Nutrition and fertilisation
Which nutrients coffee takes from the soil, how much each harvest removes, how leaf and soil analysis guide fertiliser programmes, when to apply them, and where the nitrogen that is not taken up goes.
Across the chain: Sustainability · Science
Contents
In brief
- In Colombia, the whole fruit behind 1,000 kg of green coffee removed 30.9 kg nitrogen and 36.9 kg potassium; the pulp carried most of the potassium.1
- Published sufficiency ranges for leaf nitrogen differ between institutes and authors, from 2.30–2.80% in Colombia to 3.00–3.50% in one range compiled in Brazil.1,5
- Cenicafé recommends 120–300 kg nitrogen per hectare and year for producing coffee, adjusted by soil analysis, planting density and shade.1
- In a Brazilian ¹⁵N study, fruit took up 26.3% of fertiliser nitrogen over two years; leaching and volatilisation lost 2.0% and 0.9% a year.7
- In Costa Rica, 84% of the yearly nitrous oxide from fertilised coffee soils was emitted in the periods after fertilisation.9
What a coffee harvest takes from the soil#
A coffee plant takes mineral nutrients from the soil through its roots. Some stay in roots, wood and leaves. Others go into the fruit, and the harvest carries them off the farm. According to a 2017 textbook chapter, the soil’s own reserves cannot cover the plant’s demand in most coffee regions.4
Nitrogen (N) and potassium (K) leave in the largest amounts. In Colombia, the whole fruit behind 1,000 kg of green coffee held 30.9 kg nitrogen and 36.9 kg potassium.1 Calcium, phosphorus, magnesium and sulphur followed, each below 5 kg.1 Boron, zinc, iron, manganese and copper are removed in grams, not kilograms.1
Not all of this leaves the farm with the green coffee. Much stays in the pulp and husk at the mill.1,2 In Colombia the pulp alone held 22.31 kg of the 36.9 kg potassium.1 Returning pulp to the field returns these nutrients.1,2
- Fertiliser. Mineral or organic fertiliser spread around the plant, at the start of the rains.1
- Roots. Take up nutrients and hold part of them; roots held 9.4% of fertiliser nitrogen after two years in one Brazilian study.7
- Leaves and branches. Store nutrients in the plant; aerial parts held 19.1% of fertiliser nitrogen in the same study.7
- Harvested fruit. Leaves the field; fruit took up 26.3% of fertiliser nitrogen over two years.7
- Pulp and husk. Returned from the mill as an organic fertiliser.1,2
- Leaf litter and prunings. Return nutrients to the soil surface; litter held 23.8% of fertiliser nitrogen.7
- Shade tree. A nitrogen-fixing legume adds litter and nitrogen, and may raise nitrous oxide emissions.9
- Gaseous losses. Ammonia volatilisation and nitrous oxide from the soil, highest after fertilisation.7,9
- Leaching. Nitrate carried below the root zone by drainage water.7,10
- Soil. The main nutrient reservoir; the soil to 1 m held 12.6% of fertiliser nitrogen after two years.4,7
Fertilisation replaces what the harvest removes.4 Without it, Cenicafé reports that Colombian coffee production can fall by more than 40%.1 Cenicafé is Colombia’s national coffee research centre.
Reading the plant and the soil#
Two analyses guide fertilisation. Soil analysis shows what the soil can supply; leaf analysis shows the plant’s nutritional status.4 According to the 2017 textbook chapter, leaf analysis is an efficient way to monitor it, especially in intensive systems.4
Each method samples a defined leaf at a defined time. Cenicafé takes one leaf per branch at the third or fourth node from the tip, six months before harvest.1 A Brazilian survey sampled the third and fourth leaf pairs at mid-height of the plant, when the young fruit were small.5
The result is compared with a sufficiency range: the concentration found in healthy, productive plants. These ranges differ by region and author.5 For leaf nitrogen, Cenicafé gives 2.30–2.80% for Colombia, while other published ranges reach 3.50%.1,5
Visible symptoms help too. Shortage of a mobile nutrient shows first on older leaves; shortage of a less mobile one on young leaves.1 Nitrogen shortage, for example, turns older leaves evenly yellow.1 Soil pH and liming are covered in soil acidity and liming; soil types in soils for coffee.
How much fertiliser, and when#
There is no universal dose.1,6 Cenicafé bases its programmes on soil analysis, plant age, planting density and shade.1 According to the 2017 textbook chapter, similar decision systems run in other producing countries.4
- Young plants. Cenicafé gives doses in grams per plant, starting one or two months after planting and repeating every three to four months.1
- Producing plants. With a soil analysis, Cenicafé recommends 120–300 kg nitrogen per hectare and year.1 Potassium ranges from none to 300 kg, depending on the soil.1
- High-yield trials. In dense plantings in Minas Gerais, Brazil, the highest yields came at much higher doses (see Deep dive).6
Timing follows the rains. Cenicafé times applications to the start of the rainy periods.1 It splits nitrogen and potassium into two applications in dry years and three in wet years.1 At wet sites, the extra application is meant to reduce the risk of leaching losses.1 The fruit takes up most of its nutrients two to six months after flowering.1
Fertiliser grades for coffee state phosphorus and potassium as the oxides P₂O₅ and K₂O, not as elements.1,4 One kilogram of potassium equals 1.205 kg of K₂O; one kilogram of phosphorus equals 2.291 kg of P₂O₅ (our calculation from atomic masses).
Where the nitrogen goes#
Not all fertiliser nitrogen reaches the plant. In a two-year Brazilian study, fruit, plant and litter together took up most of it, and leaching and volatilisation lost little.7 In Costa Rica, coffee soils on volcanic ash emitted most of their yearly nitrous oxide (N₂O), a greenhouse gas, after fertilisation.9 Nitrogen inputs were the main source of greenhouse gases in coffee trials in Costa Rica and Nicaragua.11 The Deep dive gives the numbers; the farm’s share in the whole footprint is covered in carbon footprint of coffee.
Removal by the harvest, measured#
Whole fruit, Colombia. Cenicafé expresses removal per 1,000 kg of green coffee (café almendra), equal to 1,250 kg of dry parchment coffee.1 The whole fruit behind that tonne held 30.9 kg N, 2.3 kg P, 36.9 kg K, 4.3 kg Ca, 2.3 kg Mg and 1.2 kg S.1 Micronutrients were 107 g Fe, 61 g Mn, 50 g B, 33 g Cu and 18 g Zn.1 Split by fraction, the green coffee held 16.79 kg N and 12.40 kg K, and the pulp 11.50 kg N and 22.31 kg K.1 Parchment and mucilage held the rest.1
Green coffee alone, Brazil. A 1963 study in São Paulo compared Mundo Novo, Caturra and Bourbon Amarelo on three soils.2 The varieties did not differ.2 The beans held 1.71% N, 0.10% P, 1.53% K, 0.27% Ca, 0.15% Mg and 0.12% S in the dry matter.2 That is 17.1 kg N and 15.3 kg K per tonne of bean dry matter (our calculation), of the same order as the Colombian bean fraction (16.79 kg N and 12.40 kg K per 1,000 kg green coffee), although the bases differ.1 By the authors’ estimate, the clean coffee carried about two-thirds of the fruit’s nitrogen, half of its phosphorus and potassium, and one-third of its calcium, magnesium and sulphur.2 The rest stays in pulp and husk, which the authors proposed returning to the field.2
Data table
| Point | kg per tonne (basis: see legend) | Source | |
|---|---|---|---|
| Nitrogen (N) | 17.1 | 17.1 | 2 |
| Nitrogen (N) | 30.9 | 30.9 | 1 |
| Potassium (K) | 15.3 | 15.3 | 2 |
| Potassium (K) | 36.9 | 36.9 | 1 |
| Calcium (Ca) | 2.7 | 2.7 | 2 |
| Calcium (Ca) | 4.3 | 4.3 | 1 |
| Phosphorus (P) | 1.0 | 1 | 2 |
| Phosphorus (P) | 2.3 | 2.3 | 1 |
| Magnesium (Mg) | 1.5 | 1.5 | 2 |
| Magnesium (Mg) | 2.3 | 2.3 | 1 |
| Sulphur (S) | 1.2 | 1.2 | 2 |
| Sulphur (S) | 1.2 | 1.2 | 1 |
Robusta, Brazil. In a 2014/2015 trial with C. canephora (Conilon BRS Ouro Preto) in Rondônia, western Amazon, fertiliser doses from 0 to 3,000 kg per hectare and year of a 20-00-20 formulation did not change nutrient concentrations in the fruit.3 Higher doses raised dry mass, and so total export.3 Across all doses the beans exported N > K > Mg > P > Ca > S; the husk exported K > N > Ca > Mg > S > P.3 From the trial means (4,455 kg bean dry matter and 121.73 kg N per hectare), the beans held about 27.3 kg N and 20.5 kg K per tonne of dry matter (our calculation).3 According to the 2017 textbook chapter, removal per tonne of marketable coffee is of the same order for robusta and arabica.4
Pulp as a nutrient source. Producing 1,250 kg of dry parchment coffee leaves about 2,700 kg of fresh pulp.1 Cenicafé puts its content at about 10.2 kg N, 1.4 kg P₂O₅, 23.8 kg K₂O, 2.2 kg CaO, 0.8 kg MgO and 0.4 kg SO₄.1 It recommends 6–12 kg of decomposed pulp per tree and year as an organic fertiliser.1
Nutrients and deficiency signs#
According to Cenicafé, nitrogen is the nutrient that most limits production in Colombia.1 Leaving nitrogen out of fertilisation lowered yield by up to 80%.1 Potassium ranks second; on soils very low in potassium (below 0.2 cmolc/kg), yield fell by nearly 30%.1 Responses to phosphorus were occasional and small, mainly below 10 mg/kg soil phosphorus.1 Magnesium deficiency is common in the leaves of productive branches; sulphur deficiency is rarely seen.1
The chapter links nitrogen to chlorophyll formation.1 It does not describe the roles of the other nutrients, and no source consulted for this entry measured them in coffee. Deficiency symptoms, as Cenicafé lists them:
| Nutrient | Symptom | Leaves affected | Source |
|---|---|---|---|
| Nitrogen (N) | Even yellowing | Older | Cenicafé1 |
| Phosphorus (P) | Uneven yellowing with reddish spots | Older | Cenicafé1 |
| Potassium (K) | Necrosis at tip and margins | Older | Cenicafé1 |
| Magnesium (Mg) | Yellowing between the veins | Older | Cenicafé1 |
| Calcium (Ca) | Yellowing at the margins | Younger | Cenicafé1 |
| Sulphur (S) | Even yellowing | Younger | Cenicafé1 |
| Boron (B) | Brown spots on the shoots | New leaves | Cenicafé1 |
| Zinc (Zn) | Small, narrow, yellowish leaves | New leaves | Cenicafé1 |
Nitrogen and sulphur both cause even yellowing; the age of the affected leaves separates them.1 According to the 2017 textbook chapter, micronutrient deficiencies are identified by such symptoms or by leaf analysis.4
Leaf and soil analysis#
Leaf sufficiency ranges. Cenicafé gives normal leaf concentrations for Colombia: N 2.30–2.80%, P 0.10–0.18%, K 1.50–2.00%, Ca 0.50–1.30% and Mg 0.30–0.40%.1 For micronutrients it gives Mn 150–220 mg/kg and Fe 90–140 mg/kg; its boron range of 40–60 carries no unit in the table.1 A 2003 Brazilian study compiled six published ranges beside its own.5 Their limits for leaf nitrogen run from 2.30% to 3.50%, and for potassium from 1.80% to 2.60%.5
Data table
| % N in the leaf (dag/kg) | Source | |
|---|---|---|
| Cenicafé, Colombia (2013) | 2.30–2.80 | 1 |
| Willson 1985 | 2.60–3.40 | 5 |
| Reuter & Robinson 1988 | 2.50–3.00 | 5 |
| Malavolta 1993 | 2.70–3.20 | 5 |
| Mills & Jones 1996 | 2.30–3.00 | 5 |
| Malavolta et al. 1997 | 2.90–3.20 | 5 |
| Matiello 1997 | 3.00–3.50 | 5 |
Regional ranges in Minas Gerais. The 2003 study sampled 312 plots on 168 farms in four regions, in a high-yield and a low-yield year.5 It took farms yielding more than 1,800 kg of green coffee per hectare, averaged over the two years, as the reference.5 The critical ranges did not differ between years or regions.5 Micronutrient problems were the most frequent finding.5
Soil classes. For producing coffee, Cenicafé classes soil phosphorus as low below 10 mg/kg and high above 20 mg/kg.1 Potassium is low below 0.2 cmolc/kg, calcium below 1.5 and magnesium below 0.6 cmolc/kg.1 Cenicafé considers a soil pH of 5.0–5.5 adequate, and toxicity becomes more likely when exchangeable aluminium exceeds 1 cmolc/kg.1 Liming is covered in soil acidity and liming.
Programmes by age and yield#
Colombia (Cenicafé). For young plants, nitrogen ranges from 5 to 16 g per plant, depending on age (2–18 months) and soil organic matter.1 Phosphorus (4–6 g P₂O₅), potassium (5–10 g K₂O) and magnesium (2–3 g MgO) per plant are added only where soil tests fall below set thresholds.1 For producing coffee with a soil analysis, the recommendation is 120–300 kg N, 0–300 kg potassium, 0–60 kg each of magnesium and phosphorus, and up to 50 kg sulphur per hectare and year.1 Without an analysis, Cenicafé suggests 300 kg N, 260 kg K₂O and 50 kg each of P₂O₅, MgO and S for more than 7,500 plants per hectare in full sun.1 Doses fall with lower planting density and with shade.1
Brazil, dense plantings (trial optima). At Martins Soares, Minas Gerais (763 m), Catuaí Vermelho 44 at 9,523 plants per hectare received 0–1,200 kg per hectare and year of N and K₂O in a 1:1 ratio.6 Over eight seasons, the dose of maximum technical efficiency was 881.7 kg N + K₂O, for a maximum mean yield of 61.9 bags per hectare.6 The paper does not state the bag weight; with the usual 60 kg bag of green coffee, that is about 3,714 kg per hectare (our calculation). In a second trial with Catucaí Amarelo 6/30 at 6,666 plants per hectare, yield did not respond in the first two seasons.6 In the four later seasons, the doses for maximum yield were 389–560 kg N and 21–373 kg K₂O per hectare, varying by season (the abstract rounds this to 424–560 kg N and 21–338 kg K₂O).6 Nitrogen reduced the swing between heavy and light crops (biennial bearing).6 These are agronomic optima of two trials, not general recommendations.
Other producing countries. No technical recommendation of an African or Asian coffee research institute was consulted for this entry. Doses here are therefore from Colombia and Brazil only.
Timing, splitting and foliar feeding#
With the rains. Cenicafé ties applications to soil moisture.1 In dry conditions or El Niño years it prefers two applications about six months apart; at wet sites or in La Niña years, three, about four months apart.1 Where rain falls in two seasons, fertiliser goes on at the start of the wetter periods; with one rainy season, at its onset.1 Fertilisers applied at low volume, such as diammonium phosphate or magnesium oxide, can go on in one dose a year.1 Urea is very soluble in water and at greater risk of loss.1
Uptake over the year. In a Brazilian ¹⁵N study, nitrogen was applied as ammonium sulphate in four splits.8 By February of the first year, the aerial parts held 71% of the fertiliser nitrogen applied.8 The share fell to 34% at harvest and 19% at the next flowering, as leaves fell and fruit was removed.8 The authors found the four-split programme adequate for the crop’s needs.8 Fruit takes up most of its nutrients two to six months after flowering, according to Cenicafé.1 How the fruit grows in that time is covered in fruit development.
Foliar feeding. According to the 2017 textbook chapter, foliar sprays are often used to correct deficiencies of zinc, boron, iron and manganese, identified by symptoms or leaf analysis.4 Cenicafé states that a beneficial effect of foliar fertilisers has not yet been shown, and leaves them out of its recommendations.1 No study consulted for this entry measured yield or uptake from foliar sprays on coffee.
Nitrogen losses and the environment#
A ¹⁵N balance in Brazil. In Piracicaba, São Paulo, coffee received 280 and 350 kg N per hectare in two seasons as ¹⁵N-labelled ammonium sulphate.7 After two years, 19.1% of the fertiliser nitrogen was in the aerial parts, 9.4% in roots, 23.8% in litter and 26.3% in fruit.7 The soil to 1 m held 12.6%.7 Leaching lost 2.0% and volatilisation 0.9% a year, which the authors called very small; 6.2% was not accounted for.7
Leaching in Costa Rica. Shaded and unshaded plantations in the Central Valley both received 300 kg N per hectare and year.10 Measured with ceramic-cup lysimeters, nitrate leaching was 24 kg nitrate nitrogen per hectare and year without shade and 9 kg with shade.10 Denitrification was higher in shaded soils, and the authors concluded that in both plantation types the potential for loss by leaching was small compared with that for gaseous loss.10
Nitrous oxide. On Andosols in Costa Rica, a coffee monoculture and coffee shaded by Inga densiflora both received 250 kg N per hectare and year.9 Over one year, the monoculture emitted 4.3 ± 0.1 kg and the shaded system 5.8 ± 0.3 kg N₂O nitrogen per hectare.9 Of the yearly N₂O, 84% was emitted in the periods after fertilisation.9 Litterfall added 153 kg N in the monoculture and 246 kg N under Inga.9 The authors concluded that nitrogen-fixing shade trees can increase N₂O emissions.9 Shade trees as a nitrogen source are discussed in shade and agroforestry.
Footprint. In long-term trials in Costa Rica and Nicaragua, organic and inorganic nitrogen inputs were the main contributor to greenhouse gas emissions in every management system.11 No study consulted for this entry measured nitrate in drinking water near coffee farms.
Nutrition, disease and cup quality#
Rust. In a controlled-environment study, high light combined with low nitrogen fertilisation changed the course of coffee leaf rust and led to heavy sporulation.12 The authors proposed vigorous varieties, shade and appropriate nitrogen fertilisation as part of an agroecological approach to the disease.12 The disease itself is covered in coffee leaf rust.
Brown eye spot and rust under organic fertilisers. A two-year Brazilian field trial (2003–2005) compared organic nutrient sources.13 Coffee fruit peel applied alone gave the greatest disease progress: 62% above the control for brown eye spot (Cercospora coffeicola) and 38% above it for rust.13 These plants had more potassium and less calcium in their leaves, lost more leaves and yielded less.13 Mixing the peel with castor bean presscake or swine waste cut brown eye spot by 38% compared with peel alone and raised leaf calcium.13 The authors concluded that better nutritional balance increased resistance to the diseases.13
Cup quality. The 2017 textbook chapter summarises older studies that disagree.4 Some found no effect of fertilisation on cup quality; others found that high nitrogen or potassium doses, or some fertiliser forms, lowered it.4 The chapter concludes that both negative and positive effects occur and that more research is needed.4 No study consulted for this entry tested fertilisation and cup quality directly.
Reference values#
| Parameter | Value reported | Conditions | Source |
|---|---|---|---|
| Removal, whole fruit | N 30.9 · P 2.3 · K 36.9 · Ca 4.3 · Mg 2.3 · S 1.2 kg | Per 1,000 kg green coffee, Colombia | Sadeghian1 |
| Removal, micronutrients | Fe 107 · Mn 61 · B 50 · Cu 33 · Zn 18 g | Per 1,000 kg green coffee, Colombia | Sadeghian1 |
| Bean concentration | N 1.71 · P 0.10 · K 1.53 · Ca 0.27 · Mg 0.15 · S 0.12% | Dry matter; three arabica varieties, São Paulo | Arzolla et al.2 |
| Bean export, robusta | ≈27.3 kg N, ≈20.5 kg K per t dry matter | Conilon, Rondônia; our calculation from trial means | Torres et al.3 |
| Leaf N, normal | 2.30–2.80% | Colombia | Sadeghian1 |
| Leaf K, normal | 1.50–2.00% | Colombia | Sadeghian1 |
| Leaf N, published ranges | 2.30–3.50% (limits of six ranges) | Compilation | Martinez et al.5 |
| Leaf K, published ranges | 1.80–2.60% (limits of six ranges) | Compilation | Martinez et al.5 |
| Soil pH, adequate | 5.0–5.5 | Colombia | Sadeghian1 |
| N, producing coffee | 120–300 kg/ha/yr | With soil analysis, Colombia | Sadeghian1 |
| N, K₂O without analysis | 300 kg N, 260 kg K₂O/ha/yr | >7,500 plants/ha, full sun, Colombia | Sadeghian1 |
| N for maximum yield | 389–560 kg/ha/yr | Dense planting trial, Minas Gerais | Valadares et al.6 |
| Applications per year | 2 (dry) – 3 (wet) | Colombia | Sadeghian1 |
| Fertiliser N in fruit | 26.3% after two years | ¹⁵N, ammonium sulphate, São Paulo | Fenilli et al.7 |
| Leaching, volatilisation | 2.0% and 0.9% of fertiliser N per year | Same study | Fenilli et al.7 |
| Nitrate leaching | 24 (no shade) vs 9 (shade) kg NO₃-N/ha/yr | 300 kg N/ha/yr, Costa Rica | Babbar & Zak10 |
| N₂O emissions | 4.3 (monoculture) vs 5.8 (Inga) kg N/ha/yr | 250 kg N/ha/yr, Andosols, Costa Rica | Hergoualc’h et al.9 |
Open questions#
- Recommendations beyond Latin America. This entry rests on Colombian and Brazilian work. No technical recommendation from an African or Asian coffee research institute was consulted for it.
- Foliar feeding. Whether foliar sprays raise yield is not established in the sources consulted here; they disagree on its place in a programme.1,4
- Nutrient roles in coffee. No source consulted for this entry measured the physiological roles of single nutrients, other than nitrogen, in coffee.
- Fertilisation and cup quality. Older studies disagree, and the 2017 textbook chapter calls for more research.4
- Gaseous versus leaching losses. The two field studies consulted here weigh them differently, on different soils and with different fertilisers.7,10
Key studies#
Sadeghian, 2013 – Nutrition of coffee plantations (Cenicafé). The Colombian national coffee research centre’s chapter on coffee nutrition. It gives nutrient removal per tonne of green coffee by fruit fraction, leaf and soil reference values, and fertiliser programmes by age, density and shade, tied to the rainy seasons.
Arzolla et al., 1963 – Macronutrients removed at harvest. Measured macronutrients in the beans and pulp of three arabica varieties on three soils in São Paulo. The varieties did not differ, and a large part of the fruit’s nutrients stayed in pulp and husk, which the authors proposed returning to the field.
Martinez et al., 2003 – Critical leaf ranges in Minas Gerais. Sampled leaves on 168 farms in four regions over a high- and a low-yield year, using high-yield farms as the reference. The ranges did not differ between years or regions, and micronutrient problems were the most frequent.
Fenilli et al., 2008 – Where fertiliser nitrogen goes. Traced ¹⁵N-labelled ammonium sulphate through a coffee plantation in São Paulo for two years. Plant, fruit, litter and soil held most of it; leaching and volatilisation removed only a few per cent a year.
Hergoualc’h et al., 2008 – Greenhouse gases from fertilised coffee soils. Measured nitrous oxide, carbon dioxide and methane for a year in fertilised coffee with and without Inga densiflora in Costa Rica. Most nitrous oxide came after fertilisation, and the shaded system emitted more.
- Foliar fertilisation: a 2017 textbook chapter describes foliar sprays as a common way to correct deficiencies of zinc, boron, iron and manganese4; Cenicafé states that a beneficial effect of foliar fertilisers has not yet been shown and leaves them out of its recommendations.1 The two sources speak of different aims: correcting a diagnosed deficiency versus raising yield.
- Micronutrients: in Colombia, micronutrient deficiencies are rarely seen in young plants and are not routinely included in fertiliser plans1; a leaf survey of 168 farms in Minas Gerais, Brazil, found micronutrient problems to be the main nutritional problem.5 The two findings concern different soils and plant ages.
- Main path of nitrogen loss: in a Brazilian ¹⁵N balance, leaching removed 2.0% of fertiliser nitrogen a year7; in Costa Rica, unshaded coffee lost 24 kg nitrate nitrogen per hectare and year by leaching, and the authors judged the potential for gaseous loss to be larger.10 Soils, rainfall and fertiliser forms differ between the sites.
Coffearium (2026). Nutrition and fertilisation. Coffearium – The open coffee compendium. Retrieved 4 November 2026, from https://coffearium.org/entries/nutrition-and-fertilisation/
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author = {{Coffearium}},
title = {{Nutrition and fertilisation}},
year = {2026},
howpublished = {Coffearium -- The open coffee compendium},
url = {https://coffearium.org/entries/nutrition-and-fertilisation/},
urldate = {2026-11-04},
note = {Retrieved 4 November 2026}
}Entries are updated when the evidence changes; the retrieval date tells your readers which version you used. Changes are listed in the Change log.
Change log
- – Babbar & Zak (1995): the authors' conclusion now reads that the potential for nitrogen loss by leaching was small compared with that for gaseous loss, in body and contested list. Reason: The abstract speaks of potential loss; it does not say that gaseous loss exceeded leaching.
- – Valadares et al. (2013), second trial: doses for maximum yield given as 389–560 kg N and 21–373 kg K2O per hectare by season, with the abstract's rounded range noted; the 60 kg bag weight marked as an assumption. Reason: The per-season values in the results differ from the abstract range, and the paper does not state the bag weight.
- – Nutrient-removal chart and caption: the Brazilian points are labelled per tonne of bean dry matter, the Colombian points per tonne of green coffee. Reason: The chart title described both series as per tonne of green coffee.
Sources
- ASadeghian Khalajabadi, S. (2013). Nutrición de cafetales. In: Manual del cafetero colombiano: investigación y tecnología para la sostenibilidad de la caficultura, Vol. 2, pp. 85–116. Federación Nacional de Cafeteros de Colombia; Cenicafé. doi:10.38141/cenbook-0026_20 · other copies
- AArzolla, S.; Gomes, L.; Sarruge, J. R.; Andrade, R. G.; Graner, E. A.; Malavolta, E. (1963). Estudos sôbre a alimentação mineral do cafeeiro, X. Extração de macronutrientes na colheita pelas variedades 'Mundo Novo', 'Caturra' e 'Bourbon Amarelo'. Anais da Escola Superior de Agricultura Luiz de Queiroz.
- ATorres, J. D.; Araújo, L. F. B. de; Espindula, M. C.; Campanharo, M.; Rocha, R. B. (2022). Export of macronutrients for coffee fruits submitted to different doses of formulation 20-00-20. Journal of Plant Nutrition 45(18), 2737–2747. doi:10.1080/01904167.2022.2027975 · other copies
- BLambot, C.; Herrera, J. C.; Bertrand, B.; Sadeghian, S.; Benavides, P.; Gaitán, A. (2017). Cultivating Coffee Quality – Terroir and Agro-Ecosystem. In: Folmer, B. (ed.), The Craft and Science of Coffee, Academic Press, ch. 2, pp. 17–49.
- AMartinez, H. E. P.; Menezes, J. F. S.; Souza, R. B. de; Alvarez Venegas, V. H.; Guimarães, P. T. G. (2003). Critical nutrient ranges and evaluation of nutritional status in coffee-tree plantations of Minas Gerais. Pesquisa Agropecuária Brasileira 38(6), 703–713. doi:10.1590/S1678-3921.pab2003.v38.6627 · other copies
- AValadares, S. V.; Neves, J. C. L.; Rosa, G. N. G. P.; Martinez, H. E. P.; Alvarez Venegas, V. H.; Lima, P. C. de (2013). Yield and production bienniality of dense coffee plantations under different levels of N and K. Pesquisa Agropecuária Brasileira 48(3), 296–303. doi:10.1590/S0100-204X2013000300008 · other copies
- AFenilli, T. A. B.; Reichardt, K.; Favarin, J. L.; Bacchi, O. O. S.; Silva, A. L.; Timm, L. C. (2008). Fertilizer ¹⁵N balance in a coffee cropping system: a case study in Brazil. Revista Brasileira de Ciência do Solo 32(4), 1459–1469. doi:10.1590/S0100-06832008000400010 · other copies
- AFenilli, T. A. B.; Reichardt, K.; Dourado-Neto, D.; Trivelin, P. C. O.; Favarin, J. L.; Costa, F. M. P.; Bacchi, O. O. S. (2007). Growth, development, and fertilizer-15N recovery by the coffee plant. Scientia Agricola 64(5), 541–547. doi:10.1590/S0103-90162007000500012 · other copies
- AHergoualc'h, K.; Skiba, U.; Harmand, J.-M.; Hénault, C. (2008). Fluxes of greenhouse gases from Andosols under coffee in monoculture or shaded by Inga densiflora in Costa Rica. Biogeochemistry 89(3), 329–345. doi:10.1007/s10533-008-9222-7 · other copies
- ABabbar, L. I.; Zak, D. R. (1995). Nitrogen loss from coffee agroecosystems in Costa Rica: leaching and denitrification in the presence and absence of shade trees. Journal of Environmental Quality 24(2), 227–233. doi:10.2134/jeq1995.00472425002400020003x · other copies
- ANoponen, M. R. A.; Edwards-Jones, G.; Haggar, J. P.; Soto, G.; Attarzadeh, N.; Healey, J. R. (2012). Greenhouse gas emissions in coffee grown with differing input levels under conventional and organic management. Agriculture, Ecosystems & Environment 151, 6–15. doi:10.1016/j.agee.2012.01.019 · other copies
- AToniutti, L.; Breitler, J. C.; Etienne, H.; Campa, C.; Doulbeau, S.; Urban, L.; Lambot, C.; Pinilla, J. C. H.; Bertrand, B. (2017). Influence of environmental conditions and genetic background of Arabica coffee (C. arabica L) on leaf rust (Hemileia vastatrix) pathogenesis. Frontiers in Plant Science 8, 2025. doi:10.3389/fpls.2017.02025 · other copies
- ASantos, F. da S.; Souza, P. E. de; Pozza, E. A.; Miranda, J. C.; Carvalho, E. A.; Fernandes, L. H. M.; Pozza, A. A. A. (2008). Organic fertilization, nutrition and the progress of brown eye spot and rust in coffee trees. Pesquisa Agropecuária Brasileira 43(7), 783–791. doi:10.1590/S0100-204X2008000700001 · other copies
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