carbon and resin technologies for gold recovery | sgs

carbon and resin technologies for gold recovery | sgs

Carbon has been traditionally used to recover gold from cyanide leachates, but recent technological advances have resulted in the use of resins as a highly efficient and cost-effective method of gold recovery. SGS has the expertise to help you develop a gold flowsheet that optimizes gold extraction, gold recovery with reasonable operational costs and environmental sustainability.

SGS project managers can work with you to develop an effective flowsheet for your gold operation. Starting at the scoping or bench scale, we will design and demonstrate a testing program that will define and optimize the crucial gold recovery parameters including mineralogy, kinetics and chemical constraints.

Whether your final flowsheet uses carbon or resin technologies, the data gathered by SGS will enable you to make important operational decisions and provide capex and opex information for your feasibility study.

SGS metallurgists developed and continue to improve on these cost-effective, time-tested and proven processes.In each, activated carbon is used to extract gold from the cyanide leach solution. Such a carbon recovery system offers high recovery rates and lower capital and operating costs. These carbon recovery techniques include:

In recent years, resin is replacing carbon as the gold recovery substrate of choice. SGS is the world leader in the development of this technology. The process used in resin recovery is similar to carbon, but the gold is adsorbed onto solid spherical polystyrene resin beads rather than activated carbon grains.

Contact SGS early in the planning stage of your gold project. Our robust technology and globally-recognized technical expertise can give you the information you need for an efficient and cost-effective gold flowsheet for your operations.

cyanide leach tests (bottle roll, vat, agitation and column)

cyanide leach tests (bottle roll, vat, agitation and column)

Nesch Mintec provides diagnostic leach test such as acid and cyanide leach during the cyanide leach process, a cyanide solution, or lixiviant, is percolated through ore contained in agitation tanks, vats, columns or heaps.Gold is dissolved by the cyanide and then removed from the vat heap or columns.It is then extracted from the pregnant leach solution by adsorption on carbon or resins. This cost-effective, proven method of ore extraction provides maximum recovery for many gold ores, including low grade and some refractory ores.

Nesch Mintec professionals develop your cyanide leach flowsheet at the bench or laboratory scale using cyanide bottle roll tests and agitation leach tanks to assess leach parameters and optimize the gold recovery.During these tests, aeration, alkalinity, agitation time and grain size are strictly controlled and the resulting data provides an accurate estimate of the gold recovery and rates of acid consumption. Such tests set the parameters for your pilot plant or final site recoveries.

gold ore roasting plant

gold ore roasting plant

To achieve optimum gold recovery from the certain sulfide ore body, the ore must be finely ground to achieve proper oxidation and mineral separation. The ore is separated into stockpiles after it has been mined. These stockpiles are based on gold content, sulfide content, and carbonate content. The ore is blended prior to being fed into the crushing circuit. The ore passes through crushing and grinding circuits to the Roaster circuit then to the Carbon and Leach circuit at a designed rate of 12,000 tpd. (13,000 /2002)

Crushing starts with the primary 42 x 65 gyratory crusher and fed to the Nordberg MP800 secondary crusher where it is crushed to 80% passing 3/4 inches. After the material is crushed it is stockpiled for feed into either grinding train. The material is ground from 1 inches to 80% passing 200 mesh (74 micron) in a double rotator-grinding mill, run by a 10,000 hp motor. Material is split with a static classifier and a dynamic classifier with the underflow reporting back to the mill and the overflow going to the Roaster circuit.

The Roaster is also a duel train with 2 22 diameter x 80 high, two-stage stationary bed Dorr Oliver Roasters. The gold ore is double-refractory. First, the gold is locked in sulfide mineral particles that must be oxidized to expose the gold for leaching. Second, the ore also contains preg-robbing carbon that will collect solubilized gold from the subsequent leaching circuit if the gold is not first removed. Both problems are addressed by roasting the finely ground ore in two roasters to produce a calcine with very low sulfur and carbon contents that is amenable to gold recovery in a conventional CIL (carbon and Leach) plant.

Offgas created from roasting is cleaned with a series of scrubbers and Mercury is separated and collected in tanks. Clean air is sent to the atmosphere. The roasted ore is sent to the neutralization tanks and then on to the CIL circuit.

The CIL circuit consists of 6 tanks, ranging from 50 high to 60 high with a 24 drop between tanks. The purpose of the CIL is to dissolve gold contained in the neutralized ore slurry by sodium cyanide leaching, and to adsorb the dissolved gold on to the surface of activated carbon.

From the splitter box, slurry flows to the C.I.L. tanks sized to provide a total of 16 hours of retention time. Each C.I.L. tank has an agitator and two Kemix wedge wire self-cleaning screens for carbon retention. Slurry discharging from the last C.I.L. tank passes vibrating carbon safety screens and is then treated with Ammonium Bisulfite (A.B.S.) for cyanide destruction. Detoxified tailings are pumped to the tailings pond. Reclaimed water from the settled tailings is pumped back to the process for reuse.

Carbon is advanced through the C.I.L. tanks on a shift basis. Loaded carbon (carbon loaded with gold up to 175 o.p.t.) from the first C.I.L. tank is sent to the existing carbon treatment plant for gold removal, electrowinning, refining, and carbon regeneration.

Somegold ore at the Roaster is double refractory. First, the gold is locked in sulfide mineral particles that must be oxidized to expose the gold for cyanide leaching (Autoclaves do this function effectively). Second, the ore also contains preg- robbing carbon that will collect solubilized gold in the leaching circuit if it is not removed (oxidized) first. Both of these problems are solved by roasting the ore at high temperature.

Coarse run of mine ore is supplied to the gyratory crusher by 85-ton haul trucks. These trucks unload the gold ore into the 120-ton capacity dump hopper above the gyratory crusher. A hydraulic rock breaker (rock-pick) breaks oversize ore within the dump pocket. Crushed product is withdrawn from the surge pocket (rock-box) below the gyratory crusher by an apron feeder discharging onto the gyratory product conveyor (501). The surge pocket variable live operating capacity ranges between 60 and 100 tons. The gyratory crusher product conveyor discharges onto the cone crusher feed conveyor (502). Primary crushed ore should be 98% passing 8 inches and 80% passing 6 inches.

Tramp metal is removed from the crushed ore using two magnets. The first magnet is located above the transfer point. The second magnet is located above the cone crusher feed conveyor immediately downstream of the baghouse dust recycle transfer point.

Dust from the primary crushing circuit is collected in the primary crushing bag house. Clean air discharged from the bag house is emitted to the atmosphere through the primary crushing baghouse stack. Collected material is returned to the cone crusher feed conveyor ahead of the second magnet for transfer to the secondary crusher system.

Ore discharge from the primary crusher circuit is fed to the double deck vibrating scalping screen of the secondary crusher circuit. Screen oversize (plus inch) is discharged to the cone crusher for secondary crushing. Conveyor transfers screen undersize and cone crusher discharge to the coarse ore stockpile.

The purpose of the roasting plant is to reduce the sulfur and organic content of the ore to increase gold recovery in downstream processes! Roasting technology is based on two stage oxygen roasting as developed by Freeport Research (2 trains) 2,000 dst silo (per roaster) 22 diameter X 80 high brick lined (170,000 bricks total)

In its simplest form, a fluidized bed is a suspension of material in a gas stream, which behaves like a liquid.Fluidized bed roasting was selected because it efficiently destroys the sulfide minerals and organic carboncomponents of the ore while maintaining excellent control of the process temperatures. Temperature control in the roaster is critical because there is a substantial decrease in gold extraction at temperatures above 1050F, and also coal combustion becomes unstable at temperatures below 1000 F. Pure oxygen was selected as the combustion gas because it: 1) promotes rapid combustion at minimum temperatures; 2) reduces the amount of roaster exhaust gas minimizing the size and cost of the gas scrubbing equipment; and 3) allows the roaster to process a higher tonnage per unit area. The two stage design is preferred because; 1) the single stage design results in significant levels of unoxidized carbon exiting the roaster, reducing gold recoveries and 2) the two stage design allows the most efficient utilization of oxygen. The roaster is operated with the gas flow countercurrent to the solids flow. The countercurrent technique maintains the maximum combustion efficiency throughout the roaster by contacting the highest oxygen concentration with the lowest solid fuel content at any point in the roaster.

The roaster feed ore is 80% passing 74 microns. It is estimated that 10 to 25% of the ground ore will be smaller than 10 microns with the actual amount depending on the extent of the particle agglomeration.

Ground ore is discharged from the grinding mill product recovery baghouse and collected in the roaster feed silos. One silo is provided for each dry grinding circuit. Each silo has a 2,000-ton live capacity providing a normal 6 hours of roaster feed. The silo is designed as a mass-flow silo. The hopper section of the silo is sufficiently steep and has a coefficient of friction that is sufficiently low to ensure that all the material is discharged. This design ensures that there are no dead areas in the silo, i.e. areas in which the ore is stagnant and wont discharge, and provides a first-in first-out operation.

Each silo discharges from a fluidized hopper at its base through a shutoff side gate capable of sealing against fluidized material, two control valves in parallel to provide volumetric flow control and an air slide to a common roaster feed distribution feed box. The fluidizing hopper design aerates the ore and helps to provide the required design discharge rate of 559 tons per hour per silo: each silo discharge can provide the full flow to both roasters.

The common roaster feed distribution box is fluidized with air. It discharges feed material to each of the two roasters feed systems. Each system includes a control valve, an air slide, a deaerator, and a feed weigh belt with drag conveyor, which discharges to the roaster feed bucket elevator. If required, a screw feeder adds coal to the weigh feed belt. From the bucket elevator, the ore is transferred to the roaster-fluidized feeder via an air slide.

Two parallel roaster circuits are provided to heat the refractory gold ore and oxidize the contained organic carbon and sulfide sulfur. Each roaster is comprised of two bubbling, fluidized-bed reactors in a single vessel, plus a fluidized feed system, first and second stage cyclone systems, and ancillary systems. The description below refers to one of the two parallel circuits.

The fluidized feeder distributes ore continuously from its hopper to the first-stage (upper) bed of the roaster. The feeder is fluidized with air and overflows into the roaster through standpipes extending into the first-stage bed.

The upper bed is maintained at a constant, uniform temperature of about 1,025F. The heat source for the first stage is provided by the ores net heat of reaction. Coal may be added to the ground ore to provide additional heating for low fuel-value ores, or fresh water may injected to cool the first stage bed for high fuel-value ores. Water may also be sprayed into the first stage freeboard to cool the roaster off-gas if excessive freeboard combustion occurs. The ore is oxidized predominantly in the first-stage.

Solids discharge continuously from the first-stage through the inner-stage solids transfer system to the second-stage (lower) bed, which is maintained at a constant, uniform temperature of 1,050F. Diesel oil, pumped through oil guns, is used for heating, as required. The oxidation of ores is essentially completed in the second stage.

Low pressure, high-purity oxygen is introduced as the fluidizing medium through the cold windbox to the second-stage bed and to the solids transfer boxes. Hot exhaust gas from the second-stage reactor is conveyed through the inter-stage gas transfer system and the hot windbox to fluidize the first-stage bed.The hot, oxygen-rich gas from the second stage promotes rapid oxidation of the organic carbon, sulfur, and fuel in the first stage bed. The first-stage exhaust gas is de-dusted in the gas discharge system before passing to the gas quench and cleaning train.

Medium-pressure, high purity oxygen is injected through aspirators into the second stage hot windbox to purge solids. These solids may enter the hot windbox with the inner-stage gas or by sifting through the first-stage gas distributor.

The exhaust gas from each roaster stage is de-dusted in a set of primary and secondary cyclones. In both stages, the coarser fraction of the elutriated solids recovered by the primary cyclone is returned to the bed. The finer fraction recovered by the secondary cyclone is fed forward through the reactors, first stage to second stage and second stage to calcine product, to reduce accumulation of fines within the fluid bed. Dust is carried over the first stage cyclone separators in the roaster off-gas (about 3% to 4.5% of the dry ore feed depending on the off-gas rate).

Dust collected within the roaster area is recovered in the roaster dust collection baghouse and returned to the roaster feed distribution box. Cleaned air is emitted to the atmosphere through the roaster baghouse stack. A critical relationship exists between roasting temperature, residence times, and the subsequent amenability of the ore to cyanide leaching. Precise control of these parameters is therefore essential.

Sulfide Sulfur..1.9% Total Carbon Matter1.4% Carbonate4% Fuel Value.300BTU Mill Product P8o..74 First Stage Bed Temp.1025 F Second Stage Bed Temp1050 F Retention Time.44 minutes Superfical Bed Velocity0.7 to 1.0 ft/s Superfical Freeboard Velocity1.5ft/s Temperature Control.Water or Coal Oxygen Consumption.10% of feed capacity Recovery90%

A loader reclaims ore from the different stockpiles and loads it in 85-ton trucks to create a relatively uniform blend. The characteristics of the blend may vary from time to time but the normal targets are as follows:

A dedicated gas quench and cooling system is provide for the off-gas for each of the two roasters followed by a common gas scrubbing system. The off-gas is first quenched with water and a wet scrubber removes the dust. The wet gas condenser then cools the off-gas stream, removing water vapor in preparation for the booster fan, wet electrostatic precipitator (ESP) and mercury scrubber. Both mercury and SO2 are removed in the regenerative scrubbers. The gas stream is then conveyed by the exhaust fan for further treatment by thermal oxidation of CO and catalytic reduction of NO5. The cleaned gas is then emitted to the atmosphere through the gas-scrubbing stack.

2 Lines The off-gas leaves the roaster freeboard at a slightly negative pressure (minus 1-inch water gauge) and passes through primary and secondary roaster cyclones. A damper on the emergency vent stack before the off-gas train acts as a pressure relief for the roaster.

By evaporative cooling, the gas quencher reduces the temperature of the roaster off-gas and saturates the gas with water, resulting in higher efficiency dust scrubbing in the next step. The co-current spray of water into the gas flow also serves to remove the coarse fraction of the dust. The dust scrubber then decreases the amount of dust to a suitable level for the condenser and wet ESP inlet and further cools the gas stream. The water used at the quencher and scrubber is a combination of condensate from the downstream wet gas condenser, cooling tower blowdown and fresh water.

The roaster off-gas enters the quencher at 1,024F (979F including an allowance of 1,500 standard cubic feet per minute for infiltration air). A co-current spray of 300 gallons per minute of water saturates the gas and cools the stream to 180F. The quencher also serves to remove 50% of the dust, resulting in an underflow density of 6% w/w solids. The spray flowrate was chosen to achieve a reasonable underflow slurry density, while minimizing water consumption.

2 Lines 99.7% particulate removal efficiency The quenched gas stream then enters the dust scrubber. This is a venturi- type scrubber that cools the gas stream to 171 F while reducing the dust concentration to the required level. The dust scrubber pressure drop is 40 inches water gauge. The water addition rate to the scrubber is 680 gallons per minute of which 64% is recycled. An additional 30 gallons per minute is added to the dust scrubber mist eliminator. The dust scrubber underflow bleed flowrate is 300 gallons per minute for the base case and 450 gallons per minute for the design case when there is a higher solid loading in the roaster off-gas. The bleed flowrate was calculated to achieve a maximum underflow slurry density of 6% w/w solids. The use of underflow recycle minimizes fresh water consumption.

An emergency water tank provides gas cooling to protect process equipment from high temperatures during upset conditions, primarily power failures. Reclaim water is used to fill this tank when necessary.

The wet gas condenser is a shell and tube heat exchanger. Gas is in the tubes and cooling water is in the shell (counter-current flow), which is used to cool the off-gas to 94 F. This temperature is controlled to achieve the maximum recommended mercury outlet temperature of 104F. Gas subcooling (below 104F) is required by the condenser to account for the heat of compression added by the booster fan. This temperature satisfies the mercury scrubber performance specification and pre-cooling prevents water condensation in the mercury tower, which would result in a high chloride bleed stream. Cooling is also beneficial at this stage because it reduces the volume of the gas stream and hence the required size of downstream equipment, recovers water in the form of condensate that can be reused in the process and condenses the majority of the mercury from the gas stream. Fresh water is providing on an intermittent basis for washing the condenser tubes.

The condensate flows by gravity to the inner section of the condensate collection tank. This tank is designed to allow efficient separation of mercury by gravity settling. A weir divides the tank into an inner section and an outer section. Condensed mercury settles to the conical bottom of the inner section, from which it is drained by gravity to the mercury collection tank in the mercury recovery area. Condensate overflows to the outer section of the tank, where it is combined with blowdown from the gas scrubbing cooling tower, blowdown from the oxygen plant cooling tower and fresh water make-up. Water is pumped separately from the outer section of the tank to the gas quencher and the dust scrubber.

A mist eliminator removes entrained water droplets from the cooled gas prior to the booster fan. The gas pressure is raised to minus 1-inch water gauge by the booster fan. This keeps the wet electrostatic precipitator under slightly negative pressure, minimizing the amount of infiltration air drawn into the system. Gas sub-cooling (below 104F) is required by the condenser to account for the heat of compression added by the booster fan.

The wet ESP was specified for an inlet particulate loading of 0.45 grains per standard cubic foot design case. The design outlet particulate loading is 0.002 grains per cubic foot (5 milligrams per normal cubic meter).

The wet ESP was specified for an inlet acid mist of 0.50 grains per standard cubic foot base case and 1.17 grains per standard cubic foot design case. The design outlet acid mist loading is 0.0083 grains per standard cubic foot (20 milligrams per normal cubic meter)

As a minimum control requirement, mercury emissions from the roaster must be limited to less than 10 tons per year. The mercury scrubber reduces the level of Hg in the off-gas to 8 x 10.5 grains per standard cubic foot (0.2 milligrams per normal cubic foot). The mercury scrubber is a patented calomel countercurrent scrubber. An acidified solution of mercuric chloride is used to scrub the mercury vapor and produce calomel.

The mercury scrubber is a packed column using open structure packing. Mercuric chloride solution containing some solid calomel is recirculated around the scrubber. A bleed stream (5 to 10% of flow) is passed to the primary settling tank where calomel settles. The primary settling tank overflow, consisting of mercuric chloride solution, is returned to the mercury scrubber. A fresh water line is provided for dilution in the primary settling tank, as required. Mercuric chloride solution is also returned to the mercury scrubber from the mercuric chloride feed tank. This portion of the mercury recovery system operates continuously with the roaster off-gas flow. All other operations are batch, based on calomel and solution levels in the system.

The counter-current dual alkali SO2 scrubber has an overall sulfur dioxide removal efficiency of 99.95%. The discharge of SO2 (sulfur dioxide) to the atmosphere will not exceed 44.9 pounds per hour. The expected SO2 content of the off-gas is 35 parts per million for the base case and 709 parts per million for operation with ores containing higher sulfur levels.

A caustic solution of sodium sulfite is used to scrub the SO2 and produce a slightly acidic sodium bisulfite solution. The spent solution from the SO2 solution is sent to two regeneration tanks in series. Slaked lime is added to the solution to react with sodium bisulfite precipitating calcium sulfite and calcium sulfate and regenerate sodium sulfite scrubbing solution. Slaked lime is mixed with the spent solution in the smaller tank, and sufficient residence time for precipitation of crystalline calcium sulfite and calcium sulfate is provided in the larger second tank. Since high rates of scaling are expected in the first regeneration tank, a spare standby reactor allows operation when the other requires cleaning. The precipitated solids from the second regeneration are thickened to 25% w/w solids with flocculant addition and sent to the neutralization tanks. The thickener overflow enters an agitated tank, the regenerated solution tank, where it is mixed with fresh soda ash solution. Soda ash make-up is required due to sodium losses in the thickener underflow. A fresh water line is provided for make-up to the regenerated solution tank as required. The regeneratedsolution is then returned to the SO2 scrubbers, with a small side stream being diverted for preparation of the soda ash solution.

A mist eliminator removes entrained droplets of scrubbing solution from the gas prior to the exhaust fan. The gas pressure is raised to 12.5 inches water gauge by the exhaust fan. This makes allowance for the pressure drop across the CO indicator and catalytic NOx units prior to the stack.

After gas quenching, de-dusting, condensing, wet ESP, Mercury removal and SO2 removal, the off-gas is sent to the CO incinerator and heat recovery unit. The off gas is first pre-heated in a low NOx propane burner from a base case temperature of a 134F to 300F, which is above the acid dew point temperature. This prevents acid corrosion of the CO incinerator and heat recuperator where it is further heated to about 1400F with hot gas from the thermal oxidizer. The off-gas then enters the CO incinerator, where propane is burned in a low NOx burner to heat off-gas to the operating temperature of 1,650F. The efficiency of CO incineration is 98.5% which reduces the CO level of the off-gas to below the permitted level of 360 parts per million in accordance with air quality standards. The off-gas leaves the heat recuperator at 650F.

The level of the NOx in the off-gas is lowered to below the permitted level of 250 parts per million by use of a selective catalytic reduction (SCR) unit. The efficiency of NOx reduction is 75%. Aqueous ammonia, injected over a zeolite catalyst, vaporizes into the gas stream, where it reacts with the NOx to produce nitrogen gas and water vapor.

The SCR unit is designed with sufficient catalyst surface area to achieve a normal ammonia slip of 5 parts per million, and guaranteed maximum slip 10 parts per million ammonia. The off-gas from NOx SCR unit is then exhausted through a stack to the atmosphere.

As the offgas contacts the water droplets, most of the water is evaporated and the offgas is cooled. In the collection tank at the bottom of the tower, the offgas (now partially saturated with water vapor) makes a sharp turn before passing through a duct to the dust scrubber. Unevaporated water collects in the collection tank and forms a slurry with some of the particulate matter that was in the offgas. The water/particulate matter slurry flows downward through a pipe to the dust scrubber seal tank, then to the roaster calcine quench tank. The gas quencher and slurry transfer system must be monitored carefully to avoid calcium sulfate (CaSO4) scale buildup.

The overflow from the primary settling tank reports to the bottom of the tower The underflow is transferred periodically to the secondary-settling tank where it is held for several days to allow further settling. Gas leaving the tower out the top goes to the Sulfur Dioxide tower

The neutralization and CIL (carbon-in -leach) processes are two of many steps which much be properly performed to ensure the success of the roasting process. The ore processing activities (such as mining, grinding, and roasting) which occur before the neutralization and CIL process are expensive. The combined costs of these steps compose most of the total operating cost of operation, with no marketable product yet produced. Once the ore reaches the neutralization and CIL section of the plant, the operator must operate the plant in a manner that recovers the metal values from the calcined ore in order to achieve the economic goal of operation.

The gold contained in the ore occurs at an average of. 17 opt (ounces per ton of ore). The gold is within the sulfide mineral matrix, which is not exposed (and therefore can not be dissolved by) a cyanide leach solution. Also the ore contains carbonaceous matter which absorbs gold in the conventional leaching process. For these reasons, The ore is considered to be double refractory. Thus a pretreatment process is required to expose this gold and achieve an acceptable gold recovery by cyanide leaching: The most common pretreatment processes are roasting and acidic pressure leaching. These process oxidize the sulfide minerals, thereby leaving a residue from which the gold can be leached and recovered.

The ore feed rate to the roaster is designed to be 12,000 short tons per day (stpd) based on 90 percent availability. This results in a normal feed rate to the neutralization tanks of 550 tons per hour (tph) = 13,000 tpd.

Neutralization To increase the pH (alkalinity) of the incoming slurry to a pH of approximately 9.5 through the addition of slaked-lime slurry in preparation for cyanide leaching. Two tanks each 48 feet in diameter, 50 feet high, and fitted with a 150 horsepower agitator mechanism, with upper and lower impellers. Retention time 1.3 hours to 1.5 hours (12% solids) ( 15,700 GPM )

Quenched calcine from both of the quench tanks is pumped to a manifold feeding the first of two agitated neutralization tanks in series. The tanks provide sufficient residence time to neutralize any acidity with addition of slaked lime slurry. The target pH is 9.5 to prevent formation of hydrogen cyanide gas in the downstream leaching circuit. A rising pH profile is maintained from the quench tank to the neutralization tanks from as low as 3 to 9.5. During periods of high lime addition ahead of the roaster or when some of the high carbonate ores are being treated, this pH profile may be higher, that is from 8 to 9.5.

In addition, neutralization tanks provide sufficient time to reach equilibrium in terms of calcium sulfate content. Experience at other plants predicts a temporary super-saturation in calcium sulfate that can cause extreme scaling in equipment through the quench/neutralization system. It is preferable that this scaling occurs in the slurry while solids are present, since the solids act as seed particles to collect the scale in preference to associated equipment.

By passes are provided to allow each of the tanks to be taken out of service. Each tank overflows to the next and eventually to the calcine thickener. The tanks are emptied for maintenance or de-scaling using sump pumps, which directs material to the thickener deaeration tank.

The neutralization tanks are aerated by process air injection in order to oxidize and precipitate 3 ferrous iron and other metals. These metals consume sodium cyanide in the C.I.L. tanks. Therefore, by minimizing their concentration in solution, sodium cyanide consumption is minimized.

Neutralized calcine slurry is thickened to 40 to 45% w/w solids before being pumped to the leaching circuit. Flocculant is added to the thickener feedwell after an in-line dilution with thickener overflow to0.01% w/w. The thickener overflows into an overflow well from which it is pumped to the quench water cooling tower or to flocculant dilution. The cooling tower cools the overflow from approximately 110F to 70F.

Three cooling tower cells drain into separate cold wells, allowing each cell to be taken off-line for maintenance as required. Each cold well drain into a common cold well from which the cooled water is pumped back to the two calcine quench areas. Reclaim water is added to the common cold well as makeup to the cooling tower circuit.

Feed for the C.I.L. circuit is drawn from the calcine thickener. The tramp oversize material in the calcine thickener underflow is removed by vibrating screens. The screen undersize passes to a two-way splitter box prior to entering the C.I.L.

Slurry discharging from the last C.I.L. tank passes vibrating carbon safety screens and is then treated with A.B.S. for cyanide destruction. Detoxified tailings are pumped to the tailing pond for reuse as process water.

Carbon is advanced through the C.l.L. tanks on a shift basis. Loaded carbon (carbon loaded with gold up to 175 o.p.t.) from the first C.l.L. tank is sent to the existing carbon treatment plant for gold removal, electrowinning, refining, and carbon regeneration.

Thickened, neutralized calcine slurry at 40 to 45% w/w solids passes through four trash screens in parallel before entering a manifold that feeds the first tank in the C.I.L. circuit. Any oversize material caught by the trash screens, such as grit from the lime added in the neutralization circuit, flows by gravity to the cyanide destruction reactor with the aid of reclaim water sprays. Reclaim water is used as spray water for the trash screens.

Carbon, added to absorb the gold in solution, flows counter-current to the slurry through the C.I.L. circuit and is maintained in the slurry at a concentration of 12 grams per liter. The cyano-aurate complex loads onto the carbon to a gold content of 175 troy ounces Au per ton of carbon. The extent of gold dissolution is approximately 91%, including a 1-% loss of soluble gold in the slurry sent to tailings, for an overall recovery of 90%.

Sodium cyanide solution (30%) is added as required in the C.I.L. tanks, one through five, at a rate of one pound of NaCN per ton of dry ore. In addition to gold leaching, cyanide is also consumed by the leaching of other metals. The target concentration of weak acid dissociable cyanide (CN wad) in the discharge is 60 parts per million. There is a provision for the addition of slaked lime to each of the six tanks in order to achieve the target operation pH of 9.5 in each tank. This ensures operation with protective alkalinity, to prevent the production of hydrogen cyanide gas. Oxygen required for the leach reactions is provided by process air injection at a rate of 5 standard cubic feet per minute per 1,000 cubic feet of tank volume.

Slurry is added to the first C.I.L. tank and carbon is added to the sixth tank in order to achieve countercurrent flow. Slurry from each tank overflows to the next tank through two interstage carbon retention screens operating in parallel, which separate carbon to prevent it from moving co-currently with the slurry. A vertical, recessed impeller pump is located in each tank to transfer the carbon-containing slurry to the previous tank. The screens are sized to handle the slurry flowrate plus the slurry recirculated due to counter-current carbon advance.

As with the neutralization tanks, bypass lines are provided to allow each tank to be taken off-line for maintenance with the use of manually placed spools. Bypass lines are also provided for each carbon transfer pump. The tanks are emptied for maintenance using the sump pump, which directs material to the feed line upstream of the trash screens.

A tower mill consists of a stationary vertical cylindrical body with a rotating screw, or auger, which extends from the top of the mill body almost to the bottom. The auger rotates at a slow speed and circulates a charge of grinding balls inside the mill.

The lime is mixed with reclaim water at the inlet to the mill. As more and more lime/water mixture enters the mill, coarse lime particles, which have not completely reacted with the water, have a tendency to settle out of the mixture and fall toward the bottom of the mill. The auger and the ball charge continue to mix the lime and reclaim water in the bottom of the mill, and the ball charge acts to grind up large particles of lime to allow it to finish reacting with the reclaim water and produce a consistent milk of lime slurry.

Six Tanks, 48 foot diameter 150 hp agitators Interstage screens-Kemix MPS 800, 2 per tank Carbon striped and regenerated at existing facility INCO/Air cyanide destruct with Ammonium bi-sulfite Three sets of tails pumps. Three per line

Current client requirements for treating low grade complex gold ores have challenged Lurgi to develop new technology. This technology, which is based on over 50 years of fluid bed roasting experience, utilizes Lurgis circulating fluid bed (CFB) to treat gold-bearing whole ores and/or concentrates while achieving high gold recovery.

The variety of the chemistry and mineralogy of different gold bearing ores requires professional pilot tests to establish the basis for flowsheets with the necessary flexibility to achieve satisfactory operation and good metallurgical results.

The roasting of gold-bearing minerals is often the first step in the metallurgical process of gold recovery. Sulfur removal and carbon burn-out are essential and in some cases where arsenic is present, the latter has to be efficiently removed in order to obtain acceptable gold recovery in the subsequent calcine leaching steps and to protect the environment.

It is characteristic of the roasting of gold-containing ores that the highest recoveries are obtained within a rather narrow range of roasting temperatures and oxygen partial pressure in the roaster gas. Ores of sufficient sulfur and carbon content can be treated autothermally. Some ores with low sulfur and carbon contents call for additional heating in order to maintain the roasting reaction.

At Cortez Gold Mines in Nevada, the first Lurgi CFB roaster for whole ore roasting has been installed for calcining 90 st/h of gold bearing refractory ore. The ore contains 1.1% sulfide sulfur, 1.1% organic carbon and 2.9% carbonate carbon on average. The limestone introduced to the process with the ore reacts with the SO2 forming gypsum. At a reactor temperature between 680 C and 720 C, SO2 concentrations of about 100 vppm were measured in the off-gas. There was no need for an installation of an SO2 treatment plant.

The plant was commissioned in 1990. The achieved gold recoveries were in the range of 82%. The roaster has been shut down for modifications to the dry grinding plant in order to receive material from new mines. Lurgi has in parallel tested these materials from the new mines in order to optimize the roaster operation in preparation of these materials becoming available.

cip system, cip process, cip gold processing - xinhai

cip system, cip process, cip gold processing - xinhai

[Introduction]: Gold CIP process adsorbs gold from cyaniding pulp by active carbon including 7 steps: leaching pulp preparation, cyaniding leaching, carbon adsorption, gold loaded carbon desorption, pregnant solution electrodeposit, carbon acid regeneration and leaching pulp.

metallurgical test work: gold processingoptions, physical ore properties, and cyanide management - sciencedirect

metallurgical test work: gold processingoptions, physical ore properties, and cyanide management - sciencedirect

This chapter presents an overview of the test work options available today in the modern metallurgical laboratory. Processing of gold ores has become a site-specific choice of techniques and processes, depending upon mineralogical, chemical, physical, and metallurgical factors. Knowledge of these is therefore important in the formulation of test work for any gold operation. This has led to significant changes in the test work methodology and philosophies that are now in general practice throughout the major gold mining countries. As engineering companies became familiar with gold ore processing and computer modeling became more sophisticated, the need for extensive pilot testing of the carbon-in-pulp process, for example, has largely disappeared. The use of refractory ore treatment options, however, such as bacterial leaching or pressure oxidation, would normally mean that pilot testing of these options is still required. Other aspects of gold mining have also become more important, including more pro-active cyanide management plans.

John E. Angove had been General Manager of SGS Lakefield Oretest Pty Ltd, a metallurgical testwork laboratory, from 1993 until retirement in 2006. He is now doing consulting work with AFT Metallurgy. Prior to this he worked as a metallurgist at Ammtec Ltd and Mt Newman Mining Company/BHP Iron Ore. He obtained a B.App.Sc. (Metallurgy) from Curtin University of Technology in 1978.

He is co-inventor of the Activox oxidation process for gold and base-metal sulfide concentrates. Mr Angove retains a keen interest in SAG milling, refractory oreprocessing, ultra-fine milling, pressure-oxidative leaching of gold and base metals, iron ore test philosophy and procedures, and industry-standard physical testing procedures.

Sevket Acar had worked for Newmont Metallurgical Services from 1985 until his retirement on April 1, 2015. He obtained a B.Sci (Mining) in 1975, M.Sci (Mineral Processing) in 1977, both from Technical University of Istanbul, Turkey, and D. E. Sci (Surface Chemistry and Chemical Metallurgy) in 1985 from Columbia University, USA. His interest is in all aspects of gold metallurgy from testing to plant design and operations troubleshooting.

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