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Download TAAG Book of Abstracts - Tropical Biology Association

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Safeguarding the future <strong>of</strong> the African elephant:<br />

Society for Conservation <strong>Biology</strong> (SCB)'s position on the<br />

use <strong>of</strong> ivory for religious objects<br />

Stephen MufutauAwoyemi<br />

Society for Conservation <strong>Biology</strong><br />

Email for correspondence: sawoyemi@gmail.com<br />

Abstract<br />

Global attention has recently been drawn to worrisome<br />

levels <strong>of</strong> elephant massacre for ivory in Africa. The 2013<br />

UNEP Rapid Assessment Report states that at the<br />

Monitoring the Illegal Killing <strong>of</strong> Elephants (MIKE)<br />

monitoring sites alone, an estimated 17,000 elephants<br />

were poached in 2011 – a figure likely to be 25,000<br />

continent wide. The report estimates the total<br />

continental population <strong>of</strong> elephants to be in the range<br />

<strong>of</strong> 420,000 to 650,000 with just three countries,<br />

Botswana, Tanzania and Zimbabwe accounting for well<br />

over half <strong>of</strong> these elephants.Trends reveal alarming<br />

declines in Central and West Africa as well as increasing<br />

risk <strong>of</strong> local extinction <strong>of</strong> some populations. It has been<br />

discovered that the demand for ivory in Asia for<br />

religious artifacts and trinkets is a substantial driver <strong>of</strong><br />

elephant poaching in Africa. This catastrophe calls for<br />

unprecedented levels <strong>of</strong> proactive action, deep<br />

commitment and collaboration across national borders,<br />

disciplines and worldviews. The elephant crisis in Africa<br />

must be tackled by addressing the problem from the<br />

root cause. Conservation biologists should work with<br />

religious leaders to address this challenge by proactively<br />

severing the demand for religious ivory and other<br />

intended uses <strong>of</strong> ivory. The Society for Conservation<br />

<strong>Biology</strong> (SCB)’s Religion and Conservation Research<br />

Collaborative (RCRC) <strong>of</strong> the Religion and Conservation<br />

<strong>Biology</strong> Working Group (RCBWG) has crafted a policy<br />

position statement on the use <strong>of</strong> ivory for religious<br />

objects. The objective <strong>of</strong> the position statement is to<br />

educate, spread awareness and pave way to engaging<br />

religious leaders in dialogue and collaboration to<br />

addressing religious ivory in Asia. It is hoped that the<br />

statement will stimulate the needed action by<br />

government, civil society and the religious community in<br />

resolving the crisis <strong>of</strong> religious ivory and the gruesome<br />

impact on the elephant populations and local<br />

communities in Africa.<br />

Keywords: Ivory, Religion, ivory, elephant tusk<br />

Population Status and possible effects <strong>of</strong> Lantana<br />

camara to the native woody species in Adwa district,<br />

Ethiopia<br />

1 *Berhane G. Asmelash and 2 Mengisteab HailuUbuy<br />

1<br />

Department <strong>of</strong> Ecology and Natural Resources<br />

Management, Norwegian University <strong>of</strong> Life Sciences, Ås,<br />

Norway<br />

2<br />

Department <strong>of</strong> Land Resource Management and<br />

Environmental Protection, Mekelle University, Ethiopia,<br />

Email for correspondence: mmailu@yahoo.com<br />

Abstract<br />

Invasion <strong>of</strong> new species to an ecosystem affected the<br />

native species diversity. The main objective was to<br />

assess the distribution <strong>of</strong> Lantana camara invasive<br />

species and effect on native species abundance in the<br />

study area. Randomly selected sampling quadrants (25,<br />

100 and 400m 2 ) were used to test the hypothesis that<br />

the L. camara invasive species have significant effect on<br />

native species abundance. The study was carried out in<br />

48 plots and various land uses such as exclosures, open<br />

area, cultivated lands and home garden. The mean<br />

numbers <strong>of</strong> species (mean ± SE) recorded in the seedling<br />

(height < 0.5m and DBH 0.5m<br />

and DBH 0.5m and DBH<br />

>5cm) were 3.33 ± 0.27, 6.50 ± 0.66 and 2.58 ± 0.31,<br />

respectively. The result confirmed that L. camara was<br />

the dominant species with highest proportion in the<br />

seedling (92%) and sapling (98%) compared to other 30<br />

woody species in the study area. L. camara invasive<br />

species in the seedling and sapling stages were<br />

significant negatively correlated with altitude, age <strong>of</strong> the<br />

exclosures, Shannon, evenness and equitability (all<br />

p0.183). The density <strong>of</strong><br />

matured L. camarawas significant but negatively<br />

correlated (r =-0.487, p = 0.000). Highest abundances <strong>of</strong><br />

L. camara invasive species per hectare were dominantly<br />

recorded and identified in the backyards (8588 ± 3705),<br />

followed by open land (7 615 ± 1 045). The cultivated<br />

land and exclosures had relatively lower number <strong>of</strong><br />

invasive species per hectare.<br />

Keywords: Invasive species, native species; species<br />

richness; relative abundances<br />

<strong>TAAG</strong> First African Student’s Conference, Nairobi. 2-4 July, 2013 38

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