Baited remote underwater video (BRUV) has been identified in the literature as a powerful long-term monitoring tool for subtidal rocky reef fish communities. To test this, a repeated-measures field experiment comparing unbaited remote underwater video (RUV) with BRUV was conducted in the Tsitsikamma National Park Marine Protected Area between June 2008 and February 2010. The results demonstrate that BRUV was more efficient at surveying the entire fish community, specifically invertebrate carnivores, generalist carnivores and cartilaginous species. On the other hand, RUV was more effective at surveying microinvertebrate carnivores. High variability in the RUV data resulted in the method requiring a greater number of samples to achieve the same diagnostic power as BRUV. However, RUV required a shorter deployment and post-sampling video analysis time, making it more time efficient. Baited remote underwater video was more sensitive in the detection of differences in abundance between habitat types, while the RUV data were more prone to an intra-species methodological bias linked to the percentage of reef visible in the frame of view. The scale of the response to the presence of bait was inconsistent among species, indicating that behaviour determined the area surveyed within the bait plume of BRUV. The benefits gained by sampling the fish community with RUV do not outweigh those obtained by altering the community through the presence of bait. However, in combination, the 2 methods are highly effective at monitoring the subtidal fish communities in the Agulhas bioregion of South Africa.
Resale or republication not permitted without written consent of the publisherMar Ecol Prog Ser 471: [235][236][237][238][239][240][241][242][243][244][245][246][247][248][249][250][251][252] 2012 trawls , Cappo et al. 2004, Watson et al. 2005, Colton & Swearer 2010, Pelletier et al. 2011. The core strengths lie in the method's ability to survey components of the fish community typically missed by UVC techniques, such as large piscivorous fish , Cappo et al. 2004, Brooks et al. 2011, the higher diagnostic power achieved through reduced variability in the data (Watson et al. 2005, Stobart et al. 2007) and the ability to provide accurate measures of fish length when set up with stereo-cameras (Harvey & Shortis 1996, Harvey et al. 2004, Watson et al. 2009). Data collected with BRUV are not biased by the presence of an observer in the water that can alter the behaviour of the fish, and observer bias during analysis is kept to a minimum, as the video is available for reanalysis if erroneous data are de tec ted (Cappo et al. 2003(Cappo et al. , 2007b. Furthermore, BRUV is a non-destructive and non-extractive sampling tool and is thus ideally suited to monitor protected fish populations inside marine reserves , Cappo et al. 2007b.As with all survey methods, BRUV is characterised by a number of shortcomings. For example, past studies indicate that BRUV is unable to survey herbivorous fish as efficiently as UVC (Colton & Swearer ...