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Abalone and Sea Star Monitoring
Band
Transect/Irregular Plot Protocol

The number and size of seastars (primarily ochre seastars Pisaster ochraceus)
and black abalone (Haliotis cracherodii) are monitored along band
transects or within irregularly-shaped plots, depending on site topography. Seastar transects are typically 2 x 5 m; abalone transects are typically 1 x
10 m. Transects are marked at both ends (and often in the center) by notched
bolts. Irregular plots are marked by four "corner" bolts. All black abalone
and ochre seastars in transects or irregular plots are counted and measured
(abalone: shell length; seastars: from center to tip of longest ray).
Timed Searches
Site-wide timed searches
have been employed at locations where abalone and seastars exist in too few
numbers to monitor within a limited area. One person spends 30 min (or 2
persons 15 min each) searching crevices and pools along the low intertidal
zone haphazardly throughout the site for possible occurrences of ochre
seastars or black abalone. Numbers encountered and size measurements (at
some sites) are recorded.
Owl Limpet Counts and Size Frequencies
The number and size
distribution of owl limpets (Lottia gigantea) are monitored
each spring and fall to follow population dynamics within 5 permanent
circular plots per site at most intertidal sites with sufficient scorable
individuals (generally > 20 individuals/plot). Plots were established in
areas of high density to obtain as many measurements as possible, preferably
> 100 per site. Plots are marked with a center bolt, notched to indicate
the plot number. Limpets are measured within a circle (typically 1 m radius,
3.14 m2 area) around each bolt. A 1m length of line or tape is
attached to the bolt and arced around to form the circle. Owl limpets found
within that circle (including those touched by the 1 m mark) are measured
with calipers to the nearest millimeter, then marked with a crayon to avoid
scoring duplication. Limpets are never removed from the rock.
Photoplots
The cover of target
species as well as other core and optional species/taxa/substrates is
sampled by photographing 5 (at most sites) permanent 50 x 75 cm plots per
target species, then scoring point contact occurrences on the photo image. Plots were established in areas of high target species density wherever
possible. Photoplots typically are scored
from the photographs in the laboratory, supplemented when possible by field
plot sketches and notes. For film photographs, each slide is projected onto
a grid of one hundred evenly-spaced points (10 x 10). Individual taxa
beneath the points are identified and recorded. When scoring digital images,
a grid is created on
an LCD computer monitor (using Adobe Photoshop)
of one hundred ev enly-spaced
points (10 x 10), and placed on a separate layer. Layering is not scored
separately using either procedure, so the total percent cover is constrained
to 100%. The top-most layer that is attached to the substrate (i.e., not an
obvious epibiont) is always scored regardless of the type of target or core
species involved. Limpets, chitons, abalone, and seastars
are scored “as is.” For other motile invertebrates, whatever
lies beneath the mobile species is scored if possible; otherwise, the point
is scored as “unidentified”. Data are
entered into a Microsoft Access database for analysis.
Transects
The cover of surfgrass (Phyllospadix
spp) is sampled by point-intercepts
along 10 m long permanent transects. Transects were established in areas of high surfgrass
density wherever possible. Most
sites have 3 replicate transects. Transects may run end to end
or be separated widely, depending on the shape and expanse of the surfgrass
bed. Each transect is
divided into 100 points distributed at 10 cm intervals. The top-layer
target, core, or optional species/taxon/substrate
is scored under each point. In addition, surfgrass
is separately scored if it occurs beneath another species. In the latter
situation, total transect cover can
be greater than 100%.
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