Mercenaria mercenaria
Date of introduction and origin
Mercenaria mercenaria originates from the east-coast
of N. America (Nova Scotia, Canada to Yucatan, Mexico. The first
live specimen was found in the Humber in 1864 and last recorded
from Cleethorpes in 1907 (Heppell 1961). It was successfully
introduced from the USA, possibly the New York area, in 1925 to
Southampton Water (Mitchell 1974). There were earlier introductions
but none resulted in the establishment of self-sustaining
populations.
Method of introduction
There was deliberate commercial introduction a barrel of live
clams was imported from the USA to be tried as eel bait. Some were
laid in the River Test arm of Southampton Water in the cooling
water discharge from the former town power station (Mitchell 1974).
The point of introduction is now under the Eastern Docks extension.
Some were introduced into the Fleet, Dorset, in the early to
mid-1960s, where they persisted for some time but do not appear to
have bred (D.R. Seaward pers. comm.). It is considered that some
clams may also have been thrown overboard into Southampton Water
from transatlantic liners using the port, but there is no direct
evidence for this unlikely event (Ansell 1963).
Reasons for success
The population has apparently increased since the 1950s,
possibly due to occupying the niche of the soft-shelled clam
Mya arenaria, which was eliminated from the estuary by the
cold winters of 1947 and 1962/63 (Mitchell 1974). The Mya
arenaria population has never recovered. Favourable physical
conditions are likely to be the prime reason for the original
colonisation. There were ideal estuarine conditions available i.e.
lowered salinity and soft substrata with temperatures elevated by
power station cooling water discharges from Southampton power
station and later Marchwood Power Station (opened in 1957) almost
opposite the original site of introduction. Further heating of
Southampton Water and the eastern Solent has occurred through
industrial cooling water discharges from ESSO Fawley and the Fawley
Power Station (Mitchell 1974, 1976). Furthermore, it appears that
this species has become physiologically adapted to be able to spawn
at 3-4·C lower (i.e. 18-19·C) than populations in its area of
origin (Mitchell 1974, 1976). Hibbert (1976) recorded some spawning
at 17·C.
Rate of spread and methods involved
Since the original introduction to upper Southampton Water in
1925, the population has spread naturally by larval dispersal along
the eastern side of Southampton Water and into Portsmouth and
Langstone Harbours in The Solent. Some dumping from the fishery has
probably helped to augment the populations in Portsmouth and
Langstone Harbours. A substantial number have also been introduced
to Newtown Harbour, Isle of Wight, and the Blackwater Estuary,
Essex. Specimens obtained from the north Isle of Wight are never
smaller than 80 mm suggesting that this population is not breeding
(J. Light & I. Killeen pers. comm.).
Distribution
The extent of its current occurrence is the eastern side of
Southampton Water, Portsmouth and Langstone Harbours, sporadically
between Newtown Harbour and Ryde Pier along the north coast of the
Isle of Wight (J. Light & I. Killeen pers. comm.) and the
Blackwater Estuary, Essex. In Europe populations exist in The
Netherlands and France but it is not known whether these are
self-sustaining.
Factors likely to influence spread and distribution
Elevated estuarine temperatures through heated industrial
discharges are likely to favour the spread of this species in
British waters, especially where the temperature required for
reproduction is reached. Dumping and deliberate introduction
attempts by fishermen and fishery scientists also influence its
spread.
Effects on the environment
It filled the niche left by the cold weather die-off of the
soft-shelled clam Mya and thus prevented they
re-establishment of Mya. Digging and dredging for this
clam has a significant effect on the environment, particularly eel
grass Zostera beds (Cox 1991; Anon. 1992). The populations
of Mercenaria in the Solent are now very low (MAFF pers.
comm.).
Effects on commercial interests
No commercial interest is known to have been adversely
affected by the arrival of this species. Instead it has supported a
thriving fishery from the 1960s to the present. Latterly the
fishery has been severely depleted, primarily due to poor spatfall
(MAFF pers. comm.), but possibly due also to the large numbers
taken and physical damage to the environment.
Control methods used and effectiveness
The species is not controlled although the population has been
severely depleted by the fishery.
Beneficial effects
See above.
Comments
The history of Mercenaria mercenaria in
England has shown that deliberate introductions can work
commercially.
References
Anon. 1992. An experimental study on the impact of clam
dredging on soft sediment macroinvertebrates. (Contractor:
Southern Science, Hampshire Laboratory, Otterbourne, Hants.)
Unpublished report to English Nature. (English Nature Research
Report, No. 13.)
Ansell, A.D. 1963. Venus mercenaria L. in Southampton
Water. Ecology, 44: 396-397.
Cox, J. 1991. Dredging for the American hardshell clam - the
implications for nature conservation. Ecos. A Review of
Conservation, 12: 50-54.
Hayward, P.J., & Ryland, J.S. eds. 1990. The
marine fauna of the British Isles and north-west Europe. 2
vols. Oxford, Clarendon Press.
Heppell, D. 1961. The naturalization in Europe of the quahog,
Mercenaria mercenaria (L.). Journal of
Conchology, 25: 21-34.
Hibbert, J.H. 1976. Production studies of a bivalve population
on an intertidal mudflat, with particular reference to the energy
budget of Mercenaria mercenaria (Linne). PhD Thesis,
University of Southampton.
Mitchell, R. 1974. Aspects of the ecology of the lamellibranch
Mercenaria mercenaria (L.) in British waters.
Hydrobiolgical Bulletin, 8: 124-138.
Mitchell, R. 1976. A possible relationship between rate of
river flow and recruitment in an estuarine bivalve population.
In: Freshwater on the sea, ed. by C.M. Skreslet,
203-209. Oslo. Association of Norwegian Oceanographers.
Acknowledgements:
Dr R. Mitchell, English Nature.