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CONSERVING THE BIODIVERSITY OF MASSACHUSETTS IN A CHANGING WORLD

This report and associated map provide information about important sites for biodiversity conservation in your area.

This information is intended for conservation planning, and is not intended for use in state regulations.

BioMap2 Conserving the Biodiversity of Massachusetts in a Changing World

Table of Contents

Introduction

What is BioMap2 – Purpose and applications

One plan, two components

Understanding Core Habitat and its components

Understanding Critical Natural Landscape and its components

Understanding Core Habitat and Critical Natural Landscape Summaries

Sources of Additional Information

Boston Overview

Core Habitat and Critical Natural Landscape Summaries

Elements of BioMap2 Cores

Core Habitat Summaries

Elements of BioMap2 Critical Natural Landscapes

Critical Natural Landscape Summaries

Natural Heritage Massachusetts Division of Fisheries and Wildlife 1 Rabbit Hill Road, Westborough, MA 01581 & Endangered phone: 508‐389‐6360 fax: 508‐389‐7890 Species Program For more information on rare species and natural communities, please see our fact sheets online at www.mass.gov/nhesp.

BioMap2 Conserving the Biodiversity of Massachusetts in a Changing World

Introduction The Massachusetts Department of Fish & Game, through the Division of Fisheries and Wildlife’s Natural Heritage & Endangered Species Program (NHESP), and The Nature Conservancy’s Massachusetts Program developed BioMap2 to protect the state’s biodiversity in the context of climate change. BioMap2 combines NHESP’s 30 years of rigorously documented rare species and natural community data with spatial data identifying wildlife species and habitats that were the focus of the Division of Fisheries and Wildlife’s 2005 State Wildlife Action Plan (SWAP). BioMap2 also integrates The Nature Conservancy’s assessment of large, well‐connected, and intact ecosystems and landscapes across the Commonwealth, incorporating concepts of ecosystem resilience Get your copy of the BioMap2 report! Download to address anticipated climate change impacts. from www.mass.gov/nhesp or contact Natural Heritage at 508-389-6360 or Protection and stewardship of BioMap2 Core [email protected]. Habitat and Critical Natural Landscape is essential to safeguard the diversity of species • Threatened species are likely to become and their habitats, intact ecosystems, and Endangered in Massachusetts in the resilient natural landscapes across foreseeable future throughout all or a Massachusetts. significant portion of their range. • Special Concern species have suffered a decline that could threaten the species if What Does Status Mean? allowed to continue unchecked or occur in The Division of Fisheries and Wildlife such small numbers or with such restricted determines a status category for each rare distribution or specialized habitat species listed under the Massachusetts requirements that they could easily become Endangered Species Act, M.G.L. c.131A, and its Threatened in Massachusetts. implementing regulations 321 CMR 10.00. Rare In addition NHESP maintains an unofficial species are categorized as Endangered, watch list of plants that are tracked due to Threatened or of Special Concern according to potential conservation interest or concern, but the following: are not regulated under the Massachusetts • Endangered species are in danger of Endangered Species Act or other laws or extinction throughout all or a significant regulations. Likewise, described natural portion of their range or are in danger of communities are not regulated by any law or extirpation from Massachusetts. regulations, but they can help to identify

BioMap2 Conserving the Biodiversity of Massachusetts in a Changing World

ecologically important areas that are worthy of Core Habitat identifies key areas that are critical protection. The status of natural communities for the long‐term persistence of rare species and reflects the documented number and acreages of other Species of Conservation Concern, as well each community type in the state: as a wide diversity of natural communities and intact ecosystems across the Commonwealth. • Critically Imperiled communities typically Protection of Core Habitats will contribute to the have 5 or fewer documented sites or have conservation of specific elements of biodiversity. very few remaining acres in the state. • Imperiled communities typically have 6‐20 Critical Natural Landscape identifies large sites or few remaining acres in the state. natural Landscape Blocks that are minimally • Vulnerable communities typically have 21‐ impacted by development. If protected, these 100 sites or limited acreage across the state. areas will provide habitat for wide‐ranging • Secure communities typically have over 100 native species, support intact ecological sites or abundant acreage across the state; processes, maintain connectivity among however, excellent examples are identified habitats, and enhance ecological resilience to as Core Habit to ensure continued natural and anthropogenic disturbances in a protection. rapidly changing world. Areas delineated as Critical Natural Landscape also include In 2005 the Massachusetts Division of Fisheries buffering upland around wetland, coastal, and and Wildlife completed a comprehensive State aquatic Core Habitats to help ensure their long‐ Wildlife Action Plan (SWAP) documenting the term integrity. status of Massachusetts wildlife and providing recommendations to help guide wildlife The long‐term persistence of Massachusetts conservation decision‐making. SWAP includes biological resources requires a determined all the wildlife species listed under the commitment to land and water conservation. Massachusetts Endangered Species Act (MESA), Protection and stewardship of both Critical as well as more than 80 species that need Natural Landscapes and Core Habitats are conservation attention but do not meet the needed to realize the biodiversity conservation requirements for inclusion under MESA. The vision of BioMap2. SWAP document is organized around habitat types in need of conservation within the Commonwealth. While the original BioMap Components of Core Habitat focused primarily on rare species protected Core Habitat identifies specific areas necessary under MESA, BioMap2 also addresses other to promote the long‐term persistence of rare Species of Conservation Concern, their habitats, species, other Species of Conservation Concern, and the ecosystems that support them to create a exemplary natural communities, and intact spatial representation of most of the elements of ecosystems. SWAP.

Rare Species BioMap2: One Plan, Two Components There are 432 native plant and animal species BioMap2 identifies two complementary spatial listed as Endangered, Threatened or Special layers, Core Habitat and Critical Natural Concern under the Massachusetts Endangered Landscape. Species Act (MESA) based on their rarity, population trends, and threats to survival. For

BioMap2 Conserving the Biodiversity of Massachusetts in a Changing World

Table 1. Species of Conservation Concern priority to natural communities with limited described in the State Wildlife Action Plan distribution and to the best examples of more and/or included on the MESA List and for which common types. habitat was mapped in BioMap2. Note that plants are not included in SWAP, and that Vernal Pools marine species such as whales and sea turtles are not included in BioMap2. Vernal pools are small, seasonal wetlands that provide important wildlife habitat, especially for

amphibians and invertebrate animals that use Taxonomic MESA‐ Non‐listed Species them to breed. BioMap2 identifies the top 5 Group listed of Conservation percent most interconnected clusters of Potential Species Concern Vernal Pools in the state. Mammals 4 5 Birds 27 23 Reptiles 10 5 Forest Cores Amphibians 4 3 In BioMap2, Core Habitat includes the best Fish 10 17 examples of large, intact forests that are least Invertebrates 102 9 impacted by roads and development, providing Plants 256 0 critical habitat for numerous woodland species. Total 413 62 For example, the interior forest habitat defined by Forest Cores supports many bird species

sensitive to the impacts of roads and BioMap2, NHESP staff identified the highest development, such as the Black‐throated Green quality habitat sites for each non‐marine species Warbler, and helps maintain ecological based on size, condition, and landscape context. processes found only in unfragmented forest patches. Other Species of Conservation Concern In addition to species on the MESA List Wetland Cores described previously, the State Wildlife Action BioMap2 used an assessment of Ecological Plan (SWAP) identifies 257 wildlife species and Integrity to identify the least disturbed wetlands 22 natural habitats most in need of conservation in the state within undeveloped landscapes— within the Commonwealth. BioMap2 includes those with intact buffers and little fragmentation species‐specific habitat areas for 45 of these or other stressors associated with development. species and habitat for 17 additional species These wetlands are most likely to support which was mapped with other coarse‐filter and critical wetland functions (i.e., natural fine‐filter approaches. hydrologic conditions, diverse plant and animal habitats, etc.) and are most likely to maintain Priority Natural Communities these functions into the future. Natural communities are assemblages of plant and animal species that share a common Aquatic Cores environment and occur together repeatedly on To delineate integrated and functional the landscape. BioMap2 gives conservation ecosystems for fish species and other aquatic

BioMap2 Conserving the Biodiversity of Massachusetts in a Changing World

Species of Conservation Concern, beyond the species and exemplary habitats described above, Legal Protection of Biodiversity BioMap2 identifies intact river corridors within BioMap2 presents a powerful vision of what which important physical and ecological Massachusetts would look like with full processes of the river or stream occur. protection of the land most important for supporting the Commonwealth’s biodiversity. While BioMap2 is a planning tool with no Components of Critical Natural Landscape regulatory function, all state‐listed species enjoy Critical Natural Landscape identifies intact legal protection under the Massachusetts landscapes in Massachusetts that are better able Endangered Species Act (M.G.L. c.131A) and its to support ecological processes and disturbance implementing regulations (321 CMR 10.00). regimes, and a wide array of species and Wetland habitat of state‐listed wildlife is also habitats over long time frames. protected under the Wetlands Protection Act Regulations (310 CMR 10.00). The Natural Landscape Blocks Heritage Atlas contains maps of Priority Habitats and Estimated Habitats, which are used, BioMap2 identifies the most intact large areas of respectively, for regulation under the predominately natural vegetation, consisting of Massachusetts Endangered Species Act and the contiguous forests, wetlands, rivers, lakes, and Wetlands Protection Act. For more information ponds, as well as coastal habitats such as barrier on rare species regulations, and to view Priority beaches and salt marshes. and Estimated Habitat maps, please see the Regulatory Review page at Upland Buffers of Wetland and Aquatic http://www.mass.gov/eea/agencies/dfg/dfw/natur Cores al‐heritage/regulatory‐review/regulatory‐maps‐ priority‐and‐estimated‐habitats/. A variety of analyses were used to identify protective upland buffers around wetlands and BioMap2 is a conservation planning tool that rivers. does not, in any way, supplant the Estimated and Priority Habitat Maps which have regulatory significance. Unless and until the Upland Habitat to Support Coastal BioMap2 vision is fully realized, we must Adaptation continue to protect our most imperiled species BioMap2 identifies undeveloped lands adjacent and their habitats. to and up to one and a half meters above existing salt marshes as Critical Natural create Core Habitat and Critical Natural Landscapes with high potential to support Landscape are complementary, and outline a inland migration of salt marsh and other coastal comprehensive conservation vision for habitats over the coming century. Massachusetts, from rare species to intact The conservation areas identified by BioMap2 landscapes. In total, these robust analyses are based on breadth and depth of data, define a suite of priority lands and waters that, if scientific expertise, and understanding of permanently protected, will support Massachusetts’ biodiversity. The numerous Massachusetts’ natural systems for generations sources of information and analyses used to to come.

BioMap2 Conserving the Biodiversity of Massachusetts in a Changing World

Understanding Core Habitat Summaries Following the Town Overview, there is a descriptive summary of each Core Habitat and Critical Natural Landscape that occurs in your city or town. These summaries highlight some of the outstanding characteristics of each Core Habitat and Critical Natural Landscape, and will help you learn more about your city or town’s biodiversity. You can find out more information about many of these species and natural communities by looking at specific fact sheets at www.mass.gov/nhesp.

Additional Information For copies of the full BioMap2 report, the Technical Report, and an interactive mapping tool, visit the BioMap2 website via the Land Protection and Planning tab at www.mass.gov/nhesp. If you have any questions about this report, or if you need help protecting land for biodiversity in your community, the Natural Heritage & Endangered Species Program staff looks forward to working with you.

Contact the Natural Heritage & Endangered Species Program By phone 508‐389‐6360 By fax 508‐389‐7890 By email [email protected] By Mail 100 Hartwell Street, Suite 230 West Boylston, MA 01583 The GIS datalayers of BioMap2 are available for download from MassGIS at www.mass.gov/mgis.

BioMap2 Conserving the Biodiversity of Massachusetts in a Changing World

Town Overview Boston at a Glance • Total Area: 31,760 acres (49.6 square miles) Boston lies within the Boston Basin Ecoregion, an • Human Population in 2010: 617,594 area defined by a rim of low hills and outlying • Open space protected in perpetuity: 4,857 hilly suburban towns. The basin itself has low acres, or 15.3% percent of total area* rolling topography and numerous urban • BioMap2 Core Habitat: 2,341 acres reservoirs, lakes, and ponds. The flat areas were • BioMap2 Core Habitat Protected: 1,108 acres once tilled, but are now almost exclusively urban or 47.3% and suburban developments. • BioMap2 Critical Natural Landscape: 540 acres • BioMap2 Critical Natural Landscape Protected: 401 acres or 74.3%.

BioMap2 Components

Core Habitats • 3 Exemplary or Priority Natural Community Cores • 3Aquatic Cores • 28 Species of Conservation Concern Cores** o 9 birds, 2 amphibians, 1 fish, 1 insects, 1 plant

Critical Natural Landscape • 3 Aquatic Core Buffers • 2 Coastal Adaptation Areas • 1Tern Foraging Area

* Calculated using MassGIS data layer “Protected and Recreational Open Space—March, 2012”. ** See next pages for complete list of species, natural communities and other biodiversity elements.

BioMap2 Conserving the Biodiversity of Massachusetts in a Changing World

BioMap2 Core Habitat and Critical Natural Landscape in Boston

BioMap2 Conserving the Biodiversity of Massachusetts in a Changing World

Species of Conservation Concern, Priority and Exemplary Natural Communities, and Other Elements of Biodiversity in Boston

Insects Moths Orange Sallow Moth, (Pyrrhia aurantiago), SC Amphibians Northern Leopard Frog, (Rana pipiens), Non‐listed SWAP Blue‐spotted Salamander, (Ambystoma laterale), SC Fishes Threespine Stickleback, (Gasterosteus aculeatus), T Birds Upland Sandpiper, (Bartramia longicauda), E Least Bittern, (Ixobrychus exilis), E Black‐crowned Night‐heron, (Nycticorax nycticorax), Non‐listed SWAP Snowy Egret, (Egretta thula), Non‐listed SWAP Common Tern, (Sterna hirundo), SC Least Tern, (Sternula antillarum), SC Barn Owl, (Tyto alba), SC Grasshopper Sparrow, (Ammodramus savannarum), T Vesper Sparrow, (Pooecetes gramineus), T Plants Longʹs Bulrush, (Scirpus longii), T Priority Natural Communities Estuarine intertidal: brackish tidal marsh, S1 Maritime shrubland community, S3 Estuarine intertidal: salt marsh, S3 Other BioMap2 Components Aquatic Core Aquatic Core Buffer Coastal Adaptation Area Tern Foraging Area

E = Endangered T = Threatened SC = Special Concern S1 = Critically Imperiled communities, typically 5 or fewer documented sites or very few remaining acres in the state. S2 = Imperiled communities, typically 6‐20 sites or few remaining acres in the state. S3 = Vulnerable communities, typically have 21‐100 sites or limited acreage across the state.

BioMap2 Conserving the Biodiversity of Massachusetts in a Changing World

BioMap2 Core Habitat in Boston Core IDs correspond with the following element lists and summaries.

BioMap2 Conserving the Biodiversity of Massachusetts in a Changing World

Elements of BioMap2 Cores This section lists all elements of BioMap2 Cores that fall entirely or partially within Boston. The elements listed here may not occur within the bounds of Boston.

Core 1497 Aquatic Core Vernal Pool Core Species of Conservation Concern Brittonʹs Violet Viola brittoniana T Longʹs Bulrush Scirpus longii T Pale Green Orchis Platanthera flava var. herbiola T Northern Leopard Frog Rana pipiens Non‐listed SWAP Least Bittern Ixobrychus exilis E

Core 1596/1613 Species of Conservation Concern Orange Sallow Moth Pyrrhia aurantiago SC

Core 1686 Aquatic Core Species of Conservation Concern Smooth Green Snake Opheodrys vernalis Non‐listed SWAP Barn Owl Tyto alba SC

Core 1711 Species of Conservation Concern Barn Owl Tyto alba SC Least Tern Sternula antillarum SC

Core 1725 Priority & Exemplary Natural Communities Estuarine intertidal: salt marsh S3 Species of Conservation Concern Barn Owl Tyto alba SC

Core 1729 Species of Conservation Concern Vesper Sparrow Pooecetes gramineus T

BioMap2 Conserving the Biodiversity of Massachusetts in a Changing World

Core 1735/1738/1757/1760/1764/1773/1784/1829 Species of Conservation Concern Barn Owl Tyto alba SC

Core 1746 Species of Conservation Concern Threespine Stickleback Gasterosteus aculeatus T

Core 1749 Species of Conservation Concern Common Tern Sterna hirundo SC

Core 1756 Species of Conservation Concern Barn Owl Tyto alba SC Black‐crowned Night‐heron Nycticorax nycticorax Non‐listed SWAP

Core 1772 Species of Conservation Concern Barn Owl Tyto alba SC Least Tern Sternula antillarum SC

Core 1788 Species of Conservation Concern Black‐crowned Night‐heron Nycticorax nycticorax Non‐listed SWAP Snowy Egret Egretta thula Non‐listed SWAP

Core 1805 Species of Conservation Concern Black‐crowned Night‐heron Nycticorax nycticorax Non‐listed SWAP Snowy Egret Egretta thula Non‐listed SWAP

Core 1806 Priority & Exemplary Natural Communities Estuarine intertidal: brackish tidal marsh S1 Maritime shrubland community S3 Species of Conservation Concern Black‐crowned Night‐heron Nycticorax nycticorax Non‐listed SWAP

Core 1868 Aquatic Core Priority & Exemplary Natural Communities Level bog S3 Species of Conservation Concern

BioMap2 Conserving the Biodiversity of Massachusetts in a Changing World

Brittonʹs Violet Viola brittoniana T Longʹs Bulrush Scirpus longii T Creeper Strophitus undulatus SC Umber Shadowdragon Neurocordulia obsoleta SC Blue‐spotted Salamander Ambystoma laterale SC

Core 1880/1913/1917 Species of Conservation Concern Common Tern Sterna hirundo SC

Core 1887 Species of Conservation Concern Barn Owl Tyto alba SC Grasshopper Sparrow Ammodramus savannarum T Least Tern Sternula antillarum SC Upland Sandpiper Bartramia longicauda E

BioMap2 Conserving the Biodiversity of Massachusetts in a Changing World

Core Habitat Summaries

Core 1497 A 979‐acre Core Habitat featuring Aquatic Core, Vernal Pool Core, and Species of Conservation Concern. Aquatic Cores are intact river corridors within which important physical and ecological processes of the river or stream occur. They delineate integrated and functional ecosystems for fish species and other aquatic Species of Conservation Concern. Vernal pools are small, seasonal wetlands that provide important wildlife habitat, especially for amphibians and invertebrate animals that use them to breed. BioMap2 identifies the top 5 percent most interconnected clusters of Potential Vernal Pools in the state. Britton’s Violet is a low‐growing, herbaceous perennial found along the edges of floodplains of freshwater rivers. Long’s Bulrush is a globally rare, robust sedge of open peaty wetlands. In Massachusetts, Long’s Bulrush is known to occur in acidic fen and wet meadow communities associated with rivers. In Massachusetts, Pale Green Orchis inhabits open to semi‐shaded habitats in rich, moderately acidic, wet areas subject to seepage, intermittent flooding, or water level fluctuation. Adult Northern Leopard Frogs are found in marshes, wet meadows, and peatlands in the narrow transition zone between open water and uplands; they retreat to the water of ponds and small streams when threatened. The herbivorous tadpoles require open water of sufficient permanence for their development. Least Bitterns are heron‐like birds that typically nest in cattail marshes interspersed with open water and are very sensitive to disturbance.

Core 1596 A 10‐acre Core Habitat featuring a Species of Conservation Concern. Orange Sallow Moths inhabit dry, open oak woodlands on rocky uplands. Their eggs are laid on false foxgloves (Aureolaria spp.) where the larvae feed on the flowers and developing seeds.

Core 1613 A 443‐acre Core Habitat featuring Species of Conservation Concern. Orange Sallow Moths inhabit dry, open oak woodlands on rocky uplands. Their eggs are laid on false foxgloves (Aureolaria spp.) where the larvae feed on the flowers and developing seeds.

Core 1686 A 923‐acre Core Habitat featuring Aquatic Core and Species of Conservation Concern.

BioMap2 Conserving the Biodiversity of Massachusetts in a Changing World

Aquatic Cores are intact river corridors within which important physical and ecological processes of the river or stream occur. They delineate integrated and functional ecosystems for fish species and other aquatic Species of Conservation Concern. A small to medium‐sized snake, adult Smooth Green Snakes are 14‐20 inches long with a uniform light green back and yellow to white venter. The Smooth Green Snake is found in moist open or lightly forested habitat where grasses and shrubs are abundant (edges of marshes, wet meadows, fields, and forest edges or open forests, grasslands, blueberry barrens, pine barrens) and prefers to forage on the ground with activity in the daytime. Smooth Green Snake overwinter in rodent burrows, ant mounds and rock crevices, either singly or communally. Barn Owls require grassy habitats for foraging, such as fresh and salt water marshes and agricultural fields. They rarely occur apart from populations of meadow voles, a primary food source, and avoid areas of deep snow and prolonged cold, which can preclude successful foraging. The Barn Owl is resourceful in making use of such nesting sites as hollow trees, cavities in cliffs or riverbanks, and artificial structures such as nest boxes, old barns, and bridges.

Core 1711 A 25‐acre Core Habitat featuring Species of Conservation Concern. Barn Owls require grassy habitats for foraging, such as fresh and salt water marshes and agricultural fields. They rarely occur apart from populations of meadow voles, a primary food source, and avoid areas of deep snow and prolonged cold, which can preclude successful foraging. The Barn Owl is resourceful in making use of such nesting sites as hollow trees, cavities in cliffs or riverbanks, and artificial structures such as nest boxes, old barns, and bridges. Diminutive yet feisty, the Least Tern is a spring and summer colonial nester on Massachusetts’ sandy beaches. For nesting, it favors for sites with little or no vegetation. In Massachusetts, the Least Tern nests on sandy or gravelly beaches periodically scoured by storm tides, resulting in sparse or no vegetation; it also takes advantage of dredge spoils. Along the coast, the Least Tern forages in shallow‐water habitats, including bays, lagoons, estuaries, river and creek mouths, tidal marshes, and ponds.

Core 1725 A 91‐acre Core Habitat featuring a Priority Natural Community and a Species of Conservation Concern. The Salt Marsh community type is a graminoid dominated, tidally flooded coastal community with several vegetative zones. Salt Marshes form in areas subject to oceanic tides, but sheltered from wave energy. This example of Salt Marsh is large for the Boston Harbor Islands and natural processes are working. The surrounding area is very disturbed with many invasive species; the salt marsh has several invasives. All salt marsh in the Harbor Islands combine as one occurrence. Barn Owls require grassy habitats for foraging, such as fresh and salt water marshes and agricultural fields. They rarely occur apart from populations of meadow voles, a primary food source, and avoid areas of deep snow and prolonged cold, which can preclude successful foraging. The Barn Owl is resourceful in making use of such nesting sites as hollow trees, cavities in cliffs or riverbanks, and artificial structures such as nest boxes, old barns, and bridges.

BioMap2 Conserving the Biodiversity of Massachusetts in a Changing World

Core 1729 A 19‐acre Core Habitat featuring a Species of Conservation Concern. Vesper Sparrows typically nest in large open, dry sites with a mixture of short herbaceous vegetation and bare ground. They have become rare breeders in Massachusetts despite being attracted to anthropogenic landscapes for breeding, such as potato fields, abandoned sandpits, and the disturbed margins of airports.

Core 1735 An 8‐acre Core Habitat featuring a Species of Conservation Concern. Barn Owls require grassy habitats for foraging, such as fresh and salt water marshes and agricultural fields. They rarely occur apart from populations of meadow voles, a primary food source, and avoid areas of deep snow and prolonged cold, which can preclude successful foraging. The Barn Owl is resourceful in making use of such nesting sites as hollow trees, cavities in cliffs or riverbanks, and artificial structures such as nest boxes, old barns, and bridges.

Core 1738 A 40‐acre Core Habitat featuring a Species of Conservation Concern. Barn Owls require grassy habitats for foraging, such as fresh and salt water marshes and agricultural fields. They rarely occur apart from populations of meadow voles, a primary food source, and avoid areas of deep snow and prolonged cold, which can preclude successful foraging. The Barn Owl is resourceful in making use of such nesting sites as hollow trees, cavities in cliffs or riverbanks, and artificial structures such as nest boxes, old barns, and bridges.

Core 1746 A <1‐acre Core Habitat featuring a Species of Conservation Concern. The freshwater Threespine Stickleback is a very small, armored fish with three serrated dorsal spines. Threespine Sticklebacks can be common in both marine and freshwater environments. However, one population of Threespine Stickleback in Massachusetts is unusual, and it is only this population which is state Threatened. This population is the southernmost, completely freshwater population known and the only freshwater population in Massachusetts.

Core 1749 A <1‐acre Core Habitat featuring a Species of Conservation Concern. The Common Tern is a small seabird that nests in colonies on sandy or gravelly islands and barrier beaches, but also occurs on rocky or cobbly beaches and salt marshes. It feeds on small fish, crustaceans, and flying insects in the open ocean, bays, tidal inlets, and between islands.

Core 1756 A 32‐acre Core Habitat featuring Species of Conservation Concern.

BioMap2 Conserving the Biodiversity of Massachusetts in a Changing World

Barn Owls require grassy habitats for foraging, such as fresh and salt water marshes and agricultural fields. They rarely occur apart from populations of meadow voles, a primary food source, and avoid areas of deep snow and prolonged cold, which can preclude successful foraging. The Barn Owl is resourceful in making use of such nesting sites as hollow trees, cavities in cliffs or riverbanks, and artificial structures such as nest boxes, old barns, and bridges. The breeding colonies of Black‐crowned Night‐herons, stocky, short‐legged herons, are widely distributed along the Massachusetts coast. Habitats of Black‐crowned Night‐herons in Massachusetts include salt marshes and tidal flats, fresh and brackish marshes, ponds, and creeks. Night‐herons are primarily nocturnal and crepuscular foragers on small fish, amphibians, crabs and other crustaceans, and insects.

Core 1757 A 90‐acre Core Habitat featuring a Species of Conservation Concern. Barn Owls require grassy habitats for foraging, such as fresh and salt water marshes and agricultural fields. They rarely occur apart from populations of meadow voles, a primary food source, and avoid areas of deep snow and prolonged cold, which can preclude successful foraging. The Barn Owl is resourceful in making use of such nesting sites as hollow trees, cavities in cliffs or riverbanks, and artificial structures such as nest boxes, old barns, and bridges.

Core 1760 A 4‐acre Core Habitat featuring a Species of Conservation Concern. Barn Owls require grassy habitats for foraging, such as fresh and salt water marshes and agricultural fields. They rarely occur apart from populations of meadow voles, a primary food source, and avoid areas of deep snow and prolonged cold, which can preclude successful foraging. The Barn Owl is resourceful in making use of such nesting sites as hollow trees, cavities in cliffs or riverbanks, and artificial structures such as nest boxes, old barns, and bridges.

Core 1764 An 18‐acre Core Habitat featuring a Species of Conservation Concern. Barn Owls require grassy habitats for foraging, such as fresh and salt water marshes and agricultural fields. They rarely occur apart from populations of meadow voles, a primary food source, and avoid areas of deep snow and prolonged cold, which can preclude successful foraging. The Barn Owl is resourceful in making use of such nesting sites as hollow trees, cavities in cliffs or riverbanks, and artificial structures such as nest boxes, old barns, and bridges.

Core 1772 A 73‐acre Core Habitat featuring Species of Conservation Concern. Barn Owls require grassy habitats for foraging, such as fresh and salt water marshes and agricultural fields. They rarely occur apart from populations of meadow voles, a primary food source, and avoid areas of deep snow and prolonged cold, which can preclude successful foraging. The Barn Owl is

BioMap2 Conserving the Biodiversity of Massachusetts in a Changing World

resourceful in making use of such nesting sites as hollow trees, cavities in cliffs or riverbanks, and artificial structures such as nest boxes, old barns, and bridges. Diminutive yet feisty, the Least Tern is a spring and summer colonial nester on Massachusetts’ sandy beaches. For nesting, it favors for sites with little or no vegetation. In Massachusetts, the Least Tern nests on sandy or gravelly beaches periodically scoured by storm tides, resulting in sparse or no vegetation; it also takes advantage of dredge spoils. Along the coast, the Least Tern forages in shallow‐water habitats, including bays, lagoons, estuaries, river and creek mouths, tidal marshes, and ponds.

Core 1773 A 22‐acre Core Habitat featuring a Species of Conservation Concern. Barn Owls require grassy habitats for foraging, such as fresh and salt water marshes and agricultural fields. They rarely occur apart from populations of meadow voles, a primary food source, and avoid areas of deep snow and prolonged cold, which can preclude successful foraging. The Barn Owl is resourceful in making use of such nesting sites as hollow trees, cavities in cliffs or riverbanks, and artificial structures such as nest boxes, old barns, and bridges.

Core 1784 A 21‐acre Core Habitat featuring a Species of Conservation Concern. Barn Owls require grassy habitats for foraging, such as fresh and salt water marshes and agricultural fields. They rarely occur apart from populations of meadow voles, a primary food source, and avoid areas of deep snow and prolonged cold, which can preclude successful foraging. The Barn Owl is resourceful in making use of such nesting sites as hollow trees, cavities in cliffs or riverbanks, and artificial structures such as nest boxes, old barns, and bridges.

Core 1788 A 13‐acre Core Habitat featuring Species of Conservation Concern. The breeding colonies of Black‐crowned Night‐herons, stocky, short‐legged herons, are widely distributed along the Massachusetts coast. Habitats of Black‐crowned Night‐herons in Massachusetts include salt marshes and tidal flats, fresh and brackish marshes, ponds, and creeks. Night‐herons are primarily nocturnal and crepuscular foragers on small fish, amphibians, crabs and other crustaceans, and insects. Medium‐sized white herons, Snowy Egrets nest in mixed colonies with other species of egrets and herons. The nests are in trees or patches of shrubs on coastal islands, presumably to reduce the likelihood of mammalian predation. Snowy Egrets forage in marshes and ponds near their breeding colonies for small fish, snails, and aquatic invertebrates.

Core 1805 A 19‐acre Core Habitat featuring Species of Conservation Concern.

BioMap2 Conserving the Biodiversity of Massachusetts in a Changing World

The breeding colonies of Black‐crowned Night‐herons, stocky, short‐legged herons, are widely distributed along the Massachusetts coast. Habitats of Black‐crowned Night‐herons in Massachusetts include salt marshes and tidal flats, fresh and brackish marshes, ponds, and creeks. Night‐herons are primarily nocturnal and crepuscular foragers on small fish, amphibians, crabs and other crustaceans, and insects. Medium‐sized white herons, Snowy Egrets nest in mixed colonies with other species of egrets and herons. The nests are in trees or patches of shrubs on coastal islands, presumably to reduce the likelihood of mammalian predation. Snowy Egrets forage in marshes and ponds near their breeding colonies for small fish, snails, and aquatic invertebrates.

Core 1806 A 21‐acre Core Habitat featuring Priority Natural Communities and a Species of Conservation Concern. The Brackish Tidal Marsh community is often found in stretches of coastal rivers where salt and fresh water mix, and consists of mixed herbaceous vegetation that is flooded by daily tides. Despite this small example of Brackish Tidal Marsh’s abundance of non‐native species it supports a good diversity of native plants. Maritime Shrubland communities are dominated by patches of dense shrubs with scattered areas of more open low growth or bare ground. These communities are coastal and receive salt spray during storms. They occur on rocky headlands or behind dunes. This Maritime Shrubland Community is very exposed to storms. Its lack of diversity with few trees is typical of the Staghorn sumac communities of the outer Harbor islands as is its thick undergrowth of non‐native grass. The breeding colonies of Black‐crowned Night‐herons, stocky, short‐legged herons, are widely distributed along the Massachusetts coast. Habitats of Black‐crowned Night‐herons in Massachusetts include salt marshes and tidal flats, fresh and brackish marshes, ponds, and creeks. Night‐herons are primarily nocturnal and crepuscular foragers on small fish, amphibians, crabs and other crustaceans, and insects.

Core 1829 A 156‐acre Core Habitat featuring a Species of Conservation Concern. Barn Owls require grassy habitats for foraging, such as fresh and salt water marshes and agricultural fields. They rarely occur apart from populations of meadow voles, a primary food source, and avoid areas of deep snow and prolonged cold, which can preclude successful foraging. The Barn Owl is resourceful in making use of such nesting sites as hollow trees, cavities in cliffs or riverbanks, and artificial structures such as nest boxes, old barns, and bridges.

Core 1868 A 3,095‐acre Core Habitat featuring Aquatic Core, Priority Natural Communities, and Species of Conservation Concern.

BioMap2 Conserving the Biodiversity of Massachusetts in a Changing World

Aquatic Cores are intact river corridors within which important physical and ecological processes of the river or stream occur. They delineate integrated and functional ecosystems for fish species and other aquatic Species of Conservation Concern. Level Bogs are dwarf‐shrub peatlands, generally with pronounced hummocks and hollows in sphagnum moss. These wetland communities are very acidic and nutrient‐poor because the peat isolates them from nutrients in groundwater and streams. This small bog in the midst of an urban park is in very good condition despite occasional buckthorn plants. It is protected and buffered from disturbance by a surrounding shrub swamp. Britton’s Violet is a low‐growing, herbaceous perennial found along the edges of floodplains of freshwater rivers. Long’s Bulrush is a globally rare, robust sedge of open peaty wetlands. In Massachusetts, Long’s Bulrush is known to occur in acidic fen and wet meadow communities associated with rivers. Creepers are freshwater mussels that inhabit low‐gradient reaches of small to large rivers with sand or gravel substrates. Cool to warm water with diverse fish assemblages best support Creepers. Umber Shadowdragons are dragonflies that are found on lakes with rocky shores and medium to large rivers that have relatively little aquatic vegetation. Shadowdragons fly only at dusk when they feed and mate in a frenzy of activity. Adult and juvenile Blue‐spotted Salamanders inhabit upland forests during most of the year, where they reside in small‐mammal burrows and other subsurface retreats. Adults migrate during late winter or early spring to breed in vernal pools and fish‐free areas of swamps, marshes, or similar wetlands. Larvae metamorphose in late summer or early fall, whereupon they disperse into upland forest.

Core 1880 A 7‐acre Core Habitat featuring a Species of Conservation Concern. The Common Tern is a small seabird that nests in colonies on sandy or gravelly islands and barrier beaches, but also occurs on rocky or cobbly beaches and salt marshes. It feeds on small fish, crustaceans, and flying insects in the open ocean, bays, tidal inlets, and between islands.

Core 1887 A 1,088‐acre Core Habitat featuring Species of Conservation Concern. Barn Owls require grassy habitats for foraging, such as fresh and salt water marshes and agricultural fields. They rarely occur apart from populations of meadow voles, a primary food source, and avoid areas of deep snow and prolonged cold, which can preclude successful foraging. The Barn Owl is resourceful in making use of such nesting sites as hollow trees, cavities in cliffs or riverbanks, and artificial structures such as nest boxes, old barns, and bridges. Grasshopper Sparrows nest in dry grasslands. Natural situations include sandplain grasslands, but they have adapted well to anthropogenic habitats such as airports and landfills. They are very sensitive to changes in plant composition and respond well to the effects of fire management.

BioMap2 Conserving the Biodiversity of Massachusetts in a Changing World

Diminutive yet feisty, the Least Tern is a spring and summer colonial nester on Massachusetts’ sandy beaches. For nesting, it favors for sites with little or no vegetation. In Massachusetts, the Least Tern nests on sandy or gravelly beaches periodically scoured by storm tides, resulting in sparse or no vegetation; it also takes advantage of dredge spoils. Along the coast, the Least Tern forages in shallow‐water habitats, including bays, lagoons, estuaries, river and creek mouths, tidal marshes, and ponds. Upland Sandpipers require very large, unbroken tracts of grassland, and in Massachusetts are now relegated mostly to anthropogenic habitats such as airports. They are very sensitive to changes in plant composition and respond well to the effects of well‐planned fire management and thoughtful mowing regimes.

Core 1913 A 17‐acre Core Habitat featuring a Species of Conservation Concern. The Common Tern is a small seabird that nests in colonies on sandy or gravelly islands and barrier beaches, but also occurs on rocky or cobbly beaches and salt marshes. It feeds on small fish, crustaceans, and flying insects in the open ocean, bays, tidal inlets, and between islands.

Core 1917 A 93‐acre Core Habitat featuring a Species of Conservation Concern. The Common Tern is a small seabird that nests in colonies on sandy or gravelly islands and barrier beaches, but also occurs on rocky or cobbly beaches and salt marshes. It feeds on small fish, crustaceans, and flying insects in the open ocean, bays, tidal inlets, and between islands.

BioMap2 Conserving the Biodiversity of Massachusetts in a Changing World

BioMap2 Critical Natural Landscape in Boston Critical Natural Landscape IDs correspond with the following element lists and summaries.

BioMap2 Conserving the Biodiversity of Massachusetts in a Changing World

Elements of BioMap2 Critical Natural Landscapes This section lists all elements of BioMap2 Critical Natural Landscapes that fall entirely or partially within Boston. The elements listed here may not occur within the bounds of Boston. CNL 743 Aquatic Core Buffer CNL 858 Aquatic Core Buffer Coastal Adaptation Area CNL 875 Coastal Adaptation Area CNL 894 Coastal Adaptation Area CNL 902 Tern Foraging Area CNL 920 Aquatic Core Buffer Wetland Core Buffer CNL 939 Coastal Adaptation Area CNL 943 Coastal Adaptation Area

BioMap2 Conserving the Biodiversity of Massachusetts in a Changing World

Critical Natural Landscape Summaries CNL 743 A 631‐acre Critical Natural Landscape featuring Aquatic Core Buffer. A variety of analyses were used to identify protective upland buffers around wetlands and rivers. One, the variable width buffers methodology, included the most intact areas around each wetland and river, by extending deeper into surrounding unfragmented habitats than into developed areas adjacent to each wetland. Other upland buffers were identified through the rare species habitat analysis. In this way, the conservation of wetland buffers will support the habitats and functionality of each wetland, and also include adjacent uplands that are important for many species that move between habitat types. CNL 858 A 868‐acre Critical Natural Landscape featuring Aquatic Core Buffer, and Coastal Adaptation Area. A variety of analyses were used to identify protective upland buffers around wetlands and rivers. One, the variable width buffers methodology, included the most intact areas around each wetland and river, by extending deeper into surrounding unfragmented habitats than into developed areas adjacent to each wetland. Other upland buffers were identified through the rare species habitat analysis. In this way, the conservation of wetland buffers will support the habitats and functionality of each wetland, and also include adjacent uplands that are important for many species that move between habitat types. The coastal habitats of Massachusetts are particularly vulnerable to potential sea‐level rise in the next century, which many estimates suggest is likely to exceed one meter. Therefore, in addition to prioritizing current coastal habitats, the creators of BioMap2 examined the landward side of salt marshes to determine where these habitats might move to as sea levels rise. Undeveloped lands adjacent to and up to one and a half meters above existing salt marshes were identified, and included as Critical Natural Landscapes with high potential to support inland migration of salt marsh and other coastal habitats over the coming century. CNL 875 A 13‐acre Critical Natural Landscape featuring Coastal Adaptation Area. The coastal habitats of Massachusetts are particularly vulnerable to potential sea‐level rise in the next century, which many estimates suggest is likely to exceed one meter. Therefore, in addition to prioritizing current coastal habitats, the creators of BioMap2 examined the landward side of salt marshes to determine where these habitats might move to as sea levels rise. Undeveloped lands adjacent to and up to one and a half meters above existing salt marshes were identified, and included as Critical Natural Landscapes with high potential to support inland migration of salt marsh and other coastal habitats over the coming century.

BioMap2 Conserving the Biodiversity of Massachusetts in a Changing World

CNL 894 A 2‐acre Critical Natural Landscape featuring Coastal Adaptation Area. The coastal habitats of Massachusetts are particularly vulnerable to potential sea‐level rise in the next century, which many estimates suggest is likely to exceed one meter. Therefore, in addition to prioritizing current coastal habitats, the creators of BioMap2 examined the landward side of salt marshes to determine where these habitats might move to as sea levels rise. Undeveloped lands adjacent to and up to one and a half meters above existing salt marshes were identified, and included as Critical Natural Landscapes with high potential to support inland migration of salt marsh and other coastal habitats over the coming century. CNL 902 A 11,336‐acre Critical Natural Landscape featuring Tern Foraging Area. Terns range widely from their breeding colonies to forage. While the breeding and staging areas for Roseate, Arctic, Common, and Least Terns were included in the Species of Conservation Concern Core Habitat for BioMap2, tern foraging areas were included in BioMap2 as part of Critical Natural Landscape. The extent of foraging habitat for Arctic, Common, and Roseate Terns depends on the size of the breeding colony. For Least Tern, all shallow marine and estuarine waters within 2 miles of recent colony sites and up to 1 mile offshore were mapped as foraging habitat. CNL 920 A 3,352‐acre Critical Natural Landscape featuring Aquatic Core Buffer and Wetland Core Buffer. A variety of analyses were used to identify protective upland buffers around wetlands and rivers. One, the variable width buffers methodology, included the most intact areas around each wetland and river, by extending deeper into surrounding unfragmented habitats than into developed areas adjacent to each wetland. Other upland buffers were identified through the rare species habitat analysis. In this way, the conservation of wetland buffers will support the habitats and functionality of each wetland, and also include adjacent uplands that are important for many species that move between habitat types. CNL 939 A <1‐acre Critical Natural Landscape featuring Coastal Adaptation Area. The coastal habitats of Massachusetts are particularly vulnerable to potential sea‐level rise in the next century, which many estimates suggest is likely to exceed one meter. Therefore, in addition to prioritizing current coastal habitats, the creators of BioMap2 examined the landward side of salt marshes to determine where these habitats might move to as sea levels rise. Undeveloped lands adjacent to and up to one and a half meters above existing salt marshes were identified, and included as Critical Natural Landscapes with high potential to support inland migration of salt marsh and other coastal habitats over the coming century.

BioMap2 Conserving the Biodiversity of Massachusetts in a Changing World

CNL 943 A 135‐acre Critical Natural Landscape featuring Coastal Adaptation Area. The coastal habitats of Massachusetts are particularly vulnerable to potential sea‐level rise in the next century, which many estimates suggest is likely to exceed one meter. Therefore, in addition to prioritizing current coastal habitats, the creators of BioMap2 examined the landward side of salt marshes to determine where these habitats might move to as sea levels rise. Undeveloped lands adjacent to and up to one and a half meters above existing salt marshes were identified, and included as Critical Natural Landscapes with high potential to support inland migration of salt marsh and other coastal habitats over the coming century.

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