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HomeMy WebLinkAboutVer _COMPLETE FILE_19810513 N'l of Natural North Carolina Department Resources &Community Develo ment 3u. h: C "1.161 1 James B. Hunt, Jr., Governor Howard N Lee, Secretary " i 91'')%%3:: 22J3 a May ]4, 1981 MEMORANDUM TO: REVIEW AGENCIES 7 FROM: JOHN PARKER pERMUS ANQ SUBJECT: MOSQUITO CONTROL PROGRAM The Morehead City office of the office of coastal. Management has scheduled a meeting following the regular enforcement conference to hear about a new proposal from the Pamlico County mosquito control staff. It is my understanding that officials of the Division of Health Services, vector control program, will also be present. As you may recall, the grid ditching routine has not been pursued since the early seventies. And many questions have been raised about the effectiveness of this program and, of course, about its impacts on the estuarine environment. As a result of the most recent concerns, Dr. Hugh Tilson of the Health Department ap- pointed an ad hoc committee to study the issue. A draft report is now available which may provide guidance for future mosquito control programs. If your agency has any interest in this matter., I urge that you arrange to attend the 1:30 P.M., May 28th meeting in the Fisheries Building in Morehead City. (?'6C L 9 J,TV, An t quaI (.)p(+urIum Ir AIfirmu:nr Aio<,r 1 -Ph;v,r DEPARTMENT OF THE ARMY WILMINGTON DISTRICT. CORPS OF ENGINEERS P. O. BOX 1650 WILMINGTON. NORTH CAROLINA 28402 SAWCO-EE IN REPLY REFER TO 22 October 1981 Mr. Russ Talley N.C. Water Quality Section Division of Environmental Management PO Box 27687 Raleigh, NC 27611 Dear Mr. Talley: On 28 May 1981 a scoping meeting was held in Morehead City, North Carolina, regarding the proposed pilot project;.by Mr. Ben Hale, Pamlico County Health Department, to perform 'ditching activities in the high salt marsh (Distichlis spicata, Spartina patens) to control mosquitoes. Following this meeting, most of the agencies and individuals attending felt that detailed environmental studies needed to be performed on the pilot project marsh before and after project completion to determine impacts. The environmental studies proposed would require d to 2 years of monitoring before and after ditching, and would involve not only documenting mosquito breeding but also include detailed investigations on detrital and other nutrient fluxes, impacts on aquatic and terrestrial species and habitats, and cumulative impacts of similar projects. I agree that detailed investigation would be needed for such proposals when impacts have not previously been adequately documented. However, Mr. Frank Yelverton of my staff has been investigating ditching activities for mosquito control in other states. Based on his investigations, Maryland, Delaware, and New Jersey have done extensive marsh ditching and have had good success in controling mosquitoes. The technique generally used is called Open Marsh Water Management (OMWM). Standards used in New Jersey for OMWM are described in enclosure 1. Both the Philadephia and Baltimore Districts, Corps of Engineers have processed Department of the Army permits for OMWM activities in the states indicated above. Processing is somewhat different between Districts and states but two things are consistent. First, the applicant must provide detailed information on mosquito breeding sites, detailed plans indicating how ditches will connect breeding sites, and stake on the ground breeding sites and ditch alignment. Second, detailed biological information on other than mosquito data is not required. SAWCO-EE 22 October 1981 ,. The reason that detailed biological information is not required is because many studies that document the impacts of OMWM have already been performed in the states' mentioned (see example study and selected bibliography in inclosure 2). Beca4se"of' the.se,;skudies and experience with OMWM, the agencies that were contacted`-.indars?d OMWM if it is performed properly (inclosure 3). Tl e,. phrase "if it is performed properly" is crucial since if the tidal ditches 'are designedproperly they provide a greater exchange of nutrients between the marsh and estuarine system, and the pond systems provide habitat for waterfowl and wading birds. On the other hand, in some cases, ditches have been designed poorly and have drained the marsh and changed the species compositions In some other cases, poor design of ditches resulted in low dissolved oxygen levels which caused the death of the fish which normally consume the mosquito larvae and the mosquito populations exploded. The marsh areas that mosquitoes use for breeding in these northern states - - - containthe-same-marsh species as the breeding areas in North Carolina, even though the nor -o - - _ __ mosquitoes and tidal amplitude in these northern states are similar to North Carolina. Therefore, it may be possible to apply the existing results of OMWM research to North Carolina. This not only would save the applicant time and money in the permit process, but would provide review agencies a broad data base for evaluation of their request. Since OMWM has not been used previously in North Carolina, we plan a meeting T! I IN golf, IIJ-1611111400 *^ the effectiveness of OMWM for control of`mosquitoes, its beneficial and adverse impacts on environment, and its possible application to North Carolina marshes. The meeting will be at 10 a.m. in the Federal Building, 310 New Bern Avenue, Room 209. In an attempt to learn from the experience of others, we have asked three individuals with experience in OMWM to attend this meeting. These individuals are Mr. Fred Ferrigno, New Jersey Division of Fish, Game, and Wildlife; Mr. Cyrus Lesser, Maryland Department of Agriculture; and Mrs. L. K. (Mike) Gantt, U.S. Fish and Wildlife Service. Mr. Ferrigno is a leading researcher on the impacts of OMWM on the environment, and we have asked him to speak on the results on his research. Mr. Lesser is an entomologist with the Maryland Department of Agriculture which is the department responsible for controlling mosquitoes in Maryland. Therefore, Mr. Lesser with speak to us on the effectiveness. of OMWM for the control of mosquitos. Finally, Mrs. Gantt was actively involved in the OMWM when she was with the U.S. Fish and Wildlife Service in Maryland. Mrs.. Gantt will talk to us about methods of ditching that conform to OMWM technquies. 2 SAWCO-EE 22 October 1981 Each presentation will last 20 to 30 minutes including a period for question' and answers. Prior to these presentations, Mr. Frank Yelverton of my staff will give a brief introduction that will include Corps permit requirements for OMWM activities. When these presentations are completed, we will break for lunch. Following lunch we will reconvene for a detailed question/answer session. Questions will be directed to a panel consisting of Mr. Yelverton, Mr. Lesser, Mr. Ferrigno, Mrs. Gantt, Mr. Hale, and Mr. Jerry Perkins, N.C. Department of Human Resources, Vector Control Branch. When this panel session is concluded, Mr. Yelverton will briefly summarize the day's discussions and will indicate the probable course of action for permit processing based on the day's events. If you have questions, contact Mr. Yelverton at (919) 343-4640 or FTS 671-4640. Sincerely, W? 3 Incl CHARLES W. HOLLIS 1. N.J. OMWM Standards Chief, Regulatory Functions Branch 2. Example OMWM Study and Bibliography 3. Agency contacts 3 ZZ .41 ., STANDARDS FOR OPEN MARSH WATER MANAGEMENT (OMWM) County mosquito commissions, Rutgers University and the New Jersey Division of Fish, Game and Shellfisheries have been perfecting one technique, Open Marsh Water Management (ON11•41M) for the control of all genera of salt marsh mosquitoes on open tidal marshes for over two decades. Perfection is achieved by continued improvement and evaluation. In order to ensure the finest quality and identify this management technique, certain standards are a necessity. These standards should be included in any riparian or other permit. Improper adherence to these standards would be a violation of the permit and infringement on the quality of the management technique. The following standards shall be utilized and strictly adhered to?in any OMWM project: 1. NEED. OMWM will be based entirely on need.and utilized on breeding marshes only. A. OMWM will be confined to the Spartina patens or mixed S. patens, short S. alterniflora or types of similar vegetation that are irregularly flooded by rains, spring or storm tides. It will not be employed on marshes that are regularly inundated or affected by daily tides such as tall saltmarsh cordgrass (S artina alterniflora), wildrice (Zizania aquatica), cattail (gip ha sue. arrow arum (Peltandra virginica , threesquare (Scirpus olne i and other types of similar vegetation. B. All alterations must directly affect mosquito breeding depressions. C. The direction and type of alteration used will depend on the dis- tribution of the mosquito breeding depressions and their proximity to natural ponds and tidal ditches. D. An experienced wildlife biologist, mosquito control worker, or both, shall stake out all breeding depressions ahead of the equipment. Depression marking shall be utilized to determine the least amount of alteration needed to eliminate mosquito breeding. E. -A11 mosquito or other ditches encountered that are not contributing to breeding mosquitoes will not be cleaned. F. When possible, ponds previously altered by mosquito ditches will be restored. II. ALTERATIONS. Three types of alterations (tidal ditches, ponds and pond radials, will be used. A. Tidal Ditches 1. All tidal ditches will be dug with suitable equipment, pre- ferably with a rotary ditcher. 2. When mosquito breeding depressions are located adjacent to a tidal, mosquito or other ditch, a tidal ditch alteration will be utilized. 3. When a tidal ditch is dug near a pond, the spoil should be deposited on the pond side. 4. Attempts should be made to dig tidal ditches to a depth of approximately three feet. Meandering or straight ditches are acceptable. 5. Main tidal ditches are used to provide tidal circulation through large areas. They should be connected to a tidal source on both ends where possible. Their location is deter- mined by the, distribution of breeding depressions. 6. Lateral tidal ditches connect breeding depressions to mains, natural tidal ditches or other laterals. Such laterals often dead-end in a breeding depression. Inclosure 1 -2- B. 7. All mosquito or other ditches that are breeding will be cleaned: 8. Spoil shall be used whenever possible?to fill adjacent mosquito breeding depressions or spread evenly over the marsh to en courage growth of existing vegetation. Pond Radials 1. All mosquito:,breeding depressions located near a natural or other permanent pond shall be connected to this pond by pond,. radials. These radials will provide access for fish to de- vour mosquito larvae in the depressions. 2. All pond radials shall be constructed with suitable equipment, preferably with a rotary ditcher. 3. To prevent drainage of a pond by muskrats or snow geese, all pond radials shall terminate at a sufficient distance from a tidal ditch: C. Ponds T -Where large numbers of mosquito breeding depressions are concentrated in a limited area, a pond alteration will be utilized. 2- Pond nstruction is accom li-shed by--the-use of the rotary ditcher, amphibious crane or other suitable equipment. 3. Ponds should be shallow, less than one foot in depth, to promote the best waterfowl, wading and shore bird use. 4. To prevent mosquito breeding during droughts, a reservoir three feet in depth shall-be installed within the pond. 5. These reservoirs should provide proper pond access by humans. Uhen large numbers of radials are used, reservoirs are unnecessary. eservoirs - out during droughts by construction of three foot ditches with a rotary ditcher or other suitable equipment. These reservoirs will connect all the lowest areas within the pond, 7. Pond spoil should be squashed and leveled without causing depressions. It should be reduced to the lowest possible lever to ensure reestablishment of existing vegetation. Spoil shall approximate the level of the existing marsh. 8. Ponds may take the shape of the breeding area or may be squared off to facilitate construction. The shape of a pond or ditch does not appreciably affect wildlife use. Depth, food --pot-en t i ci-1--a-nd a v-a i 1-ab-i-1 i-ty a-r-e--th e=-ma-i_n f-ac_to_r_s th_a t___cLe t e r- _ _ mine wildlife utilization. Ill. OBJECTIFIES A. To adequately serve the three major objectives (control mosquitoes, eliminate insecticides and enhance the tidal food web) all three alteration types (tidal ditches, ponds and pond radials) shall be utilized on each section of marsh whenever possible. Diversity provides a better marsh environment, prevents marsh surface breed- ing by all genera of mosquitoes and enhances both major branches of the tidal food web. B. Insecticide use is gradually phased out as OMWM progresses to eliminate breeding acreage. When the project is completed, all insecticide use should terminate. I`!. OTHER TECHNIOUES Impoundments, stop ditches and other types of management techniques are not OMWM. V. EVALUATION Mosquito larval dippings,- vegetational plots, invertebrate samp- ling and wildlife censuses are to be. conducted on the area treated with OMWM and compared with a control of similar composition. Y OPEN MARSH WATER'MANAGEMENT SELECTED BIBLIOGRAPHY American Public Health Association, et al. 1975. Standard Methods for the Examination of Water and Wastewater 714th ed.). Amer. Public Health Assoc., New York. 1193 p. Axtell, R.C. (ed.) 1974. Training manual for mosquito and biting fly control in coastal areas. Univ. North Carolina Sea Grant Publ. UNC-SG-74-08. 254 p. Axtell, R.C., G.A. Carlson, and D.V. DeBoard. March 1975. Demand for and cost of coastal salt marsh mosquito abatement, Tech. Bul. No. 232, North Carolina Agricultural Experiment Station, Univ. of North Carolina Sea Grant Program Publication UNC-SG-75-11. Blum, J. L. 1969. Nutrient changes in water flooding the high salt marsh. Hydrobiologia 34: 95-99. Bodola, A. 1970. An evaluation of the effectiveness of natural pools, blind sumps and champagne pools in reducing mosquito production on a salt marsh. Proc. N.J. Mosq: Exterm. Assoc. 57: 45-56. Bourn, W.S. and C. Cottam. 1950. Some biological effects of ditching tide water marshes. U.S. Fish and Wildlife Serv., Res. Rept. 19. 30 p. Bradbury, H.M. 1938. Mosquito control operations on tide marshes in Massachusetts and their effect on shore birds and waterfowl. J. Wildlife Management. 2: 49-52. Brook, J.E. 1917. The circulation of water on the drained salt marshes - the need for and the way to obtain it. Proc. NJMEA. 4:10. Bauder, K.W. 1980. The Establishment of Unified OPEN MARSH WATER MANAGEMENT Standards in New Jersey. Proc. N.J. Mosq. Exterm. Assoc. 67: 72-76. Burger, J. and J.K. Shisler. 1978. The effects of ditching a salt marsh on colony and nest site selection by herring gulls (Laurus argentatus). Amer. Midl. Natur. 100(1): 54-63. Byron, M.M. 1968. Net nutrient exchange between high marsh areas and an estuary. M.S. thesis. North Carolina State University 22 p. Carmichael, G.T.. 1957. Effectiveness of ditching in controlling salt marsh mosquitoes. Mosquito News. 17(4):265-68. Inclosure 2 Catts, E.P. Jr. 1957. Mosquito prevalence on impounded and ditched galt '. marshes, Assawoman Wildlife Area, Delaware, 1956. M.S. thesis. Univ. of Delaware. Catts, E.P. Jr., F.H. Lesser, R.F. Darsie, Jr., 0.-Florschutz, and E.E. Tindall. 1963. Wildlife and mosquito production on impounded tidal marshes in Delaware, 1956-62. Trans. N. Amer. Wildl. Conf. 28: 125-132. Chapman, H.C. and F. Ferrigno. 1956. A three-year study of mosquito breeding in natural and impounded salt marsh areas in New Jersey. Proc. N.J. Mosq. Exterm. Assoc. 43: 48-65. Clarke, J.L. 1938. Mosquito control as related to marsh conservation. Proc.. N.J. Mosq. Exterm. Assoc. 25: 139-147. Cottam, C. 1938. The coordination of mosquito control with wildlife conserva- tion. Proc. N.J. Mosq. Exterm. Assoc. 25: 217-227. Cottam, C. and W.S. Bourn. 1952. Coastal marshes adversely affected by arainage ana arougn Cottam, C., W.S. Bourn, F.C. Bishop, L.L. Williams, Jr., and W. Vogt. 1938. What's wrong with mosquito control? Trans. N. Amer. Wildl. Conf. 3: 81-107. Daiber, F.C. 1974. Salt marsh plants and future coastal salt marshes in relation to animals. In R.J. Reimold and W.H. Queen (eds.), Ecology of Darsie, R.F. Jr. and P.F. Springer. 1957. Three-year investigation of mosquito breeding in natural and impounded tidal marshes in Delaware. University of Delaware Agric. Exper. Sta. Bull. No. 320. 65 p. DeBord, D.V., G.A. Carlson, and R.C. Axtell. 1975. Demand for and cost of. coastal salt marsh mosquito abatement. N.C. Agric. Exper. Sta. Tech. Bull. No. 232. 85 p. Dukes,-J.C., R.C. Axtell, and K.L. Knight, 1974. Additional Studies of the __-Effects-of --SAIt_ Marsh-lmpoundmer?ts__on Mosquito Populations. University of N.C. Water Resources Res. Inst. Rept. No. 102. 38 p. Estrada, M., I. Valiela, and J.M. Teal. 1974. Concentration and distribution of chlorophyll in fertilized plots in a Massachusetts salt marsh. J. Exp. Mar. Biol. Ecol. 14: 47-56. Ferrigno,. F. 1961. Variations in Mosquito - Wildlife Associations on Coastal Marshes. Proc. N.J. Mosq. Exterm. Assoc. 48: 193-203. y 'Verrigno, 1970. Preliminary effects of open marsh water management on the vegetation and organisms of the salt marsh. Proc. N.J. Mosq. Exterm. Assoc. 57: 79-94. Ferrigno, F. and D.M. Jobbins. 1968. Open marsh water management. Proc. N.J. Mosq. Exterm. Assoc. 55: 104-115. Ferrigno, F., P. Slavin, and D.M. Jobbins. 1975. Saltmarsh water management for mosquito control. Proc. N.J. Mosq. Exterm. Assoc. 62: 30-38.. Ferrigno, F., L.G. MacNamara, and D.M. Jobbins. 1969. Improved Management of Coastal Meadowlands. Proc. Assoc. 56: 188-203. Fitzpatrick, G. and D.J. Sutherland. 1978. Effects of insecticides temephos (abate) and chlorpyrifos (Du of the salt-marsh snail Melampus bidentatus. Mar. Ecological Approach for N.J. Mosq. Exterm. the organophosphorus rsban) on populations Biol. 46: 23-28. Florschutz, 0., Jr. 1959. Mosquito production and wildlife usage in natural, ditched, and unditched tidal marshes at Assawoman Wildlife Area, Delaware. Proc. N.J. Mosq. Exterm. Assoc. 46: 1037111. Frolander, H.F. 1968. Statistical variation in zooplankton numbers from subsampling with a Stempel pipette. J. Water Pollution Control Fed. 40: R82-R88. Gabrielson, I.A. 1936. Information needed for a proper understanding of the effects of mosquito control work on the wildlife of tidal marshes. Proc. N.J. Mosq. Exterm. Assoc. 23: 156-163. Green, R.H. 1979. Sampling Design and Statistical Methods for Environmental Biologists. John Wiley & Sons, Inc. 257 p. Hansen, J.A., F.H. Lesser, R.W. Lombardi, J.K. Shisler, and P. Slavin. 1976. The economics of open marsh water management--a New Jersey view. Proc. N.J. Mosq. Exterm. Assoc. %63: 77-81. Headlee, T.J. 1945. The mosquitoes of New Jersey and their control. Rutgers University Press, New Brunswick, N.J. 326 p. Heinle, D.R. and D.A. Flemer. 1976. Flows of materials between poorly flooded tidal marshes and an estuary. Mar. Biol. 35: 359-373. Imber, C.F. and T.T. Blailock. 1981.. A Review of and a Plan for Mosquito Control in North Carolina. Unpublished. Krebs, C.T. and I. Valiela, 1978. Effect of experimentally applied chlorinated hydrocarbons on the biomass of the fiddler crab, Uca pugnax (Smith). Estuarine and Coastal Mar. Sci. 6.: '375-386. Kuenzler, E.J., 1961. Structure and energy flow of a mussel population in a Georgia salt marsh. Limnolo. and Oceanogr. 6(2): 191-204. m Kuenzler, E.J. and. H.L. Marshall. 1973. Effects of mosquito control #itchyng on estuarine ecosystems. Univ. N.C. Water Resources Res. Inst. Rept. No. 81. 83 p. LaSalle, R. and K.L. Knight. 1973. The effects of ditching on the mosquito populations in some sections of Juncus salt marsh in Carteret County, North Carolina. Univ. N.C. Water Resources Res. Inst.`Rept. No. 82. 162 p. LaSalle, R.N, and K.L. Knight. 1974. Effects of Salt Marsh Impoundments on Mosquito Populations. Univ. N.C. Water Resources Res. Inst. Rept. No. 92. 85 p Leslie, J.B. 1969. State mosquito control commission approaches to marsh management. Proc. N.J. Mosq. Exterm. Assoc. 56: 7-11. Lesser,_ C.R.,-1977. A method to estimate-populations of mosquito larvae in - --- _ shallow water. Mosquito News 37(3): 517-519. Lesser,.C.R. and D. Saveikis. 1979. A study o the impacts o a mosque o control integrated pest management program on selected parameters of the ecology of Chesapeake Bay high marsh communities in Maryland. Final Rept., Md. Dept, of Agric., EPA Grant No. X003147-01. 194p. Lesser, C.R., F.J. Murphey, and R.W. Lake. 1976. Some effects of grid system . mosquito control ditching on salt marsh biota in-Delaware. Mosquito News 36(1): 69-77. Lesser, F.H. 1965. Some environmental considerations of impounded tidal marshes on mosquito and waterbird prevalence, Little Creek Wildlife Area, Delaware, M.S. Thesis. Univ. Delaware. Linthurst, R.A. and R.J. Reimold. 1978a. Estimated net aerial primary productivity for selected estuarine angiosperms in Maine, Delaware, and Georgia. Ecology 59(5) 945-955. Linthurst, R.A. and R.J. Reimold. 1978b. An evaluation of methods for estimating the net aerial primary productivity of estuarine angiosperms. J. Appl. Ecol. 15:'919-931. Lotrich, V.A., W.H. Meredith, S.B. Weisberg, L.E. Hurd, and F.C. Daiber. 1979. Dissolved and particulate nutrient fluxes via tidal exchange between a salt marsh and lower Delaware Bay. Presentation at the Fifth Biennial International Estuarine Research Conf., Jekyll Island, Ga., Oct. 7-12, 1979. (publ. abstract) Neely, W.W. 1962. Saline soils and brackish waters in management of wildlife, fish, and shrimp. Trans. N. Amer. Wildl. Conf. 27: 321-334. Provost, M.W. 1977. Source reduction in salt-marsh mosquito control: past and future. Mosquito News 37(4): 689-698. Richard, G.A., 1978. Seasonal and environmental variations in sediment accretion in a Long Island salt marsh. Estuaries 1(1): 29-35. Shisler, J.K. 1973. Pioneer plants on spoil piles associated with mosquito ditching. Proc. N.J. Mosq. Exterm. Assoc. 60: 135-141. Shisler, J.K. and D.M. Jobbins. 1977a. Tidal variations in the movement of organic carbon in New Jersey salt marshes. Mar. Biol. 40: 127-134. Shisler, J.K. and D.M. Jobbins. 1977b. Salt marsh productivity as affected by the selective ditching technique, open marsh water management. Mosquito News 37(4); 631-636. Shisler, J.K., F.H. Lesser, and T.L. Schulze. 1975. Reevaluation of some effects of water management on the Mispillion Marsh, Kent County, Delaware. Proc. N.J. Mosq. Exterm. Assoc. 62: 276-278. Shisler, J.K., F.H. Lesser, B. Gooley, J. Hansen, and P. Slavin. 1978. Practical application of the rotary ditcher in pond construction. Mosquito News 38(1): 112-115. Shisler, J.K., F.H. Lesser, and T. Candeletti. 1979. An approach to the evaluation of temporary versus permanent measures in salt marsh mosquito control operations. Mosquito News 39(4): 776-780. Smalley, A.E. 1959. The role of two invertebrate populations, Littorina irrorata and Orchelimum fidicinum, in the energy flow of a salt marsh eco? system. Ph.D. Diss. Univ. Georgia. 126 p. Smith, J.B. 1904. Report of the New Jersey Agricultural Experiment Station upon the mosquitoes occurring within the State, their habits and life history. Rutgers Univ., New Brunswick, N.J. 482 p. Smith, J.B. 1907. The New Jersey salt marsh and its improvement. Bull. N.J. Agric. Exper. Sta. No. 207. 24 p. Stearns. L.A., D. MacCreary, and F.C. Daigh. 1940. Effects of ditching on the muskrat.,population of a Delaware tidewater marsh. Univ. Delaware Agric. Exper. Sta. Bull. No. 225. 55p. Strickland, J.D.H. 1960. Measuring the production of marine phytoplankton. Bull. Fish. Res. Bd. Canada 122: 1-172. Strickland, J.D.H. and T.R. Parsons. 1972. A Practical Handbook of Seawater Analysis. Bull. Fish Res. Bd. Canada 167: 1-310. (2nd ed.) Tindall, E.E. 1961. A two-year study of mosquito breeding and wildlife usage in Little Creek impounded salt marsh, Little Creek Wildlife Area, Delaware, 1959-60. Proc. N.J. Mosq. Exterm. Assoc. 48: 100-105. Urner, A. 1935. Relation of mosquito control in New Jersey to bird life of the salt marshes. Proc. N.J. Mosq. Exterm. Assoc. 22: 130-136. 14 Vollenweider, R.A. (ed.) 1969. A Manual on Methods for Measuring Primary Production in Aquatic Environments. IBP Handbook No. 12. Blackwell Sci. Publ., Oxford. 213 p, Ward, D.V. and B.L: Howes. 1974. The effects of Abate, an organophosphorus insecticide, on marsh fiddler crab populations. Bull. Environ. Contam. Toxicol. 12: 694-697. Ward, D.V. and D.A. Busch. 1976. Effects of temefos, an organophosphorus insecticide, on survival and escape behaviour of the marsh fiddler crab, Uca Pu nax. Oikos 27: 331-335. Ward, D.V. and D.F. Ludwig. 1976. Interactive effects on predation pressure and insecticide (temefos) toxicity on populations of the marsh fiddler crab, Uca pugnax. Mar. Biol. 35: 119-126. Wh-igham, D. F: 1-97-9. The---impact of , open marsh water management on the ecology of high marsh vegetation. Chesapeake Bay Center for Environmental Studies. Wolf, P.L., S.F. Shanholtzer and R.J. Reimold, 1975. Population estimates for Uca pugnax (Smith, 1870) on the Duplin Estuary Marsh, Georgia, U.S.A. (Decapoda, Brachyura, Ocypodidae) Crustaceana 29(1): 79-91. U z w a z z 0 zoo M uI v1 a 0 h n m U O a O a O F" Z w VO da z z ?O Q ? O Q E-' Q E co s o b>6 6,o `° ro N` ce E E t° 2 c y o Vi c n O 'fl Wl 'D = v c z .D to u y E 0 co O b p c Uz> .'R N U 0 J) - c ` 0 H $- y O 'C v 0 a c Z v °- 3 ou O L > cl O q 't E O. ? U L C ? . ? a ro?? b E ? o? 's p ? a v v. a o b O ?> ? •.r :: "'? ..+ G U U N ? c V u> L w Q' C U 0 0 ? ? yr U y •«+ z v •0 C C 3 _ w o o-E o.g' ?a > T O o c O u c y C U _. p : . C :C . OA E .~+ C U O e 3 c O a O ?« ° O cf U= c c ?-' 3 0 a U • a i a v u LL v 0 u N. O ?" ew 02 E v ? E L N ? O C - .0 . V v l y T V C E v v L .c .? a . + p 'p .3 CAS Ofl O O O O E v L c c> c .O O d LL .r 6 'C r. u .°? x o ?. E u E a 0 a ?cu 3 L 0 CL D y . SP o~ b E «? E `' a o > E ' ' L = E • « . ou C c d v b u y o ? 3 •- r o c i a. c 0 y «. ,. 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C O? f C's r 7 ? v1 C C C \C , O , 00 N c0 O C S > c v '? C O :1 M C I (? L C 'n s O o C G C T7 L E U v r M z O F Q L LA y Q z c F z OG X LU O F y G LL7 y m 3 y z •r. v •? v v •L v v +J t v v C p v L r - :e D E v ' L y ? •? 3 l p '_ `- .L. ? y a y U :y = ' p :J ti? p J •r. v y G v O 85 7:1 -u r- O -7 L :J -y .'_ v v 7 C 1 y E f O O E c y y c ?' ?, yU y s v c y ° o v r E a c 3 c C`0 'O O '3 y ;? 3 C 'C3 0U 7 S ?- S y O p i, L a • 7 C . J = C 'CJ U C C l ' ? .. y 'O E E L> = aOr ? ' J C `_ ? C " !1 C C C U 'y I: ? ° 'O ? ? ? 'D r C ^ E L C y r y v R V -0 -0 s E C y Q. ° L 7S ' E ° o "U -4 p 7S o• • s o =s 'fl 'fl > i y? .D J O v v .?... = v ,0 y :J :S -5 oj U y t L '> > y O C> r ' E C O O ? L 7 L > L ' ? ? ? C ? C ? t1 e Y .? C 8 v ? •r, c3 v ^ ? ,? J = = 3 C J .?.. v s CA ? L 7E y • > Y % v E s E O O u, c :2 - v 7 1 0 C v n. v U „y AGENCY CONTACTS`» NAME TELEPHONE # Mr. Fred Ferrigno (609) 628-2103 N.J. Division of Fish, Game and Wildlife Tuckahoe, NJ Dr. Dennis Whigham (301) 798-4424 Chesapeake Bay Center for Environmental Studies. Edgewater, MD Mr. Cyrus Lesser (301) 742-1562 MD Department of Agriculture Salisbury, MD Mr. Tim Goodyear (301) 226-5771 National Mar-i-ne Fi i-e e=rg Oxford, MD Mr,. George Ruddy (301) 269-5448 U.S. Fish and Wildlife Service (FTS) 922-2007 Annapolis, MD Mrs. L. K. (Mike) Gant (919) 755-4520 Raleigh, NC Mr. Woody Francis (301) 962-4500 Corps of Engineers (FTS) 922-4500 Baltimore, MD Mr. Jeffrey Steen (215) 597-4833 Corps of Engineers (FTS) 597-4833 Philadelphia, PA Mr. Bill Meredith (302) 736-4782 DE Division of Fish and Wildlife Dover, DE Inclosure 3 f C ?ry r DIVISION OF MANAGMOW Novaaber 10, 1981 HEYORANDOM TO: an Mn].ligan t L. Y. Boston, Jr. 70 SU&UCTt Meeting on Mosquito Control and Water Manageamt On November 18, 1981, a meeting will be hold with the Corps of Engineers to discuss the matter of water assawmat as a mosquito control tool in coastal Borth Carolina. I am requesting that you attend this mooting to be held is Room 209 of the Federal Building at 314 Now Bern Avenue beginning at 10 a.m. I an also by copy of this letter asking that Chuck Wakild attend the meeting with you so that the lower coast situations may also be addressed. Your joint participation in this meeting will be greatly appreciated. cca Chuck Wakild V Robert Y. Halms yj ,? 3 ... C y aa? 'W1:,Sir oNa? ???ic? R?c? W1L?`sINGTON , s November 2, 1981 MEMORANDUM Liu. oaf C;,•.?= ?nmc;?:a: •i??:?`• Mr. Steve Conrad Mr. Boe Green FROM: Neil S. Grigg SUBJECT: Meeting on Mosquito Control and Water Management TO: Mr. Mr. Mr. Mrs Mr. Dr. As you know, the use of water management for mosquito control in coastal North Carolina has been very controversial. I wawa like to call your attention to a meeting which will be held on November A. 8 by the Corps of Engineers to discuss this matter. The attached letter from Charles Hollis ex- plains. I believe you will find this of interest and that it would be to your advantage to have one of your key staff members attend. NSG/ch Attachment Ken Stewart Bob Helms Vernon Bevill Connell Purvis Anne Taylor John Morris Ed Howard 1'% ? I98I f -Irv UP i WATER QUALITY, . - SAWCO-EE DEPARTMENT OF THE ARMY ?•?.? -? , WILMINGTON DISTRICT. CORPS OF ENGINEERS P. O. 90X 1890 WILMINGTON. NORTH CAROLINA 28402 IN REMY REFER TO 22 October 1981 Mr. James F. Stamey, Chief Environmental Health Section Division of Health Services PO Box 2091 Raleigh, NC 27602 Dear Mr. Stamey: On 28 May 1981 a scoping meeting was held in Morehead City, North Carolina, regarding the proposed pilot project-by Mr. Ben Hale, Pamlico County Health Department, to perform ditching activities in the high salt marsh (Distichlis spicata, Spartina patens) to control mosquitoes. Following this meeting, most of the agencies and individuals attending felt that detailed environmental studies needed to be performed on the pilot project marsh before and after project completion to determine impacts. The environmental studies proposed would require I to 2 years of monitoring before and after ditching, and would involve not only documenting mosquito breeding but also include detailed investigations on detrital and other nutrient fluxes, impacts on aquatic and terrestrial species and habitats, and cumulative impacts of similar projects. I agree that detailed investigation would be needed for such proposals when impacts have not previously been adequately documented. However, Mr. Frank Yelverton of my staff has been investigating ditching activities for mosquito control in other states. Based on his investigations, Maryland, Delaware, and New Jersey have done extensive marsh ditching and have had good success in controling mosquitoes. The technique generally used is called Open Marsh Water Management (OMWM). Standards used in New Jersey for OMWM are described in inclosure 1. Both the Philadephia and Baltimore Districts, Corps of Engineers have processed Dapartment of the Army permits for OMWM activities in the states indicated above. Processing is somewhat different between Districts and states but two things are consistent. First, the applicant must provide detailed information on mosquito breeding sites, detailed plans indicating how ditches will connect breeding sites, and stake on the ground breeding sites and ditch alignment. Second, detailed biological information on other -- than mosquito data is not required. SAWCO-EE 22 October 1981 The reason that detailed biological infonaation is not required is because many studies that document the impacts of OMWM have already been performed in the states mentioned (see example study and selected bibliography its inclosure 2). Because of these studies and experience with OMWM, the agencies that were contacted.indorsed OMk'M if it is performed properly (inclosure 3). The phrase "if it is performed properly" is crucial since if the tidal ditches are designed properly they provide a greater exchange of nutrients between the marsh and estuarine system, and the pond systems provide habitat for waterfowl and wading birds. On the other hand, in some cases, ditches have been designed poorly and have drained the marsh and changed the species composition. In some other cases, poor design of ditches resulted in low dissolved oxygen levels which caused the death of the fish which normally consume the mosquito larvae and the mosquito populations exploded. The marsh areas that mosquitoes use for breeding in these northern states contain the same marsh species as the breeding areas in North Carolina, even though the northern marsh is more extensive. Also, the species of mosquitoes and tidal amplitude in these northern states are similar to North Carolina. Therefore, it may be possible to apply the existing results of OMWM research to North Carolina. This not only would save the applicant time and money in the permit process, but would provide review agencies a broad data base for evaluation of their request. Since OMWM has not been used previously in North Carolina, we plan a meeting in Raleigh, North Carolina, on 18 November 1981 to discuss the effectiveness of OMWM for control of mosquitoes, its beneficial and adverse impacts on environment, and its possible application to North Carolina marshes. The meeting will be at 10 a.m. in the Federal Building, 310 New Bern Avenue, Room 209. In an attempt to learn from the experience of others, we have asked three individuals with experience in OMWM to attend this meeting. These individuals are Mr. Fred Ferrigno, New Jersey Division of Fish, Game, and Wildlife; Mr. Cyrus Lesser, Maryland Department of Agriculture; and Mrs. L. K. (Mike) Gantt, U.S. Fish and Wildlife Service. Mr. Ferrigno is a leading researcher on the impacts of OMWM on the. environment, and we have asked him to speak on the results on his research. Mr. Lesser is an entomologist with the Maryland Department of Agriculture which is the department responsible for controlling mosquitoes in Maryland. Therefore, Mr. Lesser with speak to us on the effectiveness of OMWM for the control of mosquitos. Finally, Mrs. Gantt was actively involved in the OMWM when she was with the U.S. Fish and Wildlife Service in Maryland. Mrs. Gantt will talk to us about methods of ditching that conform to OMWM technquies. 2 8AWCO-EE N 22 October 1981 w Each presentation will last 20 to 30 minutes including a period for question and answers. Prior to these presentations, Mr. Frank Yelverton of my staff will give a brief introduction that will include Corps permit requirements for OMWM activities. When these presentations are completed, we will break for lunch. Following lunch we will reconvene for a detailed question/answer session. Questions will be directed to a panel consisting of Mr. Yelverton, Mr. Lesser, Mr. Ferrigno, Mrs. Gantt, Mr. Hale, and Mr. Jerry Perkins, N.C. Department of Human Resources, Vector Control Branch. When this panel session is concluded, Mr. Yelverton will briefly summarize the day's discussions and will indicate the probable course of action for permit processing based on the day's events. If you have questions, contact Mr. Yelverton at (919) 343-4640 or FTS 671-4640. Sincerely, ?i 3 Incl CHARLES W. HOLLIS 1. N.J. OMWM Standards Chief, Regulatory Functions Branch 2. Example OMWM Study and Bibliography 3. Agency contacts 3 NOR7HR INA DEPA RTMENT OF NATURAL RES ND COMMUNITY DEVELOPMENT ?- Date - 02 19 U To: From: n C Remarks: nr X198 ? Note and file __ ? Note, initial and forward ? Note and. return to me ? Your comments, please ? Note and see me about this ? For your information ? For your approval ? Prepare reply for my signature ? Per our conversation ? Prepare information for me to reply ? Per your request - ? Please answer, with copy to me ? Return with more details ? To be filed WPORTANT t , T Date Time WHILE. YOU WERE OUT AREA CODE NUMBER EXTENSION TELEPHONED PLEASE CALL CALLED TO SEE YOU " WILL CALL AGAIN WANTS TO SEE, YOU URGENT "RETURNED YOUR CALL ' Signed N. C. Dept. of Natural Resources and Community Development STANDARDS FOR OPEN MARSH WATER MANAGEMENT OM14M) County mosquito commissions, Rutgers University and the New Jersey Division o; risn, Game and Shellfisheries have been perfecting one technique, Open'Marsh :Water Managetrent (014114M) for the control of all genera of salt marsh mosquitoes on- open tidal marshes for over two decades. Perfection is achieved by continued improvement and evaluation. In order to ensure the finest quality and identify this management technique, certain standards are a necessity. These standards should be included in any riparian or other permit. Improper adherence to these standards would be a violation of the permit and infringement on the quality of the management technique. The following standards shall be utilized and strictly adhered to in any OMWM project: 1. NEED. OMWM will be based entirely on need and utilized on breeding marshes only. A. CM14M will be confined to the Spartint; patens or mixed S. patens, short S. alterniflora or types of siriilar vegetation that are irregularly flooded by rains, sprinq or storm tides. It will not be employed on marshes that are regularly inundated or affected by daily tides such as tall saltmarsh cordgrass (5 aartina alterniflora), wildrice (Zizania aquatica), cattail (lypha s .), arrow arum (Peltandra virainica , threesquare (Scirpus olne i and other types of similar vegetation. B. All alterations must directly affect mosquito breeding depressions. C. The direction and type of alteration used will depend on the dis- tribution of the mosquito breeding depressions and heir proximity to natural ponds and tidal ditches. D. An experienced wildlife biologist, mosquito control worker, or both, shall stake out all breeding depressions ahead of the equipment. Depression marking shall be utilized to determine the least amount of alteration needed to eliminate mosquito breeding. E. -All mosquito or other ditches encountered that are not contributing to breeding mosquitoes will not be cleaned. F. When possible, ponds previously altered by mosquito ditches will be restored. II. ALTERATIONS. Three types of alterations (tidal ditches, ponds and pond radials will be used. A. Tidal Ditches 1. All tidal ditches will be dug with suitable equipment, pre- ferably with a rotary ditcher. 2. When mosquito breeding depressions are located adjacent to a tidal, mosquito or other ditch, a tidal ditch alteration will be utilized. 3. When a tidal ditch is dug near a pond, the spoil should be deposited on the pond side. 4. Attempts should be made to dig tidal ditches to a depth of approximately three feet. Meandering or straight ditches are acceptable. 5. Main tidal ditches are used to provide tidal circulation through large areas. They should be connected to a tidal source on both ends where oossible. Their location is deter- mined by the distribution of breeding depressions. 6. Lateral tidal ditches connect breeding depressions to mains, natural tidal, ditches or other laterals. Such laterals often dead-end in a breeding depression. Inclosure 1 41 7. All mosquito or other ditches that are breeding will be .. cleaned. + 8. Spoil shall be used whenever possible to fill adjacent mosquito breedinq depressions or spread evenly over the marsh to en- courage growth of existing vegetation. 6. Pond Radials Al mosquito.breeding depressions located near a natural or other permanent pond shall "be.connected to this pond by pond . radials. These radials will provide access for fish to de- vour mosquito larvae in the depressions. 2. All pond radials shall be constructed with suitable equipment, preferably with a rotary ditcher. 3. To prevent drainage of a pond by muskrats or snow geese, all pond radials shall terminate at a sufficient distance from a tidal ditch. C. Ponds T. Where large numbers of mosquito breeding depressions are concentrated in a limited area, a pond alteration will be utilized. 2. Pond construction is accomplished by the use of the rotary ditcher, 'amphibious crane or other suitable equipment. 3. Ponds should be shallow, less than one foot in depth, to promote the best waterfowl, wading and shore bird use. 4. To prevent mosquito breeding during droughts, a reservoir three feet in depth shaiI -be installed within the pond. 5. These reservoirs should provide proper pond access by humans. 'then large numbers of radials are used, reservoirs are unnecessary. 6. Reservoirs for fish can be ensured,i'n natural ponds that dry out during droughts by construction of three foot ditches with a.rotary ditcher or other suitable equipment. These reservoirs will connect all the lowest areas within the pond. 7. Pond spoil should be squashed and leveled without causing depressions. It should be reduced to the lowest possible level to ensure reestablishment of existing vegetation. Spoil shall approximate the level of the existing marsh. 8. Ponds may take the shape of the breeding area or may be squared off to facilitate construction. The shape of a pond or ditch does not appreciably affect wildlife use. Depth, food potential and availability are the main factors that deter- mine wildlife utilization. Ill. OBJECTIVES A. To adequately serve the three major objectives (control mosquitoes, eliminate insecticides and enhance the tidal food web) all three alteration types (tidal ditches; ponds and pond radials) shall be utilized on each section of marsh whenever possible. Diversity provides a better marsh environment, prevents marsh surface breed- ing by all genera of mosquitoes and enhances both major branches of the tidal food web. B. Insecticide use is gradually phased out as OM14M progresses to eliminate breeding acreage. When the project is completed, all insecticide use should terminate. I`/. OTHER T. ECHNIOUES Impoundments, stop ditches and other types of management techniques are not OMWM. V. EVALUATION Mosquito larval dippings, vegetational plots, invertebrate samp- ling and wildlife censuses are to be conducted on the area treated with OMWM and compared with a control of similar composition. e ,t I t Q Maryland Delaware A 12 4) a o? U d p ? Virginia - o Q 1 N 0 20 40 km s - study areas Fig. 1. Chesapeake Bay area of Maryland showing locations of study areas. 50 M SUMMARY and CONCLUSIONS The importance of tidewater marshes in supporting complex estuarine systems is well documented. However, little or no attention has previously been given to evaluating how mosquito control practices affect the ecology of marshes along one of the most productive estuaries in the world; Chesapeake Bay. The study reported here has made a start in filling this void. In the first section of this report we evaluated three strategies of water management for mosquito control: a tidal system; a semi-tidal system; and a ion-tidal system; ai compared to an unaltered section of marsh. The systems are not new in design nor in any way innovative, but never before had the systems been comparatively evaluated as they were here. We found that in many ways, the management systems produce similar impacts. All of the management systems provided good mosquito control. All of the systems provided additional habitat for fish, shrimp and crabs, and in so doing may enhance production in the estuarine food web. All of the systems maintained good water quality, and should pose no threat to the water quality of the adjacent estuary. The use of the management systems by surface dwelling invertebrates such as Melampus snails, Amphipods and Isopods was evaluated, but no clear results were obtained. Additional time and study is needed to fully define the impact of the management systems on these invertebrates. In two important points of study we found significant differences between the three water management systems. Most importantly, we found that the tidal and semi-tidal systems display significantly lower water tables on the treated marsh as compared to the control. The closed system also lowered the marsh water table as compared to the control, but the difference was not ` statistically significant. The closed system also caused the least change in plant community zonation, whereas two of the tidal systems displayed appreciably different floral characteristics before and after ditching; with the plant community taking on a more upland characteristic after ditching. The closed system. plant community probably retained its original character due to the fact that the water table was not significantly affected by the ditching. Our findings indicate that a closed water management system, when properly applied on a natural high marsh can achieve a high degree of mosquito control and produce the least undesirable ecological effects. We recommend that a closed system management scheme be pursued when possible. However, it should be pointed out that a closed system will not be applicable to all situations. The results reported here were obtained on high S. patens/D. tens/D. spicata marshes, where the mosquito breeding is largely confined to small, randomly located depressions. In such an instance it is relatively easy to interconnect the breeding sites so that fish can move throughout the system and control mosquitoes. Mosquito control may not be achieved with a closed system on short form S. alterniflora marsh where mosquito breeding is not always confined to potholes, because, due to the low elevation of the marsh, large surface pools are often left after flooding tides or heavy rainfall. Mosquito breeding often occurs in these pools. In this case, the surface water must be drawn off to achieve mosquito control and an open or a water control system would be needed. Additional research is needed on the impact of OMWM techniques in short from S. alterniflora zone marsh. Another example of a situation in which mosquito control probably cannot be achieved with a closed system is a marsh that has been disturbed by man's activities such as diking and filling. Such practices block A natural drainage patterns and create standing water conditions which provide mosquito larvae habitat. These circumstances require an open system to effectively remove the surface water. There were no significant differences observed between the open and the water control systems in this study. Therefore, the extra time and expense required to install water control structures may not be justifiable. A rotary ditcher was found to be more efficient in excavating ditches than conventional digging equipment. The rotary ditcher also leaves no spoil piles for undesirable vegetation to colonize. However, except for the creation of spoil piles and operation speed no significant differences were noted between a rotary ditcher and more conventional equipment. The last section of this report presents results obtained in field and laboratory evaluations of the mosquito larvicide temephos (Abate R) against non-target organisms. Temephos is an organophosphate with a reported narrow range of biological activity and short residual life in the environment. It is the larvicide that is currently used to control mosquito larvae in tidewater marshes in Maryland and several other Atlantic coast states. The field test of a 5% granular formulation of temephos produced no acute toxicological effect on 6 species of non-target organisms. The laboratory test evaluated the effect of temephos on oyster larvae and spat and was the first evaluation of its kind. The laboratory test found no toxicological effect of temephos on the oysters even at several orders of magnitude higher than would be encountered by oysters in the field during the operational application of temephos to control mosquito larvae. While the above evaluations indicate that larviciding with temephos may not be environmentally detrimental, we should not embrace the technique as a panacea for mosquito control. Cost factors increase yearly with this control 1Q1 technique. Resistance in the mosquito population is likely to occur in time and there are no alternative larvicides currently available that satisfy cost, effectiveness and environmental safety requirements. Larviciding with temephos should be viewed as only a temporary measure until OMWM can be more fully implemented on Maryland's wetlands. This study, funded by a grant through the Chesapeake Bay Program, has shown that salt marsh mosquito control in the Chesapeake Bay area can be achieved in an ecologically safe manner. The study made several important contributions to more fully understanding the ecology of the Chesapeake Bay area. No previously published paper has examined the impact of a mosquito control integrated pest management program on the range of parameters examined here. This study made a significant contribution in the survey of the fish populations utilizing high marsh zones in the Bay area. The water table evaluations are unique. The impact of temephos on oyster larvae had never before been attempted due to the difficulties of performing bioassays with so sensitive an organism. However, this work was necessary to insure that using temephos near oyster seed beds would not disrupt the economically important oyster fishery industry. By participating in this study the Maryland Department of Agriculture has gained insights into the impact of its mosquito control program that would otherwise not have been possible. The future of mosquito control in the State will be influenced by the results of this study. 1 RECOMMENDATIONS 1. Salt marsh mosquito control measures should be initiated only on areas of marsh documented to produce sufficient numbers of mosquitoes to warrant control. 2. A surveillance program should be maintained to meet the above recommendation. 3. The OMWM program currently in use in Maryland should be maintained as it is the most effective and ecologically sound mosquito control technique presently available. 4. A closed system of water management should be utilized whenever con- ditions permit mosquito control to be achieved without surface water drainage. 5. When surface water drainage is required to provide mosquito control, ditching should be kept to a minimum so that water table elevations will not be altered more than necessary. 6. A rotary ditcher should be used when possible. 7. Larviciding with temephos should continue on mosquito breeding marshes not yet under the influence of OMWM. This larviciding must be co-ordinated with a sophisticated surveillance program. 8. Research on the impact of OMWM on salt marsh invertebrates should be continued. 9. Additional research on the impact of OMWM on waterfowl and submerged aquatic vegetation should be initiated. 10. Additional research on the impact of OMWM on short form Spartina aiterniflora zone marsh should be initiated. .y 1! °? 11 A 4 1979 1980 N Pvs f - -t-r ct. -- --. EFFECT OF OMW ON A?DF ES_ SOLLICITANS BREEDING - DAVIS ISLAND STUDY SITE 1917 ere b 0 O FA N rt rt (A (D :j 0 A 0 . FA FA o v rt v r i O H .? N o ? Obi In N r N O V N Cl 0 0 Co w I lJt V rt ig Po H M O rt o N F? rD O P rt M C6 0 0 w 4 ? :3 a0 w . cr W r r! O r rn r V w m w o w in .A a rt W to V I- O oQ :3 O ilm w a, 0 0• rt m w cY rt CO) cr co 0) "0 t-t w 0 K rt w0 n0 H (v Fj N D ( H W 0 H N A) F-, 10 cn N' aH a ? y t+ H P. r? W ?y ?+ Fa aH ri 10 : H 1-4 F-• F-U W H F-' F-4 }j• N W (D (D 03 N n (D 0 0 (D (D 0 0 (D 0 O 0 F- L4 14 k4 FA- I-A. 1-4 F4 W W 0' FL. w a' w ~' a rt (A O N N y ril 1r ? O O O ? f7 ?O r00 NV NV n O O'4 r N to d CO O N O a` t` O F O O O N %0 co LA ON 00 O to O\ P. LA ? O O 00 W !-? llt N N ON V W (D P- n rt w F? m O 100 O Fit 0 O F'• rt O F-j N n C w (D 0. N rt W M O K w .o V r a V rt O rt r v I (D rt H O A> P. O rt L; t3. 0 w Table 9. Quantitative mosquito larvae data. July 6, 1979. Estimated no. of Plot No. larvae per 0.018M2 mature larvae per HA Deal Is. Closed 3.1 2085 Deal Is. Water Control 0 0 Deal Is. Open 0 0 Control (1) 31.6 88,243 Fourth instar larvae and/or pupae Aedes sollicitans 64 Effect of a closed system of OMWM on Aedes sollicitans breeding in short form Spartina alterniflora June 1 to August 31, 1981 Greens Island marsh study plot No. of larvae collected per 50 dips Sample Surface Time Ditches Water Pools Control 1 3 N.D. 385 2 0 N.D. 300 3 26 N.D. 752 4 74 N.D. 47 5 0 84 18 6 66 52 103 7 or 0 0 8 0 0 0 9 210 330 53 10 430 783 0 11 50 263 1,485 12 0 16 230 13 79 70 1,323 14 18 3 0 TOTAL - 956 1,601 4,696 No. larvae/dip 1.37 3.20 6.71 1 way analysis of variance Source Degrees of Freedom Sum of Squares Mean Square F Total 37 4,498,430.34 Treatments 2 512,405.16 256,202.58 Error 35 3,986,025.19 113,886.43 2.25 MARYLAND DEPARTMENT OF AGRICULTURE OFFICE OF PLANT INDUSTRIES AND PEST MANAGEMENT MOSQUITO CONTROL DAILY SALT MARSH INSPECTION REPORT FLOODING INSPECTION RESULTS Station oad.• De th No. Dips Est. No. Larvae/Di Breeding Extent Species Sta e COUNTY DATE FLOODING CONDITION D - Station dry P - Depressions holding water F = Marsh flooded KEY # LARVAE/DIP 0 0 1 1-3 2 = 4-10 3 11-30 4 31-100 5 100+ INSPECTED BY BREEDING EXTENT 0 No breeding 1 Isolated breeding 2 Scattered 3 Widespread breeding MDA-D-523 (3-80) Y .. '._ ,?:.•` ^. .;..r .. t?*I .?? fall .. IP4 M 1 T • j¦ ?y ;x li.,ak. '? n y y'Q'!'• ..y, '? Xq' •7+ ^ ? 9? '?`4. 'a<^".., k 1?:. •a.• y Y i• p if dy1. ,1'4b,?. i.4! !:ems 5 { - ,. ; ; ,?:, E - ? `? y •• !.W a 46, '' 4•, 4 4 'A1A ` '•55 esq. , ' , ; sa / r 6 Ak I 'P r 1.? A'' 4 4?Mtd S e Ci R, ' 'N '?+ ,,gam ° A t ?' `? • ` z. ,,hh ?' `' t ? r ? ? `?y . ?? " , .. , 4.. T •p1 .... ,t Y •'+5- .'.b?} ?' y t 1 '?.? n ? >'r. P`a.. r fS?rS -4 !?'? tax, 3a ?n ,1 R p ,. ? ? ,., Y'; : ? .. J ?,?•?.?x yr } st > ¦ ?.? ? by y.' ,` ? ? j ?lY? J? ! „ 1` i" \:;; ? v. ? `?r y I? '?j? `}l, ? t ? ` ice' dq Hitii??'?99,,• -, ? ( 1!z .t } lo- 9 },:? A?? ^f y `'?'. Y +§ ? ??. ?/?.aR? "w w r_ , p M '?X OF JN?"ED STgr? lk.r?-?' s YAW O ? tl y a U N I D S A N IR M AL PROTECTION AGENCY 'Ti?,?rgC PRO'?R E G O N I V 345 COURTLAND STREET ATLANTA. GEORGIA 30365 DEC 0 g 198, Mr. Charles W. Hollis DEC' I981 PERMITS AND ENGINEERING Chief, Regulatory Functions Branch U.S. Army Corps of Engineers, Wilmington P.O. Box 1890 Wilmington, North Carolina 28402 Dear Mr. Hollis: ?? ? ?? ? 8 1981 WATER QUALITY , This is in response to the meeting of November 18, 1981, regarding Open Water Marsh Management for mosquito control in North Carolina marshes. Our understanding of the material presented is that: 1. The system is proposed only for those marsh areas where Distichlis s icata and Spartina patens represent the predominant vegetative species. 2. The optimal equipment for use in this system is the rotary ditcher propelled by a tracked vehicle which exerts less than 2.5 psi on the marsh. 3. -Larval surveys are the most accurate method of determining the necessity for implementation of such a program. 4. A 200-acre site has been selected by the Pamlico County Mosquito Control Commission for a test program. An additional 200-acre marsh adjacent to this would be used as a control. 5. It is difficult to predict the extent of necessary marsh alteration, depth of ditches and possible changes in water table levels. 6. The system should be.connected to open water for maximum effectiveness. 7. Open Water Marsh Management is an effective system of mosquito control which would reduce Aedes solicitans breeding areas and subsequent use of insecticides. 8. The Raleigh office of the U.S. Fish and Wildlife Service has offered to directly supervise the work in the test area. 2 The Environmental Protection Agency requests that an application for a permit authorizing a test program on the 200-acre site near Hobucken in Pamlico County, North Carolina, include: 1. A detailed physical description of the proposed work. 2. A description of methods and equipment to be employed, with particular attention to the psi to be exerted on the marsh. 3. A monitoring program to measure effects of the proposed work on: a. Water table. b. Indigenous vegetation. c. Aquatic and terrestrial organisms. d. Dissolved oxygen and nutrient levels in connector ditches. e. Larval populations of Aedes solicitans. In our opinion, the above information is necessary to afford this office an opportunity to fully evaluate the proposed test work. Sincerely yours, E. T. Heinen, Acting Chief Ecological Review Section Environmental Assessment Branch cc: Ms. Mike Gant, Field Supervisor U.S. Fish and Wildlife Service Raleigh, North Carolina Mr. Robert F. Helms, Director North Carolina Division of Environmental Management Mr. L. P. Benton, Jr., Chief, Environmental Operations North Carolina Department of Natural Resources and Community Development Mr. Preston Pate, Chief, Field Services North Carolina Office of Coastal Management Mr. Stuart Critcher North Carolina Wildlife Resources Commission Mr. John Parker, Permits Coordinator North Carolina Office of Coastal Management Mr. Randy Cheek, Area Supervisor National Marine Fisheries Service Beaufort, North Carolina Mr. Harold B. Allen, Acting Regional Director National Marine Fisheries Service NtED S 1qr? o s n o c UNITED STATES ENVIRONMENTAL PROTECTION AGENCY Zy. ?, ??r4< PRW"S` DEC 0 3 1961 REGION IV 345000RTLAND STREET ATLANTA. GEORGIA 30365 Mr. Charles W. Hollis Chief, Regulatory Functions Branch U.S. Army Corps of Engineers, Wilmington P.O. Box 1890 Wilmington, North Carolina 28402 Dear Mr. Hollis: WA rFR QUALII Y ?oort d /NM 17L /?••+!7 l9,n?is r a,,? W /.y/r2 n r 23 191 PER fglrs 4Nt? Fhu1"1FER,r?? This is in response to the meeting of November 18, 1981, regarding Open Water Marsh Management for mosquito control in North Carolina marshes. Our understanding of the material presented is that: 1. The system is proposed only for those marsh areas where Distichlis spicata and Spartina patens represent the predominant vegetative species. 2. The optimal equipment for use in this system is the rotary ditcher propelled by a tracked vehicle which exerts less than 2.5 psi on the marsh. 3. -Larval surveys are the most accurate method of determining the necessity for implementation of such a program. 4. A 200-acre site has been selected by the Pamlico County Mosquito Control Commission fora test program. An additional 200-acre marsh adjacent to this would be used as a control. 5. It is difficult to predict the extent of necessary marsh alteration, depth of ditches and possible changes in water table levels. 6. The system should be.connected to open water for maximum effectiveness. 7. Open Water Marsh Management is an effective system of mosquito control which would reduce Aedes solicitans breeding areas and subsequent use of insecticides. 8. The Raleigh office of the U.S. Fish and Wildlife Service has offered to directly supervise the work in the test area. i 2 The Environmental Protection Agency requests that an application for a permit authorizing a test program on the 200-acre site near Hobucken in Pamlico County, North Carolina, include: 1. A detailed physical description of the proposed work. 2. A description of methods and equipment to be employed, with particular attention to the psi to be exerted on the marsh. 3. A monitoring program to measure effects of the proposed work on: a. Water table. b. Indigenous vegetation. c. Aquatic and terrestrial organisms. d. Dissolved oxygen and nutrient levels in connector ditches. e. Larval populations of Aedes solicitans. In our opinion, the above information is necessary to afford this office an opportunity to fully evaluate the proposed test work. Sincerely yours, E. T. 4inen, Acting Chief Ecological Review Section Environmental Assessment Branch i cc: Ms. Mike Gant, Field Supervisor U.S. Fish and Wildlife Service Raleigh, North Carolina Mr. Robert F. Helms, Director North Carolina Division of Environmental Management fir. L. P. Benton, Jr., Chief, Environmental Operations i/ North Carolina Department of Natural Resources and Community Development Mr. Preston Pate, Chief, Field Services North Carolina Office of Coastal Management Mr. Stuart Critcher North Carolina Wildlife Resources Commission Mr. John Parker, Permits Coordinator North Carolina Office of Coastal Management Mr. Randy Cheek, Area Supervisor National Marine Fisheries Service Beaufort, North Carolina Mr. Harold B. Allen, Acting Regional Director National Marine Fisheries Service DEPARTMENT OF THE ARMY WILMINGTON DISTRICT. CORPS OF ENGINEERS P. O. BOX 1890 WILMINGTON. NORTH CAROLINA 28402 SAWCO-EE IN REPLY REFER TO 15 January 1982 Mr. Russ Talley N.C. Water Quality Section Division of Environmental Management PO Box 27687 Raleigh, NC 27611 Dear Mr. Talley: 1a;7? PE'RMEtS dEw ? This letter is a follow up to the meeting on open marsh water management (OMWM) held on 18 November 1981 in Raleigh, North Carolina. As you will recall, the morning session consisted of presentations on OMWM activities in Maryland, New Jersey, and Virginia and the afternoon session consisted of a question and answer period. The major thrust of this letter is to indicate what we feel is a reasonable and feasible approach to determining the biological impacts of the proposed pilot project on the marsh community. Other impacts on the environment requiring investigation will be discussed in future correspondence. The 18 November 1981 meeting and the scoping meeting held in May 1981 made it clear that detailed monitoring to determine biological impacts of the project will be required both before and after OMWM activities on the proposed project site and a nearby control site. Monitoring would include: a.. Describe in detail the purpose and need for the project. Also describe how OMWM would be implemented with special emphasis on the type of equipment and its bearing force on the marsh. b. Document mosquito breeding sites on the proposed project area and control site. (1) Stake locations of breeding sites. (2) Map location of breeding sites. (3) Overlay proposed OMWM pattern on mapped breeding sites (not required for control site). TEW ' : ;s SAWCO-EE 15 January 1982 c. Map existing vegetation and monitor any changes in productivity and species that occur following project completion. An example of a method ..that could;be used to measure productivity is by sampling end of growing season live standing crop in meter square quadrats along several transects .lines. 'Species change could also be noted in adjacent .quadrats, d. Monitor water level changes in the marsh soil before and after the proposed: project. This can be done by establishing several PVC shallow wells along the transects mentioned in "c" above. e. Determine elevation of marsh i s reams an ditches. This will be used to determine possibility of lowering marsh water table levels. These elevations should also be tied into a benchmark so that subsidence if any of the marsh can be measured following ditching. f. Monitor changes in fish and invertebrate use of the area. Fish can be periodically sampled by seining the ditches and seining or trawling adjacent creeks. Invertebrates ma b 14 , n a so y taking random samples in the ditches. g. Use of the area by terrestrial species should also be documented. h. Routine water quality parameters _(temperature, salinity, dissolved oxygen, pH, and turbidity) should be taken when fish and invertebrate samples are taken. A question that has arisen during coordination on this project is whether or not alteration of marshes by OMWM will promote nutrient enrichment of "downstream" estuarine areas. Several possible methods of addressing that question are listed below for your consideration. However,,in discussions with Dr. Sam Mozley (NCSU) and Dr. Ed Kuenzler (UNC-CH) it has been suggested that OTMNI probably will shift the locus of decomposition of particulate organic matter originating in the marsh from "downstream" estuarine areas to the marsh itself. If this does occur, significant increases (if any) in downstream nutrient concentrations"would not be expected as a result of marsh alteration via OMWM. Dr. Mozley indicated that this type of change has not been associated with environmental problems to date. We request that you consider this aspect before formulating your comments on the monitoring alternatives for nutrient flux measurements which are listed below. It's possible that nutrient flux measurements are inappropriate with this type of project. 2 SAWCO-EE 15 January 1982 Direct measurement of changes (if any) in nutrient flux before and after project construction at the project site and control would be logistically difficult. The project area is dominated by unpredictable wind tides and lunar tides are not significant. Therefore, reliable measurements of nutrient exchange between the estuary and marsh would require automatic samplers, recording gages, and personnel onsite prepared to pick up samples from the automatic samplers immediately after wind tide events. Perhaps nutrient exchange could be inferred indirectly if vegetation was monitored as indicated in part "c" above (i.e., greater productivity, more nutrient availability). Even this could present problems. If the ditch bank productivity was higher after construction than before, this could be interpreted in several ways. Increased productivity could be attributed to nutrients coming in from the estuary. On the other hand, more nutrients could be available to the marsh plants because the ditch banks are better drained, soils become more aerobic, and thus toxic materials blocking nutrient uptake are removed. (Mendelssohn, I. A. and E. D. Seneca, 1980, The influence of soil drainage on the growth of salt marsh cordgrass (Spartina alterniflora) in North Carolina. Estuarine and Coastal Marine e- nce 11: 27-40. Sci s Another possible method to indirectly infer nutrient flux is to sample for phytoplankton (counts and identifications) and chlorophyll (a) levels at the proposed site and control before and after project construction. Phytoplankton (counts and identifications) and chlorophyll (a) levels may indicate changes in nutrient input to the ditches and creeks due to OMWM. We would appreciate your comments on the above monitoring procedures by 5 February 1982. On another subject, Mrs. L. J. (Mike) Gantt with the U.S. Fish and Wildlife Service and.Mr. Cyrus Lesser, Maryland Department of Agriculture, suggested that a Technical Review Committee be established similar to that created in Maryland for review of OMWM projects. The committee in Maryland consists of interested Federal and State agency representatives and other individuals with additional expertise that is needed in project review. If this process was adopted in North Carolina, we foresee that the committee's function would be little different from the processing of a routine Corps permit action. Routine processing involves review of the project via our public notice procedure by interested citizens and representatives of Federal, State, and local agencies. The major difference would be that a particular individual within an agency (and not the agency in general) along with specific individuals with additional expertise would be assigned to review all OMWM projects. If you are interested in serving in such a capacity, please let us know by 15 January 1981. 3 4