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2020 | OriginalPaper | Chapter

9. Implementing the Principle of Equitable and Reasonable Utilization in the Nile Basin

Author : Philine Wehling

Published in: Nile Water Rights

Publisher: Springer Berlin Heidelberg

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Abstract

International water law requires transboundary watercourses to be utilized in an equitable and reasonable manner, yet to date this principle has seen little concretization. This chapter addresses the principle’s implementation along the Nile, focusing on the process involved to implement the principle in practice, and on the factors to consider when determining what constitutes equitable and reasonable use of Nile water in each riparian state. It considers the legal content of relevant factors and circumstances, reviews the respective country data from each riparian state’s perspective, and debates their importance in relation to the Nile. On this basis, the chapter discusses considerations for the weighing and overall assessment of those factors and circumstances. This illustrates the extent to which the principle can provide a conceptual framework for regulating water use: The principle’s application can generally indicate the weight that the relevant factors and circumstances carry along a particular watercourse for the purposes of determining equitable and reasonable use and eventually allocating water uses, as well as their relevance for each riparian state; it does not enable the allocation of either specific amounts of water or specific uses. The discussion also shows that attaining an optimal utilization at a basin-wide scale requires the taking into account of both the manner of use and the potential benefits, in different parts of the basin area. Ultimately, therefore, riparian states must further define their equitable-use regime through negotiations. The principle of equitable utilization functions primarily as structured guidance for such negotiations.

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Footnotes
1
The EastAfrican (2014) and Maṣris (2014).
 
2
See the Egyptian State Information Service (2019a).
 
3
Amān (2015) and Nader (2015).
 
4
ILC, Draft Articles on the Law of the Non-Navigational Uses of International Watercourses and commentaries thereto adopted by the Drafting Committee on second reading, YBILC 1994, Vol. II, Pt. 2, p. 98, para. 8.
 
5
Ibid., p. 101, para. 1.
 
6
Ibid.
 
7
Ibid., p. 102, para. 9.
 
8
In the writings of jurists, the legal content and significance of the factors for equitable utilization in general are discussed by Fuentes (1996), pp. 337–412; McIntyre (2007), pp. 155–189. See also the analysis of factors and circumstances affecting the equity and reasonableness of uses in the sub-basin of the Blue Nile at Woldetsadik (2013), pp. 208–260.
 
9
For example Lankford (2013), pp. 130–145, citing further references at p. 133. See also the Legal Assessment Model developed by Wouters et al. (2005). This model, however, is designed specifically for assessing whether one particular use is equitable and reasonable, not for guiding use allocation among riparian states.
 
10
See ICJ, Gabčíkovo-Nagymaros Project (Hungary v. Slovakia), Judgment of 25 September 1997, ICJ Reports 1997, pp. 76–80, paras. 132–147. See also McCaffrey (1998), p. 22.
 
11
Art. 24, para. 12 of the CFA.
 
12
ILC, Draft Articles on the Law of the Non-Navigational Uses of International Watercourses and commentaries thereto adopted by the Drafting Committee on second reading, YBILC 1994, Vol. II, Pt. 2, p. 101, para. 4.
 
13
Woldetsadik even concludes from this that the contribution to the waters of the Nile is one of the “controlling factors” for the equity of uses, see Woldetsadik (2013), p. 214. However, this is not apparent from the CFA, but rather both factors are listed in Art. 4, para. 2 equally side by side with the other relevant factors.
 
14
Karyabwite (2000), p. 10, Table 2 “Nile Basin repartition”. For an overview of the repartition of the Nile drainage area on the riparian states, see also NBI (2016), p. 19.
 
15
Oloo (2011), pp. 156–157.
 
16
At Aswan, for example, precipitation reaches only 3 mm per year. FAO (2005), p. 19.
 
17
This is about two-thirds of the Nile drainage area in the former Sudan before the secession of South Sudan. Salman (2011), p. 157.
 
18
FAO Aquastat, Sudan, Water resources, http://​www.​fao.​org/​nr/​water/​aquastat/​countries_​regions/​SDN/​. All websites cited in this chapter were last accessed 20 May 2019.
 
19
Ward and Roach (2012), p. 59.
 
20
Karyabwite (2000), p. 10, Table 2 “Nile Basin repartition”.
 
21
Last (2012), p. 490.
 
22
NBI (2012), p. 36.
 
23
See FAO Aquastat, Sudan, Water resources, http://​www.​fao.​org/​nr/​water/​aquastat/​countries_​regions/​SDN/​. See also Last (2012), p. 490.
 
24
See Last (2012), p. 490.
 
25
Karyabwite (2000), p. 10, Table 2 “Nile Basin repartition”.
 
26
Oloo (2011), pp. 161 and 163; Salman (2011), p. 158.
 
27
Oloo (2011), p. 163.
 
28
Smith-Morris (2012), p. 465.
 
29
Salman (2011), p. 157.
 
30
Allan (2012), p. 1186.
 
31
Waterbury (1979), p. 16.
 
32
Allan (2012), p. 1186.
 
33
Karyabwite (2000), p. 10, Table 2 “Nile Basin repartition”.
 
34
Langlands (2012), p. 1309.
 
35
Van Buren (2012a), p. 1318.
 
36
Mwiandi (2010), p. 94; Mulira (2010), p. 127.
 
37
Langlands (2012), p. 1309.
 
38
Karyabwite (2000), p. 10, Table 2 “Nile Basin repartition”.
 
39
Mwiandi (2010), p. 94; Mulira (2010), p. 127.
 
41
Mwiandi (2010), p. 96.
 
42
Karyabwite (2000), p. 10, Table 2 “Nile Basin repartition”.
 
43
Ngowi (2010), p. 58.
 
44
Bosire (2011), p. 207.
 
45
Ngowi (2010), pp. 58–59; Check (2011), pp. 97–98.
 
46
FAO Aquastat, United Republic of Tanzania, Water resources, http://​www.​fao.​org/​nr/​water/​aquastat/​countries_​regions/​TZA/​.
 
47
See FAO Aquastat, United Republic of Tanzania, Geography, climate and population, http://​www.​fao.​org/​nr/​water/​aquastat/​countries_​regions/​TZA/​.
 
48
Karyabwite (2000), p. 10, Table 2 “Nile Basin repartition”.
 
49
Arsano (2006), p. 325; Swain (2008), p. 201.
 
50
See Nkurunziza (2010), p. 15.
 
51
Mthembu-Salter (2012), p. 182.
 
52
Karyabwite (2000), p. 10, Table 2 “Nile Basin repartition”.
 
54
Karyabwite (2000), p. 10, Table 2 “Nile Basin repartition”.
 
55
Tshimanga (2010), pp. 78–79.
 
56
See Gourou (2012), p. 328.
 
57
Similarly Woldetsadik (2013), p. 216.
 
58
On the state practice, see McIntyre (2007), pp. 180–183.
 
59
ILC, Draft Articles on the Law of the Non-Navigational Uses of International Watercourses and commentaries thereto adopted by the Drafting Committee on second reading, YBILC 1994, Vol. II, Pt. 2, p. 101, para. 4.
 
60
See the commentary of the ILA on Art. V of the Helsinki Rules, ILA, Report of the Fifty-Second Conference held at Helsinki, 14–20 August 1966, pp. 488–491.
 
61
ILC, Draft Articles on the Law of the Non-Navigational Uses of International Watercourses and commentaries thereto adopted by the Drafting Committee on second reading, YBILC 1994, Vol. II, Pt. 2, p. 110, para. 4.
 
62
UN GA, Report of the Sixth Committee convening as the Working Group as the Whole, 11 April 1997, UN Doc. A/51/869, p. 5.
 
63
In the proposed Art. 7, para. 1(ix) of the draft articles. See Schwebel (1981), p. 90, para. 106.
 
64
In total, irrigated area in Egypt is 3,610,000 hectares, or 98.3% of the cultivated area. FAO Aquastat, Egypt, Irrigation and drainage, http://​www.​fao.​org/​nr/​water/​aquastat/​countries_​regions/​EGY/​index.​stm.
 
67
Report of the Krishna Water Disputes Tribunal, 1973, Vol. 2, pp. 126–127. On this question, see also McIntyre (2007), pp. 158–159.
 
68
Taha (2010), p. 192.
 
70
Ward and Roach (2012), p. 59; Swain (2008), p. 205.
 
71
The total volume of water abstracted from the Nile annually for irrigation in Ethiopia is estimated to be only 1.5 billion cubic meters. See NBI (2016), Chap. 7, Irrigation areas in Ethiopia, http://​atlas.​nilebasin.​org/​treatise/​irrigation-areas-in-ethiopia/​.
 
72
See also NBI (2016), Chap. 7, Water withdrawal for irrigation in the Nile Basin, http://​atlas.​nilebasin.​org/​treatise/​water-withdrawal-for-irrigation-in-the-nile-basin/​. For the total volume of water withdrawn from the Nile for irrigation in each of the riparian states, see Sect. 9.1.5, below.
 
73
ILC, Draft Articles on the Law of the Non-Navigational Uses of International Watercourses and commentaries thereto adopted by the Drafting Committee on second reading, YBILC 1994, Vol. II, Pt. 2, p. 101, para. 4.
 
76
Elemam (2010), p. 219.
 
77
See Sect. 9.1.2, above.
 
79
Ward and Roach (2012), p. 59; Swain (2008), p. 205.
 
80
See Taha (2010), p. 205.
 
82
Swain (2008), p. 206.
 
83
The term “Nile water” in this Chapter is used in accordance with Art. 2(b) of the CFA to comprise only the surface and groundwater runoff. As noted previously, green water is not considered part of the Nile water resources under the CFA when it comes to water use.
 
84
See NBI (2012), p. 51. See also Tafesse (2011), p. 67.
 
86
Oloo (2011), p. 161.
 
87
Kahsay (2012a), p. 476; Oloo (2011), p. 161.
 
88
Kahsay (2012a), p. 476.
 
90
Salman (2011), p. 161.
 
92
Van Buren (2012a), p. 1317.
 
93
See Arsano (2006), p. 334.
 
94
CIA, The World Factbook, Kenya, People and society, https://​www.​cia.​gov/​library/​publications/​the-world-factbook/​geos/​ke.​html. See also Van Buren (2012b), p. 652.
 
95
Van Buren (2012b), p. 652.
 
96
Mwiandi (2010), p. 110.
 
97
Van Buren (2012b), p. 653. Irrigated agriculture is minimal, see FAO Aquastat, Kenya, Irrigation and drainage, http://​www.​fao.​org/​nr/​water/​aquastat/​countries_​regions/​KEN/​. See also NBI (2016), Chap. 7, Hydraulic Infrastructure in the Nile, http://​atlas.​nilebasin.​org/​treatise/​hydraulic-infrastructure-in-the-nile/​.
 
100
See NBI (2016), Chap. 7, Hydraulic Infrastructure in the Nile, http://​atlas.​nilebasin.​org/​treatise/​hydraulic-infrastructure-in-the-nile/​. On the development of irrigation in Tanzania, see FAO Aquastat, United Republic of Tanzania, Irrigation and drainage, http://​www.​fao.​org/​nr/​water/​aquastat/​countries_​regions/​TZA/​.
 
102
Nkurunziza (2010), p. 16.
 
104
Water demand is estimated at less than 3% of the country’s available renewable water resources, see Nkurunziza (2010), p. 17.
 
107
CIA, The World Factbook, Democratic Republic of the Congo, People and society, https://​www.​cia.​gov/​library/​publications/​the-world-factbook/​geos/​cg.​html.
 
108
Gourou (2012), p. 328.
 
109
ILC, Draft Articles on the Law of the Non-Navigational Uses of International Watercourses and commentaries thereto adopted by the Drafting Committee on second reading, YBILC 1994, Vol. II, Pt. 2, p. 101, para. 4.
 
110
A possible effect of dams downstream can be, for example, to block fish migration routes upstream.
 
111
Dellapenna (2006), p. 299.
 
112
State Information Service (2019b). See also ‘Abd ar-Raḥmān (2013), p. 5; ‘Abd Ḥasnīn (2013), p. 6.
 
113
Ethiopiantimes (2011).
 
114
See Dellapenna (2006), p. 299; Waterbury (1979), pp. 14–17 and 23.
 
115
ILC, Draft Articles on the Law of the Non-Navigational Uses of International Watercourses and commentaries thereto adopted by the Drafting Committee on second reading, YBILC 1994, Vol. II, Pt. 2, p. 101, para. 4.
 
116
For a detailed discussion of the significance of existing uses in the context of the overall assessment of relevant factors and circumstances, see Fuentes (1996), pp. 356–366.
 
117
FAO Aquastat, Egypt, Water resources and use, http://​www.​fao.​org/​nr/​water/​aquastat/​countries_​regions/​EGY/​. Another 9 billion cubic meters for municipalities and 2 billion cubic meters for industries, ibid.
 
119
See Elemam (2010), p. 219. The first modern dam was built in 1861 near Cairo, this was followed in 1902 by dams on the Nile in Aswan, Asyut, and Sittah. See also NBI (2016), Chap. 7, Hydraulic Infrastructure in the Nile, http://​atlas.​nilebasin.​org/​treatise/​hydraulic-infrastructure-in-the-nile/​.
 
120
FAO (2005), p. 23, Table 7.
 
121
Overview at FAO Aquastat, Egypt, Prospects for agricultural water management, http://​www.​fao.​org/​nr/​water/​aquastat/​countries_​regions/​EGY/​.
 
123
Cascão (2009), p. 249; Ward and Roach (2012), pp. 65–66. Detailed information about the projects is available on the homepage of the Egyptian Ministry of Water Resources and Irrigation (2019a), Al-mašrū‘āt (The Projects), https://​www.​mwri.​gov.​eg/​index.​php/​ministry-2 (Arabic).
 
124
That is 200,000 feddan. Feddan is an Arabic unit of area used in Egypt, among other countries. 1 feddan is 0.42 hectares.
 
125
For details on the project, see the Egyptian Ministry of Water Resources and Irrigation (2019b), Mašrū‘ tanmīya šamāl sīynā (Northern Sinai Development Project), https://​www.​mwri.​gov.​eg/​index.​php/​ministry-2/​ministry-20 (Arabic).
 
126
That is 400,000 feddan.
 
127
For details on the project, see the Egyptian Ministry of Water Resources and Irrigation (2019c), Mašrū‘ tanmīya ǧanūb al-wādī (South Valley Development Project), https://​www.​mwri.​gov.​eg/​index.​php/​ministry-2/​ministry-21 (Arabic).
 
128
For details on the project, see the Egyptian Ministry of Water Resources and Irrigation (2019d), Mašrū‘ al-milīūn wa-nuṣf fiddān (One Million and a Half Feddan Project), https://​www.​mwri.​gov.​eg/​index.​php/​ministry-2/​ministry-25 (Arabic).
 
129
Ward and Roach (2012), p. 66.
 
130
For example Woldetsadik (2013), p. 248.
 
131
Boisson de Chazournes (2013), p. 74.
 
132
See Caponera (2007), p. 221. See also Chap. 3, Sect. 3.​2.​3.
 
133
In its decision, the tribunal observed that “the rule that States may utilize the hydraulic power of international watercourses only on condition of a prior agreement between the interested States cannot be established as a custom, even less as a general principle of law” (emphasis in original), English translation in ILR 24 (1957) p. 130, of the original Lake Lanoux Arbitration (France v. Spain), 16 November 1957, RIAA XII (1957), p. 308, para. 13.
 
134
Arsano (2010), p. 176.
 
135
Taha (2010), p. 205.
 
137
See FAO Aquastat, Sudan, Water use, http://​www.​fao.​org/​nr/​water/​aquastat/​countries_​regions/​SDN/​. Another 4% is withdrawn for municipal households, ibid.
 
138
Taha (2010), p. 194.
 
139
Ibid., p. 205.
 
141
Kharouf-Gaudig (2012), p. 99; Taha (2010), p. 182.
 
142
For more details on the Gezira Scheme, see Taha (2010), pp. 184–185, 193 and 209.
 
143
Ibid., pp. 195–196 (approximately 3,512,000 feddan).
 
144
Ibid., p. 199 (approximately 300,000 feddan).
 
145
Ibid., pp. 184–185.
 
146
Ibid., p. 186 (approximately 500,000 feddan).
 
147
‘Alī Ṭāhā (2005), p. 83; Taha (2010), p. 195.
 
149
See for example AllAfrica (2018).
 
150
See for example Taha (2010), p. 216; Arsano (2006), p. 330.
 
151
For a detailed discussion of the criteria for the consideration of potential uses, see in the context of the following presentation of potential uses by Ethiopia.
 
154
Ibid.
 
155
For a list of dams in Ethiopia, see FAO, Aquastat, Dams of Ethiopia, www.​fao.​org/​nr/​water/​aquastat/​dams/​country/​ETH-dams_​eng.​xlsx. See also NBI (2016), Chap. 7, Hydraulic Infrastructure in the Nile, http://​atlas.​nilebasin.​org/​treatise/​hydraulic-infrastructure-in-the-nile/​.
 
157
See Arsano (2010), p. 169; Salman (2013), p. 24.
 
159
Details of the project are available on the homepage of the Italian construction company carrying out the work: https://​www.​salini-impregilo.​com/​it/​lavori/​in-corso/​dighe-impianti-idroelettrici/​grand-ethiopian-renaissance-dam-project.​html. See also Kahsay (2012b), p. 501.
 
160
State Information Service (2019b). See also ‘Abd ar-Raḥmān (2013), p. 5; ‘Abd Ḥasnīn (2013), p. 6.
 
161
Commentary of the ILA on Art. VII of the Helsinki Rules, ILA, Report of the Fifty-Second Conference held at Helsinki, 14–20 August 1966, pp. 492–493.
 
162
Ward and Roach (2012), p. 67.
 
164
See World Energy Council, World Energy Resources (2013), pp. 7–8 and 21.
 
166
FAO (1997), Chap. 6.
 
167
Oloo (2011), p. 157.
 
169
See ibid.
 
170
The hydroelectric power potential of South Sudan has been evaluated several times. The largest hydroelectric power potential on the Nile is located between Nimule and Juba, where it is estimated that 1045 MW could be generated annually. UNDP (2010), p. 21.
 
171
See Arsano (2006), p. 334. Agriculture in Uganda predominantly relies on rainfall. Van Buren (2012a), p. 1317.
 
173
Van Buren (2012a), p. 1318.
 
174
See also Langlands (2012), p. 1309.
 
175
For details see Mulira (2010), pp. 134–136.
 
177
International Hydropower Association, Country profiles, Uganda, https://​www.​hydropower.​org/​country-profiles/​uganda.
 
179
The EastAfrican (2013).
 
181
It is estimated that Uganda has immense hydroelectric power potential amounting to approximately 3000 MW from the White Nile, of which less than 10% is currently being exploited. The Ugandan areas bordering Lake Victoria also have great potential for irrigated agriculture, which has similarly been barely used thus far. Van Buren (2012a), p. 1319.
 
182
Mwiandi (2010), p. 93.
 
186
See World Bank (2011), p. 6, Table 1.
 
187
See NBI (2016), Chap. 7, Hydraulic Infrastructure in the Nile, http://​atlas.​nilebasin.​org/​treatise/​hydraulic-infrastructure-in-the-nile/​. See also Van Buren (2012b), p. 655.
 
188
Mwiandi (2010), pp. 115 and 119.
 
189
There is potential for irrigated agriculture and hydroelectric power generation in Kenya along the major rivers that flow into Lake Victoria, see Mwiandi (2010), pp. 107 and 112.
 
190
See FAO Aquastat, United Republic of Tanzania, Water resources, http://​www.​fao.​org/​nr/​water/​aquastat/​countries_​regions/​TZA/​.
 
193
See Bosire (2011), pp. 203–204.
 
195
For more details on the water-use potential, see Bosire (2011), pp. 203–204.
 
196
Irrigated agriculture in Burundi has only been marginally employed thus far. FAO Aquastat, Burundi, Développement de l’irrigation et du drainage, http://​www.​fao.​org/​nr/​water/​aquastat/​countries_​regions/​BDI/​index.​stm. See also Nkurunziza (2010), p. 26.
 
199
On the water-use potential in more detail, see Nkurunziza (2010), pp. 19 and 26.
 
202
See FAO Aquastat, République démocratique du Congo, Irrigation et drainage, http://​www.​fao.​org/​nr/​water/​aquastat/​countries_​regions/​COD/​indexfra.​stm.
 
204
For details on this survey, see Tshimanga (2010), pp. 87–88.
 
205
See NBI (2016), Chap. 7, Water Withdrawal for Irrigation in the Nile Basin, http://​atlas.​nilebasin.​org/​treatise/​water-withdrawal-for-irrigation-in-the-nile-basin/​.
 
206
Annex II to the CFA.
 
207
ILC, Draft Articles on the Law of the Non-Navigational Uses of International Watercourses and commentaries thereto adopted by the Drafting Committee on second reading, YBILC 1994, Vol. II, Pt. 2, p. 101, para. 4.
 
208
On the benefits of the Aswan High Dam, see State Information Service (2019c).
 
210
ILC, Draft Articles on the Law of the Non-Navigational Uses of International Watercourses and commentaries thereto adopted by the Drafting Committee on second reading, YBILC 1994, Vol. II, Pt. 2, p. 97, para. 3. See in the same sense already the ILA’s commentary on Art. V of the Helsinki Rules, Report of the Fifty-Second Conference held at Helsinki, 14–20 August 1966, p. 487.
 
211
ILC, Draft Articles on the Law of the Non-Navigational Uses of International Watercourses and commentaries thereto adopted by the Drafting Committee on second reading, YBILC 1994, Vol. II, Pt. 2, p. 97, para. 3.
 
212
Emphasis in original. ILA, Report of the Fifty-Second Conference held at Helsinki, 14–20 August 1966, p. 487.
 
213
ILC, Draft Articles on the Law of the Non-Navigational Uses of International Watercourses and commentaries thereto adopted by the Drafting Committee on second reading, YBILC 1994, Vol. II, Pt. 2, p. 101, para. 4.
 
214
UN-Water (2017), p. 19.
 
216
See ‘Alī Ṭāhā (2005), pp. 82–83.
 
217
Waterbury (1979), p. 16.
 
218
‘Alī Ṭāhā (2005), p. 78; Kharouf-Gaudig (2012), p. 104.
 
219
See Waterbury (2002), p. 144; Salman (2014), p. 342.
 
220
‘Alī Ṭāhā (2005), p. 78; Kharouf-Gaudig (2012), p. 98.
 
221
UNDP (2010), p. 22; Salman (2014), p. 343.
 
222
UNDP (2010), p. 22.
 
224
Salman (2014), p. 343.
 
225
Convention on Wetlands of International Importance especially as Waterfowl Habitat, Ramsar, 2 February 1971, http://​www.​ramsar.​org/​sites/​default/​files/​documents/​library/​current_​convention_​text_​e.​pdf.
 
226
Salman (2014), p. 344. Sudan joined the Ramsar Convention on 7 May 2005, and South Sudan on 10 October 2013. See Ramsar Convention, Country profiles, http://​www.​ramsar.​org/​country-profiles.
 
227
Mulira (2010), p. 136.
 
228
ILC, Draft Articles on the Law of the Non-Navigational Uses of International Watercourses and commentaries thereto adopted by the Drafting Committee on second reading, YBILC 1994, Vol. II, Pt. 2, pp. 101–102, para. 4.
 
229
Internal renewable water resources are the annual flow of rivers and recharge of aquifers generated from endogenous precipitation. FAO Aquastat, Glossary, http://​www.​fao.​org/​nr/​water/​aquastat/​data/​glossary/​search.​html?​submitBtn=​-1&​termId=​4157.
 
231
Ibid.
 
232
Ibid.
 
233
Elemam (2010), p. 221.
 
235
For details see ibid. See also FAO (2005), p. 203.
 
237
Brown Weiss (2013), p. 66. For example UNEP (2012), pp. 105–106.
 
238
UNEP (2012), pp. 105–106; Brown Weiss (2007), pp. 163 and 382–383.
 
239
Türk (2012), p. 1062.
 
240
UNEP (2012), p. 106, Fig. 4.6 “Virtual water imports, exports and flows around the world”.
 
242
Taha (2010), p. 205.
 
244
The overlap between surface water (120 billion cubic meters) and groundwater (20 billion cubic meters) amounts to 18 billion cubic meters, bringing the total amount of internal renewable water resources to 122 billion cubic meters. FAO Aquastat, Ethiopia, Water resources database, http://​www.​fao.​org/​nr/​water/​aquastat/​countries_​regions/​ETH/​.
 
245
This consists of 2.7 billion cubic meters of surface water and 0.5 billion cubic meters of groundwater, with an overlap of 0.4 billion cubic meters. FAO Aquastat, Eritrea, Water resources database, http://​www.​fao.​org/​nr/​water/​aquastat/​countries_​regions/​ERI/​.
 
246
These external water resources entering the country are mainly surface water from border rivers. Ibid.
 
247
This total water volume consists of 26 billion cubic meters of internally produced surface water and 4 billion cubic meters of groundwater per year, with an overlap of 4 billion cubic meters. See FAO Aquastat, South Sudan, Water resources database, http://​www.​fao.​org/​nr/​water/​aquastat/​countries_​regions/​SSD/​index.​stm.
 
248
Ibid.
 
249
This total water volume consists of 39 billion cubic meters of internal surface water and 29 billion cubic meters of groundwater per year. As the overlap between surface water and groundwater reaches 100% of the groundwater recharge, the total amount of internal renewable water resources remains at 39 billion cubic meters. FAO Aquastat, Uganda, Water resources database, http://​www.​fao.​org/​nr/​water/​aquastat/​countries_​regions/​uga/​index.​stm.
 
250
Ibid.
 
251
Of these, 20.2 billion cubic meters is surface water and 3.5 billion cubic meters groundwater, with an estimated overlap of 3.5 billion cubic meters. FAO Aquastat, Kenya, Water resources database, http://​www.​fao.​org/​nr/​water/​aquastat/​countries_​regions/​KEN/​.
 
252
Ibid.
 
253
Mwiandi (2010), p. 109.
 
254
Of these, 80 billion cubic meters is surface water and 30 billion cubic meters is groundwater, with an overlap of 26 billion cubic meters. FAO Aquastat, United Republic of Tanzania, Water resources database, http://​www.​fao.​org/​nr/​water/​aquastat/​countries_​regions/​TZA/​.
 
255
See also FAO Aquastat, United Republic of Tanzania, Water resources, http://​www.​fao.​org/​nr/​water/​aquastat/​countries_​regions/​TZA/​index.​stm.
 
256
FAO Aquastat, United Republic of Tanzania, Water resources database, http://​www.​fao.​org/​nr/​water/​aquastat/​countries_​regions/​TZA/​.
 
257
Of these, 10.06 billion cubic meters is surface water and 7.47 billion cubic meters is groundwater, with an overlap of 7.47 billion cubic meters or 100%. FAO Aquastat, Burundi, Ressources en eau, base de données, http://​www.​fao.​org/​nr/​water/​aquastat/​countries_​regions/​BDI/​.
 
258
The Kaburantwa River is not part of the Nile River system.
 
259
FAO Aquastat, Burundi, Ressources en eau, base de données, http://​www.​fao.​org/​nr/​water/​aquastat/​countries_​regions/​BDI/​.
 
262
This total water volume consists of 9.5 billion cubic meters of internal surface water and 7 billion cubic meters of groundwater per year. As the overlap between surface water and groundwater is 7 billion cubic meters, the total amount of internal renewable water resources remains at 9.5 billion cubic meters. FAO Aquastat, Rwanda, Ressources en eau, base de données, http://​www.​fao.​org/​nr/​water/​aquastat/​countries_​regions/​RWA/​.
 
263
Ibid.
 
264
Of this total water volume, 899 billion cubic meters is surface water and 421 billion cubic meters is groundwater, with an estimated overlap of 420 billion cubic meters. FAO Aquastat, République démocratique du Congo, Ressources en eau, base de données, http://​www.​fao.​org/​nr/​water/​aquastat/​countries_​regions/​COD/​indexfra.​stm.
 
265
FAO Aquastat, République démocratique du Congo, Ressources en eau, http://​www.​fao.​org/​nr/​water/​aquastat/​countries_​regions/​COD/​indexfra.​stm.
 
266
See also Dellapenna (2003), p. 187: “Any attempt to treat the list of relevant factors as an algorithm simply misses the point.”
 
267
Art. 24, para. 12 of the CFA.
 
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Metadata
Title
Implementing the Principle of Equitable and Reasonable Utilization in the Nile Basin
Author
Philine Wehling
Copyright Year
2020
Publisher
Springer Berlin Heidelberg
DOI
https://doi.org/10.1007/978-3-662-60796-1_9