SUMMARY 293The study of fauna of any region is closely connected with the investigation of taxonomicposition of species within the taxa under consideration. Traditionally, the verbalshell description is mostly used in bivalve mollusks systematics. In spite of the numerousmodern molecular researches, the conchological features make up the basics of our knowledgein this field up to now. That is why many malacologists try to formalize valve shapein order to make possible mathematical processing of data. Calculation of shell proportionsbecame one of the first steps in this direction. This method primary used in the beginningof the 20-th century (Odhner, 1915; Mossewitsch, 1928; Mesiacev, 1931) seemed verypromising and many authors suggested results of the shell shape analysis as crucial; but forall neither ecological plasticity nor age dynamics of the shell proportions were taken intoaccount. A number of species and infraspecific forms were recognized (Derjugin, Gurjanova,1926; Mossewitsch, 1928; Mesiacev, 1931) unfoundedly as a result. The approachdescribed was very important, no doubt, but it should be notified that regression analysiswidely extends the possibilities of mathematical methods in bivalve mollusks systematics.On one hand, it allows distinguishing closely related species with similar shell proportions,and on the other it proves to be a convenient tool for exploration of an intraspecific variability(Naumov, Fedyakov, 1985, г). Moreover, it allows synonymizing mistakenly describedspecies. Thus, the analysis of relationships between different dimensions of clamshells is very useful as a parallel approach to traditional investigation of their shape, because,in some cases, it becomes more informative and permits direct comparison of differentaged samples. That is why in every case when available material allows, both proportionsof the shell and regression equations are included in species diagnoses placed in thisbook.The fauna inventory being an essential base of any faunistic investigation cannot be theend in itself nowadays. There are numerous important aspects concerning ecosystems functioning:Seasonal and long-term dynamics of species abundance in concrete biotopes is oneof them. Investigation tradition considers such changes to be related with impact of abioticfactors. Meanwhile, the more data is accumulated, the more cases of dynamics that cannotbe explained by direct influence of environmental characteristics we observe.Previous observations of dense settlements of Mytilus edulis (Lukanin et al., 1986, а, б,1989, 1990), Macoma balthica and Mya arenaria carried out by the author and his colleaguesshowed that long-term dynamics of abundance in species mentioned above cannotbe totally explained by seawater temperature and salinity oscillations. Only elder, fully developedspecimens can be often found in the colonies of some species, while juvenilesrarely are encountered (Flyachinskaya, Naumov, 2003). Mathematical simulation of colonydevelopment created by the author demonstrates cyclic oscillations of biomass and populationdensity, generating by recruitment conditions. This process can be regulated by adultmollusks. The possibility of such regulation is rather doubtless, however its mechanismswidely discussed in literature are not clear enough (Woodin, 1976; Möller, 1986; ´Olafsson,1989 and others). The model is based on the demographic vector search in arbitrary timemoment using Leslei transfer matrix depending on recruitment and differential mortalityrate in individual generations. A new function for differential mortality rate was developed.The model obtained is rather flexible. Depending on initial parameters, it can describe bothunchanging colonies and colonies, which possess different autocyclic oscillations of biomassand density. The generation of dynamics with relaxation oscillations of abundance isalso possible.Bivalve mollusks, being one of the most important benthic groups, play an essential rolein many processes, which proceed in sea floor communities. In particular, cyclic oscillationsof blue mussel abundance on a huge mussel bed was the main reason which provokedstarfish Asterias rubens to be abnormally washed ashore on the Letny Shore (Dvina Bay) in1990 (Buryakov, Naumov, 1991; Naumov, Buryakov, 1994). Obviously, the role of clams
294SUMMARYis not cut down to participation in rare events with such dramatic results, as it took place inspring 1990.It was shown during our investigation in Onega Bay that the biomass of fouling organismson hard sediment enlarges in biotopes where high number of big clams was observed(Naumov, Fedyakov, 1985, a). Possible explanations can be the following: fouling organismsand mollusks investigated need similar environmental conditions, fouling organismsare attracted by mollusks metabolites and shells of big clams can be used as an additionalsubstrate by fouling organisms.Results obtained show that both extensiveness and intensiveness of the shell foulingmostly depend on the shell length. It means that both are functions of substratum time existence,i. e., of a mollusk’s individual age. The development of fouling community on valvesof living clams resembles the primary succession on hard sediment (Naumov, Fedyakov,1985, б, в, 1993; Naumov et al., 1986, а; Naumov, 1990).Two types of such successions were described by the author and his colleagues. In thefirst case, species composition did not change during the life of substrate species. It wasobserved for living clams with vertically orientated valves, such as Mytilus edulis andModiolus modiolus. Similar development of fouling was noticed for living Elliptica elliptica(Naumov, Fedyakov, 1985, б, в, 1993; Naumov et al., 1986, а; Naumov, 1990). Thus,the succession process in this case is reduced to simple increasing the abundance of differentsessile organisms.The second type of succession was observed on horizontally orientated valves of livingChlamys islandica. Species composition of fouling organisms on different valves of scallopshells significantly differs. This allows dividing of the consortium of fouling organisms intotwo strata: upper and lower. Unlike of the first type, in this case dominant forms changemore than once, especially on the upper valve, i. e. the process affects the structure of consortium(Naumov, Fedyakov, 1985, б, в, 1993; Naumov et al., 1986, а; Naumov, 1990).The succession processes lead to climax association in both cases since fouling of oldliving clams closely resembles the fouling of rocks in the same ecosystems (Naumov,Fedyakov, 1985, б).The fraction of deposit feeders among Arctic bivalve endemics is approximately twotimes higher than in clams of other origin. This can be explained by lower phytoplanktonproduction caused by thick ice cover leading to weak illuminace in Arctic seas. One cansuggest that gathering deposit feeders feeding on decaying organic matter will have an advantageover filter feeders in such conditions (Naumov, Fedyakov, 1990, 1994). Comparisonof the proportion deposit feeders in various seas of different biogeographical regionsconfirms this hypothesis (Tabl. 0). After this suggestion, the White Sea can be defined as awaterbody intermediate between boreal and Arctic seas.The peculiarities of individual species with respect to main environmental factors areimportant for characterizing any regional fauna. Seawater temperature and salinity are mostsignificant for marine organisms. Since the White Sea waters are not stratificated by temperaturein winter, being cooled down close to 0°C or even below in the entire watercolumn,distribution of bottom animals depends on summer temperature. Original author’sdata stored in the “Benthos of the White Sea” database were used for investigation of clamdistribution concerning the temperature in July–August. The database contains results ofbenthic investigations carried out by the White Sea Biological Station (Zoological Institute)since 1981. Analysis of this material showed that the most part of the White Sea bivalvemollusks prefer summer temperature diapason ranged between 0 and 10°C. Three groups ofthem can be defined according to their ability to survive in the White Sea conditions underimpact of high temperature:1) Species which cannot withstand a short rise of temperature higher than 11°C.2) Species which can withstand a short rise of temperature approximately up to 15°C.
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CONTENTSPREFACE ...................
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Андрей Донатович Н