Asylum for Wayward Immigrants:
Historic Ports and Colonial Settlements in Northeast North America
Allison Bain1,* and Gary King2
Abstract - The arrival of Europeans along the northeastern seaboard of North America heralded the introduction of Old
World fl ora and fauna to the region. The analysis of archaeologically recovered beetle remains suggests that many species
may have journeyed across the Atlantic in ships’ ballast, food stores, and other provisions. The creation of artifi cial habitats
which occurred as a result of the fi sheries and the construction of settlements provided an ecological corridor that facilitated
the successful invasion of the European biota. Many of these adventive or accidentally introduced beetle species are associated
with synanthropic and disturbed-land habitats which would have been mimicked in the coastal colonies. The arrival of
this fauna ultimately contributed to the creation of Europeanized spaces upon the North American landscape.
1CELAT, Université Laval, 1030, Avenue des Sciences-humaines, Québec, QC G1V 0A6, Canada. 2Groupe de recherche
en archéométrie, Université Laval, 1030, Avenue des Sciences-humaines, Québec, QC G1V 0A6, Canada. *Corresponding
author - Allison.Bain@hst.ulaval.ca.
Introduction
It has been almost 40 years since historian Alfred
Crosby penned the Columbian Exchange, where he
outlined the post-Columbian transformation of the
fl ora and fauna in former European colonies around
the world (Crosby 1972). This exotic infl ux included
domesticated animals, economic and ornamental
plant and tree species, and their accompanying
weeds and insects. He later refi ned his arguments
in his 1986 seminal work Ecological Imperialism,
where he argued that the European fl ora and fauna
were easily able to invade habitats similar to those
found in Europe because these were Europeanized
spaces, with little competition (Crosby 1986, 2006).
Environmental archaeology has the privileged position
to examine many aspects of this fl oral and
faunal transfer, whether intentioned or not, and insects,
especially beetles, are recognized as valuable
sources of environmental and climatic data because
they furnish detailed information about past environments
and climates on or around archaeological
sites. In this article, we examine how archaeoentomological
studies from 17th and 18th century ports
of Quebec City, Boston, and the Ferryland site in
Newfoundland tell a story of the creation of humandominated
habitats and communities and transatlantic
biological transfer, including the introduction of
many new insect species to the New World.
Coastal or riverside ports played a key role in
shaping the New World during the colonial period,
though early explorers, whalers, and fi shermen would
have begun the Columbian Exchange. The cod-fi shing
industry in Newfoundland involved considerable
deforestation along the heavily forested landscapes
of Newfoundland; investigation of early 17th-century
documents from the Avalon Peninsula reveals complaints
about the lack of trees and the damage done
by the fi shermen (Cell 1982). Complaints about
deforestation were not unique to Newfoundland. In
fact, the Shawmut Peninsula, where the City of Boston
is located today, lacked wood resources as early
as 1648 (Mrozowski 1987:1).
Ballast dumping also contributed to environmental
changes near northeastern ports. In the 16th century,
a vessel coming out to Newfoundland for the
seasonal cod fi shery would have carried little cargo
as they took on rocks, sand, turf, peat, and any manner
of shore-side material to fi ll up and weight their
empty hulls. Early 17th-century letters from Newfoundland
complain about ship’s captains polluting
the waters due to ballast dumping (Cell 1982:225,
Lindroth 1957:157). A huge volume of ballast material
was disposed of every year, and untold tons of
European stones and soils were thus transported to
the New World. Ballast dumping in the Northeast,
with its strong tides, would have resulted in large
volumes of European materials, including turf, moving
onshore, representing an important means of
biological transfer.
Documenting changing environments
Like the analysis of other biological remains
from archaeological sediments such as plants and
bones, the interpretation of the insect fauna can
shed light on many past activities which include
hygienic, dietary, and medicinal practices (Bain
2001, 2004; Bain et al. 2008, 2009; Buckland 1978,
1990; Busvine 1976; Elias 2010; Kenward 1999;
Kenward and Hall 1995; Panagiotakopulu 2004)
and may also indicate the quality of the food consumed
by a site’s occupants (Bain 1998). As little
archaeoentomology is practiced in North America,
its use as a means to reconstruct past environments
and to explore biogeographic transformations of the
modern period (Bain and Prévost 2010, King 2010,
Prévost and Bain 2007, Schwert 1996) remains underexploited.
However, scientists such as Carl Lindroth
(1957) suggested that the careful examination
Special Volume 1:109–124
Archaeologies of the Early Modern North Atlantic
2011 Journal of the North Atlantic
110 Journal of the North Atlantic Special Volume 1
of the adventive insect fauna is one of the best means
to understand these biological mysteries. Almost
thirty years later, in Ecological Imperialism, Crosby
examined the global phenomenon of the transformation
of temperate landscapes across North America,
the eastern coast of South America, Australia, and
New Zealand into Europeanized landscapes or Neo-
Europes, containing plants and animal species which
arrived during European colonization and came to
dominate the local fl ora and fauna. The introduction
of plants we commonly refer to as weeds is a
compelling example. The decimation by disease and
warfare of the First Nations’ populations in eastern
North America left behind, at times, partly deforested
lands and fi elds ideal for the introduction of a
host of European species that included domesticated
animals, economic and medicinal plants, and of
course, their accompanying weed and insect species.
Accounts as early as the 17th century mention plants
recognized by early travellers as those found in their
native Europe (e.g., Boucher 1664, Josselyn 1671).
Unfortunately, insects and arachnids are rarely
mentioned in North American historical documents
from the 17th and 18th centuries, except when their
presence had economic impacts or was noted as a
source of irritation. The botanist and disciple of
Linneaus, Pehr Kalm, is an exceptional source for
entomological data. During a trip to North America
from 1748 to 1751, he was charged with creating
a catalogue of species in the New World. His descriptions,
which make direct comparisons to the
European flora and fauna he recognized, provide
an excellent resource for 18th-century landscape
studies and constitute one of the rare accounts that
mention insects (Rousseau and Béthune 1977:408).
The adventive coleopteran or beetle species of
eastern Canada have received significant attention
from entomologists (see review of these studies in
Klimaszewski et al. 2010:9–14), and surveys of the
present North American insect fauna indicate that
the biological transfer of European species to the
New World has clearly taken place (Sailer 1983).
This paper therefore yields an important time-depth
perspective on these otherwise invisible occupants
of the Northeast during the modern period, and suggests
that Palaearctic biota were clearly established
as early as the mid-seventeenth century, and that
the number of adventive taxa steadily increased
over time.
Identifying adventive species
Successful colonization of new habitats by
foreign species requires that the fi rst arrivals establish
viable, self-sustaining populations (Saki et
al. 2001). The traits necessary for establishment
vary in accordance with habitat type: complex and
established natural community (cf. Elton 1927),
human-disturbed habitat (cf. Horvitz et al. 1998),
and undisturbed natural island communities (cf. Elton
1958). Saki et al. (2001) argue that a successful
invasive species will exhibit a high fecundity rate as
well as competitiveness.
The advantage of a species being able to quickly
produce large numbers of offspring and out-compete
competitors is apparent when it is confronted with an
established natural community where breeding sites
are already occupied, food is already being eaten,
and shelters are currently occupied by other species.
In order to survive, the invasive species must establish
itself in a niche (using the term in a broad sense),
often through the displacement of one or more organisms
by means of interspecies competition (Saki
et al. 2001).
However, alien species are not always faced
with resistance from native species. In areas that
have been modified or destroyed by human influence
or natural disasters, niches may be vacant.
The modification or destruction of an area may
temporarily “empty” previously occupied niches
by displacing or killing the organisms who resided
in them. Moreover, major alterations to a habitat
may result in the indigenous organisms being no
longer suitably adapted to the area (cf. Whitehouse
2006, Whitehouse and Smith 2004). When the European
colonists arrived in the New World, it was
oftentimes necessary to clear forest and brush for
the construction of settlements and the cultivation
of crops. This land clearance would have displaced
some of the indigenous species and created available
niches for the invasive species (King 2011). A
European insect species which came with the rubble
and soil used as ship’s ballast would have been able
to carve out a niche in the disturbed land around the
colonial settlements and may have faced little competition
from the indigenous species, which were
likely displaced by the human-induced modifications
(King 2011). When competition for resources
and space is minimal, the only conflicts with which
an invasive species are confronted concern the ecological
constraints inherent to that species.
Recent syntheses in entomology suggest there
are identifi able means by which insects arrived to
eastern Canada. These mechanisms include: ballast
dumping, the importation of agricultural, horticultural,
silvicultural (seedling and shrub imports),
and other wood products, and the transportation of
livestock and stored grains, as well as intentional
introductions (Klimaszewski et al. 2010). However,
it is also important to consider how insects classifi
ed as adventives receive this label. Carl Lindroth’s
The Faunal Connections between Europe and North
America (Lindroth 1957) remains central to this
discussion. He suggested key criteria that must be
considered when identifying alien species, including
2011 A. Bain and G. King 111
charting its dispersal across the environment (historical
criterion) as well as identifying foreign species by
their presence in certain ecological niches (ecological
criterion). When a plant or animal species with a
restricted ecology is identifi ed in environments such
as ports and settlements along the Atlantic Coast
as part of a fauna dominated by European species,
these circumstances may suggest that it is a foreign
introduction. A particular geographic distribution
is another factor (geographical criterion) (Lindroth
1957:135–142); for example, species that have distributions
limited to the Atlantic and Pacifi c Coasts
of North America, and perhaps throughout the Great
Lakes and Mississippi waterways, are likely to have
been introduced. Host-specifi c insects are part of
the biological criterion, as they could not have been
introduced before their host plants, while the taxonomic
criterion belies the taxonomic challenges of
trying to identify new insect species or sub-species
or identify allochthonous New World populations
of Palaearctic species (Lindroth 1957:142). Understanding
the genetic makeup of certain groups will
clarify some of these taxonomic relationships (King
et al. 2009), while archaeoentomology and palaeoentomology
may contribute important, well-dated
data to these arguments.
Early ports in Northeastern North
America
Archaeological excavations at
seventeenth-century ports are key
areas to target for the detailed study
of sediment samples that may indicate
biological transfer. Well-dated,
sealed organic contexts play a fundamental
role in documenting the
introduction and impact of biota.
The forms of early ports varied
signifi cantly. At the Ferryland site
on Newfoundland’s Avalon Peninsula,
a seawall was constructed in
the 1620s, allowing ships to come
alongside for the loading and unloading
of cargo (Gaulton 1997). In
Quebec City on the shores of the St.
Lawrence River, enterprising merchants
such as Charles Aubert de la
Chesnaye built on water lots along
the shoreline to exploit this opportunity.
With a shallow foreshore
and long tidal range, large vessels
remained moored in the roadstead,
the deeper part of the river, while
smaller vessels transported material
to the shore (Rouleau 2009).
This study will focus on three
sites in the Northeast (Fig. 1) and
will outline the changes seen in the insect fauna
which are a direct result of European settlement.
Preserved beetle remains recovered during archaeological
privy or latrine excavations will be examined
from the Ferryland site, and from Boston’s Cross
Street Back Lot site. A third site, which represents
two shoreline deposits on the beach from Quebec
City’s Lower Town, will also be discussed.
Methods
Archaeoentomological data from Northeastern
shores
The insect samples analyzed spanned the early
17th to the fi rst half of the 18th century (Table 1).
Contents were studied from a privy in the seawall at
the Ferryland site on Newfoundland’s Avalon Peninsula
(1621–1673), while a second privy from the
Cross Street Back Lot site in Boston (1675–1740)
was also examined. These are compared to beachfront
accumulations in Lower Town, Quebec City at
the Îlot Hunt site, where two shoreline deposits were
formed between 1675 and 1721.
The samples were processed using kerosene
fl oatation as outlined by Kenward et al. (1980, 1986)
and modifi ed by Bain (2001), and sieved to 250
Figure 1. Map of Northeastern North America indicating the study sites. (Map
produced by Andrée Heroux).
112 Journal of the North Atlantic Special Volume 1
Table 1. Archaeoentomological evidence from early colonial period sites in the Northeast. (The symbol “+” indicates species considered
to be adventive to North America, while “*” indicates Holarctic species. Species with uncertain status are indicated by the symbol “§”.
Taxonomy after Arnett and Thomas (2000), Arnett et al. (2002), and Gordon and Skelley (2007).
Ferryland Boston Québec City
1621–1673 1675–1740 1675–1699 c. 1700–1725
Species latrine latrine beach beach
COLEOPTERA
Carabidae
Bembidion musicola Hayward X
B. petrosum petrosum Gebler* X
B. scopulinum Kirby X X
B. tetracolum Say+ X
B. versicolor LeConte or mimus Hayward X
Pterostichus adstrictus Eschscholtz* X
Stenelophus comma Fabricius X
Dicheirotrichus (Trichochellus) cognatus Gyllenhal* X
Chlaenius sericeus sericeus Forster X
Agonum sp. X
Hydrophilidae
Helophorus frosti Smetana X
Cercyon littoralis Gyllenhal* X
C. analis Paykull+ X X X
C. haemorrhoidalis Fabricius+ X
C. praetextatus Say X
C. terminatus Marsham+ X
Cercyon sp. X
Staphylinidae
Aleocharinae spp. X
Carpelimus obesus Keisenwetter+ X
C. cf.bilineatus Keisenwetter+ X
Carpelimus sp. X X
Oxytelus sculptus Gravenhorst+ X X
Anotylus insignitus Gravenhorst X
A. rugosus Fabricius§ X
Quedius mesomelinus Marsham+ X X X
Gyrohypnus fracticornis O.F. Müller+ X
Neohypnus obscurus Erichson X X
Neohypnus sp. X X
Creophilus maxillosus villosus Gravenhorst X X
Philonthus politus Linnaeus+ X X
P. validus Casey X
Trogidae
Trox scaber Linnaeus* X
Scarabaeidae
Aegialia sp. X
Aphodius bicolor Mulsant (syn Aphodius fi metarius Linnaeus)+ X
Calamosternus (syn Aphodius) granarius Linnaeus+ X
Ataenius spretulus Haldeman X
Onthophagus pennsylvanicus Harold X
Xyloryctes jamaicensis Drury X
Byrrhidae
Cytilus alternatus Say X
Elmidae
Optioservus ovalis LeConte X
Stenelmis sp. X
Dermestidae
Dermestes lardarius Linnaeus+ (larder beetle) X
Bostrichidae
Amphicerus bicaudatus Say (apple twig borer) X
Anobiidae
Ptinus fur Linnaeus+ (white marked spider beetle) X X
Tipnus unicolor Piller et Mitterpacher+ X
Priobium sericeum Say X
Trogossitidae
Tenebroides mauritanicus Linnaeus+ X
Nitidulidae
Carpophilus hemipterus Linnaeus+ X
Omosita colon Linnaeus+ X
Monotomidae
Monotoma picipes Herbst+ X
2011 A. Bain and G. King 113
microns. All samples were sorted under low-power
binocular microscopes in the laboratory, and the
recovered insect remains were mounted on micropaleontology
cards to facilitate their identifi cation.
The heads, pronota, and elytra (or fore-wings) of the
recovered beetle remains were examined, as they often
possess characters which allow identifi cation to
the genus and, at times, species level. Identifi cations
were undertaken at the Réné Martineau Insectarium
at the Canadian Forestry Services Centre in Québec
City as well as at the Eastern Cereals and Oilseeds
Research Centre (ECORC) at Agriculture Canada in
Ottawa. The coleopteran remains in this report are
presented in Table 1, respecting changes to North
American nomenclature during the last decade and
are listed taxonomically according to Arnett and
Thomas (2000), Arnett et al. (2002), and Gordon and
Skelley (2007).
Results
The following sections provide a general description
of the three faunal assemblages based on presence/
absence data. Specifi c context data and species
composition of these fauna are discussed elsewhere
(Bain 1998, Bain and Prévost 2010). The individual
numbers of each species are not key to this discussion,
as the goal of this paper is an overview of the
role of Northeastern colonial ports in accommodating
the arrival of Old World species.
Ferryland, Newfoundland
Ferryland was a successful cod-fishing community
located on Newfoundland’s Avalon Peninsula.
A local population resided year round with their
fishing fleets, and also welcomed visiting fishing
fleets during the summer season. Archaeobotanical
studies suggest that the local population ate a large
variety of locally grown fruits and seeds (Bain and
Prévost 2010, Prévost and Bain 2007). They also
consumed abundant wild game including seals and
caribou, which they harvested alongside their introduced
faunal provisions of beef, caprines, and pork
(Hodgetts 2006).
Six samples were studied from the Area C privy,
a stone structure built into the seawall, which allowed
it to be fl ushed by the daily tides (Gaulton
1997:86–87). Despite its careful engineering, a
Table 1, continued.
Ferryland Boston Québec City
1621–1673 1675–1740 1675–1699 c. 1700–1725
Species latrine latrine beach beach
Silvanidae
Oryzaephilus surinamensis Linnaeus+ (saw-toothed grain beetle) X
O. mercator Fauvel+ or surinamensis Linnaeus+ X
Uleiota debilis LeConte X
Laemophloeidae
Laemophloeus sp. X X
Cryptophagidae
Cryptophagus sp. (fungus beetle) X X
Endomychidae
Mycetaea subterranea Marsham+ (handsome fungus beetle) X X
Coccinellidae
Chilcorus stigma Say X
Latridiidae
Latridius minutus group Linnaeus+ (minute fungus beetle) X X X
Tenebrionidae
Gnatocerus cornutus Fabricius+ X
Bruchidae
Bruchus pisorum Linnaeus+ (pea weevil) X X
Chrysomelidae
Phyllotreta striolata Fabricius+ (striped fl ea beetle) X
Curculionidae
Dryophthorus americanus Bedel X
Anthonomus signatus Say (strawberry bud weevil) X X
Sitophilus granarius Linnaeus+ (granary wweevil) X X X
S. oryzae Linnaeus+ (rice weevil) X
Pelenomus fuliginosus Dietz X
Hylesinus aculeatus Say X
Polygraphus rufi pennis Kirby (four-eyed spruce bark beetle) X
Orthotomicus caelatus Eichhoff X X
Dryocoetes sp. X
Xyleborus affi nis Eichoff X
Pseudopityophthorus minutissimus Zimmermann X
Pityophthorus sp. X
Gnathotrichus materiarius Fitch X
Monarthum mali Fitch X
114 Journal of the North Atlantic Special Volume 1
substantial deposit of material accumulated within
the privy opening, resulting in a wealth of ecofacts
and artifacts (Fig. 2). After 1673, it appears to have
been used to deposit manure from the adjacent
stable, to which it was connected by a covered drain
(Gaulton 1997:86). The sediment samples discussed
here chronicle the use of the privy from the 1620s
to 1673, and the recovered beetle fauna represents
insects from the local environment which may have
accidentally fallen into the privy or been washed in,
as well as those which were incidentally deposited
into the privy with refuse (see also Bain and Prévost
2010, Prévost and Bain 2007).
In the Ferryland samples, ground beetles (Carabidae),
one species of water scavenger (Hydrophilidae),
bark beetles (Scolytidae), and fungus beetles
(Endomychidae) provide insight into the local
environment. The ground beetles are all Holarctic
in distribution, meaning they are found in northern
continents around the world. They are also wideranging
predators which normally feed on insects
such as maggots. Pterostichus adstrictus prefers
open landscapes with dry to moderately moist soil
and, at times, may be found on cultivated ground
(Lindroth 1966:487), while Bembidion petrosum
is found on bare sand often mixed with stones on
seashores (Lindroth 1963b:334). One of the most
widely spread circumpolar ground beetles is Dicheirotrichus
cognatus, living in open or thinly
wooded places, usually on dry, sandy moraines with
sparse mossy vegetation, and is commonly found
on the coastal zones of Newfoundland and Labrador
(Lindroth 1968:876). The hydrophilid beetle
Cercyon littoralis is found on the Atlantic coasts
of North America and Europe, living on beaches
under decomposing seaweed and under driftwood
and other detritus (Hansen 1987, Larsson and Gígja
1959, Smetana 1988). Two bark beetles were identifi
ed in this fauna: Orthotomicus caelatus is a species
native to North America and is found on species
of pine, spruce, or larch and often attacks stumps,
limbs, and branches of dying trees, as well as slash
(Wood 1982:664), while Polygraphus rufi pennis attacks
recently broken or cut spruce and white pine
trees (Wood 1982:389). The recovery of the endemic
scolytids, or bark beetles, suggests the use of wood
at the site. Cut wood had multiple uses in fi shing
and domestic settings, and the bark beetles suggest
weakened or cut wood.
This small fauna portrays the local environments
found at Ferryland, as they suggest a sparsely vegetated
coastal environment, with sandy moraines,
some cultivated lands and nearby beaches with detritus.
As the local coastal environment was cleared
for settlement construction, many of these species
would have been able to occupy microhabitats within
the urban environment that mirrored their natural
disturbed-land preferences. Disturbed-land species,
endemic or introduced, would have theoretically
had a competitive ecological advantage over autochthonous
woodland species, which would have been
temporarily displaced as the landscape underwent
anthropogenic transformations.
Members of the families Staphylinidae (rove
beetles) and other Hydrophilidae may be found in
contexts that contain excrement, compost, or other
rotting organic remains. Quedius mesomelinus is
often found near settled areas near outbuildings,
barns, and other farm buildings (Smetana 1971:78),
although it has also been collected in woodlands
in eastern Canada (Makja and Smetana 2007), and
in the nests of small mammals in Europe (Coiffait
1978). The hydrophilid Cercyon analis is found in
all manner of rotting organic matter, dung, decaying
plant debris, and compost piles, primarily in wet
conditions in North America, and the Palaearctic
region (Koch 1989, Smetana 1978).
The pea and granary weevils suggest the presence
of infested stores and their resulting products. These
may have been disposed of as infested stored goods
or arrived in the privy in the form of cess or human
waste. All six privy samples contained bruchids, and
as Bruchus pisorum (pea weevil) is the only member
of this genus found in Newfoundland (Bousquet
Figure 2. Excavation of the Area C Privy at Ferryland.
(Photo courtesy of James A. Tuck and the Colony of
Avalon Foundation).
2011 A. Bain and G. King 115
1991:301), it is very likely that all bruchid fragments
belong to this species. This insect is a serious pest
of fi eld or garden peas (Campbell et al. 1989:26).
Letters from Ferryland indicate seemingly abundant
pea cultivation (Pope 2004:10, 14), and the importation
of peas to Ferryland likely helped to establish
B. pisorum in Newfoundland, as it not part of the
indigenous fauna. These weevils would have been
transported within the stored peas, where the adults
overwinter (Campbell et al. 1989:27). They then
emerge in the fi eld, attacking young plants, thereby
sustaining the cycle of infestation.
Several species, which include Sitophilus granarius
(granary weevil; Fig. 3) and Oryzaephilus
surinamensis (saw-toothed grain beetle) indicate the
presence of cereal grains or grain products such as
fl our or bread. Sitophilus granarius is considered
one of the world’s most destructive pests of stored
grain (Campbell et al. 1989:224). This is a very
hardy species, as both adults and larvae are able to
overwinter in unheated storage buildings even in Canadian
winters (Campbell et al. 1989:225). Recent
accounts estimate insect-induced losses as ranging
from 5% in wheat to 40% in other stored products
in areas of the world in which insecticides are not
employed or “industrial” integrated storage control
is not practiced (McFarlane 1989, Payne 2002, Tyler
and Boxall 1984).
At Ferryland, the granary weevil was present in
all samples studied. For those living at Ferryland,
this pest fauna would likely have been a nuisance
that was not unfamiliar as it would have been a part
of English daily life. Indeed, archaeological records
indicate its presence in Britain as early as the 1st
century AD, when it likely arrived with supplies for
the Roman military with a possible re-introduction
of the species during the Norman Conquest in the
11th century (King 2010). The saw-toothed grain
beetle Oryzaephilus surinamensis is a secondary
grain pest, which is unable to exploit sound, dry
kernels, but often appears in numbers after attack by
other pests (Campbell et al. 1989:159–160), such as
the granary weevil. It is also an extremely common
pest of many kinds of foodstuffs, often infesting
dried fruits and packaged foods (Campbell et al.
1989:159, Halstead 1993).
Other species address the storage conditions
housing these grains. Members of the families Cryptophagidae
and Latridiidae generally feed on molds,
fungal spores, and decaying vegetation (Campbell
et al. 1989). Synanthropic cryptophagids generally
indicate poor storage conditions that promote
excessive growth of mold (Campbell et al 1989:
147), while the latridiid fauna, a family of exclusive
fungal feeders, also indicates a moist and moldy
environment (Bousquet 1990:129). The introduced
Mycetaea subterranea (syn. M. hirta) (handsome
fungus beetle), of the family Endomychidae, is, as
its name implies, a fungus feeder which has been
found in a wide variety of synanthropic settings including
cellars, barns, and houses. However, it has
also been collected from decaying trees and ants’
nests (Bousquet 1990:126, Horion 1961).
Two spider beetles were recovered. Tipnus unicolor
is strongly synanthropic and can be found in
cereal products, as well as in many other damp environments,
such as in wet wood or decaying litter
or other organics (Osborne 1983:459), while Ptinus
fur (white-marked spider beetle) lives in granaries,
warehouses, and houses, where it feeds on grains and
fl our. However, this species is considered polyphagous
and is also known to feed on dried and decaying
animal, fi sh, and vegetable matter (Campbell
et al. 1989:332; Follwell 1952:61; King, in press;
Osborne 1981:268). The deposition of meat into the
privy is also indicated by the presence of Creophilus
maxillosus (hairy rove beetle), a sometime predator
of fl y and beetle larvae, although this species is also
known to feed on fresh or partly decomposed meat
and old bones (Campbell et al. 1989:380, Hinton
1945). In the privy, it may have been feeding on fl y
larvae, on meat, or on fi sh.
Osborne (1983) demonstrated that insect fragments
could successfully pass through the human
dietary tract without damage. It is highly probable
that the grain and pea pests entered the latrines in
this manner. They were likely incorporated into
low quality bread or stew and then into waste. The
infesting weevils, the fungus beetles, and the spider
beetles may have all been living in the homes of the
local settlers. More likely, the cryptophagids, latri-
Figure 3. Preserved granary weevil (Sitophilus granarius)
head and pronotum from the 1620s level in the Ferryland
privy (Photo courtesy of the Environmental Archaeology
Laboratory, Université Laval).
116 Journal of the North Atlantic Special Volume 1
visioned to the Massachusetts Bay Colony in the
early 17th century.
Amongst the many pest species were pea weevils,
the granary weevil, the saw-toothed grain beetle, and
spider beetles. Phyllotreta striolata (striped fl ea
beetle), known to attack cruciferous vegetables such
as cabbage and turnips, was also identifi ed (Bain and
LeSage 1998). Nicrophorus investigator is a carrion
feeder (Anderson and Peck 1985), while Creophilus
maxillosus, Trox scaber, Dermestes lardarius, and
Omosita colon are all occasional carrion feeders
(Hinton 1945, Osborne 1983, Vaurie 1955). Dermestes
lardarius is a household pest found on a wide
variety of products including bacon, ham, dried fi sh,
and cheeses (Kingsolver 1991), and its larvae have
been known to attack and kill chicks and ducklings
(Peacock 1993). While a common infester of dried
carrion, T. scaber also attacks hides, skins, and fl eece
(Koch 1989). The presence of the adventive ground
beetle Bembidion tetracolum suggests disturbed
ground with some organic remains around or in the
privy (Lindroth 1963b:331–332, 1985), while the
presence of fruit trees is indicated by Amphicerus
bicaudatus (apple twig borer) (Fisher 1950). Several
species reveal the types of wood in use locally, such
as oak, suggested by Pseudopityophthorus minutissimus
(Bright 1976), and chestnut, indicated by the
scarab beetle Xyloryctes jamaicensis, which is often
taken beneath chestnut bark (Ritcher 1966).
While the identifi ed beetle fauna bears witness
to impressive number of introduced species that
were present at the site, this assemblage also reveals
details about daily life of household members in colonial
Boston and suggests storage conditions, while
also detailing the local urban environment in and
around the privy.
Îlot Hunt site, Quebec City
Îlot Hunt is located in the Lower Town of Quebec
City, the historic port, business, and banking center
of the city. This area was cramped between the river
and the cliff leading to Upper Town. The narrow
strip of land along the riverside was eventually extended
out into the St. Lawrence, as reclaiming land
from the river was the only solution to overcrowding
(Simoneau 2003). Charles Aubert de la Chesnaye,
one of New France’s most enterprising merchants,
was granterd two Lower Town water lots in 1687,
and the site was rapidly transformed and expanded
out into the river over the following two centuries.
De la Chesnaye built a coffer-like frame around the
lots in 1688 to combat the effects of high tides and
to allow small boats to remain within the frame for
offl oading merchandise (Fig. 4). In 1699, he built
a stone wall or wharf, sheathed in timbers behind
both water lots to counter erosion (Fig. 5) (Cloutier
2009, Rouleau 2009:232–5). A large stone defensive
diids, endomychids, and the spider beetles represent
hay or straw that was introduced into the privies
in an effort to depurate the deposits. Globally, the
samples refl ect a typical English diet at the time
of peas and bread, complemented by meat and, not
surprisingly, some fi sh. The inhabitants of Ferryland
were clearly subjected to the ravages of insect pests
on their pea and fl our stocks, which may have been
stored in rather damp conditions.
Cross Street Back Lot site, Boston
The Cross Street Back Lot site in Boston was
home of the widow Katherine Nanny Naylor, who,
to the misfortune of those around her, but happily
for archaeologists and historians, was involved in
a number of lawsuits which left a rich documentary
history connected with her, revealing details
about her daily life in Boston around the turn of the
18th century. From deeds, probate inventories, and
other historic documents, we know that she lived
on Ann Street, was married twice and had eight
children with her first husband, only two of whom
lived past childhood. While she was widowed by
her first husband, Robert Nanny, she successfully
sued her second husband and father of two more
children, Robert Naylor, for divorce (Cook 1998,
Cook and Balicki 1996). The family privy was located
in the backyard of their home on Ann Street,
an early street along the waterfront of Boston Harbor,
where wharves were constructed into the Great
Cove (Boston Harbor) before 1700 (Cheek 1998).
The privy yielded a wealth of information. Pollen
grains, seeds, bones, insects, fabric, and shoes were
all the subject of specialist studies along with material
culture analyses (Cheek 1998).
Over a thousand individual beetles were identified
from these samples, including 24 adventive
species (Bain 1998), which represent a third of
the taxa identified. Similar to the Ferryland privy,
most of the recorded members of the Staphylinidae
and Hydrophilidae families detail a privy environment
with rotting organic matter, such as composting
domestic wastes as would be expected, or floor
sweepings. Several staphylinid and hydrophilid
species may also be found in dung, which was a
likely pabulum for Oxytelus sculptus, Carpelimus
obesus and Philonthus politus (Hall et al. 1983)
as well as for the scarab beetles, including the
introduced Calamosternus granarius (Gordon
1983, Landin 1961), formerly Aphodius granarius.
Most species from the families Staphylinidae,
Hydrophilidae, and Scarabaeidiae identified in
this fauna were introduced to this region, crossing
the Atlantic hidden in and amongst food stores,
animal fodder, packing materials and ships’ ballast
brought over by colonists. Sailer (1983) posits that
C. granarius was introduced when cows were pro2011
A. Bain and G. King 117
battery, the First Dauphine
Battery, was built
on the site between 1707
and 1709, partly using de
la Chesnaye’s wall as well
as that of his neighbor,
Jean Gobin. The samples
discussed from the Îlot
Hunt site include deposits
taken from the beach
levels which pre-date the
1699 wharf construction,
and from an organic deposit
formed in the fi rst
quarter of the 18th century
directly on the shoreline.
Beach samples: 1675–
1699. These samples
were taken from a layer of
orange-colored sand containing
large amounts of
organic matter including
branches, bark, and wood
chips. This level was noted
elsewhere on the Îlot
Hunt site and on other
excavations focusing on
Figure 4. A c. AD 1695 view of Quebec City, with a red oval indicating Charles Aubert de
la Chesnaye’s property with its enclosure. (Vue de Québec, avant 1700, anonyme, National
Archives of Canada BK/340).
Figure 5. View of the walls on the de la Chesnaye and Gobin properties constructed around 1699 and later transformed into
the Dauphine Battery. (Image courtesy of the Service des communications, Ville de Québec).
118 Journal of the North Atlantic Special Volume 1
1700–1725. As previously stated, the de la Chesnaye
wharf was transformed into a defensive Battery
in 1707–1709, referred to as the First Dauphine
Battery. This deposit appears to also have formed
directly on the beach front, the shoreline of the St.
Lawrence River. Lots of stones and sand made up the
sample matrix which also contained wood, bones,
bark, fabric, and leather scraps.
Bembidion scopulinum, taken at watersides with
sterile soils or little to no vegetation, was again
found in this sample, as was Bembidion musicola,
which is, conversely, found near water with sedges
along the edges, and is easy to collect during fl ooding
(Lindroth 1963b:388). The hydrophilids Hydrochus
sp. and Helophorus frosti also indicate aquatic
habitats (Smetana 1988:19). The riffl e beetle Optioservus
ovalis is found on stream edges, on clear fresh
water with a strong current over a gravel substrate,
or amongst rocks covered with moss in clear water,
while Stenelmis from the same family (Elmidae)
is often found in cool, rapid streams (Arnett et al.
2002:117–118).
The lady bug Chilocorus stigma is found in a
wide variety of environments, some of which include
sandy substrates, and around many types of
trees (White 1983:235). The scarab beetle Aegialia
sp. also implies that the deposit accumulated on a
sandy substrate, as all members of this genus are
found in sandy settings along rivers and lakes (Ratcliffe
and Paulsen 2008:141). Felled or weakened
ash trees are represented by Hylesinus aculeatus
(eastern ash bark beetle; Campbell et al. 1989:368),
whereas Monarthrum mali is commonly found on
maples, elm, birch, beech, oak, and linden (Bright
1976:188, Wood 1982:1235).
Similar to the other insect faunas in this study is
the presence of numerous members from the families
Staphylinidae and Hydrophilidae, representing
organic remains on the beach front, likely the result
of domestic trash disposal. These species include
Quedius mesomelinus, Neohypnus sp., and Carpelimus
sp. Calamosternus granarius was also recovered,
and although often associated with the dung of
domesticated herbivores, particularly cow dung, it is
also known to feed on carrion and decaying vegetation
(Ratcliffe and Paulsen 2008:178). Moss in this
environment is indicated by Cytilus alternatus, a
member of the Byrrhidae (Arnett et al. 2002:114).
Stored products such as cereals are represented by
Sitophilus granarius (granary weevil) as well as a
member of the Latridius minutus group. While the
L. minutus group of insects exploits damp environments,
they are, along with the granary weevil,
introduced and are thought to represent the presence
of stored products in Canada (Campbell et al. 1989),
although in European contexts they are primarily
the historic Quebec City waterfront. Artifacts used
to confi rm the late 17th-century date include French
Saintonge earthenware, Beauvais and Normandy
stoneware fragments, fragments of Bellarmine
pottery, and 17th-century Dutch smoking pipes (Simoneau
2003:28). Artifacts such as gun fl ints, fi sh
hooks and line, knife handles, barrel fragments, slate
tiles, hardware, bones with butchery marks, bricks,
French bricks, and the remains of at least 34 leather
shoes represented by over 500 fragments were found
as well. According to Simoneau (2003:29), this site
is defi nitively a beach level, though one that includes
domestic, workshop, and construction wastes, and
had been affected by the tides.
Two species of ground beetles tell us about
the waterfront. Bembidion scopulinum lives on
riversides generally clear of vegetation (Lindroth
1963b:343), while another Bembidion may be the
species versicolor or mimus. Both species are often
found together, close to water or puddles and always
on soils containing organic materials, even if the
soils are sandy, clayey, or made of turf (Lindroth
1963b:378–380).
Other beetle families indicate that the environment
around this deposit was rich in decaying
organic remains, perhaps as a result of domestic
waste disposal, corroborating Cloutier’s (2009)
interpretations. These insect species include the
members of the Staphylinidae and Hydrophilidae,
which generally live in all sorts of decaying organic
material. The staphylinid Carpelimus cf. bilineatus
is common in wet compost as well as along the sandy
muddy banks of fl ood zones (Koch 1989), while the
hydrophilid Cercyon analis also prefers damp, decomposing
habitats (Smetana 1988:165). Gyrohypnus
fracticornis was present too and may indicate a
habitat containing foul compost or dung; however,
the species has also been noted in sweet compost,
like straw, and fl ood debris (Koch 1989). All three
of these species were introduced to the region.
Numerous insects of the families Endomychidae,
Latridiidae, and Anobiidae (Mycetaea subterranea,
Latridius minutus, and Ptinus sp., respectively) live
on mold and fungi associated with stored products
such as cereals (Bousquet 1990) as well as moldy
wood, hay, and straw (Koch 1989). The presence of
cut and stacked pine is indicated by remains of the
weevil Dryophthorus americanus, found on stumps,
under pine bark, and around wood piles (Blatchely
and Leng 1916).
It appears then that these beach samples represent
the Lower Town during the French regime and
this small fauna revealed a beach front littered with
organic wastes and construction debris and perhaps
the remains of stored products.
Beach level in front of the Dauphine Battery c.
2011 A. Bain and G. King 119
1950, 1967; Lindroth 1954, 1955, 1957, 1963a;
Klimaszewski et al. 2010). Sailer (1983) commented
that many introduced species likely arrived sooner
than previously thought, only they simply went
unnoticed or were not worthy of mention, as they
were simply part of the expected fauna or had no
economic signifi cance in people’s daily lives. Other
species, such the pea weevil, were specifi cally mentioned
as people tracked its route of infestation in the
17th century (Russell 1982). This documented record
is to be expected as it is a very serious pest of fi eld
peas. The specifi cs of their life cycle would have
made them diffi cult to eliminate, and they may have
been particularly problematic in the English colonies
with a diet that typically included a lot of peas.
The granary weevils exhibit a similar behavior in
regards to their oviposition in cereal kernels, which
has likely contributed to the success of their infestation
and dispersal in the past (see King 2010).
The three sites examined here were chosen as it
was hoped they would, given their proximity to the
Atlantic shoreline and St. Lawrence River, represent
faunas that were biased towards a representation of
the ecological shift experienced through the historic
period with the arrival of fi shers and other settlers.
The resulting faunas do indeed confi rm that the European
insect faunas arrived early and in important
numbers. The privy site of Boston is a startling example,
which in a single feature documents the presence
of 24 species of adventive insects in the early
18th century.
After the remaining local forests were cleared
away to make room for settlement, new urban environments
and their insect assemblages of indoor
or household fauna related to grains stores, animal
fodder and bedding, fl oor sweepings, food stores,
and other domestic wastes quickly took hold (Hall
and Kenward 1990). The ships coming out to the
New World, from an entomological perspective,
mirrored these domestic environments as they contained
all the essential elements of colonial life,
including seeds, hay, domesticated mammals, food
stores, packing materials, and furniture (see Buckland
1988, Buckland et al. 1995, Sadler 1991). For
example, the white-marked spider beetle was fi rst
recorded in the United States in 1869, though it is
known to thrive on any number of stored products,
including an entirely fi sh-based diet (Campbell et
al. 1989:332). Such an opportunistic species would
have easily been able to survive the trans-Atlantic
crossing and to thrive on shores, like at Ferryland,
where fi sh processing took place. In the three faunal
assemblages examined here, the introduced biota—
including the pea weevil, the granary weevil, and
the majority of the adventives species represented
in Table 1—largely belong to this synanthropic
environment group and likely travelled to the New
considered synanthropic mold feeders (Buckland
and Buckland 2006). Anthonomus signatus (strawberry
bud weevil) indicates local wild berries. This
weevil can cause serious economic injury to strawberries,
raspberries, and blackberries (Campbell et
al. 1989:165), and in this context, the weevil was
likely associated with waste deposits, as the active
littoral zone would not encourage the growth of
these berry species.
Fortuitously, written sources discuss the creation
of this deposit. In 16 April 1710, an ordinance stated
that all citizens of the Lower Town should “de porter
ou faire voiturer toutes leurs ordures, vidanges et
démolitions dans l’emplacement de feu sieur Aubert
de la Chesnaye dont on a tiré la terre pour faire des
batteries”. In other words, garbage was to be hauled
or carried to the property of de la Chesnaye, where
soil was removed to construct the defensive batteries
(Saucier 1958:55). We likely have evidence then
of the intentional creation of land through waste
disposal. Not surprisingly, the deposit is a mixture
of domestic trash mixed amongst natural shoreline
deposits of branches and beach fl otsam.
The beetles portray a riverside setting with
little vegetation, and the water appears to have
been relatively clean, likely due to the cleansing
effect of the high tides. The substrate appears to
have been primarily sandy, with clay mixed in.
The bark beetles are perhaps present as the result
of construction nearby, and we have clear evidence
of the disposal of domestic wastes at the river’s
edge. Interestingly, while slightly later in date,
the Dauphine Battery samples represented a fairly
indigenous fauna, particularly in regards to the
ground beetles, hydrophilids, and riffle beetles, in
comparison to the 1675–1699 samples. However,
European species were present in both contexts,
representing the creation of proto-urban faunas in
the New World.
Discussion
Ecological, climatic, and environmental transformations
are often studied from the perspective of
a single discipline or specialization. However, environmental
archaeological studies on colonial period
sites allows for the analyses of multiples lines of
data as seen in the present project. Entomologists are
keenly aware that many species of Coleoptera were
transported to the New World well before people
started collecting beetles, and especially in the 19th
century. Species composition of early insect collections
refl ects a time interval of two hundred years
or more after some initial introductions, and much
speculation about the dates, causes, and routes of
entry to the New World has focussed on the distribution
of Coleoptera to Atlantic Canada (Brown 1940,
120 Journal of the North Atlantic Special Volume 1
The introduction dates of many Old World species
recorded by archaeoentomological studies make
a signifi cant contribution to the fi elds of natural
history in general and entomology in particular.
When comparing the introduction dates generated
from insects from archaeological sediments with
suggested introduction dates published in entomological
literature, the archaeoentomological data
indicates that some species were introduced two to
three hundred years earlier than previously thought,
and clearly outline the rapidity and intensity of this
colonial biological transfer.
Conclusion
Ports and waterside settlings in colonial North
America played a critical role in facilitating the
Europeanization of the New World fl ora and fauna.
While the privies of the Ferryland and Cross Street
Back Lot sites clearly show the high proportion of
introduced species by the late 17th century, they are
primarily European domestic faunas, likely common
to households of this time period in both the Old and
New Worlds. Similarly, the autochthonous fauna
from both sites appear to indicate early human activities
along a coastal environment: deforestation and
land clearance resulting in the rough, sandy ground
common in an urbanizing landscape. The two faunas
formed on the St. Lawrence River shoreline at the
Îlot Hunt site tell a different story, as they reveal a
privileged snapshot of the transforming shoreline.
These studies are important from a historical social
perspective, elucidating details about daily life and
social and economic practices and local environments
of the colonial world, but also for their value
as natural history studies. These fragments tell the
fascinating story of a long-term biological transfer
that is still ongoing today.
Acknowledgments
First round of thanks to Beatrix Arendt and George
Hambrecht for their invitation to publish this paper and
their patience. Several entomologists from the Canadian
National Collection of Insects in Ottawa, ON, Canada,
archaeological colleagues from Timelines, Inc., John Milner
Associates, Memorial University, the Ville de Quebec,
and students from Université Laval helped us to gather,
process, and at times, identify the insect remains discussed
here—thanks to you all! Warm thanks are also extended to
Christopher Majka, David Smith, Harry Kenward, and to
an anonymous reviewer for their valuable comments on
earlier drafts of this paper.
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