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,oastal Zone Information Center J, 7) A cql- v APPENDIX 2-COASTAL CURRENTS HAWAII INSTITUTE OF GEOPHYSICS QE 500 .H35 no.64-1 Ae HAWAII'S SHORELINE Appendix II COASTAL CURRENTS AND SEWAGE DISPOSAL IN THE HAWAIIAN ISLANDS By Taivo Laevastu, Don E. Avery, and Doak C. Cox June 1964 FINAL REPORT This report was prepared as part of the Coastal Currents Project supported by contract with the Department of Planning and Economic Development, State of Hawaii. The preparation of the report was financed in part through an Urban Planning Grant from the Housin and Home Finance Agency under the provisions of Section 701 of the Housing Act of 1954 as amended. Approved by Director Date: 30 June 1964 HAWAII INSTITUTE OF GEOPHYSICS UNIVERSITY OF HAWAII CONTENTS Page CONTENTS iii List of Figures v List of Tables viii 1. INTRODUCTION 1 1.1 Waste Disposal in Coastal Waters of Hawaii 1 1.2 Importance of Coastal Currents 5 1.3 Previous Studies of Currents in Hawaiian Coastal Waters 6 1.4 The Present Studies 9 1.5 Scope and Organization of Report 11 1.6 Acknowlediments 12 2. COMPONENTS OF COASTAL CURRENTS IN HAVIAtj 13 @@.l Components of Coastal Currents in Hawaii 13 2.2 The Permanent Flow and its Eddie's 14 2.3 Tidal Currents 16 2.4 Island Effects 18 2.5 Island and Submarine Topographic Effects 22 2.6 Wind-driven Currents and Mass Transport by Waves 24 3. COASTAL CURRENTS AROUND NIIHAU ADD KAUAI 29 3.1 Niihau 29 3.2 Western Kauai 29 3.3 Northern Kauai 30 3.4 Eastern Kauai 30 3.5 Southern Kauai 31 3.6 Summary of Coastal Currents Around Niihau and Kauai 31 4. COASTAL CURRENTS AROUND OAHU 33 4.1 Northwest Coast 33 4.2 Northeast Coast-Kabuku to Ulupau Head 34 4.3 Kaneohe Day 35 4.4 Kailua. 36 4.5 Waimanalo 37 4.6 Koko Head to Makapuu 38 4.7 Mauhalua Bay 38 4-8 mamala Bay 39 4:9 Ala Wai to Kewalo 45 4.10 Honolulu Harbor-Keehi Lagoon 46 4.11 Pearl Harbor 46 4.12 Southwest Coast 47 4.13 Summary of Coastal Currents Around Oahu 49 iii iv CONTENTS (continued) Pa ge 5. COASTAL CURRENTS AROUND MOLOKAI., LANAI, KAHOOLAWE, AND MAUI 53 5.1 Molokai 53 5.2 Lanai 53 5.3 Kahoolawe 54 5.4 West Maui 54 5.5 Kahului Bay and Harbor 55 5.6 North Coast of East Maui 56 5.7 South Coast 56 5.8 Alalakeiki Channel 57 5.9 Southwest Coast 57 5.10 Summary of Coastal Currents Around Islands of the Maui Group 57 6. COASTAL CURRENTS AROUND HAWAII 59 6.1 Alenuihaha Channel 59 6.2 Northeast Coast 59 6.3 Hilo Harbor 6o 6.4 Southeast Coast 6o 6.5 Southwest Coast 61 6.6 Kailua-Kona 61 6.7 Northwest Coast 61 6.8 Summary of Coastal Currents Around Hawaii 62 7. SOME CHEMICAL., BIOLOGICAL, AND GEOLOGICAL OBSERVATIONS PERTAINING TO SEWAGE DISPOSAL 63 7.1 Distribution of Chemical Properties off Sand Island Sewer and in Kaneohe Bay 63 7.2 Bottom Deposits off Sand Island Sewer 64 7.3 Bacterial Die-off in the Sea 64 7.4 Biological Oxy@en Demand of Sea Water 67 8. APPLICATION OF COASTAL CURRENT AM RELATED INFORMATION TO SEWAGE DISPOSAL PROBLEMS IN COASTAL WATERS 69 8.1 Processes of Dispersal and Decomposition of Sewage at Sea 69 8.2 Estimation of Rates of Transport, Disper- sal, and Bacterial Die-off 72 8.3 Requirements in Coastal Current Studies for Sewage Disposal Projects 75 9. CONCLUSIONS AND REC%ffv]EVDATI0VS 77 10. ANNOTATED BIBLIOGRAPHY OF COASTAL CURRENTS IN HAWAII 81 v COMETS (continued)@ Page 11. REFERENCES 95 List of Figures Figure No. Facing Page 1. Index map of the Hawaiian Islands showing points of waste disposal into the sea and areas in which coastal currents have been investigated 4 2. February surface currents in the vicinity of the Hawaiian Islands indicating the permanent flow -pattern as deduced from dead reckoning 14 3. August surface currents in the vicinity of the Hawaiian Islands indicating the permanent flow pattern as deduced from dead reckonin6 16 4. Co-tidal chart for the Hawaiian Islands 18 5. Diagram showing superposition of tidal current vectors and resultants with permanent flow 20 6. Diagram showing current patterns around a simple circular island 22 7. Diagram showing slope convergences resulting from coupling of coastal reciprocating and offshore rotary tidal currents 24 8. Directions of drift drogues frcm two 24-hour cruises off Waianae 26 9. Results of droGue measurements of currents around Kauai 30 10. Paddle-wheel current-meter measurements from southeast of Nawiliwili, Kauai, (top) July 23-24, (bottom) July 25, 1963 32 11. Currents on the Kapaa Reef 32 Vi COMENTS (continued) Figure No. Facing Page 12. Index map to fiL;ures showing coastal currents around Oahu 34 13. Results of measurements of currents near Kaena Point, Oahu, on January 3-4, 1963 34 14. 'Results of drogue measurements of currents in Kaneohe Bay, Oahu, September 4-6, 1962 36 15. Results of droL@ue measurements of currents off Waimanalo, September 11, 1962 38 16. Results of drogue measurements of currents off Waimanalo., February 23, 1963 38 17. Results of Paddle-wheel current-meter measure- ments off Waimanalo, (top) July 15-16, (bottom) July 16-17, 1963 38 18. Results of paddle-wheel current-meter measure- ments off Wailupe Peninsula, July 11-12, 1963 38 19. Results of paadle-wheel current-meter measure- ments off Diamond Head, (top) November 24-25, (bottom) November 26-27, 1963 4o 20. Results of paddle-wheel current-meter measure- ments off Diamond Head, (top) December 4-:5, (bottom) December 8-9, 1963 4o 21. Results of paddle-wheel current-meter measure- ments off MaE;ic Island, (top) November 11-12, 1963, and off Kewalo, (bottom) August 16-17, 1963 4o 22. Results of paddle-wheel current-meter measure- ments near Sand Island sewer outfall, (top) August 4-5, (bottom) August 9-10, 1963 4o 23. Results of paadle-wheel current-meter measure- ments (top) southeast of Barbers Point, July 5-6y 1963, and (bottom) northwest of Barbers Point, July 8-9, 1963 4o vii COMNTS (continued) Figure No. Facing Page 24. Results of droGue measurements of currents off Diamond Head, August 1, 1962, showing effect of wind drag and mass transport 42 25. Results of drogue measurments of currents off Diamond HeadY August 11, 1962. Quasi- simultaneous observations at two stations 42 26. Results of drogue measurements of currents in the eastern part of Mamala Bay in 1962 durinc@ predominantly flooding currents 42 27. Results of drogue measurements of currents in the eastern part of Mamala. Bay in 1962 during predominantly ebbing currents 42 28. Results of drogue measurements of currents in the eastern part of Mamala Bay, February 24, 1963 42 29. Results of drogue measurements of currents in the eastern part of Mamala Day, March 3, 1963 42 30. Results of drogue measurements of currents in the eastern part of Mamala Bay, March 24, 1963 42 31. Distribution of turbidity off Sand Island and Ala Moana on December 28, 1962, during a predominantly ebbing current 44 32. Distribution of turbidity off Sand Island and Ala Moana on July 17, 1963, during a predominantly flooding current 44 33. Coliform concentrations derived from old Kewalo sewerY February 1941 46 34. Results of drogue measurements of currents southeast of Barbers Point., April 8, 1963 48 35. Results of droGue measurements of currents northwest of Barbers Point on April 9 and July 9, 1963 48 36. Generalized flood (top) and ebb (bottom) current patterns for Waianae area 50 viii CONTENTS (continued) Figure No. Facing Page 37. Generalized ebb current pattern around Oahu during trade wind season. Inset shows generalized flood current pattern 50 38. Generalized flood (left) and ebb (right) current patterns for Kahului area 56 39. Generalized diagram of coastal currents around the Hawaiian Islands 58 40. Distribution of chlorinity, dissolved oxygen, and phosphates off the Sand Island sewer outfall 64 41. Bacterial die-off in sewage disposed of in the ocean 66 42. Schematic circulation at the outfall of a sewer 70 List of Tables Table No. Pa,,e 1. Municipal and industrial waste disposal in coastal waters of Hawaii in 1962 2 2. Summary of previous engineering investigations of coastal currents in Hawaii 8 1. INTRODUCTION 1.1 Waste Disposal in Coastal Waters of Hawaii Throughout the world man has found it expedient to dispose of his domestic and industrial wastes in bodies of water, counting on the water's natural flow for their transportation and dilution, and on the chemical and biological processes in the water for their decomposition. In the Hawaiian Islands, which essentially lack lakes and on which the streams are steep and short, it is of course the ocean on which reliance is made. As shown in Table 1 and Figure 1, wastes of various sorts are discharged at many points into -the sea. Disregarding the solid wastes accumulated in sanitary fills behind dikes, sugar-mill wastes and sewage have been the most significant in Hawaii. Wastes from -the sugar plantations were of small importance until mech- anical harvesting operations were introduced in the late 1930's. By the late 1940's significant problems had arisen. Trash and mud brought in with the cane and washed off at the mill were being wasted to the sea at many points. The mud caused unsightly discoloration and probably affected significantly the growth of marine organisms, although the extent of such effects is yet undetermined. The trash had a tendency to raft sufficiently to constitute a hazard to navigation, and has undoubtedly contributed to the problem of stagnation in some harbors. In the last decade the problem has abated somewhat with the installation of hydroseparators at the sugar mills. Solids from the separators are trucked or sluiced to land disposal areas, but muddy water is still discharged at many coastal points and trash continues to escape at some. Table 1. Municipal and Industrial Waste Disposal in Coastal Waters of Hawaii in 1962 (Modified from Public Health Service, 1963) Est. Pop. Discharge Place Agency Served* Type* Treatment* Point KAUAI Kilauea Kilauea Sugar Co. sug. mill none Ocean Kapaa Mahelona Hospital 140 san..-s.ew. Se Ocean Kapaa Hawn. Fruit Packers Ltd. pine. can. Se Lagoon to ocean Lihue Lihue Plantation Co. sug. mill none Ditch & ocean Nawiliwili Kauai Surf Hotel 1,000 san. sew. Se, Cl Lagoon to ocean Koloa Grove-Farm Co. sug. mill Sc Lagoon to ocean Lawai Kauai Pineapple Co. pine. can. Sc Ocean Port I-llen Kauai County 500 san. sew. none Ocean Kekahe, Kekaha Sugar Co. sug. mill Sc Ditch & ocean OAHU Kahuku Kahuku Plantation Co. sug. mill Sc Lagoons & ocean 1-7aialua Waialua Agr. Co. sug. mill Se Ditch & ocean Kaneohe Honolulu Div. Sewers 150 san. sew. Se, Cl Kaneohe Bay Kaneohe Honolulu Div. Sewers 15,000 san. sew. Se, C1 Kaneohe Bay Kailue. U.S.Marine Corps 8,700 san. sew. Se, Fi, Cl Ocean Maunalua Kaiser-Hawaii Kai 2)600 san., sew. Se, Cl Lagoon to Kuapa Pond & ocean Honolulu Honolulu Div. Sewers 269,ooo san. sew. none Ocean Honolulu Calif. Packing Corp. pine. can. Se, Cl Kapalama Basin Honolulu Haim. Pine. Co. pine. can. Se; Cl Kapalama Basin Honolulu Libby, McNeil & Libby pine. can. Sc Kapalama Basin Honolulu Honolulu Airport ? san. sew. none Ocean Honolulu Tripler Hospital ? san. sew. none Ocean Hickam Field U.S. Air Force 9,000 san.sew. none Ocean Pearl Harbor U.S. Navy ? several none Pearl Harbor san. sew. Table 1. (continued) Est. Pop. Discharge Place Agency Served Type* Treatment* Point Halawa Honolulu Div. Sewers 4,700 san. sew. Se, Cl Pearl Harbor Aiea Honolulu Div. Sewers 17,000 san. sew. Se., Cl Pearl Harbor Pearl City Honolulu Div. Sewers 1,500 san. sew. Se Pearl Harbor Waipahu Oahu Sugar Co. sug. mill Se Irrigation s1stem & Pearl Harbor Walpahu Honolulu Div. Sewers 3,000 san. sew. Se, Cl Ditch & Pearl Harbor Ei,a U.S.Navy (Capehart Hsg) 5,000 san. sew. Se Pearl Harbor Ewa U.S.N.Air Station, Barbers Pt. 8,779 san, sew. Se, Cl Ocean Barber's Pt. Standard Oil Co. oil. ref. Se Lagoon to ocean Waianae Honolulu Div. Sewers 2,000 san. sew. Se Ocean MAUI Lahaina Maui County 1@000 san. sew. none Ocean Lahaina Pioneer Mill Co. sug. mill Se Ditch & ocean Wailuku Wailuku Sugar Co. sug. mill Se Ditch & ocean Wailuku Maui County T,000 san. sew. none Ocean Kahului Maui County 4@200 san. sew. none Ocean Kahului Hawn. Homes Comm. 300 san. sew. none Ocean Paia Maui County 2,100 san. sew. none Ocean Hana Hana Ranch Hotel 100 san. Sew. Se Ocean HAWAII Halaula Kohala Sugar Co. sug. mill none Ocean Halaula Kohala Sugar Co. 1.1000 san. sew. none Ocean Honokaa Honokaa Sugar Co. sug. mill none Ocean Honokaa Honokaa Sugar Co. 550 san. sew. none Ocean Paauhau Paauhau Sugar Co. sug. mill none Ocean Paauhau Paauhau Sugar Co. 550 san. sew. none Ocean Paauilo Hamakua Mill Co. sug. mill none Ocean Paauilo Hamakua Mill Co. 550 san. sew. none Ocean Ookala Kaiwiki Sugar Co. sug. mill none Ocean Ookala Kaiwiki Sugar Co. 400 san. sew. none Ocean Table 1. (continued) Est. Pop. Discharge Place Agency Served Type* Treatment* Point HAWAII (cont'd) Papaaloa Laupahoehoe Sugar Co. sug. mill none Ocean Papaaloa Laupahoehoe Sugar Co. 950 san. sew. none Ocean HakalEu Hakalau Sugar Co. sug. mill none Ocean HakalLu Hakalau Sugar Co. 570 san. sew. none Ocean Pepeekeo Pepeekeo Sugar Co. sug. mill none Ocean Pepeekeo Pepeekeo Sugar Co. 700 san. sew. none Ocean Papaikou Onomea Sugar Co. sug. mill rione Ocean Papaikou Onomea Sugar Co. 1,600 san. sew. none Ocean Wainaku Hilo Sugar Co. sug. mill none Ocean Wainaku Hilo Sugar Co. 650 san. sew. none Ocean Hilo Hilo Sugar Co. 250 san. sew. none Ocean Hilo Hawaii County 5,100 san. sew. none Hilo Bay Honuapo Hirtuchinson Sugar Co. sug. mill none Ocean Abbreviations: oil ref. = oil refinery Cl chlorination pine. can. = pineapple cannery Fi filtration san. sew. = sanitary sewer Sc screening sug. mill = sugar mill Se se ttling ............. 0 C c LANAI KAHOOLAWE LEGEND .......... WASTE DISPOSALS 0 SANITARY SEWER SU AR MILL PINEAPPLE CANNERY REFINERY INVESTIGATIONS OF CURRENTS 0 RECENT COORDINATED INVESTIGATIONS MAMALA BAY PREVIOUS INVESTIGATIONS DATA ADEQUATE TO SHOW TIDAL EFFECTS DATA ADEQUATE TO SHOW SEASONAL EFFECTS + CURRENT METER STUDY Fig. 1. Index map of the Hawaiian Islands showing points of waste disposal into the sea and areas in wh have been investigated. -5- The major waste disposal problems, however, have had to do with sewage. The disposal of most sanitary sewage in Hawaii was originally through cesspools, even in most urban areas. The remarkable permeability of most of the basaltic lavas, of which the islands are predominantly formed, and the permeability of the coral reefs commonly interbedded with other sedi- ments in the coastal plains bordering some of the islands, made such a means of disposal simple and cheap. In some areas, however, cesspools were hardly suitable even with a low concentration of population. With increas- ing urbanization, and increased density of population in the urban areas, cesspool disposal of sewage has had to give way to sanitary sewer systems that discharge into the ocean. Such systems carry industrial wastes, especially wastes from pineapple canneries, as well as domestic wastes. In most of these systems there are no treatment facilities. The raw sewage is discharged into the sea and the natural currents are relied upon to trans- port and disperse it. 1.2 Importance of Coastal Currents Although the high current velocities that are characteristic of conti- nental areas having extreme tidal ranges are not to be found in Hawaii, there still i@ considerable variation in current velocities from place to place, and also from time to time. Together with the amount and character- istics of the sewage, the currents in the vicinity of a sewer outfall are of critical importance in determining effectiveness in disposing of the v7aste without detrimental sanitary or esthetic effects. A surface drift moving rapidly toward the shore from a sewer outlet may introduce essentially still undecomposed sewage into a beach area that is otherwise highly desir- able for si-rimming. A current moving seaward may carry the same sewage away -6- .from shore and disperse it harmlessly. Thus under-.some current conditions raw sewage may safely be introduced but, under,'other conditions, extensive treatment would be required prior to release. Ideally, what is required is a knowledge of: (a) the initial dilution of the sewage as it is injected into the current moving past the sewer out- let, (b) the time required before the sewage is sufficiently dispersed and decomposed along the path it follows to be considered harmless, and (c) the direction and distance traveled by the sewage in that time. Even if the dischar.ge of the sewage is considered constant at some design ma_-I;imum value, and the character of the sewage is considered constant also, the variability of the current with time will require knowledge of the frequency of occurr- ence of current sets of various directions and velocities, including the evaluation.of periodic components. Furthermore, the geographic variability of the current requires that the knowledge not be confined to the sewer outlet but that it provide a complete picture of the currents within the distances of concern. 1. 3 Previous Studies of Currents in Hawaiian Coastal Waters Three kinds of previous investigations contribute to the understanding of the coastal currents in Hawaiian coastal i-,,aters. The first of these is the study of the general, more or less permanent current systems in the vicinity of the Islands. For many decades such current systems have been estimated by comparing the dead-reckoning positions of ships with navigational fixes. General net surface current charts by month and by one-degree squares are available for the portion of the Pacific in the vicinity of the Hawaiian Islands (Hydrographic Office, 1947, 1950; Brown, ms,.). Net current conditions for areas closer to shore, similarly obtained from ship reports, -7- are described in the U. S. Coast Pilot for the Pacific Coast and the Hawaiian Islands (coast and Geodetic Survey, 1963a). Only certain very general information, auxiliary to the problems of sewage disposal in coastal waters, can be learned from the older current charts. However, recently, more intensive studies on the ocean currents in the areas around -the islands have been made by the Honolulu Biological Laboratory of the U. S. Fish and Wildlife Service, using drift-bottle and drift-cara sLrveys and -,,jater-mass analyses (Barkley, ms. ). These studies have also been mainly concerned'with the general circulation pattern and net flow and, therefore, are applicable only very indirectly to the problems of coastal currents and mixing as they affect the disposal of sewage. How- ever, the information is of use in studies of the possibilities of disposal of solid waste in the sea. The second kind of investigation consists of local investigations, conducted by engineering firms, of the currents at existing or proposed sewer outfalls. There have been more than twenty such investigations, but the extent of the work reported varies considerably. Some are limited to descriptions of the amount of pollution prior to or following the construc- tion of an outfall. Others report the results of a day, or of a few days, of current measurements using floats or dye. Only two studies lasted as long as a year. In some, the currents were related to wind conditions; in J others, to the permanent flow; in a few, the effects of tides were recog- nized. In conjunction with one there were studies of the dispersion of sewage in the sea and of 'the rate of bacterial die-off. These local studies are listed in Table 2, and the sites of those which produced significant information on currents are plotted in Figure 1. -8- Table 2. Summary of Previous Engineering Investigations of Coastal Currents in Hawaii Drift measurements Sewage or by drogue, drift slick field Place Agency Year card dye spot, etc. measurem't* OAHU Kaiaka Bay BC&-A 1962 x x Waialua Bay BC&A 1962 x x Kaneohe HDS 1957 x Nuupia Pond H&N; BC&A 1957 x Kailua H&Njp BC&A 1950/ S x Waimanalo IVA 1963 T Kalama (Hawaii-Kai) SLT&H 1962 T Ala Moana A&A. L&W 196o T Ke-vralo KT&C 1920 x Honolulu BS 1941 F Honolulu M&E 1944 F Sand Island HDS 1951 x Sand Island AS&A 1961 x Pearl City HDS 1958 x Pearl City AS&A 1961 T Waipahu HDS 1957 x Pearl Harbor Entrance AS&A 1962 T Barber's Point TAMS 1961 x Kaneilio Point BC&A 1962 x x Pokai Bay SLT&H 1962 T x MAUI Kahului HO 1962 T x HAWAII Hilo BC&A 1961 x x Kailua-Kona A&A 1961 x x *Abbreviations: Agencies A&A HAR Austin & Assoc. H&R Herschler and Randolph AS&A Austin, Smith..& Assoc. KT&C Keller, Tay, and Collins BMA Belt, Collins, & Assoc. L&W Law and Wilson BS Bur. of Sanitation, Terr.Foard MA Marine Advisers of Health M&E Metcalf and Eddy HDS Honolulu Division of Sewers SLT&H Sunn, Low, Tom, and Hara H&N Holmes and N,@,_rver TAMS Tippets, Abbott, McCarthy,Stratton Drogue, etc. measurements x = measurements made T = measurements adequate to determine tidal effects S = measurements adequate to determine seasonal effects Sewage or slick field measurements x = measurements made F = measurements adequate to define sewage field -9- The third kind of investigation consists of current meter surveys by the U. S. Coast and Geodetic Survey in the inter-island channels and in other coastal waters. r'ualitative results of some of the studies are indi- cated in the Coast Pilot and quantitative summaries of analyses of two surveys in Auau and Kalohi Channels appear in the Tidal Current Tables of the Coast and Geodetic Survey (1963b). Analyses of most of the surveys are still incomplete, however. 1.4 The Present Studies The investigation on which 41-his report is principally based was under- taken as one component of the studies involved in the development of a general shoreline plan by the Hawaii State Department of Planning and Economic Development. It was undertaken under contract with that Department, with financing in part through an Urban Planning grant from the Federal Housing and Home Finance Agency. The proposal for the investigation was submitted by the Hawaii Institute of Geophysics in recognition that disposal of sewage from the urban areas of the Hawaiian Islands, in such a manner as to avoid pollution to recreational waters, harm to fisheries, and other damage, is becoming increasingly difficult as the urban areas and the amount of sewage deEcriled from them increase. Engineering studies of the most economical sites and means for sewage disposal at sea have been severely limited by inadequate knowledge of the local conditions that affect the released waste currents, mixinry,, and decomposition in -the sea. These conditions J, tD vary greatly from place to place, so that studies must be made locally. In addition, however, basic studies were required, because very few studies have been made of sewage disposal factors in tropical mar:.ne waters that provide any fundamental and generally applicable data. -10- As originally proposed, the general objectives of the study were: (a) to summarize available information applicable to the problems of coastal currents, mixing, and remineralization of sewage in Hairaii and similar areas; (b) to provide answers to the most pressing local problems concerning the marine environment and sewage disposal, e.g., information on current and mixing conditions in specific areas where sewage outfalls are contemplated, or where sewage disposal has been troublesomel- (c) to investigate the seasonal changes in oceanographic and meteorological conditions, and to define the "critical conditions" to be considered in planning and designing of the outfalls; (d) to generalize from the interrelated information in such a way as to permit its adaptation to a variety of locations; (e) to prepare plans, procedures, methods, and equipment for such additional local investigations as may be required -when new related problems arise. The study was started in June 1962. The field work was carried out using chartered vessels, especially the 4,@,-foot yawl, "Thunder Bird", as well as the University's 83-foot research vessel, "Neptune V,:and.to scme extent, the 40-foot "Salpa". The field work was concentrated mainly on the island of Oahu for reasons of economy and because the most immediate and serious practical problems of sewage disposal are concentrated on this island. Some field work along the coasts of Kauai has been done, however. The methods and instruments used are briefly described in an appendix to this report, irhich also contains the actual numerical data collected in the studies. Office work included the analysis of the field data and plotting of results, the review of previous reports and background literature, and the analysis cr re-analysis of some of the data obtained in the previous _11- investigations. A preliminary report on the study (Avery, Cox, and Laevastu, 1963) was submitted in January 1963. The Institute of Geophysics investiga- tion was closely coordinated with one undertaken by the Engineering Experi- ment Station of the University of Hawaii under contract with the State Department of Health and directed by William Tinniswood. Some of the most important results of th-e latter investigation are included in this report. 1.5 Scope and Organization of Report In the investigations reported here, the coastal currents of Hawaii have been more extensively observed by floats and dye than in all previous investigations, and more intensively than in most of the previous investi- gations. In addition,.continubizs recording of currents has been-carried on at a number of sites for periods ranging from a day to a month. It must be admitted, however, that this more comprehensive work has not produced a clear picture of the current systems which is satisfactory for practical needs. It has indicated, instead, that the systems are much more complex than could have been anticipated on the basis of previous knowledge and, indeed, that many of the simple concepts, on the basis of which sewer outfalls in Hawaii have been designed and even have been built, are inade- quate and in some cases are generally erroneous. However, there has emerged from the recent studies a clearer understanding of the canponents that go to making up the coastal current at any specific place, and the requirements in methods and instrumentation for the adequate study of these components. In this report the current components are first diq'aussed. serarately.." The actual resultant coastal current systems around each of -the islands are then described systematically in as much detail as present information -12- permits, regard-less of the source of the information. There follow sections on the practical application of current data, some chemical, biological,:and. geological aspects of sewage disposal, and the conclusions. The report is intended for use by persons with some scientific or engineering ccmpetence, including planners, sanitary engineers, and coastal engineers, as well as oceanographers. For the most part, descriptions of background oceanographic information that are available in textbooks have been omitted. However, oceanographic factors and processes pertinent to waste disposal in coastal i,,7aters that have not received sufficient attention in the past are pointed out and described. 1.6 Acknowledgments We are particularly indebted to the following: Roger Luther and Donald Cameron, former marine superintendent and captain, respectively, and the crew of the Neptune I, from which much of the field work was done; William Tinniswood. of the College of Engineering, who generously allowed the us-- of data derived in his concurrent study; Richard Barkley and Gunter Seckel of the Honolulu Laborator-yr, U. S. Bureau of Commercial d Fisheries., who discussed at length the present status of knowledge of the permanent flow; Bernard McMorrOW and Robert Tam of the Department of Health who discussed sewage and sanitation problems with us; William Morris of the Department of Planning and Economic Development, who provided liaison with that Departi@ent-';* EthelMcAfee'. for editorial assistance; Roy Kaneshiro and Jerry Kusunoki, for plotting the data; and tD Toshitsugu Sakou of the Institute of Qeophysics and the College of Engineering, for assistance and advice in the preparation of this report. 2. COMPONENTS OF COASTAL CURRENTS IN HAWAII 2.1 Components of Coastal Currents in Hawaii The actual surface current at any time and place is actually the re- sultant of components having several different driving forces. The oceanic current sweeping past the Islands is the underlying component. Generally, this "permanent flow" sets tO'vTard the west, but its direction varies some- what, especially seasonally, and it also has superimposed upon it large-scale eddies that may cause considerable temporary changes in direction and in strength. Tidal components result from the passage of the astronomical -tide waves past the Islands, wind components are set up by the drag of the wind on the surface, and there is also a mass transport associated with the movement of wind waves. The resultant current is of course greatly in- fluenced by the nearshore topography -- at some places the surface current converges, at others it diverges, in still others eddies are formed. Each of the components is variable in direction and in strength, and for each kind of variability there are characteristic periods. The periods for the tidal currents are well defined, semi-diurnal and diurnal. Vaxia- bilities associated with the wind, the waves, and the permanent flow have other periods, including an important annual one. No study of currents can be considered comprehensive unless it includes either continuous observations or observations at intervals close enough to disclose the effects of the shorter period variations, in a continuing program or programs repeated over at least a year to disclose the effects of the longer period variations. -13- -14- 2.2 The Permanent Flow and Its Eddies A few years ago it was generally assumed that the currents around the Hawaiian Islands were largely the result of the generally westerly flow, the Pacific North Equatorial current in the vicinity of the Islands which represents the clockwise circulation of the North Pacific. This "permanent" flow certainly exists in a statistical sense, but even in the open ocean it has been found to be so variable in direction and strength that -ener- alizations as to its characteristics are very uncertain. The data derived from ship reports and compiled by the Hydrographic Office (1947, 1950) show the irregularity (Figs. 2 and 3). The direction of set, although predominantly west or west-northwest, varies commonly fromwest-southwest to north-northwest. Northwest sets are more common within a few hundred miles of the Islands than elsewhere, probably in- dicating a deflection by the archipelago. The average velocity is a little less than 1/2 knot, but ranges from less than 0.1 knot to more than 1 knot. Monthly charts of the permanent flow at the surface prepared by Brown (ms.) from Hydrographic Office data and from which Figures 2 and 3 have been drawn., indicate a somewhat more northwesterly set, on the aver- age, in winter and spring than in summer and fall. Drift-bottle studies by the Honolulu Biological Laboratory of the Bureau of Commercial Fisheries (Barkley, ms.) particularly point up the irregularities. Drift bottles released southeast of Oahu in May 1961, for example, were recovered not only on Niihau and Kauai but also on the north- east coasts of Lanai, Molokai, and Oahu. The Bureau of Commercial Fish- eries' studies also indicate that the Islands cause eddies in the permanent flow downstream., eddies that are 20 to 50 miles across, revolving at a rate February 30 30 if se 4, IL A--, at go, 20 20 .Z 4- VL 10 10 170 160 150 0 10 2o na. ml. day-1 Fig. 2. February surface currents in the vicinity of the Hawaiian Islands indicating the permanent flow pattern as deduced from dead reckoning. -15- of one turn in 10 days (Anon., 1963). Velocities of nearly 2 knots may be attained near the outer edge of the eddies, five times or more the average velocity of the system. In the coastal areas of Hawaii the permanent drift has proved surpris- ingly difficult to disentangle from other current components, largely because of the unexpected prevalence and strength of the reversing tidal components and hence the necessity that the resultant currents be measured over a period of at least a day in order to determine and subtract the tidal effects. Areas in which the current set is believed to be essentially uni- directional, or in which the net permanent flow has been ascertained by averaging out or analyzing the reversing tidal currents, are as follows (sources of information are discussed in the sections on the current systems around the various islands): a. The northeast coast of Hawaii from Cape Kumukahi to Leleiwi Point and from Pepeekeo to Upolu Point: Set northwest. b. Southwest coast of Hawaii from Cape Kumukahi to Keauhou Point: Set southwest. c. West coast of Hawaii from Kauna Point to Keahole Point: Set generally northwest., d. Alalakeiki Channel: Net set northwest on northeast side. (A southeast set on the southwest side is also reported, however). e. South coast of Kahoolawe: Set west. f. North coast of Maui, Kahului Bay: Set northwest. Kalohi and Auau channels: Net set east about 0.1 knot (?). h. Southeast coast of Molokai: Net set northeast -16- i. Southwest coast of Molokai: Net set west. j. Northeast coast of Oahu from Waimanalo to Kahuku: Set generally northwest. k. West coast of Oahu, south of Kaena Point: Set northwest (possibly a combination of an eddy at flood and direct tidal current at ebb). 1. South coast of Kauai near Puolo Point: Set west. m. South coast of Niihau: Set west about 1.5 knots Most of the directions of set are relatively easy to account for in terms of the set of the permanent flow at sea and its probable deflection close to the island chain. The appaxent easterly net drifts in the Kalohi and Auau channels, along the Molokai coast of the Pailolo channel, and along the Kahoolawe coast of the Alalakeiki Channel are not so easily accounted for, but probably represent some form of eddying. 2-3 Tidal Currents The tides in the vicinity of the Hawaiian Islands are of mixed type, that is, they appear predominantly diurnal at some times and predominantly semi-diurnal at other times, but generally semi-diurnal with a pronounced diurnal inequality. The maximum range is about 3 feet. The tide waves move through the archipelago from the north-northeast toward the sou-Lh- southwest (Fig. 4). In the open ocean the propagation of these waves must be accompanied by a current setting approximately southwest, more or less in the direction of propagation of the tide wave, at high tide, and a current setting in the opposite direction at low tide. The nomenclature of tidal currents was developed on continental coasts where the tides form essentially standing waves. On such coasts the August 30 30 IL All IF- 4&- 20 120 N@ 10 10 170 160 150 0 io 2o na. mi. day-1 I I Fig. 3. August surface currents in the vicinity of the Hawaiian Islands indicating the permanent flow pattern as deduced from dead reckoning. -17- flooding current which carries water landward across the continental shelf and into estuaries is associated with the rising tide, and the ebbing current which carries the water seaward again is associated with the falling tide. In contrast, in the open ocean where the tides form pro- gressive waves, the maximum current velocity in the direction of propaga- tion of the tide wave tends to occur at high tide and the maximum current velocity in the opposite direction tends to occur at low tide. By extension of the original definitions of the tidal currents, the flood current under these conditions is considered to be the current setting in the direction of propagation of the tide wave, and the ebb current, that setting in the opposite direction. In the ocean the actual current directions tend to be rotated clockwise, in the northern hemisphere, from the directions they would have without rotation, so that in offshore waters particles tend to describe ellipses (Fig. 5C) instead of simply oscillating back and forth (Fig. 5A). The combination of a reciprocating tidal current and a permanent flow creates a resultant current which changes direction, within a certain range of directions, without quite reversing, as shown in Figure 5B. The ccmbi- nation of a rotary tidal current and a permanent flow creates a resultant current which may or may not have a restricted range in directions., de- pending on the ratio between the minimum velocity of the tidal current and the velocity of the permanent flow, but which has a lower velocity associ- ated with some directions than with others, as shown in Figure 5D. Considering the smallness of the tide range, the great depth of water surrounding the Islands and the general steepness of their flanks, and the smallness of the Islands in relation to the wave length of the tide., there seemed to be no reason originally for anticipating that the tidal currents would be of much significance in the vicinity of the Hawaiian Islands. Investigations with drogues at Pokai Bay (Sunn, Low, Tom, and Hara, 1962) were the first to indicate that the tidal currents are of consequence. Drogue studies and especially paddle-wheel current-meter studies in the present Institute of Geophysics project, and additional paddle-wheel current-meter studies in the associated Engineering Experiment Station project, also have indicated that tidal currents constitute one of the most important current components, and in some places are the dominant component. Further confirmation has been obtained from Roberts current-meter studies recently published by the Coast and Geodetic Survey (1963b) and from additional, unpublished Roberts meter data. The magnitude of the tidal currents in the coastal waters of Hawaii must be due to the intensification of the currents on the island shelves and in the inter-island channels,, but the processes axe not yet quantitatively understood. Further discussion of the tidal currents observed will be deferred to the next section where they 'can be related to island effects. 2.4 Island Effects Where the tides move perpendicularly onto an island shelf and toward shore, the phase relations of the tide and the tidal component of the current should expectably resemble those on a continental shelf, that is the maximum current velocities should lead somewhat the,maximum and minimum tide levels. A divergence of the flood tidal current component should be expected off the shore of the island facing the direction from which the tide wave approaches (Fig. 5A). From this divergence) currents should sweep around both sides of the island to a convergence on the opposite 16D W 159 158 157 156 -90 60 75 C. 0 5 N KAUAI 9 22-- 0 15,, 0- > 6 @Sb /0 NIIHAj! 0- OA* --0--- 105- --.90-- '--M6LOKAI 0 +15 03 'X@ 0 .... Kalohi C 0 LAN MAUI O\ N C,5 zo HAV 0 5i t9 75 0 ,45 0 10 20 Nadiwl Miles 160 W 159 158 157 156 Fig. 4. Co-tidal chart for the Hawaiian Islands. _19- s@de of the island. The positions of the convergence and divergence and the directions of set of the currents around the island should approxi- mately reverse with the ebb tide. The current pattern around a simple circular island resulting from a reciprocating tidal current superimposed on a permanent flow is shown in Figure 5B; that resulting from a rotary tidal current superimposed on a permanent flow is shown in Figure 5C. In both cases it will be noted that: (a) The flood and ebb convergences and divergences are not on the same axis; (b) There is a continuous clockwise flow between the flood con- vergence and the ebb divergence, and a continuous counter- clockwise flow between the ebb convergence and the flood divergence; and (c) In general there are inequalities on most parts of the coastline during the times in which the current sets in the ebbing direction and in the flooding direction. Considering the complexities of the relationships between tides and currents containing tidal components around even simple islands as dis- cussed above and as shown in Figure 6, it is hardly surprising that the correlation between the tides and the actual currents measured around the Hawaiian Islands should not always be simple. Some additional sources of complexity may also be mentioned. The tidal curves utilized in this study and presented in figures in this report have been based on predictions for Honolulu with standard adjustments for range and time differences at other ports (U. S. Coast and Geodetic Survey, 1962). These standard adjustments -20- took no account of the differences in phase lags and amplitude factors that can be expected between semi-diurnal and diurnal components. More- over, the sea level changes that actually occur are influenced by unpre- dicted meteorological factors, such as barometric pressure changes. The ratio between maximum tidal current velocity and tide range for the semi- diurnal tide should be double what it is for the diurnal tide. The ratio between the minimum tidal current velocity and the permanent flow velocity should be double for the semi-diurnal tidewhat it is for the diurnal tide. None of the Hawaiian islands are circular, and some are quite irregular in shape. The irregularities probably have considerable effect on phase and strength of the tidal currents, and in -some areas result in eddies. Never- theless in spi-be of the numerous sourbes of complexity the tidal current picture in some areas has been found through paddle-wheel current-meter studies to be relatively simple. Near Diamond Head, Oahu, where the current is more regular than at any other place tested, certain things occur rather consistently. In a period of 25 days of continuous observation the current reversed 98 times, without fail, for each change in the stage of the tide, indicating that the current here is mainly controlled by the tide. The ebb current is the strongest and lasts longer than the flood (See Fig. 20., Dec. 4 and 5, 1963)- It appears that the maximum ebb current tends to occur at and near low tide in anticipation of a high rise--the higher the rise the stronger the ebb (for the effects of a relatively small tidal chan6e see Fig. 20, Dec. 8 and 9, 1963). The current changes tend to follow a traveling wave pattern. See Figure 19, Nov. 25 and 26, 1963, and others. Farther west) toward Sand Island,, the current pattern becomes less EBB EBB EBB IX EBB 1X Ix 7= X Ix IM X 7= 7W M X 7M M 7M N N Im V1 XU XU in I V IV 11 M 31 X n M FLOOD FLOOD FLOOD FLOOD A. RECIPROCATING B. RECIPROCATING C. ROTARY TIDAL D. ROTARY TIDAL TIDAL CURRENTS TIDAL CURRENTS CURRENTS CURRENTS PLUS PLUS PERMANENT PERMANENT FLOW FLOW Fig. 5. Diagram showing superposition of tidal current vectors and resultants with permanent flow. 1, 11, 111, etc. = 12ths of tide period after slack tidal current. 71M 11 7) _2 M Assumptions: Northern hemisphere Azimuth of permanent flow set = 2920 Permanent flow velocity = 0. 5 Maximum tidal velocity Azimuth of tide-wave propagation = 2020 Minor axis, tidal ellipse = 0.35 Major axis, tidal ellipse _21- regular. Figure 21 shows a sample of a 2-week record taken off Magic Island., Ala Moana. As can be seen from data taken on November 11 and 12, 1963, the pattern nearly follows the Diamond Head pattern, but there is a deviation during the early hours of November 12. Figure 21 also includes a sample of data taken off Kewalo Basin in August 1963, which still shows the Diamond Head pattern, but the current appears to be more confused. Figure 22 shows a sample of data taken at the sewer outfall near Sand Island during August, 1963. The Diamond Head pattern is barely recognizable-- apparently eddies are causing the difference--although when the tidal range is greater the pattern is more recognizable. East of Diamond Head off Wailupe Peninsula (see Fig. 18) the current pattern is essentially the same as off Diamond Head. Northwest of Barbers Point the current pattern is again very uniform, as shcWn in.Rigure_23,'but the tidal current directions are opposite to those at Diamond Head. On the Pearl Harbor side of Barbers Point, however, there is considerable irregularity. Except for the relative persistence of the ebb current at Diamond Head., these observations fit in well with the concepts diagrammed in Figure 6. Diamond Head is clearly east of the flood convergence and the ebb divergence on the south side of Oahu, and Barbers Point is clearly west of them. The current pattern west of Diamond Head is progressively more confused and the pattern east of Barbers Point is similarly confusing as the areas of convergence and divergence are approached. -22- 2.5 Island and Submarine Topographic Effects The currents resulting from the combination of the permanent flow and the tidal currents are further complicated by the islands and their submarine topographic irregularities. Upstream of an island (relative to the instantaneous current direction), the approaching current diverges. Downstream, although there is a general reconvergence, the most prominent feature may be a zone of instability and eddying. The convergences and divergences are likely to be intensified at the outer edge of the island shelves where the most abrupt transitions in the tidal currents are likely to occur between offshore elliptical orbits and nearshore oscillatory motions.parallel to the coast.. The principle of slope convergence formation is illustrated in Figure 7. Slope convergences have be en observed on almost all cruises, and a special-study of them was made in the area from.Mamala. Bay to.Barbers Point on April 10-11, 1963, during a period of Kona weather when the winds were very light. The convergences were well demarcated by streaks of calm water and accumulations of seaweed and other flotsam, including sewage. The convergences nearly always occurred over steep bottom slopes, generally at 55 to 75 meters depth. Irregularities and branching were noted. Bathy- thermograph casts were made on April 10 in the vicinity of one of the convergences. These casts showed a depression of the thermocline where and when a convergence was forming, differing thermal structures on the two sides of the convergence, and mixing with minor inversions in the convergence itself, consistent with the theory of origin illustrated in Figure 7.. The surface divergences which tend to be beneficial in sewage disposal due to their dispersing effects, are not so easily recognized. They seem EBB CONVERGENCE @ MAXIMUM EBB UNI- MAXIMUM@ CLOCKWISE FLOOD CONVERGENCE4 DIRECTIONAL VELOCITY4 POSITION DIVERGENCE FLOW MAXIMUM FLOOD DIVERGENCE COUNTER BB CONVERGENCE CLOCKWISE Z POSITION,- FLOOD MAXIMUM FLOOD EBB DIVERGENCE FLOOD EBB VELOCITY DOMINATES DOMINATES DOMINATES DOMINATES REVERSING CURRENTS N REVERSING N N CURRENTS REVERSIN REVERSING CURRENT ACURRENTS SLACK EBB FLOOD EBB FLOOD FLOOD DOMINATES DOMINATES DOMINATES DOMINATES WATER CONVERGENCE MAXIMUM DIVERGENCE VELOCITY MAXIMUM 1@r COUNTER UNI- CLOCKWISE FLOOD CONVERGENCE DIRECTIONAL EBB POSITION MAXIMUM DIVERGENCE MAXIMUM, VELOCITY EBB DIVERGENCE FLOW FLOOD CONVERGENCE CLOCKWISE POSITION EBB DIVERGENCE A. RECIPROCATING B. RECIPROCATING D. ROTARY TIDAL TIDAL CURRENTS TIDAL CURRENTS CURRENTS PLUS PLUS PERMANENT PERMANENT FLOW FLOW Fig. 6. Diagram showing current patterns around a simple circular island. I, II, III, etc. 12ths of tide period after slack tidal current. E POS Fluti T'O k0l G S MA (@IMUMD@,Z"-"' Assumptions- Northern hemisphere Azimuth of permanent flow set = 2920 Permanent flow velocity = 0. 5 Maximum tidal velocity Azimuth of tide-wave propagation = 2020 Minor axis, tidal ellipse = 0. 35 Major axis, tidal ellipse -23- to be distributed over wider areas than the convergences, but they are not accompanied by elevations of the thermocline as distinct as the depressions accompanying the convergences. It is probable that the sudden appearance of large amountsof "limu" (seaweed) on Hawaiian beaches is sometimes the result of the seaweed accumulating for some timein aconvergence, and its concerted movement on shore by wind action when the convergence weakens or breaks down. La Fond (1962) has related slick streaks, observed close to the conti- nental slope, to convergences associated with internal waves. Occasionally in very calm weather we also have observed several slick streaks, which may be of the sort described by La Fond, in addition to the main zones of convergence on the island slopes. Earlier studies (Neumann, 196o) have indicated that tidal current ellipses are determined -to a great extent by bottom and coastal topography. According to Fleming and Heggarty (1962) and to Lee (personal communication) the currents tend to follow the depth contours, in general, rather than the coastal outline. Some measurements of bottom currents have been carried out on the Oahu shelf and slope using Carruthers' "Pisa" current indicator and current cone. The results showed that the bottom currents tend to follow the depth contours and are approximately the same strength as surface currents or occasionally even stronger along steep slopes. However, irregularities in coastal topography of the islands are also reflected in irregularities in the depth contours. The irregularities tend to cause eddies and anomalous currents. This is illustrated by the generalized current patterns off@bjbziae, Oahu, during flood stage, as shown in Figure 36. In the complex eddies shown, which change in tidal rhythm, currents flowing in opposite directions can be found only a small -24- distance apart (see locations A and B). An interesting eddy formation on the Pearl Harbor side of Barber's Point, Oahu, is shown in Figure34 . The measurements indicate the eddy formation around the headland. Because of the direction of the coast in relation to the direction of ebbing current and the absence of irregular- ities in bottom topography, no such eddies are formed on the nox@bh-4est side of Barbers. Point, as shown in Figure 35. Especially strong currents and large eddy formations can be expected where the current sweeps around sharp-pointed headlands., such as Kaena Point, Oahu, near which currents and eddy formations are illustrated for the period of January 3 to 4, 1963 (Fig. 13)- It should be noted that the strong current passing around Kaena Point appears not to reverse with the tide. This may be due to the strength of the permanent flow in the area, but it appears likely that it is due in part to the fact that the direction of the flood current.eddy along the coast.southeast of Kaena Point is the same as that of the ebb current itself along the same coast. The eddies formed in the lee of islands or local topographic irregu- larities are likely to persist due to inertia even after they move away from the area of formation. 2.6 Wind-driven Currents and Mass Transport by Waves The permanent flow described in section 2.2 is largely the result of the drag of wind systems over the ocean. Locally, however, wind drag may not parallel the permanent flow,.and the wind-driven current must be treated a3 a separate component. Independent wind effects are Particularly notable upwind and downwind of islands, where the currents may tend, at the very surface, to set respecttvely onshore and offshore due to wind drag Rotary tidal currents offshore Vectors for times Vectors for times of divergence- of convergence - '01_@ Period of divergence Period of convergence Convergence (tide rip) Continental slope Reciprocating tidal- currents close to -the coast Coast Fig. 7. Diagram showing slope convergences resulting from coupling of coastal reciprocating and offshore rotary tidal currents. -25- although in depth they may tend to parallel the shore. The result of the drift of surface water towards the windward coast of an island is a "piling up" of the surface mater, referred to as "Anstau". The drift of surface water offshore from the leeward side of an island results in a rise of the deeper water, referred to as "upwelling". A net offshore drift resulting from offshore winds may be seen from drogue measurements at Waianae, Oahu, as shown in Figure 8. Upwelling and anstau effects, on the leeward and windward sides of the island respectively, have also been demonstrated by observations of the depth of the thermocline, as shown by the measurements off Diamond Head given in Figure 6 of the Preliminary Report of this investigation (Avery, Cox, and Laevastu, 1963), and might also be investigated by studies of the distribution of surface temperature. Differential movement of the water with depth has been studied on windward and leeward sides of the islands in specially-designed experiments with current crosses suspended at different depths. (See Figure 9 in the Preliminary Report, Avery.,,-Cox, -and Laevastu-, .1963-. ) .-The. icoastward-seaward components at the surface have been found to be compensated usually by opposite components along the bottom (see Figs. 10 and 11 of Preliminary Report). Several simultaneous observations of the movement of current crosses, drift cards, drift bottles, dye, and wetted -paper sheets at the surface show that drift bottles and cards migrate much faster downwind than do the paper sheets at the surface. The movement of dye spots is somewhat slower than the movement of the sheets; and current crosses that have negligible windage lag behind the dye. These observations confirm the conclusions of , 26- 1 several earlier investigators that the movement of the drift bottles and drift cards is greatly affected by the wind drag on the portion of the bottle or card that extends above the surface. The comparison of the move- ment of the wetted paper sheets on the surface with the movement of the current crosses immediately below the surface, leads to the conclusion that the very surface moves faster downwind than does the water layer a few centimeters below it. This observation strengthens the hypothesis of Tomczak (1962), who indicated that there is no discontinuity at the air- water interface with respect to transfer of momentum. Rapid change of current speed with depth causes sheer and turbulence, thus increasing the mixing of any sewage close to the surface. Besides the drift caused by the wind there is a mass transport of water due to wave motion in the direction of the wave travel. This mass transport by waves has recently been investigated experimentally, as well as theoretically by Masch (1961), who gives appropriate formulae to account for the speed in relation to depth for given wave conditions. As with wind drag, the greatest velocity of mass transport by waves is at the surface. The mass transport and associated mixing by waves are important factors in sewage disposal in coastal waters. Ordinarily, the mass transport is difficult to separate from the wind drag, but in the lee of an island, where the wind blows offshore, the mass transport may be predominantly alcr6shore due to the refraction of the waves around the island. Such conditions are encountered off Waikiki. Observations there of the differential current movement with depth plotted in Figure 9 of the Preliminary Report on this investigation showed that the movement of the surface relative to the deeper waters tended to be in the direction of %propagation of the swell rather than in the direction 40 50 60 ON SHORE X x@ 5, C) x lb 7.0% 0 Cli -39-0 4,30% Z 0 ro 0 in OFF SHORE 0 0 0 ot'a 023 ozz Fig. 8. Directions of drift drogues from two 24-hour cruises off Waianae. (After Sunn, Low, Tom, and Hara, 1962.) -27- toward which the wind iras blowing. The mass transport becomes accentuated in shallow water. Mass transport of water over a reef, promoted by the breaking of the waves on the reef, is likely to provide the principal circulation inside the lagoon and a pronoun- ced current out through any existing channels. The outgoing velocities may amount to several knots, depending on the height, period, and direction of approach of the waves, the depth of water over the reef, the width of the reef, and the length of reef from which mass transport is tributary to a channel, although the current in the channels may show some tidal fluctuation in velocity because of the variation of water depth on the reef, there is no reversal. Well-devel'ored examples of reef circulation on two very different scales are those of Kaneohe Bay, Oahu ( Fig. 14) and of north Kapaa Reef, Kauai (Fig. 11). Outgoing currents in reef channels in some localities might be used effectively for sewage disposal, particularly if the sewage release could be regulated in the tidal cycle. The mass transport associated with waves breaking on a beach causes the alongshore currents that are responsible in large measure for sand transport and for the outgoing rip currents that threaten incompetent swimmers. 3. COASTAL CURRENTS AROUND NIIHAU AND KAUAI 3.1 Niihau According to the U. S. Coast Pilot for the Pacific Coast and Hawaii (coast and Geodetic Survey, 1963a) reversing currents have been observed in the Lehua Channel and in the vicinity of Kamalino. Probably the south- setting current in the Lehua Channel and the south-setting current near Kamalino represent flood tidal currents, the opposite sets representing the ebb currents. South of Kawaihoa Point a prevailing westerly current reaching a velocity of 1.5 knots is reported. Little is known about the currents east of Niihau in the Kaulakahi Channel. 3.2 Western Kauai According to the Coast Pilot (Coast and Geodetic Survey, 1963a): "Current observations taken during a 24-hour period 0.5 mile off Mana Point show a tidal current of 0.2 knot velocity at strength setting south- ward and northward along the coast. The southward maximum occurs about 3 hours after low water at Honolulu and the northward maximum 3 hours after high water. Similar observations taken near the coast about 3.5 miles southeastward of Nohili Point show a tidal current with velocities general- ly less than 0.5 knot." These observations of tidal currents, which fit in with the theoret- ical concepts discussed in section 2.4, are consistent with drogue measure- ments made on 23-24 July 1963 (Fig. 9). The measurements show a south- easterly current off Waimea during the change from ebb to flood, a south- easterly current off Kekaha during the flood, no current off Mana. during the change from flood to ebb, and northeasterly current off Nohili _219@. -30- and Makuaiki Point during the ebb. The maximum current velocities, some- what over 1 knot, were associated with the ebb current off Nchili. Other velocities were generally considerably less than 1 knot. 3.3 Northern Kauai Drogue measurements made 24 July north of Haena (Fig. 9) showed a northeast current speed of about 1 knot at the time of a rising tide, but measurements off Hanalei about two hours later during the same tide rise showed a westerly current. Measurements made 25 July off Kilauea and Anahola showed northwest to west currents with speeds as much as 1.8 knots at the time of a high tide. These measurements can be accounted for only by the persistence of the ebb current during the rising tide. The dif- ference in current directions off Haena and off Hanalei may be the result of an eddy or an abrupt reversal from ebb to flood directions or, most probably, the location of the ebb convergence in the region between Haena and Hanalei. 3.4 Eastern Kauai Drogue measurements on 25 July 1963 showed a north-setting current of 1.8 knotsstrength at low tide'off Anahola and a north-setting current of 0.5 to 1.0 knot off Kapaa about-two - hours later (Fig. 9). Off Hanamaulu, about the time of the middle of the rising tide., a series of drogues showed a current changing rapidly in both direction and strength. Drogue measurements on 23 July off NaWiliwili showed a southeast-setting current of 1.5 knots strength at high tide. These measurements are all consistent with a flood current setting southward and an ebb current setting northward along this coast. xaII ix, K A U A I Mr. VII Tp- C... 11, N-Ii-1, z, VE %ddll WhIll mS 11 1, N Cho nge of tidal currents off Nowiliwili indi- cated with bar on the tido I curves. (Ti e of fid I current change taken the m rec ord: of the Paddle- @hse f':umrrent 3 4 N-1-L "LES Fig. 9. Results of drogue measurements of currents around Kauai. -31- Paddle wheel current-meter records for the period 23-25 July 1963 taken at a station a mile south of the entrance of Nawiliwili Bay (Fig. 10) show currents reversing apparently as the result of, but not easily correlated withl tidal changes. The flood flows dominate and the phase relations are difficult to account for. Since the drogue measurements in the area agree with the theoretical pattern mentioned above, it is probable that the meter was in an area affected by eddies. A study of the currents on the north Kapaa reef by Helfrich and Kohn (1955) showed a typical reef-lagoon circulation (Fig. 11). The water was introduced over the reef edge by mass transport and flowed continuously southward on the reefY regardless of wind and tide condi- tions, escaping back to the ocean again in a deep-water inlet. Inter- estingly, Inman', Gayman, and Cox (1963) found that in spite of the strength of the southerly current the sand was transported westward across the reef by the oscillatory currents associated with the waves and under the guiding influence of small channels on the reef surface. 3.5 Southern Kauai Drogue measurements on 23 July 1963 (Fig. Q) showed west-setting currents averaging about 1 knot from off Makahuena Point to off Port Allen during a time when the tide was approaching low, was low, and beginning to rise. This direction is consistent with an ebb tide only if this part of the coast lies between the flood convergence to the west and the ebb divergence to -the east, as discussed in section 2.4. 3.6 Summary of Coastal Currents Axound Niihau and Kauai The comparatively regular shape of the island of Kauai lea to the -32- hope that the coastal currents around it would be more regular than those around the other islands. The drogue measurements made around Kauai are consistent with a current pattern with both tidal and permanent flow ccmponents in which the flood current impinges on the island and diverges somewhere west of Hanalei and possibly even as far southwest as Hanamaulu and converges again in the vicinity of Waimea, and in which the ebb current impinges on the island and diverges in the vicinity of or west of Makahuena, pos- sibly even as far northwest as Navilivili, and converges again in the, vicinity of Haena. The measurements are, however, insufficient to demon- strate the current pattern with certainty. Current-meter measurements off Nawilivili support the belief that the currents are.controlled in part by the tides, but indicate that their correlation with the tides is not simple. The current reports from Niihau are consistent with a combination of tidal and permanent flow components in which the resultant flood con- vergence and ebb divergence are at the northeast point of the island, and in which the ebb divergence is east of Kawaihoa Point and the flood convergence northwest of the Point. The currents around Niihau and Kauai are shown in simplified dia- grammatic form in Figure 39. 6 A.M. 6A.M- NOON 6 RM. N010N 6 7M. MIDMIGHT I - 1 .1 1 1 JULY 23.1963 JULY 24,1963 SPEED SCALE ;0 kW. 0 '0 TRUE NORTI 0 90E 0 -0 DEPTH OF WATER (M.L. L.W.) TO FT - 24 on METER FROM BOTTOM 3T Ft 10 I T MIDNIGHT SA@M. NOON 6 Pf M. MIDHIGHT 6A.M. JULY 25,1963 I.LY 2- 2 0 - -0 Fig. 10. Paddle-wheel current-meter measurements from southeast of Nawiliwili, Kauai, (top) July 23-24, (bottom) July 25, 1963. M 0 30' 40' 10, 20' 50' Iti + CL /* Ilk V. KEY TO CURRENT VECTORS ....... 29 OCT 1630- 1900 30 OCT 1030- 1300 -------30 OCT. 1100- 1300 301- .-.-.-.24 NOV. 1000- 1200 /,"2 O'-X44 40000", 24 NOV. 1300- 1500 v --.---25 NOV. 1100- 1300 0 150 300 met ers 0 1/8 1/4 mile 12 0 Current Vector Scale -,26' 0 50 cm/sec of i 0 1 knot DEPTH CONTOURS IN FEET Fig. 11. Currents on the Kapaa Reef (after Helfrich and Kohn, 1955, and Inman, Gayman, and Cox, 1963). 4. COASTAL CURRENTS AROUND OAHU Because of the number of separate drogue studies and current-meter studies made during the present investigation around Oahu, an index map showing the sites of these studies is included (Fig. 12). The sites of additional studies made in the course of engineering investigations are shown in Figure 1. 4.1 Northwest Coast Off Kaena Point, as reported by the Coast Pilot (Coast and Geodetic Survey, 196" @a) and as observed in the present investigations, there is a generally continuous northwestward current. Coast and Geodetic Survey observations with a Roberts current meter over a 24-hour period showed the northwest current, 0.8 mile., south of the Kaena Point light house, to have an average velocity of 0.8 knot and a maximum velocity of 1 knot. Drogue measurements in the present investigation made on 3-4 January 1963 (Fig. 13) showed a west or west-northwest current, of 1 or 2 knots speed, west of the point except at low tide when the current turned north-north- west and over one trajectory increased to 5 knots speed. At all tide stages the current west of the point was fed by convergent currents follow- ing both the north and south coasts of the Waianae Range. However, at high tide there was a divergence of about two miles southeast of Kaena Point so that at 4 miles southeast a southeast-setting current suggested the existence of a counter-clockwise eddy south of the point during the flood. A north-northwest set north of the point at low tide, together with eastward sets farther east at Waialua, similarly suggests the existence of a clockwise eddy north of the point during the ebb. -33- -34- From Kaena Point to Kahuku Point the only current studies which have been made are those of BeltY CollinsY and Associates (1962a, 0) in Kaiaka Bay, in Waialua Bay, and immediately offshore. In these studies, performed during two days in October and December 1961, the currents were observed by surface floats of various sorts, subsurface drogues, and dye. The results of the studies indicate that the floats and drogues were greatly affected directly by the wind. The records of the dye trajectories are very useful, however, in indicating current sets both in and outside the bays. Both in Waialua Bay inside the breakwater and in Kaiaka Bay the current apparently sets continuously seaward, no doubt as a result of the fresh-water streams entering the heads of the bays. Velocities are about 0-1 to 0.3 knot. Outside Kaiaka Bay the only measurements were on a ris- ing tide, when the current set southwestward with a velocity of 0.1 knot. This set agrees with that measured on a rising tideand at high tide out- side Waialua, Bay, where the velocities ranged from 0.2 to 0.3 knot. However, at low tide the:.current was..-found to set northward with a velocity of 0.1 to 0.2 knot from Waialua Bay. The currents in Kaiaka Bay are insufficient to prevent stagnation, as indicated by low oxygen content and high biological oxygen demand, and both bays are contaminated bacteriologically. The reversing tidal currents off Waialua, Bay are probably typical of much of the northwest coast of Oahu. 4.2 Northeast Coast-Kahuku to Ulupau Head According to the Coast Pilot, the "currentsoff Kahuku Point set weast- ward or northwest-mard but are sometimes negligible; tide rips have been reported a mile eastward of the point." Assuming that the tide rips occur ---------- 21'40'- ------------- 0 0 /0 ------- Gialuo ;3, Bay 0 aena Pt. Fig. 13 -------- kai Bay. A F i g. 15,16 Pearl Harbor Fi g. 17 g.35 -21, 20, A Ewa AP'PEN. Fig. 5 Hono@lulu -Makopuu - ---------- F i g.31,32 ---------- ..... Fig.34 Fig. 26,27 LFig. 23 128,29,30 ig. I APPEIN. Fig. 6 158120' 158' _7140' Fig. 12. Index map to figures showing coastal currents around Oahu. Locations of paddle-wheel current- meter measurements are shown by solid circles; Ekman current-meter measurements, by crosses; and locations of chemical studies, by triangles. 1 1 158* 20' 158*10' 21* 40'- Koeno Pt. -------------- -------- -------- 6 =4 ----------------- Scheme of Eddy Formation JM4 % IE, KAENA PT SPEED SCALE 0 2 KNOTS ------------ I" TIDE CHART TIDE CHART JANUARY 3,1963 JANUARY 4,1963 6A.M. NOON 6PIVI. 6A@M. NOON 6PIVI. 2 4 21*30'--0- or- Fig. 13. Results of measurements of currents near Kaena Point, Oahu, on January 3-4, 1963. (Measurements made during predominantly ebbing tides.) -35- at times when the current parallel to the shore is slight, observations are consistent with the concept that the ebb-stage current convergence is located in the vicinity of Kahuku Point and flood-stage current divergence is located somewhere to the southeast. The Coast Pilot also indicates that "an eastward current is reported in the vicinity of Mokumanu Islands.," near Ulupau Head. Judging from the current measurements in the vicinity of Kailua, described in section 4.4, it is unlikely that there is a continuous eastward current at this place. The report is probably meant to call attention to an occasional exception to the general westward or northipard flow described as passing the island. If so the flood-stage current convergence occurs, at least sometimes, off or northwest of Ulupau Head. Unfortunately there have been no really reliable current measurements made offshore along the coast between Kahuku Point and Ulupau Head. 4.3 Kaneohe Bay Measurments of the circulation in Kaneohe Bay (Fig. 14) indicate a well developed reef and lagoon circulation of the sort discussed in section 4.5. Water is introduced into the bay by mass transport over the reef and even through the shallow east channel. The surface circulation within the bay is apparently wind driven, and the flow along the bottom is controlled by the configuration of the channels and reefs. Discharge from the bay occurs through the deeper west channel. The measurements available indicate no tidal reversal in either channel, although it is conceivable that, during periods of calm when mass transport is minimized, there might be an outflow with the ebbing tide through the east channel and an inflow with the flooding tide through the west channel. -36- Some additional current measurements and analyses of water quality made by students in connection with studies of the distribution of zooplankton (T@,Tesukdi Piyakarnchana, oral communication) indicate that the southeast section of Kaneohe Bay, especially, is rather effectively isolated from the ocean. Although there is separate circulation within the southeast section resulting ma.'nly from wind drag, which maintains aeration even at depth, there is little exchange with the rest of the bay. A study of Nuupia Pond, a shallow walled-off arm of -the bay (Holmes and Narver and Belt, Collins, and Associates, 1959b)showed the currents in the pond to be wind-driven. A sampling program by the Division of Sewers (1957a)showed low bacter- ial concentrations except close to shore. 4.4 Kailua Mention was made of the parallelism of current sets off Kailua to the shore in a Holmes and Narver report of 1957, but the most extensive current observations in the vicinity of Kailua are those of Holmes and Narver and Belt, Collins, and Associates in 19501. Five daytime surveys were made off the base of Mokapu peninsula, one each in January, May, June, July, and August. The currents were observed with surface floats, subsurface floats, and dye. The results indicate that the floats, especially the subsurface ones, were greatly affected by direct wind drag. The dye patch trajectories, not affected by wind drag, indicated that the current set north during rising tide stages, west during a falling tide stage, and northwest at low tide. Velocities are not directly indicated but seem to have been on the order of 0.1 knot. Moku Manu Speed Scale 0 0.5 knots S,pt 4 S.@" 5 S,pt 6 0 6 12 Is 0 18 0 6 2@ 0 0 ............ Distance Scale (no. iles -6, 1962 September 4 0 K.P.P. 1. Mok.11@ it 0 Ahu 0 Lako I/ .-Ut W-d G 00 (Z) 00 ...... 00 Cy 0 0 0 0 0 4Z), 10 0 ...... WI: m Fig. 14. Results of drogue measurements of currents in Kaneohe Bay, Oahu, Septemb 1962. -37- These observations are consistent with the location of the ebb-stage convergence somewhere northwest of Kailua, but suggest that the flood-stage divergence is generally southeast of Kailua. In connection with the current surveys, a study was made of bacterial die-off as reported by Iha (1960). Even after allowing for dispersion the bacterial survival rate was only between .01 and .001 after 90 minutes. Details are discussed in section 7.3. 4.5 Waimanalo Current measurements off Waimanalo have been made by the Hawaii Insti- tute of Geophysics (see Figs.15, 16, 17) and by Marine Advisers at various times for more than a year from September 1961 to October 1962. The results of these measurements show that the currents off Waimanalo are complex and with the available data it is difficult to fit them into a definite pattern with any degree of certainty. Although northwesterly sets predominate the currents reverse at times especially in shallow water. Drogue measurements on September 11, 1962 (Fig. 15) show no reversals but a fluctuation in strength with tidal rhythm. The upper layers of water have a downwind- component toward shore. This effect is most pronounced at the surface and has been noticed at all locations where this type of measurement has been made. Drogue measurements on February 23, 1963 (Fig. 16) show currents with light trade winds blowing. The currents are weak, and since the one-meter drogues are moving up wind there certainly must be eddies here in the vertical plane as well as the horizontal. The southeast currents on the south side of Manana Island are representative of what Marine - Advisers, --Inc. found on several occasions. On January 31, 1962, and February 3, 1962, _38- their drogues traveled from inshore of Manana Island clockwise around Makapuu Point. On the second date mentioned there was no -,rind. The drogues were picked up off Hanauma Bay with an apparent av@@rage speed of more than 1 knot. Paddle-wheel cu,.rent-meter observations in 80 feet of water on July 15- 17, 1963 (Fig. 17) showed irregular current reversals. Much of th2 difference in c,,arent tat-terns a-t- Waimanalo at different times probably results a shf_ft in -Uhe pasition of -the flood current divergence from Mlakapulu '11oint, to so_,_.'.e@qbez@e no-th-uest of Waimanalo. The consequence would be a change in the set of the flood current at Waimanalo from northwest to southe-ast. [email protected] and othe-2 changes in the direction of the permanent flow are allso probably involved. 4.6 Koko Head to Makapuu Between Koko Head. and [email protected], the only current data available consists of drogu-- measurenents obtained by Sunn, Loi,-, Tom, and Hara on 8 April, 25 June, and 9 Septeh'@.Der, 19S__ (Sunn, Low, Tom, and Hara, 1962b@. These show a very clear a-_-_@d siziiple ti-d-e response. The flood flows, which set southwest., correspoi-Ild iii pha::;_e to the rising tide and the ebb flows, which set northeast. izl phase to the falling tide. Velocities as high as 1. 5 lu-ots fo-.' the flood current and. 0.8 knct for the ebb current I were measured, but 1-'hese rLight jaa'%?-e b,,-_@n _,(jmewhat intensified by wind drift. associat-ed w-lth @a 'Grade wind and a kona wind. 4.7 Maunalual B.ay Data frc@ai the paddle-ofnc@el curreut set in 80 feet of water off Wailupe Peninsula (Aina Haina) in July 10,63 (see Fig. 18) shows that a current pattern essentially like the one at Diamond Head holds for that 11570 40, w I \\ Depths of k current crosses 5 m, _-jO rn /0 1.5 rn Speed Scale 01 0 '0 SET V OL .5 1 knot 0 6 12 18 24 h EX 21023'N -1\', M 0 B A 0 3M Currents WAIMANALO at 5nn depth 'to 210 20'N (J@ Monana 11 Island MAKAPUU PT. _@E X) MO, @@not Ik at 157043'W 15704 'W U )w r-/ Fig. 15. Results of drogue measurements of currents off Waimanalo, September 11, 1962. SPEED SCALE 0.,5 knot 6 12 -18 24 h 5 QV 11 5 2 5 21023'N 0 5 /WIND 5 cm sec X 10 knots) WAIMANALO 10 10 210 20'N 'r Monona t. 50 5 ri 5-, 5 '----"MAKAPUU PT t@)7043'W GII (Depth contours in fathoms) 157040' Y5 0 5 040,W Fig. 16. Results of drogue measurements of currents off Waimanalo, February 23, 1963. NOON GPM MIDNIGHT 6A.M. NOON JULY 15, 1963 JULY 16.1963 SPEED SCALE 0 so knots .......... 0 1.0 TRUE NORTH W270 90E W j Nlo 4 0- -0 DEPTH OF WATER (M-L.L.W)-30FT=9tn METER FROM BOTTOM 10 FT - 3 -2- NOON 6 PM. MIDNIGHT 6A.M. NOON I JULY 16. 1963 SPEED SCALE JULY 17. 1963 C./se. .50 knots 0 1.0 TRUE NORTH 0 -2 W270 90E z 0 ISO S 0 - 0 DEPTH OF WATER (M.L.L.W.)- 79 FT- 24. METER FROM BOTTOM 371 FT - 11.3 . Fig. 17. Results of paddle-wheel current-meter measurements off Waimanalo, (top) July 15-16, (bottom) July 16-17, 1963. NOON 6 PM. MIDNIGHT 6A,M. NOON JULY11, 1qr03 JULY12,11963 SPEED SCALE cm/sec 1-7-1--F@T@7-1 0 50 knots 0 1.0 2- TRUE: NORTH 2 0 2 W 270 >1 W W 180 _j I- DEPTH OF WATER (M.L.L.W.)=79 FT=24m METER FROM BOTTOM = 37 FT. z 11.3 m 0- -0 Fig. 18. Results of paddle-wheel current-meter measurements off Wailupe Pensinsula, July 11-12, 1963. -39- area and probably as far as Koko Head., No current measurements were taken inside the bay near Kuliouou Beach Park. Here one would expect to find weak currents caused by eddies, currents caused by mass transport over the reef, and currents that are wind driven. 4.8 Mamala Bay Mamala Bay is the broad indentation of the southern coast of Oahu lying between Diamond Head and Barber's Point. Irt-')this bay open the Ala Moana Yacht basin, Kei!alo basi.,., Honolulu Harbor via the Honolulu Channel and via the Kal1bi Channel, a,-d Pearl Harbor. Information on the currents of Mamala, Bay has been derived from the following sources: (a) Institute of Geophysics drogue studies off Diamond Head (Figs. 24, 2.5, 26, 2T, 28, 2'9., - 30). (b) Engi neering Experiment Station paddle-wheel current meter record- ing off Diamond Head continuously for nearly a month'(Figs. 19, 20). (c) Institute of Geophysics drogue studies off Waikiki (Figs. 26, 27). (d) H.A.R. Austin and Associates and Law and Wilson (1961) drogue studies off Ala Moana. (e) Engineering Experiment Station paddle-wheel current-meter study off Magic Island (Fig. 2lip top). (f) Engineering Experiment Station paddle-wheel current meter study off Keiralo Basin (Fig. 21, bottom), (g) Institute of Geophysics drogue studies off Kewalo and Honolulu Harbors (Figs. 26, 27, 28, 29, 30). (h) Bureau of Sanitation (191i'l) studies of bacterial concentrations off the former Kewalo sewer outfall (Pig. 33). -40- (i) Metcalf and Eddy (1944) studies of bacterial concentration and slick fields from the former Kewalo outfall. (j) Division of Sewers (1951) drogue studies near the Sand Island sewer outfall. (k) Hyperion Engineers (1957) calculations based on the Division of Sewers (1952) studies. (l) Austin, Smith, and Associates (1961b)observations on the slick field from the Sand Island outfall. (m) Institute of Geophysics measurements of turbidity from the Sand Island outfall (Figs. 31 and 32). (n) Engineering Experiment Station paddle-wheel current measure- ments and dye studies in the vicinity of the Sand Island outfall. (Fig. 22). (o) Austin, Smith, and Associates (1960) drogue studies off Pearl Harbor. (p) Institute of Geophysics drogue studies off Pearl Harbor. (q) Institute of Geophysics drogue studies off Ewa (Fig. 34). (r) Institute of Geophysics paddle-wheel current-meter study southeast of Barber's Point (Fig. 23). The Institute of Geophysics current-meter study northwest of Barber's Point, although not in Mamala Bay, is also of critical importance in under- standing the current behavior in the Bay. Off Diamond Head the paddle-wheel current meter measurements continued by Tinniswood and Avery over a period from 24 November to 19 December 1963 indicate the predominance of tidal currents. Figure 19 shows some samples of the records obtained. The flood current, which persists during the rise NOON 6 P.M. MIDNIGHT 6 A.M. NOON 6 P.M. MIDNIGHT 3 - . I . . . I . . . I . . . I . I . I . . . I . . . . . NOVEMBER 24,1963 NOVEMBER 25,1963 SPEED SCALE TRUE NORTH =/"c 0 .1 '3'0'4' 0 10 20 2- rj-@ knots W 270 90E I -I - 01 0!2 '0.14'OIS 0!8 110 z 180 S W I 0- DEPTH OF WATER (M.L.L.W.) =42 FT.= 12.8m METER FROM BOTTOM 27 FT.= 8.2nn MIDNIGHT 6 A.M. NOON 6 P.M. MIDNIGHT 6 A.M. NOON 6 RIO. MIDNIGHT 3 1 , , I I , I I . . I . , I , , I . . j I I . . I . . . I NOV EMBER 26,1963 NOVEMBER 2T,1963 SPEED SCALE cm/soc TRUE NORTH 0 0 10 20 30 40 50 rr'@ kn ots W 270 @OE 0 0.2 0.4 0.. 0.8 1.0 2; ISO 2 S w 0- 6 c-ffVw DEPTH OF WATER (M.L.L.W.)=42 FT.= 12.8m METER FROM BOTTOM = 27 FT.= 8.2m 47 61 cm/sec 58 m/... Fig. 19. Results of paddle-wheel current-meter measurements off Diamond Head, (top) November 24-25, (bottom) November 26-27, 1963. MIDNIGHT 6 A.M. NOON 6 P.M. MIDNIGHT 6 A.M. NOON 6 P.M. MIDNIGHT DECEMBER 4,1963 DECEMBER 5,1963 SPEED SCALE 0 10 2@0' 3'0' 4!0' 56 knots I II I I I I I T-1 0 0.2 0.4 0.6 08 1.0 2- TRUE NORTH 0 W 270 SOE ISO S 0- DE PTH 0 F WAT E R (M. L. L.W.) 42 FT. 12. 8 rn 78 ..A..' P METER FROM BOTTOM 27 FT. - 8.2 nn MIDNIGHT 6 A.M. NOON 6 P.M. MIDNIGHT 6 A.M NOON 6 P.M. MIDNIGHT DECEMBER 8,1963 DECEMBER 9,1963 SPEED S 3- cm":@L' @0'3'0'46' 50 It no ts I I I I I T-1 0 0.2 0.4 0.6 0.8 1.0 TRUE NORTH 0 W 270C )90E w ISO w S 0- DEPTH OF WATER (M.L.L.W.) 42 FT. 12.8 rn METER FROM BOTTOM 27 FT. - 8. 2 nn Fig. 20. Results of paddle-wheel current-meter measurements off Diamond Head, (top) December 4-5, (bottom) December 8-9, 1963. MIDNIGHT 6 A.M. NOON 6 P.M. MIDNIGHT 6 A.M. N N 3- 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 , I I I I I I I I I L NOVEMBER 11,1963 NOVEMBER 12,1963 SPEED SCALE TRUE NORTH ctn/aac 0 1 T-T-T---l 0 5 10 15 20 25 KT@ knots 2 W 270 90E r--r-i i 0 0.1 0.2 03 0.4 0.5 2F ISO 2 S W I W 0 - DEPTH OF WATER (M.L.L.W.) 42 FT. 12.8m METER FROM BOTTOM 27 FT. 8.2 nn MIDNIGHT 6 A.M. NOON 6 PM. MIDNIGHT 6 A.M. NOrN 6 P.M. MIDNIGHT 3- 1 , I , @ I I @ I I I @ I I I I I I I I I I I I I I AUGUST 16,1963 AUGUST 17,1963 TRUE NORTH SPEED SCALE 0 0 5 10 15 20 25 2 IN 270 90E knots > 0 0.1 0.2 03 0.4 0.5 180 4 S 7 A 0- DEPTH OF WATER (M.L.L.W.) =42 FT.= 12.8m METER FROM BOTTOM z 27 FT.= 8.2nn I I I I I -T-1- r Fig. 21. Results of paddle-wheel current-meter measurements off Magic Island, (top) November 11-12, 1963, and off Kewalo, (bottom) August 16-17, 1963. MIDNIGHT 6 A.M. NOON 6 P.M. MIDNIGHT 6 A.M- NOON 6 P.M. MIDNIGHT 3 . . . I . I . . I I I . I . . I . I I . , I . . . I . . . I , . . , . I I . I I . 3 AUGUST 4,1963 AUGUST 5,1963 SPEED SCALE 0 5 10 15 20 25 knots TRUE NORTH 2- F-F-1 I -I , 1 1 1 0 -2 0 0.1 0.2 Q3 0.4 0.5 z - W 270 90E 180S 0- -0 DEPTH OF WATER (M.L.L.W.)-42 FT.-I2.8nn METER FROM BOTTOM 2T FT. - 8.2 m MIDNIGHT 6A.M. NOON 6 P.M. MIDNIGHT 6 A-M. NOON 6 P.M. MIDNIGHT 3 . . . . I I - I - - - I . I . - I I . . I I I , . I I . I . I I , I . . I . . I . I AUGUST 9, 1963 AUGUST 10,1963 TRUE NORTH SPEED SCALE 0 crn/sac 1 3 10 410 510 0 10 20 2- knots W 2TO 90E I I I I I 1 -1 2@ 0 02 0.4 OL6 Q8 1.0 ISO 0 t- W 0- - DEPTH OF WATER (M.L.L.W.) 48 FT. 14.6 M METER FROM BOTTOM 33 FT. - 1O.Om Fig. 22. Results of paddle-wheel current-meter measurements near Sand Island sewer out- fall, (top) August 4-5, -(bottom) August 9-10, 1963. 6 P@M. MIDNIGHT 6 A.M. NOON 6 P.M. I JULY 5, 1963 JULY 6, 1963 SPEED SCALE 0 0 0 1.0 2- TRUE NORTH 2 0 W270 90E z 0 180 > W W DEPTH OF WATER (M.L.LV1=79FT,24. 0- DISTANCE OF METER FROM BOTTOM= 3TI FT= 113. -0 6PM. MIDNIGHT 6kht. NOON I I JULY 8,1963 JULY 9,1963 SPEED SCALE cm/sec I I - I ' 1 .510 knDts 0 10 TRUE NORTH 0 2@ W270 OE S DEPTH OF WATER (M.L.L.W.)- 62 FT - 19 m METER FROM BOTTOM = 37 FT. = 11.3 m 0- 'JO Fig. 23. Results of paddle-wheel current-meter measurements (top) southeast of Barbers Point, July 5-6, 1963, and (bottom) northwest of Barbers Point, July 8-9, 1963. _41- of the tide and at the time of high tide, sets northwest in accordance with the theory discussed in section 2.4. The ebb current has the reverse set. The average velocity is approximately 0.6 knot. Characteristically the ebb velocity is greater than the flood velocity, and the ebb current before a large tide rise has reached a maximum of more than 2 knots. An offshore set during the turn of the current may be partly the effect of the winds, although it was also noted during the calm weather that predominated during the period of the current meter measurements. The records appear sufficiently regular to encourage the belief that harmonic analysis will provide the basis for useable current predictions. Drogue measurements made off Diamond Head at various times agree with the current-meter measurement's and provide, as well, some additional information to be discussed elsewhere. Less extensive paddle-wheel current measurements made about 1-1 miles 2 northwest of Barbers Point in July 1963 show similar although somewhat less regular results (Fig. 23,@bottom), -.with the flood-current :a6tting south and the ebb current setting northwest, as discussed in more detail in section @4.12. Still more irregular paddle-wheel- current-meter results were obtained a few days earlier about 3 miles east-southeast of Barbers Point as shown in F'igure 23 ("top). . Velocities averaged about 3/4 knot and reached a maximum of about 1-@- knots. Drogue measurements made in the same area in April 1963 indicate that a major part of the irregularity results from the formation of eddies especially from the swing of the flood current around the Point. Apparently the area of convergence of the flood current and the area of divergence of the ebb current must lie somewhere between Diamond Head and Barbers Point, in other words somewhere in Mamale. Bay. It is not surprising that the current patterns in the Bay are complex and irregular. -42- Between Sand Island and Diamond Head the currents generally show some similarities in phase to the currents at Diamond Head, although the velocities are lower and the irregularities increase toward Sand Island. Figure 26 summarizes drogue measurements in the area made during predominantly flood- current phases in 1962, and Figure 27 similarly s=marizes measurements for the ebb phases. Figures 28, 29, and 30 show the results of additional drogue measurements in February and March 1963 in relation to tide phases. Altogether more than 80 drogue settinEpwere made.in this area. Exceptions to the general westerly set of the flood current and easterly set of the ebb current are found in sets III and V on 24 February (Fig. 28) and set VI on 3 March (Fig. 29). These sets are in shallow water and the reversals are probably due to eddies. A comparison of Figures 29 and 30 shows that the strength of the tidal current is not alTays simply correlated with tidal amplitudes. It is also apparent, from Figure 28, that the change of direction of tidal current can occur at different times within short distances in the area west of Waikiki (cf. Fig. 28, sets IV, V, and VI). As a result of the complex current pattern and owing to the effect of variations in phase of currents in shallow and deep water, currents in opposite directions can exist with- in relatively small horizontal distances (see for example Fig. 29, sets A and* B). The effects of -vrind and mass transport were observed to depths of several fathoms in most measurements involving drogues set at several depths. However, except in direct wind-drift effects, only minor differences have been found between trade and kona conditions. Drogue measurements by H. A. R. Austin and Lawand Wilson (1961) in 10 20 iio 21* 16' ............. ............... ......... HEAD ........ P.IAMOND ............. SET ............... 5@ 15 ... ............. 200, SET "SET I 5 5 15m (depth of the 5m current cross) im SPEED SCALE 21- 14'- 0 0.5 1 KNOT SET= 15 5 TIDE CHART AUGUST 1, 1962 2- Jul 0 157 50' 6A.M NOON 6PM. (Depth contours in fathoms) Fig. 24. Results of drogue measurements of currents off Diamond Head, August 1, 1962, showing effect of wind drag and mass transport. SAN 7052'W 157050'W Speed Scale L 0 0*5 1 knot 0 6 12 18 24 81 2 DIAMOND /7 AL) 21016'N '06@ 5 0 71 0 5 1 4 TIDAL CURVE 21014'N DIAMOND 21016'N HEAD 00 0\ 7 2 6 5 21" 14'N 157052'W 157*50'W 0 1 5 km Fig. 25. Results of drogue measurements of currents off Diamond Head, August 17, 1962. Quasi-simultaneous observations at two stations. S nd ,sland OV-1 Nearly -'-stationary 21017'N--t -No movement Diamond e a 2101SN Speed Scale I I I I I l 0 1 knot a kDk 157 055'W 157050'W Fig. 26. Results of drogue measurements of currents in the eastern part of Mamala Bay in 1962 during predominantly flooding currents. Y Sand Island 1CO no movement 21017'N 8 \A Abb Diamond Head 21013'N .1111@@no movement Speed Scale 0 1 knot S asn d I.. lq@nd ,ment@ kD 0n @d ic H ,ad (D 157055'W 157-50'W Fig. 27. Results of drogue measurements of currents in the eastern part of Mamala Bay in 1962 during predominantly ebbing currents. TIDES. Z: SAND ISLAND H 0 N 'of ALA MOANA ------------- x" --------- ---- ]Z5 21-16! AX dSAN@DML N'D @A ALA MOANA 3m 115 Fig. 28. Results of drogue measurements of currents in the eastern part of Mamala Bay, Feb 1@ 54' 52, '58. W, 0 n ts; 0 SAND ISLAND H 0 N 0 L U L U 3M 1,5 ix, ALA MOANA IM, A A -------------- ------- 5of _10of -------------------- B =5 .......... AX 'of sot AL., Fig. 29. Results of drogue measurements of currents in the eastern part of Mamala Bay, M 158-54! 15W50' T, SAND ISLAND H 0 N 0 L U L U _2 IK5 --------- XV71 ALA MOANA Z --501 x ----------- ------------------------- ------ 21-16- v1- lof -3E5 ALA MOANA Fig. 30. Results of drogue measurements of currents in the eastern part of Mamala Bay, _43- front of the Ala Moana reef show quite consistent tidal-current reverses with the current setting north-northeast on the rising tide and south- southwest on the falling tide. The apparent reversal of phase may be the result of eddies consistently set up by both the flood and ebb current. The velocities measured for the south-southwesterly current sometimes exceeded 1 knot, considerably greater than those measured for the reverse current but the differenceG are probably the result of trade wind effects on the floats as well as trade wind-induced surface current. Dye and current-meter studies conducted by Tinniswood and Avery in the vicinity of the Sand Island ::ewer outfall during trade-wind weather indicate that the sewage may be carried either toward Diamond Head or toward Barber's Point. The paddle-wheel current meter showed a reversing current with some tendency to follow the Diamond Head pattern, but with stronger superimposed erratic currentj that probably repre3ented eddies. Velocities averaged about 0.2 knot and reached a maximum of about 0.4 knot. On one occasion, the paddle-wheel current meter showed that the current at the sewer outlet, 15 feet below the surface, flowed cont-inuously for 51 hours in the general direction of Waikiki; and, on another occasion, dye was followed from the sewer outlet in mid-morning to just off the Kewalo Channel by mid-afternoon. With the trade winds blowing, the surface layer moves with an offshore component that should carry floatables out to sea, but, with a kona wind blowing, the same process would carry the floatables shoreward. Additional tracer studies have used turbidity as the trace material. Figures 31 and 32 show the distribution of turbidity in the eastern part of Mamala Bay respectively during an ebbing current under "k=a conitions and during a predominantly flooding current under trade-wind conditions. -44- it should be noted that the distributions shown represent specific tide conditions and cannot be taken as averages. In Figure 31 a tongue of high turbidity at (A) results from the flow of sewage southwestward from the sewer outfall. Another tongue of high turbidity water at (B) may represent the outflow of turbid water from the Kalihi Channel. A tongue of clear water (C), from farther off shore, is flowing along the slope towards Waikiki. A sharp gradient in the concentration of pollutant is indicated by the turbidity measurements over the slope at (D). In Figure 32 the sewage flows at point (A) towards Pearl Harbor with a slight offshore component. A tongue of clear water flows in the same direction at (B) farther offshore. However, there are two concentrations of polluted water at points (C) and (D) still farther offshore over the slope. These have probably resulted from previous injections of sewage during periods of relatively low current velocity past the sewer outlet. Their distribution suggests that the net flow past the outlet first set toward the west and then swung toward the southeast during the few tide cycles that preceded the measurements. Similar studies were made by Tay monthly from June 1940 to September 1941 (Bureau of Sanitation, 1941) and by Metcalf and Eddy (1944) monthly from April to July 1944 using bacterial concentrations from the old Kewalo sewer outfall as tracers. Because of the nature of the sampling program the results cannot be expected to show fine detail, and times and tide stages at the times of collection are not indicated. Nevertheless the studies are extremely valuable because of the range of time and conditions they span. Metcalf and Eddy found that the contaminated water from the Kewalo sewer was moving only to the west or offshore, but Tay generally found a tongue of contaminated water moving eastward. The greatest SAND ISLAND SEWER 41 ------------ ------ ---- ------ 1.5 -@O ------------ 1@0 - ------ ----- --------- /,,-0-6 SAND ISLAND 1@ 7-5,@VW 157 *52'W Fig. 31. Distribution of turbidity off Sand Island and Ala Moana on December 28, 1962, during a predon A V, SAND ISLAND :v @F A ----- 6F ----------- ----------- A'@' 4 ----------- ---------- ------------ ------ ------------ c -------- 1 5 2 77777@1 --100 F 00, 157-54'W 157.52'W I Fig. 32. Distribution of turbidity off Sand Island and Ala Moana on July 17, 1963, during a predomir -45- eastward flow was in February 1941 (Fig. 33) when there was a concentration of Bacterium coli greater than 1000 per 100 ml one mile off' Kuhio Beach and a concentration greater than 100 per 100 ml 0.25 mile off the natatorium. It seems inescapable that sewage from the Sind Island outfall must at one time or another be carried to all parts of Mamala Bay, and that it must at times enter Keehi Lagoon, B.6nolulu Harbor, and probably inshore areas farther east. Drogue measurements by Austin, Smith, and Associates (196o) off the Pearl Harbor entrance and Hickam Field showed some tidal response, generally in phase with that at Diamond Head, but dominance by some other component that set continuously southwest during the six days of the study in Febru- ary, March, and April 1960, and on one day in December 1958, and that set northeast in two other days in December. The latter component probably involves wind drag. Wind data were not given for the times of the measure- ments, but it seems probable that kona winds prevailed on the two days when the set was northeast and trade winds on the other days. 4.9 Ala Wai to Kewalo Prior to the construction of the Ala Wai Yacht Harbor channel and the isolation of Kewalo Basin from the channel along the front of Ala Moana Park, there was a strong, unidirectional current flowing from the Ala Wai canal through the Yacht Harbor, augmented in the Ala Moana Park channel by water carried by mass transport over the reef, continuing through Kewalo Basin and out to sea through the Kewalo channel. Since the Ala Wai Yacht channel was dredged, and the channel along the front of Ala Moana Park was blocked off from both the Yacht Harbor and Kewalo Basin, the Ala Wai canal water has drained seaward through the yacht channel. Groundwater and storm-sewer discharge continues to flow seaward _46- through the Kewalo channU, however. Float studies by H. A. R. Austin and Associates and Law and Wilson (19a ) show that the seaward currents in both the Ala Wai and the Kewalo channels have velocities on the order of 0.1 to 0.2knot. There continues to be a slight westward flow in the Ala Moana Park channel, probably resulting from a combination of mass transport over the reef and wind drag in the channel. In the "Magic Island" channel configuration planned for construction on the Ala Moana reef (H.A.R. Austin and Associates and Law and Wilson, 1961), mass transport over a weir at the east entrance to the channel will be counted on to flush the channel westward. 4.10 Honolulu Harbor - Keehi Lagoon There seems to be practically no information on currents in Honolulu Harbor under present conditions. Keller, Tay, and Collins in 1920 described stagnant and polluted conditions that indicated inadequate tidal and stream-flow flushing. The isocol maps of Metcalf and Eddy in 1944 indicated high bacterial concentration in Honolulu Harbor and also in some tarts of Keehi Lagoon. The opening of the Kalihi ship channel frcm 'Honolulu Harbor west through Keehi Lagoon to the sea, however, has restored an original but long-closed route for circulation. The currents in the loop around Sand Island seem not to have been investigated. 4.11 Pearl Harbor Problems of sewage contamination in Pearl Harbor have been noted in several reports (Div. Sewers, 195-(b) Div. Sewers, 1958; Austin, Smith, and and Metcalf and Eddy, Assoc. 11962). A survey by Austin, Smith, and Associates (1961a) in Middle Loch off Pearl City, using surface and subsurface floats, indica-ted the LU X Q CANA PARK A Broken Line <) z -;/A 0' 0 0 )10 `30 /@r I 01, 1000 000 /@77 10,000 1,000 Z 500 100 0 V4 MAP SHOWING ISOCOLS PER 100 M.L. SAMPLES AND B-COLI DENSITIES TAKEN CO DURING THE MONTH OF FEB. 1941 0 0.5 1.0 SCALE IN MILES FROM TERRITORY BUREAU Fig. 33. Coliform concentrations derived from old Kewalo sewer, February 1941 (from Bureau of -47- existence of weak but well defined tidal components. The flood, correspond- ing in phase to the rising tide, set generally northwest toward the head of the Loch, and the ebb, corresponding in phase to the falling tide, gener- ally set southeast toward Ford Island. Superimposed on the tidal oscillations, which involved velocities only on the order of a tenth or tenths of a knot, were a prevailing seaward flow on the surface resulting from stream and spring discharge, and wind drag. The wind affected particularly the surface floats. Presumably similar conditions prevail in other parts of the Harbor. In another survey made at the harbor entrance by Austin, Smith, and Associates (1960), involving surface and subsurface floats, the flood current was shown entering the harbor with a velocity on the order of 0.2 knot, generally with the tide rise as expected. 4.12 Southwest Coast Information on currents along the southwest coast of Oahu is derived from: (a) the Coast and Geodetic Survey (1963a) Roberts current meter study just south of Kaena Point previously referred to; (b) the Institute of Geophysics drogue studies of 3-4 January 1963 at Kaena Point and 4 miles southeastY previously referred to (Fig.13). (c) float,drogue, and dye surveys in Pokai Bay and in general off the town of Waianae repeated through most of 1961 by Sunn, Low, Tom, and Hara (1962a) (Figs. 8, 36, 37). (d) similar surveys southwest of Kaneilio Point in October and November 1961 conducted by Belt, Collins, and Associates (1962b); -48- (e) remarks by Tippetts, Abbett, McCarthy, and Stratton (1961) concerning currents off BroTms Camp; (f) Institute of Geophysics drogue studies 1 to 2 miles northwest of Barber's Point in April and July 1963 (Fig. 35); and (g) an Institute of Geophysics paddle-wheel current meter study about 1-1 miles northwest of Barber's Point conducted in July 196' 2 (Fig. 23). The paddle-wheel current meter data from northwest of Barber's Point (Fig. 23) indicate, for that areal a clear though somewhat complicated tidal behavior, the flood current setting south and the ebb current setting north-northwest. The flood current was more persistent than the ebb current at the time of the measurement, although the opposite should have been expected from the theory discussed in section 2.4. The currents, instead of leading the tides, seem in general to lag behind. The maximum flood current of about 1 knot was associated with the lower of the two high tides, and the ebb tide velocities reached a still higher maximum of about 1.5 knot, The nearby drogue observations (Figs. 34,..35) agree v@lth the -current meter observations as to directions and strength of the currents. They indicate, in addition, that the current strength tends to be considerably greater in the shallow water close to shore than in the deeper water offshore, and that there is a shoreward set in the deeper water during the ebb current not found at the surface. The clockwise swing in current directions observed in the early afternoon of 9 July occurred during a change from flood current to ebb current. The Tippetts, Abbett, McCarthy, and Stratton notes on currents at Browns Camp are not inconsistent with the above information, but they add nothing to it except that the current speed may occasionally reach 2 knots. OSISAL Barbers Pt. AERO 0 M e T s ARBERS PT 12 31 \0 Scheme of the A 2 SET 13T MAGNITUDE DUE TO POOF 1[4 T SPEED SCALE 0.5 1KNOT 0 3 6A.M. NOON 6PM. 2- 4 IV 0 Wind -1 /-\N 10 5m sec-I (=10 knots) I I TIDE APRIL 8, 1963 Depth contours in fathoms A@ar b e r 06' 041 02' 1580 0 O'W 58' Fig. 34. Results of drogue measurements of currents southeast of Barbers Point, April SPEED SCALE 0 0.5 1 KNOT TIDE CHARTS 6 A.M. 6 A.M. NOON 6 RM. 6 A.M. NOON 6 PM. 2- / -- 2 - /- \ I -\"I- @Iim - I / /1 11 0- 0 JULY 9, 1963 APRIL 9, 1963 -21022 21022, 12 10 210201- 210 20' 210 20' M3 M, M 2 3 14 1? 3 J14 5 3 'r5 50 10010 10 5 1@ 0 BARBER 50m CROSSES BARBERS PT. PT. one@ 158010' 5e 158010, 158009' 4 Ir. 8 A R B E @R@ FATHOMS Fig. 35. Results of drogue, measurements of currents northwest of Barbers Point on April 9 and July 9, 1963. _49- The Sunn, Low, Tom, and Hara (196&)study of the current systems in Pokai Bay and off Waianae was in general a very intensive one, lasting a year and utilizing drift cards, drift bottles, drogues, and dye. Two of the drogue studies were carried through a 24-hour period. Together with the Belt, Collins, and Associates (1962b)study of the currents off Kaneilio Point, it provides an excellent picture of the current system of the area. Off the points the currents are essentially reversing, but generally with the same or a more exaggerated phase anomaly to the tides, as was described from the current meter observations northwest of Barbers Point. Phase anomalies were found similar to or more exaggerated than those at Barbers Point, currents setting in the direction of the flood occurring sometimes at low tide and currents setting in the ebb direction, at high tide. Inshore, between the points, the currents were more erratic as a result of eddy formation. The generalized patterns of ebb and flood currents found are shown in Figure.36. Trade winds tended. to, deflect -the @ surface currents seaward and kona,winds to deflect them landward resulting in upwelling and anstau conditions. As previously discussed, the ebb current continues to set northwest- ward to Kaena Point, whereas the southwestward flood flow along the Waianae coast must stem from a divergence about 2 miles south of the Point. 4.13 Summary of Coastal Currents Around Oahu The coastal currents around Oahu are apparently consistent in general with the pattern expected from the distortion by the island of a current while results from the superposition of a tidal current on a permanent flow. The irregular shape of the island introduces considerable irregu- larities into the pattern, and a few features of the currents do not -50- easily fit with the pattern expected. The flood current apparently impinges on the island and diverges generally at Makapuu. Point or in the vicinity of Waimanalo, but possibly on occasion as far northwest as Ulupau Head. It appears to converge some- where in the western part of Mamala, Bay. The ebb current diverges some- where off Mamala Bay, probably off the western part and appears to have a main reconvergence at Kahuku Point. Currents set almost continuously northwesterly along the northeast coast and perhaps not quite so continuously in the vicinity of Waimanalo consistent with expectations for the coastline between the flood divergence and the ebb convergence. The currents also set almost continuously westward past Kaena Point, as the result perhaps of eddying around the point. Along other shores they generally reverse with the tides, but one direction frequently predominates over the other. In the bays and at other irregularities in the shoreline eddies are formed. In some areas of Mamala Bay the current patterns are especially irregular as the result of eddying and also of the relative weakness of the tidal currents compared with wind drag and mass transport. In the shallow water near Sand Island the currents sometimes set for several days in one direction., then reverse. Pearl Harbor shows the typical tidal circulation of a deep bay with a narrow entrance. Reef and lagoon circulation is notable at Kaneohe Bay and Ala Moana. Figure37 shows diagrammatically the general pattern of the ebb currents around Oahu during the trade-wind season. In interpreting this diagram several points must be kept in mind. First, the degree of generalization is somewhat variable from place to place. In some areas, particularly the area of east-west divergence in Mamala Bay there are likely to be several WAIANAE .@@04 BAY POKAI @ZD P 590 1000 YARDS WAIANAE Not% POK I BAY 0 500 1000 YARDS Fig. 36. Generalized flood (top) and ebb (bottom) current patterns for Waianae area (from Sunn, Low, Tom, and Hara, 1962). Probable area a, convergence ring ebb current Kahuku Pt. c" -21*401 Flood Curre ------ ------ -------- Waialuo Say Koeno Pt. Strong current I to 4 knots),\,-- usually not reversing in tidol cycle Current directed 'I,,- awards Pokoi Bay 0 A H Current at the 1 , Current su rface flows at',\ Pearl Harbor reversin a small angle away---, but fl from the coast. I knot \\1 2 1* 20'- 10 Barbers Pt. E.0 Honolulu Mokapuu P int kll\ ------ Irregular Currents ----- ------ Area of divergence during ebb current 158* 20' 158* 1571 40' Fig. 37. Generalized ebb current pattern around Oahu during trade wind season. Inset shows flood current pattern. _51- zones of slope (north-south) convergence and many eddies whose positions are not predictable, whereas in other areas the predicted prevailing current be may be expected to/strong and regular. Second, the chart should not be regarded as a strictly synoptic one because the tide phases vary somewhat in time from place to place, in general being about an hour earlier on the north coast than on the south coast. The inset shows diagrammatically the general pattern of the flood currents during the trade wind season. The pattern during kona weather is less well outlined, but apparently the main differences are in the irind effects on the surface currents. Although there may be changes due to the seasonal shifts in the permanent drift, these have not been identifiable. In any case they are likely to be less pronounced than the random changes in the permanent drift, and they are certainly less pronounced than the tidal changes. 5. COASTAL CURRENTS AROUND MOLOKA.I, LANAI, KAHOOLAVTE, AND 14AUI 5.1 Molokai According to the Coast Pilot (Coast and Geodetic Survey, 1963a) currents are re-ported to set westward along the entire northern coast of Molokai, but there seem to have been no reliable observations. Again according to the Coast Pilot: "Current observations have been made at several places along the southern shore of Molokai between Kamalo and Laau Point. They indicate, in general, an eastward flow along the shore in the vicinity of Kaunakahai and Kamalo [with a velocity of about 1 knot off Kamalo], and a westward flow near Laau Point. Combined with these movements are tidal currents [with the flood setting west and the ebb setting east] . . . The westward flow near Laau Point is reported to turn sharply northward at the point A current rip often observed off Laau Point is probably the result of the conver- gence of the northwesterly current rounding the point and a southerly current following the west coast. Currents are said to set northeastward along the southeast coast. Coast and Geodetic Survey (1963b) observations in the Kalohi Channel in 1961 show reversing currents, the flood current with an average maximum velocity of 0.4 knot setting west-southwest and the ebb current with an average mw,limum velocity of 0.5 knot setting east-northeast. 5.2 Lanai No reliable current measurements have been made around Lanai except those in the Kalohi Channel, discussed in section 5.1, and those in the -53- -54- A:uau Channel, discussed in section 5.4. It seems probably that the flood tide current diverging off the northeast coast of Lanai converges again off the southwest coast, and that the ebb tide current shows the apposite relationshi- .p. However, the tidal currents should be weaker on the southwest side becuase of the lack of constriction in the narrow channels, and the permanent west or northwest drift may predominate. 5.3 Kahoola,.@Te According to the Coast Pilot the Drevailing current is westerly along the south coast of Kahoolawe, swinging to northwesterly at the westerly tip of the island. The currents in the Kealaikahiki Channel were found by Coast and Geodetic Survey (1963a) measurements in 1962 to be weak and variable and influenced by the wind. The mw:imum velocity observed was 0.'-- knot in a generally northeast direction. One may suspect that systematic tidal currents could be found by careful analysis As previously described, the currents in the Alalakeiki Channel are variable, but the prevailing drift on the Kahoolawe coast is southeasterly, 5.4 West Maui According to the Coast Pilot (Coast and Geodetic Survey, 1963a): "The current at Lahaina usually sets northward and reaches a maximum velocity of 1 or 2 knots before low water. Before high water the current is normally quite weak and may set either northward or southward." A confused current setting generally southward is reported at Mala, only a mile north of Lahaina. Still farther north at Kekaa Point reversing north and south tidal currents of 0.5 knot strength have been measured. The phase relations are not stated. Offshore in the Auau Channel tidal -55- currents were measured by the Coast and Geodetic Survey in 1962. The flood current, with an average maximurn velocity of 0.6 knot, sets east, arid the ebb current, with an average maximum velocity of 0.5 knot, sets west (Coast and Geodetic Survey, 1963b). In the Pailolo Channel, farther north, weak, variable currents with a maximum velocity of 0.6 knot were measured in the same season. It seems probably from these rather meager and somewhat inconsistent data that (a) the dominant systematic currents along the west coast of West Maui, as well as in the channels between Maui and Lanai and Molokai, are tidal in nature, with the flood current setting generally southwest in the Pailolo Channel, west in the Kalohi Channel, and southeast in the Auau Channel@ (b) these tidal currents, e:,-cept in the middle of the Auau Channel, are sufficiently weak for wind or other random effects to complicate the general pattern; and (c) the patternclose to shore, is complicated by topographic effects. Northerly currents are reported off Napili Day by the Coast Pilot, but no reliable current measurements seem to have been made along the north coast of Maui from Kekaa Point to Kahului Bay. 5.5 Kahului Bay and Harbor An intensive study of the current systems in Kahului Harbor and in the bay just outside was conducted in August and September 1962 by Herschler and RandolDh (1962) using surface and subsurface drogues, lath floats, drift bottles, drift cards, and dye. All measurements vere made during daylight hours in tradewind weather. The floats and especially the cards and drogues were found to be affected directly by the wind, and almost all of the apparent sets both inside and outside the harbor were west or southwest, parallel to the wind. The dye studies showed tidal currents reversizig near the harbor mouth and in the harbor, the flood -56- currents entering and the ebb current leaving the harbor, each with maximum velocities of about 0.3 knot (Fig _ 36);..: i3ut_sade'the_qaar:&or the dye studies showed a continuous westward drift past the entrance with an average velocity of about 0.2 knot and no tidal reversal. This drift turned northwest just west of the entrance, leaving room for an eddy in the vicinity of the Wailuku S-_Wer outfall west of the harbor. Upwelling outside the east breakwater was shown on a rising tide by chloride content greater than normal. The chloride content of the surface water in the harbor was progressively lower closer to shore as a result of ground-water discharge. The dissolved o,,,njgen content and biological oxygen demand of the water in the harbor indicated efficient flushing by the tidal currents. 5.6 Worth Coast of East Maui An eastward current has been reported off Pauwela Point and a northeastward current off Nahiku by the Coast Pilot. It seems very unlikely that these reports indicate the prevailing current direction, and there seem to have been no reliable current observations between Kahului and Hana. 5.7 South Coast The reversing currents in the Alenuihaha Channel are described in section 6.1. Near the south Maui coast, the dominance of the tidal components is pronounced. At Kauihi Head, to the east, the Coast and Geodetic Survey (1963a) has measured the south-setting flood current with a velocity of 1 kno@,and according to the Coast Pilot, the north-setting ebb current has a velocity of 1.5 knots. Near Alau Island the tidal K A HU LUI BAY KAHULUI BAY t A' WAILUKU OUTFALL WAILUKU OUTFALL Ilk f 'f *. Ilk K AHULUI OUTFALL KAHULUI OUTFALL 4- Ar N HARBOR N 'HARBOR 1@00 2000 0 1000 2000 FEET KAHULUI TO@N FEET KAHULUI TOWN 1 962 1962 from from HERSCHLER AND RANDOLPH HERSCHLER AND RANDOLPH CONSULTING ENGINEERS RISING TIDE CONSULTING ENGIN EERS FALLING TIDE HONOLULU, HAWAII WATER MOVEMENTI HONOLULU, HAWAII WATER MOVEMENT Fig. 38. Generalized flood aeft) and ebb (right) current patterns for Kahului area (from Herschler and Randolph, 1962). -57- currents have velocities of 0.5 knot, and there is said to be an eddy between the Island and Kauiki Head. Tidal currents of as much as 0.8 knot have been observed 1 niile southeast of Cape Hanamanioa (Coast and.Geodetic Survey, 1963a), but the phase relations are uncertain. 5.8 Alalakeiki Channel Coast and Geodetic Survey (1961a) observations in 1962 show the current in the Alalake 41@i Channel to be variable, probably as a result of tidal effects., with maximum velocities of 1 knot, and with a general net northwesterly, drift of 0 - '5 knot aiOng the 1--laui shore 5.9 Southi,.@est Coast A northwestward current has been reported in Maalaea Bay (Coast and Geodetic Survey, 1963a) but no reliable current observations seem to have been made anywhere along the southwest coast of 11aui from Makena to Lahaina. 5.10 Summary of Coastal Currents Around Islands of the Maui GrouT) Because of the shallow water connecting t@'iem, Molokai, Lanai, Kahoolawe, and Maui probably act some@,,,hat as a unit in diverting the permanent flow and tidal currents. It seems best therefore to summarize together the currents around these islands of the Maui group. The available coastal current data is shown in simplified diagrammatic form in Figure 39, together with some speculative interpretations of current directions shown with question marks. On the basis of the theory discussed in section 2.5, it seems probable that the principal flood current divergence is near the eastern point of Maui, although the report of easterly currents along the northeast coast -58- of East Maui may indicate that the divergence moves sometimes to the north point of East Maui. Supplementary areas of flood divergence -must be located near the east end of Yioloka 4, the northeast point of Lanai, and the east Doint of Kahoolawe. Flood convergences are probably located somewhere in the vicinity of Olowalu, Maui, off the southwest 7)oints of Kahoolawe and Lanai, and off Laau Point, the southwestern T)oint of Molokai. The principal convergence may be in any of the last three areas, but seer-is most likely to be off Laau Point. The DrinciDal ebb divergence is probably off the south point of Kahoolawe. Subsidiary divergences are probably located in Maalaea Bay, Maui, off the south coast of Lanai, and somewhere between Laau Point and Kaunakakai, Molokai. The principal ebb convergence is probably off the northeast tip of Molokai, and subsidiary convergences off the north point of West Maui, the northeast point of Lanai, and the east point of Kahoolawe. 160* 159* 158* 157o 156o 22o-NII AU .......... I ena P -o OAH X MOLOKAI C, L... P ........... Kahului B. LANAI MAU I A KEAL IKAHI@l C.-/ KA LAWE A ALALAKEIKI C. w4l ? a/, 20* N K..h.W P. HAWA 0 10 20 30 Scale in Nautical Miles Kauna P. Approx. 19* LEGEND ? A H FLOOD CURRENT EBB CURRENT -------- 100 FATHOMS 160* 159* 158* 1570 156' Fig. 39. Generalized diagram of coastal currents around the Hawaiian Islands. 6. COASTAL CURRENTS AROUND HAWAII 6.1 Alenuihaha Channel According to the Coast Pilot (Coast and Geodetic Survey, 1963a): "Daring strong trade winds the [Alenuihahal channel is quite rough and a current of 1 to 2 knots sets westward, but during the calms which fre- quently follow, there is at times an easterly set of about 1 knot, and during kona winds the easterly set may reach a velocity of 2 or 3 knots." It seems probable that these observations pertain strictly only to the surface layers most affected by wind drift. At depth, the reversibility is probably a function not only of wind direction and speed but of tide phase, the flood current vector setting southwest and the ebb current vector setting northeast. 6.2 Northeast Coast Along the northeast coast of Hawaii from Cape Kumukahi, the eastern extremity, to Upolu Point, the northern extremity, the current sets generally to the northwest, according to the Coast Pilot. However, as noted by Belt, Collins, and Associates (1961a) muddy water frcm the sugar mills along the Hilo Coast may frequently be seen moving southward. It seems possible that at some times the permanent flow follows the coast into Hilo Bay but at other times diverges from the coast at Leleiwi Point, permitting an eddy or -tidal effects to cause a reversal in Hilo Bay. The direction and strength of the trade winds may be influential in deter- mining the current direction in the outer part of Hilo Bay. -59- -6o- 6.3 Hilo Harbor Currents within Hilo Harbor, as shown by two surveys in January and April le ,161, consist of a reversing component setting into and out of the harbor, superimposed upon a net drift- out of the harbor resulting from the discharge of the Wailuku and Wailoa Rivers (Belt, Collins, and Assoc., 196-l'O. Velocities are not directly indicated in the report on the surveys but appear to be less than 0.1 knot below the surface, as indicated by the trajectories of dye patches. Subsurface drogues and especially surface floats showed longer trajectories apparently influenced by the wind as well as by the more rapid outflow of the fresher water at the surface. A dye patch outside of the entrance drifted to the northwest, at less than 0.1 knot, showing no digression toward -Che entrance on a rising tide. According to the Coast Pilot a north-northwest setting current of as much as 1 knot has been reported in the approach to the harbor, probably when the rivers are in flood. The Belt-Collins study found pollution and stagnation in the harbor indicated by both chemical and bacteriological conditions. 6.4 Southeast Coast According to the Coast Pilot, the current sets generally to the soixthwest along the southeast coast from Cape Kumukahi to Ka Lae, the southern extremity of the Island. However, also according to the Coast Pilot, there is an inshore counter current passing around Ka Lae in the reverse direction and traceable as far as Keauhou Poirr@. It seems prob- able that these observations indicate, in reality, a reversal with time rather than a reversal with position, the stronger southwesterly current resulting from the reinfcrcement of the permanent flow by a tidal current -61- during the flood and by the prevailing tradewind drift, a weaker reversed current resulting at -the ebb. 6-5 SouthwestCoast The configuration of Ka Lae suggests that an eddy may be formed in its lee durink-11 the floodl so 'Uhat the current sets generally east-south- east. The Coast Pilot in fact describes an inshore, southeast-settingg counter current along the coast from Ka Lae to Kauna Point. From Kauna Point to Keahole Point the current usually sets to the north-northwest. Velocities approaching 2 knots have been reported in the vicinity of Milolii, according to the Coast Pilot. 6.6 Kailua-Kona Float observations off Kailua-Kona by the Department of Health in may 1961 (H.A'.R. Austin and Assoc., 1961) appear to confirm the gener- ally northwest set there. The floats used were obviously Greatly in- fluenced by winds, and showed reversing trajectories that are probably almost entirely the result of the sea breeze-land breeze wind pattern characteristic of the area. There is some suggestion of the existence of a south-setting ccmponent, or at least a slackening of the northwest current, with the rising tide, but if so the tidal current is in phase with the current expectable west of !Volu Point rather than the current expectable west of Ka Lae. Austin, Smith, and Associates point out that the sea-breeze would drive floatables on shore at Kailua-Kona. 6.7 Northwest Coast Current rips are frequently reported north of Keahole Point, ac- cording to the Coast Pilot; a 0.5 knot southwesterly current has been -62- observed at Kiholo Bay; and there is practically no current at Kawaihae. These observations sugCest that the northerly current following the coast south of Keahole Point sets offshore from the coast north of that PointY leavin6 room for a south-setting eddy inshore. There are persistent reports of a constant north-setting current off MahuJ4@ona, conver-inr, off Upolu Point with the northwest-settini-, current following the northeast coast of the Island. However, Coast and Geodetic Survey measurements off Mahukona showed both north- and south-settinZ currents with velocities of nearly 1 knot. It seems probable that these reversing currents are tidal, the south set representing the flood and the north set the ebb, and that the divergence between the normal north set at Upolu. and the normal south set in Kawadhae Bay shifts north and south of Mahukona with the tide stage. 6.8 Summary of Coastal Currents Around Hawaii The available data on coastal currents around Hawaii, although meager, suggest that the major flood divergence on the island is off Cape Kumukahi. The location of the major flood convergence is uncertain and may be anywhere from Kauna Point to Kailua-Kona. The major ebb divergence is probably off Kauna Point, and the major ebb convergence is probably off Upolu Point. There appears to be a large ebb counter- current in the vicinity of Kawaihae, and there may be a counter current at any tide stage in Hilo Bay. The available current information and additional interpretation are diagrammed in Figure 7. SOME CHEMICAL, BIOLOGICAL, AND GEOLOGICAL OBSERVATIONS PERTAINING To SEWAGE DISPOSAL 7.1 Distribution of Chemical Properties off Sand Island Sewer and in Kaneohe Bay The distributions of chlorinity, dissolved oxygen, and phosphates were measured off the Sand Island sewer outfall in August 1962. The results, shown in Appendix Table 5a and plotted in Figure 40, indicate that most of the sewage is confined to a relatively thin surface layer, the thickness of which increases slightly with distance from the source. The oxygen and phosphate values suggest that the breakdown of organic matter is relatively slow close to the source but speeds up farther away. Intensive phyto- plankton growth has been noticed at a distance from the outfall,, presumably resulting from the supply of nutrients from the sewage to the originally relatively nutrient-poor oceanic waters. Some additional chemical studies were carried out in Kaneohe Bay in September 1962 to ascertain whether any stagnation of deep water occurs there. The results are shown in Appendix Table 5a. A slight stagnation of the deeper waters in the southeastern part of the Bay can be noticed with respect to sewage disposal in these waters. The water exchange and flushing of this part of the Bay are slow and the sewage is carried by surface wind-driven currents toward the Kaneohe shore. Continued attention should be given to the conditions in this part of the Bay, although the values are not alarming at present. -63- -64- 7.2 Bottom Deposits off Sand Island Sewer Pn intensive sampling of bottom deposits was made off the Sand Island sewer outfall to a distance of about lffile. Bare areas of old coral and other consolidated calcareous rocks were common, and where there was a mantle of unconsolidated sediment, it was usually coral sand. No organic or directly polluted sediments were found. The sampling indi- cated vigorous biological growth on the bottom, especially downslope about One -hQf dle from the shore where there were large colonies of mussels. The relatively richer biological growth on the bottom suggests that the sewage has a fertilizing influence. No direct effects of sewage on coral growth or its breakdown were observed. There were no living corals in the area investigated, and the pieces of coral brought up from the bottom did not indicate any acceleration of breakdown. 7-3 Bacterial Die-off in the Sea It has been universally found the bacterial concentrations in sea water polluted with sewage are lower than can be accounted for by dilution alone. The extra decrease in concentration has been variously attributed to the activity of bactericidal agents in the sea water, bacteriophages, or protozoans, to adsorption on sedimentary particles followed by sedi- mentation, or to the effects of solar radiation. Various bacteria have been found to be differentially resistant, but prior to 1959 the studies on bacterial die-off in sea water had been dcne only in the laboratory or, if in the sea, with dialysis tubes and laboratory cultures. The results were therefore quantitatively suspect, and in any case could not have been expected to pertain closely to conditions in Hawaiian waters. DEPTH IN METERS DEPTH IN METERS DEPT CD 0) .4 N 0 Q cp -------- tl N (D III 0 bD (D 0 0 t 0 b CD w OD 0 -4 Z Ln CD 0--o CD LW 3 _65- A special study of the survival of sewage bacteria in the sea was made by Iha in connection with the Holmes and Narver and Belt, Collins, and Associates (1959a)study of sewage disposal possibilities ia Kailua Bay (Iha, 196o). Actual sewage, dosed with a radioactive tracer and a dye tracer, was introduced into the bay on five occasions, one each in the months from April through September 1959. The movement of the dis- persing cloud of sewage was tracked visually by means of the dye. A sample was taken within a few minutes of the initial introduction and additional samples were taken at intervals thereafter through periods ranging from 40 to 116 minutes. The dilution of the sample was measured by the decrease in radioactivity. Concentrations of both coliform bac- teria and enterococci were measured by standard techniques. The decreasing concentrations of both coliform bacteria and entero- cocci, even after corrections for dilution, showed less t3aan 0.01 per cent survival after 30 minutes. Sedimentation was found to be insigni- ficant and bactericidal action of the sea water was judged predominantly responsible for the die-off. The survival rate for the enterococci was found to be higher than that for the coliform bacteria. Iha's results were not expressed in terms that are directly usable for computations of bacterial die-off in practical sewage disposal prob- lems. Bacterial die-off has been expressed by previous investigators in several ways, reducible to the following forms: CB 1 = X k (Conway, date?) CBO D = exp (-kT) (Chick, 1900; Brooks, 1960) -66- = exp [-k (t -to)] (Ketchum and others, 1949; Vaccavo and others, 1950) where CB = concentration of bacteria CBo = initial concentration of bacteria D = dilution factor X = distance from point of injection t = time elapsed from injection to = lag k, k', k" = constants Iha's results have been plotted in figure 41 in terms of the natural log of the bacterial concentration ratios, allowing for dilution. To these data linear regression lines have been fitted by least squares. The results fit the form; CB . CTo = exp [ -k (t-to)] CBo CT where: CT = concentration of tracer CTo= initial concentration of tracer and the constants are: Coliform bacteria Enterococci k 9.76 x 10-3 2.15 X 10-3 to -72 min. -308 min. It will be noted that initial rates of decline in bacterial concen- tration in Iha's experiments were more rapid than subsequent rates. The apparent negative values for the lag, to, are a consequence. The reasons for this behavior are not apparent, and the values of to are, perhaps open 4- __ I - L 1 A.COLIFORMS T1076 5 U_ -4- -10 10 20 30 40 50 60 70 so 90 100 I;o 120 TIME, t min. 4- 2- B.ENTEROCOCCI 0- .-4\ -2- U: W ix ME -4 \_OV 8- 10 10 20 30 40 50 60 70 80 90 100 110 120 TIME, t , min. Fig. 41. Bacterial die-off in sewage disposed off in the ocean. (Computed from data of Iha, 1960.) Roman numbers indicate months of experimental runs. CB = concentration of bacteria CBO = initial concentration of bacteria CT = concentration of tracer CTO = initial concentration of tracer -67- to question. Certainly a curvilinear relationship would fit the data better than the linear relationship used, but the significance of the improvement in fit would be questionable. It seems probable, however, that the values of k are reasonably accurate for Kailua conditionsY and certainly the over-all relationships are the best that are available for Hawaiian conditions in Seneral. 7.4 Biological Oxyg@en Demand of Sea It7ater A special study of the biolor,ical oxygen demand (BOD) of sea water has been carried out by Laevastu, Zeitlin, and Song (me). With respect to sewage disposal the main results of this study, which will be published in a separate report, are that the routine methods of BOD determination, as used with fresh water, are of questionable value in marine waters. The oxygen consumption of sea water depends on numerous factors but is largely a function of the ratio of solid surfaces and does not indicate directly the degree of pollution or the power of self-purification. A method of BOD determination involving filtration of the sea water after collection, the use of standaxdized sample bottles, and the use of standardized incubation conditions is recommended. 171 0) 0- Sewer CD out! a 11 CD 0 Surface current r- Sewer CD CD Subsurface Outfall current Section A-A 8. APPLICATION OF COASTAL CURRENT AND RELATED INFORMATION TO SEWAGE DISPOSAL PROBLEMS IN COASV1 WATERS It is the aim in disposing of sewage into natural waters that the sewage be decomposed and dispersed in as short a time and distance as possible, and paxticularly before the waters reach any shoreline or other region where the sewage can be deleterious. In this discussion of means to approach problems of sewage disposal at sea, the processes of dis- pcrsal and decomposition will be discussed first, then methods of analysis using coastal current data and other related information. 8.1 Processes of Dispersal and Decomposition of Sewage at Sea When fresh s:--wage is introduced into the sea from an outfall on -the bottom,, the sewage riszs to the surface because of i'U-s lower density, diffasinr@, on th-- way up becauso of th.-- -turbulence induced by its own motio@i. The diffusion may be promoted by injecting the sewage horizon- tally through a "diffus-.@r" having several outlets. t the sc-trface the sewage forms a s-mi-discrete body floating on and displacinn' the salt wat,Dr. Within this body there i@ a radial spread from the point of its emergence under the influence of any residual head undissipated in the ,iets rising to the surface. Eddy diffusion associated with the turbulence of the ocea)i waters mixes the sewage with the flanking and underlying salt water. The concentration of sewage in the body decreases, its salinity increases, atid its boundaries gradually disappear. The ocean current provides the continuous supply of sea water into which the sewage can be mixed, and carries away the diluted sewage. A convective -70- circulation is also set up to replace sea water mixed into the sewage Figure 42 shows diagramically the circulation pattern established at a sewer outlet. The currents transport the continuously expanding and diluting cloud of sewage away from the area of its injection. Variations in current direction and strangth complicate the picture, of course. In a rapidly moving current the initial dilution may be great, whereas in a sluggish current the sewage may remain relatively concentrated. With a tidal current reversal, sewage that is born away from the sewer outlet and diluted can later be carried back over the outlet and thus receive an additional dose of pollution. Mass transport and particularly wind drag may cause the surface and submerged parts of the sewage cloud to move in different directions The wind may drive any floatables in a direction quite unlike that taken by the suspended matter and the floatables may be re- concentrated and transported in a concentrated state in a surface convergence. The continuing dispersal of the sewage is largely the result of turbulent mixing which is generated in several ways and on several scales. On the largest scale is the eddying resulting from the insta- bility of the major ocean currents. This major eddying and the orbital motion associated with the tides lead to shearing which is responsible for eddying on a smaller scale. Large-scale eddies are generated as the currents move past islands- smaller scale eddies, as they move past irregularities in the coastline or over irregularities in the bottom. Still smaller scale eddies result from the shearing of the surface waters over deeper waters, as with wind-driven currents and mass transport. Regardless of the initial scale of the eddying, -71- the larger eddies break down to smaller ones with shorter characteris- tic periods. Recordings of currents by paddle-wheel current meters (Figs. 10, 17 through 23) or by Ekman current meters (Appendix Figs. 5 and 6) always show evidences of moderate-period turbulent fluctuations of current speeds and directions. Shorter period fluctuations invariably present cannot be recorded except by instruments having rapid responses. The biochemical T)rocesses involved in the decomposition of sewage in sea water are certainly at least as complicated as the physical processes of transport and dispersal of the sewage, and can be no raore than briefly summarized here. Depending on the o.7rygen availability in the water, itself in part a function of the dilution of the sewage, either of two possible causes of decomposition may be taken. Under stagnant, anaerobic conditions the rate of decomposition is slower and the products remain objectionable on both sanitary and aesthetic grounds. Under the aerobic conditions that generally obtain where the dilution is satisfactory, the rate is higher and the products are harmless. The decomposition is accomplished mainly by the action of micro- organisms, and under aerobic condibuions, is promoted by factors favoring the growth and activity of the micro-organisms Temperature is particularly important, the rate of deco=osition being materially higher in the warm waters characteristic of Hawaii than in the cold waters of or flowing froin high latitudes. The particle size is important because with fineness of particles goes a high ratio of surface to volume. Hydrogen ion and other chemical concentrations may be influential. -72- The most important effect ol" decomposition is, of course, the reduction in concentration of pathogenic micro-organisins, notably bacteria. This is not ordinarily measured directly, bLit by concen- tration of certain index coliforms streptococci, etc. Local studie@s (Iha-, 1960) have shown that bacteria! action of the sea water Dredomi-. natdsover the effects of bacteriophages, protozoans, sedimentaticn,-or solar radiation in reducint@ numbers of sewaL-e bacteria. 8,2 Estimation of Rates of Transport Disper-sal and Bacterial Die-off Although the various processes in bacterial transport, dispersal, and die-off in the sewage overlan and influence each other, their effects cannot be estimated unless they are assumed to be somewhat separable. Conventionally, two to five separate calculations have been involved treating two separate stages as follows: 1. In.itial stage: Estimation of initial dilution and dimensions of initial field. 2. Final stage: Calculation of combined effects of eddy diffusion, advection and bacterial die-off in a steady current: calculation of effects of eddy diffusion and bacterial die-off and super- position of effects of steady or slowly varying currents; or calculation of either of the above without the bacterial die-off and superposition of the effects of bacterial die-off. For the calculation of the effects in the jet or cone from a diffuser several formulas are available, some rational and some empi- rical (for a summary see Hyperion Engineers, 1957), the most complete of which is one by Rawn, Bowerman, and Brooks (19 %). The results vary somewhat, and there is some uncertainty as to their correspondence -73- to the initial parameters required in the eddy diffusion calculation. Most significantly perhaps, the effects of the radial spread of the sewage due to its head at the surface appear never to have been inclu- ded in an analysis. The great diversity o., methods of estimation occurs in the cal- culation of diffusion effects. The basic reasons for the diversity are the following: 1. Eddy diffusion is so extremely coriiplicated a phenomenon that there is as yet no coikolete agreement even as to basic concep- tions of its mechanism. 2. (a) The eddy diffusivity is riot a constant in a particular fluid, as is its molecular diffusivity, but varies with the scale of the phenomenon being studied. (b) The relationship between diffusivity and scale may be quite complex. (c) Even for simple cases there is disagreement as to the scale law appropriate for adoption, 3. The differential equations, at best, are so complex that, in oi@der to permit their solution, assumptions and approximations must be made that render questionable the extent to which the solutions are valid. Good summaries of diffusion concepts and scale laws are given by Sch6@nfeld and Groen (1961) and Okubo (i962), a simple method of analysis is given by Brooks (1960), enO. a practical evaluation of several formulas, rational and empirical, is given by Hyperion Engi-i-leers (1957). Bacterial die-off is usually assumed to be exponential with tjxae, although other, generally more complicated, relationships have been -74- proposed (see Hyperion Engineers, 1957). However@ the appropriate exponential constant obviously must vary considerably, depending on the availability of oxygen in the water, the temperature of the water, the particle size distribution in the sewage, and other chemical and physical characteristics of the sewage. The current data, by itself or in combination with calculated diffusion effects, may be used in the following ways: 1. The estimation of the range of likely transport directions and velocities from prospective sewage release points. The distances to which the directions of trans-Dort and the velo- cities are of interest depend, of course, on the rates of dilution and bacterial die-off and the lengths to which the sewage may travel before the bacterial concentrations drop to insignificance. 2. Appraisal of the likelihood of reinjection of sewage into a dispersing sewage field due to current reversal. 3. Estimation of the general magnitude of dilution as a function of distance and direction from prospective sewage release points, using Lagrangian types of approach, such as those of Joseph and Sendner (10,58) and Hela and Voipio (1960) from the center of a patch of sewage introduced essentially instanta- neously into the current and integrating numeri6ally-to determine the effects of continuous introduction and advection. 4. Estimation of the efficiency of general flushing of bays and similar coastal areas, using the strengths of current in and out of the bays by the method discussed by Schoenfeld and -75- Groen (1961). 5. The selection of -points probably favorable for sewage release, i.e., points from which transport to shorelines of concern is very slow or infrequent. 6. Appraisal of the possibility of accumulation of sewage in current convergences. 8.3 Requirements in Coastal Current Studies for Sewage Disposal Projects Certain complications seem liable in Hawaii to render inadequate for actual design purposes the accuracy of predictions of sewage dis- persal based solely on assumed currents and either rational or empirical formulas for diffusion. Among these may be mentioned: 1. The effects of the similarities in size between the sewage clouds of interest and both tidal ellipses and coastal and bottom irregularities, which restrict the approximation of eddy and tidal effects by either pure eddy diffusion of simple scale law or pure advection. 2. The co=lications of wind-driven currents at variance with deeper currents. 3. The significant increase in thicliness of the sewage fields as the sewage is diluted. The inescapable conclusion, then, is that a thorough local inves- tigation must be made at the site of any major sewer outfall of uncer- tain effects,,or at any major planned sewer outfall. Such an investi- gation would involve the following stages: 1. Establishment of at least one and for a complicated area -76- preferably two or more current-meter stations for long-term (1 year or more) continuous operation in the area, at points to be determined on the basis of the current components and -nattern anticipated. 2. Conduction of drogue, dye, and supplementary short-term. current meter studies throughout the area, at intervals and over periods, to outline tidal and climatic effects.. correlating these with wind, waves, tide, and tidal currents. 3. Determination from general considerations, from the results of monitoring, and from estimates of dilution and estimates of bacterial die-off, the critical conditions in the area. At times rei)resentative of critical conditions determine dilution over the field by release of dye or other traces in sufficient quantities, and preferably b3@ continuous introduction, at outfall sites or prospective outfall sites. Studies of the sort outlined, to be adequate for design purposes, will be far more extensive and costly than the studies that have customarily been made in the past in Hawaii in connection with sewer outfall projects. They will be jUStif4 ed, however, by the gains from economies in sewage treatment and outfall construction that they will make possible, and by the avoidance of losses that may be incurred through restriction of shoreline uses due to health hazards if sewer outfall plans prove inadequate. 9. CONCLUSIONS AND RECOMMENDATIONS Various wastes are discharged at sea in Hawaii. Problems arise from several, especially from sewage. The following major conclusions and recommendations regarding the coastal currents of the Islands and their effects on the dispersal of sewage at sea may be listed: 1. The dispersal of the sewage in the sea is critically deter- mined by coastal currents in the vicinity of outfalls. 2. The coastal current may have several significant components: the permanent flow, tidal currents, irind-driven currents, and mass transport. At most places the tidal components predominate. 3. The tide waves move through the archipelago from north- northeast to south-southwest. As a result of the superposition of the generally west-northwest setting permanent flow, -'Uhe flood currents diverge somewhere off the northeast side of each island, swing clockwise around the southeastern shore and counterclockwise around the southwestern shore, and converge off the southwest side. The ebb currents diverge somewhere on the south side of the island, swing clockwise around the western shore and counterclockwise around the eastern shore,, and converge on the north side. Along certain north-northeastern shores the current may set almost constantly west-northwesterly, and along certain south-southeastern shores there may be almost constantly a reverse set. 4. The tidal current movements tend to be reciprocating near shore and elliptical offshore. Convergences and diveigences result over the slopes of the islands. -77- -78- 5. Irregularities in the shoreline and bottom configuration, together with inertial effects, cause considerable phase disturbances, distortion, and eddies in the current patterns. 6. Over reefs and in lagoons the major currents are generally initiated by mass transport associated with waves. 7. The wind tends to drive the surface water in the direction of the wind"s travel, which may be onshore or offshore although the currents in depth set predominantly alongshore. Wind effects predominate in the control of surface currents in protected bays. 8. Except in the irind-driven surface currents, seasonal changes appear to be of minor significance. C> 9. With the outflow of fresh sewage into salt water, an independent circulation is induced in the vicinity of the outfall. 10. Turbidity, bacterial concentrations, and dye have proved useable as tracers fcr sewage. 11. The critical conditions with regard to sewage disposal are likely to result from a combination of onshore wind-driven current and some particular tidal current direction. 12. There may be a very few sites at which an offshore set of the current is so predominant that untreated sewage may safely be introduced through outfalls of normal length. In general, however, alongshore and shoreward sets occur, especially in the surface layers due to wind action, with sufficient frequency as to make inadvisable large discharges of untreated sewage within a few miles in any direction from a shoreline intensively used for recreation or for fishing. -79- 13. The critical conditions for the Sand Island sewer on Oahu are an ebb current, perhaps prolonged by an eddy, and a kona wind. Even during trade-wind conditions, se-vrage-laden water has been traced east as far as the Kewalo entrance in about 6 hours. It must flow farther east on occasion, and the floatables, in particular, may be driven onshore. On other occasions the sewage-laden water drifts north or west. 14. The bottom deposits off Sand Island sewer do not indicate any accumulation or excessive pollution at the bottom. 15. Current velocities and mixing in depth are sufficient on open coasts generally to minimize the risk of stagnation. 16. In deep estuaries, protected bays, and harbors, however, there may be stagnant conditions. Such conditions have been noted in parts of Kaneohe Bay and in Hilo Harbor. 17. The complexities of the coastal current patterns and the status of theoretical knowledge of the eddy diffusivity associated with them are such that no calculations of sewage dispersal from general principles and assumed conditions are likely to be entirely satisfactory. 18. Intensive local investigation should be made of dispersal from major existing outfalls and planned outfalls, involving continuous monitoring by current meter at a few sites, drogue and dye studies to outline current patterns, and dye dilution studies to indicate dilution at critical periods. 10. A14NOTATED BIBLIOGRAPHY OF COASTAL CURRENTS IN HAWAII Austin,, H.A.R. & Associates. 1961. Investigation, studies, and preliminary plans with recommendations for a sewerage system within the Kailua-Kona area, Kona, Hawaii. Report to Hawaii County. Contamination in Kailua Bay now stems from cesspools near shore. Central sewer system with complete treatment and inlan-1 discharge is recommended because floatables from any ocean outfall would be driven onshore by winds. Currents are not discussed, but measure- ments by Department of Health, shown in exhibits, indicate current setting usually northwest along shore sometimes having onshore or offshore components, and sometimes reversing southeast. Austin,, H.A.R. & Associates and Law & Wilson. 1960. Engineering feasibility studies: Part I of the comprehensive plan, Ala Moana Reef. Report to Hawaii Deparment of Land and Natural Resources. Current measurements made off Ala Moana reef and in channels Novem- ber 1959 to March 1960 by 10-ft. float. Current generally set out- ward through Kewalo, and Ala Mcana channels, but may briefly set inward on a rising tide. Illustration shows currents off reef set- ting generally to northwest though sometimes in reverse direction. Most measurements were made at high or falling tide. Austin, Smith, & Associates. 1960, Engineering investigation report for improvement to Pearl Harbor sewerage system, Pearl Harbor, Oahu, Hawaii. Report to U. S. Navy Dist. Public Works Office, 14th Naval District. Current studies made in and outside Pearl Harbor entrance by surface and subsurface floats. Surface floats indicated current sets result- -81- ing from wind, away from shore in trade weather, toward shore in Kona. Subsurface floats indicated reversing current off Hickam AFB and in Pearl Harbor entrance, but with a southwestward set superimposed at the entrance which dominates at slack water. Austin, Smith, & Associates. 1961. Engineering investigation for the proposed Pearl City Sewage treat- ment plant, Ewa, Oahu, Hawaii. Report to Division of Sewers, City and County of Honolulu. Tides in Middle Loch found to correspond in place with those in ocean, though water level higher owing to fresh water discharge. Current studies indicate that floating material discharged from proposed out- fall in Middle Loch will be deposited on Middle Loch beaches, depend- ing on wind. Stream flows and tides are also influential. Studies are continuing. Austin, Smith, & Associates. 1961. North Honolulu sewerage studies. Report to Division of Sewers, City and County of Honolulu. Describes performance of Sand Island sewer outfall., constructed in 1950. Illustrations show slick fields from outfall Jln tradewind and kona conditions. Time, tide, and detailed wind conditions are not given. Austin, Smith, & Associates and Metcalf & Eddy. 1962. Report and master plan of the Pearl City Sewage Treatment Plant near Pearl City, Oahu, Hawaii. Report to Department of Public Works, City and County of Honolulu, Results of bacteriological surveys show generally progressively increasing coliform indices throughout harbor. No new current surveys reported, but results of Austin, Smith,& Associates 1962 surveys used to estimate 8- and 24-hx@ "influence areas" about proposed sewer outlet in middle Loch for various tide and wind conditions. Treatment in successively greater degrees is proposed. -83- Belt, Collins, & Associates. 1961. Hilo sewer system study. Vol. I. Hilo Bay area pollution and preliminary investigation on its abatement and other related studies. Report to Department of' Public Works, County of Hawaii. Study of physical, chemical, and bacteriological conditions in Hilo Bay in 10 .,60 showed efffect.-s of pol-Lution and st-agnation. Salinity was low) turbidity high, pH generally on acid side, DO low, BOD high, nitrates and phosphates high, Polii)tion sources were princi- pally Waiakea Mill, Flintcote wallboard plant, and sewer outfall. Water in bay is bact--rio-logically in prohibited class for bathing 33% of time, completely satisfactory only 16% of time. Muddy water patches from sugar mills fron Hakalau south show southward drift, at Laupahoehoe sometimes southward sometimes northward. Current observations in western part of bay in April 1960 and January 1961 by dye, surface, and subsur-ILace floats show reversing movements with outward trend resulting from discharge of Wailuku River. Wind effects were negligible. Tidal effects were not described but seem very important from charts provided. Belt., Collins, & Associates. 1962. Kaiale Bay small boat harbor: Preliminary engineering and feasibility study. Currents were observed on 2 mornings in the winter of 1961 by dye and various sorts of surface floats. On both days surface drift in Kaiaka Bay paralleled the wind, setting northwest on one morning, west on the other. Direct wind effect on the floats was not taken into account, Outside the bay the current set was southwesterly on one morning. Bacterial counts in the bay were high inside the bay, low outside, the oxygen content is low in the bay, indicating stagnation. Belt, Collins, & Associates. !Q62, Kaneilio Point small beat harbor, Waianae, Oahu: Preliminary engineering and feasibility study. Report to Harbors Division, Hawaii Department of Transportation. Off Kaneilio point currents, investigated by dye and floats, set consistently northerly during one day's observation (on flood tide) -84- in stormy kona weather, northerly in the morning (ebb tide) and southerly in the afternoon (after tide turn) in one day in trade weather. Bacterial analyses showed excessive pollution near the sewage outfall but generally satisfactory to doubtful levels elsewherealong the shoreline. Belt., Collins, & Associates. 1962. Waialua Bay pollution study, Haleiwa, Oahu, Hawaii. Report to Harbors Division, Hawaii Department of Transportation. Currents studied by surface and subsurface floats, dye, and drift cards. Bacteriological analysis run on samples. In trade weather on rising tide and just after high tide, current from bay sets southwest. When streams were in flood, kona wind currents were to NW just after low tide, moving to N on falling tide. During light westerlies and with heavy surf currents set toward WNW on rising tide, NNW just after high tide. Coliform counts were high at Haleiwa Beach during trade wind conditions, high generally during flood and high surf conditions. Bureau of Sanitation. 1941. Honolulu sewage disposal survey, May 1940 - September 1941. Report to Honolulu Chamber of Commerce and Territory Board of Health. Refers to float surveys of currents made in vicinity of Kewalo out- fall, 1926, described as inadequate. Currents are difficult to determine but seem to flow either in Diamond Head or &ra direction. Slicks are noted frequently on calm days to extend toward Waikiki, ,once to about 5000 feet., with small organic particles going beyond. Thorough bacterial analyses showed pollution field southeast of outfall over 17 months. Practically all monthly sample fields showed a tongue of high pollution extending southwestward from out- falls; the greatest extent being in February 1941, when there was a B.coli concentration >1000/100 ml 1 mile off Kuhio Beach and >1706/-100 ml 1 mile off the natatorium. The Ala Wai canal served as 4 an additional center of pollution. Coast and Geodetic Survey. 1963. U. S. Coast Pilot 7: Pacific Coast 9th edition4 There is a prevailing westerly drift in the vicinity of the Hawaiian Islands. Variability is believed mostly a function of wind, but -85- strong northeast currents setting against trades have been reported. The currents in the Alenuihaha Channel and around Kauai are reported to be controlled especially by the wind. Around each island currents have been reported to set generally to west or northwest, however, counter currents have been reported close inshore in some areas, as around the southern part of Hawaii. Rips have been noted near Keahole Point on Hawaii, Laau Point on Molokai, Kaena Point and Kahuku Point on Oahu. Recent observations, mostly in 1962,indicate that the currents reverse with tides in many places, even at some places where previous information suggested a non-reversing current. Tidal currents were noted specifically near Aahukona on Hawaii; Hana, Cape Hanamanioa, Lahainal and Kekaa Point on Maui; in the Kalohi Channel; Maunalua Bay and Honolulu on Oahu; Mana and Nohili on Kauai; Kamalino on Niihau, and in the Lehua Channel. Coast and Geodetic Survey. 1963. Tidal Current Tables, 1963, Pacific Coast of North America and Asia. The following tidal currents are listed in Hawaiian waters: Place Lat. Long. Max. flood Max.-,ebb Dir. Vel. Dir. Vel. Kalohi Channel 21 0021 156056, 2350 o.4 kt 700 0.5 kt Auau Channel 20053' lc6043' 700 o.6 kt 2700 0.5 kt Divi.sion of Sewers. 1951. Report on ocean current studies for Sand Island outfall sewer, Honolulu, Oahu,T. H. Drogue and current pole measurements were conducted 2 or 3 times a week in various periods of weather September 1950 to May 1951 from near the end of the Sand Island outfall. Current pole measurements indicated currents setting on the average 30 0to the right of the wind and averaging about 4% of wind velocity .with better correlation when winds were strong than otherwise. A "tide" current was men- tioned but apparently in the sense of a prevailing flow. Possibility of reversing tidal currents was not recognized. Current reversals CD were noted but ascribed to eddies or to tidal outflow from Pearl Harbor. Current at the outfall was estimated to set W,, 270,daysl E, 37 days, S, 44 days and N, 14 days out of the year. Report does not include nor illustrate data except for 16-17 May 1951. -86- Division of Sewers. 1957. A report on sewerage master plan for Kaneohe, Koolaupoko, Oahu. Report to Department of Public Works, City and County of Honolulu. Bacterial analyses in Kaneohe Bay show very low concentrations except close to shore. No current studies were made and wind and tide conditions at times of sampling are not given. Division of Sewers. 1957. A report on sewerage master plan for Waipahu, aTa, Oahu. Report to Department of PuIblic Works, City and County of Honolulu. Recommends outfalls for treated sewage in shallow water in West Loch in belief oxygen will be adequate for aerobic decomposition, and slick field will not be objectionable. Need for control of hydro- graph at outfall recognized to prevent anaerobic bottom deposits. No current measurements. Division of Sewers. 1958. Report on sewerage master plan for Aiea to Pearl City, Ewa, Oahu. Report to Department of Public Works, City and County of Honolulu. Present Aiea sewer outfall in East LochPearl Harbor at base Pearl City Peninsula. Waiawa Stream discharge counted on for dispersal from proposed outfall for sewage in Middle Loch, but current studies recommended. Helfrich, P., and Kohn, A. J. 1955. A survey to estimate the major biological effect of a dredging operation by the Lihue Plantation Company on North Kapaa Reef, Kapaa, Kauai. Report to Lihue Plantation Company. Float measurements in October and November 1955 in a variety of wave and wind conditions showed southerly currents on the North Kapaa reef resulting from mass transport by breakers onto the reef. Average values of current were about 1 ft/sec on the central portion of the reef'and abcut 1.5 ft/sec at the south edge near an inlet. -87- Herschler & Randolph. 1962. Study of pollution in Kahului Bay, Maui, Hwjaii. Report to Hawaii State Department of Health. Sewage is discharged to bay through Kahului outfall east of' Kahului Harbor and Wailuku outfall west of harbor. Additional pollution reaches bay through Iao and Kalialinui Streams. Currents were measured with surfaCe and subsurface drogubs, lath floats, drift bottles, drift cards, and dye. All measurements were made during the day during trade wind weather. Drogues, especially', were observed to be affected directly by the wind and almost all apparent sets, both inside and outside harbor, were toward west or southwest parallel to the wind. Dye studies showed tidal currents reversing near harbor mouth and a possible eddy near Wailuku outfall, but otherwise westward drift outside harbor, turning to northwest off Iao Stream mouth; but no tidal reversal. Upwelling was noted out- side the east breakwater on a, rising tide. Chemical sampling showed generally high DO and low BOD except, in the vicinity of the Kahului outfall. Chlorides were in general low at the surface at the southwest shore of the harbor and increased toward the harbor mouth and in depth. Bacteriological sampling showed a high coli- form field at the surface outside the breakwaters .7 but low concen- tration generally at the surface elsewhere. Illustrations show that in the harbor coliform the concentrations were consistently greater at depth than@at the surface. In the vicinity of the Wailuku outfall the pollution field seems from'an illustration to drift southeastward at low tide and northward at high tide. A new Kahului outfall to deeper water is recommended. Holmes'& Narver,.Inc. 1957. Report and master plan of sewerage facility for Kailua, Koolaupoko, Oahu. Report to City and County of Honolulu. Currents outside reefs in Kailua Bay are reported to parallel shore, though direction is not indicated. The currents inside the reefs are reported to be only wind-generated and weak. Oxygen concentra- tions are hign. No details of times or conditions of observation are given. A sewage treatment plant on Mokapu peninsula, a tempor- ary outfall to Nuupia Pondand an eventual outfall to Kailua Bay are recommended. -88- Holmes & Narver and Belt, Collins, & Associates. 1959. Kailua ocean outfall sewer., ocean portion. Kailua sewage treatment plant, Kailua, Koolaupoko, Oahu, Hawaii. Report to Department of Public Works,, City and County of Honolulu. Report on oceanographic environment of proposed Kailua sewer outfall at base of Mokapu peninsula based on 12-months observations. Current observations made with dye, surface floatsand subsurface drogues. Wind conditions and tide during period of observations illustrated, but not in such a way that changes can be correlated with current changes. Conclusions are drawn that surface currents are wind driven, sometimes slower, sometimes faster than Eckman's theory indicates, but usually trending to the right of the downwind direction, in accor- dance with theory. Subsurface currents, however, move generally to the north and never to the south, in spite of winds generally from the north. Tide effects are not discussed and are not apparent in charts. Kailua Bay is now unpolluted except at the outlet of the Kawainui Canal. Chemistry is normal except for lower salinity, higher nitrogen, and lower oxygen near the canal outlet. Dilution and bac- terial die-off at the proposed sewer outlet were checked with injected mixtures of dye, radioactive carbonate, and sewage. Dilution gener- ally reduced chemical concentrations within 90 minutes to 0.1 to 0.3 of concentration 5 minutes after injection. Bacterial die-off in the same time reduced concentrations to 1/1000 to 1/100, even allow- ing for dilution. The outfall site is judged satisfactory. Holmes & Narver and Belt., Collins, & Associates.. 1959. Nuupia Pond outfall study. Kailua sewage treatment plant, Kailua, Koolaupoko, Oahu. Report to Department of Public Works, City and County of Honolulu. Investigation of Nuupia Pond (shallow walled-off arm of Kaneohe Bay) as a potential temporary outfall site for the Kailua sewer system. Currents in the pond were found to be wind driven. Aeration and mixing are sufficient to allow- -treated sewage to be discharged into the pond as an interim measure. Hyperion Engineers. 1957. Ocean outfall design. Brooks T (coefficient of time required for 90% bacterial die-off) and Con-ways K (log dilution ratio/distance) are estimated from 1952 survey of pollution from Ala Moana and Ward Avenue outfalls -89- and estimated or assumed values. Assumptions are: initial dilutions of 8 for Ala Moana, 20 for Ward Avenue; initial concentration of 430,000 coli-forms/ml in the boils, field depth 3 to 4 ft and width 1000 ft, 1-1@7tward current of 0.7 ft/sec., initial eddy aiffusivity of 3.68 ft 3 hr-1. T ranged from 0.21 hr at 1700 ft to_@'-05 br L at 12,000 ft; K from 21 x 10-4/ft at 1700 ft to 4.7 x 10 /ft at 12,1000 ft. The values of T are particularly low and those of K particularly high as compared with East and West Coast experience. The increase in T and decrease in K with distance are generally found, although there are supposed to be ccnstants. Iha, T. H. 196o. Survival of sewage bacteria in the sea. M.S. Thesis, University of Hawaii. Review of previous work shows bacterial concentrations in polluted sea water always lower than explicable by dilution alone. Bacterial disappearance attributed variously to bactericidal agents in sea water, bacteriophages, protozoans, adsorption and sedimentation, solar radiation. Various bacteria found differentially resistant. Previous work all either done in laboratory or with dialysis tubes and laboratory cultures in sea. Present experiment introduced radio- active sewage in Kailua Bay. Dilution measured by decrease in radioactivity. Concentrations of both coliforms and enterococci, corrected for dilution, showed reduction of 99.99 percent in 30 min- utes. Sedimentation was insignificant and bactericidal action judged predominant. Enterococci survival was higher than coliform. Laboratory studies confirmed insignificance'of sedimentation. Longer bacterial survival in laboratory considered due to higher ratio- of solid surfaces to volume in laboratory. Effects of temperature variation were found insignificant. Storage of samples might account for 101;,Io at most of bacterial reduction in dilute samples. Industrial Waste Disposal Study Coimission. 1955. Report of Industrial Waste Disposal Study Commission to 28th Legislature, Territory of Hawaii. Tabulation of industrial waste disposals and reports from concerns and agencies disposing of wastes or interested in results. Board of Agriculture and Forestry and Tuna Boat Owner's Assn. reported frequent oxygen deficiency in Honolulu and pollution in West Loch, Pearl Harbor on Oahu. Damage to inshore fisheries on Kauai, reduction in bait fish production in Hilo Harbor and interference with shore recreation and fishing along liamakua Coast on Ha-vraii, interference with shore recreation near Iao Stream mouth on Maui. -go- Department of Health reported -odor problems in Hilo Bay, reduction in problems on Maui. American Factors reported that at the outfall for muddy water from Lihue Mill on Kauai current sets usually to south, though sometimes to the north in kona weather. Keller, A. R., S. W. Tay, & G. M. Collins. 1920. Preliminary report on proposed sewer extensions in the Waikiki and Kali4i Districts; ai-so alleviation of the nuisance of Nuuanu Stream, Report to Mayor and Board of Supervisors, City and County of Honolulu, Tidal and stream-flow flushing is insufficient to overcome pollution and stagnation caused by overflows from the sanitary sewer. Though no current measurements appear to have been made at Waikiki tidal currents are reported such that sewage discharged offshore might be carried inshore. No outfall closer to Waikiki than that at Kakaako is recommended. Float observations in Kalihi channel indicate that prevailing current will carry sewage seaward from a proposed new outfall at Kalihi. Ultimately this sewage, that from the old Kalihi outfall and from Fort Shafter,will have to be connected to a central pumping plant discharging over the reef. Lublin, 1* Gaughey, & Associates. 1962. Plan of development for Hana Harbor. Report to Hawaii State Depattment of Transportation. Tidal currents are reported of relatively low velocity in Hana Harbor except in vicinity of existing wharf and Puukii Islandi, Direction of current not given. No details as to time of observation nor conditions pertaining at time. Lublin, McGauhey, & Associates. 1962. Plan of development for sampan harbor, Wailoa River, Hilo, Hawaii. Report to Hawaii Department of Transportation. Wailoa River peak discharge of 1000 ft-/sec (1.3 ft/sec) can be expected annually. Maximum tidal current 1.0 ft/sec on spring ebb. _91- Marine Advisers, Inc. 1961-1962. Oceanographic investigation in connection with proposed Waimanalo outfall. Report made to R.M. Towill. Corporation-Engineers. Set of charts of the Waimanalo Bay area of data taken on 16 differ- ent days between September 25, 1961 and October 31, 1962. Fifteen charts show drogue tracks vs tides and wind conditions on as many days; nine charts show temperature and salinity; and nine charts show dissolved oxygen concentration and water density for as many days. Three charts show bacterial analysis on four different days: standard plate count, coliform count, and enterococci count. Three charts show nitrates and phosphates and three charts show biochemical oxygen demands and pH for as many days. One chart shows suspended solids on one day. Currents were found to reverse, but do not follow any simple pattern. On two days drogues released in the bay drifted around Makapuu. Point and were picked up off Hanauma Bay. On one of these days there was a slight kona wind, and on the other day there was no wind. In general the surface drogues showed a definite tendency to go down wind, with the deep drogues (depth not known) showing a tendency to follow the depth contours. [Report text not seen.) Metcalf & Eddy. 1944. Report to Honolulu Sewerage Committee upon sewerage and sewerage disposal, vols. I and II. Boston. Comprehensive report on Honolulu sewerage problems. Discusses history of sewer system and outfalls. Reports observations April- June 1944 o.n slick field, sewage solids, and bacteria from Kewalo sewer outfalls; also Tay's observations in December 1940-January 1941 (Bureau of Sanitation, 1941). Concludes that under trade-wind conditions sewage moves entirely toward west from Kewalo, though easterly movement was found by Tay in winter. No details of times and tide conditions at times of observation, except for two days in July 1944 when milk bottle caps traced from Kewalo outlet, moving west on one day and north and west on second, with wind from south. Concludes that sewage should be led to Sand Island., and subjected there to short-period sedimentation. Public Health Service. 1963. Municipal and industrial waste facilities, 1962 inventory, Hawaii. U. S. Department of Health, Education, and Welfare. Tabulation of municipal and industrial waste facilities for all of -92- the islands, with notes on type of waste, treatment, etc. and reference to health problems resulting. No information on currents. Sunn, Low, Tom, & Hara. 1962. Report on oceanographic survey and study to sewage disposal for WaianaeY Oahu. Report to Department Public Works, City and County of Honolulu. Bacteriological analyses showed Waianae beaches to be generally Class A except in vicinity exi St4 ng Kaneilio Point outfall. High coliform counts were found more than 1000 feet from this outfall. Dissolved oxygen was generally high except near outfall and in a sometimes-isolated stream mouth. BOD phosphates. and nitrates were generally low. Salinity was generally reduced from normal but salinity profiles were inconsistent. Transparency was exceptionally high. The depth to the thermocline was about 300 feet in winter, 150 feet in summer. Current studies extended a year and included two 24-hr studies. Drift cards, drift bottles, drogues and dye were used. Current-meter studies were unsuccess- ful. Currents were correlated with tides as locally recorded. Some drift cards and drift bottles released off Waianae beaches were found on shores to southeast within several tenths of a mile in a few hours, and as far as &-a Beach in 8 days, and Keehi Lagoon in 27 days. Others were found on shores to the northwest within several tenths of a mile in a few hours, as far as Kaena Point in 7 days, and on Kauai and Niihau in 10 to 23 days. Drogue studies indicated currents induced largely by tides, with movements preponderantly oscillatory parallel to shore. Off points, flood current sets southeast, ebb current northwest. Eddies are set up by irregular bottom topography, as at Pokai Bay. Generalized flood and ebb patterns were portrayed. Trade winds tended to deflect drogues seaward; kona winds landward. Preliminary dilution was calculated by Rawn-Palmer formula and subsequent dilution and die- off by Pomeroy formula for proposed outfalls. Primary sewage treatment with a 2400-foot outfall was recommended. Sunn, Low, Tom, & Hara. 1962. Report on sewage disposal for the Hawaii-Kai development. [Report text not seen.] Illustrations of results of three cruises show semi-diurnal tidal currents measured by drogues, setting north- east with ebb (velocities to 89 ft/min), southwest with flood (velocities to 107 ft/min). Change from flood to ebb. Drift cards and bottles released in area were picked up at Hanauma Bay (2 days min.), Makapuu Beach (2 days), Kailua Beach (2 days), Kaneohe Bay (2 days), Maunalua Bay (14 days), Black Point (5 days), Honolulu Harbor (16 days), wailua, Kauai (23 days). -93- Tippets, Abbett, McCarthy, & Stratton. 1961. Development plan, deepwater port at Barbers Point, Oahu, Hawaii. Report to Estate of James Campbell. Tidal currents are reported generally weak. A westward drift is said to prevail. Current measurements at Erown's Camp indicate variability in direction and velocity range from 0 to 0.5 kts, occasionally to 2 k-ts. 11. REFERENCES Anonymous. 19163. Oceanic eddies southwest of Oahu surveyed. National Oceanographic Data Center Newsletter 8-63: 6-7. Austin, H. A. R. & Associates, Ltd. 196-1. Report to the County of Hawaii covering -the investigation, studies, and preliminary plans with recommendations for a sewerage system within the Kailua-Kona Area, Kona., Hawaii. 27 Pp. Austin,, H. A. R. & Associates and Law & Wilson. 1960. Engineering feasi- bility studies: Part I of -the comprehensive plan, Ala Moana Reef. Report to Hawaii Department of Land and Netxral Resources. 83 PP. Austin, Smith, & Associates, Inc. 1960. Engineering investigation report for improvement to Pearl Harbor sewerage system, Pearl Harbor, Hawaii. Rept.' to U. S. Navy Dist. Public Works Office, 14th Naval Dist. Austin, Smith, & Associate, Inc. 1961a. Engineering investigation for the proposed Pearl City Sewage treatment plant, Ewa, Oahu, Hawaii. Report to Division of Sewers, City and County of Honolulu. Austin, Smith, & Associates, Inc. 1961b. North Honolulu Sewerage Studies, November, 1961. Prepared for the Division of Sewers, City and County of Honolulu. 99 pp. Austin, Smith, & Associates, Inc. 1961c. Report [to Division of Sewers, Department of Public Works, City and County of Honolulu] covering research, topographic and hydrographic surveys, current studies and utility investigations in connection with the preparation of -95- -96- the master plan and report for the proposed Pearl City sewage treatment plant, Ewa, Oahu, Hawaii. About 20 pp. Austin., Smith, & Associates and Metcalf & Eddy. 1962. Report and master plan of the Pearl City Sewage Treatment Plant near Pearl City, Hawaii. Report to Department of Public WorksY City and County of Honolulu. Avery, Don E., Doak C. Cox, and Taivo Laevastu. 1963. Currents aroundthe Hawaiian Islands. H.I.G. Report No. 26. 40 pp. Barkley, R. A. (Unpub. ms.) Oceanographic studies in the Cantral Pacific. Belt, Collins, & Associates, Ltd. 1961a. Hilo sewer system study. Prepared for Department of Public Works. 9L,,- pp. Belt, Collins, & Associates, Ltd. 1961b. South Honolulu S'ewerage study. Prepared for the City and County of Honolulu. 250 pp. Belt, Collins, & Associates, Ltd. 1962a. Kaiaka Bay small boat harbor preliminary eng7-neering and feasibility study. Prepared for Harbors Division, Depatment of 'Transportation. -"j):)' pp. Belt., Collins, & Associates, Ltd. 1962b. Kaneilio Point small boat harbor; preliminary engineering and feasibility study. Prepared for Harbors Division, Department of Transportation. 33 pp. Belt, Collins, & Associates, Ltd. 1962c. Waialua Bay pollution study, Haleiwa, Oahu. Report to Harbors Division, Department of Transportati on. Brooks, N. H. 1960. Diffusion of sewage effluent in.an ocean current. In Pearson, E. H., ed., Proc. ist Intl. Conf. on Waste Disposal in the Marine Environment. Pergamon. p. 246-267. -97- Brown, R. P. (ms.) Atlas of surface drift charts for the central North Pacific Ocean (100 to 300N, 1500 to 1800W). Bureau of Sanitation. 1941. Honolulu sewage disposal survey, May 1940- September 1941. Report to Honolulu Chamber of Commerce and Terr. Hawaii Board of Health. Chick, Harriet. 1908. Investigation of the laws of disinfection. Hygiene 8: 655. Coast and Geodetic Survey. 1962. Tide Tables. West Coast North and South America including the Hawaiian Islands. 22)-, pp. Coast and Geodetic Survey. 1963a. U. S. Coast Pilot 7: Pacific Coast 9th ed. Coast and Geodetic Survey. 1963b. Tidal Current Tables, 1963, Pacific Coast of North America and Asia. Division of Sewers. 1951. Report on ocean current studies for Sand Island outfall sewer, Honolulu, Oahu, T.H. 11 pp. (Mimeo.) Division of Sewers, 1957a. A report on sewerage master plan for Kaneohe, Koolaupoko, Oahu. Department of Public Works, City and County of Honolulu. Division of Sewers. 1957b. A report on sewerage master plan for Waipahu, Ewa, Oahu. Department of Public Works, City and County of Honolulu. 33 PP. Division of Sewers. 1958. A report on sewerage master plan for Aiea to Pearl City, Ewa, Oahu. Department of Public Works, City and County of Honolulu. 33 PP. Fleming, R. H., and D. Heggarty. 1962. Recovery of drift bottles reJ,--ased in the southeastern Chukchi Sea and northern Bering Sea. Univ. -98- Washington, Department Oceanography, Tech. Rept. No. 70. Hela, I., and A. Voipio. 1960. Tracer dyes as means of studying turbulent diffusion in the sea. Ann. Acad. Sci. Finnica A (6) 69: 1-9. Helfrich, P., and A. J. Kohn. 1955. A survey to estimate the major biological effects of a dredging ope@ration by the Lihue Plantation Co. Ltd., on north Kapaa Reef, Kapaa, Kauai. (Ms. report.) Herschler & Randolph. 1962. Study of pollution in Kahului Bay, Maui, Hawaii. Report to the Department of Health, State of Hawaii. 115 PP; Holmes & Narver,, Inc. 1957. Report and master plan of sewerage facility for Kailua, Koolaupoko, Oahu. Report to City and County of Honolulu. Holmes & Narver, Inc. and Belt, Collins@ & Associates, Ltd. 1959a. Kailua ocean outfall sewer, ocean portion. Kailua sewage treatment plant Kailua, Koolaupoko, Oahu, Hawaii. Report to Department of Public Works, City and County of Honolulu. 125 PP. Holmes & Narver, Inc. and Belt, Collins, & Associates, Ltd. 1959b. Nuupia Pond outfall--study Kailua sewage treatment plant Kailua, Koolau- poko, Oahu, T.H. Report to Department of Public Works, City and County of Honolulu. 26 pp. Hydrographic Office. 1947. Atlas of surface currents, northeastern Pacific Ocean. H.O. Pub. No. 570. Hydrographic Office. 1950. Atlas of surface currents, northwestern Pacific Ocean. H.O. Pub. No. 569. Hyperion Engineers (a joint venture). 1957. Ocean outfall design. Final report to City of Los Angeles. -99- Iha, T. H. 1960. Survival of se-mage bacteria in the sea. M.S. Thesis, Univ. of Hawaii. Inman, D. L., W. R. Gayman, and D. C. Cox. 1963. Littoral sedimentary processes on Kauai, a subtropical high island. Pacific Science 17(l): lo6-130. Joseph, F., and H. Sendner. 1958. Uber die horizontale diffusion in Meere. Dtsch. Hydrogr. Zeitschr. 11(2). Keller, A. R., S. W. Tay, & G. M. Collins. 1920. Preliminary report on proposed sewer extensions in the Waikiki and Kalihi Districts; also alleviation of the nuisance of Nuuanu Stream. Report to Mayor and Board of Supervisors, City and County of Honolulu. Ketchum, B. H., C. L. Carey, and M. Briggs. 1949. Preliminary studies on the @vidbility and disposal of bacteria in the sea. Limnology, water supply, and waste disposal. Amer. Adv. Sci. La Fond, Eugene. 1962. Water motions associated with internal waves. In Proc. National Coastal and Shallow Water Research Conference, ist, Oct. 1961, Baltimore, Los Angeles, and Tallahassee. P. 530. (Ms.) Laevastu, T., H. Zeitlin and M. K. Song./ Investigation of the biological oxygen demand (BOD) of sea water and oxygen production by phyto- plankton under different laboratory conditions. Marine Advisers, Inc. 1961-1962. Oceanographic investigation in connection with the proposed Waimanalo outfall. Report made to R. W. Towill Corporation --Engineers. Masch, F. D. 1961. Mixing and dispersive action of wind and waves. Univ. -100- Calif., Berkeley, Inst. Eng. Res., Tech. Rept. Ser. 138, Issue 6. (Mimeo.) Metcalf & Eddy. 1944. Sewerage and sewage disposal, volumes I and II, December 11, 1944. Report to Honolulu Sewerage Committee. 227 PP. Neumann, H. 1960. Uber die bearbeitung von strombeobachtungen von mehr als funfzehn tage dauer. Dtsch. Hydrogr. Zeitschr. 13(5): 209-225. Okubo, Akira. 1962. A review of theoretical models of turbulent diffusion in the sea. The Johns Hopkins Univ., Chesapeake Bay Institute, Tech. Rept. 30. 105 PP. Public Health Service. 1963. Municipal and industrial waste facilities; 1962 inventory, Hawaii. U. S. Dept of Health, Education, and Welfare. Rawn, A. M., F. R. Bowerman, and N. H. Brooks. 1959. Diffusers for disposal of sewage in sea water. Amer. Soc. Civil Engrs., Sanitary Eng. Div. 86 (SA 2): 65-105. SchQnfeld, J. C., and P. Groen. 1961. Mixing and exchange processes. In Radioactive Waste Disposal Into the Sea. Internatl. Atomic Energy Agency, Safety Ser. 5: lOO-l32. Sunn, Low, Tom, & Hara, Inc. 1962a. Report on oceanographic survey and study relative to sewage disposal for Waianae, Oahu. Report to City and County of Honolulu. 06 pp. Sunn, Low, Tom, & Hara, Inc. 1962b. Report on sewage disposal for the Hawaii Kai Development, Hawaii Kai Community Services Company. 25 PP. -101- Tippets, Abbett, McCarthy, & Stratton. 1961. Development plan, deepwater port at Barber's Point, Oahu, Hawaii. Rept. to Estate of James Campbell. Tomczak, G. 1962. Recent investigations with drift cards for determining the influence of the wind on surface current. ICES CM 1962 Hydrogr. Comm. No. 66. Vaccaro, R. F., M. P. Briggs, C. L. Carey, and B. H. Ketchum. 1950. Viability of Escherichia coli in sea i-rater. Amer. J. Public Health. 40: 1257-1265. DATE DUE GAYLORDINo. 2333 PRINTED IN UA 366 141073256 68 -OAL4W -4;@4,