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Organic Fertilizers in Sustainable Agriculture

It is a difficult task to do well in conventional agriculture; and in my opinion, it is doubly difficult to do well in sustainable agriculture, which is characterized by profitable farming while preserving the environment as much as possible. In fact, switching from conventional to sustainable agriculture is not a simple substitution, such as replacing insecticide with a predator insect or replacing commercial KCl fertilizer with green sand. It is reasonable to say that although more in tune with nature than conventional agriculture, sustainable agriculture is information intensive and requires strong management skills. For example, cultural and biological pest control requires detailed knowledge about a pest's life cycle as well as economic threshold levels of the crop. Similarly, using chicken manure to replace urea as a N source for your crop must take into account the release pattern of organic nitrogen from the manure and the nitrogen demand pattern of your crop, so that the two can be synchronized.

A 1987 survey (WSARE, 1995) shows that 48% of sustainable farmers nation-wide have experienced with nutrient deficiencies. Thus, it is no doubt that soil fertility and plant nutrients are important to farming, whether it is conventional or sustainable. (Although sustainable farming is much broader than organic farming, the two usually use the same standards for soil amendments.)

NITROGEN

Nitrogen is needed by all plants and usually in large quantities. In fact, nitrogen is so important to plant growth, and thus to food and fiber productions of the world, that the two German scientists who first invented the process of making NH3 from atmospheric nitrogen gas (N2) and natural gas-derived hydrogen (H2) won Nobel prizes for their work in the early of this century (Today's Chemists, 1995). For example, average N concentrations needed for normal growth are about 3% for corn and coffee, 4% for tomato, and 2% for macadamia (Tamimi et al., 1994). If plants do not have enough nitrogen, they are stunted. Their leaves are small and pale-colored, sometimes even yellow or reddish-tinted. The reason is that nitrogen is a component of chlorophyll, less nitrogen results in less chlorophyll, thus less green.

Figure 1: Normal vs. Nitrogen-deficient corn leaves

In soils, nitrogen must be present as either NH4+ or NO3- before plants can absorb and use it. That explains why urea [(NH2)2CO + 2H2O ==> 2NH4OH + CO2] and ammonium nitrate (NH4NO3) have been so popular as N fertilizers in conventional farming systems.

In organic farming systems, you cannot use urea nor NH4NO3, nor any synthetic chemicals for that matter. Alternatives must be sought. Table 1 lists the total N content of various organic sources.

Table 1. Total N concentration in common organic sources as compared with urea (46% N). (Adapted from Caplan, 1992; Hue, 1995; Tandon, 1992)
Organic Source Total N (%)
Poultry manure 1.5-3.0
Pig, horse, cow manure 0.3-0.6
Green manure 1.5-5.0
Compost 0.5-2.0
Seaweed meal 2.0-3.0
Sewage sludge 1.0-5.0
Fish waste 4.0-10.0
Blood (slaughter house) 10.0-12.0
Human urine/night soil 1.0-1.5

So on the basis of total N, organic sources would have somewhere between ten and hundred times less N than urea. This means that in order to meet your crop N requirement, say 200 lb N/acre for a crop of sweet corn, you would need:

Urea (46% N) ==> 200lb/0.46 = 435 lbs/acre as urea

or compost (1% N) ==> 200/0.01 = 20,000 lbs/acre as compost or (10 Tons/acre)

This simple calculation shows that you would need large amounts of compost (or most organic N sources) relative to urea in order to supply an equal amount of N. Transportation cost might become a factor here. You might ask: so what? 10 tons/acre is affordable. Thatı s true. A close inspection, however, reveals that the assumption for the above calculation is incorrect. The above calculation had assumed that pound for pound, N from the compost is as readily available for plant uptake as N from urea, which is not true. Unlike urea which can be hydrolized into NH4 nearly instantaneously, nitrogen from compost, first must be released from its organic substrates, and this process may take from several days to several months to complete. In general, depending on types of organic materials and environmental conditions, such as temperature and moisture, only 10 to 50% of N from an organic source would be converted to NH4 in a six-month period (Hue, 1995). Thus, in order to provide 200 lbs N/acre that a crop of sweet corn needs over a growing season of approximately 3 months, you may need to apply from 20 to 50 ton/acre of compost instead of 10 tons as the first calculation had indicated. Now you start wondering if it is practical or economical to apply 50 tons of compost to each acre of your land for a crop of sweet corn. Fortunately, this is more of a requirement only during the transition period (one or two years) from the conventional farming to sustainable farming systems. After about 2 years of using composts or green manures as a N source, N release from previous yearsı applications would reduce the current application rates significantly. That explains why many sustainable farmers have seen their crop yields increase with time (WSARE, 1995).

Synchronization. The need for N fertilizers would be reduced significantly if the crop's N requirement can be timed closely to the nitrogen release from organic sources. Using ourselves as an example, we know that babies and older folks require much less food intake than teenagers or young adults.

The same principle applies to plants. Plants require different amounts of N at different stages of growth: seedlings and senescing plants definitely require much less N than flowering or fruiting plants. We also have known that different organic manures have different N releasing patterns. For example, my students and I (Deenik, Knowlton, and Hue, unpublished data) studied the N release patterns of 10 organic sources; three of them are shown here as an illustration.

This graph tells us a couple of things:

  1. First, don' t count on wood-based composts (blue line) as a source of N. In fact, adding such composts to soils may even cause N deficiency in fast growing crops such as tomato or lettuce as shown below.


    (Hue and Sobieszczyk, unpublished data)

  2. Second, N from chicken manure and chicken manure-based composts (red line) was readily available right after application, then declined gradually with time. The implication is that chicken manure can provide quite large quantities of N the first 4 to 6 weeks after application. Thus, its application should be timed closely to the fastest growing period of the crops.

  3. Third, in the green manure it took about two weeks for the N releasing reaction to start (green line). The green manure released most N between 3 and 7 weeks after application. The release remained low and nearly constant for another month (between 7 and 11 weeks) then started to increase again. We believe that this second phase came from the decomposition of microbially more resistant substrates in the green manure.

The main point is that the N release patterns of organic manures depend on many factors and require experience and knowledge to predict. This translates into the following conclusion:

Successful use of organic manures (whether it is compost, green manure or animal waste) as a N source requires more experience and better knowledge about the manure, the crop, and environmental conditions than the use of chemical fertilizers (e.g., urea).

General properties of N from organic sources.

  1. The availability of N declines as manures age or are composted.

  2. Reported nutrient contents (dry basis) of selected manures and composts.
    ___________________________________________________________________
         Organic material          Total N          P2O5           K2O
    ___________________________________________________________________
    Poultry manure               <------------- lbs/ton------------->
    Fresh broiler/rice hull        80                 50            50
    Fresh layer                    80                120            70
    Aged layer                     40                160            80
    Dairy/steer manure
    Fresh dairy separator solids   40                 15            10
    Aged steer corral scrapings    25                 30            60
    Green manure
    Cowpea                         70                 20            80
    Leucaena                       75                  7            40
    Pigeon pea                     25                 12            30
    Sugarcane                       7                  1            10
    Composts
    Broiler/rice hull              40                 85            50
    Dairy                          25                 25            55
    Dairy/poultry                  30                 40            65
    Water hyacinth                 40                 20            40
    Municipal waste                20                 10            30     
    
  3. Nitrogen from poultry manures (non-composted) is more quickly available than N in manure from cow, horses, and sheep. This is because poultry manure contains significant amounts of uric acid, which is readily decomposable. Also, roughage in cattle and horse diets results in manure that is less readily decomposed due to lignin and cellulose.

  4. Presence of bedding or litter lowers N content by dilution, but its effect on N availability cannot be easily predicted.

  5. Moist manure, when exposed to the air, undergoes significant loss of N as volatile NH3. Nitrogen losses after spreading can be significantly reduced by incorporating the manure --even shallow incorporation is adequate.

  6. Nitrogen in composts is in a more stable form than N in manures. Thus, there is a decreased likelihood of losing compost N from the system. On the other hand, composts containing less than 1.5% total N supply little or no N to crops during the first few weeks after application.

  7. Green manures are fast growing catch crops like clovers, mustard, rye, and vetches that are incorporated into the soil while they are still green in order to improve the soil and to supply N to the associated/subsequent cash crop. A properly managed legume cover crop can fix up to 150 to 200 lb N/a in 3 to 6 months (Bugg and Miller, 1991).

  8. Both manure and compost can improve soil tilth, but the timing and mechanisms may differ.

 

Cover crops and ridge tillage in sustainable farming.

In practice, cover crops such as legumes (e.g., clover, vetch) and grasses are often grown either to supply N to subsequent cash crops or to reduce nitrate leaching and soil erosion. Crop rotation and intercropping have been used to achieve this goal. Work in tropical humid regions of India has shown that corn yields and N uptake increased by 15 to 20% by intercropping with soybean or cowpea. Legume intercropping was equivalent to adding 80 kg N/ha of fertilizer N. A marked synchrony between plant growth stage and microbial population in the rhizosphere 60 days after seeding was observed in this study.

The N release from cover crops, however, depends on many factors, including the C to N ratio of the residue, its degree of incorporation into the soil and soil temperature and moisture regimes. It may take one to three weeks after cover crop incorporation before N release exceeds N immobilization. The farmer may have to decide if additional fertilizer N is needed and, if so how much. On the other hand, when the soil is not cropped, cover crops, especially grass, can reduce the potential loss of N through leaching or denitrification. In the US mainland, rye is often used as a winter cover crop to control weeds through competition and allelopathy.

Along with crop rotation and intercropping, ridge tillage is often practiced in sustainable farming. This technique only tills a zone of soil 15 to 20 cm wide and 5 to 10 cm deep at planting time. The practice creates a desirable seedbed environment, it also covers crop residue and weeds in the area between rows with soil. Subsequent between-row cultivation a couple of weeks after planting promotes mineralization of soil organic residues, controls weeds and reforms the ridge with a raised bed for future crops.


(Adapted from WSARE, 1995)

PHOSPHORUS

Along with nitrogen, phosphorus is a nutrient that plants need in relatively large quantities for normal growth. In fact, P is a structural component of DNA and RNA, the two genetic entities that are essential for growth and reproduction of living organisms. Living organisms, whether plants or humans, also derive their internal energy from P-containing compounds, mainly adenosine diphosphate (ADP) and adenosine triphosphate (ATP). This means that inadequate P supply will result in a decreased synthesis of RNA, the protein maker, leading to depressed growth.

Phosphorus-deficient plants, therefore, are stunted with a limited root system and thin stems. In many plants such as corn, guava, and tomato, seedlings look stunted, and older leaves may turn purple because of the accumulation of anthocyanins or purple pigments. Fruit trees deficient in P have few and short new shoots and malformed fruits and seeds. Thus not only low yields but also poor quality are the results of P deficiency.

Internally, most crops need from 0.2% to 0.5% P in the dry matter for normal growth. Macadamia is an exception, iron chlorosis may occur if P content is greater than 0.15% in leaves.Table 2 lists the sufficiency range pf P in leaves of selected crops (Tamimi et al., 1994).

Table 2. Sufficiency P levels in leaves of selected crops

Crop

Plant P (%)

Cabbage 0.4-0.6
Coffee 0.2-0.3
Corn 0.3-0.5
Head lettuce 0.4-0.6
Macadamia 0.08-0.10
Soybean 0.3-0.5
Sugarcane 0.2-0.3
Tomato 0.3-0.8

Unlike animals and humans who can obtain P from various food sources, plants must extract P exclusively from the soil where they grow. Also unlike humans whose gastrointestinal enzymes can break up organic P in food, plant roots can absorb P only when P is in the soil solution and in either H2PO4 - or HPO42- form. This fact is emphasized because not only do plants like H2PO4 - and HPO42- but so do soils. There is a strong competition between plants and soils for P in the soil solution. And the winner usually is soils, especially highly weathered soils like those of Hawaii and the tropics.Most of our soils here contain large amounts of iron- and aluminum-oxides or amorphous alumino silicate clays, which tie up P firmly, making P virtually unavailable for plant uptake. For example, in order to provide enough P for many of our favorite vegetables, such as lettuce and tomato, first time growers must apply approximately:

Table 3. P fertilization for good growth of most vegetables (Adapted from Hue, 1991; and Hue et al., 1994)

Soil (Series/Order) P Fertilizer (lb/A)
Hilo/Andisol 2,000
Halii/Oxisol 1,600
Paaloa/Ultisol 1,200
Lualualei/Vertisol 100
 

Of course, amounts of P required would vary, depending on how much P the soil has, to begin with. Thatı s true, and thatı s why you need a soil test before trying to amend or fertilize your soils. In fact, by adding P to the soil year after year, you might build up soil P to a point that it becomes detrimental to your crops because of excess. That was the case for several vegetable growers in the Waianai area of Oahu, Hawaii. The upside of this phenomenon is that once you have built your soil P to a good level, that level would remain for many years without any additional P input. The reason is that unlike nitrogen, P does not move easily with water. It virtually stays put. Leaching is minimal.

The next question is what can we use to build up soil P? In conventional farming you can use such fertilizers as treble superphosphate (Ca(H2PO4)2) which contains about 20% P or 46% as P2O5 or diammonium phosphate (DAP) which has coincidently the same amount of P as in treble superphosphate. These fertilizers are highly soluble, dissolve quickly in water and can provide enough P to your crops before being tied up by the soil. These P fertilizers, however, are not acceptable in organic farming. Here we must rely on different sources.

Table 4. Total P concentration in organically acceptable sources as compared with treble superphosphate (20% P) (Adapted from Nick and Bradley, 1994; and Hue, 1995)

Source Total P (%)
Rock phosphate 17-26
Bone meal 20-30
Fish meal 5-10
Wood ash 2-5
Poultry manure 0.5-1.5
Green manure 0.2-0.5
Compost 0.2-0.5
Sewage sludge 0.4-2.5

Table 4 shows P content of selected sources that are acceptable to organic farming community in most states. Among these, the first two, rock phosphate and bone meal, have reasonably high total P content: between 20 and 30%. However, P in these two sources is very insoluble, thus much less plant available than P in treble superphosphate. More specifically, P in rock phosphate and bone meal has the formula: Ca5(OH)(PO4)3 which is hydroxy apatite or apatite for short. This is the same material that our bones and teeth are made of. As our teeth can attest to it, apatite is quite durable; is very hard to dissolve in water, meaning that it provides very little phosphate to your crop in the short term.

A couple of things should be mentioned about rock phosphate. First, it is a source of P for long-term soil improvement, donı t expect any noticeable effect from it within weeks or months, unless you use huge amounts of it. Second, its solubility, and thus plant availability, depends strongly on soil pH and particle size. It is more effective in acid soils than in calcareous or alkaline soils; more effective when it is fine than coarse, and more effective in the presence of mycorrhiza than without mycorrhiza.

By contrast, P contents of chicken manure, compost, and sludge are relatively low, usually below 3%. Thus, large amounts would be needed to meet P requirement of the crop. Yet, pound for pound, P from these organic sources is quite available to plants; sometimes even more effective than treble superphosphate. Our recent work has shown that organic matter from the manure interacts with clay minerals and reduces P sorption by the soil, thereby enhancing P availability to plants (Hue, 1990; 1991).

POTASSIUM

Compared favorably with nitrogen, potassium is needed in large quantities by many crops. Table 5 lists the sufficiency range of K in selected crops.

Table 5. Sufficiency range of K in selected crops (Adapted from Tamimi et al., 1994)

Crop Tissue K (%)
Banana 3.0-5.0
Cabbage 4.5-7.5
Coffee 2.0-3.0
Corn 1.5-3.0
Lettuce 4.0-7.5
Papaya 3.0-5.0
Tomato 3.0-5.0

In plants, potassium is required for maintaining osmotic potential of cell. That is, K makes plants look turgid. Since K regulates the osmotic potential of cells, and the close or open conditions of stomata, it plays an important role in water relations in the plant. Potassium is involved in water uptake from the soil, water retention in the plant tissue, and long distance transport of water in the xylem and of photosynthates in the phloem. Potassium affects cell extension. With adequate K, cell walls are thicker, thereby improving plant resistance to lodging, pests and disease. Fruits and vegetables grown with adequate K seem to have a longer shelf life in the grocery store.

Consequently, K-deficient plants show low resistance to disease, their seeds and fruits are small and shriveled. In tomato, K deficiency results in smaller fruits whose flesh development is incomplete. In corn, the maturity is delayed and ears are smaller when K is deficient.

The stalks are weak and lodging is common. The most visual K deficiency symptom is the scorching or firing along leaf tips and margins as shown here for soybeans. In alfalfa and clovers, the first sign of K deficiency shows up as small white or yellowish dots around the outer edges of leaves. As the deficiency intensifies, these edges turn yellow, then brown, and finally die.

(Source: Potash and Phosphate Institute, Atlanta, GA)

In soils, potassium is quite mobile as compared to phosphate. It exists as K+ in soil solution and is absorbed by roots in that form. Although K+ can be retained to some extent by negative charges on clay surface, it can be displaced into the soil solution by Ca2+ or Mg2+, when gypsum or dolomite is added. Thus if K is not taken up by plants, it might be lost by leaching. One way to reduce K leaching is to add organic matter such as compost or green manure to your soil. These organic materials usually have large cation exchange capacity which can retain K effectively. Among soils, K deficiency occurs more often in sandy than in clayey soils, more often in highly weathered soils than in young soils, and more often in volcanic ash-derived soils of the Hilo coast than those of the Kona coast.

If your soil is low in K, what can you do? Commercial KCl is an easy choice in conventional farming, but not acceptable in organic farming. What alternatives do we have?

Table 6. Total K concentration in selected organically acceptable sources (Adapted from Nick and Bradley, 1994; and personal data)
Source Total K, %
Sul-Po-Mag [Mg, K, SO4] 22.0
Polyhalite [Ca, K, SO4] 10-15
Wood ash 5-10
Green sand 5-7
Green manure 2-5
Seaweed meal 2-3
Compost 0.5-2.0

The first two sources are natural deposits of potassium minerals. Sul-Po-Mag as the name implies is a double salt of magnesium and potassium sulfates. It has about 22% K. Polyhalite is a double salt of Ca and K sulfates. It has about 10 to 15% K. Like Sul-Po-Mag , polyhalite is very soluble, not much different from KCl. In terms of plant response, this material is as good as or even better than KCl or gypsum (unpublished data). There are large deposits of polyhalite in Utah, Texas, Poland, and Egypt. How commercially available is polyhalite to sustainable farmers? I do not really know.

Wood ash also contains considerable amount of potassium, and this source is also readily available (and alkaline). On the other hand, green sand has about 7% K but the availability of this K is very low. It can be used to build up K reserve for the soil, but I doubt very much that it can meet the K requirement of your fast growing crop.

It is hoped that the information provided would be useful to you in managing your soil or in assisting your clients. One thing I would like to repeat is that sustainable agriculture is more in tune with nature than conventional agriculture, but it is information intensive and requires greater management skills from the farmers than ever before.

Table 7. Average Plant Food Content of Natural and Organic Ferilizer Materials (Percentage on a Dry-Weight Basis.)
Organic Materials % N % P % K Availability Acidity
Fish Scrap 5.0 3.0 0 slowly acid
Fish Meal 10.0 4.0 0 slowly acid
Guano, Peru 13.0 8.0 2.0 moderately acid
Guano, Bat 10.0 4.0 2.0 moderately acid
Sewage Sludge 2.0-6.0 1.0-2.5 0.0-0.4 slowly acid
Dried Blood 12.0 1.5 0.8 mod. slow acid
Soybean Meal 7.0 1.2 1.5 slowly v. sl. acid
Tankage, Animal 9.0 10.0 15.5 slowly acid
Tankage, Garbage 2.5 1.5 1.5 very slowly alkaline
Tobacco Stems 1.5 0.5 5.0 slowly alkaline
Seaweed 1.0 --- 4.0-10.0 slowly ---
Bone Meal, Raw 3.5 22.0 --- slowly alkaline
Castor Pomace 6.0 1.2 0.5 slowly acid
Wood Ashes --- 2.0 4.0-10.0 quickly alkaline
Cocoa Shell Meal 2.5 1.0 2.5 slowly neutral
Cotton Seed Meal 6.0 2.5 1.5 slowly acid
Ground Rock Phosphate --- 33.0 --- very slowly alkaline
Green Sand --- 1.0 6.0 very slowly ---
Basic Slag --- 8.0 --- quickly alkaline
Horn and Hoof Meal 12.0 2.0 --- --- ---
Milorganite 6.0 2.5 --- --- ---
Peat and Muck 1.5-3.0 0.25-0.5 0.5-.10 very slowly acid
Spent Mushroom Compost 2.0 .74 1.46 moderately 6.4
 

References

  1. Bugg, R. L. and P. R. Miller. 1991. Grasses/legumes:Dream team. Sustainable Agric. News 3(4):1-4. UC Davis, CA.

  2. Caplan, B. 1992. Organic gardening. Headline Book Publ., London, UK.

  3. Hue, N. V. 1990. Interaction of Ca(H2PO4)2 applied to an Oxisol and previous sludge amendment:soil and crop response. Commun. Soil Sci. Plant Anal. 21:61-73.

  4. Hue, N. V. 1991. Effects of organic acids/anions on P sorption and phytoavailability in soils with different mineralogies. Soil Sci. 152:463-471.

  5. Hue, N. V., H. Ikawa, and X. Huang. 1994. Predicting phosphorus requirements of some Hawaii soils. Fact Sheet no. 2. CTAHR.

  6. Hue, N. V. 1995. Sewage sludge. pp. 193-239. In J. E. Rechcigl (ed) Soil amendment and environmental quality. Lewis Publ., Boca Raton, FL.

  7. Nick, J. and F. Bradley. 1994. Growing fruits and vegetables organically. Rodale Press, Emmaus, PA.

  8. Tamimi, Y., J. A. Silva, R. S. Yost, and N. V. Hue. 1994. Adequate nutrient levels in soils and plants in Hawaii. Fact Sheet no. 3. CTAHR.

  9. Today's Chemist. 1995. May issue. Am. Chem. Soc.

  10. WSARE. 1995. The basic principles of sustainable agriculture. URL: http://ext.usu.edu/wsare (the internet).

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