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Selecting and testing nitrogen fixing trees for acid soils

 

 

Agroforestry for the Pacific

Technologies

A publication of the agroforestry Infonnation Service c\o "TA/Winrock" International Rt. 3. Box :376. Morrllton AR 72110 USA

 

Acid soils the problem

How to practice low-input sustainable agriculture on marginal soils is a dilemma for small-scale fanners and government agencies responsible for providing technical assistance. This dilemma is greatest in tropical countries where population pressure is intense and much of the soil is acid and contains toxic levels of aluminium (Caudle, 1991). In the humid tropics, the relative importance of acid soils is greatest in Latin America (81%), but also significant in Africa (56%) and Asia (38%) (Sanchez, 1987).

By definition, any soil with a pH of less than 7 is acidic but the detrimental conditions for plant growth may not appear until soils have a pH of 5.0 or less. The main problems for plant growth on acid soils are infertility (low reserves of plant nutrients) and levels of exchangeable Al and manganese that are toxic to plants. Low nitrate levels and detrimental effects of high hydrogen ion concentration on plant growth may occur in some soils. The most common problem is aluminum toxicity, which generally inhibits root penetration below 1520 cm. Manganese toxicity may be associated with higher pH levels than Al toxicity.

Soil acidity and aluminum toxicity constrain agricultural production in several ways. Farmers are limited to planting crop species or cultivars that tolerate such conditions. Many acid soils "fix" or hold phosphorus, making it unavailable for plant growth. Soil acidity can also be a barrier to root development, limiting a plant's ability to reach moisture in the subsoil. In the humid tropics, soil acidity and associated problems often lead to land abandonment and the perpetuation of slash-and-burn agriculture (TropSoils, 1991).

The use of species or cultivars tolerant-of acid soils is the first step for low-input soil management (Sanchez and

Salinas, 1981; Reddell, 1993). In addition, agroforestry is considered particularly applicable to marginal soils with severe physical, chemical or drought constraints (Sanchez, 1987).

On acid soils of the tropics, the fundamental challenge is to recycle the limited nutrients available in soil-plant systems (Sutherland and Sprent, 1993). Planting nitrogen fixing trees (NFTs) and crops in agroforestry systems is one low-input technology that helps maintain levels of nitrogen a key nutrient for plant growth. Nitrogen fixing trees are also grown for wood production, shade and support for crops, live fence posts, green manure, human food, as shelterbelts and windbreaks, browse or fodder for domestic animals, and as ornamentals.

Choosing the right species

In establishing an agroforestry system on an acid soil, the first step is to identify suitable tree species. Once the best available species are identified, further investigation is needed to determine their value for agroforestry.

In choosing nitrogen-fixing tree species, careful attention should be given to select species that are adapted to local environments and that provide farmers with products and services they need. This is best done through field visits, personal interviews with farmers, and careful research. The following steps are a guide to selecting NFTs for acid soils.

1. collect information on climate, characteristics, and soils of the planting site(s)

2. determine what products and services trees should provide

3. make preliminary species selections based on information in one and two above

4. research species to verify selections

5. determine if species are native or naturalized at the planting site(s)

6. if exotic species are selected, conduct field trials to determine adaptation.

Collect information on the planting site(s)

The first research priority is to collect as much information as possible on the climate, characteristics and soils of the planting site(s). Minimum information on climate and characteristics should include:

• elevation

• average annual rainfall

• distribution of rainfall

• average annual temperature

• maximum and minimum temperatures

• incidence of frost

• number of months with less than 50 mm precipitation

• topography, including slope and aspect (N,S,E,W)

Minimum soil information should include texture, depth, drainage and pH. Include information on phosphorus, aluminum, calcium, potassium, magnesium and manganese, if available.

Testing kits and digital probes are widely available to determine pH. However, a pH test is only a general indication of soil acidity and does not indicate the level of aluminum or manganese in the soil. A good soil-testing laboratory, if available, can estimate the percent aluminum saturation - a good indicator of Al toxicity. A simple test can be run to determine manganese toxicity, if no information exists. Apply a solution of 5 percent hydrogen peroxide to a sample of soil. If the solution bubbles, the soil is likely to cause manganese toxicity in plants. The symptoms of manganese toxicity are small, stunted plants with crinkled leaves with small brown spots. Liming to pH 5.8 or 6 will correct the problem for most plants (Caudle, 1991). However, liming tree crops may not be economical.

Determine products and services trees should provide

Careful research is necessary to determine which species will provide needed products and services in a given area. This is often best done through personal interviews with farmers and study of local tree-use markets. It is important that tree species are accepted within local cultures.

Some species can be hosts to pests and diseases. For example, Erythrina species in parts of the South Pacific are host to a fruit piercing moth (Othreis fulionia Clerck). The adults damage important commercial fruits such as oranges, guava, carambola, papaya, and banana. causing serious economic losses (Muniappan, 1993).

Select species

A preliminary selection of NFTs can be mace with basic inforrnanon on climate and soils in hand. A list of NFTs for acid soils (pH 5.0 or less) and given climatic ranges on the following page may be used as a guide to select species. Underlined species are reported to grow well in soils with greater than 60% aluminum saturation.

Research species

Once species are selected, collect as much information on them as possible to verify that they are the best available choices. NET Highlights by the Nitrogen Fixing Tree Association (NFTA) are handy references - highlights are available for species marked with asterisks in the list on the next page.

Are species native or naturalized?

After preliminary selection of NFTs, further research is needed to determine if selected species are native or naturalized in the area of interest If species are present, their physical appearance would give an indication of how well they are adapted. If species are not present, then simple field trials should be conducted to determine how they will grow at the site.

Field trials to evaluate exotic species

In a Guide to Establishing Research and Demonstration Plantings with Nitrogen-Fixing Tree Species, Macklin et al. (1989' recommend a simple low-input design for species screening in situations where land, labor and technical expertise may be limited

 

Nitrogen-Fixing Tree and Shrub Species Tolerant of Acid Soils and Listed for Given Climatic Ranges

Mean Annual Rainfall >1000 mm

Mean Annual Temperature

Greater than 20°C

Less than 20°C

Acacia angustissima

Acacia. koa

Recta auriculiformis'

Acacia mearnisit

Acacia mangium

Acacia melanaxylon

Albizia lebbeck"

Alnus acuminata

Albizia saman'

enterolobuim cyclocarpum

Calltarandra calothrysus''

Chamaecytisus polments

Casuarina cunninghamiana

Ingana codonantha

Casuaria junghuhniana

Mimosa scabrella

Casuarina sumatrana"

Robinia pseudoacacia''

Cedrelinga catenaeformis

 

Cratylta argentea

 

Dalbergia nigra

 

Desmodium gyroides

 

Desmodium intortun

 

Desmodium nicaraguese

 

Desmodium velutinum

 

Enterolobium cyclocarpum

 

Enterolobium contortisiliguum

 

Erythrina abyssinca

 

Erythrina poeppigiana

 

Erythrina fusca

 

Erythrina variegata

 

Erythrina macrophulla

 

Erythrina sepium

 

Inga acrocephala

 

Inga marginata

 

Inga punctata

 

Inga spectabilis

 

Mimosa caesalpinaefolia

 

Paraserianthes falcataria

 

Pithecellobium dulce

 

Pterocarpus indicus

 
   

Mean Annual Rainfall 500 - 1000 mm

Men Annual Temperature

Greater than 20°C

Less than 20°C

Acacia holosericea'

Albizia lebbeck''

Albizia lebbeck.'

Casuanna cunninghamiana

Casuanna cunninghamiana

Chameticus palmensins

Enterolobium cyclocarpum

Enterolobiurn cyclocarpum

Gliricidia sepium''

Pithecellobium dulce

Pithecellobium dulce''

Robinia pseudoacacia"

Mean Annual Rainfall < 500 mm

Men Annual Temperature

Greater than 20°C

Less than 20°C

Acacia aneura'

Acacia aneura

Acacia holosericea'

Aiblzia lebbeck"

Albizia lebbeck

Alinus glutinoasa

Casuarlna cunningamiana

Pithecellobium dulce

Pitheceliabium dulce

 

 

Example design for a screening trial with 12 species. Each letter represents a different species, each letter within a block represents an individual tree, bold letters are trees to be measured.

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. These trials may be conducted by community organizations (farmer, church or women's groups), rural development workers (extension agents, staff of non-governmental organizations or Peace Corps Volunteers),or other types of grass-roots organizations and local government offices. Trials normally involve unreplicated plots of a relatively large number of species.

Soil and climatic conditions at the trial site should be similar to the entire planting area. If the planting area includes different environments, a should be established in each environment. It is important to select a homogeneous site for the trial to eliminate differences in soil fertility, water availability, etc. between plots.

Tree spacing should be 1 m x 1 m or 2 x 2 m. The closer spacing is appropriate for trials that will be maintained for only a year or two. Each species should be planted with at least one border row of trees around the block that will not be measured-they are likely to be affected by trees in adjoining blocks, or have increased growth on field edges. It is recommended to have at least 16 inner trees to measure (6 rows of 6 trees each). Larger blocks with a greater number of trees are recommended for longterm analysis (more than 2 years).

It is important to include indigenous and nonNFTs in screening trials for comparison. In particular, species already prominent in local forestry efforts should be included. This will enable better evaluation of new species. Naturalized species should be included when possible as they may have undergone some adaptation and selection and could prove superior.

Data collection

Measure tree survival, height and diameter at 6, 12, and 24 months after transplanting - the schedule will depend on local growing conditions. Calculate mean height, diameter and number of stems for each species after each measurement. Basal diameters are taken the first year or until diameter at breast height can be taken.

Caution! Some NFT species will be new to an area, and nothing will be known about their performance. Many introduced tree species have the potential to become weedy in new environments by invading pasture and agricultural lands, and/or crowding out native vegetation. Any species, particularly thorny or non-fodder, that begins to exhibit weediness - prolific seed production or rapid, heavy, natural seedling establishment - should be watched carefully. Such species should be considered for eradication, especially if they have no clear potential for use.

 

Further reading

Caudlc, N. (cd). 1991. Groundworks 1. Managing Soil Acidity.

Raleigh, NC: TropSoils, 28. p.p.

ECM. 1990. AUcy cropping on acid soils. PhD dissertation. Ralcigh, NC: Dept. of Soil Science, North Carolina

State Univ., 157

Macklin B., Glover, N., Chamberlain, J. and Treacy, M. 1989. A guide to cstablishme of research and demonstration plantings of nitrogen fixing trees. Malrilinton, AR NFTA, 36 pp.

Muniappan R. 1993. Pests and diseases. In M. Powell and S.

Westley (eds), Erythrina productions and a field manual.

Morrilton, AR. NFTA, 55 pp.

Reddell, P. 1993. Soil can straints tO growth of nitrogen-fixing trees tropical environments. ln: N.S. Subba Rao amd C.

Rodriguez-Barmcco (cds), Symbiosis in nitrogen fixing trees.

New Delphi: Oxford and IBH Publishing Co, pp. 65-79.

Sanchez, PA. 1987. Soil productiviy and sustainability in agroforestry systems. In: H.A Steppler and P.K.R Nair (cds),

Agroforestry: A Decade of Devedoprnent. Nairobi: ICRAF, pp.

205-23.

Sanchez, P.& and Salinas, J.G. 1981. Low input technology for managing Oxisols and Ultisols in Tropical Amcrica. Adv.

Agron., 34:279-06.

Sutherland, J.M. and Sprent, Jl. 1993. Nitrogen fixation by legume trees. In: N.S. Subba Rao and C. Rodriguez-BaTTueco

(eds), Symoiosis in nitr~ogen-f~ing trees. New Delhi: Oxford and BH Publishing Co, pp. 33-54.

TropSoils. 1991. TechnicaiReportforl988-1989. Raleigh, NC:

TropSoils Management Entity, 357 pp.