Background

Earthworms are one of the most important invasive animals, at least in terms of biomass and the number of individuals (Michaelsen [1903]; Gates [1972], [1982]; Lee [1985], Blakemore [2009], [2012a], [b]; James [2011]). Invasive earthworms continue their expansion into previously earthworm-free zones (Tiunov et al. [2006]), where they often have huge ecological impact (Bohlen et al. [2004]; Frelich et al. [2006]). In this connection, they are a major concern in some regions that were until recently devoid of earthworms. For example, it is believed that in large parts of the northern part of North America, native earthworms were eliminated by Pleistocene glaciations. While recolonization of these regions started long ago, massive invasions by European earthworms began in many places only a few decades ago, often with a dramatic impact (Gates [1982]; Scheu and Parkinson [1994]; Cameron et al. [2008]).

The Kamchatka peninsula is a geographically remote and sparsely populated region. Much of Kamchatka is covered by forests dominated by stone birch or conifers, but its forests are separated from the mainland boreal zone by a vast stretch of tundra. Species diversity of Kamchatka was significantly reduced by Pleistocene glaciations, but refugia are believed to have existed during this period, although their extent is still unclear (Egorova [2008]).

There are few studies on earthworms of Kamchatka. Currently, only four earthworm species are known for this region. Michaelsen ([1929]) and Sokolskaya ([1972], [1983]) found Eisenia nordenskioldi (Eisen 1879) on the banks of thermal springs. Sokolskaya ([1983]) reported on cosmopolitan earthworm species Bimastos parvus (Eisen 1874) (referred to in Russian literature as Allolobophora parva Eisen 1874) and Dendrodrilus rubidus tenuis (Eisen 1874) on river banks. A report on Eisenia fetida (Savigny 1826) in Petropavlovsk-Kamchatsky is mentioned by Vsevolodova-Perel ([1997]).

Therefore, all earthworm species from Kamchatka are cosmopolitan species, except for E. nordenskioldi, which is a Siberian species that is also found in Eastern Europe. Kamchatka has a rather harsh climate, so agriculture is very limited there; the number of human-mediated dispersal events should have been low, and natural colonization of Kamchatka by earthworms from the mainland is now impossible. Almost all traffic from the mainland comes by sea or, less significantly, by air. Therefore, Kamchatka is a good model for studying the capabilities of earthworms to invade and colonize boreal regions.

We collected a sample of earthworms from several anthropogenic and natural locations in Kamchatka, performed morphological identification, and obtained sequences of the mitochondrial cox1 gene. The aim of our study was to investigate the earthworm fauna of Kamchatka and to attempt to trace its origin.

Methods

Earthworms were collected in several locations in Kamchatka (Table 1). Morphological identification was performed according to Vsevolodova-Perel ([1997]). Earthworm individuals used in this study are stored in the Institute of Cytology and Genetics, Novosibirsk.

Table 1 Earthworms collected in this study

The total DNA was extracted from several caudal segments using the BioSilica DNA extraction kit according to manufacturer's instructions (BioSilica Inc., Novosibirsk, Russia). A fragment of the mitochondrial cox1 gene was amplified using the universal primers LCO1490m (5′-TACTC-AACAA-ATCACAAAGA-TATTG-G-3′; modified from Folmer et al. [1994]) and COI-E- (5′-TATAC-TTCTG-GGTGT-CCGAAGAATC-A-3′; Bely and Wray [2004]). PCR reaction mixture contained 1.5 mM MgCl2, 65 mM Tris-HCl (pH 8.8), 16 mM (NH4)2SO4, 0.05% Tween-20, 0.2 mM of each dNTP, 0.3 mM primers, and 1 U of recombinant Taq polymerase (SibEnzyme, Novosibirsk, Russia). All sequences obtained in this study were deposited in GenBank under accession nos. KJ772496-KJ772504, JX531568, JX531571, KF471787-KF471792, and KF471831-KF471842 (Table 1). When several individuals had identical cox1 sequences, only one sequence was submitted, except for Aporrectodea caliginosa.

Results

According to morphological analysis, the earthworms collected by us belonged to the species A. caliginosa (Savigny, 1826), Lumbricus rubellus (Hoffmeister, 1843), Dendrobaena octaedra (Savigny, 1826), and Dendrobaena attemsi (Michaelsen [1903]) as described by Rota and Erséus ([1997]) and Blakemore ([2012b]); Dendrodrilus rubidus tenuis, Dendrodrilus rubidus subrubicundus (Eisen, 1874), E. nordenskioldi, and E. fetida; in addition, some specimens could not be reliably identified (Table 1). Therefore, our study adds three new species (Dendrobaena octaedra, Dendrobaena attemsi, L. rubellus, and A. caliginosa) and one subspecies (Dendrodrilus rubidus subrubicundus) to the four earthworm species and subspecies that were earlier reported for Kamchatka.

We obtained 61 cox1 sequences. Molecular analysis confirmed the morphological diagnosis in all cases.

Several diverse earthworm species were found in the Paratunka town, in a compost heap near the greenhouses of the Institute of Volcanology. The location suggests that diverse biological material, including plant and soil samples, is often delivered there. cox1 sequences of two individuals of E. fetida from Paratunka were identical to those of the specimens from Denmark (GenBank accessions FJ214216 and FJ214217), France (GU013880 and GU013881), and also to three specimens of E. fetida (AY874517, AY874516, and AY874515) from the study of Pérez-Losada et al. ([2005]) (could be Spain or Ireland). The molecular problems with several previous studies of taxonomic components of the A. caliginosa, E. fetida, and E. nordenskioldi species complexes were commented on by Blakemore et al. ([2010]) and by Blakemore ([2013]). One of the individuals was identified as Dendrodrilus rubidus subrubicundus; its cox1 sequence differed from that of Dendrodrilus rubidus from Europe (DQ092900) by eight substitutions.

Two earthworms from Paratunka were morphologically identified as Dendrobaena attemsi. Some morphological characters, however, deviated from the diagnosis: pigmentation was low on the medial surface of the segments 8 to 11, the head was almost tanylobic, and the ventral surface was thickened only on the 14th and the 15th segments. The identity of this species was confirmed by a closely related cox1 barcode sequence (99% sequence similarity) of this species from the south of Sweden in the BOLD database (Ratnasingham and Hebert [2007]) and by two unpublished sequences kindly provided by Prof. R. Blakemore (courtesy of Dr Ramon Gallego of University of Auckland, New Zealand (see Blakemore [2012a])), which had only two nucleotide substitutions. No close matches (with more than 85% sequence similarity) to our sequence were found in GenBank. The only sequence of Dendrobaena attemsi from GenBank (FJ214224 from ‘USA: Olympic National Forest, Washington’) had low sequence similarity to our sequence and turned out to be close (1 substitution) to some sequences of Dendrobaena octaedra, and that individual was probably misidentified.

cox1 sequence of one L. rubellus individual from Paratunka differed from that of JN869918 from Europe by six substitutions. Another one found in the same location was identical to FJ214213 from Denmark; two worms from Krutoberegovo had the same haplotype. In addition, Krutoberegovo yielded another L. rubellus haplotype that was most closely related to JQ909123 from Ohio, USA, differing from it by seven nucleotide substitutions. Therefore, three significantly diverged L. rubellus haplotypes were found among only five L. rubellus individuals.

The site referred to as Krutoberegovo was located on a creek bank in a bottomland between the Krutoberegovo village and Petropavlovsk-Kamchatsky, about 100 m from the road and several hundred meters from the nearest village gardens. This site is infrequently visited by humans.

In addition to L. rubellus, 18 specimens of A. caliginosa were also found in Krutoberegovo. cox1 sequences of all these individuals belonged to the mitochondrial lineage 3 of this species (Porco et al. [2012]). Seventeen of them differed by one substitution from the accessions JQ908867 and JQ908830 from USA and JN869885 and JN869884 from Europe. The remaining single specimen differed from all known A. caliginosa sequences by at least 20 substitutions, which significantly exceeds the range of intralineage diversity, so that it might well represent a new lineage of A. caliginosa.

We also obtained epigeic earthworms from stone birch forest about 150 km to the north of Petropavlovsk-Kamchatsky. Two locations (about 15 km apart) are represented by small valleys separated by mountain ridges with no vegetation and are occasionally visited by humans but never had any type of agriculture. Both locations contained Dendrobaena octaedra. Molecular analysis demonstrated that individuals from the two populations belonged to different genetic lineages. cox1 sequences from individuals of one of the locations differed by a single nucleotide substitution from Dendrobaena octaedra individuals from Austria (DQ092895), Canada (EU035484), and Europe (precise location unknown, JN869900), while those of the other one was most closely related to Dendrobaena octaedra from an unknown location (JN869900), differing from it by three substitutions.

One of the locations also harbored two additional earthworm species, Dendrodrilus rubidus tenuis and E. nordenskioldi nordenskioldi. cox1 sequences of nine Dendrodrilus rubidus tenuis individuals were identical and differed from a sequence of this species from Denmark (FJ374776) by only two substitutions. Unexpectedly, two individuals identified as E. nordenskioldi nordenskioldi had sequences identical to that of E. nordenskioldi pallida (Malevich [1956]) from Khakassia (JX531522 and JX531523) and Tuva (our data).

Discussion

Representatives of A. caliginosa, L. rubellus, E. fetida, and Dendrodrilus rubidus subrubicundus were found in anthropogenic habitats and are undoubtedly introduced species in Kamchatka. In natural habitats, we found three species, Dendrobaena octaedra, Dendrodrilus rubidus tenuis, and E. nordenskioldi nordenskioldi. Analysis of cox1 sequences demonstrated that they were also of invasive origin. This corroborates the findings of Sokolskaya ([1983]) who also found invasive species (Dendrodrilus rubidus tenuis and B. parvus) in natural habitats. All of the species found by us are cosmopolites (Perel [1979]; Vsevolodova-Perel [1997]; Tiunov et al. [2006]). The only exception is E. nordenskioldi nordenskioldi, which is native to Siberia and was demonstrated to have persisted in some regions for millions of years (Shekhovtsov et al. [2013]). However, molecular genetic analysis suggests that our sample of this species from Kamchatka was also introduced from the mainland.

Finding cox1 haplotypes of E. nordenskioldi pallida in our E. nordenskioldi nordenskioldi individuals was unexpected. While those two subspecies were once considered simply different pigmentation forms of the same species (Malevich [1956]; Perel [1979]), it was later discovered that they have different ploidy levels (E. nordenskioldi pallida is diploid and E. nordenskioldi nordenskioldi is polyploid) and have different ecological properties (Vsevolodova-Perel and Bulatova [2008]; Blakemore [2013]; Vsevolodova-Perel and Leirikh [2014]). The worms we found were epigeic, while E. nordenskioldi pallida is known to be strictly endogeic. There is, however, an alternative viewpoint (D Berman, personal communication) that various degrees of pigmentation intensity (including its near absence) may be manifested in both subspecies. Our findings corroborate this viewpoint, suggesting that E. nordenskioldi pallida could have adapted to epigeic lifestyle, which resulted in changes in pigmentation.

It is generally suggested that biological invasions are usually characterized by considerable reduction of genetic diversity. For earthworms, however, this seems to be not the case: Porco et al. ([2012]) demonstrated that there is no decline in genetic diversity in several earthworm species in North America in comparison to source European populations. In contrast to Porco et al. ([2012]), we found low genetic diversity of invasive earthworms from Kamchatka. This may be explained by the fact that this region is weakly populated and, consequently, there could be much less dispersal events. Nevertheless, we found two significantly divergent cox1 haplotypes for Dendrobaena octaedra and A. caliginosa, and three for L. rubellus.

Among the factors that facilitate invasions in earthworms, frequent occurrence of parthenogenesis may be the factor that gives them the potential to rapidly colonize new regions (Gates [1972]; Blakemore [2012a], [b]). However, there were more amphimictic earthworms in our sample (L. rubellus, E. fetida, E. nordenskioldi, A. caliginosa, and Dendrodrilus rubidus subrubicundus) than parthenogenetic ones (Dendrobaena octaedra and Dendrodrilus rubidus tenuis). Cold tolerance is another important factor: all invasive earthworms reported from Kamchatka are believed to have originated in warmer climates; however, they were nevertheless able to successfully colonize this peninsula that has rather harsh climate. Some of them (Dendrobaena octaedra, A. caliginosa, and both subspecies of E. nordenskioldi) are indeed characterized by high cold tolerance both as adult worms and cocoons (Berman et al. [2002]; Berman and Meshcheryakova [2013]; Meshcheryakova and Berman [2014]). However, other species (Dendrodrilus rubidus tenuis and L. rubellus) are cold tolerant only at the cocoon stage, while adult worms die at −1°C to −3°C (Berman et al. [2010]; Meshcheryakova and Berman [2014]). This means that they have adapted to complete their developmental cycle in the short warm period. Finally, E. fetida has no cold resistance, as both adults and cocoons of this species die at −1°C (Berman et al. [2009]). However, it is evident that despite no cold tolerance, it is still capable of living in anthropogenic environment.

Conclusions

To conclude, our study added four new species and one subspecies to the four earthworm species known previously for Kamchatka. In addition, this is the first report from Asia for Dendrobaena attemsi (as confirmed by Blakemore ([2012a]) while recording it from New Zealand). Molecular genetic analysis allowed us to demonstrate that at least some earthworm species in Kamchatka are represented by several mitochondrial lineages, which most probably correspond to independent invasion events. Moreover, examination of several locations including sites without any traces of economic activity allows us to speculate that the whole earthworm fauna of Kamchatka might be of invasive origin, as the only species, E. nordenskioldi nordenskioldi, that could potentially be native to this region, was found to be of invasive origin.