GEO-6 Regional Assessment for Asia and the Pacific
New Zealand had glaciers covering around 1 160 square kilometres, with an ice volume of around 53 cubic kilometres. Between 1977 and 2005 an 11 per cent decrease in ice volume was reported (UNEP 2008). In China, rivers such as Tarim are affected due to melting of glaciers in the mountains of Tian, Kunlun, Karakoram, and the eastern Pamir (Ives 2012).
Rivers are also affected by dams and reservoirs that cause fragmentation that affects their flow and connectivity. A study on the impact of fragmentation on large river systems has found many in Asia and the Pacific to be moderately or strongly affected (Nilsson et al. 2005). The strongly affected rivers include Chang Jiang and Haihe in China.
Irrigated agriculture is a key sector, accounting for up to 90 per cent of consumptive water use. The largest areas under groundwater irrigation are in India, 39 million hectares, and China, 19 million hectares, (Siebert et al. 2010) leading to overexploitation of groundwater sources. Nearly half of the world’s total groundwater use is by Bangladesh, China, India, Nepal and Pakistan (IGRAC 2010), with groundwater levels having fallen in northern India, Pakistan and northern China (ADB 2013b). The groundwater recharge is further affected by deforestation, expanding agriculture and urban growth leading to rapid runoff that does not provide sufficient time for infiltration. A recent study has examined the world’s 37 largest aquifers, including seven in Asia and the Pacific, and determined the renewable groundwater stress calculated as the ratio between groundwater use and groundwater availability (Richey et al. 2015). Of the seven aquifers studied in the region, five are overstressed or variably stressed and two are unstressed.
Water quality
The common pollutants in the region are organics, nutrients (nitrogen and phosphorous), dissolved salts, heavy metals, pesticides and chemicals from industrial activities. The sources are untreated or partially treated sewage, agricultural runoff, industrial wastewater and landfill leachate, and nutrient and sediments washed from degraded land by heavy rainfall. Several river basins – the
84
Ganges, Haihe, Huaihe, Indus and Yellow river basins, and some river stretches in southern India – have high organic pollution (UNEP 2015). This can be further aggravated by other pollution such as increased salinity as seen in the Ganges and Indus river basins.
A major cause of water pollution is poor sanitation, including defecation in the open, leading to contamination of surface and groundwater sources by organics, nutrients and bacterial coliform. Globally, the percentage of population using improved sanitation facilities was 68 per cent in 2015 (UNDP 2015), while in Asia and the Pacific it ranged from 29 per cent in the Solomon Islands, to 100 per cent in, among others, Australia, Japan, Republic of Korea and Singapore in 2012 (World Bank 2012). In 2015, sanitation coverage was below 50 per cent in South Asia (Afghanistan, India and Nepal), Southeast Asia (Cambodia and Timor-Leste) and Pacific (Kiribati, Papua New Guinea and Solomon Islands) (UN MDG database). Only 30 per cent of the wastewater generated in urban India is treated (CPCB 2012) while the coverage in Japan is 100 per cent (Ueda and Benouahi 2009). Untreated sewage emanating from sewer leaks leads to high nitrate levels in urban groundwater, as observed in Bangkok, Jakarta and Metro Manila (Umezawa et al. 2009). Microbial pollution from human and livestock sewage, in addition to being localised, also spreads to rivers and coastal areas as observed in bays of Pacific islands, and the Java Sea coastal areas; it has also affected aquaculture in Bay of Bengal and South China Sea (UNEP 2006).
Eutrophication, the excess growth of algae, is caused by high loading of nutrients – nitrogen and phosphorous – in water bodies resulting in reduced water quality, oxygen depletion and growth of harmful algal blooms (Figure 2.4.2). The sources of nutrients are urea in fertilizers and in the manufacture of various plastics and chemicals, untreated sewage, agricultural runoff, and atmospheric wet and dry deposition of nutrients during smoke haze events (Sundarambal et al. 2010). In attempts to enhance food production, over-application of chemical fertilizers is a common practice in China, India, Philippines and Thailand, leading to high nutrient overloads (Novotny et al.
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 |
Page 157 |
Page 158 |
Page 159 |
Page 160 |
Page 161 |
Page 162 |
Page 163 |
Page 164 |
Page 165 |
Page 166 |
Page 167 |
Page 168 |
Page 169 |
Page 170 |
Page 171 |
Page 172 |
Page 173 |
Page 174 |
Page 175 |
Page 176 |
Page 177 |
Page 178 |
Page 179 |
Page 180 |
Page 181 |
Page 182 |
Page 183 |
Page 184 |
Page 185 |
Page 186 |
Page 187 |
Page 188 |
Page 189 |
Page 190 |
Page 191 |
Page 192 |
Page 193 |
Page 194 |
Page 195 |
Page 196 |
Page 197 |
Page 198 |
Page 199 |
Page 200 |
Page 201 |
Page 202 |
Page 203 |
Page 204 |
Page 205 |
Page 206 |
Page 207 |
Page 208 |
Page 209 |
Page 210 |
Page 211 |
Page 212 |
Page 213 |
Page 214 |
Page 215 |
Page 216 |
Page 217 |
Page 218 |
Page 219 |
Page 220 |
Page 221 |
Page 222 |
Page 223 |
Page 224 |
Page 225 |
Page 226 |
Page 227