A Closer Look at Reagent Consumption
Reagent performance is constantly improving, but is your plant keeping up as well?
Tips on how to assess SX plant performance and reagent usage.
By Owen Tinkler, Cytec Industries Inc.



Growth in demand for copper metal has put pressure on producers to optimize their equipment and procedures
throughout the production spectrum—mine, mill and plant. Reagent consumption in solvent extraction (SX) of
copper is one area of plant operation that can warrant examination for possible savings and efficiency gains.
Reagent consumption is an important consideration in any commercial copper solvent extraction circuit. This article examines the main factors that influence reagent consumption and considers the validity of comparing the relative performance of different plants using the widely used “Reagent Usage” metric (described as the mass of reagent consumed in a given period of time, divided by copper cathode production for the same period of time). An alternative metric— called Net Reagent Entrainment, defined as reagent consumption during a given time period divided by the PLS flow-rate for the same period—also is presented.
Reagent consumption can be divided into two categories: The first is the mechanical loss of the organic phase. The volume of organic lost is the difference between the total organic volume leaving the solvent extraction (SX) plant and the volume of recovered organic. Both are equally important considerations in the control of reagent consumption.
The second category is the loss of extractant by hydrolytic and other forms of degradation. Although all modern copper SX reagents are highly resistant to hydrolytic degradation, there are still differences in the degradation rate constants, which translates into differences in reagent consumption.

Organic Loss from the SX Circuit
The loss of organic from an SX circuit, both as entrainment into the raffinate and by removal of interfacial crud, is influenced by many factors. The most important of these are:
Mixer/Settler Design – Depending on other contributing factors, mixer/settler design can play a major role in reagent consumption. In recent years, improvements in mixer/settler design have resulted in a significant decrease in the average reagent consumption at new plants, in comparison to older plants (although it is recognized that some “older” design plants still provide good performance). Low-shear mixer design and optimized settler design have enabled plants operating with design flows and clean pregnant leach solution to operate with entrainment losses of <10 ppm and with very low interfacial crud generation.
Flow versus Design and Mixer Continuity – The flow rates of PLS and organic relative to plant design can have a significant influence on both entrainment and organic loss with crud removal. If the PLS flow is increased relative to the organic flow so that the O/A ratio drops below 1:1, the dispersion in the extract stage mixers will generally be aqueous continuous. Theoretically, aqueous continuous operation should result in increased organic in aqueous losses, but decreased aqueous in organic losses. In practice, this is observed in some but not all cases. For instance, one large commercial plant which inverted the mixer continuity in its raffinate stages from organic to aqueous continuous was actually able to lower entrainment losses from 60 ppm to 40 ppm over the course of a threeyear period, while increasing the PLS flow by more than 20%.

Figure 1: Points of reagent exit and entry into an SX circuit.
PLS Turbidity – PLS turbidity, together with the nature of the solid particles, plays an important role both in the rate of crud formation and organic in aqueous entrainment. Consequently, plants with high PLS turbidity will inevitably have higher organic consumption than plants with low PLS turbidity. In the most extreme cases, removal of interfacial crud can account for more than 60% of total organic consumption.
Return of Recovered Organic to the SX Circuit – Effective organic recovery can have a huge influence on overall reagent consumption. A range of equipment is available to recover organic both from the raffinate pond and from organic associated with crud.
Recovery of Organic Associated with Crud – Efficient recovery of organic associated with crud is one of the most straightforward ways of lowering organic consumption. Several types of process equipment have been developed to separate organic from crud, the most widely used of which are centrifuges, plate filters and filter presses.
Recovery of Entrained Organic – Recovery of entrained organic—that is, the organic floating on the raffinate pond and the rich electrolyte tank—is important both to minimize organic consumption and for good housekeeping. Organic that is left to build up on the surface of the raffinate pond or rich electrolyte tank may undergo both hydrolytic and oxidative degradation. Examples of equipment used to recover organic in the raffinate leaving the plant include Pacesetters and Jameson cells. Examples of equipment used to recover organic from the raffinate pond and electrolyte tank include tank skimmers and belt or mop skimmers. Appropriate use of baffles and booms within ranks and raffinate ponds can also assist in allowing entrained organic to accumulate on the surface where it can be recovered.
In order to get an idea of the relative impact of the various factors described above, four theoretical cases are presented in Table 1 and discussed in the section below.

Table 1: Comparison of effects influencing reagent consumption.
The two different ways of comparing reagent consumption are presented in Figure 2 for the four cases described in Table 1.
Case 1 considers a modern SX plant operating at design flow with low-turbidity PLS. The plant achieves over-theweir entrainment of organic into the raffinate of 40 ppm and organic associated with crud leaving the plant accounts for 10% of the total. Organic recovery both from crud and entrainment is efficient at 50%. Accordingly reagent consumption, expressed both as Reagent Usage and Net Reagent Entrainment, is very low.
Case 2 also considers a modern SX plant at design flow but with higher turbidity and poorer organic recovery systems in place. As a result of the higher turbidity, entrainment of organic into the raffinate is slightly higher than in Case 1 and organic associated with crud leaving the plant now accounts for 30% of the total. The poorer recovery system means that only 10% of the total organic leaving the plant is recovered. Organic consumption expressed both as Reagent Usage and Net Reagent Entrainment is approximately three times higher than in Case 1.
Case 3 considers a modern plant which has increased the PLS grade 50% to maintain production as the PLS copper grade has fallen to half the value used in Cases 1 and 2. Relative to Case 1, although PLS turbidity remains low, the higher PLS flow rate results in higher entrainment of organic into the raffinate and higher loss of organic associated with crud. Recovery of organic is as efficient as in Case 1 but with nearly double the organic in aqueous entrainment leaving the plant, the reagent usage is three times that of Case 1, while the Net Reagent Entrainment is double.
Interestingly, the reagent usage is very similar to Case 2, although Net Reagent Entrainment is only two thirds of the value in Case 2. So which is the better operating plant? Are they similar, as the reagent usage number suggests, or is the plant in Case 3 actually operating better than the plant in Case 2?

Figure 2: Reagent consumption comparison.
Finally, Case 4 considers an older plant operating with flows 50% above design to maintain production. Turbidity is similar to that of Case 2 but the less efficient design together with the higher PLS flow results in higher entrainment of organic into the raffinate and a higher percentage of organic loss with crud leaving the plant. Additionally, organic recovery is poor, with the result that reagent consumption is far higher than in the other three cases.

Conclusion While reagent usage is a useful guide to plant performance, direct comparisons may be misleading as no two plants have identical operating parameters. Recommendations for controlling organic consumption include:
•Maintain good mixer emulsion continuity in the phase that is appropriate for mixer organic/aqueous ratios (no mixed phases);
•Maintain quality of separation in settlers, including: proper crud management, minimize solids/crud leaving aqueous weir (carrying organic), and appropriate depth of organic/aqueous phase based on flow rates to maintain similar relative velocities of phases;
• Minimize mixer agitation to avoid formation of micro-droplets;
• Avoid entrainment of air that is pulled into the mixer through feed lines, pumps, or from the surface of the mixer;
• Recover organic from crud that is removed from the plant;
• Use tanks, coalescers, etc. and control flow of solutions in raffinate ponds to allow entrained organic leaving the plant to coalesce and collect in areas where it can be recovered;
• Use skimmers, organic recovery mops/ropes, etc. to collect pooled organic; and
• Properly clean recovered organic to ensure that no contamination is introduced into the SX plant, which would phase separation problems.


Owen Tinkler is regional manager–Metal Extraction Products, Europe,
Middle East and Africa for Cytec Industries Inc.
What is the effect of the type of reagent on consumption? The chart below shows a comparison of reagent usage among South American plants with annual production of > 5,000 mt/y. South America was chosen for this comparison because the plants there generally operate with flows at or very close to design. The plants are divided by reagent class: modified C-9 aldoxime based reagents and un-modified aldoxime / ketoxime based reagents.