# Insect Diversity of the Muni-Pomadze Ramsar Site: An Important Site for Biodiversity Conservation in Ghana

Authors: Rosina Kyerematen; Daniel Acquah-Lamptey; Erasmus Henaku Owusu; Roger Sigismund Anderson; Yaa Ntiamoa-Baidu
Journal: Journal of Insects
 (2014)

---

## Abstract

An inventory of species diversity of insects of the Muni-Pomadze Ramsar site, with special reference to species of conservation concern, was carried out as part of an evaluation of changes in the ecological character of the site, twenty years after designation. Samples were taken from two protected areas within the Ramsar site, in the wet (July), dry (January), and intermediate (June) seasons. Community diversity was characterized in terms of number of species accumulated, species richness, Shannon-Weiner indices of diversity, Pielou’s evenness, and Bray-Curtis similarity. A total of 134 families from 19 insect orders were recorded during the entire study period. Yenku Block A recorded the highest species richness (98) and the highest diversity index (14.97), corroborated by the highest Margalef index of 3.82 with a relatively even distribution of species (0.834) during the intermediate season, and recorded the lowest diversity (6.957) and species richness (41) during the dry season. On the whole, the Muni-Pomadzi Ramsar site showed a high diversity of insect species. The presence of species such asJunonia oenone and Papilio demodocus which are specialized in degraded habitats at Yenku Block A in large numbers is a clear indication of degradation of the forest, but the presence of forest species such as Salamis anacardii and Euphaedra crokeri is an indication that some parts of this reserve are still in good shape. A comparison of the butterfly species recorded with findings in a 1997 survey showed a marked increase in numbers from 75 to 130; this may be attributed to the habitat changes that have taken place at the site offering more diverse habitat types.


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## Body

## 1. Introduction

Insects constitute a remarkably speciose group of organisms attributed mainly to their small size, which allows them to occupy niches not available to larger organisms. They are adapted to highly differing environments from the Arctic tundra to Alpine mountain summits as well as warmer tropical rainforest and coastal mangrove swamps and are able to tolerate extremes of temperature and other environmental conditions. Estimates of global species richness of insects vary from less than five million to as many as 80 million [1].Insects are critical natural resources in ecosystems, particularly those of forests [2]. In addition to their role as efficient pollinators and natural/biological pest control agents, some insect species are important indicators in ecosystems management [3]. The habitat heterogeneity hypothesis simply predicts that more arthropod species will occur where different forms and species of plants provide greater structural heterogeneity in the vegetation [4]. Thus, greater resources are available for the coexistence of more species within each trophic group [5]. Arthropod diversity, which takes account of the relative abundance of species as well as their variety [6], would express an asymptotic relationship with increasing numbers of plant species and greater structural heterogeneity in the vegetation. Habitat heterogeneity at small spatial scales can favour the number and abundance of arthropod species in grassland [7], for example.Insects are essential in the ecosystem by helping in nutrient recycling through leaf litter and wood degradation, carrion and dung disposal, and soil turnover. They play a major role in plant pollination and maintenance of plant community composition and structure via phytophagy [1]. Their demise will therefore result in the disruption of critical ecosystem services such as pollination and source of food. There is therefore the need for the conservation and protection of these species. Indeed the forest canopy is the heart of biotic diversity and thus it is imperative that the forest be properly managed to ensure the persistence of such a unique group of nature, which is critical for ecosystem health.The Muni-Pomadze Ramsar site was designated in 1992. A few years after its designation, an assessment of the insect diversity of the site and its surroundings in relation to habitat characteristics was carried out by the Coastal Wetlands Management Project (CWMP) funded by the Global Environment Facility (GEF) [8]. This study was carried out to (i) present more detailed descriptive baseline data from an intensive entomological survey in an important site for conservation in West Africa, (ii) provide an inventory of the insect diversity and abundance with special reference to species of conservation concern, and (iii) assess the changes that have taken place in the ecological character of the Ramsar site.


## 2. Materials and Methods

### 2.1. Sampling Sites

The Muni-Pomadze Ramsar site is situated to the west of the coastal town of Winneba in the Central Region of Ghana, approximately 55 km from Accra and encompasses approximately 90 km2 of the watershed surrounding the Muni Lagoon as well as two protected areas: Yenku Block A and Yenku Block B [2, 9]. At the time of the current study, Yenku Block A, north of the village of Onyadze, was a degraded natural forest interspersed with pockets of farmlands and Teak, Eucalyptus, and Acacia plantations with a few thickets of dense shrubs. Yenku Block B which is close to Mankoadze near the coast consisted mainly of open savanna grassland interspersed with thickets and small trees. An Eucalyptus plantation bordered this area to the north at the foot of the Egyasimanku Hills with maize farms to the south.


### 2.2. Methods

The field studies were carried out in July 2011, January, and June 2012, the wet, dry, and intermediate seasons, respectively. Eight main sampling methods were employed in the collection of insects. Butterfly nets were used for butterflies, dragonflies, and other high flying insects; visual observations and counts were done for those insects that were missed by the nets and also for insects species of which individuals had already been captured since it was not necessary to capture more insects than necessary. At each site, one Malaise trap for smaller, flying, mainly nocturnal insects, one flight interception trap (FIT) designed to intercept insects in flight and five Charaxes traps for alcohol-loving butterflies and other insects that are attracted to fermenting foods were set up. Rotten banana, mashed and mixed with alcohol (palm wine and or beer), was used as bait for the Charaxes traps. In addition, pitfall and yellow pan traps (five of each) were randomly set up at each site for crawling and ground dwelling insects and insects attracted by the yellow colour; sweeping was done for vegetation-dwelling insects and handpicking with forceps was done for insects within easy reach. Light trapping which lasted about two hours was done for the nocturnal insects along a small stream at Yenku Block B.In addition to the various trapping methods, random walk sampling was undertaken by three persons for a minimum of three hours during each sampling period twice each day for seven days at each site. Visual observations and counts were done mainly for the dragonflies since they are very fast fliers and difficult to catch.Insects collected were killed using a killing bottle containing ethyl acetate and kept either in alcohol or glassine envelops for later examination and identification. Identification of insects was done with reference to the collection in the Museum of the Department of Animal Biology and Conservation Science, University of Ghana, as well as with reference to Carter [10], Gullan and Cranston [1, 11], Scholtz and Holm [12], Chinery [13, 14], Carcasson [15], Crowson [16], Belcastro and Larsen [17], Larsen [18], Miller [19], McGavin [20], Pinheiro and Ortiz [21], and Dijkstra and Clausnitzer [9].


## 2.1. Sampling Sites

The Muni-Pomadze Ramsar site is situated to the west of the coastal town of Winneba in the Central Region of Ghana, approximately 55 km from Accra and encompasses approximately 90 km2 of the watershed surrounding the Muni Lagoon as well as two protected areas: Yenku Block A and Yenku Block B [2, 9]. At the time of the current study, Yenku Block A, north of the village of Onyadze, was a degraded natural forest interspersed with pockets of farmlands and Teak, Eucalyptus, and Acacia plantations with a few thickets of dense shrubs. Yenku Block B which is close to Mankoadze near the coast consisted mainly of open savanna grassland interspersed with thickets and small trees. An Eucalyptus plantation bordered this area to the north at the foot of the Egyasimanku Hills with maize farms to the south.


## 2.2. Methods

The field studies were carried out in July 2011, January, and June 2012, the wet, dry, and intermediate seasons, respectively. Eight main sampling methods were employed in the collection of insects. Butterfly nets were used for butterflies, dragonflies, and other high flying insects; visual observations and counts were done for those insects that were missed by the nets and also for insects species of which individuals had already been captured since it was not necessary to capture more insects than necessary. At each site, one Malaise trap for smaller, flying, mainly nocturnal insects, one flight interception trap (FIT) designed to intercept insects in flight and five Charaxes traps for alcohol-loving butterflies and other insects that are attracted to fermenting foods were set up. Rotten banana, mashed and mixed with alcohol (palm wine and or beer), was used as bait for the Charaxes traps. In addition, pitfall and yellow pan traps (five of each) were randomly set up at each site for crawling and ground dwelling insects and insects attracted by the yellow colour; sweeping was done for vegetation-dwelling insects and handpicking with forceps was done for insects within easy reach. Light trapping which lasted about two hours was done for the nocturnal insects along a small stream at Yenku Block B.In addition to the various trapping methods, random walk sampling was undertaken by three persons for a minimum of three hours during each sampling period twice each day for seven days at each site. Visual observations and counts were done mainly for the dragonflies since they are very fast fliers and difficult to catch.Insects collected were killed using a killing bottle containing ethyl acetate and kept either in alcohol or glassine envelops for later examination and identification. Identification of insects was done with reference to the collection in the Museum of the Department of Animal Biology and Conservation Science, University of Ghana, as well as with reference to Carter [10], Gullan and Cranston [1, 11], Scholtz and Holm [12], Chinery [13, 14], Carcasson [15], Crowson [16], Belcastro and Larsen [17], Larsen [18], Miller [19], McGavin [20], Pinheiro and Ortiz [21], and Dijkstra and Clausnitzer [9].


## 3. Data Analyses

Cluster analysis was performed using Bray-Curtis similarity. Species contributing at least 20 individuals of the total abundance at each sampling site were included in the analysis. The original data was transformed (fourth root transformation) and standardized in order to minimize the weighting of numerically dominant species.Five diversity indices were computed [22].(1)
Total Species. S—the number of species in each sample, that is, species with nonzero counts.
(2)
Total Individuals. N—the number of individuals in each sample.
(3)
Species Richness (Margalef). d
=
(
S
-
1
)
/
log
⁡
(
N
)—This is a measure of the number of species present, making some allowance for the number of individuals.
(4)
Pielou’s Evenness. This is a measure of equitability, a measure of how evenly the individuals are distributed among the different species.
(5)
Shannon-Wiener Index. It incorporates both species richness and equitability components.


## 4. Results

A total of 8634 individual insects belonging to 134 families and 19 orders were recorded in the survey. We present the butterflies and dragonflies data separately because of their numerical abundance, conservation interest, and role as indicators of ecosystem health but group all the other insects.


### 4.1. Butterflies

130 species of butterflies (Table1) belonging to nine families were recorded during the survey: Nymphalidae, Papilionidae, Hesperiidae, Pieridae, Satyridae, Danaidae, Charaxidae, Acraedae, and Lycaenidae, with the Pieridae dominating with 39 species, followed by Nymphalidae with 37 species.Table 1
Butterfly species recorded over the entire survey period.
Species
Yenku Block A
Yenku Block B
July
January
June
July
January
June
Euryphene barombyna
2
2
1
0
0
1
Euryphenesp.
1
1
0
0
0
0
Euphaedra sarcoptera
12
2
4
0
0
0
Euphaedra edwardsi
2
1
0
0
0
0
Euphedra hapalyce
5
1
2
0
0
0
Euphaedra eleus
2
1
0
0
0
0
Euphaedra medon
9
2
3
0
0
0
Euphaedra crockeri
4
1
2
0
0
0
Euphaedra xypete
14
1
4
0
0
0
Euphaedrasp.
3
0
2
0
0
0
Eurytela dryope
12
3
23
0
0
0
Pseudoacreasp.
9
2
4
55
0
1
Pseudoneptis ianthe
3
0
2
0
0
0
Pseudoneptissp.
1
0
1
0
0
0
Diestogina feronia
2
1
1
0
0
0
Neptis melicerta
3
6
3
3
0
14
Neptis agatha
1
3
5
10
0
4
Neptis metella
2
2
9
2
0
3
Neptis merosa
1
1
3
1
0
0
Neptis seeldrayersi
0
0
2
0
0
0
Salamis anacardii
3
1
1
0
0
0
Junonia terea
43
3
27
2
0
6
Junonia oenone
1
1
2
6
5
60
Junonia octavia
0
11
2
0
0
10
Junoniasp.
2
1
2
1
1
0
Gnophodes chelys
3
3
5
0
0
0
Gnophodes betsimena
0
2
1
0
0
0
Kallima rumia
2
1
3
0
0
0
Phalanta phalanta
13
6
29
75
3
66
Ariadne enotera
8
1
14
0
0
1
Aterica galene
2
1
1
0
0
0
Atericasp.
7
0
1
0
0
0
Byblia achelola
2
4
2
0
0
0
Bybliasp.
1
1
3
0
0
0
Hypolimnas salmacis
2
2
1
0
1
0
Hypolimnas missipus
1
1
2
0
0
0
Hypolimnas dinarcha
1
2
0
0
0
0
Acraea epaea
2
3
5
7
6
13
Acraea zetes
4
5
8
37
13
65
Acraea terpsichore
0
4
7
0
0
24
Acraea pseudolycia
0
0
1
0
0
0
Acraea doubledayi
0
0
2
0
0
0
Acraea egina
1
0
3
0
0
0
Acraeasp.
1
2
4
16
4
11
Bematistis epaea
4
5
6
0
2
14
Hallelesis haliwa
2
1
0
1
0
0
Hallelesissp.
4
1
1
0
0
0
Ypthima itonia
0
1
3
0
0
0
Bicyclus zinebi
11
3
3
1
0
0
Bicyclus safitza
13
2
5
2
0
3
Bicyclus auricruda
0
1
3
0
0
0
Mycalensis safitza
1
1
5
0
0
1
Mycalensissp.
5
0
1
6
0
0
Bicyclus vansoni
0
2
0
0
0
0
Bicyclus condamini
0
1
1
0
0
0
Bicyclus vulgaris
0
1
0
0
0
0
Papilio demodocus
18
8
21
112
11
66
Papilio dardaunus
3
5
2
0
1
0
Papilio nireus
23
4
29
0
0
0
Papilio bromius
3
1
2
0
0
0
Graphium policenes
2
4
3
1
0
1
Papilio menesthius
1
2
1
0
0
2
Amauris niavus
3
2
5
1
0
0
Amauris egialea
2
1
3
1
0
0
Amaurissp.
1
1
2
1
0
0
Danaus chryssipus
2
125
8
13
24
7
Danaus limniace
0
1
2
0
0
0
Eurema brigitta
17
8
9
206
5
40
Eurema senegalensis
9
2
3
16
2
11
Eurema hecabe
6
13
8
3
1
11
Eurema lisa
11
3
4
7
1
0
Eurema brenda
0
0
1
0
0
0
Euremasp.
13
2
5
4
0
0
Colias philodice
4
2
1
0
0
0
Pieris rapae
3
4
6
0
2
26
Pierissp.
4
2
3
1
1
10
Nepheronia thalassina
18
15
21
2
3
29
Nepheronia argia
22
8
18
0
3
35
Nepheroniasp.
5
3
6
0
0
0
Leptosia alcesta
21
8
33
0
0
0
Leptosia medusa
18
10
22
0
0
0
Leptosiasp.
8
3
5
0
0
0
Appias phaola
0
1
3
0
0
0
Dixeia astarte
1
0
8
3
1
0
Dixeia cebon
8
3
23
4
2
3
Colotis erone
9
4
22
7
25
13
Colotis danae
7
2
3
5
8
3
Colotis evippe
12
8
14
11
5
7
Colotis antevippe
18
2
24
20
3
85
Colotis evinina
6
3
9
9
3
62
Colotis eunoma
4
0
5
3
2
5
Anthocharis cardamine
4
4
6
3
0
3
Belinois calypso
68
15
87
12
8
66
Belinois creona
32
5
46
9
1
20
Belinois theora
16
1
19
12
0
14
Belinois gidica
18
4
7
14
0
2
Belinois aurota
14
3
12
21
0
9
Belinois theuszi
9
8
10
7
1
0
Belinois hedyle
0
0
3
0
0
0
Catopsilla florella
78
29
31
21
21
69
Catopsillasp.
42
7
16
5
9
16
Euronia cleodora
0
0
1
0
0
0
Mylothris chloris
56
71
34
23
1
8
Mylothris poppea
34
9
27
5
1
19
Mylothrissp.
51
12
10
4
0
6
Mylothris rhodope
17
8
11
2
0
26
Charaxes varanes
9
2
1
4
0
2
Charaxes protocrea
2
1
1
0
0
0
Charaxes etheocles
0
1
1
0
0
0
Charaxes brutus
0
0
2
0
1
0
Charaxes tiridates
5
1
3
0
0
0
Charaxes cynthia
3
2
4
1
0
0
Charaxes zelica
2
1
3
0
0
0
Euxanthe eurinome
1
0
2
0
0
0
Castalius carana
3
2
1
3
5
12
Lycaena helloides
2
5
3
5
27
0
Lycaenasp.
6
2
1
5
8
0
Meza indusiata
0
3
1
0
8
0
Euchrysops albistriata
5
8
11
3
39
25
Osmodes adon
0
1
0
0
0
0
Spalgis lemolea
0
1
1
0
0
0
Poecilmitis chrysaor
0
0
1
0
0
0
Anthenesp.
0
0
1
0
0
0
Pyrrhiades lucagus
61
103
76
7
0
51
Amblyscirtis vialis
3
2
3
0
1
0
Lerodeasp.
4
3
2
1
0
0
Hesperia leonardus
2
1
4
0
0
2
Hesperiasp.
3
2
1
2
0
1
Oeneis polixenes
2
3
6
1
0
0
Coliades chalyba
0
0
3
0
0
0Table2 gives the diversity indices for the butterfly species for the three sampling seasons. Yenku Block A (YBA) was the most important site for butterflies, with the highest numbers (N
=
1061 and 1011 for July and June, resp.) and the highest species richness (S
=
106, 111, and 122 for July, January, and June, resp.), which was corroborated by the highest Margalef index (d) of 15.07 in July, 16.85 in January, and 17.49 in June. Yenku Block B (YBB) had low butterfly species richness in June (S
=
53) but relatively high abundance (N
=
1064). YBB had the lowest abundance (N
=
269) as well as a relatively low species richness (S
=
41) in January corroborated by the lowest Margalef index (d) 7.15 (Table 2).Table 2
Calculation of suite of diversity indices for butterfly species collected from the two sites at Muni-Pomadze, Yenku Block A and Yenku Block B.
Sample site
S
N
d
J
′
H
′(loge)
YBAJUL
106
1061
15.07
0.8547
3.986
YBAJAN
111
684
16.85
0.7554
3.558
YBAJUN
122
1011
17.49
0.8513
4.09
YBBJUL
60
825
8.786
0.7358
3.013
YBBJAN
41
269
7.15
0.8354
3.102
YBBJUN
53
1064
7.461
0.8602
3.415
YBA: Yenku Block A; YBB: Yenku Block B; JUL: July; JAN: January; JUN: June;S: species richness; N: number of individuals; d: Margalef’s index; J
′: Pielou’s evenness index; H
′: Shannon-Wiener index.Yenku Block B (YBB) recorded a relatively lower evenness, (J
′
=
0.7358) in July. The six species, Eurema brigitta, Papilio demodocus, Catopsilla florella, Acreae zetes, Phalanta phalanta, and Colotis antevippe, made up about 42% of the total numbers recorded at YBB in July. Both sites had a high evenness (J
′
>
0.8354) in the wet (YBAJUL) and intermediate (YBBJUN) seasons (Table 2) with individuals evenly distributed among the different species. Yenku Block A (YBA) recorded a high diversity (Margalef index d
=
16.85) in January but with a low evenness (J
′
=
0.7554) as a result of the dominance of D. chryssipusand Pyrrhiadis lucagus.From the cluster analysis (Figure1) the species population structure could be considered homogenous below a Bray-Curtis similarity of 50%. Homogeneity however begins to break down above 60%, leading to the formation of two clusters of species communities: YBAJAN, YBAJUL, and YBAJUN forming one cluster and YBBJUL and YBBJUN forming the other.Figure 1
Dendrogram of butterfly species at the two sites in Winneba July (2011), January, and June, in 2012. The cluster analysis was performed using group-average linking on Bray-Curtis species similarity from fourth root transformed abundance data.Figure2 is a dendrogram showing the relationships between butterfly species occurring at Muni-Pomadze that contributed abundance of 20 or more using group-average linking on Bray-Curtis species similarity from fourth root transformed abundance data. Above a Bray-Curtis similarity of 60% there is a formation of two clusters with more than 40 forming the main cluster which further breaks down into four distinct clusters around 73%. Red-dotted lines indicate closely related species or species of close associations.Figure 2
Dendrogram of butterfly species occurring at Muni-Pomadze using group-average linking on Bray-Curtis species similarity from fourth root transformed abundance data. The analysis was performed on species contributing abundance of 20 or more.


### 4.2. Dragonflies

Yenku Block B recorded the highest species richness (S
=
10) for dragonflies in July which was corroborated by the highest Shannon-Wiener (H
=
1.9) and Margalef (d
=
2.1) indices. Dragonflies were most abundant in July (N
=
77) at Yenku Block A with the lowest numbers recorded in January at Yenku Block B (N
=
26) (Table 3).Table 3
Diversity indices for Odonata collected from the two sites at Muni-Pomadze, Yenku Block A and Yenku Block B.
Sample
S
N
d
J
′
H
′ (loge)
YBAJUL
7
77
1.381
0.7476
1.455
YBBJUL
10
68
2.133
0.8306
1.912
YBAJAN
7
69
1.417
0.6608
1.286
YBBJAN
5
26
1.228
0.8906
1.433
YBAJUN
8
44
1.85
0.776
1.614
YBBJUN
8
40
1.898
0.8874
1.845
YBA: Yenku Block A; YBB: Yenku Block B; JUL: July; JAN: January; JUN: June;S: species richness; N: number of individuals; d: Margalef’s index; J
′: Pielou’s evenness index; H
′: Shannon-Wiener index.


### 4.3. Other Insects

A total of 3720 insects belonging to 19 other insect orders were recorded from the traps. Diptera was the most abundant (1932) as well as the most diverse order with 36 families, followed by Coleoptera with 21 families and Hymenoptera with 13 families (Table4).Table 4
Insects families recorded over the entire survey period.
Yenku Block A
Yenku Block B
Family
July
January
June
July
January
June
Gryllidae
8
7
15
6
13
11
Acrididae
6
6
4
7
5
14
Tettigonidae
3
0
4
12
3
3
Tridactylidae
0
2
5
0
1
4
Tetrigidae
2
1
1
6
2
1
Formicidae
81
96
31
75
39
29
Apidae
6
0
8
4
1
5
Evaniidae
1
3
1
3
1
1
Sphecidae
2
2
5
0
1
8
Vespidae
0
3
11
0
1
6
Braconidae
3
7
13
8
6
15
Ichneumonidae
2
2
4
4
1
3
Scelionidae
0
3
2
1
2
1
Halictidae
0
1
2
2
1
1
Pompylidae
1
0
4
0
0
3
Chalcididae
0
2
2
0
1
4
Eulophidae
1
0
3
0
2
4
Tiphiidae
2
0
1
0
0
0
Blattidae
6
5
9
1
4
1
Mantidae
2
0
1
0
0
1
Noctuidae
3
4
2
0
0
4
Arctidae
0
1
0
1
0
2
Satyridae
2
0
2
0
0
3
Pieridae
0
0
3
1
1
2
Acraeidae
0
0
1
1
0
0
Nymphalidae
0
1
2
2
0
0
Termitidae
1
1
2
0
2
5
Rhinotermitidae
0
0
1
0
0
2
Kalotermitidae
2
0
0
0
0
1
Cercopidae
5
11
6
10
26
8
Aleyrodidae
0
2
4
0
0
0
Aphididae
0
0
3
0
0
0
Fulgoridae
0
0
1
0
0
0
Cicadellidae
2
3
13
17
9
13
Delphacidae
0
0
2
3
2
2
Membracidae
0
1
0
0
0
1
Pseudococcidae
0
0
1
0
0
1
Dictyopharidae
1
0
0
2
0
1
Psyllidae
0
0
3
0
3
4
Acanalonidae
1
0
0
0
0
1
Flatidae
0
0
1
0
0
0
Isotomidae
3
33
22
1
32
27
Calliphoridae
2
2
5
31
2
3
Sepsidae
0
0
3
5
0
0
Tachinidae
4
5
13
0
12
19
Sarcophagidae
3
1
15
1
3
6
Culicidae
1
5
8
34
6
17
Muscidae
2
1
9
3
1
7
Tephritidae
69
24
29
4
5
22
Drossophilidae
1
53
24
3
5
993
Phoridae
11
14
24
7
15
28
Tipulidae
4
0
2
0
0
3
Asilidae
0
0
2
7
0
4
Diopsidae
0
0
0
0
0
1
Dolichopodidae
1
1
2
9
0
4
Syrrphidae
2
1
7
5
2
10
Rhagionidae
0
0
1
0
0
3
Stratiomyiidae
0
0
2
0
0
1
Bombylidae
2
0
2
1
0
1
Tabanidae
19
0
28
1
0
3
Glossinidae
1
0
92
0
0
8
Simulidae
2
0
0
3
0
1
Mycetophilidae
0
0
4
0
0
9
Sciaridae
0
0
2
0
0
6
Chironomidae
0
0
0
3
0
1
Ceratopogonidae
0
0
3
0
0
2
Conopidae
0
0
2
3
0
0
Lauxanidae
0
0
0
0
0
2
Psychodidae
0
0
1
0
0
0
Cecidomyiidae
1
0
2
0
0
0
Platypezidae
0
0
1
0
0
0
Trichoceridae
0
0
1
0
0
4
Acroceridae
0
0
0
0
0
2
Empididae
0
0
2
13
0
18
Therevidae
1
0
3
0
3
1
Otitidae
0
0
12
0
0
3
Anthomyiidae
0
0
0
8
0
11
Bibionidae
0
0
0
7
0
3
Chrysomelidae
11
3
12
19
2
8
Carabidae
23
0
14
8
4
2
Tenebrionidae
3
1
6
1
0
0
Scarabaeidae
167
0
44
2
0
2
Mordellidae
5
0
1
8
1
1
Phalacridae
0
0
2
0
0
1
Coccinellidae
2
0
0
0
3
0
Dermestidae
0
0
0
4
0
0
Meloidae
0
0
0
3
0
0
Curcujidae
0
1
6
0
0
14
Scolytidae
0
0
1
1
0
0
Lampyridae
0
0
5
13
0
2
Staphylinidae
5
0
15
52
0
51
Ptinidae
0
0
1
0
0
1
Lucanidae
0
0
2
0
0
1
Hesteridae
0
0
2
0
0
0
Anthicidae
0
0
0
0
0
1
Cleridae
0
0
0
0
0
1
Scaphididae
0
0
2
0
0
0
Curculionidae
5
0
6
1
0
6
Cerambycidae
1
0
1
0
0
2
Hydropsychidae
5
0
3
14
0
4
Polycentropodidae
3
0
0
0
0
5
Philopotamidae
0
0
1
4
0
0
Leptoceridae
2
0
1
10
0
2
Psychomyiidae
0
0
0
2
0
0
Thripidae
2
0
7
7
1
13
Forfinculidae
1
0
2
0
0
1
Labiidae
0
0
2
0
1
0
Carcinophoridae
0
1
1
0
0
2
Libellulidae
1
0
2
0
0
1
Coenagrionidae
0
0
0
0
0
1
Pyrrhocoridae
1
1
3
2
0
3
Coreidae
1
0
1
2
0
0
Pentatomidae
3
1
3
1
0
2
Reduvidae
0
1
3
1
2
1
Lygaeidae
0
0
2
1
1
2
Berytidae
0
1
1
0
0
0
Largidae
2
0
0
0
1
1
Nepidae
0
0
0
1
0
0
Alydidae
0
0
1
1
0
0
Cydnidae
1
0
2
0
0
1
Thyreocoridae
1
0
1
0
0
2
Ascalaphidae
0
0
1
0
0
0
Sialidae
0
0
0
1
0
0
Phasmatidae
1
0
3
0
0
1
Oligotomidae
0
0
1
0
0
0
Machilidae
0
0
0
0
0
1
Panorpidae
0
0
0
0
0
1The diversity indices for the total of 127 insect families caught in the traps are presented in (Table5) to give a comparison for the two sampling sites. Yenku Block A recorded the highest family richness (S
=
98) with a diversity ((d
=
14.97) and (H
=
3.827)) in June, but the lowest family richness (S
=
41) and the lowest family diversity (d
=
6.957) in January. Yenku Block B recorded the highest abundance of N
=
1515 with richness of S
=
91 in June. This was reduced to N
=
227 and S
=
42 in January. Insect diversity was the highest at both sites in June (intermediate season).Table 5
Diversity indices for insect families collected from the two sites at Muni-Pomadze, Yenku Block A and Yenku Block B.
Sample
S
N
d
J
′
H
′ (loge)
YBAJUL
59
513
9.294
0.6544
2.668
YBAJAN
41
314
6.957
0.694
2.577
YBAJUN
98
651
14.97
0.8347
3.827
YBBJUL
63
472
10.07
0.8245
3.416
YBBJAN
42
227
7.558
0.8075
3.018
YBBJUN
91
1515
12.29
0.4405
1.987
YBA: Yenku Block A; YBB: Yenku Block B; JUL: July; JAN: January; JUN: June;S: species richness; N: number of individuals; d: Margalef’s index; J
′: Pielou’s evenness index; H
′: Shannon-Wiener index.A cluster analysis using Bray-Curtis similarity was performed for all the insects collected from the traps at both sites for the three sampling seasons (Figure3).Figure 3
Dendrogram of all other insects collected from traps at the two sites in Winneba (YBA and YBB) in July (2011), January, and June, in 2012. The cluster analysis was performed using group-average linking on Bray-Curtis similarity from fourth root transformed abundance data.The insects were averaged over the orders and similarity analyses were performed on all 3720 insects from the 19 orders collected from the traps over the entire sampling period. The cluster analysis revealed three distinct clusters/groupings above a Bray-Curtis similarity 25% (Figure4) with homogeneity below a Bray-Curtis of 20%, indicating, a high level of dissimilarity in distribution. This gives an indication of the evenness of the distributions of insect orders at the Ramsar site.Figure 4
Dendrogram of all insect orders collected from traps at the two sites (YBA and YBB) in July (2011), January, and June, in 2012. The cluster analysis was performed using group-average linking on Bray-Curtis similarity from fourth root transformed abundance data.


## 4.1. Butterflies

130 species of butterflies (Table1) belonging to nine families were recorded during the survey: Nymphalidae, Papilionidae, Hesperiidae, Pieridae, Satyridae, Danaidae, Charaxidae, Acraedae, and Lycaenidae, with the Pieridae dominating with 39 species, followed by Nymphalidae with 37 species.Table 1
Butterfly species recorded over the entire survey period.
Species
Yenku Block A
Yenku Block B
July
January
June
July
January
June
Euryphene barombyna
2
2
1
0
0
1
Euryphenesp.
1
1
0
0
0
0
Euphaedra sarcoptera
12
2
4
0
0
0
Euphaedra edwardsi
2
1
0
0
0
0
Euphedra hapalyce
5
1
2
0
0
0
Euphaedra eleus
2
1
0
0
0
0
Euphaedra medon
9
2
3
0
0
0
Euphaedra crockeri
4
1
2
0
0
0
Euphaedra xypete
14
1
4
0
0
0
Euphaedrasp.
3
0
2
0
0
0
Eurytela dryope
12
3
23
0
0
0
Pseudoacreasp.
9
2
4
55
0
1
Pseudoneptis ianthe
3
0
2
0
0
0
Pseudoneptissp.
1
0
1
0
0
0
Diestogina feronia
2
1
1
0
0
0
Neptis melicerta
3
6
3
3
0
14
Neptis agatha
1
3
5
10
0
4
Neptis metella
2
2
9
2
0
3
Neptis merosa
1
1
3
1
0
0
Neptis seeldrayersi
0
0
2
0
0
0
Salamis anacardii
3
1
1
0
0
0
Junonia terea
43
3
27
2
0
6
Junonia oenone
1
1
2
6
5
60
Junonia octavia
0
11
2
0
0
10
Junoniasp.
2
1
2
1
1
0
Gnophodes chelys
3
3
5
0
0
0
Gnophodes betsimena
0
2
1
0
0
0
Kallima rumia
2
1
3
0
0
0
Phalanta phalanta
13
6
29
75
3
66
Ariadne enotera
8
1
14
0
0
1
Aterica galene
2
1
1
0
0
0
Atericasp.
7
0
1
0
0
0
Byblia achelola
2
4
2
0
0
0
Bybliasp.
1
1
3
0
0
0
Hypolimnas salmacis
2
2
1
0
1
0
Hypolimnas missipus
1
1
2
0
0
0
Hypolimnas dinarcha
1
2
0
0
0
0
Acraea epaea
2
3
5
7
6
13
Acraea zetes
4
5
8
37
13
65
Acraea terpsichore
0
4
7
0
0
24
Acraea pseudolycia
0
0
1
0
0
0
Acraea doubledayi
0
0
2
0
0
0
Acraea egina
1
0
3
0
0
0
Acraeasp.
1
2
4
16
4
11
Bematistis epaea
4
5
6
0
2
14
Hallelesis haliwa
2
1
0
1
0
0
Hallelesissp.
4
1
1
0
0
0
Ypthima itonia
0
1
3
0
0
0
Bicyclus zinebi
11
3
3
1
0
0
Bicyclus safitza
13
2
5
2
0
3
Bicyclus auricruda
0
1
3
0
0
0
Mycalensis safitza
1
1
5
0
0
1
Mycalensissp.
5
0
1
6
0
0
Bicyclus vansoni
0
2
0
0
0
0
Bicyclus condamini
0
1
1
0
0
0
Bicyclus vulgaris
0
1
0
0
0
0
Papilio demodocus
18
8
21
112
11
66
Papilio dardaunus
3
5
2
0
1
0
Papilio nireus
23
4
29
0
0
0
Papilio bromius
3
1
2
0
0
0
Graphium policenes
2
4
3
1
0
1
Papilio menesthius
1
2
1
0
0
2
Amauris niavus
3
2
5
1
0
0
Amauris egialea
2
1
3
1
0
0
Amaurissp.
1
1
2
1
0
0
Danaus chryssipus
2
125
8
13
24
7
Danaus limniace
0
1
2
0
0
0
Eurema brigitta
17
8
9
206
5
40
Eurema senegalensis
9
2
3
16
2
11
Eurema hecabe
6
13
8
3
1
11
Eurema lisa
11
3
4
7
1
0
Eurema brenda
0
0
1
0
0
0
Euremasp.
13
2
5
4
0
0
Colias philodice
4
2
1
0
0
0
Pieris rapae
3
4
6
0
2
26
Pierissp.
4
2
3
1
1
10
Nepheronia thalassina
18
15
21
2
3
29
Nepheronia argia
22
8
18
0
3
35
Nepheroniasp.
5
3
6
0
0
0
Leptosia alcesta
21
8
33
0
0
0
Leptosia medusa
18
10
22
0
0
0
Leptosiasp.
8
3
5
0
0
0
Appias phaola
0
1
3
0
0
0
Dixeia astarte
1
0
8
3
1
0
Dixeia cebon
8
3
23
4
2
3
Colotis erone
9
4
22
7
25
13
Colotis danae
7
2
3
5
8
3
Colotis evippe
12
8
14
11
5
7
Colotis antevippe
18
2
24
20
3
85
Colotis evinina
6
3
9
9
3
62
Colotis eunoma
4
0
5
3
2
5
Anthocharis cardamine
4
4
6
3
0
3
Belinois calypso
68
15
87
12
8
66
Belinois creona
32
5
46
9
1
20
Belinois theora
16
1
19
12
0
14
Belinois gidica
18
4
7
14
0
2
Belinois aurota
14
3
12
21
0
9
Belinois theuszi
9
8
10
7
1
0
Belinois hedyle
0
0
3
0
0
0
Catopsilla florella
78
29
31
21
21
69
Catopsillasp.
42
7
16
5
9
16
Euronia cleodora
0
0
1
0
0
0
Mylothris chloris
56
71
34
23
1
8
Mylothris poppea
34
9
27
5
1
19
Mylothrissp.
51
12
10
4
0
6
Mylothris rhodope
17
8
11
2
0
26
Charaxes varanes
9
2
1
4
0
2
Charaxes protocrea
2
1
1
0
0
0
Charaxes etheocles
0
1
1
0
0
0
Charaxes brutus
0
0
2
0
1
0
Charaxes tiridates
5
1
3
0
0
0
Charaxes cynthia
3
2
4
1
0
0
Charaxes zelica
2
1
3
0
0
0
Euxanthe eurinome
1
0
2
0
0
0
Castalius carana
3
2
1
3
5
12
Lycaena helloides
2
5
3
5
27
0
Lycaenasp.
6
2
1
5
8
0
Meza indusiata
0
3
1
0
8
0
Euchrysops albistriata
5
8
11
3
39
25
Osmodes adon
0
1
0
0
0
0
Spalgis lemolea
0
1
1
0
0
0
Poecilmitis chrysaor
0
0
1
0
0
0
Anthenesp.
0
0
1
0
0
0
Pyrrhiades lucagus
61
103
76
7
0
51
Amblyscirtis vialis
3
2
3
0
1
0
Lerodeasp.
4
3
2
1
0
0
Hesperia leonardus
2
1
4
0
0
2
Hesperiasp.
3
2
1
2
0
1
Oeneis polixenes
2
3
6
1
0
0
Coliades chalyba
0
0
3
0
0
0Table2 gives the diversity indices for the butterfly species for the three sampling seasons. Yenku Block A (YBA) was the most important site for butterflies, with the highest numbers (N
=
1061 and 1011 for July and June, resp.) and the highest species richness (S
=
106, 111, and 122 for July, January, and June, resp.), which was corroborated by the highest Margalef index (d) of 15.07 in July, 16.85 in January, and 17.49 in June. Yenku Block B (YBB) had low butterfly species richness in June (S
=
53) but relatively high abundance (N
=
1064). YBB had the lowest abundance (N
=
269) as well as a relatively low species richness (S
=
41) in January corroborated by the lowest Margalef index (d) 7.15 (Table 2).Table 2
Calculation of suite of diversity indices for butterfly species collected from the two sites at Muni-Pomadze, Yenku Block A and Yenku Block B.
Sample site
S
N
d
J
′
H
′(loge)
YBAJUL
106
1061
15.07
0.8547
3.986
YBAJAN
111
684
16.85
0.7554
3.558
YBAJUN
122
1011
17.49
0.8513
4.09
YBBJUL
60
825
8.786
0.7358
3.013
YBBJAN
41
269
7.15
0.8354
3.102
YBBJUN
53
1064
7.461
0.8602
3.415
YBA: Yenku Block A; YBB: Yenku Block B; JUL: July; JAN: January; JUN: June;S: species richness; N: number of individuals; d: Margalef’s index; J
′: Pielou’s evenness index; H
′: Shannon-Wiener index.Yenku Block B (YBB) recorded a relatively lower evenness, (J
′
=
0.7358) in July. The six species, Eurema brigitta, Papilio demodocus, Catopsilla florella, Acreae zetes, Phalanta phalanta, and Colotis antevippe, made up about 42% of the total numbers recorded at YBB in July. Both sites had a high evenness (J
′
>
0.8354) in the wet (YBAJUL) and intermediate (YBBJUN) seasons (Table 2) with individuals evenly distributed among the different species. Yenku Block A (YBA) recorded a high diversity (Margalef index d
=
16.85) in January but with a low evenness (J
′
=
0.7554) as a result of the dominance of D. chryssipusand Pyrrhiadis lucagus.From the cluster analysis (Figure1) the species population structure could be considered homogenous below a Bray-Curtis similarity of 50%. Homogeneity however begins to break down above 60%, leading to the formation of two clusters of species communities: YBAJAN, YBAJUL, and YBAJUN forming one cluster and YBBJUL and YBBJUN forming the other.Figure 1
Dendrogram of butterfly species at the two sites in Winneba July (2011), January, and June, in 2012. The cluster analysis was performed using group-average linking on Bray-Curtis species similarity from fourth root transformed abundance data.Figure2 is a dendrogram showing the relationships between butterfly species occurring at Muni-Pomadze that contributed abundance of 20 or more using group-average linking on Bray-Curtis species similarity from fourth root transformed abundance data. Above a Bray-Curtis similarity of 60% there is a formation of two clusters with more than 40 forming the main cluster which further breaks down into four distinct clusters around 73%. Red-dotted lines indicate closely related species or species of close associations.Figure 2
Dendrogram of butterfly species occurring at Muni-Pomadze using group-average linking on Bray-Curtis species similarity from fourth root transformed abundance data. The analysis was performed on species contributing abundance of 20 or more.


## 4.2. Dragonflies

Yenku Block B recorded the highest species richness (S
=
10) for dragonflies in July which was corroborated by the highest Shannon-Wiener (H
=
1.9) and Margalef (d
=
2.1) indices. Dragonflies were most abundant in July (N
=
77) at Yenku Block A with the lowest numbers recorded in January at Yenku Block B (N
=
26) (Table 3).Table 3
Diversity indices for Odonata collected from the two sites at Muni-Pomadze, Yenku Block A and Yenku Block B.
Sample
S
N
d
J
′
H
′ (loge)
YBAJUL
7
77
1.381
0.7476
1.455
YBBJUL
10
68
2.133
0.8306
1.912
YBAJAN
7
69
1.417
0.6608
1.286
YBBJAN
5
26
1.228
0.8906
1.433
YBAJUN
8
44
1.85
0.776
1.614
YBBJUN
8
40
1.898
0.8874
1.845
YBA: Yenku Block A; YBB: Yenku Block B; JUL: July; JAN: January; JUN: June;S: species richness; N: number of individuals; d: Margalef’s index; J
′: Pielou’s evenness index; H
′: Shannon-Wiener index.


## 4.3. Other Insects

A total of 3720 insects belonging to 19 other insect orders were recorded from the traps. Diptera was the most abundant (1932) as well as the most diverse order with 36 families, followed by Coleoptera with 21 families and Hymenoptera with 13 families (Table4).Table 4
Insects families recorded over the entire survey period.
Yenku Block A
Yenku Block B
Family
July
January
June
July
January
June
Gryllidae
8
7
15
6
13
11
Acrididae
6
6
4
7
5
14
Tettigonidae
3
0
4
12
3
3
Tridactylidae
0
2
5
0
1
4
Tetrigidae
2
1
1
6
2
1
Formicidae
81
96
31
75
39
29
Apidae
6
0
8
4
1
5
Evaniidae
1
3
1
3
1
1
Sphecidae
2
2
5
0
1
8
Vespidae
0
3
11
0
1
6
Braconidae
3
7
13
8
6
15
Ichneumonidae
2
2
4
4
1
3
Scelionidae
0
3
2
1
2
1
Halictidae
0
1
2
2
1
1
Pompylidae
1
0
4
0
0
3
Chalcididae
0
2
2
0
1
4
Eulophidae
1
0
3
0
2
4
Tiphiidae
2
0
1
0
0
0
Blattidae
6
5
9
1
4
1
Mantidae
2
0
1
0
0
1
Noctuidae
3
4
2
0
0
4
Arctidae
0
1
0
1
0
2
Satyridae
2
0
2
0
0
3
Pieridae
0
0
3
1
1
2
Acraeidae
0
0
1
1
0
0
Nymphalidae
0
1
2
2
0
0
Termitidae
1
1
2
0
2
5
Rhinotermitidae
0
0
1
0
0
2
Kalotermitidae
2
0
0
0
0
1
Cercopidae
5
11
6
10
26
8
Aleyrodidae
0
2
4
0
0
0
Aphididae
0
0
3
0
0
0
Fulgoridae
0
0
1
0
0
0
Cicadellidae
2
3
13
17
9
13
Delphacidae
0
0
2
3
2
2
Membracidae
0
1
0
0
0
1
Pseudococcidae
0
0
1
0
0
1
Dictyopharidae
1
0
0
2
0
1
Psyllidae
0
0
3
0
3
4
Acanalonidae
1
0
0
0
0
1
Flatidae
0
0
1
0
0
0
Isotomidae
3
33
22
1
32
27
Calliphoridae
2
2
5
31
2
3
Sepsidae
0
0
3
5
0
0
Tachinidae
4
5
13
0
12
19
Sarcophagidae
3
1
15
1
3
6
Culicidae
1
5
8
34
6
17
Muscidae
2
1
9
3
1
7
Tephritidae
69
24
29
4
5
22
Drossophilidae
1
53
24
3
5
993
Phoridae
11
14
24
7
15
28
Tipulidae
4
0
2
0
0
3
Asilidae
0
0
2
7
0
4
Diopsidae
0
0
0
0
0
1
Dolichopodidae
1
1
2
9
0
4
Syrrphidae
2
1
7
5
2
10
Rhagionidae
0
0
1
0
0
3
Stratiomyiidae
0
0
2
0
0
1
Bombylidae
2
0
2
1
0
1
Tabanidae
19
0
28
1
0
3
Glossinidae
1
0
92
0
0
8
Simulidae
2
0
0
3
0
1
Mycetophilidae
0
0
4
0
0
9
Sciaridae
0
0
2
0
0
6
Chironomidae
0
0
0
3
0
1
Ceratopogonidae
0
0
3
0
0
2
Conopidae
0
0
2
3
0
0
Lauxanidae
0
0
0
0
0
2
Psychodidae
0
0
1
0
0
0
Cecidomyiidae
1
0
2
0
0
0
Platypezidae
0
0
1
0
0
0
Trichoceridae
0
0
1
0
0
4
Acroceridae
0
0
0
0
0
2
Empididae
0
0
2
13
0
18
Therevidae
1
0
3
0
3
1
Otitidae
0
0
12
0
0
3
Anthomyiidae
0
0
0
8
0
11
Bibionidae
0
0
0
7
0
3
Chrysomelidae
11
3
12
19
2
8
Carabidae
23
0
14
8
4
2
Tenebrionidae
3
1
6
1
0
0
Scarabaeidae
167
0
44
2
0
2
Mordellidae
5
0
1
8
1
1
Phalacridae
0
0
2
0
0
1
Coccinellidae
2
0
0
0
3
0
Dermestidae
0
0
0
4
0
0
Meloidae
0
0
0
3
0
0
Curcujidae
0
1
6
0
0
14
Scolytidae
0
0
1
1
0
0
Lampyridae
0
0
5
13
0
2
Staphylinidae
5
0
15
52
0
51
Ptinidae
0
0
1
0
0
1
Lucanidae
0
0
2
0
0
1
Hesteridae
0
0
2
0
0
0
Anthicidae
0
0
0
0
0
1
Cleridae
0
0
0
0
0
1
Scaphididae
0
0
2
0
0
0
Curculionidae
5
0
6
1
0
6
Cerambycidae
1
0
1
0
0
2
Hydropsychidae
5
0
3
14
0
4
Polycentropodidae
3
0
0
0
0
5
Philopotamidae
0
0
1
4
0
0
Leptoceridae
2
0
1
10
0
2
Psychomyiidae
0
0
0
2
0
0
Thripidae
2
0
7
7
1
13
Forfinculidae
1
0
2
0
0
1
Labiidae
0
0
2
0
1
0
Carcinophoridae
0
1
1
0
0
2
Libellulidae
1
0
2
0
0
1
Coenagrionidae
0
0
0
0
0
1
Pyrrhocoridae
1
1
3
2
0
3
Coreidae
1
0
1
2
0
0
Pentatomidae
3
1
3
1
0
2
Reduvidae
0
1
3
1
2
1
Lygaeidae
0
0
2
1
1
2
Berytidae
0
1
1
0
0
0
Largidae
2
0
0
0
1
1
Nepidae
0
0
0
1
0
0
Alydidae
0
0
1
1
0
0
Cydnidae
1
0
2
0
0
1
Thyreocoridae
1
0
1
0
0
2
Ascalaphidae
0
0
1
0
0
0
Sialidae
0
0
0
1
0
0
Phasmatidae
1
0
3
0
0
1
Oligotomidae
0
0
1
0
0
0
Machilidae
0
0
0
0
0
1
Panorpidae
0
0
0
0
0
1The diversity indices for the total of 127 insect families caught in the traps are presented in (Table5) to give a comparison for the two sampling sites. Yenku Block A recorded the highest family richness (S
=
98) with a diversity ((d
=
14.97) and (H
=
3.827)) in June, but the lowest family richness (S
=
41) and the lowest family diversity (d
=
6.957) in January. Yenku Block B recorded the highest abundance of N
=
1515 with richness of S
=
91 in June. This was reduced to N
=
227 and S
=
42 in January. Insect diversity was the highest at both sites in June (intermediate season).Table 5
Diversity indices for insect families collected from the two sites at Muni-Pomadze, Yenku Block A and Yenku Block B.
Sample
S
N
d
J
′
H
′ (loge)
YBAJUL
59
513
9.294
0.6544
2.668
YBAJAN
41
314
6.957
0.694
2.577
YBAJUN
98
651
14.97
0.8347
3.827
YBBJUL
63
472
10.07
0.8245
3.416
YBBJAN
42
227
7.558
0.8075
3.018
YBBJUN
91
1515
12.29
0.4405
1.987
YBA: Yenku Block A; YBB: Yenku Block B; JUL: July; JAN: January; JUN: June;S: species richness; N: number of individuals; d: Margalef’s index; J
′: Pielou’s evenness index; H
′: Shannon-Wiener index.A cluster analysis using Bray-Curtis similarity was performed for all the insects collected from the traps at both sites for the three sampling seasons (Figure3).Figure 3
Dendrogram of all other insects collected from traps at the two sites in Winneba (YBA and YBB) in July (2011), January, and June, in 2012. The cluster analysis was performed using group-average linking on Bray-Curtis similarity from fourth root transformed abundance data.The insects were averaged over the orders and similarity analyses were performed on all 3720 insects from the 19 orders collected from the traps over the entire sampling period. The cluster analysis revealed three distinct clusters/groupings above a Bray-Curtis similarity 25% (Figure4) with homogeneity below a Bray-Curtis of 20%, indicating, a high level of dissimilarity in distribution. This gives an indication of the evenness of the distributions of insect orders at the Ramsar site.Figure 4
Dendrogram of all insect orders collected from traps at the two sites (YBA and YBB) in July (2011), January, and June, in 2012. The cluster analysis was performed using group-average linking on Bray-Curtis similarity from fourth root transformed abundance data.


## 5. Discussion

### 5.1. Butterflies

130 species of butterflies belonging to nine families were recorded during the survey. From the diversity indices for the butterfly species calculated for the three sampling seasons, the lowest abundance of butterflies at YBB in January (N
=
269) as well as a relatively low species richness (S
=
41) corroborated by the lowest Margalef index (d) 7.15 can be attributed to the fact that in January most of the vegetation covers at Yenku Block B (YBB) had been removed by burning, a common practice for that time of the year. This was in contrast to a study on butterflies of two sacred grooves in the Eastern Region of Ghana carried out by Nganso et al. [23] which reported that butterflies were more speciose and diverse in the dry season most probably due to higher temperatures.The low evenness (J
′
=
0.7358) at YBB in July can be attributed to the dominance of Eurema brigitta, Papilio demodocus, Catopsilla florella, Acreae zetes, Phalanta phalanta, and Colotis antevippewhich constituted about 42% of the total numbers recorded at YBB. These are typically open country, grassland species, and their dominance at Yenku Block B was not surprising given the open nature of the vegetation which allows for free flight and easy movement.Factors such as resource availability for adults and larval host plants, behavioural traits, and interaction with other species [21] may explain the increase in butterfly richness and diversity during the dry season at YBA. This underscores the importance of measuring and documenting local conditions as part of studies to determine species composition, even though these factors were not adequately measured in this survey.Although Yenku Block A (YBA) recorded a high diversity (Margalef indexd
=
16.85) in January, its low evenness (J
′
=
0.7554) was due to the dominance of Danaus chryssipusand Pyrrhiadis lucagus. Pyrrhiades lucagus, a fast flier from the family Hesperiidae was observed in large numbers along the fringes of the forest and also in the Teak and Acacia plantations at Yenku Block A, most probably feeding on the nectar from their flowers. D. chryssipus, though an open savannah species, was found in large numbers at Yenku Block A where portions of the Eucalytus plantation had been cut down and converted to maize and cassava farmlands, providing adequate food resources as well as pockets of open areas for easy flight for these species. Their larvae feed on milkweed (Asclepias spp.) and other related species.The species population structure could be considered homogenous, below a Bray-Curtis similarity of about 53%, however, homogeneity begins to break down leading to the formation of two clusters of species communities around 58%: YBBJUL, YBAJUL, YBAJUN, and YBBJUN forming one cluster and YBAJAN and YBBJAN forming the other (Figure1). From the cluster analysis Pyrrhiades lucagus, Danaus chrysippus, Mylothris chloris, Belinois calypso,andCatopsilla florella, for example, (linked by red-dotted lines) cluster above a Bray-Curtis similarity of 80% (Figure 2). Each of these five species was recorded in excess of 150 individuals. They have similar behavioural traits and most feed on the same or related plant species and so their clustering together is to be expected.Species of butterflies such asPapilio demodocus, P. nireus, Junonia oenone, and J. terea are known to be now much more common in West Africa than they ever were due to the widespread destruction and fragmentation of forest cover that has taken place in this part of Africa [24]. They are specialized in degraded habitats and open spaces and very few would ever be met within forest of good condition. Papillio demodocuswas observed in large numbers in the open grassland areas and also along the beach close to the Muni Lagoon. Junonia oenone, for example, though common to both sites, was recorded mainly as singletons at Yenku Block A but in much larger numbers in the thickets and grasslands along the coastal villages of Mankoaze and Akosua which were sampled as part of Yenku Block B. The presence of these species, especially at Yenku Block A, is therefore a clear indication of the forest degradation that has taken place at this site and thus can be considered as clear-cut indicator species of forest disturbance. In theory, these species are known to be generally common to have fairly wide ranges and to colonize both intact and disturbed forests [6]. The high numbers especially of J. terea and P. nireus recorded at Yenku Block A also suggest that the degraded forest at Yenku Block A is not in a particularly good shape.Species common to both sites werePhalanta phalanta, Acraea zetis, Danaus chryssipus, Eurema brigitta (which was the second most abundant species recorded), Catopssila florella, Colotis evippe and Colotis antevippe. Species such as Nepheronia thalassina, Nepheronia argia, Belinois calypso, Mylothris chloris, and Mylothris poppea, though common to both sites, were more abundant at Yenku Block A, a degraded natural forest interspersed with pockets of farmlands, Eucalyptus, Teak, and Acacia plantations with a few thickets of dense shrubs. These species are commonly found in African woodlands.Satyrids are generally dusty to dark brown and blend well with the dark vegetation of forested areas and forest undergrowths and are associated with grasses. Species such asBicyclus safitza and B. zinebi which are associated with woodland and forests throughout Africa [15] were recorded in relatively larger numbers at Yenku Block A. The increased presence of grass-feeding Satyrine species is an apparent sign of forest disturbance [24]. Grasses are generally uncommon on the Afrotropical forest floor [25] but can colonize and spread in abundance when light penetration into the forest proper increases as a result of, for example, increased edge to interior habitat or degradation of the forest canopy [26]. This coupled dynamic between grasses and Satyrines also signals the high potential of this group as indicators of forest condition, an attribute that could be beneficially exploited to help direct limited conservation resources in economically disadvantaged countries, for example, to identify priority sites for formal protection or to steer restoration efforts [26].Most of the eight species ofEuphaedra such as E. crockeri and E. eleus were found along footpaths deep in the forests of Yenku Block A. Nepheronia spp. are high fast fliers which can be seen darting in and out of the top of trees and so were recorded in larger numbers at Yenku Block A which had more trees than Yenku Block B, a more grassland open area.The Lycaenids such asLycaena helloides, Castalius carana, and Euchrysops albistriatawere found around drying puddles of water and along paths and roads in relatively larger numbers at Yenku Block B. Most of these butterflies are associated with ants that were abundant in the sampled areas.


### 5.2. Odonata

Dragonflies are relatively ever-present in freshwater wetlands, and occupy a critical trophic niche in these systems. The adults are easily sampled; they are insects that are susceptible to human disturbance and constitute good candidates for wetlands assessment [27]. Dragonflies can serve as biological indicators of environmental health [28–30]. According to [1] vegetation covering can lead to a decline in population of adult dragonflies or, in contrast, cause an increase in the species diversity according to Clark and Samways [31] and Acquah-Lamptey et al. [28].All the dragonfly species recorded in Yenku Blocks A and B are widespread species and therefore classified as of least concern [32]. The presence of species such as Pantala flavescens and Tramea basilarisindicate open areas or nearness to open areas, whereas the presence of Phoan iridipennis infer that the area it occurred in is adequately shaded, occurring especially in gallery forests [33]. Crocothemis erythreae is an open area species and usually prefers areas close to large water bodies which was the case at YBB. Palpopleura lucia and Orthetrum julia are known to be widespread and very common species; hence the high abundance recorded in this study was expected.


### 5.3. Other Insects

A total of 3720 insects belonging to 19 orders were recorded from the traps. Diptera was the most abundant (1932) as well as the most diverse order with 36 families, followed by Coleoptera with 21 families and Hymenoptera with 13 families. The high numbers of Dipterans may have resulted from the use of the Malaise traps and the flight interception traps employed in this study which are basically designed to trap small flying insects, mainly Diptera and Hymenoptera. They were set up close to streams and many of the insects recorded were aquatic species that may have been trapped on emergence or as they came to lay eggs in or close to the water. Flight interception traps are also designed to intercept the flight of small to medium-sized flying insects. In a baseline survey conducted in 1997 [8], 3151 insects belonging to 15 orders were recorded with Coleoptera, being the most abundant order (1258 individuals) followed by Hymenoptera (716) and Lepidoptera (416 individuals).Insect diversity was the highest at both sites in June (intermediate season) most probably because, during this time of the year, there are ample food resources for the insects and rainfall is not too heavy since heavy rainfall sweeps most insects away and destroys many of their food resources. The high numbers of Dipterans accounted for the highest abundance (N
=
1515) and the lowest evenness (J
′
=
0.4405) at Yenku Block B in June. Most of the Dipterans sampled were aquatic and at this time of the year water levels are just right for them whereas during the wet season most of these Dipterans as well as other aquatic insects are swept away or dislodged during the heavy rains.From the cluster analysis the insect species composition at Yenku Blocks A and B had a fairly similar species distribution for June and July (Figure3). There was a distinct cluster of species communities for both Yenku Blocks A and B in January indicating similar species composition and distribution, as was the case for the butterfly species composition, the burning that had occurred during the dry season accounted for the low numbers and diversity at both sites during the January sampling. The dominance of Hymenoptera, Diptera, Collembola, Orthoptera, and Homoptera at both sampling sites in January may explain the similarity.The cluster analysis performed on the insect orders revealed three distinct clusters/groupings above a Bray-Curtis similarity 25% with homogeneity below a Bray-Curtis of 20%, indicating a high level of dissimilarity in distribution (Figure4). It is not surprising that Thysanura and Mecoptera form outside the three main clusters since they have a similar distribution spending most or part of their life cycle in moist decaying vegetation and soil. Thysanura are among the most primitive of all insects.It is interesting to note that Diptera, Hymenoptera, and Coleoptera cluster together around 95% indicating a high level of similarity in distribution. These three orders contributed to 81% of the entire insect collection from the traps at both sites.The presence of dung beetles, Scarabaeidae, in large numbers at Yenku Block A during the wet season sampling is an indication of the presence of large mammals at this site which is typical for the kind of vegetation found at the site.


### 5.4. Changes in Insect Species Composition over the Twenty Years of Site Designation as a Ramsar Site

The total number of species recorded in the current study and composition of the various taxonomic groups suggest an increase in insect abundance when compared with the findings in the 1997 survey. However, with the exception of butterflies, a direct comparison of overall insect abundance recorded in the two studies would not be appropriate because of the limited range of techniques and different sampling methods used in the 1997 study. The sampling methods used for butterflies in the two studies were similar and therefore the results are comparable. 74 (57% of the total) butterfly species were common to both Yenku Blocks A and B in this survey as compared to 22 species (29.3% of the total) that were common to both sites in 1997 [8]. 56 species (43% of the total) were recorded only in Yenku Block A compared to 32 species (42.6% of the total) in 1997. The 130 species of butterflies from 9 families recorded in the current survey is an increase from the 75 species from five families recorded during the 1997 baseline survey [8]. Species such as Charaxes fulvescens, Graphium adamastor, Belinois ianthe, and Bebearia sophus were recorded in the 1997 survey but not in the current survey. Many species belonging to the genera Belinois, Mylothris, Eurema, Euphaedra, Colotis, and Acraea look similar in flight and can only be properly identified when captured and critically examined. The fewer number of those species recorded by Gordon and Cobblah [8] may therefore be accounted for by the fact that their records may have been based mostly on insects observed in flight and hence the possibility of mixing up these species.No butterfly species were recorded only in Yenku Block B in the current survey; however Gordon and Cobblah [8] recorded two species (2.7% of the total) that were found only at Mankoadze (Yenku Block B) in 1997. Gordon and Cobblah [8] state that several of the butterfly species such as Papilio demodocus, P. nireus, Neptis morosa, Bicyclus safitza, and Charaxes varanes recorded at Mankoadze (Yenku Block B) were strongly associated with thickets. However in the current study, P. nireus was not recorded at Yenku Block B but was rather observed in relatively large numbers at Yenku Block A darting between the Acacia trees and the open fields that had been cultivated with maize and cassava. Neptis merosa was recorded only as a singleton at Yenku Block B.Many habitat changes had occurred at the Ramsar site since its designation in 1992. The presence of pockets of farmlands created from portions of the Eucalytus plantation within Yenku Block A that had been cut down and converted to maize and cassava farmlands, for example, had created a wider range of habitat types and adequate food resources as well as pockets of open areas for easy flight allowing for the colonization of more butterfly species. At the initial stages of habitat loss, new habitats occur as gaps within the original habitat; however, as the proportion of new habitats increases in the landscape, the remaining areas of original habitat will be smaller and more isolated from one another [34].


## 5.1. Butterflies

130 species of butterflies belonging to nine families were recorded during the survey. From the diversity indices for the butterfly species calculated for the three sampling seasons, the lowest abundance of butterflies at YBB in January (N
=
269) as well as a relatively low species richness (S
=
41) corroborated by the lowest Margalef index (d) 7.15 can be attributed to the fact that in January most of the vegetation covers at Yenku Block B (YBB) had been removed by burning, a common practice for that time of the year. This was in contrast to a study on butterflies of two sacred grooves in the Eastern Region of Ghana carried out by Nganso et al. [23] which reported that butterflies were more speciose and diverse in the dry season most probably due to higher temperatures.The low evenness (J
′
=
0.7358) at YBB in July can be attributed to the dominance of Eurema brigitta, Papilio demodocus, Catopsilla florella, Acreae zetes, Phalanta phalanta, and Colotis antevippewhich constituted about 42% of the total numbers recorded at YBB. These are typically open country, grassland species, and their dominance at Yenku Block B was not surprising given the open nature of the vegetation which allows for free flight and easy movement.Factors such as resource availability for adults and larval host plants, behavioural traits, and interaction with other species [21] may explain the increase in butterfly richness and diversity during the dry season at YBA. This underscores the importance of measuring and documenting local conditions as part of studies to determine species composition, even though these factors were not adequately measured in this survey.Although Yenku Block A (YBA) recorded a high diversity (Margalef indexd
=
16.85) in January, its low evenness (J
′
=
0.7554) was due to the dominance of Danaus chryssipusand Pyrrhiadis lucagus. Pyrrhiades lucagus, a fast flier from the family Hesperiidae was observed in large numbers along the fringes of the forest and also in the Teak and Acacia plantations at Yenku Block A, most probably feeding on the nectar from their flowers. D. chryssipus, though an open savannah species, was found in large numbers at Yenku Block A where portions of the Eucalytus plantation had been cut down and converted to maize and cassava farmlands, providing adequate food resources as well as pockets of open areas for easy flight for these species. Their larvae feed on milkweed (Asclepias spp.) and other related species.The species population structure could be considered homogenous, below a Bray-Curtis similarity of about 53%, however, homogeneity begins to break down leading to the formation of two clusters of species communities around 58%: YBBJUL, YBAJUL, YBAJUN, and YBBJUN forming one cluster and YBAJAN and YBBJAN forming the other (Figure1). From the cluster analysis Pyrrhiades lucagus, Danaus chrysippus, Mylothris chloris, Belinois calypso,andCatopsilla florella, for example, (linked by red-dotted lines) cluster above a Bray-Curtis similarity of 80% (Figure 2). Each of these five species was recorded in excess of 150 individuals. They have similar behavioural traits and most feed on the same or related plant species and so their clustering together is to be expected.Species of butterflies such asPapilio demodocus, P. nireus, Junonia oenone, and J. terea are known to be now much more common in West Africa than they ever were due to the widespread destruction and fragmentation of forest cover that has taken place in this part of Africa [24]. They are specialized in degraded habitats and open spaces and very few would ever be met within forest of good condition. Papillio demodocuswas observed in large numbers in the open grassland areas and also along the beach close to the Muni Lagoon. Junonia oenone, for example, though common to both sites, was recorded mainly as singletons at Yenku Block A but in much larger numbers in the thickets and grasslands along the coastal villages of Mankoaze and Akosua which were sampled as part of Yenku Block B. The presence of these species, especially at Yenku Block A, is therefore a clear indication of the forest degradation that has taken place at this site and thus can be considered as clear-cut indicator species of forest disturbance. In theory, these species are known to be generally common to have fairly wide ranges and to colonize both intact and disturbed forests [6]. The high numbers especially of J. terea and P. nireus recorded at Yenku Block A also suggest that the degraded forest at Yenku Block A is not in a particularly good shape.Species common to both sites werePhalanta phalanta, Acraea zetis, Danaus chryssipus, Eurema brigitta (which was the second most abundant species recorded), Catopssila florella, Colotis evippe and Colotis antevippe. Species such as Nepheronia thalassina, Nepheronia argia, Belinois calypso, Mylothris chloris, and Mylothris poppea, though common to both sites, were more abundant at Yenku Block A, a degraded natural forest interspersed with pockets of farmlands, Eucalyptus, Teak, and Acacia plantations with a few thickets of dense shrubs. These species are commonly found in African woodlands.Satyrids are generally dusty to dark brown and blend well with the dark vegetation of forested areas and forest undergrowths and are associated with grasses. Species such asBicyclus safitza and B. zinebi which are associated with woodland and forests throughout Africa [15] were recorded in relatively larger numbers at Yenku Block A. The increased presence of grass-feeding Satyrine species is an apparent sign of forest disturbance [24]. Grasses are generally uncommon on the Afrotropical forest floor [25] but can colonize and spread in abundance when light penetration into the forest proper increases as a result of, for example, increased edge to interior habitat or degradation of the forest canopy [26]. This coupled dynamic between grasses and Satyrines also signals the high potential of this group as indicators of forest condition, an attribute that could be beneficially exploited to help direct limited conservation resources in economically disadvantaged countries, for example, to identify priority sites for formal protection or to steer restoration efforts [26].Most of the eight species ofEuphaedra such as E. crockeri and E. eleus were found along footpaths deep in the forests of Yenku Block A. Nepheronia spp. are high fast fliers which can be seen darting in and out of the top of trees and so were recorded in larger numbers at Yenku Block A which had more trees than Yenku Block B, a more grassland open area.The Lycaenids such asLycaena helloides, Castalius carana, and Euchrysops albistriatawere found around drying puddles of water and along paths and roads in relatively larger numbers at Yenku Block B. Most of these butterflies are associated with ants that were abundant in the sampled areas.


## 5.2. Odonata

Dragonflies are relatively ever-present in freshwater wetlands, and occupy a critical trophic niche in these systems. The adults are easily sampled; they are insects that are susceptible to human disturbance and constitute good candidates for wetlands assessment [27]. Dragonflies can serve as biological indicators of environmental health [28–30]. According to [1] vegetation covering can lead to a decline in population of adult dragonflies or, in contrast, cause an increase in the species diversity according to Clark and Samways [31] and Acquah-Lamptey et al. [28].All the dragonfly species recorded in Yenku Blocks A and B are widespread species and therefore classified as of least concern [32]. The presence of species such as Pantala flavescens and Tramea basilarisindicate open areas or nearness to open areas, whereas the presence of Phoan iridipennis infer that the area it occurred in is adequately shaded, occurring especially in gallery forests [33]. Crocothemis erythreae is an open area species and usually prefers areas close to large water bodies which was the case at YBB. Palpopleura lucia and Orthetrum julia are known to be widespread and very common species; hence the high abundance recorded in this study was expected.


## 5.3. Other Insects

A total of 3720 insects belonging to 19 orders were recorded from the traps. Diptera was the most abundant (1932) as well as the most diverse order with 36 families, followed by Coleoptera with 21 families and Hymenoptera with 13 families. The high numbers of Dipterans may have resulted from the use of the Malaise traps and the flight interception traps employed in this study which are basically designed to trap small flying insects, mainly Diptera and Hymenoptera. They were set up close to streams and many of the insects recorded were aquatic species that may have been trapped on emergence or as they came to lay eggs in or close to the water. Flight interception traps are also designed to intercept the flight of small to medium-sized flying insects. In a baseline survey conducted in 1997 [8], 3151 insects belonging to 15 orders were recorded with Coleoptera, being the most abundant order (1258 individuals) followed by Hymenoptera (716) and Lepidoptera (416 individuals).Insect diversity was the highest at both sites in June (intermediate season) most probably because, during this time of the year, there are ample food resources for the insects and rainfall is not too heavy since heavy rainfall sweeps most insects away and destroys many of their food resources. The high numbers of Dipterans accounted for the highest abundance (N
=
1515) and the lowest evenness (J
′
=
0.4405) at Yenku Block B in June. Most of the Dipterans sampled were aquatic and at this time of the year water levels are just right for them whereas during the wet season most of these Dipterans as well as other aquatic insects are swept away or dislodged during the heavy rains.From the cluster analysis the insect species composition at Yenku Blocks A and B had a fairly similar species distribution for June and July (Figure3). There was a distinct cluster of species communities for both Yenku Blocks A and B in January indicating similar species composition and distribution, as was the case for the butterfly species composition, the burning that had occurred during the dry season accounted for the low numbers and diversity at both sites during the January sampling. The dominance of Hymenoptera, Diptera, Collembola, Orthoptera, and Homoptera at both sampling sites in January may explain the similarity.The cluster analysis performed on the insect orders revealed three distinct clusters/groupings above a Bray-Curtis similarity 25% with homogeneity below a Bray-Curtis of 20%, indicating a high level of dissimilarity in distribution (Figure4). It is not surprising that Thysanura and Mecoptera form outside the three main clusters since they have a similar distribution spending most or part of their life cycle in moist decaying vegetation and soil. Thysanura are among the most primitive of all insects.It is interesting to note that Diptera, Hymenoptera, and Coleoptera cluster together around 95% indicating a high level of similarity in distribution. These three orders contributed to 81% of the entire insect collection from the traps at both sites.The presence of dung beetles, Scarabaeidae, in large numbers at Yenku Block A during the wet season sampling is an indication of the presence of large mammals at this site which is typical for the kind of vegetation found at the site.


## 5.4. Changes in Insect Species Composition over the Twenty Years of Site Designation as a Ramsar Site

The total number of species recorded in the current study and composition of the various taxonomic groups suggest an increase in insect abundance when compared with the findings in the 1997 survey. However, with the exception of butterflies, a direct comparison of overall insect abundance recorded in the two studies would not be appropriate because of the limited range of techniques and different sampling methods used in the 1997 study. The sampling methods used for butterflies in the two studies were similar and therefore the results are comparable. 74 (57% of the total) butterfly species were common to both Yenku Blocks A and B in this survey as compared to 22 species (29.3% of the total) that were common to both sites in 1997 [8]. 56 species (43% of the total) were recorded only in Yenku Block A compared to 32 species (42.6% of the total) in 1997. The 130 species of butterflies from 9 families recorded in the current survey is an increase from the 75 species from five families recorded during the 1997 baseline survey [8]. Species such as Charaxes fulvescens, Graphium adamastor, Belinois ianthe, and Bebearia sophus were recorded in the 1997 survey but not in the current survey. Many species belonging to the genera Belinois, Mylothris, Eurema, Euphaedra, Colotis, and Acraea look similar in flight and can only be properly identified when captured and critically examined. The fewer number of those species recorded by Gordon and Cobblah [8] may therefore be accounted for by the fact that their records may have been based mostly on insects observed in flight and hence the possibility of mixing up these species.No butterfly species were recorded only in Yenku Block B in the current survey; however Gordon and Cobblah [8] recorded two species (2.7% of the total) that were found only at Mankoadze (Yenku Block B) in 1997. Gordon and Cobblah [8] state that several of the butterfly species such as Papilio demodocus, P. nireus, Neptis morosa, Bicyclus safitza, and Charaxes varanes recorded at Mankoadze (Yenku Block B) were strongly associated with thickets. However in the current study, P. nireus was not recorded at Yenku Block B but was rather observed in relatively large numbers at Yenku Block A darting between the Acacia trees and the open fields that had been cultivated with maize and cassava. Neptis merosa was recorded only as a singleton at Yenku Block B.Many habitat changes had occurred at the Ramsar site since its designation in 1992. The presence of pockets of farmlands created from portions of the Eucalytus plantation within Yenku Block A that had been cut down and converted to maize and cassava farmlands, for example, had created a wider range of habitat types and adequate food resources as well as pockets of open areas for easy flight allowing for the colonization of more butterfly species. At the initial stages of habitat loss, new habitats occur as gaps within the original habitat; however, as the proportion of new habitats increases in the landscape, the remaining areas of original habitat will be smaller and more isolated from one another [34].


## 6. Conclusion

The survey revealed high levels of insect diversity at the Muni-Pomadze Ramsar site with 134 insect families belonging to 19 orders recorded, including 130 species of butterflies. Butterfly species richness was greater at Yenku Block A (130) than at Yenku Block B (74). As was the case in a survey conducted in 1997 [35], there were clear differences in butterfly fauna of the two sites which represented somewhat different habitats. These differences indicate a fine grained response by the butterfly communities to habitat changes and confirm the suggestion by [8] that butterfly monitoring at Muni would provide useful ecological indicator data to compliment those of mammals, birds, and plant species monitoring.Species such asJunonia oenone, J. terea, Papillio nireus, and P. demodocus are specialized in degraded habitats and open spaces and very few would ever be met within forest of good condition. Their presence especially at Yenku Block A in relatively large numbers is a clear indication of forest degradation (the result of the conversion of parts of the forest into farmlands).The presence of deep forest species such asSalamis anacardii, Euphaedra crokeri, Charaxes tiridatus, Hypolimnas salmacis, and Diestogina feronia however is welcome news and an indication that some parts of this reserve are still in good shape. Obviously, the forests areas at Muni-Pomadze serve as refuges for displaced species from areas where farming and other human activities have disturbed these insects.The Muni-Pomadzi Ramsar site is still in a relatively good condition although more efforts should be put in place by the Forestry Commission of Ghana to maintain it and prevent encroachment by farmers and loggers since it is a site for conservation not only in Ghana but also in West Africa.



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*Source: 985684-2014-02-20.xml*