Internal taxonomy of the Hyrcanus Group of Anopheles (Diptera: Culicidae)
and its bearing on the incrimination of vectors of malaria in the west of the
Palaearctic Region
Clement D.
Ramsdale
Varndean
Lodge, London Road, Brighton BN1 6YA, United Kingdom. Email:
clem.ramsdale@claranet.co.uk
Abstract
Knowledge
of the internal taxonomy and actual or potential importance as vectors of
malaria of the Anopheles hyrcanus
Group in the western Palaearctic is reviewed. Means of studying these neglected
disease vectors in this area are discussed.
Introduction
The
Hyrcanus Group (Genus Anopheles,
Subgenus Anopheles) comprises an unknown number of species,
some of which are vectors of malaria and other mosquito-borne diseases. The
vectorial importance of some of these species in the Oriental Faunal Region and
contiguous parts of the far eastern Palaearctic Region became evident early in
the last century, since when the group has been the subject of long series of
studies in this large area. In contrast, very little is known about the western
Palaearctic taxa, where these more or less exophilic and exophagic mosquitoes
were not generally considered to be important vectors. The advent of DDT during
the 1940s, and of Malaria Eradication Projects relying heavily on house spraying,
focused attention on the vector species of the endophilic Maculipennis Complex
with little or no interest in the more exophilic Hyrcanus Group. Briefly
re-awakened interest came in persistent or resurgent foci of malaria in the
later stages of the western Palaearctic Malaria Eradication Programmes, but
only until abandonment of these programmes shortly afterwards. Despite evidence
to the contrary, apart from a taxon described from a unique specimen collected
near Tashkent, Uzbekistan, only a single polymorphic species was recognised in
the western Palaearctic until recently, when Anopheles pseudopictus was elevated to species status.
Mosquitoes
of the Hyrcanus Group favour larval sites in marshes and similar situations,
and proliferate where crops are grown under flood irrigation. Workers tending
and harvesting crops grown under irrigation tend to sleep outside during the
hot malaria season, making them vulnerable to attack by exophagic mosquitoes.
Agricultural projects making use of impounded water for irrigation constitute
areas of continuing malaria transmission and the literature contains many
references to An. hyrcanus s.l.
acting as vectors in rice and cotton growing areas. Impoundment of water for
irrigation on a scale unprecedented in western Asia has begun. Importance of
these mosquitoes as actual or potential malaria vectors must, therefore, be
expected to increase.
It
would seem prudent to study the systematics of the Hyrcanus Group in the
western Palaearctic in order to establish the vectorial importance of its
constituent members before these planned, large irrigation projects come on
stream, allowing malaria control and/or prevention to be tackled in an informed
manner.
Anopheles hyrcanus (Pallas), first recorded from the southern shores of the
Caspian Sea, was shown to have a wide distribution extending from Iberia in
Europe to east and south-eastern Asia including some of the off-lying islands
of the Indian and Pacific Oceans. It also became apparent that the taxon
included a number of morphologically separable forms, and that some were
involved in the transmission of malaria and filariasis, particularly in the
Oriental Region and contiguous parts of the eastern Palaearctic Region. To
date, the Hyrcanus Group has been
shown to encompass a group of 29 currently recognised species (Table 1). Of
these, 26 have an Oriental or eastern Palaearctic distribution, with 4 being
placed in the Lesteri Subgroup and 4 in the Nigerrimus Subgroup, whilst
insufficient data have yet been collected to enable the others to be assigned
to subgroups (Harbach, 1994; Nguyen et al.,
2000). Only 3 currently recognised species have a western Palaearctic
distribution, here defined as occurring in the part of the Palaearctic Region
west of China and south of 50°N.
species synonym type locality
sinensis Wiedemann, 1828 Canton,
China
plumiger Dönitz, 1901 Hong
Kong
jesoensis Tsuzuki, 1902 Hokkaido,
Japan
albotaeniatus (Theobald, 1903) Perak,
Malaya
argyropus (Swellengrebel, 1914) Deli, East
Sumatra
sineroides
Yamada, 1924 Bibai,
Hokkaido, Japan
pullus Yamada, 1937 Keiki-do
and South Tyusei-do, Korea
kweiyangensis
Yao & Wu, 1944 Kweiyang,
Kweichow, China
yatsushiroensis
Miyazaki, 1951 Yatsushiro
City, Kyushu, Japan
anthropophagus Xu & Feng, 1975 Wukiang, Kiangsu China
kiangsuensis
Xu & Feng, 1975 Wukiang,
Kiangsu China
engarensis Kanda & Oguma, 1978
Engaru, Hokkaido,
Japan
changfus
Ma, 1981 Emai, Sichuan, China
dazhaius Ma, 1981 Sichuan,
China
heiheensis Ma, 1981 Aihui,
Heilungjiang, China
xiaokuanus Ma, 1981 Mudangjiang,
Heilungjiang, China
liangshanensis Kang et al.,
1984 Zhaojaio, Sichuan,
China
kunmingensis Dong & Wang, 1985 Kunming, Yunnan,
China
nimpe Nguyen et al.,
2000 Cà
Mau Province, Vietnam
vietnamensis Nguyen et al.,
1993 Son
La Province, Vietnam
peditaeniatus
(Leicester, 1908) Malaya
lesteri
Baisas & Hu, 1936 Rizal,
Luzon, Philippines
crawfordi Reid, 1953 Kuala
Lumpur and Selangor, Malaya
paraliae
Sandosham, 1959 Malaya
and Borneo
nigerrimus Giles, 1900 Calcutta,
India
indiensis Theobald, 1901 Madras,
India
bentleyi Bentley, 1902 Tezpur,
Assam, India
minutus Theobald, 1903 Lahore,
Pakistan
williamsoni Baisas & Hu, 1936 Penang,
Malaya
venhuisi Bonne-Webster, 1951 Java
pursati
Laveran, 1902 Pursat,
Cambodia
pseudosinensis Baisas,
1935 Calauan,
Luzon, Philippines
nitidus Harrison et al.,
1973 Selangor,
Malaya
pictus Loew, 1845 Rhodes,
Greece
flerowi Portschinsky, 1910 River
Amu-Darya, Uzbekistan
mesopotamiae Christophers & Chand, 1915 Lower Iraq
marzinovski Shingarev, 1926 Karayazi
Steppe, South Caucasus
popovi Schingarev, 1928 Turkestan
mahmuti Martini, 1930 Asia
Minor
pseudopictus Grassi, 1899 Italy
chodukini
Martini, 1929 Tashkent, Uzbekistan
It was
recognised at an early date that many forms of An. hyrcanus s.l. co-existed in east and south-east Asia, which
allowed malariologists a certain degree of confidence that they were working
with particular species. However, results of vector studies with these sibling
species still produced anomalous results.
Precipitin
tests of bloodmeals of females of the taxa now known as An. nigerrimus and An.
sinensis, demonstrated that a
variable, sometimes high, proportion of meals of both species may be of human
blood (Boyd, 1949). Anopheles nigerrimus naturally infected
with malaria occurred in Indochina, Malaya
(part of present day Malaysia) and Indonesia though infected specimens
were not found in Assam and the Philippines (Boyd, 1949). Similarly, An. sinensis was a confirmed vector in
Java, Sumatra, Celebes, Malaya, north Vietnam, north, central and south China,
Taiwan, Korea, and central Japan (Boyd, 1949; Covell, 1949; Puri, 1949; Ho,
1965; Ma, 1981; Beales, 1984; Chow, 1991) but was of little importance in
southern Indo-China (Boyd, 1949). Anopheles hyrcanus s.l. was reported to
be exophilic and either endophagic or exophagic in Myanmar (Burma) (Boyd,
1949), where it was an effective malaria vector in the Irrawaddy Delta (Covell,
1949). It was also considered to be a vector in eastern Sumatra, but not to be
involved in malaria transmission in Java, Borneo, Macassar and Celebes (Boyd,
1949).
Further
studies of these species in the Oriental and eastern Palaearctic Regions during
the second half of the last century (e.g. Reid, 1953, 1968; Harrison, 1972,
1973; Harrison et al., 1973, 1991;
Harrison & Scanlon (1975); Takai & Kanda, 1986; Baimai et al., 1993; and others) did much to
resolve these puzzling findings. Many named forms were found to refer to the
same species, but at the same time other good species were described in south
eastern and eastern Asia.
This
work enabled identification of further vectors within the Hyrcanus Group. In
addition to An. sinensis and An. nigerrimus, An. lesteri is considered a good vector of malaria in southern
China (Ho, 1965; Ma, 1981; Beales, 1984; Chow, 1991) and was suspected of being
the principal vector in Japan (Tanaka et
al., 1979). Other species, such as An.
anthropophagus in southern China, An.
dazhaius in Central China, An.
xiaokuanus in north China and An.
nimpe in southern Vietnam are
known to bite man and to be important or probable malaria vectors (Ma, 1981;
Chow, 1991; Nguyen et al., 2000).
Studies in the Palaearctic Region west of China
In his
review of An. hyrcanus and related
taxa in the Palaearctic Region, Martini (1929-31) regarded the described forms,
pictus, pseudopictus and sinensis
as synonyms of hyrcanus. Anopheles chodukini was described from a
unique female specimen sent to him from Taskent and, though he considered the
possibility that it may represent an extremely pale, desertic form of hyrcanus, he decided it more probably
belonged to a separate species. He regarded the other taxa described from west
of China as geographical varieties of hyrcanus
thus: hyrcanus type form
(distribution: Spain to Far East), var.
mesopotamiae (Lower Iraq), var. marmuti
(Asia Minor), var. marzinovski (Caucasus),
and var. popovi (Turkestan). He provided a key (based on hind
tarsal and wing scaling patterns) for differentiation between these forms but
admitted that differentiation could be difficult. He also provided a
description of the adult morphology, distribution, and the involvement in
malaria transmission of sinensis (which
he regarded as a synonym of hyrcanus).
Because
individual morphological variation within each taxon proved to preclude
reliable separation by means available at that time, all came to be treated as
populations of one species, An. hyrcanus, and other individual names were consigned to synonymy (Bates et al., 1949). Thus, An. hyrcanus was considered to be a
widely distributed polymorphic species with a range extending from the Iberian
Peninsula, through Europe south of the Alps and Asia south of about 50°N, to
the Pacific. Gutsevich et al. (1971)
and Gutsevich (1976) regarded all Palaearctic forms, including An. chodukini, as varieties (aberrations)
of hyrcanus. Apart from a few more
recent, fragmented, observations, this view has persisted, despite results of
the work in the Oriental Region and the east of the Palaearctic Region.
Reid
(personal communication, 1968) was of the opinion that until western
Palaearctic forms of An. hyrcanus were shown to be conspecific
with Oriental forms, they should be regarded as separate entities and suggested
that it might better to label western Palaearctic forms hyrcanus until the taxon had been adequately studied.
A
limited number of crossing experiments (Ross Institute, 1976, 1977) between
samples drawn from populations of An.
hyrcanus s.l. from Camargue (France), Çükürova (Turkey), Osmancik (Turkey)
and elsewhere, indicated that the Camargue and Osmancik populations were
conspecific, but that the Çükürova population belonged to a different species.
Preliminary morphological studies during the same investigation indicated that
a population from Jalalabad (Afghanistan) is probably conspecific with the
Camargue/Osmancik form, in which hindtarsomere 4 (TIII-4) carries pale basal
and apical white bands separated by a broad black median area. This segment is
all white in the forms found at Kunduz, Afghanistan (Ward, 1972) and Çükürova,
Turkey (Postiglione et al., 1973).
This
work was discontinued after 1977, but more recently the taxon pseudopictus, with hindtarsomere 4
(TIII-4) all white, was reinstated as a species following comparison with the
type form of hyrcanus s.l. in which
hindtarsomere 4 (TIII-4) is dark except for a white apical band. In addition to
these morphological differences, no evidence of natural hybridisation was found
in south-west Asia where these forms are sympatric (Glick, 1992).
Two
hundred and thirty years after it was first recorded at the southern end of the
Caspian Sea (Pallas, 1771), understanding of the status of An. hyrcanus s.l. in the western Palaearctic Region (west of China)
is still in an embryonic stage. This situation stems from an assumption that
the taxon was, at most, of only minor importance as a malaria vector.
Bates et al. (1949) did not regard An. hyrcanus s.l. as a primary vector,
but thought it played a part in transmission in the presence of good vectors,
and gave southern Ukraine and middle Asia as examples. Gutsevich et al. (1971) considered that its
vectorial role varied between places, depending on local conditions.
Precipitin
tests of bloodmeals have given variable results, from complete zoophily in
Romania (Bruce- Chwatt et al., 1966)
to 25% positive for human blood in Greece (Barber & Rice 1935). However,
there is ample evidence from Greece (Waterston, 1918), Bulgaria and the
Republic of Macedonia (Weyer, 1942), Turkey (Postiglione et al., 1973; Ramsdale & Haas, 1978), Afghanistan (Zahar, 1974;
Anofrieva et al., 1977) and the
neighbouring countries of Turkmenistan, Uzbekistan, Tadzhikistan, Kazakhstan
and Russia (Sergiev et al., 1993)
showing that this taxon may exhibit quite high degrees of anthropophily. It is
not known how far it was involved in the devastating outbreaks of malaria
affecting French and British forces in Greek Macedonia during the 1914-1918
World War. Nevertheless, Weyer (1942), working in the same area during the
1939-1945 War, aptly observed that An.
hyrcanus has high potential as a malaria vector where it is abundant and people
sleep in the open. Quite recent observations in the rice growing area of
the alluvial plain through which the River Axios flows found that An. hyrcanus s.l. is still one of the
principal pest mosquitoes of northern Greece (Kaiser et al., 2001).
Biting
and baited net trap collections in Turkey (Postiglione et al., 1973; personal observations) confirmed Weyers observation.
In human and animal baited net trap collections in a village of south-west
Turkey where cattle were stalled amongst the houses at night, 98% of 238 An. hyrcanus s.l. caught were in the
animal baited net trap. Night biting collections on human bait in the same
village failed to detect a single specimen attempting to bite, though many fed
on the animals. However, when the same human bait were moved into open country
away from this village, so losing the protection provided by cattle, they were
immediately subject to mass attack by blood-seeking females. Further night
biting collections in the Çükürova area of Turkey confirmed that large numbers
viciously attack humans in the absence of herds of large domestic animals.
Rice
fields, with their associated drainage systems, constitute prolific larval
sites for this mosquito, and enormous populations of An. hyrcanus s.l. occur in some irrigated cotton and rice growing
areas in Turkey and elsewhere (Postiglione et
al., 1973; Cristescu et al.,
1975; Onori et al., 1975; Cousserans et al., 1976; Anofrieva et al.,
1977; Ramsdale & Haas, 1978; Kaiser et
al., 2001).
Some of
the most intractable problems of malaria transmission occur in small or large
areas where monoculture crops, usually of rice and/or cotton, are produced
under irrigation. Domestic animals are absent or rare in these situations,
where agricultural workers sleep out of doors during the hot summers, often
around the edges of irrigated fields, particularly during the harvest
(Postiglione et al., 1973; Ramsdale
& Haas, 1978).
After many years of developing in larval
sites contaminated by crop spraying, both An.
hyrcanus s.l. and An. sacharovi had become highly
resistant to insecticides (Ramsdale, 1975; Ramsdale et al., 1980) when a serious resurgence of malaria in the Çükürova
occurred in the mid- to late-1970s. Hundreds of thousands of people slept out
of doors during the summer at this period, making it impossible to say with any
degree of certainty which of these taxa played the dominant vectorial role.
Although An. sacharovi, which readily feeds inside or outside
buildings, was undoubtedly a good vector in these circumstances, the more
exophagic An. hyrcanus s.l. may have
made a substantial contribution to malaria transmission.
Species
identification is clearly critical to any vector control programme that seeks
to be efficient as well as effective (Collins et al., 2000).
Estimation
of the possible role in malaria transmission of An. hyrcanus s.l. in the western part of the Palaearctic is
complicated by the fact that existing data refer to an unknown number of
species, each of which may have a different vector potential. It is known that
behavioural differences between populations exist, but the accumulated
information on distribution, behaviour and other aspects pertinent to malaria
transmission refers to an aggregate of species (Ramsdale & Snow, 2000).
The
size of the parasite reservoir in human populations has an obvious bearing on
malaria transmission. However, field studies should include assessment of the
effect of human ecology on vector behaviour. In the case of the Hyrcanus Group,
this aspect may be of major importance.
Acknowlwdgements
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