Kittikhun Moophayak1, Tunwadee Klong-Klaew2, Kom Sukontason2, Hiromu Kurahashi3, Jeffery K Tomberlin4, Kabkaew L Sukontason2. 1. Mahidol University Nakhon Sawan Campus, Nakhon SawanThailand, Mahidol University Nakhon Sawan Campus, Nakhon Sawan, Thailand. 2. Department of Parasitology, Faculty of Medicine, Chiang Mai University, Chiang MaiThailand, Department of Parasitology, Faculty of Medicine, Chiang Mai University, Chiang Mai, Thailand. 3. Department of Medical Entomology, National Institute of Infectious Diseases, Tokyo, Japan, Department of Medical Entomology, National Institute of Infectious Diseases, Tokyo, Japan. 4. Department of Entomology, Texas A&M University, College Station, Texas, USA.
Abstract
Distribution and occurrence of blow flies of forensic importance was performed during 2007 and 2008 in Chiang Mai and Lampang Provinces, northern Thailand. Surveys were conducted in forested areas for 30 minutes using a sweep net to collected flies attracted to a bait. A total of 2,115 blow flies belonging to six genera and 14 species were collected; Chrysomya megacephala (Fabricius) (44.7%), C. pinguis (Walker) (15.1%), C. chani Kurahashi (9.3%), C. thanomthini Kurahashi & Tumrasvin (0.3%); Achoetandrus rufifacies (Macquart) (10.5%), A. villeneuvi (Patton) (2.2%); Lucilia papuensis Macquart (2.2%), L. porphyrina (Walker) (12.4%), L. sinensis Aubertin (0.7%); Hemipyrellia ligurriens (Wiedemann) (1.3%), H. pulchra (Wiedemann) (0.1%); Hypopygiopsis infumata (Bigot) (0.6%), Hy. tumrasvini Kurahashi (0.2%) and Ceylonomyia nigripes Aubertin (0.4%). Among them, C. megacephala was the predominant species collected, particularly in the summer. The species likely to prevail in highland areas are C. pinguis, C. thanomthini, Hy. tumrasvini, L. papuensis and L. porphyrina.
Distribution and occurrence of blow flies of forensic importance was performed during 2007 and 2008 in Chiang Mai and Lampang Provinces, northern Thailand. Surveys were conducted in forested areas for 30 minutes using a sweep net to collected flies attracted to a bait. A total of 2,115 blow flies belonging to six genera and 14 species were collected; Chrysomya megacephala (Fabricius) (44.7%), C. pinguis (Walker) (15.1%), C. chani Kurahashi (9.3%), C. thanomthini Kurahashi & Tumrasvin (0.3%); Achoetandrus rufifacies (Macquart) (10.5%), A. villeneuvi (Patton) (2.2%); Lucilia papuensis Macquart (2.2%), L. porphyrina (Walker) (12.4%), L. sinensis Aubertin (0.7%); Hemipyrellia ligurriens (Wiedemann) (1.3%), H. pulchra (Wiedemann) (0.1%); Hypopygiopsis infumata (Bigot) (0.6%), Hy. tumrasvini Kurahashi (0.2%) and Ceylonomyia nigripes Aubertin (0.4%). Among them, C. megacephala was the predominant species collected, particularly in the summer. The species likely to prevail in highland areas are C. pinguis, C. thanomthini, Hy. tumrasvini, L. papuensis and L. porphyrina.
Blow flies (Diptera: Calliphoaridae) represent a key group of insects used as
entomological evidence in forensic investigations throughout the world including, but not
limited to, North America[1,5,6], Europe [2] and Asia[10,13]. A review of forensic entomology cases occurring in northern Thailand between 2000
and 2006 was conducted[13]. For 30 cases, 30 cadavers from various places of death (e.g.,
forested, suburban and urban areas) were investigated, with forested areas being the most
common places of death. However, currently, little is known about the environmental factors
regulating the distribution of blow flies, particularly those of forensic importance, such
as altitude. Up until now, studies of carrion-frequenting blow flies have been limited in Thailand[3,11].This study was conducted to elucidate species composition of blow flies in
northern Thailand and determine whether blow fly species distribution could be related to
altitude activity. This information will provide a database on blow flies from a specific
location in northern Thailand, particularly in shaded forested areas, where deaths occur
most commonly. Such information could prove vital when determining whether remains have
been moved between regions.The study periods were July 2007 for the rainy season, December 2007 for the
winter and March 2008 for the summer. Adult fly collections were performed in the forested
areas of Chiang Mai and Lampang provinces in northern Thailand. Such areas comprised of
mixed deciduous forest. Five sites were selected for each period. Four sites were selected
from Chiang Mai, i.e., Huey Tueng Tao reservoir (Mueang district);
Siridhon observatory at Doi Suthep-Pui Mt. (Mueang district); Headquarters at Doi
Suthep-Pui Mt. (Mueang district); and Doi Nang Kaew (Doi Saket district). One site was
selected from a mountainous area in Lampang province (Doi Khun Tan, Mae Ta district). Table 1 and Figures
1 and 2 display the collection sites for
assessing the distribution of carrion blow flies.
Table 1
Collection sites of carrion blow flies in northern Thailand during 2007 and
2008
Altitude (asl)
Site
Location (District, Province)
Latitude (North)
Longtidute (East)
300-450 m
A
Huey Tueng Tao (Mueang, Chiang
Mai)
18° 51′ 52″
98° 56′ 16″
B
Samoeng-Hang Dong Rd. (Hang Dong,
Chiang Mai)
18° 45′ 14″
98° 52′ 54″
451-600 m
C
Doi Khun Tarn (Mae Ta, Lampang)
18° 23′ 31″
99° 12′ 55″
751-900 m
D
Sirindhorn observatory (Mueang, Chiang
Mai)
18° 47′ 19″
98° 55′ 17″
E
Headquaters Suthep-Pui (Mueang, Chiang
Mai)
18° 48′ 40″
98° 55′ 00″
901-1,050 m
F
Doi Nang Kaew (Doi Saket, Chiang
Mai)
19° 03′ 46″
99° 22′ 37″
Fig. 1
Carrion blow fly collection sites in northern Thailand. A (Huey Tueng Tao,
Mueang, Chiang Mai); B (Samoeng-Hang Dong Rd., Hang Dong, Chiang Mai) at 300-450
m; C (Doi Khun Tarn, Mae Ta, Lampang) at 451-600 m; D (Sirindhorn observatory,
Mueang, Chiang Mai); E (Headquarters Suthep-Pui, Mueang, Chiang Mai) at 751-900 m;
F (Doi Nang Kaew, Doi Saket, Chiang Mai) at 901-1,050 m.
Fig. 2
General topography of the blow fly collections in Northern Thailand. Upper
display of site C in Fig. 1 (Doi Khun Tarn,
Mae Ta, Lampang) at 451-600 m; with lower display of site F in Fig. 1 (Doi Nang Kaew, Doi Saket, Chiang Mai)
at 901-1,050 m.
Adult flies attracted to baited meat were caught with a sweep net at different
times of the day between 10.00 a.m. and 3.00 p.m., based on the flight activity and feeding
time of flies in this group (HK, personal observation). The one-day tainted beef (500 g
placed on a plastic plate) was used as bait, which was placed on the ground. The altitudes
were coordinated using a handheld e-Trex® Garmin GPS. The collection period was
performed in 30 min. The captured flies were transferred to a transparent jar containing
ethyl acetate. The dead flies were then transferred to a transparent tube for
identification in the laboratory of the Department of Parasitology, Faculty of Medicine,
Chiang Mai University. All flies collected were pinned individually, and subsequently
identified from external morphology using the key of KURAHASHI et al.
[7] and the aid of a binocular microscope.A total of 2,115 carrion blow flies belonging to 14 species of six genera were
collected in this study. They were Chrysomya chani Kurahashi, C.
megacephala (Fabricius), C. pinguis (Walker), C.
thanomthini Kurahashi & Tumrasvin; Ceylonomyia nigripes
Aubertin; Achoetandrus rufifacies (Macquart), A.
villeneuvi (Patton); Hemipyrellia ligurriens (Wiedemann),
H. pulchra (Wiedemann); Hypopygiopsis infumata
(Bigot), Hy. tumrasvini Kurahashi; Lucilia papuensis
Macquart, L. porphyrina (Walker) and L. sinensis
Aubertin. Among them, C. megacephala was the predominant species
collected, particularly in the summer (Table 2)
which is similar to results found in previous investigations such as those in Chiang Mai[12,14], Phitsanulok in the north[3], and Ubon Ratchathani in the northeastern region of Thailand[4]. Approximately 945 of this fly species were attracted to the bait after its
placement. Their frequency of occurrence was consistent throughout the season with its
populations peaking during the summer, as previously reported in Thailand[12].
Table 2
Species composition of blow flies collected in northern Thailand during 2007
and 2008
Numbers in the yellow line represent summer collection (March 2008), those in
the blue line represent rainy season collection (July 2007) and those in the
orange line represent winter season collection (December 2007).
Numbers in the yellow line represent summer collection (March 2008), those in
the blue line represent rainy season collection (July 2007) and those in the
orange line represent winter season collection (December 2007).Data from this study indicate an altitude of distribution for each blow fly
species in mixed deciduous forests (e.g., Huey Tueng Tao reservoir, Doi
Suthep-Pui Mt., Doi Nang Kaew and Doi Khun Tan). On the basis of restricted distribution at
various altitudes, some species, such as C. pinguis, C. thanomthini, Hy.
tumrasvini, L. papuensis, and L. porphyrina are likely to
prevail in highland areas. This observation correlates with data from previous
investigations conducted in southeast Asian countries, e.g., Thailand,
Malaysia, Singapore, Cambodia, Laos, Vietnam, and the Philippines[3,7-9]. Interestingly, C. megacephala is widespread as it was commonly
collected from lowland to highland areas. A previous study revealed that C.
megacephala appears to spread up to the highest peak of Inthanon mountain in
Chiang Mai province (2,667 meters above sea level) (KL Sukontason, unpublished data),
suggesting strong adaptation to a man-made environment at various altitudes from lowland to
highland fauna (Fig. 3).
Fig. 3
Altitudinal distribution of carrion blow flies. Data gathered from Thailand
[this study, recent survey in 2013 and TUMRASVIN et al.
[14]], Malaysia and Singapore[7], Cambodia, Laos and Vietnam[8] and the Philippines[9]. Abbreviations: Ar, Achoetandrus rufifacies; Av,
A. villeneuvi; Cb, Chrysomya bezziana; Cc,
Chrysomya chani; Cm, Chrysomya megacephala;
Cp, Chrysomya pinguis; Ct, Chrysomya
thanomthini; Cn, Ceylonomyia nigripes; Hl,
Hemipyrellia ligurriens; Hp, Hemipyrellia
pulchra; Hyi, Hypopygiopsis infumata; Hyt,
Hypopygiopsis tumrasvini; Lc, Lucilia
cuprina; Lpa, Lucilia papuensis; Lpo, Lucilia
porphyrina; Ls, Lucilia sinensis.
On the other hand, no specimen of Lucilia cuprina (Wiedemann),
which is another forensically important blow fly, was captured in this study. A possible
explanation for this may be the tendency of this species to prevail more in lowland and
residential areas, which were not included in this study. L. cuprina was
collected in and around human habitations, such as restaurants, garbage piles, school
cafeterias and paddy fields in the urbanized areas of Ubon Ratchathani[4], as similarly observed in Phitsanulok province[3]. However, a study conducted by TUMRASVIN et al.
[14] in 1978 managed to collect this species at high altitudes up to 1,400 meter, but in
very low numbers. It should be noted that the altitudinal distribution of fly fauna varies,
based on seasonal changes, even in northern Thailand[14].In conclusion, the data obtained from this study provides species composition
of forensically important blow flies as related to altitude. Based on the fact that several
synanthropic species are present at a wide range of altitudes, their application for
explaining the re-location of corpses is limited, especially when the immature specimens of
these flies are found to be associated. However, in the case of some feral species having
unique foci of altitude, such data are crucial for detecting movement of corpses
post-mortem, particularly when moved from a high altitude in forested areas to lowland
residential areas.
Authors: S Lertthamnongtham; K L Sukontason; K Sukontason; S Piangjai; W Choochote; R C Vogtsberger; J K Olson Journal: Ann Trop Med Parasitol Date: 2003-01