Phosphorus
fullPhosphorus has no drinking water limit but is the nutrient that every wastewater discharge consent in Europe now regulates to 0.5 to 2 mg/L, the target of chemical and biological phosphorus removal, the recoverable resource in struvite, and, as phosphate and phosphonate, the sequestrant and antiscalant chemistry of membranes and mains.
Typical wastewaters
- municipal sewage orthophosphate, polyphosphate and organic phosphorus from excreta and detergents; total phosphorus 4 to 12 mg/L as P
- digester liquor and sludge dewatering sidestreams orthophosphate released in anaerobic digestion with ammonium and magnesium, crystallising as struvite at pH 8.5 to 9
- chemical sector effluent (cooling and heating systems, nutrient dosing) orthophosphate, polyphosphate and phosphonate from cooling and boiler conditioning and phosphate added as nutrient for the biological plant; total phosphorus 0.50 to 3.0 mg/L
- textile dyeing and finishing total phosphorus 0.4 to 2 mg/L BAT-AEL for direct discharge
- reverse osmosis concentrate phosphonate antiscalant (an HEDP derivative dosed at 5 mg/L in the case read) concentrated in the reject, counted as total phosphorus
1 · Identity
- Symbol, number
- P, 15
- Oxidation states in water
- +5 only in practice: orthophosphate (H₃PO₄, H₂PO₄⁻, HPO₄²⁻, PO₄³⁻), condensed polyphosphates that hydrolyse back to orthophosphate, organic phosphorus esters, and phosphonates (C-P bonded antiscalants such as HEDP and ATMP). Analysts split total phosphorus into reactive (ortho), acid hydrolysable (poly) and organic fractions.
- Note
- The element entry covers phosphate rock, phosphoric acid and the eutrophication warning. This chapter is the wastewater engineer's phosphorus: speciation by pH, metal salt and lime precipitation, enhanced biological removal, struvite and the limits that drive them.
2 · Occurrence in water
- Natural sources
- Weathering of apatite gives low natural orthophosphate; most surface water phosphorus is bound to particles and to iron oxides and is released from sediments under anoxic conditions. Phosphate is the limiting nutrient of most fresh waters (the element entry).
- Anthropogenic sources
- Sewage (excreta, detergents where not banned), agricultural runoff and manure, phosphate fertiliser and phosphoric acid plants, food and dairy processing, cooling water and boiler conditioning with phosphates and phosphonates (the CWW BAT conclusions note phosphorus originating from heating or cooling systems), and phosphorus added deliberately to industrial biological treatment as a nutrient.
| matrix | typical range | note |
|---|---|---|
| untreated municipal wastewater | 4 to 12 mg/L as P textbook typical values, region-dependent | total phosphorus, weak to strong domestic wastewater (Metcalf and Eddy chapter 3 typical composition table, from the chapter, not re-read) |
| seawater | 0.06 mg/L single figure; surface ocean is nutrient depleted | estimated oceanic abundance, Jefferson Lab figure via PubChem, as in the element entry |
3 · Speciation
Orthophosphate is a triprotic acid with pKa values near 2.1, 7.2 and 12.3, so in natural and waste water it is a mixture of H₂PO₄⁻ and HPO₄²⁻ around neutral pH, shifting to HPO₄²⁻ above pH 7.2; the fully deprotonated PO₄³⁻ only matters at the high pH of lime treatment. Polyphosphates hydrolyse slowly to orthophosphate, faster when warm and acidic; organic phosphorus is released by biological oxidation. Metal cations precipitate orthophosphate: aluminium and iron(III) as AlPO₄ and FePO₄ near neutral pH, calcium as hydroxyapatite above pH 10, magnesium with ammonium as struvite at pH 8.5 to 9. Phosphonates and polyphosphates at a few mg/L hold calcium carbonate and sulfate below their scaling point by threshold inhibition.
| condition | dominant species | note |
|---|---|---|
| natural and waste water, pH 6 to 8 | H₂PO₄⁻ and HPO₄²⁻ (soluble reactive phosphorus); particulate and organic P; polyphosphate from detergents and conditioning | the fraction the ascorbic acid test sees is orthophosphate |
| chemical precipitation with Al or Fe(III), pH 5.5 to 7 | AlPO₄ (s), FePO₄ (s), phosphate adsorbed on Al(OH)₃ and Fe(OH)₃ | the working range of alum and ferric chloride for phosphorus |
| lime treatment, pH above 10 | hydroxyapatite Ca₅(PO₄)₃OH (s) with CaCO₃ and Mg(OH)₂ | lime dose is set by alkalinity, not by phosphorus |
| anaerobic digester liquor and sludge dewatering, pH 7.5 to 9, high NH₄⁺ and Mg²⁺ | struvite MgNH₄PO₄.6H₂O (s) | a scale in pipes and a product in recovery reactors |
| EBPR biomass | intracellular polyphosphate, 4 to 15 percent of dry biomass in phosphorus accumulating organisms against about 2 percent in ordinary bacteria | the phosphorus leaves the plant in the waste sludge |
- Solubility
- AlPO₄ and FePO₄ have solubility minima near pH 6 to 7 and hydroxyapatite is very insoluble above pH 10; struvite solubility falls with rising pH to a minimum near pH 9 (Wu et al.). Constants are not quoted because the sources read do not print them.
- Hydrolysis
- Polyphosphates (tripolyphosphate, hexametaphosphate) hydrolyse to orthophosphate over hours to days, which is why sequestered iron and manganese eventually precipitate and why total phosphorus samples are digested before analysis.
- Complexation
- Phosphate sorbs on iron and aluminium hydroxides and competes with arsenate on adsorbents (EPA arsenic manual, via the arsenic chapter: each 0.5 mg/L of phosphate above 0.2 mg/L cuts granular ferric hydroxide capacity about 30 percent); phosphonates chelate calcium and magnesium and poison crystal growth.
- Precipitates
- AlPO₄, FePO₄, hydroxyapatite Ca₅(PO₄)₃OH and other calcium phosphates, struvite MgNH₄PO₄.6H₂O, vivianite Fe₃(PO₄)₂ in iron dosed anaerobic sludge.
4 · Role in treatment
5 · Removal and control
- Efficiency
- to 1 mg/L routinely; below 0.5 mg/L with tertiary filtration and higher metal ratios (Metcalf and Eddy chapter 6, from the chapter)
- Interferences
- organic and polyphosphate fractions are not precipitated until hydrolysed; sludge mass rises
- Efficiency
- not quoted
- Interferences
- large sludge volume
- Efficiency
- not quoted as a general figure in the source read; the reactors studied gave 5.4 and 8.3 mg/L effluent phosphate from high influent phosphorus
- Interferences
- nitrate or oxygen in the anaerobic zone, low VFA, glycogen accumulating organisms, phosphorus release in digestion
- Efficiency
- 80.8 to 95.5 percent phosphorus removal as Mg:P rose from 0.8 to 1.2 in the study quoted
- Interferences
- calcium competes to form calcium phosphate; pH above 11 loses ammonia
- Efficiency
- not quoted
- Interferences
- soluble non reactive phosphorus passes
6 · Analytics
| method | standard | detection limit | note |
|---|---|---|---|
| ascorbic acid molybdenum blue colorimetry | Standard Methods 4500-P E (after 4500-P B digestion for total P); ISO 6878; EPA 365 series | ISO 6878: 0.005 to 0.8 mg/L P without dilution | orthophosphate directly (reactive P); persulfate or acid digestion converts poly and organic P for total P; ZDHC lists ISO 6878, EPA 365.4 and SM 4500-P J for total phosphorus |
| ion chromatography | ISO 10304-1 | lower limit of application 0.1 mg/L orthophosphate | orthophosphate only |
| ICP-OES (total phosphorus) | EPA 200.7 (214.914 nm); ISO 11885 | EPA 200.7 instrument detection limit 76 µg/L, total recoverable method detection limit 0.06 mg/L | no speciation; phosphorus is not an analyte of EPA 200.8 (ICP-MS) |
- Sampling pitfalls
- Filter 0.45 µm at once for dissolved reactive phosphorus; unfiltered samples convert particulate and polyphosphate to orthophosphate on standing. Acidify or freeze samples for total phosphorus. Phosphate contamination from detergent washed glassware is the classic blank problem; phosphate free detergents and acid rinsed glass are standard.
7 · Regulatory limits
Limits change, and many are set locally. Treat these as the published values to start from, not as your compliance target: check the standard in force at your site and the numbers written into your own permit.
| body | limit | note |
|---|---|---|
| WHO GDWQ 4th ed. with addenda (2022) | no guideline | no chemical fact sheet for phosphate exists on the WHO fact sheet path |
| EU DWD 2020/2184 | not set | phosphorus is not in Annex I |
| US EPA | not regulated | absent from the primary and secondary standards |
| body | limit | note |
|---|---|---|
| EU UWWTD 91/271/EEC, Annex I Table 2 (sensitive areas) | 2 (10,000 to 100,000 p.e.); 1 (more than 100,000 p.e.) mg/L P superseded progressively by the 2024 recast | annual mean total phosphorus, or a minimum reduction of 80 percent; molecular absorption spectrophotometry as reference method |
| EU UWWTD 2024/3019 (recast), Annex I Table 2 (tertiary treatment) | 0.7 (10,000 to below 150,000 p.e.); 0.5 (150,000 p.e. and above) mg/L P time-sensitive: Article 7 plant level deadlines were not captured this session | or minimum reduction 87.5 and 90 percent; national load reduction targets of at least 75 percent of total phosphorus from 1 January 2025, 82.5 percent by 31 December 2039 and 87.5 percent by 31 December 2045; tertiary treatment is imposed on all plants of 150,000 p.e. and above and on 10,000 p.e. and above in eutrophication sensitive areas |
| EU CWW BREF BAT-AEL (Decision 2016/902), total phosphorus | 0.50 to 3.0 mg/L | applies if the emission exceeds 300 kg/yr; the lower end is typically achieved when phosphorus is added for the biological plant or originates mainly from heating or cooling systems |
| EU textiles BAT conclusions (Decision 2022/2508), total phosphorus, direct discharge | 0.4 to 2 mg/L footnotes on applicability not read | BAT-AEL as daily average |
| US EPA 40 CFR effluent guidelines | not set other categories not read | no phosphorus limit in the categories read this session (410, 423, 425, 433, 434); phosphorus limits in the US are set in NPDES permits against state nutrient criteria |
| Abu Dhabi ADS 23/2017, discharge to the marine environment (EAD) | 2.0 mg/L as P region-dependent; marine discharge only | Table 1 phosphate (as P) maximum allowable concentration |
| Abu Dhabi DoE Trade Effluent Control Regulations 2022, discharge to sewer | 50 mg/L region-dependent; sewer discharge | Table A₂ total phosphorus maximum allowable concentration |
| sector | body | limit | note |
|---|---|---|---|
| textile and leather | ZDHC Wastewater Guidelines v₂.1 (2022), total phosphorus | 3 foundational; 0.5 textile and 1 leather progressive; 0.1 textile and 0.5 leather aspirational mg/L | methods ISO 17294, ISO 11885, ISO 6878, EPA 365.4, SM 4500-P J, EPA 200.7 and 200.8 |
8 · Health and environmental effects
- Toxicity
- Orthophosphate in water is not a health concern at any level found; a person eats about 1 g of phosphate a day. White phosphorus, 50 mg fatal, is the toxic form and does not occur in water (the element entry).
- Bioaccumulation
- Phosphorus is taken up by every organism as nutrient; there is no bioaccumulation hazard in the toxicological sense.
- Ecotoxicity
- Eutrophication is the effect: phosphate is the limiting nutrient of most lakes and rivers, so discharge limits are set on ecology, not toxicity. The US EPA aquatic life table carries only elemental phosphorus (1986) with no criterion values; nutrient criteria are ecoregional and were not read.
Flags
- The 4 to 12 mg/L municipal wastewater range is a Metcalf and Eddy typical composition table cited from memory of chapter 3.
- The phosphate pKa values, the metal to phosphorus dosing ratios, the lime dose rule and the struvite scaling statement are textbook chapters not re-read this session.
- The 2024 UWWTD Article 7 deadlines for tertiary treatment by plant size were not captured; the national load reduction dates are from Article 10 as read.
- The textile BAT-AEL footnotes on when the phosphorus value applies were not read.
- The antiscalant chemistry rests on one case study (a bisphosphonate at 5 mg/L) and a textbook chapter; typical HEDP and ATMP doses and the German drinking water limit seen in search summaries were not read and are not quoted.
- The EBPR effluent figures quoted are from a laboratory study with high influent phosphorus, not a full scale plant.
- Abu Dhabi values cover two media and two parameters (marine phosphate as P 2.0 mg/L, sewer total phosphorus 50 mg/L).
Gaps
- No source read gives phosphorus in groundwater, surface water or specific industrial effluents; the eutrophication threshold concentrations were not sourced.
- EPA Nutrient Control Design Manual (2010) could not be opened (file too large for the fetch tool); Metcalf and Eddy chapters stand in.
- Typical antiscalant doses and phosphonate limits for drinking water production were not read.
- The US ecoregional nutrient criteria and the EPA 1986 Gold Book phosphorus recommendations were not read.
- The Standard Methods 4500-P E detection limit was not read; the ISO 6878 range stands in.
- Other GCC discharge standards (Saudi, Oman, Qatar) were not read.
- No solubility products for AlPO₄, FePO₄, hydroxyapatite, vivianite or struvite were read. The phosphoric acid pKa ladder is from Stumm and Morgan chapter 3 and the alum, vivianite and polyphosphate stoichiometries from Metcalf and Eddy chapters 3 and 6, from the chapter, not re-read.
- No balanced equation is written for enhanced biological phosphorus removal: the anaerobic release and aerobic uptake steps involve acetate, PHB, glycogen and intracellular polyphosphate of no fixed formula, and no source read prints a stoichiometry.
Sources
Directive (EU) 2024/3019 concerning urban wastewater treatment (recast), Articles 7 and 10 and Annex I Table 2
Commission Implementing Decision (EU) 2016/902 establishing BAT conclusions for common waste water and waste gas treatment/management systems in the chemical sector (CWW), BAT 12 Tables 1 and 2
Commission Implementing Decision (EU) 2022/2508 establishing BAT conclusions for the textiles industry, BAT-AELs for direct and indirect discharges (OJ L 325, 20.12.2022, pp. 141 to 142)
ZDHC Wastewater Guidelines Version 2.1 (November 2022), conventional parameters, anions and metals tables and sludge Table 4A
Abu Dhabi Specification ADS 23/2017, Environmental Specifications for Land-Based Liquid Discharges to the Marine Environment (Environment Agency Abu Dhabi), Table 1
Abu Dhabi Department of Energy, Trade Effluent Control Regulations 2022 (DoE/PD/R01/005, effective 1 January 2022), Appendix Tables A2 and A4
40 CFR 433.15, Pretreatment standards for existing sources (PSES), metal finishing point source category
Directive (EU) 2020/2184 on the quality of water intended for human consumption (recast), Annex I Parts B and C and Annex III
US EPA, National Primary Drinking Water Regulations (table of MCLs and treatment techniques)
WHO GDWQ 4th ed. with addenda (2022), chapter 12 chemical fact sheets on the WHO fact sheet path (no phosphate sheet exists at that path)
WHO, Hardness in Drinking-water, background document, WHO/HSE/WSH/10.01/10/Rev/1 (2011), sections 1.1 to 1.3, 2.1, 4.2 and 4.3
Wu S. et al., Effects of physicochemical parameters on struvite crystallization based on kinetics, International Journal of Environmental Research and Public Health 19(12), 7204 (2022), doi 10.3390/ijerph19127204
Xing W. et al., Dynamics of intracellular polymers in enhanced biological phosphorus removal processes under different organic carbon concentrations, BioMed Research International 2013, 761082, doi 10.1155/2013/761082, introduction
Popov K. et al., A case study of calcium carbonate crystallization during reverse osmosis water desalination in presence of novel fluorescent-tagged antiscalants, Membranes 12(2), 194 (2022), doi 10.3390/membranes12020194
US EPA, National Recommended Water Quality Criteria, Aquatic Life Criteria Table (phosphorus elemental, 1986, no values)
Standard Methods (online edition), 4500-P Phosphorus (B. digestion, E. ascorbic acid method)
ISO 6878:2004, Water quality. Determination of phosphorus. Ammonium molybdate spectrometric method
ISO 10304-1:2007, Water quality. Determination of dissolved anions by liquid chromatography of ions. Part 1: bromide, chloride, fluoride, nitrate, nitrite, phosphate and sulfate
US EPA Method 200.7, Revision 4.4 (1994), Determination of metals and trace elements in water and wastes by ICP-AES, Table 1 (wavelengths and instrument detection limits), Table 4 (method detection limits) and Table 5 (argon plasma conditions)
ISO 11885:2007, Water quality. Determination of selected elements by inductively coupled plasma optical emission spectrometry (ICP-OES)
PubChem element summary for phosphorus; estimated oceanic abundance 6 x 10^-2 mg/L (PUG View, reference 5, Jefferson Lab)
The Element Book, layer 1 entry for phosphorus (data/elements/P.json and data/reference/text/P.json)
Stumm, W. and Morgan, J. J., Aquatic Chemistry, 3rd ed. (Wiley, 1996), chapter 3 (acids and bases: phosphoric acid dissociation)
Metcalf and Eddy, Wastewater Engineering: Treatment and Resource Recovery, 5th ed. (McGraw-Hill, 2014), chapter 3 (wastewater composition), chapter 6 (chemical precipitation of phosphorus), chapter 8 (enhanced biological phosphorus removal) and chapter 15 (nutrient recovery, struvite)
Crittenden, J. C. et al., MWH's Water Treatment: Principles and Design, 3rd ed. (Wiley, 2012), chapter 17 (reverse osmosis: scaling and antiscalants)
Identity
- Name and symbol
- Phosphorus, P
- Atomic number
- 15 protons
- Position
- group 15 · period 3 · p-block · polyatomic nonmetal
- CAS number
- 7723-14-0
Atomic structure
- Atomic mass
- 30.973 u
- Electron configuration
- 1s² 2s² 2p⁶ 3s² 3p³
[Ne] 3s²³p³ - Electrons per shell
- 2, 8, 5
- Valence electrons
- 5 outer shell
| isotope | mass (u) | abundance |
|---|---|---|
| 31P | 30.973 761 998(5) | 100 % |
Physical properties
- State at room temperature
- Solid
- Melting point
- 317.3 K (44.15 °C)
- Boiling point
- 553.65 K (280.5 °C)
- Density
- 1.82 g/cm3
- Appearance
- white, red and violet are waxy, black is metallic-looking
- Thermal conductivity
- white: 0.236 W/(m·K)
- Electrical resistivity
- not in sources
- Electrical conductivity
- not in sources
- Crystal structure
- body-centred cubic
- Molar heat capacity
- 23.824 J/(mol·K)
Chemical properties
- Oxidation states
- +5, +3, -3
- Electronegativity
- 2.19 (Pauling Scale)
- Ionisation energy
- 10.487 eV
1st 1,011.8, 2nd 1,907, 3rd 2,914.1 kJ/mol - Electron affinity
- 0.746 eV
- Atomic radius
- empirical 107, covalent 107, van der Waals 180 pm
- Ionic radius
- P³⁺ 44; P⁵⁺ 38 pm
- Reactivity
- A pnictogen whose allotropes differ sharply in reactivity: white P4 is pyrophoric, red phosphorus is stable in air until about 300 C and black is the least reactive; all forms are too reactive to occur free, and the chemistry runs on the +5, +3 and -3 states.
- with water
- Does not react; white phosphorus is insoluble in water and is stored under it to keep air away.
- with oxygen, air
- White phosphorus glows in moist air (chemiluminescence) and ignites spontaneously at about 30 C, burning to phosphorus pentoxide; red phosphorus ignites at about
- with acids
- Does not react with non-oxidising acids such as hydrochloric acid, but dissolves in oxidising acids such as nitric acid.
- with halogens
- All the halogens react violently with phosphorus, white phosphorus most dramatically, giving the trihalides PX3 and, with excess chlorine or bromine, the pentahalides:
- Typical compounds
- H₃PO₄ phosphoric acid triprotic acid made by the megatonne for fertilisers
- P₄O₁₀ phosphorus pentoxide anhydride of phosphoric acid; fierce drying agent
- PCl₃ phosphorus trichloride chlorine over molten phosphorus; pesticide intermediate
- Ca₃(PO₄)₂ calcium phosphate impure in phosphate rock (apatite); bone ash
- Na₃PO₄ trisodium phosphate cleaner, water softener, boiler scale control
- PH₃ phosphine hydride, oxidised by air; from phosphides and water
Occurrence, production and use
- Crustal abundance
- 1.05×103 milligrams per kilogram
- Oceanic abundance
- 6×10-2 milligrams per liter
- Occurrence and sources
Never found free in nature, it is widely distributed in combination with minerals. Phosphate rock, which contains the mineral apatite, an impure tri-calcium phosphate, is an important source of the element. Large deposits are found in Russia, in Morocco, and in Florida, Tennessee, Utah, Idaho, and elsewhere.
- dissolved in seawater about 0.06 mg/L; crustal estimate 1,050 mg/kg (Jefferson Lab figures via PubChem)
- sedimentary phosphorite (francolite) China, Morocco, United States (Florida, North Carolina, Idaho, Utah), Russia, Jordan, Saudi Arabia, Egypt, Tunisia, Peru, Brazil, Algeria; also on continental shelves and seamounts
- igneous apatite (fluorapatite) Brazil, Canada, Finland, Russia, South Africa
- Extraction, production
- Wet-process phosphoric acid: phosphate rock digested with sulfuric acid
The tricalcium phosphate of the rock reacts with concentrated sulfuric acid; the insoluble calcium sulfate (phosphogypsum) is filtered off, and the reaction is slowed by the gypsum layer that forms on each particle (AAF BREF, PDF p242). Fluoride leaves as gas and as fluosilicic acid, which BAT says to market or dispose of, and phosphogypsum is piled with precautions (PDF p7). More than 95 percent of US phosphate rock went this way in 2024, and about 25 percent of the acid was exported as DAP, MAP and merchant acid (USGS, printed pp. 134 to 135).
Electric furnace reduction to elemental phosphorusPhosphate rock, coke as reductant and gravel for slag are heated in an electric resistance furnace; the gas passes an electrofilter to drop dust and the phosphorus vapour is condensed under water (AAF BREF, PDF p279; RSC). The small share of rock not made into acid goes this way, chiefly to glyphosate and other industrial phosphorus chemicals (USGS).
Phosphorus chlorides from white phosphorusHighly exothermic, -1,276 kJ/mol; phosphoryl chloride follows by oxidation, p217).
- Uses
Phosphorus has three main allotropes: white, red and black. White phosphorus is poisonous and can spontaneously ignite when it comes in contact with air. For this reason, white phosphorus must be stored under water and is usually used to produce phosphorus compounds. Red phosphorus is formed by heating white phosphorus to 250°C (482°F) or by exposing white phosphorus to sunlight. Red phosphorus is not poisonous and is not as dangerous as white phosphorus, although frictional heating is enough to change it back to white phosphorus. Red phosphorus is used in safety matches, fireworks, smoke bombs and pesticides. Black phosphorus is also formed by heating white phosphorus, but a mercury catalyst and a seed crystal of black phosphorus are required. Black phosphorus is the least reactive form of phosphorus and has no significant commercial uses.
Phosphoric acid (H3PO4) is used in soft drinks and to create many phosphate compounds, such as triple superphosphate fertilizer (Ca(H2PO4)2·H2O). Trisodium phosphate (Na3PO4) is used as a cleaning agent and as a water softener. Calcium phosphate (Ca3(PO4)2) is used to make china and in the production of baking powder. Some phosphorus compounds glow in the dark or emit light in response to absorbing radiation and are used in fluorescent light bulbs and television sets.
In recent years, concentrated phosphoric acids, which may contain as much as 70% to 75% P2O5 content, have become of great importance to agriculture and farm production. World-wide demand for fertilizers has caused record phosphate production. Phosphates are used in the production of special glasses, such as those used for sodium lamps.
Bone-ash calcium phosphate is used to create fine chinaware and to produce mono-calcium phosphate, used in baking powder.
Phosphorus is also important in the production of steels, phosphor bronze, and many other products. Trisodium phosphate is important as a cleaning agent, as a water softener, and for preventing boiler scale and corrosion of pipes and boiler tubes.
Phosphorus is also an essential ingredient of all cell protoplasm, nervous tissue, and bones.
- Fertilisers: diammonium and monoammonium phosphate, superphosphates and NPK compounds from wet-process acid; the largest use of phosphorus by far; phosphoric acid is the most important use of sulfuric acid world consumption of P2O5 in fertilisers 47.5 million tonnes in 2024, up from 45.8 in 2023 and projected 51.8 by 2028
- Food and animal feed: animal feed supplements from phosphoric acid; purified phosphoric acid for food uses; monocalcium phosphate in baking powder; bone ash in fine china
- Industrial phosphorus chemicals: glyphosate herbicide, the main outlet for elemental phosphorus; phosphorus trichloride and phosphoryl chloride; detergent phosphates, now being phased out; trisodium phosphate cleaner and water softener; matches, flares and incendiaries
- Batteries: lithium-iron-phosphate cathodes; more than 90 percent of LFP batteries were made in China in 2024, and purified phosphoric acid plants are being built in Quebec for them
- Steel, glass and ceramics: phosphor bronze; special glasses for sodium lamps
- Safety, toxicity
Phosphorus is very poisonous, 50 mg constituting an approximate fatal dose. Exposure to white phosphorus should not exceed 0.1 mg/m3 (8-hour time-weighted average per 40-hour work week). White phosphorus should be kept under water (as it is dangerously reactive in air) and should be handled with forceps, as contact with the skin may cause severe burns.
When exposed to sunlight or when heated in its own vapor to 250°C, it is converted to the red variety, which does not phosphoresce in air as does the white variety. This form does not ignite spontaneously and is not as dangerous as white phosphorus. It should, however, be handled with care as it does convert to the white form at some temperatures and it emits highly toxic fumes of the oxides of phosphorus when heated. The red modification is fairly stable, sublimes with a vapor pressure of 1 atm at 17C, and is used in the manufacture of safety matches, pyrotechnics, pesticides, incendiary shells, smoke bombs, tracer bullets, etc.
GHS classification, signal word Danger- H228 Flammable solid Flammable solids
- H412 Harmful to aquatic life with long lasting effects to the aquatic environment, long-term hazard
- H250 Catches fire spontaneously if exposed to air Pyrophoric liquids
- H300 Fatal if swallowed Acute toxicity, oral
- H314 Causes severe skin burns and eye damage Skin corrosion/irritation
- H330 Fatal if inhaled Acute toxicity, inhalation
- H400 Very toxic to aquatic life Hazardous to the aquatic environment, acute hazard
Discovery and name
- Discovered by
- Hennig Brand
- Discovered
- 1669
- First isolated
- not in sources
- Named by
- not in sources
- Origin of the name
- from the greek Φωσφόρος, meaning 'light-bearer'
Phosphorus exists in four or more allotropic forms: white (or yellow), red, and black (or violet). Ordinary phosphorus is a waxy white solid; when pure it is colorless and transparent. White phosphorus has two modifications: alpha and beta with a transition temperature at -3.8°C.
It is insoluble in water, but soluble in carbon disulfide. It takes fire spontaneously in air, burning to the pentoxide.
Conventions
Valence electrons are counted by the usual convention: the outer shell for s- and p-block elements, ns and (n-1)d for the d-block, ns, (n-1)d and (n-2)f for the f-block. Lanthanides and actinides are placed in the f-block with no group number. Electrical conductivity is the reciprocal of the printed resistivity. Ionic radii are Shannon effective radii, six-coordinate unless noted. Where a field reads “not in sources” the value was not found; it is a gap, not a zero. Regulatory limits are the published values and change often, so check the standard in force at your site and the numbers written into your own permit before you design to them.
Data
Element records, isotopes, radii and the descriptive text come from PubChem (NCBI), the Los Alamos National Laboratory periodic table, IUPAC CIAAW and the IAEA Atomic Mass Data Center. Appearance, thermal conductivity, electrical resistivity, crystal structure, discovery and the origin of each name come from Wikipedia and Periodic-Table-JSON, used under CC BY-SA 4.0. Hazard classifications come from the ECHA C&L inventory via PubChem. Ionic radii follow R. D. Shannon (1976). The water chapters cite their own sources at the foot of each entry, and are written to the level of Snoeyink and Jenkins, Stumm and Morgan, MWH's Water Treatment and Metcalf and Eddy.