AUVs have mapped currents and bathymetry of coral
reefs over large areas in deep water (Grasmueck et al.,
2006), and made detailed photomosaics in shallower
water (Armstrong et al., 2006). The physical oceanography of tropical coral reefs has also been surveyed by
AUVs, including currents (Fong and Jones, 2006), plume
dispersion (Jones et al., 2008), and hydrography and
bathymetry (Shcherbina et al., 2008). AUVs are also
well-suited to collect water quality data (Figure 4).
Because AUVs can move sensors rapidly over a reef, they
can help address the problem of data aliasing; aliasing
occurs when data are sampled too coarsely in space or
time to provide an understanding of nature’s dynamics.
ROVs and AUVs are well suited for collecting video
and still imagery, allowing analysis of landscape level patterns on reefs through photomosaic construction (Lirman
et al., 2007; Ludvigsen et al., 2007). Mosaics of photos,
side scan sonar, and multibeam sonar gathered by AUV
or ROV are managed in a Geographical Information System (GIS), providing reef scientists a useful tool for environmental monitoring, including assessment of the
efficacy of marine protected areas (Patterson and Relles,
2008).
Summary
Underwater robots such as AUVs and ROVs can gather
data from reef systems over depth ranges, and at time and
frequency scales, that cannot be obtained easily using other
sampling techniques. Both technologies can serve as taxicabs for sensors and imaging systems, with AUVs well
suited for large-area surveys, and ROVs suited for sample
retrieval and video inspection of more limited areas.
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AUVS (ROVS), Figure 4 Dissolved oxygen mapped over a coral reef in Florida Keys, by the Fetch1 AUV, useful in the inference of
metabolism, calcification, and carbon production. The unaliased data collected to produce this image could not have occurred
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