David R.
Stanley and Charles A. Wilson
Stanley,
D. R. and Wilson, C. A. 1996. Abundance of fishes associated with apetroleum
platform as measured with dual-beam hydroacoustics. – ICES Journal ofMarine
Science, 53: 473–475.
Stationary
dual-beam hydroacoustics was used to measure the density of fishesassociated
with a petroleum platform in the northern Gulf of Mexico from January1991
through May 1992. Mean monthly fish densities ranged from 0.19–0.41 fish m"3.Density
varied significantly with platform side, month, and depth. Fish densities
weresignificantly higher adjacent to the platform and decreased to background
levels atdistances greater than 16 m. Approximately 1990 to 28 100 fish were
associated withthe platform depending on month.
Copyright1996
International Council for the Exploration of the Sea
Key
words: artificial reef, Gulf of Mexico, hydroacoustics, petroleum platform.
D.
R. Stanley and C. A. Wilson: Coastal Fisheries Institute, Center for Coastal,Energy,
and Environmental Resources, Louisiana State University, Baton Rouge,Louisiana
70803-7503, USA. Correspondence to Stanley [tel: +1 504 388 6284,fax: +1 504
388 6513].
Introduction
There
are more than 4100 petroleum platforms presentin the northern Gulf of Mexico,
providing an additional 5000 km2of hard substatum to the approximately 2800 km2
of existing natural hard bottom. These struc-tures act as artificial reefs and
their addition is one of themost extensive habitat modifications in the world.
Research
on the abundance and composition of fish assemblages surrounding petroleum
platforms has been limited owing to logistical sampling diYculties and a lack
of applicable fisheries-independent sampling methods. Previous researchers have
used a variety of methodologies including catch per unit eVort studies and visual
surveys by SCUBA divers, remotely operated underwater vehicles, and fixed
underwater cameras; however, the majority of these studies were only short-term
snapshots of the abundance and composition offishes (Continental Shelf
Associates, 1982; Gallaway andLewbel, 1982; Putt, 1982; Stanley and Wilson,
1990,1991).
In
response to the diYculty of estimating fish abun-dance at petroleum platforms
we used a stationary array of dual-beam hydroacoustics. Hydroacoustics provides
precise and accurate estimates of absolute abundance and size distribution, is not
aVected by poor visibility, can sample at night, has target detection
capabilities to macrozooplankton sizes, and has a greater range than do visual
methods.
The
objectives of this research were to use stationary dual-beam hydroacoustics
over a 15-month period to: (1) measure and compare the abundance of fishes
associ-ated with a petroleum structure over time, (2) define the spatial
near-field influence of the platform on fish abundance.
Methods
The
study was conducted at a production petroleum platform operated by Mobil
Exploration and Produc-tion USA, Inc., located 80 km south of the Louisiana coast
in 23 m of water. It was installed in 1978 and the nearest platform was 14.5
km.
Stationary
dual-beam hydroacoustic surveys were conducted monthly at the platform from
January 1991 through May 1992, with the exceptions of February and May 1991.
Two
arrays of stationary dual-beam hydroacoustic equipment were used. Array 1 was
designed to measure the density of fishes immediately adjacent to the
plat-form. It consisted of four vertically oriented transducers; one transducer
on each side of the platform providing acoustic coverage from 2 to 20 m. Array
2 estimated the local area of influence of the platform. It consisted of four
horizontally aligned transducers, one deployed on each side of the platform at
a depth of 11 m. This arrangement allowed for estimates of relative density from
2–72 m away from the platform.
Horizontal
and vertical acoustic sampling was carried out over consecutive 24 h intervals
for each sampling trip; 2 h of hydroacoustic data were collected encompassing
dawn, noon, dusk, and midnight.
Acoustic
data were collected and processed with Bio-Sonics hydroacoustic equipment; 120
kHz dual-beam transducers were deployed on the north and west sides of the
platform, and 420 kHz dual-beam transducers were deployed on the south and east
sides of the platform. Background noise levels were approximately 20 mV at 21 m
for Array 1 and 40 mV at 72 m for Array 2. The voltage threshold used in later
analyses was 100 mV, corresponding to a minimum detectable target strength of
"56 dB, or a fish of 2.5 cm total length according to Love (1971).
Vertical
density (log(density+1)) data were modeled using a randomized block ANOVA,
blocking on side of the platform, against depth, time of day, month, and their
interactions (SAS 1986). Horizontal density (log(density+1)) data were modeled
using a randomized block ANOVA, blocking on side of the platform, against
distance, time of day, month, and their interac-tions. The total abundance estimates
at the platform were calculated by determining the local area of influ-ence of
the platform, then multiplying mean density values for each month and platform
side, in number of fish m "3, by the volume of water on each side of the platform.
Results
Fish
density was highly variable over the study period, with monthly means ranging
from 0.04–0.50 fish m -3. Vertical fish density varied significantly
with month, platform side, and water depth. Significant variations in densities
were observed with time of day within month although a consistent diel pattern
was not observed. Little pattern in fish densities from month to month was
observed; densities varied by as much as a factor of five between months. Fish
density also varied with depth and was significantly greater from 4–12 m than from
16–20 m.
Horizontal
density varied with month, side of the platform, and distance from the
platform. Fish density decreased significantly with distance from the platform.
Densities within 16 m were significantly higher than densities from 16–72 m
(Fig. 1). Since the density of fishes dropped to background levels (i.e. less
than 0.05 fish m"3) (Stanley and Wilson, unpubl. data) at dis-tances
greater than 16 m from the platform we defined the local area of influence as
16 m.
The
population of fish associated with the platform fluctuated with month from a
low of 1988 &413 in January of 1991 to a high of 28 138 &5532 in
February 1992. Total abundance estimates were highly variable from month to
month with a maximum variation of approximately 6.6 times. The average number
of fish at the platform over the study period was 12 473&3251.
Figure
1. Mean horizontal fish density (number of fish m"3) from 2–72 m from a
petroleum platform for each side of the platform for the time period January
1991 to May 1992.
Discussion
Dual-beam
hydroacoustics was a useful method for assessing the abundance of fishes and
measuring the local area of influence of a petroleum platform. The most
dramatic results were the large monthly variations in density of fishes. This
is consistent with previous research at natural and artificial reefs which
exhibit large variations in density with time (Bohnsak et al., 1991; Ebeling
and Hixon, 1991; Sale, 1991). The current hypothesis regarding fish abundance
at reefs is the open non-equilibrial system, which proposes that substantial spatial
and temporal changes occurring at local reef populations are due to variable
recruitment, emigration, and immigration (Doherty and Williams, 1988; Ebeling and
Hixon, 1991; Sale, 1991).
Since
fish density varied with both platform side and depth, and target strength
varied with side of the plat-form, comprehensive spatial sampling is required
to describe the assemblages associated with these artificial reefs. The ability
to measure changes in density through-out the water column is crucial and we
were able to accurately survey nekton in the low visibility zones which could
not be assessed using visual surveys.
Dual-beam
hydroacoustics also gave the first measurement of the local area of influence
of an artificial reef. Past researchers have inferred it to range from 5–50 m
(Continental Shelf Associates, 1982; Gerlotto et al. , 1989). Based on the
horizontal density data results, we estimate the local area of influence at 16
m; at greater distances the fish densities are similar to those detected in the
open water of the Gulf of Mexico (Stanley and Wilson, unpubl. data).
Total
fish abundance estimates at this platform were higher than those reported in
other platform studies, with an average of 12 473 fish documented over the study
period. Other researchers found 283–3955 fish associated with individual
platforms (Continental Shelf Associates, 1982; Putt, 1982; Gerlotto et al.,
1989). DiVerences in the estimated fish abundances between this study and
previous investigations may be due to the larger area of influence measured in
this study, the ability to sample in low visibility conditions, and the unobtrusive
nature of hydroacoustics.
Acknowledgements
The
authors thank Mobil Exploration and Production USA, Inc. (MEPUS) for logistical
support and access to the West Cameron 352 petroleum platform. We also thank
the sta V of WC 352 and Messrs ‘‘Doc’’ Brinkley, Curtis Cain, Jerry Hagen,
Clyde Jones, JeV Passmore, and Alan Mathieson for their help and patience with
our activities. Comments by two anonymous reviewers greatly improved the quality
of the manuscript. This study is part of a dissertation written by the senior author
and was supported by the Louisiana Department of Wildlife and Fisheries,
Coastal Fisheries Institute, Louisiana State University, MEPUS, and the Mobil Foundation.
This is LSU-CFI Publication 95-2.
References
Bohnsak, J. A.,
Johnson, D. L., and Ambrose, R. F. 1991.Ecology of artificial reef habitats. In
Artificial habitats formarine and freshwater fisheries, pp. 61–108. Ed. by W.Seaman
Jr. and L. M. Sprague. Academic Press, New York.
Continental Shelf
Associates. 1982. Study of the eVect of oiland gas activities on reef fish
populations in Gulf of MexicoOCS area. OCS Report MMS 82-10. New Orleans,Louisiana.
US Department of the Interior, MineralsManagement Service, Gulf of Mexico Outer
ContinentalShelf Region. 210 pp.
Doherty, P. J. and
Williams, D. McB. 1988. The replenishmentof coral reef fish populations.
Oceanography and MarineBiology, 26: 487–551.Ebeling, A. W. and Hixon, M. A.
1991. Tropical and temperatereef fishes: comparison of community structures. In
Theecology of fishes on coral reefs, pp. 509–563. Ed. by P. F.Sale. Academic
Press, New York.
Gallaway, B. J. and
Lewbel, G. S. 1982. The ecology ofpetroleum platforms in the northwestern Gulf
of Mexico:a community profile. US Fish and Wildlife Service, OYceof Biology
Services, Washington, D.C. FWS 10BS-82/27.Openfile report 82-03. 92 pp.
Gerlotto, F.,
Bercy, C., and Bordeau, B. 1989. Echo integrationsurvey around o Vshore oil
extraction platforms o VCameroon: observations of the repulsive eVect on fish
ofsome artificially emitted sounds. Proceedings of the Instituteof Acoustics,
19: 79–88.
Love, R. H. 1971.
Dorsal aspect target strength of an individualfish. Journal of the Acoustical
Society of America, 62:1397–1403.
Putt, Jr, R. E.
1982. A quantitative study of fish populationsassociated with a platform within
Buccaneer oil field,northwestern Gulf of Mexico. MSc Thesis. Texas A&MUniversity.
College Station, Texas. 116 pp.
Sale, P. F. 1991.
Reef fish communities: open non equilibrial systems, pp. 564–600. In The ecology
of fishes on coral reefs.Ed. by P. F. Sale. Academic Press, New York.
SAS Institute
Incorporated. 1986. SAS user’s guide: Statistics,Version 6 Edition. Cary, North
Carolina SAS Institute.956 pp.
Stanley, D. R. and
Wilson, C. A. 1990. A fishery dependentbased study of fish species composition
and associated catchrates around petroleum platforms o V Louisiana. FisheryBulletin,
88: 719–730.
Stanley, D. R. and
Wilson, C. A. 1991. Factors aVecting the abundance of selected fishes near
petroleum platforms in thenorthern Gulf of Mexico. Fishery Bulletin, 89:
149–159.
No comments:
Post a Comment