Pratov 1972 uncritically assumed Chenopodium vulvaria to occur throughout Central Asia, probably as native to the whole area because he included no mention on its status. However, Mosyakin 1996 analysed its distribution and concluded that this species is native to the Mediterranean and South-West Asia, being alien elsewhere. Chenopodium vulvaria is certainly native to the Flora Iranica area (Uotila 1997; Uotila, pers. comm.) but is considered exclusively ruderal and synanthropic in Tajikistan (Sidorenko et al. 1968) and Uzbekistan (Botschantzev 1953). Its distribution in eastern Kazakhstan (Goloskokov 1960) and southern Siberia (Lomonosova 1992) is limited, fragmented, and also connected with human activities.

Nikitina 1955 was first to report this rare synanthropic species as ruderal in one place in Alay Range. Later she (Nikitina 1967) dismissed the record as erroneous. Indeed, no relevant specimens have been uncovered in the collections of FRU which are the basis of Nikitina’s treatments.

The first confirmed record of this species in Kyrgyzstan, documented by a specimen, was made in 1961 in the ravine of Kara-Balta river (Gubanov 1970), presumably close to its entrance, on the N side of Kyrgyz Range. This ravine is facing to Kara-Balta Town situated in the Chüy Depression; the southern part of the town (close to the ravine) is a vast industrial area since the Soviet times, including a large ore grinding factory which used imported ores.

This territory was revisited in 2013 in order to explore the area of the oil refinery factory (then under construction) east of Kara-Balta Town. The construction activities brought a number of alien plants, and the presence of C. vulvaria was confirmed in the area. No direct evidence of persistence may be inferred from its presence yet, because multiple independent introductions may have taken place.

The second locality of C. vulvaria was observed by Lazkov in the vicinity of Nookat village, Alay Range, without further information on the invasion status.

We consider this species to be alien to the country because of its weedy nature, anthropogenous characters of its habitats, and the paucity of its records (Fig. 8) which all are very recent.

Figure 1.  

Vigorous plants of Anthemis ruthenica on a wasteland. Kara-Balta Town, 22.06.2013. Photo: G.Lazkov.

Figure 2.  

Local occurrences of Anthemis ruthenica may be really extensive. Kara-Balta Town, 22.06.2013. Photo: G.Lazkov.

Figure 3.  

Plants of Centaurea solstitialis at Topurak-Bel Pass, 15.08.2013. Photo: A.Sennikov.

Figure 4.  

Habitat of Centaurea solstitialis at Topurak-Bel Pass, 15.08.2013. Photo: A.Sennikov.

Figure 5.  

A young plant of Crambe orientalis. Chüy Depression, 15.04.2013. Photo: G.Lazkov.

Figure 6.  

The plants of Glaucium corniculatum are very vigorous on waste ground. Kara-Balta Town, 22.06.2013. Photo: G.Lazkov.

Figure 7.  

A sparse colony of Tragus racemosus on a roadside nearby Tokmok Town. 18.06.2013. Photo: G.Lazkov.

Figure 8.  

Distribution of Arrhenatherum elatius, Centaurea solstitialis, Chenopodium vulvaria and Crambe orientalis in Kyrgyzstan.

Figure 9.  

Distribution of Glaucium corniculatum, Hirschfeldia incana, Salvia aethiopis and Tragus racemosus in Kyrgyzstan.

Not documented; probably locally established (the status is inferred from the persistence of the species in the other countries of Central Asia). The observed populations are sparse and do not pose any threat to the native flora.

Anthemis ruthenica is an annual or biennial species native to southeastern Europe and the Caucasus (Tzvelev 1994). There are very few published records of this alien species from Central Asia. Earlier it was known from Magtymguly Village (Kopetdagh Range, Turkmenistan), western parts of Talas and Kyrgyz Ranges in Kazakhstan, and along Shakhimardan River in Uzbekistan (Kamelin and Kovalevskaya 1993). The localities in Kazakhstan are very close to the border of Kyrgyzstan, and this proximity is confirmed by a specimen at FRU that was collected at the distance of ca 10 km (vicinity of Jambyl [Taraz] Town, foothills, clayey slopes, semidesert, 14.05.1970, I.Sudnitsyna). The locality in Uzbekistan is situated in the enclave surrounded by the territory of Kyrgyzstan. The presence of this species in Kyrgyzstan was therefore expected.

The species was first reported from Kyrgyzstan on the basis of a single recent collection from Tosh-Bulak [formerly Belogorka] village on the northern side of Kyrgyz Range (Lazkov 1999). A further revision of collections at FRU revealed a number of earlier specimens of the species collected along the foothills of the northern side of Kyrgyz Range between the border with Kazakhstan and Kara-Balta Town. The species has been most frequently collected at the country border. Besides, a single herbarium specimen was collected in the Talas Depression, also very close to the border with Kazakhstan. These records make an extension of the previously known distribution area.

The species is also known from the eastern part of the Chüy Depression. It was observed by G.Lazkov (without voucher specimens) near Kant Town, Tokmok Town, and Kemin Town of Chüy Region.

At present, in Kyrgyzstan Anthemis ruthenica is widespread and locally abundant in the Chüy Depression and the western part of the Talas Depression (including foothills), completely covering the lowlands of northern Kyrgyzstan (Fig. 10). It typically occurs in wastelands, on roadsides and dry riversides. The occurrence of this species in Kyrgyzstan is not new but has been very poorly known; previously it was misidentified in collections of FRU as Pyrethrum transiliense (Herd.) Regel & Schmalh. The species has a clear tendency to get established in new territories and may potentially spread much further. Our latest observation comes from the vicinity of Kara-Balta Town from which the species was first recorded as late as 1978; vigorous stands were observed in the new factory area (Fig. 1). At present the species is truly abundant in disturbed lands of various kind around the town (Fig. 2).

Figure 10.  

Distribution of Anthemis ruthenica (triangles) in Kyrgyzstan.

Since most of the older records originated from the territories neighbouring with Kazakhstan, we conclude that the species was imported from that country in mid-Soviet times. The oldest record documented by a specimen collected in 1965 came indeed from Cholok-Aryk Village at the very border with Kazakhstan.

Established alien, naturalised (self-sustaining with established populations of a high number of individuals) in human-made and disturbed habitats at the regional scale. Spreading and invasive, locally replacing other species.

In Central Asia this species is native to Turkmenistan, Tajikistan and (with a limited distribution) Uzbekistan. It occurs on dry gravelly and clayey slopes in lowlands and foothills, and is frequently found on arable lands and wastelands, in orchards, and along roadsides and artificial brooks (Makhmedov 1993).

In Kyrgyzstan the only known population of this species, first recorded in 2000, had persisted in At-Oinok Mts. for a few years (Lazkov 2001), but the plants have no longer been found recently (Lazkov, pers. obs.). This population was situated in a ravine that is known for, among other activities, historical cultivation of fruit crops that still survived there as old big trees of Morus alba L. and Juglans regia L., and a single thick-trunked liana of Vitis vinifera L. In 2013 we observed another population of a few dozens of individuals (Fig. 3) in the southwestern foothills of the Fergana Range, near Topurak-Bel Pass, where it occurred in a sparse vegetation of the hemisavannah type on the hills of red clay planted with pistachio trees close to an isolated homestead (Fig. 4). The hills were almost completely turned into a pistachio garden in the Soviet times; the trees are still in good condition and bear a plenty of fruits. No other alien plants were observed in the site.

From the sporadic and recent character of records (Fig. 8) we infer that the species is alien to the country, most likely transported with agricultural activities in the late Soviet times from the other countries of Central Asia.

Judging from the population size at the Topurak-Bel and its good seed set, this hardy annual is locally established in Kyrgyzstan. No spread is observed from the locality, and its future is uncertain.

Synonym: Crambe amabilis Butkov & Majlun

This perennial species is native to Western Asia, ranging from Turkey to the Flora Iranica area (Hedge 1968), including Turkmenistan (Hedge 1968; Nikitin and Geldykhanov 1988).

The first record of the alien Crambe orientalis in Western Tian-Shan is dated 1922 when a specimen was collected from the foothills between Shymkent Town (Kazakhstan) and Angren River (Uzbekistan). The species occurred abundantly on grain fields and abandoned lands in this limited area, from where it was erroneously described and subsequently accepted as the local endemic C. amabilis Butkov & Majlun (Kovalevskaya 1974). Most probably it was transported to the place with cultivated plants (Botschantzev 1977).

In Kyrgystan Crambe orientalis was first recorded from the Chüy Depression in 2006 (Lazkov and Redina 2007). The present new record (that is a novelty to the Talas Depression) fills the gap in the secondary distribution area (Fig. 8). As in the Chüy Depression, the species was observed established along the railway embankments which are its major channel of dispersal, but single plants (Fig. 5) were noticed outside the railway area on the neighbouring mountain slopes.

Most likely the plants arrived from Kazakhstan where C. orientalis was commonly found in the southern territories (Lazkov and Redina 2007). In northern Kyrgyzstan the species was also observed as a garden weed (Lazkov and Redina 2007), demonstrating multiple sources and means of dispersal and possibly arrival to the country.

Established alien, spreading further along railways and with cultivated plants. Potentially invasive (as demonstrated by its naturalization in Kazakhstan and Uzbekistan), although at present almost entirely confined to human-made habitats.

Synonym: Erucastrum incanum (L.) W.D.J.Koch

Hirschfeldia incana is a Mediterranean species that has never been recorded from Central Asia as a whole. The closest approach of its native distribution area is in Iran (Hedge 1968).

New country record, and the first record in Central Asia. A single plant was noticed and collected in 2013 among shrubs in Kyr-Koo Village on the western side of Fergana Range (Fig. 9), but the area has not been specially explored for the species.

Most likely this is a casual, ephemeral introduction, caused by long-distance dispersal.

In Central Asia the distribution area of Salvia aethiopis has three isolated fragments (Makhmedov 1984, Makhmedov 1987), of which the mountainous occurrence in Turkmenistan (Borisova 1954) and southern Uzbekistan (Vvedensky 1961) may be considered native. Two isolated localities nearby Mikhailovka and Lugovoe Villages in Kazakhstan (Makhmedov 1984, Makhmedov 1987), which are very close to the border with Kyrgyszstan, are situated on the lowlands north of Kyrgyz Range (not in the foothills of Kyrgyz Range as stated in Makhmedov 1984) and obviously constitute an alien occurrence.

This conspicuous species had not been recorded from Kyrgyzstan until Lazkov et al. 2012 reported its presence on the southern side of Küngöy Ala-Too, the northern side of Alay Range and in the Chüy Depression, where it was discovered in 2011–2012. Our records extend the known occurrence of this species to the Talas Depression (Karacha-Too Mountains) and the neighbouring side of Talas Range (Kök-Say River valley), very close to the border with Kazakhstan (Fig. 9).

Its arrival from Kazakhstan may have been by the means of wind transportation because the dried plants are easy to get detached from the ground, forming a tumbleweed. The means of long-distance dispersal to the other territories are uncertain.

Several plants were observed in every locality, meaning that the species is most likely established in the country. Its further spread, especially in lowlands, is expected. The observed populations are usually sparse and pose no obvious threat to the native vegetation.

In Central Asia this species is native to Kopetdagh, Turkmenistan (Nikitin and Geldykhanov 1988). Outside its native distribution area, it has been sporadically found in Turkmenistan (ruderal in oases), Uzbekistan (Tashkent City, roadsides; Fergana City, ruderal), and Kyrgyzstan (Pazij 1974).

In Kyrgyzstan, this species had only been recorded as ruderal on experiental fields in the Chüy Depression (Pazij 1974) on the basis of collections kept at TASH. The second record in Kyrgyzstan was made in 2013 in the factory area east of Kara-Balta Town, lower part of N side of Kyrgyz Range (Fig. 9), together with Chenopodium vulvaria and Anthemis ruthenica reported here. A few flowering individuals (Fig. 6) were noticed.

Because of the low number of individuals and the ephemerous nature of the previous record, the occurrence at Kara-Balta looks casual. The species has not yet been established in Kyrgyzstan.

This economically important species is very commonly cultivated in Europe as forage and ornamental plant, often escaping and getting established (Tzvelev 1976). Its native distribution area lies in Europe, the Mediterranean and Western Asia (Tzvelev 1976). In the mountainous Central Asia, in addition to the native occurrence in Turkmenistan (Rozhevits 1932, Nikitin and Geldykhanov 1988), it was locally cultivated on experimental fields but had never been commonly introduced (Sidorenko 1957). In Kazakhstan Arrhenatherum elatius was cultivated for artificial grasslands and lawns, and characterized as easy to run wild (Gamayunova 1956).

This species has never been reported from Kyrgyzstan. We observed A. elatius growing as self-sawn relics of abandoned cultivation in the private garden in Kök-Say Village (southwestern part of the Talas Depression), originally planted for forage and now spreading along artificial brooks outside the village. Another record (Fig. 8) comes from a student excursion to the northern side of the Ysyk-Köl Lake, where the species was cultivated as ornamental plant in the resort area.

The species may be considered locally established at Kök-Say because of its persistence and spread from the place of original cultivation. In the observed place the species does not show obvious threats to the native vegetation. The invasion status of the other locality is not ascertained.

Tragus racemosus is mainly zoochorous because its diasporas may easily get attached to the cattle’s wool (Tzvelev 1976). This pasture weed, widely distributed in the Mediterranean, southeastern Europe, Asia Minor and Iran, has not been recorded in Central Asia outside its native area in Turkmenistan and doubtfully native presence in the westernmost Kazakhstan (Tzvelev 1976).

The present record is the first in Kyrgyzstan and also the first alien occurrence recorded with certainty in Central Asia. A few mature plants (Fig. 7) were observed along the roadside close to Tokmok Town, eastern part of the Chüy Depression (Fig. 9). Diasporas of T. racemosus may have been transported to the place with cattle because roadsides of any kind in the proximity of villages and towns are commonly used as pathways for cattle.

The invasion status of T. racemosus in Kyrgyzstan is not ascertained yet but its only known occurrence is likely ephemerous. For this reason the species is provisionally assessed as a casual alien in the country.