International Journal of
Biodiversity and Conservation

  • Abbreviation: Int. J. Biodivers. Conserv.
  • Language: English
  • ISSN: 2141-243X
  • DOI: 10.5897/IJBC
  • Start Year: 2009
  • Published Articles: 678

Full Length Research Paper

Efficiencies of three insect collection methods in Lamto, Côte d’Ivoire

Dohouonan Diabaté
  • Dohouonan Diabaté
  • Département Agronomie et Foresterie, Université de Man, UFR Ingénierie Agronomique Forestière et Environnementale, BP 20 Man, Côte d’Ivoire.
  • Google Scholar
Yao Tano
  • Yao Tano
  • Université Nangui Abrogoua, 02 BP 801 Abidjan 02, (225) Côte d’Ivoire.
  • Google Scholar


  •  Received: 03 May 2020
  •  Accepted: 06 July 2020
  •  Published: 31 July 2020

 ABSTRACT

Insects are of ecological and economic importance. This study was carried out to compare the efficiency of the three main insect sampling methods namely, sweep net, hand sampling and the light trap and also to show the biodiversity distribution from Lamto habitats for good biological conservation. A total of 379 individuals belonging to 9 orders were collected. Significantly, more individuals were collected by sweeping net compared to hand sampling and light trap. From the capture rate, highest rate was recorded for sweeping net (0.720) followed by hand (0.232) and light trap (0.047). The lowest value of Shannon’s index was 0.672 with the light trap followed by hand (1.375) and the highest was 1.940 with sweeping net in Lamto’s habitats. The insect orders recorded with the hand were Heteroptera, Coleoptera, Homoptera, Hymenoptera, Orthoptera, Diptera and Isoptera (F = 11.340, P value = 0.006). Light trap was more suitable to capture Lepidoptera (3.250%), Coleoptera (0.750%) and Homoptera (0.500%) (F= 6.659, P value= 0.0001). The abundance index recorded with the sweeping net commonly varied between 0.0 and 18.250%. Both sweeping net and hand insect sampling techniques were the most efficient and showed the highest insect orders complementarity. However, the use of sweep net, hand sampling and light trap were recommended to have good collection of insects.
 
Key words: Sweep net, light trap, hand sampling, insects’ conservation, capture effectiveness.


 INTRODUCTION

Territorial insects are more diverse groups of animal and are important components of ecosystem. They play important roles in the economic and ecological success of agroecosystems and are distributed in all habitats (forest and savannah) of Lamto. Large population of insects may be isolated into sub-populations from one to another due to habitat fragmentation (Hunter, 2007).  These habitats (forest and  savannah)  indirectly  through microclimate change (Li, 2017) and represent a highest importance to insect biodiversity (Wearn, 2017) and to insect abundance (Diniz et al., 2010; Elia et al., 2012; Muvengwi et al., 2017). Lamto plays an important role in supporting biodiversity conservation, for instance, provision of foods, microhabitats for the growth and distribution of insect populations. There are four seasons which are a long dry season from December to February, a long rainy season from March to July, a short dry season in August and a short rainy season from September to November. The methods used to collect insects include light trap, hand and sweep net (Noyes, 1989; Shimoda and Honda, 2013).  Moreover, the choice of an adequate sampling methodology is crucial. Hands are the traditional method for collection of epigaeic invertebrates. It has been widely used for sampling insects in biodiversity inventories (Ramírez-Hernández et al., 2018), population and community ecology (Hunter, 2007; Ramírez-Hernández et al., 2018). The light trap is the most commonly used sampling device to study the daily activity of nocturnal insects. The reason for the wide use of hand and light trap in invertebrate sampling is their simplicity of setting and using, and their low cost. However, the interpretation of hand and light trap data is subject to many problems because they rarely reflect the true abundance of the target organisms being sampled (Shweta and Rajmohana, 2016; Ramírez-Hernández et al., 2018). However, the effectiveness of light trapping as an insect sampling method was influenced by many environmental factors that influence the efficiency of the traps (Upadhyay et al., 2000; Ramírez-Hernández et al., 2018). Despite these shortcomings, light traps and hand have continued to be used (Upadhyay et al., 2000; Ramírez-Hernández et al., 2018). The effectiveness and complementarity of three sampling methods such as sweeping net, hand sampling and light trap for collecting insects were assessed to show the biodiversity distribution from Lamto habitats for good biological conservation.


 MATERIALS AND METHODS

Description of study site
 
The study area is Lamto station (6° 13 N, 5° 2 W) located in the center of Côte d’Ivoire (West Africa) in the transition forest-savannah. The landscape of Lamto is a mosaic which brings together scraps of dense semi-deciduous forests, gallery forests and savannahs (Menaut, 1971; Devineau, 1975).
 
Entomological sampling
 
Insects were collected from 23 October to 27 October 2007. Sampling was carried out between 05:30 to 08:00 from a forest and savannah vegetation using the sweep net and the hand and between 19:00 to 20:00 with the light trap, for a period of four days. Sweep net was used while walking around the road in the forest and adult insects were collected from the vegetation. In savannah, adult insects were collected from the vegetation in random sites. The collected insects were killed by ethyl acetate vapour, sorted out into different orders and mounted in insect boxes. All small and soft bodied insects were preserved in 70% ethanol in specimen bottles labeled to show sample station, sample method and collection date.
 
Identification of insects
 
Insects   were   identified   up   to   order   level   with   the   help   of entomologists and by using a binocular lens and identification keys of insects (Roth, 1974; Maurice, 1980; Delvare and Aberleng, 1989). Thus, the number of individuals collected under each order during the study period was recorded.
 
Data analysis
 
Collected insects were sorted out into orders. Total number of individuals collected under each order was used for diversity analysis. Diversity indices such as Shannon’s index were calculated by using Estimate S (version 9.1.0, 2013). An analysis with ANOVA allowed comparing between mean diversity indices and mean abundance index between the three insect collection methods.Subsequently, we calculated the abundance index (AR) and the occurrence frequency (Fo) according to the formulas, respectively:
 
 
Na: Number of sampling of individuals of order collected with method I; N: Number of total sampling with method i.


 RESULTS AND DISCUSSION

A total of 379 individuals belonging to 9 orders were collected. From the capture rate, highest rate was recorded for sweep net (0.720) followed by hand (0.232) and light trap (0.047) (Table 1). According to Shweta and Rajmohana (2016), sweep net are better than the other method to collect insects.
 
The lowest value of Shannon’s index was 0.672 with the light trap followed by hand (1.375) and the highest was 1.940 with sweep net in Lamto’s habitats (forest and savannah) (Table 2). There was a significant difference with F = 324.458, P value = 0.0001. Noyes (1989) and Shweta and Rajmohana (2016) studied parasitic hymenoptera capture rates and hymenoptera claiming sweep net to be most effective, respectively.
 
The insect orders recorded with the three insect collection methods in Lamto’s habitats were Odonata, Lepidoptera, Coleoptera, Heteroptera, Homoptera, Hymenoptera, Orthoptera, Isoptera and Diptera. In fact, the majority of insect recorded were phytophagous (Lecordier, 1975).
 
Light trap was more suitable to capture Lepidoptera (3.250%), Coleoptera (0.750%) and Homoptera (0.500%) (F = 6.659, P value = 0.0001) (Table 3). In fact, nocturnal insects are collected exclusively through light trap. According to Pachkin et al. (2019) and Marchioro et al. (2020), the light traps were more attractive for the representatives     of      Coleoptera, Homoptera and Lepidoptera. Light trapping as an insect sampling method was influenced by many environmental factors. The observations are in agreement with those of Nair et al. (2004) and Sheikh et al. (2016). In fact, the efficacy of light trap was influenced by the vegetation around the sampling site and by lunar light (Holyoak et al., 1997; Brehm and Axmacher, 2006; Shimoda and Honda, 2013; Keszthelyi et al., 2019). According to Upadhyay et al. (2000) and Sheikh et al. (2016), not all the light source proved efficient to attract and collect all the nocturnal insect species in a particular habitat.
 
 
The insect orders recorded with the hand method were Heteroptera, Coleoptera, Homoptera, Hymenoptera, Orthoptera, Diptera and Isoptera.  The  abundance  index commonly varied between 0.5 and 11.75%. The highest abundance was recorded with the Isoptera (11.75%) and the lowest was recorded with the Heteroptera (0.5%). The abundance index of Heteroptera, Homoptera, Diptera, Orthoptera, Hymenoptera, Coleoptera and Isoptera were statistically different (F= 11.340, P value = 0.006) and were 0.5, 1.25, 1.75, 1.75, 2.5, 3 and 11.75%, respectively (Table 4).
 
The abundance index recorded with the sweep net commonly varied between 0.0 and 18.250%. The highest abundance was recorded with the Lepidoptera (18.250%) and the lowest was recorded with the Isoptera (0.0%). The abundance index of Isoptera, Homoptera, Diptera, Orthoptera,       Heteroptera,       Coleoptera,      Odonata, Hymenoptera and Lepidoptera were statistically different (F = 14.192, P = 0.0001) and were 0.000, 3.250, 5.000, 6.500, 7.000, 7.000, 10.000, 11.250 and 18.250%, respectively (Table 5).
 
The lowest abundance index was due to the fact that the sampling period was theses insect period reproduction. In this sampling period, the high relative humidity reduced the activity of these insects (Butler et al., 1999; Ramamurthy et al., 2010).
 
Amongst the three insect’s collection methods, sweep net showed the maximum ability followed by hand and light trap (Table 6). The occurrence frequency of insects of various orders in light trap, hand and sweeping net were all varied from 0.000 to 100 percent (Table 6). The total catch of light trap, hand and sweeping net were 25, 75 and 75% in Homoptera; 50, 100 and 100% in Coleoptera; 100, 0 and 100% in  Lepidoptera;  0,  75  and 100% in Hymenoptera, Orthoptera and Diptera; 0, 0 and 100% in Odonata and Heteroptera and 0, 100 and 0% in Isoptera, respectively (Table 6). The observations are in agreement with those of Butler et al. (1999) and of László et al. (2012) which have mentioned that humidity of the habitat produce a rich sample of insects in general. Both sweep net and hand sampling were the most efficient and showed the highest species complementarity. Indeed, highest occurrence frequency of Coleoptera individuals with the sweep net, hand sampling and light trap showed that Lamto's habitats was sound and allow good conservation of biodiversity.
 


 CONCLUSION

The methods used  to  collect  insects  include  light  trap, hand and sweep net sampling. A total of 379 individuals belonging to 9 orders were collected. Sweep net was the best method to collect different groups of insects. From the capture rate, highest rate was recorded for sweep net followed by hand sampling and light trap. Sweep net recorded the highest number of individuals. Furthermore, the results revealed that light trap do not give efficiently to provide reliable inventories from Lamto. Both sweep net and hand sampling were the most efficient and showed the highest insect orders complementarity. However, we recommend the use of the three methods-sweeps net, hand sampling and light trap to made good collection of insects from Lamto.


 CONFLICT OF INTERESTS

The authors have not declared any conflict of interests.



 REFERENCES

Brehm G, Axmacher JC (2006). A comparison of manual and automatic moth sampling methods (Lepidoptera: Arctiidae, Geometridae) in a rain forest in Costa Rica. Environmental Entomology 35(3):757-764.
Crossref

 

Butler L, Kondo V, Barrows EM, Townsend EC (1999). Effects of weather conditions and trap types on sampling for richness and abundance of forest Lepidoptera. Environmental Entomology 28:795-811.
Crossref

 
 

Delvare G, Aberleng P (1989). Les Insectes d'Afrique et d'Amérique Tropicale. Clé pour la Reconnaissance des Familles. Laboratoire de Faunistique, Département GERDAT:Montpellier, France, 194p.

 
 

Devineau J (1975). Etude quantitative des forets galeries de Lamto (moyenne Côte d'Ivoire).Thèse de Doctorat de l'Université de Paris VI, Paris, France, 190 p.

 
 

Diniz S, Prado PI, Lewinsohn TM (2010). Species richness in natural and disturbed habitats: Asteraceae and Flower-head insects (Tephritidae: Diptera). Neotropical Entomology 39:163-171.
Crossref

 
 

Elia M, Lafortezza R, Tarasco E, Colangelo G, Sanesi G (2012). The spatial and temporal effects of fire on insect abundance in Mediterranean forest ecosystems. Forest Ecology and Management 263:262-267.
Crossref

 
 

Holyoak M, Jarosik V, Novak I (1997). Weather-induced changes in moth activity bias measurement of long-term population dynamics from light trap samples. Entomologia Experimentalis and Applicata 83:329-335.
Crossref

 
 

Hunter P (2007). The human impact on biological diversity: How species adapt to urban challenges sheds light on evolution and provides clues about conservation. Embo Reports 8:316-318.
Crossref

 
 

Keszthelyi S, János P, Puskás J, Nowinszky L (2019). Light-trap catch of cotton bollworn, Helicoverpa armigera in connection with the moon phases and geomagnetic H-index. Biologia 74:661-666.
Crossref

 
 

László N, János P, Márta L (2012). Efficiency of light-traps influenced by environmental factors. International Journal of Science and Nature 3(3):521-525.

 
 

Lecordier C (1975). Les peuplements de carabiques (Coléoptères) dans la savane de Lamto (Côte d'Ivoire). Université Pierre et Marie Curie, Paris, France, 211p.

 
 

Li WB, Liu NY, Wu YH, Zang YC, Xu Q, Chu J, Wang SY, Fang J (2017). Community composition and diversity of ground beetles (Coleoptera: Carabidae) in Yaoluoping National Nature Reserve. Journal of Insect Science 17(6):1-8.
Crossref

 
 

Marchioro M, Battisti A, Faccoli M (2020). Light Traps in Shipping Containers: A New Tool for the Early Detection of Insect Alien Species. Journal of Economic Entomology pp.1-7.

 
 

Maurice R (1980). Initiation à la morphologie, la systématique et la biologie des insectes. ORSTOM (ed.). Paris, France, 211p.

 
 

Menaut JC (1971). Etude de quelques peuplements ligneux d'une savane guinéenne de Côte d'Ivoire. Thèse de Doctorat de l'Université de Paris VI, Paris, France, 140p.

 
 

Muvengw J, Mbiba M, Ndagurwa HGT, Nyamadzawo G, Nhokovedzo P (2017). Termite diversity along a land use intensification gradient in a semi-arid savanna. Journal of Insect Conservation 21:801-812.
Crossref

 
 

Nair KSS, Sudheendrakumar VV, Sajeev TV, Mathew G, Mohanadas K, Varma RV, Sivadas TA (2004). A. solar light trap for monitoring forest insect populations. Entomon 29(2):111-117.

 
 

Noyes JS (1989). A study of five methods of sampling Hymenoptera (Insecta) in a tropical rainforest with special reference to Parasitica. Journal Natural History 23:285-298.
Crossref

 
 

Pachkin A, Kremneva O, Popov I, Zelensky R, Kurilov A, Danilov R (2019). Comparative assessment of the efficiency of lights traps of various design in corn agrocenosis. IOP Conference Series: Earth and Environmental Science 403. 012141. 
Crossref

 
 

Ramamurthy VV, Akhtar M S, Patankar NV, Menon P, Kumar R, Singh S , Ayri S, Parveen S, Mittal V (2010). Efficiency of different light sources in light traps in monitoring insect diversity. Munis Entomology and Zoology 5(1):109-114.

 
 

Ramírez-Hernández A, Escobar F, Montes de Oca E, Arellano L (2018). Assessing Three Sampling Methods to Survey and Monitor Ground Beetles (Coleoptera: Carabidae) in Riparian Cloud Forests. Environmental Entomology 47(6):1565-1572.
Crossref

 
 

Roth M (1974). Initiation à la morphologie, la systématique et la biologie des insectes. Editions de l'Office de la Recherche Scientifique Outre-Mer, France, 212 pp.

 
 

Sheikh AH, Thomas M, Bhandari R, Bunkar K (2016). Light trap and insect sampling: An overview. Journal of Current Research 8(11):40868-40873.

 
 

Shimoda M, Honda K (2013). Insect reactions to light and its applications to pest management. Applied Entomolology and Zoology 48:413-421.
Crossref

 
 

Shweta M, Rajmohana K (2016). A comparison of efficiencies of sweep net, yellow pan trap and malaise trap in sampling platygastridae (Hymenoptera: insecta). Journal Experimental Zoology 19(1):393-396.

 
 

Upadhyay RN, Dubey OP, Vaishampayan SM (2000). Study on the common predatory and parasitic species of insects collected on light trap. JNKVV Research Journal 33(1/2):50-57.

 
 

Wearn OR (2017). Mammalian species abundance across a gradient of tropical land-use intensity: A hierarchical multi-species modelling approach. Biological Conservation 212:162-171.
Crossref

 

 




          */?>