View of Effects of Land-Use Change on Under Storey Species Composition and Distribution in a Tropical Rainforest

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Effects of Land-Use Change on Under Storey Species Composition and Distribution in Tropical Rainforest

Anthony Ifechukwude ODIWE

¹*,

Joshua Oluwole OLOWOYO

²,

Olufemi AJIBOYE

¹

1Obafemi Awolowo University, Department of Botany, O.A.U. P. O. Box. 1992, Ile- Ife, Osun State, Nigeria; [email protected] (*corresponding author)

2University of Limpopo, Department of Biology, P. O. Box 139, Medunsa Campus, Garankuwa, Pretoria, 0204, South Africa

Abstract

The forest land’s conversion into tree crops plantations plays a major role in the loss of biodiversity. Therefore, understanding the impacts of land-use change on species diversity is very critical for ecosystem functioning and stability. This study was carried out to evaluate the effect of land-use changes on under storey species diversity in the Theobroma cacao and Citrus sinensis plantations. Two, 25 m × 25 m plots were sampled in each plantation and a nearby undisturbed secondary rainforest for comparison. The diameters (dbh-1.3 m) of all trees at breast height >10 cm were measured in each plot. Five line transect were systematically laid and a quadrat of 50 cm × 50 cm placed at every 1 m point to identify the under storey species (herbaceous, shrubs, tree saplings and climbers) present in each plot.

Percentage canopy, species diversity using Shannon-Wiener, Simpson’s index and Evenness were determined, while species similarity was determined using the Jaccard’s similarity index. Results indicate that woody basal area and stem density in Theobroma cacao were significantly (P<0.05) higher than the Citrus sinensis plantation. A total number of 25, 27, and 14 under storey species distributed in 16, 19 and 11 families were found in Theobroma cacao, Citrus sinensis plantations and secondary forest respectively. Panicum maximum and Axonopus compressus were the dominant grasses in the Theobroma cacao and Citrus sinensis plantations respectively. The percentage canopy cover was significantly (P<0.05) higher in the secondary forest than the plantations. The land use modification has significantly increased the under storey species composition.

Keywords: land-use change, under storey species, biodiversity, plantations, species diversity

Introduction

The lowland rainforest has been reported to be the most species-rich terrestrial ecosystem having more than 50-70% of all living organisms on approximately 6-7% of the land area (Linsenmair, 1990, 1997; Wilson, 1992).

The forests, being continuously cut down in order to build facilities for industrial complexes or to provide products for industrial development (Sanderson et al., 2004) and this has continued at a very alarming rate (Pimm et al., 1995; Prance et al., 2000). The continuous degradation of the forest reserve base has been reported to lead to the rap- id disappearance of forest cover leading to erosion, loss of biological diversity, soil degradation, and unfavorable hy- drological changes (Aweto 2000, 2001; Aweto and Ekuig- bo, 1994). It has been pointed out that about 8% of the scientifically known plant species on earth are presently on the verge of being wiped out (Chapin et al., 2000).

The impacts that have been of primary concern are the effects of land-use change on biological diversity, soil degradation and the ability of biological systems to support human needs. Tree crop species plantation has become mostly planted in most countries due to the fact that it is fast-growing and because of the economic value (Lavery

and Mead, 1998). Over the years, plantations of fast-growing exotic tree species have become increasingly important land use in the tropical regions with following tree crops species; Theobroma cacao, Cola nitida, Coffea arabica, Citrus sinensis, Elaeis guinensis, and fast-growing timber trees like Gmelina arborea, Tectona grandis plantations becoming more common in Nigeria because of their economic gain, and also the need to control soil erosion and soil degradation. The availability of plantation forestry has also been pointed out to reduce pressure on native forests (Ponce, 2000), which are rapidly being depleted (IINE- FAN, 1995).

Land-use change has been reported to have one of the largest global impacts on biodiversity (Chapin et al., 2000;

Sala et al., 2000). The type and intensity of land use change will influence the number of species occurring in different habitats. Plant species diversity has been widely studied in the plantation ecosystems (Kamo et al., 2002; Nagaike, 2002; Nagaike et al., 2003; Pourbabaei and Roostami, 2007; Yirdaw, 2001, 2003). The under storey plants have been reported to be a major component of forest ecosystems and play an important role in many ecological func- tions and processes (Nagaike et al., 2006; Roberts, 2002;

Yirdaw, 2001). Studies of plant species diversity in the for- Received 19 November 2011; accepted 24 January 2012

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slight irregularity in the rainfall distribution pattern. The weather information was obtained from the Meteorologi- cal stations located within the T and R farm of OAU. The annual rainfall at Ile-Ife averaged 1413 mm yr-¹ in a 5-year survey (Duncan, 1974) and it showed two peaks, one in July and the other in September. The mean annual tem- perature ranges from 22.5 to 31.4°C. Most soils under the plantations of these tree crops have been classified as Alfi- sol and Ultisol (Soil Survey Staff, 1990). They are formed from old parent materials which have been subjected to intensive weathering and leaching with predominant kao- linitic clay having low cation exchange capacity and less exchange sites, hence they are considered deficient in most plant nutrients (Wassel, 1969). The original vegetation of the Ife area is lowland rainforest as climax vegetation (Keay, 1959). The forest sub-type is dry-deciduous forest (Onochie, 1979).

Sampling procedure

Two sample plots, 25 m × 25 m in each plantation, (Theobroma cacao, Citrus sinensis and a nearby relatively undisturbed forest) were used for this study. The plots were laid out with a measuring tape and demarcated by narrow cut lines. The measurement was done in November (dry season month). For each site, the diameter of all the trees at breast height (dbh-1.3 m) ≥10 cm were counted, num- bered, identified and their density per plot determined in each plot. Five line transect were systemically laid in each plot and a quadrat of 50 cm × 50 cm placed at every 1 m point to identify and quantify all the under storey plant species present in each plot. Those that cannot be identified at the field were taken to IFE 1 Herbarium for proper identification. Percentage canopy was also estimated. Sev- eral terms were used for describing the biodiversity traits of the plant communities: Species richness, Shannon-Wie- ner index of species, Simpson index and Evenness index (Pieolus, 1966).

The Diversity index H’ of each sample plot was calculated using the method prescribed by Shannon and Wie- ner index (1963) as:

H=-∑ Pi ln Pi

Where Pi is the relative abundance proportion of i species and ln = Natural logarithm

Evenness index (Pieolus, 1966) also calculated thus:

S E H

= ln

where S is the total species number in each plantation, H is the diversity index and ln = natural logarithm.

Simpson’s index of diversity (1-D) which gives the probability that two randomly selected individuals in a zone belong to different subspecies and D is calculated thus:

1) (

−

=

∑

= − N N

n D n

S 1

i i i

est under storey and in plantations abounds, where high species diversity of under-story plants has been reported within plantations in surrounding natural forests (Nagai- ke, 2002; Nagaike et al., 2006; Yirdaw, 2001).

Biodiversity is changing at an unprecedented rate as a complex response to several human-induced changes (Vi- tousek et al., 1994). A high biodiversity is seen as an insurance against a decline in ecosystem service and should therefore be preserved (Yachi and Loreau, 1999). The under storey composition is changing in space and time due to a multitude of factors such as grazing, fire and rainfall, which differs in intensity and duration. It is therefore very necessary to conserve the under storey vegetation in the forest and plantations ecosystems. Although this land-use change has grown over the past years and the impact on the species diversity has been extensively studied in different parts of the world, however, little is known about the effect of the change in vegetation from forest to plantations on under storey species in Nigeria. Most research in the plantations’ ecosystems focused on the impact of conversion of forest vegetation to plantation on soil properties (Adejuwon and Ekanade, 1988; Ekanade, 1985, 1988; Wessel, 1969). Muoghalu and Odiwe (2011) have also worked on litter production and decomposition in some of these plantations. Therefore, there is the need to evaluate and document the impact of the land use changes on under storey species diversity in order to increase the understanding of species’ distribution, especially with the concerns for loss of biodiversity associated with the conversion of the rainforest to tree crops plantations.

This study specifically examined the under storey plant species in Theobroma cacao, Citrus sinensis plantations and, compares the species diversity with that of a nearby rainforest with a view to provide information that will be vital to biodiversity functioning and conservation, following the conversion of forest to plantation ecosystems, and also serves as a baseline data for future study. The following key questions were examined in this study; (i) How much of the under storey species is maintained in Theobroma cacao and Citrus sinensis, and the nearby secondary forest? (ii) What is the impact of the different land-use on the under storey species composition and distributions?

Materials and methods Study area

The study was conducted at the Teaching and Re- search (T and R) farm of the Obafemi Awolowo Univer- sity (OAU) Ile-Ife, Nigeria. Ile-Ife is situated within the rainforest zone, and the study sites are located on latitude 7° 32’ N and longitude 4° 32’ E within Ile-Ife, the eleva- tion of the area ranges from 276 to 286 m above sea level.

There are two prominent seasons in Ife area, the rainy and the dry season. The dry season is short, usually last- ing 4 months from November to March, and the longer rainy season prevails during the remaining months with

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where n_i is the number of individuals of species i which are counted/encountered, and N is the total number of all individuals counted/encountered.

The degree of similarity in species composition between the plantations and the nearby forest was compared using Jaccard’s Index of similarity:

C B A

A +

= + Cj Index s Jaccard' where:

A = number of species present in both plantations and the nearby forest

B = number of species present only in the plantation and absent from the forest

C = number of species present only in the nearby un- disturbed forest and absent from the plantation.

Statistical Analysis

One way analysis of variance was used to test for different treatment effects (land-use types) on the basal area, stem density, species diversity and evenness in each of the plots. Means of the main effects were compared using Least significant difference (LSD) test at (P<0.05). The statistical procedures were performed using SAS software, the values were first tested for normality and assumption of constant variance.

Results

A total of number of 25 and 18 under storey plant species distributed in 19 and15 families were found in Theo- broma cacao and Citrus sinensis respectively, while 14 dif- ferent species were distributed in 12 families in the nearby secondary forest (Tab. 1). The basal area and stem density were significantly (P<0.05) higher in the nearby secondary forest compared with the plantations, where Citrus sinensis plantation had the lowest value (Tab. 1)

Basal area and stem density were significantly (P<0.05) higher in the nearby secondary forest compared with the plantations (Tab. 1) with the Citrus sinensis plantation having the lowest values. There was a variations in the crown cover percentage between sampling plots of studied sites and they were significantly different (p<0.05). Percentage canopy cover was found to be 80.5% in the secondary forest, 71.5% in Theobroma cacao and 59.0% in Citrus sinensis plantations (Tab. 1).

The details of the species composition and frequencies in percentage are shown in Tab. 2. The most dominant

under storey species in Theobroma cacao plantation are:

Commenlina benghalensis (11.5%), Puozolzia guineensis (10.34%) and Talinum triangulare (8.05%). In Citrus sin- ensis plantations, the dominant species were: Fluggea viro- sa (29.06%), Spermacoce ocymoides (19.7) and Cyperus spp (9.40%), while Baissea subsessilis (41.7%), Culcasia saxati- lis (11.7%), Mallotus oppositofolius (8.33) and Salacia pall- escens (9.83%) were the dominant ones in the secondary forest. The following are the rare species of the Theobroma cacao plantations; Albizia zygia (0.57%), and Rauvolfia vomitoria (0.57%). In Citrus sinensis-Aspillia Africana (0.85%), Desmodium species, Ipomea involuncrata and Trichisia subscordata, while Baphia nitida (1.67%), Com- bretum racemosum (1.67%), Dracaena arborea (1.67%) and Hiprocratea pallens (1.67%) were the rare ones in the secondary forest, having only one individual each. Grass species are completely absent in the secondary forest while Andropogon gyanus (3.44%) and Axonopus compressus (8.55%) are the most dominant species in the Theobroma cacao and Citrus sinensis plantations respectively (Tab. 2).

The diversity index, Shannon Wiener, Simpson’s index and evenness distribution across the plantations and the forest are presented in Fig. 1. Results showed that there were significant differences (P<0.05) in mean diversity, Shannon-Wiener was highest in Theobroma cacao, and the lowest value was recorded in the secondary forest.

However, there was no significant difference (p>0.05) in the Simpson index and species evenness measures among studied sites (Fig. 1), though it followed the same trend as was observed in the Shannon Wiener, where Theobroma cacao had the highest value and in Secondary forest the least. The Simpson values showed that Theobroma cacao plantation is most diverse among the study sites. From the total under storey vegetation identified, the number of common species, between the plantations, is 7, representing 20% while only two species are common between Theobroma cacao plantations and the secondary forest giv- ing a percentage of 5.41%, and one species was common to Citrus sinensis and the secondary forest giving a percent- age of 3.33% (Tab. 3).

Of the total number of 48 under storey species identified and collected in this study, 23 of them are herbaceous plants, representing 48%. This indicates herbaceous domi-

Tab. 1. Vegetation parameters measured in the different plantations and a nearby undisturbed secondary forest

Vegetation

parameters Theobroma

cacao Citrus

sinensis Secondary forest

Species richness 25 18 14

No of families 19 15 12

Basal area (m² ha^-1) 4.18±0.57^c 12.13±0.74^ab 14.62±1.56^a

Stem density (ha^-1) 256^c 656^b 1152^a

Canopy cover (%) 59.0^c 71.5^b 80.5^a

Values with the same letter across the row are not significantly different (p>0.05)

Fig. 1. Different diversity estimates of the under storey species across the land use. Values with the same letter are not significantly different (p>0.05)

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Tab. 2. Under storey species richness (percentage frequency in bracket) and distribution in Theobroma cacao, Citrus sinensis plantations and a nearby secondary forest sample at the study sites. The negative sign (-) stand for absence of species

Species composition Family Theobroma cacao Citrus sinensis Secondary forest Herbaceous

Achyranthes aspera Amaranthecaea 4 (2.99) - -

Aspilia Africana Asteraceae 6 (3.45) 1 (0.86) -

Asystacia gangetica Acanthaceae 7 (4.02) 7 (5.98) -

Cissus gracilis Vitaceae 11 (6.32) - -

Commelina benghalensis Commelinaceae 20 (11.49)

Croton lobatus Euphorbiaceae 2 (1.50) - -

Cyathula achyranthiodes Amaranthecaea - 3 (2.56)

Cyperus spp Cyperaceae - 11 (9.4) -

Desmodium adscendes Papilionaceae 12 (6.90) - -

Desmodium spp Papilionaceae - 1 (0.86) -

Geophila obvallata Rubiaceae - - 4 (6.67)

Geophilla afzelii Rubiaceae - - 2 (3.33)

Hipprocratea pallens Celastraceae - - 1 (1.67)

Mallotus oppositifolius Euphorbiaceae - - 5 (8.33)

Puozolzia guineensis Urticaceae 18 (10.35) - -

Sida acuta Euphorbiaceae 2 (1.71) -

Spermacoce ocymoides Malvaceae - 23 (19.66) -

Synedrella nodiflora Rubiaceae - 3 (2.56) -

Talinum triangulare Portulacaceae 14 (8.06) - -

Trichlisia subscordata Asteraceae - 1 (0.86) -

Vigna gracilis Papilionaceae - 3 (2.56)

Vigna unguiculata Papilionaceae 6 - -

Xanthosoma esculentum Araceae 6 (3.45) - -

Shrub

Chromolaena odorata Asteraceae 12 (6.90) 3 (2.56) -

Combretum racemosum Combretaceae 11 (6.32) - 1 (1.67)

Culcasia saxatilis Araceae - - 7 (11.67)

Dracaena arborea Agavaceae - - 1 (1.67)

Flueggea virosa Euphorbiaceae 5 (2.87) 34 (29.06)

Lagenaria breviflora Curcubitaceae 3 (1.72) - -

Rauvolfia vomitoria Apocynaceae 1 (0.58) - -

Sphenocentrum jollyanum Menispermaceae 3 (5.0)

Tithonia diversifolia Asteraceae 4 (3.0) - -

Climber

Baissea subsessilis Apocynaceae - - 25 (41.67)

Cissampelos owariensis Menispermaceae 2 (1.15) - -

Ipomoea involucrata Convolvulaceae 2 (1.50) 1 (0.86) -

Momordica charantia Curcubitaceae 9 - -

Salacia pallescens Celastraceae 4 (3.0) 2 (1.71) 5 (8.33)

Tree sapling

Albizia zygia Mimosaceae 1 (0.58) - -

Baphia nitida Papilionaceae - - 1 (1.67)

Celtis zenkeri Ulmaceae - - 2 (3.33)

Acasia ataxacantha Mimosaceae 2 (1.15) - -

Cnestis ferruginea Connaraceae - - 2 (3.33)

Holarrhena floribunda Euphorbiaceae - 3 (2.56) -

Lecanodisus cupniodes Sapindaceae - - 1 (1.67)

Grass

Andropogon gyaanus Poaceae 6 (3.45) - -

Axonopus compressus Poaceae - 10 (8.55) -

Creeper

Aneilema condensata Commelinaceae - 9 (7.69) -

Calopogonium mucunoides Papilionaceae 6 (3.45) - -

Total 174 117 60

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forests close to the plantations site can provide baseline data that can be used in the evaluation of the impact of the land-use change on the under storey plant species diversity in plantations.

The higher number of undergrowth species (richness) recorded in the plantations in this study did not agree with the findings of Poorbabaei and Poorrrahmati (2009), where natural forest was reported to have higher species richness. The higher species’ richness in the plantations, compared with the forest, might be related to the level of disturbance, in that thinning and weeding activities were carried out in the plantations. This is in agreement with the findings of Ares et al. (2010), Dodson et al. (2008), Metlen and Fiedler (2006), Thysell and Carey (2001), Wienk et al. (2004), Zenner et al. (2006), where various form of disturbance like thinning, grazing etc. have been shown to increased under storey plant cover and diversity.

The lower basal area in the plantation might be a re- sult of the thinning cut and other management practices that were employed in the plantations while the secondary forest was not disturbed at all. This is consistent with the results of Poorbabaei and Poorrrahmati (2009), where thinning cut has also been reported to contribute to lower basal area in the Pinus taeda plantations.

The results of higher species diversity in the plantations, compared with the forest ecosystems, is in line with the findings of Koonkhunthod et al. (2007), Nagaike (2002), Nagaike et al. (2006), Poorbabaei and Poorrrah- mati (2009) who have all reported higher species diversity in the plantations compared with the forest. This is however, in contrast with the results of Munoz-Reinoso (2004), Pourbabaei and Roostami (2007), Roberts (2002), Yirdaw (2001), where species diversity had been found to be lower in the plantations. The highest undergrowth plant species diversity in the plantations is expected since species richness per sampling plot was also higher in the plantations.

The highest species diversity recorded at the Theobroma cacao compared with the Citrus sinensis plantation might be an indication that the plantation is more disturbed since weeding and cutting down of trees were done regularly at the site compared to Theobroma cacao plantation. Decocq et al. (2004) has reported that species diversity is higher in disturbed ecosystem than in undisturbed forest. Many other studies have pointed out that disturbances played a role in determining the species diversity (Rikhari et al., 1993; Sing et al., 2003).

The higher under storey species similarity between the plantations and the lower value between the plantations and the forest might be related to higher species richness in both plantations compared to forest. This might sug- gest that the secondary forest is not the main source of the seeds in plantations. The difference in relative abundance of species between the plantations and the adjacent natural forest, might have also contributed to low level of species similarity between them. Although evenness values are more or less the same across the study sites, Shannon- Wiener index diversity was highest in the plantations due nation in the vegetation. Shrubs comprise of 9 species giv-

ing a percentage of 19%, this was followed by tree species with a total number of species, representing 15% of the total under storey species in the study area. The dominant families, encountered in this study, are presented in Fig.

3. Euphorbiaceae and Papiloniaceae are the most dominant families, each with five species followed by Rubiaceae and Asteraceae families (4 species), while the following fami- lies, Amaranthaceae, Commenlinaceae, Mennispermaceae, Mimosaceae, Celastraceae and Poaceae had two species each. The details of other growth form and the family distribution of the under storey species are shown in Fig. 2 and 3 respectively. The families with just one species are not included in Fig. 3.

Discussion

The aim of this study was to determine the under storey plant species diversity in the plantations (Theobroma cacao and Citrus sinensis). In order to do this, a nearby secondary forest in the proximity was also sampled, since secondary Tab. 3. Jaccard’s similarity index (in percent) and the number of common species shown in parenthesis for plantations and natural forest

Citrus

sinensis Theobroma

cacao Secondary forest Citrus sinensis -

Theobroma cacao 20 (7) -

Secondary forest 3.33 (1) 5.41 (2) -

Fig. 2. Under storey Distribution by growth form of the different growth forms under storey species encountered across the study sites

Fig. 3. Family distribution of the dominant under storey plant species encountered across the study sites

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Kamo K, Vacharangkura T, Tiyanon S, Viriyabuncha C, Nimpila S, Doangsrisen B (2002). Plant species diversity in tropical planted forests and implication for restoration of forest ecosystems in Sakaerat, northeastern Thailand. JARQ 36(2):111-118.

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Lavery PB, Mead DJ (1998). Pinus radiata: a narrow endemic from North America takes on the world, 432-449 p. In:

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this index is more sensitive to richness (Krebs, 1999; Lud- wig and Reynolds, 1988) than evenness since the evenness are more or less the same across the study sites (Fig. 1).

The sensitivity of diversity index to richness recorded in this study, however contradicts the findings of Ludwig and Reynolds (1988) and Magurran (1988).

The higher canopy cover value in the forest causes a decline in light penetration to the forest floor compared to plantations and this might have contributed greatly to lower species richness. Some studies have shown that plantation management may have severe consequences on biodiversity compared with secondary regenerated forest, since the former system usually replaced canopy tree composition with valuable timber species (Ito et al., 2004;

Maestre and Cortina, 2004; Nagaike et al., 2006; Pourba- baei and Roostami, 2007; Wesenbeeck et al., 2003). The fact that forest canopies were completely replaced by Citrus sinensis and Theobroma cacao could have affected species diversity and composition. The presence of grass species in the plantations is an indication that the site is disturbed since the grasses can only thrive in an open area where more light is available.

Conclusions

It can be inferred from the present study that diversity of under storey species is closely related with the land-use change, species diversity increases in the plantations compared with the forests. High undergrowth species richness in the Theobroma cacao and Citrus sinensis plantations might possibly be used as a high potential for restoring biodiversity in the studied site; therefore, the changing in the land-use from forest to plantations has led to increase in the under storey plant species diversity. The results obtained could be used in planning of plantations (especially, in species selection) and managing of biodiversity in them and also as a baseline data for future references in this area. Although the main purpose of establishing these plantations was economical, the diversity and abundance of under storey regeneration, found in the plantation, in- dicated that these plantations could be effective tools in rehabilitating and increasing species diversity. There is the need to carry out further studies to assess the impact of season (rainy and dry season) on the under storey species diversity and evaluate the roles of under storey species to the nutrientcycling in both the forest and plantation ecosystems.

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