Evaluation of Albany Pine Bush
Albany County, New York
For its Merit in Meeting National Significance Criteria as a National Natural Landmark in
Representing Sand Dunes as an Example of Eolian Landforms in the
Appalachian Plateau and Ranges Physiographic Regions
Prepared by:
Todd R. Lookingbill1, Mary C. Brickle1, and Katharina A.M. Engelhardt2
Photo by Mary Brickle
March 15, 2013
1
University of Richmond
Department of Geography and the Environment
28 Westhampton Way
Richmond, VA 23173
2
University of Maryland Center for Environmental Sciences
Appalachian Laboratory
301 Braddock Road
Frostburg, Maryland 21532
Table of Contents
Executive Summary ........................................................................................................................ 1
Introduction ..................................................................................................................................... 2
Source of Site Proposal ............................................................................................................. 2
Evaluators ................................................................................................................................. 2
Scope of Evaluation .................................................................................................................. 2
Characterization of the Primary Natural Features .......................................................................... 3
Description ................................................................................................................................ 3
Primary Geological Features ............................................................................................. 3
Primary Biological Features .............................................................................................. 4
Distribution and Context ........................................................................................................... 5
Regional Variation .................................................................................................................... 6
Significance............................................................................................................................... 7
Albany Pine Bush Site Description................................................................................................. 8
Primary Natural Features .......................................................................................................... 8
Description of Geological Features.................................................................................... 8
Description of Biological Features ..................................................................................... 9
Natural History Themes Represented ..................................................................................... 11
Secondary Natural Features .................................................................................................... 12
Physical Setting ....................................................................................................................... 12
Location and Access ............................................................................................................... 13
Ownership ............................................................................................................................... 13
Land Use and Condition ......................................................................................................... 13
Historic Land Use ............................................................................................................. 13
Current Land Use and Present Condition ........................................................................ 14
Sensitive or Hazardous Resources .......................................................................................... 15
Comparative Assessment .............................................................................................................. 16
Regional Site Inventory .......................................................................................................... 16
Site Descriptions ..................................................................................................................... 16
Highest Quality Sites......................................................................................................... 16
Other Sites......................................................................................................................... 19
Comparative Analysis & Discussion ...................................................................................... 20
Evaluation Recommendations ...................................................................................................... 23
Proposed Landmark Boundary ............................................................................................... 23
Literature Cited ............................................................................................................................. 24
Figures........................................................................................................................................... 30
Appendix A: Flora and Fauna Lists .............................................................................................. 42
Appendix B: Representative Site Photographs ........................................................................... 105
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Executive Summary
The National Natural Landmark (NNL) Program encourages the preservation of the Nation’s
natural heritage. To qualify for NNL designation, a site must be one of the best examples of a
geological and/or biological feature within a biophysiographic province. The Albany Pine Bush
in Albany County, New York, supports a significant example of periglacial sand dunes, which
uniquely combines outstanding examples of geologic (Eolian Landforms; Works of Glaciers) and
ecological (Pitch Pine-Scrub Oak Barrens) themes in the Appalachian Ranges and Appalachian
Plateau biophysiographic provinces of the United States. The Albany Pine Bush is owned by
multiple private and public organizations and managed by the Albany Pine Bush Preserve
Commission. All entities have consented to allow the site to be evaluated as a potential NNL
(pNNL). This evaluation considers whether the resources at Albany Pine Bush are intact,
nationally significant, and deserving of NNL designation. It includes a general characterization
of periglacial dunes and pitch pine-scrub oak barrens, a site description of Albany Pine Bush
pNNL, a comparative assessment of similar sites, a final recommendation for designation, and a
map of the recommended boundary.
Periglacial sand dunes are fossil landscape features that are common throughout colder
climates of the world. The sand dunes are the result of wind action reworking sediments from
glacial lakes or outwash dating back to the last Ice Age. Owing to nutrient limiting sandy soils
and the heterogeneous topography of dune landscapes, sand dune ecosystems support a diverse
biota dominated by pine barrens in higher-lying drier habitats and wetlands in low-lying wet
areas at the base of dunes. This interplay of geology and ecology contributes significantly to the
natural history of the region. Therefore, consideration of a sand dune-pine barren ecosystem in
the Appalachian Ranges and Appalachian Plateau regions is warranted to encourage the
preservation of the region’s distinct natural heritage.
It is our recommendation that Albany Pine Bush pNNL meets the national significance criteria
required for the NNL Program. The proposed site is illustrative in character as it showcases how
eolian processes form regionally important and sensitive dune landscapes. The Albany Pine
Bush is one of the best examples of inland pine barren ecosystems in the world, comparable in
quality to the New Jersey Pine Barrens and other larger systems located outside the Appalachian
Mountains on the Atlantic Coastal Plain. The dry dunes, moist ravines, and bogs are habitat to
more than 1300 species of plants, 156 species of birds, more than 30 species of mammals, and 20
species of amphibians and reptiles. Many of these species are adapted specifically to sandy soils,
and several are documented species of special concern. The Albany Pine Bush is therefore of
great scientific, conservation and educational interest for study of its diverse flora and fauna.
Monitoring of the biota will need to continue to assess impacts of human use and management
activities. The biggest threats to the system are fire suppression and suburbanization. A
comparison with other periglacial sand dune sites identified Rome Sand Plains (Appalachian
Plateau region) as equal in many significance criteria except that a higher number of species of
special concern are documented and a more appropriate management plan is in place for
Albany Pine Bush pNNL.
After considerable research, discourse with experts, and a site visit we have come to the
conclusion that Albany Pine Bush pNNL is a prime candidate site to be designated as a NNL. We
include a map of the proposed landmark boundary, which delineates a total of 3,200 acres
(1,295 ha).
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Introduction
Source of Site Proposal
The Albany Pine Bush Preserve was originally recommended as a potential National Natural
Landmark (pNNL) in the Potential National Natural Landmarks of the Appalachian Plateaus
Natural Region Report (Baer et al. 1982; pp. 107-111) and Appalachian Ranges Natural Region
Ecological Report (DeSelm 1984; pp. 183-187), both commissioned by the National Park
Service. The Preserve is primarily representative of the Eolian Landforms (Theme 7) Sand
Dunes (Sub-theme 7a), and Works of Glaciers (Theme 9) Glacial Deposition (Sub-theme 9a) and
Periglacial Features (Sub-theme 9c) natural history themes under the Landforms of the Present
grouping (Group 1). It is also representative of a Barrens theme (Sub-theme Pitch Pine-Scrub
Oak Barrens) under the Land Ecosystems grouping (Group 3). The sand dunes found in Albany
Pine Bush are the result of wind action reworking sediments accumulated in glacial Lake Albany
after the Wisconsin glacier began to retreat 12,000 years ago. The glacial retreat left the sand
deposits and the lakebed sand and clay exposed to the forces of wind and rain. The resulting
ecological landscape is dominated by pitch pine-scrub oak and other communities that tend to
occur on well-drained, sandy soils that have low nutrients and wide ranges of soil moisture
during the growing season, and are dependent on frequent disturbance by fire. The site has not
previously been evaluated for NNL status. It received priority for evaluation because the site
represents themes that are currently underrepresented within the Appalachian Ranges and
Appalachian Plateau Natural Regions as outlined in "Natural History in the National Park
System and on the National Registry of Natural Landmarks" (NPS 1990).
Evaluators
Dr. Todd R. Lookingbill, Assistant Professor, Department of Geography and the Environment,
University of Richmond. Dr. Lookingbill is a landscape ecologist with research focusing on the
spatial patterning of the abiotic environment and the processes that affect species distributions
within natural and managed landscapes.
Dr. Katharina A. M. Engelhardt, Research Associate Professor, University of Maryland Center
for Environmental Science. Dr. Engelhardt studies the maintenance of biodiversity and its effects
on ecosystem functioning. Her current research focuses specifically on the feedback between
geomorphology and biodiversity to predict the effects of climate change on ecosystems.
Scope of Evaluation
The study area used in this evaluation was the Appalachian Ranges (both the Valley and Ridge
and the Blue Ridge physiographic provinces) and Appalachian Plateau Regions of the MidAtlantic United States (Figure 1). The sites selected for the comparative assessment lie within a
similar climatic zone as Albany Pine Bush with an emphasis on sites containing periglacial sand
dunes within the Appalachian Mountains (Figure 2).
The evaluation of Albany Pine Bush is based on scientific literature and conversations with
scientific experts. A site visit was conducted on July 12-13, 2011. Experts conferred with during
the course of this evaluation include: Neil Gifford (Conservation Director Albany Pine Bush
Preserve), Tyler Briggs (Fire Management and GIS Specialist Albany Pine Bush Preserve,
Wendy Craney (Communications and Outreach Director Albany Pine Bush Preserve), Mark
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Demitroff (University of Delaware Permafrost Group), Warren Abrahamson (Professor of
Biology Emeritus Bucknell University), and Brad Stratton (GIS Specialist and Data Manager
The Nature Conservancy). William Kelly (New York State Geologist) and William Patterson
(Professor of Environmental Conservation Emeritus University of Massachusetts Amherst) also
provided valuable peer review of the assessment.
Characterization of the Primary Natural Features
Description
Primary Geological Features
Eolian landforms are shaped by winds that erode, transport, and deposit materials in arid
environments where vegetation is sparse and sediments are unconsolidated. In most non-arid
landscapes, water and ice are the more typical geomorphic agents owing to their greater density.
However, in the absence of these agents, wind can be an important determinant of land
formation. Wind transports soil through suspension of small particles in the atmosphere (as dust
or haze), or through saltation and creep that lifts or rolls particles and deposits them downwind.
Wind-deposited sand bodies occur as sand sheets, ripples, and dunes. These features hold clues
to past as well as to present wind directions and intensities. They also provide a good ground
record of the most recent episodes of radical climate change, like the abrupt cooling and drying
that occurred at the onset of the Younger Dryas.
Ripples are small sand waves that feature crests and troughs whose long axes are perpendicular
to the wind direction. Sand sheets are relatively flat, sandy fields composed of sand grains that
are too large for wind to lift them off the ground and lack discernable slip faces. At the local
scale, they often cover large spatial areas. Globally, approximately 40% of eolian depositional
surfaces are sand sheets. Although dunes are the classic landform illustrating eolian processes,
sand sheets have edaphic qualities similar to dunes and therefore offer similar ecosystem
characteristics.
Sand dunes are created by the accumulation of sand into mounds or ridges. They have a gentle
upwind slope on the wind-facing side and a steep avalanche slope (“slipface”) on the downwind
or lee slope. Dunes are highly diverse and can be classified into barchan (classic crecent-shaped
unvegetated desert dunes that are perpendicular to the dominant wind direction and whose points
point downwind), parabolic (crecent-shaped vegetated dunes that are perpendicular to the
dominant wind direction and whose points curve upwind), transverse (long linear dunes that are
perpendicular to the wind direction), longitudinal (large linear dunes parallel to wind direction),
and star (several ridges radiating out from a central location) among other variations that indicate
wind speed and direction, size and amount of sand, and the presence of vegetation
(Christopherson 2011).
Periglacial sand dunes are indicators of past aridity associated with cold, dry, and windy
climates encountered during the Late Pleistocene (Markewich and Markewich 1994; Campbell et
al. 2011). As the Laurentide Ice Sheet retreated, glaciers and lake levels receded and the climate
warmed. Continued wind erosion as well as physical weathering of silicate which occurred
during periods of frost (a process known as cryofracturing), led to the formation of scree (broken
3
rock fragments) and finer sand particles, which were shaped into dunes and depressions
(wetlands can be found today in these low-lying areas). These conditions contributed to the
formation of both short, broad longitudinal dunes as well as parabolic (crescent) shaped dunes
(Bradley et al. 2010). These eolian features provide a characteristic rolling topography.
Longitudinal dunes formed when unvegetated sediments and soils were exposed to bimodal wind
regimes. Parabolic dunes formed when strong and consistent northwesterly winds encountered
vegetated dunes, which helped to anchor the sands, preventing significant dune reworking
(Bradley et al. 2010). These vegetation colonized eolian features were repeatedly reactivated
when severe drought reduced vegetation cover (Harman and Arbogast 2004; Forman et al. 2009).
Because of this strong, intuitive link between dune activity and a more arid climate, the timing of
past dune activity is often used as a proxy for paleoclimate (Werner et al. 2011).
Primary Biological Features
Pitch pine-scrub oak barrens are globally rare, early-successional ecosystems that support rich
biological communities including many rare and declining species (Boyd 2008; Kirchner et al.
2011). The geologic template of these landscapes gives rise to two relatively distinct biotic
communities (McCormick 1998). Lowland depressions, in which the water table is near the
surface, are less abundant and are dominated by wetland floristic complexes (Bried and Edinger
2009). The sandy, well-drained soils of the uplands are dominated by vegetation ecologically
adapted to dry conditions and periodic fires. These drier communities are characterized by pitch
pine (Pinus rigida) trees, a tall shrub layer consisting of scrub oak (Quercus ilicifolia) and dwarf
chestnut oak (Q. prinoides), as well as a low shrub layer consisting of blueberries (Vaccinium
angustifolium), black huckleberry (Gaylussacia baccata), and sweet fern (Comptonia peregrina).
Interspersed throughout the landscapes are often areas of grasslands dominated by prairie grasses
such as big bluestem (Andropogon gerardii), little bluestem (Schizachyrium scoparium), and
Indian grass (Sorghastrum nutans). These grassland and early-successional shrubland habitats
can be important bird and butterfly habitat, especially when embedded within an otherwise urban
matrix (Leck 1998; Gifford et al. 2010).
Frequent disturbance is required to maintain pine barren ecosystems (Little 1998). Significant
changes in vegetation followed the Younger Dryas stadial, the last major cold episode on Earth
approximately 12,900 – 11,600 years BP. Abrupt changes in climate during the period led to a
sudden return to colder, dryer conditions, facilitating reactivation of the dunes (Shuman et al.
2002). An erosion surface is created when the deposition process is temporarily disrupted by a
change of wind direction causing erosion. If deposition later resumes in the original direction,
laying down more deposits in the original orientation, the erosion surface becomes a reactivation
surface. The effects of dune reactivation may enhance habitat value for certain biota. For
example, small populations of wildfire-intolerant plant species may take refuge in these dry
sandy openings that have not been exposed to burning. These sunlit areas also are critical as
gestation sites where snakes incubate their young. Dune fields have periodically reactived
throughout the Holocene.
In addition to drought, fires have been a key historical disturbance process driving eolian activity
in pine barren landscapes (Radeloff et al. 2000). Mean fire recurrence interval for barren systems
is ~ 30 years (Buchholz and Zampella 1987). Lightning strikes have reset the vegetation
following the “pulse-reset” model of pine barrens succession since the present vegetation
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emerged following the Pleistocene glaciation (Milne 1985; Reiners 1998). Humans have used
fire as a tool in the ecosystem dating back to Native American populations who set fire to the
woods to ease travel and drive deer during hunts (Little 1979). Prescribed burning is an active
component of the management of these ecosystems today. In areas where fire has been
suppressed for long periods of time, ecological succession may give rise to both northern and
southern hardwood forests (Barnes 2003).
Distribution and Context
Periglacial sand dunes: These fossil landscape features (Harman and Arbogast 2004) are
representative of the natural heritage of the United States and can be observed throughout colder
climates of the world in North America, Europe, and Asia. Niessen et al. (1984) summarized the
worldwide occurrence of periglacial sand dunes and eolian sand sheets. Extensive eolian sands
occur in the sand belt of the West and Central European Lowlands, beginning in East Anglia and
the Scottish borderlands, extending through the Netherlands and Belgium in the west and on
through Russia in the east (Niessen et al. 1984). Smaller sand dune areas are also found in Great
Britain and Scandinavia (Niessen et al. 1984). Sand dunes are also present in Spain in the Duero
Basin and on the Manchega Plain (Rebollal and Perez-Gonzales 2008).
Dune occurrences in North America that meet the requirement for periglacial origin are widely
but sparsely distributed (Niessen et al. 1984). Fossil sand dunes are often associated with coastal
areas of the United States where sand sources are technically of marine and fluvial origin, but
were deposited a long time ago. Thus, sand dunes are commonly observed on the Coastal Plain
in Texas (Forman et al. 2009), Georgia (Ivester et al. 2001, 2003), North Carolina and South
Carolina (Markewich and Markewich 1994); the Delmarva Peninsula of Delaware and Maryland
(Denny and Owens 1979, Newell and Clark 2008); Potomac River basin (Markewich et al.
2009); Pine Barrens of New Jersey (Mawdsley 2007); Long Island, New York (Englebright et al.
2000, Girardi 2005); and Alaska (Niessen et al. 1984).
Large inland dune areas have been documented in Ohio (Campbell et al. 2011); Indiana
(Kilibarda and Blockland 2011); Kansas and Oklahoma (Werner et al. 2011); and Nebraska,
Wyoming and Colorado (Niessen et al. 1984), covering many tens of thousands of square
kilometers. Dunes are located along the shorelines of the Great Lakes (Harman and Arbogast
2004). In Canada, nearly half the dune fields are located in Alberta (Niessen et al. 1984;
Munyikwa et al. 2011). Large areas of eolian deposits also occur in Saskatchewan and Manitoba
(Niessen et al. 1984). The presence of inland sand dunes in the southern United States suggests
that the magnitude of climate change in North America was greater than previously believed
after the last Ice Age (Markewich and Markewich 1994). Although never a dominant landscape
feature of the Appalachian Plateau or Ranges, the landscape feature is now reduced from its
former distribution due to human settlement and stands as a reminder of the historic landscape.
For example, the current extent of the Albany Pine Bush represents approximately 10% of the
original postglacial sand dunes ecosystem (Barnes 2003).
Pitch pine-scrub oak barrens: The modern distribution of pine barren communities is a result of
geologic and climatic conditions as well as historic human influence in the past centuries and
millennia. Barrens by nature were marginal areas, and their historical documentation poor.
Although early colonists did not perceive the lands especially favorably, as captured by the use
5
of the term ‘barrens’, human exploitation for lumber, charcoal, tar, turpentine and real estate has
been profound (Wacker 1998; Kays and DeWan 2004). Less than a third of the 1.9 million acres
(750,000 ha) that existed in the pre-Colonial Northeast remain today (Kurczewski 1998). Most
pine barrens in the United States are found along the Atlantic Coastal Plain (Figure 2), where
underlying soils are porous and acidic marine and glacial sands. The most extensive of these
systems is the New Jersey Pine Barrens located on the Coastal Plain of southern New Jersey.
The New Jersey Pine Barrens ecosystem includes the nation’s first National Reserve and a
United Nations Biosphere Reserve. Public land ownership in the region is approximately
370,000 acres (~150,000 ha), which includes large parts of the Mullica River basin (a long-term
environmental monitoring site) and The Nature Conservancy’s Forked River Mountain Preserve.
In total, between 66% and 75% of the Pine Barrens ecosystem is protected by New Jersey
legislation and the Pinelands Commission (Boyd 2008). Low, dense forests of pine and oak,
ribbons of cedar (Chamaecyparis thyoides) and hardwood swamps, pitch pine lowlands, and
bogs and marshes combine to produce an expansive vegetative mosaic (Zampella et al. 1992,
1999; Forman 1998). The New Jersey Pinelands also contain over 12,000 acres of "pygmy
forest," consisting of pine and oak trees less than 11 feet tall which result from periods of
frequent (at least every 7 years) burning. These pine barrens have a more southern flora than
many other more northerly pine barrens in the region.
Other large pine barren ecosystems are found on Long Island and Cape Cod (Figure 2). The pine
barrens community found in the Albany Pine Bush Preserve is a globally rare ecosystem because
it is located inland, the result of glacial sand deposition in a large freshwater lake that acted as a
suitable sink for the dunes to accumulate (Barnes 2003). At least 12 inland pine barrens have
been identified (Kirchman et al. 2011), including Albany Pine Bush Preserve (Figure 2), but few
of these combine pitch pine barrens vegetation with an extensive dune formation. The pine
barrens located within central and western New York are at the north and western boundary of
the range of pitch pine (Barnes 2003).
Regional Variation
Despite the wide distribution of sand dunes in the United States, only small areas of undeveloped
and well-formed eolian sand remain in the Appalachian Ranges and Appalachian Plateau
regions. However, we identified three areas (Albany Pine Bush, Rome Sand Plains, and
Montandon Sand Dunes) that are excellent representations of inland fossil sand dunes within the
United States and the physiographic regions.
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Significance
The inland glacial sand dunes have high geologic and biologic significance. The origin of the
dunes demonstrates geologic processes of glacial deposition within the Appalachian Plateau and
Appalachian Ranges, dating from the Ordovician sea between 400 and 500 million years ago.
Over millennia, the soft shale deposits laid down have eroded, forming hills, valleys, and ridges.
The sand dunes created illustrate the importance of eolian erosion and transport in the region.
This topographic heterogeneity has a significant impact on the biology of the landscapes and has
resulted in the formation of diverse ecological communities. Diverse wetlands can be found in
scoured depressions. Although first thought to be biologically depauparate, the pitch pine-scrub
oak upland barrens are increasingly recognized for their rich flora and fauna. They also provide
an opportunity to showcase the ecological value of fire to maintaining landscape diversity.
Unfortunately, many of these sites have been lost to development in the last centuries. The value
of those that remain has been acknowledged through increasing conservation efforts and study
since the mid 1970s. These fossil landscape also provide the opportunity to further study the
natural history of the area and some of the most significant episodes of radical climate change in
recent geologic history, like the abrupt warming at the onset of the Bølling-Allerød, and abrupt
cooling that occurred at the onset of the Younger Dryas. Eolian bed forms are widely used in
Europe for paleoenvironmental reconstruction and climate change modeling, and the Pleistocene
inland dune fields along the East Coast of the United States have similar potential (French and
Demitroff 2012).
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Albany Pine Bush Site Description
The Albany Pine Bush Preserve has been proposed for this evaluation as one of the best
examples of inland sand dunes that support a pine barrens ecosystem in the Northeastern United
States. It is one of only two pine barrens to support a dynamic sand dune landscape in the
Appalachian Plateau region and one of two sand dune ecosystems within the Appalachian
Ranges region. The sand dunes are the result of wind action reworking sediments from glacial
Lake Albany, which covered the area 14,000 years ago and contained deposits of glacial sand.
This extraordinary ecosystem gives rise to a variety of habitats. In particular, the sandy, welldrained soils in this area are dominated by the globally rare, fire-dependant pitch pine-scrub oak
barrens community, home to 45 of the 538 wildlife Species of Greatest Conservation Need
(SGCN) found in New York State, including the state and federally listed endangered species,
the Karner blue butterfly (Lycaeides melissa samuelis). These primary natural history features
combined with widespread vital species habitat, ongoing and extensive educational opportunities
and the recreational value of the Preserve, offer a unique opportunity to highlight multiple
natural history themes of the Appalachian Plateau and Appalachian Ranges. The following
sections describe the ecosystems found in the Albany Pine Bush Preserve in detail.
Primary Natural Features
Albany Pine Bush pNNL is located between the cities of Albany and Schenectady in the Capital
District of upstate New York (Figure 3). The Preserve is to the southwest of the confluence of
the Mohawk and Hudson Rivers, south of the Adirondack Mountains and north of the Catskills.
This dynamic mosaic landscape consists of gently rolling sand dunes and low lying wetlands,
and contains a variety of ecological communities, most notably the pitch pine-scrub oak barrens.
Description of Geological Features
Albany Pine Bush is located at the boundary between the Appalachian Plateau and Appalachian
Ranges Provinces of New York State (Figure 1). It is representative of an important deglaciation
event in the state's history and natural history features of both physiographic regions. Shale and
siltstone of middle Ordovician age comprises the majority of the underlying bedrock of the area.
This is covered by thick glacial lake deposits from the most recent glaciation (Wisconsin). As the
glacier retreated, Glacial Lake Albany formed in the mid and upper Hudson Valley. Large sandy
areas extended from the city of Hudson north to Lake George, tracing the ancient lake shoreline.
A large delta was formed as layers of silt, sand, and clay flowed from the upper Mohawk Valley
and deposited on the lake bottom. As lake levels began to recede, the deltaic deposits were
exposed to winds, which formed the gently rolling sand dunes now underlying the Albany Pine
Bush (Barnes 2003). Thus, the dunes at Albany Pine Barrens provide a way to date at least one
stage of the post-glacial drainage of Glacial Lake Albany and the development of the modern
river drainage system.
The Preserve contains representative examples of both parabolic and longitudinal dunes (Figure
4). Prevailing northwesterly winds shaped most of the sand dunes, forming primarily parabolic
dunes that ranged from 100 to 2,000 feet in length. Typically oriented with their longest axis
running from northwest to southeast and frequently resembling Us, Js, or Ys when viewed from
above, the crescent shape of these dunes suggests they were colonized early by vegetation which
helped stabilize the dune surface and prevent significant reworking (Barnes 2003). Eolian
8
processes also contributed to the formation of short, broad, ridge-shaped longitudinal dunes,
usually between 30 to 60 feet high and typically several hundred feet long (Bradley et al. 2010).
Today, the dunes are characterized by a transitioning topography from flat to gently rolling
surfaces, with both sand swells and low domes, dotted with pitch pine and carpeted with diverse
understory plants. Average surface relief of the dunes is 20 feet, with the thickest deposits found
paralleling State Route 5 in the northern part of the Preserve. Swamps, wetlands, and shallow
ponds have come to fill in holes that were long ago eroded into the sandy soil (Figure 5; Bried
and Edinger 2009). The proposed NNL boundaries incorporate 3,200 acres of this landscape.
The sandy soils of the Albany Pine Bush are very well drained in most areas (Figure 6). Because
of this, exposed sand can be very hot in the summer months and dries out quickly after a rainfall
(Barnes 2003). The sand is underlain by silts and clays deposited during the formation of Glacial
Lake Albany. Bedrock geology is primarily Normanskill shale (Figure 7). Depth to groundwater
varies considerably throughout the park because of the dunes, though much of the Preserve is
underlain by a shallow aquifer. In areas where the aquifer is found closer to the surface, water
availability is more constant so small changes in dune topography, along with collection of
organic matter, directly affects variation in plant species in the region through hydrologic
interactions.
In colder months, the low-lying depressions between the dunes can act as "frost pockets". As the
cooler air settles into these areas, plant growth is delayed in comparison to the areas of higher
elevation. This leads to less dense patches of scrub oak in these areas, and they instead become
dominated by prairie grasses and sedges.
Description of Biological Features
The Albany Pine Bush provides one of the best and largest examples of an inland pine barren
ecosystem in the world (Barnes 2003). Before European colonization of the area, the Pine Bush
covered approximately 40 square miles, representing the largest pitch pine barrens in North
America inland of the Coastal Plain (USFS 1997). The dynamic mosaic landscape of the sand
dune ecosystem gives rise to an impressive and globally rare assemblage of plants and animals
(Milne 1985; Barnes 2003). Pitch pine-scrub oak communities dominate the Albany Pine Bush
landscape and have been the focus of conservation efforts to date (Gifford et al. 2010; APBPC
2010). Pitch pine-scrub oak communities are primarily dependent on frequent fire disturbance
and tend to occur in areas with sandy soils, which have widely varying soil moisture content
during the growing season. Natural fires have been augmented with prescribed burns in recent
decades (Gifford pers. comm.).
The fire-adapted pine barrens plant community is dominated by 20 to 40 percent pitch pine
(Pinus rigida) cover and plants associated with the pitch pine-scrub oak barrens savanna
community. Scrub oak (Quercus illicifolia) and dwarf chestnut oak (Q. prinoides) form dense
thickets in the shrubby undergrowth layer. Huckleberry (Gaylussacia baccata), lowbush
blueberry (Vaccinium angustifolium and V. pallidum), sweet-fern (Comptonia peregrina), New
Jersey tea (Ceanothus americanus), and bracken fern (Pteridium aquilinum) dominate the
undergrowth in treeless areas. Interspersed are small grasslands dominated by prairie grasses
such as big bluestem (Andropogon gerardii), little bluestem (Schyizachyrium scoparium), and
Indian grass (Sorghastrum nutans) as well as shrubby willows (Salix humilis and S. tristis).
9
These are usually found along trails, at recently disturbed sites, and in some of the low areas
between dunes where the water table may be very close to the soil surface. Common herbaceous
species include several bush clovers (Lespedeza capitata, L. hirta, L. procumbens) and
Pennsylvania sedge (Carex pensylvanica). Characteristic forbs include goat's rue (Tephrosia
virginiana) and wild lupine (Lupinus perennis). The pitch pine-scrub oak barrens community
makes up 952 acres, or 42%, of the mapped communities in the Albany Pine Bush Preserve
(USFS 1997). A complete list of all plants recorded at the site is attached as an appendix to this
report (Appendix A).
The dry, acidic soils of the Pine Bush do not promote the decomposition of litter, and the lack of
earthworms or other organisms in the dry upper layers of the sandy soil mean that organic matter
decomposed by fungi is not incorporated back into the soil (Barnes 2003). A wide assortment of
dry plant matter accumulates at the surface, creating a significant fuel source for frequent fires.
With the occurrence of these fires, much of the nitrogen in the organic matter is volatized and
lost. Because of this, nitrogen-fixing legumes, such as the wild lupine, occupy areas of recent
burns, where they have a temporary advantage in the arid, nitrogen poor soil. The exotic,
nitrogen-fixing black locust (Robinia pseudoacacia) also supplements soil nitrogen pools where
it invades (Rice et al. 2004) and can have long-lasting effects on the plant competitive dynamics
of these historically nutrient poor sites in the absence of active control measures (Malcolm et al.
2008).
Fire disturbance within a pine barrens serves to rejuvenate the natural community, drive out
exotic plant species, and increase the food and habitat supply for native insects and other animals
(e.g., Beachy and Robinson 2008). It is an important component in maintaining the unique
ecological qualities of a pine barrens community (Milne 1985). Good natural conditions for
wildfires have existed within the Albany Pine Bush Preserve for thousands of years, especially
during the frequent periods of high winds, because the sandy, nutrient-poor soil tends to be
droughty and a fuel supply of plant litter accumulates rapidly due to the retarded microbial
decomposition (Barnes 2003). It is also likely that local Native American populations historically
helped to maintain frequent fire disturbance in the area. Human occupation and use of the site
likely dates back thousands of years to Paleo-Indian hunting groups (APBPC 2010).
In areas where fire has been suppressed for long periods of time, the pine barrens have typically
undergone succession into either northern or southern hardwood forest. The southern hardwood
forests are dominated by the exotic black locust (Robinia pseudoacacia) and black cherry
(Prunus serotina), with lesser numbers of oaks (Quercus spp.), maples (Acer, spp.) and tree-of
heaven (Ailanthus altissima), also an exotic species. The shrub layer is dominated by black
raspberry (Rubus occidentalis) and other brambles (Rubus spp.), as well as shrubs characteristic
of the pine barrens described above. The northern hardwood forests are dominated by quaking
aspen (Populus tremuloides), big-toothed aspen (Populus grandidentata), and other hardwood
species including black cherry, red maple (Acer rubrum), white pine (Pinus strobus), gray birch
(Betula populifolia), green ash (Fraxinus pennsylvanica), and oaks (Quercus spp.). Currently,
roughly 500 acres of the Pine Bush Preserve are considered to be successional northern and
southern hardwood forests, but under a strict fire management plan, the majority of these areas
have the potential to be restored back to pitch pine-scrub oak pine barrens communities (Barnes
2003).
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The Albany Pine Bush is nationally recognized for its extensive populations of rare butterflies
and moths, and management plans have focused on the protection of these rare insects (APBPC
2010). There are hundreds of Lepidoptera species found in the Pine Bush, including over 40
noctuid moths (Noctuidae) considered to be pine barrens specialists. A variety of regionally rare
butterflies are also found including the dusted skipper (Atrytonopsis hianna), Henry's elfin
(Incisalia henrici), frosted elfin (Incisalia irus), Karner blue (Lycaeides melissa samuelis), and
Edward's hairstreak (Satyrium edwardsii); rare moths include the Albarufan dagger moth, broadlined catopyrrha (Catopyrrha coloraria), several noctuid moths (Apharetra purpurea,
Chaetaglaea cerata, Chytonix sensilis, Macrochilo bivittata, Zanclognatha martha), bird
dropping moth (Cerma cora), and a geometrid moth (Itame sp. 1). All of these rare species, with
one exception (the noctuid moth Macrochilo bivittata, which is associated with wetlands in the
Pine Bush), are associated with pitch pine-scrub oak barrens, grasslands, and other firemaintained communities found in dry, sandy areas. The federally listed endangered Karner blue
butterfly typically occurs in the grassy openings in the pitch pine-scrub oak barrens; its food
plant and host plant for its larvae is the wild blue lupine, distributed throughout the Albany Pine
Bush (Forrester et al. 2005). A complete list of all insects recorded at the site is attached as an
appendix to this report (Appendix A).
There is increasing evidence of a distinct and rich avian community in the pine barrens
ecosystems of the Albany Pine Bush (Beachy and Robinson 2008; Gifford et al. 2010; Bried et
al. 2011). The site has been designated as a New York State Bird Conservation Area for meeting
four of the required criteria: migratory concentration site; diverse species concentration site;
individual species concentration site; and species at risk site. Bird species of particular interest
that are found within the pine barrens include American woodcock (Scolopax minor), whip-poorwill (Caprimulgus vociferous), red-shouldered hawk (Buteo lineatus), brown thrasher
(Toxostoma rufum), ovenbird (Seiurus aurocapillus), eastern towhee (Pipilo erythrophthalmus),
common yellowthroat (Geothlypsis trichas), field sparrow (Spizella pusilla), prairie warbler
(Dendroica disolor), and pine warbler (Dendroica pinus). Reptiles and amphibians such as the
eastern hognose snake (Heterodon platirhinos) and eastern spadefoot (Scaphiopus holbrookii)
are found in the pitch pine communities. Common mammals of the pine barrens include whitetailed deer (Odocoileus virginianus), cottontail rabbits (Sylvilagus floridanus), common raccoons
(Procyon lotor), red foxes (Vulpes vulpes), fishers (Martes pennanti), eastern chipmunks
(Tamias striatus), and a variety of other rodents. A complete list of birds, reptiles, amphibians
and mammals recorded at the site is attached as an appendix to this report (Appendix A).
Natural History Themes Represented
Albany Pine Bush Preserve is representative of the Sand Dunes sub-theme (7a) under Landforms
of the Present (Group 1). This sub-theme is part of the Eolian Landforms (Theme 7) natural
history theme as identified by the NNL program. In addition, Albany Pine Bush is representative
of the Glacial Deposition (9a) and Periglacial Features (9c) sub-themes, represented as part of
the Works of Glaciers (Theme 9) natural history theme, also found under Landforms of the
Present. Of secondary importance, the dominant ecosystem found within Albany Pine Bush
represents a new Pitch Pine-Scrub Oak Barrens sub-theme under Land Ecosystems (Group 3).
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Secondary Natural Features
There are a variety of wetland communities comprising approximately 14% of the Albany Pine
Bush Preserve (Figure 5), including red-maple hardwood swamps, shallow-emergent marshes,
and typical pine barrens vernal ponds (Bried and Edinger 2009). The presence of each of these
communities typically depends on the soil substrate, depth to water table, and fire management
history of the area. Wetlands communities play an important role in maintaining the unique
function of the pine barrens ecosystem. However, they are not unique to the pine barrens
themselves because they can be found throughout the region. For example, the wetlands at
Albany Pine Bush Preserve attract a high diversity of adult dragonflies and damselfies (Bried and
Edinger 2009). The most common and largest type of wetland is the red maple-hardwood swamp
(Barnes 2003). This community is dominated by red maple and may have black ash (Fraxinus
nigra), American elm (Ulmus americana), or other co-dominants. The shrub layer can be very
dense and includes winterberry (Ilex verticillata), red osier, silky, and gray dogwoods (Cornus
sericea, C. ammomum, C. foemina), arrowwood (Viburnum recognitum), wild raisin (V.
cassinoides), and highbush blueberry (Vaccinium corymbosum). The herbaceous layer is made
up of cinnamon fern (Osmunda cinnamomea), royal fern (O. regalis), and sensitive fern
(Onoclea sensibilis). There may be openings with other herbaceous species such as skunk
cabbage, (Symplocarpus foetidus), and sedges (Carex spp.). In areas where the shrubs listed
above are the most common species type and the overhead canopy is very sparse or nonexistent,
the wetland is considered a shrub swamp.
Individual ephemeral ponds found within the pine barrens are typically small (less than 5 acres),
but a total of roughly 35 acres of intermittent pools have been mapped within the area of the Pine
Bush Preserve (Barnes 2003). These ponds fluctuate with the seasons and can sometimes not be
seen for 3 or 4 years in a row. They are windows to the shallow groundwater. The ground-fed
ponds are characterized by a diversity of grasses, sedges, herbs, and low shrubs, including threeway sedge (Dulichium arundinaceum), woolgrass (Scirpus cyperinus), cinnamon fern
(Osmundastrum cinnamomeum), leatherleaf (Chamaedaphne calyculata), mountain holly
(Nemophanthus mucronatus), and sphagnum moss (Sphagnum fallax). Small trees such as red
maple, gray birch (Betula populifolia), and pitch pine may occur along the edges or on
hummocks. Most of the pine barrens intermittent pools occur in low valleys between the dunes.
Spotted salamander (Ambystoma maculatum), Jefferson salamander (A. jeffersonianum), bluespotted salamander (A. laterale), spotted turtle (Clemmys guttata), and other amphibians and
reptiles occur in these wetlands. Several birds such as green heron (Butorides virescens) and
red-bellied woodpecker (Melanerpes carolinus) also use wetlands of the Albany Pine Bush for
habitat.
Physical Setting
Albany Pine Bush is located on the border of the Appalachian Plateaus and Ridge and Valley
Provinces. Located between the Adirondack Mountains to the north and the Catskill Mountains
to the south, elevation is low, ranging from about 260 to 360 feet above sea level. The climate of
the Albany Pine Bush is considered to be continental humid. Winters are not severe, as
surrounding river valleys and mountains moderate winter cold air masses from Canada. A
moderate maritime effect coming from the southeastern part of the state influences climate
during summer months. Some of the highest temperatures in the state are recorded in the Pine
Bush area. Air temperatures range from 102° F (39° C) in summer to -8° F (-22° C) in winter,
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with a mean annual temperature of 48° F (8.8° C). Most precipitation falls from late spring
through summer. The Catskill and Adirondack Mountains produce a rain shadow effect that
reduces the amount of total precipitation in the Pine Bush. Average annual total precipitation is
33 inches (84 cm), including about 67 inches (170 cm) of snow (Barnes 2003).
Location and Access
Albany Pine Bush is located within a 19-square-mile area of sand dunes bounded on the north by
New York Route 5, on the south by U.S. Route 20, on the east by Fuller Road, and on the west
by Route 146, Lone Pine Road, and Cordell Road. The delineated boundaries for the Albany
Pine Bush pNNL are identical to the boundaries of the Albany Pine Bush Preserve and include
all land officially managed by the Albany Pine Bush Commission. The address of the Albany
Pine Bush Preserve is 195 New Karner Road, Albany, New York 12205. To access the Preserve
from I-90, take exit 1S toward US-20/Western Ave. Merge onto Adirondack Northway and take
Crossgates Mall Rd. exit. Keep right at the fork to go on Crossgates Mall Rd. Take a slight right
and merge onto Washington Ave. exit via the ramp on the left. After 2.1 miles, turn right onto
New Karner Road. The Albany Pine Bush Preserve Discovery Center will be on your left after
0.5 miles. Over 18 miles of marked trails and 9 designated access points are found within the
Preserve (Figure 8). The Preserve is completely within the 1:24,000 scale topographic map
quadrangle “Albany NY” (42073-F7; Figure 3).
Ownership
The Preserve is composed of tracts owned and set aside by New York State, the City of Albany,
The Nature Conservancy, the Towns of Guilderland and Colonie, and some private land owners
(Figure 9). However, it is all under the primary management of the Albany Pine Bush Preserve
Commission, founded in 1988, when the State of New York recognized the pine barrens
landscape as an area needing protection for ecological, educational, and recreational purposes.
The proposed landmark boundary is the Preserve boundary.
Land Use and Condition
Historic Land Use
Historic land use in the Albany Pine Bush has not been carefully documented, however, modern
vegetation patterns have clearly been altered by species-specific responses to various human
activities in the area, such as burning, cutting, agricultural use, and sand mining (Barnes 2003).
Humans appear to have entered the region immediately following the Younger Dryas
chronozone, around 12,900 years ago and the recent discovery of arrowheads and other artifacts
of similar lithic sources (located, in particular, at the Sundler sites), indicate that Paleoindians
were well established in the region by as early as 12,600 yr BP (Bradley et al. 2010). Many
Native Americans passed through the area, and there is evidence that they introduced the earliest
instances of prescribed fire in the area. Once European settlers created the outposts of Albany
and Schenectady, the Pine Bush became known as a dangerous area, unfit for agricultural use,
prone to fires, and a hideout for smugglers, thieves, and, during the American Revolution,
English loyalties.
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In comparison to much of the land in the region, the Preserve itself has been notably less
disturbed. This is due in large part to settlers’ preferences for forest exploitation over farming.
However, historical human activity has significantly affected the biodiversity of the Albany Pine
Bush in several ways. Several nonnative species have been introduced into the area and now
thrive, successfully competing with many native plants that have been in the area for thousands
of years. The dramatic increase of plant community edges, with the increase of infrastructure
such as roads, bridges, fields, and lawns, has dramatically increased the number of species who
prefer these transitional habitat areas. Fire suppression in recent years has also dramatically
increased invasibility by nonnative species. This increase in species diversity is not necessarily a
good thing, as these new species compete with native species for critical resources.
Current Land Use and Present Condition
The Albany Pine Bush Preserve is maintained by the Albany Pine Bush Commission, with the
purpose of protecting and managing the natural communities with an emphasis on ecological,
recreational, and educational value. The Commission maintains good relations with adjacent
landowners, as they recognize the importance of facilitating a buffer habitat around the protected
lands (Gifford pers. comm.). The site is under excellent management by the Commission as
described in the Preserve’s current management plan (APBPC 2010). Plans to expand the
protected lands are highlighted, along with guidelines for continued management of the currently
protected lands through prescribed fires and related actions to maintain the existing mosaic of
pine barrens communities. Primary threats addressed in the plan are development including
direct loss of habitat, limitations to fire management, and habitat fragmentation; invasive plants,
pests and pathogens; inappropriate public use of the Preserve such as unauthorized use by allterrain vehicles; and wildlife-related impacts, primarily an over-abundance of white-tailed deer
(Odocoileus virginianus).
The biggest threat to the Albany Pine Bush Preserve is continued suburbanization and
development of the natural habitat (Figure 10). For example, inside/outside hunting cats can have
a large impact on the ecology of suburban landscapes (Loss et al. 2013); however, cold weather
and healthy cat predator populations are speculated to minimize their impact in the Pine Bush
area (Keys and DeWan 2004). Fragmentation of the adjacent habitat and excessive use by
Preserve visitors are also of serious concern. The use of horses within the park may introduce
invasive weed species through the spread of seeds in horse manure. Alterations to groundwater
hydrology may influence the presence of wetlands and intermittent ponds and their associated
plant and animal life. Use of insecticides in the area may also affect the populations of rare and
endangered moths and butterflies that populate the area. Similarly, use of herbicides along power
lines and railroads has the potential to cause significant damage to native species in the Preserve
(Forrester et al. 2005). To minimize the potential effect of future development, all proposed
development within the 13,000-acre Study Area surrounding the Preserve (Figure 11) gets
reviewed by the Albany Pine Bush Commission. The reviews include anticipated impacts to
wildlife of conservation concern, rare plants, wetlands, streams and dunes. When appropriate, the
Commission suggests various ways of avoiding and mitigating those impacts. The 2010
Management Plan (APBPC 2010) also calls for the Commission to continue to work with willing
landowners to nearly double the amount of land under full protection to 5,380 acres (Figure 11).
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Another issue related to the relatively urbanized setting is the suppression of fire in the area,
which has caused some traditional communities of pitch pine-scrub oak to convert into either
northern or southern hardwood forest. Fortunately, under careful management plans, many of
these areas have been restored to their natural pine barrens. From 1991 through 2010, 1,100 acres
of the Preserve were managed with prescribed fire and other techniques to restore and maintain
native habitat (APBPC 2010). Where fire is less practical, mechanical treatment of the barrens,
including mowing and herbicide application, has been used to limit encroachment of undesired
species and to reduce the density of understory scrub oak (Bried and Hecht 2011). For example,
girdling and herbicides are being used to reduce black locust populations. A primary goal of
these ecological management practices is to reduce scrub oak density to 30-35% (Bried and
Gifford 2010). An additional benefit of the habitat restoration ongoing in the Preserve is the
reduction of tick-borne lyme disease in the region (Morlando et al. 2011). Overall, the site
experiences numerous threats, as is typical for this natural feature, but the Preserve has the
support and infrastructure in place to maintain the integrity of the site.
Sensitive or Hazardous Resources
As one of the best remaining examples of an intact, inland pitch pine-scrub oak barrens in North
America, there are numerous species of special concern found within the Albany Pine Bush.
Federally listed endangered species and species of concern found within the Preserve include the
Karner blue butterfly (Lycaeides melissa samuelis), Albarufan dagger moth (Acronicta albarufa),
and bog bluegrass (Poa paludigena). State-listed special concern species include the inland
barrens buckmoth (Hemileuca maia ssp. 3), Jefferson salamander (Ambystoma jeffersonium),
blue-spotted salamander (Ambystoma laterale), spotted salamander (Ambystoma maculatum),
eastern hognose snake (Heterodon platirhinos), spotted turtle (Clemmys guttata), wood turtle
(Clemmys insculpta), and eastern bluebird (Sialia Sialis). Finally, state-listed rare plants include
red-rooted flatesedge (Cyperus erythrorhizos), Houghton's umbrella-sedge (Cyperus houghtonii),
and Schweinit's flatsedge (Cyperus schweinitzii).
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Comparative Assessment
Regional Site Inventory
A Regional Site Inventory was compiled through a literature and internet search and
conversations with scientific experts (see Scope of Evaluation on p. 2). The following sites were
identified for potential inclusion in the comparative assessment (listed in alphabetical order)
because they support sand dunes and other features formed through eolian processes and
associated pine barrens. Sites with asterisks are described in detail below.
Chase Lake Sand Plains, New York
Mahantango sand deposit, Pennsylvania
Millersburg sand deposit, Pennsylvania
*Montandon Sand Dunes, Pennsylvania
*Rome Sand Plains, New York
Saratoga Sand Plains, New York
Site Descriptions
Although the largest examples of intact pine barren ecosystems are found in the Coastal Plain of
New Jersey and New York (Figure 2), we do not include these locations as detailed comparative
sites. Instead, we focus our comparative analysis on sites that, like Albany Pine Bush, are located
in the Appalachian Mountain Regions of the Eastern United States. Despite the wide distribution
of sand dunes in the United States, only small areas of eolian sand remain in the Appalachian
Ranges and Appalachian Plateau. However, the three areas identified (Albany Pine Bush, Rome
Sand Plains, and Montandon Sand Dunes) are excellent representations of fossil sand dunes
within the United States and the physiographic regions.
Highest Quality Sites
Montandon Sand Dunes
Montandon Sand Dunes in Northumberland County, Pennsylvania, was listed as a pNNL in the
Potential National Natural Landmarks of the Appalachian Ranges Natural Region, Geological
Report (Clark 1985; pp. 256-258) because of its transverse and parabolic dune formation. It is
also listed in “Outstanding Scenic Geological Features of Pennsylvania” (Geyer and Bolles
1979). Peltier (1949) extensively surveyed the terraces of the Susquehanna River and its
branches and documented three significant deposits of dune sand along the West Branch of the
Susquehanna River. The Montandon sand dunes are the best representation of typical eolian
sediment deposits within the Susquehanna River basin. The other two areas (Mahantango and
Millerburg sand deposits) are described briefly below under “Other Sites”.
The Montandon sand dunes are 10 to 13 feet high (Peltier 1949) and are considered to be
periglacial relicts of the last period of glaciation (Clark 1985) when the Wisconsinian glacier
flushed large amounts of sediment into the West Branch of the Susquehanna River (Chase 1977).
The sediment was deposited on flood plains downstream. After glacial retreat, the river cut
downward, lowering the water table and drying out the land surface. The dry sediment was now
loose and blown by prevailing winds from the west, first into transverse and parallel sand dunes
and then into parabolic dunes that extend to the east of the transverse dunes. Due to anchoring by
vegetation, parabolic dunes have their tails oriented upwind to the west and the convex steep
16
slope oriented downwind (Chase 1977). The dune field is approximately 0.5 to 1.5 miles wide
and 4 miles long. A windblown silt layer (loess) is also present, as are ventifacts (pebbles, stones,
or boulders that have been shaped by wind-driven sand or ice crystals; French and Demitroff
2012), which both support the thesis that eolian processes have extensively structured this area
(Chase 1977).
The Montandon sand dune site and associated wetlands has been studied extensively by
undergraduate students at nearby Bucknell University (Frisbee 1955, Meriwether et al. 1975,
Zalewski 1989, Mecum 1992, Chartrand 1994, Hochman et al. 1996). Hochman et al. (1996)
recorded six plants of special concern for Pennsylvania including three that are endangered
(Carex bullata, Juncus scirpoides, and Ludwigia polycarpa), one threatened (Leptoloma
cognatum) and two rare (Rotala ramosior and Schoenoplectus fluviatilis). Two state-threatened
bird species have also been recorded (Botaurus lentiginosus and Ixobrychus exilis), as well as
seven vulnerable species (Hochman et al. 1996). This area was extensively logged (Abrahamson
pers. comm.) and the overstory is dominated by oaks and red maple (Acer rubrum; Zalewski
1998). Pine communities that are typically associated with dune complexes appear to be absent.
Sand dunes are present both north and south of Route 45, which bisects the sand dune area along
an E-W axis. The dune complex south of Route 45 is currently in agriculture and leased to
Central Builders Supply of Sunbury, PA (Zalewski 1998). This company is currently extracting
sand and gravel such that the southern dune complex will likely not exist in the future. The
northern area is owned by numerous landowners but none have been aggressive with their land
management (Abrahamson pers. comm.). All-terrain vehicles use the area during the year.
Other features of the area include a marsh sandwiched between the transverse dunes and the
parabolic dunes. This marsh is considered the most significant graminoid marsh in central
Pennsylvania (U.S. Fish and Wildlife Service 1990). The southern wetlands are now protected by
a conservation easement held by the Merrill Linn Land & Waterways Conservancy (Abrahamson
pers. comm.). None of the sand dune area, however, is protected or is managed to protect the
ecosystem.
Rome Sand Plains
The Rome Sand Plains is a 16,000-acre (6,500 ha) area of up to 30-50 foot deep fossil sand
dunes that support pitch pine heath barrens. A 3,875-acre (1,568-ha) preserve is located in and
around the city of Rome within Oneida County, New York, and is currently protected under a
consolidated management plan (Rome Sand Plains Resource Management Team 2006). Outside
this area, the Rome Sand Plains have been fragmented and degraded by development, mining,
and farming.
Rome Sand Plains was once at the bottom of glacial Lake Iroquois that covered most of central
New York at the end of the last ice age. Sands were exposed to the prevailing westerly winds
when the lake receded, shifting the sands into crescent-shaped fossil sand dunes (Rome Sand
Plains Resource Management Team 2006). Also present are a series of eskers, including one
geologically rare bifurcated, or forked, esker, formed by deposits of sand and gravel by subglacial streams (Rome Sand Plains Resource Management Team 2006).
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Analysis of fossil sediment and pollen samples suggest that Rome Sand Plains was dominated by
a mesophytic deciduous-coniferous forest approximately 5,000 to 500 years ago. Fire was
relatively infrequent. The pitch pine community originated more recently (<500 years) when fire
disturbances became more prevalent due to Native American hunting or clearing and Colonial
land clearing for agriculture and logging. With the cessation of these disturbances in the past 50
years, the Rome Sand Plains is succeeding to a more mesic community (Rome Sand Plains
Resource Management Team 2006).
Today, Pitch Pine Heath Barrens is the dominant vegetation community found on the welldrained sand dunes at Rome Sand Plains (Rome Sand Plains Resource Management Team 2006).
Pitch pine (Pinus rigida) is the dominant tree in this community; heaths or scrub oaks (Quercus
ilicifolia) dominate the shrub layer. Within the herbaceous layer, wild blue lupine (Lupinus
perennis) is the major food source for the frosted elfin butterfly (Incisalia irus), a state-ranked
(S1S3) species (Pfitsch and Williams 2009) and the Karner blue butterfly (Lycaeides melissa
samuelis), a state and federally endangered species that does not currently exist at Rome Sand
Plains. Other communities at Rome Sand Plains include a Pitch Pine-Blueberry Peat Swamp, a
Pine Barrens Intermittent Pond, a Black Spruce--Tamarack Bog, a Highbush Blueberry Bog
Thicket, a Rich Hemlock-Hardwood Peat Swamp, a Hemlock-Hardwood Swamp, a Red MapleHardwood Swamp, and an Appalachian Oak-Pine Forest.
The Globally (G4) and State (S1) listed climbing fern (Lygodium palmatum) is found at Rome
Sand Plains. There are also historic records of ten rare plant species. Several orchids, pitcher
plant and sundew occur in various bogs. Other notable species include pitch pine, scrub oak,
tamarack, roseshell azalea, sphagnum moss, cinnamon fern, cranberry, blueberry, trailing arbutus
and viburnum. In addition to plant species, several state-listed wildlife species are recorded for
Rome Sand Plains including frosted elfin (Incisalia irus), two specis of noctuid moths
(Zanclognatha martha and Lithophane thaxteri), midland clubtail (Gomphus fraternus), redshouldered hawk (Buteo lineatus), spotted turtle (Clemmys guttata), wood turtle (Clemmys
insculpta), and spotted salamander (Ambystoma maculatum). A 1995 survey recorded 219
species of Lepidoptera (Rome Sand Plains Resource Management Team 2006). Sixty-three
species of sand wasps have been recorded (Kurczewski 1998).
Rome Sand Plains has a unique cultural history (Rome Sand Plains Resource Management Team
2006). Wood Creek connected the Mohawk River with Oneida Lake and points west and was
therefore used as a travel route for Native Americans, military, settlers and traders. Fort Stanwix
was constructed to protect the route between the Mohawk River and Wood Creek. Until the Erie
Canal was opened in 1825, Wood Creek was considered a transportation route of national
significance, and attempts were made between 1790 and 1820 to improve passage. These cultural
remains are still visible today and contribute to the natural and cultural diversity of Rome Sand
Plains. The Rome Sand Plains was lightly developed with farms during the 19th and early 20th
century, although the sandy soils and wetlands constrained these activities (Rome Sand Plains
Resource Management Team 2006). The area was logged, mined, and hunted. The New York
Central and Hudson Railroad was constructed through the Rome Sand Plains in the mid-19th
century and resulted in several fires. Fire frequency decreased with the switch to diesel trains in
the mid-20th century and subsequently the abandonment of the railroad tracks in 1975 (Rome
Sand Plains Resource Management Team 2006). In response to mining permit applications,
18
different conservation-minded organizations started acquiring lands within the Rome Sand Plains
in the 1980’s to protect its unique geology and ecology. In 1997, the Rome Sand Plains Resource
Management Team was created.
The site is cooperatively managed by the Rome Sand Plains Resource Management Team, which
includes representatives from New York State Department of Environmental Conservation, The
Nature Conservancy, the City of Rome, Oneida County, the Izaak Walton League, the State
Department of Transportation, the New York State Canals Corporation, the State Museum, the
Mohawk Valley Heritage Corridor Commission, New York Rivers United, the Adirondack
Mountain Club, the Rome Area Chamber of Commerce, the Oneida Nation, the Rome Historical
Society, and the West Rome Riders, Inc, among others. This team published the Rome Sand
Plains Consolidated Management Plan (Rome Sand Plains Resource Management Team 2006;
http://www.dec.ny.gov/lands/22572.html) for 3,875 acres of the 16,000-acre Sand Plains area in
2006 to protect, maintain and enhance the geological, ecological and historical values of the
Sand Plains, and promote recreational opportunities. Its principal goal is to protect the pitch pine
heath barrens ecosystem that exists at Rome Sand Plains. Lands that are managed under this
management plan are principally owned by the New York State Department of Environmental
Conservation, Oneida County, The Nature Conservancy and the Izaak Walton League. Private
property is interspersed throughout these lands but is not managed under the management plan.
The signage and trail system within Rome Sand plains illustrate the diversity of features found at
the site. The area is easily accessible by road and trail. Research at Rome Sand Plains has
focused on inventorying the flora and fauna and examining the feasibility of using the Rome
Sand Plains as a recovery location for the Karner blue butterfly, which is currently absent from
the site (Rome Sand Plains Resource Management Team 2006). Research has examined the fire
history at Rome Sand Plains to determine the best management strategies for the area. Other
research has focused on the geologic and hydrogeologic links between the ground water and
wetlands. Archeological and historic research is conducted as well. Researchers are affiliated
with The Nature Conservancy, The State University of New York, Hamilton College, Rutgers
University, Colgate University, Utica College and the New York State Museum. Local high
school and college teachers use Rome Sand Plains as an outdoor classroom. A Rome Sand Plains
Management Team newsletter and local newspapers articles and outreach activities educate the
general public.
Other Sites
Chase Lake Sandplains
This site includes a small complex of kettlehole wetlands in a pine-successional northern
hardwood landscape near the Adirondack foothills (Bried and Edinger 2009).
Mahantango sand deposit
Peltier (1949) recognizes an area approximately 1 mile north of the town of Mahantango as a
significant wind-borne deposit of very fine sand. The sand deposit covers a hilltop 139 feet
above the river and is approximately 10 feet thick. Actual dunes do not appear to be present and
nothing else is known of this site.
19
Millersburg sand deposit
Similar to the Mahantango sand deposit, Peltier (1949) recognizes an area near the town of
Millersburg as a significant wind-borne sand deposit. The sand deposit occurs 80 feet above the
Wiconisco Creek, a tributary to the Susquehanna River. The upper, silty A-horizon is only 4-6
inches thick and is underlain by a 1-4 foot deposit of reddish brown, very compact sand that
breaks into small lumps rather than grains. Dunes are not present and other information about
this site is not available.
Saratoga Sandplains
Similar to Chase Lake, Bried and Edinger (2009) briefly describe the 800-acre (325 ha) firesuppressed pine-oak landscape within Wilton Wildlife Preserve & Park. The site was created to
protect the federally endangered Karner blue butterfly (Lycaeides melissa samuelis).
Comparative Analysis & Discussion
We compare Albany Pine Bush pNNL to the two other potential sites in the region that best
illustrate similar eolian processes (Montandon Sand Dunes and Rome Sand Plains). In only one
case, however, are sand dunes associated with characteristic and well managed pine barrens –
Rome Sand Plains. Other sites that feature wind-borne sand exist in the Appalachian Ranges and
Appalachian Plateau regions, but these sites do not currently support pine barrens. These
secondary sites are therefore not considered in comparison with Albany Pine Bush.
1. Comparison of pNNL with Rome Sand Plains
Albany Pine Bush is most closely matched with Rome Sand Plains. We therefore consider both
primary (illustrative character and present condition) and secondary (diversity, rarity, and value
for science and education) features to illustrate similarities and differences.
A) Illustrative Character: Both areas profoundly illustrate pine barrens that have
developed on fossil sand dunes. Both areas illustrate how glacial retreat during the
last ice age left behind patches of sand and crushed rock known as glacial drift, which
was blown by wind to form the sand dunes. These sandy systems are home to a
unique, rare, and vulnerable inland pine barren ecosystem. Thus, the Albany Pine
Bush and the Rome Sand Plains rank equally in Illustrative Character, though Rome
Sand Plains is on the wet end of the continuum for a pine barrens, with 46% of total
land area classified as wetlands, as compared to 14% of Albany Pine Bush Preserve.
B) Present Condition: At both sites, the sand dune / pine barrens ecosystem consists of
protected areas interspersed with private unprotected lands. Thus, both the Albany
Pine Bush and the Rome Sand Plains are fragmented with varied disturbance
histories. Suburbanization threatens the health and integrity of the ecosystem at both
sites. Consequently, management teams composed of several government and private
partners have developed comprehensive management plans to ensure that protected
lands are managed appropriately. Site management has been highly effective in the
Albany Pine Bush Preserve, with an active staff having applied management to more
than 1,700 acres to date and providing for a 300-acre expansion of endangered Karner
blue butterfly habitat. The Rome Sand Plains have known significantly less
management and are consequently more heavily forested, with less representation of
20
the characteristic open pitch pine-scrub oak barrens. Thus, the Albany Pine Bush has
been ranked as slightly higher in Present Condition than Rome Sand Plains.
C) Diversity: Both areas support a diversity of habitats that illustrate the unique interplay
between geology and ecology. High pine barrens located on fossil sand dunes, lowlying bogs and wetlands, and transitional meadows create a diverse ecological
resource. The Rome Sand Plains is rich in cultural resources centered on Wood
Creek, which figured prominently in the activities of the Iroquois Nation, the early
transportation history of the United States and the American Revolution. The low
relief of the Rome Sand Plains landscape offers small-scale views of subtle beauty.
Likewise, the juxtaposition of pine barrens and wetlands creates a unique and scenic
landscape mosaic of wet and dry habitats at Albany Pine Bush. Low-lying wetland
communities include red-maple hardwood swamps, shallow-emergent marshes, and
intermittent ponds. Similar to Rome Sand Plains, the Albany Pine Bush offers
beautiful scenery and opportunities for repose through its low-relief landscape views.
D) Rarity: Both areas support rare and endangered flora and fauna. Rome Sand Plains is
home to the Globally (G4) and State (S1) listed climbing fern (Lygodium palmatum).
Several state-listed wildlife species are recorded for Rome Sand Plains including
frosted elfin (Incisalia irus), two species of noctuid moths (Zanclognatha martha and
Lithophane thaxteri), midland clubtail (Gomphus fraternus), red-shouldered hawk
(Buteo lineatus), spotted turtle (Clemmys guttata), wood turtle (Clemmys insculpta),
and spotted salamander (Ambystoma maculatum). Albany Pine Bush is home to
hundreds of Lepidoptera species, including over 40 noctuid moths (Noctuidae)
considered to be pine barrens specialists. Federally listed endangered species and
species of concern found within Albany Pine Bush include the Karner blue butterfly
(Lycaeides melissa samuelis), Albarufan dagger moth (Acronicta albarufa), and bog
bluegrass (Poa paludigena). State-listed species of concern include the inland barrens
buckmoth (Hemileuca maia ssp. 3), frosted elfin (Incisalia irus), Jefferson
salamander (Ambystoma jeffersonium), blue-spotted salamander (Ambystoma
laterale), spotted salamander (Ambystoma maculatum), Eastern hognose snake
(Heterodon platirhinos), spotted turtle (Clemmys guttata), wood turtle (Clemmys
insculpta), red-shouldered hawk (Buteo lineatus) and Eastern bluebird (Sialia Sialis).
State-listed rare plants include red-rooted flatesedge (Cyperus erythrorhizos),
Houghton's umbrella-sedge (Cyperus houghtonii), and Schweinit's flatsedge (Cyperus
schweinitzii). The Karner blue butterfly is currently absent at Rome Sand Plains, and
the Rome Sand Plains Management Plan (2006) highlights the need to restore this
species. This difference, and the higher number of federal and state-listed species of
concern that have been documented at Albany Pine Bush leads us to rank Albany
Pine Bush as higher than Rome Sand Plains. Albany Pine Bush also has the added
distinction of being a designated New York State Bird Conservation Area.
21
E) Value for Science and Education: Both sites are highly engaged in science education.
A broad range of research projects are conducted at both sites. A greater number of
published and easily accessible articles are available for Albany Pine Bush, including
Barnes (2003) excellent overview of the site. The New York State Geological Survey,
the NYS Museum and several academic institutions have and continue to conduct
research on the geological and biological aspects of the Albany Pine Bush. Some of
these research activities have been ongoing for decades. Both sites support easily
accessible trails, and both sites have signage that highlights important features of the
landscape. The Discovery Center (pictured in Appendix B) opened at Albany Pine
Bush in 2007 and serves tens of thousands of visitors a year with interactive exhibits
and activities that explore the Preserve’s geological significance, plants and animals,
management principles, and human impacts. Management teams at both sites are
highly engaged in education and outreach. Thus, value of science and education is
high at both sites, with a slight edge to Albany Pine Bush.
2. Comparison of pNNL with Montandon Sand Dunes
The primary features of Albany Pine Bush ranked higher than those of Montandon Sand Dunes.
We therefore only consider primary features in our comparison.
A) Illustrative Character: Both areas support characteristic sand dunes that were formed
through eolian processes. Both sites support vegetation characteristic of sandy,
coastal areas. However, Albany Pine Bush better documents and illustrates the pine
barrens character. We therefore rank Albany Pine Bush higher than Montandon Sand
Dunes in Illustrative Character.
B) Present Condition: Albany Pine Bush ranks higher than Montandon Sand Dunes in
Present Condition. Montandon Sand Dunes was historically intensively mined,
logged, and farmed. Currently, the southern part of the sand dune complex is mined
for sand and gravel. The integrity of the Albany Pine Bush is threatened as well, but
the Albany Pine Bush Preserve Commission is actively engaged to preserve the
character of the site.
In summary, we rank Rome Sand Plains and the Albany Pine Bush as near-equal in many
characteristics. Rome Sand Plains lies firmly within the Appalachian Plateau region whereas the
Albany Pine Bush straddles both the Appalachian Plateau and Appalachian Ranges region. We
rank Albany Pine Bush higher than Rome Sand Plains because of the presence of the Karner blue
butterfly and a greater variety of observed and documented federally and state-listed species of
concern. Educational, outreach and management infrastructure also were evaluated as superior at
Albany Pine Bush, and the site excels in its breadth and intensity of scientific investigation.
22
Evaluation Recommendations
After careful evaluation of both primary and secondary features of the periglacial sand dunes
and pitch pine-scrub oak barrens found at Albany Pine Bush, we recommend the site for
designation as a National Natural Landmark. The designation would fill a current gap within the
NNL Program for Eolian Landforms in the Appalachian Plateau and Appalachian Ranges
provinces. The proposed site showcases how eolian processes form regionally important sand
dune landscapes. Despite the wide distribution of sand dunes in the United States, only small
areas of eolian sand occur in the Appalachian Ranges and Appalachian Plateau. Albany Pine
Bush provides an illustrative example of this fossil landscape feature in combination with one of
the best examples of inland pine-barren ecosystems in the world. These fire-maintained
ecosystems are generally more common on the Atlantic Coastal Plain and support a distinct and
diverse flora and fauna.
In comparing Albany Pine Bush to other potential sites in the Appalachian Plateau and Ranges
provinces, we rank it slightly above Rome Sand Plains in meeting NNL significance criteria.
This prioritization is based on higher biodiversity within the park including the presence of a
greater number of species of concern such as the Karner blue butterfly (Lycaeides melissa
samuelis), a state and federally-listed endangered species, and the implementation of a successful
management plan. The education, outreach, and scientific infrastructure at Albany Pine Bush is
also outstanding. Other potential comparative sites are either inferior in quality (e.g., Montandon
Sand Dunes) and/or are poorly documented.
Proposed Landmark Boundary
The proposed landmark boundary includes all Preserve land currently overseen by the Albany
Pine Bush Commission (Figure 12). Any land added to the management area in the future will be
evaluated accordingly. Although this boundary includes multiple landowners, it is managed in its
entirety by a single entity. All landowners have consented to allow the site to be evaluated and
potentially listed as a National Natural Landmark. The vector boundary layer for the Preserve
was provided by the Commission. The site is coarsely bound on the north by New York Route 5,
on the south by U.S. Route 20, on the east by Fuller Road, and on the west by Route 146, Lone
Pine Road, and Cordell Road.
23
Literature Cited
Albany Pine Bush Preserve Commission (APBPC). 2010. Management Plan and Final
Environmental Impact Statement for The Albany Pine Bush Preserve. September 16, 2010. 148
pp.
Baer CH, Behling RE, Little RS. 1982. A survey of potential natural landmarks of the
Appalachian Plateaus region: University of West Virginia, Morgantown, 472 p. [NTIS acc. no.
PB83 -119750]
Barnes JK. 2003. Natural History of the Albany Pine Bush. New York State Museum, NY
Beachy BL, Robinson GR. 2008. Divergence in avian communities following woody plant
invasions in a pine barrens ecosystem. Natural Areas Journal 28: 395-403.
Boyd, HP. 2008. The Ecological Pine Barrens of New Jersey. Plexus Publishing, Inc. Medford,
NJ.
Bradley JW, Younge M, Kozlowski A. 2010. Chapter 12: The Sundler Sites: Reconstructing the
Late Pleistocene Landscape and Its People in the Captial Region of New York. Soldiers, Cities,
and Ladscapes: Papers in Honor of Charles L. Fisher. Drooker, PB, Hart, JP. University of the
State of New York, The State Education Department. 213-223.
Bried JT, Edinger GJ. 2009. Baseline floristic assessment and classification of pine barrens
vernal ponds. Journal of the Torrey Botanical Society 136: 128-136.
Bried JT, Gifford NA. 2010. Mowing and herbicide of Scrub Oaks in Pine Barrens: Baseline
data. Ecological Restoration 28: 245-248.
Bried JT, Hecht JA. 2011. Comparison of herbicide treatments to control native aspen
encroachment in pine barrens. Natural Areas Journal 31: 288-293.
Bried JT, Langwig KE, DeWan AA, Gifford NA. 2011. Habitat associations and survey effort
for shrubland birds in an urban pine barrens preserve. Landscape and Urban Planning 99: 218225.
Buchholz K, Zampella RA. 1987. A 30-year fire history of the New Jersey Pine Plains. Bulletin
of the New Jersey Academy of Science. 32:61-69.
Campbell MC, Fisher TG, Goble RJ. 2011. Terrestrial sensitivity to abrupt cooling recorded by
aeolian activity in northwest Ohio, USA. Quaternary Research 75: 411–416.
Chartrand AJ. 1994. A vegetative study of the communities of the Montandon, Pennsylvania
swamp and woodland area. Undergraudate thesis, Bucknell University. 69pp.
24
Chase CM. 1977. Central Pennsylvania sand dunes. Pennsylvania Geology 8: 9-12.
Christopherson RW. 2012. Geosystems: An Introduction to Physical Geography. 8th ed. PrenticeHall.
Clark GM. 1985. Potential geological natural landmarks for the Appalachian Ranges natural
region theme study: University of Tennessee, Knoxville (July 24, 1985), 713 p. [NTIS acc. no.
PB91-116624]
Denny CS, Owens JP. 1979. Sand Dunes on the Central Delmarva Peninsula, Maryland and
Delaware. U.S. Geological Survey Professional Paper 1067–C. 15 pp.
DeSelm HR. 1984. Potential national natural landmarks of the Appalachian Ranges natural
region, ecological report: University of Tennessee, Knoxville (Sept., 1984), 559 p. [NTIS acc.
no. PB85-159275]
Englebright SC, Hanson GN, Rasbury T, Lamont EE. 2000. On the origin of parabolic dunes
near Friar’s Head, Long Island, New York. The Quarterly Newsletter: Long Island Botanical
Society. 10, 1: 1–11.
Forman RTT. 1998. Pine Barrens: Ecosystem and Landscape. Rutgers University Press, New
Brunswick, N.J.
Forman SL, Nordt L, Gomez J, Pierson J. 2009. Late Holocene dune migration on the south
Texas sand sheet. Geomorphology 108: 159–170.
Forrester JA, Leopold DJ, Hafner SD. 2005. Maintaining critical habitat in a heavily managed
landscape: Effects of power line corridor management on Karner blue butterfly (Lycaeides
melissa samuelis) habitat. Restoration Ecology 13: 488-498.
French HM, Demitroff M. 2012. Late-Pleistocene paleohydrology, eolian activity and frozen
ground, New Jersey Pine Barrens, eastern USA. Netherlands Journal of Geosciences 91: 25–35.
Frisbee R. 1977. Report on swamp and woodland north of Montandon. Undergraduate report,
Bucknell University. 57pp.
Geyer AR, Bolles WH. 1979. Outstanding scenic geologic features of Pennsylvania.
Pennsylvania Geological Survey 4th. Environmental Geology Report EG7, Part 1, 508 pp.
Gifford NA, Deppen JM, Bried JT. 2010. Importance of an urban pine barrens for the
conservation of early-successional shrubland birds. Landscape and Urban Planning 94: 54-62.
Girardi JD. 2005. Comparative GPR study of Pleistocene and modern parabolic dunes, Long
Island. Paper No. 12–6. Geological Society of America Abstracts with Programs 37: 1–23.
25
Gifford NA, Deppens JM, Bried JT. 2010. Importance of an urban pine barrens for the
conservation of early-successional shrubland birds. Landscape and Urban Planning 94: 54–62
Harman JR, Arbogast AF. 2004. Environmental ethics and coastal dunes in western lower
Michigan: developing a rationale for ecosystem preservation. Annals of the Association of
American Geographers 94: 23–36.
Hochman ER, Abrahamson WG, Clark JG. 1996. Montandon marsh: a vegetation description of
a potentially endangered wetland. Journal of the Pennsylvania Academy of Sciences 70: 22-29.
Ivester AH, Leigh DS. 2003. Riverine dunes on the Coastal Plain of Georgia, USA.
Geomorphology 51: 289–311.
Ivester AH, Leigh DS, Godfrey-Smith DI. 2001. Chronology of inland eolian dunes on the
Coastal Plain of Georgia, USA. Quaternary Research 55: 293–302.
Kays RW, DeWan AA. 2004. Ecological impact of inside/outside house cats around a suburban
nature preserve. Animal Conservation 7: 273-283.
Kilibarda Z, Blockland J. 2011. Morphology and origin of the Fair Oaks Dunes in NW Indiana,
USA. Geomorphology 125: 305–318.
Kirchner JJ, Ralston J, Gifford NA. 2011. Stable isotope analysis of fall migration stopover by
six passerine species in an inland pitch pine-scrub oak barren. The Wilson Journal of
Ornithology 123: 548–556.
Kurczewski FE. 1998. Distribution, status, evaluation, and recommendations for the protection
of Tachysphex pechumani Krombein, the antennal-waving wasp. Natural Areas Journal 18: 242254.
Little S. 1946. The effects of forest fires on the stand: history of New Jersey’s Pine Region.
Forest Management Paper 2:1-43.
Loss SR, Will T, Marra PP. 2013. The impact of free-ranging domestic cats on wildlife of the
United States. Nature Communications 4:1396.
Little S. 1998. Fire and plant succession in the New Jersey Pine Barrens, p. 229-313. In R. T. T.
Forman, [ed.], Pine Barrens: Ecosystem and Landscape. Rutgers University Press, New
Brunswick, New Jersey.
Malcolm GM, Bush DS, Rice SK. 2008. Soil nitrogen conditions approach preinvasion levels
following restoration of nitrogen-fixing black locust (Robinia pseudoacacia) stands in a pine-oak
ecosystem. Restoration Ecology 16: 70-78.
26
Markewich HW, Litwin RJ, Pavich MJ, Brook GA. 2009. Late Pleistocene eolian features in
southeastern Maryland and Chesapeake Bay region indicate strong WNW-NW winds
accompanied growth of the Laurentide Ice Sheet. Quaternary Research. 71, 3: 409–425.
Markewich HW, Markewich W. 1994. An Overview of Pleistocene and Holocene Inland Dunes
in Georgia and the Carolinas- Morphology, Distribution, Age and Paleoclimate. U.S. Geological
Survey Bulletin 2069. United States Government Printing Office, Washington, DC, 32 pp.
Marsh B. 1998. Wind-transverse corrugations in Pleistocene periglacial landscapes of central
Pennsylvania. Quaternary Research 49: 149–156.
Mawdsley JR. 2007. Ecology, distribution, and conservation biology of the tiger beetle Cicindela
patruela consentanea Dejean (Coleoptera: Carabidae: Cicindelinae). Proceedings of the
Entomological Society of Washington 109: 17–28.
McCormick J. 1998. The vegetation of the New Jersey Pine Barrens, p. 229-242. In R. T. T.
Forman, [ed.], Pine Barrens: Ecosystem and Landscape. Rutgers University Press, New
Brunswick, New Jersey.
Mecum LK. 1992. 1992 breeding bird survey of Montandon marsh and wetlands. Undergraduate
Thesis, Bucknell University. 147pp.
Meriwether E., Coon D, McKone M, Kreamer G. 1975. Notes on the biology of Montandon
marsh. Undergraduate thesis, Bucknell University. 12pp.
Milne BT. 1985. Upland vegetational gradients and post-fire succession in the Albany Pine
Bush, New York. Bulletin of the Torrey Botanical Club 112: 21–34.
Morlando S, Scmidt SJ, LoGiudice K. 2011. Reduction in Lyme disease as an economic benefit
of habitat restoration. Restoration Ecology 20: 498–504.
Munyikwa K, Feathers JK, Rittenour TM, Shrimpton HK. 2011. Constraining the Late
Wisconsinan retreat of the Laurentide ice sheet from western Canada using luminescence ages
from postglacial aeolian dunes. Quaternary Geochronology 6: 407–422.
National Park Service. 1990. Natural History in the Natural Park System and on the National
Registry of Natural Landmarks: Natural Resource Report NPS/NR/NRTR–90/03, U.S. Dept. of
the Interior, National Park Service, Washington, D.C. (Sept., 1990), 99 pp.
Newell WL, Clark I. 2008. Geomorphic Map of Worcester County, Maryland, Interpreted from a
LIDAR-Based Digital Elevation Model. U.S. Geological Survey Report Series 2008–1005,
Reston, VA, 34 pp.
Niessen ACHM, Koster EA, Galloway JP. 1984. Periglacial Sand Dunes and Eolian Sand
Sheets: An Annotated Bibliography. Open-File Report 84–167, United States Geological Survey,
61 pp.
27
Peltier LC. 1949. Pleistocene Terraces of the Susquehanna River Pennsylvania. Pennsylvania
Geological Survey, Fourth Series, Bulletin G23. Department of Internal Affairs, Topographic
and Geologic Survey. Commonwealth of Pennsylvania, Harrisburg.
Radeloff VC, Mladenoff DJ, Boyce MS. 2000. A historical perspective and future outlook on
landscape scale restoration in the northwest Wisconsin pine barrens. Restoration Ecology 8: 119126.
Rebollal MB, Perez-Gonzales A. 2008. Inland aeolian deposits of the Iberian Peninsula: Sand
dunes and clay dunes of the Duero Basin and the Manchega Plain. Palaeoclimatic considerations.
Geomorphology 102: 207-220
Reiners WA. 1998. Ecological research opportunities in the New Jersey Pine Barrens, p. 557567. In R. T. T. Forman, [ed.], Pine Barrens: Ecosystem and Landscape. Rutgers University
Press, New Brunswick, New Jersey.
Rice SK, B. Westerman B, Federici R. 2004. Impacts of the exotic, nitrogen-fixing black locust
(Robinia pseudoacacia) on nitrogen-cycling in a pine-oak ecosystem. Plant Ecology 174: 97107.
Rome Sand Plains Management Team. 2006. Rome Sand Plains Consolidated Management Plan.
96pp. http://www.dec.ny.gov/docs/lands_forests_pdf/rspump.pdf
Shuman B, Webb T, Bartlein P, Williams J. 2002. The anatomy of a climatic oscillation:
vegetation change in eastern North America during the Younger Dryas chronozone. Quaternary
Science Reviews 21: 1777-1791.
United States Fish and Wildlife Service Region 5, Northeast Region. 1990. Regional wetlands
concept plan emergency wetlands resources act. Newton Corner, MA.
United States Fish and Wildlife Service. 1997. Significant Habitats and Habitat Complexes of
the New York Bight Watershed - Complex #30 Albany Pine Bush.
van Dam AR, van Dam MH. 2008. Impact of off-road vehicle use on dune endemic Coleoptera.
Annals of the Entomological Society of America. 101: 411–417.
Wacker PO. 1998. Human Exploitation of the New Jersey Pine Barrens before 1900, p. 3-21. In
R. T. T. Forman, [ed.], Pine Barrens: Ecosystem and Landscape. Rutgers University Press, New
Brunswick, New Jersey.
Werner CM, Mason JA, Hanson PR. 2011. Non-linear connections between dune activity and
climate in the High Plains, Kansas and Oklahoma, USA. Quaternary Research 75: 267–277.
Zalewski ME. 1989. Montandon marsh dune vegetation: Potential restoration species.
Undergraduate Thesis, Bucknell University. 82pp.
28
Zampella RA, Moore GA, Good RE. 1992. Gradient analysis of pitch pine (Pinus rigida Mill.)
lowland communities in the New Jersey Pinelands. Bulletin of the Torrey Botanical Club.
119:253-261.
Zampella RA, Laidig KJ, Lathrop RG, Bognar JA. 1999. Size-class structure and hardwood
recruitment in Atlantic white cedar swamps of the New Jersey pinelands. Journal of the Torrey
Botanical Society. 126:268-275.
29
Figure 1. Map of physiographic provinces. The Appalachian Ranges are
represented by the Valley and Ridge and the Blue Ridge physiographic
provinces. Geographic data from USGS clearinghouse.
30
Figure 2. Locations of Pine Barrens of the Northeast United States. Map from
Brad Stratton of The Nature Conservancy.
0
31
25
50
100 Miles
´
Figure 3. Albany Pine Bush location map. Data from Albany NY Quad Sheet
7.5-minute USGS topographic quad sheets.
32
Figure 4. Examples of both Longitudinal and Parabolic Dunes in the preserve.
2-Foot Contour Data obtained from NY State GIS Clearinghouse website.
33
Figure 5. Map of wetland resources in the preserve. Data from the National
Wetlands Inventory.
34
Figure 6. Soils of Albany Pine Bush. Sand dunes are highlighted as a primary
natural feature at the site. Data from New York State Museum.
35
Figure 7. Bedrock Geology for Albany Pine Bush. Data from New York State
Museum.
36
Figure 8. Access to Albany Pine Bush, including trails and roads. Data
provided by Neil Gifford, Albany Pine Bush Preserve.
37
Figure 9. Ownership map for Albany Pine Bush and surrounding lands.
Colored parcels are lands within the proposed NNL boundary. Brown parcels
represent adjacent parcels. Data provided by Brad Stratton of The Nature
Conservancy.
38
Figure 10. Land cover map for Albany Pine Bush and surrounding lands.
Data from 2006 National Landcover Dataset.
39
Figure 11. Albany Pine Bush Preserve Commission’s Area of Study and
recommended expansion of Preserve Boundary. Data from Neil Gifford,
Albany Pine Bush Preserve.
40
Figure 12. Albany Pine Bush proposed National Natural Landmark
boundary.
41
Appendix A: Albany Pine Bush Preserve Species List
VASCULAR PLANTS
Compiled and edited by George R. Robinson with the assistance of Kathleen Moore, State
University of New York at Albany
This checklist is derived from five sources: (1) historic surveys of the Pine Bush region
by Stanley Smith, Homer House and other botanists, as recorded in Rittner (1976); (2)
collections and records maintained by the Albany Pine Bush Preserve Commission; (3) wetland
surveys by Mattox (1994); (4) New York Natural Heritage Program surveys (Schneider 1991 and
Hunt 1996); and (5) records and collections from scientists at the University at Albany. The
original and primary sources for most records are notes and collections of Stanley Smith,
archived at the New York State Museum. An asterisk (*) following an entry in this list indicates
that the species is considered a non-indigenous introduction. Nomenclature follows Mitchell and
Tucker (1997), as does classification of native/non-native status. The text of this list is largely
derived from a 3779-entry electronic database of New York State plants compiled by Richard
Mitchell, New York State Museum, in 1999. Following each common name is an indication of
the probable status of the species -- i.e., whether it remains extant in the Pine Bush. Species
whose status is "[y]" have been confirmed on the basis of recent surveys noted above, with
assistance from scientists at the New York State Museum and staff of the Albany Pine Bush
Commission. Those with “[n]” status have been deemed extirpated. Those left blank (“[ ]”)
may or may not persist in the Albany Pine Bush. Readers who encounter unrecorded or
unconfirmed species are asked to bring them to the attention of George Robinson at the
University at Albany or Christopher Hawver of the Albany Pine Bush Preserve Commission.
Selaginellaceae
Selaginella apoda (L.) Fern.
Creeping spikemoss [y]
Equisetaceae
Equisetum arvense L.
common horsetail [y]
Equisetum fluviatile L.
Water horsetail [y]
Equisetum hyemale L.
Scouring rush [y]
Equisetum pratense Ehrh.
Meadow horsetail [y]
Equisetum scirpoides Michx.
Dwarf scouring rush [ ]
Equisetum sylvaticum L.
Woodland horsetail [y]
Equisetum variegatum Schleich. ex
Weber & Mohr.
Variegated horsetail [y]
Lycopodiaceae
Huperzia lucidula (Michx.) Trev.
Shining fir clubmoss [ ]
Lycopodiella inundata (L.) Holub
Northern bog clubmoss [y]
Lycopodium clavatum L.
Staghorn clubmoss [y]
Lycopodium complanatum x
tristachyum
Zeiller's clubmoss [ ]
Lycopodium obscurum L.
Ground pine
Lycopodium tristachyum Pursh
Ground cedar [y]
Ophioglossaceae
Botrychium dissectum Spreng.
42
Cut-leaf grape-fern [y]
Botrychium matricariifolium (A.
Braun ex Dowell) A. Braun ex Koch
Daisy-leaf grape-fern [y]
Botrychium multifidum (Gmel.)
Rupr.
Leathery grape-fern [ ]
Botrychium simplex E. Hitchc.
Dwarf grape fern [ ]
Botrychium virginianum (L.) Sw.
Rattlesnake fern [y]
Ophioglossum pusillum Raf.
Northern adder's-tongue [ ]
Dryopteris marginalis (L.) A. Gray
Marginal wood fern [y]
Matteuccia struthiopteris (L.) Todaro
Ostrich fern [y]
Onoclea sensibilis L.
Sensitive fern [y]
Polypodium virginianum L.
Rock polypody [ ]
Polystichum acrostichoides (Michx.)
Schott
Shield fern [y]
Dennstaedtiaceae
Dennstaedtia punctilobula (Michx.)
Moore
Hay-scented fern [y]
Pteridium aquilinum (L.) Kuhn ex
Decken
Bracken [y]
Pteridaceae
Adiantum pedatum L.
Maidenhair fern [y]
Dryopteridaceae
Athyrium filix-femina (L.) Roth ex
Mertens var. angustum (Willd.)
Lawson
Northern lady-fern [y]
Athyrium filix-femina (L.) Roth ex
Mertens var. asplenioides (Michx.)
Farw.
Southern lady-fern [y]
Cystopteris bulbifera (L.) Bernh.
Bulblet fern [ ]
Cystopteris fragilis (L.) Bernh.
Fragile fern [ ]
Deparia acrostichoides (Sw.) Kato
Silvery spleenwort [ ]
Dryopteris carthusiana (Vill.) Fuchs
Spinulose wood fern [y]
Dryopteris clintoniana (D. Eaton ex
A. Gray) Dowell
Clinton's shield fern [ ]
Dryopteris cristata (L.) A. Gray
Cested wood fern [y]
Dryopteris goldiana (Hooker ex
Goldie) A. Gray
Gant wood fern [ ]
Dryopteris intermedia (Muhl. ex
Willd.) A. Gray
Fancy fern [y]
Osmundaceae
Osmunda cinnamomea L.
Cinnamon fern [y]
Osmunda claytoniana L.
Interrupted fern [y]
Osmunda regalis L. var. spectabilis
(Willd.) A. Gray
Royal fern [y]
Thelypteridaceae
Phegopteris connectilis (Michx.)
Watt
Northern beech fern [ ]
Phegopteris hexagonoptera (Michx.)
Fee
Broad beech fern [ ]
Thelypteris noveboracensis (L.)
Nieuwl.
New York fern [y]
Thelypteris palustris Schott var.
pubescens (Laws.) Fernald
Marsh fern [y]
Blechnaceae
Woodwardia virginica (L.) Sm.
Virginia chain fern [ ]
43
Ceratophyllum demersum L.
Coontail [y]
Taxaceae
Taxus canadensis Marsh.
American yew [ ]
Nymphaeaceae
Nuphar advena (Soland. ex Ait.) R.
Br. ex Ait. F.
Yellow pondlily [y]
Nymphaea odorata Dryand ex Ait.
White waterlily [y]
Pinaceae
Abies balsamea (L.) Mill.
Balsam fir [ ]
Larix laricina (DuRoi) Koch
Tamarack, larch [y]
Picea abies (L.) Karst.*
Norway spruce [y]
Pinus rigida Mill.
Pitch pine [y]
Pinus strobus L.
White pine [y]
Pinus sylvestris L.*
Scotch pine [y]
Tsuga canadensis (L.) Carr.
Eastern hemlock [y]
Ranunculaceae
Actaea pachypoda Ell.
White baneberry [ ]
Actaea spicata ssp. rubra L. (Ait.)
Hulten
Red baneberry [y]
Anemone canadensis L.
Canada anemone [y]
Anemone cylindrica A. Gray
Thimbleweed [y]
Anemone quinquefolia L.
Wood anemone [y]
Anemone virginiana L.
Thimbleweed [y]
Aquilegia canadensis L.
Wild columbine [y]
Caltha palustris L.
Marsh marigold [y]
Clematis occidentalis (Hornem.) DC.
Purple clematis [ ]
Clematis virginiana L.
Virgin's-bower [y]
Coptis trifolia (L.) Salisb.
Goldthreads [y]
Hepatica nobilis Mill. var. obtusa
(Pursh) Steyerm.
Blunt-lobed hepatica [y]
Ranunculus abortivus L.
var. abortivus
Small-flowered buttercup [y]
Ranunculus acris L.*
Common buttercup [y]
Ranunculus bulbosus L.*
Bulbous crowfoot [ ]
Ranunculus flabellaris Raf. ex Bigel.
Yellow water-buttercup [n]
Cupressaceae
Juniperus virginiana L.
Eastern red cedar [y]
Lauraceae
Lindera benzoin (L.) Blume
Spicebush [y]
Sassafras albidum (Nutt.) Nees
Sassafras [y]
Magnoliaceae
Liriodendron tulipifera L.
Tulip tree [ ]
Aristolochiaceae
Asarum canadense L.
Wild ginger [y]
Cabombaceae
Brasenia schreberi Gmel.
Water-shield [ ]
Cabomba caroliniana A. Gray*
Fanwort [y]
Ceratophyllaceae
44
Ranunculus flammula L.
Creeping spearwort [ ]
Ranunculus hispidus Michx.
var. nitidus (Muhl. ex Ell.)
Duncan
Swamp buttercup [y]
Ranunculus pensylvanicus L. f.
Bristly buttercup [y]
Ranunculus recurvatus Poir. ex Lam.
Hooked buttercup [y]
Ranunculus repens L.*
Creeping buttercup [y]
Ranunculus sceleratus L.*
Cursed crowfoot [y]
Thalictrum dioicum L.
Early meadow-rue [y]
Thalictrum pubescens Pursh
Tall meadow-rue [y]
Thalictrum revolutum DC.
Waxy meadow-rue [ ]
Thalictrum thalictroides (L.) Eames
& Boivin
Rue anemone [y]
Cornfield poppy [ ]
Papaver rhoeas L.*
Corn poppy [ ]
Sanguinaria canadensis L.
Bloodroot [y]
Hamamelidaceae
Hamamelis virginiana L.
Witch-hazel [y]
Urticaceae
Boehmeria cylindrica (L.) Sw.
False-nettle [y]
Laportea canadensis (L.) Wedd.
Wood-nettle [ ]
Parietaria pensylvanica Muhl. ex
Willd.
Pellitory [ ]
Pilea pumila (L.) A. Gray
Richweed [y]
Urtica dioica L.
ssp. gracilis (Ait.) Selander*
Stinging nettle [y]
Berberidaceae
Berberis thunbergii DC.*
Japanese barberry [y]
Berberis vulgaris L.*
European barberry [y]
Caulophyllum thalictroides (L.)
Michx.
Blue cohosh [y]
Podophyllum peltatum L.
May-apple [y]
Moraceae
Morus alba L.*
White mulberry [y]
Cannabaceae
Humulus japonicus Sieb. & Zucc.*
Japanese hops [ ]
Humulus lupulus L.*
Common hop [ ]
Ulmaceae
Ulmus americana L.
American elm [y]
Ulmus pumila L.*
Dwarf elm [y]
Ulmus rubra Muhl.
Slippery elm [y]
Fumariaceae
Dicentra cucullaria (L.) Bernh.
Dutchman's-breeches [y]
Papaveraceae
Chelidonium majus L.*
Greater celandine [y]
Eschscholzia californica Cham. ex
Nees*
California poppy [ ]
Papaver dubium L.*
Juglandaceae
Carya cordiformis (Wang.) Koch
Bitternut [y]
Carya glabra (Mill.) Sweet
45
American beech [y]
Quercus alba L.
White oak [y]
Quercus alba bicolor
Hybrid oak [ ]
Quercus bicolor Willd.
Swamp white oak [y]
Quercus coccinea Muenchh.
Scarlet oak [y]
Quercus ilicifolia Wang.
Scrub oak [y]
Quercus montana Willd.
Chestnut oak [y]
Quercus prinoides Willd.
Dwarf chestnut oak [y]
Quercus rubra L.
Red oak [y]
Quercus velutina Lam.
Black oak [y]
Pignut [y]
Carya ovata (Mill.) Koch
Shagbark hickory [y]
Carya tomentosa (Poir. ex Lam.)
Nutt.
Mockernut [y]
Juglans cinerea L.
Butternut [y]
Myricaceae
Comptonia peregrina (L.) Coult.
Sweet-fern [y]
Myrica pensylvanica Loisel. ex
Duhamel
Bayberry [ ]
Betulaceae
Alnus incana (L.) Moench ssp.
rugosa serrulata
Speckled alder [y]
Alnus serrulata (Dryand. ex Ait.)
Willd.
Smooth alder [y]
Betula alleghaniensis Britt.
Yellow birch [y]
Betula lenta L.
Sweet birch [y]
Betula papyrifera Marsh.
Paper birch [y]
Betula populifolia Marsh.
Gray birch [y]
Carpinus caroliniana Walt.
ssp. virginiana (Marsh.)
Furlow
Hop hornbeam [y]
Corylus americana Walt.
Hazelnut [y]
Corylus cornuta Marsh.
Beaked hazel [y]
Ostrya virginiana (Mill.) Koch
Hop hornbeam [y]
Caryophyllaceae
Agrostemma githago L.*
Corn-cockle [ ]
Arenaria serpyllifolia L.*
Thyme-leaf sandwort [ ]
Cerastium fontanum Baumg. emend
Jalas*
Common mouse-ear [y]
Dianthus armeria L.*
Deptford pink [y]
Lychnis coronaria (L.) Desr.*
Rose-campion [ ]
Lychnis viscaria L.*
German catch-fly [ ]
Minuartia michauxii (Fenzl) Farw.
Rock sand-wort [ ]
Moehringia laterifolia (L.) Fenzl
Grove sandwort [y]
Myosoton aquaticum (L.) Moench*
Giant chickweed [ ]
Sagina procumbens L.*
Pearlwort [ ]
Saponaria officinalis L.*
Bouncing-bet [y]
Scleranthus annuus L.*
Knawel [y]
Fagaceae
Castanea dentata (Marsh.) Borkh.
American chestnut [y]
Fagus grandifolia Ehrh.
46
Silene antirrhina L.
Sleepy catch-fly [y]
Silene armeria L.*
Sweet-william [y]
Silene dichotoma Ehrh.*
Forked catch-fly [ ]
Silene latifolia Poir.*
White campion [y]
Silene vulgaris (Moench) Garcke*
Bladder-campion [y]
Stellaria borealis Bigel.
Northern starwort [ ]
Stellaria graminea L.*
Common stitchwort, lesser
stitchwort [y]
Stellaria longifolia Muhl. ex Willd.
Needle-leaf starwort [ ]
Stellaria media (L.) Vill.*
Common chickweed [y]
Maple-leaf goosefoot [ ]
Cycloloma atriplicifolium (Spreng.)
Coult.*
Winged pigweed [y]
Salsola kali L.*
Russian thistle [y]
Portulacaceae
Claytonia caroliniana Michx.
Broad-leaved spring beauty[ ]
Portulaca oleracea L.*
Purslane [y]
Nyctaginaceae
Mirabilis hirsuta (Pursh) MacM.*
Hairy umbrella-wort [ ]
Mirabilis nyctaginea (Michx.)
MacM.*
Heartleaf umbrella-wort [y]
Amaranthaceae
Amaranthus albus L.*
Tumbleweed [y]
Amaranthus blitoides S. Wats.*
Prostrate amaranth [y]
Amaranthus hybridus L.*
Green amaranth [ ]
Amaranthus powellii S. Wats.*
Amaranth [ ]
Amaranthus retroflexus L.
Pigweed [y]
Molluginaceae
Mollugo verticillata L.*
Carpetweed [ ]
Phytolaccaceae
Phytolacca americana L.
Poke [y]
Polygonaceae
Fagopyrum esculentum Moench.*
Buckwheat [ ]
Polygonella articulata (L.) Meisn.
Jointweed [y]
Polygonum achoreum Blake
Homeless knotweed [ ]
Polygonum amphibium L.
var. laevimarginatum L.
Water lady's thumb [ ]
Polygonum arifolium L.
Arrowleaf tearthumb [y]
Polygonum aviculare L.*
Knotweed [y]
Polygonum careyi Olney
Smartweed [y]
Polygonum cespitosum Blume
Chenopodiaceae
Atriplex patula L.
Seaside orach [ ]
Bassia scoparia (L.) A. Scott*
Summer cypress [ ]
Chenopodium album L.*
Lamb's-quarters [y]
Chenopodium ambrosioides L.*
Mexican tea [ ]
Chenopodium botrys L.*
Jerusalem-oak [ ]
Chenopodium pratericola Rydb.*
Narrow-leaf goosefoot [ ]
Chenopodium simplex (Torrey) Raf.
47
var. longisetum (DeBruyn)
Stewart*
Japanese lady's-thumb [y]
Polygonum convolvulus L.*
Black bindweed [y]
Polygonum cuspidatum Sieb. &
Zucc.*
Japanese bamboo [y]
Polygonum erectum L.
Erect knotweed [ ]
Polygonum hydropiper L.*
Common smartweed [y]
Polygonum hydropiperoides Michx.
Mild water-pepper [y]
Polygonum lapathifolium L.*
Willow-weed [y]
Polygonum pensylvanicum L.
Pinkweed [y]
Polygonum persicaria L.*
Lady's-thumb [y]
Polygonum punctatum Ell. var.
confertiflorum (Meisn.) Fassett
Dotted smartweed [y]
Polygonum punctatum Ell.
var. punctatum
Dotted smartweed [y]
Polygonum ramosissimum Michx.
var. ramosissimum*
Knotweed [y]
Polygonum sagittatum L.
Tearthumb [y]
Polygonum scandens L.
Climbing false-buckwheat [y]
Polygonum scandens L. var.
dumetorum (L.) Gleason*
Climbing false-buckwheat [ ]
Polygonum virginianum L.
Jumpseed [y]
Rumex acetosella L.*
Sheep sorrel [y]
Rumex altissimus Wood
Pale dock [y]
Rumex crispus L.*
Curly dock [y]
Rumex obtusifolius L.*
Bitter-dock, red-veined dock []
Rumex orbiculatus A. Gray
Great water dock [y]
Rumex patientia L.*
Patience dock [y]
Rumex verticillatus L.
Swamp dock [ ]
Clusiaceae
Hypericum boreale (Britt.) Bickn.
Northern dwarf St. John's
wort [ ]
Hypericum canadense L.
Canadian St. John's-wort [ ]
Hypericum ellipticum Hooker
Pale St. John's-wort [ ]
Hypericum gentianoides (L.) BSP.
Orange-grass [ ]
Hypericum kalmianum L.
Kalm St. John's-wort [ ]
Hypericum majus (A. Gray) Britt.
Canadian St. John's-wort [ ]
Hypericum mutilum L.
Dwarf St. John's-wort [y]
Hypericum perforatum L.*
Common St. John's-wort [y]
Hypericum punctatum Lam.
St. John's-wort [y]
Triadenum fraseri (Spach) Gleason
Marsh St. John's-wort [y]
Triadenum virginicum (L.) Raf.
Marsh St. John's-wort [y]
Malvaceae
Abutilon theophrasti Medik.*
Velvet-leaf [y]
Malva neglecta Wallr.*
Cheeses [y]
Tiliaceae
Tilia americana L. var. americana
Basswood [y]
Tilia americana L. var. heterophylla
(Vent.) Loud.
White basswood [ ]
Droseraceae
48
Drosera intermedia Hayne
Sundew [n]
Drosera rotundifolia L.
Round-leaf sundew [y]
Viola palmata L.
Early blue violet [ ]
Viola pedata L.
Bird's-foot violet [y]
Viola pubescens Ait.
Downy yellow violet [ ]
Viola rostrata Pursh
Long-spurred violet [y]
Viola rotundifolia Michx.
Round-leaf violet [ ]
Viola sagittata Ait.
Arrow-leaf violet [y]
Viola sagittata sororia
Violet [ ]
Viola selkirkii Pursh ex Goldie
Great spurred violet [ ]
Viola septentrionalis Greene
Northern blue violet [ ]
Viola sororia Willd.
Woolly blue violet [ ]
Viola tricolor L.*
Johnny jump-up [ ]
Sarraceniaceae
Sarracenia purpurea L.
Pitcher-plant [n]
Cucurbitaceae
Cucumis sativus L.*
Garden cucumber [ ]
Echinocystis lobata (Michx.) Torrey
& A. Gray
Wild cucumber [y]
Sicyos angulatus L.
Bur cucumber [y]
Cistaceae
Helianthemum bicknellii Fern.
Pine-barren frostweed [ ]
Helianthemum canadense (L.)
Michx.
Frostweed [y]
Lechea intermedia Leggett ex Britt.
Pinweed [ ]
Lechea mucronata Raf. ex Desv.
Pinweed [ ]
Salicaceae
Populus alba L.*
White poplar [y]
Populus balsamifera L.
Balsam poplar [y]
Populus deltoides Bartr. ex Marsh.
Cottonwood [y]
Populus grandidentata Mixhx.
Big-toothed aspen [y]
Populus nigra L.*
Lombardy poplar [ ]
Populus tremuloides Michx.
Quaking aspen [y]
Salix alba L.*
White willow [y]
Salix bebbiana Sarg.
Beaked willow [y]
Salix discolor Muhl.
Pussy-willow [y]
Salix eriocephala Michx.
Stiff willow [ ]
Salix exigua Nutt.
Sandbar willow [y]
Violaceae
Viola affinis LeConte
Leconte violet [ ]
Viola blanda Willd.
Sweet white violet [y]
Viola canadensis L.
Tall white violet [ ]
Viola conspersa Reichenb.
American dog-violet [y]
Viola cucullata Ait.
Blue marsh violet [y]
Viola lanceolata L.
Lance-leaf violet [y]
Viola macloskeyi Lloyd
ssp. pallens (Banks ex DC.)
M. Baker
Pale violet [y]
49
Cardamine diphylla (Michx.) Wood
Two-leaf toothwort [y]
Cardamine pensylvanica Muhl. ex
Willd.
Pennsylvania bittercress [y]
Coronopus didymus (L.) Sm.*
Wart-cress [ ]
Draba verna L.*
Whitlow-grass [ ]
Erucastrum gallicum (Willd.)
Schulz*
French rocket [ ]
Lepidium campestre (L.) R. Br. ex
Ait.*
Cow-cress [y]
Lepidium densiflorum Schrad.*
Bird's peppergrass [y]
Lepidium virginicum L.
Wild peppergrass [y]
Lobularia maritima (L.) Desv.*
Sweet alyssum [ ]
Raphanus raphanistrum L.*
Wild radish [y]
Rorippa nasturtium-aquaticum (L.)
Hayek*
Watercress [y]
Rorippa palustris (L.) Besser
ssp. fernaldiana (Butters &
Abbe) Jonsell*
Marsh watercress [n]
Rorippa sylvestris (L.) Besser*
Creeping yellow-cress [ ]
Sinapis arvensis L.*
Charlock [y]
Sisymbrium altissimum L.*
Tumble-mustard [y]
Sisymbrium officinale (L.) Scop.*
Hedge-mustard [ ]
Salix fragilis L.*
Crack-willow [ ]
Salix humilis Marsh. var. humilis
Prairie willow [y]
Salix humilis Marsh. var. tristis
(Ait.) Griggs
Dwarf upland willow, dune
willow [y]
Salix lucida Muhl.
Shining willow [y]
Salix nigra Marsh.
Black willow [y]
Salix pedicellaris Pursh
Bog willow [y]
Salix pentandra L.*
Bay-leaf willow [ ]
Salix petiolaris Sm.
Slender willow [y]
Salix petiolaris sericea
Willow [ ]
Salix purpurea L.*
Purple willow [ ]
Salix sericea Marsh.
Silky willow [y]
Brassicaceae
Alyssum alyssoides (L.) L.*
Alyssum [y]
Arabis glabra (L.) Bernh.
Tower-mustard [y]
Arabis laevigata (Muhl. ex Willd.)
Poir. ex Lam
Smooth rock-cress [y]
Arabis lyrata (L.)
Lyre-leaf rock-cress [ ]
Barbarea vulgaris R. Br. ex Ait.*
Cress [y]
Berteroa incana (L.) DC.*
Hoary alyssum [y]
Brassica nigra (L.) Koch*
Black mustard [y]
Capsella bursa-pastoris (L.) Medik.*
Shepherd's-purse [y]
Cardamine bulbosa (Schreb. ex
Muhl.) BSP.
Spring cress [y]
Capparidaceae
Polanisia dodecandra (L.) DC*
Clammyweed [y]
Ericaceae
Andromeda glaucophylla Link
Marsh rosemary [ ]
50
Chamaedaphne calyculata (L.)
Moench
Leatherleaf [y]
Chimaphila maculata (L.) Pursh
Spotted wintergreen [y]
Chimaphila umbellata (L.) Bart.
ssp. cisatlantica (Blake)
Hultn
Pipsissewa [y]
Epigaea repens L.
Trailing arbutus [y]
Gaultheria procumbens L.
Wintergreen [y]
Gaylussacia baccata (Wang.) Koch
Black huckleberry [y]
Kalmia angustifolia L.
Sheep laurel [y]
Kalmia polifolia Wang.
Bog laurel [n]
Lyonia ligustrina (L.) DC.
Maleberry [y]
Moneses uniflora (L.) A. Gray
One-flowered wintergreen [ ]
Monotropa uniflora L.
Indian-pipe [y]
Orthilia secunda (L.) House
One-sided wintergreen [ ]
Pterospora andromedea Nutt.
Pine-drops [ ]
Pyrola americana Sweet
Wild lily-of-the-valley [y]
Pyrola asarifolia Michx.
Pink wintergreen [ ]
Pyrola chlorantha Sw.
Green shinleaf [ ]
Pyrola elliptica Nutt.
Shinleaf [y]
Rhododendron groenlandicum
(Oeder) Kron & Judd
Labrador tea [n]
Rhododendron periclymenoides
(Michx.) Shinners
Pinkster-flower [y]
Rhododendron prinophyllum (Small)
Millais
Eearly azalea [y]
Rhododendron viscosum (L.) Torrey
Swamp azalea [y]
Vaccinium angustifolium Ait.
Lowbush blueberry [y]
Vaccinium corymbosum L.
Highbush blueberry [y]
Vaccinium macrocarpon Ait.
American cranberry [ ]
Vaccinium pallidum Ait.
Sugar huckleberry, low
blueberry [y]
Vaccinium stamineum L.
Deerberry [y]
Primulaceae
Lysimachia ciliata L.
Fringed loosestrife [y]
Lysimachia nummularia L.
Moneywort [y]
Lysimachia quadriflora Sims
Four-flowered loosestrife [y]
Lysimachia quadrifolia terrestris
Hybrid loosestrife [ ]
Lysimachia terrestris (L.) BSP.
Swamp-candles [y]
Lysimachia thyrsiflora L.
Tufted loosestrife [y]
Lysimachia vulgaris L.*
Garden loosestrife [ ]
Trientalis borealis Raf.
Starflower [y]
Rosaceae
Agrimonia gryposepala Wallr.
Common agrimony [y]
Agrimonia parviflora Soland ex Ait.
Agrimony [ ]
Agrimonia pubescens Wallr.
Agrimony [ ]
Agrimonia rostellata Wallr.
Agrimony [ ]
Agrimonia striata Michx.
Agrimony [ ]
Amelanchier arborea (Michx. f.)
Fern.
Shadbush [y]
51
Amelanchier arborea canadensis
Serviceberry [ ]
Amelanchier canadensis (L.) Medik.
Serviceberry [y]
Amelanchier humilis Wieg.
Bush juneberry [y]
Amelanchier laevis Wieg.
Smooth shadbush [y]
Amelanchier sanguinea (Pursh) DC.
Roundleaf juneberry [y]
Amelanchier stolonifera Wieg.
Bush juneberry [y]
Aronia arbutifolia (L.) Pers.
Red chokeberry [y]
Aronia melanocarpa (Michx.) Ell.
Black chokeberry [y]
A. X prunifolia. (A. arbutifolia X A.
melanocarpa) Chaenomeles japonica
(Thunb.) Lindl. ex Spach*
Lesser flowering quince [ ]
Crataegus brainerdii Sarg.
Hawthorn [ ]
Crataegus chrysocarpa Ashe
Round-leaf hawthorn [ ]
Crataegus coccinioides Ashe
Hawthorn [ ]
Crataegus crusgalli L.
Cockspur [y]
Crataegus holmesiana Ashe
Hawthorn [ ]
Crataegus intricata Lange
Hawthorn [ ]
Crataegus macrosperma Ashe
Big-fruited haw [y]
Crataegus monogyna Jacq.*
English hawthorn [ ]
Crataegus opulens Sarg.
Hawthorn [n]
Crataegus pedicellata Sarg.
Scarlet thorn [ ]
Crataegus pringlei Sarg.
Hawthorn [ ]
Crataegus pruinosa (Wendl. f.) Koch
Hawthorn [ ]
Crataegus punctata Jacq.
Dotted haw [ ]
Crataegus succulenta Schrad. ex
Link
Hawthorn [ ]
Fragaria chiloensis (L.) Mill.*
Coast strawberry [y]
Fragaria chiloensis virginiana*
Strawberry [ ]
Fragaria virginiana Dcne.
Field strawberry [y]
Geum aleppicum Jacq.
Yellow avens [y]
Geum canadense Jacq.
White avens [y]
Geum laciniatum Murr.
Rough avens [y]
Geum rivale L.
Purple avens [y]
Malus pumila Mill.*
Common apple [y]
Physocarpus opulifolius (L.) Maxim.
Ninebark [ ]
Potentilla anserina L.
Silverweed [ ]
Potentilla argentea L.*
Silvery cinquefoil [ ]
Potentilla canadensis L.
Dwarf cinquefoil [y]
Potentilla intermedia L.*
Cinquefoil [y]
Potentilla norvegica L.
ssp. monspeliensis (L.)
Azchers. & Grbn.
Rough cinquefoil [y]
Potentilla palustris (L.) Scop.
Marsh cinquefoil [ ]
Potentilla recta L.*
Sulfer cinquefoil [y]
Potentilla simplex Michx.
Common cinquefoil [y]
Prunus americana Marsh.
Hedge-plum [y]
Prunus pensylvanica L. f.
Pin-cherry [y]
Prunus persica (L.) Batsch*
Peach [ ]
52
Prunus pumila L. var. susquehanae
(Hort. ex Willd.) Jaeger
Sand cherry [y]
Prunus serotina Ehrh.
Black cherry [y]
Prunus virginiana L.
Choke-cherry [y]
Pyrus communis L.*
Pear [ ]
Rosa canina L.*
Dog rose [ ]
Rosa carolina L.
Pasture rose [y]
Rosa eglanteria L.*
Sweetbrier [ ]
Rosa palustris Marsh.
Swamp rose [y]
Rosa rugosa Thunb.*
Japanese rose [ ]
Rosa setigera Michx.
Prairie rose [ ]
Rosa virginiana Mill.
Wild rose [ ]
Rubus allegheniensis Porter ex
Bailey
Northern blackberry [y]
Rubus argutus Link
Tall blackberry [y]
Rubus arundelanus Blanch.
Sand blackberry [ ]
Rubus canadensis L.
Thornless blackberry [ ]
Rubus flagellaris Willd.
American dewberry [y]
Rubus hispidus L.
Swamp dewberry [y]
Rubus idaeus L.
Red raspberry [y]
Rubus idaeus L. ssp. strigosus
(Michx.) Focke
Wild raspberry [y]
Rubus occidentalis L.
Black raspberry [y]
Rubus odoratus L.
Pink thimbleberry [y]
Rubus pensilvanicus Poir. ex Lam.
Highbush blackberry [ ]
Rubus pubescens Raf.
Dwarf raspberry [y]
Rubus setosus Bigel.
Bog blackberry [ ]
Sorbaria sorbifolia (L.) A. Br.*
False spiraea [ ]
Sorbus aucuparia L.*
European mountain ash [y]
Spiraea alba
var. alba DuRoi
Meadow-sweet [y]
Spiraea alba DuRoi
var. latifolia (Ait.) Dippel
Meadow-sweet [y]
Spiraea douglasii salicifolia*
Spiraea [ ]
Spiraea tomentosa L.
Hardhack [y]
Waldsteinia fragarioides (Michx.)
Tratt.
Barren strawberry [ ]
Saxifragaceae
Chrysosplenium americanum
Schwein. ex Hooker
Golden saxifrage [y]
Mitella diphylla L.
Coolwort [y]
Parnassia glauca Raf.
Grass-of-Parnassus [n]
Saxifraga pensylvanica L.
Swamp saxifrage [n]
Tiarella cordifolia L.
Foamflower [y]
Crassulaceae
Penthorum sedoides L.
Ditch-stonecrop [y]
Sedum sarmentosum Bunge*
Orpine [ ]
Sedum spurium Bieb.*
Rosy stonecrop [ ]
Sedum telephium L.*
Live-forever [ ]
53
Grossulariaceae
Ribes americanum Mill.
Wild black currant [y]
Ribes cynosbati L.
Dogberry [y]
Ribes hirtellum Michx.
Northern gooseberry [ ]
Ribes rubrum L.*
Northern red currant [ ]
Ribes triste Pallas
Swamp red currant [y]
Trailing lespedeza [ ]
Lespedeza thunbergii (DC.) Nakai*
Lespedeza [ ]
Lotus corniculata L.*
Bird's-foot trefoil [y]
Lupinus perennis L.
Wild lupine [y]
Medicago lupulina L.*
Black medick [y]
Medicago sativa L.*
Alfalfa [ ]
Melilotus alba Desr. ex Lam.*
White sweet-clover [y]
Melilotus officinalis (L.) Pallas*
Yellow melilotus [y]
Robinia hispida L.*
Rose-acacia [y]
Robinia pseudo-acacia L.*
Black locust [y]
Robinia viscosa Vent. ex Vauq.*
Clammy locust [ ]
Senna hebecarpa (Fern.) Irwin &
Barneby
Wild senna [ ]
Strophostyles helvula (L.) Ell.
Annual woolly-bean [ ]
Tephrosia virginiana (L.) Pers.
Goat's-rue [y]
Trifolium arvense L.*
Rabbit's-foot clover [y]
Trifolium aureum Pollich*
Yellow clover [ ]
Trifolium campestre Schreb.*
Hop-clover [ ]
Trifolium dubium Sibth.*
Hop-clover [ ]
Trifolium hybridum L.*
Alsike clover [ ]
Trifolium incarnatum L.*
Scarlet clover [y]
Trifolium pratense L.*
Red clover [y]
Trifolium repens L.*
White clover [y]
Vicia cracca L.
Cow-vetch [y]
Fabaceae
Amorpha fruticosa L.*
False indigo [ ]
Amphicarpaea bracteata (L.) Rickett
& Stafleu [ ]
Hog-peanut [y]
Apios americana Medik.
Groundnut [y]
Baptisia tinctoria (L.) Vent.
Wild indigo [ ]
Coronilla varia L.*
Crown-vetch [y]
Desmodium canadense (L.) DC.
Giant tick-clover [y]
Desmodium canescens (L.) DC.
Hoary tick-clover [y]
Desmodium glutinosum (Muhl. ex
Willd.) Wood
Sticky tick-clover [y]
Desmodium nudiflorum (L.) DC.
Tick-trefoil [y]
Desmodium rotundifolium DC.
Tick-clover [ ]
Genista tinctoria L.*
Dyer's greenweed [ ]
Gleditsia triacanthos L.*
Honey locust [y]
Lathyrus latifolius L.*
Everlasting pea [ ]
Lespedeza capitata Michx.
Bush clover [y]
Lespedeza hirta (L.) Hornem.
Lespedeza [y]
Lespedeza procumbens Michx.
54
Vicia sativa L.*
Common vetch [y]
Vicia tetrasperma (L.) Schreb.*
Lentil-vetch [y]
Vicia villosa ssp. villosa Roth*
Hairy vetch [ ]
Wisteria sinensis (Sims) Sweet*
Chinese wisteria [y]
Sundrops [ ]
Lythraceae
Lythrum alatum Pursh
Winged loosestrife [n]
Lythrum salicaria L.*
Purple loosestrife [y]
Rotala ramosior (L.) Koehne ex
Mart.
Tooth-cup [n]
Haloragaceae
Proserpinaca palustris L. var. crebra
Fern. & Grisc.
Mermaid-weed [ ]
Thymeliaceae
Daphne mezereum L.*
Daphne [ ]
Dirca palustris L.
Leatherwood [y]
Onagraceae
Circaea alpina L.
Dwarf enchanter's nightshade [y]
Circaea lutetiana L. ssp. canadensis
(L.) Aschers. & Magnus
Enchanter's nightshade [y]
Epilobium angustifolium L.
Willow-herb [y]
Epilobium ciliatum Raf.
Willow-herb [y]
Epilobium coloratum Biehl.
Purple-leaf willow-herb [y]
Epilobium hirsutum L.*
European fireweed [ ]
Epilobium leptophyllum Raf.
Willow-herb [y]
Epilobium strictum Muhl. ex Spreng.
Downy willow-weed [ ]
Gaura biennis L.*
Gaura [ ]
Ludwigia alternifolia L.
Seedbox [y]
Ludwigia palustris (L.) Ell.
Water purslane [y]
Oenothera biennis L.
Common evening-primrose [y]
Oenothera clelandii Dietrich, Raven
& Wagner*
Evening primrose [ ]
Oenothera parviflora L.
Evening primrose [ ]
Oenothera perennis L.
Trapaceae
Trapa natans L.*
Water-chestnut [y]
Cornaceae
Cornus alternifolia L. f.
Green osier [y]
Cornus amomum
ssp. amomum Mill.
Silky dogwood [y]
Cornus canadensis L.
Bunchberry [y]
Cornus florida L.
Flowering dogwood [y]
Cornus foemina Mill. ssp. racemosa
(Lam.) J. Wilson
Gray dogwood [y]
Cornus rugosa Lam.
Round-leaf dogwood [y]
Cornus sericea L.
Red-osier [y]
Nyssaceae
Nyssa sylvatica Marsh.
Black gum [y]
Santalaceae
Comandra umbellata (L.) Nutt.
Bastard-toadflax [y]
55
Virginia creeper [y]
Vitis aestivalis Michx.
Summer grape [y]
Vitis riparia Michx.
Frost grape [y]
Vitis vulpina L.
Winter grape [ ]
Celastraceae
Celastrus orbiculata Thunb.*
Oriental bittersweet [y]
Celastrus scandens L.
American bittersweet [y]
Euonymus americana L.
Strawberry-bush [y]
Euonymus europaea L.*
European spindle-tree [y]
Linaceae
Linum sulcatum Ridd.
Yellow wild flax [ ]
Aquifoliaceae
Ilex laevigata (Pursh) A. Gray
Smooth winterberry [ ]
Ilex verticillata (L.) A. Gray
Winterberry [y]
Nemopanthus mucronatus (L.)
Loesener ex Koehne
Mountain holly [y]
Rhamnaceae
Ceanothus americanus L.
New Jersey tea [y]
Rhamnus alnifolia L'Her.
Alder-leaf buckthorn [n]
Rhamnus cathartica L.*
Common buckthorn [y]
Rhamnus frangula L.*
Smooth buckthorn [y]
Euphorbiaceae
Acalypha virginica L. var.
rhomboidea (Raf.) Cooperrider
Three-seeded mercury [y]
Chamaesyce glyptosperma
(Engelm.) Small
Spurge [y]
Chamaesyce maculata (L.) Small
Eyebane [y]
Chamaesyce nutans (Lag.) Small
Eyebane [ ]
Euphorbia corollata L.
Flowering spurge [y]
Euphorbia cyparissias L.*
Cypress spurge [y]
Euphorbia esula L.*
Wolf's-milk [ ]
Euphorbia marginata Pursh*
Snow-on-the-mountain [y]
Polygalaceae
Polygala paucifolia Willd.
Fringed milkwort [y]
Polygala polygama Walt.
Bitter milkwort [ ]
Polygala sanguinea L.
Rose milkwort [y]
Polygala senega L.
Seneca snakeroot [ ]
Polygala verticillata L.
Whorled milkwort [ ]
Polygala verticillata L. var. isocycla
Fern.
Whorled milkwort [ ]
Aceraceae
Acer campestre L.*
Hedge-maple [ ]
Acer negundo L.
Box-elder [y]
Acer nigrum Michx. f.
Black maple [ ]
Acer pensylvanicum L.
Striped maple [y]
Vitaceae
Parthenocissus quinquefolia (L.)
Planch. ex DC.
Virginia creeper [y]
Parthenocissus vitacea (L.) Planch.
ex DC.
56
Acer rubrum var. rubrum L.
Red maple [y]
Acer saccharum Marsh.
Sugar maple [ ]
Impatiens pallida Nutt.
Pale jewelweed [y]
Oxalidaceae
Oxalis corniculata L.*
Lady's-sorrel [y]
Oxalis stricta L.
Lady's-sorrel [y]
Hippocastanaceae
Aesculus hippocastanum L.*
Horse-chestnut [ ]
Simaroubaceae
Ailanthus altissima (Mill.) Swingle*
Tree-of-heaven [y]
Apiaceae
Angelica atropurpurea L.
Alexanders [y]
Cicuta bulbifera L.
Water-hemlock [y]
Cicuta maculata L.
Poison hemlock [y]
Cryptotaenia canadensis (L.) DC.
Honewort [y]
Daucus carota L.*
Queen-Anne's-lace [y]
Hydrocotyle americana L.
Pennywort [y]
Osmorhiza claytonii (Michx.) Clarke
Sweet jarvil [ ]
Pastinaca sativa L.*
Wild parsnip [y]
Pimpinella major (L.) Huds.*
Pimpinella [ ]
Sanicula marilandica L.
Black snakeroot [y]
Sanicula odorata (Raf.) Pryer &
Phillippe
Sanicle [ ]
Sanicula trifoliata Bickn.
Sanicle [ ]
Sium suave Walt.
Water-parsnip [y]
Zizia aptera (A. Gray) Fern.
Golden Alexanders [ ]
Zizia aurea (L.) Koch
Golden Alexanders [y]
Anacardiaceae
Cotinus coggygria Scop.*
Smoke-tree [ ]
Rhus copallinum L.
Winged sumac [y]
Rhus glabra L.
Smooth sumac [y]
Rhus hirta (L.) Sudworth
Staghorn sumac [y]
Toxicodendron radicans (L.) Kuntze
Poison ivy [y]
Toxicodendron vernix (L.) Kuntze
Poison sumac [y]
Rutaceae
Dictamnus albus L.*
Gas-plant [ ]
Zanthoxylum americanum Mill.
Prickly ash [y]
Staphyleaceae
Staphylea trifolia L.
Bladdernut [y]
Geraniaceae
Geranium bicknellii Britt.
Geranium [ ]
Geranium maculatum L.
Wild geranium [y]
Araliaceae
Aralia nudicaulis L.
Wild sarsaparilla [y]
Aralia racemosa L.
Balsaminaceae
Impatiens capensis Meerb.
Spotted touch-me-not [y]
57
Spikenard [ ]
Panax quinquefolius L.
Ginseng [ ]
Panax trifolius L.
Dwarf ginseng [ ]
Fringed gentian [y]
Solanaceae
Datura stramonium L.
Jimson weed [y]
Petunia axillaris (Lam.) BSP.*
Garden petunia [ ]
Physalis heterophylla Nees
Clammy ground-cherry [y]
Physalis longifolia Nutt.
Long-leaf ground-cherry [ ]
Physalis virginiana Mill.
Virginia ground-cherry [ ]
Solanum carolinense L.
Horse-nettle [y]
Solanum dulcamara L.*
Trailing nightshade [y]
Solanum ptycanthum Dunal.*
Black nightshade [y]
Apocynaceae
Apocynum androsaemifolium L.
Spreading dogbane [y]
Apocynum androsaemifolium
cannabinum
Dogbane [ ]
Apocynum cannabinum L. var.
cannabinum
Indian hemp [y]
Apocynum cannabinum L.
var. hypericifolium A. Gray
Indian hemp [ ]
Asclepiadaceae
Asclepias amplexicaulis Sm.
Blunt-leaf milkweed [y]
Asclepias exaltata L.
Poke milkweed [y]
Asclepias incarnata L. var. pulchra
(Ehrh. ex Willd.) Pers.
Swamp milkweed [y]
Asclepias quadrifolia Jacq.
Four-leaf milkweed [ ]
Asclepias syriaca L.
Common milkweed [y]
Asclepias tuberosa L.
var. interior (Woodson)
Shinners
Butterfly-weed [y]
Convolvulaceae
Calystegia sepium (L.) R Br.
Hedge-bindweed [y]
Calystegia spithamea (L.) Pursh
Low bindweed [y]
Convolvulus arvensis L.*
Field bindweed [ ]
Ipomoea purpurea (L.) Roth*
Common morning-glory [y]
Polemoniaceae
Phlox divaricata L.
Blue phlox [y]
Phlox paniculata L.
Fall phlox [y]
Cuscutaceae
Cuscuta gronovii Willd. ex Schultz
Dodder [y]
Gentianaceae
Bartonia virginica (L.) BSP.
Bartonia [y]
Gentiana clausa Raf.
Blind gentian [ ]
Gentiana saponaria L.
Soapwort gentian [ ]
Gentianella quinquefolia (L.) Small
Stiff gentian [ ]
Gentianopsis crinita (Froel.) Ma
Hydrophyllaceae
Hydrophyllum virginianum L.
Virginia waterleaf [ ]
Menyanthaceae
58
Menyanthes trifoliata L. var. minor
Raf.
Buckbean [ ]
Dotted horsemint [ ]
Nepeta cataria L.*
Catnip [y]
Origanum vulgare L.*
Marjoram [ ]
Physostegia virginiana (L.) Benth.
False dragon head [ ]
Prunella vulgaris L.*
Self-heal [y]
Pycnanthemum tenuifolium Schrad.
Mountain-mint [ ]
Pycnanthemum virginianum (L.)
Durieu & Jacks. ex Fern. & B.
Robinson
Mountain-mint [y]
Scutellaria galericulata L.
Common skullcap [y]
Scutellaria lateriflora L.
Mad-dog skullcap [y]
Stachys hyssopifolia Michx.
Hedge-nettle [n]
Stachys palustris L.*
Woundwort [ ]
Trichostema dichotomum L.
Blue-curls [y]
Lamiaceae
Ajuga reptans L.*
Carpet-bugleweed [ ]
Clinopodium vulgare L.*
Basil [ ]
Collinsonia canadensis L.
Richweed [y]
Galeopsis tetrahit L. var. bifida
(Boenn) Lej. & Court.*
Hemp-nettle [y]
Glechoma hederacea L.*
Ground-ivy [y]
Hedeoma pulegioides (L.) Pers.
Mock-pennyroyal [ ]
Leonurus cardiaca L.*
Motherwort [y]
Lycopus americanus Muhl. ex Bart.
Water-horehound [y]
Lycopus europaeus L.*
European water-horehound[ ]
Lycopus uniflorus Michx.
Water-horehound [y]
Lycopus virginicus L.
Water-horehound [n]
Melissa officinalis L.*
Balm [ ]
Mentha aquatica L.*
Peppermint [ ]
Mentha arvensis L.*
Field mint [ ]
Mentha canadensis L.
Field mint [ ]
Mentha spicata L.*
Spearmint [ ]
Moluccella laevis L.*
Mollucca-balm [n]
Monarda fistulosa L.
Wild bergamont [y]
Monarda punctata L.
Dotted horsemint [y]
Monarda punctata L. var. villicaulis
(Pennell) Shinners
Boraginaceae
Anchusa officinalis L.*
Alkanet [ ]
Cynoglossum officinale L.*
Hound's-tongue [y]
Echium vulgare L.*
Blue-devil [y]
Hackelia virginiana (L.) Johnst.
Stickseed [y]
Lithospermum officinale L.*
European gromwell [y]
Myosotis arvensis (L.) Hill*
Forget-me-not [ ]
Myosotis laxa Lehm.
Wild forget-me-not [y]
Myosotis scorpioides L.*
Forget-me-not [y]
Onosmodium molle Michx. ssp.
hispidissimum (Mackz.) Boivin
Marble-seed [ ]
59
Onosmodium virginianum (L.) A.
DC.
False gromwell [ ]
Pedicularis canadensis L.
Lousewort [ ]
Penstemon hirsutus (L.) Willd.
Penstemon [y]
Schwalbea americana L.
Chaffseed [n]
Scrophularia lanceolata Pursh
Hare-figwort [ ]
Verbascum blattaria L.*
Moth-mullein [y]
Verbascum thapsus L.*
Mullein [y]
Veronica americana (Raf.) Schwein.
ex Benth.
American speedwell [y]
Veronica anagallis-aquatica L.
Water speedwell [ ]
Veronica beccabunga L.*
Brooklime [ ]
Veronica chamaedrys L.*
Bird's-eye speedwell [ ]
Veronica longifolia L.*
Speedwell [ ]
Veronica officinalis L.*
Speedwell [y]
Veronica peregrina L.
Neckweed [ ]
Veronica scutellata L.
Marsh speedwell [y]
Veronica serpyllifolia L.
ssp. serpyllifolia*
Thyme-leaf speedwell [ ]
Verbenaceae
Verbena hastata L.
Blue vervain [y]
Verbena urticifolia L.
White vervain [y]
Plantaginaceae
Plantago lanceolata L.*
Buck-horn plantain [y]
Plantago major L.*
Common plantain [y]
Plantago patagonica Jacq.*
Plantain [n]
Plantago psyllium L.*
Whorled plantain [ ]
Plantago rugelii Dcne.
Pale plantain [y]
Scrophulariaceae
Agalinis tenuifolia (Vahl) Raf. var.
tenuifolia
Gerardia [y]
Aureolaria flava (L.) Farw. var. flava
Yellow false-foxglove [ ]
Chaenorrhinum minus (L.) Lange*
Dwarf snapdragon [ ]
Chelone glabra L.
Turtle-heads [y]
Gratiola aurea Muhl.
Golden-pert [n]
Gratiola neglecta Torrey
Mud-hyssop [n]
Linaria canadensis (L.) Dumort.
Old-field toadflax [ ]
Linaria vulgaris Mill.*
Butter-and-eggs [y]
Lindernia dubia (L.) Pennell
False-pimpernel [ ]
Melampyrum lineare Desr.
Cow-wheat [y]
Mimulus ringens L.
Common monkeyflower [y]
Bignoniaceae
Catalpa speciosa (Warder ex Barney)
Engelm.*
Catalpa [y]
Oleaceae
Fraxinus americana L.
White ash [y]
Fraxinus nigra Marsh.
Black ash [ ]
Fraxinus pennsylvanica Marsh.
Green ash [y]
60
Ligustrum obtusifolium Sieb. &
Zucc.*
Privet [ ]
Syringa vulgaris L.*
Lilac [y]
Wild-licorice [y]
Galium palustre L.
Ditch bedstraw [y]
Galium tinctorium (L.) Scop.
Bedstraw [y]
Galium trifidum L.*
Bedstraw [y]
Galium triflorum Michx.
Sweet-scented bedstraw [y]
Mitchella repens L.
Partridge-berry [y]
Orobanchaceae
Epifagus virginiana (L.) Bartr.
Beech-drops [y]
Orobanche uniflora L.
One-flowered cancer-root [ ]
Lentibulariaceae
Utricularia gibba L.
Cone-spur bladderwort [n]
Utricularia macrorhiza LeConte
Common bladderwort [ ]
Caprifoliaceae
Diervilla lonicera Mill.
Bush honeysuckle [y]
Linnaea borealis L. ssp. longiflora
(Torrey) Hulten
Twinflower [y]
Lonicera canadensis Bartr.
Fly honeysuckle [y]
Lonicera dioica L. var. dioica
Wild honeysuckle [ ]
Lonicera japonica Thunb.*
Japanese honeysuckle [y]
Lonicera morrowii A. Gray*
Fly honeysuckle [y]
Lonicera morrowii tatarica*
Fly honeysuckle [y]
Lonicera sempervirens L.
Trumpet honeysuckle [y]
Lonicera tatarica L.*
Tartarian honeysuckle [y]
Lonicera xylosteum L.*
Fly honeysuckle [ ]
Sambucus canadensis L.
Black elderberry [y]
Sambucus racemosa L. ssp. pubens
(Michx.) House
Red elderberry [y]
Symphoricarpos albus (L.) Blake
var. laevigatus (Fern.) Blake
Snowberry [ ]
Symphoricarpos orbiculatus
Moench*
Coralberry [y]
Triosteum perfoliatum L.
Campanulaceae
Campanula rapunculoides L.*
Creeping bellflower [ ]
Campanula rotundifolia L.
Harebell [y]
Lobelia cardinalis L.
Cardinal-flower [n]
Lobelia dortmanna L.
Water lobelia [ ]
Lobelia inflata L.
Indian-tobacco [y]
Lobelia siphilitica L.
Great lobelia [y]
Lobelia spicata Lam.
Pale-spiked lobelia [ ]
Triodanis perfoliata (L.) Nieuwl.*
Venus' looking-glass [y]
Rubiaceae
Cephalanthus occidentalis L.
Buttonbush [y]
Galium aparine L.
Bedstraw [y]
Galium asprellum Michx.
Rough bedstraw [y]
Galium boreale L.
Northern bedstraw [y]
Galium circaezans Michx.
61
Tinker's-weed [ ]
Viburnum acerifolium L.
Maple-leaf viburnum [y]
Viburnum dentatum L.
Southern arrowwood [y]
Viburnum dentatum L. var. lucidum
Ait.
Southern arrowwood [y]
Viburnum lantanoides Michx.
Hobblebush [y]
Viburnum lentago L.
Sheepberry [y]
Viburnum nudum L. var. nudum
Possom-haw [n]
Viburnum nudum L. var. cassinoides
(L.) Torrey & A. Gray
Wild raisin [y]
Viburnum opulus L. var. opulus*
Guelder-rose [ ]
Viburnum opulus L. var.
americanum Ait.
Highbush cranberry [y]
Viburnum rafanesquianum Schultes
Downy arrowwood [ ]
Anaphalis margaritacea (L.) Benth.
& Hooker f. ex Cla
Pearly-everlasting [y]
Antennaria neglecta Greene ssp.
neglecta
Everlasting [y]
Antennaria neglecta Greene ssp.
neodioica (Greene) Bayer
Smaller cat's-foot [ ]
Antennaria plantaginifolia (L.)
Richards.
Everlasting [y]
Anthemis cotula L.*
Mayweed [ ]
Arctium minus (Hill) Bernh.*
Common burdock [y]
Artemisia absinthium L.*
Absinthe [ ]
Artemisia biennis Willd.*
Sage-weed [ ]
Aster acuminatus Michx.
Mountain aster [ ]
Aster cordifolius L.
Blue aster [y]
Aster divaricatus L.
White aster [y]
Aster ericoides L.
White wreath aster [y]
Aster infirmus Michx.
Cornel-leaved aster [y]
Aster laevis L.
Smooth blue aster [y]
Aster lanceolatus Willd.
var. simplex (Willd.) A.
Jones
Old-field aster [ ]
Aster lateriflorus (L.) Britt.
Calico aster [y]
Aster linariifolius L.
Stiff-leaf aster [y]
Aster macrophyllus L.
Bigleaf aster [ ]
Aster novae-angliae L.
New England aster [y]
Aster novi-belgii L. var. novi-belgii
New York aster [ ]
Valerianaceae
Valeriana officinalis L.*
Common valerian [ ]
Valerianella umbilicata (Sulliv.)
Wood
Beaked corn-salad [ ]
Dipsacaceae
Dipsacus fullonum L.*
Teasel [y]
Asteraceae
Achillea millefolium L. var.
millefolium
Common yarrow [y]
Ambrosia artemisiifolia L.
Ragweed [y]
Ambrosia psilostachya DC*
Western ragweed [y]
Ambrosia trifida L.
Giant ragweed [y]
62
Cirsium discolor (Muhl. ex Willd.)
Spreng.
Field-thistle [ ]
Cirsium muticum Michx.
Swamp-thistle [y]
Cirsium pumilum (Nutt.) Spreng.
Bull-thistle [ ]
Cirsium vulgare (Savi) Tenore*
Bull-thistle [y]
Conyza canadensis (L.) Cronq. var.
canadensis
Horseweed [y]
Coreopsis grandiflora Hogg ex
Sweet*
Coreopsis [ ]
Coreopsis lanceolata L.*
Coreopsis [y]
Cosmos bipinnatus Cav.*
Cosmos [ ]
Crepis biennis L.*
Hawk's-beard [ ]
Crepis tectorum L.*
Hawk's-beard [y]
Erechtites hieracifolia (L.) Raf. ex
DC. var. hieracifolia
Fireweed [y]
Erigeron annuus (L.) Pers.
Daisy-fleabane [y]
Erigeron philadelphicus L.
Fleabane [y]
Erigeron pulchellus Michx.
Robin's-plantain [ ]
Erigeron strigosus Muhl. ex Willd.
Daisy-fleabane [y]
Eupatorium coelestinum L.*
Mistflower [ ]
Eupatorium dubium Willd.
Joe-pye-weed [y]
Eupatorium fistulosum Barratt
Joe-pye-weed [y]
Eupatorium maculatum L.
Spotted Joe-pye-weed [y]
Eupatorium perfoliatum L.
Thoroughwort [y]
Eupatorium purpureum L.
Sweet Joe-pye-weed [ ]
Aster novi-belgii var. tardiflorus (L.)
A. Jones
Late-flowering New York aster [ ]
Aster patens Ait.
Late purple aster [y]
Aster paternus Cronq.
White-topped aster [y]
Aster pilosus Willd.
Heath aster [ ]
Aster praealtus Poir.
Willow aster [ ]
Aster prenanthoides Muhl. ex Willd.
Zig-zag aster [y]
Aster puniceus L.
Purple-stemmed aster [y]
Aster schreberi Nees
Large-leaf aster [ ]
Aster umbellatus Mill.
Flat-top white aster [y]
Aster undulatus L.
Wavy-leaf aster [y]
Bidens cernua L.
Stick-tights [y]
Bidens connata Muhl. ex Willd
Beggar-ticks [ ]
Bidens frondosa L.
Beggar-ticks [y]
Bidens tripartita L.*
Beggar-ticks [y]
Bidens vulgata Greene
Beggar-ticks [y]
Calendula officinalis L.*
Pot-marigold [ ]
Centaurea cyanus L.*
Bluebottle [ ]
Centaurea jacea L.*
Brown knapweed [ ]
Centaurea maculosa Lam.*
Bushy knapweed [y]
Centaurea paniculata L.*
Knapweed [ ]
Cichorium intybus L.*
Chicory [y]
Cirsium arvense (L.) Scop.*
Canada thistle [y]
63
Hieracium lachenalii Gmel.*
Hawkweed [ ]
Hieracium paniculatum L.
Hawkweed [y]
Hieracium pilosella L.*
Mouse-ear hawkweed [ ]
Hieracium piloselloides Vill.*
King-devil [ ]
Hieracium scabrum Michx.
Hawkweed [ ]
Hieracium venosum L.
Rattlesnake-weed [y]
Inula helenium L.*
Elecampane [ ]
Krigia virginica (L.) Willd.
Dwarf dandelion [y]
Lactuca biennis (Moench) Fern.
Wild lettuce [y]
Lactuca canadensis L.
Wild lettuce [y]
Lactuca serriola L.*
Prickly lettuce [y]
Leucanthemum vulgare Lam.*
Ox-eye daisy [y]
Liatris scariosa (L.) Willd. var.
novae-angliae Lunell
New England blazing-star [ ]
Matricaria discoidea DC.*
Pinapple-weed [y]
Petasites frigidus (L.) Fries var.
palmatus (Ait.) Cronq.
Sweet coltsfoot [ ]
Prenanthes alba L.
White lettuce [ ]
Prenanthes altissima L.
Rattlesnake-root [ ]
Prenanthes serpentaria Pursh
Lion's-foot [y]
Prenanthes trifoliolata (Cass.) Fern.
Gall-of-the-earth [y]
Ratibida columnifera (Nutt.) Wooton
& Standl.*
Prairie coneflower [n]
Rudbeckia hirta L. var. pulcherrima
Farw.*
Black-eyed-Susan [y]
Eupatorium rugosum Houtt.
White snakeroot [y]
Eupatorium sessilifolium L.
Upland boneset [ ]
Euthamia graminifolia (L.) Nutt. ex
Cass.
Bush goldenrod [y]
Gaillardia aristata pulchella*
Blanket-flower [ ]
Galinsoga quadriradiata Ruiz &
Pav.*
Quickweed [ ]
Gnaphalium obtusifolium L.
Catfoot [ ]
Gnaphalium uliginosum L.*
Low cudweed [y]
Grindelia squarrosa (Pursh) Dunal*
Gumweed [ ]
Helenium autumnale L.
var. autumnale
Sneezeweed [y]
Helenium flexuosum Raf.*
Sneezeweed [ ]
Helianthus annuus L.*
Common sunflower [y]
Helianthus decapetalus L.
Thin-leaf sunflower [ ]
Helianthus divaricatus L.
Woodland sunflower [y]
Helianthus mollis Lam.*
Ashy sunflower [ ]
Helianthus petiolaris Nutt.*
Sunflower [ ]
Helianthus strumosus L.
Wood-sunflower [y]
Helianthus tuberosus L.*
Jerusalem artichoke [y]
Heliopsis helianthoides (L.) Sweet
Ox-eye [ ]
Hieracium aurantiacum L.*
Orange hawkweed [y]
Hieracium caespitosum Dumort.*
King-devil [y]
Hieracium floribundum Wimm. &
Grab.
Smoothish hawkweed [ ]
64
Rudbeckia laciniata L.
Cut-leaf coneflower [y]
Senecio aureus L.
Golden ragwort [y]
Senecio obovatus Muhl. ex Willd.
Ragwort [ ]
Solidago arguta Ait.
Cutleaf goldenrod [y]
Solidago bicolor L.
White goldenrod [y]
Solidago caesia L.
Wreath goldenrod [y]
Solidago canadensis L. var.
canadensis
Canada goldenrod [y]
Solidago canadensis L. var. scabra
(Muhl.) Torrey & A. Gray
Tall goldenrod [ ]
Solidago flexicaulis L.
Zig-zag goldenrod [y]
Solidago gigantea Ait.
Late goldenrod [y]
Solidago hispida Muhl. ex Willd.
Goldenrod [y]
Solidago juncea Ait.
Early goldenrod [y]
Solidago nemoralis Ait.
Rough goldenrod [y]
Solidago patula Muhl. ex Willd.
Spreading goldenrod [y]
Solidago puberula Nutt.
Downy goldenrod [ ]
Solidago rugosa Mill.
ssp. rugosa
Tall-hairy goldenrod [y]
Sonchus arvensis L.*
Sow-thistle [ ]
Sonchus asper (L.) Hill*
Spiny sow-thistle [y]
Sonchus oleraceus L.*
Sow-thistle [y]
Tanacetum vulgare L.*
Tansy [y]
Taraxacum officinale Weber ex
Wiggers*
Common dandelion [y]
Tragopogon dubius Scop.*
Goat's-beard [y]
Tragopogon pratensis L.*
Yellow goat's-beard [y]
Tussilago farfara L.*
Coltsfoot [y]
Xanthium strumarium L.
Cocklebur [ ]
Alismataceae
Alisma subcordatum Raf.
Water-plantain [ ]
Alisma triviale Pursh
Water-plantain [ ]
Sagittaria cuneata Sheldon
Wapato [y]
Sagittaria latifolia Willd.
Wapato [y]
Sagittaria rigida Pursh
Arrowhead [ ]
Hydrocharitaceae
Elodea canadensis L. Rich. ex
Michx.
Waterweed [y]
Najadaceae
Najas flexilis (Willd.) Rostk. &
Schmidt
Naiad [n]
Najas gracillima (A. Br. ex Engelm.)
Magnus
Naiad [n]
Najas minor All.*
Naiad [ ]
Potamogetonaceae
Potamogeton crispus L.*
Pondweed [y]
Potamogeton epihydrus Raf.
Pondweed [ ]
Potamogeton foliosus Raf.
Pondweed [y]
Potamogeton natans L.
Pondweed [y]
Potamogeton nodosus Poir.
65
Pondweed [y]
Potamogeton pectinatus L.
sago pondweed [ ]
Potamogeton perfoliatus L.
Pondweed [ ]
Potamogeton pusillus L.
Pondweed [ ]
Tradescantia virginiana L.*
Spiderwort [y]
Xyridaceae
Xyris torta Sm.
Slender yellow-eyed grass [n]
Juncaceae
Juncus acuminatus Michx.
Sharp-fruited rush [y]
Juncus articulatus L.
Jointed rush [ ]
Juncus brevicaudatus (Engelm.)
Fern.
Narrow-panicled rush [y]
Juncus bufonius L.
Toad-rush [y]
Juncus canadensis Gay ex LaHarpe
Canada rush [y]
Juncus dichotomus Ell. var.
platyphyllus Wieg.
Forked rush [y]
Juncus dudleyi Wieg.
Dudley's rush [ ]
Juncus effusus L.
Common rush [y]
Juncus greenei Oakes & Tuckerm.
Greene's rush [ ]
Juncus marginatus Rostk.
Grass-leaf rush [y]
Juncus nodosus L.
Knotted rush [n]
Juncus tenuis Willd.
Slender yard-rush [y]
Juncus torreyi Cov.
Torrey's rush [y]
Luzula campestris (L.) DC. in Lam.
& DC. var. multiflora (Retz.) Lej.
Wood-rush [y]
Luzula campestris (L.) DC. in Lam.
& DC. var. pallescens (Wahl.) Wahl.
Common wood-rush [y]
Zannichelliaceae
Zannichellia palustris L.
Horned pondweed [n]
Araceae
Acorus americanus (Raf.) Raf.
Sweetflag [ ]
Arisaema triphyllum (L.) Schott ex
Schott & Endl. ssp. stewardsonii
(Britt.) Huttleston
Jack-in-the-pulpit [y]
Peltandra virginica (L.) Schott ex
Schott & Endl.
Arrowleaf [ ]
Symplocarpus foetidus (L.) Salisb.
ex Nutt.
Skunk-cabbage [y]
Lemnaceae
Lemna minor L.
Duckweed [y]
Lemna trisulca L.
Star duckweed [ ]
Spirodela polyrhiza (L.) Schleid.
Giant duckweed [y]
Wolffia borealis (Engelm.) Landolt
Watermeal [y]
Wolffia columbiana Karst.
Watermeal [y]
Commelinaceae
Commelina communis L.*
Dayflower [ ]
Tradescantia occidentalis (Britt.)
Smyth*
Spiderwort [n]
Tradescantia ohiensis Raf.
Spiderwort [y]
Poaceae
Agrostis capillaris L.*
Colonial bent [y]
66
Agrostis gigantea Roth*
Redtop [y]
Agrostis hyemalis (Walt.) BSP.
Southern hairgrass [y]
Agrostis perennans (Walt.) Tuckerm.
Autumn bent [y]
Agrostis scabra Willd.
Hairgrass [y]
Agrostis stolonifera L. var. palustris
(Huds.) Farw.
Creeping bent [y]
Agrostis stolonifera L. var.
stolonifera
Creeping bent [ ]
Alopecurus aequalis Sobol.
Short-awn foxtail [y]
Andropogon gerardii Vitman
Big bluestem [y]
Anthoxanthum odoratum L.*
Sweet vernalgrass [ ]
Aristida dichotoma Michx.
Poverty-grass [ ]
Aristida oligantha Michx.*
Prairie three-awn [y]
Avena fatua L. ssp. sativa (L.)
Thell.*
Oats [ ]
Brachyelytrum erectum (Schreb. ex
Spreng.) Beauv.
Bearded-shorthusk [ ]
Bromus arvensis L.*
Field chess [ ]
Bromus ciliatus L.
Fringed brome [ ]
Bromus commutatus Schrad.*
Hairy chess [ ]
Bromus inermis Leyss.*
Smooth brome [y]
Bromus japonicus Thunb. ex Murr.*
Japanese chess [y]
Bromus kalmii A. Gray
Brome [ ]
Bromus pubescens Muhl. ex Willd.*
Canada brome [y]
Bromus secalinus L.*
Cheat [ ]
Bromus tectorum L.*
Downy chess [y]
Calamagrostis canadensis (Michx.)
Beauv. var. canadensis
Bluejoint grass [y]
Calamagrostis stricta (Timm) Koeler
ssp. inexpansa (A. Gray) C. Greene
var. lacustris (Kearn.) C. Greene
Northern reed-grass [ ]
Cenchrus longispinus (Hack.) Fern.
Field sandbur [y]
Cinna arundinacea L.
Stout woodreed [y]
Cinna latifolia (Trev. ex Goepp.)
Griseb.
Drooping woodreed [ ]
Dactylis glomerata L.*
Orchard grass [y]
Danthonia spicata (L.) Beauv. ex R.
& S.
Poverty-grass [ ]
Deschampsia cespitosa L. Beauv.
Tufted hairgrass [ ]
Deschampsia flexuosa (L.) Trin.
Common hairgrass [y]
Digitaria cognatum (Schultes) Pilger
Fall witchgrass [ ]
Digitaria filiformis (L.) Koeler
Slender crabgrass [ ]
Digitaria ischaemum (Schreb. ex
Schweig.) Schreb. ex Muhl.
Smooth crabgrass [y]
Digitaria sanguinalis (L.) Scop.*
Tall crabgrass [y]
Echinochloa crusgalli (L.) Beauv.
ssp. crusgalli*
Barnyard grass [y]
Echinochloa crusgalli (L.) Beauv.
ssp. edulis Hitchc.*
Japanese millet [ ]
Echinochloa muricata (Beauv.) Fern.
Cockspur grass [n]
Echinochloa muricata var. muricata
(Beauv.) Fern.
Cockspur grass [ ]
Echinochloa walteri (Pursh) Heller
67
Water-millet [y]
Elymus canadensis L.
Canada wild-rye [y]
Elymus hystrix L.
Bottlebrush [y]
Elymus riparius Wieg.
Marsh wild-rye [y]
Elymus villosus Muhl. ex Willd.
Wild-rye [ ]
Elymus virginicus L. var. virginicus
Virginia wild-rye [y]
Elytrigia repens (L.) Nevski*
Quackgrass [ ]
Eragrostis capillaris (L.) Nees
Lacegrass [ ]
Eragrostis cilianensis (All.) Mosher*
Stinkgrass [y]
Eragrostis hypnoides (Lam.) BSP.
Lovegrass [ ]
Eragrostis minor Host*
Lovegrass [ ]
Eragrostis pectinacea (Michx.) Nees
Lovegrass [y]
Eragrostis spectabilis (Pursh) Steud.
Purple lovegrass [y]
Festuca elatior L.*
Tall fescue [y]
Festuca heterophylla Lam.*
Fescue [ ]
Festuca ovina L.*
Sheep fescue [y]
Festuca rubra L. ssp. falax Thuill.*
Chewing's fescue [ ]
Festuca rubra L. ssp. rubra*
Red fescue [ ]
Festuca subverticillata (Pers.)
Alexe'ev
Nodding fescue [ ]
Festuca trachyphylla (Hackel)
Krajina*
Sheep fescue [ ]
Glyceria acutiflora Torrey
Mannagrass [y]
Glyceria borealis (Nash) Batchelder
Northern mannagrass [n]
Glyceria canadensis (Michx.) Trin.
Rattlesnake grass [y]
Glyceria grandis S. Wats.
Reed meadowgrass [y]
Glyceria melicaria (Michx.) Hubb.
Slender mannagrass [y]
Glyceria melicaria striata
Mannagrass [ ]
Glyceria striata (Laml) Hitchc.
Fowl mannagrass [y]
Hordeum pusillum Nutt.
Little barley [y]
Leersia oryzoides (L.) Sw.
Rice cutgrass [y]
Leersia virginica Willd.
Whitegrass [ ]
Lolium perenne L.*
English ryegrass [y]
Lolium perenne L.
var. aristatum Willd.
Italian rye grass [ ]
Muhlenbergia frondosa (Poir.) Fern.
Wirestem muhly [y]
Muhlenbergia glomerata (Willd.)
Trin.
Spike muhly [ ]
Muhlenbergia mexicana (L.) Trin.
Satin-grass [y]
Muhlenbergia schreberi Gmel.
Nimble-will [ ]
Muhlenbergia sylvatica (Torrey)
Torrey ex A. Gray
Woodland drop-seed [ ]
Muhlenbergia tenuiflora (Willd.)
BSP.
Woodland drop-seed [ ]
Oryzopsis asperifolia Michx.
Spreading ricegrass [y]
Oryzopsis pungens (Torrey ex
Spreng.) Hitchc.
Ricegrass [ ]
Panicum acuminatum Sw.
Panic grass [y]
Panicum capillare L.
Witchgrass [y]
Panicum clandestinum L.
Deer-tongue [y]
68
Panicum depauperatum Muhl.
Poverty panic grass [y]
Panicum dichotomiflorum Michx.
Smooth panic grass [ ]
Panicum dichotomiflorum Michx.
var. dichotomiflorum
Smooth panic grass [ ]
Panicum dichotomum L.
Panic grass [y]
Panicum gattingeri Nash
Panic grass [ ]
Panicum latifolium L.
panic grass [y]
Panicum linearifolium Scribn. ex
Nash
Panic grass [ ]
Panicum ovale L.
Panic grass [ ]
Panicum philadelphicum Bernh. ex
Trin.
Panic grass [ ]
Panicum rigidulum Bosc ex Nees
Panic grass [ ]
Panicum scabulorum Lam. var.
thinium (Hitchc. & Chase) C. Reed
Panic grass [y]
Panicum sphaerocarpon Ell.
Panic grass [ ]
Panicum villosissimum Nash
Panic grass [ ]
Panicum virgatum L. var. spissum
Linder
Switchgrass [y]
Panicum xanthophysum A. Gray
Panic grass [ ]
Paspalum setaceum Michx. var.
setaceum
Slender beardgrass [ ]
Paspalum setaceum Michx. var.
stramineum (Nash) Banks
Slender beardgrass [ ]
Phalaris arundinacea L.
Reed canary-grass [n]
Phalaris canariensis L.*
Canary-grass [y]
Phleum pratense L.*
Timothy [y]
Phragmites australis (Cav.) Trin. ex
Steud.*
Common reed [y]
Poa alsodes A. Gray
Speargrass [y]
Poa annua L.*
Annual bluegrass [y]
Poa compressa L.*
Canada bluegrass [y]
Poa languida Hitchc.
Woodland bluegrass [y]
Poa paludigena Fern. & Wieg.
Slender marsh bluegrass [y]
Poa palustris L.
Fowl bluegrass [ ]
Poa pratensis L.*
Kentucky bluegrass [y]
Poa trivialis L.*
Rough bluegrass [ ]
Schizachyrium scoparium (Michx.)
Nash
Little blue-stem [y]
Secale cereale L.*
Rye [ ]
Setaria pumila (Poir.) Schultes*
Foxtail [y]
Setaria verticillata (L.) Beauv.*
Bur bristlegrass [ ]
Setaria viridis (L.) Beauv.
Green foxtail [y]
Sorghastrum nutans (L.) Nash ex
Small
Indian grass [y]
Sphenopholis obtusata (Michx.)
Scribn.
Prairie wedgegrass [ ]
Sporobolus neglectus Nash
Poverty-grass [ ]
Sporobolus vaginiflorus (Torrey ex
A. Gray) Wood
Poverty-grass [ ]
Torreyochloa pallida (Torrey)
Church
Pale mannagrass [ ]
Triticum aestivum L.*
69
Carex cristatella Britt. ex Britt. &
Brown
Sedge [y]
Carex cumulata (Bailey) Mackz.
Sedge [ ]
Carex debilis Michx.
var. rudgei Bailey
Sedge [ ]
Carex deweyana Schwein.
Sedge [y]
Carex disperma Dewey
Sedge [n]
Carex echinata Murr.
Sedge [ ]
Carex festucacea Schkuhr ex Willd.
Sedge [ ]
Carex foenea Willd.
Sedge [y]
Carex folliculata L.
Sedge [ ]
Carex gracilescens Steud.
Sedge [y]
Carex gracillima Schwein.
Sedge [y]
Carex granularis Muhl. ex Willd.
Sedge [ ]
Carex gynandra Schwein.
Sedge [y]
Carex hystericina Muhl. ex Willd.
Sedge [y]
Carex interior Bailey
Sedge [y]
Carex intumescens Rudge
Sedge [y]
Carex lacustris Willd.
Sedge [y]
Carex laevivaginata (Kk.)Mackz.
ex Britt. & Brown
Sedge [y]
Carex lasiocarpa Ehrh. ssp.
americana (Fern.) Hulten
Sedge [n]
Carex laxiculmis Schwein.
Sedge [ ]
Carex laxiflora Lam.
Sedge [ ]
Wheat [y]
Cyperaceae
Bulbostylis capillaris (L.) Clarke
Sand-rush [ ]
Carex amphibola Steud. var. turgida
Fern.
Sedge [y]
Carex annectens (Bickn.) Bickn.
Sedge [ ]
Carex appalachica Webber & Ball
Sedge [y]
Carex aquatilis Wahl.
Sedge [y]
Carex arctata Boott ex Hooker
Sedge [ ]
Carex atlantica Bailey
Sedge [ ]
Carex baileyi Britt.
Sedge [y]
Carex bebbii (Bailey) Olney ex Fern.
Sedge [y]
Carex blanda Dewey
Sedge [y]
Carex brevior (Dewey) Mackz. ex
Lunell
Sedge [y]
Carex bromoides Schkuhr ex Willd.
Sedge [y]
Carex bushii Mackz.
Sedge [ ]
Carex buxbaumii Wahl.
Sedge [n]
Carex canescens L.
Sedge [y]
Carex cephalophora Muhl. ex Willd.
Sedge [ ]
Carex comosa Boott
Sedge [y]
Carex complanata Torrey & Hooker
Sedge [ ]
Carex conoidea Schkuhr ex Willd.
Sedge [ ]
Carex crinita Lam.
Sedge [y]
70
Carex leptalea Wahl.
Sedge [y]
Carex leptonervia (Fern.) Fern.
Sedge [ ]
Carex lupulina Muhl. ex Willd.
Sedge [y]
Carex lurida Wahl.
Sedge [y]
Carex muhlenbergii Schkuhr ex
Willd. var. muhlenbergii
Sedge [y]
Carex nigromarginata Schwein.
Sedge [ ]
Carex normalis Mackz.
Sedge [ ]
Carex pedunculata Muhl. ex Willd.
Sedge [y]
Carex pellita Muhl.
Sedge [ ]
Carex pensylvanica Lam.
Sedge [y]
Carex plantaginea Lam.
plantain-sedge [ ]
Carex prairea Dewey ex Wood
Sedge [ ]
Carex projecta Mackz.
Sedge [y]
Carex pseudocyperus L.
Sedge [y]
Carex radiata (Wahl.) Small
Sedge [y]
Carex retrorsa Schwein.
Sedge [y]
Carex rosea Schkuhr ex Willd.
Sedge [y]
Carex rostrata Stokes ex With. var.
utriculata (Boott) Bailey
Sedge [n]
Carex rugosperma Mackz.
Sedge [y]
Carex scabrata Schwein.
Sedge [y]
Carex scoparia (L.) Schkuhr ex
Willd.
Sedge [y]
Carex squarrosa L.
Sedge [ ]
Carex stipata Muhl. ex Willd.
Sedge [y]
Carex straminea Willd. ex Schkuhr
Sedge [y]
Carex stricta Lam.
Sedge [y]
Carex swanii (Fern.) Mackz.
Sedge [y]
Carex tenera Dewey
Sedge [y]
Carex tonsa (Fern.) Bickn.
Sedge [y]
Carex torta Boott & Tuckerm.
Sedge [y]
Carex tribuloides Wahl.
Sedge [y]
Carex trichocarpa Schkuhr ex Willd.
Sedge [y]
Carex trisperma Dewey
Sedge [n]
Carex tuckermanii Dewey
Sedge [ ]
Carex vaginata Taush
Sedge [ ]
Carex vesicaria L.
Sedge [y]
Carex vestita Willd.
Sedge [y]
Carex vulpinoidea Michx.
Sedge [y]
Cyperus bipartitus Torrey
Flat sedge [y]
Cyperus diandrus Torrey
cyperus [ ]
Cyperus erythrorhizos Muhl.
cyperus [y]
Cyperus esculentus L.*
Yellow nut-grass [ ]
Cyperus houghtonii Torrey
Flat sedge [y]
Cyperus lupulinus (Spreng.) Marcks
ssp. lupulinus
Flat sedge [y]
Cyperus odoratus L.
Flat sedge [y]
71
Cyperus schweinitzii Torrey
Flat sedge [y]
Cyperus squarrosus L.
Cyperus [ ]
Cyperus strigosus L.
Galingale [y]
Dulichium arundinaceum (L.) Britt.
Three-way sedge [y]
Eleocharis acicularis (L.) R. & S.
Hairgrass [y]
Eleocharis elliptica Kunth
Slender spikerush [y]
Eleocharis erythropoda Steud.
Spikerush [y]
Eleocharis intermedia Schultes
Spikerbush [y]
Eleocharis obtusa (Willd.) Schultes
var. obtusa
Spikerush [y]
Eleocharis palustris (L.) R. & S.
Creeping spikerbush [y]
Eriophorum tenellum Nutt.
Rough cottongrass [n]
Eriophorum virginicum L.
Tawny cottongrass [n]
Fimbristylis autumnalis (L.) R. & S.
Fimbry [y]
Rhynchospora alba (L.) Vahl
White beakrush [ ]
Scirpus acutus Muhl. ex Bigel.
Hard-stem bulrush [y]
Scirpus atrocinctus Fern.
Northern bulrush [y]
Scirpus atrovirens Willd.
Bulrush [y]
Scirpus cyperinus (L.) Kunth
Woolgrass [y]
Scirpus expansus Fern.
Bulrush [y]
Scirpus georgianus Harper
Bulrush [ ]
Scirpus microcarpus Presl
Bulrush [y]
Scirpus polyphyllus Vahl
Leafy bulrush [n]
Scirpus tabernaemontani Gmel.
Soft-stem bulrush [y]
Scleria triglomerata Michx.
Nutrush [ ]
Sparganiaceae
Sparganium americanum Nutt.
Bur-reed [y]
Sparganium erectum L.
Bur-reed [y]
Sparganium eurycarpum Engelm. ex
A. Gray
Bur-reed [y]
Typhaceae
Typha angustifolia L.
Narrow-leaf cat-tail [y]
Typha angustifolia latifolia
Cat-tail [y]
Typha latifolia L.
Common cat-tail [y]
Liliaceae
Allium canadense L.
Wild garlic [y]
Allium cepa L.*
Onion [ ]
Asparagus officinalis L.*
Asparagus [y]
Clintonia borealis (Ait.) Raf.
Woodlily [y]
Erythronium albidum Nutt.
White troutlily [ ]
Erythronium americanum Ker
Yellow adder's-tongue [y]
Hemerocallis fulva (L.) L.*
Orange day-lily [y]
Hemerocallis lilioasphodelus L.*
Yellow day-lily [y]
Hosta ventricosa (Salisb.) Stearn*
Blue hosta [y]
Hypoxis hirsuta (L.) Cov.
Stargrass [ ]
Lilium canadense L.
Canada lily [y]
Lilium philadelphicum L.
Woodlily [y]
72
Maianthemum canadense Desf.
False lily-of-the-valley [y]
Maianthemum racemosum L.
False solomon's-seal [y]
Maianthemum stellatum L.
Starflower [ ]
Medeola virginiana L.
Indian cucumber-root [y]
Narcissus poeticus L. var. recurvus
(Haw.) Fernandez*
Poet's narcissus [ ]
Polygonatum pubescens (Willd.)
Pursh
Solomon's-seal [y]
Streptopus roseus Michx.
Rose mandarin [y]
Trillium cernuum L.
Nodding trillium [y]
Trillium erectum L.
Purple trillium [ ]
Trillium grandiflorum (Michx.)
Salisb.
White trillium [ ]
Trillium undulatum Willd.
Painted trillium [y]
Uvularia grandiflora Sm.
Bellwort [y]
Uvularia perfoliata L.
Strawbell [y]
Uvularia sessilifolia L.
Wild-oats [y]
Veratrum viride Ait.
False or white hellebore [y]
Pickerel-weed [ ]
Smilacaceae
Smilax herbacea L.
Jacob's-ladder [y]
Orchidaceae
Arethusa bulbosa L.
Swamp pink [n]
Calopogon tuberosus (L.) BSP.
Grass pink [n]
Corallorhiza trifida Chat.
Pale coral-root [ ]
Cypripedium acaule Ait.
Pink ladyslipper [y]
Cypripedium reginae Walt.
Showy ladyslipper [ ]
Epipactis helleborine (L.) Crantz*
Helleborine [y]
Galearis spectabilis (L.) Raf.
Showy orchis [ ]
Goodyera pubescens (Willd.) R. Br.
Downy rattlesnake-plantain[ ]
Goodyera tesselata Lodd.
Rattlesnake plantain [ ]
Isotria verticillata (Muhl. ex Willd.)
Raf.
Large whorled pogonia [ ]
Liparis loeselii (L.) L. Rich.
Bog twayblade [y]
Malaxis bayardii Fern.
Adder's-mouth [y]
Platanthera ciliaris (L.) Lindl.
Orange orchid [ ]
Platanthera clavellata (Michx.) Luer
Green woodland orchid [ ]
Platanthera dilatata (Pursh) Lindl. ex
Beck
Bog-candle [ ]
Platanthera hookeri (Torrey ex A.
Gray) Lindl.
Hooker's orchid [ ]
Platanthera lacera (Michx.) G. Don
Ragged fringed orchid [n]
Platanthera orbiculata (Pursh) Lindl.
Round-leaved orchid [ ]
Iridaceae
Iris pseudacorus L.
Yellow iris [y]
Iris versicolor L.
Blue flag [y]
Sisyrinchium angustifolium Mill.
Blue-eyed grass [ ]
Sisyrinchium montanum Greene
Blue-eyed grass [y]
Pontederiaceae
Pontederia cordata L.
73
Spiranthes lacera (Raf.) Raf.
Slender lady's-tresses [ ]
Platanthera psycodes (L.) Lindl.
Purple fringed orchid [y]
Pogonia ophioglossoides (L.) Juss.
Rose pogonia [ ]
Spiranthes cernua (L.) L. Rich.
Nodding lady's-tresses [y]
Spiranthes ochroleuca (Rydb. ex
Britt.) Rydb.
Creamy lady’s tresses [y]
Statistical summary
128 plant families
486 genera
1212 total plant taxa (species, subspecies and varieties)
740 taxa (61.1%) confirmed (judged to be extant in the Albany Pine Bush)
41 taxa (3.4%) probably extirpated
431 taxa (35.6 %) uncertain
900 native taxa (74.3% of the total), 570 confirmed
312 non-native taxa (25.7% of the total), 170 confirmed
43 species of conservation interest, 14 confirmed, 6 probably extirpated
References
Hunt, D. M. 1995. NYFA Base List, Flora of the Albany Pine Bush. New York Natural Heritage
Program, Latham, New York.
Mattox, J. E. 1994. Wetland Vascular Flora of the Pine Bush, Albany and Schenectady
Counties, New York State, in the 19th and 20th Centuries. Master’s Thesis, Graduate
School of Environmental Studies, Bard College, Annondale, New York.
Mitchell, R. S., and G. C. Tucker. 1997. Revised Checklist of New York State Plants. New
York State Museum Bulletin 490: 400 pages.
Rittner, D. (ed.). 1976. Pine Bush: Albany’s Last Frontier. Pine Bush Historic Preservation
Project, Albany, New York.
Schneider, K. J., C. Reschke, and S. M. Young. 1991. Inventory of the rare plants, animals, and
ecological communities of the Albany Pine Bush Preserve. Report to the Albany Pine
Bush Commission. New York Natural Heritage Program, Latham, New York.
74
INSECTS
The following list of insects is as it appears in Appendix C of the Albany Pine Bush Natural
History Book.
Class Insecta: Order Coleoptera
The following list of eight tiger beetles from the Albany Pine Bush is based on a list
presented by McCabe (1993). An early record of the northeastern beach tiger beetle is almost
certainly an error, as this species is restricted to seacoasts, where adults prey on small
invertebrates and scavenge dead fish in the intertidal zone. The species marked with superscript
X (X) is thought to be extirpated from the Albany Pine Bush.
Cicindelidae
Cicindela duodecimguttata Dejean
Cicindela formosa Say
Cicindela patruela DejeanX
Cicindela punctulata Olivier
Cicindela repanda Dejean
Cicindela scutelaris Say
Cicindela sexguttata Fabricius
Cicindela tranquebarica Herbst
The following list of 76 longhorned beetles from the Albany Pine Bush is base on a list
publichsed by McCabe and Huether (1986). Nomenclature has been rectified with that found in
Yanega (1996). The list is probably incomplete, and further collecting could add names of
previously unrecorded species. However, before this list was published in 1986, none of the
pspeces had been recorded from the Pine Bush. The elderberry longhorned beetle, has declined
markedly in Massachusettes, where it is now regarded as a species of specieal concern. The
reasons for the apparent decline are unknown.
Cerambycidea (Aseminae)
Arhopalus rusticus obsletus (Randall)
Asemum striatum (Linnaeus)
Cerambycidae (Cerambycinae)
Cerambycidae (Lamiinae)
Aneflomorpha subpubescens
Acanthocinus obsoletus (Olivier)
Anelaphus villosus (Fabricius)
Aegomorphus modestus (Gyllenhal)
Batyle suturalis suturalis (Say)
Astylopsis macula (Say)
Clytus ruricola (Olivier)
Astylopsis sexguttata (Say)
Cyrtophorus verrucosus (Olivier)
Ecyrus dasycerus dasycerus (Say)
Euderces picipes (Fabricius)
Eupogonius tomentosus (Haldeman)
Megacyllene robiniae (Forster)
Goes debilis LeConte
Molorchus bimaculatus bimaculatus Say
Goes pulcher (Haldeman)
Neoclytus acuminatus acuminatus (Fabricius)Hebestola nebulosa (Haldeman)
Parelaphidion incertum (Newman)
Hippopsis lemniscata (Fabricius)
Phymatodes aereus (Newman)
Hyperplatys aspera (Say)
Phymatodes amoenus (Say)
Lepturges angulatus (LeConte)
Phymatodes testaceus (Linnaeus)
Lepturges confluens (Haldeman)
Phymatodes unicolor (Randall)
Lepturges pictus (LeConte)
75
Xylotrechus sagittatus sagittatus (Germar)
Liopinus alpha (Say)
Monochamus notatus (Drury)
Monochamus scutellatus scutellatus (Say)
Monochamus titillator (Fabricius)
Oberea ocellata (Haldeman)
Oberea perspicillata (Haldeman)
Oberea triumctat (Swederus)
Psenocerus supernotatus (Say)
Saperda calcarata (Say)
Saperda candida (Fabricus)
Saperda imitans (Felt and Joutel)
Saperda inornata (Say)
Saperda lateralis (Fabricius)
Saperda obliqua (Say)
Saperda tridentata (Olivier)
Saperda vistita (Say)
Sternidius variegats (Haldeman)
Tetraopes melanurus (Schonherr)
Tetraopes tetraophthalmus (Forster
Tetrops praeusta (Linnaeus)
Urgleptes signatus (LeConte)
Cerambycidae (Lepturinae)
Acmaeops discoideus (Haldeman)
Analeptura lineola (Say)
Brachyleptura champlaini (Casey)
Brachyleptura circumdata (Olivier)
Brachyleptura vagans (Olivier)
Brachyleptura rubrica (Say)
Charisalia americana (Haldeman)
Desmocerus palliatus (Forster)
Gaurotes cyanipennis (Say)
Grammoptera haematites (Newman)
Grammoptera subargeniata (Kirby)
Judolia cordifera (Olivier)
Leptura subhamata (Randall)
Metacmoeops vittata (Swederus)
Pidonia ruficollis (Say)
Rhagium inquisitor (Linnaeus)
Strangalepta abbreviata (Germar)
Strangalia luteicornis (Fabricius)
Strophiona nitens (Forster)
Trachysida mutabilis (Newman)
Cerambycidae (Prioninae)
Typocerus velutinus velutinus (Olivier)
Orthosoma brunneum (Forster)
Prionus laticullis (Drury)
Prionus pocularis Dalmeister
Class Insecta: Order Diptera
The folowing list of 36 robber fly species from the Albany Pine Bush is baed on a list
compiled by McCabe and Weber (1994). Species marked with a superscript X (X) are thought to
be extirpated from the Albany Pine Bush. The species marked with a superscript S (S) are
believed to be a pine barrens specialist or obligate.
Asilidae
Asilus erythroenemius (Hine)
Atomosia puella (Wiedemann)
Ceraturgus cruciatus (Say)
Cerotainia macrocera (Say)
Cyrtopogon falto (Walker)
Cyrtopogon laphriformis (Curran)X
Cyrtopogon lutatius (Walker)
Cyrtopogon maginalis (Loew)
Dioctria baumhaueri (Meigen)
Diogmites basalis (Walker)
Diogmites umbrinus (Loew)
Laphria index (McAtee)
Laphria posticata (Say)
Laphria sadales (Walker)
Laphria thoracica (Fabricius)
Laphria virginica (Banks)
Lasiopogon currani (Cole and Wilcox)
Lasiopogon terricola (Johnson)
Leptogaster flavipes (Loew)
Leptogaster glabrata (Wiedemann)
Machimus notatus (Wiedemann)
Machimus sadyates (Walker)
76
Efferia aestuans (Linnaeus)
Holopogon guttulus (Wiedemann)
Laphria aktis (McAtee)
Laphria cinerea (Black)S
Laphria divisor (Bans)
Laphria flavicollis (Say)
Laphria franciscana (Bigot)
Machimus snowii (Hine)
Neoitamus flavofemoratus (Hine)
Neoitamus orphe (Walker)
Ommatius tibialis (Say)
Proctacanthus philadelphicus (Macquart)
Proctacanthus rufus (Williston)
Promachus bastardii (Macquart)X
Class Insecta: Order Trichoptera
The following list of 57 caddisfly species from the Albany Pine Bush is based on lists
published by McCabe (1980, 1986). Nomenclature and taxonomic arrangement have been
updated to comply, in most cases, with Nomina Insecta Nearctica.
Arctopsychidae
Parapsyche apicalis (Banks)
Frenesia missa (Milne)
Glyphotaelius histilis (Hagen)
Ironoquia lyrata (Ross)
Ironoquia parvula (Banks)
Ironoquia punctatissiums (Walker)
Limnephilus canadensis (Banks)
Limnephilus indivisus (Walker)
Limnephilu ornatus (Banks)
Limnephilus sericeus (Say)
Limnephilus submoilifer (Walker)
Liminiphilus sp.
Nemotaulius hostilis (Hagen)
Neophylax fuscus (Banks)
Onocosmoecus quadrinotatus(Banks)
Pseudostenophylax uniformis (Bet.)
Psychoglypha subborealis (Banks)
Pycnopsyche circularis (Provancher)
Pycnopsyche divergens (Walker)
Pycnopsyche indiana (Ross)
Pycnopsyche luculenta (Betten)
Pycnopsyche guttifer (Walker)
Pycnopsyche scabripennis (Rambus)
Pycnopsyche sp.
Brachycentridae
Brachycentrus americanu (Banks)
Hydropsychidae
Ceratopsyche slossonae (Banks)
Diplectrona modesta (Banks)
Hydropsyche betteni (Ross)
Hydropsyche sp.
Lepidostomatidae
Lepidostoma sp.
Leptoceridae
Ceraclea flavus (Banks)
Ceraclea resugens (Walker)
Mystacides sepulchralis (Walker)
Nectopsyche albidus (Walker)
Nectopsyche sp.
Oecetis cinerascens (Hagen)
Oecetis sp. 1
Oecetis sp. 2
Triaenodes baris (Ross)
Triaenodes ignitus (Walker)
Triaenodes marginata (Sibley)
Triaenodes tarda (Milne)
Molannidae
Molanna blenda (Sibley)
Molanna sp.
Philoptamidae
Chimarra aterrima (Hagen)
Limnephilidae
Anabolia consocius (Walker)
Caborius lyratus (Ross)
Frenesia deifficilis (Walker)
Phryganeidae
Agrypnia coloratta (Hagen)
77
Agrypnia vestita (Walker)
Banksiola crotchi (Banks)
Banksiola dossuaria (Say)
Oligostomis pardalis (Walker)
Phryganea sayi (Milne)
Ptilostomis ocellifera (Walker)
Polycentropodidae
Polycentropus interruptus (Banks)
Rhyacophilidae
Rhyacophila fuscula (Walker)
Class Insecta: Order Lepidoptera
by Tim L. McCabe, New York State Museum
In the following list of 101 butterflies and skippers from the Albany Pine Bush,
nomenclature and classification, in large part, folow the Check List of Lepidotera of America
North of Mexico (Hodges et al. 1983). Common names are those found in the Peterson Field
Guide to Eastern Butterflies (Opler and Malikul 1992). Species marked with a superscript X (X)
are thought to be extirpated from the Albany Pine Bush.
Erynnis persius ScudderX
Persius dusky wing
Euphys bimacula G. & R.
Two-spotted skipper
Euphyes conspicuus Edwards
Black dash
Euphyes dion Edwards
Dion skipper
Euphyes vestris Bdv.
Dun skipper
Hesperia leonardus Harr.
Leonard's skipper
Hesperia metea Scudder
Cobweb skipper
Hesperia sassacus Harr.
Indian skipper
Pholisora catullus F.
Common sooty wing
Poanes hobomok Harr.
Hobomok skipper
Poanes massasoit Scudder
Mulberry wing skipper
Poanes viator zizaniae Shapiro
Broad-winged skipper
Polites coras Cramer
Peck's skipper
Polites mystic Edwards
Long dash
Polites origenes F.
Crossline skipper
Hesperiidae (36 species)
Achalarus lyciades Gey.
Hoary edge
Amblyscirtes hegon Scudder
Pepper and salt skipper
Amblyscirtes vialis Edwards
Roadside skipper
Ancyloxypha numitor F.
Least skipper
Atrytone delaware Edwards
Delaware skipper
Atrytonopsis hiana Scudder
Dusted skipper
Calpodes ethlius Stoll (stray, last
recorded in 1893)
Brazilian skipper
Epargyreus clarus Cramer
Silver-spotted skipper
Erynnis baptisiae Forbes
Wild indigo dusky wing
Erynnis brizo Bdv. & LeconteX
Sleepy dusky wing
Erynnis icelus Scudder & Burgess
Dreamy dusky wing
Erynnis juvenalis F.
Juvenal's dusky wing
Erynnis lucilius Scudder & BurgessX
Columbine dusky wing
Erynnis martialis Scudder
Mottled dusky wing
78
Polites themistocles Latr
Tawny-edged skipper
Pompeius verna Edwards
Little glassywing
Pyrgus communis Grt.
(migrant, new record)
Checkered skipper
Thorybes bathyllus J. E. Smith
Southern cloudy wing
Thorybes pylades Scudder
Northern cloudy wing
Thymelicus lineola Ochs.
(European introduction)
European skipper
Wallengrenia egeremet Scudder
Northern broken dash
Pieris rapae L.
Cabbage butterfly
Pieris virginiensis EdwardsX
West Virginia butterfly
Pontia protodice Bdv. & LeconteX
Checkered white
Lycaenidae (18 species)
Celastrina ladon ladon Cramer
Spring azure
Celastrina ladon lucia Kby.
Spring azure
Everes comyntas Godt.
Eastern tailed blue
Feniseca tarquinius F.
Harvester
Harkenclenus titus F.
Coral hairstreak
Incisalia augustinus Kby.
Brown elfin
Incisalia henrici G. & R.
Henry's elfin
Incisalisa irus Godt.
Frosted elfin
Incisalia niphon Hbn.
Eastern pine elfin
Lycaeides melissa samuelis Nabokov
Karner blue
Lycaena hyllus Cramer
Bronze copper
Lycaena phlaeas L.
American copper
Satyrium acadicum Edwards
Acadian hairstreak
Satyrium calanus Hbn.
Banded hairstreak
Satyrium caryaevorum McD.
Hickory hairstreak
Satyrium edwardsii G. & R.
Edward's hairstreak
Satyrium liparops Leconte
Striped hairstreak
Strymon melinus Hbn.
Gray hairstreak
Papilionidae (6 species)
Battus philenor L.
Pipe-vine swallowtail
Papilio canadensis R. & J.
Canadian swallowtail
Papilio cresphontes Cramer
Giant swallowtail
Papilio glaucus L.
Tiger swallowtail
Papilio polyxenes E.
Black swallowtail
Papilio troilus L
Spicebush swallowtail
Pieridae (9 species)
Colias eurytheme Bdv.
Alfalfa butterfly
Colias interior ScudderX
Pink-edged sulphur
(last recorded 1884)
Colias philodice Godart
Clouded sulphur
Eurem lisa Bdv. & Leconte (migrant)
Little sulphur
Phoebis sennae L. (migrant; new
record)
Cloudless sulphur
Pieris napi L.X
Mustard white
Nymphalidae (25 species)
79
Question mark
Polygonia progne Cramer
Gray comma
Speyeria aphrodite F.
Aphrodite fritillary
Speyeria cybele Fabricius
Great spangled fritillary
Speyeria idalia DruryX
Regal fritillary
Vanessa atalanta L. (migrant)
Red admiral
Vanessa cardui Linnaeus (migrant)
Painted lady
Vanessa virginiensis Drury (migrant)
American painted lady
Boloria bellona F.
Meadow fritillary
Boloria selene D. & S.
Silver-bordered fritillary
Chlosyne harrisii Scudder
Harris checkerspot
Chlosyne cycteis Doubleday
Silvery checkerspot
Euphydryas phaeton Drury
Baltimore
Euptoieta claudia Cramer
Variegated fritillary
Junonia coenia Hbn.
Buckeye
Limenitis archippus Cramer
Viceroy
Limenitis arthemis arthemis Drury
Banded purple
Limenitis arthemis astyanax
Fabricius
Red-spotted purple
Nymphalis antiopa L.
Mourning cloak
Nymphalis milberti Godt.
Milber'ts tortoise shell
Nymphalis vau-album D. & S.
Compton tortoise shell
Phyciodes batesii ReakirtX
Tawny cresent
Phyciodes tharos Drury
Pearl cresent
Polygonia common Harr.
Hop merchant
Polygonia interrogationis F.
Satyridae (6 species)
Cercyonis pegala Fabricius
Common wood nymph
Coenonympha inornata Edwards
Inornate ringlet
Enodia anthedon A. H. Clark
Northern pearly eye
Megisto cymela Cramer
Little wood satry
Satyrodes appalachia R. Chermock
Appalachian eyed brown
Satyrodes eurydice Johansson
Eyed brown
Danaidae (1 species)
Danaus plexippus L. (migrant)
Monarch
In the following list of Albany Pine Bush moths, nomenclature follow that found in the
Check List of the Lepidoptera of America North of Mexico (Hodges et al. 1983), unless thename
is a recent combination or recently described species. Geometrid nomenclature follows Scoble
(1999). Species marked with a superscrpt X (X) have not been found in the course of intensive
collecting effort over the past 25 years. Species marked with a superscript R (R) are known in the
Pine Bush only from recent collecting, during the past 25 years. Species marked with a
superscript S (S) are believed to be pine barrens specialists or obligates, dependent on
characteristic vegetation, sandy and arid environments, periodic fires, or some other ecological
characteristic of the Pine Bush for their continued existence in this area.
Zygaenidae (3 species)
Acoloithus falsarius Clem.
80
Harrisina americana Guer.
Pyromopha dimidata H.-S.X
Dichorda iridaria Gn.
Dyspteris abortivaria H.-S.
Dysstroma citrata L.
Dysstrom hersiliata Gn.
Ecliptopera silaceata D. & S.
Ematurga amitaria Gn.
Ennomos magnaria Gn.
Ennomos susignaria Hbn.
Ephirrhoe alternata Mueller
Erannis tiliaria Harr.
Erastria coloraria F.
Eubaphe mendica Wlk.
Euchlaena serrata Drury
Euchlaena muzaria Wlk.
Euchlaena johnsonaria Fitch
Euchlaena marginaraia Minot
Euchlaena irraria B. & McD.
Eufidonia notartaria Wlk.
Eugonobapta nivosaria Gn.
Eulithis diversilineata Hbn.
Eulithis testata L.
Eulithis explanata Wlk.
Eumacaria latiferrugata Wlk.
Euphyia unangulata Haw.
Eupithecia albicapitata Pack
Eupithecia lariciata Freyer
Eupithecia miserulata Grt.
Eupithecia ravocostaliata Pack.
Eusarca confusaria Hbn.
Eutrapela clemataria J. E. Smith
Glena cribrataria Gn.
Gueneria similaria Wlk.
Haematopis grataria F.
Heliomata cycladata G. & R.
Hesperumia suphuraria Pack.
Heterophleps triguttaria H. S.
Homochlodes fritillaria Gn.
Horisme intestinata Gn.
Hydrelia condensata Wlk.
Hydrelia albifera Wlk.
Hydriomena perfracta Swett
Hydriomena divisaria Wlk.
Hydriomena transfigurata Swett
Hydriomena pluviata Gn.
Hypagyrtis unipunctat Haw.
Idaea bonifata Hulst
Megalopygidae (1 species)
Lagoa crispata Pack.X
Thyrididae (2 species)
Thyris maculata Harr.
Thyris sepulchralis Guer.
Thyatiridae (3 species)
Euthyatira pudens Gn.
Habrosyne scripta Gosse
Psedothyatria cymatophoroides Gn.
Drepanidae (4 species)
Drepana arcuata Wlk.
Drepana bilineata Pack.
Eudeilinia herminata Gn.
Oreta rosea Wlk.
Geometridae (165 species)
Aethalura intertexta Wlk.
Alsophila pometaria Harr.
Anavitrinella pampinaria Gn.
Antepione thisoaria Gn.
Anticlea vasiliata Gn.
Anticlea multiferata Wlk.
Apodrepanulatrix liberaria Wlk.
Archiearis infans Moesch.X
Besmzquereivoraria Gn.
Biston betularia L.
Cabera erythemaria Gn.
Cabera variolaria Gn.
Campaea perlata Gn.
Caripeta divisata Wlk.
Caripeta piniata Pack.
Cepphi decoloraria Hulst
Cepphis armataria H.-S.
Chlorochlamys chloroleucaria Gn.
Cingilia catenaria DruryX
Cladara limitaria Wlk.
Cladara angulineata G. & R.
Cladara atroliturata Wlk.
Costiconvexa centrostrigaria Woll.
Cyclophora pendulinaria Gn.
81
Idaea demissaria Hbn.
Idaea dimidiata Hufn.
Iridopsis vellivolata Hulst
Iridopsis humaria Gn.
Iridopsis larvaria Gn.
Lambdina fiscellaria Gn.
Lobophora nivigerata Wlk.
Lobophora montanata Pack.
Lomographa semiclarata Wlk.
Lomographa vestaliata Gn.
Lomographa glomeraria Grt.
Lycia ursaria Wlk.
Lytrosis unitaria H. S.
Macaria aemulataria Hulst
Macaria ulsterata Pears.
Macaria transitaria Wlk.
Macaria minorata Pack.
Macaria bicolorata F.
Macaria bisignata Wlk.
Macaria pinistrobata Ferg.
Macaria granitata gn.
Macaria ocellinata Gn.
Macaria mellistrigata Grt.
Macaria gnophosaria Gn.
Melanolophis canadaria Gn.
Mesoleuca ruficillata Gn.
Mesothea incertata Wlk.
Metanema inatomaria Gn.
Metanema determinata Wlk.
Metarranthis duaria Gn.
Metarranthis anuglaria B. and McD.
Metarranthis indeclinata Wlk.
Metarranthis hypochraria H. S.
Metarranthis apiciaria Pack.X
Metarranthis obfirmaria Hbn.
Micaria pustularia Gn.
Micaria ribearia Fitch
Micaria evagaria Hulst
Micaria argillacearia Pack.
Micaria n. sp.
Nematocampa resistaria H. S.
Nemoria bistriaria Hbn.
Nemoria rubrifrontaria Pack.
Nemoria mimosaria Gn
Nepytia canosaria Wlk.
Nepytia semiclusaria Wlk.X
Operophtera bruceata Hulst
Orthofidonia flavivenata Hulst
Orthonama obstipata F.
Paleacrita vernata Peck
Patalene olyzonaria Wlk.
Pero honestaria Wlk
Pero morrisonaria Hy. Edw.
Pero ancetaria Hbn.
Petrophora subaequaria Wlk.
Phaeoura quernaria Smith
Phigalia titea Cramer
Phigalia strigataria Minot
Plagodis pulveraria L.
Plagodis serinaria H. S.
Plagodis kuetzingi Grt.
Plagodis phlogosaria Gn.
Plagodis fervidaria H. S.
Plagodis alcoolaria Gn.
Pleuroprucha insulsaria Gn
Probole alienaria H. S.
Probole amicaria H. S.
Prochoerodes lineola Goeze
Protitame virginalis Hulst
Rheumaptera prunivorata Ferg.
Rheumaptera hastata L.
Scopula limboundata Haw.
Scopula quadrilineata Pack.
Scopula siccata McD.
Scopula inductata Gn.
Selenia alciphearia Wlk.
Sicya macularia Harr.
Spargania magnoliata Gn.
Spodolepis substriataria Hulst
Synchlora aerata F.
Tacparia detersata Gn.
Tetracis crocallata Gn.
Tetracis cachexiata Gn.
Thera juniperata L.
Trichodezia albovittata Gn.
Triphosa haesitata Gn.
Venusia duodecemlineata Pack.
Venusia comptaria Wlk.
Xanthorhoe labradorensis Pack.
Xanthorhoe ferrugata Cl.
Xanthorhoe lacustrata Gn.
Xanthotype urticaria Swett
82
Xanthotype sospeta Drury
Eumorpha pandorus Hbn.
Hemaris diffinis Bdv.
Hemaris gracilis G. and R.X
Hemaris thysbe F.
Hyles gallii Rottemburg (European
introduction)
Hyles lineata F. (migrant)
Laothoe juglandis J. E. Smith
Laparabombycoides Wlk.
Laparaconiferarum J. E. Smith
Manduca quinquemaculata Haw.
Manduca sexta L.
Pachysphinx modesta Harr.
Paonias astylus DruryX
Paonias excaecatus J. E. Smith
Paonias myops J. E. Smith
Smerinthus cerisyi Kby.
Smerinthus jamaicensis Drury
Sphecodina abbottii Swainson
Sphinx chersis Strkr.
Sphinx eremitus Strkr.
Sphinx canadensis Bdv.
Sphinx drupiferarum J. E. Smith
Sphinx kalimiae J. E. Smith
Sphinx luscitiosa Clem.
Sphinx poecila Stephens
Epiplemidae (2 species)
Calledapteryx dryopterata Grt.
Callizzia amorata Pack.
Mimallonidae (1 species)
Lacosoma chiridota Grt.
Apatelodidae (2 species)
Apatelodes torrefacta J. E. Smith
Olceclostera angelica Grt.
Lasiocampidae (6 species)
Artace cribraria LjunghX
Malacosoma americanum F.
Malacosoma disstria Hbn
Phyllodesma americana Harr.
Tolype laricis Fitch
Tolype velleda Stoll
Saturniidae (12 species)
Actias luna L
Anisota senatoria J. E. Smith
Anisota virginiensis Drury
Antheraea polyphemus Cramer
Automeris io F.
Callosamia promethea Drury
Citheronia regalis F.X
Eacles imperialis Drury
Hemileuca maia Drury
Hyalophora cecropia L.
Notodontidae (46 species)
Cerura scitiscripta Wlk.
Clostera albonsigma Fitch
Clostera apicalis Wlk.
Clostera inclusa Hbn.
Clostera strigosa Grt.
Dasylophia anguina J. E. Smith
Dasylophia thyatiroides Wlk.
Datana intergerrima G. and R.X
Datana ministra DruryX
Ellida caniplaga Wlk.
Furcula borealis Guer. Meneville
Furcula cinerea Wlk.
Furcula modesta Hudson
Furcula scolopendrina Bdv.
Gluphisia avimacula Hudson
Gluphisia lintneri Grt.
Gluphisia septentrionis Wlk.
Heterocampa biundata Wlk.
Sphingidae (36 species)
Agrius cingulatus F. (stray
individuals)
Amphion floridensis B. P. Clark
Ceratomia amyntor Geyer
Ceratomis catalpae Bdv.
Veratomia undulosa Wlk.
Darapsa myron Cram.
Darapsa pholus Cram.
Darapsa versicolor Harr.X
Deidamia inscripta Harr.
Dolba hyloeus Drury
Eumorpha achemon Drury
83
Heterocampa guttiviatta Wlk.
Heterocampa obliqua Pack.
Hyparax aurora J. E. Smith
Hyperaeschra georgiea H. S.
Lochmaeus bilineata Pack.
Lochmaeus manteo Doubleday
Macrurocampa marthesia Cram.
Misogada unicolor Pack.
Nadata gibbosa J. E. Smith
Nerice bidentata Wlk.
Notodonta scitipeniis Wlk.
Notodonta simplaria Graef
Odontosia elegans Strk.
Oligocentaria lignicolor Wlk.
Oligocentria semirufescens Wlk.
Peridea angulosa J. E. Smith
Peridea basitriens Wlk.
Peridea ferrugiea Pack.
Pheosia rimosa Pack.
Schizura apicalis G. and R.
Schizura badia Pack.
Schizura concinna J. E. Smith
Schizura ipomoeae Doubleday
Schizura leptinoides Grt.
Schizura unicornis J. E. Smith
Schizura albifrons J. E. Smith
Schizura canicosta Francl.
Schizura leucitys Francl.
Grammia virguncula W. Kby.
Halysidota tessellaris Sm.
Haploa confusa Lyman
Haploa lectonei Guer. Meneville
Haploa clymene Brown
Holomelina aurantiaca Hbn.
Holomelina ferruginosa Wlk.
Holomelina laeta Guer. Meneville
Holomelina opella Grt.
Hyphantria cunea Drury
Hypoprepia fucosa Hbn.
Hypoprepia miniata Kby.
Lophocampa caryae Hbn.
Lophocampa maculata Harr
Lycomorpha pholus Drury
Phragmatobia assimilans Wlk.X
Phragmatobia fuliginosa L.
Pyrrharctia isabella J. E. Smith
Spilosoma congrua Wlk.
Spilosoma dubia Wlk.
Spilosoma latipennis Stretch
Spilosma virginica F.
Lymantriidae (11 species)
Dasychira basiflava Pack.
Dasychira dorsipennata (B. and
McD.)
Dasychira obliquata G. and R
Dasychira pinicola Dyar
Dasychira plagiata Wlk.
Dasychira vagans B. and McD.
Leucoma salicis L.
Lymantria dispar L
Orgyia antiqua L
Orgyia definita Pack.
Orgyia leucostigma J. E. Smith
Arctiidae (39 species)
Apantesis nais Drury
Apantesis phalerata Harr.
Cisseps fulvicollis Hbn.
Clemensia albata Pack.
Ctenucha virginica Esp.
Cycnia oregonensis Stretch
Cycnia tenera Hbn.
Ecpantheria scribonia StollX
Eilema bicolor Grt.X
Estigmene acrea Drury
Euchaetes egle Drury
Grammia arge Drury
Grammia celia Saunders
Grammia parthenice W. Kby.
Grammia phyllira Drury
Grammia virgo L.
Noctuidae (563 species)
Abagrotis alternata Grt.
Abagrotis cupida Grt.S
Abrostoal ovalis Gn.R
Abrostola urentis Gn.
Achatia distineta Hbn.
Achatodes zeae Harr.
Acronicta albarufa Grt.S
Acronicta clarescens Grn
84
Acronicta connecta Grt.X
Acronicta dactylina Grt.
Acronicta falcula Grt.S
Acronicta fragilis Gn
Acronicta grisea Wlk.
Acronicta hamamelis Gn
Acronicta hasta Gn.
Acronicta hastulifera J. E. Smith
Acronicta impressa Wlk.
Acronicta increta Morr.
Acronicta innotat Gn.
Acronicta interrupta Gn.
Acronicta laetifica Sm.
Acronicta lanceolaria Grt.SX
Acronicta leporina L.
Acronicta lepusculina Gn.
Acronicta lithospila Grt.
Acronicta lobeliae Gn.
Acronicta longa Gn.
Acronicta modica Wlk.
Acronicta morula G. and R.
Acronicta noctivaga Grt.
Acronicta oblinita J. E. Smith
Acronicta pruni Harr.X
Acronicta radcliffei Harv.SX
Acronicta retardata Wlk.
Acronicta sperata Grt.S
Acronicta spinigera Gn.S
Acronicta subochrea Grt.
Acronicta superans Gn.
Acronicta tristis Sm.S
Acronicta vinnula Grt.
Actebia fennica Tauscher
Adita chionanthi J. E. Smith
Agnorisma badinodis Grt.
Agriopodes fallax H. S.
Agroperina lutosa AndrewsX
Agrotis gladiaria Morr.
Agrotis ipsilon Hufn.
Agrotis stigmosa Morr.
Agrotis subterranea F.R (migrant)
Agrotis venerabilis Wlk.
Agrotis volubilis Harv.S
Alypia octomaculata F.
Amolita fessa Grt.
Amolita roseola Sm.R
Amphipoea americana Speyer
Amphipoea interoceanica Sm.
Amphipoea velata Wlk.
Amphipyra glabella Morr.
Amphipyra pyramidoides Gn.
Amphipyra tragopoginis Cl.
Amyna octo Gn. (migrant)
Anagrapha falcifera Kby.
Anaplectoides prasina D. and S.
Anaplectoides pressus Grt.
Anathix puta G. and R.
Anathix ralla G. and R.
Anicla infecta Ochs. (migrant)
Anorthodes tarda Gn.R
Anticarsia gemmatalis Hbn.
(migrant)
Apamea alia Gn.
Apamea amputartrix Fitch
Apamea apamiformis Gn.
Apamea burgessi Morr.X
Apamea cariosa Gn.
Apamea cristata Grt.
Apamea devastator Brace
Apamea dubitans Wlk.
Apamea helva Grt.
Apamea impulsa Gn.
Apamea lignicolora Gn.
Apamea nigrior Sm.
Apamea ophiogramma Grt.R
Apamea plutonia Grt.
Apamea remissa Hbn.
Apamea sordens Hufn.
Apamea verbascoides Gn.
Apamea vultuosa Grt.
Apharetra dentata Grt.S
Aplectoides condita Gn.
Archanara laeta Morr.
Archanara oblonga Grt.
Archenara subflava Grt.
Argyrostrotis anilis Drury
Argyrostrotis quadrifilaris Hbn.
Ascalapha odorata L.X (tropica
migrant)
Athetis miranda Grt.
Autographa ampla Wlk.
Autographa precationis Gn.
85
Bagisara rectifascia Grt.
Baileya dormitans Gn.
Baileya doubledayi Gn.
Baileya levitans Sm.
Baileya ophthalmica Gn.
Balsa labecula Grt.
Balsa malana Fitch
Balsa tristrigella Wlk.
Bellura obliqua Wlk.
Bleptina caradrinalis Gn.
Brachylomis discinigra Wlk.
Caenurgina crassiuscula Haw.
Caenurgina erechtea Cram.
Callopistria cordata Ljungh
Callopistria mollissima Gn.
Calophasia lunula Hufn.R
Calyptra canadensis Bethune
Capis curvata Grt.
Caradrina meralis Morr.S
Caradrina multifera Wlk.
Caradrina lineolata Wlk.
Catocala amatrix Hbn.
Catocala amica Hbn.
Catocala andromedae Gn.
Catocala antinympha Hbn.
Catocala blandula Hulst
Catocala briseis Edw.
Catocala cara Gn.
Catocala cerogama Gn.
Catocala clintoni Grt.X
Catocala coccinata Grt.
Catocala concumbens Wlk.
Catocala connubialis Gn.
Catocala crataegi Saunders
Catocala gracilis Edw.S
Catocala grynea Cram.
Catocala habilis Grt.
Catocala ilia Cram.
Catocala judith Strkr.
Catocala lineella Grt.
Catocala meskei Grt.
Catocala micronympha Gn.
Catocala mira Grt.
Catocala neogama J. E. Smith
Catocala n. sp. (near jair Stkr.)
Catocala palaeogama Gn.
Catocala parta Gn.
Catocala piatrix Grt.
Catocala praeclara G. and R.
Catocala pretiosa Lint.X
Catocala relicta Wlk.
Catocala residua Grt.
Catocala retecta Grt.
Catocala similis Edw.S
Catocala sordina Grt. S
Catocala subnata Grt.
Catocala ultronia Hbn.
Catocala unijuga Wlk.
Catocala vidua J. E. Smith
Catocala whitneyi DodgeX
Celiptera frustulum Gn.
Cerastis fishii Grt.
Cerastis tenebrifera Wlk.
Cerma cerintha Tr.
Cerma cora Hbn.S
Chaetaglaea cerata Franel.S
Chaetaglaea sericea Morr.
Chaetaglaea tremula Harv.S
Charadra deridens Gn.
Chersotis juneta Grt.
Chrysanympha formosa Grt.S
Chytolita morbidalis Gn.
Chytolita petrealis Grt.
Chytolita palliatricula Gn.
Chytonix sensilis Grt.S
Cirrhophanus triangulifer Grt.SX
Cissusa spadix Cram.S
Colobochyla interpuncta Grt.S
Colocasia flavicornis Sm.
Colocasia propinquilinea Grt.
Condica vecors Gn.
Condica videns Gn.
Conservula anodonta Gn.
Covialeria grotei Morr.
Cosmia calami Harv.
Crambodes talidiformis Gn.
Crocigrapha normani Grt.
Cryptocala acadiensis BethuneS
Cucullia asteroides Gn.
Cucullia convexipennis G. and R.
Cucullia lucifuga D. and S.
Cucullia omissa Dod
86
Cucullia postera Gn.
Cucullia speyeri Lint.S
Deltote albidula Gn.
Deltote bellicula Hbn.
Deltote muscosula Gn.
Deltote musta G. and R.
Diachrysia aereoides Grt.
Diachrysia balluca Gey.
Diarisia jucunda Wlk.X
Diarisia rubifera Grt.X
Discestra trifolii Hufn.
Dypterygia rozmani Berio
Dyspyralis illocata WarrenS
Dyspyralis nigella Stkr.
Dyspyralis puncticosta Sm.
Egira dolosa Grt.
Elaphria festivoides Gn.
Elaphria grat Hbn.
Elaphria versicolor Grt.
Enargia decolor Wlk.
Enargia infumata Grt.
Enargia mephisto Franel.
Eosphoropteryx thyatyroides Gn.
Epiglaea apiata Grt.SX
Epiglaea decliva Grt.
Eremobina jocasta Smith
Euagrotis forbesi Franel.
Euagrotis illapsa Wlk.
Eucirroedia pampina Gn.
Euclidia cuspidae Hbn.
Eudryas grata F.
Eudryas unio Hbn.
Eueretagrotis attenta Grt.
Eueretagrotis perattenta Grt.
Eueretagrtois sigmoides Gn.
Eugraphe subrosea opacifrons Grt.X
Euparthenos nubilis Hbn.
Euplexia benesimilis McD.
Eupsilia devia Grt.
Eupsilia morrisoni Grt.
Eupsilia n. sp.
Eupsilia sidus Gn.S
Eupsilia tristigmata Grt.
Eupsilia vinulenta Grt.
Eurois occulta L.X
Eutolype rolandi Grt.
Euxoa albipennis Grt.
Euxoa bostoniensis Grt.
Euxoa campestris Grt.
Euxoa detersa Wlk.
Euxoa divergens Wlk.
Euxoa fumalis Grt.
Euxoa messoria Harr.
Euxoa mimallonis Grt.
Euxoa obeliscoides Gn.
Euxoa ochrogaster Gn.
Euxoa perpolita Morr.X
Euxoa redimicula Morr.
Euxoa scandens Riley
Euxoa tessallata Harr.
Euxoa velleripennis Grt.
Fagitana littera Gn.X
Faronta diffusa Wlk.
Feltia herilis Grt.
Feltia jaculifera Gn.
Feltia subgothica Haw.
Feltia tricosa Lint.
Feralia jocosa Gn.
Feralia major Sm.
Gabara subnivosella Wlk.S
Galgula partita Gn.
Graphiphora auger Fab.
Hadena capsularis Gn.
Harrisimemna trisignata Wlk.
Helicoverpa zea Boddie
Helotropha reniformis Grt.
Heptagrotis phyllophora Grt.
Himella fidelis Grt.R
Homoglaea hircina Morr.
Homohadena badistriga Grt.S
Homohadena infixa Wlk.
Homophoberia apicosa Haw.
Homorthodes furfurata Grt.
Hydraecia immanis Gn.X
Hydraecia micacea Esp.R
Hypena abalienalis Wlk.
Hypena atomaria Sm.
Hypena baltimoralis Gn.
Hypena bijugalis Wlk.
Hypena edictalis Wlk.
Hypena humuli Harr.
Hypena madefactalis Gn.
87
Hypena manalis Wlk.
Hypena palparia Wlk.
Hypena sordidula Grt.X
Hypenodes caducus Dyar
Hypenodes fractilinea Sm.
Hypenodes palustris FergusonR
Hyperstrotia secta Grt
Hyperstrotia villificans B. and McD.
Hypocoena inquinata Gn.
Hyppa xylinoides Gn.
Idia aemula Hbn.
Idia americalis Gn.
Idia concisa Wlk.
Idia denticulalis Harv.
Idia diminuendis B. and McD.
Idia forbesi French
Idia laurenti Sm.
Idia lubricalis Gey.
Idia rotundalis Wlk.
Idia scobialis Grt.
Ipimorpha pleonectusa Grt.
Lacanobia atlantica Grt.R
Lacanobia subjuncta G. and R.
Lacinipolia anguina Grt.
Lacinipolia lorea Gn.
Lacinipolia lustralis Grt.
Lacinipolia meditata Grt.
Lacinipolia olivacea Morr.
Lacinipolia renigera Steph.
Lascoria ambigualis Wlk.
Ledaea perditalis Wlk.
Lemmeria digitalis Grt.
Leucania adjuta Grt.
Leucania commoides Gn.
Leucania inermis Fbs.
Leucania insueta Gn.
Leucania lapidaria Grt.
Leucania linita Gn.
Leucania multilinea Wlk.
Leucania phragmatidicola Gn.
Leucania pseudargyria Gn.
Leucania ursula Fbs.
Leuconycta diphteroides Gn.
Leuconycta lepidula Grt.X
Ltihomia germana Morr.X
Lithophane amanda Sm.
Lithophane antennata Wlk.
Lithophane baileyi Grt.
Lithophane bethunei G. and R.
Lithophane disposita Morr.
Lithophane fagina Morr.
Lithophane georgii Grt.X
Lithophane grotei Riley
Lithophane hemina Grt.
Lithophane innominata Sm.
Lithophane laticinerea Grt.
Lithophane lepida Grt.SX
Lithophane oriunda Grt.
Lithophane patelaeta Wlk.
Lithophane petulca Grt.
Lithophane pexata Grt.
Lithophane querquera Grt.S
Lithophane semiusta Grt.X
Lithophane thaxteri Grt.X
Lithophane unimoda Lint.
Lomanaltes eductalis Wlk.
Luperina passer Gn.
Macrochilo absorptalis Wlk.
Macrochilo bivittata Grt.
Macrochilo hypocritalis Ferg.
Macrochilo litophora Grt.
Macrochilo louisiana Fbs.
Macrochilo orciferalis Wlk.
Macronoctua onusta Grt.
Magusa orbifera Wlk. (migrant)
Maliattha synochitis Gn.
Marathyssa basalis Wlk.
Marathyssa inficita Wlk.
Meganola minuscula Zell
Meganola spoida Francl.R
Melanchra adjuncta Gn.
Melanchra assimilis Morr.
Melanchra picta Harr.
Melanogramma auricinctaria Grt.
Melaporphyria immortua Grt.X
Meropleon diversicolor Morr.
Metalectra discalis Grt.
Metalectra quadrisignata Wlk.
Metaxaglaea inulta Grt.
Metaxaglaea viatica Grt.
Mocis latipes Gn. (migrant)
Morrisonia confusa Hbn.
88
Morrisonia evicta Grt.
Morrisonia latex Gn.
Nedra ramosula Gn.
Nephelodes minians Gn.
Noctua pronuba L.R
Nola cilicoides Grt.
Nola ovilla Grt.
Nola pustulata Wlk.
Nola triquetrana Fitch
Nycteola frigidana Wlk.X
Ochropleura plecta L.
Ogdoconta cinereola Gn.
Oligia bridghami G. and R.
Oligia chlorostigma Harv.R
Oligia crytora Francl.
Oligia exhausta Sm.
Oligia fractilinea Grt.
Oligia illocata Wlk.
Oligia mactata Gn.
Oligia modica Gn.
Oligia obtusa Sm.R
Ophiuche abjuralis Wlk.
Orthodes crenulata Butler
Orthodes cynica Gn.
Orthosia alurina Sm.
Orthosia hibisci Gn.
Orthosia revicta Morr.
Orthosia rubescens Wlk.
Paectes oculatrix Gn.
Palthis angulalis Hbn.
Palthis asopialis Gn.
Pangrapta decoralis Hbn.
Panopoda carneicosta Gn.
Panopoda rufimargo Hbn.
Panthea acronyctoides Wlk.
Panthea furcilla Pack.
Papaipema n. sp.
Papaipema arctivorens Hamp.
Papaipema baptisiae Bird
Papaipema eupatorii Lyman
Papaipema furcata Sm.
Papaipema impecuniosa Grt.
Papaipema inquaesita G. and R.
Papaipema lysimachiae BirdS
Papaipema nebris Gn.
Papaipema nepheleptena Dyar
Papaipema pterisii Bird
Papaipema rigida Grt.
Papaipema unimoda Sm.
Parahypenodes quadralis B.& Mc.DR
Parallelia bistriaris Hbn.
Parascotia mineta Francl.R
Parastichtis suspecta Hbn.
Peridroma saucia Hbn.
Phalaenophana pyramusalis Wlk.
Phalaenostola eumelusalis Wlk.
Phalaenostola hanhami Sm.
Phalaenostola larentioides Grt.
Phalaenostola metonalis Wlk.
Phlogophora iris Gn.
Phlogophora periculosa Gn.
Phoberia atomaris Hbn.
Phoberia orthosioides Gn.
Phosphila miseliodies Gn.X
Plagiomimicus pityochromus Grt.X
Plathypena scabra F.
Platypolia anceps Steph.XS
Plusia contexta Grt.
Plusia putnami Grt.
Plusia venusta Wlk.
Plusiodonta compressipalpis Gn.
Polia detracta Wlk.
Polia goodelli Grt.
Polia imbrifera Gn.
Polia nimbosa Gn.
Polia purpurissata Grt.
Polygrammate hebraeicum Hbn.
Polypogon cruralis Gn.
Polypogon laevigata Grt.
Polypogon lituralis Hbn.
Polypogon martha BarnesS
Polypogon n. sp.
Polypogon ochreipennis Grt.
Polypogon pedipilalis Gn.
Polypogon protumnusalis Wlk.
Protolampra brunneicollis Grt.
Protolampra rufipectus Morr.X
Protorthodes oviduca Gn.
Psaphida reumens Wlk.
Psectraglaea carnosa Grt.SX
Pseudaletia unipuncta Haw.
Pseudeustrotia carneola Gn.
89
Syngrapha rectangula W. Kby.
Tarachidia candefacta Hbn.
Tarachidia erastrioides Gn.
Thysania zenobia Cram.X (migrant)
Trachaea delicata Grt.
Tricholia signata Wlk.
Trichoplusia ni Hbn.
Trichordestra legitima Grt.
Trichordestra lilacina Harv.X
Trichosilia geniculata G. and R.
Ufeus plicatus Grt.R
Ufeus satyricus Grt.X
Ulolonche culea Gn.
Ulolonche modesta Morr.
Xanthia n. sp. (nr. togata Esp.)
Xestia adela Franel.
Xestia badicollis Grt.X
Xestia dilucida Morr.
Xestia dolosa Franel.
Xestia elimata Gn.RS
Xestia normaniana Grt.
Xestia smithii Snellen
Xylena cineritia Grt.S
Xylena curvimacula Morr.
Xylena nupera Lint.
Xylena thoracica Putnam-CramerX
Xylomoia chagnoni B. and McD.
Xylotype capax Grt.SX
Xystopeplus rufago Hbn.S
Zale aeruginosa Gn.
Zale curema Sm.S
Zale duplicata Bethune
Zale galbanata Morr.
Zale helata Sm.
Zale horrida Hbn.
Zale lunata Drury (migrant)
Zale lunifera Hbn.R
Zale metatoidse McD.SX
Zale mmerea Gn.
Zale obliqua Gn.S
Zale phaerapna Franel.RS
Zale submediana StrandS
Zale undularis Drury
Zale unilineata Grt.
Pseudeva purpurigera Wlk.
Pseudohermonassa biearnea Gn.
Pseudoplusia includens Wlk.
Pseudorthodes vecors Gn.
Psychomorpha epimenis Drury
Pyreferra ceromatica Grt.X
Pyreferra citrombra Franel.R
Pyreferra hesperidago Gn.
Pyreferra pettiti Grt.S
Pyrrhia adela Laf. and Milk
Pyrrhia exprimens Wlk.
Raphia frater Grt.
Redectis vitrea Grt.
Renia discoloralis Gn.
Renia flavipunctalis Gey.
Renia salusalis Wlk.
Rhizedra lutosa Hbn.R
Rivula propinqualis Gn.
Schinia arcigera Gn.
Schinia florida Gn.
Schinia lynx Gn.
Schinia nundina Drury
Schinia rivulosa Gn.
Schinia septentrionalis Wlk.
Schinia tuberculum Hbn.
Scolecocampa liburna Geyer
Scoliopteryx libatrix L.
Sideridis congermana Morr.S
Sideridis maryx Gn.S
Sideridis rosea Harv.
Simyra henrici Grt.
Spaelotis clandestina Harr.
Spargaloma sexpunelata Grt.
Spartiniphaga includens Wlk.
Spartiniphaga panatela Sm.
Spiramater lutra Gn.
Spotoptera exigua Hbn. (migrant)
Spodoptera frugiperda J. E. Smith
(migrant)
Spodoptera ornithogalli Gn.
(migrant)
Sunira bicolorago Gn.
Sutyna privata Wlk.
Synedoida grandirena Haw.R
Syngrapha abstrusa Eichlin
90
Class Insecta: Order Hymenoptera
The following list of 33 ant species from the Albany Pine Bush is extracted from the
work of Dolores Savignano (1990, 1994). Additional information was provided by Dr. Ryk P.
Spoor, Albany College of Pharmacy, and Dr. Stephen Cover, Museum of Camparative Zoology,
Harvard University.
Formicidae (Formincinae)
Camponotus americanus (Mayr)
Camponotus novaeboracensis (Fitch)
Camponotus pennsylvanicus (DeGeer)
Formica difficilis (Emery)
Formica exsectoides (Forel)
Formica lasioides (Emery)
Formica querquetulana (Ken. & Den.)
Formica subsericea (Say)
Formica incerta (Emery)
Formica nitidiventris (Emery)
Formica schaufussi (Mayr)
Lasius alienus (Foerster)
Lasius neoniger (Emery)
Paratrechina parvula (Mayr)
Polyergus lucidus (Mayr)
Prenolepis imparis (Say)
Formicide (Myrmicinae)
Acanthomyops interjectus (Mayr)
Aphaenogaster Rudis (Emery)
Aphaenogaster trachae (Forel)
Crematogaster cerai (Fitch)
Crematogaster linealata (Say)
Iridomyrmex pruinossus (Roger)
Leptothorax ambigeus (Emery)
Monomorium emaginatum (DuBois)
Myrmica americana (Weber)
Myrmica fractiorsis (Emery)
Myrmica pinetorune (Wheeler)
Pheidole pilifera (Roger)
Solenopsis molesia (Say)
Tetramorium caespirum (Linnaeus)
Formicidae (Dolichoderinae)
Dolichoderus plagiaus (Mayr)
Dolichoderus tascaenbergi (Mayr)
Tapinoma sessile (Say)
91
FISHES
The following list of 30 Albany Pine Bush fish species is taken from The Pine Bush
Intermunicipal Study (Bristol, Litynski, Wojcik, P.C. 1980). The taxonomic arrangement and
nomenclature follow Smith (1985).
Class Osteichthyes: Order Anguilliformes
Anguillidae
Anguilla rostrata ( Lesueur)
American eel Blockhouse Creek, Hunger Kill, Kaikout Kill, Stuyvesant Plaza Pond
Class Osteichthyes: Order Siluriformes
Ictaluridae
Ictalurus natalis (Lesueur)
Yellow bullhead Lake Rensselaer, Lisha Kill
Ictalurus nebulosus (Lesueur)
Brown bullhead Stuyvesant Plaza Pond, Lake Rensselaer, Lisha Kill, Glass Pond
Class Osteichthyes: Order Cypriniformes
Catostomidae
Catostomus catostomus (Forster)
Longnose sucker Lake Rensselaer
Catostomus commersoni (Lacepede)
White sucker Glass Pond, Hunger Kill, Lisha Kill, East Branch Hunger Kill
Cyprinidae
Carassius auratus (Linnaeus) (introduced from eastern Asia, China)
Goldfish Glass Pond, East Branch Hunger Kill, Lisha Kill
Cyprinus carpio Linnaeus (introduced from Europe, temperate Asia)
Common carp Lisha Kill, Lake Rensselaer
Notemigonus crysoleucas (Mitchill)
Golden shiner Lake Rensselaer, Stuyvesant Plaza Pond, Glass Pond
Rhinichthys atratulus (Mermann)
Eastern blacknose dace Lisha Kill, East Branch Hunger Kill
Rhinichthys cataractae (Valenciennes)
Longnose dace Lisha Kill
Semotilus atromaculatus (Mitchill)
Creek chub Lisha Kill
Semotilus margarita (Cope)
Pearl dace Glass Pond, East Branch Hunger Kill
Notropis cornutus (Mitchill)
Common shiner Glass Pond, Lisha Kill
Pimephales notatus (Rafinesque)
Bluntnose minnow Lisha Kill
Pimephales promelas (Rafinesque)
Fathead minnow Glass Pond
92
Class Osteichthyes: Order Salmoniformes
Salmonidae
Salmo trutta Linnaeus (introduced from Europe, western Asia)
Brown trout Hunger Kill
Salvelinus fontinalis (Mitchill)
Brook trout Glass Pond, Hunger Kill, Kaikout Kill
Esocidae
Esox lucius Linnaeus
Northern pike Lake Rennselaer (stocked)
Class Osteichthyes: Order Atheriniformes
Cyprinodontidae
Fundulus diaphanus (Lesueur)
Banded killfish Hunger Kill, Glass Pond
Class Osteichthyes: Order Perciformes
Centrarchidae
Ambloplites rupestris (Rafinesque)
Rock bass Lisha Kill, Lake Rensselaer
Lepomis gibbosus (Linnaeus)
Pumpkinseed Lake Rensselaer, Glass Pond, Lisha Kill, Stuyvesant Plaza Pond
Lepomis macrochirus Lacepede
Smallmouth bass Lisha Kill, Lake Rensselaer (stocked)
Micropterus salmoides (Lacepede)
Largemouth bass Glass Pond, Lake Rensselaer, Lisha Kill, Stuybesant Plaza Rd
Pomoxis nigromaculatus (Lesueur)
Black crappie Lake Rensselaer, Stuyvesant Plaza Pond
Percidae
Etheostoma olmstedi (Storer)
Tessellated darter Lisha Kill
Perca flavescens (Mitchill)
Yellow perch Lake Rensselaer, Lisha Kill, Stuyvesant Plaza Pond
Percina caprodes (Rafinesque)
Logperch Lisha Kill
Stizostedion vitreum (Mitchill)
Walleye Lake Rensselaer (stocked)
Class Osteichthyes: Order Scorpaeniformes
Cottidae
Cottus cognatus Richardson
Slimy sculpin East Branch Hunger Kill, Hunger Kill, Kaikout Kill
93
AMPHIBIANS AND REPTILES
The list of amphibians and reptiles recorded from the Albany Pine Bush is derived from
the work of Stewat and Rossi (1981) and named according to the Society for the Study of
Amphibians and Reptiles' list of Standard Common and Current Scientific Names for North
American Amphibians and Reptiles (Collins 1997). Stewart and Rossi's work was based on
detailed study of museum specimens, literature records dating as far back as 1835, and personal
observations of competent herpetologists from 1949 to 1977. Some additions have been made to
the list since then. Several species listed here have not been found in more recent years
(Hunsinger 1999).
Class Amphibia: Order Caudata
Ambystomatidae
Ambystoma jeffersonianum (Green)
Jefferson salamander
Ambystoma laterale Hallowell
Blue-spotted salamander
Ambystoma maculatum (Shaw)
Spotted salamander
Plethodontidae
Desmognathus fuscus (Green)
Northern dusky salamander
Eurycea bislineata (Green)
Northern two-lined salamander
Plethodon cinereus (Green)
Northern redback salamander
Salamandridae
Notophthalamus viridescens viridescens (Rafinesque)
Red-spotted newt
Class Amphibia: Order Anura
Bufonidae
Bufo americanus americanus Holbrook
Eastern American toad
Bufo fowleri Hinckley
Fowler's toad
Hylidae
Pseudacris crucifer (Wied-Neuwied)
Spring peeper
Hyla versicolor (LeConte)
Gray treefrog
Pelobatidae
Scaphiopus holbrookii (Harlan)
Eastern spadefoot
Ranidae
Rana catesbeiana (Shaw)
94
Bullfrog
Rana clamitans (Latreille)
Green frog
Rana pipiens (Schreber)
Northern leopard frog
Rana sylvatica (LeConte)
Wood frog
Class Reptilia: Order Testudines
Chelydridae
Chelydra serpentina serpentina (Linnaeus)
Common snapping turtle
Kinosternidae
Sternotherus odoratus (Latreille)
Common musk turtle
Emydidae
Chrysemys picta (Schneider)
Painted turtle
Clemmys guttata (Schneider)
Spotted turtle
Clemmys insculpta (LeConte)
Wood turtle
Terrapene carolina caroline (Linnaeus)
Eastern box turtle
Trachemys scripta elegans (Wied-Neuwied)
Red-eared slider
Class Reptilia: Order Squamata, Suborder Serpentes
Colubridae
Carphophis amoenus amoenus (Say)
Eastern worm snake
Coluber constrictor constrictor (Linnaeus)
Northern black racer
Elaphe obsoleta obsoleta (Say)
Black rat snake
Heterodon platirhinos (Latreille)
Eastern hognose snake
Lampropeltis triangulum triangulum (Lacepede)
Eastern milk snake
Liochlorophis vernalis (Harlan)
Smooth green snake
Nerodia sipedon sipedon (Linnaeus)
Northern water snake
Storeria dekayi dekayi (Holbrook)
Northern brown snake
Storeria occipitomaculata (Storer)
95
Redbelly snake
Thamnophis sirtalis sirtalis (Linnaeus)
Eastern garter snake
96
BIRDS
The following list of birds recorded from the Albany Pine Bush was provided by Neil
Gifford, Conservation Director, Albany Pine Bush. It is current as of August 2011.
Ducks, Geese, Swans
Branta canadensis
Anas platyrhynchos
Aix sponsa
Goose, Canada
Mallard
Duck, Wood
Grouse, Turkeys, Pheasants
Meleagris gallopavo
Turkey, Wild
Bonasa umbellus
Grouse, Ruffed
Herons, Bitterns
Butorides striatus
Ardea herodias
.
Heron, Green-backed
Heron, Great Blue
Hawks, Falcons, Eagles, Vultures
Cathartes aura
Vulture, Turkey
Accipiter striatus
Hawk, Sharp-shinned
Accipiter cooperii
Hawk, Cooper's
Buteo lineatus
Hawk, Red-shouldered
Buteo jamaicensis
Hawk, Red-tailed
Falco sparverius
Kestrel, American
Accipiter gentilis
Goshawk
Plovers, Sandpipers
Charadrius semipalmatus
Charadrius vociferus
Tringa solitaria
Actitus macularia
Scolopax minor
Plover, Semipalmated
Killdeer
Sandpiper, Solitary
Sandpiper, Spotted
Woodcock, American
Gulls, Terns
Larus delawarensis
Larus argentatus
Larus marinus
Gull, Ring-billed
Gull, Herring
Gull, Great black-backed
Doves, Pigeons
Columba livia
Dove, Rock
97
Zenaida macroura
Dove, Mourning
Cuckoos
Coccyzus americanus
Coccyzus erythropthalmus
Cuckoo, Yellow-billed
Cuckoo, Black-billed
Owls
Bubo virginianus
Strix varia
Otus asio
Aegolius acadicus
Owl, Great Horned
Owl, Barred
Owl, Screech
Owl, Saw-whet
Swifts, Hummingbirds
Chaetura pelagica
Archilochus colubris
Swift, Chimney
Hummingbird, Ruby-throated
Kingfishers
Ceryle alcyon
Kingfisher, Belted
Woodpeckers
Melanerpes carolinus
Sphyrapicus varius
Picoides pubescens
Picoides villosus
Dryocopus pileatus
Colaptes auratus
Woodpecker, Red-bellied
Sapsucker, Yellow-bellied
Woodpecker, Downy
Woodpecker, Hairy
Woodpecker, Pileated
Flicker, Northern
Flycatchers, Kingbirds
Contopus virens
Empidonax
alnorum/traillii
Sayornis phoebe
Myiarchus crinitus
Tyrannus tyrannus
Wood-pewee, Eastern
Flycatcher, Traill's
(Alder/Willow)
Phoebe, Eastern
Flycatcher, Great crested
Kingbird, Eastern
Vireos
Vireo flavifrons
Vireo solitarius
Vireo olivaceus
Vireo philadelphicus
Vireo gilvus
Vireo, Yellow-throated
Vireo, Blue-headed
Vireo, Red-eyed
Vireo, Philadelphia
Vireo, Warbling
98
Crows, Jays
Cyanocitta cristata
Corvus brachyrhynchos
Corvus ossifragus
Corvus corax
Jay, Blue
Crow, American
Crow, Fish
Raven, Common
Swallows
Tachycineta bicolor
Progne subis
Riparia riparia
Hirundo rustica
Swallow, Tree
Martin, Purple
Swallow, Bank
Swallow, Barn
Chickadees, Titmice
Parus bicolor
Parus atricapillus
Titmouse, Tufted
Chickadee, Black-capped
Creepers
Certhia americana
Creeper, Brown
Nuthatches
Sitta carolinensis
Sitta canadensis
Nuthatch, White-breasted
Nuthatch, Red-breasted
Wrens
Troglodytes aedon
Troglodytes troglodytes
Thryothorus ludovicianus
Wren, House
Wren, Winter
Wren, Carolina
Kinglets, Gnatcatchers
Regulus calendula
Regulus satrapa
Kinglet, Ruby-crowned
Kinglet, Golden-crowned
Thrushes
Sialia sialis
Hylocichla mustelina
Catharus fuscescens
Catharus minimus
Catharus ustulatus
Catharus guttatus
Turdus migratorius
Bluebird, Eastern
Thrush, Wood
Veery
Thrush, Gray-cheeked
Thrush, Swainson's
Thrush, Hermit
Robin, American
99
Mockingbirds, Thrashers
Dumetella carolinensis
Mimus polyglottos
Toxostoma rufum
Catbird, Gray
Mockingbird, Northern
Thrasher, Brown
Starlings
Sturnus vulgaris
Starling, European
Waxwings
Bombycilla cedrorum
Waxwing, Cedar
Warblers
Vermivora pinus
Vermivora chrysoptera
Oreothlypis peregrina
Vermivora ruficapilla
Parula americana
Dendroica pensylvanica
Dendroica tigrina
Dendroica magnolia
Dendroica coronata
Mniotilta varia
Dendroica caerulescens
Dendroica fusca
Dendroica virens
Dendroica discolor
Dendroica castanea
Dendroica striata
Dendroica pinus
Dendroica
Dendroica petechia
Wilsonia canadensis
Wilsonia citrina
Oporornis philadelphia
Seiurus aurocapillus
Seiurus noveboracensis
Geothlypis trichas
Setophaga ruticilla
Warbler, Blue-winged
Warbler, Golden-winged
Warbler, Tennessee
Warbler, Nashville
Parula, Northern
Warbler, Chestnut-sided
Warbler, Cape May
Warbler, Magnolia
Warbler, Myrtle
Warbler, Black-and-white
Warbler, Black-throated Blue
Warbler, Blackburnian
Warbler, Black-throated Green
Warbler, Prairie
Warbler, Bay-breasted
Warbler, Blackpoll
Warbler, Pine
Warbler, Yellow palm
Warbler, Yellow
Warbler, Canada
Warbler, Hooded
Warbler, Mourning
Ovenbird
Waterthrush, Northern
Yellowthroat, Common
Redstart, American
Tanagers
100
Piranga olivacea
Tanager, Scarlet
Sparrows
Pipilo erythrophthalmus
Spizella pusilla
Spizella passerina
Melospiza lincolnii
Melospiza melodia
Melospiza georgiana
Zonotrichia albicollis
Zonotrichia leucophrys
Junco hyemalis
Towhee, Eastern
Sparrow, Field
Sparrow, Chipping
Sparrow, Lincoln's
Sparrow, Song
Sparrow, Swamp
Sparrow, White-throated
Sparrow, White-crowned
Junco, Slate-colored
Cardinals, Grosbeaks, Buntings
Pheucticus ludovicianus
Grosbeak, Rose-breasted
Cardinalis cardinalis
Cardinal, Northern
Passerina cyanea
Bunting, Indigo
Blackbirds, Orioles, Cowbirds
Agelaius phoeniceus
Blackbird, Red-winged
Quiscalus quiscula
Grackle, Common
Molothrus ater
Cowbird, Brown-headed
Icterus galbula
Oriole, Baltimore
Icterus spurius
Oriole, Orchard
Finches
Carpodacus purpureus
Carpodacus mexicanus
Loxia curvirostra
Carduelis pinus
Carduelis tristis
Finch, Purple
Finch, House
Crossbill, Red
Siskin, Pine
Goldfinch, American
Weaver Finches
Passer doesticus
Sparrow, House
101
MAMMALS
The following list of mammals recorded from the Albany Pine Bush was compiled by
combining lists from Miller (1976) and The Pine Bush Intermunicipal Study (Miller 1980).
Roland Kays (RK) of the New York State Museum provided new data. Taxa are arranged
accordeing to Whitaker and Hamilton (1998). The northern myotis, previously regarded as an
eastern forest Keen's bat, is now considered a seperate species. The native red fox of the United
States was long recognized as a separate species, Vulpes fulva, but recently acquired evidence
indicates that it is the same as the Old World red fox.
Class Mammalia: Order Didelphimorphia
Didelphidae
Didelphis virginiana (Kerr)
Virginia opossum
Class Mammalia: Order Insectivora
Soricidae
Blarina brevieauda (Say)
Northern short-tailed shrew
Sorex cinereus (Kerr)
Masked shrew
Talpidae
Condylura cristata (Linnaeus)
Star-nosed mole
Parascalops breweri (Bachman)
Hairy-tailed mole
Class Mammalia: Order Chiroptera
Vespertilionidae
Eptesicus fuscus (Palisot de Beauvois)
Big brown bat
Lasiurus borealis (Muller)
Eastern red bat
Myotis lucifugus (LeConte)
Little brown myotis
Myotis septentrionalis (Trouessart)
Northern myotis
Class Mammalia: Order Lagomorpha
Leporidae
Sylvilagus floridanus (Allen)
Eastern cottontail
Class Mammalia: Order Rodentia
Scruridae
Glaucomys volans (Linnaeus)
102
Southern flying squirrel
Marmota monas (Linnaeus)
Woodchuck, groundhog
Sciurus carolinensis (Gmelin)
Eastern gray squirrel
Tamias striatus (Linnaeus)
Eastern chipmunk
Tamiasciurus hudsonicus (Erxleben)
Red squirrel, chickaree
Dipodidae (Zapodinae)
Napaeozapus insignis (Miller)
Woodland jumping mouse
Zapus hudsonius (Zimmermann)
Meadow jumping mouse (extremely rare)
Muridae (Arvicolinae)
Clethrionomys gapperi (Vigors)
Southern red-backed vole
Microtus pennsylvanicus (Ord)
Meadow vole
Microtus pinetoru (LeConte)
Woodland vole (RK: new record)
Ondatra zibethicus (Linnaeus)
Common muskrat
Muridae (Murinae)
Mus musculus (Linnaeus)
House mouse
Rattus norvegicus (Berkenhout)
Norway rat, brown rat
Muridae (Sigmodontinae)
Peromyscus leucopus (Rafinesque)
White-footed mouse
Peromyscus maniculatus (Wagner)
Woodland deer mouse
Erethizontidae
Erethizon dorsatum (Linnaeus)
North American porcupine (RK: new record)
Class Mammalia: Order Carnivora
Canidae
Canis latrans (Say)
Coyote
Urocyon cinereoargenteus (Schreber)
Gray fox
Vulpes vulpes (Linnaeus)
Red fox
Ursidae
103
Ursus americanus (Pallas)
Black bear (rare visitor)
Procyonidae
Procyon lotor (Linnaeus)
Common raccoon
Mustelidae
Martes pennanti (Erxleben)
Fisher (RK: new record)
Mustela erminea (Linnaeus)
Ermine (short-tailed weasel)
Mustela frenata (Lichtenstein)
Long-tailed weasel
Mustela vison (Schreber)
Mink (extremely rare)
Mephitidae
Mephitis mephitis (Schreber)
Striped skunk
Felidae
Felis catus (Linnaeus)
Domestic cat
Lync rufus (Schreber)
Bobcat (rare visitor; RK: new record)
Class Mammalia: Order Artiodactyla
Cervidae
Odocoileus virginianus (Zimmermann)
White-tailed deer
104
Appendix(B:(Representative(Site(Photographs!
Photos by Mary Brickle
(above and below): A view of the "great dune" - the longest
sand dune in the preserve
105
Landscapes
(above and below): The most desirable pine barrens landscape
in the park; taken near Kings Road, to the west of Karner
Barrens West trail
106
(above and below): Further examples of a healthy pine barrens
landscape; taken near Karner Barrens West
107
(above and below): Section of the preserve burned in the past 2-3 years;
the canopy is of a desirable quality (open, pitch pine dominated)
108
(above): An intermittent pool found in Albany Pine Bush
109
Education*and*Access*
(above): The Discovery Center at Albany Pine Bush
(below): Example of signage at the site
110
111
Management
(above): Habitat Management in progress at Albany Pine Bush
(below): Area recently cleared of invasive black locust forest and reseeded
112
(above and below): Area recently cleared of invasive
black locust forest and reseeded
113
(above): Sprouting pitch pine seedlings
(below): A patch of protected prairie willow
114
Flora&and&Fauna&
(left): A large flowering lupine; taken on the Yellow Trail, near the
lower section of the great dune
(right and below): A male karner blue butterfly is being released
115
(above): The Great Spangled Fritillary resting on a Milkweed plant
(below): The Inland Barrens Buckmoth Caterpillar
116
Examples of desirable undergrowth in pitch pine-scrub oak ecosystem
(above): dwarf chestnut oak. (below): wild lupine, blueberry, and sweet fern
117
(above and below): Examples of prescribed fire management in the preserve
Photos by Neil Gifford
118
(above): Wild black and red raspberries found in the park
(below): Wild blueberries growing in Albany Pine Bush
119