Ecological Impact of Introduced Crayfish on Benthic Fishes in a British Lowland River

Pacifastacus leniusculus (Dana), a native crayfish of western North America, was introduced into the U.K. in 1976. Our study examined some interactions between P. leniusculus and benthic fish in a British lowland river, the River Great Ouse. In a river survey an inverse correlation was found between the abundance of crayfish and the two dominant benthic fishes, bullhead (Cottus gobio L.) and stone loach (   Noemacheilus barbatulus [L.]) in six riffles. The benthic fishes were least abundant in the riffle nearest the original site of crayfish introduction and gradually increased in abundance both up and down river as crayfish abundance decreased. The hypotheses that crayfish compete with bullheads and stone loach for shelter and prey on fish were tested by laboratory experiments in an outdoor artificial stream (6 × 2 m) with recirculating water and 12 artificial shelters on the bottom. In competition experiments 12 fish of one species were alternatively kept alone and with 12 crayfish for 3-day cycles lasting a total of 12 days. The results showed that crayfish out-competed both fish species for shelter. Predation was measured by keeping 24 fish of each species alone and with 36 crayfish for 10 days respectively in the artificial stream. The mortalities of both fish species were significantly higher when crayfish were present. The loss of fish could be partly due to predation because crayfish guts contained the remains of some lost fish and they were observed preying on both fishes in a tank. In the river crayfish lived at high densities reaching ≥ to 20 m⁻² in riffles, and they continued to disperse. This may lead to a great reduction in benthic fish abundance if not local extinctions.     

Importance of heterotrophic planktonic communities in a mussel culture environment: the Grande Entrée lagoon,Magdalen Islands (Québec,Canada)

Mussel culture in coastal environments relies on the availability of food of sufficient quality and quantity. Both to determine this availability and to examine impacts that this aquaculture practice may have on the environment, it is important to have good knowledge of the type of plankton communities present in aquaculture sites. It is usually thought that phytoplankton make up the bulk of mussel diet in many of these sites. Here we show that the Grande-Entrée lagoon [Magdalen Islands, Gulf of St Lawrence (GSL), Canada], where commercial mussel culture has been on-going since 1980, differs from this pattern. Heterotrophic protists dominate for most of the summer-early fall season (apart from short diatom bursts), with a high average biomass of 160 mg C m⁻³. The dominance of small-sized phytoplankton cells (notably green algae), low nutrient concentrations (e.g. 0.3 μM NO₃⁻ on average) and high biomass of heterotrophic protists (mostly naked ciliates and tintinnids) all point to the importance of the microbial food web in this shallow marine environment. Sustained cultivation of suspended mussels in the lagoon suggests that these heterotrophic protists could be an important source of food for the mussels, supplementing the small amount of phytoplankton present.     

Rehydration of desiccated intertidal brown algae: Release of dissolved organic carbon and water uptake

The release of dissolved organic carbon (DOC) by Ascophyllum nodosum (L.) Le Jol. and Fucus vesiculusus L. during rehydration was investigated after desiccation under experimental conditions. During 30 min of rehydration of plants which had lost up to 70% of their water, A. nodosum released about 2 to 10 mg C/100 g dry weight, while F. vesiculosus released 10 to 50 times more. When dried to water losses exceeding 70%, plants of both species yielded similar amounts of DOC, approximating 2 g C/100 g dry weight. Considerable variance in the amounts of DOC released by individual plant of both species was observed over the whole range of water losses tested. Among the DOC released, the portion of carbohydrate-C was O to 5% with A. nodosum but 2 to 47% with F. vesiculosus. This difference was most pronounced when less than 100 mg C/100 g dry weight were released. A. nodosum regained a smaller percentage of its original weight than F. vesiculosus after 30 min of rehydration when more than 30% of fresh weight were lost during desiccation. Curves were obtained which enable the estimation of water losses in naturally desiccated specimens within 30 min.     

Restoration of native biotic communities on land disturbed by metalliferous mining

The worldwide expansion of the metalliferous mining industry has caused increased attention to be directed at the reclamation of mine wastes. Until recently the majority of reclamation procedures were based on substrate amelioration with innocuous covering materials, the application of fertilisers and the sowing of non-indigenous species. Reinstatement of the native flora and fauna was rarely attempted. However, in several countries the mining legislation now requires reinstatement of at least the native vegetation as a reclamation objective. Many mines are located in natural ecosystems such as tropical and temperate forest, and arctic and alpine tundra where faithful reinstatement of the native flora and, if possible, the fauna is the prime objective.Despite the adverse physical and chemical properties of metal mine wastes, the requirements for the restoration of native floras and faunas are not impossible to meet. This paper reviews procedures for the restoration of native vegetation on land disturbed by metalliferous mining, and assesses the success of the procedures where appropriate evidence is available. Using these methods it has often been possible to create a permanent, self-perpetuating and relatively maintenance-free native vegetation which provides a diverse mosaic of habitats for native fauna to colonise. However, the development of methods for reinstatement of native biological communities on metalliferous mine wastes is in its infancy. Proper criteria have not yet been established for the assessment of the success of reinstatement and there is a paucity of published qualitative information on the success of restoration of native plant communities, particularly information covering a sufficient period of time to be ecologically meaningful.     

The contribution of derelict mineral and industrial sites to the conservation of rare plants in the United Kingdom

The contribution of derelict industrial sites to the conservation of rare plants in the British Isles is reviewed. Many sites have acquired considerable biological interest and have been designated Sites of Special Scientific Interest or nature reserves. In most cases the development of wildlife interest has in the past been fortuitous rather than planned. There is, however, increasing evidence that the deliberate re-development of specific areas of derelict land for wildlife conservation is technical feasible. Whilst the forward planning of new mineral developments must continue to take account of existing wildlife values to minimise potential conflict and losses, nature conservation may, in certain circumstances, be considered as viable an endopoint as the more commonplace objectives of landscape rehabilitation. Further development of this policy could provide a means of compensating for the inevitable losses that will occur in the future, and greater attention must be paid to the potential of derelict industrial sites in this context.