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The 150-meter transects shall be sampled using digital video in progressive scan mode. The diver shall swim at a speed of approximately 6 meter/min with a constant camera distance of 25 cm above bottom . If the diver is moved off the transect by surge, the diver shall return to the point where he/she was disturbed by the wave action , and resume filming at that point. The video transects shall be reviewed during the course of the survey to ensure that there are no gaps in the data due to diver error and that the quality of the video is acceptable for video analysis. Any missing video transect data or poor quality video shall be refilmed during the course of the monitoring event. Landscape panoramic views shall be recorded with the digital video camera at the start and end of each transect, and at each interruption of the transect by a sand gap/recommencement at the next hardbottom ridge. Close-up digital still video/photographs shall be obtained of representative benthos along the transect to aid in identification during video analysis. Still photographs shall be obtained using the digital video camera or digital still camera at all quadrat locations, vertical ledges, large Oculina spp. colonies or Siderastrea siderea colonies along the transect or adjacent to transect (within underwater visibility during transect establishment) , and changes in benthic landscape along the transect. Voucher sampling of macroalgae shall be conducted to assist with video identification of macroalgae genera . Video Transect Analysis During each monitoring even , two, 20-meter long segments of the video transect shall be quantitatively analyzed using PointCount'99 or a comparable software package based upon the random point count method for estimation of percent cover from digitally frame- grabbed underwater video images. The first 20-meter segment shall correspond to the first 20 meters of hardbottom (commence at the 0 point at the exposed nearshore hardbottom edge and continue to the 20-meter mark) . The second 20-meter segment shall cross hardbottom between 50 and 100 meters along each transect. The exact location of the second 20-meter segment shall be determined at the time of transect establishment based upon the benthic landscape and location of hardbottom ridges along the transect, and shall be referenced to the nearest pin along the transect for repeated occupation of the same stretch of transect for video analysis. DGPS positioning will be obtained for the start point of the second 20-meter segment along each transect. Each 20-meter segment shall result in approximately 100 non-overlapping frame- grabbed images. A unique set of 20 random points shall be generated at the time of frame-grabbing and stored with each set of images so that the same points are assessed during each monitoring event. This also ensures that each person examining a particular image will view the same points, thereby allowing for double-blind counting for quality assurance and control purposes. Ten percent (10%) of the images shall be counted by two scorers to assess inter-observer variability. An estimate of percent cover (projected to the surface) will be performed for each image according to the following functional groups/categories: scleractinian corals (to the genus level), octocorals, macroalgae (to the genus level if possible, if not, then according to the following breakdown : calcareous red , calcareous green , fleshy brown, fleshy red , fleshy green) , microalgae/cyanobacteria , sponges, tunicates, hydroids, wormrock, zoanthids, urchins, holothuroids, and substrate. Substrate shall be broken down into the following categories: unconsolidated substrate (rubble/shell hash , rhodoliths) , sediment over C:U)o enls aml Se ngslIona wVkLocal SottugslTemporary traem Fllea\OMEW a FINAL.Eoc 2