The Census Man Cometh
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Modeling Population Dynamics of Roseate Terns (Sterna Dougallii) In
Ecological Modelling 368 (2018) 298–311 Contents lists available at ScienceDirect Ecological Modelling j ournal homepage: www.elsevier.com/locate/ecolmodel Modeling population dynamics of roseate terns (Sterna dougallii) in the Northwest Atlantic Ocean a,b,c,∗ d e b Manuel García-Quismondo , Ian C.T. Nisbet , Carolyn Mostello , J. Michael Reed a Research Group on Natural Computing, University of Sevilla, ETS Ingeniería Informática, Av. Reina Mercedes, s/n, Sevilla 41012, Spain b Dept. of Biology, Tufts University, Medford, MA 02155, USA c Darrin Fresh Water Institute, Rensselaer Polytechnic Institute, 110 8th Street, 307 MRC, Troy, NY 12180, USA d I.C.T. Nisbet & Company, 150 Alder Lane, North Falmouth, MA 02556, USA e Massachusetts Division of Fisheries & Wildlife, 1 Rabbit Hill Road, Westborough, MA 01581, USA a r t i c l e i n f o a b s t r a c t Article history: The endangered population of roseate terns (Sterna dougallii) in the Northwestern Atlantic Ocean consists Received 12 September 2017 of a network of large and small breeding colonies on islands. This type of fragmented population poses an Received in revised form 5 December 2017 exceptional opportunity to investigate dispersal, a mechanism that is fundamental in population dynam- Accepted 6 December 2017 ics and is crucial to understand the spatio-temporal and genetic structure of animal populations. Dispersal is difficult to study because it requires concurrent data compilation at multiple sites. Models of popula- Keywords: tion dynamics in birds that focus on dispersal and include a large number of breeding sites are rare in Roseate terns literature. -
Commonwealth of Massachusetts Energy Facilities Siting Board
COMMONWEALTH OF MASSACHUSETTS ENERGY FACILITIES SITING BOARD ) Petition of Vineyard Wind LLC Pursuant to G.L. c. ) 164, § 69J for Approval to Construct, Operate, and ) Maintain Transmission Facilities in Massachusetts ) for the Delivery of Energy from an Offshore Wind ) EFSB 20-01 Energy Facility Located in Federal Waters to an ) NSTAR Electric (d/b/a Eversource Energy) ) Substation Located in the Town of Barnstable, ) Massachusetts. ) ) ) Petition of Vineyard Wind LLC Pursuant to G.L. c. ) 40A, § 3 for Exemptions from the Operation of the ) Zoning Ordinance of the Town of Barnstable for ) the Construction and Operation of New Transmission Facilities for the Delivery of Energy ) D.P.U. 20-56 from an Offshore Wind Energy Facility Located in ) Federal Waters to an NSTAR Electric (d/b/a. ) Eversource Energy) Substation Located in the ) Town of Barnstable, Massachusetts. ) ) ) Petition of Vineyard Wind LLC Pursuant to G.L. c. ) 164, § 72 for Approval to Construct, Operate, and ) Maintain Transmission Lines in Massachusetts for ) the Delivery of Energy from an Offshore Wind ) D.P.U 20-57 Energy Facility Located in Federal Waters to an ) NSTAR Electric (d/b/a Eversource Energy) ) Substation Located in the Town of Barnstable, ) Massachusetts. ) ) AFFIDAVIT OF AARON LANG I, Aaron Lang, Esq., do depose and state as follows: 1. I make this affidavit of my own personal knowledge. 2. I am an attorney at Foley Hoag LLP, counsel for Vineyard Wind LLC (“Vineyard Wind”) in this proceeding before the Energy Facilities Siting Board. 3. On September 16, 2020, the Presiding Officer issued a letter to Vineyard Wind containing translation, publication, posting, and service requirements for the Notice of Adjudication and Public Comment Hearing (“Notice”) and the Notice of Public Comment Hearing Please Read Document (“Please Read Document”) in the above-captioned proceeding. -
Massachusetts Ocean Management Plan
Massachusetts Ocean Management Plan Volume 2 Baseline Assessment and Science Framework December 2009 Introduction Volume 2 of the Massachusetts Ocean Management Plan focuses on the data and scientific aspects of the plan and its implementation. It includes these two separate documents: • Baseline Assessment of the Massachusetts Ocean Planning Area - This Oceans Act-mandated product includes information cataloging the current state of knowledge regarding human uses, natural resources, and other ecosystem factors in Massachusetts ocean waters. • Science Framework - This document provides a blueprint for ocean management- related science and research needs in Massachusetts, including priorities for the next five years. i Baseline Assessment of the Massachusetts Ocean Management Planning Area Acknowledgements The authors thank Emily Chambliss and Dan Sampson for their help in preparing Geographic Information System (GIS) data for presentation in the figures. We also thank Anne Donovan and Arden Miller, who helped with the editing and layout of this document. Special thanks go to Walter Barnhardt, Ed Bell, Michael Bothner, Erin Burke, Tay Evans, Deb Hadden, Dave Janik, Matt Liebman, Victor Mastone, Adrienne Pappal, Mark Rousseau, Tom Shields, Jan Smith, Page Valentine, John Weber, and Brad Wellock, who helped us write specific sections of this assessment. We are grateful to Wendy Leo, Peter Ralston, and Andrea Rex of the Massachusetts Water Resources Authority for data and assistance writing the water quality subchapter. Robert Buchsbaum, Becky Harris, Simon Perkins, and Wayne Petersen from Massachusetts Audubon provided expert advice on the avifauna subchapter. Kevin Brander, David Burns, and Kathleen Keohane from the Massachusetts Department of Environmental Protection and Robin Pearlman from the U.S. -
GRAY SEAL (Halichoerus Grypus): Western North Atlantic Stock 1998
December 1998 GRAY SEAL (Halichoerus grypus): Western North Atlantic Stock STOCK DEFINITION AND GEOGRAPHIC RANGE The gray seal is found in the western North Atlantic from New England to Labrador and is centered in the Sabel Island region of Nova Scotia (Katona et al. 1993; Davies 1957). This stock is separated by both geography and differences in the breeding season from the eastern Atlantic stock (Bonner 1981). The western Atlantic stock is distributed and breeds principally in eastern Canadian waters; however, small numbers of animals and pupping have been observed on several isolated islands along the Maine coast and in Nantucket-Vineyard Sound, Massachusetts (Katona et al. 1993; Rough 1995; J. R. Gilbert, pers. comm., University of Maine, Orono, ME). In recent years, a year-round breeding population of approximately 400 animals has been documented on the outer Cape Cod and Nantucket Island (Dennis Murley, pers. comm., Mass. Audubon Society, Wellfleet, MA). Gilbert (pers. comm) has also documented a resident colony in Maine. POPULATION SIZE Estimates of the total western Atlantic gray seal population are not available; however, four estimates of portions of the stock are available for Sable Island, the Maine coast, and Muskeget Island (Nantucket) and Monomoy, (Cape Cod) Massachusetts (Table 1). The 1986 population estimate for individuals on Sable Island, Nova Scotia that are one year old and older was between 100,000 and 130,000 animals (Stobo and Zwanenburg 1990). The 1993 estimate of the Sable Island and Gulf of St. Lawrence stocks was 143,000 animals (Mohn and Bowen 1994). The population in waters off Maine has increased from about 30 in the early 1980's to between 500-1,000 animals in 1993; recently 29-49 pups/year have been recorded in Penobscot Bay (J. -
GRAY SEAL (Halichoerus Grypus Grypus): Western North Atlantic Stock
May 2015 GRAY SEAL (Halichoerus grypus grypus): Western North Atlantic Stock STOCK DEFINITION AND GEOGRAPHIC RANGE The gray seal is found on both sides of the North Atlantic, with three major populations: eastern Canada, northwestern Europe and the Baltic Sea (Katona et al. 1993). The western North Atlantic stock is equivalent to the eastern Canada population, and ranges from New Jersey to Labrador (Davies 1957; Mansfield 1966; Katona et al. 1993; Lesage and Hammill 2001; DiGiovanni, pers. comm., Riverhead Foundation for Marine Research and Preservation). This stock is separated by geography, differences in the breeding season, and mitochondrial DNA variation from the northeastern Atlantic stock (Bonner 1981; Boskovic et al. 1996; Lesage and Hammill 2001). There are three breeding concentrations in eastern Canada: Sable Island, Gulf of St. Lawrence, and along the coast of Nova Scotia (Laviguer and Hammill 1993). Tagging studies indicate that there is little intermixing between the two breeding groups (Zwanenberg and Bowen 1990) and, for management purposes, they are treated by the Canadian Department of Fisheries and Oceans (DFO) as separate stocks (Mohn and Bowen 1996). Outside the breeding period, there is overlap in the distribution of animals from the three colonies (Lavigueur and Hammill 1993; Harvey et al. 2008; Breed et al. 2006, 2009, Hammill, pers. comm. DFO, Mont-Joli, Quebec, Canada). In the mid- 1980s, small numbers of animals and pupping were observed on several isolated islands along the Maine coast and in Nantucket-Vineyard Sound, Massachusetts (Katona et al. 1993; Rough 1995: Gilbert et al. 2005). In the late 1990s, a year-round breeding population of approximately 400+ animals was documented on outer Cape Cod and Muskeget Figure 1. -
Roseate Tern Sterna Dougallii
COSEWIC Assessment and Update Status Report on the Roseate Tern Sterna dougallii in Canada Roseate Tern. Diane Pierce © 1995 ENDANGERED 2009 COSEWIC status reports are working documents used in assigning the status of wildlife species suspected of being at risk. This report may be cited as follows: COSEWIC. 2009. COSEWIC assessment and update status report on the Roseate Tern Sterna dougallii in Canada. Committee on the Status of Endangered Wildlife in Canada. Ottawa. vii + 48 pp. (www.sararegistry.gc.ca/status/status_e.cfm). Previous reports: COSEWIC. 1999. COSEWIC assessment and update status report on the Roseate Tern Sterna dougallii in Canada. Committee on the Status of Endangered Wildlife in Canada. Ottawa. vi + 28 pp. (www.sararegistry.gc.ca/status/status_e.cfm) Whittam, R.M. 1999. Update COSEWIC status report on the Roseate Tern Sterna dougallii in Canada. Committee on the Status of Endangered Wildlife in Canada. Ottawa. 1-28 pp. Kirkham, I.R. and D.N. Nettleship. 1986. COSEWIC status report on the Roseate Tern Sterna dougallii in Canada. Committee on the Status of Endangered Wildlife in Canada. Ottawa. 49 pp. Production note: COSEWIC would like to acknowledge Becky Whittam for writing the status report on the Roseate Tern Sterna dougallii in Canada, prepared under contract with Environment Canada, overseen and edited by Richard Cannings and Jon McCracken, Co-chairs, COSEWIC Birds Specialist Subcommittee. For additional copies contact: COSEWIC Secretariat c/o Canadian Wildlife Service Environment Canada Ottawa, ON K1A 0H3 Tel.: 819-953-3215 Fax: 819-994-3684 E-mail: COSEWIC/[email protected] http://www.cosewic.gc.ca Également disponible en français sous le titre Ếvaluation et Rapport de situation du COSEPAC sur la Sterne de Dougall (Sterna dougallii) au Canada – Mise à jour. -
The Mussel Resources of the North Atlantic Region
United states Depa tment of the Interior, Oscar ~ . Chapman, Secretary Fish and ice, Albert M. Day, Director J Fishery Leaflet 364 Wash in ton 25 D. C. Januar 1950 THE MUSSEL RESOURCES OF THE NORTH ATLANTIC REGION ~RT J --THE SURVEY TO DISCOVER THE LOCATIONS AND AREAS OF THE NORTH ATLANTIC MUSSEL-PRODUCING BEDS By Leslie W. Scattergood~~ and Clyde C, Taylor ~d~ '!his is the first of three papers discussing the World War II pro motion of the North Atlantic mussel fishery. The present article is primarily concerned "'i th the quantitative resul ts of a survey of the productivi~ of mussel areas. INTRODUCTION During the recent war, the fishing industry had tte problem of increasing its production despite relative shortages of manpower, equipment, and materials o One of the ways of efficiently augmenting the catch of fish and shellfish was to uti lize species ordinarily disregarded. One of the probable sources of sea food was the edible mussel (yGtilus edulis), which is so common along , the North Atlantic Coast of the United States. This species cap be harvested dur ing that time of the year when the small-boat fishery is least active. In the late winter and the spring months, the mussels a,re in good con dition for marketing, as it is then that they reach their fattest condition, and in this period other fishing activities are at a low level. The mussel, although relatively unknown to the American public p has attained great popularity in Europe. Large quantities have been consumed in European coun tries for hundreds of yearso The annual English, Welsh, and Scotch production of this shellfish, as re corded in the statistical reports of the British Ministry of Agriculture and Fish eries" ave,raged about 19 million pounds ("in the shell" weight) for the lS-year period between 1924 and 1938. -
STATUS of the PIPING PLOVER in MASSACHUSETTS by George W. Gove, Ashland
STATUS OF THE PIPING PLOVER IN MASSACHUSETTS by George W. Gove, Ashland On January 10, 1986, the Piping Plover (Charadrius melodus) was added to the U. S. Fish and Wildlife Service list of endangered and threatened species of wildlife. The entire breeding popula tion of this species in North America has been estimated at less than 2200 pairs. Piping Plovers breed in the Great Plains from southern Alberta eastward to Minnesota, the Dakotas, and Nebraska; at scattered locations around the Great Lakes; and on the Atlantic Coast from the north shore of the Gulf of St. Lawrence and the Maritimes to Virginia and the Carolines. They winter along the Atlantic and Gulf coasts from South Carolina to Texas and north ern Mexico. The U. S. Fish and Wildlife Service designated the Great Lakes population, which is down to less than twenty pairs, as "endangered," a term applied when extinction is imminent, and the Great Plains and Atlantic Coast populations as "threatened" (describing the state that is precursor to "endangered"). The decline of the Atlantic Coast population has been attributed to increasing recreational use and development of ocean beaches. In Massachusetts, the Piping Plover breeds coastally from Salis bury south and east to Cape Cod, the islands, and Westport. It is normally found in the state from mid-March through mid-September. This species makes a shallow nest, sometimes lined with fragments of shells, with pebbles, or wrack, along ocean beaches and filled- in areas near inlets and bays. The normal clutch of pale, sand- colored, speckled eggs is four. Incubation is underway by mid- May in Massachusetts. -
Scott M. Melvin Massachusetts Division of Fisheries and Wildlife Field Headquarters, Rt
STATUS OF PIPING PLOVERS IN MASSACHUSETTS - 1992 SUMMARY Scott M. Melvin Massachusetts Division of Fisheries and Wildlife Field Headquarters, Rt. 135 Westborough, MA 01581 Observers reported a total of 213 breeding pairs of Piping Plovers (Charadrius melodus) at 58 sites in Massachusetts in 1992 (Table 1) . Breeding pairs are defined as pairs observed with either a nest or unfledged chicks or that exhibit site tenacity and evidence of pair bonding and territoriality. Observer effort in 1992, measured as number of sites surveyed and intensity of census effort at each site, was roughly comparable to previous efforts since 1986. In at least 2 instances, pairs that nested unsuccessfully were believed to have moved to new sites and renested. These pairs were included in counts of pairs at both sites where they nested, but were counted only once in the overall state total (Table 1). Also not included in the state total were 2 birds seen for only 3 days at fisbury Great Pond on Martha's Vineyard, and a single bird that was present at Cockeast Pond in Westport. The 1992 total of 213 pairs is the highest count of Piping Plovers recorded in Massachusetts since comprehensive statewide surveys began in 1985, and represents an increase of 53 pairs over the 1991 count of 160 pairs (Table 2). Numbers increased in 6 bf 7 regions of the state; only Martha's Vineyard/Elizabeth Islands decreased by 1 pair. The largest increases came on the Lower Cape (from 50 to 84 pairs in 1991 vs. 1992) and the Upper Cape (from 21 to 32 pairs). -
GRAY SEAL (Halichoerus Grypus): Western North Atlantic Stock 2000
September 2000 GRAY SEAL (Halichoerus grypus): Western North Atlantic Stock STOCK DEFINITION AND GEOGRAPHIC RANGE The gray seal is found on both sides of the North Atlantic, with three major populations: in eastern Canada; northwestern Europe and the Baltic Sea (Katona et al. 1993). The western North A tlantic population occurs from New England to Labrador and is centered in the Sable Island region of Nova Scotia (Katona et al. 1993; D avies 195 7). This stock is separated by both geography and differences in the breeding season from the eastern Atlantic stock (Bonner 1981). The western North Atlantic stock is distributed and breeds principally in eastern Canadian waters (Man sfield 1966). There are two breeding concentrations in eastern Canada; one at Sable Island, and a second that breeds on the pack ice in the Gulf of St. Lawrence (Hammill et al. 1998). Tagging studies indicate that there is little intermixing between the two breeding groups (Zwanenberg and Bowen 1990), and for management purposes, they are treated as separate populations (Mohn and Bowen 1996). However, small numbers of animals and pupping have been observed on several isolated islands along the Maine coast and in Nantucket-Vineyard Sound, Massachusetts (Katona et al. 1993; Rough 1995; J. R. Gilbert, pers. comm ., University of Maine, Orono, ME). In recent years, a year-round breeding population of approximately 400 animals has been documented on outer Cape Cod and Nantucket Island (Dennis Murley, pers. comm., Mass. Audubon Society, W ellfleet, MA ). Gilbert (pers. comm .) has also do cumented a resident colony in Maine. POPULATION SIZE Estimates of the total western Atlantic gray seal population are not available; however, four estimates of portions of the stock are available for Sable Island, the Maine coast, and Muskeget Island (Nantucket) and Monomoy, (Cape Cod) Massachusetts (Table 1). -
“Penikese Offers You the Choice Between Two Worlds. One Is a Place Where You Can Always Find Someone Other Than Yourself to Blame for Your Troubles
“Penikese offers you the choice between two worlds. One is a place where you can always find someone other than yourself to blame for your troubles. It is a place where what you do and where you go is decided for you by the various agencies that our society created to manage the lives of the people who cannot make it on their own. When you live in this world you can have no real friends since everyone there cares only about himself. The other world is a place where people accept the responsibility for their own lives. Here a man is measured against the values of honesty, compassion, and the courage to do what is right instead of what is easiest. This is the world we hope Penikese will convince you to choose for yourself.” From a school brochure, circa 1975, by George Cadwalader. CONTENTS 2 2003 DIRECTORS’ REPORT 4 BOARD, COMMITTEES, STAFF, AND ASSOCIATES 5 FINANCIALS 6 CLINICAL SPOTLIGHT: WORKING WITH CHOICES 12 PENIKESE ON THE MAP 14 THE EDUCATIONAL PROGRAM 15 THE WILDLIFE SANCTUARY 16 REFLECTIONS FROM GEORGE CADWALADER 18 OUR DONORS AND SUPPORTERS 1 2003 Annual Report: Over the Bar Penikese at 30 Years 30 years is an extraordinary accomplishment for any small non-profit because, like small businesses, so many come and quickly go. Penikese’s longevity and prosperity is all the more remarkable given its challenges: sharing its Woods Hole home base with several larger, prestigious and acclaimed missions, working with an extremely difficult population, and no less, serving as a private school in an ever-shifting operating climate over which it has little control. -
A Springtime Exploration of Essex County's Coastal Islands, With
bo33-1:BO32-1.qxd 6/2/2011 6:26 AM Page 12 A Springtime Exploration of Essex County’s Coastal Islands, with Notes on Their Historical Use by Colonially Nesting Birds Jim Berry For over thirty years I have lived on the North Shore of Massachusetts without a boat and have long wondered what colonially nesting birds, in what numbers, have nested on the many islands along the Essex County coast. All I knew was that large gulls and cormorants nest on some of them, that terns used to nest on them, and that herons have used at least three of them, but beyond that I didn’t know many details. In 2004 I got a chance to learn more when I found out that my friends Mary Capkanis and Dave Peterson had acquired a boat, and that Mary had obtained a pilot’s license. Both are longtime birders, and both have experience surveying waterbird colonies in various parts of the U.S. Finally, I had the means to do some island- hopping with friends who were serious about surveying for nesting birds. We made three outings, on May 12, May 14, and May 31. Linda Pivacek accompanied us on the third trip. We were unable to get out in June and of course needed more trips, later in the nesting season, to complete even a preliminary census. But in those three days we visited (with very few landings) most of the 30+ islands between Rockport and Nahant that are large enough to support nesting birds. I had three goals for these trips: (1) to see where gulls and cormorants are nesting and in roughly what numbers, and whether terns still nest on any of the islands; (2) to find out whether herons are currently nesting on any islands other than Kettle, off Manchester; and (3) to look for evidence of nesting by other species, such as Common Eiders (Somateria mollissima), which have increased dramatically as nesters in Boston Harbor, and Great Cormorants (Phalacrocorax carbo), Black Guillemots (Cepphus grylle), and American Oystercatchers (Haematopus palliatus), for which there are no documented nesting records in Essex County.