Erbium (Er) and water: occurrence, chemistry and removal

Erbium is a rare-earth element that can occur in water as dissolved species or in particles. Its chemical form, the other substances in the water and the intended recovery objective determine which treatment options are worth testing.

How can erbium enter water?

Erbium occurs in minerals including monazite and bastnaesite. Water in contact with erbium-bearing minerals or materials may carry dissolved erbium or mineral particles. Mineral processing, laboratory work and recycling of erbium-containing materials are potential pathways to investigate where those activities occur. Their presence does not establish contamination at a particular site; sampling is needed.

Erbium is used in optical-fibre amplifiers and some speciality glasses. For general elemental properties, see erbium.

Erbium chemistry in water

The common oxidation state is Er(III). Acidity, complexing substances and other ions influence how much erbium remains dissolved. Analytical solution guidance identifies poorly soluble erbium carbonate, oxalate and fluoride and warns against neutral or basic media when maintaining analytical solutions.

A water-soluble salt does not guarantee that erbium remains dissolved after mixing with another stream. Changing the pH or adding a substance that binds erbium can change its distribution between liquid and solids. Assess the actual water composition rather than predicting treatment solely from the original reagent name.

Distinguish total erbium from the dissolved fraction defined by the sampling and filtration method. Fine particles and colloids can complicate the distinction. Use consistent sample preparation when comparing untreated and treated water.

Removing erbium from water

Settling and filtration can separate erbium-containing particles when their size and settling behaviour permit. Dissolved erbium requires capture of dissolved species or conversion into a separable solid. Precipitation should be assessed with measurements of residual dissolved erbium and solids separation, including the effects of competing ions and complexing substances.

Erbium-specific research has investigated adsorption and desorption using D113-III resin in batch and column systems. A separate study examined crosslinked sericin-alginate beads, including the effects of pH, dose, contact time, temperature, competing ions and reuse. Such studies establish performance under their experimental conditions; they do not establish a universal operating pH, capacity or removal percentage for a different water.

Concentration and recovery

Adsorption followed by desorption, or ion exchange followed by elution, can transfer captured erbium to another liquid stream. A smaller final volume can increase its concentration. The sericin-alginate study demonstrated enrichment through reuse of the eluent, illustrating the distinction between removing erbium from water and collecting it in a recovery stream.

Measure erbium removal, mass recovery and product purity separately. Other rare-earth elements and salts may be concentrated at the same time. A mass balance should cover feed, treated water, solids, spent media and regeneration liquids.

Information useful for treatment assessment

  • Flow, temperature, pH and variation in water composition.
  • Total and dissolved erbium, with the sampling and filtration method.
  • Other rare-earth elements, major ions, suspended solids and known complexing substances.
  • The treated-water target and the desired recovery product.
  • The composition and destination of sludge, spent media and regeneration liquids.

Report concentrations on a consistent basis. A value expressed as elemental Er excludes counterions and water of crystallisation and differs from the mass concentration of an erbium salt.

Sources