www.elsevier.com/locate/meegid
Infection, Genetics and Evolution 7 (2007) 93–102
Genetic diversity and molecular identification of mosquito species in
the Anopheles maculatus group using the ITS2 region of rDNA
C. Walton a,*, P. Somboon b, S.M. O’Loughlin a, S. Zhang c, R.E. Harbach d, Y.-M. Linton d,B. Chen c,e, K. Nolan f, S. Duong g, M.-Y. Fong h, I. Vythilingum i, Z.D. Mohammed j,
Ho Dinh Trung k, R.K. Butlin c,l
a Faculty of Life Sciences, University of Manchester, Manchester M13 9PT, UKb Department of Parasitology, Faculty of Medicine, Chiang Mai University, Chiang Mai 50200, Thailand
c School of Biology, University of Leeds, Leeds LS2 9JT, UKd Department of Entomology, The Natural History Museum, London SW7 5BD, UK
e College of Plant Protection, Southwest Agricultural University, Chongqing 400716, PR Chinaf Department of Biological Sciences, University of Warwick, Warwick CV4 7AL, UK
g National Center for Malaria, Parasitology and Entomology, Ministry of Health, Phnom Penh, Cambodiah Department of Parasitology, University of Malaya, Kuala Lumpur, Malaysia
i Institute for Medical Research, Kuala Lumpur, Malaysiaj Institute of Biological Sciences, University of Malaya, Kuala Lumpur, Malaysia
k Department of Entomology, National Institute of Malariology, Parasitology and Entomology, Hanoi, Vietnaml Department of Animal and Plant Sciences, University of Sheffield, Sheffield S10 2TN, UK
Received 6 September 2004; received in revised form 11 May 2006; accepted 12 May 2006
Available online 19 June 2006
Abstract
The species diversity and genetic structure of mosquitoes belonging to the Anopheles maculatus group in Southeast Asia were investigated
using the internal transcribed spacer 2 (ITS2) of ribosomal DNA (rDNA). A molecular phylogeny indicates the presence of at least one hitherto
unrecognised species. Mosquitoes of chromosomal form K from eastern Thailand have a unique ITS2 sequence that is 3.7% divergent from the next
most closely related taxon (An. sawadwongporni) in the group. In the context of negligible intraspecific variation at ITS2, this suggests that
chromosomal form K is most probably a distinct species. Although An. maculatus sensu stricto from northern Thailand and southern Thailand/
peninsular Malaysia differ from each other in chromosomal banding pattern and vectorial capacity, no intraspecific variation was observed in the
ITS2 sequences of this species over this entire geographic area despite an extensive survey. A PCR-based identification method was developed to
distinguish five species of the group (An. maculatus, An. dravidicus, An. pseudowillmori, An. sawadwongporni and chromosomal form K) to assist
field-based studies in northwestern Thailand. Sequences from 187 mosquitoes (mostly An. maculatus and An. sawadwongporni) revealed no
intraspecific variation in specimens from Thailand, Cambodia, mainland China, Malaysia, Taiwan and Vietnam, suggesting that this identification
method will be widely applicable in Southeast Asia. The lack of detectable genetic structure also suggests that populations of these species are
either connected by gene flow and/or share a recent common history.
# 2006 Elsevier B.V. All rights reserved.
Keywords: Anopheles maculatus group; Malaria; Southeast Asia; ITS2; Genetic structure
1. Introduction
Anopheline mosquitoes occur typically as groups of closely
related species that cannot always be distinguished reliably
* Corresponding author. Tel.: +44 161 275 1533; fax: +44 161 275 3938.
E-mail address: [email protected] (C. Walton).
1567-1348/$ – see front matter # 2006 Elsevier B.V. All rights reserved.
doi:10.1016/j.meegid.2006.05.001
using morphological characters. Members of species com-
plexes or groups can differ in biological attributes such as
anthropogenicity, exophagy/endophagy, exophily/endophily,
longevity and larval habitat preference. These characteristics
relate to the vectorial capacity of a species and the means by
which effective vector control can be implemented (Subbarao,
1998). Consequently, the development of reliable molecular
tools for species identification, and an understanding of
C. Walton et al. / Infection, Genetics and Evolution 7 (2007) 93–10294
intraspecific genetic diversity and population structure play
important roles in the development of vector control strategies
(Collins et al., 2000).
The Anopheles maculatus group is an assemblage of eight
recognised species in the Oriental Region (Harbach, 2004).
Members of the group occur from the Indian subcontinent
through Southeast Asia to Taiwan. Adults are difficult to
distinguish morphologically due to overlapping characters. The
presence of several species within the group was resolved
primarily with the use of cytological methods (Green and
Baimai, 1984; Green et al., 1985, 1992; Baimai et al., 1993).
The group was revised by Rattanarithikul and Green (1986) and
Rattanarithikul and Harbach (1991), who recognised eight
morphologically similar species. Table 1 shows how the species
designations relate to the cytological forms and their
geographic ranges. Chromosomal form K (Baimai, 1989;
Baimai et al., 1993) has not yet been formally recognised as a
species. Chromosomal forms B and E are currently regarded as
cytotypes of An. maculatus. As noted by Green et al. (1985),
these chromosomal forms either represent sibling species or
reflect geographic variation within An. maculatus. In general,
form B is found throughout northern Thailand but is replaced
by form E in southern Thailand and peninsular Malaysia (Green
et al., 1985). Cross-mating studies found no evidence of post-
mating reproductive incompatibility between the two cytotypes
(Baimai et al., 1984). The two chromosomal forms can be
distinguished using cuticular hydrocarbons (Kittayapong et al.,
1990), and using these markers it was inferred that the two
chromosomal forms are sympatric at some sites in peninsular
Malaysia (Kittayapong et al., 1993). This suggests that the
chromosomal forms correspond to separate species, and any
barriers to reproduction are likely to be pre-mating.
Members of the Maculatus Group are known to be involved
in malaria transmission, but the vectorial capacity of individual
species remains unclear from previous studies due to the
difficulty in species identification using morphology alone.
This uncertainty is aggravated by the observation that the
ability of a species to transmit malaria can vary depending upon
local factors such as environmental conditions and population
size. For example, although An. willmori has been recorded as a
major vector in Nepal (Pradhan et al., 1970), it has never been
Table 1
The chromosomal forms of the An. maculatus group with their corresponding form
Formal species name Chromosomal form
An. maculatus (Theobald) B, E, Fa, K
An. sawadwongporni (Rattanarithikul and Green) A
An. pseudowillmori (Theobald) I
An. dravidicus (Christophers) C
An. notanandai (Rattanarithikul and Green) G
An. willmori (James) H
An. dispar (Rattanarithikul and Harbach) J
An. greeni (Rattanarithikul and Harbach) D
Information is taken from Rattanarithikul and Green (1986), Green et al. (1992) aa Form F has now been excluded.
implicated as such in Thailand where it is apparently rare. An.
maculatus is widespread but is only considered to be a major
vector in southern Thailand and peninsular Malaysia (Hodgkin,
1956; Rahman et al., 1993). Since the presence of malaria
transmitted by An. maculatus correlates with the presence of
form E, it is possible that only this chromosomal form is able to
transmit malaria to any significant extent (Rongnoparut et al.,
1996; Kittayapong et al., 1993; Upatham et al., 1988). An.
maculatus is considered to be a principal vector in Java (Barcus
et al., 2002), but its cytotype and specific identity remain
undetermined. Anopheles pseudowillmori (Green et al., 1991)
and An. maculatus and An. sawadwongporni (Rattanarithikul
et al., 1996; Somboon et al., 1998), have been found infected
with malaria parasites in Thailand.
As part of a large-scale study carried out in northwestern
Thailand to understand the ecology and biting behaviour of all
potential malaria vector species in relation to land cover and
land use change, it was necessary to be able to distinguish
species of the Maculatus Group. This excludes An. dispar and
An. greeni which are confined to the Philippines (Rattanar-
ithikul and Harbach, 1991), and which can readily be identified
using the ITS2-RFLP assay of Torres et al. (2000). The other six
species of the An. maculatus group potentially occur in
northwestern Thailand, although only An. maculatus and An.
sawadwongporni are considered to be widespread (Green et al.,
1991). Two molecular methods have been developed to
distinguish some members of the An. maculatus group in
China (Ma et al., 2002; Li et al., 2003), but these were
unavailable at the start of this study and to our knowledge they
have not been tested for use in Thailand. The number of
specimens to be screened in such studies is often large.
Cytological methods of identification are not suitable as they
are stage-specific, time-consuming and laborious to perform.
PCR-based methods of identification are preferable as they are
relatively quick, straightforward and reliable. Regions of the
ribosomal DNA (rDNA) are often the markers of choice in
Anopheles for this purpose as there are often fixed differences
even between closely related species (Collins and Paskewitz,
1996; Walton et al., 1999a).
The aim of this work was two-fold: (1) to explore the genetic
diversity of the An. maculatus group and (2) to develop a PCR-
al names and reported distributions
Distribution
Bangladesh, Cambodia, China, India, Indonesia, Laos, Malaysia,
Myanmar, Nepal, Pakistan, Sri Lanka, Taiwan, Thailand, Vietnam
Cambodia, China, Myanmar, Thailand, Vietnam
China (Yunnan), India (Punjab, Assam, Kasauli), Nepal, Thailand
(northwest), Vietnam (Tonkin)
India (Nilgiri Hills), Myanmar (Kale Valley), Thailand (northern)
Thailand (Kanchanaburi, Nakhon Phanom, Phetchaburi)
India (Punjab, Almora Kumao, Kasauli, Kalpa, Assam), Nepal,
Pakistan (Kashmir), Thailand (Chiang Mai)
Philippines
Philippines
nd Baimai et al. (1993).
C. Walton et al. / Infection, Genetics and Evolution 7 (2007) 93–102 95
based identification method to reliably distinguish species of
the group in northwestern Thailand, which could be used in a
large-scale epidemiological and ecological study. The marker
used for these purposes was the second internal transcribed
spacer (ITS2) that separates the 5.8S and 28S rDNA subunits.
The diversity of the An. maculatus group was investigated, not
only within the study foci in northwestern Thailand, but also in
the rest of Thailand and other Southeast Asian countries. This
enabled us to evaluate the geographic extent over which the
identification method is potentially applicable since this is
dependent upon the distribution of genetic diversity of ITS2
within and between species.
2. Materials and methods
2.1. Mosquito collection and morphological and
chromosomal identification
Adult mosquitoes were collected using animal and human
baits at sites 1 and 2 in northwestern Thailand (Fig. 1, Table 2),
and progeny broods were raised from some females. Larvae
were collected from the edges of running streams and reared to
adulthood. Collections of larvae and adults were made at the
mountain site 3 (Doi Inthanon) in an attempt to collect the
higher altitude species An. willmori, but only An. maculatus and
An. pseudowillmori were found. Specimens were identified to
species based on adult and egg morphology (Rattanarithikul
and Green, 1986) (keys are unavailable for immature stages of
the An. maculatus group) and/or metaphase karyotypes (Baimai
et al., 1993). Mosquitoes that could be reliably identified to
species (some of which were from progeny broods and some of
which were field-caught mosquitoes) were designated as
reference specimens. Some siblings of the progeny broods
were retained as vouchers in The Natural History Museum,
London. In collections from sites 4 to 8, made during routine
Fig. 1. Outline map of Thailand and part of Southeast Asia showing the 33 mosquito
the epidemiological and entomological study area in northwestern Thailand.
collections in our ecological and epidemiological study, the
mosquitoes were identified to the group level only and
subsequently sequenced or tested using the identification assay
developed herein. Mosquitoes from other localities in Thailand,
Cambodia, mainland China, Malaysia, Taiwan and Vietnam
were also sequenced to examine geographical diversity.
2.2. DNA extraction, amplification and sequencing of ITS2
DNA was extracted from whole individual mosquitoes using
a salting-out protocol (Sunnucks and Hales, 1996). One
microlitre of DNA (equivalent to 1/800 of a mosquito) was used
in each 50 ml PCR reaction. The rDNA ITS2 was amplified
using primers 5.8F (50-TGTGAACTGCAGGACACATG-30)and 28R (50-ATGCTTAAATTTAGGGGGTA-30) (Collins and
Paskewitz, 1996). The concentrations of the reactants were:
0.2 mM of each primer, 200 mM dNTP, 2.5 mM MgCl2, 20 mM
(NH4)2SO4, 75 mM Tris–HCl (pH 8.8) and 0.01% (w/v)
‘Tween’. One unit of Thermoprime Plus DNA Polymerase
(ABgene, Epsom, UK) was used per reaction. The samples
were heated at 94 8C for 5 min before 35 cycles of amplification
at 94 8C for 1 min, 61 8C for 30 s and 72 8C for 30 s followed by
a final extension step of 5 min. The amplification products were
purified on columns and sequenced using the PCR primers and
fluorescent chemistry (Applied Biosystems, Warrington, UK).
Sequences were aligned and checked manually in SeqEdit
(version 1.0.3) (Applied Biosystems, Warrington, UK). Most of
the sequencing was done in both directions, including that for
all reference specimens, all specimens of An. pseudowillmori,
chromosomal form K and Anopheles dravidicus from Thailand,
and at least two specimens from each sampling site. The
remainder were confirmed to be one of the established
sequences by comparison of the ITS2 sequence generated by
sequencing in a single direction, but if there was any ambiguity
they were then sequenced in both directions.
collection sites listed in Table 2. The box indicates the approximate coverage of
C. Walton et al. / Infection, Genetics and Evolution 7 (2007) 93–10296
Table 2
Number of specimens of each species sequenced for ITS2 from each site
Site no. Date (month/year) Collection sites (country, province, village/town) Species
MAC SAW PSEU DRAV K
1 November 2000 Thailand, Mae Hong Son, Ban Mae Top Nua 10 6 3 3 –
2 November 2000 Thailand, Lampang, Ban Den Udom – 8 – – –
3 April 2001 Thailand, Chiang Mai, Doi Inthanon 6 – – – –
4 June 2001–December 2002 Thailand, Mae Hong Son, Ban Nong Khao Klang 2 – – – –
5 June 2001–December 2002 Thailand, Mae Hong Son, Ban Huai Pong Khan Nai – 2 – – –
6 June 2001–December 2002 Thailand, Mae Hong Son, Huai Chang Kham 3 8 – 1 –
7 June 2001–December 2002 Thailand, Chiang Mai, Ban Huai Ngu 2 1 – – –
8 June 2001–December 2002 Thailand, Lamphun, Ban Pang – 8 – – –
9 October 1996 Thailand, Loei, Ban Pa Kow Lam 4 3 – – –
10 October 1996 Thailand, Sakhon Nakhon, Ban Kok Klang 1 – – – –
11 October 1996–December 2004 Thailand, Ubon Ratchathani, Na Chaluai and Kang
Ka Lao National Park
– – – – 3
12 July 2001 Thailand, Kanchanaburi, Ban Phu Toei 3 – – – –
13 July 2001 Thailand, Prachaup Khiri Khan, Huey Rae 1 1 – – –
14 July 2001 Thailand, Prachaup Khiri Khan, Palau-U 3 2 – –
15 July 2001 Thailand, Chumphon, Ban Noi Chok Kwa 5 – – –
16 July 2001 Thailand, Ranong, Ban Hing Chang 6 – – – –
17 July 2001 Thailand, Song Khla, Pedang Besar 5 – – – –
18 August 2003 Malaysia, Terengganu, Kampungs Jenagor, Basong,
Payah Kayu and Dura
11 – – – –
19 August 2003 Malaysia, Pahang, Sungai Beruas 4 – – – –
20 August 2003 Malaysia, Johor, Kota Tinggi 3 – – – –
21 August 2001 China, Guangxi, Pubei, Chengguan 13 – – – –
22 August 2001 China, Guangdong, Huidong, Daling 14 – – – –
23 September 2000 China, Taiwan, Taitung 8 – – – –
24 June 2001 China, Hainan, Changjiang, Shilu – 1 – – –
25 June 2003 Vietnam, Lang Son, Trang Dinh, Chi Minh 1 – 1 – –
26 July 2000 Vietnam, Ninh Binh, Cucphuong National Forest 5 – – – –
27 May 2004 Vietnam, Nghe An, Thanh Chuong, Thanh Lam 1 – – – –
28 2003 Vietnam, Quang Binh, Le Thuy, Ngan Thuy 3 – – 3
29 June 2004 Vietnam, Quang Ninh, Ba Che, Thanh Lam 5 – – – –
30 October 2003 Cambodia, Preah Vihear, Ror Vieng, Romeny – – – – 3
31 June 2003 Cambodia, Ratanakiri, Ochum, Chaongchan 6 1 – – –
32 October 2003 Cambodia, Pailin, Pang Rolim – 1 – – –
33 June 2003 Cambodia, Pursat, Dey Kra Hom – 3 – – –
Total per species 122 48 4 4 9
The morphologically identified specimens came from sites 1 and 2 and cytologically identified specimens of form K were collected at site 11. Other specimens were
identified from field collections as belonging to the An. maculatus group and identified to species based on ITS2 sequences. Collection sites were at or near the
localities indicated and their approximate locations are shown in Fig. 1. MAC, An. maculatus; SAW, An. sawadwongporni; PSEU, An. pseudowillmori; DRAV, An.
dravidicus; K, form K (see text).
2.3. Sequence alignment and phylogenetic analysis
DNA sequences were aligned using Clustal W version 1.7
(Thompson et al., 1994). Phylogenetic relationships were
inferred using maximum-likelihood (ML), maximum parsi-
mony and neighbour-joining methods in PHYLIP version 3.5c
Table 3
Primers used in the multiplex PCR and expected sizes of the fragments amplified
Primer Sequence Lengt
5.8F 50-ATCACTCGGCTCGTGGATCG-30 20
MAC 50-GACGGTCAGTCTGGTAAAGT-30 20
PSEU 50-GCCCCCGGGTGTCAAACAG-30 19
SAW 50-ACGGTCCCGCATCAGGTGC-30 19
K 50-TTCATCGCTCGCCCTTACAA-30 20
DRAV 50-GCCTACTTTGAGCGAGACCA-30 20
(Felsenstein, 1989). Kimura two-parameter distances with a
transition/transversion ratio of two were used for tree
construction with the neighbour-joining method. The model
for the ML method used one category of substitution rates,
empirical base-frequencies and an expected transition/transver-
sion ratio of 2. The global search option was also used in ML
from each species
h (bp) Species Fragment size (bp)
Universal forward
An. maculatus 180
An. pseudowillmori 203
An. sawadwongporni 242
Form K 301
An. dravidicus 477
C. Walton et al. / Infection, Genetics and Evolution 7 (2007) 93–102 97
tree construction to further explore alternative tree topologies.
Bootstrap supports were based on 1000 re-sampled datasets
using SEQBOOT in PHYLIP. Trees were visualised using
TREEVIEW (Page, 2001).
2.4. PCR conditions for the identification method
Reactants: 0.2 mM of primers 5.8F, MAC, DRAV, K and
0.1 mM of primers SAW and PSEU (primers defined in
Table 3); 2.5 mM MgCl2; 200 mM dNTP; 20 mM (NH4)2SO4,
75 mM Tris–HCl (pH 8.8) and 0.01% (w/v) ‘Tween’; 0.5 units
of Thermoprime Plus DNA Polymerase (ABgene, Epsom, UK);
and 1 ml of genomic DNA sample in a total reaction volume of
25 ml. The samples were heated at 94 8C for 5 min before 35
cycles of amplification at 94 8C for 1 min, 61 8C for 30 s and
72 8C for 30 s followed by a final extension step of 5 min.
3. Results
Adult and larval mosquitoes from sites 1 to 3 in northwestern
Thailand (Fig. 1, Table 2) were identified morphologically to
obtain a set of reference specimens for the study area. Four
species of the An. maculatus group were identified: An.
maculatus, An. sawadwongporni, An. dravidicus and An.
pseudowillmori. Despite numerous entomological surveys, An.
notanandai has not been recorded from this region of Thailand,
so it is possible that it does not occur there. Although An. willmori
has been recorded in northwestern Thailand, it is associated with
higher altitudes and is therefore unlikely to occur in the majority
of entomological and epidemiological surveys.
The reference specimens from sites 1 to 3 (16 An. maculatus,
14 An. sawadwongporni, 3 An. pseudowillmori and 3 An.
dravidicus (Table 2, Fig. 1)) were sequenced for ITS2. The
sequences for the four species are quite distinct from each other
and no intraspecific variation was found (Fig. 2). To further
establish that only these species were present at the field sites in
northwestern Thailand, the ITS2 sequences of 27 additional
specimens from sites 4 to 8 (Table 2, Fig. 1) were also obtained.
Each was found to have a sequence identical to one of the four
reference sequences.
To assess the level of geographical variation, another 146
mosquitoes, collected from other areas within Thailand and
from other countries in Southeast Asia, were sequenced for
ITS2 (Table 2). Despite the wide geographical range covered,
no intraspecific variation was found. In the case of An.
maculatus, this involved specimens from northern and southern
Thailand, Cambodia, China (Guangxi, Guangdong and
Taiwan), Malaysia and Vietnam, and for An. sawadwongporni
specimens were from mainland China, Cambodia, Vietnam and
northern and southern Thailand. However, three specimens that
were identified as chromosomal form K from eastern Thailand
(site 11, Table 2 and Fig. 1) had a quite distinct ITS2 sequence
(sequence K in Fig. 2) differing by 14 base substitutions and the
length of an indel from the next most closely related sequence,
of An. sawadwongporni (Fig. 2). This sequence was also
obtained from three specimens from Cambodia (site 30) and
three from Vietnam (site 28).
Comparisons were made between the species-specific ITS2
sequence found in this study and ITS2 sequences of the same
species from mainland China and Malaysia that were available
from GenBank. Several bases (�20) from the beginning and
end of the database sequences were excluded in these
comparisons as the multiple differences observed in these
regions, in comparisons with our sequences, are most likely due
to sequencing errors in the database sequences (as the region
near to the primer can be difficult to read), or possibly due to the
inclusion of primer sequences with the submitted sequence. On
this basis, ITS2 sequences from An. maculatus (AF261950),
An. sawadwongporni (AF512551) and An. dravidicus
(AF261951) from mainland China were identical to those
found in our study. The ITS2 sequence of An. pseudowillmori
(AF512550), however, differed at seven sites from the sequence
of Thai specimens. A second (partial) sequence from An.
pseudowillmori (AF261952) was more similar to the sequence
of Thai specimens although it still differed by at least one base.
(This sequence was not included in the phylogenetic analysis
because it was incomplete.) The two database sequences of An.
maculatus from Malaysia (AF500072 and AF500073) both
differed at three bases (32, 150 and 240, Fig. 2) from the
sequence of this species that we obtained from Thai, Chinese,
Malaysian and Cambodian mosquitoes. AF500072 (MAC
Malay1) differed at another two bases and AF500073 (MAC
Malay2) differed at another six bases from our sequence of An.
maculatus.
A molecular phylogeny (Fig. 3) was constructed using all the
unique ITS2 sequences of members of the An. maculatus group
available from this study and from GenBank, using the
alignment in Fig. 2. The gene tree in Fig. 3 was constructed
using maximum-likelihood and is unrooted because an
outgroup with easily aligned ITS2 is not available. ML and
maximum parsimony methods of tree construction resulted in
the same tree topology. However, the relative positions of An.
willmori, An. dravidicus, An. dispar and An. greeni were altered
when the neighbour-joining method was used, although the
latter two species still clustered with An. maculatus. There is
low bootstrap support (�56%) for the deeper branching events.
Nevertheless, Fig. 3 illustrates clearly that the specimens of
chromosomal form K are most closely related to An.
sawadwongporni, yet show a level of sequence divergence
comparable to that between other species of the group. These
sequences have been deposited in GenBank (accession numbers
DQ518615–DQ518629).
The identification method is based on the principle of allele-
specific amplification in which Thermus aquaticus (Taq) DNA
polymerase is unable to extend primers that are mismatched to
their template DNA (Ugozzoli and Wallace, 1991; Scott et al.,
1993). The alignment of the sequences from each species
(Fig. 2) was used to design species-specific amplification
primers with a reverse orientation (Table 3, Fig. 2). A single
universal primer (5.8F) binds to the 5.8S gene in all species in
the forward orientation (Collins and Paskewitz, 1996). The
reaction conditions were optimised with respect to annealing
temperature, magnesium concentration, primer concentration
and polymerase concentration to ensure that each species-
C. Walton et al. / Infection, Genetics and Evolution 7 (2007) 93–10298
Fig. 2. Alignment of ITS2 sequences of members of the An. maculatus group collected and sequenced in this study: An. maculatus (MAC), An. sawadwongporni
(SAW), An. pseudowillmori (PSEU), An. dravidicus (DRAV) and chromosomal form K (K); together with differing sequences obtained from GenBank: An.
pseudowillmori (PSEU China; accession number: AF512550) and An. willmori from China (WILL; AF512552), An. dispar (DISPAR; AF234778) and An. greeni
(GREENI; AF234779) from the Philippines; and two sequences of An. maculatus, one from Jeram Kedah, Negeri Sembilan, central peninsular Malaysia (MAC
Malay1; AF500072) and the other from Johore in southern peninsular Malaysia (MAC Malay2; AF500073). Dots indicate identity with the reference sequence from
An. maculatus and a dash denotes a deletion with respect to the other sequences. Boxes indicate the binding sites of the species-specific primers (Table 2).
C. Walton et al. / Infection, Genetics and Evolution 7 (2007) 93–102 99
Fig. 3. Unrooted phylogenetic tree constructed using maximum-likelihood,
showing bootstrap values �50%. (Asterisk (*) indicates a partial sequence of
An. pseudowillmori from China, AF261952 only differs by a single base
insertion from sequences of Thai and Vietnamese specimens.)
specific primer (in combination with the universal primer) only
amplifies DNA from the corresponding species and there is no
cross-amplification with any of the other primers. The
optimised reaction conditions for the identification method
are given in Section 2. Inclusion of all the primers in a single
PCR reaction with DNA from one of the five species generates a
PCR product of a diagnostic length (Table 3) that can be
detected by agarose gel electrophoresis (Fig. 4).
Since large number of mosquitoes need to be identified for
meaningful epidemiological and ecological field studies, we
sought to develop a quick, reliable method of processing
mosquitoes. The use of a crude extraction method (see Section
2), rather than a complex DNA extraction method that yields
Fig. 4. A 1.5% agarose gel showing the amplification products generated from
the multiplex PCR using DNA isolated from individual mosquitoes of known
species. Lane 1: 20 bp marker; lanes 2 and 15: 100 bp marker; lanes 3 and 4: An.
maculatus; lanes 5 and 6: An. pseudowillmori; lanes 7 and 8: An. sawadwong-
porni; lanes 9 and 10: chromosomal form K; lanes 11 and 12: An. dravidicus;
lane 13: no DNA control; lane 14: 50 bp marker.
DNA of high quality, was therefore investigated. Ten-fold serial
dilutions of crude DNA samples (prepared from heads) were
used in the multiplex PCR. Amplification was successful across
four orders of magnitude of sample concentration, indicating
that this simple method of DNA extraction is extremely robust.
Extracted samples have been used successfully for up to 2
weeks after preparation when stored frozen. The DNA is
unlikely to be suitable for long-term storage but the method
does enable the identification procedure to be repeated if
necessary. Legs or heads can be used for DNA extraction
enabling the remainder of the mosquito to be used for other
assays, preserved for long-term storage for other studies, or
retained as a voucher. Routinely, whole mosquitoes are boiled
for 15 min in 200 ml of water and 1 ml used in the above PCR
identification method.
4. Discussion
4.1. Species diversity
The sequencing survey and phylogenetic analysis (Fig. 3)
indicate greater species diversity in the An. maculatus group
than has been recognised formally up to now. In the general
context of low intraspecific variation, the high degree of
differentiation of the specimens of chromosomal form K from
the other species (3.7% divergence from the most closely
related species, An. sawadwongporni; Fig. 3) is strong evidence
that these belong to another species. Divergence among
members of mosquito species complexes varies but can be
substantial (e.g. �10–18% at ITS2 among members of the An.
annularis group, unpublished data). However, divergence at
ITS2 can be much lower than this even between well-
recognised species; for example, it is only 0.6% between An.
dirus and An. baimaii (Walton et al., 1999b), 1.0% between An.
maculipennis and An. daciae (Nicolescu et al., 2004), and 0.4–
1.6% among members of the An. gambiae complex (Paskewitz
et al., 1993). The species status of this chromosomal and
genetic form needs to be confirmed by observing sympatry
without heterozygotes using chromosomal or other markers.
Although it is possible that form K corresponds to An.
notanandai, it is unlikely since An. notanandai corresponds to
chromosomal form G and has previously only been reported
from eastern Thailand (Table 1, Rattanarithikul and Green,
1986). According to R. Rattanarithikul (personal communica-
tion to REH), form K is morphologically similar to, but
distinguishable from, An. notanadai, providing additional
evidence that form K represents another species of the An.
maculatus group.
There are two sequences for An. pseudowillmori from
Yunnan Province, China in the database. One sequence
(AF261952) appears to be the same as the Thai and Vietnamese
sequences generated in this study (see below). The other
sequence (AF512550) exhibits seven differences from the
sequences of Thai An. pseudowillmori even after the ends are
trimmed. It is therefore possible that these sequences
correspond to two different, yet very closely related species.
However, since it is unknown whether the Chinese specimens
C. Walton et al. / Infection, Genetics and Evolution 7 (2007) 93–102100
were collected from the same or different places within Yunnan,
they may merely represent geographically isolated and diffe-
rentiated populations of An. pseudowillmori.
The taxonomic status of chromosomal forms B and E of An.
maculatus remains unclear, although the apparent difference in
vectorial capacity between them makes this distinction
particularly worthwhile to clarify. Previous collection records
with associated chromosomal data indicate the northernmost
collection of chromosomal form E is from Phato, Rangong (at
latitudes of 098460N and less) (Green et al., 1985), but
according to Rongnoparut et al. (1999) this form occurs as far
north as �128N. The majority of our specimens are therefore
expected to be form B, but those from sites 13, 14, 15, 16 and 17
in peninsular Thailand, and especially those from sites 18, 19
and 20 in Malaysia, are most likely to be chromosomal form E.
Despite the likelihood that our specimens include both
chromosomal forms, only a single ITS2 sequence was detected.
The two GenBank sequences of Malaysian An. maculatus
differ by several bases from the sequences that we obtained from
specimens of An. maculatus collected in Thailand, China,
Cambodia, Vietnam, Malaysia and Vietnam. This difference
could correspond to the two chromosomal forms if the Malaysian
mosquitoes from the database are all form E and our mosquitoes
are all chromosomal form B, although, as argued above, this
seems unlikely. Rather than indicating any form of intraspecific
variation or the presence of cryptic species, the differences in the
Malaysian sequences may be due to sequencing errors. This is
supported by the fact that the sequencing we report here was
carried out independently in two laboratories without any
conflict. Furthermore, errors in GenBank sequences have been
noted previously (Linton et al., 2002). It is clearly important to
gather more sequence data (from more variable loci), ideally
coupled with chromosomal data and epidemiological data, from
An. maculatus in Malaysia.
4.2. Phylogenetic relationships
Fig. 3 shows clearly that the putative species corresponding to
chromosomal form K is the sister of An. sawadwongporni.
Ongoing studies have shown that the adults of both taxa have
overlapping morphological characters, but their eggs are clearly
distinct. Moreover, crossing experiments revealed post-zygotic
isolation between chromosomal form K and both An. maculatus
(form B) and An. sawadwongporni (P. Somboon, unpublished
data). It can also be seen that the two genetic forms of An.
pseudowillmori are substantially divergent from other members
of the An. maculatus group. However, the low bootstrap support
(�56%) for the deeper branching events in Fig. 3, illustrates that
the rapidly evolving ITS2 locus is unable to resolve the deeper
relationships. A full understanding of the phylogenetic relation-
ships within the group will require the analysis of other loci, such
as more conserved regions of the rDNA or mtDNA genes.
4.3. Intraspecific diversity
Despite considerable geographic sampling, no intraspecific
variation was found in ITS2 in the 187 specimens that we
sequenced. (This assumes that we have correctly interpreted the
level of divergence observed between putative species K and
other members of the group as representing interspecific
divergence rather than intraspecific variation.) The only
indication of intraspecific variation came from comparisons
made with sequences obtained from sequence databases. The
difference of a one base insertion in An. pseudowillmori from
China (AF261952) relative to the sequences of Thai specimens
could be due to sequencing error since the other three species in
Thailand and China (An. sawadwongporni, An. maculatus and
An. dravidicus) were identical to each other (once starting and
ending sequences are edited from the Chinese sequences). Given
that we found no variation in An. maculatus from Thailand,
China, Cambodia, Vietnam and Malaysia, the variation observed
between the sequences of the two Malaysian specimens is
unexpectedly high. It would be helpful if this locus could be
sequenced from more individuals from countries neighbouring
Thailand, particularly China and Malaysia, to establish the extent
of any intraspecific variation within members of the group.
The lack of intraspecific variation that is generally observed
over a large geographic area could imply sufficient gene flow to
allow homogenisation of sequences of the rDNA genes by
concerted evolution (Elder and Turner, 1995). Alternatively, it
could reflect a demographic history of these populations in
which they have been derived sufficiently recently to have
prevented diversification from the ancestral sequence. The very
low level of population structure detected in An. maculatus in
Thailand using microsatellites (Rongnoparut et al., 1999) is
consistent with both of these hypotheses.
4.4. Applicability of the identification method
When the molecular identification method was applied to
240 adult mosquitoes of the An. maculatus group from our field
study in northwestern Thailand, it was able to amplify>94% of
the specimens, with the unidentified specimens being attributed
to degraded DNA due to poor preservation. An. maculatus and
An. sawadwongporni are the most abundant species (51.7% and
42.1% of the total, respectively), correlating with their
widespread distribution indicated in Table 2. An. dravidicus
and An. pseudowillmori were rarely encountered (2.1% and
4.2% of the total, respectively), but this could, in part, be due to
differences in feeding preferences as all specimens were
captured on human bait. Chromosomal form K was never
encountered, which together with its incidence at sites 11, 28
and 30, suggests that it has an eastern distribution in mainland
Southeast Asia.
The general lack of intraspecific variation in ITS2 sequence
makes the identification method likely to be very useful over a
large geographic area—apparently at least in Malaysia, most of
Thailand, parts of China, and most probably Cambodia,
Vietnam and Taiwan. However, the method will not distinguish
the two sequences of ITS2 obtained from An. pseudowillmori in
China. The inclusion of chromosomal form K in the
identification method will help to extend its usefulness to
eastern Thailand, and to Vietnam and Cambodia where this
form also occurs. In some areas it will be necessary to adapt the
C. Walton et al. / Infection, Genetics and Evolution 7 (2007) 93–102 101
method to include the identification of additional species, for
example, An. willmori in high altitude areas and An. notanandai
in west-central Thailand. The sequence alignment (Fig. 2)
illustrates that there appears to be ample variability between
species, and the region is sufficiently lengthy to enable primers
to be designed for additional species. Before the method is
deployed in new areas, it is clearly advisable to assess which
species are present and the extent of intraspecific variation by
sequencing the ITS2 region of specimens from the area.
In conclusion, the identification method presented here is
likely to work over a large geographic area with scope to
modify it to include additional species. Furthermore, it is very
robust to the use of a simple and rapid DNA extraction method
and to the concentration of DNA used. For this reason, and the
fact that the method requires only a single step, a PCR reaction,
before running the samples on an agarose gel, the method is an
eminently practical tool for large-scale field-based studies
where reliable species identification is important.
Acknowledgements
We thank the many people who contributed to the mosquito
collections for this study, including: Dr. Samsak Prajakwong,
former director of the Office of Vector-Borne Disease Control
No. 2 in Chiang Mai, Thailand, and his staff, particularly Mr.
Raksakul Kantawong, for their assistance in collection and
identification of mosquito specimens in Thailand; Conor Cahill
and Mark Isenstadt for assistance with collections in north-
western Thailand; Dr. Hwa-Jen Teng, Division of Vector-borne
Infectious Diseases, Taiwan, and Prof. Masahiro Takagi and Dr.
Yoshio Tsuda, Institute of Tropical Medicine, Nagasaki
University, Japan, for organizing the collection of specimens
in Taiwan; Dr. Ngyuen Duc Manh and staff of the National
Institute of Malariology, Parasitology and Entomology, Hanoi,
Vietnam, for collecting and providing specimens from
Vietnam; Dr. Tho Sochanta and other staff of the National
Center for Malaria, Parasitology and Entomology, Cambodia,
for their assistance in the collection and identification of
mosquitoes in Cambodia. This work was part of the
RISKMODEL and MALVECASIA projects funded by the
European Union, grant numbers QLK2-CT-2000-01787 and
ERBIC 18CT970211, respectively.
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