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Aquaculture, fish resources and rural livelihoods: a village CGE analysis from Namibia’s Zambezi Region

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Abstract

Aquaculture is widely recognised as a way to reduce malnutrition and poverty. So far, research has mainly focused on Asia, and the few studies available from sub-Saharan Africa are predominantly ex-post partial analyses. By constructing a village computable general equilibrium (CGE) model, we aim to investigate whether aquaculture improves local livelihoods and simultaneously has the potential to counteract local overfishing. We apply this to a rural case study region in Namibia where malnutrition, poverty and fish resource overexploitation are current problems. Our village CGE model shows that aquaculture would be a viable livelihood activity improving household incomes and utility through labour reallocations. Furthermore, aquaculture can counteract malnutrition through increased fish consumption. Higher opportunity costs lead to households leaving the fisheries and switching to aquaculture. These substitution effects offer the possibility of reducing the pressure on local freshwater fish stocks. Policy makers can use the results to introduce aquaculture interventions in rural areas. Our findings indicate that such interventions should take particular account of the poorest households, which are most dependent on fisheries. The derived opportunity costs provide information about payments that are necessary to make policy interventions acceptable for different household groups.

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Fig. 1
Fig. 2

Source: Own figure based on Lofgren et al. (2002)

Fig. 3

Source: Own figure

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Notes

  1. For a detailed specification of the class of CGE model used, see Lofgren et al. (2002).

  2. The key modelling power of complementarity is that it chooses which inequality to satisfy as equality. Complementary slackness means that for each choice variable we must find the optimal solution that either (1) the marginal condition holds with a strict equality; or (2) the choice variable in question must take a zero value; or (3) both of the above (Bishop et al. 2001). This implies: if there is slack in a constrained resource (leftovers), then additional quantities of that resource must have no value. Likewise, if there is slack in the (shadow) price non-negativity constraint requirement (i.e. the price is not zero) then there must be scarce supplies (no leftovers).

  3. GAMS is designed for the construction and solution of large and complex mathematical programming models. It enables solving of various kinds of economic models including linear and nonlinear optimisation as well as equilibrium modelling (Brooke et al. 1992).

  4. The consumer bundle of the case study region includes maize, beef, milk, fish, rice, wheat, noodle, oil, potato, orange, bread, chicken, egg and non-food items.

  5. In contrast, the Armington (1969) assumption is based on imperfect transformability and substitutability. He used constant elasticity of substitution for imports and constant elasticity of transformation for exports, which mathematically avoid a total elimination of unproductive trade flows. Hence, he did not allow any regime shifts. No country ever shifts completely from importing or exporting a commodity (Ackermann and Gallagher 2008).

  6. This is ensured by simultaneous adjustments in three (endogenous) components of absorption: household consumption, investment quantity and government consumption. Under other investment-driven closures (value of savings adjusts), the quantities of investment and government consumption are both fixed, only household consumption is flexible (Lofgren et al. 2002).

  7. Marginal interventions cannot be estimated reliably within the modelling system.

  8. A SAM is a comprehensive economy-wide data framework and represents the whole economic system by explaining all payments within the economy for a single year. It plays an important role in policy planning at the regional and village level (Morton et al. 2016).

  9. Overall robustness: the CGE results remained robust when applying an alternative production function (Cobb–Douglas).

  10. Livelihood diversification can be defined as the process by which rural households construct a diverse portfolio of activities in order to survive and to improve their standards of living (Ellis 1998).

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Acknowledgements

This article has been written in the context of the project ‘SASSCAL—Southern African Service Science Centre for Climate Change and Adaptive Land Management’ (http://www.sasscal.org/). The project is funded by the German Ministry of Education and Research (BMBF) [01LG1201H].

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Correspondence to Steven Gronau.

Appendices

Appendix A: Stylised social accounting matrix of the Sikunga Conservancy

 

Activities

Commodities

(A1)

(A2)

(A3)

(A4)

(A5)

(A6)

(C1)

(C2)

(C3)

(C4)

(C5)

(C6)

(C7)

(C8)

Activities

 (A1) Maize

      

14.08

       

 (A2) Rice

       

187.20

      

 (A3) Livestock

        

58.55

     

 (A4) Fish resources

         

64.13

    

 (A5) Forest resources

          

765.29

   

 (A6) Off-farm employment

           

89.76

44.10

4.40

Commodities

 (C1) Maize

4.92

             

 (C2) Rice

     

0.48

        

 (C3) Livestock

              

 (C4) Fish resources

   

12.67

          

 (C5) Forest resources

              

 (C6) Off-farm employment

              

 (C7) Food items

     

21.36

        

 (C8) Non-food items

     

3.90

        

Factors

 (F1) Unskilled labour

8.80

42.85

49.18

19.33

35.99

63.40

        

 (F2) Skilled labour

 

13.85

   

48.28

        

 (F3) Land

7.80

130.51

16.27

  

0.85

        

 (F4) Livestock

  

7.23

           

 (F5) Fish

   

44.25

          

 (F6) Forest

    

786.22

         

Institutions

 (H1) Subsistence farmers

              

 (H2) Fish and forest users

              

 (H3) Skilled off-farm

              

 (H4) Senior members

              

 (H5) Government

              

(H6) Conservancy

              

 (H7) Other

              

Capital

(S1) Cash savings

              

(S2) Agricultural capital

              

(ROW) Rest of World

      

41.95

4.69

9.22

10.11

0.83

21.14

69.85

70.74

Totals

21.52

187.21

72.68

76.25

822.21

138.27

56.03

191.89

67.77

74.24

766.12

110.90

113.95

75.14

 

Factors

Institutions

Capital

 

(F1)

(F2)

(F3)

(F4)

(F5)

(F6)

(H1)

(H2)

(H3)

(H4)

(H5)

(H6)

(H7)

(S1)

(S2)

(ROW)

Activities

 (A1) Maize

      

3.05

2.39

0.96

1.05

      

 (A2) Rice

                

 (A3) Livestock

      

4.03

2.38

1.22

6.50

      

 (A4) Fish resources

      

1.95

8.18

0.03

1.96

      

 (A5) Forest resources

      

25.83

20.31

5,84

4.95

      

 (A6) Off-farm employment

                

Commodities

 (C1) Maize

      

18.09

11.83

5.52

6.51

    

1.41

7.75

 (C2) Rice

      

1.82

1.71

0.88

1.04

     

185.96

 (C3) Livestock

      

1.86

2.01

1.05

4.31

    

39.90

18.65

 (C4) Fish resources

      

3.39

1.68

1.06

2.13

     

53.30

 (C5) Forest resources

      

0.24

0.07

0.06

0.46

 

748.98

  

12.65

3.67

 (C6) Off-farm employment

      

7.84

4.20

3.97

5.98

32.89

39.86

11.13

  

5.04

 (C7) Food items

      

17.45

11.39

9.51

10.14

     

44.10

 (C8) Non-food items

      

24.45

16.11

11.59

14.69

     

4.40

Factors

 (F1) Unskilled labour

               

27.20

 (F2) Skilled labour

               

58.97

 (F3) Land

                

 (F4) Livestock

                

 (F5) Fish

                

 (F6) Forest

                

Institutions

 (H1) Subsistence farmers

76.46

14.98

5.55

3.76

1.21

9.10

    

17.82

 

0.66

  

12.72

 (H2) Fish and forest users

62.66

12.68

7.70

2.48

5.15

12.31

    

9.00

    

6.41

 (H3) Skilled off-farm

69.46

92.62

3.15

− 0.57

0.13

1.31

    

2.52

    

2.06

 (H4) Senior members

16.62

0.81

7.67

1.56

0.20

1.88

    

16.54

 

5.28

  

5.87

 (H5) Government

  

130.51

             

 (H6) Conservancy

  

0.85

 

37.55

761.62

          

 (H7) Other

      

0.85

0.62

0.23

0.52

      

Capital

 (S1) Cash savings

      

14.86

13.02

121.76

− 20.94

51.73

11.19

− 14.85

   

 (S2) Agricultural capital

      

14.54

20.58

6.29

12.54

      

 (ROW) Rest of World

21.55

     

2.03

1.92

0.72

4.59

   

176.78

  

Total

246.75

121.09

155.43

7.23

44.25

786.22

142.26

118.4

170.69

56.43

130.5

800.03

2.22

176.78

53.96

436.10

  1. Values reported in one-thousand US Dollars

Appendix B: Aquaculture module input data

Requirement of a 665 m2 fish pond

References

Fingerlings (1000 pieces per year at 0.1 US$ each)

Murphy and Lilungwe (2012)

Feed (nearly 500 kg maize bran per year at 0.175 US$ per kg)

Gronau et al. (2017), Hilundwa and Teweldemedhin (2016)

Fertiliser (almost 600 kg manure per year at 0.75 US$ per kg)

Nunoo et al. (2014), Quagrainie et al. (2005)

Labour costs (clearing, feeding, harvesting, monitoring, recording) at 0.51 US$ per m2

Nunoo et al. (2014)

Construction (approximately 5 labourers at 3 US$ per day and 20 days) at 300 US$

Hilundwa and Teweldemedhin (2016)

Equipment (e.g. shovels, hooks, pick-axes, tanks/buckets, boats, wheelbarrow, fishing gear) at 150 US$ (0.075 US$ per m2)

Nunoo et al. (2014)

Depreciation is based on a productive life of 10 years for a pond and 3 years for the equipment (i.e. 10 and 33% respectively per year must be replaced).

Nunoo et al. (2014)

Land at 98.72 US$ per pond (factor value).

Own estimation

Fish at 0.4 US$ per kg (factor value).

Morton et al. (2016)

Fish at 1 US$ per kg (home consumption) and 2 US$ per kg (market sales)

Murphy and Lilungwe (2012); NNF (2013)

Harvesting is done once or twice a year and produces a yield of 1020 kg.

Murphy and Lilungwe (2012)

Appendix C: Food composition table (FAO 2012; WFP 2017b)

Per 100 g

Energy (kcal)

Fat (g)

Iodine (µg)

Iron (mg)

Protein (g)

Vitamin A (µg)

Zinc (mg)

Maize

353

4.5

0.0

3.5

9.0

50.0

1.7

Beef

126

4.3

0.0

2.1

21.7

0.0

3.6

Dairy

63

3.6

15.0

0.2

3.3

40.0

0.3

Fish

86

1.5

40.5

0.9

17.6

21.0

1.3

Rice

353

0.5

0.0

0.7

6.1

0.0

1.1

Wheat

351

1.5

0.0

2.0

10.4

0.0

1.8

Noodle

359

1.5

0.0

1.2

12.5

0.0

1.4

Vegetable oil

900

100.0

11.0

0.0

0.0

0.0

0.0

Potato

80

0.1

0.0

0.9

1.9

1.0

0.3

Orange

45

0.3

0.0

0.2

0.7

8.0

0.1

Bread

249

1.8

6.0

1.2

8.4

0.0

0.6

Chicken

134

5.9

8.0

1.1

20.4

17.0

1.4

Egg

139

9.5

53.0

1.8

12.6

160.0

1.3

Appendix D: Parameters used for production, utility and biological fish growth functions

 

Parameter

Value

Unit

Reference

Fish pond production function

Aggregate intermediate input coefficient

24.6

Percent

Own calculation

Aggregate value-added (factor) coefficient

75.4

Percent

Own calculation

Feed (share parameter of intermediate input use)

31.6

Percent

Own calculation

Fertiliser (share parameter of intermediate input use)

3.3

Percent

Own calculation

Fingerlings and depreciation pond and equipment (share parameter of intermediate input use)

65.1

Percent

Own calculation

Land (share parameter of factor use)

40.1

Percent

Own calculation

Labour (share parameter of factor use)

11.7

Percent

Own calculation

Fish (share parameter of factor use)

48.2

Percent

Own calculation

Utility function

Technical coefficient (ν)

0.25

Coefficient

Winter et al. (2015)

Wealth state of household group 1 and 2 (α and β)

0.2

Exponent

Angelsen (1999) and Winter et al. (2015)

Wealth state of household group 3 and 4 (α and β)

0.9

Exponent

Angelsen (1999) and Winter et al. (2015)

Biological fish growth function

Annual growth rate (r)

10

Percent

FAO (2013)

Carrying capacity in Sikunga Conservancy (Zambezi Region); yield for tropical natural fish production systems (k)

1,600,000

kg

Hay et al. (2002) and Welcomme et al. (2010)

Fish stock in Sikunga Conservancy (Zambezi Region) (F)

1,000,000

kg

Hay et al. (2002)

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Gronau, S., Winter, E. & Grote, U. Aquaculture, fish resources and rural livelihoods: a village CGE analysis from Namibia’s Zambezi Region. Environ Dev Sustain 22, 615–642 (2020). https://doi.org/10.1007/s10668-018-0212-1

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