124 Appendix XII – Southern Palms Beach Club assessment report................................................ 125
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Introduction
Artificial beachfront lighting contributes to the degradation of sea turtle nesting grounds
because natural light guiding gravid females and their young to the sea is diminished by light
pollution from beachfront properties. The resulting disorientation (loss of bearings) and
misorientation (incorrect orientation) is especially acute in the hatchling stage (U.S. Fish and
Wildlife Service 1999), and the consequences are often fatal (Mrosovsky and Carr 1967;
Mrosovsky and Shettleworth 1968; Philibosian 1976; Dickerson and Nelson 1989; Witherington
and Bjorndal 1991; Witherington and Martin 2003). Working towards a solution to this problem,
this document explores light pollution mitigation processes and techniques at four hotel
properties in Barbados, West Indies.
Over the course of the last century, human activity along the coastline has reduced the
reproductive success of marine turtles in the Caribbean Sea and elsewhere (Kemf et al. 2000;
Lutz and Musick 1996; MTSG 1995). As a result of coastal land use patterns, and centuries of
largely unmanaged exploitation, incidental capture and international trade, sea turtles are
recognized as endangered species by international law (Frazier 2002) and are fully protected by
more than half of all Wider Caribbean governments (Fleming 2001; Bräutigam and Eckert 2006),
including Barbados (Horrocks 1992). All six Caribbean-occurring species are classified as
Endangered or Critically Endangered by the ICUN Red List of Threatened Species either
because of reduced range of habitat, recent decline in population sizes, or both (Pritchard 1996;
WWF 2004; IUCN 2007).
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The hawksbill turtle (Eretmochelys imbricata) has also been affected by widespread
over-exploitation for traditional crafting industries associated with its keratinized carapace
scutes, known as tortoiseshell or bekko (King 1982; Meylan and Donnelly 1999; Kemf et al.
2000; Bräutigam and Eckert 2006; Reuter and Crawford 2006). Notwithstanding, signs of
population increases are evident at remnant nesting colonies where long-term protection has been
the norm, including Barbados (Krueger et al. 2003; Beggs et al. 2007).
In furtherance of national conservation policies in Barbados, where, as in many other
nations, threats persist even after implementation of protective legislation and ratification of
international trade treaties (see Bräutigam and Eckert 2006 for a summary of legislation and
treaty obligations in Barbados), my objective was to assess and quantify the nation’s dominant
sea turtle survival threat (beachfront lighting) and to offer specific recommendations for
mitigation, thereby demonstrating to the hotel industry that there are feasible and practical
solutions to light pollution.
Artificial beachfront lighting has increased tremendously (Frazer 1992) resulting in the
inadvertent mortality of thousands of hatchlings (Eckert and Horrocks 2002; Witherington and
Martin 2003). Artificial light is often associated with built development adjoining the beach,
including hotels, private homes, villas, condos, streets, and parking lots. Depending on the
location, certain property types dominant the landscape – but of all the various beachfront
properties in Barbados and elsewhere, large hotels tend to have the most significant effect on the
beaches they abut.
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Tackling light pollution in large hotels might seem daunting due to the scale of some
complexes, the number of fixtures, and the amount of light emitted towards the beach. However,
hotel premises can work to the advantage of mitigating beachfront lighting. First, large hotel
properties can be elongated along significant portions of beach, which can be managed as a
whole. Correcting light pollution at a single hotel can have a considerable impact to the
nocturnal environment for an entire bay. It can be mentioned that the financial capacity of the
hotel sector (PKF 2006) can enable change to take place in the management regimes of adjoining
beaches at a much faster pace than is likely to occur with similar regimes for beachside roads and
parks managed by Government (McConney et al. 2003). However the strength of this argument
is diminished since light pollution mitigation is not expensive and is often cost effective once
implemented. Third, hotels are usually organized under an industry representative that can
provide direction for a larger portfolio of hotel properties. Finally, hotels are critiqued by third
party evaluation/certification organizations and the guests they cater to. Both of these groups,
when led correctly, can provide the recognition warranted from increased responsibility among
individual hotels.
Barbados in the Spotlight
In Barbados, the southwest coast has many beachfront hotels. The low wave energy
beaches of the Caribbean Sea attract tourists as well hawksbill sea turtles. The overlap has
resulted in the degradation of turtle nesting grounds due to artificial beachfront lighting that
affects both hatchlings and nesting females. Problems associated with artificial lighting have
only worsened since being identified (Potter 1996; Meylan and Donnelly 1999).
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It is no coincidence that in 2000, the Wider Caribbean Sea Turtle Conservation Network
(WIDECAST), the Barbados Sea Turtle Project, and the Tourism Development Corporation
sponsored an event titled “Sea Turtles and Beachfront Lighting: An Interactive Workshop for
Industry Professionals and Policy-Makers in Barbados” (Eckert and Horrocks 2002). The
workshop culminated in several recommendations and pledges by the hotel industry in Barbados
that demonstrated their commitment to the survival of sea turtles (Appendix I).
Among the pledges made by the hotel industry in Barbados was the pledge to “undertake
a lighting assessment and investigate [their] capacities to participate in ‘turtle friendly’ lighting
schemes [and to] implement, as soon as practicable, ‘turtle friendly’ lighting on all beaches”
(Eckert and Horrocks 2002). A formal lighting assessment provides the most effective
foundation by which specific lighting issues, recurring along the coast, can be addressed. It also
provides the information required for hotels to prioritize, implement, and evaluate the lighting
improvements so desperately needed on the island.
The lighting assessment tool has been used successfully both in the United States and in
parts of the Caribbean. This technique focuses on identifying the most serious light pollution
problems and making recommendations as to the most efficient way(s) to reduce the amount of
light that reaches the beach, encapsulated by the three Golden Rules of correcting lighting
problems: keep it low, keep it shielded, keep it long [wavelength]
(http://www.myfwc.com/seaturtle/lighting/lighting_course.htm). The three Golden Rules are not
substitutes for lights that can safely be turned off at night during the nesting and hatching
seasons.
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Mitigating light pollution is sensible and straightforward, but often overlooked as a
provision for a healthy beach environment. As a result, many beach communities come to
recognize the negative impacts of artificial lighting only after much of the nesting habitat has
already been degraded. Once this point has been reached, legislative intervention is helpful
because unilateral action by one or two properties can be ineffective in a densely developed
landscape. Some governments have responded by taking protection of their sea turtles to the
next level: by passing lighting ordinances and other appropriate laws. The leader in this field is
clearly the State of Florida, USA, where many municipalities and other communities have passed
lighting ordinances in compliance with state mandates (see Witherington and Martin 2003).
Like most countries in the Caribbean, Barbados does not have specific regulations
concerning beachfront lighting and the resulting loss of many thousands of endangered hawksbill
hatchlings who are fatally disoriented every year is a serious threat to conservation (Eckert and
Horrocks 2002). There are also numerous cases of nesting females finding their way into
backyard swimming pools and drains (Barry H. Krueger, Barbados Sea Turtle Project, personal
communication, 2006). As the number of these incidences grow, it is clear that the issue must be
addressed through a stakeholder (hotels, hospitality industry representative, government and
community) led process that will effectively mitigate this threat on a national basis.
Participating Hotels
With a view to evaluating the extent to which hotels had implemented the pledges made
at the 2000 hotelier workshop (Eckert and Horrocks 2002), the Barbados Sea Turtle Project
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initiated a partnership with WIDECAST to conduct formal lighting assessments at four
prominent beachfront hotels in Barbados – Fairmont Royal Pavilion, Sandy Lane, Turtle Beach
Resort, and Southern Palms Beach Club (Assessments Reports). The four hotels were chosen
because of their leadership in environmental consciousness, location on critical nesting beach
habitat, unresolved beachfront lighting and/or past interests/efforts in mitigating artificial
beachfront lighting. The hotels differ in ownership, clientele, architecture, and degree of light
pollution. Each was asked, and agreed, to participate in a voluntary lighting assessment during
the summer of 2006 (Appendix II).
The selected hotels are not to blame for the lighting problems in Barbados, even if they
do hold some responsibility. Also, they do not represent the worst case scenarios, for there are
many other beaches with high levels of artificial lighting. Finally, correcting the beachfront
lighting at these four hotels will not solve the national problem; however, their assessments act
as a baseline to ameliorating the conflict between beachfront lighting and sea turtle nesting
grounds.
Aware that Barbados lacks a national lighting ordinance, leaving any emphasis on ‘turtle
friendly’ lighting to the discretion of the hotelier, we hope that this study and attendant
recommendations will not only spur participating hotels to make significant progress towards
turtle friendly, energy efficient and safe alternatives, but will provide models of success that can
be replicated at other properties in Barbados and beyond.
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Fairmont Royal Pavilion
The Fairmont Royal Pavilion hosts 72 deluxe ocean-front rooms, running along 1000 feet
of beach. The cost of the most expensive room is approximately $550 USD/night. The hotel is
couple-oriented and will not book families with children under the age of 13 during the busy
season (November to April). It is managed under Fairmont Hotels and Resorts, “the largest
luxury hotel company in North America”, ensuring consistency to its clientele by applying strict
company standards regarding amenities for all its properties (www.fairmont.com/royalpavilion).
Sandy Lane
Preferred Hotels and Resorts certifies Sandy Lane through their Standards of Excellence
program since they offer only the highest quality of service. Of the 112 luxury rooms and suites,
totaling approximately 116,000 square feet, 79 view the ocean. The cost of the rooms range
from $450 USD/night to $900 USD/night, with the price of one of the villas reaching $24,000
USD/night during the busy season. The clientele is varied, consisting of family, honeymoon
couples and small niche corporate and incentive groups. The property stretches along 1000 feet
of beachfront (www.sandylane.com/introduction/index.html).
Turtle Beach Resort
Turtle Beach Resort was the only all-inclusive hotel assessed, which is why the cost per
night is upwards of $1,000 USD. It has 166 spacious suites, many with panoramic ocean views.
It is a four star hotel, managed under Elegant Hotels Group Barbados and caters to families
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offering a variety of activities for all ages. The hotel extends along 1,500 feet of beach
(www.turtlebeachresortbarbados.com).
Southern Palms Beach Club
Of the four hotels, the Southern Palms Beach Club had the least expensive rooms with
the most costly ones reaching $350 USD/night. According to the website, the hotel “welcomes
the young who want to do it all, the couple that just wants to enjoy each other’s company in the
tranquil beauty of the island, or the family with children.” Southern Palms Beach Club has 92
rooms of which 53 view the ocean. The property is situated along 1000 feet of beachfront
(www.southernpalms.net).
Methodology
The overall procedure to conducting a lighting survey is simple; walk the beach and
identify sources of light observed. In Florida, properties identified as having problem lights are
warned and then an assessment is conducted. The assessment usually involves the completion of
a lighting evaluation form (Appendix III), which is handed to the property owners (R. Erik
Martin, Ecological Associates, personal communication). A modified version of the lighting
evaluation form (Appendix IV) from Ecological Associates, Inc was still used, but the data was
ultimately conveyed in the user friendly assessment reports.
Each assessment report is broken down into several sections, beginning with an
introduction, where readers are reminded of the effects of beachfront lighting on endangered sea
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turtles and why hotels play such a critical role in mitigating light pollution. A survey method
section details the systematic nature of this procedure and why it took place during the hours it
did. The following section, making up the bulk of the report, defines the ranking scale used to
evaluate fixtures based on intensity and details the recommendations given.
It is first explained that each fixture receives a rank of 1, 2, or 3 and the meaning that
each rank holds. It is the inability to quantify the impact of light on marine turtles that led to the
development of a ranking scale in the first place. The ranking (1, 2 or 3) was modified from the
scale used by Ecological Associate, Inc. As explained in each assessment report, a rank of “1”
describes indirect light visible by an observer on the beach, but not likely to present a strong
attraction to nesting or hatching turtles. A rank of “2” describes direct light or a visible globe,
glowing element, lamp, or reflector likely to disorient turtles. Both “1” and “2” ranking lights
are not strong enough to cast a discernible shadow on the beach during a dark night. A rank of
“3” describes a light source strong enough to cast a shadow on the beach regardless of the
illumination being direct or indirect. Ideally, a beach should not have any source of illumination
to rank, revealing a score of zero and hence no need for an assessment. However, in context of
reality a rank of “1” is preferred over a rank of “2”, which is preferred over a rank of “3.”
Three important aspects of the ranking scale are its simplicity, objectivity, and
reproducibility. It can be understood by maintenance personnel who will most likely be
implementing the recommendations. It can also be easily understood by upper management who
will be making the lighting scheme decisions during renovations or new additions. This will
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allow current fixtures to be corrected properly and quickly, and allow the introduction of turtle
friendly alternatives in future lighting designs.
The ranking scale is also objective because each fixture assessment will result in the same
ranking, regardless of the assessor. This consistency will aid in reproducibility, providing a
baseline for hotels to track their progress from nesting season to nesting season.
The assessment reports then list of all the recommendations given in the assessments,
which correspond to small, user-friendly illustrations. Each assessment report has a different list
because each property is unique, but many recommendations are shared. Please note that this list
is not exhaustive.
Next in the assessment report are the evaluations of the fixture types, which is succinctly
displayed on one easy to view page. The display includes a labeled photograph, the assigned
rank, location, number of fixtures of that kind, comments (if necessary), and the illustrated
recommendations. Most fixtures have more than one recommendation, some more involved than
others, which is the main reason why recommendation illustrations were used. They are much
easier to absorb than repetitive text. If certain fixtures required a more in depth explanation than
the illustration could offer or if distinct issues arose, then the comment section was utilized.
The fixture type evaluations themselves are ordered based on the degree of rank (1, 2 or
3) as a primary tier. Since a rank of “3” indicates the most problematic light they are all listed
first, then the “2” ranking lights and finally the “1” ranking lights. Within the primary tier, the
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order is based on the number of fixtures of that kind, color, the creativity involved in resolving
the lighting problem, the attention it will require, or the cost to implementing the
recommendation. The order within the primary tier (1, 2 or 3) is more subjective because precise
quantification on the impacts to marine turtles is still not possible.
The user friendly format is intended to direct a hotel’s focus on the most problematic
lights, provide easy to understand recommendation illustrations and present a simple ranking
scheme. It is hoped that the ease of quick referencing the assessment will foster a more
favorable response by busy hotel staff and managers.
The assessment reports conclude by commending the hotels on their past and present
efforts in beachfront light reduction, but reaffirm the importance in executing the
recommendations. An internet resources section directs readers to any of the websites where
certain bulbs or fixtures mentioned in the assessment can be bought or viewed.
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Management Issues
Hatchling Arena Assays
The potential effectiveness of the recommendations given in the assessment reports was
simulated by the results from hatchling arena assays. Historically, such experiments were
performed when the effect on hatchlings of certain lighting schemes or designs were uncertain
Hotel
↕
Sea
P<0.0005
0.0025<P<0.005
Site 1
Site 2
Hotel A Hotel B Hotel
↕ Site 1
Sea
P<0.0005
P>0.25
P<0.0005
Site 2
Site 3
Site 4
0.005<P<0.01
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(Ecological Associates 2002). Unfortunately for Barbados, uncertainty is not the reason for
performing such experiments since hatchling disorientation is so severe (JEK, personal
observation; Eckert and Horrocks 2002). The experiments demonstrate the effect hotels can
have by reducing beachfront light.
The experiment was performed in front of two hotels (Hotels A and B). The assay acts as
a staged hatching event inside a designated circular arena. The arena had a one meter radius
divided into 36 sections. A trench was dug for the arena’s perimeter and each of the 36 sections,
representing 10 degrees of a circle, were divided off using cardboard slots each separated by a
17.5 cm arc length. The arena was modified from Salmon and Witherington (1995). Two
property arenas were positioned directly in front of Hotel A (Site 1 and 2) and Hotel B (Site 1
and 2). Hotel B had two additional peripheral arenas, one 25 meters north of the property (Site
3) and one 25 meters south of the property (Site 4).
The hatchlings used were collected from hotels where they had emerged and been
previously disoriented that night. Twelve (12) neonates were placed center circle, facing the sea
and released one at a time (modified from Salmon and Witherington 1995). This was carried out
in two rounds for each arena. The first round was performed with lights on as they would be
during normal early evening operation. The second round was carried out with all “3” ranking
lights turned off. The data recorded for each hatchling included its final position at the
perimeter, the length of its track, and the time needed to reach the arena boundary.
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In Salmon and Witherington (1995), “Rayleigh tests were used to determine whether the
orientation of a group of turtles in any one experiment differed significantly from random” (p.
933). This experiment used a Watson-Wilson test for two samples, which incorporates the
Rayleigh test to determine if there is a difference in the means between the two rounds (Zar
1984). Orientation for each experiment did differ significantly from random and all (lights on –
lights off) pairs were significantly different except for one. The exception was Site 2 at Hotel B
(P>0.25) where one floodlight (with a rank of “3”) was unable to be turned off.
The results of this analysis reinforce the importance of hotel cooperation in mitigation
beachfront lighting. The results obtained from the peripheral arenas at Hotel B help demonstrate
lights can affect more than the area of beach they directly illuminate. The broadcast of some
fixtures can affect an entire bay by actually drawing hatchlings from darker section of beach out
of the water (JEK, personal observation).
Commonalities among Properties
Most hotels provide the same service and similar functions. For example, they provide
restaurants, balcony rooms, large windows for unobstructed viewing, and security for protection.
Usually little thought is put into the side effects of providing these services, which usually go
unnoticed, unless you are a beachfront hotel. The side effects of common services are much
more serious for hotels that abut endangered sea turtle nesting grounds.
One common problem observed at all four hotels was the issue of beachfront restaurants.
In most cases, there was no intentional illumination of the beach associated with the restaurants.
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Ceiling and wall mounted light fixtures were the main source of broadcast out of the restaurant.
Recommendations included concealing wall mounted fixtures and shielding ceiling fixtures. The
light from these fixture types usually provide two purposes. One is to illuminate the space where
people walk and the other is to illuminate the food and faces at the table. Ultimately, all light
sources used to illuminate spaces of beach front buildings should be lowered behind opaque
objects. Louvered foot lights installed into the wall of the restaurants are excellent examples.
Landscaping is another excellent means to screening light and was recommended quite often. As
for illuminating the table area, table lamps with shades and LED candles were recommended in
the assessments. Shaded table lamps and LED candles are both efficient light sources because
they provide the illumination needed at a dinner table without broadcasting light beyond the
restaurant.
Decorative lighting should be one of the easier categories of lighting to mitigate because
they serve only to enhance ambiance and the best recommendation is to eliminate. However,
this might be much harder in practice because of their popularity on hotel beachfronts. Although
such fixtures are festive, it was highly encouraged that decorative lighting be reserved for areas
not visible from the beach because it is “much more harmful to sea turtles than it is useful to
people” (Witherington and Martin 2003, p.21).
Recommendations for lights that serve multiple purposes are more difficult. Two
commonly paired categories of lighting were security and area lighting, most of which are
spotlights. Security lighting includes lights that illuminate a perimeter or an area for the soul
purpose of preventing crime. An area light is defined as a source of illumination for spaces such
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as walkways, patios, or steps. When it comes to mitigating artificial beachfront lighting,
separating light sources into their separate functions creates greater ease in resolving the lighting
problem. Thus, lights and fixtures which primarily provide for security are best handled by
recommending the installation of motion detectors. For area lighting, it was recommended that
fixtures be replaced with a turtle friendly alternative, such as a louvered bollard or path light,
which can be easily concealed behind opaque objects. Area lighting that intentionally included
portions of beach was highly discouraged.
Along with multi-purpose lighting fixtures, the assessment of hotels can be quite difficult
because of the depth, height and length of the hotel complex, which only increase the number
and types of fixtures to be evaluated and corrected. Both the Southern Palms Beach Club and the
Fairmont Royal Pavilion, a hotel with only beachfront rooms, exemplify the length factor. Each
hotel is stretched along 1,000 feet of beach front with buildings and fixtures occupying most
every foot.
The properties of Sandy Lane and Turtle Beach Resort stretch back from the beach
servicing the depth factor. Evaluation and mitigation difficulties arise when forward lights are
corrected but its improvement is only counteracted by lights from behind. This is why it is
important to work with the hotels during an assessment so that brighter forward lights can be
turned off to obtain the true effect of the lights from behind.
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Height was not an issue for the hotels assessed in Barbados since most did not exceed
four stories. One advantage in not exceeding four stories is the ability to exploit vegetation as a
buffer between lights and the beach. This becomes less applicable with high rise hotels.
All three issue of height, depth and length are compounded by the proximity to the beach.
Lights become more disruptive to sea turtles the closer the hotel is to the ocean. The Fairmont
Royal Pavilion and the Southern Palms Club are closest to the beach. This is the main reason
why most lights at these hotels ranked as high as they did. Pushing these same hotels with the
same lights back from the water would lessen the effect on sea turtles. It was not recommended
in the assessments that hotels move their building back from the water, since property setbacks is
the responsibility government managing the coastal zones.
Distinct Issues
Just as the lighting problems shared among the four hotels are likely to be observed
throughout the Caribbean, so too are the unique lighting problems observed between the hotels.
In this report, uniqueness is defined either by the reason why a particular lighting problem is
present or by the mitigation technique used to correct the problem.
As mentioned previously, beachfront restaurants are quite common and the effect on the
beach from lighting these areas is compounded by their length and close proximity to the beach.
Not mentioned was the overlap between hatchling emergence from the nest and restaurant’s
operational hours. Witherington et al. (1990) demonstrated that peak emergence of loggerhead
turtles on Florida beaches is around midnight, with 31% emerging before that time. Although no
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formal study has been completed in Barbados, emergence patterns for hawksbills appear to be
similar, with a significant portion of nests emerging before midnight (Asanchia Harewood,
Barbados Sea Turtle Project, personal communication). This is also the time in which many
beachfront restaurants are open for business (thus fully lit).
The Palm Terrace Restaurant at the Fairmont Royal Pavilion is no exception with hours
of operation from 19:00 to 21:45. Of the four hotels, the Palm Terrace Restaurant is the most
extreme for beach proximity, even the hotels website exclaims that the “sea [is] so close that it
almost reaches the table” (www.fairmont.com/royalpavilion). Moreover, the dining space is
separated from the outside by large wide arches, giving space for ample light to exit onto the
beach. The recommendations related to this restaurant are what make this example unique.
The problem fixtures at the Palm Terrace Restaurant were the spot lights located at the
wall and ceiling junctions. Some fixtures created wall wash, while others were directed into the
dining space, but their bulbs were still visible from the beach. As with other restaurants, fixture
replacements and repositioning were recommended. The fixtures pointed directly towards the
beach were recommended for removal. However, it was indicated that these fixtures could not
be removed. Working on this assumption, it was recommended that the fixtures be lowered,
shielded and concealed. In any other case, planting a vegetation buffer in the space between the
restaurant and the beach would be advisable, but because such space doesn’t exist in this case,
the recommended action would need to originate from within the restaurant. It was suggested
that potted coconut palms within the dining area be positioned to block the high mounted
spotlights. However, even with repositioning of some spotlights and the urging of substituting
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still others with lower level lights, it is most likely indirect light would still present a problem.
As a final barrier to the beach it was recommended that the arches be landscaped in such a way
to reduce the space from which light could leave the dining ares, but still allowing guests to view
the ocean.
Ironically, a unique lighting problem was observed at Sandy Lane, which has very low
ranking lights, a likely situation for premier luxury and award winning hotels. However, one
fixture type was somehow overlooked. The hotels beachfront was illuminated from dusk until
2:00 by very large, blue tinted, tree mounted floodlights. These four fixtures embody everything
that a light should not be with regards to being sea turtle friendly, not to mention their high
maintenance. Because they are mounted to trees they are highly visible and their broadcast is
directed out across the bay and onto peripheral beaches. They emit short wavelength light, the
color most attractive to sea turtles and they shine at such very high intensity that it is likely even
a red version of these lights would cause problems. These lights are purely aesthetic and the best
recommendation is their elimination. However, it was indicated that these lights are prized by
Dermot Desmond, Sandy Lane’s owner. If the fixtures must remain, then it was urged their use
be restricted to outside the turtle nesting season for Barbados (May – November).
The final unique lighting problem to be discussed is the one observed at the Southern
Palms Beach Club. This property’s waterfront is lined with yellow spot lights. This particular
situation has improved after the 2000 “Sea Turtle and Beachfront Lighting Workshop,” where
wattage was reduced and white spotlights were replaced with yellow spotlights. But the fact
remains; artificial light continues to reach the beach mis-orientating almost all emergences (JEK,
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personal observation). Management indicated that the lights remain for guest safety and for
security cameras. The question to use beachside, nighttime running security cameras as the best
means for added security was raised in the assessment. It was unique that Southern Palms Beach
Club was the only hotel on the island with operational beachside, nighttime running security
cameras. Ironically, the light provided by these fixtures and others was actually not bright
enough to provide a clear image for the cameras. Therefore, other security measures were
recommended as a substitute.
Guests walking the beach at night do not actually need artificial light to see because
human eyes are capable of sight in low light when allowed to adjust (Hecht 2001). This is
possible if walkways and steps to the beach are outlined with red LEDs. This would provide
safety, while at the same time allowing the human eye to adjust naturally. The preference of
tourists to have a lit beach is probably indifferent, but when educated about the effects had by
artificial lights on marine turtles, their preference is likely to favor darker beaches.
Lighting and Crime Misconceptions
As stated in the proceedings of “Sea Turtle and Beachfront Lighting: An Interactive
Workshop for Industry Professionals and Policy-Makers in Barbados,” “the issue of safety and
security of guests continue to concern the hotel sector.” Eckert and Horrocks (2002) state in the
Epilogue: “perceived issues of guests hotels have been a major impediment to light reduction on
Barbados’ beaches”.
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The issue of safety and sea turtle lighting is common enough to be including in the
frequently asked question section of the Technical Report by Witherington and Martin (2003):
How can the sacrifice of human safety and security to save a few sea turtles be justified?
Thankfully, no such choice is necessary. The safety and security of humans can be
preserved without jeopardizing sea turtles. The goal of any program to reduce sea turtle
harassment and mortality caused by lighting is to manage light so that it performs the
necessary function without reaching the nesting beach. Still, some may contend that any
inconvenience at all is too much and that the concerns of humans should always outweigh
those for turtles. People insistent on this generalization should not ignore the large and
resolute constituency that values sea turtles. Sea turtles are valuable to people both
ecologically and for pure enjoyment. In many ways, the protection of sea turtles is in our
own best interests (p. 69).
The question above asks about the justification for the compromise between security and
saving a few turtles. If nothing else, then it must be noted that implementing sea turtle friendly
lighting will save a lot more than a few turtles in Barbados. Thousands of hatchlings are affected
every year by lighting on Barbados, which hosts one of the largest hawksbill rookeries in the
Caribbean (Beggs 2007). The degradation of this population due to artificial lighting does not
bode well for the Caribbean’s overall population. There are many islands and nations that also
hosts important rookeries for other species of turtles, which are also valuable to people and
tourism economies. Fortunately, as mentioned in the quoted answer, there is no compromise
between security and dark beaches. Both can exist in harmony.
23
Security and dark beaches can exist in harmony for two main reasons. First, security
does not have to come in the form of continuous beachfront lighting. There are different means
of providing added security, without constant illumination of the beach. Motion detector lights
are an excellent example. The light comes on when needed alerting hotel personnel that
someone as entered the detector’s field of view and also can scare away suspicious persons
(www.darksky.org). Good security guards with flashlights also provide excellent protection
from crime as this is a very common safety measure already observed by hotels in Barbados
(JEK, personal observation).
Second and more importantly than substituting continuous beachfront illumination, is the
correlation between security lighting and crime prevention. It should be noted that many sources
state that crime most often occurs during the day. But for the percentage of crimes that do occur
at night, the presence of light is often of little concern. The website for the International Dark
Skies Association (IDA) asks if security lights prevent crimes and they answer with uncertainty
(www.darksky.org). A study by the United Kingdom’s Home Office Crime Prevention Unit on
street lighting and crime discovered that improvements in street lighting do little to prevent crime
and criminals are less often deterred by light (Ramsay and Newton 1991). Another study by the
group concluded that increasing intensity of street lighting also does not improve criminal
activity (Atkins et al. 1991). Although the crime prevention studies do not look at beach lighting
and examine areas with crime rates much higher that what is observed in Barbados or other
Caribbean islands, the results are telling (Nuttall 2000).
24
Witherington and Martin (2003) respond to the comment that “[c]rime will increase if
the beach is not lighted” by stating:
Generally, beaches are not areas where there is a great need for crime prevention. Very
little valuable property is stored on beaches and there is seldom much nighttime human
activity to require security. Fortunately, areas adjacent to nesting beaches where people
reside, work, recreate, and store valuables can be lighted for protection without affecting
turtles on the nesting beach. Where this type of light management was legislated in
Florida coastal communities, the Florida State Attorney’s Office has found no subsequent
increase in crime (p. 68).
Volusia County, Florida, USA is a good example of the harmony existing between darker
beaches and security. The county has one of the strictest coastal lighting ordinances in the state.
When their lighting ordinance was passed in 1989, businesses feared losses and worries about
crime spikes were also raised. As it turns out, no such things materialized (Lelis 2003; William
“Bill” Sorrentino Sr., Zoning Compliance Division, Daytona Beach, FL, personal
communication).
Next Steps and Broader Recommendations
Other than the recommended implementations at the specific properties, there are several
next steps that need to be considered by the hotel industry, its representatives (e.g. Barbados
Hotel and Tourism Association, Tourism Development Corporation of Barbados), and
25
Government. These include follow-up assessments, examinations of other beachfront properties,
energy audits, economic analysis, legislative action, and public awareness campaigns.
Properties with the most significant lighting issues should receive priority attention in
terms of training, assessment, mitigation, and evaluation. Hotels that have not formally assessed
their beachfront lighting should be encouraged to do so. Training is available through
WIDECAST (contact Prof. Julia Horrocks, WIDECAST Country Coordinator, at the University
of the West Indies). Once the initial lighting assessment is complete using the ranking scale
provided in this document and after recommendations have been implemented, routine follow-up
assessments should ensue. The ranking scale allows hotels to track the progress of their lighting
after each formal lighting assessment. In most cases, the initial lighting assessment should
suffice in resolving all lighting problems. But because of potential changes associated with
renovation, revised landscaping, storm damage, etc. lighting will need to be constantly re-
evaluated. Although formal lighting assessment might not need to occur but every five years,
hotels need to be reminded before every turtle season to re-evaluate the lighting conditions
present and remedy off-season lighting schemes that are not turtle friendly.
The Barbados Sea Turtle Project (BSTP) operates a national Sea Turtle Hotline, a method
for turtle activity to be reported. Hatchling disorientation calls were logged for the 2006 season,
which approximately ranks properties in terms of sea turtle activity. The BSTP also documents
hatchling disorientation not reported by the Hotline. Between the two methods of reporting sea
turtle disorientation events, the Hotline calls are easiest to prioritize because they represent only
a subset of total disorientation events. In addition, Barbados hotels are ardent about calling the
26
hotline, even if only one hatchling is found. Therefore, hotline calls are a close proxy to actual
disorientation events for hotel properties because of the high probability of the events being
reported due to guests, security guards, and length of beach lined by hotels.
Collecting disorientated hatchlings can be both fun and educational for guests, but this
somber reality can take away from more critical monitoring of adult females. If such systems are
in place, then hotels should be encouraged to participate because the number of disorientation
events for a property reported is an opportunity for positive improvement. It should not be seen
as embarrassing or wrong. Hotel participation greatly extends the management ability for
monitoring organizations and quick identification and correction of light pollution at active
properties will help both parties involved. If hatchlings are provided an environment where they
may enter the water as nature intended, then the strain on monitoring organizations and hotels is
removed. Monitoring organizations could spend more time monitoring beaches and provide
more appropriate outlets for hotel guest education. Security guards would also be relieved from
having to constantly save endangered species and focus on their assigned job.
Internally, hotels can help themselves become better stewards of the environment in
which they rely on by adopting sea turtle policy statements within their environmental
management systems (EMS). For example, “X Hotel recognizes its responsibility to the coastal
environment on which it operates. We are committed to reducing our footprint on this ecosystem
by the following: 1) Preventing light pollution, 2) Removing chairs at night and using umbrellas
with a flat base instead of staking the post directly in the sand and 3) Collaborating with
stakeholders to ensure sustainable operations for coastal areas including other beachfront
27
properties owners, biologists, guests, surrounding community, government and industry
representatives.”
Efforts to reduce light pollution are not exclusive from improvements in energy
efficiency, architectural design and local markets. One, lighting is the second most significant
daily expenditure for hotels in the Caribbean region (Tourism Global Inc. 2006). Two, energy
efficient lighting will support the efforts announced by the Caribbean Tourism Association to
neutralize carbon emissions from the tourism industry (The Caribbean 2007).
An energy audit was not performed at the four participating hotels to demonstrate the cost
savings of energy efficient lighting. However, reducing wattage, keeping lights off, and
installing LEDs, compact fluorescents and/or fixtures that direct light more efficiently could
possibly help save money in a region where energy costs are some of the highest in the world
(www.climate.org/programs/washington_summit4.shtml). It has also been suggested that energy
efficient lighting translates into elegance (www.lrc.rpi.edu), thus increased revenue since
sophisticated lighting attracts today’s sophisticated traveler (Anonymous 2004; Ruffino 2007).
Providing this type of lighting will become increasingly easy as new technologies are developed
and LED and CFL fixture types are diversified (Dean Gallagher, Florida Fish and Wildlife
Conservation Commission, personal communication).
It was recommended that the Fairmont Royal Pavilion purchase turtle friendly fixtures
manufactured locally by Earthworks Pottery. This particular recommendation, when
implemented, would create a link with local industry and delight guests with authentic
28
presentation (MacCannell 1973; Poon 2003; Tourism Global Inc. 2006). It is hoped that the
purchase of locally manufactured fixtures or locally supplied bulbs would improve economic
development (Witter 2002; Duval 2004; Pattullo 2005; Tourism Global Inc. 2006; Travelwatch
2006). The implementation of such recommendations would almost certainly differ between
hotel types. Large multinational cooperate hotels, such as ones owned by Fairmont Hotels and
Resorts, might have some difficulty in providing the authentically local experience, while still
adhering to their strict company wide standards that apply to architecture as well. Locally owned
and smaller hotels might find such recommendations easier and welcoming. In any case, an
economic analysis on the role of beachfront lighting reduction with regards to local material
would be interesting.
Hotels can also be helped by third party organizations already in place, such as Green
Globe. The benchmarks set by this organization, and others like it, assist the tourism industry
meet the triple bottom line by becoming more sustainable. For countries that do not have
specific lighting regulation, these programs have the potential to positively impact the
beachfront. Criteria for turtle friendly lighting could be included in the existing standards. This
might fit particular well under the ecosystem management and conservation impact area of the
Green Globe program.
For beaches that do not have serious lighting issues, a more efficient focus might be an
entire bay. This might be more appropriate if each property had only a few lighting problems to
be assessed. Cooperation between property owners would be much more important in this case
because different property types would most likely be assessed.
29
Ultimately, lighting legislation needs to be passed for long-term commitment to protect
beaches from light pollution. Lighting legislation is also necessary because unilateral voluntary
action usually falls short since some properties will inevitably refuse to mitigate their lighting.
Unfortunately, beachfront artificial lighting, in most cases, is a symptom to a greater problem of
coastal management and the effort to correct how society makes use of the coast will take much
longer than correcting light pollution.
A good lighting ordinance should have a clearly stated purpose, set standards for existing
and new developments for both public and private properties, and be mandatory. The
effectiveness of a lighting ordinance could be increased by allowing existing properties to phase
in appropriate lighting designs and require new construction to take immediate action. It should
also be embedded in a larger conservation strategy as well as a sustainable coastal zone
management plan.
In summary, four hotels in Barbados with support from their industry representative have
committed to the lighting assessment pledge stemming from a first of its kind lighting workshop
in the region. The resulting user friendly assessment reports provide a simple and objective
ranking scheme based on light fixture intensity, which can be used to ratchet down the effect of a
light. The reports also set a lighting baseline for the four hotels so that improvements in
beachfront lighting may be tracked. In addition, the reports act as a clearinghouse of
recommendations for problematic lighting schemes observed at most hotels.
30
Hotels are an excellent focus point for reducing artificial beachfront lighting, especially
in Barbados, since they encompass a significant portion of beachfront and are influenced by
other parties. But ultimately, if stakeholders in Barbados want to lead by example and take a
long term stance to light pollution impacts on sea turtles, legislation should be introduced.
Mitigating beachfront light pollution will safeguard the reproductive stage for sea turtles,
increase beach quality and safety for tourists, dovetail hotel management priorities in energy
conservation and sustainable operations and be a step forward towards better management of
coastal zones and natural resources.
31
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Appendix I - Resolutions, pledges, and recommendations emerging the meeting title: Sea Turtles and Beachfront Lighting: An Interactive Workshop for Industry Professionals and Policy-Makers in Barbados held in 2000
Sea Turtles and Beachfront Lighting: An Interactive Workshop for Industry Professionals
and Policy-Makers in Barbados
An Interactive Workshop hosted by the Barbados Sea Turtle Project and Wider Caribbean Sea Turtle Conservation Network (WIDECAST)
Sponsored by the Tourism Development Corporation of Barbados Glitter Bay Fairmont Hotel
- 13 October 2000 -
RESOLUTION OF THE MEETING 1
RECOGNISING that Caribbean sea turtles species are classified either as Endangered or Critically Endangered by international authorities, and are fully protected in Barbados under the Fisheries (Management) Regulations, 1997; CONCERNED that sea turtle populations in Barbados have declined dramatically over the course of the 20th century, due to threats both domestic and foreign; AWARE that natural sandy beach habitat is essential to the survival of the tourism industry in Barbados, as well as to the survival of our sea turtles; ALARMED that the majority of sea turtle hatchlings emerging from the beaches of Barbados are confused and disoriented by artificial lighting and that, as a result, thousands of them die every year; SENSITIVE to the impact the modern tourism industry, including coastal construction and artificial beachfront lighting, has on the plight of sea turtles; ENLIGHTENED, based on the results of this workshop, about how the coast-based tourism industry can participate in sea turtle conservation and protection; and COMMITTED to taking effective action, both as individuals and as an industry, to ensure the survival of sea turtles in Barbados - WE PLEDGE TO:
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ADOPT a Policy Statement regarding the protection of sea turtles on hotel grounds; REVISE Standard Operating Procedures (SOPs) to implement the Sea Turtle Policy Statement and further encourage reporting and protecting nesting turtles and hatchlings by hotels and other beachfront properties;
SEEK to ensure that funding is available to support annual training (by the Barbados Sea Turtle Project) of support staff in those departments that are responsible for actualisation of the Sea Turtle Policy Statement; UNDERTAKE a lighting assessment (following the guidance of Witherington and Martin, 2000) and investigate our individual hotel and villa capacities to participate in “turtle friendly” lighting schemes; and IMPLEMENT, as soon as practicable, “turtle friendly” lighting on all beaches (e.g., replace HPS lights with LPS alternatives, install motion-sensitive security lights, turn off purely aesthetic lights at 9:00 PM during peak nesting and hatching seasons). RECOMMENDATIONS OF THE MEETING TO PROMOTE full implementation of the RESOLUTION, we recommend that the Tourism Development Corporation, in consultation with the Barbados Sea Turtle Project and the Wider Caribbean Sea Turtle Conservation Network (WIDECAST) and in collaboration with other local (BHTA) and regional (CAST) industry coalitions:
PROVIDE the hoteliers, villa rental agencies, Ministries and other relevant agencies in Barbados with a draft to be adopted and implemented by the hotel and villa rental community nation-wide, with each establishment ensuring that its SOPs are revised as necessary;
PROVIDE the hoteliers and villa rental agencies in Barbados with standard guidelines and criteria for implementing the Sea Turtle Policy Statement; and
PROVIDE coastal hoteliers and landowners with emergency numbers for reporting sea turtle sightings and violations, and a calendar noting the nesting and hatching months of local sea turtle species.
__________________ 1 excerpted from: Eckert, K. L. and J. A. Horrocks (Editors). 2002. Proceedings of “Sea Turtles and Beachfront Lighting: An Interactive Workshop for Industry Professionals and Policy-Makers in Barbados”, 13 October 2000. Sponsored by the Wider Caribbean Sea Turtle Conservation Network (WIDECAST), the Barbados Sea Turtle Project, and the Tourism Development Corporation of Barbados. WIDECAST Technical Report 1. v + 44 pp.
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Appendix II - Hotel invitation letter to participate in lighting assessment
10 July 2006 Dear Mr. Michael Pownall,
On October 13, 2000, Kelly Robinson, then Executive Director of the Caribbean Alliance for Sustainable Tourism (CAST), opened the Caribbean’s first industry meeting on “Sea Turtles and Beachfront Lighting: An interactive Workshop for Industry Profes-sionals and Policy Makers in Barbados” at Fairmont Glitter Bay Hotel in Barbados. The Workshop, hosted by the Barbados Sea Turtle Project (BSTP, UWI) and the Wider Carib-bean Sea Turtle Conservation Network (WIDECAST), and funded by the Tourism Devel-opment Corporation, was the first of its kind in the region. Ms. Robinson, herself a hotel industry professional with first-hand experience of the negative impacts of beachfront lighting on nesting sea turtles and their hatchlings in the Dominican Republic and elsewhere, was pleased to offer the commitment of CAST in tackling and resolving the conflicts between beachfront development and the survival of the region’s depleted and endangered sea turtles.
The Workshop showed that there are indeed solutions to the challenges of lighting a
property while protecting sea turtles nesting on adjacent beaches, and that many of these solutions simultaneously offer economic rewards in terms of improving energy efficiency. The Proceedings of the Workshop (Eckert and Horrocks, 2002) were subse-quently circulated to all hotels in Barbados. In a Resolution adopted unanimously, Workshop participants pledged to undertake lighting assessments of their properties and to implement as soon as practicable “turtle friendly” solutions to problem lights. Over the intervening years, several hotels have contacted the BSTP to request assis-tance in addressing lighting issues, and indeed some have already implemented solutions.
This year, again with funding from the Tourism Development Corporation, we are
undertaking an evaluation of the extent to which the recommendations emerging from the 2000 Workshop held in Barbados have been implemented, and an assessment of whether the situation for sea turtle survival on Barbados’ beaches has improved in the last five years. To accomplish this, we have requested assistance from the BSTP in iden-tifying four prestigious hotels on the west and south coasts of Barbados, situated adja-cent to important nesting beaches, that have expressed interest in addressing the con-flicts that they recognise between their lighting and sea turtle survival, and whose leadership in addressing the lighting problem is likely to be emulated by other hotels. In
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response to our request, the BSTP has recommended your hotel, Sandy Lane, be invited to participate in this important study as one of these four case studies.
If our invitation is accepted, we propose to conduct a formal lighting assessment of
each property, including the beaches adjoining your property at Sandy Lane. This will require standardized daytime and nighttime lighting inspections and surveys
to be conducted (cf. Witherington and Martin, 2000). Each hotel will be asked, in ad-vance, to identify a contact (e.g. Chief Engineer, maintenance or security personnel) who can assist in the assessment by identifying the purpose of each light source and the circumstances under which it is used. The inspections will be undertaken by Mr. John English Knowles from Duke University in North Carolina, USA. He has been fully trained to undertake this type of work by Erik Martin of Ecological Associates, Inc., an inspector for lighting compliance in Florida and co-author of the definitive text, “Under-standing, Assessing, & Resolving Light Pollution Problems on Sea Turtle Nesting Beaches” (http://www.nests-certified.org/pdf/LightingTechReport.pdf).
Daytime surveys will identify and document all potential sources of light reaching
the beach. Nighttime inspections will determine the extent to which each light iden-tified during the day, is having a negative effect on nesting habitat. Each inspection will result in a ranking and scoring of light pollution sources, and specific recommenda-tions will be made in a report for each hotel. Hotels will be requested to study and inter-nalize the report, and to implement some recommendations (those that require no or minimal expense to implement) immediately, and others as practicable. Simultaneous to the inspections, documentation of sea turtle disorientation will be undertaken with the assistance of the BSTP, allowing an assessment of problem lights before and after mitigation measures are taken.
A Final Project Report will summarize the findings and provide a suite of tools that we
hope will be useful to any hotel seeking to enhance the survival of sea turtles nesting on their property. Following up on the 2000 Workshop Resolution, the Report will feature a draft Sea Turtle Policy Statement suitable for integration into hotel environmental man-agement systems (EMS), a list of locally available lighting technologies, a protocol for conducting a lighting assessment, sample data sheets, helpful illustrations and photo-graphs, potential energy saving calculations, and a list of contacts to assist hoteliers and others in implementing “turtle friendly” lighting schemes that will launch both your hotel and Barbados as leaders in this field.
The Final Project Report will also act as a baseline for future assessments – enabling
stakeholders in Barbados to track progress in light reduction one year, five years, or ten years into the future – and will provide a model for other Caribbean countries, facing similar coastal management issues, to follow in their efforts to initiate a national dia-logue with the tourism industry on this important topic.
Last, but certainly not least, the project will aid significantly in the survival and sus-
tainability of Barbados’ marine turtles. A sustainable future is clearly a possibility, as evi-denced by the attention already given to this issue in Barbados. WIDECAST – with the support and endorsement of the UN Environment Programme (UNEP-CEP) and the
39
Caribbean Alliance for Sustainable Tourism (CAST) – is proud to be conducting this assessment in collaboration with its affiliate, the BSTP, in Barbados and, fully recognising the leadership role that your property has already shown in seeking solutions that will promote harmony between nesting turtles, hatchlings, and coastal development, we are confident that together we can set an example for other properties to follow.
We sincerely hope that you will take up our invitation to participate, and we re-
spectfully request that you send a response to Prof. Julia Horrocks, Director of the Bar-bados Sea Turtle Project (Tel: 417-4320; Fax 417 4325) as soon as possible. I assure you that the evaluation and assessment will be conducted with science-based protocols that do not intrude on your busy staff, and that the underlying motive is to assist your management team with solutions that will enhance your property in ways that promote the survival or our endangered sea turtles without compromising aesthetics, security, or economic viability.
We look forward to working with you!
Yours very sincerely,
Karen Eckert, Ph.D. Executive Director ______________ Eckert, K. L. and J. A. Horrocks (Editors). 2002. Proceedings of “Sea Turtles and Beachfront Light-ing: An Interactive Workshop for Industry Professionals and Policy-Makers in Barbados”, 13 Octo-ber 2000. Sponsored by the Wider Caribbean Sea Turtle Conservation Network (WIDECAST), the Barbados Sea Turtle Project, and the Tourism Development Corporation of Barbados. WIDECAST Technical Report 1. v + 43 pp. Witherington, B. E. and R. E. Martin. 2000. Understanding, Assessing, and Resolving Light Pollution Problems on Sea Turtle Nesting Beaches. Florida Marine Research Institute Technical Report TR-2 revised edition. Tallahassee, Florida. 73 pp.
40
Appendix III - Original lighting evaluation form Lighting Evaluation Form Facility Name/Address: Light Location: Type of Observation (Circle One): Initial Daytime Initial Nighttime Follow-up Nighttime Date/Time of Observation: Observer(s): General Comments: Light Visible From Beach: YES NO Fixture Type: Photo #: Current Problem Code: 1 2 3 4 5 OFF NOB Comments: Recommended Modifications: Observed Modifications: Additional Modifications Required: YES NO
41
Appendix IV - Modified lighting evaluation form Lighting Evaluation Form
Facility Name/Address: Light Location: Type of Observation (Circle): Daytime Early Nighttime Late Nighttime Follow-up Nighttime Date/Time of Observation: Observer(s): General Comments: Light Visible From Beach: YES NO Fixture Type: Photo #: Rank: 1 2 3 OFF NOB Comments: ____________________________________________________________________ Recommended Modifications: ______________________________________________________________________________ Observed Modifications: ______________________________________________________________________________ Additional Modifications Required: YES NO
42
Appendix V – Fairmont Royal Pavilion property map
Appendix VI – Fairmont Royal Pavilion assessment report
Nat
iona
l Ass
essm
ent o
f Bea
chfro
nt L
ight
ing
and
its
Effe
ct o
n th
e Su
rviv
al o
f End
ange
red
Mar
ine
Turtl
es
in B
arba
dos,
Wes
t Ind
ies
Prop
erty
Ass
essm
ent:
The
Fairm
ont R
oyal
Pav
ilion
Resp
ectfu
lly s
ubm
itted
Jo
hn E
nglis
h Kn
owle
s
INT
RO
DU
CT
ION
In p
artn
ersh
ip w
ith th
e B
arba
dos
Sea
Turtl
e Pr
ojec
t (B
STP)
, lo
cal
affil
iate
of
the
Wid
er C
arib
bean
Sea
Tur
tle C
onse
rvat
ion
Net
wor
k (W
IDEC
AST
), an
d th
e To
uris
m D
evel
opm
ent C
orpo
ratio
n in
Bar
bado
s, a
form
al l
ight
ing
asse
ssm
ent
was
con
duct
ed a
t th
e Fa
irmon
t R
oyal
Pa
vilio
n as
pa
rt of
a
follo
w-u
p in
itiat
ive
to
impl
emen
t re
com
men
datio
ns m
ade
at a
nat
iona
l “S
ea T
urtle
s an
d B
each
fron
t Lig
htin
g” w
orks
hop
held
in 2
000
(Eck
ert a
nd H
orro
cks,
2002
). Th
e ev
alua
tion
of l
ight
ing
asso
ciat
ed w
ith t
he F
airm
ont
Roy
al P
avili
on p
rope
rty a
ttest
s to
the
eff
orts
and
ded
icat
ion
of t
he
hote
l ind
ustry
and
the
BST
P in
impr
ovin
g th
e co
nditi
ons
of a
rtific
ial
beac
h lig
htin
g, w
hich
is
wel
l kn
own
to b
e de
trim
enta
l to
bot
h ha
tchl
ings
and
nes
ting
sea
turtl
es (E
cker
t and
Hor
rock
s, 20
02).
Th
e Fa
irmon
t Roy
al P
avili
on h
as id
entif
ied
itsel
f as
a le
ader
in
add
ress
ing
the
light
ing
prob
lem
by
volu
ntar
ily p
artic
ipat
ing
in th
is
asse
ssm
ent.
The
pro
perty
– a
long
with
fou
r (4
) ot
her
beac
hfro
nt
hote
ls –
was
cho
sen
beca
use
it pl
ays
a cr
ucia
l rol
e in
the
qual
ity o
f se
a tu
rtle
nest
ing
habi
tat.
The
inte
nt o
f th
e lig
htin
g as
sess
men
t was
to
ev
alua
te
curr
ent
cond
ition
s, an
d to
pr
opos
e so
lutio
ns
and
reco
mm
enda
tions
for
eac
h lig
ht i
dent
ified
as
cont
ribut
ing
to t
he
noct
urna
l illu
min
atio
n of
the
nest
ing
beac
h.
The
atte
ntio
n of
suc
h w
ork
is c
ritic
al in
the
surv
ival
of
the
haw
ksbi
ll se
a tu
rtle,
Ere
tmoc
hely
s im
bric
ata,
a c
ritic
ally
end
ange
red
spec
ies
wor
ldw
ide
(cf.
IUC
N R
edLi
st).
Bar
bado
s pl
ays
a ve
ry
impo
rtant
rol
e in
the
sur
viva
l of
thi
s sp
ecie
s, its
sou
thw
est
coas
t ha
ving
bee
n id
entif
ied
as o
ne o
f the
mos
t im
porta
nt n
estin
g gr
ound
s re
mai
ning
in th
e W
ider
Car
ibbe
an R
egio
n.
Arti
ficia
l be
achf
ront
lig
htin
g,
char
acte
rized
as
“l
ight
po
llutio
n” b
y W
ither
ingt
on a
nd M
artin
(20
03,
p. V
), is
the
mos
t se
rious
con
tem
pora
ry th
reat
to th
e su
rviv
al o
f sea
turtl
es in
Bar
bado
s (E
cker
t an
d H
orro
cks,
2002
). M
arin
e tu
rtles
are
mos
t se
nsiti
ve t
o sh
orte
r w
avel
engt
hs (
emitt
ed b
y bl
ue, g
reen
and
whi
te li
ght),
whi
ch
they
use
as
a se
a-fin
ding
cue
. W
hen
such
ligh
ts a
re v
isib
le fr
om th
e be
ach
the
effe
ct o
n se
a tu
rtles
is tr
emen
dous
.
W
ither
ingt
on
and
Mar
tin
(200
3)
sugg
est
the
follo
win
g ap
proa
ch t
o m
itiga
te “
light
pol
lutio
n” b
y ei
ther
elim
inat
ing
the
fixtu
re o
r by
adju
stin
g w
avel
engt
h or
inte
nsity
: W
e ha
ve n
o re
liabl
e fo
rmul
a th
at c
an b
e us
ed t
o ca
lcul
ate
how
muc
h ea
ch li
ght s
ourc
e w
ill a
ffec
t se
a tu
rtles
. W
e do
kn
ow,
how
ever
, th
at i
f sp
ectra
l em
issi
ons
are
equi
vale
nt,
redu
cing
int
ensi
ty w
ill r
educ
e ef
fect
s, an
d if
inte
nsiti
es a
re
sim
ilar,
subs
titut
ing
less
attr
activ
e so
urce
s (li
ke y
ello
w b
ug
or r
ed l
ight
s) w
ill a
lso
redu
ce e
ffec
ts.
A s
ound
stra
tegy
, th
eref
ore,
wou
ld b
e to
red
uce
effe
cts
on s
ea t
urtle
s by
m
anip
ulat
ion
both
int
ensi
ty a
nd c
olor
. A
s fe
w l
ight
s as
pr
actic
able
sh
ould
be
us
ed,
and
for
light
ing
deem
ed
esse
ntia
l, lo
ng w
avel
engt
h lig
ht s
ourc
es s
houl
d re
plac
e m
ore
disr
uptiv
e lig
ht s
ourc
es a
nd i
nten
sity
sho
uld
be r
educ
ed b
y us
ing
lam
ps o
f min
imal
wat
tage
that
are
hou
sed
with
in w
ell-
dire
cted
fix
ture
s ai
med
dow
n an
d aw
ay f
rom
the
bea
ch (
p.
23).
In p
oint
, dire
ct li
ght o
n th
e be
ach
can
be h
ighl
y di
srup
tive
to
both
adu
lt tu
rtles
and
hat
chlin
gs a
nd, e
limin
atin
g so
urce
s of
dire
ct
light
rea
chin
g th
e be
ach
is p
refe
rred
ove
r al
l ot
her
cons
erva
tion
alte
rnat
ives
(W
ither
ingt
on a
nd M
artin
, 20
03).
In
circ
umst
ance
s w
here
elim
inat
ing
light
sou
rces
– e
ither
by
turn
ing
them
off
or
by
rem
ovin
g th
e fix
ture
s al
l to
geth
er
– is
no
t pr
actic
al,
seve
ral
alte
rnat
ives
are
ava
ilabl
e w
hich
dire
ct l
ight
mor
e ef
ficie
ntly
and
/or
shie
ld th
e so
urce
from
the
beac
h.
Sim
ilarly
, in
dire
ct
light
ing
is
also
hi
ghly
di
srup
tive.
W
ither
ingt
on a
nd M
artin
rei
tera
te t
hat,
“lum
inai
res
shou
ld n
ot b
e di
rect
ed o
nto…
any
obje
ct v
isib
le f
rom
the
bea
ch,”
thi
s in
clud
es
wal
ls, c
eilin
gs, a
nd v
eget
atio
n (p
. 21)
. A
form
of i
nten
tiona
l ind
irect
lig
htin
g ca
n be
dec
orat
ive,
suc
h as
glo
win
g be
achf
ront
veg
etat
ion.
Alth
ough
enc
hant
ing
for s
ome,
such
a p
ract
ice
shou
ld b
e re
serv
ed fo
r ar
eas
out o
f si
ght f
rom
the
beac
h.
If in
dire
ct li
ght i
s un
inte
ntio
nal,
then
mod
ern
fixtu
res a
re h
ighl
y re
com
men
ded
that
will
pre
vent
“w
all
was
h” (t
he il
lum
inat
ion
of th
e si
de o
r faç
ade
of a
bui
ldin
g).
So
far
, th
e di
scus
sion
abo
ve h
as b
een
on e
xter
ior
fixtu
res;
ho
wev
er in
terio
r lig
htin
g is
als
o a
sour
ce o
f “lig
ht p
ollu
tion.
”
The
crite
ria f
or i
dent
ifyin
g pr
oble
ms
caus
ed b
y in
door
lig
htin
g ar
e th
e sa
me
as t
hose
for
ide
ntify
ing
prob
lem
s ca
used
by
outd
oor
light
ing…
[A
s w
ith a
n ou
tdoo
r lig
ht, a
n]
indo
or li
ght i
s a p
robl
em if
it is
vis
ible
from
the
beac
h.
Indo
or li
ghtin
g fr
om b
uild
ings
that
are
clo
se to
the
beac
h, a
re
very
tall,
or h
ave
larg
e se
a-si
de w
indo
ws
caus
es th
e gr
eate
st
prob
lem
for
sea
tur
tles.
Bec
ause
ind
oor
light
ing
is u
sual
ly
not
mea
nt t
o lig
ht t
he o
utdo
ors,
the
unw
ante
d ef
fect
s of
in
door
lig
htin
g ca
n ea
sily
be
el
imin
ated
w
ithou
t co
mpr
omis
ing
the
inte
nded
fu
nctio
n of
th
e lig
ht
(With
erin
gton
and
Mar
tin, 2
003,
p. 2
2).
In t
ruth
, th
e Fa
irmon
t R
oyal
Pav
ilion
doe
s no
t ha
ve d
irect
co
ntro
l ov
er w
hich
roo
m l
ight
s ar
e ut
ilize
d by
gue
sts.
How
ever
, in
door
ligh
ts b
e ca
n m
inim
ized
fro
m r
each
ing
the
beac
h by
sim
ply
info
rmin
g an
d re
min
ding
gue
sts
to c
lose
opa
que
curta
ins
durin
g ev
enin
g ho
urs w
hen
room
ligh
ts a
re o
n.
The
hote
l do
es h
ave
dire
ct c
ontro
l ov
er a
lmos
t al
l ot
her
fixtu
res,
whi
ch c
ast l
ight
ont
o or
vis
ible
fro
m th
e be
ach.
It
is th
ese
fixtu
res t
hat m
ake
up th
e bu
lk o
f thi
s ass
essm
ent.
In
th
e se
ctio
ns
that
fo
llow
I
prov
ide
spec
ific
reco
mm
enda
tions
for
miti
gatio
n of
the
se f
ixtu
res,
and
deta
il m
y m
etho
ds a
nd r
esul
ts.
If
cons
train
ts h
inde
r th
e im
plem
enta
tion
of
parti
cula
r re
com
men
datio
ns,
one
optio
n is
tha
t ef
fect
ive
actio
n be
ta
ken
in h
igh
prio
rity
case
s (R
ank
“3”
light
s, se
e M
ETH
OD
S) a
nd
that
low
er p
riorit
y ac
tions
be
budg
eted
ove
r tim
e.
In g
ener
al, a
nd in
keep
ing
with
the
deci
sion
s of
the
2000
“Se
a Tu
rtles
and
Bea
chfr
ont
Ligh
ting”
wor
ksho
p, r
ecom
men
datio
ns a
re b
ased
on
best
pra
ctic
es
and
curr
ent
scie
nce
as a
rticu
late
d by
With
erin
gton
and
Mar
tin
(200
3).
ME
TH
OD
S D
aytim
e Li
ghtin
g Su
rvey
A b
asel
ine
dayt
ime
light
ing
surv
ey w
as c
ondu
cted
on
foot
on
3 Ju
ne 2
006
by o
bser
ving
ligh
ting
fixtu
res
and
bulb
s di
rect
ly v
isib
le
from
the
beac
h. T
he e
ntire
pro
perty
was
acc
esse
d to
cla
rify,
iden
tify,
an
d/or
cou
nt p
artic
ular
fix
ture
(s).
All
exte
rior
light
s w
ithin
line
-of-
sigh
t of
the
obs
erve
r [J
ohn
Engl
ish
Kno
wle
s] w
ere
desc
ribed
with
re
spec
t to
fix
ture
typ
e an
d lo
catio
n.
The
func
tion
of l
ight
s w
as
dedu
ced
by th
e ob
serv
er;
how
ever
, sub
sequ
ent
mee
tings
with
hot
el
man
agem
ent
staf
f in
sure
d th
at
the
corr
ect
func
tiona
lity
was
do
cum
ente
d in
eac
h ca
se.
Lig
ht f
ixtu
res
with
lam
ps (
light
bul
bs)
visi
ble
from
the
beac
h an
d th
ose
that
wer
e de
sign
ed o
r pos
ition
ed s
o th
at t
hey
wou
ld l
ikel
y ill
umin
ate
the
beac
h w
ere
cons
ider
ed t
o be
po
tent
ially
pro
blem
atic
.
Nig
httim
e Li
ghtin
g Su
rvey
In c
oord
inat
ion
with
hot
el m
anag
emen
t, a
nigh
ttim
e lig
htin
g su
rvey
was
con
duct
ed o
n fo
ot o
n 23
July
200
6. D
urin
g th
e ni
ghtti
me
surv
ey, e
ach
light
iden
tifie
d in
the
dayt
ime
surv
ey w
as lo
cate
d an
d ev
alua
ted
with
res
pect
to
its p
oten
tial
effe
ct o
n se
a tu
rtles
. Li
ghts
un
seen
dur
ing
the
day,
but
vis
ible
whe
n em
ittin
g lig
ht,
wer
e al
so
eval
uate
d. E
ach
light
was
rate
d an
d ra
nked
on
a sc
ale
of 1
to 3
.
The
Ligh
ts
Fo
llow
ing
are
the
surv
eyed
lig
hts
liste
d fr
om t
he m
ost
disr
uptiv
e (R
ank
3) t
o th
e le
ast
disr
uptiv
e (R
ank
1) f
or m
arin
e tu
rtles
. A
rank
of “
1” d
escr
ibes
indi
rect
ligh
t vis
ible
by
an o
bser
ver
on th
e be
ach,
but
not
like
ly to
pre
sent
a st
rong
attr
actio
n to
nes
ting
or
hatc
hing
tur
tles.
A r
ank
of “
2” d
escr
ibes
a v
isib
le g
lobe
, glo
win
g el
emen
t, la
mp,
or
refle
ctor
like
ly to
dis
orie
nt tu
rtles
, but
not
stro
ng
enou
gh to
cas
t a sh
adow
on
the
beac
h. A
nd a
rank
of “
3” d
escr
ibes
a
light
sou
rce
stro
ng e
noug
h to
cas
t a s
hado
w o
n th
e be
ach
rega
rdle
ss
of w
heth
er th
e ill
umin
atio
n is
dire
ct o
r ind
irect
.
Even
the
sm
alle
st l
ight
s ca
n ra
nk a
s a
“3”
if th
ey c
ast
a sh
adow
on
the
beac
h; t
heir
clos
e pr
oxim
ity t
o th
e be
ach
and
thei
r lo
w v
ertic
al p
lace
men
t nea
r the
hor
izon
can
be
just
as
diso
rient
atin
g as
a m
ore
pow
erfu
l lig
ht fu
rther
aw
ay.
The
“3”
rank
ing
light
s ha
ve
been
pla
ced
first
in th
e as
sess
men
t bec
ause
of t
heir
pote
ntia
lly m
ore
serio
us e
ffec
ts o
n m
arin
e tu
rtles
. T
he f
ocus
of
corr
ectiv
e ac
tions
sh
ould
beg
in w
ith th
ese
light
s, as
thei
r miti
gatio
n w
ill h
ave
the
mos
t si
gnifi
cant
impa
ct o
n th
e be
ach
envi
ronm
ent.
W
ithin
eac
h ra
nk –
1, 2
, 3 –
fixt
ures
list
ed fi
rst a
re e
xpec
ted
to r
equi
re t
he g
reat
est
atte
ntio
n ei
ther
in
num
ber,
expe
nse,
or
crea
tivity
. Th
e lis
t con
tinue
s th
roug
h fix
ture
s th
at a
re p
rogr
essi
vely
si
mpl
er a
nd/o
r ch
eape
r to
miti
gate
. F
or e
ach
light
the
num
ber
of
fixtu
res
visi
ble
from
the
bea
ch,
the
fixtu
re t
ype,
loc
atio
n, r
ank,
co
mm
ents
(if
an
y),
func
tion,
pic
ture
an
d re
com
men
datio
ns
are
docu
men
ted.
Eac
h re
com
men
datio
n is
spec
ific
to a
n in
divi
dual
ligh
t, an
d m
ay
incl
ude
one
or
man
y ex
plan
ator
y re
mar
ks.
So
me
reco
mm
enda
tions
will
per
tain
to m
itiga
ting
the
curr
ent f
ixtu
re; o
ther
s w
ill su
gges
t the
repl
acem
ent o
f a fi
xtur
e w
ith a
n al
tern
ativ
e.
Rec
omm
enda
tions
are
illu
stra
ted
by th
e fo
llow
ing:
Pe
rman
ently
elim
inat
e fix
ture
. So
me
case
s are
spec
ific
to th
e nu
mbe
r or l
ocat
ion
of th
e fix
ture
s.
Rep
ositi
on fi
xtur
e to
the
land
war
d si
de o
f the
tree
or o
bjec
t. A
im fi
xtur
e aw
ay fr
om th
e be
ach.
Rep
lace
exi
stin
g fix
ture
with
a m
ore
dire
cted
and
fun
ctio
nal
path
lig
ht,
and
re-p
ositi
on
it to
el
imin
ate
any
dire
ct
(or
indi
rect
) ill
umin
atio
n of
the
beac
h.
In
stal
l low
wat
tage
(40
wat
ts o
r les
s) y
ello
w b
ug li
ght b
ulb.
In
stal
l com
pact
flu
ores
cent
Tur
tle S
afe
Ligh
ting
lam
ps (
light
bul
bs).
Se
e IN
TE
RN
ET
RE
SOU
RC
ES.
OR
Rep
lace
exi
stin
g fix
ture
with
a m
ore
dire
cted
, m
ore
func
tiona
l do
wnl
ight
.
R
epla
ce e
xist
ing
fixtu
re w
ith a
mor
e di
rect
ed, m
ore
func
tiona
l ste
p lig
ht p
ositi
oned
to e
limin
ate
any
dire
ct (
or in
dire
ct)
illum
inat
ion
of
the
beac
h.
R
educ
e in
tens
ity o
f lig
ht o
r low
er w
atta
ge.
Plan
t, la
ndsc
ape,
or i
mpr
ove
nativ
e ve
geta
tion
buff
er to
elim
inat
e or
sc
reen
any
dire
ct (o
r ind
irect
) illu
min
atio
n of
the
beac
h.
Inst
all h
ood,
aim
aw
ay f
rom
bea
ch, a
nd c
onne
ct f
ixtu
re to
a m
otio
n de
tect
or.
K
eep
light
s of
f w
hen
not
in u
se,
espe
cial
ly l
ight
s cl
oses
t to
the
be
ach.
In
form
gu
ests
vi
a ta
ble
tent
s, do
or
hang
ers,
or
othe
r ed
ucat
iona
l mat
eria
ls a
bout
fixt
ures
und
er th
eir c
ontro
l.
In
stal
l shi
eld
or m
ask
of su
ffic
ient
size
that
cov
ers a
n ar
ch o
f 180
° on
the
ocea
n si
de.
Sh
ade
arch
es.
Inst
all a
Hub
bell
Skyc
ap o
r sim
ilar s
hiel
d.
Fo
r sec
urity
, ins
tall
a m
otio
n de
tect
or so
it o
nly
com
es o
n w
hen
som
ebod
y is
on
the
beac
h (m
otio
n de
tect
ors c
an b
e de
sign
ed to
be
enga
ged
or d
isen
gage
d).
El
imin
ate
fixtu
res a
nd u
se lo
w ta
ble
lam
ps (s
uch
as A
urel
le L
ED
Can
dle
Serie
s or M
axxi
ma
MLC
-01
LED
Fla
mel
ess C
andl
e) o
r ca
ndle
s. Th
is w
ould
serv
e th
e pu
rpos
e of
illu
min
atin
g th
e ta
bles
w
ithou
t uni
nten
ded
broa
dcas
t bey
ond
the
rest
aura
nt.
C
ocon
ut p
alm
mou
nted
hoo
ded
spot
light
Rank
: 3
Ligh
t Lo
catio
n: C
ocon
ut p
alm
at
Wat
er S
ports
Cen
tre a
t so
uthe
rn
end
of p
rope
rty
Num
ber o
f fix
ture
s: 2
C
omm
ents
: Cur
rent
ly, t
he li
ght i
s di
rect
ed to
war
d th
e bo
at ra
mp
and
step
s. A
bet
ter
alte
rnat
ive
in i
llum
inat
ing
the
step
s w
ould
be
to
inst
all s
mal
l red
foot
/ste
p lig
hts.
Thes
e lig
hts
shou
ld b
e co
nnec
ted
to
a m
otio
n de
tect
or s
o th
ey o
nly
com
e on
whe
n ne
eded
. If
ligh
ts a
re
need
ed f
or s
ecur
ity, t
hen
low
-pro
file,
louv
ered
bol
lard
s w
ith b
each
-si
de s
hiel
ds c
ould
be
used
. To
min
imiz
e th
e ef
fect
s of
thes
e lig
hts
on
sea
turtl
es, t
hey
shou
ld b
e co
nnec
ted
to a
mot
ion
dete
ctor
and
eith
er
low
-pre
ssur
e so
dium
vap
or la
mps
or
yello
w b
ug li
ght b
ulbs
sho
uld
be u
sed.
Re
com
men
datio
ns:
Pi
ctur
e 1
of b
are
spot
light
Pi
ctur
e 2
of b
are
spot
light
Rank
: 3
Ligh
t Loc
atio
n: R
oof W
ater
Spo
rts C
entre
N
umbe
r of f
ixtu
res:
2
Reco
mm
enda
tions
:
Fl
oodl
ight
Rank
: 3
Ligh
t Loc
atio
n: N
orth
bea
ch b
y ve
nder
stal
ls
Num
ber o
f fix
ture
s: 1
Re
com
men
datio
ns:
L
arge
r sp
otlig
hts f
or st
age
Sm
alle
r co
conu
t pal
m m
ount
ed sp
otlig
ht
Sm
alle
r sp
otlig
ht
Rank
: 3
Ligh
t Loc
atio
n: P
alm
Ter
race
Res
taur
ant
Num
ber
of f
ixtu
res:
21
smal
ler
spot
light
s, 4
larg
er s
potli
ghts
for
st
age
of w
hich
2 a
re o
rang
e an
d 2
are
whi
te
Com
men
ts:
The
rest
aura
nt p
rese
nts
a un
ique
cha
lleng
e be
caus
e it
is
dire
ctly
on
the
beac
h.
Usi
ng w
all-m
ount
ed d
ownl
ight
s, st
ep li
ghts
, an
d/or
oth
er d
irect
iona
l fix
ture
s in
com
bina
tion
with
low
-leve
l sm
all
tabl
e lig
hts
can
min
imiz
e th
e am
ount
of
light
leav
ing
the
rest
aura
nt.
The
dow
nlig
hts
shou
ld b
e m
ount
ed lo
w e
noug
h so
that
they
do
not
illum
inat
e th
e be
ach.
V
eget
atio
n ca
n al
so b
e pl
ante
d in
side
the
ar
ches
in s
uch
a w
ay a
s to
lim
it th
e am
ount
of l
ight
pas
sing
thro
ugh
them
, bu
t no
t ob
stru
ctin
g th
e vi
ew o
f se
ated
gue
sts.
In
addi
tion,
so
me
fixtu
res
do c
ontri
bute
to “
wal
l was
h.”
It s
houl
d be
not
ed th
at
“wal
l was
h” f
rom
a y
ello
w o
r re
d lig
ht is
muc
h le
ss d
isru
ptiv
e th
an
“wal
l was
h” f
rom
a w
hite
ligh
t. T
here
fore
, to
furth
er m
inim
ize
the
detri
men
tal
effe
cts
to s
ea t
urtle
s, ye
llow
bug
lig
ht b
ulbs
or
Turtl
e Fr
iend
ly
Ligh
ting
lam
ps
may
be
us
ed.
B
y fo
llow
ing
thes
e re
com
men
datio
ns n
eith
er t
he d
inin
g ex
perie
nce
of R
oyal
Pav
ilion
gu
ests
no
r th
e be
havi
or
of
sea
turtl
e ha
tchl
ings
sh
ould
be
co
mpr
omis
ed.
Re
com
men
datio
ns o
n ex
istin
g fix
ture
s:
Ulti
mat
e re
com
men
datio
n:
Sugg
este
d la
ndsc
apin
g of
arc
hes:
W
all m
ount
ed c
andl
e ho
lder
fixt
ure
Rank
: 3
Ligh
t Loc
atio
n: C
afe
Tabo
ras
Num
ber o
f fix
ture
s: 6
C
omm
ents
: C
afé
Tabo
ras
pres
ents
a u
niqu
e ca
se t
hat
can
be e
asily
m
itiga
ted.
The
cur
rent
ligh
ts a
re a
sou
rce
of d
irect
ligh
t on
the
beac
h an
d th
eir
repl
acem
ent
with
a
mod
ern
alte
rnat
ive
is
high
ly
reco
mm
ende
d. A
fixt
ure
that
shie
lds t
he li
ght b
ulb
from
the
beac
h as
w
ell a
s cu
stom
ers
is p
refe
rred
ove
r the
exi
stin
g ba
re b
ulb
light
s. T
he
curr
ent f
ixtu
re c
ould
be
mad
e tu
rtle
frie
ndly
by
repl
acin
g th
e gl
ass
chim
neys
with
an
opaq
ue o
ne,
conc
ealin
g th
e bu
lb.
Ear
thw
orks
co
uld
poss
ibly
des
ign
such
a fi
xtur
e th
ereb
y in
crea
sing
the
qual
ity o
f th
e be
ach,
the
rest
aura
nt, a
nd su
ppor
ting
the
loca
l eco
nom
y.
Reco
mm
enda
tions
on
exis
ting
fixtu
res:
U
ltim
ate
reco
mm
enda
tion:
W
all m
ount
ed sh
ell s
hape
d sc
once
on
balc
ony
Pe
riod
ligh
t on
balc
ony
Rank
: 3 –
per
iod
light
, 3 -
shel
l sco
nce
light
oor
Bal
coni
es o
f N
orth
nsta
llatio
n of
tur
tle f
riend
ly f
ixtu
res,
the
Ligh
t Lo
catio
n: F
irst,
Seco
nd, a
nd T
hird
Fl
and
Sout
h bu
ildin
gs
Num
ber o
f fix
ture
s: 1
38
Com
men
ts:
Unt
il th
e i
detri
men
tal e
ffec
ts o
f the
ligh
t can
be
redu
ced
by s
hiel
ding
or t
intin
g of
gla
ss o
n th
e cu
rren
t fix
ture
s. H
owev
er,
this
pro
babl
y w
ill n
ot
com
plet
ely
elim
inat
e di
rect
illu
min
atio
n of
the
beac
h.
Bec
ause
the
shel
l sco
nce
shie
lds
the
bare
bul
b fr
om th
e be
ach,
it is
pre
ferr
ed to
th
e pe
riod
light
. H
owev
er,
cons
ider
able
lig
ht f
rom
the
sco
nce
is
refle
cted
off
the
balc
ony
wal
l tow
ards
the
beac
h. It
is re
com
men
ded
that
the
curr
ent b
ulb
be re
plac
ed w
ith a
low
-wat
tage
yel
low
bug
ligh
t bu
lb o
r Tur
tle S
afe
Ligh
ting
lam
p. S
mal
l por
tabl
e bo
ok li
ghts
can
be
plac
ed in
eve
ry ro
om fo
r gue
sts t
hat p
refe
r to
read
on
the
balc
onie
s at
nigh
t.
Reco
mm
enda
tions
on
the
exis
ting
fixtu
res,
espe
cial
ly t
he p
erio
d lig
ht:
Ulti
mat
e re
com
men
datio
n:
T
urtle
fri
endl
y do
wn
light
whe
n us
ed w
ith b
ug l
ight
(pi
ctur
e fr
om
http
://w
ww
.thom
aslig
htin
g.co
m/c
atal
og/p
rodd
etai
l.asp
?cno
=SL
9270
-8)
Pi
ctur
e 1
of sm
all s
potli
ghts
Pi
ctur
e 2
of sm
all s
potli
ghts
Rank
: 3
Ligh
t Loc
atio
n: C
afe
Tabo
ras
Num
ber o
f fix
ture
s: 1
3 Re
com
men
datio
ns:
C
ocon
ut p
alm
mou
nted
hoo
ded
spot
light
N
orth
Bea
ch il
lum
inat
ed a
t nig
ht
Rank
: 3
Ligh
t Loc
atio
n: N
orth
bea
ch
Num
ber o
f fix
ture
s: 1
0 C
omm
ents
: T
he b
est
optio
n is
to
elim
inat
e th
e lig
ht,
eith
er b
y tu
rnin
g th
em a
ll of
f or
rem
ovin
g th
e fix
ture
s. I
f th
e pu
rpos
e of
the
light
is
to i
llum
inat
e di
ning
or
ente
rtain
men
t ev
ents
, th
en h
avin
g th
em o
n fo
r sh
ort d
urat
ions
on
rand
om n
ight
s is
bet
ter
than
hav
ing
them
on
all t
he ti
me.
If t
he li
ghts
are
not
nee
ded
for a
n ev
ent,
then
it
is r
ecom
men
ded
that
the
y ar
e tu
rned
off
. I
f al
l lig
hts
cann
ot b
e re
mov
ed o
r tu
rned
off
, the
n it
is r
ecom
men
ded
that
the
num
ber
of
light
s (c
urre
ntly
10)
and
wat
tage
of
each
lam
p be
red
uced
. T
he
inst
alla
tion
of y
ello
w b
ug l
ight
bul
bs i
s al
so r
ecom
men
ded
and
a Tu
rtle
frie
ndly
C
F PA
R-3
8 sn
ap-o
n fil
ter
is
avai
labl
e (S
ee
INT
ER
NE
T R
ESO
UR
CE
S).
Reco
mm
enda
tions
on
the
num
ber o
f fix
ture
s:
Reco
mm
enda
tions
on
exis
ting
or re
mai
ning
fixt
ures
:
C
ompa
ct F
luor
esce
nt P
AR
-38
(pic
ture
from
ht
tp://
ww
w.b
ulbc
o.co
m/c
fpar
38.h
tml)
Sn
ap-o
n re
d fil
ter
to b
e us
ed w
ith C
F PA
R-3
8 (p
ictu
re fr
om
http
://w
ww
.turt
lesa
felig
htin
g.co
m/T
urtle
Safe
%20
1.0/
mai
nfra
me.
htm
l)
Y
ello
w P
AR
-38
Bug
Lam
p (p
ictu
re fr
om
http
://w
ww
.doi
tyou
rsel
f.com
/invt
/106
3239
)
D
usk-
to-d
awn
secu
rity
ligh
t
Rank
: 3
Ligh
t Loc
atio
n: N
orth
bea
ch
Num
ber o
f fix
ture
s: 1
C
omm
ents
: Th
e be
st r
ecom
men
datio
n an
d pr
efer
red
optio
n is
to
elim
inat
e th
e lig
ht.
If th
e pu
rpos
e of
the
light
is to
illu
min
ate
dini
ng
or e
nter
tain
men
t, th
en it
sho
uld
be s
hiel
ded
and
turn
ed o
ff w
hen
not
need
ed.
If th
e pu
rpos
e of
the
light
is to
illu
min
ate
the
beac
h so
that
se
curit
y ca
n vi
ew p
oten
tial
tresp
asse
rs,
then
a m
ore
effe
ctiv
e an
d ec
onom
ical
mea
ns m
ight
be
to i
nsta
ll a
mot
ion
dete
ctor
so
that
se
curit
y is
ale
rted
whe
n so
meo
ne a
ppro
ache
s th
e ho
tel.
Sec
urity
pe
rson
nel
can
alw
ays
use
flash
light
s to
illu
min
ate
any
sect
ion
of
beac
h w
hen
they
pre
fer.
Re
com
men
datio
ns o
n ex
istin
g fix
ture
:
U
ltim
ate
reco
mm
enda
tion:
U
p di
rect
ed h
oode
d sp
otlig
ht a
t the
bas
e of
the
coco
nut p
alm
C
ocon
ut p
alm
mou
nted
hoo
ded
spot
light
whi
ch is
dow
n di
rect
ed
Rank
: 3
Ligh
t Lo
catio
n: T
wo
spot
light
s at
bas
e of
coc
onut
pal
m a
imed
up,
on
e sp
otlig
ht m
ount
ed in
coc
onut
pal
m a
imed
dow
n at
bea
ch w
ithin
“g
arde
n ar
ea”
in fr
ont o
f Pal
m T
erra
ce R
esta
uran
t N
umbe
r of f
ixtu
res:
3
Com
men
ts:
The
dow
n po
sitio
ned
coco
nut
palm
mou
nted
lig
ht i
s ca
stin
g a
grea
t de
al o
f di
rect
lig
ht o
n th
e be
ach
and
of t
he t
hree
sp
otlig
hts w
ould
be
the
mos
t dis
rupt
ive
to th
e se
a fin
ding
beh
avio
r of
hatc
hlin
gs.
The
best
rec
omm
enda
tion
is it
s el
imin
atio
n.
The
othe
r tw
o sp
otlig
hts
at t
he b
ase
of t
he c
ocon
ut p
alm
sho
uld
also
be
elim
inat
ed.
Re
com
men
datio
ns:
C
ocon
ut p
alm
mou
nted
hoo
ded
spot
light
M
ahog
any
tree
mou
nted
hoo
ded
spot
light
Rank
: 3
Ligh
t Loc
atio
n: M
ount
ed o
n on
e co
conu
t pal
m, t
he o
ther
is m
ount
ed
on th
e m
ahog
any
betw
een
Caf
e Ta
bora
s and
sout
h bu
ildin
g N
umbe
r of f
ixtu
res:
2
Com
men
ts: A
com
mon
reco
mm
enda
tion
to c
orre
ct li
ghtin
g pr
oble
ms
is lo
wer
ligh
t bel
ow a
poi
nt th
at is
not
vis
ible
from
the
beac
h. I
n th
is
situ
atio
n, th
e pu
rpos
e of
the
light
s is
to il
lum
inat
e th
e te
rrac
e/pa
tio o
f C
afé
Tabo
ras.
Thi
s ca
n be
don
e w
ithou
t hig
h m
ount
ed tr
ee fi
xtur
es,
whi
ch i
ncre
ase
stra
y lig
ht r
each
ing
the
beac
h.
A m
ore
pref
erre
d al
tern
ativ
e is
to lo
wer
ligh
ts a
nd p
lace
them
beh
ind
an o
paqu
e ob
ject
. Th
is c
an b
e ac
com
plis
hed
here
by
plac
ing
light
s on
the
land
war
d si
de
of w
all.
Lan
dsca
ped
vege
tatio
n ca
n al
so b
e ad
vant
ageo
us i
n en
surin
g th
at l
ittle
lig
ht a
s po
ssib
le r
each
es t
he b
each
. L
ower
ing
light
s be
hind
opa
que
obje
cts
and
vege
tatio
n in
crea
ses
the
qual
ity o
f th
e en
viro
nmen
t fo
r bo
th t
he h
atch
lings
on
the
beac
h an
d di
nnin
g gu
ests
on
the
terr
ace.
Thi
s way
the
purp
ose
of th
e lig
hts h
as n
ot b
een
com
prom
ised
.
Reco
mm
enda
tions
:
C
ocon
ut p
alm
mou
nted
hoo
ded
spot
light
clo
sest
to b
each
C
ocon
ut p
alm
mou
nted
hoo
ded
spot
light
furt
hest
from
bea
ch
Rank
: Off
at t
he ti
me
of a
sses
smen
t – F
ixtu
re c
lose
st to
bea
ch, 2
- Fi
xtur
e se
t fur
ther
bac
k Li
ght L
ocat
ion:
Coc
onut
pal
ms j
ust s
outh
of n
orth
bui
ldin
g N
umbe
r: 2
C
omm
ents
: O
f the
two
light
s, th
e on
e th
at w
ould
be
mos
t dis
rupt
ive
to t
he s
ea f
indi
ng b
ehav
ior
of h
atch
lings
is
the
one
clos
est
to t
he
beac
h. E
limin
atin
g th
e lig
ht c
lose
st to
the
sea
or k
eepi
ng it
off
is th
e be
st r
ecom
men
datio
n.
The
othe
r lig
ht s
houl
d be
red
irect
ed a
nd
repo
sitio
ned
away
from
the
beac
h.
Reco
mm
enda
tions
:
SUM
MA
RY
The
effo
rt of
the
Fai
rmon
t R
oyal
Pav
ilion
doe
s no
t go
un
notic
ed in
thei
r ne
ver
endi
ng q
uest
for
impr
ovem
ents
. Th
e ho
tel
cons
tant
ly s
trive
s fo
r a m
ore
suita
ble
beac
h en
viro
nmen
t, w
hich
onl
y in
crea
ses
its q
ualit
y as
a lu
xury
reso
rt. T
he F
airm
ont R
oyal
Pav
ilion
is
pra
ised
for s
uppo
rting
um
brel
las
with
a fl
at b
ase
inst
ead
of s
piki
ng
the
post
dire
ctly
into
the
sand
. Th
is a
nd th
e co
ntin
ued
effo
rt to
sta
ck
beac
h ch
airs
will
ens
ure
that
nes
ts a
re n
ot d
amag
ed a
nd m
othe
r tu
rtles
are
not
obs
truct
ed f
rom
cra
wlin
g al
ong
the
beac
h. A
noth
er
obvi
ous
cons
ider
atio
n in
se
asid
e am
bien
ce
is
the
hood
ing
of
beac
hfro
nt s
potli
ghts
. Su
ch a
fix
ture
will
red
uce
glar
e an
d im
prov
e th
e ni
ght s
ky fo
r gue
sts.
How
ever
, the
impa
ct o
f alm
ost a
ll ev
alua
ted
light
s, in
clud
ing
the
spot
light
s, is
com
poun
ded
for
two
reas
ons.
Firs
t, th
e Fa
irmon
t R
oyal
Pav
ilion
bea
ch s
ide
prop
erty
is
elon
gate
d.
Seco
nd,
this
el
onga
ted
edge
of t
he p
rope
rty is
dire
ctly
on
top
of th
e co
astli
ne w
ith
little
or n
o se
t bac
k. I
n th
is p
artic
ular
situ
atio
n ev
en a
sm
all b
ulb
is
prob
lem
atic
and
is
why
nea
rly a
ll fix
ture
s ar
e ca
tego
rized
as
mos
t di
srup
tive
to m
arin
e tu
rtles
(Ran
k 3)
. Ev
en w
ith a
hoo
d, a
spot
light
dire
ctly
on
the
beac
h ca
n ca
use
an e
gg-b
earin
g fe
mal
e to
tur
n aw
ay f
rom
sui
tabl
e ne
stin
g ha
bita
t.
This
mig
ht re
sult
in th
e tu
rtle
layi
ng h
er c
lutc
h in
a s
ub o
ptim
al a
rea
som
ewhe
re e
lse
dow
n th
e be
ach.
In
add
ition
, a
beac
h ce
nter
ed s
potli
ght
can
caus
e ex
trem
e di
sorie
ntat
ion
to h
atch
lings
, pre
vent
ing
them
fro
m e
ver
reac
hing
the
sea.
In
man
y ca
ses,
mis
dire
cted
hat
chlin
gs a
re e
aten
by
crab
s or
die
fr
om h
eat e
xpos
ure
the
follo
win
g m
orni
ng.
The
cum
ulat
ive
effe
ct o
f m
ultip
le b
alco
ny l
ight
s ha
s an
ev
en g
reat
er im
pact
on
mar
ine
turtl
es.
It is
hig
hly
reco
mm
ende
d th
at
a m
oder
n al
tern
ativ
e is
inst
alle
d on
bea
ch fr
ont b
alco
nies
. B
ut e
ven
with
turtl
e-fr
iend
ly f
ixtu
res,
balc
ony
light
s sh
ould
be
kept
off
whe
n no
t in
use.
The
two
rest
aura
nts
also
pos
e a
chal
leng
e in
red
ucin
g lig
ht
pollu
tion,
sin
ce th
ey to
o si
t dire
ctly
on
the
beac
h. T
he s
olut
ion
mus
t m
eet
the
need
s of
din
ing
gues
ts a
nd m
arin
e tu
rtles
, si
nce
the
rest
aura
nt’s
op
erat
ion
over
laps
w
ith
the
emer
genc
e of
m
ost
hatc
hlin
gs.
Th
e ci
rcum
stan
ces
pres
ent
at t
he r
esta
uran
t w
ill r
equi
re
crea
tivity
and
a c
lear
und
erst
andi
ng o
f lig
ht p
ollu
tion
miti
gatio
n th
at
this
ass
essm
ent
hope
s to
cul
tivat
e.
One
rec
omm
enda
tion
is t
o in
corp
orat
e la
ndsc
apin
g or
veg
etat
ion
into
a t
urtle
frie
ndly
lig
htin
g sc
hem
e.
In t
his
case
, it
wou
ld b
e im
porta
nt t
o en
sure
tha
t th
e ve
geta
tion
is n
ot il
lum
inat
ed in
suc
h a
way
that
is v
isib
le f
rom
the
beac
h.
The
reco
mm
enda
tions
, on
ce i
mpl
emen
ted,
will
not
onl
y im
prov
e be
ach
cond
ition
s fo
r m
arin
e tu
rtles
, but
will
con
tribu
te t
o th
e ex
istin
g so
phis
ticat
ed t
hem
e in
lig
htin
g am
bian
ce o
f th
is r
esor
t w
hile
redu
cing
ope
ratio
nal e
xpen
ses
thro
ugh
an e
xpec
tatio
n of
low
er
ener
gy u
se.
To
enco
urag
e lig
htin
g im
prov
emen
ts a
nd a
ssis
t in
im
plem
enta
tion,
the
Tour
ism
Dev
elop
men
t Cor
pora
tion
is a
vaila
ble
to p
urch
ase
item
s (fix
ture
s, C
F bu
g lig
hts)
in b
ulk,
whi
ch w
ill fu
rther
re
duce
the
cost
of r
etro
fittin
g an
d in
nova
tion.
Th
e Fa
irmon
t R
oyal
Pav
ilion
pla
ys a
n es
sent
ial
role
in
the
surv
ival
of
the
enda
nger
ed t
urtle
s th
at u
se i
ts b
each
es, a
nd i
s w
ell
posi
tione
d to
ser
ve a
s a
mod
el f
or s
ea tu
rtle
frie
ndly
env
ironm
enta
l m
anag
emen
t sys
tem
s els
ewhe
re in
Bar
bado
s and
bey
ond.
INT
ER
NE
T R
ESO
UR
CE
S
Turtl
e sa
fe li
ghtin
g pr
oduc
ts
ww
w.tu
rtles
afel
ight
ing.
com
ht
tp://
ww
w.tu
rtles
afel
ight
ing.
com
/Tur
tleSa
fe%
201.
0/pr
oduc
t%20
she
ets/
Snap
OnF
ilter
Turtl
e fr
iend
ly fi
xtur
e ht
tp://
ww
w.th
omas
light
ing.
com
/cat
alog
/pro
ddet
ail.a
sp?c
no=S
L927
0-8 C
F PA
R 3
8 ht
tp://
ww
w.p
rism
aeca
t.lig
htin
g.ph
ilips
.com
/Lig
htSi
te/W
hirlw
ind.
asp
x?ec
a=LN
PPLA
&cp
f=U
SNPU
S&st
g=A
CT&
lan=
US+
&ec
u=LM
P%7c
PLC
%7c
NP&
cnt_
key=
CI_
PAR
38%
7cPL
C&
t=1&
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r_m
d=1
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nav_
key=
1885
&na
v=N
ull&
loc=
us_e
n&le
ftnav
=1_1
_4_1
_4
http
://ge
net.g
elig
htin
g.co
m/L
ight
Prod
ucts
/Dis
patc
her?
REQ
UES
T=C
ON
SUM
ERSP
ECPA
GE&
PRO
DU
CTC
OD
E=21
739
http
://w
ww
.nam
.ligh
ting.
phili
ps.c
om/u
s/co
nsum
er/m
arat
hon/
disp
lay.
php?
mod
e=2
PAR
38
bug
light
ht
tp://
gene
t.gel
ight
ing.
com
/Lig
htPr
oduc
ts/D
ispa
tche
r?R
EQU
EST=
CO
NSU
MER
SPEC
PAG
E&PR
OD
UC
TCO
DE=
2094
5 L
ITE
RA
TU
RE
CIT
ED
WIT
HER
ING
TON
, B. E
. and
R. E
. MA
RTI
N. 2
003.
Und
erst
andi
ng,
asse
ssin
g,
and
reso
lvin
g lig
ht-p
ollu
tion
prob
lem
s on
se
a tu
rtle
nest
ing
beac
hes.
3rd
ed.
rev.
Flo
rida
Mar
ine
Res
earc
h In
stitu
te
Tech
nica
l Rep
ort T
R-2
. 73
p.
ECK
ERT,
K. L
. and
J. A
. HO
RR
OC
KS
(Edi
tors
). 20
02. P
roce
edin
gs
of “
Sea
Turtl
es a
nd B
each
fron
t Lig
htin
g: A
n In
tera
ctiv
e W
orks
hop
for
Indu
stry
Pro
fess
iona
ls a
nd P
olic
y-M
aker
s in
Bar
bado
s”,
13
Oct
ober
20
00.
Spon
sore
d by
th
e W
ider
C
arib
bean
Se
a Tu
rtle
Con
serv
atio
n N
etw
ork
(WID
ECA
ST),
the
Bar
bado
s Se
a Tu
rtle
Proj
ect,
and
the
Tour
ism
Dev
elop
men
t C
orpo
ratio
n of
Bar
bado
s. W
IDEC
AST
Tec
hnic
al R
epor
t 1. v
+ 4
3 pp
. A
CK
NO
WL
ED
GM
EN
TS
I
am d
eepl
y in
debt
ed t
o th
e st
aff
and
man
agem
ent
of t
he
Fairm
ont
Roy
al
Pavi
lion,
in
clud
ing
Nic
hola
s Em
ery,
G
ener
al
Man
ager
and
And
re B
erub
e, C
hief
Eng
inee
r for
thei
r col
labo
ratio
n in
th
is a
sses
smen
t. T
hey
wer
e ex
traor
dina
rily
kind
in a
ccom
mod
atin
g m
y re
ques
ts, w
hich
ofte
n in
volv
ed th
eir w
orki
ng o
ff-h
ours
, inc
ludi
ng
late
at n
ight
. Eq
ually
impo
rtant
, the
ass
essm
ent w
ould
not
hav
e be
en
poss
ible
with
out t
he f
ores
ight
and
fin
anci
al s
uppo
rt of
the
Tour
ism
D
evel
opm
ent
Cor
pora
tion
of
Bar
bado
s.
I w
ould
al
so
like
to
reco
gniz
e th
e tir
eles
s ef
forts
of
the
Bar
bado
s Se
a Tu
rtle
Proj
ect,
espe
cial
ly D
r. Ju
lia H
orro
cks,
Bar
ry K
rueg
er a
nd th
eir 2
006
seas
onal
st
aff.
The
pro
fess
iona
l wor
k of
the
BST
P ha
s se
t a h
igh
stan
dard
for
rese
arch
and
con
serv
atio
n in
Bar
bado
s an
d th
roug
hout
the
Car
ibbe
an
regi
on.
With
out
thei
r co
llabo
ratio
n, i
nclu
ding
pro
vidi
ng m
e w
ith
hous
ing,
trai
ning
, acc
ess
to d
ata
and
othe
r tec
hnic
al in
form
atio
n, a
nd
the
oppo
rtuni
ty to
con
tribu
te to
thei
r im
porta
nt fi
eld
wor
k, w
hich
has
be
en p
rofe
ssio
nally
and
per
sona
lly e
nric
hing
for
me,
thi
s lig
htin
g as
sess
men
t cou
ld n
ot h
ave
been
acc
ompl
ishe
d. F
inal
ly, I
am
gra
tefu
l to
Dr.
Kar
en E
cker
t, Ex
ecut
ive
Dire
ctor
of
WID
ECA
ST a
nd m
y ac
adem
ic a
dvis
or a
t D
uke
Uni
vers
ity’s
Nic
hola
s Sc
hool
of
the
Envi
ronm
ent,
for
her
enco
urag
emen
t of
m
y ef
forts
an
d he
r le
ader
ship
in C
arib
bean
sea
turtl
e co
nser
vatio
n is
sues
in g
ener
al, a
nd
to E
rik M
artin
of
Ecol
ogic
al A
ssoc
iate
s, In
c. f
or h
is k
indn
ess
and
patie
nce
in t
rain
ing
me
in t
he p
roto
cols
of
prof
essi
onal
bea
chfr
ont
light
ing
asse
ssm
ents
, a fi
eld
in w
hich
he
is w
ell-r
ecog
nize
d.
Appendix VII – Sandy Lane property map
1
Appendix VIII – Sandy Lane assessment report
Nat
iona
l Ass
essm
ent o
f Bea
chfro
nt L
ight
ing
and
its
Effe
ct o
n th
e Su
rviv
al o
f End
ange
red
Mar
ine
Turtl
es
in B
arba
dos,
Wes
t Ind
ies
Prop
erty
Ass
essm
ent:
SAN
DY L
AN
E
Resp
ectfu
lly s
ubm
itted
Jo
hn E
nglis
h Kn
owle
s
INT
RO
DU
CT
ION
In p
artn
ersh
ip w
ith th
e B
arba
dos
Sea
Turtl
e Pr
ojec
t (B
STP)
, lo
cal
affil
iate
of
the
Wid
er C
arib
bean
Sea
Tur
tle C
onse
rvat
ion
Net
wor
k (W
IDEC
AST
), an
d th
e To
uris
m D
evel
opm
ent C
orpo
ratio
n in
Bar
bado
s, a
form
al l
ight
ing
asse
ssm
ent
was
con
duct
ed a
t Sa
ndy
Lane
as
part
of a
follo
w-u
p in
itiat
ive
to im
plem
ent r
ecom
men
datio
ns
mad
e at
a n
atio
nal “
Sea
Turtl
es a
nd B
each
fron
t Lig
htin
g” w
orks
hop
held
in 2
000
(Eck
ert a
nd H
orro
cks,
2002
).
The
eval
uatio
n of
lig
htin
g as
soci
ated
with
the
San
dy L
ane
prop
erty
atte
sts
to th
e ef
forts
and
ded
icat
ion
of th
e ho
tel i
ndus
try a
nd
the
BST
P in
im
prov
ing
the
cond
ition
s of
arti
ficia
l be
ach
light
ing,
w
hich
is w
ell k
now
n to
be
detri
men
tal t
o bo
th h
atch
lings
and
nes
ting
sea
turtl
es (E
cker
t and
Hor
rock
s, 20
02).
Sa
ndy
Lane
has
iden
tifie
d its
elf a
s a
lead
er in
add
ress
ing
the
light
ing
prob
lem
by
volu
ntar
ily p
artic
ipat
ing
in th
is a
sses
smen
t. T
he
prop
erty
– a
long
with
fou
r (4
) ot
her
beac
hfro
nt h
otel
s –
was
cho
sen
beca
use
it pl
ays
a cr
ucia
l ro
le i
n th
e qu
ality
of
sea
turtl
e ne
stin
g ha
bita
t. T
he in
tent
of t
he li
ghtin
g as
sess
men
t was
to e
valu
ate
curr
ent
cond
ition
s, an
d to
pro
pose
sol
utio
ns a
nd r
ecom
men
datio
ns f
or e
ach
light
ide
ntifi
ed a
s co
ntrib
utin
g to
the
noc
turn
al i
llum
inat
ion
of t
he
nest
ing
beac
h.
The
atte
ntio
n of
suc
h w
ork
is c
ritic
al in
the
surv
ival
of
the
haw
ksbi
ll se
a tu
rtle,
Ere
tmoc
hely
s im
bric
ata,
a c
ritic
ally
end
ange
red
spec
ies
wor
ldw
ide
(cf.
IUC
N R
edLi
st).
Bar
bado
s pl
ays
a ve
ry
impo
rtant
rol
e in
the
sur
viva
l of
thi
s sp
ecie
s, its
sou
thw
est
coas
t ha
ving
bee
n id
entif
ied
as o
ne o
f the
mos
t im
porta
nt n
estin
g gr
ound
s re
mai
ning
in th
e W
ider
Car
ibbe
an R
egio
n.
Arti
ficia
l be
achf
ront
lig
htin
g,
char
acte
rized
as
“l
ight
po
llutio
n” b
y W
ither
ingt
on a
nd M
artin
(20
03,
p. V
), is
the
mos
t se
rious
con
tem
pora
ry th
reat
to th
e su
rviv
al o
f sea
turtl
es in
Bar
bado
s (E
cker
t an
d H
orro
cks,
2002
). M
arin
e tu
rtles
are
mos
t se
nsiti
ve t
o sh
orte
r w
avel
engt
hs (
blue
s an
d gr
eens
), w
hich
the
y us
e as
a s
ea-
findi
ng c
ue.
Sho
rter
wav
elen
gths
are
als
o em
itted
by
whi
te l
ight
.
Whe
n su
ch
light
s ar
e vi
sibl
e fr
om
the
beac
h,
the
effe
ct
is
trem
endo
us.
With
erin
gton
an
d M
artin
(2
003)
su
gges
t th
e fo
llow
ing
appr
oach
to
miti
gate
“lig
ht p
ollu
tion”
by
eith
er e
limin
atin
g th
e fix
ture
or b
y ad
just
ing
wav
elen
gth
or in
tens
ity:
We
have
no
relia
ble
form
ula
that
can
be
used
to
calc
ulat
e ho
w m
uch
each
ligh
t sou
rce
will
aff
ect
sea
turtl
es.
We
do
know
, ho
wev
er,
that
if
spec
tral
emis
sion
s ar
e eq
uiva
lent
, re
duci
ng i
nten
sity
will
red
uce
effe
cts,
and
if in
tens
ities
are
si
mila
r, su
bstit
utin
g le
ss a
ttrac
tive
sour
ces
(like
yel
low
bug
or
red
lig
hts)
will
als
o re
duce
eff
ects
. A
sou
nd s
trate
gy,
ther
efor
e, w
ould
be
to r
educ
e ef
fect
s on
sea
tur
tles
by
man
ipul
atio
n bo
th i
nten
sity
and
col
or.
As
few
lig
hts
as
prac
ticab
le
shou
ld
be
used
, an
d fo
r lig
htin
g de
emed
es
sent
ial,
long
wav
elen
gth
light
sou
rces
sho
uld
repl
ace
mor
e di
srup
tive
light
sou
rces
and
int
ensi
ty s
houl
d be
red
uced
by
usin
g la
mps
of m
inim
al w
atta
ge th
at a
re h
ouse
d w
ithin
wel
l-di
rect
ed f
ixtu
res
aim
ed d
own
and
away
fro
m t
he b
each
(p.
23
). In
poi
nt, d
irect
ligh
t on
the
beac
h ca
n be
hig
hly
disr
uptiv
e to
bo
th a
dult
turtl
es a
nd h
atch
lings
, and
elim
inat
ing
sour
ces
of d
irect
lig
ht r
each
ing
the
beac
h is
pre
ferr
ed o
ver
all
othe
r co
nser
vatio
n al
tern
ativ
es (
With
erin
gton
and
Mar
tin,
2003
). I
n ci
rcum
stan
ces
whe
re e
limin
atin
g lig
ht s
ourc
es –
eith
er b
y tu
rnin
g th
em o
ff o
r by
re
mov
ing
the
fixtu
res
all
toge
ther
–
is
not
prac
tical
, se
vera
l al
tern
ativ
es a
re a
vaila
ble
whi
ch d
irect
lig
ht m
ore
effic
ient
ly a
nd/o
r sh
ield
the
sou
rce
from
the
bea
ch.
Man
y of
the
se m
oder
n fix
ture
s al
so p
reve
nt “
wal
l was
h” (t
he il
lum
inat
ion
of th
e si
de o
r faç
ade
of a
bu
ildin
g) a
nd a
re h
ighl
y re
com
men
ded
over
fix
ture
s th
at e
xpos
e a
bare
bul
b to
the
beac
hfro
nt.
In th
e ca
se o
f dec
orat
ive
light
ing,
whi
ch “
has
limite
d us
e fo
r an
y pu
rpos
e ot
her
than
aes
thet
ic e
nhan
cem
ent
[and
whe
n] n
ear
nest
ing
beac
hes
may
be
muc
h m
ore
harm
ful t
o se
a tu
rtles
than
it is
us
eful
to
pe
ople
” (W
ither
ingt
on
and
Mar
tin,
2003
, p.
20
-21)
, m
itiga
tion
is l
imite
d.
For
exam
ple,
eve
n if
the
four
hig
h-in
tens
ity
blue
flo
od l
ight
s cu
rren
tly p
ositi
oned
alo
ng t
he b
each
-fac
e of
the
ho
tel c
ould
be
alte
red
to e
mit
the
wav
elen
gths
leas
t dis
rupt
ive
to s
ea
turtl
es (
red)
, th
ere
wou
ld s
till
mos
t lik
ely
be d
etrim
enta
l ef
fect
s.
This
goe
s w
ithou
t m
entio
ning
the
im
prac
tical
ity o
f su
ch b
right
oc
eanf
ront
lig
hts
that
eff
ect
beac
h zo
nes
beyo
nd t
he S
andy
Lan
e pr
oper
ty.
(With
erin
gton
an
d M
artin
, 20
03;
JEK
, pe
rson
al
obse
rvat
ion)
In
the
sec
tions
tha
t fo
llow
I w
ill d
etai
l m
y m
etho
ds a
nd
resu
lts,
and
prov
ide
spec
ific
reco
mm
enda
tions
for
miti
gatio
n.
If
cons
train
ts
hind
er
the
impl
emen
tatio
n of
pa
rticu
lar
reco
mm
enda
tions
, one
opt
ion
is th
at e
ffec
tive
actio
n be
take
n in
hig
h pr
iorit
y ca
ses
(Ran
k “3
” lig
hts,
see
MET
HO
DS)
and
tha
t lo
wer
pr
iorit
y ac
tions
be
budg
eted
ove
r tim
e.
In
gene
ral,
and
in k
eepi
ng
with
the
deci
sion
s of t
he 2
000
“Sea
Tur
tles a
nd B
each
fron
t Lig
htin
g”
wor
ksho
p, r
ecom
men
datio
ns a
re b
ased
on
best
pra
ctic
es a
nd c
urre
nt
scie
nce
as a
rticu
late
d by
With
erin
gton
and
Mar
tin (2
003)
.
ME
TH
OD
S D
aytim
e Li
ghtin
g Su
rvey
A b
asel
ine
dayt
ime
light
ing
surv
ey w
as c
ondu
cted
on
foot
on
23 J
uly
2006
by
obse
rvin
g lig
htin
g fix
ture
s an
d bu
lbs d
irect
ly v
isib
le
from
the
beac
h. T
he e
ntire
pro
perty
was
acc
esse
d to
cla
rify,
iden
tify,
an
d/or
cou
nt p
artic
ular
fix
ture
(s).
All
exte
rior
light
s w
ithin
line
-of-
sigh
t of
the
obs
erve
r [J
ohn
Engl
ish
Kno
wle
s] w
ere
desc
ribed
with
re
spec
t to
fix
ture
typ
e an
d lo
catio
n.
The
func
tion
of l
ight
s w
as
dedu
ced
by th
e ob
serv
er;
how
ever
, sub
sequ
ent
mee
tings
with
hot
el
man
agem
ent
staf
f in
sure
d th
at
the
corr
ect
func
tiona
lity
was
do
cum
ente
d in
eac
h ca
se.
Lig
ht f
ixtu
res
with
lam
ps (
light
bul
bs)
visi
ble
from
the
beac
h an
d th
ose
that
wer
e de
sign
ed o
r pos
ition
ed s
o th
at t
hey
wou
ld l
ikel
y ill
umin
ate
the
beac
h w
ere
cons
ider
ed t
o be
po
tent
ially
pro
blem
atic
.
Nig
httim
e Li
ghtin
g Su
rvey
In c
oord
inat
ion
with
hot
el m
anag
emen
t, a
nigh
ttim
e lig
htin
g su
rvey
was
con
duct
ed o
n fo
ot o
n 23
July
200
6. D
urin
g th
e ni
ghtti
me
surv
ey, e
ach
light
iden
tifie
d in
the
dayt
ime
surv
ey w
as lo
cate
d an
d ev
alua
ted
with
res
pect
to
its p
oten
tial
effe
ct o
n se
a tu
rtles
. Li
ghts
un
seen
dur
ing
the
day,
but
vis
ible
whe
n em
ittin
g lig
ht,
wer
e al
so
eval
uate
d. E
ach
light
was
rate
d an
d ra
nked
on
a sc
ale
of 1
to 3
.
The
nigh
ttim
e su
rvey
inv
olve
d tw
o in
spec
tions
, one
bef
ore
mid
nigh
t and
one
afte
r mid
nigh
t, al
low
ing
for a
n ac
cura
te ra
nkin
g of
ea
ch in
divi
dual
ligh
t sou
rce
in th
e co
ntex
t of
chan
ging
bac
kgro
und
illum
inat
ion
of
diff
eren
t lig
htin
g co
nditi
ons
and
inte
nsiti
es
thro
ugho
ut t
he n
ight
. B
ecau
se p
artic
ular
ly b
right
lig
hts
less
en t
he
degr
ee o
r th
e ac
tual
brig
htne
ss o
f th
e lig
hts
behi
nd t
hem
, an
d be
caus
e so
me
light
s ar
e ex
tingu
ishe
d la
te a
t ni
ght
unde
r no
rmal
op
erat
ing
proc
edur
e, t
he o
bser
ver
was
abl
e to
use
the
seq
uent
ial
insp
ectio
ns
to
mor
e ac
cura
tely
ch
arac
teriz
e th
ose
light
s th
at
rem
aine
d.
The
Ligh
ts
Fo
llow
ing
are
the
surv
eyed
lig
hts
liste
d fr
om t
he m
ost
disr
uptiv
e (R
ank
3) t
o th
e le
ast
disr
uptiv
e (R
ank
1) f
or m
arin
e tu
rtles
. A
rank
of “
1” d
escr
ibes
indi
rect
ligh
t vis
ible
by
an o
bser
ver
on th
e be
ach,
but
not
like
ly to
pre
sent
a st
rong
attr
actio
n to
nes
ting
or
hatc
hing
tur
tles.
A r
ank
of “
2” d
escr
ibes
a v
isib
le g
lobe
, glo
win
g el
emen
t, la
mp,
or
refle
ctor
like
ly to
dis
orie
nt tu
rtles
, but
not
stro
ng
enou
gh to
cas
t a sh
adow
on
the
beac
h. A
nd a
rank
of “
3” d
escr
ibes
a
light
sou
rce
stro
ng e
noug
h to
cas
t a s
hado
w o
n th
e be
ach
rega
rdle
ss
of w
heth
er th
e ill
umin
atio
n is
dire
ct o
r ind
irect
.
Even
the
sm
alle
st l
ight
s ca
n ra
nk a
s a
“3”
if th
ey c
ast
a sh
adow
on
the
beac
h; t
heir
clos
e pr
oxim
ity t
o th
e be
ach
and
thei
r lo
w v
ertic
al p
lace
men
t nea
r the
hor
izon
can
be
just
as
diso
rient
atin
g as
a m
ore
pow
erfu
l lig
ht fu
rther
aw
ay.
The
“3”
rank
ing
light
s ha
ve
been
pla
ced
first
in th
e as
sess
men
t bec
ause
of t
heir
pote
ntia
lly m
ore
serio
us e
ffec
ts o
n m
arin
e tu
rtles
. T
he f
ocus
of
corr
ectiv
e ac
tions
sh
ould
beg
in w
ith th
ese
light
s, as
thei
r miti
gatio
n w
ill h
ave
the
mos
t si
gnifi
cant
impa
ct o
n th
e be
ach
envi
ronm
ent.
W
ithin
eac
h ra
nk –
1, 2
, 3 –
fixt
ures
list
ed fi
rst a
re e
xpec
ted
to r
equi
re t
he g
reat
est
atte
ntio
n ei
ther
in
num
ber,
expe
nse,
or
crea
tivity
. Th
e lis
t con
tinue
s th
roug
h fix
ture
s th
at a
re p
rogr
essi
vely
si
mpl
er a
nd/o
r ch
eape
r to
miti
gate
. F
or e
ach
light
the
num
ber
of
fixtu
res
visi
ble
from
the
bea
ch,
the
fixtu
re t
ype,
loc
atio
n, r
ank,
co
mm
ents
(if
an
y),
func
tion,
pic
ture
an
d re
com
men
datio
ns
are
docu
men
ted.
Eac
h re
com
men
datio
n is
spec
ific
to a
n in
divi
dual
ligh
t, an
d m
ay
incl
ude
one
or
man
y ex
plan
ator
y re
mar
ks.
So
me
reco
mm
enda
tions
will
per
tain
to m
itiga
ting
the
curr
ent f
ixtu
re; o
ther
s w
ill su
gges
t the
repl
acem
ent o
f a fi
xtur
e w
ith a
n al
tern
ativ
e.
Rec
omm
enda
tions
are
illu
stra
ted
by th
e fo
llow
ing:
Perm
anen
tly e
limin
ate
fixtu
re.
Som
e ca
ses a
re sp
ecifi
c to
the
num
ber o
r loc
atio
n of
the
fixtu
res.
Rep
ositi
on fi
xtur
e to
the
land
war
d si
de o
f the
tree
or o
bjec
t.
Aim
fixt
ure
away
from
the
beac
h.
In
stal
l low
wat
tage
(50
wat
ts o
r les
s) y
ello
w b
ug li
ght b
ulb.
In
stal
l hoo
d of
suff
icie
nt d
epth
and
wid
th.
R
educ
e in
tens
ity o
f lig
ht o
r low
er w
atta
ge.
Sh
ield
seaw
ard
side
of f
ixtu
res t
hat a
re v
isib
le fr
om th
e be
ach.
Kee
p lig
hts
off
whe
n no
t in
use
, es
peci
ally
lig
hts
clos
est
to t
he
beac
h.
Info
rm
gues
ts
via
tabl
e te
nts,
door
ha
nger
s, or
ot
her
educ
atio
nal m
ater
ials
abo
ut fi
xtur
es u
nder
thei
r con
trol.
In
stal
l shi
eld
or m
ask
of su
ffic
ient
size
that
cov
ers a
n ar
ch o
f 180
° on
the
ocea
n si
de.
Po
sitio
n lip
ove
r rop
e lig
htin
g to
con
ceal
bar
e bu
lbs.
R
epla
ce w
ith re
d LE
D ro
pe li
ghtin
g.
Rep
lace
exi
stin
g fix
ture
with
a m
ore
dire
cted
, mor
e fu
nctio
nal s
tep
light
pos
ition
ed to
elim
inat
e an
y di
rect
(or
indi
rect
) ill
umin
atio
n of
th
e be
ach.
R
emov
e w
hen
not i
n us
e.
Ex
tingu
ish
whe
n no
t in
use.
R
epla
ce e
xist
ing
fixtu
re w
ith a
mor
e di
rect
ed,
mor
e fu
nctio
nal
dow
nlig
ht.
Rep
lace
exi
stin
g fix
ture
with
a m
ore
dire
cted
and
fun
ctio
nal
path
lig
ht,
and
re-p
ositi
on
it to
el
imin
ate
any
dire
ct
(or
indi
rect
) ill
umin
atio
n of
the
beac
h.
In
stal
l com
pact
flu
ores
cent
Tur
tle S
afe
Ligh
ting
lam
ps (
light
bul
bs).
Se
e IN
TE
RN
ET
RE
SOU
RC
ES.
In
stal
l red
LED
bul
b.
Use
dim
mer
to le
ssen
the
effe
ct o
f ind
irect
ligh
t lea
ving
the
dini
ng
area
.
Elim
inat
e fix
ture
s and
use
low
tabl
e la
mps
(suc
h as
Aur
elle
LED
C
andl
e Se
ries o
r Max
xim
a M
LC-0
1 LE
D F
lam
eles
s Can
dle)
or
cand
les.
This
wou
ld se
rve
the
purp
ose
of il
lum
inat
ing
the
tabl
e w
ithou
t uni
nten
ded
broa
dcas
t bey
ond
the
rest
aura
nt.
Plac
e sm
all l
amp
shad
e ov
er b
are
bulb
s to
prev
ent t
heir
visi
bilit
y fr
om th
e be
ach.
C
ap o
r cov
er to
p of
fixt
ure
to p
reve
nt u
p-lig
htin
g an
d “w
all w
ash.
”
In
stal
l red
filte
r.
V
ery
larg
e tr
ee m
ount
ed fl
oodl
ight
Rank
: 3
Num
ber o
f fix
ture
s: 4
Li
ght L
ocat
ion:
Tre
es (s
ome
man
chin
eel)
alon
g be
ach
fron
t C
omm
ents
: Th
ese
high
int
ensi
ty,
blue
flo
odlig
hts
are
extre
mel
y di
srup
tive
to th
e se
a fin
ding
beh
avio
r of
mar
ine
turtl
es, s
o m
uch
so
that
the
y ca
n at
tract
hat
chlin
gs f
rom
the
oce
an,
whi
ch e
nter
ed t
he
wat
er f
rom
dar
ker
stre
tche
s of
the
bea
ch (
pers
onal
obs
erva
tion,
JE
K)!
Kee
p of
f du
ring
the
nest
ing/
hatc
hing
se
ason
(M
ay
– N
ovem
ber)
. Re
com
men
datio
ns:
o
r
T
ree
mou
nted
hoo
ded
spot
light
Rank
: 3
Num
ber o
f fix
ture
s: 1
4
Ligh
t Loc
atio
n: B
each
side
tree
s alo
ng p
rope
rty
Com
men
ts:
For
purp
oses
of
illum
inat
ing
wal
king
pat
hs, l
ow p
rofil
e lig
hts,
such
as
path
lig
hts,
are
reco
mm
ende
d ov
er h
ighe
r m
ount
ed
spot
light
s.
Reco
mm
enda
tions
on
the
num
ber o
f fix
ture
s:
Reco
mm
enda
tions
on
exis
ting
or re
mai
ning
fixt
ures
:
U
ltim
ate
reco
mm
enda
tion:
R
ope
light
ing
Rank
: 3
Leng
th o
f rop
e lig
htin
g: 2
33 m
eter
s Li
ght L
ocat
ion:
Alo
ng b
each
side
wal
l C
omm
ents
: A
lthou
gh le
ss in
tens
e th
an s
ome
flood
light
s, tin
y w
hite
lig
hts t
hat a
re lo
w to
the
horiz
on p
rese
nt a
real
obs
tacl
e to
hat
chlin
gs,
espe
cial
ly o
n da
rk n
ight
s. E
ven
a sh
ort s
trip
can
emit
enou
gh li
ght
on th
e la
ndw
ard
side
to le
ad h
atch
lings
ast
ray.
Re
com
men
datio
n on
loca
tion
of ro
pe li
ghtin
g:
Reco
mm
enda
tion
for e
xist
ing
fixtu
res:
Re
plac
emen
t Rec
omm
enda
tion
B
are
spot
light
Rank
: 3
Num
ber o
f fix
ture
: 7
Ligh
t Loc
atio
n: T
ree
on n
orth
end
of p
rope
rty (
in p
ictu
re),
tree
near
th
e no
rth g
azeb
o, B
ajan
Blu
e R
esta
uran
t tre
e C
omm
ents
: Th
ese
light
s ar
e us
ed o
n sp
ecia
l occ
asio
ns.
Inst
allin
g a
hood
ove
r the
bul
bs w
ill in
crea
se th
e ae
sthe
tics
for g
uest
s as
wel
l as
dire
ct li
ght i
n a
mor
e ef
ficie
nt m
anne
r.
Reco
mm
enda
tions
:
L
arge
torc
h w
ith o
pen
flam
e Ra
nk:
3 N
umbe
r of f
ixtu
res:
2
Ligh
t Loc
atio
n: O
n be
ach,
cen
ter p
rope
rty
Reco
mm
enda
tions
:
T
ree
mou
nted
hoo
ded
spot
light
Ra
nk:
2 N
umbe
r of f
ixtu
res:
2
Ligh
t Loc
atio
n: T
rees
in lo
wer
terr
ace
Reco
mm
enda
tions
:
W
all m
ount
ed c
andl
e ho
ldin
g fix
ture
Rank
: 2
Num
ber o
f fix
ture
s: 1
76
Ligh
t Loc
atio
n: B
alco
nies
of n
orth
and
sout
h w
ings
Re
com
men
datio
ns fo
r exi
stin
g fix
ture
s:
U
ltim
ate
reco
mm
enda
tion:
U
mbr
ella
mou
nted
spot
light
Rank
: 2
Num
ber o
f fix
ture
s: 2
0 Li
ght L
ocat
ion:
Baj
an B
lue
Res
taur
ant
Com
men
ts:
Eve
n th
ough
the
se r
ank
as m
oder
ate
for
pote
ntia
lly
disr
uptin
g th
e se
a fin
ding
beh
avio
r of
mar
ine
turtl
es,
thes
e lig
hts
caus
e si
gnifi
cant
bro
adca
st o
f in
dire
ct li
ght.
Bou
ncin
g lig
ht o
ff th
e um
brel
la d
oes
illum
inat
e th
e di
ning
are
a, b
ut a
lso
boun
ces
light
in
man
y ot
her
dire
ctio
ns,
incl
udin
g th
e be
ach.
H
ighl
y di
rect
ed l
ow
prof
ile l
ight
s sh
ould
be
used
in
the
illum
inat
ion
of a
bea
ch f
ront
di
ning
are
a.
Reco
mm
enda
tions
for e
xist
ing
fixtu
res:
U
ltim
ate
reco
mm
enda
tion:
C
olum
n m
ount
ed c
andl
e lig
ht
Rank
: 2
Num
ber o
f fix
ture
s: 1
4 Li
ght L
ocat
ion:
Baj
an B
lue
Res
taur
ant
Com
men
ts: B
ajan
Blu
e R
esta
uran
t pre
sent
s a
uniq
ue c
ase
that
can
be
easi
ly m
itiga
ted.
Th
e cu
rren
t lig
hts
are
a so
urce
of
dire
ct li
ght a
nd
thei
r rep
lace
men
t with
a m
oder
n al
tern
ativ
e is
hig
hly
reco
mm
ende
d.
A f
ixtu
re t
hat
shie
lds
the
light
bul
b fr
om t
he b
each
as
wel
l as
re
stau
rant
gue
sts
is p
refe
rred
ove
r th
e ex
istin
g ba
re b
ulb
light
s fo
r bo
th m
arin
e tu
rtles
and
the
rest
aura
nt e
nviro
nmen
t.
Reco
mm
enda
tions
:
U
p di
rect
ed h
oode
d sp
otlig
ht w
ithin
law
n an
d gr
ound
cove
r
U
p di
rect
ed h
oode
d sp
otlig
hts a
t the
bas
e of
a tr
ee
Rank
: 2
Num
ber o
f fix
ture
s: 1
6 Li
ght L
ocat
ion:
Gra
ss a
rea
in f
ront
of
first
flo
or r
oom
s fo
r bo
th th
e no
rth a
nd so
uth
win
gs
Com
men
ts:
“Lum
inai
res
shou
ld n
ot b
e di
rect
ed o
nto…
any
obje
ct
visi
ble
from
th
e be
ach”
(W
ither
ingt
on).
G
low
ing
beac
hfro
nt
vege
tatio
n is
hi
ghly
di
srup
tive
to
the
sea
findi
ng
beha
vior
of
hatc
hlin
gs e
spec
ially
on
moo
nles
s ni
ghts
. I
t is
rec
omm
ende
d th
at
such
“ae
sthe
tics”
are
not
em
ploy
ed d
irect
ly b
each
fron
t.
Reco
mm
enda
tions
on
the
num
ber o
f fix
ture
s:
Reco
mm
enda
tions
on
exis
ting
or re
mai
ning
fixt
ures
:
Ulti
mat
e re
com
men
datio
n:
W
all m
ount
ed c
andl
e lig
ht
Rank
: 2
Num
ber o
f fix
ture
s: 2
Li
ght L
ocat
ion:
Upp
er te
rrac
e ju
st o
utsi
de lo
bby
Reco
mm
enda
tions
:
Exam
ples
of a
ccep
tabl
e fix
ture
s:
W
all m
ount
ed w
ick
Rank
: 2
Num
ber o
f fix
ture
s: 2
8 Li
ght L
ocat
ion:
L’a
cajo
u Re
com
men
datio
ns:
R
eces
sed
step
ligh
ts
Rank
: 2
Num
ber o
f fix
ture
s: 5
2 Li
ght L
ocat
ion:
Ter
race
stai
rway
C
omm
ents
: Use
red
light
Re
com
men
datio
ns:
O
ne c
hand
elie
r fix
ture
, but
thre
e bu
lbs
Rank
: 2
Num
ber o
f fix
ture
s: 1
cha
ndel
ier f
ixtu
re, b
ut 3
bul
bs
Ligh
t Loc
atio
n: L
obby
C
omm
ents
: It i
s im
porta
nt to
con
ceal
sour
ces o
f dire
ct li
ght.
Re
com
men
datio
ns:
C
eilin
g m
ount
ed sp
otlig
ht o
ver
fron
t des
k Ra
nk:
2 N
umbe
r of f
ixtu
res:
2
Ligh
t Loc
atio
n: L
obby
Re
com
men
datio
ns:
Sm
all c
eilin
g m
ount
ed sp
otlig
ht in
res
taur
ant
Rank
: 2
Num
ber o
f fix
ture
s: 1
1 Li
ght L
ocat
ion:
Baj
an B
lue
Res
taur
ant
Reco
mm
enda
tions
:
T
iki t
orch
with
ope
n fla
me
Rank
: 2
Num
ber o
f fix
ture
s: 1
3 Li
ght L
ocat
ion:
On
beac
h, in
fron
t of B
ajan
Blu
e R
esta
uran
t, Lo
wer
te
rrac
e.
Reco
mm
enda
tions
:
B
alco
ny u
plig
ht
Rank
: 1
Num
ber o
f fix
ture
s: 3
44
Ligh
t Loc
atio
n: B
alco
nies
C
omm
ents
: Th
e ba
lcon
y ro
oms
at S
andy
Lan
e ha
ve t
hree
diff
eren
t ty
pes
of f
ixtu
res
pres
ent o
n ea
ch b
alco
ny.
The
cand
le ty
pe f
ixtu
res
have
the
gre
ates
t po
tent
ial
to d
isru
pt t
he s
ea f
indi
ng b
ehav
ior
of
mar
ine
turtl
es.
If
thes
e fix
ture
s ar
e re
plac
ed w
ith a
mod
ern
turtl
e fr
iend
ly a
ltern
ativ
e, th
en th
ey b
ecom
e le
ast p
robl
emat
ic.
The
seco
nd
cate
gorie
s of
lig
hts
are
the
lam
ps, w
hich
are
min
imal
ly d
isru
ptiv
e.
Fina
lly,
the
up l
ight
s ar
e m
oder
atel
y di
srup
tive
beca
use
of “
wal
l w
ashi
ng”,
eve
n th
ough
the
bul
b is
con
ceal
ed.
Thi
s is
why
dow
n lig
hts
are
alw
ays
reco
mm
ende
d ov
er u
p lig
hts.
To
miti
gate
the
ef
fect
s on
mar
ine
turtl
es, t
he c
urre
nt fi
xtur
es c
ould
be
inst
alle
d w
ith
bug
light
s or
tur
tle f
riend
ly l
amps
. T
he w
atta
ge c
ould
als
o be
lo
wer
ed.
How
ever
, w
ith a
dequ
ate
light
ing
alre
ady
pres
ent,
the
elim
inat
ion
of th
e up
ligh
ts o
n be
ach
fron
t bal
coni
es is
an
optio
n.
Reco
mm
enda
tions
on
the
exis
ting
fixtu
res:
Ulti
mat
e re
com
men
datio
n w
hen
adeq
uate
lig
htin
g is
al
read
y pr
ovid
ed:
W
all m
ount
ed c
lay
cove
red
fixtu
re
B
otto
m v
iew
Rank
: 1
Num
ber o
f fix
ture
s: 1
8 Li
ght L
ocat
ion:
Upp
er a
nd lo
wer
terr
ace
Reco
mm
enda
tions
:
U
p di
rect
ed h
oode
d sp
otlig
ht o
n gr
ound
Rank
: 1
Num
ber o
f fix
ture
s: 1
3 Li
ght L
ocat
ion:
Low
er te
rrac
e (b
elow
tree
s in
natu
ral a
rea)
Re
com
men
datio
ns o
n th
e nu
mbe
r of f
ixtu
res:
Re
com
men
datio
ns o
n ex
istin
g or
rem
aini
ng fi
xtur
es:
U
ltim
ate
reco
mm
enda
tion:
G
roun
d re
cess
ed sp
otlig
ht
Rank
: 1
Num
ber o
f fix
ture
s: 1
0 Li
ght L
ocat
ion:
Bea
chsi
de g
rass
y ar
eas
Com
men
ts:
“Lum
inai
res
shou
ld n
ot b
e di
rect
ed o
nto…
any
obje
ct
visi
ble
from
th
e be
ach”
(W
ither
ingt
on).
G
low
ing
beac
hfro
nt
vege
tatio
n is
hi
ghly
di
srup
tive
to
the
sea
findi
ng
beha
vior
of
hatc
hlin
gs e
spec
ially
on
moo
nles
s ni
ghts
. I
t is
rec
omm
ende
d th
at
such
“ae
sthe
tics”
are
not
em
ploy
ed d
irect
ly b
each
fron
t.
Reco
mm
enda
tions
on
the
num
ber o
f fix
ture
s:
Reco
mm
enda
tions
on
exis
ting
or re
mai
ning
fixt
ures
:
U
ltim
ate
reco
mm
enda
tion:
L
amp
with
shad
e
Rank
: 1
Num
ber o
f fix
ture
s: 7
5 Li
ght
Loca
tion:
Pre
sent
on
the
balc
onie
s of
the
nor
th a
nd s
outh
w
ings
Re
com
men
datio
ns:
W
all m
ount
ed u
p di
rect
ed c
lay
scon
ce
Rank
: 1
Num
ber o
f fix
ture
s: 4
Li
ght L
ocat
ion:
Upp
er a
nd lo
wer
terr
ace
C
omm
ents
: Fix
ture
doe
s co
ntrib
ute
to “
wal
l was
h”.
A d
own
light
is
pref
erre
d ov
er a
n up
ligh
t. T
he e
limin
atio
n of
the
fixtu
re is
alw
ays
an o
ptio
n w
ith a
dequ
ate
light
ing
alre
ady
pres
ent.
Reco
mm
enda
tions
on
the
exis
ting
fixtu
res:
Ulti
mat
e re
com
men
datio
n w
hen
adeq
uate
lig
htin
g is
al
read
y pr
ovid
ed:
W
all m
ount
ed u
plig
ht
Rank
: 1
Num
ber o
f fix
ture
s: 6
Li
ght L
ocat
ion:
Low
er T
erra
ce
Com
men
ts: F
ixtu
re d
oes
cont
ribut
e to
“w
all w
ash”
. A
dow
n lig
ht is
pr
efer
red
over
an
up li
ght.
The
elim
inat
ion
of th
e fix
ture
is a
lway
s an
opt
ion
with
ade
quat
e lig
htin
g al
read
y pr
esen
t.
Reco
mm
enda
tions
on
the
exis
ting
fixtu
res:
Ulti
mat
e re
com
men
datio
n w
hen
adeq
uate
lig
htin
g is
al
read
y pr
ovid
ed:
R
eces
sed
ceili
ng li
ght i
n re
stau
rant
Ra
nk:
1 N
umbe
r of f
ixtu
res:
70
Ligh
t Loc
atio
n: B
ajan
Blu
e R
esta
uran
t C
omm
ents
: Not
all
fixtu
res a
re v
isib
le fr
om b
each
. Re
com
men
datio
ns:
Sm
all c
ircu
lar
rece
ssed
cei
ling
light
Ra
nk:
1 N
umbe
r of f
ixtu
res:
59
Ligh
t Loc
atio
n: C
eilin
g of
sta
irwel
l in
north
win
g an
d th
ird f
loor
of
both
nor
th a
nd so
uth
win
gs
Com
men
ts: N
ot a
ll fix
ture
s are
vis
ible
from
bea
ch.
Reco
mm
enda
tions
:
R
eces
sed
ceili
ng sp
otlig
ht in
squa
re fi
xtur
e Ra
nk:
1 N
umbe
r of f
ixtu
res:
55
Ligh
t Loc
atio
n: C
eilin
g of
L’a
cajo
u R
esta
uran
t C
omm
ents
: Not
all
fixtu
res a
re v
isib
le fr
om th
e be
ach.
Re
com
men
datio
ns:
L
arge
r ci
rcul
ar r
eces
sed
light
Ra
nk:
1 N
umbe
r of f
ixtu
res:
21
Ligh
t Loc
atio
n: C
eilin
g of
ow
ner’
s pen
thou
se
Com
men
ts:
Not
all
fixtu
res a
re v
isib
le fr
om b
each
.
Reco
mm
enda
tions
:
L
arge
st r
eces
sed
ceili
ng li
ght i
n lo
bby
Rank
: 1
Num
ber o
f fix
ture
s: 6
Li
ght L
ocat
ion:
Lob
by
Com
men
ts:
Not
all
fixtu
res
are
visi
ble
from
bea
ch.
The
num
ber
give
n is
of f
ixtu
res t
hat a
re v
isib
le fr
om th
e be
ach
Reco
mm
enda
tions
:
R
eces
sed
ceili
ng sp
otlig
hts
Rank
: 1
Num
ber o
f fix
ture
s: 2
4 Li
ght L
ocat
ion:
Cei
ling
of b
oth
gaze
bos
Com
men
ts: G
azeb
o em
ploy
ees c
laim
ligh
ts a
re to
o ho
t! Re
com
men
datio
ns:
Fl
oodl
ight
Ra
nk:
1 N
umbe
r of f
ixtu
res:
2
Ligh
t Loc
atio
n: A
bove
rafte
rs o
f bot
h ga
zebo
s Re
com
men
datio
ns:
C
hand
elie
r Ra
nk:
1 N
umbe
r of f
ixtu
res:
5
Ligh
t Loc
atio
n: L
ower
terr
ace
Com
men
ts: N
ot a
ll fix
ture
s are
vis
ible
from
the
beac
h.
Reco
mm
enda
tions
:
U
nder
wat
er r
eces
sed
spot
light
at t
he b
ase
of th
e fo
unta
in
Rank
: 1
Num
ber o
f fix
ture
s: 2
Li
ght L
ocat
ion:
Nor
th w
ing
foun
tain
Re
com
men
datio
ns:
SUM
MA
RY
As
a pr
emie
r lux
ury
esta
blis
hmen
t, it
is n
ot c
oinc
iden
tal t
hat
mos
t of t
he li
ghts
at S
andy
Lan
e ra
nk c
ompa
rativ
ely
low
in te
rms
of
thei
r po
tent
ial
to d
isru
pt a
nd d
isor
ient
end
ange
red
mar
ine
turtl
es.
The
maj
ority
of f
ixtu
res
conc
eal t
he a
ctua
l lum
inai
re o
r bul
b. A
bar
e bu
lb c
an b
e ja
rrin
g an
d ga
rish
for
hum
ans
and
sea
turtl
es a
like,
but
th
e m
ajor
ity o
f th
e co
nditi
ons
at S
andy
Lan
e ar
e no
thin
g le
ss t
han
very
ple
asin
g.
The
atm
osph
ere
of l
ow l
ight
lev
els
and
tast
eful
fix
ture
s on
ly e
nhan
ces
the
tour
ism
exp
erie
nce
one
rece
ives
at S
andy
La
ne, a
nd th
e re
sort
is c
omm
ende
d fo
r suc
h ar
chite
ctur
al d
esig
n an
d co
nsid
erat
ion.
San
dy L
ane
also
con
tribu
tes d
irect
ly to
the
surv
ival
of
mar
ine
turtl
es in
oth
er w
ays,
incl
udin
g st
acki
ng b
each
cha
irs a
t nig
ht,
in a
n ef
fort
to p
reve
nt th
e en
tang
lem
ent o
f egg
-bea
ring
fem
ale
turtl
es
craw
ling
on th
e be
ach.
That
sa
id,
the
rela
tivel
y fe
w
light
s th
at
rank
as
m
ost
disr
uptiv
e to
mar
ine
turtl
es (
Ran
k 3)
do
so a
t ve
ry h
igh
and
dist
urbi
ng in
tens
ities
. It
is h
oped
that
by
actin
g on
thes
e fix
ture
s –
mos
tly
tree-
mou
nted
sp
otlig
hts
and
strin
g lig
htin
g al
ong
the
beac
hfro
nt –
as a
prio
rity,
this
eva
luat
ion
will
impr
ove
the
cond
ition
s of
the
beac
h en
viro
nmen
t for
bot
h th
e gu
ests
at S
andy
Lan
e an
d th
e m
arin
e tu
rtles
that
rely
on
the
beac
h fo
r the
suc
cess
ful i
ncub
atio
n of
th
eir
youn
g.
The
impr
ovem
ents
will
onl
y in
crea
se S
andy
Lan
e’s
qual
ity,
prov
idin
g it
yet
anot
her
com
petit
ive
edge
aga
inst
oth
er
priv
atel
y ow
ned,
lux
ury
hote
ls i
n th
e C
arib
bean
and
aro
und
the
wor
ld.
The
reco
mm
enda
tions
, on
ce i
mpl
emen
ted,
will
not
onl
y im
prov
e be
ach
cond
ition
s fo
r m
arin
e tu
rtles
, but
will
con
tribu
te t
o th
e ex
istin
g so
phis
ticat
ed t
hem
e in
lig
htin
g am
bian
ce o
f th
is r
esor
t w
hile
redu
cing
ope
ratio
nal e
xpen
ses
thro
ugh
an e
xpec
tatio
n of
low
er
ener
gy u
se.
To
enco
urag
e lig
htin
g im
prov
emen
ts a
nd a
ssis
t in
im
plem
enta
tion,
the
Tour
ism
Dev
elop
men
t Cor
pora
tion
is a
vaila
ble
to p
urch
ase
item
s (fix
ture
s, C
F bu
g lig
hts)
in b
ulk,
whi
ch w
ill fu
rther
re
duce
the
cost
of r
etro
fittin
g an
d in
nova
tion.
Alo
ng w
ith a
n im
prov
ed b
each
fron
t in
ter
ms
of l
ight
ing
com
es a
par
alle
l re
spon
sibi
lity
for
cons
erva
tion-
min
ded
beac
hfro
nt
man
agem
ent
in
gene
ral,
incl
udin
g,
for
exam
ple,
su
ppor
ting
umbr
ella
s w
ith a
flat
bas
e in
stea
d of
sta
king
the
post
dire
ctly
into
the
sand
and
cle
arin
g le
aves
with
a h
and
rake
rat
her
than
a t
ract
or.
Sand
y La
ne p
lays
an
esse
ntia
l rol
e in
the
surv
ival
of t
he e
ndan
gere
d tu
rtles
that
use
its
beac
hes,
and
is w
ell p
ositi
oned
to s
erve
as
a m
odel
fo
r sea
turtl
e fr
iend
ly e
nviro
nmen
tal m
anag
emen
t sys
tem
s el
sew
here
in
Bar
bado
s and
bey
ond.
INT
ER
NE
T R
ESO
UR
CE
S w
ww
.turtl
esaf
elig
htin
g.co
m
LIT
ER
AT
UR
E C
ITE
D
W
ITH
ERIN
GTO
N, B
. E. a
nd R
. E. M
AR
TIN
. 200
3. U
nder
stan
ding
, as
sess
ing,
an
d re
solv
ing
light
-pol
lutio
n pr
oble
ms
on
sea
turtl
e ne
stin
g be
ache
s. 3r
d ed
. re
v. F
lorid
a M
arin
e R
esea
rch
Inst
itute
Te
chni
cal R
epor
t TR
-2. 7
3 p.
EC
KER
T, K
. L. a
nd J
. A. H
OR
RO
CK
S (E
dito
rs).
2002
. Pro
ceed
ings
of
“Se
a Tu
rtles
and
Bea
chfr
ont L
ight
ing:
An
Inte
ract
ive
Wor
ksho
p fo
r In
dust
ry P
rofe
ssio
nals
and
Pol
icy-
Mak
ers
in B
arba
dos”
, 13
O
ctob
er
2000
. Sp
onso
red
by
the
Wid
er
Car
ibbe
an
Sea
Turtl
e C
onse
rvat
ion
Net
wor
k (W
IDEC
AST
), th
e B
arba
dos
Sea
Turtl
e Pr
ojec
t, an
d th
e To
uris
m D
evel
opm
ent
Cor
pora
tion
of B
arba
dos.
WID
ECA
ST T
echn
ical
Rep
ort 1
. v +
43
pp.
AC
KN
OW
LE
DG
ME
NT
S
I am
dee
ply
inde
bted
to th
e st
aff
and
man
agem
ent o
f Sa
ndy
Lane
, in
clud
ing
Mic
hael
Pow
nall,
Chi
ef E
xecu
tive
Off
icer
, Pa
ula
Yar
de,
Chi
ef
Engi
neer
, La
wre
nce
Cum
berb
atch
, D
irect
or
of
Engi
neer
ing,
and
Leo
Bla
ckm
an a
nd t
he r
est
of t
he e
ngin
eerin
g de
partm
ent
for
thei
r co
llabo
ratio
n in
thi
s as
sess
men
t. T
hey
wer
e ex
traor
dina
rily
kind
in
acco
mm
odat
ing
my
requ
ests
, w
hich
ofte
n in
volv
ed t
heir
wor
king
off
-hou
rs,
incl
udin
g la
te a
t ni
ght.
Equ
ally
im
porta
nt, t
he a
sses
smen
t wou
ld n
ot h
ave
been
pos
sibl
e w
ithou
t the
fo
resi
ght
and
finan
cial
su
ppor
t of
th
e To
uris
m
Dev
elop
men
t C
orpo
ratio
n of
Bar
bado
s. I
wou
ld a
lso
like
to r
ecog
nize
the
tirel
ess
effo
rts o
f th
e B
arba
dos
Sea
Turtl
e Pr
ojec
t, es
peci
ally
Dr.
Julia
H
orro
cks,
Bar
ry
Kru
eger
an
d th
eir
2006
se
ason
al
staf
f.
The
prof
essi
onal
wor
k of
the
BST
P ha
s se
t a h
igh
stan
dard
for
res
earc
h an
d co
nser
vatio
n in
Bar
bado
s an
d th
roug
hout
the
Car
ibbe
an r
egio
n.
With
out
thei
r co
llabo
ratio
n, i
nclu
ding
pro
vidi
ng m
e w
ith h
ousi
ng,
train
ing,
acc
ess
to d
ata
and
othe
r te
chni
cal
info
rmat
ion,
and
the
op
portu
nity
to
cont
ribut
e to
the
ir im
porta
nt f
ield
wor
k, w
hich
has
be
en p
rofe
ssio
nally
and
per
sona
lly e
nric
hing
for
me,
thi
s lig
htin
g as
sess
men
t cou
ld n
ot h
ave
been
acc
ompl
ishe
d. F
inal
ly, I
am
gra
tefu
l to
Dr.
Kar
en E
cker
t, Ex
ecut
ive
Dire
ctor
of
WID
ECA
ST a
nd m
y ac
adem
ic a
dvis
or a
t D
uke
Uni
vers
ity’s
Nic
hola
s Sc
hool
of
the
Envi
ronm
ent,
for
her
enco
urag
emen
t of
m
y ef
forts
an
d he
r le
ader
ship
in C
arib
bean
sea
turtl
e co
nser
vatio
n is
sues
in g
ener
al, a
nd
to E
rik M
artin
of
Ecol
ogic
al A
ssoc
iate
s, In
c. f
or h
is k
indn
ess
and
patie
nce
in t
rain
ing
me
in t
he p
roto
cols
of
prof
essi
onal
bea
chfr
ont
light
ing
asse
ssm
ents
, a fi
eld
in w
hich
he
is w
ell-r
ecog
nize
d.
Appendix IX –Turtle Beach Resort property map
Appendix X– Turtle Beach Resort assessment report
Nat
iona
l Ass
essm
ent o
f Bea
chfro
nt L
ight
ing
and
its
Effe
ct o
n th
e Su
rviv
al o
f End
ange
red
Mar
ine
Turtl
es
in B
arba
dos,
Wes
t Ind
ies
Prop
erty
Ass
essm
ent:
Turtl
e Be
ach
Reso
rt
Resp
ectfu
lly s
ubm
itted
Jo
hn E
nglis
h Kn
owle
s
INT
RO
DU
CT
ION
In p
artn
ersh
ip w
ith th
e B
arba
dos
Sea
Turtl
e Pr
ojec
t (B
STP)
, lo
cal
affil
iate
of
the
Wid
er C
arib
bean
Sea
Tur
tle C
onse
rvat
ion
Net
wor
k (W
IDEC
AST
), an
d th
e To
uris
m D
evel
opm
ent C
orpo
ratio
n in
Bar
bado
s, a
form
al l
ight
ing
asse
ssm
ent
was
con
duct
ed a
t th
e Tu
rtle
Bea
ch R
esor
t as
par
t of
a f
ollo
w-u
p in
itiat
ive
to i
mpl
emen
t re
com
men
datio
ns m
ade
at a
nat
iona
l “S
ea T
urtle
s an
d B
each
fron
t Li
ghtin
g” w
orks
hop
held
in 2
000
(Eck
ert a
nd H
orro
cks,
2002
).
The
eval
uatio
n of
ligh
ting
asso
ciat
ed w
ith th
e Tu
rtle
Bea
ch
Res
ort
prop
erty
atte
sts
to t
he e
ffor
ts a
nd d
edic
atio
n of
the
hot
el
indu
stry
and
the
BST
P in
impr
ovin
g th
e co
nditi
ons o
f arti
ficia
l bea
ch
light
ing,
whi
ch i
s w
ell
know
n to
be
detri
men
tal
to b
oth
hatc
hlin
gs
and
nest
ing
sea
turtl
es (E
cker
t and
Hor
rock
s, 20
02).
Tu
rtle
Bea
ch R
esor
t ha
s id
entif
ied
itsel
f as
a l
eade
r in
ad
dres
sing
the
lig
htin
g pr
oble
m b
y vo
lunt
arily
par
ticip
atin
g in
thi
s as
sess
men
t. T
he p
rope
rty –
alo
ng w
ith f
our
(4)
othe
r be
achf
ront
ho
tels
– w
as c
hose
n be
caus
e it
play
s a
cruc
ial r
ole
in th
e qu
ality
of
sea
turtl
e ne
stin
g ha
bita
t. T
he in
tent
of
the
light
ing
asse
ssm
ent w
as
to
eval
uate
cu
rren
t co
nditi
ons,
and
to
prop
ose
solu
tions
an
d re
com
men
datio
ns f
or e
ach
light
ide
ntifi
ed a
s co
ntrib
utin
g to
the
no
ctur
nal i
llum
inat
ion
of th
e ne
stin
g be
ach.
Th
e at
tent
ion
of s
uch
wor
k is
crit
ical
in th
e su
rviv
al o
f th
e ha
wks
bill
sea
turtl
e, E
retm
oche
lys
imbr
icat
a, a
crit
ical
ly e
ndan
gere
d sp
ecie
s w
orld
wid
e (c
f. IU
CN
Red
List
). B
arba
dos
play
s a
very
im
porta
nt r
ole
in t
he s
urvi
val
of t
his
spec
ies,
its s
outh
wes
t co
ast
havi
ng b
een
iden
tifie
d as
one
of t
he m
ost i
mpo
rtant
nes
ting
grou
nds
rem
aini
ng in
the
Wid
er C
arib
bean
Reg
ion.
A
rtific
ial
beac
hfro
nt
light
ing,
ch
arac
teriz
ed
as
“lig
ht
pollu
tion”
by
With
erin
gton
and
Mar
tin (
2003
, p.
V),
is t
he m
ost
serio
us c
onte
mpo
rary
thre
at to
the
surv
ival
of s
ea tu
rtles
in B
arba
dos
(Eck
ert
and
Hor
rock
s, 20
02).
Mar
ine
turtl
es a
re m
ost
sens
itive
to
shor
ter
wav
elen
gths
(bl
ues
and
gree
ns),
whi
ch t
hey
use
as a
sea
-fin
ding
cue
. S
horte
r w
avel
engt
hs a
re a
lso
emitt
ed b
y w
hite
lig
ht.
Whe
n su
ch
light
s ar
e vi
sibl
e fr
om
the
beac
h,
the
effe
ct
is
trem
endo
us.
With
erin
gton
an
d M
artin
(2
003)
su
gges
t th
e fo
llow
ing
appr
oach
to
miti
gate
“lig
ht p
ollu
tion”
by
eith
er e
limin
atin
g th
e fix
ture
or b
y ad
just
ing
wav
elen
gth
or in
tens
ity:
We
have
no
relia
ble
form
ula
that
can
be
used
to
calc
ulat
e ho
w m
uch
each
ligh
t sou
rce
will
aff
ect
sea
turtl
es.
We
do
know
, ho
wev
er,
that
if
spec
tral
emis
sion
s ar
e eq
uiva
lent
, re
duci
ng i
nten
sity
will
red
uce
effe
cts,
and
if in
tens
ities
are
si
mila
r, su
bstit
utin
g le
ss a
ttrac
tive
sour
ces
(like
yel
low
bug
or
red
lig
hts)
will
als
o re
duce
eff
ects
. A
sou
nd s
trate
gy,
ther
efor
e, w
ould
be
to r
educ
e ef
fect
s on
sea
tur
tles
by
man
ipul
atio
n bo
th i
nten
sity
and
col
or.
As
few
lig
hts
as
prac
ticab
le
shou
ld
be
used
, an
d fo
r lig
htin
g de
emed
es
sent
ial,
long
wav
elen
gth
light
sou
rces
sho
uld
repl
ace
mor
e di
srup
tive
light
sou
rces
and
int
ensi
ty s
houl
d be
red
uced
by
usin
g la
mps
of m
inim
al w
atta
ge th
at a
re h
ouse
d w
ithin
wel
l-di
rect
ed f
ixtu
res
aim
ed d
own
and
away
fro
m t
he b
each
(p.
23
). In
poi
nt, d
irect
ligh
t on
the
beac
h ca
n be
hig
hly
disr
uptiv
e to
bo
th a
dult
turtl
es a
nd h
atch
lings
and
, elim
inat
ing
sour
ces
of d
irect
lig
ht r
each
ing
the
beac
h is
pre
ferr
ed o
ver
all
othe
r co
nser
vatio
n al
tern
ativ
es (
With
erin
gton
and
Mar
tin,
2003
). I
n ci
rcum
stan
ces
whe
re e
limin
atin
g lig
ht s
ourc
es –
eith
er b
y tu
rnin
g th
em o
ff o
r by
re
mov
ing
the
fixtu
res
all
toge
ther
–
is
not
prac
tical
, se
vera
l al
tern
ativ
es a
re a
vaila
ble
whi
ch d
irect
lig
ht m
ore
effic
ient
ly a
nd/o
r sh
ield
the
sour
ce fr
om th
e be
ach.
Si
mila
rly,
indi
rect
lig
htin
g is
al
so
high
ly
disr
uptiv
e.
With
erin
gton
and
Mar
tin r
eite
rate
tha
t, “l
umin
aire
s sh
ould
not
be
dire
cted
ont
o…an
y ob
ject
vis
ible
fro
m t
he b
each
,” t
his
incl
udes
w
alls
, cei
lings
, and
veg
etat
ion
(p. 2
1).
A fo
rm o
f int
entio
nal i
ndire
ct
light
ing
can
be d
ecor
ativ
e, w
hich
“ha
s lim
ited
use
for
any
purp
ose
othe
r th
an a
esth
etic
enh
ance
men
t [a
nd w
hen]
nea
r ne
stin
g be
ache
s m
ay b
e m
uch
mor
e ha
rmfu
l to
sea
turtl
es th
an it
is u
sefu
l to
peop
le”
(p. 2
0-21
). M
itiga
tion
tech
niqu
es fo
r dec
orat
ive
light
ing
are
limite
d an
d su
ch a
pra
ctic
e sh
ould
be
rese
rved
for a
reas
out
of s
ight
from
the
beac
h.
If i
ndire
ct l
ight
is
unin
tent
iona
l, th
en m
oder
n fix
ture
s ar
e hi
ghly
reco
mm
ende
d th
at w
ill p
reve
nt “
wal
l was
h” (t
he il
lum
inat
ion
of th
e si
de o
r faç
ade
of a
bui
ldin
g).
So
far
, the
dis
cuss
ion
abov
e ha
s be
en c
ente
red
on e
xter
ior
fixtu
res;
ho
wev
er
inte
rior
light
ing
is
also
a
sour
ce
of
“lig
ht
pollu
tion.
”
The
crite
ria f
or i
dent
ifyin
g pr
oble
ms
caus
ed b
y in
door
lig
htin
g ar
e th
e sa
me
as t
hose
for
ide
ntify
ing
prob
lem
s ca
used
by
outd
oor
light
ing…
[A
s w
ith a
n ou
tdoo
r lig
ht, a
n]
indo
or li
ght i
s a p
robl
em if
it is
vis
ible
from
the
beac
h.
Indo
or li
ghtin
g fr
om b
uild
ings
that
are
clo
se to
the
beac
h, a
re
very
tall,
or h
ave
larg
e se
a-si
de w
indo
ws
caus
es th
e gr
eate
st
prob
lem
for
sea
tur
tles.
Bec
ause
ind
oor
light
ing
is u
sual
ly
not
mea
nt t
o lig
ht t
he o
utdo
ors,
the
unw
ante
d ef
fect
s of
in
door
lig
htin
g ca
n ea
sily
be
el
imin
ated
w
ithou
t co
mpr
omis
ing
the
inte
nded
fu
nctio
n of
th
e lig
ht
(With
erin
gton
and
Mar
tin, 2
003,
p. 2
2).
In tr
uth,
the
Turtl
e B
each
Res
ort d
oes
not h
ave
dire
ct c
ontro
l ov
er w
hich
roo
m l
ight
s ar
e ut
ilize
d by
gue
sts.
How
ever
, in
door
lig
hts
be
can
min
imiz
ed
from
re
achi
ng
the
beac
h by
si
mpl
y in
form
ing
and
rem
indi
ng g
uest
s to
clo
se o
paqu
e cu
rtain
s du
ring
even
ing
hour
s whe
n ro
om li
ghts
are
on.
Th
e ho
tel
does
hav
e di
rect
con
trol
over
alm
ost
all
othe
r fix
ture
s th
at c
ast l
ight
vis
ible
from
the
beac
h. I
t is
thes
e fix
ture
s th
at
mak
e up
the
bulk
of t
his a
sses
smen
t. In
the
sec
tions
tha
t fo
llow
I w
ill d
etai
l m
y m
etho
ds a
nd
resu
lts,
and
prov
ide
spec
ific
reco
mm
enda
tions
for
miti
gatio
n.
If
cons
train
ts
hind
er
the
impl
emen
tatio
n of
pa
rticu
lar
reco
mm
enda
tions
, one
opt
ion
is th
at e
ffec
tive
actio
n be
take
n in
hig
h pr
iorit
y ca
ses
(Ran
k “3
” lig
hts,
see
MET
HO
DS)
and
tha
t lo
wer
pr
iorit
y ac
tions
be
budg
eted
ove
r tim
e.
In
gene
ral,
and
in k
eepi
ng
with
the
deci
sion
s of t
he 2
000
“Sea
Tur
tles a
nd B
each
fron
t Lig
htin
g”
wor
ksho
p, r
ecom
men
datio
ns a
re b
ased
on
best
pra
ctic
es a
nd c
urre
nt
scie
nce
as a
rticu
late
d by
With
erin
gton
and
Mar
tin (2
003)
. M
ET
HO
DS
Day
time
Ligh
ting
Surv
ey
A
bas
elin
e da
ytim
e lig
htin
g su
rvey
was
con
duct
ed o
n fo
ot o
n 26
Jul
y 20
06 b
y ob
serv
ing
light
ing
fixtu
res
and
bulb
s dire
ctly
vis
ible
fr
om th
e be
ach.
The
ent
ire p
rope
rty w
as a
cces
sed
to c
larif
y, id
entif
y,
and/
or c
ount
par
ticul
ar f
ixtu
re(s
). A
ll ex
terio
r lig
hts
with
in li
ne-o
f-si
ght
of t
he o
bser
ver
[Joh
n En
glis
h K
now
les]
wer
e de
scrib
ed w
ith
resp
ect
to f
ixtu
re t
ype
and
loca
tion.
Th
e fu
nctio
n of
lig
hts
was
de
duce
d by
the
obse
rver
; ho
wev
er, s
ubse
quen
t m
eetin
gs w
ith h
otel
m
anag
emen
t st
aff
insu
red
that
th
e co
rrec
t fu
nctio
nalit
y w
as
docu
men
ted
in e
ach
case
. L
ight
fix
ture
s w
ith l
amps
(lig
ht b
ulbs
) vi
sibl
e fr
om th
e be
ach
and
thos
e th
at w
ere
desi
gned
or p
ositi
oned
so
that
the
y w
ould
lik
ely
illum
inat
e th
e be
ach
wer
e co
nsid
ered
to
be
pote
ntia
lly p
robl
emat
ic.
N
ight
time
Ligh
ting
Surv
ey
In
coo
rdin
atio
n w
ith h
otel
man
agem
ent,
a ni
ghtti
me
light
ing
surv
ey w
as c
ondu
cted
on
foot
on
26 Ju
ly 2
006.
Dur
ing
the
nigh
ttim
e su
rvey
, eac
h lig
ht id
entif
ied
in th
e da
ytim
e su
rvey
was
loca
ted
and
eval
uate
d w
ith r
espe
ct t
o its
pot
entia
l ef
fect
on
sea
turtl
es.
Ligh
ts
unse
en d
urin
g th
e da
y, b
ut v
isib
le w
hen
emitt
ing
light
, w
ere
also
ev
alua
ted.
Eac
h lig
ht w
as ra
ted
and
rank
ed o
n a
scal
e of
1 to
3.
The
nigh
ttim
e su
rvey
inv
olve
d tw
o in
spec
tions
, one
bef
ore
mid
nigh
t and
one
afte
r mid
nigh
t, al
low
ing
for a
n ac
cura
te ra
nkin
g of
ea
ch in
divi
dual
ligh
t sou
rce
in th
e co
ntex
t of
chan
ging
bac
kgro
und
illum
inat
ion
of
diff
eren
t lig
htin
g co
nditi
ons
and
inte
nsiti
es
thro
ugho
ut t
he n
ight
. B
ecau
se p
artic
ular
ly b
right
lig
hts
less
en t
he
degr
ee o
r th
e ac
tual
brig
htne
ss o
f th
e lig
hts
behi
nd t
hem
, an
d be
caus
e so
me
light
s ar
e ex
tingu
ishe
d la
te a
t ni
ght
unde
r no
rmal
op
erat
ing
proc
edur
e, t
he o
bser
ver
was
abl
e to
use
the
seq
uent
ial
insp
ectio
ns
to
mor
e ac
cura
tely
ch
arac
teriz
e th
ose
light
s th
at
rem
aine
d.
The
Ligh
ts
Fo
llow
ing
are
the
surv
eyed
lig
hts
liste
d fr
om t
he m
ost
disr
uptiv
e (R
ank
3) t
o th
e le
ast
disr
uptiv
e (R
ank
1) f
or m
arin
e tu
rtles
. A
rank
of “
1” d
escr
ibes
indi
rect
ligh
t vis
ible
by
an o
bser
ver
on th
e be
ach,
but
not
like
ly to
pre
sent
a st
rong
attr
actio
n to
nes
ting
or
hatc
hing
tur
tles.
A r
ank
of “
2” d
escr
ibes
a v
isib
le g
lobe
, glo
win
g el
emen
t, la
mp,
or
refle
ctor
like
ly to
dis
orie
nt tu
rtles
, but
not
stro
ng
enou
gh to
cas
t a sh
adow
on
the
beac
h. A
nd a
rank
of “
3” d
escr
ibes
a
light
sou
rce
stro
ng e
noug
h to
cas
t a s
hado
w o
n th
e be
ach
rega
rdle
ss
of w
heth
er th
e ill
umin
atio
n is
dire
ct o
r ind
irect
.
Even
the
sm
alle
st l
ight
s ca
n ra
nk a
s a
“3”
if th
ey c
ast
a sh
adow
on
the
beac
h; t
heir
clos
e pr
oxim
ity t
o th
e be
ach
and
thei
r lo
w v
ertic
al p
lace
men
t nea
r the
hor
izon
can
be
just
as
diso
rient
atin
g as
a m
ore
pow
erfu
l lig
ht fu
rther
aw
ay.
The
“3”
rank
ing
light
s ha
ve
been
pla
ced
first
in th
e as
sess
men
t bec
ause
of t
heir
pote
ntia
lly m
ore
serio
us e
ffec
ts o
n m
arin
e tu
rtles
. T
he f
ocus
of
corr
ectiv
e ac
tions
sh
ould
beg
in w
ith th
ese
light
s, as
thei
r miti
gatio
n w
ill h
ave
the
mos
t si
gnifi
cant
impa
ct o
n th
e be
ach
envi
ronm
ent.
W
ithin
eac
h ra
nk –
1, 2
, 3 –
fixt
ures
list
ed fi
rst a
re e
xpec
ted
to r
equi
re t
he g
reat
est
atte
ntio
n ei
ther
in
num
ber,
expe
nse,
or
crea
tivity
. Th
e lis
t con
tinue
s th
roug
h fix
ture
s th
at a
re p
rogr
essi
vely
si
mpl
er a
nd/o
r ch
eape
r to
miti
gate
. F
or e
ach
light
the
num
ber
of
fixtu
res
visi
ble
from
the
bea
ch,
the
fixtu
re t
ype,
loc
atio
n, r
ank,
co
mm
ents
(if
an
y),
func
tion,
pic
ture
an
d re
com
men
datio
ns
are
docu
men
ted.
Eac
h re
com
men
datio
n is
spec
ific
to a
n in
divi
dual
ligh
t, an
d m
ay
incl
ude
one
or
man
y ex
plan
ator
y re
mar
ks.
So
me
reco
mm
enda
tions
will
per
tain
to m
itiga
ting
the
curr
ent f
ixtu
re; o
ther
s w
ill su
gges
t the
repl
acem
ent o
f a fi
xtur
e w
ith a
n al
tern
ativ
e.
Rec
omm
enda
tions
are
illu
stra
ted
by th
e fo
llow
ing:
Pe
rman
ently
elim
inat
e fix
ture
. So
me
case
s are
spec
ific
to th
e nu
mbe
r of f
ixtu
res.
Rep
ositi
on fi
xtur
e to
land
war
d si
de o
f tre
e or
obj
ect.
Aim
fixt
ure
away
from
the
beac
h.
R
epla
ce e
xist
ing
fixtu
re w
ith a
mor
e di
rect
ed a
nd f
unct
iona
l bol
lard
w
ith e
xter
nal l
ouve
rs.
Rep
lace
exi
stin
g fix
ture
with
a m
ore
dire
cted
and
fun
ctio
nal
path
lig
ht th
at is
pos
ition
ed a
s to
not
dire
ctly
or
indi
rect
ly il
lum
inat
e th
e be
ach.
In
stal
l low
wat
tage
(50
wat
ts o
r les
s) y
ello
w b
ug li
ght b
ulb.
In
stal
l com
pact
fluo
resc
ent T
urtle
Saf
e Li
ghtin
g la
mps
(lig
ht b
ulbs
).
See
INT
ER
NE
T R
ESO
UR
CE
S.
R
epla
ce
exis
ting
fixtu
re
with
a
mor
e di
rect
ed
and
func
tiona
l do
wnl
ight
.
Inst
all h
ood
of su
ffic
ient
dep
th a
nd w
idth
.
R
educ
e in
tens
ity o
f lig
ht o
r low
er w
atta
ge.
Pl
ant,
land
scap
e, o
r im
prov
e na
tive
vege
tatio
n bu
ffer
so
that
ligh
t is
scre
ened
and
not
dire
ctly
vis
ible
from
the
beac
h.
K
eep
light
s of
f whe
n no
t in
use,
esp
ecia
lly fo
r lig
hts
that
are
clo
sest
to
the
bea
ch.
Info
rm g
uest
s vi
a ta
ble
tent
s, do
or h
ange
rs,
or o
ther
ed
ucat
iona
l m
ater
ials
(e.
g. t
he i
nfor
mat
ion
book
lets
in
each
roo
m)
abou
t fix
ture
s und
er th
eir c
ontro
l.
Elim
inat
e fix
ture
s and
use
low
tabl
e la
mps
(suc
h as
Aur
elle
LED
C
andl
e Se
ries o
r Max
xim
a M
LC-0
1 LE
D F
lam
eles
s Can
dle)
or
cand
les.
This
wou
ld se
rve
the
purp
ose
of il
lum
inat
ing
the
tabl
es
with
out u
nint
ende
d br
oadc
ast o
ut o
f the
rest
aura
nt.
U
se d
imm
er to
less
en th
e ef
fect
of
indi
rect
ligh
t lea
ving
the
dini
ng
area
.
In
stal
l red
filte
r
Ex
tingu
ish
whe
n no
t in
use.
Tre
e m
ount
ed h
oode
d sp
otlig
ht
Rank
: 3
Num
ber o
f fix
ture
s: 2
1 Li
ght L
ocat
ion:
Mou
nted
on
coco
nut p
alm
s/ca
suar
inas
beg
inni
ng a
t B
blo
ck a
nd c
ontin
uing
eas
t to
the
end
of th
e pr
oper
ty
Com
men
ts:
The
bes
t op
tion
is t
o el
imin
ate
the
light
, ei
ther
by
turn
ing
them
all
off o
r rem
ovin
g th
e fix
ture
s. If
all
light
s ca
nnot
be
rem
oved
or
turn
ed o
ff, t
hen
it is
rec
omm
ende
d th
at t
he n
umbe
r of
lig
hts
(cur
rent
ly 2
1) a
nd w
atta
ge o
f ea
ch l
amp
be r
educ
ed.
Som
e lig
hts
coul
d al
so b
e lo
wer
ed.
The
inst
alla
tion
of y
ello
w b
ug li
ghts
is
also
rec
omm
ende
d.
Ligh
ts t
hat
poin
t di
rect
ly t
owar
ds t
he b
each
sh
ould
be
repo
sitio
ned.
Fo
r th
e pu
rpos
e of
illu
min
atin
g th
e ho
tel
grou
nds i
n th
is a
rea,
low
pro
file
light
s are
pre
ferr
ed.
Re
com
men
datio
ns o
n th
e nu
mbe
r of f
ixtu
res:
Re
com
men
datio
ns o
n ex
istin
g or
rem
aini
ng fi
xtur
es:
Ulti
mat
e re
com
men
datio
n:
Post
mou
nted
glo
be li
ght
Po
st m
ount
ed li
ght w
ithou
t glo
be fi
xtur
e
Rank
: 3
Num
ber o
f fix
ture
s: 1
6 Li
ght L
ocat
ion:
Wat
erfr
ont R
esta
uran
t C
omm
ents
: D
urin
g th
e fe
w
nigh
ts
a w
eek
of
oper
atio
n,
the
Wat
erfr
ont
Res
taur
ant
pres
ents
a u
niqu
e ca
se t
hat
can
be e
asily
m
itiga
ted.
The
cur
rent
ligh
ts a
re a
sou
rce
of d
irect
ligh
t on
the
beac
h an
d th
eir
repl
acem
ent
with
a m
oder
n al
tern
ativ
e is
enc
oura
ged.
Ea
rthw
orks
cou
ld p
ossi
bly
desi
gn s
uch
a fix
ture
ther
eby
incr
easi
ng
the
qual
ity o
f th
e be
ach,
the
res
taur
ant,
and
supp
ortin
g th
e lo
cal
econ
omy.
In
add
ition
, st
rate
gic
land
scap
ing
can
be e
mpl
oyed
to
conc
eal
the
curr
ent
fixtu
res
from
the
bea
ch, a
tas
k se
emin
gly
wel
l em
ploy
ed b
y th
e Tu
rtle
Bea
ch R
esor
t with
its l
ush
hote
l gro
unds
.
Reco
mm
enda
tions
on
exis
ting
fixtu
res:
U
ltim
ate
reco
mm
enda
tions
:
Ora
nge
flood
/sta
ge li
ght
Ra
nk:
3 N
umbe
r of f
ixtu
res:
1
Ligh
t Loc
atio
n: O
verh
and
of re
stau
rant
C
omm
ents
: W
hen
the
light
is
on (
durin
g a
perf
orm
ance
) it
does
re
ach
the
beac
h.
Stra
tegi
c la
ndsc
apin
g co
uld
conc
eal
light
(e.
g.
nativ
e ve
geta
tion
that
surr
ound
s the
Jacu
zzi a
rea)
. Re
com
men
datio
ns:
Cei
ling
mou
nted
col
ored
spot
light
Ra
nk:
3 N
umbe
r of f
ixtu
res:
4
Ligh
t Loc
atio
n: C
eilin
g of
Wat
erfr
ont R
esta
uran
t C
omm
ents
: A
red
filte
red
light
is p
refe
rred
ove
r oth
er c
olor
s. L
ight
s do
n’t s
eem
to b
e of
con
cern
sinc
e th
ey a
re ra
rely
use
d.
Reco
mm
enda
tions
:
Wal
l mou
nted
dow
nlig
ht
Ra
nk:
2 N
umbe
r of f
ixtu
res:
62
Ligh
t Loc
atio
n: B
alco
nies
of C
blo
ck
Com
men
ts:
The
fix
ture
off
sets
the
bulb
fro
m th
e w
all r
educ
ing
the
amou
nt o
f “w
all w
ashi
ng”
that
can
occ
ur w
ith f
ixtu
res
flush
to th
e w
all.
Ins
talli
ng a
yel
low
bug
lig
ht b
ulb
will
gre
atly
min
imiz
e th
e ch
ance
s of
dis
rupt
ing
the
sea
findi
ng b
ehav
ior o
f mar
ine
turtl
es.
The
yello
w li
ght i
s als
o no
t vis
ible
to m
ost i
nsec
ts.
How
ever
, gue
sts n
eed
to b
e re
min
ded
to tu
rn li
ghts
off
whe
n no
t in
use.
Re
com
men
datio
ns:
Fluo
resc
ent a
nd in
cand
esce
nt b
ulbs
cov
ered
by
perf
orat
ed w
ood
box
Ra
nk:
2 N
umbe
r of f
ixtu
res:
16
Li
ght
Loca
tion:
Wat
erfr
ont
Res
taur
ant,
Bat
hroo
ms
at W
ater
fron
t R
esta
uran
t C
omm
ents
: T
he o
nly
fixtu
re v
isib
le f
rom
the
bea
ch i
s th
e on
e lo
cate
d at
the
wom
en’s
bat
hroo
m.
The
num
ber g
iven
is th
e nu
mbe
r of
fix
ture
s on
the
hot
el g
roun
ds.
The
se f
ixtu
res
are
enco
urag
ed
beca
use
the
bare
bul
b is
con
ceal
ed a
nd l
ight
is
dire
cted
dow
n.
How
ever
, a
yello
w b
ug l
ight
in
the
wom
en’s
bat
hroo
m f
ixtu
re i
s pr
efer
red
over
the
curr
ent w
hite
inca
ndes
cent
bul
b Re
com
men
datio
ns:
Smal
l bar
e sp
otlig
ht
Ra
nk:
2 N
umbe
r of f
ixtu
res:
3
Ligh
t Loc
atio
n: H
angi
ng a
bove
Res
taur
ant
Reco
mm
enda
tions
:
o
r
or
Roo
m li
ghts
Rank
: 1
Num
ber o
f bal
coni
es v
isib
le fr
om th
e be
ach:
172
Li
ght L
ocat
ion:
Oce
an v
iew
room
s Re
com
men
datio
ns
from
W
ither
ingt
on
and
Mar
tin
2003
on
“M
inim
izin
g be
ach
light
ing
from
indo
or so
urce
s”:
1. T
urni
ng o
ff l
ight
ing
in r
oom
s th
at a
re n
ot i
n us
e.
Rem
inde
r no
tices
pla
ced
on s
witc
hes
in o
cean
fron
t ro
oms
can
help
in
this
ef
fort.
2.
Rel
ocat
ing
mov
eabl
e la
mps
aw
ay f
rom
win
dow
s th
at a
re v
isib
le
from
the
beac
h.
3. T
intin
g or
app
lyin
g w
indo
w t
reat
men
ts t
o w
indo
ws
visi
ble
from
th
e be
ach
so th
at li
ght p
assi
ng fr
om in
side
to o
utsi
de is
sub
stan
tially
re
duce
d.
A g
ood
tinte
d gl
ass
or w
indo
w-ti
ntin
g tre
atm
ent
will
re
duce
vis
ible
ligh
t fro
m th
e in
side
to 4
5% o
r le
ss (
trans
mitt
ance
≤
45%
). W
indo
w g
lass
may
be
eith
er ti
nted
dur
ing
its m
anuf
actu
re o
r tin
ted
late
r w
ith a
n ap
plie
d fil
m.
Win
dow
tre
atm
ents
(sh
adin
g m
ater
ials
) ar
e le
ss p
erm
anen
t an
d ca
n re
duce
lig
ht t
rans
mitt
ance
m
ore
than
tint
s and
film
s can
. A
com
plet
e bl
ocki
ng o
f lig
ht is
idea
l.
4. C
losi
ng o
paqu
e cu
rtain
s or
blin
ds a
fter
dark
to c
ompl
etel
y co
ver
win
dow
s vi
sibl
e fr
om t
he b
each
. T
his
is a
n in
expe
nsiv
e so
lutio
n be
caus
e m
ost
hom
e w
indo
ws
have
cur
tain
s or
blin
ds t
o pr
ovid
e pr
ivac
y to
the
occu
pant
s (p.
22)
.
Pict
ure
1 of
wal
l mou
nted
dow
nlig
ht
Pi
ctur
e 2
of w
all m
ount
ed d
ownl
ight
Rank
: 1
Num
ber o
f fix
ture
s: 1
28
Ligh
t Loc
atio
n: B
alco
nies
of A
, B, D
and
E b
lock
Re
com
men
datio
ns:
Smal
l rec
esse
d ce
iling
spot
light
Ra
nk:
1 N
umbe
r of f
ixtu
res:
40
Li
ght L
ocat
ion:
Abo
ve d
oors
in E
blo
ck
Com
men
ts:
The
se l
ight
s ar
e ca
usin
g si
gnifi
cant
am
ount
s of
“w
all
was
h” i
n th
e co
rrid
or b
etw
een
D a
nd E
blo
ck a
s w
ell
as a
long
the
ba
ck o
f D b
lock
. C
umul
ativ
ely
they
are
pot
entia
lly d
isru
ptiv
e. T
he
num
ber g
iven
is th
e nu
mbe
r of f
ixtu
res
that
are
cau
sing
vis
ible
“w
all
was
h” f
rom
the
beac
h. O
ne o
ptio
n m
ight
be
to in
stal
l a R
30 a
mbe
r bu
g lig
ht o
r som
ethi
ng si
mila
r. S
ee IN
TE
RN
ET
RE
SOU
RC
ES.
Re
com
men
datio
ns:
Gre
en p
athw
ay li
ght
Ra
nk:
1 N
umbe
r of f
ixtu
res:
6
Ligh
t Loc
atio
n: S
idew
alk
to E
blo
ck
Reco
mm
enda
tions
:
Path
way
ligh
t
Ra
nk:
1 N
umbe
r of f
ixtu
res:
6
Ligh
t Loc
atio
n: A
roun
d po
ol a
rea
in fr
ont o
f C b
lock
/ pat
h fr
om k
id
pool
to D
and
E b
lock
C
omm
ents
: N
ot a
ll fix
ture
s are
vis
ible
from
bea
ch.
Reco
mm
enda
tions
:
Hoo
ded
spot
light
Ra
nk:
1 N
umbe
r of f
ixtu
res:
2
Ligh
t Loc
atio
n: G
rass
are
a in
fron
t of E
blo
ck
Com
men
ts:
Thi
s lig
ht d
oes
cont
ribut
e to
“w
all w
ash.
” T
he li
ght i
s no
t di
rect
ed u
p, w
hich
is
high
ly e
ncou
rage
d.
In t
he e
ffor
t to
ill
umin
ate
the
law
n in
fro
nt o
f E
bloc
k ot
her
light
fix
ture
s ca
n be
em
ploy
ed t
hat
do n
ot u
nint
entio
nally
ref
lect
lig
ht o
ff t
he w
alls
of
build
ings
.
Reco
mm
enda
tions
:
o
r
Up
dire
cted
hoo
ded
spot
light
Ra
nk:
1 N
umbe
r of f
ixtu
res:
3
Ligh
t Loc
atio
n: G
roun
d of
the
Jacu
zzi a
rea
Reco
mm
enda
tion
on e
xist
ing
fixtu
res:
U
ltim
ate
reco
mm
enda
tions
:
o
r
Gre
en fl
oodl
ight
Ra
nk:
1 N
umbe
r of f
ixtu
res:
2
Ligh
t Loc
atio
n: Ja
cuzz
i are
a C
omm
ents
: St
rate
gic
land
scap
ing
coul
d co
ncea
l ill
umin
ated
ve
geta
tion.
Re
com
men
datio
n on
exi
stin
g fix
ture
s:
U
ltim
ate
reco
mm
enda
tion:
Dow
nlig
ht
Ra
nk:
1 N
umbe
r of f
ixtu
res:
1
Ligh
t Loc
atio
n: R
afte
rs o
f Res
taur
ant
Com
men
ts:
Reco
mm
enda
tions
:
o
r
or
or
Tik
i tor
ch w
ith o
pen
flam
e
Ra
nk:
Lig
hts o
ff
Num
ber o
f fix
ture
s: 1
0 Li
ght L
ocat
ion:
Aro
und
Wat
erfr
ont R
esta
uran
t at e
dge
of v
eget
atio
n an
d al
ong
mai
n en
tranc
e of
bea
ch
Com
men
ts:
The
num
ber
give
n w
as th
e nu
mbe
r of
tiki
torc
hes
that
w
ere
out a
nd v
isib
le d
urin
g th
e tim
e of
the
asse
ssm
ent.
Re
com
men
datio
ns:
SUM
MA
RY
The
Turtl
e B
each
Res
ort i
s co
mm
ende
d in
reta
inin
g so
me
of
the
best
ligh
ting
cond
ition
s ob
serv
ed a
t any
bea
chfr
ont h
otel
on
the
isla
nd.
Firs
t, tu
rtle
frie
ndly
fix
ture
s ar
e in
stal
led
on a
ll ba
lcon
ies.
Th
ese
fixtu
res
are
idea
l be
caus
e th
e ba
re b
ulb
is r
eces
sed
and
conc
eale
d, p
reve
ntin
g di
rect
lig
ht r
each
ing
the
beac
h.
In a
dditi
on,
the
fixtu
res
are
offs
et f
rom
the
wal
l re
duci
ng t
he a
mou
nt “
wal
l w
ash.
” S
econ
d, n
ativ
e ve
geta
tion
is u
sed
as a
scr
een,
red
ucin
g th
e am
ount
of
light
rea
chin
g th
e be
ach.
Th
ird,
the
wat
ersp
orts
sta
nd
does
not
hav
e an
y ex
terio
r lig
htin
g.
Man
y su
ch b
each
fron
t st
ands
of
ten
have
ext
erio
r lig
htin
g an
d le
ad t
o ex
trem
e di
sorie
ntat
ion
of
mar
ine
turtl
es.
Last
ly, i
t is
obse
rved
that
som
e of
the
tree
mou
nted
sp
otlig
hts
are
disc
onne
cted
to
inte
ntio
nally
red
uce
diso
rient
atio
n of
ha
tchl
ings
.
N
ever
thel
ess,
ther
e is
stil
l ro
om f
or i
mpr
ovem
ents
. F
or
inst
ance
, stra
tegi
c la
ndsc
apin
g sh
ould
be
cont
inue
d as
this
is o
ne o
f th
e ea
sies
t w
ays
to r
educ
e be
achf
ront
lig
htin
g.
Als
o, b
ug l
ight
s sh
ould
be
inst
alle
d in
all
balc
ony
fixtu
res.
Bug
lig
hts
emit
a w
avel
engt
h th
at
is
less
at
tract
ive
to
hatc
hlin
gs,
as
wel
l as
m
osqu
itoes
. It
is a
lso
reco
mm
ende
d th
at th
e nu
mbe
r of t
ree
mou
nted
sp
otlig
ht b
e re
duce
d or
low
ered
. T
he i
llum
inat
ion
of t
he h
otel
gr
ound
s ca
n ea
sily
be
acco
mpl
ishe
d by
low
pro
file
path
ligh
ts.
It is
im
porta
nt to
rem
embe
r th
at b
each
fro
nt li
ghts
sho
uld
be tu
rned
off
w
hen
not
in u
se.
Thi
s in
clud
es s
oda
mac
hine
s, te
levi
sion
s, an
d de
cora
tive
light
ing
(e.g
. stri
ng li
ghts
on
the
band
sta
nd).
As
far
as
deco
rativ
e lig
htin
g is
con
cern
ed, r
ed l
ight
is
alw
ays
pref
erre
d ov
er
gree
n or
whi
te (e
.g. r
ope
light
ing
alon
g th
e po
ol b
ridge
s).
Th
e fe
w re
com
men
datio
ns, o
nce
impl
emen
ted,
will
not
onl
y im
prov
e be
ach
cond
ition
s fo
r m
arin
e tu
rtles
, but
will
con
tribu
te t
o th
e ex
istin
g so
phis
ticat
ed t
hem
e in
lig
htin
g am
bian
ce o
f th
is r
esor
t w
hile
redu
cing
ope
ratio
nal e
xpen
ses
thro
ugh
an e
xpec
tatio
n of
low
er
ener
gy u
se.
To
enco
urag
e lig
htin
g im
prov
emen
ts a
nd a
ssis
t in
im
plem
enta
tion,
the
Tour
ism
Dev
elop
men
t Cor
pora
tion
is a
vaila
ble
to p
urch
ase
item
s (fix
ture
s, C
F bu
g lig
hts)
in b
ulk,
whi
ch w
ill fu
rther
re
duce
the
cost
of r
etro
fittin
g an
d in
nova
tion.
A
long
with
an
impr
oved
bea
chfr
ont
in t
erm
s of
lig
htin
g co
mes
a p
aral
lel
resp
onsi
bilit
y fo
r co
nser
vatio
n-m
inde
d be
achf
ront
m
anag
emen
t in
gen
eral
, in
clud
ing,
for
exa
mpl
e, s
tack
ing
beac
h ch
airs
to
ensu
re t
hat
mot
her
turtl
es a
re n
ot o
bstru
cted
dur
ing
thei
r cr
awl t
o an
d fr
om th
e w
ater
. Tu
rtle
Bea
ch R
esor
t pla
ys a
n es
sent
ial
role
in th
e su
rviv
al o
f the
end
ange
red
turtl
es th
at u
se it
s be
ache
s, an
d is
wel
l po
sitio
ned
to s
erve
as
a m
odel
for
sea
tur
tle f
riend
ly
envi
ronm
enta
l m
anag
emen
t sy
stem
s el
sew
here
in
Bar
bado
s an
d be
yond
. IN
TE
RN
ET
RE
SOU
RC
ES
Tu
rtle
safe
ligh
ting
prod
ucts
w
ww
.turtl
esaf
elig
htin
g.co
m
http
://w
ww
.turtl
esaf
elig
htin
g.co
m/T
urtle
Safe
%20
1.0/
prod
uct%
20sh
eet
s/Sn
apO
nFilt
er.p
df
CF
PAR
38
http
://w
ww
.pris
mae
cat.l
ight
ing.
phili
ps.c
om/L
ight
Site
/Whi
rlwin
d.as
px?
eca=
LNPP
LA&
cpf=
USN
PUS&
stg=
AC
T&la
n=U
S+&
ecu=
LMP%
7cPL
C%
7cN
P&cn
t_ke
y=C
I_PA
R38
%7c
PLC
&t=
1&tre
e=0&
scr_
md
=111
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y=18
85&
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_en&
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ht
tp://
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t.gel
ight
ing.
com
/Lig
htPr
oduc
ts/D
ispa
tche
r?R
EQU
EST=
CO
NSU
MER
SPEC
PAG
E&PR
OD
UC
TCO
DE=
2173
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ww
w.n
am.li
ghtin
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ilips
.com
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umer
/mar
atho
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y.ph
p?m
ode=
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R30
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ber B
ug L
ight
ht
tps:
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re.ls
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om/R
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ER-B
UG
-LIG
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LON
G-C
ON
E-P3
8C0.
aspx
?Use
rID
=535
513&
Sess
ionI
D=r
NFp
6CR
YN
JPrx
JVbs
KIr
L
ITE
RA
TU
RE
CIT
ED
WIT
HER
ING
TON
, B. E
. and
R. E
. MA
RTI
N. 2
003.
Und
erst
andi
ng,
asse
ssin
g,
and
reso
lvin
g lig
ht-p
ollu
tion
prob
lem
s on
se
a tu
rtle
nest
ing
beac
hes.
3rd
ed.
rev.
Flo
rida
Mar
ine
Res
earc
h In
stitu
te
Tech
nica
l Rep
ort T
R-2
. 73
p.
ECK
ERT,
K. L
. and
J. A
. HO
RR
OC
KS
(Edi
tors
). 20
02. P
roce
edin
gs
of “
Sea
Turtl
es a
nd B
each
fron
t Lig
htin
g: A
n In
tera
ctiv
e W
orks
hop
for
Indu
stry
Pro
fess
iona
ls a
nd P
olic
y-M
aker
s in
Bar
bado
s”,
13
Oct
ober
20
00.
Spon
sore
d by
th
e W
ider
C
arib
bean
Se
a Tu
rtle
Con
serv
atio
n N
etw
ork
(WID
ECA
ST),
the
Bar
bado
s Se
a Tu
rtle
Proj
ect,
and
the
Tour
ism
Dev
elop
men
t C
orpo
ratio
n of
Bar
bado
s. W
IDEC
AST
Tec
hnic
al R
epor
t 1. v
+ 4
3 pp
. A
CK
NO
WL
ED
GM
EN
TS
I
am d
eepl
y in
debt
ed t
o th
e st
aff
and
man
agem
ent
of t
he
Turtl
e B
each
Res
ort,
incl
udin
g A
dria
n G
rant
, G
ener
al M
anag
er,
Stev
en
John
, A
ssis
tant
M
aint
enan
ce
Supe
rvis
or,
and
Woo
drow
Tr
otm
an,
Mai
nten
ance
Sup
ervi
sor
for
thei
r co
llabo
ratio
n in
thi
s as
sess
men
t. T
hey
wer
e ex
traor
dina
rily
kind
in
acco
mm
odat
ing
my
requ
ests
, w
hich
ofte
n in
volv
ed t
heir
wor
king
off
-hou
rs,
incl
udin
g la
te a
t nig
ht.
Equa
lly im
porta
nt, t
he a
sses
smen
t wou
ld n
ot h
ave
been
po
ssib
le w
ithou
t the
for
esig
ht a
nd f
inan
cial
sup
port
of th
e To
uris
m
Dev
elop
men
t C
orpo
ratio
n of
B
arba
dos.
I
wou
ld
also
lik
e to
re
cogn
ize
the
tirel
ess
effo
rts o
f th
e B
arba
dos
Sea
Turtl
e Pr
ojec
t,
espe
cial
ly D
r. Ju
lia H
orro
cks,
Bar
ry K
rueg
er a
nd th
eir 2
006
seas
onal
st
aff.
The
pro
fess
iona
l wor
k of
the
BST
P ha
s se
t a h
igh
stan
dard
for
rese
arch
and
con
serv
atio
n in
Bar
bado
s an
d th
roug
hout
the
Car
ibbe
an
regi
on.
With
out
thei
r co
llabo
ratio
n, i
nclu
ding
pro
vidi
ng m
e w
ith
hous
ing,
trai
ning
, acc
ess
to d
ata
and
othe
r tec
hnic
al in
form
atio
n, a
nd
the
oppo
rtuni
ty to
con
tribu
te to
thei
r im
porta
nt fi
eld
wor
k, w
hich
has
be
en p
rofe
ssio
nally
and
per
sona
lly e
nric
hing
for
me,
thi
s lig
htin
g as
sess
men
t cou
ld n
ot h
ave
been
acc
ompl
ishe
d. F
inal
ly, I
am
gra
tefu
l to
Dr.
Kar
en E
cker
t, Ex
ecut
ive
Dire
ctor
of
WID
ECA
ST a
nd m
y ac
adem
ic a
dvis
or a
t D
uke
Uni
vers
ity’s
Nic
hola
s Sc
hool
of
the
Envi
ronm
ent,
for
her
enco
urag
emen
t of
m
y ef
forts
an
d he
r le
ader
ship
in C
arib
bean
sea
turtl
e co
nser
vatio
n is
sues
in g
ener
al, a
nd
to E
rik M
artin
of
Ecol
ogic
al A
ssoc
iate
s, In
c. f
or h
is k
indn
ess
and
patie
nce
in t
rain
ing
me
in t
he p
roto
cols
of
prof
essi
onal
bea
chfr
ont
light
ing
asse
ssm
ents
, a fi
eld
in w
hich
he
is w
ell-r
ecog
nize
d.
Appendix XI – Southern Palms Beach Club property map
Appendix XII – Southern Palms Beach Club assessment report
Nat
iona
l Ass
essm
ent o
f Bea
chfro
nt L
ight
ing
and
its
Effe
ct o
n th
e Su
rviv
al o
f End
ange
red
Mar
ine
Turtl
es
in B
arba
dos,
Wes
t Ind
ies
Prop
erty
Ass
essm
ent:
Sout
hern
Pal
ms
Beac
h C
lub
Re
spec
tfully
sub
mitt
ed
John
Eng
lish
Know
les
INT
RO
DU
CT
ION
In p
artn
ersh
ip w
ith th
e B
arba
dos
Sea
Turtl
e Pr
ojec
t (B
STP)
, lo
cal
affil
iate
of
the
Wid
er C
arib
bean
Sea
Tur
tle C
onse
rvat
ion
Net
wor
k (W
IDEC
AST
), an
d th
e To
uris
m D
evel
opm
ent C
orpo
ratio
n in
Bar
bado
s, a
form
al l
ight
ing
asse
ssm
ent
was
con
duct
ed a
t th
e So
uthe
rn P
alm
s B
each
Clu
b as
par
t of
a f
ollo
w-u
p in
itiat
ive
to
impl
emen
t re
com
men
datio
ns m
ade
at a
nat
iona
l “S
ea T
urtle
s an
d B
each
fron
t Lig
htin
g” w
orks
hop
held
in 2
000
(Eck
ert a
nd H
orro
cks,
2002
). Th
e ev
alua
tion
of l
ight
ing
asso
ciat
ed w
ith t
he S
outh
ern
Palm
s Bea
ch C
lub
prop
erty
atte
sts t
o th
e ef
forts
and
ded
icat
ion
of th
e ho
tel i
ndus
try a
nd th
e B
STP
in im
prov
ing
the
cond
ition
s of
arti
ficia
l be
ach
light
ing,
whi
ch i
s w
ell
know
n to
be
detri
men
tal
to b
oth
hatc
hlin
gs a
nd n
estin
g se
a tu
rtles
(Eck
ert a
nd H
orro
cks,
2002
).
The
Sout
hern
Pal
ms
Bea
ch C
lub
has
iden
tifie
d its
elf
as a
le
ader
in a
ddre
ssin
g th
e lig
htin
g pr
oble
m b
y vo
lunt
arily
par
ticip
atin
g in
thi
s as
sess
men
t. T
he p
rope
rty –
alo
ng w
ith f
our
(4)
othe
r be
achf
ront
hot
els
– w
as c
hose
n be
caus
e it
play
s a
cruc
ial r
ole
in th
e qu
ality
of
sea
turtl
e ne
stin
g ha
bita
t. T
he i
nten
t of
the
lig
htin
g as
sess
men
t w
as t
o ev
alua
te c
urre
nt c
ondi
tions
, an
d to
pro
pose
so
lutio
ns
and
reco
mm
enda
tions
fo
r ea
ch
light
id
entif
ied
as
cont
ribut
ing
to th
e no
ctur
nal i
llum
inat
ion
of th
e ne
stin
g be
ach.
Th
e at
tent
ion
of s
uch
wor
k is
crit
ical
in th
e su
rviv
al o
f th
e ha
wks
bill
sea
turtl
e, E
retm
oche
lys
imbr
icat
a, a
crit
ical
ly e
ndan
gere
d sp
ecie
s w
orld
wid
e (c
f. IU
CN
Red
List
). B
arba
dos
play
s a
very
im
porta
nt r
ole
in t
he s
urvi
val
of t
his
spec
ies,
its s
outh
wes
t co
ast
havi
ng b
een
iden
tifie
d as
one
of t
he m
ost i
mpo
rtant
nes
ting
grou
nds
rem
aini
ng in
the
Wid
er C
arib
bean
Reg
ion.
A
rtific
ial
beac
hfro
nt
light
ing,
ch
arac
teriz
ed
as
“lig
ht
pollu
tion”
by
With
erin
gton
and
Mar
tin (
2003
, p.
V),
is t
he m
ost
serio
us c
onte
mpo
rary
thre
at to
the
surv
ival
of s
ea tu
rtles
in B
arba
dos
(Eck
ert
and
Hor
rock
s, 20
02).
Mar
ine
turtl
es a
re m
ost
sens
itive
to
shor
ter
wav
elen
gths
(bl
ues
and
gree
ns),
whi
ch t
hey
use
as a
sea
-
findi
ng c
ue.
Sho
rter
wav
elen
gths
are
als
o em
itted
by
whi
te l
ight
. W
hen
such
lig
hts
are
visi
ble
from
th
e be
ach,
th
e ef
fect
is
tre
men
dous
.
W
ither
ingt
on
and
Mar
tin
(200
3)
sugg
est
the
follo
win
g ap
proa
ch t
o m
itiga
te “
light
pol
lutio
n” b
y ei
ther
elim
inat
ing
the
fixtu
re o
r by
adju
stin
g w
avel
engt
h or
inte
nsity
: W
e ha
ve n
o re
liabl
e fo
rmul
a th
at c
an b
e us
ed t
o ca
lcul
ate
how
muc
h ea
ch li
ght s
ourc
e w
ill a
ffec
t se
a tu
rtles
. W
e do
kn
ow,
how
ever
, th
at i
f sp
ectra
l em
issi
ons
are
equi
vale
nt,
redu
cing
int
ensi
ty w
ill r
educ
e ef
fect
s, an
d if
inte
nsiti
es a
re
sim
ilar,
subs
titut
ing
less
attr
activ
e so
urce
s (li
ke y
ello
w b
ug
or r
ed l
ight
s) w
ill a
lso
redu
ce e
ffec
ts.
A s
ound
stra
tegy
, th
eref
ore,
wou
ld b
e to
red
uce
effe
cts
on s
ea t
urtle
s by
m
anip
ulat
ion
both
int
ensi
ty a
nd c
olor
. A
s fe
w l
ight
s as
pr
actic
able
sh
ould
be
us
ed,
and
for
light
ing
deem
ed
esse
ntia
l, lo
ng w
avel
engt
h lig
ht s
ourc
es s
houl
d re
plac
e m
ore
disr
uptiv
e lig
ht s
ourc
es a
nd i
nten
sity
sho
uld
be r
educ
ed b
y us
ing
lam
ps o
f min
imal
wat
tage
that
are
hou
sed
with
in w
ell-
dire
cted
fix
ture
s ai
med
dow
n an
d aw
ay f
rom
the
bea
ch (
p.
23).
In p
oint
, dire
ct li
ght o
n th
e be
ach
can
be h
ighl
y di
srup
tive
to
both
adu
lt tu
rtles
and
hat
chlin
gs, a
nd e
limin
atin
g so
urce
s of
dire
ct
light
rea
chin
g th
e be
ach
is p
refe
rred
ove
r al
l ot
her
cons
erva
tion
alte
rnat
ives
(W
ither
ingt
on a
nd M
artin
, 20
03).
In
circ
umst
ance
s w
here
elim
inat
ing
light
sou
rces
– e
ither
by
turn
ing
them
off
or
by
rem
ovin
g th
e fix
ture
s al
l to
geth
er
– is
no
t pr
actic
al,
seve
ral
alte
rnat
ives
are
ava
ilabl
e w
hich
dire
ct l
ight
mor
e ef
ficie
ntly
and
/or
shie
ld t
he s
ourc
e fr
om t
he b
each
. M
any
of t
hese
mod
ern
fixtu
res
also
pre
vent
“w
all w
ash”
(the
illu
min
atio
n of
the
side
or f
açad
e of
a
build
ing)
and
are
hig
hly
reco
mm
ende
d ov
er f
ixtu
res
that
exp
ose
a ba
re b
ulb
to th
e be
achf
ront
.
So f
ar,
mos
t of
the
dis
cuss
ion
abov
e ha
s be
en o
n ex
terio
r fix
ture
s;
how
ever
in
terio
r lig
htin
g is
al
so
a so
urce
of
“l
ight
po
llutio
n.”
The
crite
ria f
or i
dent
ifyin
g pr
oble
ms
caus
ed b
y in
door
lig
htin
g ar
e th
e sa
me
as t
hose
for
ide
ntify
ing
prob
lem
s ca
used
by
outd
oor
light
ing…
[A
s w
ith a
n ou
tdoo
r lig
ht, a
n]
indo
or li
ght i
s a p
robl
em if
it is
vis
ible
from
the
beac
h.
Indo
or li
ghtin
g fr
om b
uild
ings
that
are
clo
se to
the
beac
h, a
re
very
tall,
or h
ave
larg
e se
a-si
de w
indo
ws
caus
es th
e gr
eate
st
prob
lem
for
sea
tur
tles.
Bec
ause
ind
oor
light
ing
is u
sual
ly
not
mea
nt t
o lig
ht t
he o
utdo
ors,
the
unw
ante
d ef
fect
s of
in
door
lig
htin
g ca
n ea
sily
be
el
imin
ated
w
ithou
t co
mpr
omis
ing
the
inte
nded
fu
nctio
n of
th
e lig
ht
(With
erin
gton
and
Mar
tin, 2
003,
p. 2
2).
In tr
uth,
the
Sout
hern
Pal
ms B
each
Clu
b do
es n
ot h
ave
dire
ct
cont
rol
over
whi
ch r
oom
lig
hts
are
utili
zed
by g
uest
s. H
owev
er,
indo
or li
ghts
be
can
min
imiz
ed f
rom
rea
chin
g th
e be
ach
by s
impl
y in
form
ing
and
rem
indi
ng g
uest
s to
clo
se o
paqu
e cu
rtain
s du
ring
even
ing
hour
s whe
n ro
om li
ghts
are
on.
Th
e ho
tel
does
hav
e di
rect
con
trol
over
alm
ost
all
othe
r fix
ture
s, w
hich
cas
t lig
ht o
nto
or v
isib
le f
rom
the
beac
h.
It is
thes
e fix
ture
s tha
t mak
e up
the
bulk
of t
his a
sses
smen
t.
In
the
sect
ions
th
at
follo
w
I pr
ovid
e sp
ecifi
c re
com
men
datio
ns f
or m
itiga
tion
of t
hese
fix
ture
s, an
d de
tail
my
met
hods
and
res
ults
. I
f co
nstra
ints
hin
der
the
impl
emen
tatio
n of
pa
rticu
lar
reco
mm
enda
tions
, on
e op
tion
is t
hat
effe
ctiv
e ac
tion
be
take
n in
hig
h pr
iorit
y ca
ses
(Ran
k “3
” lig
hts,
see
MET
HO
DS)
and
th
at lo
wer
prio
rity
actio
ns b
e bu
dget
ed o
ver t
ime.
In
gen
eral
, and
in
keep
ing
with
the
deci
sion
s of
the
2000
“Se
a Tu
rtles
and
Bea
chfr
ont
Ligh
ting”
wor
ksho
p, r
ecom
men
datio
ns a
re b
ased
on
best
pra
ctic
es
and
curr
ent
scie
nce
as a
rticu
late
d by
With
erin
gton
and
Mar
tin
(200
3).
M
ET
HO
DS
Day
time
Ligh
ting
Surv
ey
A
bas
elin
e da
ytim
e lig
htin
g su
rvey
was
con
duct
ed o
n fo
ot o
n 25
Jul
y 20
06 b
y ob
serv
ing
light
ing
fixtu
res
and
bulb
s dire
ctly
vis
ible
fr
om th
e be
ach.
The
ent
ire p
rope
rty w
as a
cces
sed
to c
larif
y, id
entif
y,
and/
or c
ount
par
ticul
ar f
ixtu
re(s
). A
ll ex
terio
r lig
hts
with
in li
ne-o
f-si
ght
of t
he o
bser
ver
[Joh
n En
glis
h K
now
les]
wer
e de
scrib
ed w
ith
resp
ect
to f
ixtu
re t
ype
and
loca
tion.
Th
e fu
nctio
n of
lig
hts
was
de
duce
d by
the
obse
rver
; ho
wev
er, s
ubse
quen
t m
eetin
gs w
ith h
otel
m
anag
emen
t st
aff
insu
red
that
th
e co
rrec
t fu
nctio
nalit
y w
as
docu
men
ted
in e
ach
case
. L
ight
fix
ture
s w
ith l
amps
(lig
ht b
ulbs
) vi
sibl
e fr
om th
e be
ach
and
thos
e th
at w
ere
desi
gned
or p
ositi
oned
so
that
the
y w
ould
lik
ely
illum
inat
e th
e be
ach
wer
e co
nsid
ered
to
be
pote
ntia
lly p
robl
emat
ic.
N
ight
time
Ligh
ting
Surv
ey
In
coo
rdin
atio
n w
ith h
otel
man
agem
ent,
a ni
ghtti
me
light
ing
surv
ey w
as c
ondu
cted
on
foot
on
25 Ju
ly 2
006.
Dur
ing
the
nigh
ttim
e su
rvey
, eac
h lig
ht id
entif
ied
in th
e da
ytim
e su
rvey
was
loca
ted
and
eval
uate
d w
ith r
espe
ct t
o its
pot
entia
l ef
fect
on
sea
turtl
es.
Ligh
ts
unse
en d
urin
g th
e da
y, b
ut v
isib
le w
hen
emitt
ing
light
, w
ere
also
ev
alua
ted.
Eac
h lig
ht w
as ra
ted
and
rank
ed o
n a
scal
e of
1 to
3.
Th
e ni
ghtti
me
surv
ey i
nvol
ved
two
insp
ectio
ns, o
ne b
efor
e m
idni
ght a
nd o
ne a
fter m
idni
ght,
allo
win
g fo
r an
accu
rate
rank
ing
of
each
indi
vidu
al li
ght s
ourc
e in
the
cont
ext o
f ch
angi
ng b
ackg
roun
d ill
umin
atio
n of
di
ffer
ent
light
ing
cond
ition
s an
d in
tens
ities
th
roug
hout
the
nig
ht.
Bec
ause
par
ticul
arly
brig
ht l
ight
s le
ssen
the
degr
ee o
r th
e ac
tual
brig
htne
ss o
f th
e lig
hts
behi
nd t
hem
, an
d be
caus
e so
me
light
s ar
e ex
tingu
ishe
d la
te a
t ni
ght
unde
r no
rmal
op
erat
ing
proc
edur
e, t
he o
bser
ver
was
abl
e to
use
the
seq
uent
ial
insp
ectio
ns
to
mor
e ac
cura
tely
ch
arac
teriz
e th
ose
light
s th
at
rem
aine
d.
The
Ligh
ts
Fo
llow
ing
are
the
surv
eyed
lig
hts
liste
d fr
om t
he m
ost
disr
uptiv
e (R
ank
3) t
o th
e le
ast
disr
uptiv
e (R
ank
1) f
or m
arin
e tu
rtles
. A
rank
of “
1” d
escr
ibes
indi
rect
ligh
t vis
ible
by
an o
bser
ver
on th
e be
ach,
but
not
like
ly to
pre
sent
a st
rong
attr
actio
n to
nes
ting
or
hatc
hing
tur
tles.
A r
ank
of “
2” d
escr
ibes
a v
isib
le g
lobe
, glo
win
g el
emen
t, la
mp,
or
refle
ctor
like
ly to
dis
orie
nt tu
rtles
, but
not
stro
ng
enou
gh to
cas
t a sh
adow
on
the
beac
h. A
nd a
rank
of “
3” d
escr
ibes
a
light
sou
rce
stro
ng e
noug
h to
cas
t a s
hado
w o
n th
e be
ach
rega
rdle
ss
of w
heth
er th
e ill
umin
atio
n is
dire
ct o
r ind
irect
.
Even
the
sm
alle
st l
ight
s ca
n ra
nk a
s a
“3”
if th
ey c
ast
a sh
adow
on
the
beac
h; t
heir
clos
e pr
oxim
ity t
o th
e be
ach
and
thei
r lo
w v
ertic
al p
lace
men
t nea
r the
hor
izon
can
be
just
as
diso
rient
atin
g as
a m
ore
pow
erfu
l lig
ht fu
rther
aw
ay.
The
“3”
rank
ing
light
s ha
ve
been
pla
ced
first
in th
e as
sess
men
t bec
ause
of t
heir
pote
ntia
lly m
ore
serio
us e
ffec
ts o
n m
arin
e tu
rtles
. T
he f
ocus
of
corr
ectiv
e ac
tions
sh
ould
beg
in w
ith th
ese
light
s, as
thei
r miti
gatio
n w
ill h
ave
the
mos
t si
gnifi
cant
impa
ct o
n th
e be
ach
envi
ronm
ent.
W
ithin
eac
h ra
nk –
1, 2
, 3 –
fixt
ures
list
ed fi
rst a
re e
xpec
ted
to r
equi
re t
he g
reat
est
atte
ntio
n ei
ther
in
num
ber,
expe
nse,
or
crea
tivity
. Th
e lis
t con
tinue
s th
roug
h fix
ture
s th
at a
re p
rogr
essi
vely
si
mpl
er a
nd/o
r ch
eape
r to
miti
gate
. F
or e
ach
light
the
num
ber
of
fixtu
res
visi
ble
from
the
bea
ch,
the
fixtu
re t
ype,
loc
atio
n, r
ank,
co
mm
ents
(if
an
y),
func
tion,
pic
ture
an
d re
com
men
datio
ns
are
docu
men
ted.
Eac
h re
com
men
datio
n is
spec
ific
to a
n in
divi
dual
ligh
t, an
d m
ay
incl
ude
one
or
man
y ex
plan
ator
y re
mar
ks.
So
me
reco
mm
enda
tions
will
per
tain
to m
itiga
ting
the
curr
ent f
ixtu
re; o
ther
s w
ill su
gges
t the
repl
acem
ent o
f a fi
xtur
e w
ith a
n al
tern
ativ
e.
Rec
omm
enda
tions
are
illu
stra
ted
by th
e fo
llow
ing:
Pe
rman
ently
elim
inat
e fix
ture
. So
me
case
s are
spec
ific
to th
e nu
mbe
r or l
ocat
ion
of th
e fix
ture
s.
Rep
ositi
on fi
xtur
e to
the
land
war
d si
de o
f the
tree
or o
bjec
t. In
stal
l hoo
d, lo
wer
wat
tage
, and
aim
fixt
ure
away
from
the
beac
h.
A
im fi
xtur
e aw
ay fr
om th
e be
ach.
In
stal
l shi
eld
or m
ask
of su
ffic
ient
size
that
cov
ers a
n ar
ch o
f 180
° on
the
ocea
n si
de
Rep
lace
exi
stin
g fix
ture
with
a m
ore
dire
cted
and
fun
ctio
nal b
olla
rd
with
ext
erna
l lou
vers
.
R
epla
ce e
xist
ing
fixtu
re w
ith a
mor
e di
rect
ed a
nd f
unct
iona
l pa
th
light
, an
d re
-pos
ition
it
to
elim
inat
e an
y di
rect
(o
r in
dire
ct)
illum
inat
ion
of th
e be
ach.
In
stal
l low
wat
tage
(50
wat
ts o
r les
s) y
ello
w b
ug li
ght b
ulb.
In
stal
l com
pact
flu
ores
cent
Tur
tle S
afe
Ligh
ting
lam
ps (
light
bul
bs).
Se
e IN
TE
RN
ET
RE
SOU
RC
ES.
Rep
lace
exi
stin
g fix
ture
with
a m
ore
dire
cted
, m
ore
func
tiona
l do
wnl
ight
.
R
epla
ce e
xist
ing
fixtu
re w
ith a
mor
e di
rect
ed, m
ore
func
tiona
l ste
p lig
ht p
ositi
oned
to e
limin
ate
any
dire
ct (
or in
dire
ct)
illum
inat
ion
of
the
beac
h.
In
stal
l co
vers
or
filte
rs a
cros
s be
ach
faci
ng s
ides
of
fixtu
re t
o el
imin
ate
any
dire
ct (o
r ind
irect
) illu
min
atio
n of
the
beac
h.
In
stal
l hoo
d of
suff
icie
nt d
epth
and
wid
th.
Red
uce
inte
nsity
of l
ight
or l
ower
wat
tage
. Sh
ield
seaw
ard
side
of f
ixtu
res t
hat a
re v
isib
le fr
om th
e be
ach.
Pl
ant,
land
scap
e, o
r im
prov
e na
tive
vege
tatio
n bu
ffer
to
elim
inat
e an
y di
rect
(or i
ndire
ct) i
llum
inat
ion
of th
e be
ach.
In
stal
l ho
od,
aim
fix
ture
aw
ay f
rom
the
bea
ch,
and
conn
ect
to a
m
otio
n de
tect
or.
K
eep
light
s of
f w
hen
not i
n us
e, e
spec
ially
for
ligh
ts c
lose
st to
the
beac
h.
In
form
gu
ests
vi
a ta
ble
tent
s, do
or
hang
ers,
or
othe
r ed
ucat
iona
l mat
eria
ls a
bout
fixt
ures
und
er th
eir c
ontro
l.
W
hite
un-
hood
ed sp
otlig
ht
Rank
: 3
Num
ber o
f fix
ture
s: 1
7 Li
ght L
ocat
ion:
Coc
onut
pal
ms
from
just
eas
t of C
apri
to e
aste
rn e
nd
of p
rope
rty/L
ady
Smith
/roof
of
the
Khu
s K
hus
Bar
, Gar
den
Terr
ace
and
Off
the
Bar
/mai
n po
ol a
rea
Com
men
ts: L
ight
s se
rve
to il
lum
inat
e th
e be
ach
for s
ecur
ity c
amer
as
and
perc
eive
d gu
est s
afet
y.
Reco
mm
enda
tions
on
the
num
ber o
f fix
ture
s:
Reco
mm
enda
tions
on
exis
ting
or re
mai
ning
fixt
ures
:
Y
ello
w u
n-ho
oded
spot
light
Ra
nk:
3 N
umbe
r of f
ixtu
res:
16
Ligh
t Lo
catio
n: S
eaw
ard
side
of
trees
tha
t ar
e lo
cate
d fr
om t
he
wes
tern
end
to c
ente
r pro
perty
Re
com
men
datio
ns o
n th
e nu
mbe
r of f
ixtu
res:
Re
com
men
datio
ns o
n ex
istin
g or
rem
aini
ng fi
xtur
es:
Po
st m
ount
ed q
uadr
uple
glo
be
Rank
: 3
Num
ber o
f fix
ture
s: 1
5 Li
ght L
ocat
ion:
Lan
dwar
d si
de o
f be
ach
wal
l. T
hey
are
pres
ent o
n th
e be
ach
side
of
the
Car
lisle
roo
ms,
the
Palm
cou
rt an
d ar
ound
the
mai
n po
ol a
rea
in f
ront
of
the
lobb
y.
One
is v
isib
le b
etw
een
Lady
Sm
ith a
nd th
e B
anya
n C
ourt
Bui
ldin
g C
omm
ents
: T
hese
fix
ture
s at
tem
pt t
o pr
ovid
e en
ough
lig
ht f
or t
he
secu
rity
cam
eras
loc
ated
on
the
prop
erty
dur
ing
the
even
ing
hour
s (S
ee S
UM
MA
RY
). T
he r
ecom
men
datio
n gi
ven
is o
ne t
hat
only
co
nsid
ers
the
seco
ndar
y pu
rpos
e of
the
light
s, w
hich
is to
illu
min
ate
the
cour
tyar
d du
ring
the
even
ing
for
cros
sing
on
foot
. S
uch
illum
inat
ion
can
use
low
leve
ls o
f lig
ht.
In a
dditi
on, t
he s
ea w
all a
t So
uthe
rn P
alm
s B
each
Clu
b pr
ovid
es a
n ex
celle
nt o
paqu
e ob
ject
that
ca
n co
ncea
l low
pro
file
light
s.
Reco
mm
enda
tions
:
W
all m
ount
ed c
lay
cove
red
light
Si
de v
iew
of f
ixtu
re
Fi
xtur
e w
ith r
ain
shie
ld th
at a
lso
acts
to p
reve
nt w
all
was
h fr
om th
e up
dir
ecte
d lig
ht
Rank
: 3
Num
ber o
f fix
ture
s: 7
0 Li
ght L
ocat
ion:
Pre
sent
on
mos
t bal
coni
es
Com
men
ts:
The
clay
fix
ture
s sh
ield
the
bar
e bu
lb f
rom
the
bea
ch,
whi
ch i
s pr
efer
red
over
all
othe
r ba
lcon
y lig
ht a
nd w
all
mou
nted
lig
hts
on th
e pr
oper
ty.
Of t
he 7
0 fix
ture
s, th
e on
es w
ith ra
in s
hiel
ds
are
the
mos
t tu
rtle
frie
ndly
bec
ause
the
lig
ht i
s pr
even
ted
from
w
ashi
ng th
e w
all i
n an
up
dire
ctio
n.
Reco
mm
enda
tions
:
W
all m
ount
ed d
ownl
ight
Rank
: 3
Num
ber o
f fix
ture
s: 4
Li
ght
Loca
tion:
Sec
ond
floor
bal
cony
roo
ms
on e
aste
rn p
ortio
n of
th
e C
arlis
le R
oom
s Bui
ldin
g Re
com
men
datio
ns fo
r exi
stin
g fix
ture
s:
Ulti
mat
e re
com
men
datio
n:
W
all m
ount
ed u
plig
ht
Rank
: 3
Num
ber o
f fix
ture
s: 4
Li
ght
Loca
tion:
Firs
t flo
or r
oom
s on
eas
tern
end
of
the
Car
lisle
R
oom
s Bui
ldin
g Re
com
men
datio
ns fo
r exi
stin
g fix
ture
s:
Ulti
mat
e re
com
men
datio
n:
O
rang
e un
-hoo
ded
spot
light
Ra
nk:
3 N
umbe
r of f
ixtu
res:
3
Ligh
t Lo
catio
n: C
ocon
ut p
alm
s in
mai
n po
ol a
rea/
east
fac
e of
B
anya
n C
ourt
Bui
ldin
g C
omm
ents
: A
n or
ange
wav
elen
gth
is l
ess
disr
uptiv
e th
an a
pur
e w
hite
ligh
t, w
hich
em
it al
l wav
elen
gths
incl
udin
g th
e m
ost d
isru
ptiv
e (g
reen
and
blu
e).
Re
com
men
datio
ns:
Si
ngle
glo
be
Rank
: 3
Num
ber o
f fix
ture
s: 1
Li
ght L
ocat
ion:
Hed
ge o
n th
e be
ach
side
of t
he P
alm
Cou
rt B
uild
ing
Reco
mm
enda
tions
:
A
rch
mou
nted
inca
ndes
cent
ligh
t Ra
nk:
3 N
umbe
r of f
ixtu
res:
1
Ligh
t Loc
atio
n: A
rche
d ga
p of
con
cret
e di
vide
r bet
wee
n La
dy S
mith
an
d B
anya
n C
ourt
Bui
ldin
g Re
com
men
datio
ns:
C
olum
n m
ount
ed c
lay
fixtu
re w
ith a
n in
cand
esce
nt b
ulb
Rank
: 3
Num
ber o
f fix
ture
s: 2
Li
ght L
ocat
ion:
Circ
le T
erra
ce
Com
men
ts:
Rec
esse
d bu
lbs
are
pref
erre
d ov
er b
are
bulb
s fo
r be
ach
fron
t lig
htin
g.
Reco
mm
enda
tions
for e
xist
ing
fixtu
res:
Ulti
mat
e re
com
men
datio
n:
W
hite
un-
hood
ed in
cand
esce
nt b
ulbs
in sp
otlig
ht fi
xtur
es
Rank
: 3
Num
ber o
f fix
ture
s: 7
Li
ght L
ocat
ion:
Jas
min
e C
ourt
Bui
ldin
g/O
n tre
e ju
st w
est o
f Ban
yan
Cou
rt B
uild
ing/
Sund
ecks
of
C
resc
ent
Bea
ch
Bui
ldin
g/La
dy
Smith
/Hai
rdre
ssin
g Sa
lon
Bui
ldin
g Re
com
men
datio
ns:
C
lay
scon
ce u
plig
ht
Cla
y sc
once
dow
nlig
ht
Rank
: 3
Num
ber o
f fix
ture
s: 9
Li
ght L
ocat
ion:
Bal
coni
es o
n w
est f
ace
of P
alm
Cou
rt B
uild
ing
Com
men
ts:
The
curr
ent p
ositi
on o
f the
fixt
ures
indu
ces
“wal
l was
h.
The
light
can
be
dire
cted
mor
e ef
ficie
ntly
if fi
xtur
e w
as a
dow
nlig
ht
Reco
mm
enda
tions
:
Sm
all r
eces
sed
ceili
ng sp
otlig
ht
Rank
: 3
Num
ber o
f fix
ture
s: 1
00
Ligh
t Lo
catio
n:
Cei
ling
of
lobb
y,
Khu
s K
hus
Bar
, R
onde
lle
Res
taur
ant,
Gar
den
Terr
ace
Res
taur
ant,
Off
the
Bar
are
a C
omm
ents
: N
ot a
ll fix
ture
s ar
e vi
sibl
e fr
om b
each
, the
one
s th
at a
re
visi
ble
are
so a
t sha
rp a
ngle
s fro
m h
igh
up o
n th
e be
ach.
Re
com
men
datio
ns:
Sm
all r
eces
sed
ceili
ng in
cand
esce
nt li
ght b
ulb
fixtu
re
Rank
: 3
Num
ber o
f fix
ture
s: 1
7 Li
ght L
ocat
ion:
Ter
race
and
Khu
s Khu
s Bar
C
omm
ents
: N
ot a
ll ar
e vi
sibl
e fr
om b
each
. Th
e on
es a
t Khu
s K
hus
Bar
are
vis
ible
onl
y at
sha
rp a
ngle
s fr
om h
igh
up o
n th
e be
ach.
The
ro
of’s
low
ove
rhan
g pr
ovid
es g
ood
cove
r.
Reco
mm
enda
tions
:
L
arge
r re
cess
ed c
eilin
g in
cand
esce
nt li
ght b
ulb
fixtu
re
Rank
: 3
Num
ber o
f fix
ture
s: 3
Li
ght L
ocat
ion:
Wes
t end
of K
hus K
hus B
ar
Com
men
ts:
Ligh
ts
are
only
on
th
ree
nigh
ts
a w
eek
durin
g pe
rfor
man
ces
Reco
mm
enda
tions
:
W
all m
ount
ed g
lobe
ligh
t
Rank
: L
ight
s wer
e of
f, bu
t pro
babl
y ra
nk a
s a “
3” w
hen
on
Num
ber o
f fix
ture
s: 3
Li
ght L
ocat
ion:
Sec
ond
floor
bea
ch fr
ont b
alco
ny o
f Car
lisle
Roo
ms
Bui
ldin
g/Ja
smin
e C
ourt
Bui
ldin
g th
ird fl
oor
Com
men
ts:
The
use
of 2
5 or
40
wat
t bu
lbs
is e
ncou
rage
d, w
ith
emph
asis
pla
ced
on 2
5 w
att y
ello
w b
ug li
ght b
ulbs
. Re
com
men
datio
ns fo
r exi
stin
g fix
ture
s:
Ulti
mat
e re
com
men
datio
n:
R
oom
ligh
ts
Rank
: 2,
but
mos
t lik
ely
a ra
nk o
f “3”
for
room
s clo
sest
to th
e be
ach
Num
ber o
f roo
ms v
isib
le fr
om th
e be
ach:
53
Li
ght L
ocat
ion:
Bea
chfr
ont o
f hot
el
Reco
mm
enda
tions
fr
om
With
erin
gton
an
d M
artin
20
03
on
“Min
imiz
ing
beac
h lig
htin
g fr
om in
door
sour
ces”
: 1.
Tur
ning
off
lig
htin
g in
roo
ms
that
are
not
in
use.
R
emin
der
notic
es p
lace
d on
sw
itche
s in
oce
anfr
ont
room
s ca
n he
lp i
n th
is
effo
rt.
2. R
eloc
atin
g m
ovea
ble
lam
ps a
way
fro
m w
indo
ws
that
are
vis
ible
fr
om th
e be
ach.
3.
Tin
ting
or a
pply
ing
win
dow
tre
atm
ents
to
win
dow
s vi
sibl
e fr
om
the
beac
h so
that
ligh
t pas
sing
from
insi
de to
out
side
is s
ubst
antia
lly
redu
ced.
A
goo
d tin
ted
glas
s or
win
dow
-tint
ing
treat
men
t w
ill
redu
ce v
isib
le li
ght f
rom
the
insi
de to
45%
or
less
(tra
nsm
ittan
ce ≤
45
%).
Win
dow
gla
ss m
ay b
e ei
ther
tint
ed d
urin
g its
man
ufac
ture
or
tinte
d la
ter
with
an
appl
ied
film
. W
indo
w t
reat
men
ts (
shad
ing
mat
eria
ls)
are
less
per
man
ent
and
can
redu
ce l
ight
tra
nsm
ittan
ce
mor
e th
an ti
nts a
nd fi
lms c
an.
A c
ompl
ete
bloc
king
of l
ight
is id
eal.
4.
Clo
sing
opa
que
curta
ins
or b
linds
afte
r da
rk to
com
plet
ely
cove
r w
indo
ws
visi
ble
from
the
bea
ch.
Thi
s is
an
inex
pens
ive
solu
tion
beca
use
mos
t ho
me
win
dow
s ha
ve c
urta
ins
or b
linds
to
prov
ide
priv
acy
to th
e oc
cupa
nts (
p. 2
2).
G
reen
pat
h lig
ht
A
rchi
tect
ural
bol
lard
s with
ext
erna
l lou
vers
Rank
: 2
Num
ber o
f fix
ture
s: 2
Li
ght L
ocat
ion:
Mai
n po
ol a
rea
Com
men
ts:
The
pur
pose
of
illum
inat
ing
the
wal
king
pat
h by
thes
e lig
hts
is d
iffus
ed b
ecau
se o
f ot
her
light
s su
rrou
ndin
g th
e m
ain
pool
ar
ea.
How
ever
, the
se ty
pes
of p
ath
light
s ar
e hi
ghly
rec
omm
ende
d.
They
are
low
to
the
grou
nd a
nd e
ffic
ient
ly d
irect
lig
ht w
here
it
is
need
ed, r
educ
ing
unin
tend
ed b
road
cast
. If
des
ired,
the
re a
re o
ther
st
yles
of
path
lig
htin
g av
aila
ble
with
tur
tle f
riend
ly d
esig
ns (
See
INT
ER
NE
T R
ESO
UR
CE
S).
Ano
ther
cho
ice
of t
urtle
frie
ndly
lig
htin
g is
th
e bo
llard
.
(Pic
ture
d,
also
se
e IN
TE
RN
ET
R
ESO
UR
CE
S).
In a
ny c
ase,
bot
h pa
th l
ight
s an
d bo
llard
s sh
ould
ha
ve r
eces
sed
bulb
s, hi
dden
ref
lect
ors,
and
bug
light
s. B
olla
rds
shou
ld h
ave
exte
rnal
louv
ers .
Re
com
men
datio
ns
on
exis
ting
fixtu
re
and
unde
r ex
istin
g lig
ht
cond
ition
s:
Reco
mm
enda
tions
und
er d
arke
r lig
htin
g co
nditi
ons:
C
eilin
g m
ount
ed li
ght
Rank
: 2
Num
ber o
f fix
ture
s: 4
Li
ght
Loca
tion:
Wal
kway
bet
wee
n ki
tche
n bu
ildin
g an
d C
resc
ent
Bea
ch B
uild
ing
Com
men
ts:
Onl
y tw
o ar
e vi
sibl
e fr
om th
e be
ach.
Re
com
men
datio
ns:
Sm
all b
lack
pat
h lig
ht
Rank
: 1
Num
ber o
f fix
ture
s: 9
Li
ght L
ocat
ion:
Cou
rtyar
d of
Pal
m C
ourt
and
Lady
Sm
ith B
uild
ing.
Th
ey a
re a
lso
pres
ent
in t
he m
ain
pool
are
a.
In a
dditi
on, t
wo
are
loca
ted
in fr
ont o
f nor
th fa
ce o
f Pal
m C
ourt
Bui
ldin
g.
Reco
mm
enda
tions
:
Sp
otlig
ht
Rank
: L
ight
off
N
umbe
r of f
ixtu
res:
3
Ligh
t Lo
catio
n: P
lace
d ar
ound
bas
e of
sta
tue
in t
he c
ourty
ard
of
Palm
Cou
rt, Ja
smin
e C
ourt
and
Cap
ri B
uild
ings
C
omm
ents
: Fix
ture
s are
not
in u
se a
nd o
nly
one
bulb
is p
rese
nt.
Reco
mm
enda
tions
:
W
hite
un-
hood
ed w
all m
ount
ed sp
otlig
ht
Rank
: L
ight
off
N
umbe
r of f
ixtu
res:
1
Ligh
t Loc
atio
n: V
ery
north
end
of w
all o
n ha
irdre
ssin
g sa
lon
Reco
mm
enda
tions
:
SUM
MA
RY
The
effo
rts o
f th
e So
uthe
rn P
alm
s B
each
Clu
b do
not
go
unno
ticed
in t
heir
neve
r en
ding
que
st f
or i
mpr
ovem
ents
. Th
ey a
re
com
men
ded
on t
he i
nsta
llatio
n of
yel
low
spo
tligh
ts a
nd t
heir
clay
co
vere
d ba
lcon
y lig
hts.
It is
obv
ious
the
hot
el c
onst
antly
stri
ves
to
prov
ide
a m
ore
suita
ble
beac
h en
viro
nmen
t, in
crea
sing
qua
lity
for i
ts
gues
ts a
nd tu
rtles
.
How
ever
, th
e im
pact
of
al
mos
t al
l ev
alua
ted
light
s is
co
mpo
unde
d fo
r tw
o re
ason
s. F
irst,
the
Sout
hern
Pal
ms
Bea
ch C
lub
prop
erty
is
elon
gate
d al
ong
the
ocea
n (a
ppro
xim
atel
y 10
00 f
eet).
Se
cond
, thi
s el
onga
ted
edge
of
the
prop
erty
is d
irect
ly o
n to
p of
the
beac
h w
ith li
ttle
or n
o se
t bac
k. T
his
plac
es li
mita
tions
on
stra
tegi
c la
ndsc
apin
g an
d in
crea
ses
the
effe
cts
of e
ven
the
smal
lest
lig
hts.
H
owev
er,
solu
tions
are
ava
ilabl
e to
mee
t th
e ne
eds
of b
oth
gues
ts
and
mar
ine
turtl
es.
The
y w
ill h
ave
to in
volv
e cr
eativ
ity a
nd a
cle
ar
unde
rsta
ndin
g of
ligh
t-pol
lutio
n pr
even
tion.
The
rank
ing
syst
em c
an b
e us
ed a
s a
guid
e in
und
erst
andi
ng
why
ligh
ts a
re m
ore
disr
uptiv
e to
turtl
es th
an o
ther
s. Id
eally
, a s
core
of
zer
o is
pre
ferr
ed, w
here
ther
e ar
e no
ligh
ts v
isib
le o
r det
ecte
d fr
om
the
beac
h.
Mov
ing
from
idea
l to
real
ity, a
ran
k of
“1”
is p
refe
rred
ov
er a
rank
of “
2”, w
hich
is p
refe
rred
ove
r a ra
nk o
f “3”
. H
owev
er,
even
if a
pro
perty
con
tain
s on
ly th
e le
ast d
isru
ptiv
e lig
hts
(Ran
k 1)
, th
ere
will
stil
l be
moo
nles
s ni
ghts
whe
re e
ven
the
smal
lest
and
di
mm
est
light
s ca
n ha
ve a
n ef
fect
. T
he r
anki
ng s
yste
m c
an a
lso
allo
w o
ne t
o ra
tche
t do
wn
the
effe
ct o
f a
light
. Fo
r ex
ampl
e, i
f a
light
ran
ks a
s a
“3”,
the
n it
is i
mpo
rtant
to
cons
ider
wha
t ac
tions
m
ight
dec
reas
e it
to a
rank
of “
2.”
The
num
ber
of l
ight
s is
als
o im
porta
nt.
Few
er l
ight
s ar
e pr
efer
red
over
man
y lig
hts.
For
inst
ance
, if
ther
e ar
e fif
ty r
ed a
nd
yello
w li
ghts
on
the
beac
h, th
en th
e fa
ct r
emai
ns th
at th
ere
are
still
fif
ty li
ghts
on
the
beac
h. E
ven
if th
e lig
hts
are
filte
red,
few
er li
ghts
ar
e al
way
s rec
omm
ende
d.
As
for
filte
rs, i
t is
impo
rtant
that
pro
per
ones
are
ins
talle
d.
Ther
e ar
e m
any
yello
wed
col
ored
ligh
ts a
vaila
ble
on th
e m
arke
t tha
t ar
e no
t mon
ochr
omat
ic a
nd a
lthou
gh th
ey m
ight
app
ear y
ello
w to
the
hum
an
eye,
ha
tchl
ings
m
ight
pe
rcei
ve
diff
eren
t w
avel
engt
hs
(esp
ecia
lly s
horte
r w
avel
engt
hs o
f w
hich
the
y ar
e at
tract
ed t
o).
It
has
been
sho
wn
that
the
lea
st d
isru
ptiv
e lig
hts
to h
atch
lings
are
ye
llow
bug
ligh
ts o
r lig
hts o
f a p
ure
yello
w w
avel
engt
h.
It
is p
ossi
ble
to h
ave
both
a tu
rtle
frie
ndly
bea
ch in
term
s of
lig
htin
g an
d a
secu
re p
rope
rty.
Acc
ordi
ng t
o W
ither
ingt
on,
“lig
ht
illum
inan
ce l
evel
s ne
cess
ary
for
safe
ty a
nd s
ecur
ity a
re r
athe
r lo
w
(0.2
-1.0
fo
otca
ndle
s or
2-
11
lux,
re
com
men
ded
for
fenc
e [o
r pe
rimet
er] s
ecur
ity a
nd p
arki
ng a
reas
)” (p
. 21)
. Th
e de
cisi
on to
use
be
ach
fron
t cam
eras
at n
ight
, whi
ch re
quire
s a
sign
ifica
nt a
mou
nt o
f lig
htin
g fo
r re
solu
tion
purp
oses
as
an a
dded
sec
urity
mea
sure
mus
t be
eva
luat
ed c
lose
ly.
Whe
n co
nsid
erin
g ex
tra s
ecur
ity m
easu
res
for
a pr
oper
ty s
ever
al q
uest
ions
mig
ht a
rise.
W
hy i
s So
uthe
rn P
alm
s B
each
Clu
b on
e of
the
few
hot
els
oper
atin
g be
achf
ront
cam
eras
at
nigh
t?
Is i
t po
ssib
le f
or b
each
cam
eras
to
be u
sed
durin
g th
e da
y on
ly?
Can
nig
httim
e us
e of
cam
eras
be
rese
rved
for
sec
tions
of
the
prop
erty
tha
t w
ill n
ot i
ndire
ctly
dis
orie
ntat
e m
arin
e tu
rtle?
C
an
stra
tegi
c pl
acem
ent
of m
otio
n de
tect
ing
light
s be
use
d to
ale
rt se
curit
y pe
rson
nel w
hen
a pa
rticu
lar a
rea
is c
ross
ed b
y an
obj
ect o
f a
certa
in h
eigh
t, w
hich
will
avo
id d
etec
tion
of a
nim
als,
such
as
cats
?
Can
inf
rare
d se
nsor
s be
pos
ition
ed a
long
a b
uild
ing’
s pe
rimet
er t
o al
ert
secu
rity
pers
onne
l w
hen
beam
s ar
e br
oken
(Se
e IN
TE
RN
ET
R
ESO
UR
CE
S)?
The
alte
rnat
ives
to e
xtra
sec
urity
mea
sure
s m
ight
w
ork
just
as
wel
l, if
not b
ette
r tha
n ca
mer
as.
In a
ny c
ase,
pro
vidi
ng
grea
ter s
ecur
ity fo
r gue
sts,
mor
e th
an th
e st
anda
rd se
curit
y pe
rson
nel,
is a
lway
s app
laud
ed a
nd e
ncou
rage
d.
If
the
dec
isio
n to
elim
inat
e ni
ghtti
me
use
of b
each
fro
nt
cam
eras
(al
ong
with
the
lig
hts)
is
impl
emen
ted,
the
n it
does
not
m
ean
the
area
s of
con
cern
hav
e to
go
in d
arkn
ess.
The
cou
rtyar
ds
can
be l
it by
low
pro
file
land
scap
e lig
hts,
path
lig
hts,
or b
olla
rds.
The
seaw
all p
rovi
des
the
idea
l opa
que
obje
ct fr
om w
hich
low
pro
file
light
s can
be
conc
eale
d.
Th
e re
com
men
datio
ns,
once
im
plem
ente
d, w
ill n
ot o
nly
impr
ove
beac
h co
nditi
ons
for
mar
ine
turtl
es, b
ut w
ill c
ontri
bute
to
the
exis
ting
soph
istic
ated
the
me
in l
ight
ing
ambi
ance
of
this
res
ort
whi
le re
duci
ng o
pera
tiona
l exp
ense
s th
roug
h an
exp
ecta
tion
of lo
wer
en
ergy
use
. T
o en
cour
age
light
ing
impr
ovem
ents
and
ass
ist
in
impl
emen
tatio
n, th
e To
uris
m D
evel
opm
ent C
orpo
ratio
n is
ava
ilabl
e to
pur
chas
e ite
ms (
fixtu
res,
CF
bug
light
s) in
bul
k, w
hich
will
furth
er
redu
ce th
e co
st o
f ret
rofit
ting
and
inno
vatio
n.
Th
e So
uthe
rn P
alm
s B
each
Clu
b pl
ays
an e
ssen
tial
role
in
the
surv
ival
of t
he e
ndan
gere
d tu
rtles
that
use
its
beac
hes,
and
is w
ell
posi
tione
d to
ser
ve a
s a
mod
el f
or s
ea tu
rtle
frie
ndly
env
ironm
enta
l m
anag
emen
t sys
tem
s els
ewhe
re in
Bar
bado
s and
bey
ond.
IN
TE
RN
ET
RE
SOU
RC
ES
M
anuf
actu
rers
and
Dis
tribu
tors
of P
ath
and
Land
scap
e Li
ghtin
g ht
tp://
ww
w.ru
udlig
htin
g.co
m/li
tera
ture
/land
scap
e_fa
mily
.asp
?msc
ssi
d=&
coni
d=&
dc=9
&vt
=12
ww
w.fx
l.com
A
rchi
tect
ural
Bol
lard
s ht
tp://
ww
w.g
reen
leel
ight
ing.
com
/PD
Fs/g
reen
lee/
data
shee
ts/A
BR
_AB
S_Se
ries.p
df
http
://w
ww
.acu
itybr
ands
light
ing.
com
/libr
ary/
PSG
/LL/
Out
door
%20
Lig
htin
g/Si
te%
20Li
ghtin
g/B
olla
rds/
KB
D.p
df
Man
ufac
ture
r of I
nfra
red
Det
ectio
n w
ww
.opt
exeu
rope
.com
Tu
rtle
safe
ligh
ting
prod
ucts
w
ww
.turtl
esaf
elig
htin
g.co
m
LIT
ER
AT
UR
E C
ITE
D
W
ITH
ERIN
GTO
N, B
. E. a
nd R
. E. M
AR
TIN
. 200
3. U
nder
stan
ding
, as
sess
ing,
an
d re
solv
ing
light
-pol
lutio
n pr
oble
ms
on
sea
turtl
e ne
stin
g be
ache
s. 3r
d ed
. re
v. F
lorid
a M
arin
e R
esea
rch
Inst
itute
Te
chni
cal R
epor
t TR
-2. 7
3 p.
EC
KER
T, K
. L. a
nd J
. A. H
OR
RO
CK
S (E
dito
rs).
2002
. Pro
ceed
ings
of
“Se
a Tu
rtles
and
Bea
chfr
ont L
ight
ing:
An
Inte
ract
ive
Wor
ksho
p fo
r In
dust
ry P
rofe
ssio
nals
and
Pol
icy-
Mak
ers
in B
arba
dos”
, 13
O
ctob
er
2000
. Sp
onso
red
by
the
Wid
er
Car
ibbe
an
Sea
Turtl
e C
onse
rvat
ion
Net
wor
k (W
IDEC
AST
), th
e B
arba
dos
Sea
Turtl
e Pr
ojec
t, an
d th
e To
uris
m D
evel
opm
ent
Cor
pora
tion
of B
arba
dos.
WID
ECA
ST T
echn
ical
Rep
ort 1
. v +
43
pp.
AC
KN
OW
LE
DG
ME
NT
S
I am
dee
ply
inde
bted
to
the
staf
f an
d m
anag
emen
t of
the
So
uthe
rn
Palm
s B
each
C
lub,
in
clud
ing
Brit
ta
Polla
rd,
Gen
eral
M
anag
er,
Jenn
i W
ilson
, A
ctiv
ities
D
irect
or
and
Rog
er
Yar
de,
Elec
trici
an f
or t
heir
colla
bora
tion
in t
his
asse
ssm
ent.
The
y w
ere
extra
ordi
naril
y ki
nd i
n ac
com
mod
atin
g m
y re
ques
ts,
whi
ch o
ften
invo
lved
the
ir w
orki
ng o
ff-h
ours
, in
clud
ing
late
at
nigh
t. E
qual
ly
impo
rtant
, the
ass
essm
ent w
ould
not
hav
e be
en p
ossi
ble
with
out t
he
fore
sigh
t an
d fin
anci
al
supp
ort
of
the
Tour
ism
D
evel
opm
ent
Cor
pora
tion
of B
arba
dos.
I w
ould
als
o lik
e to
rec
ogni
ze th
e tir
eles
s ef
forts
of
the
Bar
bado
s Se
a Tu
rtle
Proj
ect,
espe
cial
ly D
r. Ju
lia
Hor
rock
s, B
arry
K
rueg
er
and
thei
r 20
06
seas
onal
st
aff.
Th
e pr
ofes
sion
al w
ork
of th
e B
STP
has
set a
hig
h st
anda
rd f
or r
esea
rch
and
cons
erva
tion
in B
arba
dos
and
thro
ugho
ut th
e C
arib
bean
reg
ion.
W
ithou
t th
eir
colla
bora
tion,
inc
ludi
ng p
rovi
ding
me
with
hou
sing
, tra
inin
g, a
cces
s to
dat
a an
d ot
her
tech
nica
l in
form
atio
n, a
nd t
he
oppo
rtuni
ty t
o co
ntrib
ute
to t
heir
impo
rtant
fie
ld w
ork,
whi
ch h
as
been
pro
fess
iona
lly a
nd p
erso
nally
enr
ichi
ng f
or m
e, t
his
light
ing
asse
ssm
ent c
ould
not
hav
e be
en a
ccom
plis
hed.
Fin
ally
, I a
m g
rate
ful
to D
r. K
aren
Eck
ert,
Exec
utiv
e D
irect
or o
f W
IDEC
AST
and
my
acad
emic
adv
isor
at
Duk
e U
nive
rsity
’s N
icho
las
Scho
ol o
f th
e En
viro
nmen
t, fo
r he
r en
cour
agem
ent
of
my
effo
rts
and
her
lead
ersh
ip in
Car
ibbe
an s
ea tu
rtle
cons
erva
tion
issu
es in
gen
eral
, and
to
Erik
Mar
tin o
f Ec
olog
ical
Ass
ocia
tes,
Inc.
for
his
kin
dnes
s an
d pa
tienc
e in
tra
inin
g m
e in
the
pro
toco
ls o
f pr
ofes
sion
al b
each
fron
t lig
htin
g as
sess
men
ts, a
fiel
d in
whi
ch h
e is
wel
l-rec
ogni
zed.