Incorporating dugong habitats into the marine protected area design for the Great Barrier Reef Marine Park, Queensland, Australia

2008 ◽  
Vol 51 (4) ◽  
pp. 368-375 ◽  
Author(s):  
Kirstin Dobbs ◽  
Leanne Fernandes ◽  
Suzanne Slegers ◽  
Belinda Jago ◽  
Leanne Thompson ◽  
...  
Keyword(s):  
Great Barrier Reef ◽  
Protected Area ◽  
Marine Protected Area ◽  
Barrier Reef ◽  
Marine Park

Incorporating marine turtle habitats into the marine protected area design for the Great Barrier Reef Marine Park, Queensland, Australia

2007 ◽  
Vol 13 (4) ◽  
pp. 293 ◽  
Author(s):  
Kirstin Dobbs ◽  
Leanne Fernandes ◽  
Suzanne Slegers ◽  
Belinda Jago ◽  
Leanne Thompson ◽  
...  
Keyword(s):  
Great Barrier Reef ◽  
Marine Protected Area ◽  
Design Guidelines ◽  
Marine Turtle ◽  
Barrier Reef ◽  
Traditional Use ◽  
Marine Park ◽  
Nesting Sites ◽  
Foraging Site ◽  
Very High

Marine turtle habitats were considered in the design of the new zoning network for the Great Barrier Reef Marine Park as part of the Representative Areas Programme. One of the specific design guidelines developed was the incorporation of marine turtle inter-nesting and foraging habitats into the overall network of no-take areas. The guideline was refined further for individual nesting and foraging sites to incorporate all very high priority nesting sites and to incorporate 20% of each identified foraging site, respectively. Marine turtle inter-nesting habitat increased in no-take area protection from 781 km2 to 1 886 km2 (23.4% to 56.5% of all identified sites); marine turtle foraging habitat increased in no-take area protection from 3 063 km2 to 12 490 km2 (7.1% to 29.1% of all identified sites). Although the nesting and foraging principles were not achieved in total for all identified marine turtle sites, overall the level of protection afforded by the Great Barrier Reef Marine Park Zoning Plan 2003 increased for nearly all marine turtle sites identified. Additionally, other activities (e.g. water quality, fisheries, traditional use of marine resources) occurring in the Great Barrier Reef Marine Park that may impact upon marine turtles are being addressed via other mechanisms.

Management of Water Quality in the Great Barrier Reef Marine Park

1989 ◽  
Vol 21 (2) ◽  
pp. 31-38 ◽  
Author(s):  
Simon Woodley
Keyword(s):  
Water Quality ◽  
Coral Reef ◽  
Great Barrier Reef ◽  
Barrier Reef ◽  
Management Issue ◽  
Reef System ◽  
Marine Park ◽  
World Heritage List ◽  
The World ◽  
Coral Reef System

The Great Barrier Reef is the largest coral reef system in the world. It is recognised and appreciated worldwide as a unique environment and for this reason has been inscribed on the World Heritage List. The Reef is economically-important to Queensland and Australia, supporting substantial tourism and fishing industries. Management of the Great Barrier Reef to ensure conservation of its natural qualities in perpetuity is achieved through the establishment of the Great Barrier Reef Marine Park. The maintenance of water quality to protect the reef and the industries which depend on it is becoming an increasingly important management issue requiring better knowledge and possibly new standards of treatment and discharge.

Aerial Surveys of Sea Turtles in the Northern Great Barrier-Reef Marine Park

1989 ◽  
Vol 16 (3) ◽  
pp. 239 ◽  
Author(s):  
H Marsh ◽  
WK Saalfeld
Keyword(s):  
Great Barrier Reef ◽  
Sea Turtles ◽  
Analysis Of Covariance ◽  
Seagrass Beds ◽  
Barrier Reef ◽  
Sea State ◽  
Water Turbidity ◽  
Density Estimates ◽  
Marine Park ◽  
Specific Correction

In 1984 and 1985, during surveys designed primarily to census dugongs, six species of sea turtles were counted from the air at an overall sampling intensity of 9% over a total area of 31 288 km2 within the northern sections of the Great Barrier Reef Marine Park. The sea turtles were not identified to species. We attempted to correct sightings for perception bias (the proportion of animals visible in the transect which are missed by observers), and to standardise for availability bias (the.proportion of animals that are invisible due to water turbidity) with survey-specific correction factors. The resultant minimum population estimate in November 1985 was (mean � s.e.) 32 187 � 2532 sea turtles at an overall density of 1.03 � 0.08 km-2, a precision of 8%. We consider this to be a gross underestimate of numbers present. Significant differences between population and density estimates obtained from repeat surveys of the same areas were accounted for by differences in Beaufort sea state and cloud cover. The analysis of covariance data suggested that we had not been successful in standardising all biases. Turtles were widely distributed throughout the Great Barrier Reef lagoon from inshore seagrass beds to mid- and outer-shelf reefs. Highest densities were observed on inshore seagrass beds and on mid-shelf reefs, particularly between Murdoch Island and Cape Melville, and in Princess Charlotte Bay. Maps of density and distribution are given. We discuss the value and limitations of this survey regime for censusing sea turtles.

scholarly journals Lessons Learned from Australia’s Stakeholder Engagement Efforts for MPA Planning

2018 ◽  
Author(s):  
OCTO
Keyword(s):  
Great Barrier Reef ◽  
Stakeholder Engagement ◽  
Planning Process ◽  
Lessons Learned ◽  
Barrier Reef ◽  
Marine Park

Jon Day shares key lessons learned from stakeholder engagement efforts during the Representative Areas Program in the Great Barrier Reef, which was a key part of the comprehensive rezoning of the entire Marine Park between 1999 and 2003. As a result of this planning process, the total area of no-take zones increased from less than 5% to over one-third of the Marine Park, highlighting in large part the importance of effectively engaging stakeholders.

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