Fertilizer
An old fertilizer spreader
A large, modern fertilizer spreader
Fertilizers are soil amendments applied to promote plant growth; the main nutrients present in fertilizer are nitrogen, phosphorus, and potassium (the 'macronutrients') and other nutrients ('micronutrients') are added in smaller amounts. Fertilizers are usually directly applied to soil, and also sprayed on leaves ('foliar feeding').
Fertilizers are roughly broken up between organic and inorganic fertilizer, with the main difference between the two being sourcing, and not necessarily differences in nutrient content.
Organic fertilizers and some mined inorganic fertilizers have been used for many centuries, whereas chemically synthesized inorganic fertilizers were only widely developed during the industrial revolution. Increased understanding and use of fertilizers were important parts of the pre-industrial British Agricultural Revolution and the industrial green revolution of the 20th century.
Tennessee Valley Authority: "Results of Fertilizer" demonstration 1942
Fertilizers typically provide, in varying proportions:
- the three primary macronutrients: nitrogen (N), phosphorus (P), and potassium (K).
- the three secondary macronutrients: calcium (Ca), sulfur (S), magnesium (Mg).
- and the micronutrients or trace minerals: boron (B), chlorine (Cl), manganese (Mn), iron (Fe), zinc (Zn), copper (Cu), molybdenum (Mo) and selenium (Se).
The macronutrients are consumed in larger quantities and are present in plant tissue in quantities from 0.2% to 4.0% (on a dry matter weight basis). Micronutrients are consumed in smaller quantities and are present in plant tissue in quantities measured in parts per million (ppm), ranging from 5 to 200 ppm, or less than 0.02% dry weight.[1]
Labeling of fertilizers
Macronutrient fertilizers
Macronutrient fertilizers are labeled with an NPK analysis and also "N-P-K-S" in Australia.[2]
An example of labeling for the fertilizer potash is composed of 1:1 potassium to carbonate by volume, or 47:53 by weight (owing to differences in molecular weight between the potassium and carbonate). Traditional analysis of 100g of KCl would yield 60g of K2O. The percentage yield of K2O from the original 100g of fertilizer is the number shown on the label. A potash fertilizer would thus be labeled 0-0-60, not 0-0-52.
History
The modern understanding of plant nutrition dates to the 19th century and the work of Justus von Liebig, among others. Management of soil fertility, however, has been the pre-occupation of farmers for thousands of years.
Type of Fertilizer
Fertilizers come in various shapes and forms. The most typical form is granular fertilizer (powder form), usually come in a bag / box. The next most common form is liquid fertilizer; some advantages of liquid lawn fertilizer are its immediate effect and wide coverage. Moreover, there is also a form of slow-release fertilizer which solves the problem of "burning" the plants due to excessive nutrients. This kind of fertilizer come in various form like fertilizer spikes, tabs, etc. Finally, organic fertilizer is on the rise as people are resorting to a green / environmental friendly products. Although organic fertilizer usually contain less nutrients, some people still prefer organic due to natural ingredients.
Inorganic fertilizer (synthetic fertilizer)
Fertilizers are broadly divided into organic fertilizers (composed of enriched organic matter—plant or animal), or inorganic fertilizers (composed of synthetic chemicals and/or minerals).
Inorganic fertilizer is often synthesized using the Haber-Bosch process, which produces ammonia as the end product. This ammonia is used as a feedstock for other nitrogen fertilizers, such as anhydrous ammonium nitrate and urea. These concentrated products may be diluted with water to form a concentrated liquid fertilizer (e.g. UAN). Ammonia can be combined with rock phosphate and potassium fertilizer in the Odda Process to produce compound fertilizer.
The use of synthetic nitrogen fertilizers has increased steadily in the last 50 years, rising almost 20-fold to the current rate of 1 billion tonnes of nitrogen per year.[3] The use of phosphate fertilizers has also increased from 9 million tonnes per year in 1960 to 40 million tonnes per year in 2000. A maize crop yielding 6-9 tonnes of grain per hectare requires 30–50 kg of phosphate fertilizer to be applied, soybean requires 20–25 kg per hectare.[4] Yara International is the world's largest producer of nitrogen based fertilizers.[5]
Application
Synthetic fertilizers are commonly used to treat fields used for growing maize, followed by barley, sorghum, rapeseed, soy and sunflower. One study has shown that application of nitrogen fertilizer on off-season cover crops can increase the biomass (and subsequent green manure value) of these crops, while having a beneficial effect on soil nitrogen levels for the main crop planted during the summer season.[7]
Nutrients in soil develop in symbiosis, which can be thrown out of balance with high concentrations of fertilizers. The interconnectedness and complexity of this soil ‘food web’ means any appraisal of soil function must necessarily take into account interactions with the living communities that exist within the soil. Stability of the system is reduced by the use of nitrogen-containing inorganic and organic fertilizers, which cause soil acidification.
Problems with inorganic fertilizer
Trace mineral depletion
Many inorganic fertilizers may not replace trace mineral elements in the soil which become gradually depleted by crops. This depletion has been linked to studies which have shown a marked fall (up to 75%) in the quantities of such minerals present in fruit and vegetables.[8]
In Western Australia deficiencies of zinc, copper, manganese, iron and molybdenum were identified as limiting the growth of broad-acre crops and pastures in the 1940s and 1950s. Soils in Western Australia are very old, highly weathered and deficient in many of the major nutrients and trace elements. Since this time these trace elements are routinely added to inorganic fertilizers used in agriculture in this state.
Overfertilization
Fertilizer burn
Over-fertilization of a vital nutrient can be as detrimental as underfertilization.[9] "Fertilizer burn" can occur when too much fertilizer is applied, resulting in a drying out of the roots and damage or even death of the plant.[10]
High energy consumption
The production of synthetic ammonia currently consumes about 5% of global natural gas consumption, which is somewhat under 2% of world energy production.[11]
Natural gas is overwhelmingly used for the production of ammonia, but other energy sources, together with a hydrogen source, can be used for the production of nitrogen compounds suitable for fertilizers. The cost of natural gas makes up about 90% of the cost of producing ammonia.[12] The increase in price of natural gases over the past decade, along with other factors such as increasing demand, have contributed to an increase in fertilizer price[13].
Long-Term Sustainability
Inorganic fertilizers are now produced in ways which theoretically cannot be continued indefinitely. Potassium and phosphorus come from mines (or saline lakes such as the Dead Sea) and such resources are limited. More effective fertilizer utilization practices may, however, decrease present usage from mines. Improved knowledge of crop production practices can potentially decrease fertilizer usage of P and K without reducing the critical need to improve and increase crop yields. Atmospheric (unfixed) nitrogen is effectively unlimited (forming over 70% of the atmospheric gases), but this is not in a form useful to plants. To make nitrogen accessible to plants requires nitrogen fixation (conversion of atmospheric nitrogen to a plant-accessible form).
Artificial nitrogen fertilizers are typically synthesized using fossil fuels such as natural gas and coal, which are limited resources. In lieu of converting natural gas to syngas for use in the Haber process, it is also possible to convert renewable biomass to syngas (or wood gas) to supply the necessary energy for the process, though the amount of land and resources (ironically often including fertilizer) necessary for such a project may be prohibitive (see Energy conservation in the United States).
Organic fertilizer
Compost bin for small-scale production of organic fertilizer
A large commercial compost operation
Organic fertilizers include naturally occurring organic materials, (e.g. manure, worm castings, compost, seaweed, guano), or naturally occurring mineral deposits (e.g. saltpeter).
Benefits of organic fertilizer
Organic fertilizers have been known improve the biodiversity (soil life) and long-term productivity of soil,[14][15] and may prove a large depository for excess carbon dioxide.[16][17][18]
Organic nutrients increase the abundance of soil organisms by providing organic matter and micronutrients for organisms such as fungal mycorrhiza,[19] (which aid plants in absorbing nutrients), and can drastically reduce external inputs of pesticides, energy and fertilizer, at the cost of decreased yield.[20]
Comparison with inorganic fertilizer
Organic fertilizer nutrient content, solubility, and nutrient release rates are typically all lower than inorganic fertilizers.[21][22] One study found that over a 140-day period, after 7 leachings:
- Organic fertilizers had released between 25% and 60% of their nitrogen content
- Controlled release fertilizers (CRFs) had a relatively constant rate of release
- Soluble fertilizer released most of its nitrogen content at the first leaching
In general, the nutrients in organic fertilizer are both more dilute and also much less readily available to plants. According to UC IPM, all organic fertilizers are classified as 'slow-release' fertilizers, and therefore cannot cause nitrogen burn.[23]
Organic fertilizers from composts and other sources can be quite variable from one batch to the next.[24] Without batch testing, amounts of applied nutrient cannot be precisely known. Nevertheless they are at least as effective as chemical fertilizers over longer periods of use.[25]
Chicken litter, which consists of chicken manure and sawdust, is one example of an organic fertilizer that has been shown to better condition soil for harvest than synthesized fertilizer. Researchers at the Agricultural Research Service (ARS) studied the effects of using chicken litter, an organic fertilizer, versus synthetic fertilizers on cotton fields. They found that fields that were fertilized with chicken litter had cotton yields 12% higher than those fields fertilized with synthetic fertilizers. While the yields for chicken litter were higher, researchers predict that commercially sold chicken litter would cost about $17 more per ton than synthetic fertilizer.[26] Other ARS studies have found that algae used to capture nitrogen and phosphorus runoff from agricultural fields can not only prevent water contamination of these nutrients, but also can be used as an organic fertilizer. Originally, scientists developed the algal turf scrubber to reduce nutrient runoff and increase the quality of the water flowing into streams, rivers, and lakes. However, they found that this nutrient-rich algae, once dried, can be applied to cucumber and corn seedlings and result in growth comparable to that seen using synthetic fertilizers. [27]
Organic fertilizer sources
Animal
Decomposing animal manure, an organic fertilizer source
Animal-sourced urea , are suitable for application organic agriculture, while pure synthetic forms of urea are not.[28][29] The common thread that can be seen through these examples is that organic agriculture attempts to define itself through minimal processing (in contrast to the man-made Haber process), as well as being naturally occurring or via natural biological processes such as composting.
Sewage sludge use in organic agricultural operations in the U.S. has been extremely limited and rare due to USDA prohibition of the practice (due to toxic metal accumulation, among other factors).[30][31][32] The USDA now requires 3rd-party certification of high-nitrogen liquid organic fertilizers sold in the U.S.[33]
Plant
Cover crops are also grown to enrich soil as a green manure through nitrogen fixation from the atmosphere;[34] as well as phosphorus (through nutrient mobilization)[35] content of soils.
Mineral
Naturally mined powdered limestone,[36] mined rock phosphate and sodium nitrate, are inorganic (in a chemical sense), are energetically intensive to harvest, yet are approved for usage in organic agriculture in minimal amounts.[36][37][38]
Environmental effects of fertilizer use
Runoff of
soil and fertilizer during a rain storm
Water
Eutrophication
The nitrogen-rich compounds found in fertilizer run-off is the primary cause of a serious depletion of oxygen in many parts of the ocean, especially in coastal zones; the resulting lack of dissolved oxygen is greatly reducing the ability of these areas to sustain oceanic fauna.[39] Visually, water may become cloudy and discolored (green, yellow, brown, or red).
About half of all the lakes in the United States are now eutrophic, while the number of oceanic dead zones near inhabited coastlines are increasing.[40] As of 2006, the application of nitrogen fertilizer is being increasingly controlled in Britain and the United States. If eutrophication can be reversed, it may take decades before the accumulated nitrates in groundwater can be broken down by natural processes.
High application rates of inorganic nitrogen fertilizers in order to maximize crop yields, combined with the high solubilities of these fertilizers leads to increased runoff into surface water as well as leaching into groundwater.[41][42][43] The use of ammonium nitrate in inorganic fertilizers is particularly damaging, as plants absorb ammonium ions preferentially over nitrate ions, while excess nitrate ions which are not absorbed dissolve (by rain or irrigation) into runoff or groundwater.[44]
Blue Baby Syndrome
Nitrate levels above 10 mg/L (10 ppm) in groundwater can cause 'blue baby syndrome' (acquired methemoglobinemia), leading to hypoxia (which can lead to coma and death if not treated).[45]
Soil
Soil acidification
Nitrogen-containing inorganic and organic fertilizers can cause soil acidification when added.[46] [4]. This may lead to decreases in nutrient availability which may be offset by liming.
Persistent organic pollutants
Toxic persistent organic pollutants ("POPs"), such as Dioxins, polychlorinated dibenzo-p-dioxins (PCDDs), and polychlorinated dibenzofurans (PCDFs) have been detected in agricultural fertilizers and soil amendments[47]
Heavy metal accumulation
The concentration of up to 100 mg/kg of cadmium in phosphate minerals (for example, minerals from Nauru[48] and the Christmas islands[49]) increases the contamination of soil with cadmium, for example in New Zealand.[50]
Uranium is another example of a contaminant often found in phosphate fertilizers (at levels from 7 to 100 pCi/g).[51] Eventually these heavy metals can build up to unacceptable levels and build up in vegetable produce.[50] (See cadmium poisoning) Average annual intake of uranium by adults is estimated to be about 0.5 mg (500 μg) from ingestion of food and water and 0.6 μg from breathing air.[52]
Steel industry wastes, recycled into fertilizers for their high levels of zinc (essential to plant growth), wastes can include the following toxic metals: lead arsenic, cadmium, chromium, and nickel. The most common toxic elements in this type of fertilizer are mercury, lead, and arsenic.[54][55] Concerns have been raised concerning fish meal mercury content by at least one source in Spain[56]
Also, highly radioactive Polonium-210 contained in phosphate fertilizers is absorbed by the roots of plants and stored in its tissues; tobacco derived from plants fertilized by rock phosphates contains Polonium-210 which emits alpha radiation estimated to cause about 11,700 lung cancer deaths each year worldwide.[57][58] [59][60][61][62]
For these reasons, it is recommended that nutrient budgeting, through careful observation and monitoring of crops, take place to mitigate the effects of excess fertilizer application.
Other problems
Atmospheric effects
Global methane concentrations (surface and atmospheric) for 2005; note distinct plumes
Methane emissions from crop fields (notably rice paddy fields) are increased by the application of ammonium-based fertilizers; these emissions contribute greatly to global climate change as methane is a potent greenhouse gas.[63]
Through the increasing use of nitrogen fertilizer, which is added at a rate of 1 billion tons per year presently[64] to the already existing amount of reactive nitrogen, nitrous oxide (N2O) has become the third most important greenhouse gas after carbon dioxide and methane. It has a global warming potential 296 times larger than an equal mass of carbon dioxide and it also contributes to stratospheric ozone depletion.[65]
Storage and application of some nitrogen fertilizers in some weather or soil conditions can cause emissions of the potent greenhouse gas—nitrous oxide. Ammonia gas (NH3) may be emitted following application of 'inorganic' fertilizers and/or manures and slurries.
The use of fertilizers on a global scale emits significant quantities of greenhouse gas into the atmosphere. Emissions come about through the use of:[66]
By changing processes and procedures, it is possible to mitigate some, but not all, of these effects on anthropogenic climate change.
Increased pest health
Excessive nitrogen fertilizer applications can also lead to pest problems by increasing the birth rate, longevity and overall fitness of certain agricultural pests.[67][68][69][70][71][72]
See also
- Soil fertility
- Manure
- Organic fertilizer
- Fertigation
- NPK rating
- Fertilizer labeling
- Agriculture and the environment
- Phosphogypsum
References
- ↑ "AESL Plant Analysis Handbook - Nutrient Content of Plant". Aesl.ces.uga.edu. http://aesl.ces.uga.edu/publications/plant/Nutrient.htm. Retrieved 2010-08-25.
- ↑ "Draft Code of Practice for Fertilier Description and Labeling". Fertilizer Industry Federation Association (FIFA). 2008-09-15. http://docs.google.com/viewer?a=v&q=cache:CgW191hwEBIJ:www.fifa.asn.au/files/pdf/regulation/Draft%2520Code%2520of%2520Practice%2520for%2520Fertilizer%2520Description%2520%26%2520Labelling.pdf+labeling+of+fertilizer&hl=en&gl=us&sig=AHIEtbSJjp1liw8XbwDLtw2aqua-xK0n1g. Retrieved 3 February 2010.
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- ↑ Vance; Uhde-Stone & Allan (2003). "Phosphorus acquisition and use: critical adaptations by plants for securing a non renewable resource.". New Phythologist (Blackwell Publishing) 157 (3): 423–447. doi:10.1046/j.1469-8137.2003.00695.x. http://www.jstor.org/pss/1514050.
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- ↑ United Nations Food and Agriculture Organization, Livestock's Long Shadow: Environmental Issues and Options, Table 3.3 retrieved 29 Jun 2009
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- ↑ IFA - Statistics - Fertilizer Indicators - Details - Raw material reserves (2002-10. Retrieved 2007-04-21.
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- ↑ Alternative Farming Systems Information Center. "Organic Production and Organic Food: Information Access Tools". Nal.usda.gov. http://www.nal.usda.gov/afsic/pubs/ofp/ofp.shtml#resources. Retrieved 2010-08-25.
- ↑ "Rapid Growth Found in Oxygen-Starved Ocean ‘Dead Zones’", NY Times, Aug. 14, 2008
- ↑ John Heilprin, Associated Press. "Discovery Channel :: News - Animals :: U.N.: Ocean 'Dead Zones' Growing". Dsc.discovery.com. http://dsc.discovery.com/news/2006/10/20/deadzone_pla.html. Retrieved 2010-08-25.
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- ↑ Hussein EM (1994). "Radioactivity of phosphate ore, superphosphate, and phosphogypsum in Abu-zaabal phosphate". Health Physics 67 (3): 280–282. doi:10.1097/00004032-199409000-00010. PMID 8056596.
- ↑ Barisic D, Lulic S, Miletic P (1992). "Radium and uranium in phosphate fertilizers and their impact on the radioactivity of waters". Water Research 26: 607–611. doi:10.1016/0043-1354(92)90234-U.
- ↑ Scholten LC, Timmermans CWM (1992). "Natural radioactivity in phosphate fertilizers". Nutrient cycling in agroecosystems 43: 103–107. doi:10.1007/BF00747688.
- ↑ American Public Health Association, Framing Health Matters, Waking a Sleeping Giant: The Tobacco Industry’s Response to the Polonium-210 Issue: Monique E. Muggli, MPH, Jon O. Ebbert, MD, Channing Robertson, PhD and Richard D. Hurt, MD [1]
- ↑ Journal of the Royal Society of Medicine, The big idea: polonium, radon and cigarettes, Tidd J R Soc Med.2008; 101: 156-157 [2]
- ↑ The Age Melbourne Australia, Big Tobacco covered up radiation danger, William Birnbauer [3]
- ↑ Bodelier, Paul, L.E.; Peter Roslev3, Thilo Henckel1 & Peter Frenzel1 (November 1999). "Stimulation by ammonium-based fertilizers of methane oxidation in soil around rice roots". Nature 403 (6768): 421–424. doi:10.1038/35000193. PMID 10667792. http://www.nature.com/nature/journal/v403/n6768/abs/403421a0.html. Retrieved Feb 2, 2009.
- ↑ http://www.nature.com/nature/journal/v451/n7176/fig_tab/nature06592_F1.html An Earth-system perspective of the global nitrogen cycle Nicolas Gruber & James N. Galloway Nature 451, 293-296(17 January 2008) doi:10.1038/nature06592
- ↑ "Human alteration of the nitrogen cycle, threats, benefits and opportunities" UNESCO - SCOPE Policy briefs, April 2007
- ↑ Food and Agricultural Organization of the U.N. retrieved 9 Aug 2007
- ↑ Jahn GC (2004). "Effect of soil nutrients on the growth, survival and fecundity of insect pests of rice: an overview and a theory of pest outbreaks with consideration of research approaches. Multitrophic interactions in Soil and Integrated Control". International Organization for Biological Control (IOBC) wprs Bulletin 27 (1): 115–122.
- ↑ Jahn GC, Sanchez ER, Cox PG (2001). "The quest for connections: developing a research agenda for integrated pest and nutrient management". International Rice Research Institute - Discussion Paper 42: 18.
- ↑ Jahn GC, Cox PG, Rubia-Sanchez E, Cohen M (2001). "The quest for connections: developing a research agenda for integrated pest and nutrient management. pp. 413-430,". S. Peng and B. Hardy [eds.] "Rice Research for Food Security and Poverty Alleviation". Proceeding the International Rice Research Conference, 31 March – 3 April 2000, Los Baños, Philippines. Los Baños (Philippines): International Rice Research Institute.: 692.
- ↑ Jahn GC, Almazan LP, Pacia J (2005). "Effect of nitrogen fertilizer on the intrinsic rate of increase of the rusty plum aphid, Hysteroneura setariae (Thomas) (Homoptera: Aphididae) on rice (Oryza sativa L.)". Environmental Entomology 34 (4): 938–943.
- ↑ Preap V, Zalucki MP, Nesbitt HJ, Jahn GC (2001). "Effect of fertilizer, pesticide treatment, and plant variety on realized fecundity and survival rates of Nilaparvata lugens (Stål); Generating Outbreaks in Cambodia". Journal of Asia Pacific Entomology 4 (1): 75–84. doi:10.1016/S1226-8615(08)60107-7.
- ↑ Preap V, Zalucki MP, Jahn GC (2002). "Effect of nitrogen fertilizer and host plant variety on fecundity and early instar survival of Nilaparvata lugens (Stål): immediate response". Proceedings of the 4th International Workshop on Inter-Country Forecasting System and Management for Planthopper in East Asia. 13–15 November 2002. Guilin China. Published by Rural Development Administration (RDA) and the Food and Agriculture Organization (FAO): 163–180,226.
External links
Physiological plant disorders : Plant nutrition deficiencies |
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Boron deficiency | Calcium deficiency | Iron deficiency | Magnesium deficiency | Manganese deficiency | Nitrogen deficiency | Phosphorus deficiency | Potassium deficiency | Micronutrient deficiency
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