This page contains a Flash digital edition of a book.
GEO-6 Regional Asssement for West Asia


In the Arabian Peninsula, for instance, the two countries which have the highest levels of endemic plants, Yemen (including the Socotra Archipelago) and Oman, have Red List assessments of plants; listing 699 endemic taxa (69 per cent of the endemic flora of this area), of which 476 have been assessed for the global IUCN Red List.


Of these, 220 are threatened with extinction, with 20 classed as critically endangered, 38 as endangered and 162 as vulnerable.


In Bahrain, two of the seven species of marine turtle - the hawksbill and the green turtle - occur in the waters of the ROPME Sea Area. Worldwide, the IUCN Red List classifies the hawksbill turtle as critically endangered and the green turtle as endangered. At the local and regional level, the populations of these species are threatened and the number of foraging habitats and nesting grounds are continually declining.


At least 21 species of cetaceans are known in West Asia. Only a few of these have been studied in any detail. One example is the humpback whale, the distribution of which appears to be centred in the Arabian Sea of Oman. Humpback whales are also known to occur, albeit less regularly, in the ROPME Sea Area, Oman Sea and the Red Sea. Estimates of the Arabian Sea humpback whale population from studies in Oman suggest that fewer than 100 individuals remain.


Increasing threats from human activities cause this population to be in danger of extinction and urgent conservation action is required. The only other population data for cetaceans in the region is an assessment of trends for dolphins in the ROPME Sea Area, in which a statistically significant decline in the population – of more than 70 per cent – was documented over a period of little more than a decade.


In Iraq, where habitat modification in the form of water diversion, dredging, pollution and overfishing are contributing to species loss, 20 freshwater fish species are threatened, constituting 50 per cent of the native freshwater fish species in the country.


70


Whilst it is true that plants can be cultivated elsewhere and saved from extinction, the cultural history that a plant carries with it in its native habitat cannot be maintained through cultivation in another region. There are several examples of plants used in traditional medicine in the region that are now threatened due to overharvesting.


2.4.2 Pressures on biodiversity Encroachment on natural habitats


The rapid increase in population coupled with unprecedented growth in urbanisation puts pressure on biodiversity through encroachment on fragile natural habitats. For instance, in the Gulf, urbanisation coupled with coastal development involving intensive reclamation and dredging activities is leading to habitat destruction and biodiversity loss (Halpern et al. 2008; Van Lavieren et al. 2011). It is estimated that more than 40 per cent of the Gulf coast has been developed (Hamza and Munawar 2009) due to rapid economic, social and industrial growth (Halpern et al. 2008). This comes as a result of the shortage of available land in some countries and relatively inexpensive reclamation costs (Burt et al. 2012).


In the Mashriq countries, a significant portion of the East Mediterranean coastal landscape has undergone a concentration of populations and economic activities. For instance, 55 per cent of Lebanon’s population is concentrated in five large cities along the coast. This negatively affects biodiversity and natural ecosystems (Lebanon, Ministry of Environment 2010). It has been reported that numbers of plant species and plant families in the waterfront of the city of Beirut have been reduced by almost 64 per cent and 75 per cent respectively compared to 1930s numbers (Chmaitelly 2007).


Mass-scale development affects the hydrology of coasts and natural coastal features such as mangrove swamps, reefs and beaches, leading to biodiversity loss. This is shown in the tourism development on the Red Sea and in many coastal areas of the Gulf Cooperation Council (GCC) countries (Gelil 2008). Increasing investment plans for


Page 1  |  Page 2  |  Page 3  |  Page 4  |  Page 5  |  Page 6  |  Page 7  |  Page 8  |  Page 9  |  Page 10  |  Page 11  |  Page 12  |  Page 13  |  Page 14  |  Page 15  |  Page 16  |  Page 17  |  Page 18  |  Page 19  |  Page 20  |  Page 21  |  Page 22  |  Page 23  |  Page 24  |  Page 25  |  Page 26  |  Page 27  |  Page 28  |  Page 29  |  Page 30  |  Page 31  |  Page 32  |  Page 33  |  Page 34  |  Page 35  |  Page 36  |  Page 37  |  Page 38  |  Page 39  |  Page 40  |  Page 41  |  Page 42  |  Page 43  |  Page 44  |  Page 45  |  Page 46  |  Page 47  |  Page 48  |  Page 49  |  Page 50  |  Page 51  |  Page 52  |  Page 53  |  Page 54  |  Page 55  |  Page 56  |  Page 57  |  Page 58  |  Page 59  |  Page 60  |  Page 61  |  Page 62  |  Page 63  |  Page 64  |  Page 65  |  Page 66  |  Page 67  |  Page 68  |  Page 69  |  Page 70  |  Page 71  |  Page 72  |  Page 73  |  Page 74  |  Page 75  |  Page 76  |  Page 77  |  Page 78  |  Page 79  |  Page 80  |  Page 81  |  Page 82  |  Page 83  |  Page 84  |  Page 85  |  Page 86  |  Page 87  |  Page 88  |  Page 89  |  Page 90  |  Page 91  |  Page 92  |  Page 93  |  Page 94  |  Page 95  |  Page 96  |  Page 97  |  Page 98  |  Page 99  |  Page 100  |  Page 101  |  Page 102  |  Page 103  |  Page 104  |  Page 105  |  Page 106  |  Page 107  |  Page 108  |  Page 109  |  Page 110  |  Page 111  |  Page 112  |  Page 113  |  Page 114  |  Page 115  |  Page 116  |  Page 117  |  Page 118  |  Page 119  |  Page 120  |  Page 121  |  Page 122  |  Page 123  |  Page 124  |  Page 125  |  Page 126  |  Page 127  |  Page 128  |  Page 129  |  Page 130  |  Page 131  |  Page 132  |  Page 133  |  Page 134  |  Page 135  |  Page 136  |  Page 137  |  Page 138  |  Page 139  |  Page 140  |  Page 141  |  Page 142  |  Page 143  |  Page 144  |  Page 145  |  Page 146  |  Page 147  |  Page 148  |  Page 149  |  Page 150  |  Page 151  |  Page 152  |  Page 153  |  Page 154  |  Page 155  |  Page 156