Bo Wa SIS 4 See ee : Coast. Erg: MR 80-1 (I) (pd A082 S29) Ecological Evaluation of a Beach Nourishment Project at Hallandale (Broward County), Florida Py leat Volume | Evaluation of Fish Populations Adjacent to Borrow Areas of Beach Nourishment Project, Hallandale (Broward County), Florida by Walter R. Courtenay, Jr., Ben C. Hartig, and Gerard R. Loisel MISCELLANEOUS REPORT NO. 80-1 (I) FEBRUARY 1980 WHOL DOCUMENT } COLLECTION / Se a Approved for public release; distribution unlimited. Prepared for U.S. ARMY, CORPS OF ENGINEERS COASTAL ENGINEERING Be RESEARCH CENTER pret Kingman Building Po Fort Belvoir, Va. 22060 ooHwa0 Reprint or republication of any of this material shall give appropriate credit to the U.S. Army Coastal Engineering Research Center. Limited free distribution within the United States of single copies of this publication has been made by this Center. Additional copies are available from: National Technical Information Service ATTN: Operations Division 5285 Port Royal Road Springfield, Virginia 22161 The findings in this report are not to be construed as an official Department of the Army position unless so designated by other authorized documents. Wu TC 0 0301 0089843 3 UNCLASSTFIED SECURITY CLASSIFICATION OF THIS PAGE (When Data Entered) REPORT DOCUMENTATION PAGE 1. REPORT NUMBER 2. GOVT ACCESSION NO. it 40-1 (ol ie 4. TITLE (and Subtitle) ECOLOGICAL EVALUATION OF A BEACH NOURISHMENT PROJECT AT HALLANDALE (BROWARD CQUNTY), FLORIDA Volume I. Evaluation of Fish Populations Adjacent to Borrow Areas of Beach Nourishment Project, Hallandale (Broward County), Florida READ INSTRUCTIONS BEFORE COMPLETING FORM 5. TYPE OF REPORT & PERIOD COVERED Miscellaneous Report 6. PERFORMING ORG. REPORT NUMBER 8. CONTRACT OR GRANT NUMBER(s) 7. AUTHOR(s) Walter R. Courtenay, Jr. Ben C. Hartig Gerard R. Loisel 9. PERFORMING ORGANIZATION NAME AND ADDRESS a -Department of Biological Sciences > Clorida Atlantic Universi: De, — Boca Raton, Florida 33431 11. CONTROLLING OFFICE NAME AND ADDRESS Department of the Army Coastal Engineering Research Center Kingman Building, Fort Belvoir, Virginia 22060 14. MONITORING AGENCY NAME & ADDRESS(if different from Controlling Office) DACW72-78-M-0769 10. PROGRAM ELEMENT, PROJECT, TASK AREA & WORK UNIT NUMBERS G31266 12. REPORT DATE February 1980 13. NUMBER OF PAGES 2xF 2O 0: 15. SECURITY CLASS. (of this report) UNCLASSIFIED 15a. DECLASSIFICATION/ DOWNGRADING SCHEDULE 16. DISTRIBUTION STATEMENT (of this Report) Approved for public release; distribution unlimited. DISTRIBUTION STATEMENT (of the abstract entered in Block 20, if different from Report) . SUPPLEMENTARY NOTES . KEY WORDS (Continue on reverse side if necessary and identify by block number) Beach nourishment Fish Borrow areas Hallandale, Florida Coral om reverse side if necessary and identify by block number) ABSTRACT (Continue A study of the fish populations within the surf zone and over the first and second reefs off Hallandale (Broward County), Florida, was conducted, 7 years following dredging for a beach restoration project. This study utilized an observational and recording technique adapted from Jones and Thompson (1978). The data were compared with those of an earlier study conducted in 1971-72. (continued) DD , een 1473 ~—s EprTion OF’? Nov 65 1S OBSOLETE UNCLASSTETED ini —————= SECURITY CLASSIFICATION OF THIS PAGE (When Data Entered) UNCLASSIFIED SECURITY CLASSIFICATION OF THIS PAGE(When Data Entered) In the 1971-72 study, conducted during and subsequent to dredging activities, 42 species of fishes belonging to 24 families were found. The present study revealed the presence of 114 species of fishes belonging to 36 families. The dusky jawfish (Opistognathus whttehurstt), common along the first reef platform in 1971-72, was found to be absent. The absence of this fish is attributed to an alteration of the substrate on the first reef by incursion of fine sediments. Damage to the second reef observed during 1971-72 was not evident during this study. 2 UNCLASSIFIED SECURITY CLASSIFICATION OF THIS PAGE(When Data Entered) PREFACE This report (Vol. I) is published to provide coastal engineers the first comprehensive study of the impact of beach nourishment and offshore borrowing on nearshore and coral reef fish populations. In Volume II, benthic communities adjacent a restored beach are analyzed and compared to similar nearby communities. Both studies were con- ducted at Hallandale (Broward County), Florida. The work was carried out under the coastal ecology research program at the U.S. Army Coastal Engineering Research Center (CERC). This report was prepared by Dr. W.R. Courtenay, Jr., Professor of Zoology, B.C. Hartig, a candidate for the Master of Science degree, and G.R. Loisel who recently completed the Master of Science in Teach- ing degree, Florida Atlantic University, Boca Raton, Florida, under CERC Contract No. DACW72-78-M-0769. The authors express their appreciation to A. Abel and W.N. Watkins for photographic support, J.L. Lane for typing support, and J. Marcusky and T. McKay for the use of boats. Special thanks are due L.M. Stanaland for her assistance on this study from September to December 1978. R.M. Yancey was the contract monitor, under the general super- vision of E.J. Pullen, Chief, Coastal Ecology Branch, CERC. Comments on this publication are invited. Approved for publication in accordance with Public Law 166, 79th Congress, approved 31 July 1945, as supplemented by Public Law 172, 88th Congress, approved 7 November 1963. Colonel, Corps of Engineers Commander and Director CONTENTS Page CONVERSION FACTORS, U.S. CUSTOMARY TO METRIC (SI). .... ee I JON AU ODOR ITO 3 ohio Moa 6 bg vo Molo le 0 16 1G to 0 6) v0 pi’ 00 7 iil MATERUAE SR METHOD Sa wAND PROCEDURES my am sill anil nmr nine 8 IIE DFSCRIUPMION Ol SMUD NBA. oo G8 6 0 6 60 6 6 0 6 0 8 6 g) IV RESULT Siar i vctely te el iment ventiol eenccetven hay enter) colunsiMmon tenia at meen ae) entre tmE LE) V DUS CUSSTONPAND BEON GLE W SHON Sia recneefarrsuireiiitey talent cin op sere ys ea VI RECOMMENDATIONS 2554 eum cet ae ceNeliren era cay Nanton ret emiers make - per ieee LITERATURE: S@IsDED) (ov feo wtiet re Neo te tatiagene ertaroy oun ray coments A out ek Ure tenn man] APPENDIX] DISHES (ORS THE sHATIEAND AGE RARE AY mules annem.) ie naie lettre star tir al air aaaeCS, FIGURES 1 Location of study area and plan of southeastern Florida shelf. morphollogiya vnc, (Sal'sa vores! cco cot lela epieedieeus owl esue me ey peel ai meatier al a a) 2.) Shelt morphollogyaotes Hallandale ee) steve er aol snenme tnt eute Arey ye a ate na Sy Higher) profile vareamoty files mee tip laletor1l ae nee A Outside ledgeyareasot secondexreets pillat-cormn reer mn etme nn nn ee 5. Lop ef Second’ reefy platform.) ay ce elect oad nena kee meee ae CONVERSION FACTORS, U.S. CUSTOMARY TO METRIC (SI) UNITS OF MEASUREMENT U.S. customary units of measurement used in this report can be converted to metric (SI) units as follows: Multiply by To obtain inches 25.4 millimeters oo! centimeters square inches 6.452 square centimeters cubic inches 16.39 cubic centimeters feet 30.48 centimeters 0.3048 meters square feet 0.0929 square meters cubic feet 0.0283 cubic meters yards 0.9144 meters Square yards 0.836 square meters cubic yards 0.7646 cubic meters miles 1.6093 kilometers square miles 259.0 hectares knots OSS kilometers per hour acres 0.4047 hectares foot-pounds HSS O'S newton meters millibars 1.0197 x 1073 kilograms per square centimeter ounces 28.35 grams pounds 453.6 grams 0.4536 kilograms ton, long 1.0160 metric tons ton, short 0.9072 metric tons degrees (angle) 0.01745 radians Fahrenheit degrees 5/9 Celsius degrees or Kelvins! 1To obtain Celsius (C) temperature readings from Fahrenheit (F) readings, MSseiekonmmullialy Chm (5/9) (hase) To obtain Kelvin (K) readings, use formula: K = (5/9) (F -32) + 273.15. EVALUATION OF FISH POPULATIONS ADJACENT TO BORROW AREAS OF BEACH NOURISHMENT PROJECT, HALLANDALE (BROWARD COUNTY) , FLORIDA by Walter R. Courtenay, Jr. Ben C. Harttg and Gerard R. Lotselt I. INTRODUCTION For several years, a significant number of beaches along the southeastern coast of Florida have undergone severe erosion (U.S. Army Engineer District, Jacksonville, 1965). A major beach nourishment and restoration program in this area, the Broward County Beach Erosion Control Project, was authorized by the Rivers and Harbors Act of 27 October 1965. One segment of the project, Hallandale in southeastern Broward County, was nourished with offshore sand between 21 July and 21 September 1971. Courtenay, et al. (1973, 1974) noted damage by dredging activities off Hallandale to an extensive area of offshore patch reefs extending out to and including the offshore edge of the second reef platform. Damage was reported as being most evident within a radius of 400 to 800 meters of the borrow area; however, a reevaluation of data indicates the area of damage was between 130 and 220 meters of the nearest borrow area, encompassing an area of approximately 2.5 square kilometers. The reef damage was attributed to rehandling of fill material, to the type of dredging equipment used, and to a piece of dredging equipment that overturned in a storm (Courtenay, et al., 1973, 1974). Algae and permanently attached bivalve mollusks were killed by burial. Soft corals were not affected but hard corals showed substantial damage. Motile species such as lobsters, crabs, shrimps, and fishes apparently left the area during dredging but began to reappear within 4 months following cessation of dredging activities. This study assesses the status of fish populations within the borrow areas, in areas of reef damage, and adjacent areas within approximately 0.5 kilometer from the borrow areas off Hallandale, 7 years after dredging. The data were compared with those obtained during a previous study (Courtenay, et al., 1974). Although the assessment techniques used in the 1971-72 study differ from those used during this project, valid comparisons were made. The 1971-72 study was conducted using the ichthyocide rotenone as the primary sampling technique. While rotenone will kill most fishes and many of the more cryptic or secretive species, it is not a quantitative sampling method; several larger fishes, especially sharks, rays, and some pelagic and benthic bony fishes will actively avoid rotenone. The present study utilized an observational and recording technique adapted from Jones and Thompson (1978). The need for replicate series sampling precluded the use of ichthyocides. Jones and Thompson compared results of their technique in reefs at John Pennekamp State Park off Key Largo (Monroe County), Florida with Starck's (1968) study using rotenone at Alligator Reef (Monroe County), Florida. Their study showed that the observational and recording technique of eight replicates per station accounted for 93.5 percent of the more commonly occurring suprabenthic (above- bottom) fishes on Florida reefs. However, the technique did not account for the majority of cryptic species. . II. MATERIALS, METHODS, AND PROCEDURES The assessment of fish populations adjacent to borrow areas off Hallandale began in September 1978 and was completed in March 1979. Fishes were observed and recorded by a technique adapted from Jones and Thompson (1978). The procedure required a pair of observers, equipped with scuba, a watch, and an underwater writing slate. The divers were allowed 50 minutes to locate and record as many fish species as possible within the confines of the study area. There were no specific transects. The 50-minute diving time was subdivided into five 10- minute periods. Species were recorded only once and tallied in the specific 10-minute interval in which they were first seen. Fishes occurring within the first 10-minute interval were given a score of five, those within the second interval a four, etc., to the fifth interval for a score of one. The assumption is that the species occurring within the earliest time intervals are likely to be the most abundant. Each diver's species tally at the end of the 50-minute dive was considered as one run. There were 10 runs or replicates made in the surf zone, 12 runs on the first reef, and 12 runs on the second reef. The number of runs was considered sufficient in a particular area when no new species were observed in two consecutive dives. The scores for each species from each run were summed and averaged. The values ranged from 0.08 to 5.0. These figures were then plotted on a graph against their frequency of occurrence. Cutoff points were then assigned five abundance ratings: species with values ranging from 0.08 to 0.42 were considered rare (R); 0.50 to 1.58, occasional (0); 1.67 to 2.75, frequent (F); and 2.83 to 3.92, common (C). A species with a value ranging from 4.0 to 5.0 was given an abundant (A) rating. These ratings were then compared with those of Courtenay, et al. (1974). Lists of fish species observed are given in the Appendix. They are cited by families in a sequence after Bailey, et al. (1970). Starck's (1968) method of denoting primary reef species (P) and secondary reef species (S) has been followed. Primary reef spectes are species characteristically associated with the reefs. Secondary reef spectes are species which, though normal residents of reef areas, are more ubiqitous in their selection and utilization of habitats. Seine and hand nets, underwater photography, and the anesthetic quinaldine were used to aid in the collection and identi- fication of some species. III. DESCRIPTION OF THE STUDY AREA Hallandale, located in southeastern Broward County (Fig. 1), is bordered by a single rock groin to the north and a series of apartment or condominium buildings at the southern limit. Off Hallandale, three areas or zones of study were used to investigate the long-term effects of beach nourishment on the fishes of the area: the surf zone, the first reef, and the outer or second reef (Gitce2 ye The surf zone is an area of sandy bottom, extending from the beach to approximately 10 meters offshore. Beyond the surf zone is an area of sandy bottom that extends an additional 40 meters out to the inshore edge of the first reef. The substrate throughout this area appears to consist of dredged fill subsequently eroded from the beach by wave action. The water in this area is usually milk-colored due to wave action on fine silts. Fishes inhabiting the surf zone are generally small and characteristic of sandy areas. The water depth in the surf zone reaches 1 meter. The first reef has a predominantly low profile, with its inshore margin located approximately 50 meters and its offshore edge approximately 100 meters from the beach. The water depth is 5 to 7 meters. The northern part is mostly flat and barren, of patchy rock with few live corals present. Few fishes are seen on this section of the reef. Southward along the reef edge, the height increases with a prominent ledge approximately 1 meter high originating near the southern boundary of the study area (Fig. 3). This higher relief part of the reef is characterized by much more cover and an increase in live corals and diversity of the fishes present. The water over the first reef is also usually turbid, but less so than in the surf zone (Marsh, et al., in preparation, 1980). Beyond the first reef is an expanse of sandy bottom that extends for approximately 60 meters to the inshore edge of the second reef. The second reef is approximately 500 meters wide with an 8- to 13-meter water depth. The water is usually clearer than at the first reef. The second reef has a higher profile, with an extensive outside ledge that reaches 3 meters in some places (Fig. 4). This reef has a profusion of live, soft and hard corals and a large network of potholes and small ledges which afford more cover to the PALM BEACK™ ¥ LAKE WORTH EXPLANATION Cs Shoreline Shoreface Gs Reef Lines SS) 87 Flats Glas = Sediment Slope N-S Scale in Yords 5000 ° 5000 10000 E-W Scale in Yards 2000 1000 ° 2000 4000 Figure 1. Location of study area and plan of southeastern Florida shelf morphology (after Duane and Meisburger, 1969). 10 25 59 80° 06 BORROW AREAS SECOND REEF Depth in Meters Figure 2. Shelf morphology off Hallandale. IEA Figure 3. Higher profile area of first reef platform. Figure 4. Outside ledge area of second reef platform. WA fishes inhabiting this area (Fig. 5). The fish fauna of the second reef consists of larger and more numerous fishes than on the first reef. The "typical" reef fishes, such as angelfishes (Chaetodonttdae), butterflyfishes (Chaetodontidae) and damselfishes (Pomacentridae), are better represented in both species and numbers. Some of the larger and faster fishes, such as cero mackerel (Scomberomorus regalts) and blue runner (Caranx crysos), were observed on the second reef and not Ons thewtarsitemseetr sas SS a Figure 5. Top of second reef platform. IV. RESULTS Courtenay, et al. (1974) noted considerable turbidity nearshore off the nourished beach. This condition still exists with underwater visibility rarely exceeding 2 meters. The bottom is strewn with rocks and fine sand and silt. Much of this material covers the first reef. Underwater visibility over the first reef was generally between 3 to 4 meters but increased to 6 to 8 meters over the second reef. A total of 114 species of fishes belonging to 36 families was observed in the study area (App.). Nine species belonging to seven families were found in the surf zone. The permit (Trachinotus faleatus) was the most abundant species in this area. The spotfin mojarra (Euctnostomus argenteus) and the sand drum (Umbrina corotdes) were also common. Lack of cover, wave action, and limited INS} food are among the factors limiting the number of fish species occupying the surf zone. On the first reef 67 species representing 26 families of fishes (see App:) were observed. Courtenay, et al. (1974) suggested that the low profile of this reef area provides jimited cover and, therefore, restricts the number of species of fishes found there. The most abundant species found on this reef in 1978-79 was the slippery dick (Halichoeres bivittatus). Tomtate (Haemulon aurolineatun), high-hat (Equetus acuntnatus), cocoa damselfish (Pomacentrus vartabilts), bluehead (Lhalassoma bifasetatum), red- tail parrotfish (Sparisoma chrysopterun), and doctorfish (Acanthurus chirurgus) were also abundant. Sizable aggregations of grunts (Pomadasyidae), angelfishes, and parrotfishes (Scartdae) occurred at specific locations on the first reef. Damselfishes were also well represented. Courtenay, et al. (1974) recorded the dusky jawfish (Opistognathus whitehurstt), a burrowing species, as common along the platform of the first reef. No specimens of this fish were observed there in 1978-79. The absence of this species is probably caused by the substrate having been altered by incursion of finer materials, possibly eroded beach fill materials. Eighty-nine species belonging to 30 families of fishes were observed on the second reef (App.). The most abundant species was the bluehead. Bicolor damselfish (Pomacentrus partitus), slippery dicks, and doctorfish were also abundant. Gobies (Gobiidae), parrotfishes, angelfishes, grunts, and sea basses (Serranidae) were also well represented on this reef. Certain species such as the longspine squirrelfish (Holocentrus rufus), tobaccofish (Serranus tabacarius), harlequin bass (Serranus ttgrinus), and blue chromis (Chromts cyaneus) were present on the seaward side of the second reef but absent on the inshore side. The blue goby (loglossus callturus), a burrowing fish, was seen frequently in the sandy area adjacent to the second reef. Another burrowing species, the yellowhead jawfish (Opistognathus aurtfrons), however, was rare. Other fishes observed over the sandy areas adjacent to the second reef include the sand perch (Diplectrum formosum) , tobaccofish, yellowfin mojarra (Gerres cinereus), and bridled goby (Coryphopterus glaucofraenun) . V. DISCUSSION AND CONCLUSIONS Courtenay, et al. (1974) list 42 species belonging to 24 families of fishes as having been collected in the area of the Hallandale beach restoration project; they emphasize, however, that sampling in the study area was incomplete. The present study revealed the presence of 114 species of fishes belonging to 36 families. In the 1971-72 survey, fish collections were made using the ichthyocide rotenone. The present study used underwater observations primarily and the anesthetic quinaldine as an inciden- tal collecting method. 14 The results of the present study demonstrate that although the fish fauna in the Hallandale area is rich, the dusky jawfish may have been affected adversely by dredging activities and later by beach erosion. The first reef appears to have been affected directly by deposition of sediment that further reduced the bottom relief and grain size of the substrate. The dusky jawfish, a shallow-water burrowing species, has been used as an indicator species in studies of the effects of beach nourishment projects (Courtenay, et al., 1974). Thompson (1974) showed that this species typically burrows in sand areas at the edge of a vertical surface, usually of rock or dead coral, and never on a level surface. There these fishes excavate permanent burrows on the reef platform which they abandon only under condi- tions of considerable stress. In the previous study (Courtenay, et al., 1974), dusky jawfish were common on the first reef. This species was not observed during this study. The absence of this species probably can be attributed to an alteration of the substrate and habitat possibly due to deposition of fill materials. The fine-grained sediment is unstable for burrowing. Deposition on the first reef also reduced the available vertical surfaces. During 1971-72, the first reef received only negligible damage from erosion of the filled beach. The present study indicates that the movement of fines covered the lower profile portions of the first reef. Certain species such as the belted cardinalfish (Apogon townsendt) and the roughhead blenny (Acanthemblemarta aspera) , collected at Hallandale in 1971-72 (Courtenay, et al., 1974), were not observed in this study. Courtenay, et al. (1974) predicted a decline of fishes and other marine animals on the first reef should further beach erosion occur. The second reef, located farther offshore, showed no effects of the 1971 beach restoration project or erosion and incursion of sediment. Previous damage (scouring, siltation, etc.) which had occurred as direct effects of dredging was not evident. Corals were abundant and thriving and the reef structure supported a rich fish fauna. Certain fish species such as the bridled goby, the rock beauty (Holacanthus tricolor), and the barred hamlet (Aypoplectrus puella), absent or listed as rare by Courtenay, et al. (1974), were abundant in this survey. The presence of these fishes in numbers of individ- uals is attributed to improved conditions following cessation of dredging activities. In summary, the fish fauna of the second reef off Hallandale shows no damage as a result of the dredging activities of 1971. The first reef, however, has been affected adversely by incursion of sediment. VI. RECOMMENDATIONS The recommendations of Courtenay, et al. (1974) are repeated. Before, during, and after beach restoration projects, "surveys should be conducted by both competent biologists and engineering surveyors..." IS) Duane and Meisburger (1969) recommend sand in the linear second flat for beach fill material based on accessibility, continuity of the deposits, and suitability. They cautioned, however, that these deposits contained a substantial amount of material that could become mechanically degraded in the turbulent littoral zone. This study indicates that the potential effects of incur- sion of eroded beach-fill materials on nearshore reefs should be considered in environmental impact studies for future beach restoration and nourishment projects in southeastern Florida. 16 LITERATURE CITED BAILEY, R. M., et al., "A List of Common and Scientific Names of Fishes from the United States and Canada,"' SP-6, 3d ed., American Fisheries Society, Washington, D.C., 1970. COURTENAY, W. R., JR., et al., "Ecological Monitoring of Two Beach Nourishment Projects in Broward County, Florida,"' Shore & Beach, Wo, 405 97S, jes BLS. COURTENAY, W. R., JR., et al., "Ecological Monitoring of Beach Erosion Control Projects, Broward County, Florida, and Adjacent Areas,'' TM-41, U.S. Army, Corps of Engineers, Coastal Engineer- ing Research Center, Fort Belvoir, Va., Feb. 1974. DUANE, D. B., AND MEISBURGER, E. P., "Geomorphology and Sediments of the Nearshore Continental Shelf, Miami to Palm Beach, Florida,"' TM-29, U.S. Army, Corps of Engineers, Coastal Engineer- ing Research Center, Washington, D.C., Nov. 1969. JONES, R. S., AND THOMPSON, M. J., ''Comparison of Florida Reef Fish Assemblages Using a Rapid Visual Technique," Bulletin of Marine Setence, Vol. 28, 1978, pp. 159-172. MARSH, G. A., et al., "Evaluation of Benthic Communities Adjacent to.a Restored Beach, Hallandale (Broward County), Florida," Vol. II, MR 80-1, Hcologteal Evaluatton of a Beach Nourtshment Project at Hallandale (Broward County), Flortda, U.S. Army, Corps of Engineers, Coastal Engineering Research Center, Fort Belvoir, Va. (in preparation, 1980). STARCK, W. A., II, 'A List of Fishes of Alligator Reef, Florida with Comments on the Nature of the Florida Reef Fish Fauna," Undersea Btology, Vol. 1, No. 1, 1968, pp. 6-42. THOMPSON, M. J., "Burrowing and Burrow-Associated Behavior in the Dusky Jawfish, Opistognathus whitehursti,"' Unpublished M.S. Thesis, Florida Atlantic University, Boca Raton, Fla., 1974. U.S. ARMY ENGINEER DISTRICT, JACKSONVILLE, "Appraisal Report on Beach Conditions in Florida," Jacksonville, Fla., Jan. 1965. 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