Selenium

    group 16 · period 4 · p-block · polyatomic nonmetal

    fullSelenium is regulated in drinking water by WHO (40 µg/L provisional), the EU (20 µg/L) and the US (0.05 mg/L), is the pollutant that drove biological treatment of power plant FGD wastewater, and has a treatment chemistry that turns entirely on whether it is selenite, which iron removes, or selenate, which almost nothing removes except reduction and membranes.

    Typical wastewaters

    • coal power plant flue gas desulfurisation wastewater selenate SeO₄²⁻ with selenite in a high nitrate scrubber water; reduced to elemental Se(0) in anoxic bioreactors BAT limits 70 µg/L daily and 29 µg/L monthly; nitrate is consumed before selenium
    • coal gasification wastewater and combustion residual leachate total selenium; gasification wastewater limited to 453 µg/L daily and 227 µg/L monthly a limit, not a measured range
    • petroleum refinery effluent dissolved selenium; species not given by the source US EPA source list for the selenium MCL
    • mine drainage (coal, phosphate and sulfide mining) dissolved selenium; selenate is favoured where the water is oxic and alkaline, selenite at near neutral and acid pH the US EPA lists mines as a source; no mine water concentration was read
    • agricultural drainage from seleniferous soils selenate in high sulfate drainage water, with organic selenium (selenomethionine, dimethylselenide) the case behind the nanofiltration study cited by WHO
    • copper refinery anode slime processing selenium in the anode slime processing effluent; species not given by the source
    • textile wet processing total selenium, a sample and report only ZDHC parameter; sludge reporting limit 5 mg/kg dry weight
    In the ledger's plant and process records, discharged by: Base metal ores (Cu, Ni, Pb, Sn, Zn) (Mining) · Coal, lignite and peat (Mining) · Industrial minerals (potash, salt, kaolin, magnesite and others) (Mining) · Precious metal ores (Au, Ag, Pt): gold and silver extraction (Mining) · Uranium ore (Mining)

    1 · Identity

    Symbol, number
    Se, 34
    Oxidation states in water
    +6 selenate, SeO₄²⁻, the soluble, mobile form of alkaline oxidising water; +4 selenite, H₂SeO₃, HSeO₃⁻ and SeO₃²⁻, the form that adsorbs to iron and aluminium oxides; 0 elemental selenium, insoluble, the product of chemical and biological reduction; -2 selenides and hydrogen selenide in strongly reducing sediments; organic selenium (selenomethionine, dimethylselenide) in biota and drainage water.
    Note
    The element entry covers anode slimes, glass and photovoltaics; this chapter is selenite against selenate.

    2 · Occurrence in water

    Natural sources
    Crustal selenium 50 to 90 µg/kg, higher in some volcanic, sedimentary and carbonate rocks; soils 5 to 1,200,000 µg/kg. Selenites and selenates are soluble, so selenium leaches from well aerated alkaline soils; elemental selenium and selenides are insoluble, so it is retained in wet, poorly aerated soils. Dissolved selenium rises at both high and low pH (WHO background document).
    Anthropogenic sources
    Flue gas desulfurisation wastewater, gasification wastewater and combustion residual leachate at coal power plants, regulated in 40 CFR 423.13; discharges from petroleum refineries and mines (EPA NPDWR); copper refinery anode slime processing (element entry); agricultural drainage from seleniferous soils, the case behind the nanofiltration study cited by WHO; coal, phosphate and sulfide mining (element entry, MWEI BREF); selenium is a textile sludge and report only wastewater parameter for ZDHC.
    matrixtypical rangenote
    groundwater and surface water0.06 to about 400 µg/L
    region-dependent; 1930s to 1960s US compilations
    some groundwater approaches 6,000 µg/L
    tap water, public supplies worldwidemuch less than 10, may exceed 50 µg/Lregion-dependent50 to 160 µg/L in a high selenium soil area of China
    well water in a poisoning case9 mg/Lsingle casea family exposed for about 3 months lost hair and nails and recovered on changing supply
    seawater0.0002 mg/L
    single abundance figure, no range
    estimated oceanic abundance, Jefferson Lab via PubChem
    industrial wastewater, coal gasification (regulated level)453 daily maximum; 227 monthly µg/La limit, not a measured rangethe 40 CFR 423.13(j) BAT limits for gasification wastewater, which show the order of magnitude of raw selenium in that stream; raw concentrations were not read

    3 · Speciation

    The common forms in water are selenite, Se(IV), and selenate, Se(VI); conversion of selenite to selenate is slow, both exist together, and neither is oxidised or reduced easily under treatment conditions (WHO citing Sorg and Logsdon 1978). Selenate is more soluble and much harder to remove by coagulation than selenite, so oxidising selenite would be a mistake. Acidic and reducing conditions reduce selenite to elemental selenium; alkaline and oxidising conditions favour selenate. Chlorine oxidises selenite to selenate only under harsh conditions and selenium is unlikely to react with ozone, chlorine dioxide or chloramines.

    conditiondominant speciesnote
    oxic, alkaline water, pH 7 to 9SeO₄²⁻selenate; mobile, poorly sorbed; passes coagulation, alumina at natural pH and activated carbon
    oxic water, near neutral and acid pHHSeO₃⁻ and SeO₃²⁻, sorbed on iron and aluminium oxidesselenite; removed by ferric coagulation below pH 7 and by iron oxide media
    reducing sediment, anoxic bioreactor, zero valent ironSe (s), elemental, as nanospheres on bacterial cells or in iron corrosion productsthe sink that biological FGD treatment and iron reduction exploit
    strongly sulfidic, reducingselenides, HSe⁻poorly absorbed, insoluble metal selenides; not covered by the water sources beyond the statement of insolubility
    biota, drainage waterselenomethionine, selenocysteine, dimethylselenideteratogenic to birds and fish; the reason the US criterion is a fish tissue value
    Solubility
    Selenite and selenate salts of the common cations are soluble; elemental selenium and metal selenides are insoluble (WHO). No solubility products are printed in the sources read.
    Hydrolysis
    Selenous acid and selenic acid dissociate stepwise with pH; the sources read do not print the constants, so none are quoted. In the pH 6 to 9 range selenite is HSeO₃⁻ or SeO₃²⁻ and selenate is the divalent anion.
    Complexation
    Selenite sorbs on iron and aluminium oxide surfaces and on iron oxide coated sand (capacity about 1 mg/g); selenate sorbs weakly; nitrate interferes with selenium adsorption on soil (WHO). No constants quoted.
    Precipitates
    Elemental selenium from reduction; selenite carried on ferric hydroxide floc; metal selenides under sulfidic conditions.
    HSeOX3XSeOX3X2+HX+\ce{HSeO3^- <=> SeO3^2- + H+}
    second dissociation of selenous acid, in the natural pH range; constant not printed in the sources read
    SeOX4X2+2HX++2eXSeOX3X2+HX2O\ce{SeO4^2- + 2 H+ + 2 e- -> SeO3^2- + H2O}
    first step of biological or chemical reduction; slow abiotically; electron balance written here, the EPA describes the reduction in words
    SeOX3X2+6HX++4eXSe(s)+3HX2O\ce{SeO3^2- + 6 H+ + 4 e- -> Se (s) + 3 H2O}
    anoxic fixed film bioreactor at negative ORP; ferrous hydroxide at pH 8.8; zero valent iron; the elemental selenium forms nanospheres on the cell walls (EPA) or reports with iron oxyhydroxide corrosion products (WHO citing Zhang 2005)
    FeX2(SOX4)X3+6HX2O2Fe(OH)X3(s)+3HX2SOX4\ce{Fe2(SO4)3 + 6 H2O -> 2 Fe(OH)3 (s) + 3 H2SO4}
    ferric sulfate clarification below pH 7, the most effective coagulation condition for selenite in the tests cited by WHO; selenite adsorbs on the fresh hydroxide, selenate does not
    SeOX3X2+2Fe(s)+6HX+Se(s)+2FeX2++3HX2O\ce{SeO3^2- + 2 Fe (s) + 6 H+ -> Se (s) + 2 Fe^2+ + 3 H2O}
    zero valent iron: two iron atoms give the four electrons that take selenite to elemental selenium, and the selenium reports with the iron oxyhydroxide corrosion products (WHO citing Zhang 2005); arsenate and molybdate compete for the same iron surfaces; the electron balance is written here, WHO describes the reduction in words
    SeOX3X2+4Fe(OH)X2(s)+3HX2OSe(s)+4Fe(OH)X3(s)+2OHX\ce{SeO3^2- + 4 Fe(OH)2 (s) + 3 H2O -> Se (s) + 4 Fe(OH)3 (s) + 2 OH-}
    ferrous hydroxide at pH 8.8 (WHO citing Zingaro 1997): four Fe(II) are oxidised to Fe(III) for one selenite reduced to red elemental selenium; 4 µg/L to below 1 µg/L in the test quoted; the electron balance is written here, WHO names the reagent and the pH only

    4 · Role in treatment

    as a problem
    selenate is not removed by conventional treatment
    SeO₄²⁻ sorbs weakly and does not coagulate
    WHO: lime, ferric sulfate, alum and activated carbon are moderately effective for selenite and ineffective for selenate; powdered carbon at 100 mg/L removed under 4 percent of either
    no pre-oxidation lever
    chlorine, ozone, chlorine dioxide and chloramine do not usefully change the oxidation state under treatment conditions, and oxidation would make removal worse
    the opposite of arsenic, where oxidation to As(V) is the first step
    nitrate competition
    nitrate interferes with selenium adsorption on soil and is reduced ahead of selenate in anoxic bioreactors
    95 percent soil adsorption in the absence of nitrate (WHO); FGD bioreactors are sized for high or low nitrate (EPA TDD cost curves)
    bioaccumulation, not water toxicity, sets the aquatic limit
    selenium enters food webs from sediment and algae and reaches teratogenic levels in bird and fish eggs
    the US 2016 criterion is 15.1 mg/kg dry weight in egg or ovary with water column values of 1.5 µg/L (lakes) and 3.1 µg/L (rivers) as translations
    power plant compliance dates
    the FGD wastewater limits carry technology bases and dates that changed in 2015, 2020 and 2024
    the 2024 rule moves most FGD wastewater to no discharge by 31 December 2034 at the latest

    5 · Removal and control

    ferric coagulation and clarification (selenite only)
    selenite adsorbed on fresh ferric hydroxide floc; lime and alum do the same less well
    FeX2(SOX4)X3+6HX2O2Fe(OH)X3(s)+3HX2SOX4\ce{Fe2(SO4)3 + 6 H2O -> 2 Fe(OH)3 (s) + 3 H2SO4}
    greatest removal with ferric sulfate at pH below 7 (WHO citing 1986 tests); ineffective for selenate
    Efficiency
    moderate for selenite; ineffective for selenate; no percentage printed
    Interferences
    selenate; phosphate and silicate competing for the iron surface
    adsorption on iron oxide coated sand, aluminium oxide coated sand and activated alumina
    surface complexation of selenite, more slowly selenate, on metal oxide surfaces
    iron coated sand: complete Se(IV) removal from 10 mg/L with 100 g/L sand in 10 minutes, Se(VI) in about 90 minutes, capacity about 1 mg/g; alumina coated sand 0.5 mg/g Se(IV) and 0.25 mg/g Se(VI); activated alumina 98 percent at pH 5 (WHO)
    Efficiency
    98 percent on activated alumina at pH 5; treatment of 4 µg/L natural water with iron(II) hydroxide at pH 8.8 gave below 1 µg/L
    Interferences
    selenate at natural pH; nitrate; competing anions
    biological reduction in anoxic fixed film bioreactors (FGD wastewater)
    after chemical precipitation, bacteria on an activated carbon or porous bed reduce selenate and selenite to elemental selenium, which forms nanospheres adhering to the cell walls; arsenic, cadmium, nickel and mercury are reduced to sulfides in the same bed
    SeOX3X2+6HX++4eXSe(s)+3HX2O\ce{SeO3^2- + 6 H+ + 4 e- -> Se (s) + 3 H2O}
    plug flow bed with an aerobic top zone (nitrification, organic carbon oxidation) and an anoxic lower zone at negative ORP (denitrification, then selenium reduction); high residence time systems 10 to 16 hours, low residence time systems 1 to 4 hours, fluidised bed reactors on granular activated carbon; the technology basis of the 2015 and 2020 US limits
    Efficiency
    to the 2020 BAT limits of 70 µg/L daily and 29 µg/L monthly (chemical precipitation plus low residence time reduction); the voluntary incentives limit of 10 µg/L needs more
    Interferences
    nitrate consumed first; cold water; oxidant carry-over; the sludge and spent carbon carry the selenium
    reduction with ferrous hydroxide or zero valent iron
    Fe(II) reduces selenite and selenate to elemental selenium; zero valent iron corrodes to iron oxyhydroxides that carry it
    SeOX4X2+2HX++2eXSeOX3X2+HX2O\ce{SeO4^2- + 2 H+ + 2 e- -> SeO3^2- + H2O}
    iron(II) hydroxide at pH 8.8 (WHO citing Zingaro 1997); arsenate and molybdate affect selenate removal by zero valent iron (Zhang 2005)
    Efficiency
    4 µg/L to below 1 µg/L in the ferrous hydroxide test
    Interferences
    arsenate, molybdate, oxygen
    anion exchange
    strong base resin exchanges selenate and selenite
    synthetic resins remove Se(VI) from groundwater; laboratory work suggests both forms are removable (WHO)
    Efficiency
    not quantified in the source
    Interferences
    sulfate and nitrate compete, as for arsenate
    reverse osmosis and nanofiltration
    rejection of the divalent anions
    cellulose acetate and triacetate membranes effective for both selenite and selenate; nanofiltration of highly contaminated agricultural drainage in laboratory studies
    Efficiency
    over 95 percent (RO); 95 percent (NF)
    Interferences
    scaling in high sulfate drainage water; concentrate disposal
    blending and source selection
    dilution of a seleniferous source
    WHO names alternative sources and blending low with high selenium sources as options before removal
    Efficiency
    by ratio

    6 · Analytics

    methodstandarddetection limitnote
    hydride generation AASStandard Methods 3114 B and Cabout 0.5 µg/L with 100 mL samples (WHO)the most convenient method in the WHO review; hydride generation needs Se(IV), so total selenium requires pre-reduction of selenate
    ICP-MSEPA 200.8 (mass 82); ISO 17294-2; Standard Methods 3125similar to hydride AAS per WHO; EPA 200.8 instrument detection limit 5 µg/L scanning and 1.3 µg/L selected ion monitoring at mass 82, the poorest in the tableargon dimer at mass 80 and krypton at mass 82 interfere (EPA 200.8 notes the isobaric krypton overlap); collision cell instruments do far better than the 1994 figures
    speciation, Se(IV) and Se(VI)no numbered standard readnot readneeded to choose between coagulation and reduction; hydride generation with and without pre-reduction is the classic split
    Sampling pitfalls
    Acidify for total selenium; filter 0.45 µm in the field for dissolved selenium. Interconversion of selenite and selenate is slow, so speciation samples are less fragile than arsenic, but hydride methods respond only to Se(IV) and undercount selenate unless the sample is pre-reduced. Hydride generation interferences from transition metals are real in FGD and mine water.

    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.

    drinking water
    bodylimitnote
    WHO GDWQ 4th ed. with addenda (2022)40 µg/Lprovisional because of uncertainties in the scientific database; 20 percent of the upper tolerable intake of 400 µg/day allocated to water; most drinking water is far below 10 µg/L; for most Member States a guideline is unnecessary; assessment 2010
    EU DWD 2020/218420 µg/LAnnex I Part B; 30 µg/L applies in regions where geological conditions could lead to high selenium in groundwater; uncertainty of measurement 40 percent of the parametric value (Annex III)
    US EPA NPDWR0.05 mg/LMCL and MCLG both 0.05 mg/L; health effects listed as hair or fingernail loss, numbness, circulatory problems; sources listed as refineries, natural deposits, mines
    US EPA health advisory (2018 table)0.05 mg/Llifetime health advisory equal to the MCL; RfD 0.005 mg/kg per day, DWEL 0.2 mg/L
    discharge
    bodylimitnote
    EU CWW BREF BAT-AEL (Decision 2016/902)not set selenium is not a BAT 12 parameter
    US EPA 40 CFR 423.13(g)(1), steam electric FGD wastewater (2020 BAT)70 daily maximum; 29 30-day average µg/L total selenium
    time-sensitive: the 2024 rule requires no discharge of FGD wastewater by a date no later than 31 December 2034 for most plants
    with arsenic 18 and 8 µg/L, mercury 103 and 34 ng/L, nitrate plus nitrite 4 and 3 mg/L as N; technology basis chemical precipitation plus low residence time biological reduction
    US EPA 40 CFR 423.13(g)(3), FGD wastewater, voluntary incentives programme10 µg/L total selenium, daily maximumtime-sensitivewith arsenic 5 µg/L, mercury 23 and 10 ng/L, nitrate plus nitrite 2.0 and 1.2 mg/L, bromide 0.2 mg/L, TDS 306 and 149 mg/L; for discharges generated after 31 December 2023
    US EPA 40 CFR 423.13(j)(1), gasification wastewater (BAT)453 daily maximum; 227 30-day average µg/L total seleniumwith arsenic 4 µg/L, mercury 1.8 and 1.3 ng/L, TDS 38 and 22 mg/L
    Abu Dhabi ADS 23/2017, discharge to the marine environment (EAD)0.02 mg/L
    region-dependent; marine discharge only
    Table 1 maximum allowable concentration at the point of discharge
    Abu Dhabi DoE Trade Effluent Control Regulations 2022, discharge to sewer10 mg/L
    region-dependent; sewer discharge, not receiving water
    Table A₄ maximum allowable concentration for trade effluent to the sewer network; 500 times the marine value
    industry thresholds
    sectorbodylimitnote
    textileZDHC Wastewater Guidelines v₂.1 (2022), Table 2not set selenium is a sample and report only wastewater parameter for textiles (methods EPA 200.8, 6010C, 6020A, HJ 700); sludge total selenium reporting limit 5 mg/kg dry weight (Table 4A)

    8 · Health and environmental effects

    Toxicity
    Essential: about 25 selenoproteins; recommended intakes 26 to 35 µg/day for adults, upper tolerable limit 400 µg/day. Deficiency is Keshan disease and Kaschin-Beck disease; excess is selenosis (brittle hair and nails, skin lesions, nerve changes) at dietary intakes above about 900 µg/day, with symptoms in Chinese villages at about 5 mg/day. Selenite, selenate, selenocysteine and selenomethionine kill laboratory animals at single doses of 1.5 to 6 mg/kg. Not classifiable as a carcinogen; several selenium compounds are anticarcinogenic in animals (WHO).
    Bioaccumulation
    Selenium is taken up into proteins as selenocysteine and selenomethionine and moves through food webs; selenate, selenite and the seleno amino acids are teratogenic in birds and fish, the basis of the aquatic bird deformities in central California cited by WHO and of the fish tissue form of the US criterion.
    Ecotoxicity
    US EPA 2016 freshwater criterion: egg or ovary 15.1 mg/kg dry weight, whole body 8.5, muscle 11.3, water column 1.5 µg/L in lentic and 3.1 µg/L in lotic systems (30 day averages), with an intermittent exposure element; fish tissue governs except when selenium inputs are increasing. Saltwater criteria 290 µg/L acute and 71 µg/L chronic (1999).

    Flags

    • The WHO natural water ranges are US compilations from 1937 to 1968 and vary by region; no recent survey was read.
    • The seawater figure (0.2 µg/L) is a single abundance figure from Jefferson Lab via PubChem.
    • Dissociation constants of selenous and selenic acid are not printed in the sources read; none are quoted.
    • The selenate and selenite reduction half reactions are electron balances written here; the EPA and WHO describe the reductions in words.
    • The US FGD limits carry compliance dates and were changed again by the 2024 supplemental rule, which was not read in full.
    • Abu Dhabi values cover two media (marine 0.02 mg/L, sewer 10 mg/L); other GCC states not read.
    • EPA 200.8 detection limits for selenium are 1994 quadrupole figures without a collision cell.
    • The WHO selenium document names a branded activated alumina in the 98 percent figure; the brand is omitted here.

    Gaps

    • No measured selenium concentrations in FGD wastewater, refinery effluent, mine drainage or municipal wastewater were read; only the regulated levels.
    • No removal percentages for full scale biological FGD treatment beyond the limits it was designed to meet.
    • Selenium speciation methods (HPLC-ICP-MS, hydride with and without pre-reduction) were not read as numbered standards.
    • No solubility products, adsorption constants or acid dissociation constants are printed in the sources read.
    • The 2024 steam electric supplemental rule and other GCC discharge standards were not read.
    • Selenium in the EU EQS directive and in the AMR or pharma sector lists was not checked.
    • The zero valent iron and ferrous hydroxide reductions are written as electron balances from the reagents and pH values WHO gives; neither source prints a stoichiometry, and no carbon source stoichiometry was read for the biological selenate reduction step.

    Sources

    WHO Guidelines for Drinking-water Quality, 4th ed. incorporating the first and second addenda (2022), chapter 12 chemical fact sheet, Selenium (pp. 459 to 461)
    WHO, Selenium in Drinking-water, background document for development of WHO Guidelines for Drinking-water Quality, WHO/HSE/WSH/10.01/14 (2011), sections 1, 2, 5 and 6
    Directive (EU) 2020/2184 on the quality of water intended for human consumption (recast), Annex I Parts B and C and Annex III Table 1
    US EPA, National Primary Drinking Water Regulations (table of MCLs)
    US EPA, 2018 Edition of the Drinking Water Standards and Health Advisories Tables, EPA 822-F-18-001 (March 2018)
    40 CFR 423.13, Effluent limitations guidelines representing BAT, steam electric power generating point source category (cooling tower blowdown, FGD wastewater, gasification wastewater)
    US EPA, Supplemental Technical Development Document for the 2020 Steam Electric Reconsideration Rule, EPA 821-R-20-004 (August 2020), section 4 (biological treatment of FGD wastewater)
    US EPA, Aquatic Life Ambient Water Quality Criterion for Selenium in Freshwater 2016, fact sheet (June 2016)
    US EPA, National Recommended Water Quality Criteria, Aquatic Life Criteria Table and Appendix B (hardness equations)
    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 4 and BAT 12 Table 3 with footnotes 24 to 29
    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 Table A4
    ZDHC Wastewater Guidelines Version 2.1 (November 2022), Table 1M (organotins), Table 2 (heavy metals) and Tables 4A and 4B (sludge)
    US EPA Method 200.8, Revision 5.4 (1994), Determination of trace elements in waters and wastes by ICP-MS, Table 1 instrument detection limits
    Standard Methods (online edition), 3114 Arsenic and Selenium by Hydride Generation/Atomic Absorption Spectrometry
    Standard Methods (online edition), 3125 Metals by Inductively Coupled Plasma-Mass Spectrometry
    ISO 17294-2:2023, Water quality. Application of ICP-MS. Part 2: Determination of selected elements including uranium isotopes
    The Element Book, own entry for selenium (data/elements/Se.json and data/reference/text/Se.json)
    PubChem element summary for selenium; estimated oceanic abundance 2 x 10^-4 mg/L from Jefferson Lab

    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.