Magnesium
fullMagnesium is the second cation of hardness, the harder half to soften because it needs pH above 10.5 and a second dose of lime, the metal of brucite and struvite scale and of deliberate struvite recovery, a possibly protective nutrient in drinking water that WHO declines to set a guideline for, and, as magnesium hydroxide slurry, a safer substitute for lime and caustic in pH control.
Typical wastewaters
- digester supernatant and sludge dewatering liquors Mg²⁺ with ammonium and phosphate released in digestion, precipitating struvite MgNH₄PO₄ above about pH 8
- desalination brine Mg²⁺ concentrated from 1290 mg/L in seawater; magnesium compounds are recovered from seawater and brines
- reverse osmosis concentrate Mg²⁺ concentrated with the hardness; Mg(OH)₂ scaling at high pH held off with antiscalant
- ion exchange softener regenerant Mg²⁺ and Ca²⁺ in spent NaCl brine
- textile dyeing (magnesium sulfate mordant) Mg²⁺ with sulfate from the mordant
1 · Identity
- Symbol, number
- Mg, 12
- Oxidation states in water
- +2 only, as the strongly hydrated Mg²⁺ ion. It hydrolyses only above pH 9, precipitates as Mg(OH)₂ (brucite) above about pH 10.5, forms carbonate and sulfate ion pairs in hard and saline water, and unlike calcium does not precipitate as a simple carbonate from fresh water. The element entry has the tightly bound hydration and the chlorophyll centre.
- Note
- The element entry carries the ores, the metal, seawater and brine extraction and the industrial magnesia uses. This chapter is magnesium as hardness, as scale, as struvite and as a reagent. The carbonate equilibria are in the carbon chapter; calcium carbonate softening is in the calcium chapter with the shared equations kept there; ammonium and phosphate point here for struvite.
2 · Occurrence in water
- Natural sources
- Dissolution of dolomite, magnesite, olivine and serpentine and of magnesium in sedimentary rocks, seepage and runoff from soils (WHO hardness document); seawater at about 1290 mg/L, the third most abundant ion after chloride and sodium, and evaporite brines (element entry). Magnesium is present in natural groundwater usually at lower concentrations than calcium, from negligible to about 50 mg/L and rarely above 100 mg/L (WHO).
- Anthropogenic sources
- Magnesium hydroxide and magnesium oxide dosed for pH control and as alkalinity, magnesium sulfate and chloride in industrial processes (the element entry lists the sulfate as a dye mordant), desalination brine, dolomitic lime, magnesium in digester supernatant and dewatering liquors where it meets ammonium and phosphate.
| matrix | typical range | note |
|---|---|---|
| groundwater | negligible to about 50 mg/L | rarely above 100 mg/L; calcium is usually higher, so calcium contributes more to hardness |
| drinking water, hardness (calcium plus magnesium) | 10 to 500 mg/L as CaCO3 | the range in drinking water; below 60 mg/L soft, 60 to 120 moderately hard, 120 to 180 hard, above 180 very hard |
| drinking water, magnesium intake | 2.3 (soft water areas) to 52.1 (hard water areas) mg/day from water | reported adult intakes from water; food supplies over 80 percent of the total |
| seawater | 1290 mg/Lsingle figure | oceanic abundance figure, Jefferson Lab via PubChem, quoted in the element entry; magnesium compounds are recovered from seawater and brines |
| municipal wastewater and digester liquor | not read | no survey read; magnesium in sludge liquors is what precipitates struvite with the ammonium and phosphate released in digestion |
3 · Speciation
Magnesium is Mg²⁺ across the pH range of natural water, with MgSO₄, MgHCO₃⁺ and MgCO₃ ion pairs in mineralised and sea water. It hydrolyses to MgOH⁺ only above pH 9 and precipitates as Mg(OH)₂ above about pH 10.5, a pH unit higher than calcium carbonate, which is why magnesium hardness needs the excess lime and the higher pH of the softening process. Magnesium carbonate does not precipitate from fresh water (it is far more soluble than calcite and forms hydrated salts only in brines), so magnesium hardness is removed as hydroxide, not carbonate. Where ammonium and phosphate are both present, as in anaerobic digester liquors, magnesium precipitates as struvite, MgNH₄PO₄ hexahydrate, above about pH 8 (Metcalf and Eddy chapter 15).
| condition | dominant species | note |
|---|---|---|
| natural water, pH 6 to 9 | Mg²⁺; MgSO₄ and MgHCO₃⁺ ion pairs in hard water | half the hardness in dolomitic and seawater influenced supplies |
| lime softening, pH 10.5 to 11.3 | Mg(OH)₂ (s) | the magnesium removal condition; calcium carbonate has already precipitated at 10.3 |
| digester supernatant and dewatering liquor, pH above 8 | MgNH₄PO₄.6H₂O (struvite) on pipe walls, pumps and centrifuges | CO₂ loss raises the pH and triggers it |
| seawater and reverse osmosis concentrate | Mg²⁺ with MgSO₄ ion pairs; Mg(OH)₂ if the concentrate is dosed alkaline | brucite scaling is a risk in alkaline second pass reverse osmosis |
| magnesium hydroxide slurry dosing | Mg(OH)₂ particles dissolving slowly to Mg²⁺ and OH- | cannot overshoot pH 9 to 10 because the solid stops dissolving there |
- Solubility
- Magnesium chloride, sulfate, nitrate and bicarbonate are freely soluble; magnesium hydroxide is sparingly soluble and controls magnesium above pH 10.5; magnesium carbonate is much more soluble than calcium carbonate and does not control magnesium in fresh water; struvite is sparingly soluble at alkaline pH. No solubility product is quoted because none was read this session.
- Hydrolysis
- Mg²⁺ is a very weak acid; MgOH⁺ forms only above pH 9 and Mg(OH)₂ precipitates above 10.5. Magnesium oxide hydrates to the hydroxide in water.
- Complexation
- Sulfate, bicarbonate and carbonate ion pairs; magnesium binds phosphate and organic ligands more weakly than calcium; in seawater about 10 percent of magnesium is paired with sulfate (Stumm and Morgan chapter 6, from the chapter). Constants not quoted.
- Precipitates
- Mg(OH)₂ brucite (lime softening, caustic dosing, alkaline scaling); MgNH₄PO₄.6H₂O struvite (digester liquors, deliberate recovery); MgCO₃ hydrates and dolomite only in brines and over geological time; magnesium silicate in high silica boiler and cooling water (not read this session).
4 · Role in treatment
5 · Removal and control
- Efficiency
- magnesium to about 10 mg/L as CaCO₃ (40 mg/L total hardness residual is typical, from the chapter)
- Interferences
- temperature, silica, organic matter; gelatinous Mg(OH)₂ sludge
- Efficiency
- to below 1 mg/L as CaCO₃
- Interferences
- iron and manganese foul the resin; brine disposal
- Efficiency
- above 90 percent for magnesium by nanofiltration (general, not from a source read)
- Interferences
- scaling
- Efficiency
- to the brucite solubility at the pH reached
- Efficiency
- not applicable to magnesium
- Interferences
- calcium competes to form calcium phosphate
6 · Analytics
| method | standard | detection limit | note |
|---|---|---|---|
| EDTA titration (hardness) and calculation | Standard Methods 2340 C (total hardness), 3500-Mg B (magnesium by calculation from hardness minus calcium); ISO 6059 | about 1 mg/L as CaCO₃ | titration at pH 10 with Eriochrome Black T; magnesium is total hardness minus calcium hardness (calcium titrated at pH 12 to 13 with murexide) |
| flame atomic absorption | Standard Methods 3111 B; ISO 7980 | not read | lanthanum added to suppress phosphate and aluminium interference |
| ICP-OES and ICP-MS | EPA 200.7; Standard Methods 3120 B; ISO 11885; ISO 17294-2 | not read | routine; hardness reported as 2.497 times calcium plus 4.118 times magnesium in mg/L as CaCO₃ |
| ion chromatography, cations | ISO 14911 | not read |
- Sampling pitfalls
- Acidify with nitric acid to keep magnesium and calcium in solution when the sample warms or degasses; an unacidified hard water sample loses calcium carbonate, and a struvite forming liquor loses magnesium, on the bench. Filter digester liquors immediately for dissolved magnesium. Report hardness units clearly: mg/L as CaCO₃ is not mg/L magnesium (factor 4.12), and German, French and English degrees are still met.
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), hardness | no guideline | not of health concern at levels found in drinking water; may affect acceptability; insufficient data to propose minimum or maximum mineral concentrations; assessment 1993, revised 2011; drinking water can be a contributor to calcium and magnesium intake and stabilisation of demineralised water is always necessary before distribution |
| WHO GDWQ, acceptability | above about 200 scale; below 100 corrosion mg/L as CaCO3 | hardness above about 200 mg/L may cause scale deposition and higher soap consumption; soft water below 100 mg/L may have low buffering capacity and be corrosive (hardness background document) |
| EU DWD 2020/2184 | not set | no parametric value for hardness, calcium or magnesium; Annex I Part C says water should not be aggressive or corrosive and that calcium and magnesium salts could be added to demineralised or softened water, with minimum concentrations of calcium, magnesium or TDS that could be established |
| US EPA | not regulated | no primary or secondary standard for magnesium or hardness; hardness appears among the effects of the 500 mg/L TDS secondary standard |
| body | limit | note |
|---|---|---|
| EU CWW BREF BAT-AEL (Decision 2016/902) | not set | magnesium is not among the BAT 12 parameters |
| US EPA 40 CFR 133.102, secondary treatment | not set | no federal magnesium or hardness effluent limit |
| Abu Dhabi ADS 23/2017, discharge to the marine environment (EAD) | not set region-dependent; marine discharge only | no magnesium row in Table 1 |
| Abu Dhabi DoE Trade Effluent Control Regulations 2022, discharge to sewer | not set region-dependent; sewer discharge | no magnesium row; TDS 2000 mg/L (Table A₁) is the nearest constraint |
| sector | body | limit | note |
|---|---|---|---|
| textile | ZDHC Wastewater Guidelines v₂.1 (2022) | not set | magnesium is not a ZDHC parameter |
8 · Health and environmental effects
- Toxicity
- Essential: the fourth most abundant cation in the body, needed by hundreds of enzymes; intake 250 to 350 mg/day (element entry); food supplies over 80 percent and drinking water 2 to 52 mg/day depending on hardness (WHO). Low magnesium status is implicated in hypertension, insulin resistance and cardiovascular disease, and there is evidence, debated and not proving causality, of a protective effect of water magnesium or hardness on cardiovascular mortality, with benefits where observed at about 10 mg/L magnesium and above (WHO hardness document). Magnesium with sulfate above about 250 mg/L each is laxative. Not toxic in water (element entry).
- Bioaccumulation
- Not applicable.
- Ecotoxicity
- No US EPA aquatic criterion for magnesium; hardness raises the toxicity thresholds of metals, which is why the metal criteria are hardness dependent (aluminium criterion by pH, hardness and DOC in the criteria table).
Flags
- Lime softening stoichiometry, pH end points, residual hardness and the Mg(OH)₂ sludge remark are cited to MWH chapter 22 from memory of the text, not re-read.
- The struvite conditions and the magnesium to phosphate ratio are from Metcalf and Eddy chapter 15 likewise.
- Nanofiltration rejection and the magnesium nutrient use are general practice, not from sources read.
- The conversion factors (4.12 mg CaCO₃ per mg Mg, 2.497 per mg Ca) are computed from molar masses here.
- No Abu Dhabi document limits magnesium in either medium; other GCC states not read.
Gaps
- No solubility products for brucite, magnesite or struvite are quoted; Stumm and Morgan and Metcalf and Eddy have them.
- No survey of magnesium in sewage, digester liquors or industrial effluents was read.
- No lime dose, sludge production or struvite reactor performance figures beyond the stoichiometry are quoted.
- The WHO 2009 monograph on calcium and magnesium in drinking water (public health significance) was not read; the 2011 hardness document cites it.
- Magnesium silicate scaling and magnesium in cooling water chemistry are not sourced here.
- Other GCC discharge standards were not read.
- The magnesia remineralisation and magnesium silicate stoichiometries are written here; WHO states the principle of restoring magnesium and the silicon chapter of the book carries the silica chemistry, neither prints these equations.
Sources
WHO, Hardness in Drinking-water, background document for development of WHO Guidelines for Drinking-water Quality, WHO/HSE/WSH/10.01/10/Rev/1 (2011), sections 1 to 4
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
40 CFR 141.135, Treatment technique for control of disinfection byproduct precursors (Step 1 TOC removal table, enhanced coagulation target pH)
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
US EPA, National Recommended Water Quality Criteria, Aquatic Life Criteria Table
MWH, Water Treatment: Principles and Design, 3rd ed. (Wiley, 2012), chapter 16 (ion exchange softening) and chapter 22 (lime soda softening, magnesium hydroxide precipitation, sludge)
Metcalf and Eddy, Wastewater Engineering: Treatment and Resource Recovery, 5th ed. (McGraw-Hill, 2014), chapter 15 (struvite formation and recovery from sidestreams)
Stumm, W. and Morgan, J. J., Aquatic Chemistry, 3rd ed. (Wiley, 1996), chapter 6 (ion pairs in seawater) and chapter 7 (magnesium hydroxide and carbonate solubility)
Standard Methods for the Examination of Water and Wastewater (online edition), 2340 Hardness, 3500-Mg, 3111 B, 3120 B
The Element Book, entries for magnesium (seawater abundance, brine and seawater recovery, magnesium hydroxide as a lime substitute, dietary intake) (data/elements/Mg.json, data/reference/text/Mg.json)
The Element Book, water chapter for silicon (data/water/Si.json): amorphous silica solubility ceiling, magnesium silicate scale and silica removal on magnesium hydroxide
Identity
- Name and symbol
- Magnesium, Mg
- Atomic number
- 12 protons
- Position
- group 2 · period 3 · s-block · alkaline earth metal
- CAS number
- 7439-95-4
Atomic structure
- Atomic mass
- 24.305 u
- Electron configuration
- 1s² 2s² 2p⁶ 3s²
[Ne] 3s² - Electrons per shell
- 2, 8, 2
- Valence electrons
- 2 outer shell
| isotope | mass (u) | abundance |
|---|---|---|
| 24Mg | 23.985041697(14) | 78.99 % |
| 25Mg | 24.985836976(50) | 10 % |
| 26Mg | 25.982592968(31) | 11.01 % |
Physical properties
- State at room temperature
- Solid
- Melting point
- 923 K (649.85 °C)
- Boiling point
- 1,363 K (1,089.85 °C)
- Density
- 1.74 g/cm3
- Appearance
- shiny grey solid
- Thermal conductivity
- 156 W/(m·K)
- Electrical resistivity
- 43.9 nΩ·m at 20 °C
- Electrical conductivity
- 22.78 MS/m
- Crystal structure
- hexagonal close packed
- Molar heat capacity
- 24.869 J/(mol·K)
Chemical properties
- Oxidation states
- +2
- Electronegativity
- 1.31 (Pauling Scale)
- Ionisation energy
- 7.646 eV
1st 737.7, 2nd 1,450.7, 3rd 7,732.7 kJ/mol - Electron affinity
- 0 eV
- Atomic radius
- empirical 141, covalent 141, van der Waals 173 pm
- Ionic radius
- Mg²⁺ 72 pm
- Reactivity
- An alkaline earth metal ([Ne] 3s2) that is intrinsically very reactive but shielded in air by a thin passivating film of magnesium oxide; ribbon and powder ignite easily and burn fiercely.
- with water
- Barely reacts with cold water behind its oxide film, but reacts with water vapour and steam to give the oxide or hydroxide and hydrogen; water must never be used on burning magnesium:
- with oxygen, air
- Tarnishes only slightly in air because of the passivating oxide; heated, especially when finely divided, it burns with a dazzling white flame to magnesium oxide, with some nitride from the air:
- with acids
- Reacts readily with dilute hydrochloric and sulfuric acid to the salt and hydrogen; with very dilute nitric acid hydrogen forms but is contaminated with nitrogen oxides:
- with halogens
- Reacts with the halogens to ionic dihalides such as magnesium chloride:
- Typical compounds
- MgO magnesium oxide magnesia; dead-burned magnesite for furnace bricks
- Mg(OH)₂ magnesium hydroxide milk of magnesia
- MgCl₂ magnesium chloride from brine and sea water; electrolysed to the metal
- MgSO₄.7H₂O magnesium sulfate heptahydrate Epsom salts
- MgCO₃ magnesium carbonate magnesite, the ore; dolomite with calcium
- C₂H₅MgBr ethylmagnesium bromide a Grignard reagent, from magnesium and bromoethane
Occurrence, production and use
- Crustal abundance
- 2.33×104 milligrams per kilogram
- Oceanic abundance
- 1.29×103 milligrams per liter
- Occurrence and sources
The metal is now principally obtained in the U.S. by electrolysis of fused magnesium chloride derived from brines, wells, and sea water.
- dissolved in seawater about 1,290 mg/L; crustal estimate 23,300 mg/kg (Jefferson Lab figures via PubChem)
- magnesite (MgCO3), dolomite, brucite (Mg(OH)2) China, Russia, Brazil, Turkey, Austria, Slovakia, Spain, Greece; identified world magnesite resources 13 billion tonnes
- magnesium in seawater, well and lake brines world coastlines and saline lakes; US compounds in 2024 came from seawater in California and Delaware, well brines in Michigan and lake brines in Utah; resources in the billions of tonnes
- olivine, serpentine, forsterite, evaporites widespread; serpentine including asbestos-mine tailings is an unquantified but very large potential source of magnesia
- Extraction, production
- Electrolysis of fused magnesium chloride derived from brines, wells and seawater
The principal US route while it operated; a Utah smelter on Great Salt Lake brine is estimated to have stopped in 2022. Described in words only, no equation printed.
Reduction of magnesium oxide with siliconStated by the RSC as the other commercial route; the source names reactants only, so no stoichiometry is given here.
Magnesium compounds: magnesium hydroxide from seawater and brines; caustic-calcined and dead-burned magnesia from magnesiteAbout 78 percent of US magnesium compounds in 2024 were consumed as caustic-calcined magnesia, magnesium chloride, hydroxide and sulfates, the rest as dead-burned and fused magnesia and olivine for refractories (USGS, printed pp. 112 to 113).
- Uses
Magnesium burns with a brilliant white light and is used in pyrotechnics, flares and photographic flashbulbs. Magnesium is the lightest metal that can be used to build things, although its use as a structural material is limited since it burns at relatively low temperatures. Magnesium is frequently alloyed with aluminum, which makes aluminum easier to roll, extrude and weld. Magnesium-aluminum alloys are used where strong, lightweight materials are required, such as in airplanes, missiles and rockets. Cameras, horseshoes, baseball catchers' masks and snowshoes are other items that are made from magnesium alloys.
Magnesium oxide (MgO), also known as magnesia, is the second most abundant compound in the earth's crust. Magnesium oxide is used in some antacids, in making crucibles and insulating materials, in refining some metals from their ores and in some types of cements. When combined with water (H2O), magnesia forms magnesium hydroxide (Mg(OH)2), better known as milk of magnesia, which is commonly used as an antacid and as a laxative.
Hydrated magnesium sulphate (MgSO4·7H2O), better known as Epsom salt, was discovered in 1618 by a farmer in Epsom, England, when his cows refused to drink the water from a certain mineral well. He tasted the water and found that it tasted very bitter. He also noticed that it helped heal scratches and rashes on his skin. Epsom salt is still used today to treat minor skin abrasions.
Other magnesium compounds include magnesium carbonate (MgCO3) and magnesium fluoride (MgF2). Magnesium carbonate is used to make some types of paints and inks and is added to table salt to prevent caking. A thin film of magnesium fluoride is applied to optical lenses to help reduce glare and reflections.
Uses include flashlight photography, flares, and pyrotechnics, including incendiary bombs. It is one third lighter than aluminum, and in alloys is essential for airplane and missile construction. The metal improves the mechanical, fabrication, and welding characteristics of aluminum when used as an alloying agent. Magnesium is used in producing nodular graphite in cast iron, and is used as an additive to conventional propellants.
It is also used as a reducing agent in the production of pure uranium and other metals from their salts. The hydroxide (milk of magnesia), chloride, sulfate (Epsom salts), and citrate are used in medicine. Dead-burned magnesite is employed for refractory purposes such as brick and liners in furnaces and converters.
- Transport and aluminium alloys: die castings for the automotive industry; alloying agent that improves the mechanical, fabrication and welding characteristics of aluminium, in aircraft, cars, packaging, laptops and power tools castings 65 percent of reported US consumption and aluminium-base alloys 22 percent of primary magnesium in 2024
- Iron and steel: desulfurisation of molten iron and steel, preferred over calcium carbide because carbide makes acetylene with water; nodular graphite in cast iron desulfurisation 6 percent of US primary magnesium consumption in 2024
- Refractories: dead-burned and fused magnesia bricks and liners for furnaces and converters; olivine about 22 percent of US magnesium compounds in 2024
- Chemicals and pharmaceuticals: Grignard reagents for organic synthesis; reducing agent for uranium and other metals, including beryllium from its fluoride; magnesium chloride, sulfate and hydroxide as chemical products; milk of magnesia and Epsom salts in medicine
- Textiles: magnesium sulfate as a mordant for dyes
- Environmental and water treatment: magnesium hydroxide for pH control as a substitute for lime; caustic-calcined magnesia, chloride and hydroxide in environmental uses, the leading US market for magnesium compounds; magnesium chloride for road deicing
- Agriculture: magnesium oxide in cattle feed and fertilisers
- Safety, toxicity
Because serious fires can occur, great care should be taken in handling magnesium metal, especially when finely divided. Water should not be used on burning magnesium or on magnesium fires.
GHS classification, signal word Danger- H250 Catches fire spontaneously if exposed to air Pyrophoric liquids
- H260 In contact with water releases flammable gases which may ignite spontaneously Substances and mixtures which in contact with water, emit flammable gases
- H228 Flammable solid Flammable solids
- H252 Self-heating in large quantities; may catch fire Self-heating substances and mixtures
- H261 In contact with water releases flammable gas Substances and mixtures which in contact with water, emit flammable gases
- H335 May cause respiratory irritation Specific target organ toxicity, single exposure; Respiratory tract irritation
- H315 Causes skin irritation Skin corrosion/irritation
- H319 Causes serious eye irritation Serious eye damage/eye irritation
Discovery and name
- Discovered by
- Joseph Black
- Discovered
- 1755
- First isolated
- Humphry Davy
- Named by
- not in sources
- Origin of the name
- after Magnesia, Greece
Magnesium is a light, silvery-white, and fairly tough metal. It tarnishes slightly in air, and finely divided magnesium readily ignites upon heating in air and burns with a dazzling white flame.
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.