BIRD OBSERVER of Easm N MASSACHUSETTS Iip I
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A Roxbury Review: Conglomerates of Greater Boston
C2-1 A ROXBURY REVIEW by Margaret D. Thompson, Department of Geosciences, Wellesley College Anne M. Grunow, Byrd Polar Research Center, Ohio State University INTRODUCTION Conglomerate throughout the Boston Basin in eastern Massachusetts (Fig. 1) has long been called after the Roxbury district of Boston (early references in Holmes, 1859 and Shaler, 1869) and subdivided into three members typified by strata in the encircling communities of Brookline, Dorchester and the Squantum section of Quincy, MA (Emerson, 1917). NEIGC field trips, beginning with one led by W.O. Crosby in 1905, and also GSA-related field trips have provided regular opportunities for generations of geologists to debate the depositional settings of all of these rocks, particularly the possible glacial origin of the Squantum "Tillite". It appears, however, that none of these outings has ever included a stop in Roxbury itself (Table I and lettered localities in Fig. 1). A main purpose of this trip will be to visit the nominal Roxbury type locality in a section of the historic quarries where recent re-development includes the newly opened Puddingstone Park. Other stops will permit comparison of type Roxbury Conglomerate with other rocks traditionally assigned to this formation and highlight geochronological and paleomagnetic data bearing on the ages of these units. Table I. Forty Years of Field Trips in the Roxbury Conglomerate Stop locations Trip leader(s)/year Title (listed alphabetically; (abbreviations below) Caldwell (1964) The Squantum Formation: Paleozoic Tillite or -
Rapid Formation and Degradation of Barrier Spits in Areas with Low Rates of Littoral Drift*
Marine Geology, 49 (1982) 257-278 257 Elsevier Scientific Publishing Company, Amsterdam- Printed in The Netherlands RAPID FORMATION AND DEGRADATION OF BARRIER SPITS IN AREAS WITH LOW RATES OF LITTORAL DRIFT* D.G. AUBREY and A.G. GAINES, Jr. Woods Hole Oceanographic Institution, Woods Hole, MA 02543 (U.S.A.) (Received February 8, 1982; revised and accepted April 6, 1982) ABSTRACT Aubrey, D.G. and Gaines Jr., A.G., 1982. Rapid formation and degradation of barrier spits in areas with low rates of littoral drift. Mar. Geol., 49: 257-278. A small barrier beach exposed to low-energy waves and a small tidal range (0.7 m) along Nantucket Sound, Mass., has experienced a remarkable growth phase followed by rapid attrition during the past century. In a region of low longshore-transport rates, the barrier spit elongated approximately 1.5 km from 1844 to 1954, developing beyond the baymouth, parallel to the adjacent Nantucket Sound coast. Degradation of the barrier spit was initiated by a succession of hurricanes in 1954 (Carol, Edna and Hazel). A breach opened and stabilized near the bay end of the one kilometer long inlet channel, providing direct access for exchange of baywater with Nantucket Sound, and separating the barrier beach into two nearly equal limbs. The disconnected northeast limb migrated shorewards, beginning near the 1954 inlet and progressing northeastward, filling the relict inlet channel behind it. At present, about ten percent of the northeast limb is subaerial: the rest of the limb has completely filled the former channel and disappeared. The southwest limb of the barrier beach has migrated shoreward, but otherwise has not changed significantly since the breach. -
Summary of 2017 Massachusetts Piping Plover Census Data
SUMMARY OF THE 2017 MASSACHUSETTS PIPING PLOVER CENSUS Bill Byrne, MassWildlife SUMMARY OF THE 2017 MASSACHUSETTS PIPING PLOVER CENSUS ABSTRACT This report summarizes data on abundance, distribution, and reproductive success of Piping Plovers (Charadrius melodus) in Massachusetts during the 2017 breeding season. Observers reported breeding pairs of Piping Plovers present at 147 sites; 180 additional sites were surveyed at least once, but no breeding pairs were detected at them. The population increased 1.4% relative to 2016. The Index Count (statewide census conducted 1-9 June) was 633 pairs, and the Adjusted Total Count (estimated total number of breeding pairs statewide for the entire 2017 breeding season) was 650.5 pairs. A total of 688 chicks were reported fledged in 2017, for an overall productivity of 1.07 fledglings per pair, based on data from 98.4% of pairs. Prepared by: Natural Heritage & Endangered Species Program Massachusetts Division of Fisheries & Wildlife 2 SUMMARY OF THE 2017 MASSACHUSETTS PIPING PLOVER CENSUS INTRODUCTION Piping Plovers are small, sand-colored shorebirds that nest on sandy beaches and dunes along the Atlantic Coast from North Carolina to Newfoundland. The U.S. Atlantic Coast population of Piping Plovers has been federally listed as Threatened, pursuant to the U.S. Endangered Species Act, since 1986. The species is also listed as Threatened by the Massachusetts Division of Fisheries and Wildlife pursuant to Massachusetts’ Endangered Species Act. Population monitoring is an integral part of recovery efforts for Atlantic Coast Piping Plovers (U.S. Fish and Wildlife Service 1996, Hecht and Melvin 2009a, b). It allows wildlife managers to identify limiting factors, assess effects of management actions and regulatory protection, and track progress toward recovery. -
Boston Harbor South Watersheds 2004 Assessment Report
Boston Harbor South Watersheds 2004 Assessment Report June 30, 2004 Prepared for: Massachusetts Executive Office of Environmental Affairs Prepared by: Neponset River Watershed Association University of Massachusetts, Urban Harbors Institute Boston Harbor Association Fore River Watershed Association Weir River Watershed Association Contents How rapidly is open space being lost?.......................................................35 Introduction ix What % of the shoreline is publicly accessible?........................................35 References for Boston Inner Harbor Watershed........................................37 Common Assessment for All Watersheds 1 Does bacterial pollution limit fishing or recreation? ...................................1 Neponset River Watershed 41 Does nutrient pollution pose a threat to aquatic life? ..................................1 Does bacterial pollution limit fishing or recreational use? ......................46 Do dissolved oxygen levels support aquatic life?........................................5 Does nutrient pollution pose a threat to aquatic life or other uses?...........48 Are there other water quality problems? ....................................................6 Do dissolved oxygen (DO) levels support aquatic life? ..........................51 Do water supply or wastewater management impact instream flows?........7 Are there other indicators that limit use of the watershed? .....................53 Roughly what percentage of the watersheds is impervious? .....................8 Do water supply, -
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. -
Quincy Report
2019 GREATEST FLOOD RISK: HISTORICAL FLOOD EVENTS SEVERE WINTER • 9/1938 “The Great New England Hurricane” 10-17 inches of rain and 20-foot storm surge WEATHER COASTAL EROSION • 2/1978 “Blizzard of ’78” 30 inch snowfall, 30-foot waves off shore 24 RL claims COASTAL AND INLAND FLOODING • 10/1991 “Perfect Storm” 25 foot waves coincided with high tide 69 RL claims NOR’ EASTERS • 4/2010 “Nor’easter” 7 inches rain, coastal flooding and high tide. 52 RL claims • 1/2018 Nor’easter “Greyson” Peak winds coinciding with high tide broke Boston Harbor 1978 high tide record. • 3/2018- Nor’easters “Riley & Skylar” Blizzard, high wind and storm surge. FEMA DR-4372/ 4379 2) Identify Risk from “All Hazards” TOP NATURAL HAZARD RISKS FOR QUINCY image sample Coastal Flooding Flood Inland Flooding Storms and Tides Related Culvert Failures Storm Surge Sea Level Rise Climate Severe Snow and Blizzards Change Winter Extreme Precipitation Ice Storms Hurricanes Coastal Climatic Nor’easters Related Erosion & Shoreline Change Tropical Storm Tsunami Urban Fire Fire Earthquake Geologic Wildfire Landslides High Wind Severe Extreme Temperature (Heat and Cold Tornado Weather Drought Thunderstorm AREAS OF FLOODING CONCERNS FEMA REPETITIVE LOSS CLAIMS RL HOUGHS NECK GERMANTOWN RL FURNACE BROOK Identify extent & magnitude of flooding from tides, storm surge, and sea level rise… CLIMATE CHANGE FLOODING IMPACTS • Recommended approach for sea level rise estimates for projecting future coastal flooding risk in Quincy MA Sea Level Rise Time Period Projection² Likely Range³ (Feet) -
2019 Coastal Massachusetts COASTSWEEP Results
Results of the COASTSWEEP 2019 Cleanups Organization Coordinator Site(s) Town(s) People Pounds Miles Sustainable Practices Karla Cabral Craigville Beach, Covells Beach Barnstable 29 46 0.50 Sustainable Practices Karla Cabral Kalmus Beach Barnstable 9 18 0.50 Town of Barnstable Susan Brinckerhoff Millway Beach Barnstable 23 2 0.50 Town of Barnstable Betsy Wheeler Rendezvous Lane Barnstable 1 10 0.50 Town of Barnstable Robert Parsons Scudders Lane Barnstable 13 50 1 Town of Barnstable Fred Stepanis Sandy Neck Beach Barnstable 37 100 6.00 Sustainable Practices Patrick Otton Town Beach Barnstable 13 40 0.75 Rotary Club of Osterville Anke Rudy Dowes Beach Barnstable 38 50 2.00 Wellfleet Recycling Committee and Sustainable Christine Shreves Duck Harbor Barnstable 11 25 0.25 Practices Salem Sound Coastwatch Margaret Duffy Dane Street Beach Beverly 24 30 0.50 Endicott College Lori Mitchener Endicott College Beach Beverly 2 7 0.25 Salem Sound Coastwatch Margaret Duffy West Beach Beverly 8 13 1.00 Glen Urquhart School Laura Doyle Dane Street Beach Beverly 25 10 0.25 Salem Sound Coastwatch Margaret Duffy McPherson Park Beverly 8 20 0.25 Results of the COASTSWEEP 2019 Cleanups Organization Coordinator Site(s) Town(s) People Pounds Miles Salem Sound Coastwatch Margaret Duffy Sandy Point Beverly 7 60 0.50 Urban Harbors Institute and the School for the Kimberly Starbuck UMass Boston Beach Boston 100 200 2.00 Environment at UMass Boston Tenacre Country Day School Leah Staffier Carson Beach Boston 30 30 0.50 ClearView Healthcare Partners Mara Blumenstein