Understanding regulatory frameworks for large marine protected areas: Permits of the Great Barrier Reef Marine Park

2019 ◽  
Vol 237 ◽  
pp. 3-11 ◽  
Author(s):  
Graeme S. Cumming ◽  
Kirstin A. Dobbs
Author(s):  
Ray Hilborn ◽  
Ulrike Hilborn

What are marine protected areas? One of the crown jewels of marine ecosystems is the Great Barrier Reef (GBR) off the northeast coast of Australia. The reef stretches along 2,600 km of the Queensland coast and consists of 900 islands and 2,900 reefs. It...


2005 ◽  
Vol 19 (6) ◽  
pp. 1733-1744 ◽  
Author(s):  
LEANNE FERNANDES ◽  
JON DAY ◽  
ADAM LEWIS ◽  
SUZANNE SLEGERS ◽  
BRIGID KERRIGAN ◽  
...  

1989 ◽  
Vol 21 (2) ◽  
pp. 31-38 ◽  
Author(s):  
Simon Woodley

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.


1989 ◽  
Vol 16 (3) ◽  
pp. 239 ◽  
Author(s):  
H Marsh ◽  
WK Saalfeld

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.


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