Metadata:
  Identification_Information:
    Citation:
      Citation_Information:
        Originator: Dr. Richard E. Brock
        Originator: Sea Grant
        Originator: University Of Hawaii at Manoa
        Originator: Dr. Roger S. Fujioka
        Originator: Dr. Jamse E.T. Moncur
        Originator: Water Resources Research Center
        Originator: University Of Hawaii at Manoa
        Publication_Date: Unknown
        Title: COMMUNITY STRUCTURE OF FISH AND MACROBENTHOS
AT SELECTED SHALLOW-WATER SITES IN RELATION TO THE
BARBERS POINT OUTFALL, OAHU, HAWAII, 1991-1999
    Description:
      Abstract: This report provides the results of the eight years of an annual quantitative
monitoring of shallow marine communities inshore of the Barbers Point Ocean Outfall
located in 61 m of water offshore of Ewa Beach, Oahu, Hawaii. The monitoring effort
focuses on benthic and fish community structure and is designed to detect changes in
these communities. Field sampling was first carried out in August 1991 when three study
stations were established: Station BP-1, a control station 2.2 km inshore and east of the
outfall terminus; Station BP-2, an experimental station about 1.6 km inshore of the
terminus; and Station BP-3, an experimental station about 2.9 km west and inshore of the
terminus. The second field effort, completed in May and September 1993, resurveyed the
above stations as well as established a fourth station (BP-4) on and adjacent to the basalt
armor caprock protecting the discharge pipe in 13 m of water and directly inshore of the
outfall terminus. Subsequent field surveys were completed in March and April 1994, in
June 1995, in May 1996, in February and April 1997, in January and March 1998, and the
most recent in January 1999. These permanently marked stations are sited to capitalize on
presumed gradients of impact that may be created by the discharge and movement of
treated sewage effluent toward the shore and the coral reef communities. Data from the
first survey suggested that marine communities offshore of Ewa Beach receive
disturbance from a number of possible sources, with the largest perturbation probably
coming from natural disturbance caused by occasional wave impact. This was most
evident at the station directly inshore of the outfall. Data from Station BP-4 showed that
benthic communities situated on armor rock which rises above the flat limestone
substratum are not subjected to the same sand scour as those situated on the limestone;
thus the coral communities on the elevated caprock are better developed on this substrate.
A comparison of the data from the eight annual surveys indicated that no
statistically significant change has occurred in the measured biological parameters at
these permanent stations, despite the imposition of a major hurricane on these marine
communities in September 1992. Thus the data to date support the contention that the
operation of the Barbers Point deep-ocean outfall is not having a quantifiable impact on
the coral reef resources situated inshore of the outfall terminus.
      Purpose: Determine the status of the marine resources in the vicinity of the discharge 
in an effort to quantitatively ascertain if any impacts are occurring to the 
coral reef biota.
      Supplemental_Information: NOAASupplemental: 
Entry_ID: Unknown 
Sensor_Name: YSI Model 57 Oxygen meter
Sensor_Name: visual census 
Sensor_Name: hand-held refractometer
Source_Name: Water Resources Research Center/Sea Grant Annual Outfall Monitoring
Originating_Center: University of Hawaii Storage_Medium: ASCII, MS Word 
Reference: None 
Online_size: 8700 kilobytes
    Time_Period_of_Content:
      Time_Period_Information:
        Range_of_Dates/Times:
          Beginning_Date: 19910819
          Ending_Date: 19990127
      Currentness_Reference: ground condition
    Status:
      Progress: Complete
      Maintenance_and_Update_Frequency: Annually
    Spatial_Domain:
      Bounding_Coordinates:
        West_Bounding_Coordinate: -158.07
        East_Bounding_Coordinate: -158.03
        North_Bounding_Coordinate: 21.32
        South_Bounding_Coordinate: 21.3
    Keywords:
      Theme:
        Theme_Keyword_Thesaurus: None
        Theme_Keyword: Coastal studies,
        Theme_Keyword: Coral reef monitoring and assessment,
        Theme_Keyword: substatum percent cover (coral, algal, rock, sand)
        Theme_Keyword: macroinvertebrate census
        Theme_Keyword: fish census
        Theme_Keyword: fish species
        Theme_Keyword: fish biomass
        Theme_Keyword: invertebrate species
        Theme_Keyword: coral species
        Theme_Keyword: algal species
        Theme_Keyword: percent oxygen concentration
        Theme_Keyword: temperature
        Theme_Keyword: salinity
        Theme_Keyword: water clarity (turbidity), extinction
      Place:
        Place_Keyword_Thesaurus: None
        Place_Keyword: Pacific Ocean
        Place_Keyword: Hawaii
        Place_Keyword: Oahu
        Place_Keyword: Ewa Beach 
        Place_Keyword: Barbers Point (Kalaeloa)
      Stratum:
        Stratum_Keyword_Thesaurus: None
        Stratum_Keyword: Benthic
    Access_Constraints: None
    Use_Constraints: Dataset credit required
    Point_of_Contact:
      Contact_Information:
        Contact_Person_Primary:
          Contact_Person: Dr. Richard Brock
          Contact_Organization: Sea Grant/University of Hawaii
        Contact_Position: Principal Investigator
        Contact_Address:
          Address_Type: mailing address
          Address: 2525 Correa Rd, HIG 213
          City: Honolulu
          State_or_Province: Hawaii
          Postal_Code: 96822
          Country: USA
        Contact_Voice_Telephone: 808-956-2859
        Contact_Electronic_Mail_Address: brockr@hawaii.edu
    Data_Set_Credit: Water Resources Research Center
University Of Hawaii at Manoa
Sea Grant
    Native_Data_Set_Environment: ASCII text, MS Word
  Data_Quality_Information:
    Logical_Consistency_Report: see Process Step
    Completeness_Report: The surveys were 100% complete
    Lineage:
      Process_Step:
        Process_Description: SAMPLING STATIONS:
Four permanently marked stations were selected for the monitoring of benthic and
fish community response to possible sewage impacts. 
The first three stations (BP-1, BP-2, and BP-3) were
established in 1991 and the fourth (BP-4) in 1993. The stations and the rationale for their
selection are given below:
Station BP-1: Located about 2.2 km inshore and to the east (northeast) of the deep
ocean outfall terminus. This station, which is utilized as a control site, is located in water
ranging from 14.9 to 15.8 m in depth. Although complex, prevailing currents
move in an inshore and westerly direction approximately parallel to the shoreline (figure
34 in Laevastu et al. 1964). Thus this station is probably outside (to the east) of any
shoreward-moving sewage plume. The substratum at this station is primarily limestone,
with corals having a patchy distribution across it. Coral coverage may locally exceed
70%. Occasionally shallow sand areas located in depressions are found.
Station BP-2: Located about 0.25 km east of the sewer line and approximately 1.6
km inshore and slightly east (northeast) of the discharge terminus in water ranging from
11.3 to 11.9 m in depth. The substratum at this experimental site is a relatively featureless
limestone flat with few corals present.
Station BP-3: Located about 2.9 km west and inshore (northwest) of the terminus of
the sewage diffuser in water 16.5 to 16.8 m in depth. The substratum at this experimental
site is a mix of rubble/sand and emergent limestone with corals. Coral coverage, which is
about 25%, is greater at this station than at Station BP-2.
Station BP-4 Located on the sewer line and approximately 1.4 km inshore of the
discharge terminus in water ranging from 12.2 to 13.4 m in depth. The substratum varies
from basalt caprock overlying the discharge pipe to relatively flat and featureless
limestone adjacent to the discharge pipe. This station was established in 1993 to
demonstrate the effect that the elevated basalt caprock substratum has on benthic and fish
community development in an area that otherwise is flat and featureless and subjected to
occasional sand scour.
At each station two transect lines were permanently established using metal stakes
and plastic-coated no. 14 copper wire. The transects are 20 m in length and have an
orientation that is parallel to shore. Two transects were established at each location to
provide some replication. On each transect are five permanently marked locations (0 m, 5
m, 10 m, 15 m, and 20 m) for the taking of photographs of the benthic communities. A
single 0.67 m ? 1 m photographic quadrat was established at each of the marked points,
for a total sampling of 3.35 m2 of substratum on each transect line.
Because of a lawsuit initiated by Hawaiis Thousand Friends and the Sierra Legal
Defense Fund regarding the Barbers Point discharge in 1992-93, additional field
sampling was carried out beginning in 1993. The coverage by photo-quadrats was
increased from three to five sites, and a visual assessment of benthic communities using a
1 m x 1 m quadrat was made at each of the photo-quadrat sites (i.e., at the 0 m, 5 m, 10
m, 15 m, and 20 m points on each transect) to provide additional information regarding
smaller organisms not readily seen with the photo-quadrat method, such as recently
recruited benthic species. These changes have made both the photo- and visual quadrat
assessment methods the same as those used to survey the Sand Island deep-ocean outfall
stations offshore of Honolulu.

METHODOLOGY:
Background:
-----------
The Honouliuli Wastewater Treatment Plant (WWTP) located in Ewa, Oahu,
Hawaii, has been in operation since 1982. It releases approximately 22 mgd (0.96 m3/s)
of primary treated sewage through a 2,670-m pipe at a depth of 61 m offshore of Ewa
Beach, Oahu. In recent years controversy has arisen regarding the impact that sewage
effluent from the Honouliuli WWTP may have on inshore coral reef species.
Accordingly, commencing in 1991 this study was undertaken in an attempt to
quantitatively ascertain the impacts that may be occurring. 

Strategy:
---------
Marine environmental surveys are usually performed to evaluate the feasibility of,
and ecosystem response to, specific proposed activities. Appropriate survey
methodologies reflect the nature of the proposed action(s). An action that may have an
acute impact (such as channel dredging) requires a survey designed to determine the
route of least harm and the projected rate and degree of ecosystem recovery. Impacts that
are more chronic or progressive require different strategies for measurement.
Management of chronic stress to a marine ecosystem requires identification of system
perturbations that exceed boundaries of natural fluctuations. Thus a thorough
understanding of normal ecosystem variability is required in order to separate the impact
signal from background noise.
The impacts confronting the marine ecosystem offshore of Ewa Beach are most
probably those associated with chronic or progressive stresses. Because of the proximity
of the population center and industry to the east, marine communities fronting Ewa
Beach are probably subjected to a wide array of impacts. Thus a sampling strategy must
attempt to separate impacts due to wastewater treatment plant effluent on coral reef
communities located at some distance shoreward from a host of other possible
perturbations originating in the Honolulu and Pearl Harbor areas.
The waters fronting Ewa Beach, into which the deep-ocean outfall discharges, can
be considered in terms of gradients. There are numerous gradients due to point-source
and nonpoint-source (such as storm drains and streams) inputs that are occurring to the
east. Because many of these inputs have probably been occurring for a considerable
period of time, the species composition and functional relationships of the benthic and
fish communities at any given location in the waters offshore of Ewa Beach are those
that have evolved under the influence of these ongoing perturbations.
As noted above, if impacts are occurring in the shallow marine communities off
Ewa Beach because of effluent discharged from the deep-ocean outfall, they are
probably chronic in nature which would probably manifest themselves as a slow decline
in the communities so impacted. Gradients of stress or impact should be evident with
distance from impact source(s). Thus, to quantitatively define these impacts, one should
monitor these communities through time in areas suspected of being impacted, as well as
in similar communities at varying distances away from the suspected source(s). This
rationale has been used in developing the sampling strategy for this study.

Materials and methods:
----------------------
The quantitative sampling of macrofauna of marine communities presents a number
of problems, many of which are related to the scale on which one wishes to quantitatively
enumerate organism abundance. Marine communities in the waters offshore of Ewa
Beach may be spatially defined in a range of a few hundred square centimeters (such as
the community residing in a Pocillopora meandrina coral head) to many hectares (such
as areas which are covered by major biotopes). Because considerable interest focuses on
visually dominant corals, diurnally exposed macroinvertebrates, and fishes, we designed
a sampling program to delineate changes that may be occurring in communities at this
scale.
Fish abundance and diversity is often related to small-scale topographical relief
over short linear distances. A long transect may bisect a number of topographical features
(e.g., coral mounds, sand flats, and algal beds), thus sampling more than one community
and obscuring distinctive features of individual communities. To alleviate this problem, a
short transect (20 m in length), which has proven adequate for sampling many Hawaii
benthic communities (see Brock 1982; Brock and Norris 1989), was used.
Information is collected at each transect location using methods including a visual
assessment of fishes, benthic photo-quadrats and quadrats for field appraisals of cover
estimates by sessile forms (e.g., algae, corals, and colonial invertebrates), and counting of
diurnally exposed motile macroinvertebrates along the transect line. Fish censuses are
conducted over a 4 m x 20 m corridor (the permanent transect line). All fishes within this
area to the water's surface are counted. A single diver equipped with scuba, slate, and
pencil enters the water, then counts and records all fishes in the prescribed area (method
modified from Brock 1954). Besides counting the individuals of all fishes seen, the
length of each is estimated for later use in the determination of fish standing crop using
linear regression techniques (Ricker 1975). Species-specific regression coefficients have
been developed over the last 30 years by the author and others at the University of
Hawaii, the Naval Undersea Center (see Evans 1974), and the Hawaii Division of
Aquatic Resources from weight and body measurements of captured fishes; for many
species, the coefficients have been developed using sample sizes in excess of a hundred
individuals. The same individual (the author) performs all fish censuses to keep any bias
relatively constant between counts and stations.
Besides divers frightening wary fishes, other problems with the visual census
technique include underestimating the size of cryptic species such as moray eels (family
Muraenidae) and nocturnal species such as squirrelfishes (family Holocentridae) and
bigeyes or aweoweo (family Priacanthidae). This problem is compounded in areas
of high relief and coral coverage that afford numerous shelter sites. Species lists and
abundance estimates are more accurate for areas of low relief, although some fishes with
cryptic habits or protective coloration, such as scorpionfishes or nohu (family
Scorpaenidae) and flatfishes (family Bothidae), might still be missed. Another problem is
the reduced effectiveness of the visual census technique in turbid water. This is
compounded by the difficulty of counting fishes that move quickly or are very numerous.
Additionally, bias related to the experience of the census taker should be considered in
making comparisons between surveys. Despite these problems, the visual census
technique carried out by divers is probably the most accurate nondestructive assessment
method currently available for counting diurnally active fishes (Brock 1982).
A number of methods are utilized to quantitatively assess benthic communities at
each station, including the taking of photographs at locations marked for repeated
sampling through time (each covering 0.67 m2). Photographs provide a permanent record
from which coverage of corals and other sessile forms can be estimated. Cover estimates
from photographs are recorded as percent cover. Additionally, to help with later analysis
in the laboratory of the coverage recorded in photographs, a visual appraisal of each
quadrat is made in the field, and notes taken on the species present. Beginning with the
1993 survey, supplementary information on benthic coverage was obtained by using 1 m
x 1 m quadrats at the 0 m, 5 m, 10 m, 15 m, and 20 m points on each transect line. In
these quadrats a visual assessment of cover was made for each species present. Diurnally
exposed motile macroinvertebrates greater than 2 cm in some dimension are censused in
the same 4 m x 20 m corridor used for the fish counts.
If macrothalloid algae were encountered in the quadrats, they were quantitatively
recorded as percent cover. Emphasis was placed on those species that are visually
dominant, and no attempt was made to quantitatively assess the multitude of microalgal
species that constitute the algal turf so characteristic of many coral reef habitats.
As requested by regulatory agencies, divers made simple physical measurements at
the four stations. Measurements of percent oxygen concentration and temperature were
made with a YSI Model 57 Oxygen meter, salinity was taken with a hand-held
refractometer, and water clarity was determined using a 12-inch secchi disk. Oxygen
measurements were taken approximately 1 m below the water surface and 1 m above the
bottom.
Data were subjected to simple nonparametric statistical procedures provided in the
SAS Institute statistical package (SAS Institute Inc. 1985). Nonparametric methods were
used to avoid meeting requirements of normal distribution and homogeneity of variance
in the data. Data were analyzed using the Kruskal-Wallis analysis of variance to discern
statistically significant differences among ranked means for each transect site and
sampling period; this procedure is outlined by Siegel (1956) and Sokal and Rohlf (1995).
The a posteriori Student-Newman-Keuls multiple-range test (SAS Institute Inc. 1985)
was also used to elucidate differences between locations.
During fieldwork, an effort was made to note the presence of any green sea turtles
(a threatened species) within or near the study sites.

INSTRUMENT TYPES:
-SCUBA
-Visual census
-Photography
-Percent oxygen concentration and temperature were made with a YSI Model 57 Oxygen meter, 
salinity was taken with a hand-held refractometer, and water clarity was determined using 
a 12-inch secchi disk.

REFERENCES: 

Alevizon, W., R. Richardson, P. Pitts, and G. Serviss. 1985. Coral zonation and patterns
  of community structure in Bahamian reef fishes. Bull. Mar. Sci. 36:304-318.
Anderson, G.R.V., A.H. Ehrlich, P.R. Ehrlich, J.D. Roughgarden, B.C. Russell, and F.H.
  Talbot. 1981. The community structure of coral reef fishes. Am. Nat. 117:476-495.
Bathen, K.H. 1978. Circulation atlas for Oahu, Hawaii. Sea Grant Misc. Rep. UNIHI-
  SEAGRANT-MR-78-05, University of Hawaii Sea Grant College Program,
  Honolulu. 94 pp.
Brock, R.E. 1982. A critique on the visual census method for assessing coral reef fish
  populations. Bull. Mar. Sci. 32:269-276.
Brock, R.E., C. Lewis, and R.C. Wass. 1979. Stability and structure of a fish community
  on a coral patch reef in Hawaii. Mar. Biol. 54:281-292.
Brock, R.E., and J.E. Norris. 1989. An analysis of the efficacy of four artificial reef
  designs in tropical waters. Bull. Mar. Sci. 44:934-941.
Brock, V.E. 1954. A preliminary report on a method of estimating reef fish populations.
  J. Wildlife Mgmt. 18:297-308.
Connell, J. 1978. Diversity in tropical rain forests and coral reefs. Science 199:1302-
  1310.
Dollar, S.J. 1982. Wave stress and coral community structure in Hawaii. Coral Reefs
  1:71-81.
Eckert, G.J. 1985. Settlement of coral reef fishes to different natural substrata and at
  different depths. Proc. 5th Int. Coral Reef Congr. 5:385-390.
Evans, E.C. (editor). 1974. Pearl Harbor biological survey final report. Report No.
  NUC-TN-1128, Naval Undersea Center, Hawaii Laboratory.
Gladfelter, W.B., and E.H. Gladfelter. 1978. Fish community structure as a function of
  habitat structure on West Indian patch reefs. Rev. Biol. Trop. 26(Supplement 1):65-84.
Goldman, B., and F.H. Talbot. 1975. Aspects of the ecology of coral reef fishes. In
  Biology and Geology of Coral Reefs, Vol. III, Biology 2, ed. O.A. Jones and R.
  Endean, pp. 124-154. New York: Academic Press.
Grigg, R. 1983. Community structure, succession and development of coral reefs in
  Hawaii. Mar. Ecol. Prog. Ser. 11:1-14.
Grigg, R., and J. Maragos. 1974. Recolonization of hermatypic corals on submerged lava
  flows in Hawaii. Ecology 55:387-395.
Hamilton, P., J. Singer, and E. Waddell. 1995. Ocean current measurements. Project MB-
  6 (38 pp. + 2 appendixes) in Mamala Bay study final report, vol. I. Prepared by
  Mamala Bay Study Commission, Honolulu. Paginated by sections.
Highsmith, R.C. 1982. Reproduction by fragmentation in corals. Mar. Ecol. Prog. Ser.
  7:207-226.
Laevastu, T., D.E. Avery, and D.C. Cox. 1964. Coastal currents and sewage disposal in
  the Hawaiian Islands. HIG-64-1, Hawaii Institute of Geophysics, University of
  Hawaii, Honolulu. 101 pp.
Ogden, J.C., and J.P. Ebersole. 1981. Scale and community structure of coral reef fishes:
  A long-term study of a large artificial reef. Mar. Ecol. Prog. Ser. 4:97-104.
Ricker, W.E. 1975. Computation and interpretation of biological statistics of fish
  populations. Bull. Fish. Res. Bd. Canada 191. 382 pp.
Sale, P.J. 1977. Maintenance of high diversity in coral reef fish communities. Am. Nat.
  111:337-359.
Shulman, M.J. 1984. Resource limitation and recruitment patterns in a coral reef fish
  assemblage. J. Exp. Mar. Biol. Ecol. 74:85-109.
Shulman, M.J., J.C. Ogden, J.P. Ebersole, W.N. McFarland, S.L. Miller, and N.G. Wolf.
  1983. Priority effects in the recruitment of juvenile coral reef fishes. Ecology
  64:1508-1513.
Siegel, S. 1956. Nonparametric statistics for the behavioral sciences. New York:
  McGraw-Hill Book Co. 312 pp.
Sokal, R.R., and F.J. Rohlf. 1995. Biometry: The principles and practice of statistics in
  biological research. 3d edition. San Francisco: W.H. Freeman & Co. 887 pp.
Walsh, W.J. 1983. Stability of a coral reef fish community following a catastrophic
  storm. Coral Reefs 2:49-63.
Walsh, W.J. 1985. Reef fish community dynamics on small artificial reefs: The influence
  of isolation, habitat structure, and biogeography. Bull. Mar. Sci. 36:357-376.
Woodley, J.D., and 19 others. 1981. Hurricane Allen\306s impact on Jamaican coral reefs.
  Science 214:749-755.
        Process_Date: Unknown
        Process_Contact:
          Contact_Information:
            Contact_Person_Primary:
              Contact_Person: Dr. Richard Brock
              Contact_Organization: Sea Grant/University of Hawaii
            Contact_Position: Principal Investigator
            Contact_Address:
              Address_Type: mailing address
              Address: 2525 Correa Rd, HIG 213
              City: Honolulu
              State_or_Province: Hawaii
              Postal_Code: 96822
              Country: USA
            Contact_Voice_Telephone: 808-956-2859
            Contact_Electronic_Mail_Address: brockr@hawaii.edu
  Entity_and_Attribute_Information:
    Overview_Description:
      Entity_and_Attribute_Overview: FILE FORMATS: 
All files given as MS WORD 97 documents and redundant text files.



subdirectory: /dat/1991:
FILENAME      COMMENT
BPFM91.DOC    Original data report with tables
bp91doc.txt   same as text without tables

bp91app.doc
bp91app.txt   APPENDIX TABLE A.1.     RESULTS OF QUANTITATIVE VISUAL FISH CENSUS 
              CONDUCTED AT 3 LOCATIONS OFFSHORE OF EWA BEACH, OAHU, HAWAII, AUGUST 1991

bp91tb1.doc
bp91tb1.txt   TABLE 1.  SUMMARY OF BIOLOGICAL OBSERVATIONS MADE AT TRANSECT A
              (INSHORE) AT STATION BP-1, 20 AUGUST 1991

bp91tb2.doc
bp91tb2.txt   TABLE 2.  SUMMARY OF BIOLOGICAL OBSERVATIONS MADE AT TRANSECT B
              (OFFSHORE) AT STATION BP-1, 20 AUGUST 1991

bp91tb3.doc
bp91tb3.txt   TABLE 3.  SUMMARY OF BIOLOGICAL OBSERVATIONS MADE AT TRANSECT A
              (INSHORE) AT STATION BP-2, 19 AUGUST 1991

bp91tb4.doc
bp91tb4.txt   TABLE 4.  SUMMARY OF BIOLOGICAL OBSERVATIONS MADE AT TRANSECT B
              (OFFSHORE) AT STATION BP-2, 19 AUGUST 1991

bp91tb5.doc
bp91tb5.txt   TABLE 5.  SUMMARY OF BIOLOGICAL OBSERVATIONS MADE AT TRANSECT A
              (INSHORE) AT STATION BP-3, 19 AUGUST 1991

bp91tb6.doc
bp91tb6.txt   TABLE 6.  SUMMARY OF BIOLOGICAL OBSERVATIONS MADE AT TRANSECT B
              (OFFSHORE) AT STATION BP-3, 19 AUGUST 1991

subdirectory: /dat/1993:
BPFM93.DOC    Original data report with tables
bp93doc.txt   same as text without tables

bp93app.doc
bp93app.txt   APPENDIX. Results of Quantitative Visual Fish Censuses Conducted on 
              Two Transects Each at Four Stations Offshore of Ewa Beach, Oahu, Hawaii,
              25-26 May and 10 September 1993  

bp93tb1.doc
bp93tb1.txt   TABLE 1. Summary of Biological Observations Made at Transect BP-1-A, 
              2.2 km Inshore and Northeast of Barbers Point Deep Ocean Outfall Terminus 
              (Station BP-1), May 1993

bp93tb2.doc
bp93tb2.txt   TABLE 2. Summary of Results of the Photographic Quadrat Survey, 1993 

bp93tb3.doc
bp93tb3.txt   TABLE 3. Summary of Biological Observations Made at Transect BP-1-B, 
              2.2 km Inshore and Northeast of Barbers Point Deep Ocean Outfall 
              Terminus (Station BP-1), May 1993

bp93tb4.doc
bp93tb4.txt   TABLE 4. Summary of Biological Observations Made at Transect BP-2-A, 
              250 m East of the Discharge Pipe and 1.5 km Inshore and Northeast of 
              Barbers Point Deep Ocean Outfall Terminus (Station BP-2), May 1993

bp93tb5.doc
bp93tb5.txt   TABLE 5. Summary of Biological Observations Made at Transect BP-2-B, 
              250 m East of the Discharge Pipe and 1.5 km Inshore and Northeast of 
              Barbers Point Deep Ocean Outfall Terminus (Station BP-2), May 1993

bp93tb6.doc
bp93tb6.txt   TABLE 6. Summary of Biological Observations Made at Transect BP-3-A, 
              3.3 km West and Inshore of Barbers Point Deep Ocean Outfall Terminus 
              (Station BP-3), May 1993

bp93tb7.doc
bp93tb7.txt   TABLE 7. Summary of Biological Observations Made at Transect BP-3-B, 
              3.3 km West and Inshore of Barbers Point Deep Ocean Outfall Terminus 
              (Station BP-3), May 1993

bp93tb8.doc
bp93tb8.txt   TABLE 8. Summary of Biological Observations Made at Transect BP-4-A, 
              Situated on the Basalt Caprock of the Barbers Point Discharge Pipe, 
              Approximately 1.4 km Inshore (North) of Barbers Point Deep Ocean
              Outfall Terminus (Station BP-4), September 1993

bp93tb9.doc
bp93tb9.txt   TABLE 9. Summary of Biological Observations Made at Transect BP-4-B, 
              Situated on the Smooth Limestone Substratum 15 m East of the Basalt 
              Caprock of the Honouliuli Discharge Pipe, Approximately 1.4 km Inshore 
              (North) of Barbers Point Deep Ocean Outfall Terminus (Station BP-4), 
              September 1993

bp93tb10.doc
bp93tb10.txt  TABLE 10. Summary of Physical Measurements Made at Each Station 
              in the Vicinity of Transect Pairs, 2 October 1991 and 
              16 September 1993

subdirectory: /dat/1994:
BPFM94.DOC    Original data report with tables
bp94doc.txt   same as text without tables

bp94app.doc
bp94app.txt   APPENDIX. Results of Quantitative Visual Fish Censuses Conducted on 
              Two Transects Each at Four Stations Offshore of Ewa Beach, Oahu, Hawaii, 
              25 and 27 April 1994

bp94tb01.doc
bp94tb01.txt  TABLE 1. Summary of Biological Observations Made at Transect BP-1-A, 
              2.2 km Inshore and Northeast of Barbers Point Ocean Outfall Terminus 
              on 27 April 1994

bp94tb02.doc
bp94tb02.txt  TABLE 2. Summary of the Results of the Photographic Quadrat Survey for 
              Stations BP-1 Through BP-4, Barbers Point Ocean Outfall, Ewa Beach, Oahu, 
              Hawaii, 2-4 March 1994

bp94tb03.doc
bp94tb03.txt  TABLE 3. Summary of Biological Observations Made at Transect BP-1-B, 
              2.2 km Inshore and Northeast of Barbers Point Ocean Outfall Terminus 
              on 27 April 1994

bp94tb04.doc
bp94tb04.txt  TABLE 4. Summary of Biological Observations Made at Transect BP-2-A, 
              0.25 km East of the Discharge Pipe and 1.5 km Inshore and Northeast of 
              Barbers Point Ocean Outfall Terminus on 25 April 1994

bp94tb05.doc
bp94tb05.txt  TABLE 5. Summary of Biological Observations Made at Transect BP-2-B, 
              0.25 km East of the Discharge Pipe and 1.5 km Inshore and Northeast 
              of Barbers Point Ocean Outfall Terminus on 25 April 1994

bp94tb06.doc
bp94tb06.txt  TABLE 6. Summary of Biological Observations Made at Transect BP-3-A, 
              3.3 km West and Inshore of Barbers Point Ocean Outfall Terminus 
              on 25 April 1994

bp94tb07.doc
bp94tb07.txt  TABLE 7. Summary of Biological Observations Made at Transect BP-3-B, 
              3.3 km West and Inshore of Barbers Point Ocean Outfall Terminus 
              on 25 April 1994

bp94tb08.doc
bp94tb08.txt  TABLE 8. Summary of Biological Observations Made at Transect BP-4-A, 
              Situated on the Basalt Caprock of the Barbers Point Discharge Pipe, 
              Approximately 1.4 km Inshore (North) of Barbers Point Ocean Outfall
              Terminus on 25 April 1994

bp94tb09.doc
bp94tb09.txt  TABLE 9. Summary of Biological Observations Made at Transect BP-4-B, 
              Situated on Smooth Limestone Substratum 15 m East of the Basalt Caprock 
              of the Barbers Point Discharge Pipe, Approximately 1.4 km Inshore (North) 
              of Barbers Point Ocean Outfall Terminus on 25 April 1994

bp94tb10.doc
bp94tb10.txt  TABLE 10. Summary of Physical Measurements Made at Each Station in 
              the Vicinity of Transect Pairs, 2 October 1991, 16 September 1993, 
              and 28 April 1994

bp94tb11.doc
bp94tb11.txt  TABLE 11. Summary of the Biological Parameters Measured at Stations 
              Sampled in August 1991, May and September 1993, and April 1994

subdirectory: /dat/1995:
BPFM95.DOC    Original data report with tables
bp95doc.txt   same as text without tables

bp95app.doc
bp95app.txt   APPENDIX. Results of Quantitative Visual Fish Censuses Conducted on 
              Two Transects Each at Four Stations Offshore of Ewa Beach, Oahu, Hawaii, 
              19-20 June 1995

bp95tb01.doc
bp95tb01.txt  TABLE 1. Summary of Biological Observations Made at Transect BP-1-A, 
              2.2 km Inshore and Northeast of Barbers Point Ocean Outfall Terminus, 
              on 19 June 1995

bp95tb02.doc
bp95tb02.txt  TABLE 2. Summary of the Results of the Photographic Quadrat Survey for 
              Stations BP-1 Through BP-4, Barbers Point Ocean Outfall, Ewa Beach, Oahu, 
              Hawaii, February 1995

bp95tb03.doc
bp95tb03.txt  TABLE 3. Summary of Biological Observations Made at Transect BP-1-B, 
              2.2 km Inshore and Northeast of Barbers Point Ocean Outfall Terminus, 
              on 19 June 1995

bp95tb04.doc
bp95tb04.txt  TABLE 4. Summary of Biological Observations Made at Transect BP-2-A, 
              0.25 km East of the Discharge Pipe and 1.5 km Inshore and Northeast 
              of Barbers Point Ocean Outfall Terminus, on 19 June 1995

bp95tb05.doc
bp95tb05.txt  TABLE 5. Summary of Biological Observations Made at Transect BP-2-B, 
              0.25 km East of the Discharge Pipe and 1.5 km Inshore and Northeast of 
              Barbers Point Ocean Outfall Terminus, on 19 June 1995

bp95tb06.doc
bp95tb06.txt  TABLE 6. Summary of Biological Observations Made at Transect BP-3-A, 
              3.3 km West and Inshore of Barbers Point Ocean Outfall Terminus, 
              on 20 June 1995

bp95tb07.doc
bp95tb07.txt  TABLE 7. Summary of Biological Observations Made at Transect BP-3-B, 
              3.3 km West and Inshore of Barbers Point Ocean Outfall Terminus, 
              on 20 June 1995

bp95tb08.doc
bp95tb08.txt  TABLE 8. Summary of Biological Observations Made at Transect BP-4-A, 
              Situated on the Basalt Caprock of the Barbers Point Discharge Pipe, 
              Approximately 1.4 km Inshore (North) of Barbers Point Ocean Outfall
              Terminus, on 19 June 1995

bp95tb09.doc
bp95tb09.txt  TABLE 9. Summary of Biological Observations Made at Transect BP-4-B, 
              Situated on Smooth Limestone Substratum 15 m East of the Basalt Caprock 
              of the Barbers Point Discharge Pipe, Approximately 1.4 km
              Inshore (North) of Barbers Point Ocean Outfall Terminus, on 19 June 1995


bp95tb10.doc
bp95tb10.txt  TABLE 10. Summary of Physical Measurements Made at Each Station in the 
              Vicinity of Transect Pairs, 2 October 1991, 16 September 1993, 28 April 
              1994, and 22 June 1995

bp95tb11.doc
bp95tb11.txt  TABLE 11. Summary of the Biological Parameters Measured at Stations 
              Sampled in August 1991, May and September 1993, April 1994, and June 1995


subdirectory: /dat/1996:
BPFM96.DOC    Original data report with tables
bp96doc.txt   same as text without tables

bp96app.doc
bp96app.txt   APPENDIX. Results of Quantitative Visual Fish Censuses Conducted on Two 
              Transects Each at Four Stations Offshore of Ewa Beach, Oahu, Hawaii, 
              14-15 May 1996

bp96tb01.doc
bp96tb01.txt  TABLE 1. Summary of Biological Observations Made at Transect BP-1-A, 
              2.2 km Northeast and Inshore of Barbers Point Ocean Outfall Terminus, 
              on 14 May 1996

bp96tb02.doc
bp96tb02.txt  TABLE 2. Summary of the Results of the Photographic Quadrat Survey for 
              Stations BP-1 Through BP-4, Barbers Point Ocean Outfall, Ewa Beach, Oahu, 
              Hawaii, 1996

bp96tb03.doc
bp96tb03.txt  TABLE 3. Summary of Biological Observations Made at Transect BP-1-B, 
              2.2 km Inshore and Northeast of Barbers Point Ocean Outfall Terminus, 
              on 14 May 1996

bp96tb04.doc
bp96tb04.txt  TABLE 4. Summary of Biological Observations Made at Transect BP-2-A, 
              0.25 km East of the Discharge Pipe and 1.5 km Inshore and Northeast 
              of Barbers Point Ocean Outfall Terminus, on 14 May 1996

bp96tb05.doc
bp96tb05.txt  TABLE 5. Summary of Biological Observations Made at Transect BP-2-B, 
              0.25 km East of the Discharge Pipe and 1.5 km Inshore and Northeast 
              of Barbers Point Ocean Outfall Terminus, on 14 May 1996

bp96tb06.doc
bp96tb06.txt  TABLE 6. Summary of Biological Observations Made at Transect BP-3-A, 
              3.3 km West and Inshore of Barbers Point Ocean Outfall Terminus, 
              on 15 May 1996

bp96tb07.doc
bp96tb07.txt  TABLE 7. Summary of Biological Observations Made at Transect BP-3-B, 
              3.3 km West and Inshore of Barbers Point Ocean Outfall Terminus, 
              on 15 May 1996

bp96tb08.doc
bp96tb08.txt  TABLE 8. Summary of Biological Observations Made at Transect BP-4-A, 
              Situated on the Basalt Caprock of the Barbers Point Discharge Pipe, 
              Approximately 1.4 km Inshore (North) of Barbers Point Ocean Outfall
              Terminus, on 14 May 1996

bp96tb09.doc
bp96tb09.txt  TABLE 9. Summary of Biological Observations Made at Transect BP-4-B, 
              Situated on Smooth Limestone Substratum 15 m East of the Basalt Caprock 
              of the Barbers Point Discharge Pipe, Approximately 1.4 km Inshore 
              (North) of Barbers Point Ocean Outfall Terminus, on 14 May 1996

bp96tb10.doc
bp96tb10.txt  TABLE 10. Summary of Physical Measurements Made at Each Station in 
              the Vicinity of Transect Pairs, 2 October 1991, 16 September 1993, 
              28 April 1994, 22 June 1995, and 20 May 1996

bp96tb11.doc
bp96tb11.txt  TABLE 11. Summary of the Biological Parameters Measured at Stations 
              Sampled in August 1991, May and September 1993, April 1994, June 1995, 
              and May 1996

subdirectory: /dat/1997:
BPFM97.DOC    Original data report with tables
bp97doc.txt   same as text without tables

bp97tb01.doc
bp97tb01.txt  TABLE 1. Summary of Biological Observations Made at Transect BP-1-A, 
              2.2 km Northeast and Inshore of Barbers Point Ocean Outfall Terminus, 
              on 19 February 1997

bp97tb02.doc
bp97tb02.txt  TABLE 2. Summary of the Results of the Photographic Quadrat Survey for 
              Stations BP-1 Through BP-4, Barbers Point Ocean Outfall, Ewa Beach, Oahu, 
              Hawaii, 1997

bp97tb03.doc
bp97tb03.txt  TABLE 3. Summary of Biological Observations Made at Transect BP-1-B, 
              2.2 km Inshore and Northeast of Barbers Point Ocean Outfall Terminus, 
              on 19 February 1997

bp97tb04.doc
bp97tb04.txt  TABLE 4. Summary of Biological Observations Made at Transect BP-2-A, 
              0.25 km East of the Discharge Pipe and 1.5 km Inshore and Northeast 
              of Barbers Point Ocean Outfall Terminus, on 19 February 1997

bp97tb05.doc
bp97tb05.txt  TABLE 5. Summary of Biological Observations Made at Transect BP-2-B, 
              0.25 km East of the Discharge Pipe and 1.5 km Inshore and Northeast 
              of Barbers Point Ocean Outfall Terminus, on 19 February 1997

bp97tb06.doc
bp97tb06.txt  TABLE 6. Summary of Biological Observations Made at Transect BP-3-A, 
              3.3 km West and Inshore of Barbers Point Ocean Outfall Terminus, 
              on 21 February 1997

bp97tb07.doc
bp97tb07.txt  TABLE 7. Summary of Biological Observations Made at Transect BP-3-B, 
              3.3 km West and Inshore of Barbers Point Ocean Outfall Terminus, 
              on 21 February 1997

bp97tb08.doc
bp97tb08.txt  TABLE 8. Summary of Biological Observations Made at Transect BP-4-A, 
              Situated on the Basalt Caprock of the Barbers Point Discharge Pipe, 
              Approximately 1.4 km Inshore (North) of Barbers Point Ocean Outfall
              Terminus, on 19 February 1997

bp97tb09.doc
bp97tb09.txt  TABLE 9. Summary of Biological Observations Made at Transect BP-4-B, 
              Situated on Smooth Limestone Substratum 15 m East of the Basalt 
              Caprock of the Barbers Point Discharge Pipe, Approximately 1.4 km
              Inshore (North) of Barbers Point Ocean Outfall Terminus, 
              on 19 February 1997

bp97tb10.doc
bp97tb10.txt  TABLE 10. Summary of Physical Measurements Made at Each Station 
              in the Vicinity of Transect Pairs, 2 October 1991, 16 September 1993, 
              28 April 1994, 22 June 1995, 20 May 1996, and 27 February 1997

bp97tb11.doc
bp97tb11.txt  TABLE 11. Summary of the Biological Parameters Measured at Stations 
              Sampled in August 1991, May and September 1993, April 1994, June 1995, 
              May 1996, and February 1997

bp97tba1.doc
bp97tba1.txt  TABLE A.1. Results of Quantitative Visual Fish Censuses Conducted on 
              Two Transects Each at Four Stations Offshore of Ewa Beach, Oahu, Hawaii, 
              19 and 21 February 1997

bp97tba2.doc
bp97tba2.txt  TABLE A.2. Summary of Coral Cover Data for Each Visually Assessed Quadrat 
              on Each Transect for 1991 and 1993 Through 1997

subdirectory: /dat/1998:
BPFM98.DOC    Original data report with tables
bp98doc.txt   same as text without tables

bp98tb01.doc
bp98tb01.txt  TABLE 1. Summary of Biological Observations Made at Transect BP-1-A, 
              2.2 km Northeast and Inshore of Barbers Point Ocean Outfall Terminus, 
              on 29 January 1998

bp98tb02.doc
bp98tb02.txt  TABLE 2. Summary of the Results of the Photographic Quadrat Survey for 
              Transects at Stations BP-1 Through BP-4, Barbers Point Ocean Outfall, 
              Ewa Beach, Oahu, Hawaii, 1998

bp98tb03.doc
bp98tb03.txt  TABLE 3. Summary of Biological Observations Made at Transect BP-1-B, 
              2.2 km Inshore and Northeast of Barbers Point Ocean Outfall Terminus, 
              on 29 January 1998

bp98tb04.doc
bp98tb04.txt  TABLE 4. Summary of Biological Observations Made at Transect BP-2-A, 
              0.25 km East of the Discharge Pipe and 1.5 km Inshore and Northeast 
              of Barbers Point Ocean Outfall Terminus, on 29 January 1998

bp98tb05.doc
bp98tb05.txt  TABLE 5. Summary of Biological Observations Made at Transect BP-2-B, 
              0.25 km East of the Discharge Pipe and 1.5 km Inshore and Northeast 
              of Barbers Point Ocean Outfall Terminus, on 29 January 1998

bp98tb06.doc
bp98tb06.txt  TABLE 6. Summary of Biological Observations Made at Transect BP-3-A, 
              3.3 km West and Inshore of Barbers Point Ocean Outfall Terminus, 
              on 30 January 1998

bp98tb07.doc
bp98tb07.txt  TABLE 7. Summary of Biological Observations Made at Transect BP-3-B, 
              3.3 km West and Inshore of Barbers Point Ocean Outfall Terminus, 
              on 30 January 1998

bp98tb08.doc
bp98tb08.txt  TABLE 8. Summary of Biological Observations Made at Transect BP-4-A, 
              Situated on the Basalt Caprock of the Barbers Point Discharge Pipe, 
              Approximately 1.4 km Inshore (North) of Barbers Point Ocean Outfall
              Terminus, on 29 January 1998

bp98tb09.doc
bp98tb09.txt  TABLE 9. Summary of Biological Observations Made at Transect BP-4-B, 
              Situated on Smooth Limestone Substratum 15 m East of the Basalt Caprock 
              of the Barbers Point Discharge Pipe, Approximately 1.4 km Inshore 
              (North) of Barbers Point Ocean Outfall Terminus, on 29 January 1998

bp98tb10.doc
bp98tb10.txt  TABLE 10. Summary of Physical Measurements Made at Each Station 
              in the Vicinity of Transect Pairs, 2 October 1991, 16 September 1993, 
              28 April 1994, 22 June 1995, 20 May 1996, 27 February 1997, and 
              5 February 1998

bp98tb11.doc
bp98tb11.txt  TABLE 11. Summary of the Biological Parameters Measured at Stations 
              Sampled in August 1991, May and September 1993, April 1994, June 1995, 
              May 1996, February 1997, and January 1998

bp98tba1.doc
bp98tba1.txt  TABLE A.1. Results of Quantitative Visual Fish Censuses Conducted on 
              Two Transects Each at Four Stations Offshore of Ewa Beach, Oahu, Hawaii, 
              29 and 30 January 1998

bp98tba2.doc
bp98tba2.txt  TABLE A.2. Summary of Coral Cover Data for Each Visually Assessed Quadrat 
              on Each Transect for 1991 and 1993 Through 1998

subdirectory: /dat/1999:
BPFM99.DOC    Original data report with tables
bp99doc.txt   same as text without tables

bp99tb01.doc
bp99tb01.txt  TABLE 1. Summary of Biological Observations Made at Transect BP-1-A, 
              2.2 km Northeast and Inshore of Barbers Point Ocean Outfall Terminus, 
              on 11 January 1999

bp99tb02.doc
bp99tb02.txt  TABLE 2. Summary of the Results of the Photographic Quadrat Survey for 
              Transects at Stations BP-1 Through BP-4, Barbers Point Ocean Outfall, 
              Ewa Beach, Oahu, Hawaii, 1999

bp99tb03.doc
bp99tb03.txt  TABLE 3. Summary of Biological Observations Made at Transect BP-1-B, 
              2.2 km Inshore and Northeast of Barbers Point Ocean Outfall Terminus, 
              on 11 January 1999

bp99tb04.doc
bp99tb04.txt  TABLE 4. Summary of Biological Observations Made at Transect BP-2-A, 
              0.25 km East of the Discharge Pipe and 1.5 km Inshore and Northeast 
              of Barbers Point Ocean Outfall Terminus, on 11 January 1999

bp99tb05.doc
bp99tb05.txt  TABLE 5. Summary of Biological Observations Made at Transect BP-2-B, 
              0.25 km East of the Discharge Pipe and 1.5 km Inshore and Northeast 
              of Barbers Point Ocean Outfall Terminus, on 11 January 1999

bp99tb06.doc
bp99tb06.txt  TABLE 6. Summary of Biological Observations Made at Transect BP-3-A, 
              3.3 km West and Inshore of Barbers Point Ocean Outfall Terminus, 
              on 15 January 1999

bp99tb07.doc
bp99tb07.txt  TABLE 7. Summary of Biological Observations Made at Transect BP-3-B, 
              3.3 km West and Inshore of Barbers Point Ocean Outfall Terminus, 
              on 15 January 1999

bp99tb08.doc
bp99tb08.txt  TABLE 8. Summary of Biological Observations Made at Transect BP-4-A, 
              Situated on the Basalt Caprock of the Barbers Point Discharge Pipe, 
              Approximately 1.4 km Inshore (North) of Barbers Point Ocean Outfall
              Terminus, on 11 January 1999

bp99tb09.doc
bp99tb09.txt  TABLE 9. Summary of Biological Observations Made at Transect BP-4-B, 
              Situated on Smooth Limestone Substratum 15 m East of the Basalt 
              Caprock of the Barbers Point Discharge Pipe, Approximately 1.4 km
              Inshore (North) of Barbers Point Ocean Outfall Terminus, 
              on 11 January 1999

bp99tb10.doc
bp99tb10.txt  TABLE 10. Summary of Physical Measurements Made at Each Station 
              in the Vicinity of Transect Pairs, 2 October 1991, 16 September 1993, 
              28 April 1994, 22 June 1995, 20 May 1996, 27 February 1997, 
              5 February 1998, and 27 January 1999

bp99tb11.doc
bp99tb11.txt  TABLE 11. Summary of the Biological Parameters Measured at Stations 
              Sampled in August 1991, May and September 1993, April 1994, June 1995, 
              May 1996, February 1997, January 1998, and January 1999

bp99tba1.doc
bp99tba1.txt  TABLE A.1. Results of Quantitative Visual Fish Censuses Conducted 
              on Two Transects Each at Four Stations Offshore of Ewa Beach, Oahu, 
              Hawaii, 11 and 15 January 1999

bp99tba2.doc
bp99tba2.txt  TABLE A.2. Summary of Coral Cover Data for Each Visually Assessed 
              Quadrat on Each Transect for 1991 and 1993 Through 1999

NOTE: the text version of the MS WORD tables is of the following form:

column header(s)
row header(s)
  (row for each column header field)
additional row header(s)
  (row for each column header field given above,
   if a value is not given, then the respective row is blank)
additional row header(s)
  ....
  ....

For example, the text version of mo98tb6.doc starts out:

Transect
Parameter

T-1
T-2
T-3
T-4
T-5

No. of Algal Species
2
0
2
2
2

this would appear in the mo98tb6.doc file as:

                                Transect
Parameter                T-1    T-2    T-3    T-4    T-5
No. of Algal Species       2      0      2      2      2
      Entity_and_Attribute_Detail_Citation: None
  Distribution_Information:
    Distributor:
      Contact_Information:
        Contact_Organization_Primary:
          Contact_Organization: NOAA/NESDIS/National Oceanographic Data Center
          Contact_Person: Data Access Group, User Services Team
        Contact_Address:
          Address_Type: mailing and physical
          Address: SSMC-3 Fourth Floor
          Address: 1315 East West Highway
          City: Silver Spring
          State_or_Province: MD
          Postal_Code: 20910-3282
          Country: USA
        Contact_Voice_Telephone: 301-713-3277
        Contact_Facsimile_Telephone: 301-713-3302
        Contact_Electronic_Mail_Address: services@nodc.noaa.gov
        Hours_of_Service: 8am-5pm, Monday through Friday
    Resource_Description: NODC Accession Number 0000174
    Distribution_Liability: NOAA makes no warranty regarding these data,expressed or implied, nor does the fact of distribution constitute such a warranty.  NOAA, NESDIS, NODC and NCDDC cannot assume liability for any damages caused by any errors or omissions in these data, nor as a result of the failure of these data to function on a particular system.
    Standard_Order_Process:
      Digital_Form:
        Digital_Transfer_Information:
          Format_Name: MS Excel, and ACSII CSV
        Digital_Transfer_Option:
          Online_Option:
            Computer_Contact_Information:
              Network_Address:
                Network_Resource_Name: http://data.nodc.noaa.gov/accession/0000174
      Fees: Prices vary depending on data set, output medium and ordering mechanism. A standard handling charge, with additional costs for special handling, may be added to the basic cost of the data.
      Ordering_Instructions: Prepayment by check, money order or bank card is required. Orders may be placed via fax, email, regular mail, telephone or via the NNDC Online Store.
  Metadata_Reference_Information:
    Metadata_Date: 20090903
    Metadata_Contact:
      Contact_Information:
        Contact_Person_Primary:
          Contact_Person: Mr. Patrick C. Caldwell
          Contact_Organization: NOAA/NESDIS/NODC/NCDDC
        Contact_Position: Hawaii/US Pacific Liaison
        Contact_Address:
          Address_Type: mailing
          Address: 1000 Pope Road, MSB 316
          Address: Dept. of Oceanography
          Address: University of Hawaii at Manoa
          City: Honolulu
          State_or_Province: Hawaii
          Postal_Code: 96822
          Country: USA
        Contact_Voice_Telephone: (808)-956-4105
        Contact_Facsimile_Telephone: (808) 956-2352
        Contact_Electronic_Mail_Address: caldwell@soest.hawaii.edu
        Hours_of_Service: 8 AM to 5 PM weekdays
        Contact_Instructions: check services@nodc.noaa.gov if not available
    Metadata_Standard_Name: FGDC Content Standard for Digital Geospatial Metadata
    Metadata_Standard_Version: FGDC-STD-001-1998
