Information on shore‐based recreational fishing is essential for the sustainable management of nearshore fish stocks. However, obtaining estimates of catch and effort from such fishing activity can be complex and expensive due to the large spatial scales over which surveys are typically conducted and the fine‐scale temporal resolution that is desired. Complementary surveys are one option for improving the accuracy of estimates. A pilot study was conducted in Perth, Western Australia, from April to June 2010 to test an expanded aerial–roving survey design that incorporated remotely operated cameras. Cameras recorded the distribution of shore‐based fishing activity across a 24‐h day, highlighting an afternoon peak as well as some nighttime activity, which is rarely captured in existing survey designs. This information was combined with instantaneous counts of shore fishers from aerial surveys and trip length data that were obtained from 1,194 incomplete trip interviews conducted during roving creel surveys; the resulting estimate of fishing effort was 213,460 angler‐hours (SE = 18,141; relative SE [RSE] = 8%). Catch rates, which were calculated from roving creel survey data on the numbers of retained fish, were combined with fishing effort to estimate a total retained catch of 355,801 fish (SE = 41,446; RSE = 12%). The Australian herring Arripis georgianus was the dominant species, with a retained catch of 229,779 fish (SE = 39,007; RSE = 17%). In comparison with other on‐site techniques, the incorporation of cameras into an aerial–roving survey design provides a generic, cost‐effective method for measuring the distribution of shore‐based fishing activity across a 24‐h day. Our findings improve the understanding of the exploitation of nearshore fish stocks along the Perth coast. Our method has broad application to many other recreational fisheries around the world, especially where nighttime fishing is popular.
Received June 28, 2012; accepted August 24, 2012
A rare opportunity to test hypotheses about potential fishery benefits of large-scale closures was initiated in July 2004 when an additional 28.4% of the 348 000 km2 Great Barrier Reef (GBR) region of Queensland, Australia was closed to all fishing. Advice to the Australian and Queensland governments that supported this initiative predicted these additional closures would generate minimal (10%) initial reductions in both catch and landed value within the GBR area, with recovery of catches becoming apparent after three years. To test these predictions, commercial fisheries data from the GBR area and from the two adjacent (non-GBR) areas of Queensland were compared for the periods immediately before and after the closures were implemented. The observed means for total annual catch and value within the GBR declined from preclosure (2000-2003) levels of 12780 Mg and Australian $160 million, to initial post-closure (2005-2008) levels of 8143 Mg and $102 million; decreases of 35% and 36% respectively. Because the reference areas in the non-GBR had minimal changes in catch and value, the beyond-BACI (before, after, control, impact) analyses estimated initial net reductions within the GBR of 35% for both total catch and value. There was no evidence of recovery in total catch levels or any comparative improvement in catch rates within the GBR nine years after implementation. These results are not consistent with the advice to governments that the closures would have minimal initial impacts and rapidly generate benefits to fisheries in the GBR through increased juvenile recruitment and adult spillovers. Instead, the absence of evidence of recovery in catches to date currently supports an alternative hypothesis that where there is already effective fisheries management, the closing of areas to all fishing will generate reductions in overall catches similar to the percentage of the fished area that is closed.
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