gowings swamp botanic hist or report
TRANSCRIPT
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GGoowwiinngg’’ss SSwwaammpp
aanndd TThhoorreeaauu’’ss BBoogg An Historic Wetland in Concord, MA
HISTORICAL SURVEY AND BOTANICAL INVENTORY
Published by Sudbury Valley Trustees, April 2010
Researched and prepared by Cherrie Corey, consulting naturalist
Project made possible through the generous support of the
Concord-Carlisle Community Chest and neighbors of Gowing’s Swamp
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Gowing’s Swamp, Historical Survey and Botanical Inventory 2009 -- 2
...It is in vain to dream of a wildness distant from ourselves. There is none such. It is the bog
in our brain and bowels, the primitive vigor of Nature in us, that inspires that dream..Consider how remote and novel that [Gowing's] swamp. Beneath it is a quaking bed of
sphagnum, and in it grow Andromeda polifolia, Kalmia glauca, Menyanthes, Gaylussacia
dumosa, Vaccinium oxycoccus, plants which scarcely a citizen of Concord ever sees. It would
be as novel to them to stand there as in a conservatory, or in Greenland...
Henry David Thoreau - August 30, 1856
Purpose of this ProjectThis project was undertaken to provide a consolidated historical summary and updated
botanical inventory and assessment of Gowing’s Swamp, a historically and scientifically
significant bog complex and glaciated landscape located in Concord, MA and partially ownedand stewarded by Sudbury Valley Trustees. In a time when there is both increasing public
interest in and potential development pressures on this ecologically rare and sensitive
landscape, this report provides a basis for determining future stewardship and conservationmanagement priorities, as well as a comprehensive benchmark from which to gauge changes
over time. The survey will also provide a basis for interpretation opportunities and
educational program planning.
Introduction and Summary
Gowing’s Swamp, an 8.9 acre wetland complex, is nestled within Concord’s agricultural EastQuarter and its American Mile historic
district, a short walk from famed
Meriam’s Corner. As both a uniquelycomplex wetland ecosystem and a
beautiful geologically sculpted
landscape, Gowing’s Swamp has madeits mark in literary and scientific
circles for more than 150 years. It
remains one of the longestcontinuously studied natural areas in
Concord, MA, if not beyond.
Gowing’s Swamp’s ecology and florarepresent a locally rare and thriving
example of a level bog ecosystem in the midst of a populated suburban neighborhood. It’sfloating sphagnum mat, ‘exotic’ northern plant community, and its serene location attractedThoreau’s devoted attention in the mid-19
thc., resulting in its continuous scientific study and
documentation on through the present. It is the crucible within which our modern scientific
understanding of peatland biochemistry and ecology in New England and more generally wasrefined.
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Gowing’s Swamp holds a place in literature and historical accounts as a landscape that
transports and transforms its visitors. It likely was an important natural and spiritual resourcefor this area’s earliest peoples as evidenced in a rich archaeological record (see Appendix A).
The historic cart path and agricultural fields to the east of the wetland were once part of
Concord’s Great Field. Now preserved, they continue to provide the experience of the
landscape as it was more than 350 years ago. The Minutemen passed along the bog’sshoreline on approach to their engagement with British soldiers at Meriam Corner on April
19, 1776. It has inspired many of Concord’s luminaries and those who study them from afar.
The juxtaposition of Gowing’s Swamp to town designated open spaces and the interlacing of trail networks continues to provide ongoing access for public enjoyment and foraging
wildlife. Without question, this special landscape continues to offer significant scientific and
public educational opportunities and nourishes, informs, and inspires all who walk its trails.
Plant Community Survey and Botanical Inventory
Contents of Botanical Review1. Plant community descriptions, including community structure and species
composition based on site visits which were conducted from January – December
2009.2. Lists of vascular plants, lichens, and a sampling of fungi. Lists include scientific
names based on Gleason and Cronquist’s Manual of Vascular Plants of NortheasternUnited States and Adjacent Canada and Sorrie and Somers’ Vascular Plants of
Massachusetts: A County Checklist . Two vascular plant lists include:
• Vascular species listed by site to indicate what is growing in each habitat andthe species relative abundance in that habitat.
• A complete list of all vascular and non-vascular plant species arranged
alphabetically by botanical family to show the total number of species, their
families, and rare or invasive status for the entire property.
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3. Plant Community and Trail Map.
4. The botanical inventory and photo documentation of prominent plant species and
significant fungi and lichen species will be shifted to a Filemaker database and made
available by the consulting botanist in 2010.
Summary of Botanical Findings1. Four prominent natural communities make up the landscape in and around Gowing’s
Swamp, and are described according to the Massachusetts draft list of natural
communities:
• Level bog with kettlehole level bog sub-community
• Woodland vernal pools – east, south, and west
• Mixed Deciduous Oak-White Pine forest (with overlapping sub-communities)
• Field and hedgerows
2. A total of 220 vascular and non-vascular species were identified on approximately
22.4 acres of wetland and terrestrial habitat (inclusive in contiguous properties owned
by Sudbury Valley Trustees (SVT), Meriam Close Conservation Trust, and residentPaul Ware) with a total of 26 introduced or cultivated non-native species (or 12% of
the total species). Gowing’s Swamp’s level bog and level kettlehole bog habitats
comprise 8.9 acres of the survey area.
3. Gowing’s Swamp’s locally rare hydrogeology and botanical profile, it’s long historyof scientific and literary interest and documentation, and its relatively pristine
condition give it importance as one of the town’s and the region’s most significant
wetlands
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4. Gowing’s Swamp’s 8.9 acre level bog community appears to be comprised entirely of
native plant species.5. Two healthy stands of black spruce grow in Gowing’s Swamp. Black spruce is locally
rare in southern New England and this is the only known remaining station within the
town of Concord.
6. A dense tangle of invasive species dominates the eastern shoreline of Gowing’sSwamp and the field edges that abut it, providing a vigorous and self-perpetuating
seed source for the entire area. Eradication of these invasive plants (listed below)
along the northeastern corner of SVT property needs to be given high priority.Isolated patches of purple loosestrife east and north of the swamp ought to be
addressed as well. Buckthorn is taking hold in the forest understory, eventually
threatening native shrubs and wild flowers, and should be removed as resources allow.7. Rare or unusual plants for the property and the area include:
• Black spruce ( Picea marianna)
• Bog rosemary ( Andromeda polifolia)
• Bog or pale laurel ( Kalmia polifolia)
• Purple pitcher-plant (Sarracenia purpurea)• Round-leaved sundew ( Drosera rotundifolia)
• Small-flowered cranberry (Vaccinium oxycoccus)
• Tawny cotton sedge ( Eriophorum virginicum)
• 53 lichen species, including 3 not found elsewhere in the local area (Cladonia
incrassata, Parmeliopsis subambigua, and Pseudevernia consocians)
• Mountain holly ( Nemopanthus mucronatus)
The entire area in and around Gowing’s Swamp is part of a 2008 designated NHESP PriorityHabitat area.
Stewardship Recommendations
Protect sensitive species in their habitats
Plan public access guidelines, educational programs, and management/conservation prioritiesthat safeguard the plants and natural communities listed below
• Kettlehole level bog (southern end of wetland) – black spruce, purple pitcher-plant, bog rosemary, pale laurel, small-flowered cranberry, round-leaved sundew and
affiliated lichen species; a smaller dispersed ring of black spruce, tamarack, purple pitcher-plant, bog rosemary and associated lichen species grows in a shallower
kettlehole depression on the NW end of the wetland
• Three connected certified vernal pools (including Gowing’s Swamp and two outer
pools), plus one isolated woodland vernal pool, reside within the survey area. All butthe isolated vernal pool (on private property) are owned (or partially owned) and
monitored by SVT. All are state certified.
• Several hundred pink ladyslipper plants (Cyprepedium acaule) thrive in the forested
areas to the west and north of Gowing’s Swamp. One identified location for
rattlesnake plantain exists at the height of the western ridge. Though both species are
fairly common and widely distributed, orchids are difficult to propagate, grow veryslowly, and are often targets of poaching by aspiring gardeners.
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Control invasive exotic species according to sensitivity of the species/plant community they
impact, degree of invasiveness, and feasibility of control over time.
Priority:
• Oriental bittersweet, multiflora rose, buckthorn, and Japanese honeysuckle along the
eastern shoreline comprise 95% of all plants along ENE shoreline of Gowing’s
Swamp
• Purple loosestrife in two locations: 1) the field along northeastern shoreline (part of Meriam Close Conservation Trust), and 2) in the private meadow (LeBlanc
conservation restriction) bordering SVT’s southeastern property line. While the
meadow is currently mowed each fall, consider talking to property owner aboutoptions for collaborative control of this plant.
•
Isolated barberries appear in a few edge locations around the survey area. Remove asfound.
Secondary:
• Buckthorn along northern and eastern shoreline (dense colony) and path and in forestunderstory along SE esker trail
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Tertiary:
• Buckthorn along SW shoreline and in forest understory down to shoreline on westernslope and around isolated woodland vernal pool
• Isolated autumn olive seedlings on northern edge of wet meadow and eastern edge of
cart path near outer, eastern pool. Large autumn olive shrubs alongwoodland/cemetery boundary can be left as resource for neighborhood harvest and
public education.
• Monitor large stand of Japanese knotweed along eastern shore of eastern vernal pool.Explore best measures to eradicate or control it.
Consider appropriate public uses
• Public access into Gowing’s Swamp and onto its floating sphagnum mat in non-winter months should be discouraged to prevent trampling or collecting of sensitive species
and potential for personal injury.
• Public programs generally should be limited to 16 participants including the leader to
minimize impact• Dog walking guidelines and/or
restrictions should be thoughtfullyconsidered. Numerous off-leash dogs
and their owners have walked the
wetland’s perimeter trail on a daily basis for decades – and are some of the
area’s most ardent preservation
supporters. At minimum, recommendowners clean up after their dogs and
keep them on lead when close to
shoreline (for safety of both thewetland and dogs).
The shorelines receive the most impact from wandering visitors and dogs. The sparse
herbaceous layer in the woodlands appears to receive relatively little damage, and theareas most sensitive wetland plants are inaccessible during the growing season,
damage due to trampling appears to be minimal. Consider posting use guidelines thatemphasize both protection of the area and the enjoyment of its visitors.
Study Potential Impact of Closing Historic Outflow Channel, east side
• With the goal of preserving Gowing’s Swamp’s natural ombrotrophic condition, the
consulting botanist recommends consulting with hydrologists Harry Hemond (MIT),Charlie Harvey (MIT), and bog ecologists regarding the relative long-term ecological
impact of keeping the historical eastern outflow channel open or filling it in.
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Educational Program Opportunities Gowing’s Swamp, and the forested glacial bowl it
occupies, has long provided an inspirational refuge
for naturalists and writers, an outdoor laboratoryfor the scientific community, and an open-air
classroom for students of all ages from both withinand well beyond Concord. The beauty and rich
historic and scientific resources within and around
Gowing’s Swamp offer a wide range of public
education and school curricular opportunities.
These may include general interpretive walks,
primary/secondary/college field trips and studies,student internships and special projects, outdoor
laboratory for naturalist and teacher training. Program topics can include (but are not limited
to) Thoreau studies, bog ecology, local hydrogeology, botany and plant communities,Concord’s agrarian and land use history, and local archaeological history.
Opportunities for ongoing research1. Confirm identification and update nomenclature of species in plant inventory2. Update species inventory over time
3. Monitor populations of sensitive plant species listed above4. Conduct inventories of butterflies/moths and dragonflies/damselflies giving special
attention to the possibility of any rare bog-dwelling species that might be found here
(ebony and banded boghaunter dragonflies, pitcher-plant borer moth, bog elfin butterfly)
5. Long-term water sampling:
Work with local specialist to develop a pH monitoring system and schedule for
Gowing’s Swamp and Thoreau’s bog. Sampling records can help determine obviousshifts in pH and locations of these shifts
6. Couple pH monitoring with shoreline and aquatic plant surveys within 20’ of mean
high water levels. Track introduction or spread of species indicative of pH shifts in thewetland.
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SITE DESCRIPTION
Gowing’s Swamp’s, an 8.9
acre level bog surrounded
by a geologically sculptedlandscape, occupies a long,
heart-shaped basin at the
center of 23 acres of woodland, wetlands, and
bordering fields. Situatedabove a groundwater
divide, Gowing’s Swamp
depends solely on rainwater for its recharge
(ombrotrophic) and is
consequently deficient inthe life supporting nutrients(ogliotrophic) necessary for
most common wetland
species of plants and other organisms. The dry, porous upland slopes support a mixed hardwood forest covering 50% of
the survey area. Three certified vernal pools lie to the east, south, and west of Gowing’s
Swamp, with the first two being connected by drainage channels to the bog. At the southernend of Gowing’s Swamp, a mature kettlehole level bog has filled in a deeper depression with
about one acre of an open sphagnum mat covered with bog rosemary, pale laurel, pitcher-
plants, sundews, cranberries, tawny cotton grass, and leatherleaf, ringed by tamarack and a
thriving stand of black spruce, and by an outer encircling tangle of maleberry, highbush blueberry, and leatherleaf ( see photo above). This smaller bog-within-a-bog is historically
known as Thoreau’s Bog in honor of Thoreau’s considerable scientific, philosophical, and
spiritual interest in it. Gowing’s Swamp is the last known, remaining location of black sprucein Concord and is locally rare in southern New England. Lichen species specific to these bog
and northern dwelling trees are diverse and numerous and include some locally unusual
species.
The 2010 fieldwork and inventory confirm that Gowing’s Swamp is a thriving level bog north
to south, containing the kettlehole level bog on its southern end and a dense peat layer supporting additional black spruce and tamarack on the northern end. (Previously, in
scientific papers and general articles, the surrounding wetland has been described as a redmaple swamp, which it is not, though occasional red maples do take hold in its eastern half
due to abundant seed sources along the shoreline.)
A trail encircles Gowing’s Swamp and connects on all sides to both public and private trail
networks, many with well-documented histories from Colonial times to the present. Thesetrails form a hub to an extensive, radiating network of federal, state, and local trails,
including: Minuteman National Historic Park trails to the southeast, East Quarter Farm
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Community Gardens and town trail to the east, Great Meadows National Wildlife Refuge
trails to the northeast, the Bay Circuit Trail to the northeast and west connecting to historictown trails in Concord Center, the Moses Pond trail to the northwest, and the American Mile
historic district to the south. Increasingly these trails are enjoyed by both local residents and
visitors and provide vast interpretive, educational, and recreational opportunities.
Gowing’s Swamp is also centrally located to contiguous tracks of town-designated open
space, providing a central link to active wildlife corridors. Local trackers and neighborhood
reports confirm a variety of wild creatures that live and forage in this vital area. The bogwaters and three outer vernal pools are breeding sites for spotted salamanders, wood frog,
pickerel frog, green frog, spring peepers, and gray tree frogs. Fox, fisher, coyote, skunk, deer,
raccoon, garter snake, and a variety of rodents frequent the woodland and fields. Opossumare occasionally seen and otter sign has been documented in the area. A variety of birds
frequent and inhabit the bog and surrounding woodland and thickets. A list of those seen by
and reported to this reviewer is included in Appendix B. A sampling of notable insectsincludes Appalachian brown, mourning cloak, sulfur, and monarch butterflies; primrose moth;
and several species of dragonflies including ebony jewelwing.
Site Location Gowing’s Swamp is located in Concord, Massachusetts (42º27’43”N, 71º19’42”W) just
below the eastern terminus of Revolutionary Ridge, one-quarter mile northwest of Meriam
Corner (intersection of Lexington/Old Bedford roads), and behind and southwest of theRipley School. Public access and parking is recommended from the Ripley School parking
lot at the end of Meriam Rd.
HISTORICAL REVIEW
Early Settlement and Land Use Summary• Indigenous presence: 12,000-1632 years ago
• First clearing for agriculture: between 7000-1000 years ago
• Great Field: 1650-1750, with field areas persisting into 21st
c.
• Minutemen route across Great Field and down old cart road – April 19, 1776
• Jabez Gowing purchases Lexington Rd. house and fields extending to bog in 1830’s,appears on 1852 town map
• Thomas Burke purchases house and 50 acres (including fields east of GS) in 1871
• Irish and Italian immigrant expand market-based farming in East Quarter: 1900
• Catholic cemetery appears on Beers Pub. map, early 1870’s
• Ditching of wetlands for field irrigation (late 1800’s – early 1900’s)
• Gleason photos of Gowing’s Swamp: 1920’s
• Independence Road development: early 1940’s
• All but one irrigation drain filled in: 1930’s
• Chestnut blight begins: 1940’s
• Ripley School built: 1960’s
• State proposes rerouting of Rte. 62 through sandpit on Lexington Rd., across
Gowing’s Swamp to Old Bedford Road: early 1960’s
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• Eaton’s botanical survey, MAS monograph “Gowing’s Swamp”: 1969
• Harold Hemond (MIT) begins hydrogeologic study: late 1970’s, first monograph inearly 1980’s
• Meriam Close development and conservation trust (early 1980’s)
• Burke Farm land sold to town: 2005 (Photo: view west across field toward Gowing’s
Swamp)
• Cemetery expands into remaining land abutting northern boundary of survey area
• New baseball diamond opens 2010, back of Burke/Meriam Farm field
• All but a portion of the wetland’s east end and shoreline is included in Concord’sAmerican Mile historic district as of 2010.
Scientific and Literary History
Gowing’s Swamp was one of Thoreau’s most beloved Concord landscapes, providing him
with solace, curiosity, and contemplation just a short walk from his family home on Virginia
Road. Swamps, and particularly this bogland, were landscapes of deep inspiration for
Thoreau. He referenced Gowing’s Swamp in 37 entries in his Journal, in Walden, and in hisessay Walking. He made detailed measurements and drawings of the mature kettlehole bog
within the southern portion of the greater level bog complex, recorded inventories of its plant
life, and made intuitive observations of the environmental importance of bogs and swampsgenerally that were rare for naturalists and scientists of his era.
Both during his life and after his death, other naturalists, scientists, and writers followed
Thoreau’s inspiration:
In her book, The Alcott’s as I Knew Them (1909), Clara Gowing wrote, “A favorite resort
with us girls near our homes…was to a pool which F.B. Sanborn in his ‘Reminiscences of Seventy Years’ calls Gowing’s Swamp…We named the place Paradise and spent many happy
hours there.”
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Herbert W. Gleason, recorded numerous photographic images of the bog and surrounding
wetland between 1917-20, providing an invaluable visual benchmark for landscape changessince that time.
In 1969, Mass. Audubon published a booklet by local botanist Richard J. Eaton, entitled
“Gowing’s Swamp” which recounts Thoreau’s studies and adds Eaton’s own updated andexpanded plant inventories for the wetland. In 1974, Eaton includes these earlier observations
in his Flora of Concord.
An H.W. Gleason photograph of Gowing’s Swamp is included in the 1975 Sierra Club
publication, Thoreau Country.
Beginning in the 1970’s and
continuing over the last 30+ years,
MIT Prof. Harold Hemond, did anexhaustive and pioneering study of
the bog’s hydrology andgeochemistry, determining it to be
ombrotrophic in nature, fed only byrainwater, and maintained by
delicate hydrological, biochemical
and growth cycles. Hemond’sfindings update the definition of
this wetland’s ecology and the
underlying hydrology of thelandscape from 1980 forward.
Through numerous citations and publications of Hemond’s studies,
including papers in Ecological Monographs (1980), the Canadian Journal of Botany (1981),
and Ecology (1983), Gowing’s Swamp has gained name recognition for it’s unique ecologicalfeatures and Hemond’s pioneering research in northeastern bog biochemistry and ecology.
As a literary note, in 1996, Gowing’s Swamp received mention in Postmodern Wetlands:
Culture, History, and Ecology (Edinburgh U. Press), in a piece by Ron Giblett titled, “HenryDavid Thoreau: The Patron Saint of Swamps.”
In 2001, Cherrie Corey wrote an historical, botanical, and personal reflection about the bogtitled, “Bog and Soul: A Concord Experience” for Concord Magazine web-zine. The article
can be seen at http://www.concordma.com/magazine/sepoct01/gowingsbog.html.
Since 2004, Richard Primack, biology professor at Boston University, and his students have
been studying historical records of Concord’s plant life and bird sightings for his work on
global warming indicators. They have inventoried the plants of Gowing’s Swamp and other
Concord locations with reference to Thoreau’s, Eaton’s, and Hosmer’s records. Primack’sstudies of Concord’s flora and fauna have appeared in numerous scientific journals and
national magazines.
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A substantial archive of historic and scientific documentation and public testimony aboutGowing’s Swamp is consolidated in Concord town files for the Planning Board, the Natural
Resources Commission, and the Zoning Board of Appeals and is available for review upon
request. The Concord Museum holds an important collection of archaeological artifacts found
in the immediate vicinity of Gowing’s Swamp.
Conservation History and Context In 1970, the significance of Gowing’s
Swamp/Thoreau’s Bog caught the attention of several
area conservation organizations and Sudbury ValleyTrustees purchased the wetland’s eastern third and
shoreline, including half of Thoreau’s Bog on
December, 1 1970. In 2001, a portion of field andwetlands bordering the southeastern boundary of the
SVT property and eastern vernal pool also was putinto a permanent conservation restriction, granted to
SVT by Thomas and Cynthia Ann LeBlanc. The CR references adjacency to Minuteman Historic Park and
Gowings Swamp as well as its own wetlands, which
are within Concord’s Groundwater Conservancydistrict. In the early 1980’s, as a result of the Meriam
Close planned residential development southwest of
the wetland, additional open space provisions addedthe central and southwestern portions of the wetland
into permanently protected status, as the MeriamClose Conservation Trust. Today, roughly four-fifths of the wetland and surrounding
shoreline is protected by permanent conservation restrictions. The wooded, upland slope of
the wetland’s NW shoreline, the NW corner of the wetland and roughly half of the northernshoreline currently are privately owned by Lexington Road resident, Paul Ware. Gowing’s
Swamp, nearby vernal pools and much of its surrounding shorelines are included in both
Concord’s Water Conservancy District and its American Mile Historic District, and was
designated NHESP Priority Habitat area in 2008.
From 2007-09, the Town of Concord reviewed an application for a Special Permit for an 11-
unit PRD accessed from 201 Independence Road that, if built, would occupy the northwesterncorner of the privately held land 100’ west and north of Gowing’s Swamp’s shoreline. The
Special Permit was ultimately granted alongside an agreement between the applicant and the
town that conservation restrictions would be applied to substantial acreage within thewetland’s north shore 100’ buffer zone and much of the upland forest along Gowing’s
Swamps northwestern shoreline ( see Concord Dept. of Natural Resources files). There
continues to be strong local interest in the long-term preservation of this parcel, but it’s
ultimate disposition still is unclear at this time.
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Structure of the Landscape
Topography
Gowing’s Swamp sits 131.2 feet above sea level bounded to its southwest by the forested
slopes of Revolutionary Ridge, which rises up to 150 feet above sea level at its eastern edge.A deep and picturesque woodland vernal pool is located just below the ridge west of
Gowing’s Swamp. An esker, or ice channel filling, builds from southwest to southeastforming the other elevated shoreline of the wetland. Two vernal pools lie just east and south
of the esker. Gowing’s Swamp’s entire shoreline, east to northeast, is relatively level with the
wetland’s surface water due to the glacial outwash plain to the ENE.
Surficial Geology The large glacial basin that contains Gowing’s Swamp, its forested shorelines, and outwash plain meadows was formed and sculpted some 12,000 years ago during the retreat of the
glacial ice front and thedeposits from Lake Concord.The melting of large, buried ice
masses created the kettleholes
that now contain Gowing’s
Swamp, the vernal pool to itssouth, and the woodland vernal
pool upslope to its west. The
deeper water depths and standsof black spruce in both the
south and northwestern portion
of the wetland suggest that twolarge ice masses were likely
responsible for the wetlands
shape and floral composition.Their slow melting created
deep kettlehole depressions that, over thousands of years, have filled in with sphagnum and
accumulating peat layers. The outwash topography, including the islanded esker, or ice
channel filling, off the northern shore, suggest that the melting waters of both areas flowedtoward what’s now the northeastern corner of the wetland. The persistence of smaller ice
masses created terraces of shallower depressions along the western slope. (Photo: NW corner
showing shallow kettlehole depression with black spruce/tamarack/pine stand, islanded esker
on right, and glacial outwash channel in back center.)
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Soils
A mapping of
major soil types
underlying the
Gowing’sSwamp
landscape
provides aninitial blueprint
for likely plant
communities anddiscoveries we
might expect to
find there.
Soils typical of an outwash plain
are found alongGowing’s Swamp’s forested northern shoreline and forming a narrow, east-facing band at the
height of the esker (or ice-channel filling) in the wetland’s southeastern corner. Formed from
sandy glaciofluvial materials that are derived from granite and gneiss, these acidic Wareham deposits (32B, pink) drain poorly.
The wetland basin containing Gowing’s Swamp is lined with very deep, poorly draining, andextremely acidic (>4.5 pH) organic soils known as Freetown muck (52A, blue). Formed in
more than 4 feet of highly decomposed material this soil is typically found in bogs and acidicshrub swamps.
Revolutionary Ridge, which rises up to 150 feet above the Gowing’s Swamp basin, is formedfrom water sorted sand and gravel deposited at the high point of Lake Concord. These
Hinckley series soils (253B, purple) are very deep, excessively drained, and shed little runoff.
Mixed oaks, white pine and hemlock favor this extremely to moderately acid growing
medium.
Underlying the fields and hedgerows to the east and northeast of the wetland’s shoreline, deep
and moderately well drained soils typical of the Deerfield series (256A, green) profile arecharacteristic. Deerfield soils are commonly adjacent to poorly drained Wareham soils, are
strongly to moderately acid and typically have supported truck farms (like those historically in
Concord’s East Quarter) or white pine, gray birch, red maple, mixed oaks, and sugar maplewhen forested.
(Soil survey information and map from Soil Survey Staff, Natural Resources Conservation
Service, U.S. Dept. of Agriculture. Web Soil Survey. Available online athttp://websoilsurvey.nrcs.usda.gov/, accessed 2/1/10. Numbers adjacent to the soil type
correlate with the numbers on the soil maps.)
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Hydrology The Gowing’s Swamp basin sits perched above and
isolated from a groundwater divide. The watershed
around its southern end drains south to Elm Brook,
then to Mill Brook, and ultimately into the ConcordRiver. The watershed on the wetland’s northern end
drains north directly into the Concord River. The
Concord River flows east into the Merrimac River.
Gowing’s Swamp is an ombrotrophic wetland.
Existing in hydraulic isolation from the underlyingwater table, it relies solely on rainwater for its
recharge and on evapotranspiration for overall
regulation of water levels. The acidity of therainwater combined with the highly acidic soil
substrates in and around the wetland combine to keepthe bog waters around 3.8 pH. It is this extremely
acid condition, combined with low mineral andnutrient availability, and a protective topography that
favors a cool microclimate that accounts for a locally
rare and thriving community of northern and bog-loving plants.
Typically, ombrotrophic water bodies have no measurable flow pattern. However, an historic
irrigation ditch penetrating the southeastern shoreline drains excess water from the bog duringhigh water periods through a channel and into an outer vernal pool. The outlet does draw
water toward it during high water periods, primarily from the more open moat areas to thenorthwest, forming a barely perceptible clockwise flow pattern within the upper portions of
Gowing’s Swamp.
Historic evidence remains of additional efforts to tap the
bog to irrigate surrounding farm fields. Remnants of a
ditch and filled in French drain are visible between
Gowing’s Swamp and the southern vernal pool. Rusty pipes with spigots still standing just north and south of the
Gowing’s Swamp shoreline. The eastern vernal pool
receives overflow water through a channel from Gowing’sSwamp. It, in turn, drains minimally through a small
French drain into the south-lying vernal pool which in
turn drains high water through an historic ditch at itssouthern terminus. This ditch crosses under the cart road
and ends at a farm pond in the historic Burke Field. The
ditches, drains, and pipes leave evidence that interference
with the bog’s hydraulic isolation did occur within the last150+ years. While it may have temporarily effected the
bog’s water levels and chemistry and caused some floral
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transitions in the outer vegetation rings, the draining doesn’t seem to have had a long-term
impact on the sensitive ecology within the kettlehole level bog on the wetland’s southern end.This may have to do with the relatively short time that the irrigation channels remained in
active use.
Due to the soil composition of the surrounding shorelines, the lower elevation of the outlet ponds, and the lack of development and impermeable surfaces within the larger glacial bowl
containing the wetland, there is, to date, no water inlet or discernable natural runoff that
naturally flows into Gowing’s Swamp. However during the unseasonably high water duringthe summer of 2009 and spring of 2010, the eastern vernal pool and outflow channel flooded,
raising the concern that backwash and nutrient contamination can occur during such periods.
In his letter to Stephen Johnson, SVT’s executive director in 1997, the late Stephen M. Meyer recommended blocking this remaining outlet ditch to assure the bog’s natural ombrotrophic
state.
Gowing’s Swamp outlet – an historical irrigation channel through
eastern shoreline
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Botanical Survey Findings
Survey Process This latest botanical survey was conducted by the author from May 2009 to February 2010.
The site was visited on an average of twice a month by the consulting naturalist. This survey
builds upon observations and documentation by Thoreau, Richard Eaton, Ray Angelo, Dr.Harry Hemond, and Don Miller and serves as a basis for clarifying the classification of the
wetland’s plant community association.
Survey Areas
The property was divided into five main survey locations
based on four general types of plant communities with sub-areas delineated in the narrative based on logical
management units and land ownership. These include:
• Gowing’s Swamp and Thoreau’s Bog
• Vernal pools
• Forested ridges and shorelines• Fields (including small wet meadow) and hedgerows
Survey Nomenclature and Sighting Details
Two plant lists complement these site descriptions:
• By site alphabetically by botanical family and genus
• Combined plant list alphabetically by botanical
family/genus for all species found.
Lists use scientific names based on Gleason and Cronquist’s
Manual of Vascular Plants of Northeastern United States and Adjacent Canada and Sorrieand Somers’ Vascular Plants of Massachusetts: A County Checklist . Given the
reclassification and name changes that have occurred for many plants in recent years, the
USDA’s Plants Database was consulted for recent updates (http://plants.usda.gov).
The consulting naturalist made every effort to provide a complete and accurate list by site for
the entire survey area, with an emphasis on plants most critical for conservation and
management planning. Ongoing additions and corrections are encouraged, particularly for willows and graminoid, fungi, and moss species which are not this reviewer’s strength.
In this environment, plants can be absent or inaccessible one year and present the next. Due to
record rainfall and water levels from early June through mid-July in 2009, the wetland plantswere either submerged or difficult to access, making detailed inventory difficult during the
height of the flowering season. The naturalist was not present for most of August. The surveywas extended into the winter months when frozen surfaces provided greater access to plants
within the kettlehole bog and deeper areas of the surrounding moat.
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Special note should be made of any future reappearance of plants that were historically
recorded by Thoreau, Eaton, and Hemond which haven’t been seen in recent years. Theseinclude:
Arceuthobium sp., Dwarf mistletoe (oral history accounts)Calla palustris, Wild Calla (Eaton)
Eriophorum spissum, Cotton grass (Eaton), possible seen by D. Miller (2007)Gaylussacia dumosa, Dwarf huckleberry (Thoreau)Menyanthes trifoliate, Bog buckbean (Eaton) Rhodora canadensis, Rhodora (Thoreau, Hemond)Scheuchzeria palustris, Pod rush (Thoreau)
Viburnum cassinoides, Witherod (Eaton)
Photo by Cynthia Ross
Dwarf mistletoe reported to once have grown in Gowing’s Swamp
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Gowing’s Swamp and Thoreau’s Bog
Hope and the future for me are not in lawns and cultivated fields, not in towns and cities,but in the impervious and quaking swamps. Thoreau (from Walking )
Environmental Setting
Gowing’s Swamp, an 8.9 acre ombrotrophic wetland located in a glacial bowl with an
opening to the northeast, is actually not a swamp at all. It’s physical and botanical structureconstitute a locally rare and thriving level bog community with a large, continuous floating
sphagnum mat and characteristic ericaceous shrubs and acid-loving herbaceous plants
dominating its landscape. The bog is surrounded by a moat that averages 12-15 feet in widthand ranges in depth from .5-4 feet depending on seasonal rainfall and point of entry.
A fully articulated kettlehole level bog inhabits a deeper depression (42º27’44.53”N,
71º19’41.35”W) within the Gowing’s Swamp basin at the southern end. This .93 acre area,locally known as “Thoreau’s Bog” for his recorded study of this special area, has all the
attributes of a mature kettlehole bog complete with concentric plant zones, locally rare boreal
tree and shrub species, and carnivorous plants. A shallower depression in Gowing’s Swamp’snorthwestern corner (42º27’47.95”N, 71º19’46.56”W) contains some of the same boreal tree
and herbaceous species but lacks the open sphagnum mat surrounded by concentric vegetation
zones.
Vegetation Description
Gowing’s Swamp’s specialized plant community grows on a substrate of floating sphagnummoss and an underlying deep peat layer of decomposing organic material. Due to its
hydrological and geologic features and the ecological effects of peat decomposition, the
wetland maintains a stable acidic and mineral poor environment. A continuous colony of
sphagnum moss covers the entire wetland. While some thin layers of sphagnum can be found
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close to shore, the sphagnum mat reaches sufficient thickness, about 15 ft. from the shoreline,
to support the root masses of shrubs, grasses and herbaceous plants and the weight of small tomoderately sized animals.
An acidic shrub community dominates the overall wetland landscape including, in descending
proportions – leatherleaf (Chamaedaphne calyculata), maleberry ( Lyonia ligustrina – shown below), sheep laurel ( Kalmia angustifolia), highbush blueberry, and dangleberry (Gaylussacia frondosa). Individual and larger stands of
Winterberry ( Ilex verticillata) occur throughout Gowing’s Swamp but are heartiest
along the northeast to northwest shorelines
indicating that some nutrient exchange alongthese shorelines may raise the wetland’s pH
slightly in these areas. Remnants of dead red
maples and struggling saplings are few andconcentrated in the northeast and northwest
portions of the mat. A somewhat larger number of trees occurs along the eastern
shoreline and may be what’s left of a moredominant stand described by Eaton (1969).
Since Eaton’s time the broader, more northerly portion of Gowing’s Swamp has been
described by some as a red maple swamp. It appears that this misattribution may have begunwith Eaton’s observations and the presence of a few conspicuous living and dead trees on the
eastern side of the wetland. However, a predominant and well-established sun-loving,
ericaceous shrub community growing on a floating sphagnum mat throughout the wetlandmore closely fits the state’s classification of a level bog .
A small variety of graminoid species and herbaceous plants grow on the outer reaches of the
mat and in shallower waters near the shoreline. Three-way sedge ( Dulichium arundinaceum) ,
rattlesnake grass (Glyceria canadensis) , manna grass (Glyceria obtusa), common rush( Juncas effuses), and smaller patches of wool grass (Scirpus cyperinus) are signatures here.
There is a small patch (about 50 plants) of Narrow-leaved cattail (Typha latifolia) near the
northwestern shoreline (likely from a seed source due north). Sparse showings of marsh St.
Johnswort (Triadenum virginicum), marsh bedstraw (Galium trifidum ssp. trifidum), swampcandles ( Lysimachia terrestris), and northern bugleweed ( Lycopus uniflorus) add seasonal
variety among the grasses. Massachusetts fern (Thelypteris simulata) grows in the damp soils
near openings in the shrub canopy along the southeastern shoreline and cinnamon fern gracesthe shore throughout the southern end of the wetland.
Along the damp wooded shorelines, sweet pepperbush (Clethra alnifolia), swamp azalea( Rhododendron viscosum), and highbush blueberry (Vaccinium corymbosum) appear
commonly from the southeast to southwest and sparingly in the north. The distinct crimson
glow of small groves of black gum (Nyssa sylvatica) trees is particularly apparent along the
northwestern shoreline and eastern shore of the islanded esker in autumn. The less commonmountain holly ( Nemopanthus mucronatus) reveals itself best in early August when Eaton
said its “habit of growth is such as to rank it among our most beautiful of native shrubs”
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(1969). Individual shrubs were found along the east facing shorelines in the southern end of
Gowing’s Swamp and on the island to the north. Two healthy specimens of poison sumac, a perilous bog loving species, are growing in the northeastern shallows both near the mainland
and along the island’s shoreline.
In the southern portion of Gowing’s Swamp lies Thoreau’s Bog, which has been studiedcontinuously by naturalists and scientists since Thoreau published his own investigations and
deeply felt reflections about this rare wetland gem. This thriving kettlehole bog within a bog
may contain the last remaining significant stand of black spruce in Concord.
MIT professor Harry Hemond, has been studying the bog’s hydrology and biochemistry for
more than 30 years. In his ongoing research, he has determined that acidity levels of 3.8 pHremain relatively constant over time within the kettlehole bog itself. Very specialized plants
that are adapted to this impoverished growing medium and deep peat layer dominate this sub-
community. Standing in the center of this kettlehole bog, a low mat of sphagnum interlacedwith bog rosemary ( Andromeda polifolia), large and small cranberries (Vaccinium
macrocarpon and V. oxycoccus), tawny cotton sedge ( Eriophorum virginicum) , andoccasional bonsais of tamarack ( Larix laricina) and black spruce (Picea Marianna) radiates
out about 75’ in all directions.
Within this bowl shaped area, one first notices
the exotic feeling of the place with its vastopen sky above and the surrounding ridges to
the southeast and west fringed in tall straight
pines with a mixture of oak along the southernrim. A dense and healthy stand of mature
black spruce (some 150+) dominate the outer edge of the open mat forming a tall ring of
woody vegetation along with tamarack and
spindly white pine. Just below these conifers asofter border of leatherleaf and maleberry fill
in around the bog mat. In the shaded recesses
under these woody stands, the inconspicuous,
carnivorous purple pitcher plants (Sarracenia purpurea) thrive. Near the soft center of the bog, round-leaved sundew ( Drosera rotundifolia) can occasionally be spotted. A small and
less organized stand of black spruce, tamarack, and associated bog flora also are found in the
middle of the northwestern quadrant of Gowing’sSwamp.
Lichens form an important part of any bogcommunity and several species rarely encountered in
the local area were found here. Black spruce and
tamarack branches host veritable gardens of beautiful
lichen species including: crumpled rag lichen( Platismatia tuckermanii – shown right), burred
horsehair lichen ( Bryoria furcellata) , boreal oakmoss
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lichen ( Evernia mesomorpha) , hooded tube lichen ( Hypogymnia physodes) , Fringed wrinkle
lichen (Tuckermannopsis americanaand bristly and brushy beard lichens (Usnea hirta and U.
strigosa) to name a few. Cladonia incrassata, Parmeliopsis subambigua, and Pseudevernia
consocians were identified during this survey, by Doug Greene and Elizabeth Knieper, as the
only recorded station for these species in the Concord-Lincoln area.
Beyond the circular open mat and ring of trees is a dense, almost impenetrable outer shrub
ring of maleberry, blueberry, and sheep laurel characteristically protecting the inner two rings.
The concentric configurations of the Thoreau’s Bog give way to the predominant acidicshrubs and surrounding moat of the outer level bog community.
Management Issues The health of this level bog community depends on it isolation from both the surrounding
water table and surface runoff contamination. Any introduction of surface runoff, nutrients,
pesticides and herbicides, and salts and other minerals could incrementally raise the pH andmineral content of the greater bog environment both opening the way for transitional wetland
plant species to move in while threatening the restrictive nutritional needs of the locally rare bog species that depend on a stable acidic environment.
Annually survey shoreline for signs of erosion, yard waste, and trail wear within at least the
100’ setback zone from the wetland – particularly along SE, northern, and eastern shorelines.
These disturbances over time can result in a disturbance of the bogs water chemistry andoverall ecology.
Conduct focused perimeter plant surveys of bordering vegetation within the wetland everyfive years, monitoring 30’ out from the high water mark. Under current conditions, priority
areas should include: the eastern shoreline with special attention paid in the vicinity of theoutlet channel, the southwestern corner in the vicinity of the steepest shoreline grades, and the
northern shoreline especially in the glacial outwash zone where moat waters seasonally reach
out into the field.
Further study and analysis should be
given to the idea of closing off the
remaining historical irrigation channeldraining out from Gowing’s Swamp’s
eastern shore. The presence of this
channel creates a modest, butmeasureable flow pattern in this
otherwise still ombrotrophic
environment. While drainage typicallyflows outward toward the somewhat
lower eastern vernal pool, record
precipitation in 2009-10 resulted in
backwash through this channel for upto 7 days on at least two occasions.
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NHESP Classification Gowing’s Swamp corresponds most closely to the Level Bogcommunity in the NHESP classification system with its predominance of tall and short shrubs
that are predominantly ericaceous. Most of the suggested indicator species apply. Thoreau’s
Bog – as defined by its concentric rings of woody vegetation (black spruce and tamarack)
surrounding an open inner mat of sphagnum moss, bog rosemary, pale laurel, tawny tussock grass, pitcher-plants, round-leaved sundew, cranberries, and conifer bonsais – is characteristic
of a Kettlehole Level Bog sub-community.
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Vernal Pools
Isolated vernal pool above western shoreline
Environmental Setting
Due to the glacial carving of the Gowing’s Swamp landscape, an unusual number of vernal
pools coexist in a relatively small area. These include Gowing’s Swamp itself, a pool to itseast, another pool complex to its south, and small isolated pool upland to its west. Though an
historical drainage ditch system links the main wetland to two outer pools to the east and
south, all three were likely isolated seasonal pools prior to its construction more than 100years ago. All three pools are state certified. Ownership of Gowing’s Swamp is split between
three parties -- Sudbury Valley Trustees, Meriam Close Conservation Trust, and resident Paul
Ware. The eastern most vernal pool is owned by SVT and the southeastern pool by SVT, the
Meriam Close Conservation Trust and R. and M. Mandel. A fourth, certified pool lies at the bottom of a deep, wooded kettlehole depression just above Gowing’s Swamp’s western
shoreline. This pool currently is privately owned by both Paul Ware (southeastern half) and
Charles Doolittle (northwestern half).
Vegetation Description
Containing vegetation characteristic of a level
bog community, Gowing’s Swamp is distinctfrom the other three vernal pools and has
already been described in detail.
The eastern vernal pool might well be named
Buttonbush pool for the nearly homogenous
stand of waist-height Cephalanthus
occidentalis that dominates its shallow waters
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and sunnier eastern half. The buttonbush has been growing here for sufficient years to reach a
mature height of about 15 feet, which might suggest that acidity levels are high enough for itto become established (>4.7 pH) but not enough for it to thrive (<5.5 pH). In the western
shallows of the pool, a few clumps of sweet pepper-bush (Clethra alnifolia) are intermixed
with healthy steeplebush (Spiraea tomentosa) both of which tolerate >4.5 pH. Mature red
maple, birch trees, and high bush blueberries line the pool’s western edge, while theremainder of its shoreline is lined with a tangle of invasive plants, mainly buckthorn and
multiflora rose. A large, established stand of Japanese knotweed dominates its eastern edge.
Two large willow trees (Salix sp.) grow at the pools eastern edge backed by a mown field thatfills with purple loosestrife and various goldenrods each summer. An historic cart path runs
along the eastern border of the pool and receives regular recreational foot traffic. The pool is
fed mainly by rainwater and, during high water periods, from runoff through Gowing’sSwamp’s outlet channel.
The southeast lying vernal pool complex fills a series of kettleholes
that stretches along the outer lengthof the esker that forms the
southeastern shoreline of Gowing’sSwamp. The pool begins near the
east lying field and the south
terminus of the eastern vernal pool,filling a long narrow basin along
the length of the esker. It then
narrows where the esker andopposing steep shorelines come
together. From there it brancheswest to a widened cul-de-sac
immediately below the Meriam
Close housing development and south where it widens into a half-acre shrub swampdominated by highbush blueberries and red maple remnants. An historic outlet channel drains
the pool to the southeast during seasonal high water periods, flowing between houses and
under the historic cart path, through a pond in an adjacent Burke Field, and ultimately on into
the Mill Brook to the south. Dense stands of sweet pepper-bush with intrusions of buckthornand greenbriar grow along the pool’s northern and western shorelines. Highbush blueberry
filles in shallower areas from the high to low water marks. Duckweed (Lemna sp.) appears to
be the only aquatic plant that makes this pool its home. A mature grove of Norway sprucedominates its steep southern shoreline. Part of a mature and sprawling witch-hazel grove
graces the pool’s northwestern shore and follows the damp remnants of an old irrigation ditch
that runs from the pool northward toward a filled in French drain from the main bog. ( Photo,
March 2010)
The isolated vernal pool on the forested slope west of Gowing’s Swamp lies at the bottom of
a 10-25% grade on all sides. With a lush growth of northern hemlock (Tsuga canadensis)trailing down along its southwestern shoreline, high ridges to its west and northwest and the
ridge trail running along its east-southeastern borders, this vernal pool landscape provides a
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wildly picturesque and serene counterpoint to the suburban development perched high above
its waters. Its steep basin, shaded by towering red oaks and white pines has very sparseunderstory except for some spreading of buckthorn to the north, occasional black or sweet
birch ( Betula lenta) to the south, and sarsaparilla ( Aralia nudicaulis) and hayscented fern
( Dennstaedtia punctilobula) as the only notable groundcover. A weathered pine snag, riddled
with pileated woodpecker holes, dominates the ravine.
Management Issues
Annually survey the vernal pool shorelines for signs of erosion, yard waste dumping, and trailwear within the 100’ setback zone from the wetlands. Consider removing invasive plant
species along shorelines while their numbers are still at manageable levels. Purple loosestrife
stands to the southeast of SVT’s vernal pool could eventually invade the pool itself.
The question about whether or not to seal off the historic drainage ditch connecting Gowing’s
Swamp to the east lying vernal pool has been raised by several over the years (R. Eaton, 1969;S. Meyer, 1997). The record high water levels in 2010 resulted in prolonged periods where
the eastern pool was filled to the level of the drain channel creating a backwash toward theGowing’s Swamp end. A period of annual water testing within Gowing’s Swamp along all
the major shorelines and within the eastern vernal pool may help to answer questions aboutthe gradient of acidity from the shoreline toward the center of the level bog and the possible
effects that backwash from the eastern pool, surface runoff, or occasional groundwater shifts
may be having on the wetland over time.
NHESP Classification
The four vernal pools are certified under Massachusetts guidelines and qualify for all relatedstate and local protections. Woodland vernal pools are small, shallow depressions isolated
from other surface waters, which flood for at least 2-3 months annually. They provide criticalhabitat for amphibians and certain aquatic invertebrates, such as fairy shrimp. Because they
are ephemeral, they typically do not have fish.
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Forest Matrix: Mixed Oaks/White Pine
Oak-pine forest on western slope
Environmental Setting: A forest matrix dominated by mixed oaks and white pine coversabout 50% (11+ acres) of the survey area, in upland shorelines from the southeast to
southwest, rising up along a steep and glaciated ridge line, then down to more level area along
the northern shoreline of Gowing’s Swamp, and out over an islanded esker (or ice channelfilling) that bisects the wetland’s northern end. Dramatically changing grades and
topography, variable sun and wind exposures, and underlying differences in soil types are
evidenced by subtle shifts in forest composition from south to north.
Because of the highly porous glacial soils, most rainfall and snow melt moves directly into the
groundwater below, rather than over surface and down into the wetland. In recent years,unusually high rainfall periods and more extreme storm activity have resulted in runoff and
some significant erosion along the southeastern ridgelines above Gowing’s Swamp and along
some of the woodland trails.
The age and mix of the forest also conveys the land use history in this early settlement area.The northern and eastern portions of the survey area were likely cleared and cultivated over
the past millennium. This is evidenced in the archaeological record (see Attachment A) and inthe documented history of Concord’s Great Field, common lands used for tillage and pasture
beginning in the 1650’s, that extended from the town’s center east through this area. Theupland forest adjacent to this common land shows floral evidence of having been managed as
a woodlot and transitioned (through disease and lumbering) from a dominance of chestnut to
oaks.
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Vegetation Description:
While the forest matrix is predominantly a composition of mixed oak and pine, thedramatically variable topography and land use impacts result in some isolated areas of
specialized diversity. The damp forest lowland on the eastern edge of Gowing’s Swamp is
dominated by red maples, intermixed with a few ‘old field’ white pines, white oak, andmature paper birches. Highbush blueberry (Vaccinium corymbosum) fills in the shrubby
understory with ever increasing numbers of young buckthorn ( Frangula spp.) moving into
any available open spaces. Massachusetts and cinnamon ferns grow in the muddy areaswhere dappled sunlight can penetrate. The only nannyberry (Viburnum lentago) shrub
recorded in this inventory grows at the edge of the drainage
ditch connecting the bog to the eastern vernal pool, just to theleft of the footbridge. Eaton (1969) lists wild raisin
(Viburnum cassinoides) at Gowing’s Swamp, which was notseen in this survey. A healthy colony of Lycopodium
obscurum appoints the shoreline near the footbridge andsparse patches of Canada mayflower (Maianthemum
canadensis), wintergreen (Gaultheria procumbens), and
starflower (Trientalis borealis) are found here and in thegravelly forest lowlands and plateaus through the inventory
area.
Moving up the esker bordering the wetland to the southeast,
the forest canopy transitions to an open, mature stand of white pine. Here, the highbush blueberries give way to lowbush blueberries (Vaccinium
angustifolium) with an otherwise patchy groundcover of winterberry, clubmosses (both Lycopodium obscurum and L. clavatum), pink ladyslippers, bracken fern (on the west facingslope), and numerous mushroom species in season. One chokeberry shrub was noted in the
midslope transition zone, an area quickly being crowded out by rapidly advancing buckthorn
and greenbrier. An isolated and healthy stand of
Norway spruce grows at the crest of the esker (as wellas on the nearby shoreline of the south-lying vernal
pool). These stands mark the location of underlying
Wareham deposits, poorly draining granite/gneiss soilof the outwash plain. Pinesap (Monotropa hypopithys)
also grows here. The only mature sassafras grove in
the survey area grows on the southeast facing slope of the esker where the white pine transitions back to a
pine-oak forest matrix.
The pine forest appears to be about 80-90 years old.Many of the trees have a dbh of 25-40 inches and are
about 50-70 feet high with one or two larger trees at the
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height of the esker and along the shoreline. Photographs taken by Herbert Gleason in the
1920’s show very few trees along this ridge, which would confirm this estimate.
Descending the esker to the southwest, red and white oaks become increasingly dominant
with an understory shift to maple-leaved viburnum (Viburnum acerifolium), sweet pepper-
bush (Clethra alnifolia), and highbush blueberry on the lower slopes. Many of the oaks bothhere and throughout the forest are large and
multi-stemmed indicating that this likely
served as a woodlot some 80-100 yearsago. Hayscented fern (Dennstaedtia
punctilobula) predominates as the
groundcover under these stands. As theforest trail drops down again to the level of
Gowing’s Swamp, it is flanked on both
sides by a dense, mature grove of sweet pepper-bush. Just beyond, a large and
beautiful colony of witch-hazel grows inthe moist soils that connect the bog to the
south-lying vernal pool. Near the trailintersection along the protected southwest
corner of the forested survey area, several large specimens of red oak and white pine
dominate the landscape. These were likely left as shade trees by the water’s edge, during periods of wood harvesting. In this shady, protected area there is a small and singular pocket
of additional hardwood species including American beech ( Fagus grandifolia), Hop-
hornbeam (Ostrea virginiana), and shagbark hickory (Carya ovata).
The forest matrix in the southwestern portion of the survey area occupies the narrow low,damp areas along the bog and a precipitous slope rising directly from the shoreline trail which
is populated by a nearly pure stand of white pine. The largest white pine in the survey area
(52 inches/dbh) is anchored deeply into the hillside and towers above the trail. A few maturehemlock grow here along with several venerable and towering paper birch. Vigorous
American chestnut (Castanea dentate)
sprouts begin to appear as the trail
turns north and increase in number along the western ridgeline and level,
forested shoreline to the north. Red
maple, paper birch, speckled alder ( Alnus incana var. rugosa), and sweet
pepper-bush co-mingle with highbush
blueberry, the occasional mountainholly ( Nemopanthus mucronatus –
shown right), and pernicious buckthorn
along the water’s edge. Cinnamon
fern, Massachusetts fern and a fewroyal fern (Osmunda regalis) fill in at ground level. Due to the added sunlight, disturbance
from flooding and footfall, and opportunities for greater seed dispersal in this area several
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wildflowers occur uniquely here. These include whorled aster (Oclemena acuminata ) , heart-
leaved aster (Symphyotrichum cordifolium), blue-stemmed goldenrod (Solidago caesia), and panicled hawkweed (Hieracium paniculatum) along with the more generally present
partridge-berry (Mitchella repens) and Canada mayflower.
Along the western edge of Gowing’s Swamp, theforest rises steeply to a plateau and ridgeline that
marks the highest waterline of glacial LakeConcord. The Hinkley series soil that forms this
glacial kame is very porous and sheds little runoff.
A mature forest community of mixed oaks, white
pine, and the occasional paper birch grow alongthese slopes, with a healthy understory of sweet or black birch ( Betula lenta), American chestnut, and
beaked hazelnut (Corylus cornuta). Most of the
oaks on this ridge are large, multi-trunked trees
which appear to have been coppiced (harvested to produce additional stump sprouts) about80-120 years ago. One such tree has six trunks sprouting from its base. The groundcover in
this area is predominantly partridgeberry, patchy Canada mayflower, wintergreen, wild
sarsaparilla ( Aralia nudicaulis), sessile bellwort or wild oats (Uvularia sessilifolia), spottedwintergreen (Chimaphila maculata), Indian cucumber-root (Medeola virginiana), and an
abundance of pink ladyslippers (more than 200 blooming plants were counted along the trail
during mid-May 2009). There is one small colony of northern bush honeysuckle ( Diervilla lonicera), which blooms in mid-June, growing to the left of the trail that rises from the
wetland’s southwestern shoreline. One small but mature grove of hemlock grows on the steep
slope that descends from the top of the ridge, forming the western side of a deep kettlehole
that contains the isolated, woodland vernal pool located on this plateau.
Some 50+ bushy stump sprouts of American
chestnut grow along this plateau and the wetland’sforested northern shoreline, indicating that
chestnut had a significant presence here. Chestnut
was heavily harvested during Thoreau’s lifetimeand any that remained would have succumbed to
the blight (Cryphonectria parasitica) after 1904.
Because its wood is resistant to rot, these stumpshave prevailed underground. A few 20-40 foot,
well-formed trees grow in this plateau area,
however, due to the density of the overarchingcanopy these currently don’t receive enough lightto bloom.
Descending the forest trail toward Gowing’s Swamp’s gently sloping northern shoreline, theforest matrix shifts to a younger (60-80 year), more homogenous area of single-stemmed red
oaks with a few large white pines and periodic red maples and white oaks (Quercus alba)
along the wetland’s shoreline. The shrub layer is patchy with occasional highbush blueberry
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(Vaccinium corymbosum), American chestnut sprouts, some thickets of white pine saplings,
American hazelnut (Corylus americana), and basswood (Tilia americana) saplingsconcentrated along trail and forest edges and the shoreline. Buckthorn species, of course, are
prevalent throughout. Though the herbaceous layer is sparse, Canada mayflower, sarsaparilla,
pink ladyslippers, and Indian pipes (Monotropa uniflora) are frequent with a few patches of
starflower and isolated spotted wintergreen. The apparent age of the mature oaks along withthe shoreline presence of a few shrub oak and spindly common juniper ( Juniperus communis)
suggest that until about 1930-40 the historic field and pasture land to the north extended to the
wetland’s northern shoreline. Wareham outwash soils occur here as they do in the southeastcorner of the survey area, marked once again by a small stand of Norway spruce and an
isolated clump of pinesap (Monotropa hypopithys).
Management Issues:
Buckthorn has spread significantly in the last eight years within the forest understory,
sprouting from the shallow waters up to the ridgetops throughout the woodland areas. If allowed to spread unchecked it will soon out compete the natural understory and create
conditions too shady for the relatively sparse but diverse herbaceous groundcover species. Inthe last 3-5 years, native greenbrier and invasive multiflora rose have begun to overtake
highbush blueberries in the vegetation transition zones along the esker trail and around theshorelines of the vernal pools. A targeted removal and control program for all invasive
species is recommended along the forested shorelines and ridge areas. Invasive species of all
varieties are most prevalent throughout the survey area’s southeastern and southern areas,much of which is owned by SVT.
With the record rainfall and strong storm activity in 2009-10, bank erosion has become amore significant concern along the steep wooded slopes of the SW corner of the trail circuit
and wetland. This could inevitably effect both forested slope stability and contamination of the bog through runoff and should be monitored.
Inspection of hemlocks revealed a few wooly adelgid sacs on two trees west of the isolatedvernal pool above Gowing Swamp’s western shoreline. These should be monitored over time.
NHESP Classification:This forest matrix reflects the profiles of a Forest Seep community, a Successional White Pine
forest, an Oak-Hickory forest, and a White Pine-Oak forest. The forest seep community fills
in the moist area between Gowing’s Swamp and the east lying vernal pool and contains redmaple, white birch, white oak, and small white pines with highbush blueberry dominating the
understory. The successional white pine forest -- characterized by a dominant stand of white
pine with a pine needle carpet and a thin herbaceous layer -- grows along the top of the esker in the southeast corner of the survey area. This area transitions into an oak-hickory
community to the south and southwest with a mix of white pine, red and white oaks, a couple
of hickories, sassafras, American chestnut, witch-hazel, and hop-hornbeam, with a shrub layer
of maple-leaved viburnum and sweet pepper-bush. The white pine-oak forest comes in alongthe western shoreline and dominates both the steeper western ridge, the area north of
Gowing’s Swamp, and the islanded esker that extends south from the northern shoreline.
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and a stonewall and hedgerow on the right, beyond which lies the town’s Burke Meriam Farm
field. Beyond the mown field, the cart road passes by a currently unmanaged area of grassland and thickets which border the east lying vernal pool and the SVT trail entrance. As
it passes the eastern shore of Gowing’s Swamp, the back fields of the Ripley School meet its
western edge. Just beyond the wetland’s NE corner, the old card road turns west and merges
with a paved access drive of the newly expanded cemetery. The wetland’s northeasternshoreline is bounded by a small wet meadow habitat and dry upland grassland.
Deep, well-drained, and moderately acidic soils typical of the Deerfield series and low-lyingagricultural areas underlie areas to the east and northeast of the wetland. An area of Freetown
muck extends from the bog into the open grassy area on the northeastern shoreline, creating
the substrate for a small wet meadow community. Under the remaining expanse of hedgerowand forest edge bordering Gowing’s Swamp’s northern shoreline, Wareham outwash soils
account for a slightly different mix of woody and herbaceous edge plants.
Vegetation Description
Much of the open area along the old cart road is dominated by non-native forage grassesincluding redtop (Agrostis gigantean) creeping bent grass (Agrostis stolonifera), sweet vernal
grass (Anthoxanthum odoratum), orchard grass ( Dactylis glomerata), hairy panic grass(Dichanthelium acuminatum), timothy ( Phleum pratense), and Kentucky blue grass (Poa
pratensis). In late May through June, the grasses are interwoven with several non-native
flowering field herbs including blue alfalfa (Medicago sativa), various clovers (Trifolium
hybridum, T. pratense, and T. repens), sheep sorrel (Rumex acetosella), yellow wood-sorrel
(Oxalis europea), common winter cress ( Barbarea vulgaris), and lesser stitchwort (Stellaria graminea). The occasional evening lychnis (Silene latifolia ssp. alba), rough-fruitedcinquefoil ( Potentilla recta), common mullein (Verbascum thapsus), evening primrose
(Oenothera biennis), and early (Solidago juncea), tall (S. altissima), and rough-stemmedgoldenrods (S. rugosa) flower later in the summer.
This grassy area is currently not mown and over thelast 20 years a variety of native and invasive shrubs
and vines have taken over. A large stand of Japanese
knotweed dominates the area between the eastern
vernal pool and the cart road. Gray birch, multiflorarose, small white pine, a few scrub oak, and a
substantial colony of European buckthorn have
turned the grasslands to the north of the vernal poolto a thicket, extending nearly to the footpath to the
SVT trailhead. On the other side of the footpath,
covering the area from the Gowing’s Swampshoreline out toward the cart road another dense and spreading thicket of Oriental bittersweet
and multiflora rose has overwhelmed the native shrubs, trees, and is encroaching on the field
grasses. Pussywillows were once numerous in this area.
Across the cart road to the east, a stone wall runs from the swamp all the way to Old Bedford
Road. Along the wall grow several large, old red and white oak trees, some black cherry, and
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red maple. Morrow’s honeysuckle, autumn olive, staghorn sumac, multiflora rose,
bittersweet, scrub oak, and a few buckthorn fill out the hedgerow. Another hedgerow,dominated by red maple, abuts the shoreline of Gowing’s Swamp across from the Ripley
School field. In addition to the Morrow’s honeysuckle, multiflora rose, bittersweet, and
buckthorn, several crab apple trees (Malus sp.) and a silky dogwood (Cornus amonum) catch
attention during spring bloom. A culturally revealing selection of herbaceous plants provideground cover including lily-of-the-valley, false solomon’s seal (Maianthemum racemosum),
Virginia creeper, and poison ivy. This is the only station in the entire survey area where any
of these species were found. The color of their fruits and particularly catch attention in thefall.
As the shoreline rounds thenortheast corner of the wetland it
flattens to water level revealing the
remnants of a glacial outwashchannel. The underlying soils
transition from mesic Deerfieldseries to Freetown muck along the
water’s edge, to Wareham outwashsoils fanning away from the
wetland. The vigorous agricultural
history of this field area and recentleveling of the upland areas to
accommodate the cemetery
expansion has likely mixed some of the Deerfield and Wareham soils together here. This open landscape contains dry upland field
habitat grading down to a wet meadow area bordering a transitional area of moisture-lovingtrees and shrubs.
Along the northeast corner of Gowing’s Swamp’s shoreline and the field edge, gray birch,quaking aspen ( Populus tremuloides), white pine, and rapidly spreading bittersweet vines and
buckthorn mix with highbush blueberry, swamp azalea, sweet pepperbush, black chokeberry
( Pyrus melanocarpa), maleberry ( Lyonia ligustrina) and dangleberry (Gaylussacia dumosa).
This is the only location where the last two shrubs can be viewed up close without having toenter the bog. The groundcover in this wetland edge habitat, includes plants that can tolerate
both a bit of shade and periodic flooding, including Massachusetts fern (Thelypteris simulata),
sensitive fern (Onoclea sensibilis), northern dewberry ( Rubus flagellaris), willowleaf aster
(Symphyotrichum praealtum), and various moss and grass species.
Due to Gowing’s Swamp’s slow draining ecology, high water resulting from seasonal
snowmelt and heavy precipitation floods into the adjacent, low-lying field. Following record
rainfall in March 2010, some 15 inches of standing water covered the open area to within 15feet from the shoreline. Typically spring flooding is half this amount, though it provides
enough moisture through early summer to keep these soils spongy out some 40-50 feet from
the bogs edge. These seasonal conditions have resulted in a wet meadow microhabitat that is particularly diverse due to the added acidity and the presence of seed sources from the
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adjacent bog. Willow and
graminoid species highlight thisarea. Since these are not the
consulting botanist’s area of
expertise, identified species should
be re-examined for verification inthe future. Two or more willow
species appear to be growing in
these damp areas including whatappear to be large pussy willow
(Salix discolor ), Bebb’s willow (S.bebbiana), and black willow (S.
nigra). Several sedges including
sallow sedge (Carex lurida),
pennslyvania sedge (C. pensylvanica), three-way sedge
( Dulichium arundinaceum), andwool grass – considered a bulrush (Scirpus cyperinus) grow here along with Canada and
common rush, (Juncus canadensis and J. effuses). Manna grass (Glyceria obtusa) makes amodest showing in the wet field areas likely seeded by larger concentrations growing just
within Gowing’s Swamp. Some forbs and a fern that grow in this wet meadow area include
steeplebush (Spiraea tomentosa), bugleweed ( Lycopus americanus), purple loosestrife, andsensitive fern.
Throughout the upland field, introduced species of meadowwildflowers grow along with a few natives. A mixture of
upland grasses and sedges, which were not inventoried as partof this survey, form the tangled groundcover for early flowers
of lesser stichwort (Stellaria graminea), dwarf cinquefoil
( Potentilla simplex), and silvery cinquefoil ( Potentilla
argentea). Later in the summer, the field fills with continuous
blooms of Queen Anne’s lace ( Daucus carota), black-eyed
susan ( Rudbeckia hirta), common mullein (Verbascum
thapsus), common fleabane ( Erigeron philadelphicus),common milkweed ( Asclepias syriaca), common St. Johnswort
( Hypericum perforatum), sweet everlasting
( Pseudognaphalium obtusifolium), showy tick-trefoil ( Desmodium canadense), king devil( Hieracium caespitosum), common evening primrose (Oenothera biennis), and purple
loosestrife ( Lythrum salicaria). Several species of goldenrod grow at the field edges
throughout the summer and early fall, including lance-leaved goldenrod ( Euthamia
graminifolia), early goldenrod (Solidago juncea), Canada goldenrod (S. canadensis), and tall
goldenrod (S. altissima). New England aster (Symphyotrichum novae-angliae) and common
yarrow ( Achillea millefolium) grow just beyond the bounds of the survey area but could likelyreseed here.
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The upland field area has not been seasonally mown and small trees and shrubs are beginning
to take hold. Gray birch, scrub oak (Quercus ilicifolia) and autumn olive ( Elaeagnus umbellata) punctuate the flowery expanse. Various butterflies, moths, and Odonata species
were encountered during the survey, including the more spectacular primrose moth (Schinia florida) and ebony jewelwing (Calopteryx maculata).
Management Issues
The fields, hedgerows, and cart roadthat wrap around Gowing’s Swamp are
historic remnants of Concord’s Great
Field. It is recommended that these bemaintained to provide both biological
and aesthetic diversity as well as
historical continuity of the landscape.The invasive exotics should be of
primary concern as they provide asource of infestation into the shoreline
and forest areas. Nearly the entireeastern shoreline of Gowing’s Swamp
and the eastern vernal pool are choked
with invasive plants – bittersweet ( see
photo), buckthorn, multiflora rose and in lesser amounts Japanese honeysuckle, autumn olive,
and purple loosestrife. Cut and daub eradication of the woody invasives should be a high
priority. Poison ivy encroaching on the cart path at the NE corner needs to be addressed. Lateseason mowing of the northern and eastern upland fields will help maintain their diversity
while discouraging a succession to woody colonizers. Bluebirds are resident throughout theyear and it is recommended that the bluebird houses be repaired or replaced and maintained
on the NE corner of the property.
NHESP Classification
This area fits the state classification of wet meadow and cultural grassland communities.
A wet meadow is described by the MNHP as a temporarily flooded, but persistently moist
wetland community dominated by graminoids. The mucky mineral soils are saturated duringthe growing season but generally not inundated. Repeated disturbance, usually from grazing
or mowing, keeps these communities free of woody plants. A cultural grassland is an open
habitat created by humans and usually maintained by annual mowing or haying. These plantcommunities generally occur on sand or other droughty, low nutrient soils and often involve
cemeteries, airports, or historic pastures or hayfields.
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Acknowledgements
Gowing’s Swamp has long received reverent and detailed attention from the scientific and
literary communities and this report, in large part, acknowledges and references those studies
and writings that have been compiled over the past 150+ years, beginning with Thoreau’s
Journal entries. In the process of researching and preparing this report, I’ve receivedgenerous and invaluable guidance, contributions, and recollections from local scientists,
naturalists, historians, town authorities, and residents who hold the deep history of Gowing’sSwamp in their collective memories, archives, and published works. My gratitude goes to
Ray Angelo (Associate, Harvard U. Herbarium, noted authority on Thoreau’s botanical
legacy), Deborah Bier (Concord Magazine blog editor), Shirley Blancke (Concord
archaeologist, compiled attached list of artifacts), Brian Donahue (author of The Great
Meadow, 2004) Kay Fairweather (fungi specialist), Doug Greene (lichen specialist, compiled
lichen list for this report), Thurston Handley (horticulturist and Gowing’s Swamp neighbor),
Charles Harvey (MIT hydrogeologist and Concord resident), Harry Hemond (MIT geochemistand author of definitive scientific papers on Gowing’s Swamp and northeastern bog
geochemistry), Elizabeth Knieper (lichen specialist), Donald Miller (SVT intern 2007,compiled preliminary plant inventory of Gowing’s Swamp), Lydia Rogers (Walden KeepingTrack), Lou Sideris (MNHP, Dir. of Interpretation), Mary Walker (local botanist), Bryan
Windmiller (local herpetologist), and many more not listed here.
Additional appreciation goes to the Concord Planning Office staff, Delia Kaye and Cindy
Gray of the Concord Dept. of Natural Resources, and the Special Collections staff at the
Concord Free Public Library for providing a wealth of historical maps, photos, and written
documentation about Gowing’s Swamp and to naturalist Deb Allen for the use of some of her photographs. A special thank you to Louise Berliner, Tom Wilson, Chuck Doolittle, Steven
Sbardella, John Nevins, and the many other residents of Independence Road and the
Revolutionary Ridge and Gowing’s Swamp neighborhoods for their support, assistance, andencouragement during this project. Unless otherwise noted, all photographs were taken by the
author and consulting naturalist for this report, Cherrie Corey.
Doug Greene and Elizabeth Knieper identifying lichens
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Bibliography
Burke, Gerard J. oral history archive Interviewed by Renee Garrelick (5.31.2005), Concord Oral
History Program.
http://www.concordlibrary.org/scollect/Fin_Aids/OH_Texts/Burke.html
Champman, Rachel R. and Harold F. Hemond. (1981) Denitrogen fixation by surface peat and Sphagnum in an ombrotrophic bog. Canadian Journal of Botany, 60: 538-43
Corey, Cherrie. “Bog and Soul: A Concord Experience,” The Concord Magazine, Sept/Oct 2001,
http://www.concordma.com/magazine/sepoct01/gowingsbog.html
Donahue, Brian. (2004) The Great Field: Farmers and the Land in Colonial Concord (New Haven:
Yale U. Press)
Eaton, Richard J. (1969) “Gowing’s Swamp,” (Mass. Audubon Society)
Eaton, Richard J. (1974) A Flora of Concord from Thoreau’s time to the Present Day. (Cambridge,
MA: Harvard U., Museum of Comparative Zoology)
Gowing, Clara. (1909) The Alcott’s as I Knew Them. (Boston: C.M. Clark Pub. Co.)
Hemond, Harold. (1980) The Biochemistry of Thoreau’s Bog, Concord, Massachusetts. Ecological
Monographs, 50(4), pp. 507-526
Hemond, Harold. (1983) The Nitrogen Budget of Thoreau’s Bog . Ecology, Vol. 64, No. 1, pp. 99-109.
Koteff, Carl. (1964) Surficial geology of the Concord quadrangle. (Massachusetts: U.S. Geological
Survey, Geologic Quadrangle Map GQ-331)
Giblett, Rod. (1997) Postmodern Wetlands: Culture, History, and Ecology. (Edinburgh U. Press)
Robbins Collection of Herbert Wendell Gleason Photographic negatives of Images of Concord, Mass.,
1899-1937
Sorrie, Bruce A. and Paul Sommers. (1999) The Vascular Plants of Massachusetts: A CountyChecklist . (Massachusetts Division of Fisheries and Wildlife, Natural Heritage & Endangered Species
Programs)
Thoreau Country: Photographs and Text Selections from the works of H. D. Thoreau, (Sierra Club
publication), 1975
Thoreau, Henry D. The Journal of Henry D. Thoreau, 1837-1861, Volumes 1-2. (Dover Publications), 1962
USDA, NRCS. (2010) The PLANTS Database (http://plants.usda.gov). (Baton Rouge, LA: National
Plant Data Center)
Web Soil Survey. Soil Survey Staff, Natural Resources Conservation Service, U.S. Dept. of
Agriculture. Available online at http://websoilsurvey.nrcs.usda.gov/, accessed 2/1/10
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Appendix A – Archaeology
June 2008
Report on the archaeological sites next to Gowing’s Swamp, Concord, MA
All the fields on the north side of Gowing’s Swamp contain archaeological sites. On the
south side, Revolutionary Ridge, only a tiny site is known at the far east end, which produced one
artifact. This does not mean there are no sites on the ridge, but that artifacts in the past were only
found in plowed fields. An archaeological survey is needed to find them in unplowed land.
The Gowing’s Swamp area is the southern part of what was known as “The Great Fields,”
which extended north to the river and comprised the fields both north and south of route 62.
Blancke conducted archaeological surveys and excavation of the northern section in connection
with Sleepy Hollow Cemetery expansion. Traces of a wigwam floor were found there that were
radiocarbon dated to c. 1450 C.E. (Shirley Blancke 2003. Archaeological Data Recovery at
Sleepy Hollow North Cemetery Expansion: Final Report, Phase 2. Concord, Massachusetts.
Report on file, Massachusetts Historical Commission, Boston).
Artifacts from archaeological sites immediately adjacent to Gowings Swamp were picked
up by two important collectors, Adams Tolman, and Benjamin L. Smith, a founder of the
Massachusetts Archaeological Society, and are in the Concord Museum. A list of them is
provided below. The sites are registered with the Massachusetts Historical Commission and the
site numbers refer to MHC maps. The town of Concord has a by-law saying that archaeological
material should be considered in any development.
In the fields north of the swamp and west of Old Bedford road is site 19-MD-476, which
covers the whole area and comprises an older site 19-MD-97. The area south of St. Bernard’s
cemetery is numbered 19-MD-945 and comprises the older site 19-MD-98. The numbers 476 and
945 effectively cover the whole area north of the swamp and were designated because artifacts
have been picked up in those areas in recent years by Peter Waksman and Bill Eldridge. Artifacts
in the old collections come from 19-MD-97 and -98. Collections from site 19-MD-100 north of
route 62 also include some material from the Gowings swamp area (Benjamin Smith).
The area south of St. Bernard’s cemetery is part of the old Foss Farm on which was found
a very unusual artifact of current interest to Maine archaeologists because it appears to have come
from Maine. It is a large, 6 in. slate spearhead that resembles a medieval European metal one, but
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is several thousand years old. Benjamin Smith wrote a 5-page description of it. From site 19-MD-
98 there is a spectacular ulu, or woman’s semi-circular knife, of slate that is also 6 in. long. It is
unusual to find an unbroken specimen of these. It has a hole drilled in the handle, presumably to
tie it to a belt.
A rough timeline for the occupation of these sites is provided by the types of the projectile
points (spearheads, dart-heads, arrowheads). They cover 4 time periods: Middle and Late Archaic,
and Early and Middle Woodland, that extend from 7000 years ago to 1000 years ago
approximately. The quantity of chipping waste is unusual for Concord sites and indicates that a
great deal of stone tool manufacturing was conducted in the Great Fields
The combined totals of artifacts for sites 19-MD-97 and -98 from the Tolman and Smith
collections are as follows:
Total artifacts: 355
32 projectile points (ranging from Middle Archaic to Middle Woodland periods)
1 pestle2 gouges
1 sinker 1 hoe
1 perforator 2 small pounding stones
7 edge tools (knives, scrapers)3 ulus
3 bifacial blade fragments, pendant.300 pieces of chipping waste (flakes and chunks of rhyolite, quartz, quartzite, argillite)
The artifacts collected from site 19-MD-100 north of route 62 included some from the
southern area. The chipping waste was so extensive it could be weighed in grams, and the amount
collected in the Gowings swamp area for all types of stone weighed 2,213 grams (4½ lb.) (Shirley
Blancke 1987. Archaeological Site Examination of the Bedford Street Housing, Asparagus Farm
area, Concord, Massachusetts. Report on file, Massachusetts Historical Commission, Boston).
Shirley BlanckeAssociate Curator for ArchaeologyConcord [email protected]
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Appendix B – Bird ListObserved by Cherrie Corey, 2008-10
Little green heron
Wood duck
American woodcock Cooper’s hawk
Red-tailed hawk Wild turkey
Mourning dove
Barred owl
Screech owlsWood pewee
Red-bellied woodpecker
Downy woodpecker Hairy woodpecker
Northern flicker Pileated woodpecker Eastern phoebe
Catbird
Blue-headed vireoBlue jay
American crow
Common raven
Black-capped chickadeeTufted titmouse
White-breasted nuthatch
Brown creeper
Carolina wrenGolden-crowned kinglet
Eastern bluebirdWood thrush
Hermit thrush
American robin
CatbirdMockingbird
Cedar waxwing
Yellow warbler Common yellowthroat
Field sparrowTree sparrowSong sparrow
Swamp sparrow
White-thoated sparrowDark-eyed junco
Northern cardinal
Red-winged blackbird
Brown-headed cowbird Northern oriole
Pine siskin
American goldfinch
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Appendix C – Gowing's Swamp Botanical Inventory, 2009-10
Plant Type and Family Sort
Plant Group Nat/Int Family Scientific Name Common
Fungi N Amanitaceae Amanita muscaria Fly Agaric
Fungi N Amanitaceae Amanita spp.
Fungi N Amanitaceae Limacella glischera? Slimy, gilled mushrooms
Fungi N Auriculariaceae Auricularia sp.
Fungi N Clavariaceae Ramariopsis sp.?
Fungi N Entolomataceae Entoloma strictius?
Fungi N Exobasidiaceae Exobasidium vaccinii Azalea gall
Fungi N Hygrophoraceae Hygrocybe cantharellus?
Fungi N Meripilaceae Grifola frondosa Hen of the Woods
Fungi N Physaraceae Fuligo septica Dog Vomit slime mold
Fungi N Polyporaceae Piptoporus betulinus Birch polypore
Fungi N Polyporaceae Polyporus squamosus Dryad's Saddle or Pheasant's Tail
Fungi N Poriceae Trametes versicolor Turkey-tail
Fungi N Reticulariaceae Lycogala epidendrum Wolf's Milk slime moldFungi N Russulaceae Russula emetica? The Sickener
Fungi N Tricholomataceae Clitocybe nuda Blewitt
Lichens N Agyriaceae Sarea resinae Serea lichen
Lichens N Arthoniaceae Arthonia caesia Frosted comma lichen
Lichens N Candelariaceae Candelaria concolor Lemon candle-flame lichen
Lichens N Candelariaceae Candelariella efflorescens Powdery gold-speck lichen
Lichens N Cladoniaceae Cladonia coniocraea Common powderhorn
Lichens N Cladoniaceae Cladonia cristatella British soldier lichen
Lichens N CladoniaceaeCladonia macilenta var.bacillaris Lipstick powderhorn race
Lichens N Fuscideaceae Fuscidea arboricola Quilt lichen
Lichens N Fuscideaceae Ropalospora viridis Ropalospora lichen
Lichens N Lecanoraceae Lecanora hybocarpa Bumpy rim lichenLichens N Lecanoraceae Lecanora strobilina Mealy rim lichen
Lichens N Lecanoraceae Lecanora symmicta Fused rim lichen
Lichens N Lecanoraceae Lecanora thysanophora Mapledust rim lichen
Lichens N Lecanoraceae Pyrrhospora varians Crimson dot lichen
Lichens N LecanoraceaeScoliciosporumchlorococcum
City dot lichen or Green needlelichen
Lichens N Lecideaceae Hypocenomyce friesii Clam lichen
Lichens N Lecideaceae Hypogymnia physodes Hooded tubelichen
Lichens N Leprariaceae Lepraria incana Dust Lichen
Lichens N Leprariaceae Lepraria neglecta Zoned dust lichen
Lichens N Micareaceae Micarea erratica A dot lichen
Lichens N Mycocaliciaceae Phaeocalicium polyporaeum Phaeocaliciumlichen
Lichens N Parmeliaceae Bryoria furcellata Burred horsehair lichenLichens N Parmeliaceae Evernia mesomorpha Boreal oakmoss lichen
Lichens N Parmeliaceae Flavoparmelia caperata Common greenshield lichen
Lichens N Parmeliaceae Imshaugia aleurites Hooded tube Lichen
Lichens N Parmeliaceae Melanelixia subaurifera Abraded camouflage lichen
Lichens N Parmeliaceae Parmelia squarrosa Bottlebrush shield lichen
Lichens N Parmeliaceae Parmelia sulcata Hammered shield lichen
Lichens N Parmeliaceae Punctelia rudecta Rough speckeled shield lichen
Lichens N Parmeliaceae Tuckermannopsis americana Fringed wrinkle-lichen
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Lichens N Parmeliaceae Usnea hirta Bristly beard lichen
Lichens N Parmeliaceae Usnea strigosa Brushy beard lichen
Lichens N Pertusariaceae Ochrolechia androgyna Powdery saucer lichen
Lichens N Pertusariaceae Ochrolechia arborea Saucer lichen
Lichens N Physciaceae Amandinea punctata Tiny button lichen
Lichens N Physciaceae Buellia stillingiana Common button lichen
Lichens N Physciaceae Phaeophyscia rubropulchra Orange-cored shadowlichenLichens N Physciaceae Physcia millegrana Mealy rosette lichen
Lichens N Porpidiaceae Porpidia albocaerulescens Smoky-eyed boulder lichen
Lichens N Thelenellaceae Julella fallaciosa Julella lichen
Lichens N Trapeliaceae Trapeliopsis flexuosa Board lichens
Ferns-Allies N Dennstaedtiaceae Pteridium aquilinum Bracken fern
Ferns-Allies N Dennstaedtiaceae Dennstaedtia punctilobula Hayscented fern
Ferns-Allies N Dryopteridaceae Dryopteris intermedia Intermediate/Evergreen wood-fern
Ferns-Allies N Dryopteridaceae Onoclea sensibilis Sensitive fern
Ferns-Allies N Dryopteridaceae Lycopodium clavatum Running clubmoss
Ferns-Allies N Lycopodiaceae Lycopodium obscurum Rare club-moss
Ferns-Allies N Osmundaceae Osmunda cinnamomea Cinnamon fern
Ferns-Allies N Osmundaceae Osmunda regalis Royal fern
Ferns-Allies N Polytricaceae Polytrichum sp. Hair-cap moss sp.Ferns-Allies N Sphagnaceae Sphagnum spp. Sphagnum moss
Ferns-Allies N Thelypteridaceae Thelypteris noveboracensis New York fern
Ferns-Allies N Thelypteridaceae Thelypteris simulata Massachusetts fern
Gram N Cyperaceae Carex lurida Sallow sedge
Gram N Cyperaceae Carex pensylvanica Pennsylvania sedge
Gram N Cyperaceae Dulichium arundinaceum Three-way sedge
Gram N Cyperaceae Eriophorum virginicum Tawny cotton grass
Gram N Cyperaceae Scirpus cyperinus Wool grass
Gram N Juncaceae Juncus canadensis Canadian rush
Gram N Juncaceae Juncus effusus Common rush
Gram I Poaceae Agrostis gigantea Redtop
Gram I Poaceae Agrostis stolonifera Creeping bent grass
Gram N Poaceae Anthoxanthum odoratum Sweet vernal grass
Gram N Poaceae Dactylis glomerata Orchard grass
Gram N Poaceae Dicanthelium acuminatum Wooly panic grass
Gram N Poaceae Glyceria canadensis Rattlesnake grass
Gram N Poaceae Glyceria obtusa Manna grass
Gram N Poaceae Holcus lanatus Velvet grass
Gram N Poaceae Phleum pratense Timothy
Gram N Poaceae Poa pratensis Kentucky blue grass
Gram N Poaceae Schizachyrium scoparium Little bluestem
Gram N Typhaceae Typha latifolia Narrow-leaved cattail
Conifer N Cupressaceae Juniperus communis Common juniper
Conifer N Cupressaceae Juniperus virginiana Eastern red cedar
Conifer N Pinaceae Larix laricina Tamarack, American larchConifer N Pinaceae Picea marianna Black spruce
Conifer N Pinaceae Picea abies Norway spruce
Conifer N Pinaceae Pinus strobus White pine
Conifer N Pinaceae Tsuga canadensis Eastern hemlock
Tree/Shrub/Vine N Aceraceae Acer rubrum Red maple
Tree/Shrub/Vine N Aceraceae Acer saccharum Sugar maple
Tree/Shrub/Vine N Anacardiaceae Rhus typina Staghorn sumac
Tree/Shrub/Vine N Anacardiaceae Rhus vernix Poison sumac
Tree/Shrub/Vine N Anacardiaceae Toxicodendron radicans Poison ivy
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Tree/Shrub/Vine N Aquifoliaceae Ilex verticillata Winterberry
Tree/Shrub/Vine N AquifoliaceaeNemopanthus (Ilex)mucronatus Mountain holly or Catberry
Tree/Shrub/Vine N Berberidaceae Berberis thunbergii Japanese barberry
Tree/Shrub/Vine N Betulaceae Alnus incana var. rugosa Speckled alder
Tree/Shrub/Vine N Betulaceae Betula lenta Black birch
Tree/Shrub/Vine N Betulaceae Betula papyrifera Paper birch
Tree/Shrub/Vine N Betulaceae Betula populifolia Gray birch
Tree/Shrub/Vine N Betulaceae Ostrya virginiana American hophornbeam
Tree/Shrub/Vine I Caprifoliaceae Lonicera morrowii Morrow's honeysuckle
Tree/Shrub/Vine N Caprifoliaceae Sambucas canadensis Common elderberry
Tree/Shrub/Vine N Caprifoliaceae Viburnum acerifolium Maple-leaved viburnum
Tree/Shrub/Vine I Celastraceae Celastrus orbiculata Oriental bittersweet
Tree/Shrub/Vine N Clethraceae Chamaedaphne calyculata Leatherleaf
Tree/Shrub/Vine N Clethraceae Clethra alnifolia Sweet pepperbush
Tree/Shrub/Vine N Ericaceae Gaylussacia frondosa Blue huckleberry or Dangleberry
Tree/Shrub/Vine N Ericaceae Kalmia angustifolia Sheep laurel
Tree/Shrub/Vine N Ericaceae Kalmia polifolia Bog or Pale laurel
Tree/Shrub/Vine N Ericaceae Lyonia ligustrina Maleberry
Tree/Shrub/Vine N Ericaceae Rhododendron viscosum Swamp azaleaTree/Shrub/Vine N Ericaceae Vaccinium angustifolium Lowbush blueberry
Tree/Shrub/Vine N Ericaceae Vaccinium corymbosum Highbush blueberry
Tree/Shrub/Vine N Fagaceae Castanea dentata American chestnut
Tree/Shrub/Vine N Fagaceae Fagus grandifolia American beech
Tree/Shrub/Vine N Fagaceae Quercus bicolor Swamp white-oak
Tree/Shrub/Vine N Fagaceae Quercus ilicifolia Shrub oak
Tree/Shrub/Vine N Fagaceae Quercus rubra var. ambigua Northern red oak
Tree/Shrub/Vine N Fagaceae Quercus velutina Black oak
Tree/Shrub/Vine N Hamamelidaceae Hamamelis virginiana Witch-hazel
Tree/Shrub/Vine N Juglandaceae Carya ovata Shagbark hickory
Tree/Shrub/Vine N Lauraceae Sassafras albidum Sassafras
Tree/Shrub/Vine N Nyssaceae Nyssa sylvatica Black gum
Tree/Shrub/Vine I Rhamnaceae Rhamnus cathartica L. Euro. buckthornTree/Shrub/Vine I Rosaceae Malus sp. Crab apple
Tree/Shrub/Vine I Rosaceae Rosa multiflora Multiflora rose
Tree/Shrub/Vine N Rosaceae Prunus serotina Black cherry
Tree/Shrub/Vine N Rosaceae Pyrus melanocarpa Black chokeberry
Tree/Shrub/Vine N Rosaceae Spirea tomentosa Steeplebush
Tree/Shrub/Vine N Rubiaceae Cephalanthus occidentalis Buttonbush
Tree/Shrub/Vine N Salicaceae Populus grandidentata Big-toothed aspen
Tree/Shrub/Vine N Salicaceae Populus tremuloides Quaking aspen
Tree/Shrub/Vine N Salicaceae Salix discolor Pussy willow
Tree/Shrub/Vine N Salicaceae Salix nigra Black willow
Tree/Shrub/Vine I Salicaceae Salix sepulcralis Weeping willow
Tree/Shrub/Vine N Salicaceae Salix spp. Willow ssp.
Tree/Shrub/Vine N Smilacaceae Smilax rotundifolia Common greenbrier
Tree/Shrub/Vine N Tiliaceae Tilia americana American basswood
Tree/Shrub/Vine N Vitaceae Parthenocissus quinquefolia Virginia creeper
Tree/Shrub/Vine N Vitaceae Vitis labrusca Fox (Concord) grape
Forbs I Apiaceae Daucus carota Queen Anne's Lace
Forbs N Asclepiadaceae Asclepias syriaca Common milkweed
Forbs N Araceae Symplocarpus foetidus Skunk cabbage
Forbs N Araliaceae Aralia nudicaulis Wild sarsaparilla
Forbs N Asteraceae Ambrosia artemisiifolia Ragweed
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Forbs N Asteraceae Artemesia vulgaris Common mugwort
Forbs N Asteraceae Aster laterifolius Calico aster
Forbs N Asteraceae Symphyotrichum praealtum Willowleaf aster
Forbs N Asteraceae Bidens connata Swamp beggar-ticks
Forbs N Asteraceae Conyza canadensis Horseweed
Forbs N Asteraceae Erigeron annuus Daisy fleabane
Forbs N Asteraceae Erigeron philadelphicus FleabaneForbs N Asteraceae Eurybia divaricata White wood aster
Forbs N Asteraceae Euthamia graminifolia Grass-leaved goldenrod
Forbs N AsteraceaePseudognaphalium obtusifolium Sweet everlasting
Forbs I Asteraceae Hieracium caespitosum King devil (Hawkweed)
Forbs N Asteraceae Hieracium paniculatum Panicled hawkweed
Forbs N Asteraceae Oclemena acuminata Whorled wood aster
Forbs N Asteraceae Prenanthes trifoliolata Gall-of-the-earth
Forbs N Asteraceae Solidago caesia Blue-stemmed goldenrod
Forbs N Asteraceae Solidago gigantea Late goldenrod
Forbs N Asteraceae Solidago juncea Early goldenrod
Forbs N Asteraceae Solidago rugosa Rough-stemmed goldenrod
Forbs N Asteraceae Symphyotrichum cordifolium Heart-leaved aster
Forbs N AsteraceaeEupatoriadelphus maculatusvar. foliosum Spotted Joe-pye weed
Forbs I Betulaceae Corylus cornuta Beaked hazelnut
Forbs I Brassicaceae Barbarea vulgaris Winter cress
Forbs N Caprifoliaceae Diervilla lonicera Northern bush-honeysuckle
Forbs I Caryophyllaceae Silene latifolia ssp. alba Evening lychnis
Forbs I Clusiaceae Hypericum perforatum Common St. Johnswort
Forbs N Clusiaceae Triadenum virginicum Marsh St.Johnswort
Forbs N Droseraceae Drosera rotundifolia Round-leaved sundew
Forbs N Ericaceae Andromeda polifolia Bog rosemary
Forbs N Ericaceae Gaultheria procumbens Wintergreen, Checkerberry*
Forbs N Ericaceae Rhodora canadensis Rodora
Forbs N Ericaceae Vaccinium macrocarpon Large cranberryForbs N Ericaceae Vaccinium oxycoccus Small or wren's egg cranberry
Forbs N Fabaceae Desmodium canadense Showy tick-trefoil
Forbs I Fabaceae Medicago sativa Alfalfa
Forbs I Fabaceae Melilotus officinalis Yellow (White) sweet clover
Forbs I Fabaceae Trifolium arvense Rabbit's-foot clover
Forbs I Fabaceae Trifolium hybridum Alsike clover
Forbs I Fabaceae Trifolium pratense Red clover
Forbs I Fabaceae Trifolium repens White clover
Forbs I Fabaceae Vicia cracca Cow vetch
Forbs N Lamiaceae Lycopus uniflorus Bugleweed
Forbs N Lemnaceae Lemna minor Common duckweed
Forbs N Liliaceae Maianthemum canadense Canada mayflower
Forbs N Liliaceae Maianthemum racemosum False solomon's-sealForbs N Liliaceae Medeola virginiana Indian cucumber-root
Forbs N Liliaceae Trientalis borealis Starflower
Forbs N Liliaceae Uvularia sessilifolia Sessile-leaved bellwort
Forbs I Lythraceae Lythrum salicaria Purple loosestrife
Forbs N Monotropaceae Monotropa hypopithys Pinesap
Forbs N Monotropaceae Monotropa uniflora Indian pipe
Forbs N Onagraceae Circaea alpina Small enchanter's nightshade
Forbs N Onagraceae Oenothera biennis Common evening primrose
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Forbs N Orchidaceae Cypripedium acaule Pink ladyslipper
Forbs N Orchidaceae Goodyera pubescens Downy rattlesnake plantain
Forbs N Oxalidaceae Oxalis stricta Yellow wood-sorrel
Forbs I Polygonaceae Polygonum cuspidatum Japanese knotweed
Forbs I Polygonaceae Rumex acetocella Sheep sorrel
Forbs N Primulaceae Lysimachia terrestris Swamp candle
Forbs N Pyrolaceae Chimaphila maculata Spotted wingergreenForbs N Ranunculaceae Anemone quinquefolia Wood anenome
Forbs I Rosaceae Potentilla argentea Silvery cinquefoil
Forbs N Rosaceae Potentilla canadensis Dwarf cinquefoil
Forbs I Rosaceae Potentilla recta Rough-fruited cinquefoil
Forbs N Rosaceae Rubus flagellaris Northern dewberry
Forbs N Rosaceae Spiraea tomentosa Steeplebush
Forbs N Rubiaceae Galium trifidum ssp trifidum Marsh bedstraw
Forbs N Rubiaceae Mitchella repens Partridge-berry
Forbs N Sarraceniacea Sarracenia purpurea Purple pitcher-plant
Plant Community SortPlantCom Family Scientific Name Common Name
Field/Hedgerows Asclepiadaceae Asclepias syriaca Common milkweed
Field/Hedgerows Anacardiaceae Rhus typina Staghorn sumac
Field/Hedgerows Anacardiaceae Toxicodendron radicans Poison ivy
Field/Hedgerows Apiaceae Daucus carota Queen Anne's lace
Field/Hedgerows Asteraceae Ambrosia artemisiifolia Common ragweed
Field/Hedgerows Asteraceae Artemesia vulgaris Common mugwort
Field/Hedgerows Asteraceae Aster laterifolius Calico aster
Field/Hedgerows Asteraceae Aster praealtus Willow-leaved aster
Field/Hedgerows Asteraceae Erigeron annuus Daisy fleabane
Field/Hedgerows Asteraceae Erigeron philadelphicus Fleabane
Field/Hedgerows Asteraceae Gnaphalium obtusifolium Sweet everlastingField/Hedgerows Asteraceae Hieracium caespitosum King devil (Hawkweed)
Field/Hedgerows Asteraceae Hieracium paniculatum Panicled hawkweed
Field/Hedgerows Asteraceae Solidago caesia Blue-stemmed goldenrod
Field/Hedgerows Asteraceae Solidago gigantea Late goldenrod
Field/Hedgerows Asteraceae Solidago juncea Early goldenrod
Field/Hedgerows Asteraceae Solidago rugosa Rough-stemmed goldenrod
Field/Hedgerows Asteraceae Symphyotrichum praealtum Willow-leaved aster
Field/Hedgerows Brassicaceae Barbarea vulgaris Winter cress
Field/Hedgerows Caprifoliaceae Lonicera morrowii Morrow's honeysuckle
Field/Hedgerows Caprifoliaceae Sambucas canadensis Common elderberry
Field/Hedgerows Caprifoliaceae Viburnnum dentatum Northern arrowweeod
Field/Hedgerows Caryophyllaceae Silene latifolia ssp. alba Evening lychnis
Field/Hedgerows Celastraceae Celastrus orbiculata Oriental bittersweet
Field/Hedgerows Clusiaceae Hypericum perforatum Common St. Johnswort
Field/Hedgerows Cornaceae Cornus amonum Silky (Swamp) dogwood
Field/Hedgerows Fabaceae Desmodium canadense Showy tick-trefoil
Field/Hedgerows Fabaceae Medicago sativa Alfalfa
Field/Hedgerows Fabaceae Melilotus officinalis Yellow (White) sweet clover
Field/Hedgerows Fabaceae Trifolium arvense Rabbit's-foot clover
Field/Hedgerows Fabaceae Trifolium hybridum Alsike clover
Field/Hedgerows Fabaceae Trifolium pratense Red clover
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Field/Hedgerows Fabaceae Trifolium repens White clover
Field/Hedgerows Fabaceae Vicia cracca Cow vetch
Field/Hedgerows Liliaceae Uvularia sessilifolia Sessile-leaved bellwort
Field/Hedgerows Lythraceae Lythrum salicaria Purple loosestrife
Field/Hedgerows Monotropaceae Monotropa uniflora Indian pipe
Field/Hedgerows Onagraceae Circaea alpina Small enchanter's nightshade
Field/Hedgerows Onagraceae Oenothera biennis Common evening primroseField/Hedgerows Oxalidaceae Oxalis stricta Yellow wood-sorrel
Field/Hedgerows Poaceae Anthoxanthum odoratum Sweet vernal grass
Field/Hedgerows Poaceae Calamagrostis canadensis Blue joint-grass
Field/Hedgerows PoaceaeDicanthelium acuminatum var.fasciculatum Wooly or fascicled panic-grass
Field/Hedgerows Poaceae Poa pratensis Kentucky blue grass
Field/Hedgerows Polygonaceae Polygonum cuspidatum Japanese knotweed
Field/Hedgerows Polygonaceae Rumex acetocella Sheep sorrel
Field/Hedgerows Polytricaceae Polytrichum sp. Hair-cap moss sp.
Field/Hedgerows Ranunculaceae Potentilla argentea Silvery cinquefoil
Field/Hedgerows Ranunculaceae Potentilla simplex Old field cinquefoil
Field/Hedgerows Rosaceae Malus sp. Crab apple
Field/Hedgerows Rosaceae Potentilla recta Rough-fruited cinquefoilField/Hedgerows Rosaceae Rosa multiflora Multiflora rose
Field/Hedgerows Rosaceae Spirea tomentosa Steeplebush
Field/Hedgerows Salicaceae Populus grandidentata Big-toothed aspen
Field/Hedgerows Salicaceae Populus tremuloides Quaking aspen
Field/Hedgerows Salicaceae Salix bebbiana Bebb's willow
Field/Hedgerows Salicaceae Salix discolor Pussy willow
Field/Hedgerows Salicaceae Salix nigra Black willow
Field/Hedgerows Salicaceae Salix petiolaris Meadow willow (sp.?)
Field/Hedgerows Salicaceae Salix sepulcralis Weeping willow
Field/Hedgerows Salicaceae Salix spp. Willow ssp.
Field/Hedgerows Vitaceae Parthenocissus quinquefolia Virginia creeper
Field/Hedgerows Vitaceae Vitis labrusca Fox (Concord) grape
Wet Meadow Asteraceae Bidens connata Swamp beggar-ticksWet Meadow Asteraceae Euthamia graminifolia Grass-leaved goldenrod
Wet Meadow AsteraceaeEupatoriadelphus maculatus var.foliosum Joe-pye weed
Wet Meadow Betulaceae Alnus incana var. rugosa Speckled alder
Wet Meadow Betulaceae Betula populifolia Gray birch
Wet Meadow Cyperaceae Carex lurida Sallow sedge
Wet Meadow Cyperaceae Carex pensylvanica Pennsylvania sedge
Wet Meadow Cyperaceae Scirpus cyperinus Wool grass
Wet Meadow Dryopteridaceae Onoclea sensibilis Sensitive fern
Wet Meadow Lamiaceae Lycopus uniflorus Northern bugleweed
Wet Meadow Poaceae Agrostis gigantea Redtop
Wet Meadow Poaceae Agrostis stolonifera Creeping bent grass
Wet Meadow Poaceae Glyceria obtusa Manna grassWet Meadow Rosaceae Rubus flagellaris Northern dewberry
Wet Meadow Rosaceae Spiraea tomentosa Steeplebush
Forest matrix Aceraceae Acer rubrum Red maple
Forest matrix Aceraceae Acer saccharum Sugar maple
Forest matrix Amanitaceae Amanita muscaria Fly agaric
Forest matrix Amanitaceae Amanita spp.
Forest matrix Amanitaceae Limacella glischera? Slimy, gilled mushrooms
Forest matrix Araliaceae Aralia nudicaulis Wild sarsaparilla
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Forest matrix Asteraceae Eurybia divaricata White wood aster
Forest matrix Asteraceae Oclemena acuminata Whorled wood aster
Forest matrix Asteraceae Prenanthes trifoliolata Gall-of-the-earth
Forest matrix Asteraceae Symphyotrichum cordifolium Heart-leaved aster
Forest matrix Asteraceae Symphyotrichum lowrieanum Lowrie's aster
Forest matrix Auriculariaceae Auricularia sp.
Forest matrix Berberidaceae Berberis thunbergii Japanese barberryForest matrix Betulaceae Betula lenta Black birch
Forest matrix Betulaceae Betula papyrifera Paper birch
Forest matrix Betulaceae Corylus cornuta Beaked hazelnut
Forest matrix Betulaceae Ostrya virginiana American hophornbeam
Forest matrix Caprifoliaceae Diervilla lonicera Northern bush-honeysuckle
Forest matrix Caprifoliaceae Viburnum acerifolium Maple-leaved viburnum
Forest matrix Caprifoliaceae Viburnum lentago Nannyberry
Forest matrix Clavariaceae Ramariopsis sp.?
Forest matrix Clethraceae Clethra alnifolia Sweet pepperbush
Forest matrix Cupressaceae Juniperus communis Common juniper
Forest matrix Cupressaceae Juniperus virginiana Eastern red cedar
Forest matrix Dennstaedtiaceae Dennstaedtia punctilobula Hayscented fern
Forest matrix Dennstaedtiaceae Pteridium aquilinum Bracken fernForest matrix Dryopteridaceae Dryopteris intermedia Intermediate/Evergreen wood-fern
Forest matrix Entolomataceae Entoloma strictius?
Forest matrix Ericaceae Gaultheria procumbens Wintergreen, Checkerberry
Forest matrix Ericaceae Vaccinium angustifolium Lowbush blueberry
Forest matrix Ericaceae Vaccinium corymbosum Highbush blueberry
Forest matrix Exobasidiaceae Exobasidium vaccinii Azalea gall
Forest matrix Fagaceae Castanea dentata American chestnut
Forest matrix Fagaceae Fagus grandifolia American beech
Forest matrix Fagaceae Quercus bicolor Swamp white-oak
Forest matrix Fagaceae Quercus ilicifolia Shrub oak
Forest matrix Fagaceae Quercus rubra var. ambigua Northern red oak
Forest matrix Fagaceae Quercus velutina Black oak
Forest matrix Hamamelidaceae Hamamelis virginiana Witch-hazel
Forest matrix Hygrophoraceae Hygrocybe cantharellus?
Forest matrix Juglandaceae Carya ovata Shagbark hickory
Forest matrix Lauraceae Sassafras albidum Sassafras
Forest matrix Liliaceae Maianthemum canadense Canada mayflower
Forest matrix Liliaceae Maianthemum racemosum False solomon's-seal
Forest matrix Liliaceae Medeola virginiana Indian cucumber-root
Forest matrix Liliaceae Trientalis borealis Starflower
Forest matrix Lycopodiaceae Lycopodium clavatum Running clubmoss
Forest matrix Lycopodiaceae Lycopodium obscurum Rare clubmoss
Forest matrix Meripilaceae Grifola frondosa Hen of the woods
Forest matrix Monotropaceae Monotropa hypopithys Pinesap
Forest matrix Nyssaceae Nyssa sylvatica Black gumForest matrix Orchidaceae Cypripedium acaule Pink ladyslipper
Forest matrix Orchidaceae Goodyera pubescens Downy rattlesnake plantain
Forest matrix Physaraceae Fuligo septica Dog vomit slime mold
Forest matrix Pinaceae Picea abies Norway spruce
Forest matrix Pinaceae Pinus strobus White pine
Forest matrix Pinaceae Tsuga canadensis Eastern Hemlock
Forest matrix Polyporaceae Piptoporus betulinus Birch polypore
Forest matrix Polyporaceae Polyporus squamosus Dryad's Saddle or Pheasant's Tail
Forest matrix Poriceae Trametes versicolor Turkey-tail
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Gowing’s Swamp, Historical Survey and Botanical Inventory 2009 -- 50
Forest matrix Pyrolaceae Chimaphila maculata Spotted wingergreen
Forest matrix Ranunculaceae Anemone quinquefolia Wood anenome
Forest matrix Reticulariaceae Lycogala epidendrum Wolf's Milk slime mold
Forest matrix Rhamnaceae Rhamnus cathartica L. Euro. buckthorn
Forest matrix Rosaceae Prunus serotina Black cherry
Forest matrix Rosaceae Pyrus melanocarpa Black chokeberry
Forest matrix Rubiaceae Mitchella repens Partridge-berryForest matrix Smilacaceae Smilax rotundifolia Common greenbrier
Forest matrix Thelypteridaceae Thelypteris noveboracensis New York fern
Forest matrix Tiliaceae Tilia americana American basswood
Forest matrix Tricholomataceae Clitocybe nuda Blewitt
Kettlehole Bog Clethraceae Chamaedaphne calyculata Leatherleaf
Kettlehole Bog Cyperaceae Eriophorum virginicum Tawny cotton-grass
Kettlehole Bog Droseraceae Drosera rotundifolia Round-leaved sundew
Kettlehole Bog Ericaceae Andromeda polifolia Bog rosemary
Kettlehole Bog Ericaceae Kalmia polifolia Bog or Pale laurel
Kettlehole Bog Ericaceae Rhodora canadensisRodora (reported observation,Hemond)
Kettlehole Bog Ericaceae Vaccinium macrocarpon Large cranberry
Kettlehole Bog Ericaceae Vaccinium oxycoccus Small or wren's egg cranberryKettlehole Bog Pinaceae Larix laricina Tamarack, American larch
Kettlehole Bog Pinaceae Picea marianna Black spruce
Kettlehole Bog Sarraceniacea Sarracenia purpurea Purple pitcher-plant
Level Bog Aceraceae Acer rubrum Red maple
Level Bog Agyriaceae Sarea resinae Serea lichen
Level Bog Anacardiaceae Rhus vernix Poison sumac
Level Bog Aquifoliaceae Ilex verticillata Winterberry
Level Bog Aquifoliaceae Nemopanthus (Ilex) mucronatus Mountain holly or Catberry
Level Bog Araceae Symplocarpus foetidus Skunk cabbage
Level Bog Arthoniaceae Arthonia caesia Frosted comma lichen
Level Bog Candelariaceae Candelaria concolor Lemon candle-flame lichen
Level Bog Candelariaceae Candelariella efflorescens Powdery Gold-speck Lichen
Level Bog Cladoniaceae Cladonia coniocraea Common PowderhornLevel Bog Cladoniaceae Cladonia cristatella British soldier lichen
Level Bog Cladoniaceae Cladonia macilenta var. bacillaris Lipstick powderhorn lichen
Level Bog Clethraceae Clethra alnifolia Sweet pepperbush
Level Bog Clusiaceae Triadenum virginicum Marsh St. Johnswort
Level Bog Cyperaceae Dulichium arundinaceum Three-way sedge
Level Bog Ericaceae Gaylussacia frondosa Blue huckleberry or Dangleberry
Level Bog Ericaceae Kalmia angustifolia Sheep laurel
Level Bog Ericaceae Lyonia ligustrina Maleberry
Level Bog Ericaceae Rhododendron viscosum Swamp azalea
Level Bog Fuscideaceae Fuscidea arboricola Quilt lichen
Level Bog Fuscideaceae Ropalospora viridis Ropalospora lichen
Level Bog Juncaceae Juncas effusus Common rush
Level Bog Lamiaceae Lycopus uniflorus Northern bugleweed
Level Bog Lecanoraceae Lecanora hybocarpa Bumpy rim lichen
Level Bog Lecanoraceae Lecanora strobilina Mealy rim lichen
Level Bog Lecanoraceae Lecanora symmicta Fused rim lichen
Level Bog Lecanoraceae Lecanora thysanophora Mapledust rim lichen
Level Bog Lecanoraceae Pyrrhospora varians Crimson Dot lichen
Level Bog Lecanoraceae Scoliciosporum chlorococcum City dot lichen or Green needle lichen
Level Bog Lecideaceae Hypocenomyce friesii Clam lichen
Level Bog Lecideaceae Hypogymnia physodes Hooded tube lichen
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Level Bog Micareaceae Micarea erratica Dot lichen
Level Bog Mycocaliciaceae Phaeocalicium polyporaeum Phaeocalicium lichen
Level Bog Osmundaceae Osmunda cinnamomea Cinnamon fern
Level Bog Osmundaceae Osmunda regalis Royal fern
Level Bog Parmeliaceae Bryoria furcellata Burred horsehair lichen
Level Bog Parmeliaceae Evernia mesomorpha Boreal oakmoss lichen
Level Bog Parmeliaceae Flavoparmelia caperata Common greenshield lichenLevel Bog Parmeliaceae Imshaugia aleurites Hooded tube Lichen
Level Bog Parmeliaceae Melanelixia subaurifera Abraded camouflage lichen
Level Bog Parmeliaceae Parmelia squarrosa Bottlebrush shield lichen
Level Bog Parmeliaceae Parmelia sulcata Hammered shield lichen
Level Bog Parmeliaceae Punctelia rudecta Rough speckeled shield lichen
Level Bog Parmeliaceae Tuckermannopsis americana Fringed wrinkle-lichen
Level Bog Parmeliaceae Usnea hirta Bristly beard lichen
Level Bog Parmeliaceae Usnea strigosa Brushy beard lichen
Level Bog Pertusariaceae Ochrolechia androgyna Powdery saucer lichen
Level Bog Pertusariaceae Ochrolechia arborea Saucer lichen
Level Bog Physciaceae Amandinea punctata Tiny button lichen
Level Bog Physciaceae Buellia stillingiana Common button lichen
Level Bog Physciaceae Phaeophyscia rubropulchra Orange-cored shadow LichenLevel Bog Physciaceae Physcia millegrana Mealy rosette Lichen
Level Bog Poaceae Glyceria canadensis Rattlesnake manna-grass
Level Bog Poaceae Glyceria obtusa Manna grass
Level Bog Porpidiaceae Porpidia albocaerulescens Smoky-eyedboulder lichen
Level Bog Primulaceae Lysimachia terrestris Swamp candle
Level Bog Rubiaceae Galium trifidum ssp trifidum Marsh Bedstraw
Level Bog Russulaceae Russula emetica? Sickener
Level Bog Sphagnaceae Sphagnum spp. Sphagnum moss
Level Bog Thelenellaceae Julella fallaciosa Julella lichen
Level Bog Thelypteridaceae Thelypteris simulata Massachusetts fern
Level Bog Trapeliaceae Trapeliopsis flexuosa Board Lichens
Level Bog Typhaceae Typha latifolia Narrow-leaved cattail
Level Bog Leprariaceae Lepraria incana Dust Lichen
Level Bog Leprariaceae Lepraria neglecta Zoned dust lichen
Vernal pool Aceraceae Acer rubrum Red maple
Vernal pool Clethraceae Clethra alnifolia Sweet pepper-bush
Vernal pool Ericaceae Vaccinium corymbosum Highbush blueberry
Vernal pool Lemnaceae Lemna sp. Duckweed
Vernal pool Rosaceae Spirea tomentosa Steeplebush
Vernal pool Rubiaceae Cephalanthus occidentalis Buttonbush
Vernal pool Salicaceae Salix spp. Willow sp.