Tin

    group 14 · period 5 · p-block · post-transition metal

    fullInorganic tin has no drinking water guideline (WHO 2003: well below health concern) and is almost insoluble, but tin is in this chapter for its organic compounds: tributyltin is an EU priority hazardous substance with the lowest quality standard in the directive (0.0002 µg/L), banned from ship antifouling since 2008, and organotins are a ZDHC textile wastewater parameter; on the inorganic side tin plating and tinplate lines are ledger industries, tin(II) chloride is the reductant of mercury analysis and Abu Dhabi limits tin to sewer at 10 mg/L.

    Typical wastewaters

    • electroplating and metal finishing (tin plating and tinplate lines) Sn²⁺ and its chloride complexes from acid baths, stannate Sn(OH)₆²⁻ from alkaline baths; hydrous tin oxide precipitates on neutralisation the US metal finishing category covers tin plating but sets no tin limit
    • textile and leather finishing and coating (organotin biocides and stabilisers) mono, di and tributyl, methyl, octyl and phenyl tins, sorbed to solids; 0.01 µg/L reporting limit per compound MRSL substances, so detection above the reporting limit is a failure
    • harbours, ship hull maintenance and dredge spoil (legacy antifouling paint) tributyltin cation (C₄H₉)₃Sn⁺ with its chloride and hydroxide, sorbed to sediment and remobilised by dredging; dibutyl and monobutyl tin as degradation products application banned since 17 September 2008 under the AFS Convention

    1 · Identity

    Symbol, number
    Sn, 50
    Oxidation states in water
    +4 as hydrous SnO₂ and stannic hydroxide, insoluble at any natural pH, and as stannate Sn(OH)₆²⁻ only in strong alkali; +2 as Sn²⁺, a reductant that hydrolyses readily and oxidises to Sn(IV) in air, used as tin(II) chloride; and the organotins, above all the tributyltin cation (C₄H₉)₃Sn⁺, a lipophilic biocide that behaves like an organic pollutant, not like a metal.
    Note
    The element entry gives the allotropes, cassiterite, tinplate and the halides, and its reactivity text notes tin resists distilled water, sea water and soft tap water under its oxide film. The water chapter splits at the carbon tin bond: inorganic tin is a non problem, organotin a priority hazard.

    2 · Occurrence in water

    Natural sources
    Weathering of cassiterite is slow and the product is insoluble SnO₂; natural water carries inorganic tin at trace levels. WHO: levels in drinking water above 1 to 2 µg/L are exceptional.
    Anthropogenic sources
    Tinplate for cans (food is the main exposure); tin solder in domestic plumbing, increasing, and tin proposed as a corrosion inhibitor (WHO); tin plating and tinplate lines (metal finishing); organotin antifouling paints on ships, banned from application since the AFS Convention entered into force on 17 September 2008 but persistent in harbour sediment; organotin PVC stabilisers and organotin biocides in textiles and leather (ZDHC Table 1M); the ledger's chemical and textile chapters carry the plant figures.
    matrixtypical rangenote
    drinking waterbelow 1 to 2 µg/Llevels greater than 1 to 2 µg/L are exceptional (WHO fact sheet)

    3 · Speciation

    Inorganic tin(IV) is hydrolysed completely to hydrous tin dioxide at every natural pH, so it is particulate and immobile, which is why drinking water carries so little and why tin resists water under its oxide film. Tin(II) is a reductant: in air it oxidises to Sn(IV) within hours and hydrolyses on the way, so tin(II) chloride solutions are kept acid and fresh. The organotins are different in kind: the tributyltin cation is stable to hydrolysis, lipophilic, adsorbed to suspended solids and sediment, and degrades slowly by stepwise dealkylation to dibutyl, monobutyl and inorganic tin; it is toxic to molluscs at nanograms per litre, hence an EQS three orders of magnitude below any metal's.

    conditiondominant speciesnote
    any natural water, oxicSnO₂ (s) and hydrous tin oxide colloids; trace Sn(OH)₄ (aq)inorganic tin is a particle
    strong alkaliSn(OH)₆²⁻ (stannate)alkaline tin plating baths and hot alkali (element reactivity text: hot alkali gives stannates)
    acid, reducing, fresh tin(II) chlorideSn²⁺, SnCl⁺, SnCl₃⁻oxidises to Sn(IV) in air; the mercury reductant
    harbour water and sediment, textile effluenttributyltin cation (C₄H₉)₃Sn⁺ and its chloride and hydroxide; dibutyl and monobutyl tin as degradation products; sorbed to solidsthe priority hazardous substance
    Solubility
    SnO₂ is insoluble; tin(II) salts are soluble but unstable; organotins are sparingly soluble organics that partition to solids. No solubility products quoted; the sources read print none.
    Hydrolysis
    Sn(IV) complete; Sn(II) readily, to Sn(OH)₂ and basic salts unless kept acid (Stumm and Morgan chapter 6, from the chapter, not re-read).
    Complexation
    Chloride for Sn(II); fluoride and hydroxide for Sn(IV) in plating; the organotins carry their ligands covalently.
    Precipitates
    SnO₂ and hydrous tin oxide; Sn(OH)₂ and basic tin(II) salts; SnS and SnS₂ in sulfidic sediment; organotins sorbed on sediment rather than precipitated.
    SnX4++2HX2OSnOX2(s)+4HX+\ce{Sn^4+ + 2 H2O -> SnO2 (s) + 4 H+}
    complete at any natural pH; the reason inorganic tin is particulate and drinking water carries below 1 to 2 µg/L (hydrolysis per Stumm and Morgan chapter 6, from the chapter, not re-read)
    SnX2++2HX2OSn(OH)X2(s)+2HX+\ce{Sn^2+ + 2 H2O <=> Sn(OH)2 (s) + 2 H+}
    tin(II) hydrolysis unless the solution is kept acid; the solid oxidises to SnO2 in air (Stumm and Morgan chapter 6, from the chapter, not re-read)
    2SnX2++OX2+4HX+2SnX4++2HX2O\ce{2 Sn^2+ + O2 + 4 H+ -> 2 Sn^4+ + 2 H2O}
    air oxidation of tin(II) in solution, complete within hours, which is why a stannous chloride reductant is kept acid, closed and fresh and why tin(II) is never a lasting species in an aerated effluent; the Sn(IV) then hydrolyses straight to hydrous tin dioxide
    HgX2++SnX2+Hg(l)+SnX4+\ce{Hg^2+ + Sn^2+ -> Hg (l) + Sn^4+}
    tin(II) chloride reduction of mercury(II) to the metal, the basis of cold vapour mercury analysis (Standard Methods 3112 B) and of chemical reduction of mercury from effluent (the EPA capsule report cited in the book's mercury chapter)
    SnOX2(s)+2OHX+2HX2OSn(OH)X6X2\ce{SnO2 (s) + 2 OH- + 2 H2O -> Sn(OH)6^2-}
    hot or strong alkali; the stannate that makes an alkaline tin plating bath work and the reason a caustic rinse redissolves the tin oxide that neutralisation had precipitated (element reactivity text: hot alkali gives stannates)

    4 · Role in treatment

    as a problem
    tributyltin in harbours, dredge spoil and receiving water
    legacy antifouling paint and hull maintenance release the tributyltin cation, which sorbs to sediment and is remobilised by dredging
    imposex in whelks and shell deformation in oysters (IMO); EU annual average EQS 0.0002 µg/L is below the reporting limit of the ZDHC method (0.01 µg/L)
    organotins in textile and leather effluent
    organotin biocides and stabilisers in finishing and coating
    ZDHC Table 1M lists mono, di and tri butyl, methyl, octyl and phenyl tins, tetrabutyl, tripropyl, tetraoctyl, tricyclohexyl and tetraethyl tins with a 0.01 µg/L reporting limit
    tin plating rinses
    acid tin(II) and alkaline stannate baths carried into rinse water
    the US metal finishing category covers tin plating but sets no tin limit (40 CFR 433.14 lists no tin)
    tin(II) as an oxidant demand
    tin(II) consumes chlorine and oxygen
    small; no figure read
    as a reagent
    tin(II) chloride, reductant
    reduces Hg(II) to elemental mercury for cold vapour atomic absorption and for chemical reduction of mercury from effluent
    HgX2++SnX2+Hg(l)+SnX4+\ce{Hg^2+ + Sn^2+ -> Hg (l) + Sn^4+}
    acid solution, fresh reagent; Standard Methods 3112 B; the EPA mercury capsule report names stannous chloride among reductants (book's mercury chapter)
    tin as a corrosion inhibitor (proposed)
    tin based inhibitors and tin solder in plumbing
    WHO fact sheet notes the proposal without detail

    5 · Removal and control

    solids separation (inorganic tin)
    tin(IV) is already particulate; coagulation, settling and filtration remove it with the solids; plating rinses precipitate hydrous tin oxide on neutralisation
    SnX4++2HX2OSnOX2(s)+4HX+\ce{Sn^4+ + 2 H2O -> SnO2 (s) + 4 H+}
    any pH above the acid bath; the CWW BREF's generic chemical precipitation and filtration
    Efficiency
    not quoted; inorganic tin residuals are not a regulated problem
    Interferences
    fluoride and stannate complexes in plating baths
    sorption to sludge (organotins)
    tributyltin and its degradation products partition to suspended solids and biomass and leave with the sludge; slow dealkylation in the sludge and sediment
    no design figure read; the ZDHC guidelines regulate the effluent, not the process
    Efficiency
    not quoted
    source elimination
    the AFS Convention bans application of organotin biocides in antifouling systems; ZDHC MRSL bans organotins in textile chemistry
    adopted 5 October 2001, in force 17 September 2008 (IMO)
    Interferences
    legacy sediment

    6 · Analytics

    methodstandarddetection limitnote
    ICP-MS (inorganic tin)ISO 17294-2 (tin among its elements); Standard Methods 3125; tin is not an analyte of EPA 200.8, where mass 118 appears only in a correctionnot readdigest: tin oxide is refractory
    organotins by derivatisation and GC-MSISO 17353 (derivatisation with sodium tetraethylborate, GC-MS), the ZDHC methodZDHC reporting limit 0.01 µg/L per compoundthe EU tributyltin EQS of 0.0002 µg/L is fifty times below this reporting limit
    Sampling pitfalls
    Inorganic tin needs digestion; tin(II) needs acid and prompt analysis or it oxidises. Organotins sorb to glass and solids and photodegrade: sample in amber glass, keep cold, extract quickly, and report whole water because the sediment fraction carries most of the tributyltin.

    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), inorganic tinno guideline occurs in drinking water at concentrations well below those of health concern; JECFA PTWI 14 mg/kg body weight from a TDI of 2 mg/kg for acute gastric irritation; assessment 2003
    EU DWD 2020/2184not set tin is not a parameter of Annex I
    US EPAnot regulated tin is in neither the primary nor the secondary table
    discharge
    bodylimitnote
    EU EQS (Directive 2013/39/EU), tributyltin compounds (tributyltin cation), priority hazardous substance 300.0002 annual average; 0.0015 maximum allowable µg/Lsame values for inland and other surface waters; CAS 36643-28-4
    EU CWW BREF BAT-AEL (Decision 2016/902)not set tin is not among the metals with a BAT-AEL
    US EPA 40 CFR 433.14, metal finishing (BAT)not set tin plating is in the category but tin has no limit
    Abu Dhabi ADS 23/2017, discharge to the marine environment (EAD)not set region-dependentno tin or organotin row in Table 1
    Abu Dhabi DoE Trade Effluent Control Regulations 2022, discharge to sewer10 mg/L
    region-dependent; sewer discharge, not receiving water
    Table A₄ Metals, tin
    industry thresholds
    sectorbodylimitnote
    textile and leatherZDHC Wastewater Guidelines v₂.1 (2022), Table 2, tinnot set tin is listed as sample and report only; no foundational, progressive or aspirational limit
    textile and leatherZDHC Wastewater Guidelines v₂.1 (2022), Table 1M organotin compounds0.01 µg/Lreporting limit per compound (mono, di and tri butyl, methyl, octyl and phenyl tins and others) by ISO 17353; MRSL substances, so detection above the reporting limit is a failure

    8 · Health and environmental effects

    Toxicity
    Inorganic tin is poorly absorbed, does not accumulate and is rapidly excreted; the only human effect is acute gastric irritation from canned beverages above 150 mg/kg or foods above 250 mg/kg; rat NOAEL 20 mg/kg per day in a long term feeding study, no carcinogenicity or teratogenicity (WHO fact sheet). Organotin toxicity is the reason for the chapter and is not covered by the WHO tin fact sheet.
    Bioaccumulation
    Inorganic tin does not accumulate in tissues (WHO). Tributyltin bioaccumulates in molluscs and fish and biomagnifies; the EQS regime treats it as a priority hazardous substance for that reason.
    Ecotoxicity
    Tributyltin causes imposex (sex change) in whelks and shell deformation in oysters at nanograms per litre (IMO). US EPA aquatic life criteria for tributyltin (2004): freshwater 0.46 µg/L acute and 0.072 µg/L chronic, saltwater 0.42 and 0.0074 µg/L; EU annual average EQS 0.0002 µg/L.

    Flags

    • The hydrolysis equations are cited to Stumm and Morgan chapter 6 from memory of the text, not re-read this session.
    • The mercury reduction equation is the electron balance; the book's mercury chapter names stannous chloride as a reductant from the EPA capsule report without printing it.
    • No natural water, seawater, wastewater or tributyltin concentration was read; only the WHO drinking water statement and the limits.
    • Organotin degradation and sorption behaviour is textbook environmental chemistry, not from a source read; no figure is given.
    • EU law was read on legislation.gov.uk mirrors because eur-lex did not respond; eur-lex urls kept for consistency.
    • Abu Dhabi: sewer 10 mg/L, no marine row; other GCC states not read.
    • Standard Methods and ISO method numbers other than those in the sources read (EPA 200.8, ISO 17294-2 and the methods the WHO documents cite) are quoted from memory and were not confirmed this session. ISO 17294-2 is cited for tin from the standard's title list, not from the text.

    Gaps

    • No concentration of tin or tributyltin in natural water, seawater, sediment, sewage or plating effluent was read.
    • The WHO background document on inorganic tin (2004) and any organotin risk assessment were not read.
    • Tin plating bath chemistry and rinse treatment are not described in any source read; the ledger's chemical chapter may hold them.
    • No detection limit for inorganic tin by ICP was read.
    • EU law was read on legislation.gov.uk mirrors; other GCC discharge standards were not read.
    • The stepwise dealkylation of tributyltin to dibutyl, monobutyl and inorganic tin is described by the sources as a pathway; none prints a stoichiometry or a rate, so no degradation equation is written.

    Sources

    WHO Guidelines for Drinking-water Quality, 4th ed. incorporating the first and second addenda (2022), chapter 12 chemical fact sheet, Inorganic tin (pp. 412 to 413)
    International Maritime Organization, International Convention on the Control of Harmful Anti-fouling Systems on Ships (AFS), adopted 5 October 2001, in force 17 September 2008
    The Element Book, water chapter for mercury (data/water/Hg.json), Standard Methods 3112 B cold vapour method and the EPA capsule report's stannous chloride reduction
    Directive (EU) 2020/2184 on the quality of water intended for human consumption (recast), Annex I Part B (read on the legislation.gov.uk mirror of the directive)
    US EPA, National Primary Drinking Water Regulations (table of MCLs and treatment techniques)
    Directive 2013/39/EU amending Directives 2000/60/EC and 2008/105/EC as regards priority substances, Annex I Part A (read as the legislation.gov.uk PDF of the adopted directive)
    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 Table 3 and footnotes c, d and g (read on the legislation.gov.uk mirror)
    Best Available Techniques Reference Document for Common Waste Water and Waste Gas Treatment/Management Systems in the Chemical Sector (CWW BREF 2016), chapter 3 (chemical precipitation with hydroxide and sulfide, ion exchange)
    40 CFR 433.14, Effluent limitations (BAT), metal finishing point source category
    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 Metals
    ZDHC Wastewater Guidelines Version 2.1 (November 2022), Table 2 heavy metals and Table 4A sludge
    US EPA Method 200.8, Revision 5.4 (1994), Determination of trace elements in waters and wastes by ICP-MS, sections 1.7 and 7.1, Table 1 (instrument detection limits)
    US EPA, National Recommended Water Quality Criteria, Aquatic Life Criteria Table
    Standard Methods for the Examination of Water and Wastewater (online edition), 3111 (flame AAS), 3120 (ICP-OES), 3125 (ICP-MS)
    Stumm, W. and Morgan, J. J., Aquatic Chemistry, 3rd ed. (Wiley, 1996), chapter 6 (metal ions in aqueous solution: hydrolysis and complexation) and chapter 7 (precipitation and dissolution)
    The Element Book, element entry and reference text for tin (data/elements/Sn.json, data/reference/text/Sn.json): oxide film, hot alkali gives stannates

    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.