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120

L. Camara and M. B. de Mesquita

8.1Geographical Survey About Terraced Landscapes in Peru

Peru has vast terraced areas, and, since the 1980s, an attempt has been made to identify and develop an inventory of the terraced system. In 1982, Masson (1994) estimated one million hectares of terraces. That gure is based on the natural resource inventories and evaluations developed by ONERN (Ocina Nacional de Evaluación de Recursos Naturales; National Ofce for the Evaluation of Natural Resources) between 1968 and 1982 on the western side of the Andes. ONERNs goal was knowledge of the conservation status of terraced surfaces, but it should be emphasized that ONERN published neither the survey nor an ofcial cartography of functional and abandoned terraces.

In 1996, INRENA (Instituto Nacional de Recursos Naturales; National Institute of Natural Resources) determined the existence of 256,945 ha of pre-Hispanic terraces in eight Peruvian regions. Until recently, no other national inventory had been conducted.

However, in 2010, AgroRural led the initiative. AgroRural (the Rural Agricultural Productive Development Program) is part of the Ministry of Agriculture, and it initiated a major project to inventory and characterize the agricultural terraces of 95 municipalities in 11 Peruvian regions. The municipalities were selected via several indicators: the presence of at least 50200 terraced hectares, which justies structural intervention for water access; the importance of the municipality itself and the role it plays within the province; the farmerswillingness to work on terraces; communication mechanisms between the municipality and markets; and the presence of municipal, rather than private, land. This latter indicator was considered because community work is more benecial to the population than individual labor, which requires a larger workforce.

Operating along the Andes Mountains, the AgroRural project aims to gather a base of territorial knowledge, develop innovative technologies, and implement recovery interventionspromoting a large-scale territorial transformation. Fundamentally, the objective is coordinating social and institutional strategies to develop a recovery program for specic areas (micro-basins). These micro-basins can be the subjects of a basic pilot programstudying them, developing investment programs and public policies to recover abandoned terraces, and harnessing the terracespotential to counteract the effects climate change has on agricultural production.

The AgroRural inventory has attempted to document areas with the highest concentration of terraces regionally. The programs objective is not to detect and describe all terraced areas, but, rather, to document maximum production capacity and the possibility of socio-economic investment returns.

As shown in Table 8.1, AgroRurals systematization and inventory of agricultural terraces has cataloged 340,719.11 terraced hectares, of which 259,319.04 are in use and 81,400.06 abandoned. AgroRural also estimates another 150,000 ha of

8 Terraced Landscapes in Perù: Terraces and Social Water Management

121

Table 8.1 Inventory of

 

 

 

 

Region

State of terraces

Total (ha)

terraced areas in Peru

 

In use (ha)

Abandoned (ha)

 

 

 

 

 

Cusco

43,273.09

16,029.81

59,302.90

 

Lima

35,066.91

20,927.97

55,994.89

 

Ayacucho

36,655.33

9723.89

46,379.22

 

Apurimac

30,652.48

13,475.02

44,127.50

 

Arequipa

35,276.36

7680.05

42,956.41

 

Puno

20,705.62

2828.65

23,534.27

 

Huancavelica

17,634.44

4244.55

21,878.99

 

Tacna

11,174.67

2709.33

13,884.00

 

Moquegua

11,247.23

1739.77

12,987.01

 

Amazonas

11,121.77

539.68

11,661.44

 

Junin

6511.13

1501.34

8012.48

 

Total

259,319.04

81,400.06

340,719.11

 

Source Eguren and Marapi (2014)

 

terraces that were not included in the program. This report concludes that the regions with the most terraced hectares are Cusco, Lima, and Ayacucho.

Considering the municipalities involved in the program and eldwork in different communities of four regions, the altimetry of densely terraced areas can be identied.1 Most of the inter-Andean valleys are between 2500 and 4000 m above sea level. The terraced areas corresponding to the lowest altitudes (23003500 m) are the best preserved and used for agricultural production, as can be seen in Fig. 8.1. The terraces of Andamarca in the Ayacucho region are located at an altitude ranging from 3100 to 3400 m. Terraces higher than 3500 m are usually abandoned and, in a few cases, are covered by weeds and small shrubs.

The terraces at 25003500 m have a temperate climate, support a wide variety of crops, and have a vegetative cover of greater intensity than the higher terraces. In addition, irrigation facilities (canals, springs, lagoons, wetlands, etc.) are wellconserved, and rainfall is more regular, ranging from 500 to 1000 mm per year.2 The clivometric prole has very accentuated values, ranging between 15 and 75%. Among the terraces with slopes up to 50%, cultivable surfaces can have an area of up to 30 m, and wall heights vary from 1 to 4 m. Slopes above 70% show a decrease in the average surface of the embankments up to a maximum of 2.0 m, and

wall heights vary from 2.5 to 10 m.

Terrace crops are characterized by a high degree of biological diversity and vary according to the altitude. Many species and varieties are cultivated: grains and

1Because AgroRural has not published its full study, the data analyzed here are the result of the authors eld experience reconnaissance.

2SENAMHI (2009)

122

L. Camara and M. B. de Mesquita

Fig. 8.1 Well-preserved terracing in Andamarca. Photo L. Camara

cereals, legumes, tubers, vegetables and spices, fruits, fruit trees, native trees, etc. (Tovar 1995; Tapia and Fries 2007). An important aspect of agronomic knowledge is crop managementoptimizing sowing and harvesting, developing specic methods of conservation and soil fertilization, choosing cultivable varieties, and understanding the available technologies.

The mechanisms regulating soil fertility in the Andes are modulated by many variablesclimatic, altimetric, pedological, topographic, crop intensity, etc. Farmers in the area practice crop rotation and cultivate different types of plants in the same terrace to encourage a symbiotic relationship between the cropsfeeding, not just the harvest, but also the land. Such mechanisms imitate nature by diversifying plant species. In most agricultural systems, both practices combine to ensure biodiversity.

Most farmers grow 1215 plots regularly and others on rotation. Crop distribution is extremely heterogenous. Some elds have only one crop, others more, sometimes in alternating rows, often cultivated in small plots of 2025 m2 with 3040 different cultivars. Some may even have 100 different cultivars, thanks to a socially regulated exchange. This heterogeneity involves continuous experimentation, not only to avoid risks, but, above all, to create new varieties; this favors hybridization and crossbreeding between different crops. The local varieties, in fact, are most suited for the climate and the soil, and they express their best potential in the territory where they have acclimated over the centuries. For this reason, they are

8 Terraced Landscapes in Perù: Terraces and Social Water Management

123

more resistant and require less external interventions. They are, therefore, more sustainable, both from an environmental and an economic point of view. In this sense, biodiversity is conrmed a unique and precious heritage: genetic but also cultural, social, and economic.

The following map (Fig. 8.2), elaborated with AgroRurals data, shows the regional distribution of terracing in the Lima region. Mostly, Lima has a high percentage of abandoned areas respect to inventory, most of them are also uncultivated lands or difcult to dene. One of the causes is the emigration trends. For example, in 23 of 33 municipalities in the province of Yauyos the population does

Fig. 8.2 Terraced areas in Lima region (elaborated by Francesco Ferrarese and Lianet Camara on data provided by AgroRural)