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Forensic Research & Criminology International Journal

Research Article Volume 11 Issue 4

Comparison between insects gathered on a death corpse from the study site and insects obtained by rearing larvae within the laboratory under natural environmental conditions 

Feugang Youmessi

Department of Animal Biology and Physiology, University of Yaounde I, Cameroon

Correspondence: Feugang Youmessi Francis Dupont, Department of Animal Biology and Physiology, University of Yaounde I, Cameroon

Received: October 19, 2023 | Published: November 3, 2023

Citation: Youmessi F. Comparison between insects gathered on a death corpse from the study site and insects obtained by rearing larvae within the laboratory under natural environmental conditions. Forensic Res Criminol Int J. 2023;11(4):126-132. DOI: 10.15406/frcij.2023.11.00381

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Abstract

Forensic entomology is the use of insect and others arthropods in solving crime. During this purpose, forensic entomologists use carrion insect communities to produce evidence in case of murder, suicide, neglect, accident or poaching, since they are natural witnesses of the crime scene.  This offers of insects as physical evidence during legal procedures are use worldwide except in Africa where the documentation of this domain is poor.   The present study was to compare the diversity of necrophagous insect gathered at the study site and that of the insect  obtain from the rearing of thier larvae in the laboratory under natural environmental conditions. Adult flies were identified to species level. Overall, 3414 adult flies were obtained both from the census on the field and from the rearing in the laboratory. These flies belong to 3 classes of insects namely, Insect, Arachnida and Myriapoda with 3343, 70 and 1 individual respectively, distributed amongst 9 orders, 30 families, 20 genus and 27 species.

Keywords: forensic entomology, necrophagous insect, larvae, Cameroon

Introduction

Nowadays, Forensic entomology or medico-legal entomology is one of the modern means of investigations essential for strengthening criminal justice systems.1,2 This discipline also named medico-criminal entomology deals with the use of results gathered from the study of insects and other arthropods collected on and around the crime scene in solving crime. The community of insects retrieved from a corpse or carcass is used in forensic investigations primarily to develop an estimate of when the person or animal died; a period commonly termed the post mortem interval (P.M.I.)3 which is the time lapse since death. During the progression of corpse decay, the microenvironment of the corpse will undergo change; simultaneously, the composition of the insect community will also undergo changes Hu Guoliang et al.,4,5 This decaying process varies in response to the effect of multiple influencing parameters such as biotic and abiotic factors. These biotic factors are mostly related to the cause and manner of death and the characteristics of the animal body such as body mass, age, gender, injuries, or medical treatments whereas the abiotic conditions consist of moisture, clothing, concealment, weather, hygrometry, insect activity, temperature and humidity.6–8 The two last factors are the most significant influencing the rate of decomposition.9

During criminal affairs, forensic entomologists use carrion insect communities to produce evidence in case of murder, suicide, neglect, accident or poaching,10 since they are natural agents of decomposition involved in nutrient recycling.11–13 They are also important in human and veterinary medicine as transmitters of pathogens and myasis agents (Rognes, 1991), and in forensic entomology as indicators of post mortem interval.1,9 Insects are also good promising candidates as animal feed ingredients, especially blow flies12 whose adult and larval stages can be used as animal food.14–17 Amongst the different ways in which insects are used, the outputs of carrion insect communities have been explored quite intensively worldwide except in Africa in general and particularly in Cameroon where only some few papers are available.9,18–20 Up to date, nothing has been written on the comparison between the necroentomofauna gathered at the study site and that of those emerging from the rearing of their larvae in the laboratory under normal atmospheric conditions.

To sidestep this lack, the present study was designed using ten carcasses of Rats Rattus norvegicus, Berkenhout, 1769 Var Wistar within the campus of the University of Yaounde 1. The purpose of this pilot paper is to emphasize the relationship between necrophagous insects collected on the field and their counterparts emerging from the rearing of their larvae in the laboratory under natural ambient air conditions and provide knowledge on corpse insect communities related to that of their larvae in the Central African Sub region. It has been proven that insects are the most diverse group of animals, estimated at over 5.5 million species worldwide,21 there is an immense population of unexplored or under-explored species that may bring new perspectives to science.14

Material and methods

Study site

The present study was carried out on the campus of the University of Yaounde I (11°33’01”E, 3°51’35”N) Cameroon. Yaounde is a city located in the heart of the Central African Sub-region, at about 250 KM from the Atlantic Ocean. The area is 304 KM2 with some valleys and mountains having between 700 and 1200m of altitude.22 The climate is equatorial and characterized by four distinct seasons: a short rainy season (April to June), a long rainy season (September to mid November), a long dry season (mid November to March) and a short dry season (July to August). The mean annual rainfall is 1600 mm and the average annual temperature fluctuates between 19°C to 33°C.23,24 The landscape of this part of the city is characterized by the presence of Elaeis guineensis (Arecaceae) and Musa sp. (Musaceae).

Animals and experimental setup

Rats9 where obtained from the Physiology laboratory of the faculty of science of the University of Yaoundé 1, alive and in very good health. Ten of them, each weighing about 210g were euthanized with carbondioxide, killed by slaughter according to ethical rules and immediately placed on top of a 10cm layer of sterilized soil put inside a rectangular plastic box (10cm x 20cm x 15cm).  The whole setup was then deposited inside a wooden cage (120cm x 120cm x 120cm) protected with a 5cm mesh to allow colonization of carcasses by insects, while preventing scavenger attacks.25 These carcasses were left to decay under natural environmental conditions up to the skeletonized stage.  Every day, the cage was visited three times (08:00GMT, 12:00GMT and 16:00GMT), for 20 minutes and carcasses examined for sampling purposes, during the first and second stages of decomposition i.e. from Day 1 to Day4 according to Wolff et al.26 Then, arthropod sampling was undertaken once daily at 12:00 GMT.

During carcass examination, flying insects were sampled simultaneously with the monitoring of environmental conditions. The insect communities were caught with the help of an insect hand held net and killed by vaporizing with 70% alcohol, then picked with flexible forceps to keep inside 70% alcohol within a plastic container for further identification. The carcass survey continued and when all the larvae migrated inside the soil beneath eight days after death, they were removed and placed on top of another layer of sterilized layer of soil as written above for the continuation of the experiment. The other soil together with these larvae was carried to the laboratory for rearing under natural environmental parameters.  All harvested necroentomofauna were identified to various levels of taxonomy using a binocular stereomicroscope and various dichotomic keys.19,27–30

Data analysis

The categorization of taxa was evaluated according to the modified formula of Dajoz31 where the rate of occurrence (C) of each taxa is: C= Ni/N*100 where Ni is the number of occurrence of a given taxa during the survey and N is the total number of all the individual census during the whole experiment. The results are analyzed as:  C > 25% = consistent species, 5% ≤ C ≤ 25% = accessories species and C < 5% = rare species.

Results

During the experimental time period, 3414 adult flies were obtained both from the census on the field and from the rearing in the laboratory within the natural ambient air conditions. These flies belong to 3 classes of insects namely, Insect, Arachnida and Myriapoda with 3343, 70 and 1individual respectively, distributed amongst 9 orders, 30 families,20 genus and 27 species (Table 1).

Classes

Orders

Families

Genus/Species

     

Hemipyrelliafernandica (Macquart, 1855)

     

Chrysomyasp. (Robineau-Desvoidy, 1830)

   

 Calliphoridae

Undeterminated

     

Luciliasp. (Robineau-Desvoidy, 1830)

     

Luciliacuprina (Wiedemann, 1830)

     

Chrysomyaputoria (Wiedemann, 1830)

     

Chrysomyaalbiceps (Wiedemann, 1819)

     

Chrysomyalaxifrons (Villeneuve, 1814)

     

Hemipyrelliasp. (Towsend, 1918)

   

Drosophilidae

Undeterminated

   

Heleomyzidae

 Undeterminated

   

Muscidae

Muscasp. (Linnaeus, 1758)

     

Ophyrasp. (Robineau-Desvoidy, 1830)

     

Atherigonasp. (Rondani, 1856)

     

Hydrotaeasp.(Robineau-Desvoidy, 1830)

   

Fanniidae

Undeterminated

 

 Diptera

Sepsidae

Sepsissp. (Fallén, 1810)

   

Phoridae

 Undeterminated

   

Anophelidae

 Undeterminated

   

Lauxanniidae

 Undeterminated

   

Sarcophagidae

Sarcophagaafrica(Wiedemann, 1824)

     

Sarcophagasp. (Meigen, 1826)

 

 

Staphylinidae

 Undeterminated

   

Silphidae

 Undeterminated

   

Histeridae

 Undeterminated

 

Coleoptera

Cleridae

 Undeterminated

   

Formicidae

Pheidolesp. (Wilson & Taylor, 1967)

     

Myrmicariaopaciventris (Emery, 1893)

     

Odontomachus troglodytes (Santschi, 1914)

     

Tetramoriumsp. (Santschi, 1924)

     

Cardiocondylaemeryi (Menozzi, 1930)

     

Tapinomaluteum (Emery, 1895)

     

Plagiolepisbrunni (Mayr, 1895)

     

Lepisiotasp. (Santschi, 1926)

   

Chalcididae

Undeterminated

   

Ponerinae

Odontomachussp.  (Smith, 1863)

   

Scelionidae

 Undeterminated

 

Hymenoptera

Braconidae

Paramesiussp. (Westwood, 1832)

   

Braconidae

Coelalysianigriceps(Szépligeti, 1911)

     

Undeterminated

   

Pteromalidae

Spalangiasp. (Latreille, 1805)

 

Dictyoptera

Blattidae

 Undeterminated

 Insecta

Hemiptera

Aphididae

Undeterminated

   

Undeterminated

 Undeterminated

 

Orthoptera

Gryllidae

Undeterminated

 

Diplopoda

Undeterminated

 Undeterminated

Myriapoda

Chilopoda

Chilopodae

Undeterminated

Arachnida

Araneida

Undeterminated

Undeterminated

Table 1 Synoptic table showing the overall number of individuals gathered both on the field and at the laboratory during the entire experiment

Adult flies collected on the field

2062 adult’s flies were gathered at the study site. The most abundant order consisted of Diptera with 1309 (63,48%) individuals, dominated by Calliphoridae with 648 flies(31,43%) (Table 2).Within Diptera, the family Calliphoridae was followed successively by Sepsidae and Muscidae with populations of 254 (12,32%) and 183 (8,87%), respectively.  This order was followed by the Hymenoptera families Formicidae and Chalcididae with 250 (12,12%) and 147 (7,13) respectively. Then came the Coleopterans with 136 (6,60%) individuals of Staphylinidae. These three orders comprised 1618 individuals representing 78,47% of the field collection. Some of the samples gathered from the field were identified up to the genus/species level. These ones are organized successively as follow: 254 (12,32%) flies of Sepsis (Fallén, 1810), 150 (7,27%) Chrysomya putoria (Wiedemann, 1830), 142 (6,89%) Chrysomya albiceps (Wiedemann, 1819), 132 (6,40%) Hemipyrellia fernandica (Macquart, 1855), 122 (5,92%) Lucilia (Robineau-Desvoidy, 1830) and 112 (5,43%) Ophyra (Robineau-Desvoidy, 1830).

Species

Field

Laboratory

Ni

%

Ni

%

Ni

%

Atherigona sp. (Rondani, 1856)

3

0,15

1

0,07

4

0,12

Cardiocondyla emeryi (Menozzi, 1930)

9

0,44

0

0,00

9

0,26

Chrysomya albiceps (Wiedemann, 1819)

142

6,89

101

7,47

243

7,12

Chrysomya laxifrons (Villeneuve, 1814)

14

0,68

3

0,22

17

0,50

Chrysomya putoria (Wiedemann, 1830)

150

7,27

107

7,91

257

7,53

Chrysomya sp. (R-D, 1830)

6

0,29

19

1,41

25

0,73

Hemipyrellia fernandica (Manquart, 1855)

132

6,40

221

16,35

353

10,34

Hemipyrellia sp. (Towsend, 1918)

0

0,00

22

1,63

22

0,64

Hydrotaea sp. (R-D, 1830)

0

0,00

36

2,66

36

1,05

Lepisiota sp. (Santschi, 1926)

23

1,12

0

0,00

23

0,67

Lucilia cuprina (Wiedemann, 1830)

9

0,44

0

0,00

9

0,26

Lucilia sp. (R-D, 1830)

122

5,92

35

2,59

157

4,60

Musca sp.(Linnaeus, 1758)

68

3,30

9

0,67

77

2,26

Myrmicaria opaciventris (Emery, 1893)

4

0,19

0

0,00

4

0,12

Odontomachus troglodytes (Santschi, 1914)

45

2,18

0

0,00

45

1,32

Ophyra sp. (R-D, 1830)

112

5,43

0

0,00

112

3,28

Paramesius sp. (Westwood, 1832)

6

0,29

0

0,00

6

0,18

Paratrechina sp. (Motschulsky, 1863)

13

0,63

0

0,00

13

0,38

Pheidole p.(Westwood, 1839)

95

4,61

0

0,00

95

2,78

Plagiolepis brunni (Mayr, 1895)

12

0,58

0

0,00

12

0,35

Sarcophaga africa (Wiedemann, 1824)

0

0,00

8

0,59

8

0,23

Sarcophaga inaequalis (Austein, 1909)

0

0,00

1

0,07

1

0,03

Sarcophaga sp. (Meigen, 1826)

0

0,00

5

0,37

5

0,15

Sepsis sp. (Fallén, 1010)

254

12,32

2

0,15

256

7,50

Tapinoma luteum (Emery, 1895)

16

0,78

0

0,00

16

0,47

Tetramorium sp. (Mayr, 1855)

33

1,60

0

0,00

33

0,97

Undetermined

794

38,51

782

57,84

1576

46,16

General Total

2062

100,00

1352

100,00

3414

100,00

Table 2 Descriptive statistics according to species and area of flies sampling
Legend: Ni=Abundance and %=Percentage.

Adult flies gathered from the larvae rearing at the laboratory

1352 were collected after the emergence of the adults flies from the rearing of the larvae in the laboratory under normal atmospheric conditions (Table 2). Coleopterans with 758 (56,07%) individuals represented the most abundant group with Dermestidae and Staphylinidae numbered respectively 697 (51,55%) and 50 (3,70%) specimens. Then, Diptera included 594 (43,93%) with 507 (37,50%) specimens of Calliphoridae and 46 (3,40%) specimens of Muscidae.  All the adults flies obtained in the laboratory belong to the above two orders only. The abundance of the emerged insects are organized as follow: 221 (16,35%) adult of Hemipyrellia fernandica (Macquart, 1855), 107 (7,91%) Chrysomya putoria (Wiedemann, 1830), 101 (7,47%) Chrysomya albiceps (Wiedemann, 1819), 36 (2,66%) Hydrotaea (R-D, 1830) and 35 (2,59%) Lucilia (R-D, 1830).

Adult flies sampled from the field and their counterparts from the rearing of larvae at the laboratory

The analysis of the entomofauna census on the field and their counterparts emerging from the rearing larvae in the laboratory looks slightly similar according to the variation of their abundance (Table 2). The most abundant specimens caught at the field was genus Sepsis (Fallén, 1810) with 254 (12,32%) individuals while Hemipyrellia fernandica (Macquart, 1855) were the most abundant on the field with 221 (16,35%) individuals. The second and the third highest number of insects collected at both sites were Chrysomya putoria (Wiedemann, 1830) containing 150 (7,27%) and 101 (7,91%) from the field and the laboratory, respectively. These flies were followed successively by Chrysomya albiceps (Wiedemann, 1819) hosted 142 (6,89%) and 101 (7,47%); Hemipyrellia fernandica (Macquart, 1855) with 132 (6,40%) and Hydrotaea [ 36 (2,66%)] came in the fourth position from the field and the laboratory respectively. The fifth position was occupied by Lucilia (R-D, 1830) at both sites with 122 (5,43%) and 35 (2,59%) respectively. 112 (5,43%) specimens of Ophyra (R-D, 1830) were caught on the field even though none of them emerged as imago within the laboratory.

The slight difference noted about the abundances maybe explained by the fact that some species are part of the necroentomofauna mainly only for feeding (e.g.: Sepsis sp., Ophyra sp., Pheidole sp., Musca sp. and Odontomachus troglodytes (Santschi, 1914) while some are using carcasses as food and reproduction ground (e.g.: Hemipyrellia fernandica (Macquart, 1855), Chrysomya putoria (Wiedemann, 1830), C. albiceps (Wiedemann, 1819) and Lucilia sp. (R-D, 1830). The data analysis illustrated that the most consistent (C > 25%) species belongs to the orders of Diptera and Coleoptera with 55,74% and 27,91% respectively making a total of 83,65% of the entomofauna counted during the experiment. The accessory species with occurrence (C) (5% ≤ C ≤ 25%) are made up of only Hymenoptera (11,98%) and the rare species are Araneida, Hemiptera, Diplopoda, Orthoptera, Dictyoptera and Chilopoda with 2,05%, 1,87%, 0,15%, 0,12% and 0,03 chronologically (Table 3).

 

Field

Laboratory

Orders

Ni

%

Ni

%

Total Ni

Total %

Araneida

70

3,39

0

0,00

70

2,05

Chilopoda

1

0,05

0

0,00

1

0,03

Coleoptera

195

9,46

758

56,07

953

27,91

Dictyoptera

4

0,19

0

0,00

4

0,12

Diplopoda

5

0,24

0

0,00

5

0,15

Diptera

1309

63,48

594

43,93

1903

55,74

Hemiptera

64

3,10

0

0,00

64

1,87

Hymenoptera

409

19,84

0

0,00

409

11,98

Orthoptera

5

0,24

0

0,00

5

0,15

General Total

2062

100,00

1352

100,00

3414

100,00

Table 3 Occurrences of different taxa gathered during the experimental period

Discussion

To the best of our knowledge, this study is the first published data worldwide, regarding the comparison between field necroentomofauna and their counterparts emerging from the rearing of larvae within the laboratory. The estimation of post mortem interval is a key aspect of forensic entomology given that it helps to solve criminal affairs during legal procedures in court. During our experiment, carcasses were evaluated every day for 20 minutes and after their migration, the larvae where carried to the laboratory for rearing, similar to the methods adopted by Pittner et al.32 during their field study to evaluate PMI estimation methods for advanced decomposition stages at forensic research filed in northern Germany,9,18–20 while conducting forensic entomology research in Yaounde, Cameroon.

In accordance with Matuszewski et al.,33 the data on abundances of various insects in necroentomofauna assemblages in the present study site showed the domination of the orders Diptera and Coleoptera. These two taxa were sampled from the field and from the individuals emerging from the rearing in the laboratory showing that although the necroentomofauna involved in the carcass decay varied between biogeographical regions, ecological guilds are consistent and functioned in a very consistent way worldwide as emphasized by the above authors.

Order diptera

The order Diptera was the most abundant and diverse taxa and the species sampled were distributed amongst the families Calliphoridae, Muscidae, Sarcophagidae, Anophelidae, Drossophilidae, Fanniidae, Heleomyzidae, Lauxanniidae, Micropezidae, Phoridae, Sciaridae and Sepsidae. These findings are in accordance with the result obtained by Dao et al.,34–43 This similarity can be explained by the same/unique behavioral habits of diet and reproduction noted on necroentomofauna around the world independent of areas. The diversity within family mainly the Calliphoridae was Hemipyrellia fernandica (Macquart, 1855), Chrysomya putoria (Wiedemann, 1830), Chrysomya albiceps (Wiedemann, 1819), Chrysomya sp. (Robineau-Desvoidy, 1830), Lucilia cuprina (Wiedemann, 1830), Lucilia sp. (Robineau-Desvoidy, 1830), Chrysomya laxifrons (Villeneuve, 1814) and Hemipyrellia sp (Towsend, 1928). This high diversity looks like that of Shiuh-Feng Shiao and Ta-ChuanYeh (2008), Silahuddin et al. (2015) and can be the consequence of the high egg-laying behavior of the females firstly and the well-developed sensorial and olfactive organs located within their antennas. 

Nevertheless the families gathered during our experiment look like those obtained in many countries, the species diversity varied within families in countries like Côte d’Ivoire, Egypt, Algeria, Namibia and South Africa where these researchers sampled the species Calliphora vicina, C. vomitoria, Chrysomya marginalis, C. megacephala, C. rififacies, Protophormia terranovae, Lucila Caesar, Fannia caricularis, Sarcophaga carnaria, S. haemorrhoidalis, S. tibalis, S. inzi, S. exuberans, Liosarcophaga emmrichiana, Hermetia illucens, Piophila casei, Hydrotaea sinigera, Haematobia minuta, Chrysomya chloropyga, Drosophilia spp, Musca domestica. This results are in line with those of Villet10,44 in South Africa and can be due to the fact that organisms’ geographical distributions will rarely coincide over the spatial scale of a continent like Africa where abiotic parameters vary significantly within the Sub-region and even within a country; even if necroentomophagous insects such as blowflies are mobile. This is apparently largely due to differences in physiological tolerance to climatic variables such as relative humidity and temperature.

Order coleoptera

The order Coleoptera was the second most abundant taxa and the species sampled belong to the following families: Cleridae, Histeridae, Silphidae and Staphylinidae contrary to some studies where in addition to the above families, this order was also composed of Nitidulidae, Scarabaeidae, Catopidae, Ptinidae, Trogiidae and Carabidae. This variation can be the consequence of the permanent amelioration of faunistic inventory sampling methods during experiments with time. This idea is supported by Baz et al.,45 Gotelli et al.,46 Woodcock et al.,47 and Tews et al.48 who highlight that faunistic inventory is generally incomplete due to the fact that the number of inventoried species continues increasing with sampling efforts (1). It can also be the result of the study areas with proper climatic parameters since the above authors set up their research where temperature oscillated from 3,3 to 43°C and total rainfall of 451 to 521 mm (2) and finally the type of insect trapping substrat as they used carcasses of Pig (Sus scrofa domesticus).49

Other arthropods

In addition to the taxa mentioned above, carcasses were also colonized by other arthropods namely Bostrichidae, Phoridae, Ptiliidae, Sarcophagidae, Sciaridae and Sepsidae. Surprisingly, most of them were absent from the field specimens but only recorded from the adult flies emerging from the rearing within the laboratory. This output which is in accordance with the results of Maisonhaute and Forbes (2020) can be due to interspecific competition which only allowed the above mentioned families time to lay eggs and quickly escape from the carcasses avoiding being eaten by predators. Maybe some species mainly dry eaters such as Coleopterans first visited the carcasses for egg laying to procreate before coming later for feeding. This may be the reason why they were absent from the field species list and only appeared after laboratory larvae rearing even thought their abundance was low as registered by the op.cit authors.50

Overall, the main types of the insects assessed on cadaver during this research have also been sampled in Africa.9,10,18–20,33,35,36,39,41,43,44,51–63 This parallelism of the results maybe a consequence of the cosmopolitan, easy adaptation to various biotopes and abiotic determinants that govern the development of various necrophagous flies.

Conclusion

The present study maybe amongst the first published data on the comparison between field necroentomofauna and its counterparts emerging from the rearing of their larvae within the laboratory under natural environmental conditions. The outcome of this work illustrated the overall diversity of this specific type of entomofauna, with the collection of 2062 insects from the field and 1352 emerging from larvae reared in the laboratory making a total of 3414 flies distributed amongst 30 families, 20 genus and 27 species. Nevertheless, this research work has only been performed one time at one location within a unique habitat/ecosystem in Cameroon, the results are similar to those obtained in other countries with differences due to biotic and abiotic variations within species and location/study sites. This antagonism observation confirms the importance/emergence of conducting local studies and replicates to maximize information’s on necroentomofauna for the wellbeing of future investigations by researchers, lawyers, law officers, law enforcement agents, and criminal investigators. It also provides a base line for students with respect to the use forensic entomology to elucidate various types of crime within the city of Yaounde.

Acknowledgments

None.

Conflicts of interest

The author declares there is no conflict of interest.

References

  1. Gennard D. Forensic entomology: an introduction. Wiley Chichester, UK. 2007. p. 224.
  2. Dekeirsschieter J. Etude des odeurs emises par des carcasses de Porc (Sus srofa domesticus L.) en décomposition et suivi de la colonisation post mortempar les insectes nécrophages. Mémoire de fin d’études. Faculté universitaire des Sciences agronomiques de Gembloux. 2007. p. 104.
  3. Smith KGV. A manual of forensic entomology. British Museum (Natural History), London, 1986. p. 205.
  4. Byrd JH, Castner JL. Forensic Entomology. The utility of Arthropods in legal investigations. 2nd edn. CRC, London. 2009.
  5. Amendt J, Goff M L, Campobasso CP, et al. Current concepts in forensic entomology. Springer Belin. 2010.
  6. Zhou C, Byard RW. Factors and processes causing accelerated decomposition in human cadavers- an overview. J Forensic Legal Med. 2011;18:6–9.
  7. Vass AA. Odor mortis. Forensic Sci Int. 2012;222:234–241.
  8. Vass AA, Barshick SA, Sega G. Decomposition chemistry of human remains: a new methodology for determining the post mortem interval. J Forensic Sci. 2002;47(3):542–553.
  9. Feugang Youmessi FD, Nwane PB, Djieto-lordon C, et al. Blowflies reared in laboratory conditions from maggots collected on Rat (Rattus norvegicus Berkenhout, 1769, var Wistar) carrions in Yaoundé (Cameroon, Central Africa). Asian Journal of Biology. 2021;12(2):33–43.
  10. Villet MH. African Carrion Ecosystems and their Insect Communities in Relation to Forensic Entomology. Pest Technology. 2011;5(1):1–15.
  11. Prado e Castro C, Serrano A, Martins da Silva P, et al. Carrion flies of forensic interest: a study of seasonal community composition and succession in Lisbon, Portugal. Medical and veterinary entomology. 2012;26(4):417–431.
  12. Prado e Castro C, Szpila K, Martínez-Sánchez A, et al. The blow flies of the Madeira Archipelago: species diversity, distribution and identification (Diptera:  Calliphoridae). Zookeys. 2016;634:101–123.
  13. Khoobdel M, Akbarzadeh K, Jafari H, et al. Diversity and abundance of medically-important flies in the Iranian Triple Islands; the Greater Tunb, Lesser Tund and Abu-Musa. Iranian Journal Of Military Medicine. 2013;14(4):261–270.
  14. Prado e Castro, Ameixa OMCC. Blow flies (Diptera: Calliphoridae) promising candidates as animal feed ingredients. Journal of Insects as food and feed. 2021;7(7):1065–1076.
  15. Bbosa T, Ndagire CT, Mukisa IM, et al. Nutritional characteristics of selected insects in Uganda for use as alternative protein sources in fodd and feed. Journal of Insect Science. 2019;19(6):23–30.
  16. Parry NJ, Pieterse E, Weldon CW. Stocking rate and organic waste type affect development of three Chrysomya species and Lucilia sericata (Diptera: Calliphoridae): Implications for bioconservation. Journal of applied entomology. 2020;144:94–108.
  17. Rabani V, Cheatsazan H, Davani S. Proteomics and lipidomics of black soldier fly (Diptera: Stratiomyidae) and blow fly (Diptera: Calliphoridae) larvae. Journal of insect science. 2019;19(9):29–36.
  18. Feugang Youmessi FD, Bilong Bilong CF, Cherix D, et al. Biodiversity study of arthropods collected on rat carrion in Yaounde, Cameroon: first study on forensic entomology in Central Africa. International Journal of Biosciences. 2012;2(1):1–8.
  19. Feugang Youmessi FD, De Coninck E, Hubrecht F, et al. First records on five species of Calliphoridae (Diptera) reared from maggot collected on rat carrions corpse during a forensic entomology experiment in the campus of the University of Yaounde I-Cameroon. International Journal of Biosciences. 2012;2(3):75–80.
  20. Braet Y, Achterberg Cornelis Van, Feugang Youmessi FD. Coelalysia nigriceps (Szépligeti, 1911) reared during a forensic study in Cameroon, with remarks on synonymy and biology (Hymenoptera, Braconidae, Alysiinae). Bulletin de la Société entomologique de France. 2012;117(3):381–389.
  21. Stork NE. How many species of insects and other terrestrial arthropods are there on Earth? Annual review of entomology. 2018;63:31–45.
  22. Nguegang AP. L’agriculture urbaine camerounaise. Au-delà des procès, un modèle sociocultural à intégrer dans l’aménagement urbain. Geo carrefour. 2008;85–93.
  23. Suchel F. G. Les régions climatiques du Cameroun : les climats du Cameroun. Thèse de Doctorat d’Etat. Université Saint Etienne. France. 1988;4:1188.
  24. Kengne Fodouop, Atangana P. Une diversité du milieu biophysique exceptionnelle In le Cameroun: Autopsie d’une exception plurielle en Afrique, Kengne Fodouop (ed) – L’Harmatan. 2010;25–44.
  25. Sukontason K, Sukontason KL, Piangjai S, et al. Survey of forensically-relevant fly species in hiang Mai, northern Thailand. Journal of Vector Ecology. 2003;28(1):135–138.
  26. Wolff M, Uribe A, Ortiz A, et al. A preliminary study of forensic entomology in Medellin, Colombia. Forensic Science International. 2001;120(1–2):53–59.
  27. Szpila K. Key of European and Mediterranean blowflies (Diptera: Calliphoridae) of forensic importance adult flies. 2009;1–18.
  28. Whitworth T. Keys to the genera and species of blowflies (Diptera: Calliphoridae) of a West Indies and description of a new species of Lucilia (Robineau-Desvoidy). Zootaxa. 2010;2663:1–35.
  29. Irish S, Lindsay T, Wyatt N. Key to adult of Afrotropical species of the genus Chrysomya (Robineau-Desvoidy) (Diptera-Calliphoridae). African Entomology. 2014;22(2):297–306.
  30. Rochefort S, Marjolaine Giroux, Jade Savage, et al. Key to forensically important Piophilidae (Diptera) in the Neartic Region. Canadian Journal of Arthropod Identification. 2015;27(1):37.
  31. Dajoz R. Les notions de biocénoses et d’écosystème In Précis d’écologie. 5ème edition, Dunnod. 1985;248–276.
  32. Pittner Stefan, Bugelli Valentina, Weitgasser Katharina, et al. A field study to evaluate PMI estimation methods for advanced decomposition stages. International Journal of Legal medicine. 2020;134(4):1361–1373.
  33. Matuszewski S, Bajerlein D, Konwerski S, et al. Insect succession and carrion decomposition in selected forests in Central Europe. Part 2: Composition and residency patterns of carrion fauna. Foernsic science international. 2010;195:42–51.
  34. Dao Hassane, Aboua LR Nondenot, Koffi Alexandre F. Influence of seasons on the process of colonization by insects of Pigs Corpses exposed to the Open Air in Sub-Sudanese Zone of Côte d’Ivoire. International Journal of Science and Research. 2018;8(4):1822–1828.
  35. Dao Hassane, Aboua Louis R Nondenot, Koffi Alexandre F. Influence of the ecological zone on the necrophagous insects’ activities involved in the process of decomposition of Pigs Carcasses (Sus scrofa domesticus L.) exposed to the open air in the Sub-sudanese zone of Côte d’Ivoire. International Journal of entomology Research. 2018;3(5):07–16.
  36. Franklin KA, Nondenot ALR, Hassane D, et al. Process of colonization by necrophagous insects of a Pig Corpse (susscrofa domesticus L.) exposed at open air, in the Southern Forest Zone of Côte d’Ivoire. International Journal of Current Research and Academic Review. 2017;5(7):103–114.
  37. Heo CC, Marwi MA, Salleh AFM, et al. A preliminary studies of insect succession on a pig carcass in a palm oil plantation in Malaysia. Trop Biomed. 2007;24(2):23–27.
  38. Carvalho LML, Linhares AX. Seasonality of insect succession and pig carcass decomposition in a natural forest area in southeastern Brazil. J Forensic Sci. 2001;4693):604–608.
  39. Odo PE, Iloba BN. Forensic entomology: an inventory of arthropods collected on the decomposing pig carrions during the dry season in Warri, Southern Nigeria. International research journal of science and technology. 2020;1(4):277–285.
  40. Buenaventura E, Lloyd M, Perilla López JM, et al. Protein-encoding ultraconserved elements provide a new phylogenomic perspective of Oestroidaflies (Diptera: Calyptritae). Systematic entomology. 2020;46:5–27.
  41. Sebastião M, Prado e Castro C. A preliminary study of carrion insects and their succession in Luanda, Angola. Journal of medical entomology. 2018;20(10):1–6.
  42. Feugang Youmessi FD, Djieto lordon C, Ateba Awona JC. Congrès International sur la Diversité Biologique des Invertébrés en Milieux Agricoles et Forestiers. Acte Publié: Recherche des indicateurs entomologiques de datation des cadavres : cas du rat Rattus rattus (Linnaeus, 1768 var wistar) à Yaoundé, Cameroun. 2008.
  43. Feugang Youmessi FD. Etudes des indicateurs entomologiques utilisables lors des enquêtes criminelles: cas des Arthropodes de Rattus norvegicus (Berkenhout, 1769) Muridé souche Wistar à Yaoundé. Thèse de Doctorat Ph/D, Université de Yaoundé 1, Cameroun. 2014.
  44. Richards CS, Williams KA, Villet MH. Predicting geographic distribution of seven species (Diptera: Calliphoridae) in South Africa. African Entomology. 2009;17:170–182.
  45. Baz Arturo, Cifrin Blanca, Vega Daniel Martin. Patterns of diversity and abundance of carrion insect assemblages in the Natural Park “Hoces del Río Riaza” (Central Spain). Journal of Insect Science. 2014;14(162):1–10.
  46. Gotelli NJ, Colwell RK. Quantifying biodiversity: procedures and pitfalls in the measurement and comparison of species richness. Ecol Lett. 2001;4:379–391.
  47. Woodcock BA, Watt AD, Leather SR. Aggregation, habitat quality and coexistence: a case study on carrion fly communities in slug cadavers. J Anim Ecol. 2002;71:131–140.
  48. Tews J, Brose U, Grimm V, et al. Animal species diversity driven by habitat heterogeneity/diversity: the importance of keystone structures. J Biogeogr. 2002;31(1):79–92.
  49. Moretti Thiago de Carvalho, Ribeiro Odair Bendito, Thyssen Patrícia Jacqueline, et al. Insects on decomposing carcasses of small rodents in a secondary forest in Southeastern Brazil. I. 2008;105(4):691–696.
  50. Byrd JH, Tomberlin JK. Insects of forensic importance In: Byrd J. H., Tomberlin J. K., editors. Forensic entomology: the utility of arthropods in legal investigations. Third edition Boca Raton (FL): CRC Press, Taylor & Francis; 2020. p.15–62.
  51. Farah F. Contribution à l’étude de la colonisation préférentielle d’un cadavre animal par les insectes nécrophages. Mémoire. Université de cocody, UFR Biosciences. Abidjan, Côte d’Ivoire. 2010. p. 38.
  52. Matuzewski szymon, Hall Martin JR, Moreau Gaétan, et al. Pigs Vs People: the use of pigs as analogues for humans in forensic entomology and taphonomy research. International journal of legal medicine. 2019;134(2):793–810.
  53. Caballero U, Jorge L, n-Corte L. Beetle succession and diversity between clothed sun-exposed and shaded pig carrion in tropical dry forest Landscape in Southern Mexico. Forensic science international. 2014;245:143–150.
  54. Payne JA. A summer carrion study of the baby pig (Sus scrofa Linnaeus). Ecology. 1965;46(5):592–602.
  55. Payne JA, King EW, Beinhart G. Arthropod succession and decomposition of buried pigs. Nature. 1968;219(5159):1180–1181.
  56. Connor M, Baigent C, Hansen ES. Testing the use of pigs as human proxies in decomposite studies. J forensic Sci. 2018;63(5):1350–1355.
  57. Hu G, Wang M, Wang Y, et al. Development of Necrobia rufipes (De Geer, 1775) (Coleoptera: Cleridae) under constant temperatures and its implication in forensic entomology. Forensic Science International. 2020;311:1–14.
  58. Maisonhaute Julie-Éléonore, Forbes Shari L. Decomposition process and arthropod succession on pig carcasses in Quebec (Canada). Canadian society of forensic science journal. 2009;54(1):1–26.
  59. Da silva Âz, Hoffmeister CH, Anyos VA, et al. Necrophagous Diptera associated with wild animal carcasses in Southern Brazil. Revista Brasileira de Entomologia. 2014;58(4):337–342.
  60. Manuel Sebastão, Prado e Castro Catarina. A preliminary study of carrion insects and their succession in Luanda, Angola. Journal of medical entomology. 2018;56(2):378–383.
  61. Silahuddin SA, Baha Latif, Hiromu Kurahashi, et al. The importance of habitat in the ecology of decomposition on Rabbit Carcasses in Malaysia: Implications in forensic entomology. Journal of Med Entomol. 2015;52(1):9–23.
  62. Rognes K. Blowflies. (Diptera, Calliphoridae) of Fennoscandia and Denmark. Scandinavian Science Press. 1991. p. 272. 
  63. Chiuh Feng Shiao, Ta-chuanYeh. Larval competition of Chrysomya megacephala and Chrysomya rufifacies (Diptera: Calliphoridae): behavior and ecological studies of two blow fly species of forensic significance. Journal of Medical Entomology. 2008;45(4):785–799.
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