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HomeMy WebLinkAboutThe Premium - An Endangered Waterway 8/1/1977 • THE PREMIUM - AN ENDANGERED WATERWAY By Robert E. White, P.E. ,. "1• .a,{', „•''v', 1'^!i�'t(,,4 r'+ ,.. ,,I,.,,;.Y ,rte ,,'---7,0"--.!..., �,..n...1i1�.M► ,���*..N.,•'±�'i• y. . ),I, • %*., h •.�r; �..�,�'?.a•1F mak, y " �, .\• 1 5 .{;ASf''li f. .� .2 a ,��h ' ± r� . '4'..,:.,P, jets l�l.f�� ~ +1 �, •• i'•'$.406','• ,� ` . .,fix* • << ` { d iii d a a' 1 ,�rf,l.. r�C ' ,. .,r l } ,. •1 rA VRA i�*l fit,�4'Cfd y r• - �..r !. f�ryISSk . �t tira a?$1g ' ,j 4.-,i ",` ' rSSc.S; � 31."'�,)1- 1., r" .'. .., , i r,�'i.hrci'�+kr Yr4c.:f h1,_r� 1t h r s ,'� ,._.�. F :.a.1' t wr )I '" j`''rF ',.•.s 7t d . 1� baa •••• :M,,` tt ,f � i•'. I Premium Marsh—Larchmont, New York • August, 1977 Table of Contents Page Introduction and History 1 Damage Suffered by the Waterway 3 1. The Premium Mill Pond 3 2 . The Premium River 5 Why the Premium Should be Restored 7 Proposals for Saving the Waterway 9 1. The Premium Mill Pond 9 2. The Premium River 10 Sedimentation & Flooding 11 Drawing up a Plan 12 Financing the Project 12 Conclusion 13 Acknowledgments 14 References 14 Appendix Figure 1, Map of the Premium Waterway Figure 2 . "Mud Cat" Dredge THE PREMIUM AN ENDANGERED WATERWAY Robert E. White, P .E. Introduction and History The "Premium" is a tidal estuary of Long Island Sound in Southern Westchester County. It consists of a winding stream, the Premium River, and a lower body of water, the Premium Mill Pond. The River meanders from the Boston Post Road in the Village of Larchmont down to the "Red" Bridge at Pryer Manor Road in Larchmont and New Rochelle. Below the "Red" Bridge is the Mill Pond which was formed by an old rock dam thrown across the mouth of the estuary between the mainland of the City of New Rochelle and the peninsula known now as Premium Point. An even older dam had existed since prior to 1741 at the site of the present Red Bridge when the Palmer family, which owned a large manor in the vicinity, used the impounded tidal waters to provide power for the first Premium Grist Mill. The Palmer farm house burned and was rebuilt in 1776 by James Mott who had purchased the property and operated the mill. This farm house is now a residence; it is the oldest ' building in the Village of Larchmont and has been designated as an historic building by the Daughters of the American Revolution and is so marked by a plaque. James Mott' s grand- father ' s grandfather was John Richbell who in 1661 bought the entire area from the Siwanoy Indians . (1, 2) The waterway being relatively narrow above the first dam site, little power could be generated and so in 1801 the Motts built the present much larger dam. At the dam was installed one of the largest flour mills in the country. Drawings show a tall millhouse at the Premium Point end of the dam; the mill was equipped with twelve large grindstones . It was operated by the Mott family and successors until the 1880 ' s . From an ecological point of view, it is interesting to note that in 1855 the Mill Pond was leased "for planting and then removing oysters . . . . " And even earlier than the white man' s works were the stone and log weirs believed to have been built by the Indians to trap fish running with the tide. (3) The Premium River has two branches, the East and the West, whose confluence is at the foot of Willow Avenue in Larchmont. The part of the East Branch which is affected by tides (up to the Post Road) is often known as Pine Brook (see Village of Larchmont maps) and certainly, above the Post Road this stream is known as Pine Brook. About 45 years ago, Pine Brook was forced to run in a rectangular reinforced concrete box culvert whose mouth, about 4 feet high and 8 feet wide, can be seen on the south side of the Post Road at the west end of Kane Park. The rough crest of the overflow section of the old mill dam is at an elevation of about two feet below high tide in New Rochelle harbor so that the normal rise and fall of tides in the Premium Mill Pond and River is also about two feet. The dam also serves as the foundation for a bridge and causeway which is the access that Premium Point residents have to the mainland. About 40% of the shoreline of the Premium River is public property: the nature preserves of the Town of Mamaroneck, the Village of Larchmont playgrounds and parks - Lorenzen, Willow and Kane - and Larchmont streets that dead end at the River. These streets are Jochum, Elm, Chestnut, Oak and Guion. There is also Red Bridge. The remaining 60% is bordered by private residences and lands . The Premium River Conservation Area of the Town of Mamaroneck is mostly a "high" tidal marsh and has been the subject of considerable study by environmentalists . (4 , 5) Formerly, part of the Conservation Area and Lorenzen play- ground were municipal dumps as recently as the early 1960 ' s when awareness of the value of the tidal marshes forced the cessation of dumping at these locations , The Premium Waterway is in many ways a most valuable asset to the public and also to the neighboring property owners . Some of its valuable features are: scenic. The winding stream opening out into the Mill Pond affords some of the most beautiful waterscapes to be seen anywhere, especially in an urban setting. recreation. The Waterway is - in many cases , was - the site of a number of activities : fishing, bird-watching, ice skating, canoeing and boating and even sailing (on the Mill Pond) . Formerly there was also crabbing and swimming. -2- - tidal marshlands . These are now universally re- cognized to be extremely valuable in support of fishing and bird life, cleansing of polluted waters, flood alleviation, and as an educational resource. - it is a wildlife conservation area. Arbib, of the Laboratory of Ornithology, Cornell University, states that the Sound shore of Westchester is one of the routes for migrant birds and thousands of ducks and geese winter in the bays and inlets . And he cites as one of "the best lookouts . . . Premium Point, New Rochelle-Larchmont" . (6 , p. 100) John Bull of the American Museum of Natural History, felt the area "was unique from a wildlife standpoint for an area so close to the City" . (7) However, over a period of time and especially the past two to four years, it has become obvious that the Premium River is silting up at a rate that has recently become quite alarming and this seriously tareatens to wipe out the tidal wetlands and other valuable features outlined above. Pollution from oil and sewage is also having a very detrimental effect. On June 19 , 1977 a group of concerned citizens made up of owners of residential property bordering the River met to see what could be done to arrest and, if possible, reverse the destructive sedimentation occurring in the bed and along the banks of the River. This group at its organization meeting informally adopted the name of "The River People" . After considerable discussion it was voted that a report on the various aspects of the Premium Waterway problem be prepared; the writer of this paper was elected to do this . Subsequently, at a regular meeting on July 7 , 1977 in White Plains of the Westchester County Soil and Water Conservation District, the Chairman of the District, Mrs . Edith Read, also suggested that a report with proposals be submitted looking to possible assistance under Public Law 566 . Assistance under P .L. 566 could be technical and/or grants of money or credit. P .L. 566 is titled the "Watershed Protection and Flood Prevention Act, as Amended" . Damage Suffered by the Waterway. 1. The Premium Mill Pond The Mill Pond has seen deposition of fine organic clay particles over the past two centuries . Except where scour due to swift currents has taken place - at the "Red" Bridge and at the dam-bridge-causeway - the Mill Pond is now about -3- 1-1/2 to 3 feet deep in most places. Because of their firm- ness, the particles of sediment tend to remain for a long time in suspension and most of them are carried out by the tides into New Rochelle harbor. The net effect, however, over the years has been the raising of the bottom of the Mill Pond from what must have been low tide level in the pre-Mill Pond era to its present shallow state. (Normal rise and fall of the tide in New Rochelle harbor is about 7-1/2 feet. ) The shallowness of the Mill Pond and the slow currents over most of its area is encouraging the prolific growth of the "sea lettuce" type of algae. There are two effects of sunlight at work here which encourage growth: (1) the ultra- violet rays penetrate to the bottom and (2) the water in summer is warmed to perhaps 80° or more. The algae crop matures in May and June and comes loose and moved by wind and tide, floats up and down the Waterway. During low tide, where the algae gets stranded on mud banks and flats in the River it becomes a silt catcher lending to further sedimentation; the stranded algae also bakes out under the hot summer sun and stinks. It is also a nuisance to boaters whose oars and propellers become fouled. . . . algae blooms may deplete water of oxygen to such an extent that fish and other living organisms die" . (Statement of Dr. Robert DeSanto, Assistant Professor of Zoology at Connecticut College, 1970 Senate Hearings on "Preserving the Future of Long Island Sound) "Complicating matters further, after the algae bloom has run its course, it is decomposed by bacteria at the river bottom. The bacterial action uses up oxygen from the water. If the amount of decomposing algae is sufficiently great, the bacteria will remove so much oxygen that fish and other forms of life will sufficate and die . . . " (8) It is observed at every low tide during the summer months that the Premium River turns very turbid with a reddish-brown color, no doubt caused by some sort of algae. At the south east corner of the Mill Pond there is a narrow neck of beach connecting what must have been Premium Point in geological times past when it was an island, to the Larchmont mainland. Along this neck, the Village of Larchmont owns a "beach lot" and immediately to the west the Town of Mamaroneck owns 150 feet of sandy beach. In 1933 , the writer remembers , a paved road crossed this area; alongside the road, on the Mill Pond side, was a stone wall whose northern side -4- was lapped by the waters of the Pond. Since 1933 , storm waves have removed sand from the beach on the Long Island Sound side and deposited it on top of the road and on into the Mill Pond where it forms a pile an estimated three feet thick by 250 feet long by 50 feet wide thus slightly diminishing the area of the Mill Pond. The implications of this are discussed later on. 2 . The Premium River The Premium River is silting up for almost its entire length. Various types of deposition are taking place. For example, not far upstream from the Red Bridge where the River widens out between the foot of Guion Lane and the 1776 Mott Mansion mud flats have formed in the center of the stream. These mud flats, since two or three years ago, have become visible at every low tide. Formerly, they were visible only on rare occasions of exceptionally low, low tide which were allowed by the leaky condition of the old Mill Dam. Deposition has also taken place on the western shore. One result of this is that it is difficult, if not impossible to launch a row-boat at low tide from some properties on Wildwood Circle and on Guion Lane where this was formerly possible. Another evidence of this is the fact that formerly ice-skating and ice-hockey were popular sports when the weather permitted. Now this is not possible as the ice will not form on water which is over a mud flat which is exposed at every low tide. What was an area big enough to accommodate a hockey game is now only large enough for cutting tight figure-eights . Silting also takes place along both banks of the River; in certain cases there are stone sea walls which used to have a foot or two of water at their bases at low tide. Now they are many feet from the water and marsh grasses are growing along the bases of the sea walls . These grasses trap sediment which leads to further growth of mud banks and eventual destruction of the stream or the acceleration of the natural evolution to grass to shrubs to trees. Another result of the silting up of the beds and banks of the River is to diminish the amount of water in the stream with the consequence that the remaining water at low tide becomes a thick, murky dark brown with a strong odor. It will not even support eels which were once plentiful in the River, but which are now disappearing. Before the eel population -5- was all but destroyed, crabs of the blue, fiddler and horseshoe varieties were made extinct. Yet they were so plentiful 25-30 years ago that it was a common pastime of the neighborhood youngsters in rowboats or walking along the sea walls to catch blue crabs with dip nets. Opposite the writer' s home there always used to be a resident king fisher. Since last year he is gone. No doubt there isn' t enough River food available to him. Sedimentation, a recognized form of pollution, has also been documented by Dr. James M. Utter, Assistant Professor of Natural Sciences, SUNY, Purchase, N.Y. in a report (4) on work done in 1973 on the Premium River and two other local salt marshes. Dr. Utter' s report should be read in its entirety by all interested, but here are a few quotes from the report. "Premium is filling in with sediment. . . . The primary concern . . . is increased sediment runoff from adjacent areas onto the marsh. Two possible sources are apparent: the house construction activities on and near Dillon Road and the operation of Tony ' s Nursery on the Boston Post Road where large mounds of topsoil are stored . . . Preliminary analysis . . . and the mapping of surface sediments (Figure 4) [which shows deposits of sand, clay, organic muck & shells at the confluence of the east (Pine Brook) and west branches of the Premium] clearly indicate a present source of inorganic material is the Pine Brook watershed. " Other sources of documentation of sedimentation could be: photographs of residents in the area; aerial photographs especially those taken at low tide; topographic data from surveys made about 25 years ago by the Westchester County Department of Public Works in connection with construction in 1954 of the large sewer crossing the River and leading to the sewage treatment plant in Echo Bay. New Rochelle; the Bachelor ' s thesis of Morein Cohen (5) . Dr. Utter (4) has also investigated the coliform pollution of the Premium and found it to be extremely high: "Samples were taken at or near high tide, [therefor] dilution of any polluted in flow is maximum and thus bacterial concen- trations are minimum if the imput is continuous. " In other words, if the pollution were to be measured at low tide, it would be found to be many times worse. "Data from the Premium Area show consistently high coliform counts . . . the range in concen- trations was . . . nearly 3 times the sanitary code limits for -6- a bathing beach. . . . The significance of the coliform levels should again be emphasized. They are indices of the level of raw sewage contamination [which] is a public health problem because of the pathiogenic organisms that can be passed in fecal material which may then reinfect humans through the oral route or wounds . Such pathogens include: [here Dr. Utter lists 10 viruses among them polio, hepatitus and salmonella] . " In his report, Dr. Utter also says that possible sources of contamination are broken sewers and malfunctioning septic systems. Also in the Utter report, oil and lead pollution are mentioned as problems . The significance of this should not be lost on the City of New Rochelle because the Premium discharges its contami- nation into New Rochelle Harbor from which littoral currents can carry it to New Rochelle beaches and to Larchmont and Mamaroneck beaches as well . The Premium River at present is also disfigured aesthetically by various kinds of debris which have been allowed to accumulate over recent years . Such trash consists of dead branches and limbs of trees , cuttings, shopping carts , beer cans and other natural and man-made junk. Many of these objects are silt-catchers and aggravate the sedimentation problem. They also interfere with boating - and fishing, if there were any fish. Why the Premium Should Be Restored The Premium River, its adjoining marshes , open spaces and the Mill Pond are priceless scenic and environmental assets . Every such body of water is unique and has its own special qualities . Premium is unique in its beauty and the wildness of its marshes in an urban setting close in to the Metropolis . It has historical importance and the other qualities barely touched upon in the introduction to this paper. Any diminution of its assets diminishes us all spiritually and also financially. In the latter respect it may be instructive to read the testimony of a Connecticut real estate broker given at the Hearings on "Preserving the Future of Long Island Sound" (8) . The broker, Mr. Peter Millares was being questioned by Senator Charles Mathias of Maryland: -7- "Senator Mathias. Would you say that the proximity of that beach has some impact on residential values in that area? Mr. Millaras. It certainly does . Any of our shore front or beach property naturally carries a good value to it. Senator Mathias . If conditions in the Sound were allowed to continue to deteriorate, so that a film of oil and debris accumulated on the beach, would that have a significant impact on property values? Mr. Millaras. It certainly would. We find that water - so-called waterfront properties up into the higher reach of the Thames River have lost their value as waterfront property because of this condition. People no longer consider paying a premium for water- front property of which they' re not able to enjoy as you would waterfront property as we would like to understand it to be - a clean beach, clean sand, and a place that you and your children and yourself may bathe. Senator Mathias . In your judgment as a realtor and member of the business community here, will this ultimately have a deteriorating effect on the local tax here on these properties? Mr. Millaras . It will. It will follow. The base, the tax base, will have to be lowered as the values diminish. " Other authorities may be cited, authorities who specifically refer to the Premium area. Utter (4) : "Due to the importance of wetlands in the economy of ecosystems , it is critical that they be protected. This has been recognized on a state wide level by the Tidal Wetlands Law. . . . Their protection will be dependent upon wise use and control of the entire watershed of which they are a part and the channels connecting the marshes to the open estuary. " Raymond & May, professional planning consultants (9 , p. 125) : "The areas . . . represent the finest natural areas -8- • in the Town , . . The entire proposed preserve area is a natural asset and should not be permitted to be developed for private purposes. " *Alas, along the west bank of "Pine Brook" this development by the nursery to the great detriment of the area has been allowed to take place. Review Committee of the Town of Mamaroneck (10 p. 93) : "Recommended Action of Master Plan [Raymond & May, 1966] is "still a desirable objective" . Larchmont League of Women Voters , In its planning consensus of 1968 which was based on the Raymond & May Master Plan it "supports Raymond & May proposal relating to . . . 3 . Premium Mill Pond acquisition. " The LWV' s of Larchmont and Mamaroneck reached, in 1971, a consensus on recreation and pointed out that no action had been taken on many recommendations such as "application of open space act provisions to preserve large open areas; joint development by the Town of Mamaroneck and the Village of Larchmont of the Premium River area for conserva- tion and recreation; and development of existing beach land into a Premium Beach Conservation Area" - and this seems to be the stand of the League at present as well (11) . • Proposals for Saving the Waterway. Many actions may be taken regarding the problems of the Waterway and no action may be taken at all, To the author, the latter course is unthinkable and so a proposal is made for each aspect. These proposals are those of the author whose background is that of a civil engineer with the merest smattering of knowledge of ecology. The author hopes that these proposals and this paper will provide a spring- board for discussions leading to fruitful action. 1 , The Premium Mill Pond. Where the storms have spilled sand into the Mill Pond (Area "A" on Fig. 2) this sand should be excavated from the Pond and placed on the now somewhat rocky Long Island Sound beach to improve the Village and Town-owned beaches. This sand shifting can be done rather cheaply, without the necessity for hauling or disposal off-site. A dragline operating on firm, dry land, together with a bull-dozer can quickly do this grading at a small expense per cubic yard and with negligible disturbance to the Pond and neighboring property owners . * Raymond & May even suggested a small boat dock, a tea house and garden, and a music pavilion opposite Woodbine Park. • -9- Concerning the algae, it is proposed that a large valve or sluice gate be built into the existing dam. This sluice gate would allow the Mill Pond to be drained at the time when the algae blooms . When the wind and tide are right, the algae would be carried out into Long Island Sound where it would present no problem compared to what it does in the com- paratively tiny waters of the Premium. It is believed that this sort of thing is done at the Van Amringe Mill Pond in Greenhaven in Mamaroneck and Rye. 2. The Premium River The lower reach of the Premium (designated as Area B) should be dredged out by hydraulic dredge, preferably of the locally available Mud-Cat type which measures 8 ' x 31 ' with a 21" draft and is highly portable (Fig. 2) . The depth to which dredging is done should be about 2 feet below mean low water with shaping of banks to lesser depths . Disposal of spoil should be done within pumping distance capacity of the dredge, which with a Mud-Cat, is about 1600 feet. Disposal otherwise would be very difficult and costly. One means, used in the past but no longer available , is dumping in the Sound off Eaton's Neck. Another would be to tow the spoil to the Atlantic Ocean, but this is prohibitively expensive. A third method of disposal that has been suggested is filling in some ravine upstate or in Connecticut; this may bear investigating, but it too obviously is not cheap. A fourth possibility that has come to light only in the past few days is that of disposing of the spoil on islands that may be built in Long Island Sound off the Connecticut shore. The purpose of the islands is to provide recreational and conser- vation areas, By cooperation and coordination in this venture the spoil from the Premium dredging would only have to be moved a short distance with resultant economy. Disposal of spoil in the Mill Pond has the advantage of (1) low cost and (2) an extremely valuable tidal wetland can be established using this spoil . It can be stated, I think, without fear of contradiction that tidal wetlands are valuable on many accounts and this has led to many states , including New York, to enact legislation for saving all existing tidal wetlands, It follows , therefore, that if means can be found to establish new tidal wetlands , this would be a very desirable thing to do. Fortunately, as suggested by Dr. Utter (foot-note p. 42) , there is a firm, Environmental Concern, Inc . , specializing in salt-marsh building that has had much success -10- since 1972 in this new specialized field, including a one-acre salt marsh in a Greenwich, Conn. tidal pond at Greenwich Point (1974) . This is a rapidly expanding field now that the feasi- bility of establishing tidal marshes has been proven. One example of this is that the Corps of Engineers Waterways Experi- ment Station "is engaged in a five-year, $30-million program to explore new, ecologically sound uses of part of the 380 million yards of sediment the Corps dredges up each year. " Dr. Conrad J. Kirby, head of the Station ' s environmental effects laboratory said, "If we can find the uses that blend into natural wildlife systems, such as using spoil, . . . that ' s the kind of thing we ' re aiming for. " (12) The middle and upper reaches of the River have received and retained sediments that are predominantly sandy (4 , 5) . As such, they are free-draining and would make excellent fill if nearby, convenient areas could be found to accept such fill. Two areas immediately adjacent to the Premium River are the Village parks, Lorenzen Ball-field and Woodbine Playground. Preliminary to receiving the sandy sediments dredged from the IIM bed of the Premium, the top soil in these parks could be bull- dozed into a pile. After the dredged spoil was deposited and • graded, the top soil would be spread on the spoil foundation and re-seeded. These recreation areas would not be taken out of service for a great length of time. Much of the Lorenzen Ball-Park is at quite a low elevation and is subject to flooding; therefore raising it a couple of feet would be a distinct improvement. It is possible that Lorenzen is a large enough area for receiving dredge spoil so that Woodbine Playground would not have to be used for the same purpose. Sedimentation & Flooding . A separate problem has already been brought to the attention of the Westchester County Soil and Water Conservation District by Mr. Fred Kellogg, Village Engineer. This is the flooding of homes along Pine Brook north of the Boston Post Road. Recurrent flooding here has caused much damage and anguish in the past (14) . The writer believes that one of the factors aggravating the Pine Brook flooding is the choking up of the Premium River by sediments deposited mainly at the confluence of the two branches of the Premium River. This choking effect is caused by the raising of the bed of the River by the coarser sediments where they are deposited. This in turn causes a steeper back- water curve and helps put the culvert under greater pressure 41/ -11- with consequent backing up of drainage lines into house cellars . Dredging of the Premium would help alleviate this condition. Drawing up a Plan. Because the concerned municipalities are the Village of Larchmont, the Town of Mamaroneck and the City of New Rochelle, it is assumed that they would cooperate in drawing up a plan for saving the Waterway. Presumably this would start at the level of the respective Planning Commissions. Governmental assistance - technical, at least - would be provided by the Westchester County Soil and Water Conservation District under PL 566 . Possibly there are other sources of various kinds of assistance available from other organizations such as National Audubon Society, the Nature Conservancy, Corps of Engineers , etc. etc . as well as two very effective local groups , the Conservation Advisory Commission and the L. I .F.E. Center, Inc. Topographical and shallow soil surveys would have to be made. These surveys would give the basic data: - cubic yards of dredging, area of spoil piles to be planted, and the like - necessary for approximate cost estimates . Experts in the ecology, such as Environmental Concern, Inc. and Dr. Utter, should also be consulted on environmental impact, establishment of the Tidal Wetland in the Mill Pond and other related aspects . Financing the Project. Once a carefully thought out plan and specifications are drawn up, and costs estimated, financing can be sought. Sources might be public: the three municipalities plus County, State and Federal, the latter under P .L. 566 , the "Watershed Protection and Flood Prevention Act, as Amended" ; in addition, there may be foundation grants for worthy conservation projects . Of course, all these should be explored at the proper time. Assessments against properties adjacent, or in close proximity, to the Waterway might be considered although it would seem - according to the Millaras testimony (8) - that these properties have already been damaged and that if restoration of the Waterway is made, the tax base would be restored to the status quo and that it would therefore be unfair to make additional assess- ments against these properties . -12- One thing to be borne in mind is that according to the proposed Plan, the Waterway is not only saved, but additional things of substantial value are established: the Tidal Wetland in the Mill Pond, the raising of the Lorenzen Ball-Park, the sluice-gate in the dam and over the years these things will remain as tangible assets . Another source of financing might be recovery to some extent from Tony ' s Nursery to the extent that operations on this property have contributed to the sedimentation in the River today. In this connection the position of the New York State Department of Environmental Conservation (DEC) is unequivocal. Commissioner Peter A.A. Berle stated in connection with an up-state case involving ammonia contamination of ground water "The settlement is based on the department' s strongly held position that one who degrades a public resource is responsible for restoration. The department firmly believes that the public should not have to pay for the removal of pollution caused by private firms which damage or destroy public resources . " The cleanup in this case, said Berle, "could approach $1 million. " (13) Conversely, if public bodies cause damage, they "should have to pay for the removal of pollution" they _have caused.. For example , the Village of Larchmont puts sand on its highways and streets in icy weather. There is no doubt that in the watershed of the Premium River this sand finds its way into the River and increases the problem. Therefor the Village should pay its share of the removal. There may be other offenders, for example , the Thruway when it was built or perhaps the recent grading of the so-called Heaphy property on the Boston Post Road opposite Tony' s Nursery. A source of help in this connection could be the employment of some public interest law firm such as the National Resources Defense Council (to name only one) . Conclusion The Premium Waterway is too valuable an environmental asset to be allowed to deteriorate further. The destructive processes should be halted and even rolled-back. The larger community - local , state and Federal - has the technical and financial resources to accomplish this endeavor without delay and before it is too late. -13- Finally, a quotation from the New York Times of August 7 , 1977 may be apt: In an environmental message in late May, President Carter spoke of the need "to acquire and protect our natural and historic heritage. " The President emphasized rapid acquisition of the "most signifi- cant and endangered areas . " Mr. Ribicoff (Senator from Connecticut) feels that Long Island Sound, described by Daniel Webster as "the American Mediterranean" , is now threatened with pollution of its waters and shares and is an ideal candidate for the kind of protection mentioned by the President. Acknowledgements The writer wishes to thank the following who reviewed the draft of this paper and who made valuable comments nearly all of which have been incorporated: Mr. Alex Buchman; Mrs . Elie Fredston of the Town of Mamaroneck Conservation Advisory Commission; Mr. & Mrs . James Johnson, the latter of the L. I .F.E. Center, C.A.C. and many other environmentally concerned groups ; Fred Kellogg, Village Engineer; Mrs . Edith Kleiner; Village Trustee Lawrence Lowy and Mrs . Lowy; Robert S . Warshaw, Esq. ; and Mrs . Phyllis Wittner, President Pryer Manor Association. References (1) Scharf , Thomas J. "History of Westchester County, N.Y. " L.E. Preston, Philadelphia 1886 , p. 876 (2) Seacord & Hardawdy, "Historical Landmarks of New Rochelle" New Rochelle Trust Co. , New Rochelle, N.Y. 1938 (3) Philip Reisman tapes in Larchmont Public Library, 1975 . (4) Utter, Dr, James B. , "Larchmont Harbor Salt Marsh Ecosystems : Second Progress Report" . Environmental Sciences Program, Publication 2 Division of Natural Sciences, S.U.N.Y. , Purchase, N.Y. January, 1975 . -14- (5) Cohen, Morein "Recent Trends of Sediment Accumulation in the Premium Salt Marsh, Larchmont, N.Y. " Bachelor of Arts Thesis SUNY, Purchase, N.Y. February, 1975 . (6) Arbib, Robert S. Jr. et al, "Enjoying Birds Around New York City" , Houghton Mifflin, Boston 1966 . (7) Mary Ann Johnson, letter of August 9 , 1976 to Office of Environmental Analysis, Albany. (8) "Preserving the Future of Long Island Sound" , hearings before the Subcommittee on Executive Reorganization and Government Research of the Committee on Gov' t Operations U.S. Senate, 91st Congress, 2nd Session on S . 2472 , July 7 , 1972 . U.S. Gov' t Printing Office, Washington, 1970 . (9) "Comprehensive Master Plan, Village of Larchmont" , Raymond & May Associates, Planning Consultants , White Plains , N.Y. May, 1966. (10) 1976 Report of the Review Committee of the 1966 Master Plan for the Unincorporated Area of the Town of Mamaroneck, N.Y. (11) Local Action Workshop: Fact sheet for April 26 , 1977 meeting of Larchmont League of Women Voters . (12) Webster, Bayard, "Army Engineers Creating Salt Marshes From Sediment" , N.Y. Times , May 2 , 1975 . (13) Bird, David, "Company to Clean Up Upstate Pollutants" , N.Y. Times, July 1, 1977 . (14) "Flood Insurance Study" Village of Larchmont, by U.S . Dept. of H.U.D. , Federal Insurance Administration, Mar. 1, 1977 . -15- • CHKD.BY ---- DATE Premium Water Way. Westchester JOB No. 504ie : 1"j400' County, N.Y. / 1_t \ N "` o l I .. e5 A r l ,.I F 'ti XiM�UNc�A' ' lip s O 5 �o\ _ Y \ 'f'� j! 'E ,-1 < E 1' Z Dredge Excavation Areas<'.N ' A. North Side of Sea Wall in SE corner of ;,;;r; i m LOUIS E. SHENMAN District Salsa Manager-Eastern • Figure 2 . "MUD CAT" Dredge MUD CAT tumor.CAR RENDL 'Illmm.,••••• 30 ' 2" x 8 ' 0" x 27" draft WT. = 16000 lbs . Material MUD CAT DIVISION Removal Capacity 50-120 cy/hr. National Car Rental System,Inc. 1 , Discharge Pipe 8" Diam. Telephone: North 93 Farview Avenue I 201/265-2440 Paramus, New Jersey 07652 • , ------- ___ --%•••,--"?' P . ......it V.... • ... -..... • o'.... tri".•• , •..tr.''.,'+,1.,.,... ‘I 1 . ,111' aidl.itord.I 1414 , . ,., . .. .: , 'I' • iniutic. , , .,,,i1‘ .,,..„,,,:,0,,,olitApiko.,,,; -.-ii); ?-,1 •—, ,..•,,i -,.„•...„.,,,,,•,.. ‘,... 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Fill your small dredging needs. . .. .:- • National's MUD CAT machine is designed to remove muck, weeds, silt, sand, sludge and industrial wastes. This powerful machine cuts up and pumps away these materials safely and efficiently. Improves lakes and streams for recreation and fish production, restores reservoir capacities for domestic and industrial water supplies and renews ii-,.. __....., __ _ . 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' 'I,,ttt,'.'I , til„,,•erkiii:','"5::011,$.9$•''' '%.‘ AtA4•AWa '''-i .'; -.4tia...Aiitr. 't .N.4.:'"•-•''-' 'M.77- 7"........-77:. •„;,„. -'A t ..''' tr .I.M-4,--A. AVVI.;:`im4 'I,whri- •v..-.7.;,, ily4tXttok, ....s.„;'*, .:''-t.,,,: „;,,,,,,, ;-•itr ,...0-..,,,7 ,,..7..,-,-s.,;01, ,,,,,vt,54:c.,,,,,v411=i, 1-0 •. . t ., Al. ,ig?* re v, tiiki,,`O ,,c,, 0..... 4,1 .,,40, ',,, 4 *!,'.4! „iet . ;:441,101.* ...„ Ittir . '',- , *Ai.1 , itrftVr rnOiartS t t• ' '14,,Pt,4:1'1 j kili A., %4A- . .j.' kt.' „i,. 41.kar, 11: •• "NZ V‘ii 'e 4 *. ' 1 IV '11'6'.' ''K ...q . Mk;:. .. s N. „ .4 4' . . 77k44 A, *l'• ,',. .,',,. , F"0-A.. r ..-41t' *..1 -,,x It";-, ' v.:4: 4- '.4 : ' '-'.''.g, /*Ilat44.46 -*.t. • -', -,•,-.,, • s,, 'NI- ' •.- A,ii..4: ...,•,.: AA*. .t:•t* ',. ..-' r*- a 'g •••• Sedimentation . . . the cause or the problem. , National's MUD CAT Machine is a sound method of sediment removal which can be used wherever underwater sedimentation occurs. Depending on conditions, the . . MUD CAT can remove sedimentary materials at a rate of 50-120 cubic yards per hour. , . . . ....*.• ,-, r'....:..—:;:-•-• ,,:i . •. . .e.: . . .• • .. r, , •:. . . - •, •,,,.. , ..,. , .0 I 1 .esT .0 //I''',"' - ! -• • .m 'i"0tte-'.2.l,er..,:..inx1-g•r.1---.,r.-1111..1-..• .'a. t,.,4.•,• 4.•.•••.•-4:t:a ._.-..1-*,.l:.k4.'‘6.i•.1t1•'C.'.i.o-r.v.r o"'.2t1...'.i;:II.i._4Itir'.,:i•t4t,r.i-,.4,m,tr1--1aa--oo-,i,s',-.,q.'°ma"..4 hL.4„i.t ,--,-4.;f.....e...•...;1-7l,_-4.—.‘-,!1_._.--?„1 FA-.Ait--.i-.m_-..l___;ita '•.1r;...e. .•..',.pi•-;i1P.,4,'-'-'-,; ..'.t.---%r'rs''r'iP'-c.—''.''.'r..‘.,„t:tr-.,.-:,j"ei,,-.-.,t-r i.,„-,ii-it.,p,e.,mi,-,..1-%,i-i.,l„'.......,-r.:i,'r.-_'•1,,V.4_t-..'-."_:..;•:fL.,..--W- 1..q•.—" 1..,'..!t 4''•,•,,..',.,'-1''40'-4''1•,.-"..il2•..'.."-- 7•••4•. ,.., ,- .... -- _ .r-__=-,c,, , -. , ..., ,,,... 4.1...,., _____ ,...z_.-- I---... ..-4',1140... .., . ' k, •3” . I ii.. 641 , ' kAt,.or.A A •••••=""f.- f...- .'''.' A ,. . .0 IC _ , .. -•v:, R•P:,4 , 4 ' 1147'.=. ' 7?-'-'-7a:•••% _•_.. _ s . 'Cit,• 1 .1 National's MUD CAT can "out reach" a drag line, yet it The business end of the MUD CAT is a patented hori- i is small enough to be easily transported from site to site. zontal cutter head mounted on the end of a hydraulically Only two men are required to operate the MUD CAT operated boom. The cutter head is equipped with cutter ) which operates in water depths where you might expect knives which dislodge and cut up material with scissor- '.; only a rowboat could go . . . as shallow as 27 inches. A like action. .4 crane can be used to launch and retrieve the MUD CAT. The spiral auger in the cutter head drives the material to 4 1 the pump suction intake. This aggressive rotating, cutting action can remove sediment in an 8 ft. wide swath down to i a depth of 10'/2 ft. (Model MC10) or 15 ft.(Model MC15). Bottom contours are left even and ridge-free without dan- ..1...mm...... i r,..„ �t iili'• (t';__._ il ,rf. giPAT irrla' 'lllrrrrrrrrrr,'�i'eA'e ►e►' t',. I 11 1111 1 r'' �'J A,0-.0./ rAi/Atlp1t;lid/tfr4lfl'1;E�`'•il1 64, ►' I. 6 • « -, - vfrY 'rW y,,•dk't: n .. ,baiit,:aw..w y.7.;....,,..-a.....,.,:„ � � .... .-.. ...KYwv I-,•11'T'! 1r.Y }T. s ''..".1.•.?—',".. - .. .... I..w....c . ... Y''l ..4.. Fr.' .. r.r.= :'• '•1.1' ....+..�. .w.. .,�.t • �...rlr.'' y..�.....�. .. • c:;ICS`. vrRw'slf.:±....Lw4 `p"",5:.'G7.'9i4d . .... _..._ :. f • 7 'r :,,,,7•:•••4,4.1. K3•I e,7a+X'f,,.7:-.;.•L, , •Y t } ,..:' •. - '. yr,• +aNvr�Y? "5. �"i• "..•�r. '..... ' . ... ; .,•:.. _ i..•..' : . , +t, • .r.,.,: . '_M.'..!. ,.+ ,±, �y{ •` }l K Uu•.S{ ft'. zr.�y' -< t.•� t i '''t iN+"I :,.Y 4 '+li ,wb}� ''iy, i ';: ' L��6ti•:jr •jA " Y giIr4' . WSf �. 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T�� • '„•,,. _rww. 1 *•••• . ,... . . , ..�iN me.........Mr•+K�9w� KJlN.Y_�7Y+1.011,.K.1G ,w,.�'�+. �*p -+��_ wy'4W �.�w • • ,<r ~� a4itr + S�' 4.„,..,,,..4,.. � � 4l L ',, .. �� t 4h! � •3p�� h1" J7 ^ '•�J �`�M iC - �e11Y:- � a ' ..i- � ha .t s ' u !' • 4' 4, ��k" 5is0�� *! .�*�A4M . � w„,,7•44,,, rR , qiCil, . .4, S4.-y � 441• w � , � L4. ,tY y,'f h.. ;•?44,1''.A. * ' A .r grf•L C• 01, •':i , •4'a' Xs .. ; AllitAC.:!,•'' Ri'W ',?•. 4 / .• rk 5Y� >..44 •' • RA;, ,. e •National's MUD CAT Machine . . . tuie solution. • Permanency of treatment will vary with such factors as erosion control, surface - ,,1 run-off, nutrient content, water movement, discharge rate, effluent make-up and i suspended-solids content. -i t , ,��Y , , !T t " a+...14 is I,,f 1.. *..crit�f ,,,.w.� �-r ..r, tyt r sq 4, �. 1S _ I i ir•,s., ' -'M '�3 , . r_ aF, : ,. : 4.4 , y� .F -a ! ,/ ,.4., ' .r ti �-►a'+g .y..t' w :i_ ,1 `.. •cam4,; q +e-:- A =: ai t _ti+.. r � 4 f .:, '+ . -''• ,l k' Ffdr . r f_J,t�4, d..”(.f !+- l�',� � y C: .,�`' a.r �'.>�ie:' . " omM .4 w >•• ', '.14s4".4.-.1.-"r-� - -.,_. Tt.,,M ,,,,.-y;.. . f r� Z . v : I3 -z t• 45i '•••`''„ '' ' 'i'4-;''_4} ,C�i rYb r tNAr4944/dO ‘t. NI ''''''....7; �'wt.'4 iMfs 'Si., 6 'a. •. ".. � �tYyl.::t:v�:inir�+<ntatK:u3�v-wei''#. .�t ^�i� :,. A unique mud shield shrouds the cutter head entrapping A high-powered centrifugal pump feeds the material suspended material and minimizing turbidity.Teeth along through a discharge pipe to a pre-selected spoil area the forward edge provide additional cutting capability up to a half-mile away. Eight inch diameter pipe is when material protrudes above the water. supplied in convenient 20 ft. sections which can be quickly hand assembled over land or water. Most jobs can be set-up by two men in less than a day. National Car Rental's MUD CAT Machine specifications. i ..... . Model MC-10 Model MC-15 General: Length •30'2" Length. -38'9" Width -.8'0' Width • •8'0 Height :0.A.9'3' 'Height 0.A.9'3" ' Weight .. .16,000-lbs Dry, . • ..;;,•,. ••Weight 19,800 lbs,Dry • Draft -27" Draft.: • -21" Floatingclearance .6'1"with Lights Retp9YedloatingClearance - .' 6'1"with Lights Removed Fl+el Capacity 560.01ons j. fuel Capacity 360 gallons Flotation: Pontoons-Two 30"x32"x24'0" Pontoons•Two 30"x32"x24'0" 12 Gauge H.R.Steel with Internal Bulkheads and Plus Two 30"x32''x6'0" Stiffeners;formed for rigidity;polyurethane 12 Gauge H.R.Steel with Internal Bulkheads and foam filled Stiffeners;formed for rigidity;polyurethane foam filled • . Cutter Auger: Auger: Assembly: Diameter 9" Diameter I j Pitch -9" Pitch -9" I Flighting •3/8" Flighting -3/8" Speed •63 RPM or 105 RPM Speed .63 RPM or 105 RPM .• Cutter Knives•44 Detachable Heat-Treated Blades Cutter Knives-44 Detachable Heat-Treated Blades Cutter Bars•34 Detachable Heat-Treated Blades Cutter Bars-34 Detachable Heat-Treated Blades Auger Torque-4000 in.lbs. Auger Torque•4000 in.lbs. Rotates to Cut Slope up to 45 degrees j • Mud Shield: 14"x8'Hydraulically Adjustable 14"x 8' Hydraulically Adjustable , Working Cut -8' wide x 18"maximum depth Cut-8'wide x 18"maximum depth j Capacity: Operating Depth- 10'6"maximum Operating Depth-15'maximum 1 1• Engine: Detroit Diesel 6-71 RC Detroit Diesel 6.71 RC 175 BHP @ 1800 RPM 175 BHP @ 1800 RPM • Drive: Clutch-Manual,14"Dia.Disc& Pressure Plate Clutch•Manual,14"Dia.Disc& Pressure Plate Reduction-Gear Ratio 1.55/1 -Drive Coupling- Reduction-Gear Ratio 1.55/1 •Drive Coupling- Flex Type Flex Type • Pump: Centrifugal Closed Impeller Centrifugal Closed Impeller I Impeller Diameter-18 1/2" Impeller Diameter-18 1/2" , , Suction Diameter-.8 ... .• ..: Suction Diameter-8." Discharge Diameter-6" Discharge Diameter•6" i Shaft Diameter,•2 7/8".• + . Shaft Diameter-2 7/8" il• Capacity•2000 GPM @ 1200 RPM against 155'Head Capacity•2000 GPM @ 1200 RPM against 155'Head Material Removal-50.120 cu.yds./hr. Material Removal-50-120 cu.yds./hr. i Service Capacity•75 GPM @2800 RPM Capacity•75 GPM @ 2800 RPM `I Water Pump: Pressure•80 PSI Pressure-80 PSI Hydraulic 2 Pumps with Circuit Divider 2 Pumps with Circuit Divider System: Capacity Each Pump-11 GPM @ 1800 RPM Capacity Each Pump•11 GPM @ 1800 RPM Reservoir-60 Gallon Reservoir-60 Gallon Circuit One-Auger Drive Circuit One•Auger Drive ' Circuit Two•Boom,Sluice Gate,Mud Shield and Winch Circuit Two•Boom,Sluice Gate,Mud Shield and Winch Relief Valve Setting: Relief Valve Setting: Auger-1600 PSI Auger-1600 PSI Others-1100 PSI Others•1100 PSI Propulsion: Capstan Type Hydraulic Winch Capstan Type Hydraulic Winch Traverse Speed-50 FPM Maximum Fwd.& Rev. Traverse Speed -50 FPM Maximum Fwd.& Rev. Average Cutting Speed-8 to 12 FPM Average Cutting Speed•8 to 12 FPM Electrical Voltage-24V Voltage-24V System: Alt.Output-45 Ampere Alt.Output-45 Ampere Batteries•12V Series Wired Batteries• I 2V Series Wired Circuits-2 Wire System Full Ground Circuits-2 Wire System Full Ground Finish: Two coats of Epoxy Paint on Epoxy Zinc Chromate Two coats of Epoxy Paint on Epoxy Zinc Chromate Primer Primer MUD CAT Machines are operating in a growing list of countries throughout the world. To obtain complete information, call the MUD CAT Division of National Car Rental System, Inc., toll free at 800/328-7333. In Minnesota call collect 612/830-2486 or telex 29-0767. Or write: ri MUD CAT Division L '� 4IPP . National Car Rental System, Inc. MUD CAT 5501 Green Valley Drive _____�. Minnu�nnlie Minnacnt-2 CSd27 THE PREMIUM MARSH SUMMER 1980 THE DEMISE OF AN ESTUARY BY ROBERT P. HOHBERG B.S. , M.A. , P.D. INTRODUCTION The purpose of this study is four-fold: 1.) To review the data of previous studies of the Premium Marsh including: RECENT TRENDS OF SEDIMENT ACCUMULATION IN THE PREMIUM SALT MARSH, LARCHMONT, NEW YORK by Morein Cohen THE PREMIUM - AN ENDANGERED WATERWAY by Robert E. White, P.E. PREMIUM RIVER DREDGING FEASABILITY STUDY by James B. Cropper ADDENDUM TO REPORT BY ROBERT WHITE by Mary Anne Johnson LARCHMONT HARBOR SALT MARSH ECOSYSTEMS by Dr. James M. Utter LOCAL COASTAL MANAGEMENT PROGRAM NEW ROCHELLE, NEW YORK Prepared by Raymond, Parish, Pine & Weiner Inc. CORING STUDY OF THE PREMIUM MARSH - Author Unknown 2.) To analyze and condense the data of the above mentioned reports in order to provide direction for obtaining additional pertinate data. 3.) To execute the additional field work and analysis to obtain this data. 4.) To provide recommendations, on the basis of the data collected, for further management of the Premium Marsh area. -1- Introduction: (Continued) 1.) A series of reports and studies on the Premium have been prepared over the last several years. The following list of problems of the Premium, while not exhaustive, can serve as a good indication of the complexity of the matter: A.) Sedimentation caused by sand and other materials delivered by the various storm drains, some of which originate in New Rochelle and emptied into the river which is contained entirely in the Town of Mamaroneck and the Village of Larchmont. B.) Sedimentation caused by construction activities on prop- erties near the river. C.) Sedimentation contributed by incoming tides. D.) Growth of algae induced by shallower, and often, warmer, waters. E.) Pollution that may be caused by broken sewer lines or inoperative septic systems, mostly in New Rochelle. These are likely to be at least partially responsible for the high Coliform counts. F.) Pollution that may be caused by incoming tides. G.) Presence of manmade and natural objects in the river, from logs to shopping carts which, besides being unsightly, are also silt catchers. The fact is that the priceless resource represented by the Premium Marsh is gradually being lost as a result of these highly complex causes that are inter-municipal- in nature (Raymond, Parish, Pine & Weiner Inc.) Ecologic succession of a salt marsh ordinarily follows a pattern of gradual succession from mud or sand flat to intertidal marsh to high marsh associations through sediment and organic matter accumulation. This is called the Shaler Theory of marsh formation and is hypothesized to be the type that pertains to Premium River Salt Marsh. In most New England salt marshes it takes two hundred years or more for the intertidal sections to fill in beyond the mean high water level where high marsh vegetation could take root and survive (Morein Cohen) . Manmade intervention dates back to 1741 as noted in the Robert E. White report stating "An even older dam had existed since prior to 1741 at the site of the present Red Bridge when the Palmer family which owned a large manor in the vicinity, used the impounded tidal waters to provide power for the first Premium Grist Mill". -2- Introduction: (Continued) We may conclude that thanks to manmade intervention dating beyond 1741, the Shaler Theory has had adequate time to fulfill its predictions for the Premium Marsh. 2.) A potential wetland site's evaluation must include studies of salinity, tidal range, hydraulic patterns, exposure to wind or wave action, elevation and depths of H2O the area to be converted to wetland, and presence or absence of suitable surrounding habitat. I would also recommend that you get an expert in the field of saltwater biology, who could give you advice on what depth of dredging should be contemplated that would be best from the standpoint of improving the habitat for waterfowl and the fishery of the Premium River. (James B. Cropper) . Since I have been trained in both Marine Biology and Biological Oceanography, I decided that a study of salinity would be most appropriate even to the point of indicating tidal range in an estuarine. The latter parameter would be approached in a search for the presence of a Halocline within the estuary. All of the reports mentioned in section one (1.) have alluded in some respects to the problem of sedimentation. The waters which are blamed for such sedimentation range from the Premium River, Pinebrook River to the tidal waters of the sound itself. In order to resolve the problem of which of these waters are most responsible for delivering these sediments, I decided to include measurements of Turbidity which would pinpoint those waters carrying the largest number of particles. Should a pattern in concentration gradient occur, this might also indicate those areas of unloading. 3.) Measurements of salinity were taken with a Yellow Springs Industry (YSI) model 33 S C T salinometer. This meter is a portable electronic device which provides near instant read out on conductivity, temperature and salinity (reported as parts per thousand = 0/00) . The instrument makes use of a fifty foot (50') probe which I marked at intervals of half a meter (0.5m) . Data-on turbidity were collected by means of a Hach Portalab Turbidimeter which is a portable nephelometer complete with a 10 N T U turbidity standard. All measurements are reported as Nephelometric Turbidity Units (NTU) . -3- 4.) Water samples were collected by means of a five (5) flush (Lamotte) sampling bottle with the temperature measured by a Celsius alcohol field thermometer. Each sample was analyzed within minutes after its col- lection . A metric marked line attached to the sampling bottle afforded measurement of the depth at which the sample was taken. Three (3) sampling series were undertaken with most of the measure- ments taken at high tide. Some additional samples were collected at low tide. The first two (2) series employed measurements of both turbidity and salinity. The third and last series concerns itself with a search for a Halocline within the estuary. The first two (2) series includes analysis of thirty three (33) samples. The Halocline series includes forty one (41) measurements of salinity. All pertinent data are recorded in the appendix of this report. Sampling stations were selected with an eye to remain in mid-channel and to record physical landmarks in order to identify each sampling station for reliability. Each station is coded and described in the record of this report found in the appendix. The coded stations are indicated on a map (by Mary Anne Johnson) designated as Figure 1 also included in the appendix of this report. The first series indicates that the incurrent waters of Long Island Sound carries a small amount of particles (3.6 N.T.U.) , at station one (1) at the Weir, by comparison to an immediate rise in particle carrying at station two (2) , Red Bridge, (8.6 N.T.U.) with subsequent higher readings as you proceed upstream from Red Bridge. At station twelve (12) midway between the second turn in the channel from Woodbine Ave. and the foot of Willow Park (Oak Ave.) , tested out at 32.0 N.T.U. , which is the highest suspended particle reading of this series. The following upstream station which is thirteen (13) , at the foot of Willow Park (Oak Ave.) ,drops to 16. 0 N.T.U. indicating that half the suspended particles carried by the incoming tide is unloaded at or about the confluence of the Pinebrook and Premium Rivers. The continuance of this phenomenon can only lead to a marshy mud flat which will eventually block the excurrent waters of both rivers. Turbidity data upstream from station thirteen (13) along the Premium River, indicates more unloading at station fourteen (14)b. with an in- crease in carrying capacity to station fifteen (15) b. Upstream from this station (15b) further unloading occurs at station sixteen (16) b. This indicates that more particle pollution is picked up at the drainage ditch and then is unloaded at the outfall of the Premium River behind the Larchmont Diner. -4- A low tide reading at station one (1) , at the Weir, records 4.2 N.T.U. ( a. 6 N.T.U. difference from high tide) which shows little or no discharge of particles into the sound. A low tide reading at station two (2) , at Red Bridge, records 24.0 N.T.U. (a 15.4 N.T.U. difference from high tide) shows considerable discharge of particles into the Premium Mill Pond. These readings tend to convince me that the sus- pended particles from Red Bridge towards the confluence of Premium and Pinebrook Rivers slosh back and forth from the Premium Mill Pond and back again to the mud flats of the river beds with no purging action into the Sound. At station sixteen (16)a. , the Pinebrook outfall at the Post Road, suspended particle readings were at the highest, 20.0 N.T.U. , at neap high tide with considerable discharge from the outfall. The lowest reading was 5.5 N.T.U. with a spring high tide and low discharge from the outfall. Neap low tide and spring low tide readings at this station were 10.0 N.T.U. and 15.0 N.T.U. respectively. These data indicate that the Pinebrook River adds particles to the marsh system at high discharge and low tide conditions with only slight carrying capacity at spring high tide with low discharge. Inaddition salinity readings of 2.0 0/00 to 0.5 0/00 reveal that it is river water and not tidal sound waters that are carrying these particles. Station sixteen (16) b. , at the Premium River behind the Larchmont Diner, reads 20.0 N.T.U. with a salinity of 23.0 0/00 at spring high tide. This same station analyzes 7.5 N.T.U. with a salinity of 1.9 0/00 at neap high tide. The former set of data shows the particle carrying capacity of tidal waters while the latter indicates the small carrying capacity of the Premium River at its outfall. Analysis of station fifteen (15) b. , Premium River at the foot of the drainage ditch, ind- icates 21.0 N.T.U. with a salinity of 21.5 0/00 at High Tide. This station shows the highest carrying capacity of the Premium-River under the influence of tidal waters. The second series was run with an eye to discover the carrying capacity of the waters within the Premium Mill Pond. Again the reading at station one (1) at the Weir, was 6.2 N.T.U. ( a difference of 2.6 N.T.U. from the first reading) indicating small particle contribution from the- Sound. Since this reading was taken a month later, algae bloom organic matter could easily account for the 2.6 N.T.U. difference. Slight increases in particle carrying occur upstream toward Red Bridge with some small unloading at station one (1) c. , Premium Pond opposite Everett's Island. A larger increase to 9.4 N.T.U. is found at station one (1) d. opposite the edge of the wall at Trinity House. a reading of 8.3 N.T.U. at station two (2) , at Red Bridge, reliably compares to the first reading of 8.6 N.T.U. -5- The second series data bolsters the conclusion that the highest particle carrying waters are those upstream from Red Bridge. The third and last series concerns itself with a search for a Halocline within the Premium estuary. Consistant sampling was taken at surface, 0.5m, and 1.0m depths (excepting stations 15b, 13, and 10 where a 0.5m depth was reached) . The salinity reported in this series was only slightly higher than that recorded in the first two series which indicates good reliability. The slight rise in salinity readings could well be the result of later sampling in the summer months with a small amount of rainfall in the watershed, consolidating the salinity readings from the Halocline series and the first two series, I may conclude that the Halocline, when present, must exist upstream from station fifteen (15) a. , foot of Elm Ave. , in the Pinebrook River and upstream from station fifteen (15) b, at the foot of the Drainage Ditch, in the Premium River. Salinity for the Halocline series has a mean of 26.6 0/00, highest 28.0 0/00 to the lowest 25.3 0/00 (range) . Salinity for the second series has a mean of 16.9 0/00, highest 26.9 0/00 to the lowest 0.5 0/00 (range) . Salinity for the first series has a mean of 19.6 0/00, highest 27.0 0/00 to the lowest 0.5 0/00 (range) . The mean salinity for all three series is 21.0 0/00, highest 26.6 0/00 to the lowest 16.9 0/00 (range) . In perusing these salinity statistics one should be mindful of the fact that the first two (2) series include the fresh water station readings at or about the outfalls of both the Pinebrook and Premium Rivers. Comparing the mean salinity of all three series (including "fresh water" data) of 21.0 0/00 to the mean salinity of 16.8 0/00 reported by James M. Utter (January 1975) , I find a 4.2 0/00 rise in salinity . Since the 1975 data does not include any salinity readings approaching that of fresh water, a more accurate comparison would have to be on the basis of 11.9 0/00 salinity and higher. On this basis I would compare the mean salinity of all three series as 25.2 0/00 to the mean salinity of 16.8 0/00 reported by James M. Utter (January 1975) . This comparison indicates an 8.4 0/00 rise in salinity since 7/30/75. -6- The significance of the above comparison becomes much more meaning- ful when one ponders the following statement: "When a bay or part of a river mouth is temporarily cut off from the sea by a sand bar, the salinity may actually increase beyond that of the open ocean due to evaporation"- Fundamentals of Ecology by Eugene P. Odum. Therefore, I conclude that the sediment deposits in mud flat configurations, especially at the confluence of the Pinebrook and Premium Rivers, are acting like a sand bar configuration and are well in the process of cutting off the rivers from the sound outlet. If one further considers, "recall that fresh water usually has a salinity of less than 0.5 0/00" - Fundamentals of Ecology - by Eugene P. Odum, then the tidal range of Long Island Sound extends to the outfall of the Pinebrook River at the Post Road (16a) and the Premium River behind the Larchmont Diner (16b) . Coupling this with the turbidty data, I conclude that the force to reckon with in the management of the Premium Marsh is the tidal waters of the Long Island Sound which dominates the system. The rivers, them- selves, are rel$gated to nothing more than storm drain outlets. This last statement is further born out by the position of a possible Halocline existing upstream of Elm Ave. (Pinebrook River) and upstream of the drainage ditch (Premium River) 4. Conclusions: 1.) The dominant force in the Premium Marsh is the tidal waters of the Long Island Sound 2.) The Sound contributes very little particle carrying waters into the system. 3.) The most turbid (particle carrying) waters are those upstream from Red Bridge. 4.) Particulate pollution occurs in the greatest part from the environ- ment around the system upstream from Red Bridge. 5.) Salinity data indicates: A.) A river system well on its way to being blocked up by mud flat deposition. B.) The end of the system remaining an estuary as revealed by the absence of a clearly defined Halocline and increased Salinity. 6.) The Pinebrook and Premium Rivers will back up, under flood conditions, should the prevaioing factors be allowed to continue unchecked. -7- Recommendations: 1.) The Premium Marsh system must be restored toward the following objectives: A.) Restoration of free flowing river channels by: 1.) Removing the mud flat blockage in the channel at the foot of Willow Park (Oak Ave.) - station 13 2.) Improvement of tidal flow through Red Bridge (station 2) and at the Weir (station 1) 3.) Restoration and installation of retaining walls and wooden bulwarks along the Mamaroneck and New Rochelle shorelines (stations 5, 6, 7, ). B.) Initiation and periodic repetition of the following studies: 1.) bottom contour 2.) channel velocities 3.) coliform counts 4.) bottom sediment chemical analysis 5.) mean high tide and low tide levels 6.) analysis of dominant vegetation 2.) Investigation and Research for sources of possible funding for the above recommendations. -8- . APPENDIX Station: Date: Time: 1.) At the Weir 7/9/80 10:00 A.M. Conditions: Water Temperature: 200C Bright Sun Air Temperature: 23°C High Tide Depth: Sample Description: 2.0 m Slightly Cloudy No Odor Tests: Note: Turbidity 3.6 N.T.U. Striped Bass caught at site as reported by fisherman First Series Station: Date: Time: 2.) At Red Bridge 7/10/80 10:54 A.M. Conditions: Water Temperature: 23°C Overcast Air Temperature: 24°C Occasional Sun High Tide Depth: Sample Description: 1.5 m Cloudy No Odor Tests: Note: Small fish activity Turbidity 8.6 N.T.V. -1- Station: Date: Time: 3.) First turn in Channel 7/11/80 12:38 P.M. upstream from Red Bridge Conditions: Water Temperature: 25°C Hazy Sun Air Temperature: 23°C High Tide Depth: Sample Description: 1.0 m Cloudy No Odor Tests: Turbidity 9.9 N.T.V. First Series Station: Date: Time: 4.) Second turn in Channel 7/12/80 12:31 P.M. upstream from Red Bridge Conditions: Water Temperature: 25°C Bright Sun Air Temperature: 30°C ,High Tide Depth: Sample Description: 1.0 m Cloudy No Odor Tests: Note: • Turbidity 10. 1 N.T.U. Dead Raccoon in water First Series -2- Station: Date: Time: 5.) First house upstream from 7/13/80 12:40 P.M. second turn in Channel after Red Bridge Conditions: Water Temperature: 24°C Cloudy Air Temperature: 29°C High Tide Depth: Sample Description: 0.5 m Cloudy No Odor Tests: Turbidity 18.0 N.T.U. First Series Station: Date: Time: 6.) At the foot of 7/14/80 1:31 P.M. Hazel Lane Conditions: Water Temperature: 26°C Bright Sun Air Temperature: 33°C High Tide Depth: Sample Description: 0.25 m Cloudy No Odor Tests: Turbidity 12.0 N.T.U. First Series -3- Station: Date: Time: 7.) At the foot of 7/15/80 2:48 P.M. Guion Lane Conditions: Water Temperature: 27°C Overcast Air Temperature: 31°C High Tide Depth: Sample Description: 0.25 m Cloudy No Odor Tests: Turbidity 15.0 N.T.U. First Series Station: Date: Time: 8.) First landing upstream 7/16/80 3:17 P.M. Guion Lane Conditions: Water Temperature: 27°C Hazy Sun Air Temperature: 37°C High Tide Depth: Sample Description: 0.25 m Cloudy Foul Odor Tests: Turbidity 20.0 N.T.U. Salinity 26.5 0/00 First Series -4- Station: Date: Time: 9.) Foot of 7/18/80 4: 35 P.M. Woodbine Ave. Conditions: Water Temperature: 29°C Bright Sun Air Temperature: 32°C High Tide Depth: Sample Description: 0.25 m Cloudy No Odor Tests: Note: Turbidity 16.N.T.U. Oil slicks on Salinity 26.0 0/00 the water surface First Series Station: Date: Time: 10.) First turn in Channel 7/19/80 5:45 P.M. upstream from Woodbine Ave. Conditions: Water Temperature: 28°C Sunny Air Temperature: 30°C High Tide Depth: Sample Description: 0.5 m Cloudy Slight Odor Tests: Turbidity 15.0 N.T.U. Salinity 26.5 0/00 First Series -5- Station: Date: Time: 11.) Second turn in Channel 7/25/80 10:28 A.M. upstream from Woodbine Ave. Conditions: Water Temperature: 25°C Sunny Air Temperature: 30°C High Tide Depth: Sample Description: 0.5 m Cloudy Rotten egg odor Tests: Turbidity 26.0 N.T.U. Salinity 27.0 0/00 First Series Station: Date: Time: 12.) Midway between second turn 7/26/80 11:15 A.M. in Channel from Woodbine Ave. and the foot of Willow Park ( Oak Ave.) Conditions: Water Temperature: 28°C Sunny Air Temperature: 32°C High Tide Depth: Sample Description: 0.25 m Cloudy No Odor Tests: Turbidity 32.0 N.T.U. Salinity 25.0 0/00 First Series -6- Station: Date: Time: 13.) Foot of Willow Park 8/3/80 6:15 P.M. (Oak Ave.) Conditions: Water Temperature: 30°C Bright Sun Air Temperature: , 33°C High Tide Depth: Sample Description: 0.25 m Cloudy No Odor Tests: Turbidity 16.0 N.T.U. Salinity 25.0 0/00 First Series Station: Date: Time: 14. a.) Corner of the retaining 8/4/80 7:19 A.M. wall at Tony's Nursery Conditions: Water Temperature: 26°C Hazy Sun Air Temperature: 29°C High Tide Depth: Sample Description: 0.1 m Cloudy Slight Odor Tests: Turbidity 19.0 N.T.U. Salinity 18.5 0/00 First Series -7- Station: Date: Time: 15. a.) Foot of Elm Ave. 8/5/80 8:15 A.M. Conditions: Water Temperature: 23°C Sunny Air Temperature: 25°C High Tide Depth: Sample Description: 0. 1 m Cloudy Oily Odor Tests: Turbidity 14.0 N.T.U. Salinity 11.5 0/00 First Series Station: Date: Time: 16. a.) Pinebrook outfall at the 7/21/80 5:45 A.M. Post Road Conditions: Water Temperature: 22°C Hazy Sunrise Air Temperature: 28°C High Tide (neap) Considerable Discharge from the Outfall Depth: Sample Description: 0. 1 m Cloudy Slight Odor Tests: Turbidity 20.0 N.T.U. Salinity 0.5 0/00 First Series -8- Station: Date: Time: 16. a. ) Pinebrook outfall at 8/9/80 12:11 P.M. the Post Road Conditions: Water Temperature: 22°C Sunny Air Temperature: 31°C High Tide (Spring) Depth: Sample Description: 0. 1 m Clear Oily Odor Tests: Turbidity 5.5 N.T.U. Salinity 2.0 0/00 First Series Station: Date: Time: 14 b. ) Premium River 8/10/80 1:05 P.M. at Lorenzen Park Conditions: Water Temperature: 290 C Sunny Air Temperature: 29°C High Tide Depth: Sample Description: 0.25 m Cloudy Odor of rotten eggs Tests: Turbidity 14.0 N.T.U. Salinity 25.2 0/00 First Series -9- Station: Date: Time: 15 b. ) Premium River, foot of 8/11/80 1:35 P.M. Drainage Ditch Conditions: Water Temperature: 280C Sunny Air Temperature: 32°C High Tide Depth: Sample Description: 0.3 m , Cloudy No Odor Tests: Turbidity 21.0 N.T.U. Salinity 21.5 0/00 First Series Station: Date: Time: 16 b. ) Premium River, behind 8/7/80 9: 15 A.M. Larchmont Diner Conditions: Water Temperature: 22°C Sunny Air Temperature: 26°C High Tide (neap) Depth: Sample Description: Surface Clear Oily Odor Tests: Turbidity 7.5 N.T.U. Salinity 1.9 0/00 First Series -10- Station: Date: Time: 16. b) Premium River, behind 8/28/80 2:15 P.M. Larchmont Diner Conditions: Water Temperature: 28°C Sunny Air Temperature: 31°C High Tide(Spring) Depth: Description: Surface Slight Amber Color No Odor Tests: Turbidity 20.0 N.T.U. Salinity 23.) 0/00 First Series Station: Date: Time: 2.) Red Bridge 7/22/80 7:45 P.M. Conditions: Water Temperature: 31°C Cloudy Air Temperature: 26° High Tide (neap) Depth: Sample Description: 1.5 m Cloudy Slight Odor Tests: Turbidity 20.0 N.T.U. Salinity 27.0 0/00 First Series -11- Station: Date: Time: 1.) At the Weir 8/28/80 7:35 A.M. Conditions: Water Temperature: 25°C Hazy Sun Air Temperature: 25°C Low Tide Depth: Sample Description: 0.25 m Slightly Cloudy No Odor Tests: Turbidity 4.2 N.T.U. Salinity 26.5 0/00 Low Tide Series Station: Date: Time: 2.) Red Bridge 7/24/80 3:18 P.M. Conditions: Water Temperature: 26°C Sunny Air Temperature: 31°C Low Tide (Spring) Depth: Sample Description: 0.5 m Cloudy Slight Musty Odor Tests: Turbidity 24.0 N.T.U. Salinity 25.0 0/00 Low Tide Series -12- Station: Date: Time: 16 a) Pinebrook outfall at 8/6/80 3:13 P.M. the Post Road Conditions: Water Temperature: 20°C Sunny Air Temperature: 30°C Low Tide (neap) Depth: Sample Description: 0.1 m Clear No Odor Tests: Turbidity 10.0 N.T.U. Salinity 0.5 0/00 Low Tide Series Station: Date: Time: 16 a.) Pinebrook outfall at 7/17/80 10:23 A.M. the Post Road Conditions: Water Temperature: 20°C Overcast with drizzle Air Temperature: 28°C Low Tide (Spring) Depth: Sample Description: 0. 1 m Cloudy No Odor Tests: Turbidity 15.0 N.T.U. Salinity 0.5 0/00 Low Tide Series -13- Station: Date: Time: 1.) At the Weir 8/12/80 12:11 P.M. Conditions: Water Temperature: 25°C Sunny Air Temperature: 29°C High Tide Depth: Sample Description: 1.0 m Clear No Odor Tests: Turbidity 6.2 N.T.U. Salinity 25.0 0/00 Second Series Station: Date: Time: 1 a.) Premium Pond at White 8/15/80 2:45 P.M. House on island Conditions: Water Temperature: 24°C Partly Cloudy Air Temperature: 28°C High Tide Depth: Sample Description: 3.5 m Clear No Odor Tests: Turbidity 6.3 N.T.U. Salinity 24.5 0/00 Second Series -14- Station: Date: Time: 1 b) Premium Pond at the 8/16/80 3:04 P.M. second house upstream from the white island house Conditions: Water Temperature: 23°C Cloudy Air Temperature: 24°C High Tide (neap) High Wind Depth: Sample Description: 2.5 m Clear No Odor Tests: Turbidity 6.7 N.T.U. Salinity 24.25 0/00 Second Series Station: . Date: Time: 1 c) Premium Pond opposite 8/13/80 2:05 P.M. Everett's Island Conditions: Water Temperature: 25°C Sunny Air Temperature: 30°C High Tide Depth: Sample Description: 1.0 m Clear No Odor Tests: Turbidity 5.5 N.T.U. Salinity 24.0 0/00 Second Series -15- Station: Date: Time: 1 d) Opposite the edge of 8/20/80 6:10 P.M. the wall at Trinity House Conditions: Water Temperature: 24°C Overcast Air Temperature: 24°C High Tide Depth: Sample Description: 0.5 m Clear No Odor Tests: Turbidity 9.4 N.T.U. Salinity 21.0 0/00 Second Series Station: Date: Time: 2.) At Red Bridge 8/23/80 10:24 A.M. Conditions: Water Temperature: 22°C Sunny Air Temperature: 25°C Crest of High Tide Depth: Sample Description: 1.6 m Clear No Odor Tests: Turbidity 8. 3 N.T.U. Salinity 26.9 0/00 Second Series -16- Station: Date: Time: 16 a) Pinebrook outfall at 8/14/80 3:00 P.M. the Post Road Conditions: Water Temperature: 22°C Overcast Air Temperature: 27°C High Tide (Spring) Depth: Sample Description: 0.3 m Clear Odor of Oil Tests: Turbidity 9.0 N.T.U. Salinity 5.5 0/00 Second Series -17- Station: Date: Time: 2. ) At Red Bridge 8/27/80 7:19 P.M. Conditions: Hazy Sun Low Tide (neap) Salinity: Depth: Temperature: 25.0 0/00 Surface 28.5°C 26.0 0/00 0.5 m 28.0°C 26.2 0/00 1.0 m 28.0°C Halocline Series Station: Date: Time: 1.) At Weir 8/28/80 7:35 A.M. Conditions: Hazy Sun Low Tide Salinity: Depth: Temperature: 26..5 0/00 Surface 24.5°C 26.9 0/00 0.5 m 24.5°C 26.9 0/00 1.0 m 25.0°C Halocline Series -18- Station: Date: Time: 1. 5 b) Premium River at 8/25/80 12:11 P.M. foot of Drainage Ditch Conditions: Sunny High Tide Salinity: Depth: Temperature: 24.0 0/00 Surface 29.0°C 26.0 0/00 0.5 m 26.0°C Halocline Series Station: Date: Time: 1. 5 a) Foot of Elm Ave. 8/25/80 11:56 A.M. Conditions: Sunny High Tide Salinity: Depth: Temperature: 23.0 0/00 Surface 26°C 26.0 0/00 0.5 m 26°C • 27.0 0/00 1.0 m 26°C Halocline Series -19- Station: Date: Time: 13.) Foot of Oak Ave. at 8/25/80 12:21 P.M. Willow Park Conditions: Sunny High Tide Salinity: Depth: Temperature: 25.0 0/00 Surface 29°C 26.9 0/00 0.5 m 26°C Halocline Series Station: Date: Time: 12) Midway between second 8/26/80 12:34 P.M. turn in channel from Woodbine Ave. and the foot of Willow Park Conditions: Sunny High Tide Salinity: Depth: Temperature: 25.0 0/00 Surface 28.5°C 25.0 0/00 0.5 m 28.0°C 27.0 0/00 1.0 m 26.0°C Halocline Series -20- Station: Date: Time: 11.) Second turn in channel 8/26/80 12:45 P.M. upstream from Woodbine Ave. Conditions: Sunny High Tide Salinity: Depth: Temperature: 27.0 0/00 Surface 26°C 27.5 0/00 0.5 m 25.5°C_ 27.5 0/00 1.0 m 25.0°C Halocline Series Station: Date: Time: 10. ) First turn in channel 8/26/80 12:50 P.M. upstream from Woodbine Ave. Conditions: Sunny High Tide Salinity: Depth: Temperature: 27.0 0/00 Surface 26°C 27.0 0/00 0.5 m 26°C Halocline Series -21- Station: Date: Time: 9. ) Foot of Woodbine Ave. 8/26/80 12:58 P.M. Conditions: Sunny High Tide Salinity: Depth: Temperature: 26.5 0/00 Surface " 26.5°C 27.0 0/00 0.5 m 25°C 27.2 0/00 1.0 m 25°C Halocline Series Station: Date: Time: 8.) First landing upstream 8/26/80 1:04 P.M. from Guion Lane Conditions: Sunny High Tide Salinity: Depth: Temperature: 26.9 0/00 Surface 26.5°C 27.0 0/00 0.5 m 26°C 27.2 0/00 1.0 m 25°C Halocline Series -22- Station: Date: Time: 7.) At the foot of Guion Lane 8/24/80 11:16 A.M. Conditions: Sunny Crest of High Tide Salinity: Depth: Temperature: 27.0 0/00 Surface 24.5°C 27.0 0/00 0.5 m 24.0°C 27.0 0/00 1.0 m 23.0°C Halocline Series Station: Date: Time: 6.) At foot of Hazel Lane 8/26/80 1:08 P.M. Conditions: Sunny High Tide Salinity: Depth: Temperature: 26.5 0/00 Surface 27°C 27.0 0/00 0.5 m 26°C 27.0 0/00 1.0 m 26°C Halocline Series -23- Station: Date: Time: 3.) First turn in channel 8/26/80 1:19 P.M. from Red Bridge Conditions: Sunny High Tide Salinity: Depth: Temperature: 26.2 0/00 Surface 27°C 27.0 0/00 0.5 m 26.5°C 27.0 0/00 1.0 m 26.0°C Halocline Series Station: Date: Time: 2) Red Bridge 8/22/80 8:59 P.M. Conditions: Overcast High Tide Salinity: Depth: Temperature: 27.5 0/00 Surface 20°C 27.0 0/00 0.5 m 20.5°C 27.0 0/00 1.0 m 20.5°C Halocline Series -24- Station: Date: Time: 1 b) Second house from Island 8/23/80 9:30 A.M. House in Premium Pond Conditions: Sunny High Tide , Salinity: Depth: Temperature: 28.0 0/00 Surface 22°C 28.0 0/00 0.5 m 22°C 28.0 0/00 1.0 m 22°C 28.5 0/00 1.5 m 21.5°C Station: Date: Time: 1.) At Weir 8/21/80 7:53 A.M. Conditions: Overcast High Tide Salinity: Depth Temperature: 26.5 0/00 Surface 22°C 27.0 0/00 0.5 m 21.5°C 26.9 0/00 1.0 m 22.2°C 27.9 0/00 1.5 m 21.5°C Halocline Series -25- r .f: t / - ,,nab 1 ' / .0 ti . •--... 411111.11111i6.' '- 1 sit Na, of State Designated Tidal Wetlands r�, ,� —14 VIZ H.M. - High Marsh or Salt Meadow • S.M. - Coastal Shoals, Bars and Mudflats _ " 3 1 Y L.Z. - Inshore Waters. (Littoral Zone) ; F.C. - Formerly Connected Tidal Wetlands. , Zoning: Pryer Manor . II �. }ai, Cityof New Rochelle - 11-1A '� Middle Reach of Mamaroneck - R-IO - Low Density - • r' ` . __ of Zoning: Premium Waterway � Premium ;,,� 511- LC 2 River •• Town of Mamaroneck - R-6 v Z • R-10 - Low Density '. R-30 - Low Dens' • ` � / t 'Jr City of New Rochelle - R-1A. , t �� `Locher Reach Village of Larchmont - R-5 __,--f C` - • \ .of I - :Premium River R-7.5 � 1 ��'' R-12.5 d-Yre t.. .. R-30 • i .."Red" Bridge i/ ! Ufa_' � . -jlrr-r#P##V- -"-1 . - Premit:m Y ! v • Ii p'.►J` r : - t• It Mill . - ; Causeway and pF '01 Dais 1:1- 6,----_,,, I ` I. ...• Pond ( - A G -1.-1 - `" -- - 1� _ . .. . . •far.' o `��‘t)- W -f Q• t ong I3land Sound l Figure 4 --- pTI 1 • • . , 1 i I . 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