Oxygen
fullOxygen is the master redox variable of water: dissolved oxygen decides whether a river lives, whether iron and manganese stay dissolved, whether a treatment plant nitrifies or denitrifies and whether a main corrodes; ozone, hydrogen peroxide and the hydroxyl radical are the strongest oxidants in the treatment toolbox; and oxygen transfer is the largest energy cost of wastewater treatment.
Typical wastewaters
- municipal sewage and other biodegradable discharges dissolved oxygen depleted by the oxygen demand of organic carbon and ammonia; Abu Dhabi marine discharge must carry at least 3.0 mg/L at the point of discharge
- textile dyeing and finishing and leather tanning dissolved oxygen measured on site and reported, no limit value
- urban waste water treatment plant discharges (EU) oxygen demand of the effluent: BOD₅ 25 mg/L O₂ and COD 125 mg/L O₂, or 70 to 90 and 75 percent reduction Annex I Table 1
- dairy processing effluent BOD₅, the oxygen consumed in five days, as the regulated parameter receiving stations BPT 0.475 kg BOD₅ per 1,000 kg BOD₅ input daily maximum, 0.190 30-day average
- palm oil mill effluent dissolved oxygen 2.6 to 4.1 mg/L with BOD 254 to 1,541 mg/L and COD 1,231 to 2,422 mg/L eight smallholder mills, Nigeria
- intensive aquaculture effluent carbonaceous BOD₅ consumed across fluidised sand biofilters; outlet cBOD₅ 1.7 mg/L, 66 to 82 percent removal
- dam spillway tailwater (total dissolved gas supersaturation) supersaturated dissolved oxygen and nitrogen from spill; EPA criterion 110 percent total dissolved gas, waivers to 120 percent Columbia and Snake River dams
- regulated river below a hydropower station total gas pressure 96 to 133 percent, a chronic pollutant toxic to aquatic respiration Otra River, Norway; fish deaths with gas bubble trauma
1 · Identity
- Symbol, number
- O, 8
- Oxidation states in water
- -2 in water itself and in every oxyanion and oxide (sulfate, nitrate, phosphate, carbonate, the hydroxide precipitates); 0 as dissolved O₂ and as ozone O₃ (a neutral molecule that acts as a two electron oxidant to O₂); -1 in hydrogen peroxide and the hydroxyl radical, the intermediates of advanced oxidation. Superoxide and singlet oxygen appear in mechanisms but not in plant design.
- Note
- The element entry carries the atmosphere, air separation and the biological importance of O₂. This chapter is dissolved oxygen, ozone, peroxide and the oxidation and corrosion they drive. The Fe(II) oxygenation rate law and the oxidant doses for iron and manganese are in the iron chapter; nitrification oxygen demand is in the nitrogen chapter; aerobic BOD oxidation is in the carbon chapter; bromate is in the bromine chapter.
2 · Occurrence in water
- Natural sources
- Dissolved oxygen enters from the atmosphere and from photosynthesis and is consumed by respiration and by the oxidation of reduced species; saturation falls with temperature and salinity, so warm, saline water holds least. Groundwater below the water table and stratified lake bottoms run out of oxygen and turn over to Fe(II), Mn(II), ammonia, sulfide and methane; that anoxic boundary is where most groundwater treatment problems begin (iron chapter). Ozone and peroxide occur naturally only at trace levels from photochemistry.
- Anthropogenic sources
- Oxygen depletion by sewage and other biodegradable discharges, the oldest water pollution problem and the reason for BOD limits; supersaturation below dams and in algal blooms; ozone generated on site for disinfection and oxidation; hydrogen peroxide dosed for advanced oxidation, sulfide control and dechlorination; pure oxygen and enriched air in activated sludge; oxygen scavengers (sulfite) in boiler feedwater.
| matrix | typical range | note |
|---|---|---|
| fresh water, dissolved oxygen at air saturation, sea level | 14.6 at 0 C; 9.1 at 20 C; 7.6 at 30 C mg/Ltextbook table from memory | solubility of oxygen in fresh water at one atmosphere, Metcalf and Eddy Appendix D, from the table and not re-read; lower with salinity and altitude |
| ozonated drinking water, ozone residual | below 0.1 to 1 mg/L | typical concentrations found during water treatment; the solubility of 100 percent ozone at 20 C is only 570 mg/L and feed gas is below 14 percent ozone; residual 0.2 mg/L after 2.5 to 2.7 mg/L doses in a taste and odour study |
| activated sludge aeration basin, dissolved oxygen | 1.5 to 2.0 mg/Ldesign practice, not a survey | the usual operating set point for carbon removal and nitrification (Metcalf and Eddy chapter 8, from the chapter) |
| marine discharge, Abu Dhabi | at least 3.0 mg/L region-dependent; a limit, not a survey | the minimum dissolved oxygen an effluent may carry at the point of discharge |
| seawater, oxygen as element | 857,000 mg/Lnot dissolved oxygen | the element entry's oceanic abundance figure counts the oxygen in the water molecules; dissolved O₂ in surface seawater is a few mg/L less than fresh water at the same temperature (general) |
3 · Speciation
Dissolved oxygen is a neutral gas whose equilibrium concentration follows Henry's law and whose kinetics are everything: thermodynamically it should oxidise every reduced species in water, but it reacts fast only with Fe(II) above pH 7, sulfide and sulfite, and needs bacteria for ammonia, organic carbon and methane. Ozone is a stronger oxidant, second only to the hydroxyl radical among chemicals used in water treatment, sparingly soluble, and it decomposes spontaneously by a radical chain that yields about 1.5 mol of hydroxyl radicals per mol of ozone in pure water; under acid conditions direct molecular ozone oxidation dominates, at high pH or with UV or hydrogen peroxide the hydroxyl radical route takes over, which is the basis of advanced oxidation (EPA chapter 3). Hydroxyl radicals react at 10^10 to 10^13 per mol per second, near diffusion control, live microseconds and never exceed about 10⁻12 mol/L; bicarbonate and carbonate scavenge them.
| condition | dominant species | note |
|---|---|---|
| oxic surface water and treated water | O₂ (aq) near saturation | Fe and Mn as oxides, nitrogen as nitrate, sulfur as sulfate |
| anoxic groundwater, sediment, digester | no O₂; oxygen bound in sulfate, nitrate, then carbonate as the electron acceptors are used in order | the redox ladder: oxygen, nitrate, manganese oxide, iron oxide, sulfate, carbon dioxide (Stumm and Morgan chapter 8) |
| ozonated water, pH below 7 | molecular O₃ (aq) with a measurable residual | disinfection credit needs a residual; low pH and alkalinity stabilise ozone |
| ozonated water, pH above 8, or with UV or H₂O₂ | hydroxyl radicals from ozone decomposition, little ozone residual | advanced oxidation; more bromate where bromide is present |
| peroxide dosed water | H₂O₂, a weak acid (pKa about 11.6) and a slow oxidant alone | activated by UV, ozone or Fe(II) to hydroxyl radicals; also a reductant toward chlorine and permanganate |
- Solubility
- Oxygen: about 9.1 mg/L at 20 C in fresh water at sea level, falling with temperature and salinity (Metcalf and Eddy Appendix D). Ozone: 570 mg/L at 20 C for pure ozone gas, more soluble than oxygen but chlorine is 12 times more soluble than ozone; with feed gas below 14 percent ozone the driving force limits residuals to about 1 mg/L (EPA). Hydrogen peroxide is miscible.
- Hydrolysis
- Not applicable to O₂ and O₃. Hydrogen peroxide is a very weak acid.
- Complexation
- Molecular oxygen binds to Fe(II) and Mn(II) centres in the first step of their oxidation and to haemoglobin; no aqueous complexes of consequence in treatment.
- Precipitates
- Oxygen is the oxidant that makes the precipitates: Fe(OH)₃, MnO₂, elemental sulfur from sulfide, and calcium carbonate where CO₂ is stripped by aeration. Oxygen itself does not precipitate.
4 · Role in treatment
5 · Removal and control
- Efficiency
- to µg/L
- Interferences
- air leaks
- Efficiency
- complete
- Efficiency
- not quantified
- Efficiency
- to saturation
6 · Analytics
| method | standard | detection limit | note |
|---|---|---|---|
| dissolved oxygen, iodometric (Winkler) | Standard Methods 4500-O B and C; ISO 5813 | about 0.1 mg/L | the reference method; azide modification for nitrite; fix on site |
| dissolved oxygen, membrane electrode | Standard Methods 4500-O G; ISO 5814; EPA 360.1 | about 0.1 mg/L | the ZDHC on-site method; needs flow past the membrane and temperature and salinity correction |
| dissolved oxygen, optical luminescence | ISO 17289; ASTM D₈₈₈ | about 0.1 mg/L | no membrane, no flow dependence; the usual process probe |
| ozone residual, indigo colorimetry | Standard Methods 4500-O₃ B | about 0.01 mg/L | EPA: iodometric methods suffer interference from chlorine, peroxide, manganese, nitrogen oxides and ozone decomposition products; indigo is the reference; stripping methods for gas phase |
| hydrogen peroxide | titanium sulfate or peroxidase colorimetry; permanganate titration for stock | not read | no standard method number read |
- Sampling pitfalls
- Dissolved oxygen must be measured in situ or fixed on site: a sample gains oxygen from air on the way to the laboratory if it is anoxic and loses it if it is supersaturated, and biological activity in the bottle changes it in minutes. Fill BOD bottles by displacement without bubbles. Ozone and peroxide residuals decay within minutes and are measured at the sampling point. Temperature, salinity and barometric pressure are needed to convert dissolved oxygen to percent saturation.
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 health based guideline for dissolved oxygen; it is an operational parameter (the 2022 fact sheet URL for dissolved oxygen returns no document, and the chapter 10 text was not read); ozone has no guideline value, bromate 10 µg/L is in the bromine chapter |
| EU DWD 2020/2184 | not set | no dissolved oxygen or ozone parameter in Annex I; oxidisability 5.0 mg/L O₂ is a measure of organic carbon (carbon chapter); bromate 10 µg/L |
| US EPA | not regulated | no dissolved oxygen standard and no maximum residual disinfectant level for ozone; bromate MCL 0.010 mg/L and the Stage 1 and 2 DBP rules apply to ozone plants |
| body | limit | note |
|---|---|---|
| EU CWW BREF BAT-AEL (Decision 2016/902) | not set | no dissolved oxygen parameter; the oxygen demand parameters (TOC, COD, BOD) are in the carbon chapter |
| US EPA 40 CFR 133.102, secondary treatment | not set | no federal effluent dissolved oxygen requirement; minimum dissolved oxygen in the receiving water comes from state standards built on the 1986 criteria |
| Abu Dhabi ADS 23/2017, discharge to the marine environment (EAD) | at least 3.0 mg/L region-dependent; marine discharge only | Table 1, dissolved oxygen, a minimum not a maximum |
| Abu Dhabi DoE Trade Effluent Control Regulations 2022, discharge to sewer | not set region-dependent; sewer discharge | no dissolved oxygen row for sewer discharge |
| sector | body | limit | note |
|---|---|---|---|
| textile and leather | ZDHC Wastewater Guidelines v₂.1 (2022), dissolved oxygen | sample and report only mg/L | Table 3, measured on site by ISO 5814, EPA 360.1 or SM 4500-O G; no limit value |
8 · Health and environmental effects
- Toxicity
- Dissolved oxygen is not a health parameter in drinking water. Ozone gas is toxic, above 0.2 mg/m₃ for an 8-hour day (element entry), and highly corrosive; ambient monitoring at 0.1 ppm by volume protects plant staff (EPA). Hydrogen peroxide is an irritant and oxidiser in the concentrated solutions dosed. Oxygen enriched atmospheres raise fire risk (element entry: above 25 percent many organic materials are highly flammable).
- Bioaccumulation
- Not applicable.
- Ecotoxicity
- Dissolved oxygen is the aquatic life criterion: the US EPA 1986 freshwater criteria and the saltwater criteria for Cape Cod to Cape Hatteras set minimum concentrations by life stage and averaging period (cited in the criteria table, the numbers not read this session); the Abu Dhabi marine specification requires at least 3.0 mg/L in the discharge itself. Ozone and peroxide residuals are acutely toxic to aquatic life and are destroyed before discharge.
Flags
- The oxygen solubility figures and the aeration set point are Metcalf and Eddy Appendix D and chapter 8 from memory, not re-read this session.
- The peroxone and Fenton stoichiometries are the accepted net reactions written here; the EPA manual and Metcalf and Eddy describe the processes without printing them.
- The EPA dissolved oxygen criteria document is a scanned PDF whose text could not be extracted; numeric criteria are therefore not quoted.
- The WHO position on dissolved oxygen is inferred from the absence of a fact sheet; chapter 10 of the GDWQ was not read.
- Deaeration and peroxide quenching performance are general practice, not from sources read.
- Abu Dhabi values cover two media (marine outfall DO at least 3.0 mg/L; sewer no row); other GCC states not read.
Gaps
- No dissolved oxygen survey of rivers, groundwater or effluents was read; saturation values and set points stand in.
- The numeric US dissolved oxygen criteria (1986) and the WHO chapter 10 text were not read.
- No CT values for ozone disinfection are quoted; the EPA manual has the tables.
- No oxygen transfer efficiencies, alpha factors or energy figures are quoted.
- Hydrogen peroxide dosing rates for sulfide, dechlorination and Fenton are not sourced; hydrogen sulfide chemistry is in the sulfur chapter.
- Other GCC discharge standards were not read.
Sources
Metcalf and Eddy, Wastewater Engineering: Treatment and Resource Recovery, 5th ed. (McGraw-Hill, 2014), chapter 5 (aeration), chapter 6 (advanced oxidation, Fenton), chapter 8 (activated sludge dissolved oxygen), Appendix D (oxygen solubility)
MWH, Water Treatment: Principles and Design, 3rd ed. (Wiley, 2012), chapter 22 (internal corrosion, oxygen as cathodic reactant)
Stumm, W. and Morgan, J. J., Aquatic Chemistry, 3rd ed. (Wiley, 1996), chapter 8 (redox sequence of electron acceptors)
WHO GDWQ 4th ed. with addenda (2022), chapter 12 fact sheets read this session (pH, p. 452) confirming no dissolved oxygen sheet at the 2022 URL pattern
Directive (EU) 2020/2184 on the quality of water intended for human consumption (recast), Annex I Parts B and C
US EPA, National Primary Drinking Water Regulations (table of MCLs and MCLGs)
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
Standard Methods for the Examination of Water and Wastewater (online edition), 4500-O Oxygen (Dissolved), 4500-O3 Ozone (Residual)
The Element Book, entries for oxygen (ozone formation, toxicity threshold, pure oxygen treatment, Fenton narrative, oceanic abundance) (data/elements/O.json, data/reference/text/O.json)
Council Directive 91/271/EEC concerning urban waste water treatment, Annex I Table 1 (read on the legislation.gov.uk mirror)
40 CFR 405.12, Effluent limitations (BPT), dairy products processing point source category, Subpart A receiving stations
Ohimain E. I., Seiyaboh E. I., Izah S. C., Oghenegueke E. V., Some selected physico-chemical and heavy metal properties of palm oil mill effluents (2012), Zenodo record 3441038, doi 10.5281/zenodo.3441037 (abstract)
Davidson J., Helwig N., Summerfelt S. T., Fluidized sand biofilters used to remove ammonia, biochemical oxygen demand, total coliform bacteria, and suspended solids from an intensive aquaculture effluent, Aquacultural Engineering 39(1), 6 to 15 (2008), doi 10.1016/j.aquaeng.2008.04.002 (abstract)
McGrath K. E., Dawley E. M., Geist D. R., Total Dissolved Gas Effects on Fishes of the Lower Columbia River, Pacific Northwest National Laboratory report for the US Army Corps of Engineers (2006), doi 10.2172/918864 (abstract)
Lennox R. J., Thiemer K., Vollset K. W., Pulg U. and others, Behavioural response of brown trout (Salmo trutta) to total dissolved gas supersaturation in a regulated river, Ecohydrology 15(1), e2363 (2022), doi 10.1002/eco.2363 (abstract)
Identity
- Name and symbol
- Oxygen, O
- Atomic number
- 8 protons
- Position
- group 16 · period 2 · p-block · diatomic nonmetal
- CAS number
- 7782-44-7
Atomic structure
- Atomic mass
- 15.9994 u
- Electron configuration
- 1s² 2s² 2p⁴
[He] 2s²²p⁴ - Electrons per shell
- 2, 6
- Valence electrons
- 6 outer shell
| isotope | mass (u) | abundance |
|---|---|---|
| 16O | 15.99491461957(17) | 99.757 % |
| 17O | 16.99913175650(69) | 0.038 % |
| 18O | 17.99915961286(76) | 0.205 % |
Physical properties
- State at room temperature
- Gas
- Melting point
- 54.36 K (-218.79 °C)
- Boiling point
- 90.2 K (-182.95 °C)
- Density
- 0.0014 g/cm3 (gas at STP, so 1.429 g/L)
- Appearance
- gas: colorlessliquid and solid: pale blue
- Thermal conductivity
- 26.58×10-3 W/(m·K)
- Electrical resistivity
- not in sources
- Electrical conductivity
- not in sources
- Crystal structure
- cubic
- Molar heat capacity
- not in sources
Chemical properties
- Oxidation states
- -2
- Electronegativity
- 3.44 (Pauling Scale)
- Ionisation energy
- 13.618 eV
1st 1,313.9, 2nd 3,388.3, 3rd 5,300.5 kJ/mol - Electron affinity
- 1.461 eV
- Atomic radius
- empirical 66, covalent 66, van der Waals 152 pm
- Ionic radius
- O²⁻ 140 pm
- Reactivity
- A highly electronegative nonmetal and potent oxidiser; O2 combines with nearly every element to give oxides, slowly at room temperature (rusting, autoxidation of organics) and rapidly in combustion.
- with water
- Does not react; it dissolves sparingly, more in cold water, which is what sustains aquatic life.
- with oxygen, air
- O2 does not react with itself, but an electric discharge or ultraviolet light converts it to the reactive allotrope ozone:
- with acids
- Does not react with acids.
- with halogens
- Does not combine with fluorine under ambient conditions; oxygen difluoride and dioxygen difluoride form only in an electric discharge at low temperature and decompose on warming, and there is no direct reaction with chlorine:
- Typical compounds
- H₂O water the most familiar oxide; nine tenths of it by mass is oxygen
- SiO₂ silicon dioxide quartz and sand; the crust is largely silicates
- Fe₂O₃ iron(III) oxide hematite and rust
- Al₂O₃ aluminium oxide corundum, bauxite, ruby and sapphire
- CO₂ carbon dioxide trace gas of the air, product of respiration and burning
- H₂O₂ hydrogen peroxide peroxide, oxygen in the minus one state
Occurrence, production and use
- Crustal abundance
- 4.61×105 milligrams per kilogram
- Oceanic abundance
- 8.57×105 milligrams per liter
- Occurrence and sources
Oxygen is the third most abundant element found in the sun, and it plays a part in the carbon-nitrogen cycle, the process once thought to give the sun and stars their energy. Oxygen under excited conditions is responsible for the bright red and yellow-green colors of the Aurora Borealis.
A gaseous element, oxygen forms 21% of the atmosphere by volume and is obtained by liquefaction and fractional distillation. The atmosphere of Mars contains about 0.15% oxygen. The element and its compounds make up 49.2%, by weight, of the earth's crust. About two thirds of the human body and nine tenths of water is oxygen.
In the laboratory it can be prepared by the electrolysis of water or by heating potassium chlorate with manganese dioxide as a catalyst.
- dissolved in seawater about 857,000 mg/L; crustal estimate 461,000 mg/kg (Jefferson Lab figures via PubChem)
- O2 in air 21 percent of the atmosphere by volume; the industrial source
- water and silicate, oxide and carbonate rocks 49.2 percent of the crust by mass and nine tenths of water by weight
- dissolved oxygen surface waters, sustaining aerobic life
- Extraction, production
- Cryogenic distillation of liquid air, pressure-swing adsorption over zeolite, or ceramic membrane separation
Physical separation, no chemical reaction; about 99 percent of supply. Zeolite beds adsorb nitrogen and let oxygen pass; ceramic membranes give higher purity.
Electrolysis of waterAbout 1 percent of supply; described in words only, no equation printed in the sources.
- Uses
Oxygen is a highly reactive element and is capable of combining with most other elements. It is required by most living organisms and for most forms of combustion. Impurities in molten pig iron are burned away with streams of high pressure oxygen to produce steel. Oxygen can also be combined with acetylene (C2H2) to produce an extremely hot flame used for welding. Liquid oxygen, when combined with liquid hydrogen, makes an excellent rocket fuel. Ozone (O3) forms a thin, protective layer around the earth that shields the surface from the sun's ultraviolet radiation. Oxygen is also a component of hundreds of thousands of organic compounds.
Plants and animals rely on oxygen for respiration. Hospitals frequently prescribe oxygen for patients with respiratory ailments.
- Iron and steel: oxygen enrichment of blast furnaces and steelmaking; the greatest commercial use of the gas
- Chemicals: ammonia oxidation for nitric acid, p124); ethylene oxide by direct oxidation over silver at 15 to 25 bar, C2H4 + 1/2 , releasing 105 kJ/mol, with the side reaction releasing 1,323 kJ/mol (LVOC BREF, PDF p400); oxychlorination of ethylene, C2H4 + 1/2 , releasing 239 kJ/mol, which recycles the HCl from VCM cracking (PDF p528); sulfur dioxide conversion, SO2 + 1/2 , delta H0 = -99 kJ/mol, the heart of the sulfuric acid contact process (AAF BREF, PDF p179); formaldehyde, CH3OH + 1/2 , delta H = -159 kJ/mol over a metal oxide catalyst (LVOC BREF, PDF p375); synthesis gas for ammonia and methanol; hydrogen peroxide
- Water and waste water treatment: pure oxygen or oxygen-enriched air in activated sludge aeration (CWW BREF, PDF p316 and p321); ozone, with or without UV, hydrogen peroxide and Fenton's reagent as chemical oxidants (PDF p247); a growing use in the treatment of sewage and industrial effluent
- Metal fabrication: oxy-acetylene welding and cutting
- Medicine: oxygen therapy for respiratory ailments
- Safety, toxicity
- not in sources
Discovery and name
- Discovered by
- Michael SendivogiusCarl Wilhelm Scheele
- Discovered
- 1604, 1771
- First isolated
- not in sources
- Named by
- Antoine Lavoisier
- Origin of the name
- from the Greek ὀξύς (acid, literally 'sharp', from the taste of acids) and -γενής (producer)
The gas is colorless, odorless, and tasteless. The liquid and solid forms are a pale blue color and are strongly paramagnetic.
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.