40 | Central and West Asia and North Africa (CWANA) Report

Table 2-2. Land degradation: Severity of human-induced degradation in CWANA.

Total area (1000 km2)

None

Light

Moderate

Severe

Very
severe

Cause

Type

(%)

North Africa

5,552

50.6

12.8

10.5

25.4

4.6

A, O, D

N, W, C

Nile Valley and Red Sea

4,581

42.4

16.2

17.5

14.2

2.4

A, O, D

N, W, C

Arabian Peninsula

2,374

24.0

34.3

20.2

32.4

6.0

A, O, D

N, W, C

South and West Asia

4,551

8.2

4.3

31.6

39.6

17.3

A, O, D, V

N, W, C, P

Central Asia and Caucasus

3,998

57.9

11.4

15.8

13.3

2.1

A, O, D

N, W, C, P

Cause: A = agriculture; D = deforestation; O = overgrazing; V = over exploitation of vegetation

Type: C = chemical deterioration; N = water erosion; P = physical deterioration; W = wind erosion

Source: Terrastat, FAO database, 2006.

has resulted in rising groundwater and soil salinization. For instance, nearly half the irrigated lands in Central Asia are affected by salinity (Kijne, 2005). The largest part of saltaffected soils and saline waters exists in the lower reaches of Amu-Darya and Syr-Darya basins, where salinity threatens food production.

2.1.5.2 Water-quality deterioration

Wastewater from household, municipal and industrial activities; agricultural drainage containing residues of pesticides, fertilizers and soil and reaction products of amendments; and overexploitation of brackish groundwater are the major contributors to deteriorating water quality in CWANA (Qadir, Sharma et al., 2007). In addition, drought has a negative influence on aquatic and land ecosystems and on the quantity and salinization of surface water and groundwater. More than half the major rivers in CWANA are seriously depleted and polluted, degrading surrounding ecosystems and threatening the health and livelihoods of the people depending on these rivers.

 

Wastewater and sludge. Water diverted for household, municipal and industrial activities generates wastewater containing undesirable constituents, depending on the source of the wastewater and its treatment. In most countries of CWANA, domestic wastewater is not segregated from industrial wastewater and other activities (Qadir et al., 2007). The wastewater is often discharged, untreated, into open drains, sometimes getting mixed with storm or fresh water. It is then channeled into natural water bodies or used in agriculture. In some cases, wastewater undergoes treatment.

Most wastewater treatment plants are of simple design or not adequately functioning in the region. Wastewater is diverted to farmers' fields-treated, partly treated, diluted or untreated. It is used by urban and periurban agriculture to grow crops, with vegetables being the most common, across CWANA (Lazarova and Bahri, 2005). Grain, fodders and industrial crops are cultivated as a secondary preference. In addition, parks, sports grounds and road plantings are irrigated with wastewater. Examples of wastewater aquaculture are also found in countries such as Kazakhstan.

Table 2-3. Major soil constraints in CWANA.

Total area
 (1000 km2)

Sodicity

Shallowness

Erosion risk

(%)

North Africa

5,552

0.2

22.0

8.0

Nile Valley and Red

4,581

1.5

21.8

8.6

Sea

Arabian peninsula

2,374

0.0

22.6

7.4

South and West Asia

4,551

0.9

25.8

19.6

Central Asia and

3,997

28.4

16.3

5.0

Caucasus

Source: Terrastat, FAO database, 2006.