Thickening and the Water Loop: Trash Screens, Flocculant, and Tailings
The CIL can be chemically perfect and still receive the wrong feed. Dilute slurry shortens residence time; grit loads pumps and screens; uncaptured water leaves with tailings and…
The CIL can be chemically perfect and still receive the wrong feed. Dilute slurry shortens residence time; grit loads pumps and screens; uncaptured water leaves with tailings and takes solution losses with it. Thickening, trash removal, and the return-water path decide what “correct chemistry” actually contacts.
Water and solids loop
Trash removal, densification, and tailings screening decide what chemistry the CIL actually receives.
If the trash screen or thickener drifts, the CIL chemistry is still “correct” on paper while the physical feed is wrong.
What arrives from classification
Cyclone overflow is typically a relatively dilute slurry. Before leach or thickening, plant practice often screens for trash and wood chips that would otherwise:
blind interstage and tailings screens;
abrade pumps and agitators;
carry organics toward carbon (foulant type I pathways).
An illustrative trash-screen design uses dual decks with 0.6 × 0.5 mm apertures — confirm against your own screens. Wiper or deck condition is part of the leach’s reliability, not a separate utilities task.
Thickener: one vessel, three products
A continuous thickener produces:
Underflow — densified slurry toward leach or disposal density;
Overflow — clarified water for recycle;
Bed / rake load — mechanical duty that must match feed and polymer.
Illustrative teaching ranges for gold plants:
Parameter
Illustrative range (confirm on site)
Underflow solids
~50–60% solids (density often tracked as RD ~1.5–1.7)
Overflow
Clear enough for recycle without re-grinding fines to leach
Flocculant
Dose and make-up quality set floc size and bed permeability
Density is a control variable
Condition
What the circuit sees
Operator response direction
Under-densified
Short CIL residence, high water report, pump overload risk
Review flocculant, bed level, feed rate
Over-densified
Poor mixing, high torque, starved tanks
Reduce bed, check rake and feed balance
Dirty overflow
Recycle carries fines back to mills or leach
Flocculant / feed solids review
High bed level
Torque and rake stress
Step feed or dilute carefully — do not only raise polymer
Under-thickening and over-thickening are opposite failures with opposite evidence: one is a water and volume problem; the other is a solids-handling and mixing problem.
Residence time still applies after the thickener
Active volume and flow still govern:
residence (h) = total active volume (m³) / slurry flow (m³/h)
If density rises without updating the flow measurement basis (volume vs mass solids), the calculated residence lies. Always state whether flow is volumetric slurry, dry tonnes, or solids flux.
CIL density window
An illustrative CIL design uses ~40–50% solids with relative density targets in a band such as 1.45–1.60, while the thickener runs denser before dilution or stock-tank control. The exact split is circuit-specific. What matters is that thickener density, stock-tank density, and tank RD are one control chain, not three independent charts.
Tailings screen: the last gate
Before slimes disposal, a tailings screen (often ~0.8 mm in teaching examples):
returns oversize carbon to the circuit (inventory protection);
gives a visual and sampling point for fines and carbon loss;
closes the water story — what passes is residue plus solution.
Carbon appearing on the tailings screen points upstream: interstage screens, wipers, seals, transfer batches.
Failure stories
Cloudy overflow after a polymer change — floc too fine or over-dosed; bed may blind. Check make-up water, age of solution, and dose rate together.
CIL residence “too short” on the calculator — actual flow rose, a tank is bypassed, or density basis changed so the volume used is wrong.
High solution losses to tailings — free cyanide and gold in the residue solution; look at pH, destruction, and whether water is leaving uncaptured.
Rising power on the rake — bed depth, grit, or over-feed; forcing polymer without a bed strategy risks torque trips.
0.6 × 0.5 mm
illustrative trash-screen aperture
50–60%
illustrative thickener underflow solids band
0.8 mm
illustrative tailings-screen aperture
water_and_residence.py
1# Illustrative: active CIL volume vs slurry flow after thickening2active_volume_m363593flow_m3_per_h140# thickener-underflow-fed slurry (example)4residence_hactive_volume_m3flow_m3_per_h5printf"nominal residence = {residence_h:.1f} h"6print"If flow metric changes (RD or %solids), recompute before judging chemistry."
Check yourself
Check yourselfOverflow becomes turbid while underflow density also falls. What single system is failing first?
The thickening step as a whole — flocculant make-up/dose, feed rate, or bed management — is not separating solids from water; both symptoms follow from failed clarification and densification.
Check yourselfWhy is raising CIL flow a leach risk even when chemistry setpoints are unchanged?
Residence time drops; gold has less time to dissolve and carbon less time to adsorb before the next tank. Recovery can fall with identical free cyanide and pH.
Check yourselfWhat does carbon on the tailings screen tell you about interstage screens?
Fine carbon has bypassed upstream retensioning. Inspect interstage screen integrity, wipers, and seals before adding more carbon inventory.
Thickener rakes, pumps, and screens have mechanical energy and pinch points; effluent streams may carry residual cyanide. This is a teaching aid — follow site isolation and environmental procedures.