P.I. - Dr. James Moncur, Economics
Sponsor - City of Honolulu, Wastewater Management Department
Researchers at the University of Hawaii's Water Resources Research
Center (WRRC) continue to monitor the marine fauna around the City and County
of Honolulu's ocean sewage outfalls at Sand Island, Barbers Point, Waianae
and Mokapu. This monitoring is performed in order to detect any effects
that the discharge of sewage effluent at the outfall may be having on the
surrounding ecosystem, and is conducted in partial fulfillment of the requirements
for a waiver from secondary treatment granted to the Sand Island Wastewater
Treatment Plant (SIWWTP) by the Federal Environmental Protection Agency
(EPA). The following describes the work done at Sand Island, however most
of the same research tasks are also being done at the abovementioned other
outfalls.
WRRC researchers started monitoring the benthic fauna around the City's outfalls on an irregular basis in 1985. In 1995 the Center
completed a 5 year contract with the City's Department of Wastewater Management to monitor marine life at the Sand Island, Barbers
Point, and Waianae outfalls annually, and at the Mokapu outfall once during this period. In 1997 another 5 year contract was entered into, followed by another in 2002, and the biomonitoring work continues. In order to detect changes over time, every effort has been made to be consistent in the methodology used from year to year. Due to extreme natural fluctuations inherent in populations of the marine organisms being monitored, differentiating between natural changes and man-made changes is problematic. In order to be able to tell if a change in the population of organisms is within the bounds of natural variability or is due to pollution, a sufficiently lengthy period of observation is needed to determine what the normal fluctuations are, and to be able to tell when there is a true imbalance.
The WRRC team performs a variety of studies in the vicinity of the outfalls. One type of study involved obtaining samples of
sediment from the ocean floor at various locations around the outfalls and sorting through this material to determine the types and
numbers of certain groups; polychaetes (worms), mollusks, and crustaceans, of bottom dwelling organisms living therein. The research
team comprises some of Hawaii's foremost authorities on the biology of these groups of organisms. Samples are taken from the same
locations every year in order to see if changes in the population makeup and distribution are occuring. Such changes could
indicate imbalances in the ecosystem around the outfall.
The work performed by the WRRC biomonitoring group is only one facet of the
overall study conducted at the outfalls. Samples of sediment are also sent to
an EPA certified contract lab on the mainland for chemical analysis to detect
a number of so-called priority pollutants according to EPA guidelines. Other
chemical analyses are performed by the City's own laboratory. Some of the parameters
examined include total organic carbon, oil and grease, total Kjeldahl nitrogen,
oxidation-reduction potential, and grain size analysis. Changes in these parameters
can signal an accumulation of sewage derived sediment around the outfall.
Another aspect of the study looks at larger life forms around the outfall. Fish and coral communities at various sites are observed
and quantified.
As with the sediment dwelling animals, the fish and corals are monitored at the same sites every year. These fish and coral censuses
are performed by divers in shallow waters shoreward of the diffuser pipe. Further out, at the diffuser where the depth of water
makes diving hazardous, remotely controlled video cameras are used to monitor the fish and other animals.
In 1994 a supplemental study was added to the project. Livers removed from fish caught at sites around the outfall are analyzed for
pathological changes to the cells that could be attributable to pollution.
The data collected are analyzed statistically, significant changes in any population observations or parameters of chemistry are
noted, and the findings are reported to the EPA for their consideration.
SUMMARY OF OBSERVATIONS
AT SAND ISLAND 1990-1995
POLYCHAETES
Dr. Julie Brock, University of Hawaii, Department of Zoology

Polychaete abundance and species composition have remained stable over the years of study,
with Station B3 (see figure 1 - Sand Island outfall) usually having fewer species and lower abundances than the other six stations.
The only species to appear in large numbers at zone of initial dilution (ZID) stations Z and B3 from 1987 (even before the
monitoring period reported here) to 1992 was Neanthes arenaceodentata, but its numbers declined and it was not found
at Station B3 in 1993 and 1994. Only three individuals of this species were present in 1994 and 1995. A smaller species,
Ophyotrocha spA become abundant at some of the ZID stations in 1995.
CORAL REEF STUDY
Dr. Richard E. Brock, University of Hawaii, Hawaii Institute of Marine
Biology
Analysis of the five years of data collected from the six permanently marked transects at the coral reef stations shows that there
has been no statistically significant change in the following biological measures: percent coral cover, number of invertebrate
species, total number of invertebrates, number of fish species, total number of fish, and biomass of fishes present at each station.
The mean number of coral species has shown a statistically significant increase over the five-year period. Hurricane Iniki,
which occurred in September 1992, impacted marine communities along the south shore of O'ahu. Coral communities received
considerable damage, especially at the westernmost study site. Recovery in these communities is evident from the data collected
since the storm.
CRUSTACEANS
Dr. William J. Cooke
The crustacean community in the area of the Sand Island outfall is the least diverse of the
three south shore outfalls monitored , with 68 taxa collected through 1994. The average yearly collection has included
approximately 37 taxa. Typically, Sand Island stations have between 5 and 19 taxa. The only outfall effect appears to be at
Station B3, which has consistently been lowest (except in 1992 when it was second lowest) in diversity. Other stations which
might be expected to experience some effects from the outfall (such as Station Z) have shown reasonable diversity since 1990.
Whatever impact the outfall may be having on crustacean populations, it appears to be restricted to the area immediately adjacent
to the end of the outfall pipe.
MOLLUSKS
Dr. E. Alison Kay, University of Hawaii, Department of Zoology
The patterns of abundance and species composition of the benthic assemblages of micromollusks were repeated year
after year between 1990 and 1994 in a series of peaks and valleys, each peak or valley marking one of the seven stations and showing
impressive stability, but neither peaks nor valleys appear to reflect the influence of the wastewater outfall. The most abundant
micromollusks are three species of epifaunal detritivores and the sea cucumber parasite Balcis. Mollusk abundance is
consistently greatest at station B2 with a lesser abundance peak at B4; relatively more species are collected at the easternmost
stations, B5 and B6. Station B1 is recognizable as the only station with large numbers of the microgastropod Finella
pupoides.
Click on this picture to see a graph of mollusk counts at the Sand Island sampling stations from 1986
to 1995
REMOTE VIDEO INSPECTION
Dr. Richard E. Brock, University of Hawaii, Hawaii Institute of Marine Biology
Because the Sand Island Ocean Outfall diffuser lies at depths below safe diving limits, remotely controlled
video cameras have been used annually since 1991 to inspect the marine communities along the pipe. This system provides data
which are difficult to quantify, and many uncontrollable variable factors such as weather, water clarity, winds, and currents
can dramatically affect the quality of the videotapes. Other difficulties inherent in the remote video system include poor
camera resolution, constantly changing camera angle, small fish sizes, and the fishes' nature to flee from the approaching
camera. Nevertheless, the tapes are useful in affording the researchers a qualitative perspective on communities in the deep
water along the diffuser pipe. Five permanent transects have been established along the 1,036-meter-long diffuser. These
cover about 40% of the total length of the pipe. The 1992 tape showed an increase in number of species, number of individuals,
and total biomass over 1991. The 1993 tape showed a decrease in these parameters from the previous year. In 1994 these
numbers rose again. Changes in the mean numbers of fish between these time periods were statistically significant, but
changes in biomass were not. Starting in the year 2000 the ROV studies will be discontinued at the Sand Island outfall as
the EPA believes that the data already collected is sufficient.
FISH LIVER HISTOPATHOLOGY
Dr. James A. Brock, Department of Land and Natural Resources
Chronic exposure to cancer-inducing chemicals has been associated with the increased occurrence of skin and liver
tumors in wild fish populations. The shelter and protection from predators afforded by the outfall and diffuser pipes have
resulted in a relatively high fish population density around the outfall. Necropsy was carried out in 1992, 1994, and 1995
on fish collected along the Sand Island Ocean Outfall diffuser to determine if tumors indicative of exposure to cancer-inducing
chemicals are occurring on fish exposed to the effluent. No skin or liver neoplasms were found in the 71 fish representing six
species examined.
DATA ANALYSIS
The data obtained in the analysis of the sediment samples were subjected to a number of statistical tests designed
to detect significant changes in the populations of benthic organisms found at the various sampling sites spatially and from year
to year. The response patterns of benthic infauna near the Sand Island, Barbers Point, Waianae, and Mokapu Ocean Outfalls showed
little indication of a strong influence of the sewage effluent.
Additional information can be obtained by contacting:
Water Resources Research Center
University of Hawaii at Manoa
2540 Dole St. Holmes Hall 283
Honolulu, HI 96822
tel: (808) 956-7847
fax: (808) 956-5044
email: morav@hawaii.edu