Summaries of STRT Project Reports 1) Canbolat, A.F., 1999, The Investigation of Sea Turtle Populations in Köyceğiz-Dalyan and Patara Specially Protected Areas, Final Report, Ministry of Environment APSA, Ankara, 73 p. The Investigation of Sea Turtle Populations in Köyceğiz-Dalyan and Patara Specially Protected Areas Summary of Project Report Field studies of 1999 in Dalyan and Patara Special Protection Areas started on June 15th, 1999 and were finished on September 15th-20th, 1999. In this research, number of Caretta caretta emergences observed in Dalyan Beach was 871 with 276 ( 31.69%) resulting in nests while it was 264 for Patara Beach 79 (29.92%) of which resulted in nests. Caretta caretta nesting was determined to reach the highest density ratios during June in Dalyan and during July in Patara. The densest nesting activity was observed in Boğaz section in Dalyan Beach and in both the southeastern part and sections near Stream Esen in Patara Beach. Average distance of nests from the sea was 16.32 m for Dalyan while it was 32.58 m for Patara. Nests in Dalyan Beach were exposed to
high predation ratio of about 55.07%. On the other hand, predation ratio on
nests in Patara Beach was about 27.85. The increasing fox predation in Küçük
Kumsal (small beach) section of Dalyan causes a great decline in hatchling
productivity that Dalyan beach has had of very high percentages for previous
years. It has come up that taking immediate measures against high predation
ratios affecting the hatchling productivity especially in Dalyan beach is an
obligation. Regarding this year’s data, the ratio
of nests with hatchlings is 44.20% in Dalyan Beach and 60.76% in Patara Beach. The means and necessary measures to be
taken in order to preserve Caretta caretta adults, nests, eggs and
hatchlings in Dalyan and Patara Beaches are described in “Conservation and
Management” section. 2) Canbolat, A.F., 2000, Conservation of Belek Sea Turtles '99, Final Report, Belek Tourism Investors Association (BETUYAB), Ankara, 142 p. Conservation of Belek Sea Turtles '99 Summary of Project Report Belek province has been chosen as the
research area, regarding the results of the studies in 1996-1998 showing that it
hosts approximately 20% of the total nesting potential of Caretta caretta
(Yerli and Canbolat, 1998a,b; Yerli et al., 1998) among 17 beaches (Baran and
Kasparek, 1989) determined as nesting sites. During the breeding season in 1999,
612 Caretta caretta nests have been determined in the region on a 29.5 km
long beach, which is located between Aksu River on the west and Sarısu River on
the east. These results in terms of total number of nests revealed that Belek
region is the second largest sea turtle nesting area in the Mediterranean after
Zakynthos Island of Greece. The most important sections in terms of
local distribution of nests in Belek are determined to be the sections between Köprüçay-Burun
(%30.4), Siteler-Köprüçay (%18.0) and Kum Tepesi-Siteler (%13.7) while
the most important sections in terms of nesting density are the sections between
Siteler-Köprüçay (110.0 nests/km), Köprüçay-Burun (44.3nests/km) and Kum
Tepesi-Siteler (30.0 nests/km). The ratio of predated nests in the
whole region is determined as 42.7% while the ratio of nests with hatchling
emergence is 49.4%. The most important natural factor affecting the hatchling
success of the nests in the region is determined to be fox predation, whereas
the human originated negative factors are determined to be related with the
usage of beach equipment such as sun parasols and chaise lounges,
arbours and the traffic on the beach. Artificial lighting from tourism
establishments, summer houses and vehicle traffic in the region have a
disorientating effect on the hatchlings by misdirecting them instead of heading
towards the sea besides affecting the local distribution of nesting activity.
Death ratios are determined to increase among hatchlings disoriented by
artificial lights when compared to the ones heading directly towards the sea. Regarding the scientific data obtained,
necessary general and regional conservation-management plans are made to
preserve the potential circumstance of the sea turtle population in the region,
to normalize the hatchlings success, to prevent the disorientation of hatchlings
and to minimize the negative effects. The following necessary and highly
applicable management plans are suggested for coastal and beach usage: In the content of general approach for
the conservation of sea turtles in the region; -
To establish a particular committee
in the province named "The Committee for Monitoring and Evaluating the
Sea Turtles of Antalya" -
"Revision of Regional Planning" such as
reinsuring the section between Köprüçay-Sarısu
back in to the scope of APSA (Authority for the Protection of Special Areas)
that had been excluded and reserved as a Tourism Development Area -
To establish a "Sea Turtle Research, Conservation, Rehabilitation and
Education Center" regarding the importance of nesting sites in and
around Belek region. In the content of regional approach for
the conservation of sea turtles in the region; -
To prevent the possible adult deaths in the region -
To ensure the continuing of
nestings -
To increase the hatchling success -
To prevent the disorientation of hatchlings 3) Canbolat, A.F., 2000, Project for
Monitoring Sea Turtles in Belek Specially Protected Area, Final Report, Ministry
of Environment APSA, Ankara, 132 p. Project
for Monitoring Sea Turtles in Belek Specially Protected
Area Summary of Project Report Extensive research by Canbolat
(2000) has revealed that Belek Beach -which is approximately 29.5 kilometers
long- is the second largest known nesting area for Caretta
caretta in the whole Mediterranean after the Zakynthos Island of Greece. Data
gained from the study conducted in the same region during the nesting season in
year 2000 also verify the results of Canbolat (2000)'s study. These results
put forward the strong need of paying more attention to the conservation studies
in the region in order to preserve our coastal beauties and the sea turtles as
one of our most important biological riches as well as to fulfill the
responsibilities we have overtaken by signing international conventions. In the Special Protection Area of 13.3
kilometers between Acısu River on the west and Sarısu River on the east, 490 Caretta
caretta nests and 3 Chelonia mydas nests have been determined during
the nesting season in year 2000. In Belek Specially Protected Area; sections
between Köprüçay-Burun (29.8%), Siteler-Köprüçay (28.0%) and Kum
Tepesi-Siteler (19.8%) have been defined as the most important areas in terms of
local distribution of the nests; whereas sections between
Siteler-Köprüçay (137.0 nests/km), Köprüçay-Burun (34.8 nests/km)
and Kum Kepesi-Siteler (34.6 nests/km) have been determined to be the most
important areas in terms of density of nesting activity. These results showed
that the region is a "Primarily Vulnerable Region for Sea Turtles". For the whole Specially Protected Area
of Belek, the ratio of predated nests is determined as 28.1% while the ratio of
nests with hatchling emergence is 62.0%. It has also been determined that the
most important natural factor affecting the hatchling success of the nests is
the fox predation, while the human resourced negative factors are related with
the usage of beach equipment such as sun parasols and chaise-lounges as well as
the arbours and the vehicle usage on the beach. Artificial lights from tourism
establishments, secondary residences and heavy vehicle usage; have a strong
negative effect on the local distribution of the nests in relation with their
density as well as causing disorientation on the hatchlings. A higher death
ratio has been determined among hatchlings which have disoriented when compared
to the hatchlings that have headed directly towards the sea. In order to put the application
programs suggested in this project into practice, it is a must to propose a
workshop in Belek as soon as possible where all related persons, affiliations
and institutions should attend. 4) Canbolat, A.F., 2000, 2nd Sub-project
of Ecological Survey on the Conservation of Sea Turtles in Belek Beach-Antalya,
Development Report, Ministry of Environment, General Directorate of Environment,
Ankara, 130 p. 2nd
Sub-project of Ecological Survey on the Conservation of Sea Turtles in Belek
Beach-Antalya Summary
of Project Report Data gained from Canbolat (2000a)'s
study in the region in 1999 showed that Belek beach -which is approximately 29.5
kilometers long- is the second largest known nesting area for Caretta
caretta in the whole Mediterranean after the Zakhynthos Island of Greece.
Data gained from this study conducted in the region and in Special Protection
Areas (Canbolat, 2000b) during the nesting season in year 2000 also verify the
results of Canbolat (2000a)'s study. These results put forward the strong
need of paying more attention to the conservation studies in the region in order
to preserve our coastal beauties and the sea turtles as one of our most
important biological riches as well as to fulfill the responsibilities we have
overtaken in terms of signing international conventions. In the area of 16.0 kilometers between
Aksu River on the west and Acısu River on the east, 192 Caretta caretta
nests and 5 Chelonia mydas nests have been determined during the nesting
season in year 2000. In Belek Specially Protected Area; sections between Belpark-Acısu
(38.0%) and Beşgöz-Asteria (32.3%) have been defined as the most important
areas in terms of local distribution of the nests; whereas areas between Aksu-Beşgöz
(19.2 nests/km) and Beşgöz-Asteria (17.7 nests/km) have been determined to be
the most important areas in terms of the density of nesting activity. For the whole Special Protected Area of
Belek, the ratio of predated nests is determined as 29.0% while the ratio of
nests with hatchling emergence is 61.5%. It has also been determined that the
most important natural factor affecting the hatchling success of the nests is
the fox predation, whereas the human resourced negative factors are related with
the usage of beach equipment such as sun parasols and chaise-lounges as well as
the arbours and vehicle usage on the beaches. Artificial lights from tourism
establishments, secondary residences and heavy vehicle usage; have a strong
negative effect on the local distribution of the nests in relation with their
density as well as causing disorientation on the hatchlings. A higher death
ratio has been determined among hatchlings, which have disoriented when compared
to the hatchlings that have headed directly towards the sea. In order to put the application
programs suggested in this project into practice, it is a must to propose a
workshop in Belek as soon as possible where all related persons, affiliations
and institutions should attend. 5) Canbolat, A.F., 2001, Biology,
Conservation and Management of Caretta caretta in Belek Tourism Center,
Belek Tourism Investors Association (BETUYAB) Publications, Ankara, in press. Publications
of Ali Fuat Canbolat, Ph.D You may find all studies of Ali Fuat
Canbolat, Ph.D since 1988 at yunus.hacettepe.edu.tr/~canbolat. |