1. Sixty samples were collected from 12
locations in Purewa Creek, Hobson Bay, Orakei Creek and Orakei
Basin during December 97-January 98. Within each location, five
quadrats (0.25 m2) were randomly placed on the sediment surface
and all organisms counted. Sediment cores (15cm diameter, 15-cm
depth) were taken adjacent to these quadrats and organisms extracted
by washing through a 1-mm mesh sieve.
2. The only previous quantitative survey by Bioresearchers (1996)
had used 3 replicate core samples washed through a 0.5-mm sieve.
Their samples were characterised by large numbers of organisms
(often numbering several hundred) but low species richness. In
particular, they noted high abundances of polychaetes and amphipods.
3. Our samples were characterised by much lower abundances, possibly
due to the larger mesh size, which could have resulted in poor
retention of small worms and amphipods. Many of our samples from
Orakei Creek, for instance, contained empty tubes (likely to have
been from corophiid amphipods).
4. Both studies of Orakei Creek revealed average infaunal species
richness in the order of 4-8 species per core. Two additional
species were found in our quadrat sampling (which covers a much
larger surface area than the cores).
5. Our study, however, found a higher average richness of infauna
in Orakei Basin (6-10 species) compared to the earlier study (3.7
species). Of note was the fact that we found native cockles,
wedge shells and nut shells in the Basin. These had not been found
by Bioresearchers, probably because they had not sampled close
to the floodgate area.
6. Because of the low level of sampling by Bioresearchers in the
Basin (only 6 core samples) it is not realistic to directly compare
the two data sets to ascertain changes in recent years.
7. Surface algal mats were a feature of all 4 sites sampled in
Orakei Basin. These mats have the potential to eliminate native
epifaunal species while encouraging introduced species such as
Asian date mussels. However, the mats were not as thick
nor as foul-smelling as reported previously. This may have contributed
to the results obtained.
8. Our survey confirmed by Hayward's sampling, suggests that many
species from the general Hobson Bay area are already present in
at least some parts of Orakei Basin, but in low numbers.
9. Species likely to return to the Basin should it become fully
tidal are truly intertidal species that require regular exposure
to air (e.g., Diloma, Turbo, Amphibola, Xenostobus, and
of course mangroves). In addition, largely intertidal bivalves
such as cockles and wedge shells should increase in numbers.
10. Further sampling in the area (planned in April 1998) will
give a better indication of the distribution and abundance patterns
of the organisms present. It appears based on present information,
however, that the benthic ecology of Orakei Basin is constrained
by two main features - lack of regular tidal flushing and the
buildup of algal mats.