INTERIM
REPORT ON THE ARTIFICIAL REEF
CONSTRUCTED
IN THE LONG BAY-OKURA MARINE RESERVE, AUCKLAND
29th July 2002
PERMIT
AO1/1 26th APRIL 2001
Preamble:
The aim of the research was to construct two small
patterns of artificial reef comprising different sizes of pierced concrete
hemispherical shells. These were constructed utilising the American system
called Reefballs. Colonisation of these is now being monitored. It is hoped
to extend the study to include work on sedimentation rates and the impact on the
benthic population. It is anticipated that this activity will fulfil a range of
positive outcomes:
(i)
increase
conservation awareness from the use of the Reserve as an educational resource
and recreational dive site.
(ii)
permit
future informed decisions to be made on artificial reef construction in New
Zealand.
(iii)
monitor the
problems of run off which are faced by the reserve.
Reef 1 Zig
Zag Reef:
The reef is located at 360 40 52 S, 1740
45 14.8 E in 5.5 m at minimum spring low tides. It comprises twelve concrete
hemispherical shells made of 60 MPa concrete with microsilca added. There are
nine Bay Balls [mass approximately 300 kg, height 0.7 m, base diameter 1.0 m
with about 10 piercings] in a N S line. At the Northern end, there is a
Pallet Ball [mass approximately 1200 kg height 0.9 m; base diameter 1.2m with
about 15 piercings]. ]. At the Southern end, there are two further Pallet
Balls; one with a 30x30 cm slate plate attached to a vertical surface and the
other with a plate attached to close the top hole of the unit; i.e. in a
horizontal position. These slates are the same as the ones utilised by current
E. O. S. intertidal studies. Placement took approximately 6 weeks because of
tide/weather/logistical constraints. All 12 units lie on a N S line parallel
to the beach with an angle of approximately 450 between this line
and the zigzags and about 1.0 metre between each.
Reef 2
Octagon Reef.
The reef is located at 360 40 51.1 S,
1740 45 19.6 E in 6.2 m at minimum spring low tides. This also comprises
twelve units with four of the smaller Bay Ball units planted as the central
core. There are four Bay Balls around the perimeter; a Pallet Ball at the
Eastern point of the octagon; and one further Pallet Ball on the Southern
margin. There are slate plates attached to a vertical surface of both these
Pallet Balls. Another Pallet Ball is placed on the western side. The last
Pallet Ball forms a tail to the south since inclement weather prevented it
being placed in geometrical perfection. All the spacings are again about 1.0
metre.
Colonisation
sequence:
Hard surfaces were colonised firstly by planktonic
organisms, e.g. pelagic phytoplankton. The first settlement to be observed
(after a period of about 6-7 days) was a microfilamentous brown algae
(unidentified, but common in the Gulf). The next colonising organisms were
vagrant (and opportunistic) benthos, such as the cushion star: Patiriella regularis, and the hermit
crab: Pagurus sp. c.f. P. novaezelandiae and herbivorous
gastropods like the whelk: Cominella
adspersa (egg cases of the latter were recorded on a number of the
reefballs). Concurrent with this, nektonic organisms like the
spotty: Notolabrus celidotus and
triplefins: Fosterygium varium and Fosterygium sp. feed on small invertebrates
and graze on the algae. The next wave of colonisation observed was that of
sciaphilic invertebrates such as barnacles and polychaete worms. Two
settlements of the rapidly colonising barnacle Austrominius modestus were recorded; the first occurring about ten
days after the placement of the reefballs. A second, more numerous settlement
event of A. modestus occurred about
four weeks later. Of the annelids, the first was the spiny tubeworm: Spirobranchus cariniferus which settled
about two-three weeks after reefball placement. After a month, these reached
lengths of up to 12 mm.
Both artificial reefs are close to being fully
colonised. Biodiversity on the two reefs is still somewhat low but new species
continue to colonise the reef. Most noticeable was the new settlement of the
ascidian (Sea squirt) Asterocarpa
coerulea around the sides of numerous of the Reef Balls. Larger
macro-algae, brown seaweed Carpophyllum
maschalocarpum (still at early stage approximately 5cm long) is
establishing itself around the top of some of the Reef Balls. Also identified
on the zigzag reef were two Large Trophon (Xymene
ambiguus), these are typically sandy shore species and are probably
resident in the area. A new fish
species, a juvenile Sweep (Scorpis lineolatus)
was present at the Octagon Reef. Juvenile sweep are often found on shallow
reefs, close to shelter (provided by the Reef Balls?).
The unidentified filamentous brown algae still
dominates coverage on the reef balls, however the barnacle A.modestus are now densely populated particularly on the zigzag
reef, with several settlements of barnacles evident (small and large live
shells, and older empty shells). A.modestus
is also dominating percentage coverage on the slate tiles over the spiny
tubeworm Spirobranchus cariniferus (which
was formally dominant). Numbers of Cominella
adspersa and the starfish Patiriella
regularis appear down. What appeared to be snapper divots were observed
around the surrounding reefs. There appears to be an abnormally high sedimentation
rate on the two Artificial Reefs, which may contribute to the absence of some
organisms. Further studies on sedimentation rates will hopefully follow.
May - June 2002
Zigzag Reef:
The zigzag reef is now entirely colonised. The make
up of organisms on the reef has markedly changed over the past few months. Both
biodiversity and biomass of organisms on and immediately around the reefballs
has increased, with the appearance of a host of new organisms and an increase
in numbers of some already existing organisms (personal observations). Most
noticeable was the number of fish, a few new species of which may now be
resident. The zigzag reef has seen the arrival of a number of juvenile fish
from the summer spawning season, seeking shelter and food, swimming in and
around the reef. Schools of small Snapper (less than 90mm long in schools
>50), Trevally (less than 100mm long in schools >50), Blue Maomao, and
Sweep (less than 70mm), were observed swimming around the reef, with dozens of
juvenile Goatfish (Upeneichthys lineatus),
(less than 90mm in length), pale in colour swimming along the bottom feeding on
small invertebrates in and amongst the reefballs. There were also numerous
adult Parore (Girella tricuspidata)
swimming in amongst the reefballs, some large up to 300-350mm long, some adult
Red Pig Fish. The Spotties, Triplefins, and adult Sweep are still present in
similar numbers. The triple fins have increased in size. There were many
snapper divots around the reef, and a few larger snapper (up to around 250mm)
were seen on the outskirts of the reef, at the edge of our level of visibility.
The once dominant filamentous algae has been greatly
reduced in percent coverage to a few percent only. It has been replaced with a
dense covering of barnacles (A.modestus),
tube worms (including Spirobranchus
cariniferus), and rock oysters (Saccostrea
glomerata). These are already creating second and third layers in places
colonising on top of dead and empty shells already attached to the reefballs.
There are now at least three different tubeworms
including Chaetopteros sp, and Spirobranchus cariniferus. The third species (unidentified) has a
large surface coverage on the outside of the reefballs (approx 20%). There have
been at least two different settlements of S.glomerata
with an older smaller settlement of oysters up to 40mm long (1-2% coverage)
and a more numerous recent settlement of oysters up to 20mm long (approx 10%
coverage). The oysters are more prominent on the inside cavity walls and hole
walls of the reefballs than the outside.
There is a small number of juvenile green-lipped
mussels (Perna caniculus),
approximately 2 cm long, establishing themselves in the base of the side hole
walls. New gastropods to the zigzag reef include the Siphon Whelk (Penion sulcatus), the Spotted Whelk (Cominella maculosa), and the Oyster
Borer (Lepsiella scobina) which are
all carnivorous and were located on the outside of the reefballs.
Brown macro-algae up to 10cm long (possibly Halopteris novae-zelandiae) is
establishing itself within the holes of the reefballs with at least two species
of sponges also are colonising the outside of reefballs. Dozens of small
shrimps are to be seen seeking shelter in small cracks underneath the
reefballs.
The population of cushion stars is noticeably down
from previous dives, with an increase of a larger starfish, Coscinasterias calamaria (up to 200mm)
resting in the holes of the reefballs and on inside cavity walls.
Colonisation on the
octagon reef is not yet complete at around 80-90%. The colonisation makeup is very similar to that of the zigzag
reef with a few differences, most notably the difference in coverage of
barnacles and oysters. Very few oysters and barnacles have colonised the
octagon reef in comparison to the zigzag reef. The filamentous algae is still
present though in increasingly smaller coverage but the tubeworms have a much
greater dominance (S,cariniferis, and
the unidentified species). There are
similar numbers and species of juvenile fish present, with various schools
sheltering within the octagon.
Overall change in biota:
New organisms are present in the area. These have
either migrated from other parts of the marine reserve, or have settled from
the moving water body. (A combination of both is likely). The latter group
probably would not have colonised the area if the reefballs had not been
present. It is very encouraging to
observe such large numbers of juveniles present.
Comparison of surfaces:
No significant differences in the colonisation of the
smooth areas of concrete surface, rough aggregate surfaces nor the slate plates
have been noted.
Bottom Conditions:
Sediment: The sites selected have bottom sediments classified as grey-brown shelly muddy fine sand. Sediments around the reefballs contain a larger amount of fine silt than could be expected in this environment. The origin of this is probably urban run-off. There are large numbers of empty bivalve shells on/near the surface.
Two trial sedimentation collectors (made from a PVC
pipe 100mm in diameter and 700mm long, staked to the seafloor) have been tested
around the octagon reef in attempt to study the rates of sedimentation.
Settlement: The reefballs still show no appreciable settlement
into the sediment. The holes in the base of the units were left open and no
additional thickening measures taken in manufacture. There have been many
storms over the period with onshore winds gusting up to 100 kmh-1
however the site selected appears to be well protected, with the artificial
reef remaining stable with no significant scouring even after storm periods.
Concrete pH Tests
Tests of the
surface pH of the well-weathered units stored at Gibbons Crib Walls show that
the surface pH lies in the range 8 9. Technical difficulties with the AUT
Datasonde have prevented any meaningful results being taken from the reefballs
in the water as yet. The lack of difference in colonisation between the
available surfaces tends to indicate that the pH range of the concrete
substrate is satisfactory.
Project team:-
|
Supervisor:- Professor John Buckeridge
|
Jonathan Jaffrey
Trent Taylor |
Earth and Oceanic Science
Research Centre Faculty of Science and Engineering
|
|
Paul
Murphy |
Auckland University of
Technology
|