Monitoring Protocol
Purpose: to accurately and
efficiently monitor spatial and temporal variation in fish abundance. The
sampling design is focused primarily on detecting change in abundant to
moderately abundant reef fish across all 24 study sites sampled on a bimonthly
basis. The simple, low-replicate design minimizes site survey time while
maximizing repeated surveying of sites to obtain estimates of temporal variation
in adult and juvenile abundance.
A. Sampling Design
Design of transect layout used at permanent
transects. Two 60 m neutral gray transect lines are positioned along six permanent
stainless-steel eyebolts. Divers survey four 25 m transects separated by 10 m
buffer areas between replicates.
B. Survey Protocol
Transects are located by
differential GPS. Fish densities of all observed species are estimated by visual
strip transect search along each permanent transect line. Two pairs of divers
survey the lines, each pair searching two of the 25 m lines. The search of each
line consists of two divers, swimming side-by-side on each side of the line,
surveying a column 2 m wide. On the outward-bound leg, larger planktivores and
wide-ranging fishes within 4 m of the bottom are recorded. On the return leg,
fishes closely associated with the bottom, juveniles, and fishes hiding in
cracks and crevices are recorded. Each site is scheduled to be surveyed
bi-monthly, weather permitting, for a total of six surveys per year.
C. Power Analysis
(based on first survey)
Mean
Density = |
per
100m2 |
MDD
= |
Minimum Detectable
Difference of design (in fish per 100m2) with a=0.05
b=0.10. |
%
Change = |
detectable
percent change in abundance. Change greater than this between surveys
would result in a statistically significant difference. |
Species |
Mean
Density |
Standard
Deviation |
MDD |
%
Change |
Aquarium
Species |
|
|
|
|
Acanthurus
achilles |
0.86 |
1.03 |
0.41 |
47 |
Acanthurus
olivaceus |
0.85 |
1.81 |
0.72 |
85 |
Centropyge
potteri |
2.09 |
1.30 |
0.52 |
25 |
Chaetodon
auriga |
0.09 |
0.29 |
0.11 |
132 |
Chaetodon
fremblii |
0.04 |
0.21 |
0.08 |
191 |
Chaetodon
lunula |
0.33 |
0.58 |
0.23 |
70 |
Chaetodon
multicinctus |
5.78 |
1.67 |
0.66 |
11 |
Chaetodon
ornatissimus |
1.66 |
1.24 |
0.49 |
30 |
Chaetodon
quadrimaculatus |
0.80 |
1.02 |
0.41 |
51 |
Chaetodon
unimaculatus |
0.09 |
0.29 |
0.11 |
132 |
Ctenochaetus
hawaiiensis |
0.65 |
0.97 |
0.39 |
59 |
Ctenochaetus
strigosus |
21.67 |
9.03 |
3.60 |
17 |
Zebrasoma
flavescens |
14.46 |
9.66 |
3.85 |
27 |
Non-Aquarium
Species |
|
|
|
|
Abudefduf
abdominalis |
1.00 |
2.10 |
0.84 |
84 |
Acanthurus
blochii |
0.04 |
0.21 |
0.08 |
191 |
Acanthurus
leucopareius |
0.17 |
0.65 |
0.26 |
149 |
Acanthurus
nigricans |
0.30 |
0.63 |
0.25 |
83 |
Acanthurus
nigrofuscus |
9.03 |
4.74 |
1.89 |
21 |
Acanthurus
nigroris |
1.27 |
1.35 |
0.54 |
42 |
Acanthurus
thompsoni |
2.08 |
3.40 |
1.35 |
65 |
Acanthurus
triostegus |
0.61 |
1.77 |
0.71 |
116 |
Aluterus
scriptus |
0.04 |
0.21 |
0.08 |
191 |
Anampses
cuvier |
0.04 |
0.21 |
0.08 |
191 |
Aphareus
furca |
0.09 |
0.29 |
0.11 |
132 |
Apogon
kallopterus |
0.13 |
0.63 |
0.25 |
191 |
Apogon
menesemus |
0.13 |
0.46 |
0.18 |
140 |
Apogon
spp. |
0.22 |
0.60 |
0.24 |
110 |
Arothron
meleagris |
0.13 |
0.34 |
0.14 |
105 |
Aulostomus
chinensis |
0.40 |
0.60 |
0.24 |
59 |
Balistes
polylepis |
0.04 |
0.21 |
0.08 |
191 |
Bodianus
bilunulatus |
0.13 |
0.34 |
0.14 |
105 |
Calotomus
carolinus |
0.09 |
0.29 |
0.11 |
132 |
Cantherhines
dumerilii |
0.35 |
0.71 |
0.28 |
82 |
Canthigaster
amboinensis |
0.13 |
0.46 |
0.18 |
140 |
Canthigaster
jactator |
2.51 |
2.87 |
1.14 |
46 |
Caracanthus
typicus |
0.04 |
0.21 |
0.08 |
191 |
Cephalopholis
argus |
0.93 |
0.65 |
0.26 |
28 |
Chaetodon
lineolatus |
0.04 |
0.21 |
0.08 |
191 |
Chaetodon
miliaris |
0.32 |
1.17 |
0.47 |
146 |
Chromis
agilis |
20.50 |
16.54 |
6.59 |
32 |
Chromis
hanui |
3.36 |
2.30 |
0.92 |
27 |
Chromis
ovalis |
10.46 |
36.16 |
14.40 |
138 |
Chromis
vanderbilti |
20.06 |
31.66 |
12.61 |
63 |
Chromis
verater |
1.01 |
2.34 |
0.93 |
92 |
Cirrhitops
fasciatus |
0.20 |
0.54 |
0.21 |
110 |
Cirrhitus
pinnulatus |
0.17 |
0.49 |
0.20 |
112 |
Cirripectes
vanderbilti |
0.17 |
0.39 |
0.15 |
89 |
Coris
flavovittata |
0.17 |
0.39 |
0.15 |
89 |
Coris
gaimard |
0.87 |
0.77 |
0.31 |
35 |
Coris
venusta |
0.13 |
0.34 |
0.14 |
105 |
Dascyllus
albisella |
0.91 |
1.62 |
0.65 |
71 |
Exallias
brevis |
0.37 |
0.61 |
0.24 |
65 |
Fistularia
commersonii |
0.17 |
0.49 |
0.20 |
112 |
Forcipiger
flavissimus |
0.92 |
1.07 |
0.42 |
46 |
Forcipiger
longirostris |
0.96 |
1.12 |
0.44 |
47 |
Gomphosus
varius |
1.80 |
1.41 |
0.56 |
31 |
Gymnothorax
flavimarginatus |
0.17 |
0.39 |
0.15 |
89 |
Gymnothorax
meleagris |
0.30 |
0.56 |
0.22 |
73 |
Gymnothorax
spp. |
0.09 |
0.42 |
0.17 |
191 |
Halichoeres
ornatissimus |
1.84 |
1.24 |
0.50 |
27 |
Hemitaurichthys
polylepis |
0.78 |
2.32 |
0.92 |
118 |
Hemitaurichthys
thompsoni |
0.61 |
2.31 |
0.92 |
151 |
Labroides
phthirophagus |
1.87 |
0.96 |
0.38 |
20 |
Lutjanus
kasmira |
0.22 |
0.74 |
0.29 |
135 |
Macropharyngodon
geoffroyi |
0.13 |
0.34 |
0.14 |
105 |
Melichthys
niger |
2.06 |
3.51 |
1.40 |
68 |
Melichthys
vidua |
0.71 |
0.71 |
0.28 |
40 |
Monotaxis
grandoculis |
0.49 |
1.28 |
0.51 |
105 |
Mulloidichthys
flavolineatus |
0.09 |
0.42 |
0.17 |
191 |
Mulloidichthys
vanicolensis |
5.61 |
14.04 |
5.59 |
100 |
Myripristis
amaena |
0.13 |
0.63 |
0.25 |
191 |
Myripristis
berndti |
4.12 |
7.15 |
2.85 |
69 |
Myripristis
kuntee |
2.01 |
4.24 |
1.69 |
84 |
Naso
hexacanthus |
0.22 |
0.52 |
0.21 |
95 |
Naso
lituratus |
1.99 |
1.54 |
0.61 |
31 |
Neoniphon
sammara |
0.43 |
0.90 |
0.36 |
82 |
Novaculichthys
taeniourus |
0.04 |
0.21 |
0.08 |
191 |
Ostracion
meleagris |
0.22 |
0.50 |
0.20 |
91 |
Oxycheilinus
unifasciatus |
0.67 |
0.60 |
0.24 |
35 |
Paracirrhites
arcatus |
5.69 |
6.76 |
2.69 |
47 |
Paracirrhites
forsteri |
1.04 |
0.73 |
0.29 |
28 |
Parupeneus
bifasciatus |
0.91 |
1.12 |
0.45 |
49 |
Parupeneus
cyclostomus |
0.26 |
0.75 |
0.30 |
115 |
Parupeneus
multifasciatus |
1.26 |
0.99 |
0.39 |
31 |
Parupeneus
porphyreus |
0.04 |
0.21 |
0.08 |
191 |
Pervagor
aspricaudus |
0.51 |
1.02 |
0.41 |
80 |
Plagiotremus
goslinei |
0.26 |
0.54 |
0.22 |
83 |
Plectroglyphidodon
imparipennis |
0.22 |
0.52 |
0.21 |
95 |
Plectroglyphidodon
johnstonianus |
2.57 |
1.22 |
0.49 |
19 |
Priacanthus
meeki |
0.04 |
0.21 |
0.08 |
191 |
Pseudocheilinus
evanidus |
2.19 |
1.29 |
0.51 |
23 |
Pseudocheilinus
octotaenia |
3.29 |
1.79 |
0.71 |
22 |
Pseudocheilinus
tetrataenia |
1.91 |
1.32 |
0.53 |
27 |
Pseudojuloides
cerasinus |
0.26 |
0.75 |
0.30 |
115 |
Sargocentron
ensiferum |
0.26 |
0.92 |
0.36 |
140 |
Sargocentron
spiniferum |
0.09 |
0.29 |
0.11 |
132 |
Sargocentron
spp. |
0.22 |
0.67 |
0.27 |
123 |
Sargocentron
tiere |
0.04 |
0.21 |
0.08 |
191 |
Sargocentron
xantherythrum |
0.26 |
0.69 |
0.27 |
105 |
Saurida
gracilis |
0.04 |
0.21 |
0.08 |
191 |
Scarus
dubius |
0.13 |
0.46 |
0.18 |
140 |
Scarus
perspicillatus |
0.04 |
0.21 |
0.08 |
191 |
Scarus
psittacus |
0.20 |
0.94 |
0.37 |
191 |
Scarus
rubroviolaceus |
0.48 |
1.08 |
0.43 |
90 |
Scarus
sordidus |
2.50 |
3.70 |
1.47 |
59 |
Scorpaenopsis
cacopsis |
0.09 |
0.29 |
0.11 |
132 |
Scorpaenopsis
diabolus |
0.04 |
0.21 |
0.08 |
191 |
Stegastes
fasciolatus |
1.86 |
2.77 |
1.10 |
59 |
Stethojulis
balteata |
0.49 |
0.61 |
0.24 |
49 |
Sufflamen
bursa |
1.54 |
0.83 |
0.33 |
21 |
Synodus
dermatogenys |
0.04 |
0.21 |
0.08 |
191 |
Synodus
spp. |
0.04 |
0.21 |
0.08 |
191 |
Synodus
ulae |
0.04 |
0.21 |
0.08 |
191 |
Synodus
variegatus |
0.04 |
0.21 |
0.08 |
191 |
Thalassoma
ballieui |
0.04 |
0.21 |
0.08 |
191 |
Thalassoma
duperrey |
6.51 |
2.58 |
1.03 |
16 |
Xanthichthys
auromarginatus |
0.73 |
1.35 |
0.54 |
74 |
Zanclus
cornutus |
0.73 |
0.87 |
0.35 |
47 |
D. Coral Assessment
Protocol
We will utilize standard methods
developed in conjunction with the Hawai'i Coral Reef Assessment and Monitoring
Program (CRAMP) to estimate substratum
abundance, diversity and distribution. Currently these include digital video
imaging to record 50 contiguous frames along each transect line (n=200
photographs for each site). Images are analyzed
to obtain percent cover estimates for substratum types. See coral
monitoring for more information.
|