Sodium
fullSodium is the conservative cation of water: the major ion of seawater and brackish water, an EU indicator parameter at 200 mg/L, a taste and dietary concern rather than a toxicant, the ion that softeners and every sodium reagent (hypochlorite, caustic, soda ash, bicarbonate, brine) add to water, and, as the sodium adsorption ratio, the number that decides whether an irrigation water ruins the soil.
Typical wastewaters
- municipal sewage Na⁺, conservative; sewage effluent carries the sodium of treatment chemicals (fluoride, bicarbonate, hypochlorite up to 30 mg/L together) and of domestic softeners (over 300 mg/L)
- textile wet processing Na⁺ with chloride and sulfate from dyeing salt and neutralisation, reported as total dissolved solids; not removed by a standard effluent plant
- desalination brine (reverse osmosis concentrate, thermal distillation) Na⁺ with Cl⁻ concentrated from seawater or brackish water; the marine discharge specification exempts desalination brine
- ion exchange regenerant (softener spent brine) NaCl brine carrying the exchanged calcium and magnesium; spent brine disposal is the environmental cost of ion exchange
- road de-icing runoff NaCl salt runoff to surface water and groundwater
1 · Identity
- Symbol, number
- Na, 11
- Oxidation states in water
- +1 only, as the hydrated Na⁺ ion; no hydrolysis, no complexes of consequence, no insoluble salts in fresh water (the element entry: almost every sodium salt is soluble). Sodium is what is left when everything else has been removed, which is why it leaves treatment plants as salinity.
- Note
- The element entry carries the metal, halite, soda ash and caustic soda production. This chapter is sodium as a dissolved ion, as a reagent counter-ion and as sodicity. Sodium hypochlorite chemistry is in the chlorine chapter, the carbonate equilibria in the carbon chapter, and the dechlorination sulfite salts in the chlorine chapter.
2 · Occurrence in water
- Natural sources
- Sodium is ubiquitous in water because its salts are so soluble; it is leached from the terrestrial environment to groundwater and surface water, and seawater is the reservoir (WHO background document). Saline intrusion, mineral deposits and sea spray raise it; sodium bicarbonate groundwater forms where calcium is exchanged for sodium on clays, giving soft, high sodium, high fluoride and high boron water (general geochemistry).
- Anthropogenic sources
- Sewage effluent, road de-icing salt, and treatment chemicals: sodium fluoride, sodium bicarbonate and sodium hypochlorite together can add up to 30 mg/L and domestic water softeners over 300 mg/L (WHO); industrial brines, reverse osmosis concentrate, ion exchange regenerant, caustic soda and soda ash dosing, and the sodium salts of every industry (textile dyeing salt, chlor-alkali, pulp, food).
| matrix | typical range | note |
|---|---|---|
| drinking water, typical | below 20 mg/Lregion-dependent; old surveys | most supplies; can exceed 250 mg/L in some countries; a 1963 to 1966 US survey of 2100 samples ranged 0.4 to 1900 mg/L with 42 percent above 20 mg/L and 5 percent above 250 mg/L; a later survey of 630 systems ranged below 1 to 402 mg/L |
| groundwater supplies, US (989 community systems) | median 16.4; 99th percentile 517 mg/LUS survey | 37 percent above 30 mg/L and 13 percent above 120 mg/L in the National Inorganic and Radionuclide Survey |
| surface water, US rivers | 20 (Mississippi) to 120,000 (Great Salt Lake) mg/Lextremes, not a distribution | the range the EPA advisory quotes for US surface waters |
| seawater | 10,800 mg/Lsingle figure | oceanic abundance figure, Jefferson Lab via PubChem, quoted in the element entry |
| drinking water after domestic softening | over 300 mg/L | can reach this; usually much lower; the stoichiometry adds 0.46 mg sodium per mg of hardness as CaCO₃ exchanged |
| municipal and industrial wastewater | not read | no effluent survey read; textile effluent salt is high enough that ZDHC requires TDS to be reported ahead of a future limit |
3 · Speciation
Sodium is Na⁺ everywhere in water: no hydrolysis, no redox, no precipitation, ion pairs with sulfate and carbonate that matter only in brines. It is conservative, so it tracks salinity, and its ratio to calcium and magnesium (the sodium adsorption ratio, SAR) rather than its concentration decides its effect on soil: a high sodium, low calcium water disperses clay and destroys infiltration (FAO 29). Its taste threshold depends on the anion: about 20 mg/L as sodium carbonate, 150 as chloride, 190 as nitrate, 220 as sulfate and 420 as bicarbonate at room temperature (WHO).
| condition | dominant species | note |
|---|---|---|
| all natural and treated water | Na⁺ (hydrated) | conservative; passes every process except membranes, distillation and ion exchange |
| irrigation water with a high ratio of sodium to calcium plus magnesium | Na⁺ exchanging onto soil clay for Ca²⁺ and Mg²⁺ | sodic soil, reduced infiltration; evaluate SAR together with electrical conductivity (FAO 29) |
| brines and reverse osmosis concentrate | Na⁺ with NaSO₄⁻ and NaCO₃⁻ ion pairs | not relevant below a few g/L |
- Solubility
- Sodium chloride 357 g/L and sodium carbonate 71 g/L at 0 C (WHO); all common sodium salts dissolve freely, so sodium has no solubility control in water and is never removed by precipitation.
- Hydrolysis
- None; Na⁺ is neither an acid nor a base in water. The pH of a sodium salt solution is that of its anion (carbonate alkaline, chloride neutral).
- Complexation
- Negligible; weak outer sphere ion pairs with sulfate and carbonate only at high ionic strength (general; not quantified in the sources read).
- Precipitates
- None from water. Sodium is the counter-ion left in solution when calcium, magnesium and metals are precipitated with sodium reagents.
4 · Role in treatment
5 · Removal and control
- Efficiency
- rejection above 99 percent for seawater membranes (general, not from a source read)
- Interferences
- scaling by calcium carbonate and sulfate in the concentrate; boron and CO₂ pass (boron and carbon chapters)
- Efficiency
- not quantified
- Efficiency
- essentially complete
- Efficiency
- to µg/L in mixed beds (general)
- Efficiency
- nil
- Efficiency
- not applicable
6 · Analytics
| method | standard | detection limit | note |
|---|---|---|---|
| flame atomic absorption or flame emission | Standard Methods 3111 B; 3500-Na B (flame emission); ISO 9964-1 and 9964-3 | 2 µg/L by flame AAS (WHO) | the classical methods; ionisation suppression with potassium |
| ICP-OES | EPA 200.7; Standard Methods 3120 B; ISO 11885 | 40 µg/L by ICP-AES (WHO) | sodium is among the routine ICP analytes |
| ion chromatography, cations | Standard Methods 4110 (anions) with cation columns; ISO 14911 | not read | gives sodium, potassium, ammonium, calcium and magnesium together, the SAR set |
| SAR calculation | FAO 29 Figure 1 | not applicable | SAR equals sodium divided by the square root of half the sum of calcium and magnesium, all in meq/L; adjusted SAR corrects for calcium precipitation with bicarbonate |
- Sampling pitfalls
- Sodium is the easiest ion to contaminate and the hardest to lose: sweat, glass leaching, sodium containing preservatives and detergents raise it. Use plastic bottles rinsed with the sample; acidify with nitric acid only if metals share the bottle. Report the anion balance; sodium is often calculated by difference in old data and is then only as good as the other ions.
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 firm conclusions on sodium in drinking water and hypertension, so no health based guideline; above 200 mg/L unacceptable taste; assessment 1993 |
| EU DWD 2020/2184 | 200 mg/L | Annex I Part C indicator parameter |
| US EPA | not regulated | no primary or secondary standard; 2003 drinking water advisory recommends 30 to 60 mg/L for taste (not enforceable, a guideline for States) and keeps the 20 mg/L guidance level for people restricted to 500 mg/day sodium, not to be extrapolated to the whole population; sodium results are reported to the State health authority |
| body | limit | note |
|---|---|---|
| EU CWW BREF BAT-AEL (Decision 2016/902) | not set | sodium and salinity are not BAT 12 parameters; the BAT conclusions require monitoring of salts among the relevant pollutants in the waste water stream inventory |
| US EPA 40 CFR 133.102, secondary treatment | not set | no federal sodium or TDS effluent limit; salinity limits are permit specific |
| Abu Dhabi ADS 23/2017, discharge to the marine environment (EAD) | not set region-dependent; marine discharge only | no sodium, chloride or TDS row; desalination brine is exempt from the specification |
| Abu Dhabi DoE Trade Effluent Control Regulations 2022, discharge to sewer | TDS 2000; chloride 1000 mg/L region-dependent; sewer discharge | Tables A₁ and A₂; sodium itself is not listed, these two rows bracket it |
| sector | body | limit | note |
|---|---|---|---|
| textile and leather | ZDHC Wastewater Guidelines v₂.1 (2022), total dissolved solids | sample and report only mg/L | Table 3; salt used in wet processing or formed by neutralisation is not removed by a standard effluent plant, so TDS is reported ahead of a future limit |
| irrigation | FAO Irrigation and Drainage Paper 29 (1985), Table 1 | SAR below 3 none; 3 to 9 slight to moderate; above 9 severe (surface irrigation, sensitive crops); sprinkler below 3 meq/L none, above 3 slight to moderate SAR and meq/L | infiltration is evaluated from SAR and conductivity together; usual range of sodium in irrigation water 0 to 40 meq/L and SAR 0 to 15 |
8 · Health and environmental effects
- Toxicity
- Essential; adults need about 500 mg/day and Western diets supply 2 to 8 g/day, so drinking water at 20 mg/L (about 40 mg/day) is a minor source (WHO). Acute effects only from gross overdoses of salt; infants with gastrointestinal fluid loss are vulnerable to hypernatraemia. The link between sodium and hypertension is established for diet but no firm conclusion can be drawn for drinking water sodium, hence no guideline (WHO). EPA's 20 mg/L guidance protects people on 500 mg/day diets.
- Bioaccumulation
- Not applicable; regulated by the kidney.
- Ecotoxicity
- No US EPA aquatic criterion for sodium; salinity and chloride criteria apply. In soil the effect is physical: sodic dispersion of clay and loss of infiltration (FAO 29).
Flags
- The WHO drinking water surveys are US data from the 1960s to 1980s; the EPA survey is from about 2001.
- Ion exchange stoichiometry and regenerant doses are cited to MWH chapter 16 from memory of the text, not re-read.
- Reverse osmosis rejection and mixed bed sodium leakage are general practice, not from sources read.
- The sodium added per unit hardness (0.46 mg per mg CaCO₃) and per mg NaOH (0.58) are computed from atomic weights here.
- Abu Dhabi has no sodium limit in either medium; the sewer TDS and chloride rows are quoted as the bracket; other GCC states not read.
Gaps
- No sewage or industrial effluent sodium survey was read; the ZDHC TDS reporting requirement stands in for textile.
- No membrane rejection, resin capacity or brine volume figures are quoted.
- The WHO chapter 10 acceptability text on sodium and TDS was not read; the fact sheets stand in.
- The sodium content of reclaimed water for irrigation and the adjusted SAR calculation were not transcribed from FAO 29.
- Other GCC discharge standards were not read; none of the Abu Dhabi documents limits sodium directly.
- The chlor-alkali, on-site hypochlorite, sodium aluminate and soil exchange equations are written as the mass balances behind statements the sources make in words; no cell efficiency, salt consumption or soil exchange constant was read.
Sources
WHO, Sodium in Drinking-water, background document for development of WHO Guidelines for Drinking-water Quality, WHO/SDE/WSH/03.04/15 (2003; text of 1996)
US EPA, Drinking Water Advisory: Consumer Acceptability Advice and Health Effects Analysis on Sodium, EPA 822-R-03-006 (February 2003), executive summary and occurrence section
Directive (EU) 2020/2184 on the quality of water intended for human consumption (recast), Annex I Parts B and C
US EPA, Secondary Drinking Water Standards: Guidance for Nuisance Chemicals
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 with footnotes
40 CFR 133.102, Secondary treatment (BOD5, suspended solids, pH)
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), Schedule A Tables A1, A2 and A4
ZDHC Wastewater Guidelines Version 2.1 (November 2022), Table 3 conventional parameters and anions
Ayers, R. S. and Westcot, D. W., Water Quality for Agriculture, FAO Irrigation and Drainage Paper 29 Rev. 1 (1985), Tables 1 and 2 and Figure 1 (SAR)
US EPA, National Recommended Water Quality Criteria, Aquatic Life Criteria Table
US EPA, Alternative Disinfectants and Oxidants Guidance Manual, EPA 815-R-99-014 (April 1999), section 2.7.2.2 (sodium hypochlorite) and the dechlorination salts in the chlorine chapter
MWH, Water Treatment: Principles and Design, 3rd ed. (Wiley, 2012), chapter 16 (ion exchange: softening, demineralisation, regeneration) and chapter 22 (lime soda softening)
Metcalf and Eddy, Wastewater Engineering: Treatment and Resource Recovery, 5th ed. (McGraw-Hill, 2014), chapter 7 (alkalinity supplements for nitrification)
Standard Methods for the Examination of Water and Wastewater (online edition), 3111 B, 3120 B, 3500-Na B
The Element Book, entries for sodium (seawater abundance, salt and soda ash production, conservative ion narrative) (data/elements/Na.json, data/reference/text/Na.json)
Stumm, W. and Morgan, J. J., Aquatic Chemistry, 3rd ed. (Wiley, 1996), chapter 6 (ion pairs at high ionic strength)
Identity
- Name and symbol
- Sodium, Na
- Atomic number
- 11 protons
- Position
- group 1 · period 3 · s-block · alkali metal
- CAS number
- 7440-23-5
Atomic structure
- Atomic mass
- 22.989 u
- Electron configuration
- 1s² 2s² 2p⁶ 3s¹
[Ne] 3s¹ - Electrons per shell
- 2, 8, 1
- Valence electrons
- 1 outer shell
| isotope | mass (u) | abundance |
|---|---|---|
| 23Na | 22.989 769 28(2) | 100 % |
Physical properties
- State at room temperature
- Solid
- Melting point
- 370.95 K (97.8 °C)
- Boiling point
- 1,156 K (882.85 °C)
- Density
- 0.97 g/cm3
- Appearance
- silvery white metallic
- Thermal conductivity
- 142 W/(m·K)
- Electrical resistivity
- 47.7 nΩ·m at 20 °C
- Electrical conductivity
- 20.96 MS/m
- Crystal structure
- body-centered cubic
- Molar heat capacity
- 28.23 J/(mol·K)
Chemical properties
- Oxidation states
- +1
- Electronegativity
- 0.93 (Pauling Scale)
- Ionisation energy
- 5.139 eV
1st 495.8, 2nd 4,562, 3rd 6,910.3 kJ/mol - Electron affinity
- 0.548 eV
- Atomic radius
- empirical 166, covalent 166, van der Waals 227 pm
- Ionic radius
- Na⁺ 102 pm
- Reactivity
- An alkali metal with one 3s electron and a strongly negative reduction potential (about -2.7 V); highly reactive, more so than lithium and less than potassium, never found free in nature.
- with water
- Reacts vigorously with cold water, melting into a ball that skates over the surface, to sodium hydroxide and hydrogen, which may catch fire:
- with oxygen, air
- Tarnishes within seconds in air; heated in air or oxygen it burns with an orange flame, mainly to sodium peroxide with some oxide:
- with acids
- Reacts violently with dilute acids to the sodium salt and hydrogen.
- with halogens
- Reacts vigorously with all the halogens to the ionic sodium halides:
- Typical compounds
- NaCl sodium chloride rock salt and sea salt; source of nearly all sodium chemistry
- NaOH sodium hydroxide caustic soda, from brine electrolysis; soap and paper
- Na₂CO₃ sodium carbonate soda ash; glass making and water softening
- NaHCO₃ sodium hydrogen carbonate baking soda
- NaNO₃ sodium nitrate Chile saltpeter; fertiliser
- Na₂S₂O₃.5H₂O sodium thiosulfate pentahydrate hypo, the photographic fixer
Occurrence, production and use
- Crustal abundance
- 2.36×104 milligrams per kilogram
- Oceanic abundance
- 1.08×104 milligrams per liter
- Occurrence and sources
Sodium is present in fair abundance in the sun and stars. The D lines of sodium are among the most prominent in the solar spectrum. Sodium is the fourth most abundant element on earth, comprising about 2.6% of the earth's crust; it is the most abundant of the alkali group of metals.
It is now obtained commercially by the electrolysis of absolutely dry fused sodium chloride. This method is much cheaper than that of electrolyzing sodium hydroxide, as was used several years ago.
- dissolved in seawater about 10,800 mg/L; crustal estimate 23,600 mg/kg (Jefferson Lab figures via PubChem)
- halite, rock salt (NaCl); salt in brine; solar salt evaporite beds and domes, wells and saline lakes; US 2024 output by type: salt in brine 42 percent, rock salt 40, solar 9, vacuum pan 9; the salt content of the oceans is nearly unlimited
- trona and sodium carbonate brines Green River Basin, Wyoming, the world's largest trona deposit; Searles and Owens Lakes, California; Turkey, Botswana, Kenya, Ethiopia
- Extraction, production
- Mining of rock salt, solution mining as brine, solar evaporation of seawater and lake brines
Physical; brine is the form the chemical industry buys, 91 percent of chemical-feedstock salt in the United States in 2024.
Chlor-alkali electrolysis of brine to sodium hydroxide, chlorine and hydrogenAnode, all cell types: . Cathode, membrane and diaphragm cells: . Mercury cells make an amalgam first (CAK BREF, PDF p40). EU-27 and EFTA caustic consumption was 9,611 kt in 2012 (PDF p32).
Natural soda ash from trona; synthetic soda ash from salt and limestoneSynthetic soda ash from salt and limestone costs more energy and releases more CO2 than natural (USGS, printed pp. 164 to 165); its stoichiometry is not printed in the cached sources.
- Uses
Sodium is used in the production of titanium, sodamide, sodium cyanide, sodium peroxide, and sodium hydride. Liquid sodium has been used as a coolant for nuclear reactors. Sodium vapor is used in streetlights and produces a brilliant yellow light.
Sodium also forms many useful compounds. Some of the most common are: table salt (NaCl), soda ash (Na2CO3), baking soda (NaHCO3), caustic soda (NaOH), Chile saltpeter (NaNO3) and borax (Na2B4O7·10H2O).
Metallic sodium is vital in the manufacture of esters and in the preparation of organic compounds. The metal may be used to improve the structure of certain alloys, descale metal, and purify molten metals.
An alloy of sodium with potassium, NaK, is an important heat transfer agent.
- Chemicals: salt as feedstock for chlorine and caustic soda; caustic soda in organic synthesis, neutralisation of acids, gas scrubbing, phosphates and other inorganics; soda ash in chemicals and detergents; sodium metal for esters and organic synthesis chemical industry 39 percent of US salt sales in 2024, chlor-alkali the main consumer (USGS); EU-27 and EFTA caustic soda 2012: organics 30.1 percent, miscellaneous 15.8, other inorganics 12.5 (CAK BREF, PDF p32); US soda ash 2024: chemicals 29 percent (USGS)
- Glass: soda ash as the flux in glassmaking, a use dating from antiquity glass 45 percent of US soda ash consumption in 2024
- Food and beverage: salt as flavouring and preservative; caustic soda for fruit and vegetable peeling, ice cream, thickeners and wrappings food processing 4 percent of US salt in 2024; food industries 5.3 percent of EU-27 and EFTA caustic soda in 2012
- Pulp, paper and textiles: caustic soda for pulp, paper and cellulose; bleach for textiles; rayon (viscose) spinning EU-27 and EFTA caustic soda in 2012: pulp, paper and cellulose 13.4 percent, bleach 3.9, rayon 1.5
- Water treatment: sodium hydroxide to raise pH and precipitate heavy metals; sodium carbonate for precipitation (CWW BREF, PDF p203 and p237); caustic for flocculation and acidity control water treatment 5.0 percent of EU-27 and EFTA caustic soda in 2012; 1 percent of US soda ash in 2024
- Safety, toxicity
Sodium metal should be handled with great care. It cannot be maintained in an inert atmosphere and contact with water and other substances with which sodium reacts should be avoided.
GHS classification, signal word Danger- H260 In contact with water releases flammable gases which may ignite spontaneously Substances and mixtures which in contact with water, emit flammable gases
- H314 Causes severe skin burns and eye damage Skin corrosion/irritation
- H318 Causes serious eye damage Serious eye damage/eye irritation
Discovery and name
- Discovered by
- Humphry Davy
- Discovered
- 1807
- First isolated
- not in sources
- Named by
- not in sources
- Origin of the name
- possibly from Arabic suda, 'headache', for soda's use as an anticephalalgic
Sodium, like every reactive element, is never found free in nature. Sodium is a soft, bright, silvery metal which floats on water. Decomposition in water results in the evolution of hydrogen and the formation of the hydroxide. It may or may not ignite spontaneously on water, depending on the amount of oxide and metal exposed to the water. It normally does not ignite in air at temperatures below 115°C.
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.