Journal of Threatened Taxa |
www.threatenedtaxa.org | 26 May 2022 | 14(5): 21043–21054
ISSN 0974-7907
(Online) | ISSN 0974-7893 (Print)
https://doi.org/10.11609/jott.5490.14.5.21043-21054
#5490 | Received 23
August 2019 | Final received 16 January 2021 | Finally accepted 07 April 2022
Bionomics study of Mansonia (Diptera: Culicidae) in a filariasis-endemic area of Sedang Village, Banyuasin
Regency, South Sumatra, Indonesia
Rini Pratiwi
1, Chairil Anwar 2, Ahmad Ghiffari 3 & Adri Huda 4
1,2 Department of
Parasitology, Faculty of Medical Science, Sriwijaya
University, Ogan Ilir
30662, South Sumatera, Indonesia.
1 Department of
Health, The Government of Banyuasin District, Pangkalan Balai 30911, Indonesia.
3 Department of
Parasitology, Faculty of Medical Science, University of Muhammadiyah Palembang,
Palembang 30263, South Sumatera, Indonesia.
4 Department of
Chemistry, Faculty of Mathematics and Natural Science, University of Sumatera
Utara, Medan 20155, North Sumatera, Indonesia.
1 dr_ninik.6575@yahoo.com
(corresponding author), 2 chairil53@fk.unsri.ac.id, 3 dokter.ghi@gmail.com,
4 adri.huda28@gmail.com
Editor: Anonymity
requested Date of publication:
26 May 2022 (online & print)
Citation: Pratiwi,
R., C. Anwar, A. Ghiffari & A. Huda (2022). Bionomics study of Mansonia (Diptera: Culicidae) in a filariasis-endemic area of Sedang Village, Banyuasin
Regency, South Sumatra, Indonesia. Journal of Threatened Taxa 14(5): 21043–21054. https://doi.org/10.11609/jott.5490.14.5.21043-21054
Copyright: © Pratiwi
et al. 2022. Creative Commons Attribution
4.0 International License. JoTT allows unrestricted use, reproduction, and
distribution of this article in any medium by providing adequate credit to the
author(s) and the source of publication.
Funding: There is no funding
declared in the present study.
Competing interests: The authors
declare no competing interests.
Author details: Dr. Rini Pratiwi, M.Kes., graduated from Department of Environmental Science with a specific research topic on
how the environmental
condition affected the filariasis vector
transmission. Currently, Rini is a head of health department in Banyuasin regency and also a lecture
in the department of parasitology, faculty of medical science, Sriwijaya University.
Prof. dr. Chairil
Anwar, DTM&H, DAPK, Sp.Park, Ph.D., is a Professor in Faculty
of Medical Science, Sriwijaya University. Prof. Anwar has the
expertise on parasitology which
proved by a series of scientific publication of tropical parasitology. Dr. Ahmad Ghiffari, M.Kes., is currently a PhD
student in Environmental Science
Department of Sriwijaya
University. His research focused on tropical disease especially the one occurred in South Sumatera, Indonesia.
Dr. Adri Huda,
S.Si., earned Ph.D. in Environmental Science, Sriwijaya University.
His role was to give some other
point of view related to the present studies.
Author contributions: RP—conceptualization, research
design, field supervisor, writing.
CA—research supervisor, evaluation, data interpretation. AG—data
interpretation, data analysis. AH—writing,
data visualization, writing, data analysis.
Acknowledgements: Authors acknowledge the
Government of Banyuasin District for supporting the
present research.
Abstract: An investigation of bionomic
study of Mansonia species was
successfully conducted in Sedang village which is one
of the filariasis-endemic areas in Indonesia. The study was carried out for 14
months from April 2017 to May 2018. In order to trap the local mosquitoes in
the study area, indoor and outdoor human landing collection method was
adopted. During the study, 7,908
mosquitoes were collected which consisted of 13 genera and 40 species of
mosquitoes. Moreover, Mansonia uniformis, M. annulifera, and
M. indiana were found to be the most abundant,
dominant, and high frequency mosquitoes. The filariasis vector analysis through
polymerase chain reaction test confirmed that only Mansonia
annulifera positively detected as the filariasis
vector. Furthermore, the longevity calculation showed that 81% of all the
collected Mansonia spp. had already oviposited their eggs which indicates that the studied area
possesses high possibilities of filariasis transmission.
Keywords: Filariasis diseases, filariasis
vector analysis, Mansonia spp.,
mosquitoes, tropical diseases, vector transimission.
INTRODUCTION
Filariasis is a zoonotic disease
caused by the infestation with microfilaria, which is found in tropical areas,
such as Indonesia. This disease has caught the attention of world researchers
and policy-makers alike, especially in tropical and subtropical countries
because it has infected more than 120 million people in 72 countries and more
than 90% of filarial infections are infected by Wuchereria
bancrofti and Brugia
malayi which are transmitted by Culex and Mansonia mosquitoes (cdc.gov). Several
studies have reported that Brugia malayi has dominantly caused the transmission of
filarial infection in many Asian countries like China, South Korea, Japan,
India, Myanmar, Indonesia, Malaysia, the Philippines, Thailand, and Bonaire
Islands (Kanjanavas et al. 2009; Tan et al. 2011;
Saeed et al. 2015).
To be more specific in Indonesia,
Banyuasin is a regency in the South Sumatra province
of Indonesia, which has been designated as an area where filariasis is endemic
(Ministry Health of Republic of Indonesia 2016). In 2014, there were 142 cases
of 173 provincial cases of chronic filariasis in Indonesia, in which Banyuasin has a high rate of endemicity, with an average microfilarial rate of 2.02%. Geographically, Banyuasin is a lowland filled with swamps, coastlines, rice
paddies, and plantation fields, which makes it an ideal mosquito breeding
ground. However, based on our knowledge, there is no record of comprehensive
bionomics study in Banyuasin. Thus, this study will
contribute to eradicating filariasis, mainly by vector control and case
management (Saeed et al. 2015).
Herein, the present study aims to
determine the bionomic study of Mansonia
species in Banyuasin including their diversity,
abundance, dominance, and preference. The main reason for choosing this area was based on
the high filariasis cases reported in provincial case of filariasis in Indonesia. It is supported by the fact
that the studied area still has high microfilaria rate which is 0.93% after conducting Mass Drug
Administration (MDA) programmes
by the Ministry of Health, Republic of Indonesia for the last three year
(2013–2016) to eliminate
the filariasis in this area. Therefore, the results are
expected to provide evidence base and references to strategize a further
prevention action to reduce the number of filariasis cases in Banyuasin regency, South Sumatera, Indonesia. The results
could also become the reference and information baseline about the diversity
and behavior of Mansonia spp. in Indonesia
which enhance knowledge in Entomology.
MATERIALS
AND METHODS
Study Area
The research was focused in
Sedang Village which is located in
Suak Tapeh District in Banyuasin Regency, South Sumatera-Indonesia. The
research area had the coordinate of 2.853S and
104.579E with the altitude of 10 m. The
studied area has a tropical weather with an
average temperature of 26–28 oC and humidity ranging 89–92 %. The study area is dominated by high water bodies
such as swamplands, ponds which has water plantations (Department Health of Banyuasin District,
2016). Image 1 presents the landscape of studied area taken using a drone.
Mosquito collection
All the obtained mosquitoes in
this study were collected once a month for 14 months started from April 2017 to
May 2018. Human landing collection (HLC) method was followed for both indoor and outdoor for 24 hours
from 18.00 until 17.00 in the next day by six teams which consist of 12
volunteers. The six teams were divided into two teams (three team each condition) to collect the biting mosquitoes
indoor and outdoor condition. The mosquitoes attached and rested to humans or
wall shelters (rested only) were collected using aspirator for 40 minutes/hour
and 10 minutes/hour, respectively. For consideration, all the research activities
had been approved by the ethics team of Sriwijaya
University (Ethical Access Certificate No. 522 / kepkrsmhfkunsri
/ 2016).
Mosquito identification
All the collected-mosquitoes were
further identified using the Rampa & Wharton identification book and carefully counted (Wharton 1978; Rattanarithikul 2005). In this study, only female
mosquitoes were collected as biting mosquitoes since the male mosquitoes did
not bite the volunteers in human landing method (Shirai et al. 2002). The females of Mansonia were then dissected to determine parity
using dilatation methods and identify the ovarian as parous or nulliparous
(Image 2).
Data analysis
All the collected mosquitoes in
biting and resting positions were summarized and divided into several
categories including diversity, abundance, frequency, dominance, man-hours
density, man-biting rate, and resting rate. The detailed calculation to determine
each category was shown in several formulas below.
Abundance= (Total number of collected
mosquitoes per species / Total number of collected mosquitoes) x 100 % (1)
Frequency= Total number of collected
mosquitoes per species / Total collecting hours
(2)
Dominance= Frequency x Abundance (3)
Man-hours
density= Total
number of collected mosquitoes per species / Total collection hours per day x
number of day x number of collector x duration of collection (minutes) (4)
Man-biting
rate= Total number of collected biting mosquitoes / Total number of collector x
number of collection hours (5)
Resting rate=
(Total number of collected resting mosquitoes per species / Total number of
collected resting mosquitoes) x 100%
(6)
Longevity (P)= A√B
where A=
Physiological age of collected mosquitoes (gonotrophic cycle); B= Proportion of
porous from several dissected mosquitoes; P= Daily life opportunities.
Estimated age of mosquito population= 1 / -log eP (7)
Biomolecular examination
The molecular examination was
carried out to determine the filariasis vector through DNA isolation from the
heads of the Mansonia spp. Twenty-five
mg sample kept in 1.5 ml microtube was smashed with pastel and added with 180
µl buffer ATL and 20 µl proteinase K. After vortex, the sample was incubated at
56 oC until lysed. Then 200 µl buffer AL
and 200 µl ethanol (96–100 %) was added and vortexed, respectively, followed by
the spinning period with Dneasy Mini Spin (Blood
& Kit 2006). Brugia malayi
specific primers were forward (5’-GCGCATAAATTCATCAGC-3’) and reverse
(5’-GCGCAAAACTTAATTACAAAAGC-3’) amplified using thermal PCR (Haryuningtyas & Subekti
2008). The PCR temperature and the master mixes were according to Goodman et
al. (2003). The amplicon was later electrophoresed at 80 volts for 40 minutes.
The gel was 2% agarose TAE with ethidium bromide and read after the DNA ladder
addition under ultraviolet light using Gel doc. The PCR results positively
result in a band at 326 bp as Brugia
malayi.
RESULT
AND DISCUSSION
Mosquito collections
Table 1 showed the diversity and
total number of collected mosquitoes. During the research period, there were
7,908 mosquitoes collected which consisted of 13 genera including Mansonia, Culex, Aedes,
Anopheles, Coquilettidia, Topomyia,
Armigeres, Triptoides, Miomyia, Malaya, Uranataenia, Hodgesia, and Urotonia.
From the 13 genera, all the obtained mosquitoes were analyzed and divided into
40 species. The most dominant diversity was
from the genera Culex which has 12 species, followed by Aedes (9 species), Mansonia
(6 species), Anopheles (3 species), Coquilettidia
(2 species), and 1 species from Armigeres, Triptoides, Malaya, Urotonia, Uranataenia, Topomyia, Coquilettidia, Hodgesia, Topomyia, & Miomyia.
In case of number, Mansonia spp. was
found as the highest collected mosquitoes where 4,448 Mansonia
spp. (56.30%) had successfully collected and identified during the research
period. On the other hand, Culex spp. had the highest species diversity
and was the second most abundant of collected mosquitoes which consists of
1,843 mosquitoes (23.33%).
The result was similar with the
work conducted by Rohani (2013) who had reported the
bionomic study in Malaysia and reported six genera of mosquitoes collected
which were Aedes, Anopheles, Armigeres, Culex, Coquilettidia,
and Mansonia which consist of only 27
species. However, the study reported that Culex spp. was the highest
collected mosquito followed by Anopheles, Armigeres,
Mansonia, Aedes,
and Coquilettidia. As comparison in Indonesia,
Sugiarto (2017) also reported the bionomic study in
North Borneo Island, and found that Anopheles mosquitoes as the most
collected mosquitoes during the research period. We can infer that there is
a difference in the diversity and
abundance of mosquito species in each studied area due to variations in
geographical characteristics, climate, and the availability of breeding grounds
and resting places (Rohani et al. 2013; Sugiarto et al. 2017). Moreover, this finding can
contribute as the information about a fingerprint of specific species located
in Sedang village of Banyuasin
district, South Sumatera-Indonesia.
In order to see the potential of
filariasis transmission vector, the further study was focused on Mansonia spp. as the most collected mosquitoes
during the present study. It was because of the report of Mansonia
spp. as the vector of filariasis compared to the other genera (Kumar et al.
1992).
The species identification showed six
species of Mansonia collected in this study
including M. uniformis, M. annulifera,
M. indiana, M. bonneae, M. annulata, and M. dives. M. uniformis
was found as the most abundant species (41.25%) followed by M. annulifera (35.63%), and M. indiana
(22.14%). The detailed number and percentage of collected Mansonia
spp. as a function of its species can be seen in Table 2.
To be more specific in seasonal
distribution during the study period, M. uniformis,
and M. annulifera were found as the most
predominant mosquito species as they were present in almost all months, while M.
indiana as the third highest number collected
mosquito was not present in December 2017. The other Mansonia
species have relatively low dominance by occurring only in the specific months.
For example, M. bonneae was collected only in
April 2017, May 2017, July 2017, January 2018, and March 2018; M. annulata in May 2017, September 2017, October 2017,
January 2018, and February 2018; and M. dives was only detected in June
2017 and December 2017. Moreover, the period between April 2017 and June 2017
were found as the highest occurrence period of Mansonia
species. It is because the air temperature and relative humidity were 27–28 oC and 90%, respectively which is the most
suitable period for mosquitoes to breed than other seasons.
Frequency, abundance, and
dominance of Mansonia mosquito
The analysis result for the
frequency, abundance, and dominance of mosquitoes biting outdoor and biting
indoor is presented in Table 3. M. uniformis, M. Annulifera, and M. indiana
become the top number of abundance and dominance compared to other species.
Correlating with the number of collected mosquitoes, M. uniformis
has the highest frequency both indoor and outdoor, abundance in indoor, and
dominance in both condition. It was followed by M. annulifera
and M. indiana which become the second and
third species having the highest abundance and dominance under M. uniformis. But, M. annulifera
was found as the highest outdoor abundance compared to all Mansonia
spp. including M. uniformis as the highest
collected mosquito.
In term of resting activities,
there was a correlation between the biting activity and resting activity. Table
4 showed that M. uniformis, M. annulifera and M. indiana
were the species that also had the highest outdoor and indoor resting
frequency, abundance, and dominance compared with other species. In general, we
can say that the high biting activity was positively followed by t high resting
activity. However, M. annulifera showed a
difference where it had high biting behavior and less resting activity.
The hourly biting behavior of
most collected Mansonia spp.
The study was aimed to
investigate the detailed biting time of M. uniformis,
M. annulifera, and M. indiana
as the highest species collected and active during the research period. Figure
2 showed that M. uniformis as the most
collected species had the highest activity in the evening in both conditions
(indoor and outdoor). It began at 1800 h and slightly decreased after 1900 h.
However, the biting activity fluctuated and relatively increased in the early
morning (after 0600 h) and continuously increased until the highest peak at
1800 h and 1900 h for indoor and outdoor activities, respectively. Moreover,
the biting behavior patterns in outdoor and indoor was quite similar, instead
the number of mosquitoes caught are different. The outdoor biting activity was
higher than the indoor biting activity, indicating the M. uniformis was categorized as the exophage species.
Figure 3 showed the biting
activity as a function of time of M. annulifera
for 24 hours of collecting period. The outdoor biting activity began at 1800 h
with the highest biting activity at 1900 h. The biting activity slowly decreased till midnight and then again
slightly decreased after 0400 h. During
noon, most of M. annulifera had low
biting activity until 1600 h and started to increase after 1700 h. The biting
activity was different with the indoor biting behavior of M. annulifera which began the biting activities at 0600 hoand had the highest peak of biting activity at 0300 h.
The indoor biting activity started to drop at 0400 h to 1100 h and fluctuated
between 1200 h and 1700 h. The biting behavior pattern of M. annulifera was different in the highest biting activity
in outdoor and indoor condition, but had
similar behavior in the low biting activity. Based on the number of
collected species, M. annulifera identified as
exophage species which had a higher number of collected mosquitoes in outdoor
compared to the number of catch mosquito in indoor condition.
Figure 4 showed the biting
activities of M. indiana as the third most
collected mosquitoes in this present study. The highest peak of biting activity
of M. indiana conducted at 1800 h and 1900 h
for indoor condition and outdoor condition, respectively. However, there were
an extremely decreased after the highest biting activity for outdoor condition,
while the indoor condition showed a slightly decrease after the highest peak
activity. The biting behavior of M. indiana was
relatively different in outdoor and indoor condition at the highest biting
activity was at 1800 h to 2300 h, but having the similar activity after the
highest peak period. Based on the number of biting activity, M. indiana was the exophage species which had higher
outdoor biting activity than indoor biting activity.
In this study, Mansonia spp. had a higher outdoor biting activity
than indoor biting activity. It was in accordance with the study reported by Supranelfy et al. (2012) where Mansonia
spp. bites more frequently outdoor than indoor condition. However, as the
fraction of indoor biting behaviour remained high, we
would still have to take them into account. The availability of the main indoor
host (humans), or reservoir hosts (i.e., pets), attracted the adult mosquitoes
to do more activities indoors. Besides, the environmental factors including climate,
geography, and geology, the socio-economic-cultural environment (the
environment produced by interpersonal interactions) potentially modify the
outdoor/indoor ratio of biting activity of Mansonia.
Study the resting behavior of
most collected Mansonia spp.
The bionomic study was continued
by investigating the resting behavior of Mansonia
species. In Figure 5, the resting activity of M. uniformis
was quite similar with the biting activity (Figure 2). The highest peak of
highest resting peak was conducted in the similar time of highest peak of
biting activity. The result indicated that most of M. uniformis
did resting activity when doing biting activity. The high number of resting
activity also indicated that there was a high number of mosquito population in
those range of time (1800–1900 h). Moreover, the resting mosquitoes was
slightly down in number after the highest peak of resting activity until
2300 h and become fluctuating after 2300
h until 1700 h the next day. The resting paths for indoor and outdoor condition
were relatively similar, indicating the condition (indoor or outdoor) did not
affect resting behavior. In terms of number, the number of resting activities
was found higher in indoor condition than outdoor condition. However, it could
not be said that M. uniformis was categorized
as endophage species since it was an exophage species based on biting behavior.
The most possibility reason why there were high number of M. uniformis found in indoor condition was because of the
presences of suitable place for resting.
The resting behavior of M. annulifera was found similar with the resting behavior
of M. uniformis where the pathway was
correlated with the biting activity. To be more specific, the outdoor resting
activity began at 1800 h and had the highest peak at 1900 h. The outdoor
resting behavior fluctuated between 2000 h and 0500 h the next day. However,
the indoor resting behavior was completely different with the outdoor resting behavior
where M. annulifera had the highest peak of
resting activity at 2300 h. The resting behavior was similar with its biting
activity, indicating M. annulifera relatively
did the resting after biting activity in both condition (outdoor and indoor).
In case of number, the resting activity in outdoor condition was higher than
the number of indoor resting behavior, meaning M. annulifera
was categorized as the exophage species. However, the result was different with
the study reported by Kumar (1992) who reported M. annulifera
as the endophage species.
Figure 7 shows the resting forms
of M. indiana for 24 hours of collecting time.
The result showed that the outdoor resting activity started at 1800 h with the
highest peak at 1900 h. After the highest resting activity, the number of
resting mosquitoes decreased and relatively fluctuated until the next day. In
indoor condition, the resting time started 1800 h, which also become the
highest peak of resting time. The resting activity dropped after the high peak
and continuously fluctuated until the next day. The outdoor and indoor
resting activity was quite similar but having the different in quantity. The
number of resting M. indiana in outdoor
condition was found higher than the number of resting M. indiana
in indoor resting activity, indicating M. indiana
as the exophage species.
From the study of resting
behavior of most collected Mansonia spp., most
of mosquitoes had the similar rhythm with the biting activity, indicating the
biting activity was always followed by the resting activity before continuing
doing their activity. However, it was only a hypothetic theory based on the
rhythm of biting and resting activity.
Mosquitos density
Table 5 reveals that in Sedang village, the outdoor man hour density of M. uniformis was 10.43 mosquitos per
person-hour in which M. annulifera and M. indiana were 10.78 and 6.05 mosquito per person-hour,
respectively. On the other hand, the indoor man hour density of M. uniformis, M. annulifera,
M. indiana were 9.06, 8.08, and 4.75 mosquitos
per person-hours, respectively. It should be a concern because the potential
for filariasis transmission is very high. The result was different with the one
reported by Sabesan et al. (1991) where the average
of man hour density for M. annulifera, M. uniformis, and M. indiana
indoor were 3.29, 0.25, and 0.01, respectively.
Santoso et al. (2016) conducted a study
of Mansonia species in Jambi Province, Indonesia and
reported that the man hour density was below five (Santoso
et al. 2016). In this study, we found that outdoor and indoor MHD of Mansonia spp. have more than five which meant
that the potential for filariasis transmission was very high. It was supported
by the regulation of the Minister of Health of the Republic of Indonesia No. 50
of 2017 where the value of man hour density should be under five. In addition,
the high the man density was supported by the data of man biting rate (Table
6). The result showed that the highest man-biting rate was M. uniformis (156.67) followed by M. annulifera (151.67), and M. indiana
(86.83), which correlated with the biting activities of Mansonia
spp.
Dissection was performed on the
ovaries of mosquitos to find out whether the mosquitos had laid their eggs or
not. In Sedang village, the dissection was carried
out using 1,878 Mansonia spp. Table 7 explains
that 1,878 Mansonia spp. mosquitos had a
dissection in which 1,451 and 427 were parous and nulliparous, respectively.
The longevity was performed to see how long the mosquito life expectancy. To
obtain the longevity, the parity rates was calculated. The result showed that
the paruty rate of M. uniformis,
M. annulifera, and M. indiana
were 0,79, 0,72, and 0,81, respectively, indicating there are 79%, 72%, and
81% of these mosquitos have oviposited their eggs.
Based on the parity rate, the
population longevity of M. uniformis, M. annulifera, and M. indiana
was found to be 13.35 days, 9,21 days and 14,61 days, respectively. The
result found that Mansonia was ideal as the
host of filariasis transmission where the growth period of microfilariae in the
body of mosquitoes that become hosts ranges from 10–14 days. To be more
specific, Brugia species need 8–10
days, the Wuchereria species takes 10–14
days (Ministy Heath of Republic of Indonesia
2016). According to Gilles & Warrel (1993), the cycle of mosquitoes and the age are
obtained to support the development of the parasite cycle in the body of
mosquitoes. The number of longevity determined how long the host could transmit
the disease, when associated with the parasite life cycle. Observation of the
age of life was one of the most important factors in determining the
discrimination of vectors so that transmission can be detected somewhere (Mardiana 2009).
The PCR study was performed to
support the longevity and the potential of filariasis transmission. In Figure
10, there was a correct band size of Brugia
malayi which detected in I4 sample which come
from M. annulifera. There was no positive band
size of Brugia malayi
detected in the other sample, indicating only M. annulifera
potentially transmitted the filariasis. However, the result could not be a
final conclusion since the other Mansonia species
was potential as the host for filariasis transmission.
CONCLUSION
In conclusion, M. uniformis, M. annulifera, and M. indiana have the highest frequency, abundance, and
dominance. The biting activity and resting rhythm are available in 24 hours and
they also had a big parity rate and longevity. They eventually had the greatest
number of MHD and MBR, which could be contributed to the high rate of
filariasis transmission. M. annulifera was
confirmed as the potential filariasis vector based on PCR examination.
Table 1. The diversity of
mosquitoes in Sedang Village, Banyuasin Regency, South
Sumatera-Indonesia collected in the period of April 2017 to May 2018.
|
Species |
Number of collected mosquitoes |
% |
1 |
Mansonia uniformis |
1,835 |
23.20 |
2 |
Mansonia annulifera |
1,585 |
20.06 |
3 |
Mansonia indiana |
985 |
12.50 |
4 |
Mansonia bonneae |
30 |
0.40 |
5 |
Mansonia annulata |
9 |
0.11 |
6 |
Mansonia dives |
4 |
0.05 |
7 |
Culex gelidus |
795 |
10.06 |
8 |
Culex quinquifasciatus |
629 |
7.96 |
9 |
Culex tritaeniorhynchus |
211 |
2.67 |
10 |
Culex vishnui |
124 |
1.56 |
11 |
Culex sitiens |
46 |
0.58 |
12 |
Culex fuscocephalus |
23 |
0.29 |
13 |
Culex hutchinsoni |
10 |
0.12 |
14 |
Culex bitaeniorhyncus |
1 |
0.01 |
15 |
Culex pseudosinensi |
1 |
0.01 |
16 |
Culex nigropunctatus |
1 |
0.01 |
17 |
Culex infula |
1 |
0.01 |
18 |
Culex sinensis |
1 |
0.01 |
19 |
Aedes aegypti |
339 |
4.29 |
20 |
Aedes albopictus |
55 |
0.70 |
21 |
Aedes butleri |
30 |
0.40 |
22 |
Aedes pulchriventer |
11 |
0.14 |
23 |
Aedes albolineatus |
6 |
0.07 |
24 |
Aedes sp. |
5 |
0.06 |
25 |
Aedes lineatopennis |
3 |
0.04 |
26 |
Aedes anandelei |
1 |
0.01 |
27 |
Aedes poicilius |
1 |
0.01 |
28 |
Anopheles nigerrimus |
12 |
0.15 |
29 |
Anopheles separatus |
7 |
0.09 |
30 |
Anopheles barbirostris |
1 |
0.01 |
31 |
Coquillettidia crassipes |
5 |
0.06 |
32 |
Coquilettidia nigrosignata |
3 |
0.03 |
33 |
Topomyia sp. |
542 |
6.90 |
34 |
Armigeres subalbatus |
340 |
4.30 |
35 |
Tripteroides sp. |
235 |
2.97 |
36 |
Mimomyia sp. |
5 |
0.06 |
37 |
Malaya jacobsoni |
5 |
0.06 |
38 |
Uranataenia sp. |
2 |
0.02 |
39 |
Hodgesia sp. |
1 |
0.01 |
40 |
Uratonia longinistis |
1 |
|
|
Total |
7,901 |
100.00 |
Table 2. The diversity of Mansonia spp in Sedang Village, Banyuasin
Regency, South Sumatera, Indonesia.
Species |
Number of collected
mosquitoes |
Percentage (%) |
M. uniformis |
1,835 |
41.25 |
M. annulifera |
1,585 |
35.63 |
M. indiana |
985 |
22.14 |
M. bonneae |
30 |
0.7 |
M. annulata |
9 |
0.2 |
M. dives |
4 |
0.08 |
Totally |
4448 |
100 |
Table 3. Frequency, abundance,
and dominance of Mansonia spp. biting activity in outdoor
and indoor in Sedang Village.
Species |
Outdoor Frequency |
Indoor Frequency |
Outdoor Abundance |
Indoor abundance |
Outdoor dominance |
Indoor dominance |
M. uniformis |
0.50 |
0.42 |
37.90 |
41.15 |
19.06 |
17.51 |
M. annulifera |
0.44 |
0.42 |
39.18 |
36.72 |
17.40 |
15.63 |
M. indiana |
0.38 |
0.38 |
22.00 |
21.56 |
8.32 |
8.15 |
M. bonneae |
0.03 |
0.009 |
0.68 |
0.38 |
0.02 |
0.003 |
M. annulata |
0.003 |
0.003 |
0.15 |
0.09 |
0.0004 |
0.0003 |
M. dives |
0.50 |
0.42 |
0.07 |
0.09 |
0.04 |
0.04 |
Table 4. Frequency, abundance,
the dominance of Mansonia resting indoor and outdoor
in Sedang village.
Species |
Outdoor Frequency |
Indoor Frequency |
Outdoor abundance |
Indoor abundance |
Outdoor dominance |
Indoor dominance |
M. uniformis |
0.41 |
0.46 |
39.96 |
46.88 |
16.41 |
21.49 |
M. annulifera |
0.42 |
0.44 |
35.24 |
30.40 |
14.68 |
13.30 |
M. indiana |
0.34 |
0.36 |
23.52 |
21.57 |
7.98 |
7.83 |
M. bonneae |
0.02 |
0.03 |
0.79 |
0.86 |
0.02 |
0.03 |
M. annulata |
0.009 |
0.009 |
0.003 |
0.3 |
0.027 |
0.002 |
M. dives |
0.006 |
0.0 |
0.2 |
0.0 |
0.001 |
0.0 |
Table 5. The density of collected Mansonia
spp.
Species |
Outdoor biting |
Man hour density (MHD) |
Indoor biting |
Man hour density (MHD) |
M. uniformis |
503 |
10.43 |
437 |
9.06 |
M. annulifera |
520 |
10.78 |
390 |
8.08 |
M. indiana |
292 |
6.05 |
229 |
4.75 |
M. bonneae |
9 |
0.19 |
4 |
0.08 |
M. annulata |
2 |
0.04 |
1 |
0.04 |
M. dives |
1 |
0.02 |
1 |
0.04 |
Table 6. Man biting rate data.
Species |
Outdoor Biting |
Indoor Biting |
Total |
MBR |
M. uniformis |
503 |
437 |
940 |
156.67 |
M. annulifera |
520 |
390 |
910 |
151.67 |
M. indiana |
292 |
229 |
521 |
86.83 |
M. bonneae |
9 |
4 |
13 |
2.17 |
M. annulata |
2 |
1 |
3 |
0.50 |
M. dives |
1 |
1 |
2 |
0.33 |
Table 7. Parity rate and longevity.
Species |
Number of dissection |
Parous |
Nulliparous |
Parity rate |
Longevity (days) |
M. uniformis |
636 |
508 |
128 |
0.79 |
13.35 |
M. annulifera |
680 |
491 |
189 |
0.72 |
9.21 |
M. indiana |
544 |
443 |
101 |
0.81 |
14.61 |
M. bonneae |
9 |
3 |
6 |
0.33 |
2.7 |
M. annulata |
5 |
2 |
3 |
0.4 |
3.3 |
M. dives |
4 |
4 |
0 |
1 |
- |
For figures &
images - - click here
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