Gold

    group 11 · period 6 · d-block · transition metal

    minorGold itself is absent from water, but gold extraction is a water problem: cyanidation dissolves gold as the dicyanoaurate anion in 300 to 500 mg/L cyanide solutions, and the effluent story is weak acid dissociable cyanide, limited in EU tailings ponds to 10 mg/L and barred from discharge by US cyanidation mills.

    Typical wastewaters

    • gold cyanidation (leach solution and tailings) the dicyanoaurate anion Au(CN)₂⁻ in alkaline cyanide solution (300 to 500 mg/L NaCN, pH 10.5) with free and weak acid dissociable cyanide in excess; gold is recovered on carbon before the pulp reaches the pond the effluent problem is the cyanide, not the gold: leachate 120 to 450 mg/L free cyanide before destruction, 0.06 to 1.94 mg/L after
    • tailings pond discharge (after cyanide destruction) residual weak acid dissociable and total cyanide, 0 to 2 mg/L, with negligible gold; iron cyanides survive as total cyanide Kittila and Ovacik report no discharge, all water pumped back to the process

    1 · Identity

    Symbol, number
    Au, 79
    Oxidation states in water
    +1 as the dicyanoaurate anion Au(CN)₂⁻, the only form in which gold is carried in process water; +3 as chloro complexes in aqua regia and chloride leaching; 0 as native metal, insoluble in water (element entry, MWEI BREF).
    Note
    The element entry covers the metal and its chemistry. The water chapter is the cyanide leach circuit and its effluent.

    2 · Occurrence in water

    Natural sources
    Negligible; native gold in placers and veins; seawater gold is at the nanogram per litre level (element entry).
    Anthropogenic sources
    Cyanidation of gold and silver ores: leach solutions at 300 to 500 mg/L NaCN (a minimum of about 350 mg/L), heap leach and agitated pulp leach, carbon in pulp recovery; artisanal mercury amalgamation in the ledger.
    matrixtypical rangenote
    cyanidation leach solution300 to 500 mg/L as NaCNthe cyanide, not the gold; the gold cyanide complex is very stable and needs only slightly more than stoichiometric cyanide, the excess going to other cyanide consumers
    extractive waste leachate before destruction120 to 450 free cyanide; 150 to 300 average entering destruction tanks (Kittila) mg/Lthree sitesBoliden 120, Ovacik 200, Rio Narcea 400 to 450 mg/L as NaCN, pH 10.5 (Table 4.27)
    cyanide destruction outflow0.06 to 0.88 (WAD, Ovacik); 0.31 to 1.94 (total, Boliden); 1 to 40 (WAD, Rio Narcea) mg/Lthree sitesBoliden destroyed 99.5 percent of free cyanide; further degradation occurs naturally in the pond
    tailings pond discharge0 to 0.33 (Boliden, total); 0.2 to 2 (Rio Narcea, WAD); no discharge (Ovacik, Kittila) mg/Lthree sitesKittila pumps all water back to the process

    3 · Speciation

    Gold is a noble metal insoluble in water; a complexing agent such as cyanide, which stabilises the gold species in solution, and an oxidant, such as oxygen, are required to dissolve it (MWEI BREF). In alkaline cyanide solution (pH above 10.5 so that HCN does not volatilise) gold is Au(CN)₂⁻, a very stable anion recovered on activated carbon or by zinc precipitation. Chloride, bromide, thiourea and thiosulfate form less stable complexes and need more aggressive conditions.

    conditiondominant speciesnote
    alkaline cyanide leach, pH 10.5Au(CN)₂⁻with free CN⁻ in excess; sulfide minerals consume cyanide to thiocyanate
    natural waterAu (s), particulateno dissolved gold of significance
    Solubility
    The metal is insoluble; sodium dicyanoaurate is soluble.
    Hydrolysis
    not relevant
    Complexation
    Cyanide above all; thiosulfate, thiourea, chloride and bromide as alternatives (MWEI).
    Precipitates
    Gold cemented on zinc (Merrill Crowe) and eluted from carbon; not water treatment solids.
    4Au+8CNX+OX2+2HX2O4Au(CN)X2X+4OHX\ce{4 Au + 8 CN^- + O2 + 2 H2O -> 4 Au(CN)2^- + 4 OH-}
    the Elsner equation for cyanide leaching with dissolved oxygen as oxidant at pH above 10.5; the MWEI BREF describes the reaction without printing it, and the book's element entry gives cyanide dissolution

    4 · Role in treatment

    as a problem
    cyanide in tailings and effluent
    free, weak acid dissociable (WAD, including zinc, copper, nickel, cadmium and silver complexes) and total cyanide (including the iron, cobalt and gold complexes) leave the leach
    several stages of cyanide destruction may be needed (MWEI BREF); the EU pond limit is 10 mg/L WAD from 1 May 2018 (Directive 2006/21/EC); US cyanidation mills may not discharge process wastewater (40 CFR 440.103)
    gold locked in carbon fines and sludges
    not a water quality issue but a recovery loss
    as a reagent
    none
    gold is not dosed; cyanide is the reagent and is covered under carbon and nitrogen

    5 · Removal and control

    cyanide destruction (oxidation) and natural degradation in ponds
    chemical oxidation of free and WAD cyanide in one or more stages, then volatilisation, photolysis and biodegradation in the pond
    Boliden destroyed 99.5 percent of free cyanide; the MTWR BREF (2009) describes the stages; the specific oxidants were not read this session
    Efficiency
    99.5 percent free cyanide (Boliden)
    Interferences
    iron cyanides survive as total cyanide
    zero discharge and recycle
    all water pumped from the leached extractive waste pond back to the process
    Kittila mine; Ovacik reports no discharge from the deposition area
    Efficiency
    no release
    Interferences
    water balance in wet climates

    6 · Analytics

    methodstandarddetection limitnote
    free, WAD and total cyanideISO 6703 and ISO 14403 (as listed by ZDHC); EPA 335not readWAD cyanide is measured after distillation at pH 4.5; the figures in Table 4.27 are measured daily to continuously online
    gold by fire assay and ICPnot relevant to water
    Sampling pitfalls
    Cyanide samples must be preserved with sodium hydroxide to pH above 12 and kept dark and cold; sulfide and oxidants interfere and must be removed.

    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)no guideline gold is not evaluated; cyanide has its own entry
    EU DWD 2020/2184not set
    US EPA NPDWRnot regulated cyanide (as free cyanide) has an MCL of 0.2 mg/L
    discharge
    bodylimitnote
    EU Directive 2006/21/EC Article 13(6), weak acid dissociable cyanide in the pond10 mg/L (ppm) WAD cyanideat the point of discharge of tailings into the pond; 50 ppm from 1 May 2008, 25 ppm from 1 May 2013, 10 ppm from 1 May 2018 for existing facilities, 10 ppm at once for new permits
    US EPA 40 CFR 440.103, mills using the cyanidation process to extract gold or silverno discharge no discharge of process wastewater to navigable waters, except the net precipitation excess subject to the mine drainage limits (copper 0.15, zinc 0.75, lead 0.3, mercury 0.001, cadmium 0.05 mg/L monthly)
    EU CWW BREF BAT-AEL (Decision 2016/902)not set
    industry thresholds
    sectorbodylimitnote
    textileZDHC Wastewater Guidelines v₂.1 (2022)not set gold is not a parameter; total cyanide is limited at 0.2, 0.1 and 0.05 mg/L for textile

    8 · Health and environmental effects

    Toxicity
    Metallic gold is inert; the toxicity of gold mine effluent is cyanide and the co-leached metals, not gold.
    Bioaccumulation
    not relevant
    Ecotoxicity
    not relevant

    Flags

    • The Elsner equation is written here; the MWEI BREF describes the reaction in words.
    • Table 4.27 figures are three European sites reported in the 2009 MTWR BREF and re-quoted in 2018.
    • Cyanide destruction chemistries (sulfur dioxide and air, peroxide, alkaline chlorination) were not read this session and are not named as sources.

    Gaps

    • No source read gives dissolved gold in any water; the seawater figure is the book entry's.
    • The cyanide destruction reactions and their reagent doses are not sourced.
    • The International Cyanide Management Code limits were not read.
    • Thiosulfate leaching effluents and artisanal mercury amalgamation are in the ledger, not here.

    Sources

    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.