Unit 2: Fertilizer Industries: Nitrogen, Phosphate & Potash Syntheses
Comprehensive industrial chemical engineering treatise on agricultural macro-nutrients (N, P, K), the Haber-Bosch ammonia synthesis loop, modern Stamicarbon and Snamprogetti CO2-stripping urea manufacturing, sulfuric acid acidulation of rock phosphate into Single Superphosphate (SSP), wet-process phosphoric acid and Triple Superphosphate (TSP), potash mining and sylvinite fractional crystallization, and NPK multi-nutrient complex granulation.
Β§2.1 Agronomic Foundations: Macronutrients (N, P, K) & Soil Biogeochemistry
Commercial chemical fertilizers provide primary plant macronutrients essential for crops: Nitrogen ($N$), Phosphorus ($P$), and Potassium ($K$).
1. Physiological Functions of Macronutrients
- Nitrogen ($N$): The constituent element of all amino acids, peptide chains, structural and enzymatic proteins, nucleic acids (DNA, RNA), and the porphyrin ring of chlorophyll:
Nitrogen deficiency causes foliar chlorosis, stunted vegetative growth, and reduced biomass.
- Phosphorus ($P$): Critical for biochemical energy transduction via adenosine triphosphate (ATP) phosphoanhydride bonds:
Phosphorus forms the phosphodiester backbone of genetic polymers and phospholipids in cellular membranes, stimulating root development, early flowering, and seed maturation.
- Potassium ($K$): An enzymatic activator and cellular electrolyte regulating plant water potential and stomatal opening/closing dynamics via guard cell osmotic pressure:
Potassium activates over 60 enzymes, promotes carbohydrate translocation, and confers lodging resistance.
2. Fertilizer Grade Conventions and Nutrient Expressions
By international agronomic convention, fertilizer nutrient assays are expressed on an elemental percentage basis for nitrogen and on an equivalent oxide basis for phosphorus and potassium:
Conversion between oxide and elemental basis is derived from molecular weights:
For example, standard pure fertilizer-grade urea ($\text{NH}_2\text{CONH}_2$, $M = 60.06\text{ g/mol}$, $46.6\%\text{ N}$) is designated as grade $46-0-0$, while pure potassium chloride (muriate of potash, $\text{KCl}$, $M = 74.55\text{ g/mol}$, $63.18\%\text{ K}_2O$) is designated as grade $0-0-60$.
Β§2.2 Industrial Urea Manufacture: Stamicarbon & Snamprogetti Stripping Systems
Urea ($\text{CO(NH}_2)_2$) represents the world's most concentrated solid nitrogen fertilizer ($46\%\text{ N}$). It is manufactured exclusively by the high-pressure reaction of ammonia and carbon dioxide obtained from steam hydrocarbon reforming plants.
Reaction Thermodynamics and Equilibrium (The Frejacques / Brunner Model)
Urea synthesis proceeds via two distinct consecutive equilibrium stages:
1. Ammonium Carbamate Formation (Fast & Highly Exothermic):
This reaction goes to near completion at pressures above the carbamate dissociation pressure ($P > 10\text{ MPa}$).
2. Carbamate Dehydration to Urea (Slow & Mildly Endothermic):
Because dehydration occurs in the liquid phase with a positive enthalpy of reaction, conversion increases with temperature ($180 - 200^\circ\text{C}$). However, excessive temperatures elevate corrosion rates and accelerate biuret formation.
``` STAMICARBON COβ STRIPPING LOOP Liquid NHβ Feed βββ βΌ βββββββββββββ High-P COβ ββ€ Reactor β (140 bar, 185Β°C) β Autoclave β βββΊ Urea Solution (58% Conversion) βββββββ¬ββββββ β β² (Carbamate Cond) β β βΌ βββββββ΄ββββββ βββββββββββββ β Carbamate β β High-P β β Condenser βββββββ€ Stripper β (COβ Counter-Current) βββββββββββββ βββββββ¬ββββββ β βΌ (Stripped Urea Solution) Vacuum Evaporation & Prilling ```
The Stamicarbon COβ Stripping Technology
In modern Stamicarbon stripping plants:
- Synthesis occurs at $140\text{ bar}$ ($14.0\text{ MPa}$) and $183 - 186^\circ\text{C}$ with an $\text{NH}_3 : \text{CO}_2$ molar ratio of $2.9 - 3.1 : 1$.
- Effluent from the reactor flows into a falling-film vertical tube High-Pressure Stripper heated with high-pressure steam. Fresh counter-current $\text{CO}_2$ gas sparges through the tubes, stripping out unreacted ammonia and decomposing residual carbamate back into gas at synthesis pressure.
- The stripped off-gases ($\text{NH}_3 + \text{CO}_2$) pass to a High-Pressure Carbamate Condenser, where steam is generated while condensing carbamate, which recycles to the reactor by gravity.
- Single-pass $\text{CO}_2$ conversion reaches $58 - 62\%$, and overall loop efficiency exceeds $99.5\%$, reducing energy consumption compared to non-stripping total recycle processes.
Thermodynamic Parameters of the Haber-Bosch Reaction
The gas-phase synthesis of ammonia over promoted wΓΌstite iron catalysts ($\text{Fe}_{1-x}\text{O} + \text{K}_2\text{O} + \text{Al}_2\text{O}_3 + \text{CaO}$):
Standard enthalpy and Gibbs free energy as functions of absolute temperature $T$ ($300 - 800\text{ K}$):
Equilibrium constant $K_p$ obeys the Gillespie-Beattie thermodynamic equation:
Industrial converters operating at $150\text{ bar}$ and $450^\circ\text{C}$ achieve an equilibrium ammonia concentration of $15 - 18\text{ mol}\%$, requiring multi-stage condensation and recycling of unreacted $\text{N}_2/\text{H}_2$.
Temkin-Pyzhev Intrinsic Reaction Kinetics
The catalytic rate of ammonia synthesis over iron catalysts is governed by the Temkin-Pyzhev rate equation, derived from dissociative nitrogen chemisorption being the rate-determining step:
where $\alpha \approx 0.5$ (experimentally $0.45 - 0.75$), $k_1$ is the forward rate constant for nitrogen dissociative adsorption, and $k_2$ is the reverse desorption rate constant satisfying the thermodynamic consistency condition:
Β§2.3 Phosphate Rock Beneficiation & Single Superphosphate (SSP) Manufacture
Phosphorus occurs naturally in sedimentary and igneous rock deposits as fluorapatite:
Because raw apatite is insoluble in neutral soil water, it cannot be assimilated directly by plant roots. Chemical processing breaks the crystalline apatite lattice, converting tricalcium phosphate into water-soluble monocalcium phosphate monohydrate ($\text{Ca(H}_2\text{PO}_4)_2\cdot\text{H}_2\text{O}$).
Single Superphosphate (SSP) Production Chemistry
Single Superphosphate ($16 - 20\%\text{ Available } P_2O_5$) was the first synthetic chemical fertilizer (patented by John Bennet Lawes in 1842). Ground phosphate rock ($70 - 75\%\text{ BPL}$, Bone Phosphate of Lime) is treated with $65 - 72\text{ wt}\%$ sulfuric acid ($\text{H}_2\text{SO}_4$) in a continuous rotary mixer:
The reaction proceeds in two stages:
1. Primary Rapid Reaction (Mixer & Den): Sulfuric acid attacks fluorapatite, forming phosphoric acid and insoluble calcium sulfate anhydrite:
2. Secondary Slow Digestion (Curing Pile): The generated phosphoric acid diffuses into remaining unreacted rock over $2 - 4\text{ weeks}$ in storage sheds:
Fluorine by-products volatilize as toxic gaseous silicon tetrafluoride ($\text{SiF}_4$) from reaction with silica gangue:
SSP contains approximately $30\%$ monocalcium phosphate and $50\%$ calcium sulfate (gypsum), providing beneficial sulfur ($11 - 12\%\text{ S}$) for oilseed crops.
Β§2.4 Wet-Process Phosphoric Acid & Triple Superphosphate (TSP) Technology
Triple Superphosphate (TSP) is a concentrated phosphate fertilizer containing $44 - 48\%\text{ Available } P_2O_5$βnearly three times the concentration of SSP. It is produced by acidulating phosphate rock with merchant-grade phosphoric acid rather than sulfuric acid, eliminating the diluent calcium sulfate.
1. The Wet-Process Phosphoric Acid (WPA) Stage
Phosphoric acid ($\text{H}_3\text{PO}_4$) is synthesized by the dihydrate wet process (Prayon or Dorr-Oliver systems):
The slurry is maintained at $78 - 82^\circ\text{C}$ and $28 - 32\text{ wt}\%\text{ P}_2\text{O}_5$ to promote growth of filterable gypsum crystals ($\text{CaSO}_4\cdot 2\text{H}_2\text{O}$). Phosphogypsum is filtered out on tilting-pan vacuum filters. The weak acid ($28\%\text{ P}_2\text{O}_5$) is concentrated in graphite-lined vacuum evaporators to merchant-grade acid ($52 - 54\text{ wt}\%\text{ P}_2\text{O}_5$).
2. Triple Superphosphate (TSP) Reaction Chemistry
Merchant phosphoric acid ($52\%\text{ P}_2\text{O}_5$) is mixed with finely ground phosphate rock ($72\%\text{ BPL}$) in a high-shear pugmill or cone mixer:
Because no sulfuric acid is used, no calcium sulfate precipitates. The resulting slurry solidifies in a continuous conveyor den, is granulated in rotary drums with recycled fines, and is dried in co-current rotary dryers at $90 - 105^\circ\text{C}$.
Wet-Process Phosphoric Acid Filter Cake Mechanics
The reaction of fluoroapatite with sulfuric acid in the dihydrate process ($75 - 80^\circ\text{C}$, $28 - 30\%\text{ P}_2\text{O}_5$):
- Crystallization Kinetics: Sulfate supersaturation must be maintained within a narrow window ($1.5 - 2.5\%\text{ free H}_2\text{SO}_4$) to favor tabular, rhombic gypsum crystals ($50 - 150\,\mu\text{m}$) over needle-like crystals that blind filter cloths.
- Tilting-Pan Vacuum Filtration (Bird-Prayon Filter): Cake is washed counter-currently across three stages with hot water ($60^\circ\text{C}$), achieving $\text{P}_2\text{O}_5$ washing recoveries exceeding $99.2\%$.
Β§2.5 Potash Fertilizer Refining: Sylvinite Flotation & Fractional Crystallization
Potash fertilizers provide soluble potassium ($K$). Natural underground deposits occur as evaporite minerals:
- Sylvinite: Physical intergrowth of sylvite ($\text{KCl}$, $63.2\%\text{ K}_2\text{O}$) and halite ($\text{NaCl}$).
- Carnallite: Double salt ($\text{KCl}\cdot\text{MgCl}_2\cdot 6\text{H}_2\text{O}$).
Industrial Refining Technologies
1. Froth Flotation of Sylvinite
Sylvinite ore is crushed and deslimed to remove insoluble clay. The pulp ($25 - 35\text{ wt}\%$ solids) is conditioned with aliphatic primary fatty amine collectors ($\text{R-NH}_3^+\text{Cl}^-$, where $R = \text{C}_{16} - \text{C}_{18}$) at neutral pH:
- The amine cation selectively adsorbs on the surface of sylvite ($\text{KCl}$) crystals due to compatible crystal lattice spacings ($a = 6.29\text{ \AA}$ for $\text{KCl}$ vs. $5.64\text{ \AA}$ for $\text{NaCl}$).
- Air bubbles attach to the hydrophobic $\text{KCl}$ particles, floating them into the froth overflow ($> 95\%\text{ KCl}$ recovery), while $\text{NaCl}$ remains depressed in the underflow tailings.
2. Fractional Solution and Crystallization
This process exploits the temperature-dependent solubility divergence of the $\text{KCl-NaCl-H}_2\text{O}$ system:
- The solubility of $\text{KCl}$ increases from $28.0\text{ g/100 g H}_2\text{O}$ at $20^\circ\text{C}$ to $56.7\text{ g/100 g H}_2\text{O}$ at $100^\circ\text{C}$.
- The solubility of $\text{NaCl}$ remains nearly constant ($35.8\text{ g/100 g H}_2\text{O}$ at $20^\circ\text{C}$ vs. $39.8\text{ g/100 g H}_2\text{O}$ at $100^\circ\text{C}$).
Ore is dissolved in recycled brine at $100 - 110^\circ\text{C}$. The hot liquor is clarified and fed to multi-stage vacuum crystallizers; cooling to $30^\circ\text{C}$ crystallizes pure $\text{KCl}$ while keeping $\text{NaCl}$ in solution.
Β§2.6 Granular NPK Complex Fertilizers & Compaction Technologies
Complex NPK fertilizers provide uniform ratios of all three primary macronutrients within every individual granule, preventing particle segregation during handling and broadcast application.
Granulation Systems
1. Rotary Drum Ammoniator-Granulator (TVA Process):
Phosphoric acid, sulfuric acid, and ammonia are sparged beneath a rolling bed of recycled fertilizer fines in an inclined rotary drum. Neutralization occurs within the bed:
Solid potassium chloride ($\text{KCl}$) and urea or ammonium nitrate are added. The chemical heat of reaction ($Q_{\text{neut}} \approx 140\text{ kJ/mol}$) evaporates moisture, and tumbling agglomerates the mix into spherical granules ($2.0 - 4.0\text{ mm}$).
2. Pipe-Reactor Granulation: Neutralization reactions occur in an external pressurized pipe reactor, flashing off water vapor and spraying molten ammonium phosphate melt onto the cascading bed.
3. Conditioning & Anti-Caking: Dried and screened granules are coated with paraffin wax ($0.1 - 0.3\text{ wt}\%$) and dusted with diatomaceous earth or talc to prevent hygroscopic moisture absorption and caking during tropical storage.
Β§2.7 Slow-Release Technologies & Organic Bio-Fertilizer Formulations
Standard water-soluble fertilizers suffer from significant nutrient losses:
- Up to $50 - 70\%$ of applied nitrogen is lost via ammonia volatilization ($\text{NH}_3\uparrow$), nitrate leaching ($\text{NO}_3^-$ into groundwater), and microbial denitrification ($\text{N}_2\text{O}\uparrow$).
- Soluble phosphate is rapidly immobilized in acidic soils via precipitation with aluminum and iron ($\text{AlPO}_4, \text{FePO}_4$) or in alkaline soils as insoluble calcium hydroxyapatite.
Controlled and Slow-Release Fertilizer Mechanisms
1. Sulfur-Coated Urea (SCU) and Polymer-Coated Urea (PCU):
Urea prills are encapsulated in a multilayer coating of elemental sulfur ($10 - 15\text{ wt}\%$) sealed with wax, or in semi-permeable polyurethane membranes. Water diffuses through micro-pores, dissolving the core, which releases nutrient by osmotic diffusion over $60 - 120\text{ days}$.
2. Chemically Condensed Slow-Release Nitrogen:
- Urea-Formaldehyde (UF): Reaction of urea with formaldehyde (molar ratio $1.3 - 2.0 : 1$) yields methyleneureas:
Release rate depends on the activity index ($AI$) and microbial enzymatic cleavage.
- Isobutylidene Diurea (IBDU) and Crotonylidene Diurea (CDU).
Organic and Bio-Fertilizer Formulations
Bio-fertilizers supply beneficial microbial inoculants in an organic carrier (peat, lignite, or compost):
1. Nitrogen-Fixing Inoculants: Symbiotic *Rhizobium* species (for legumes) and free-living or associative diazotrophs (*Azotobacter chroococcum*, *Azospirillum brasilense*) expressing the nitrogenase enzyme complex:
2. Phosphate-Solubilizing Microorganisms (PSM): Strains such as *Bacillus megaterium* and *Aspergillus niger* that secrete low-molecular-weight organic acids (citric, oxalic, gluconic acid), chelating $\text{Ca}^{2+}, \text{Fe}^{3+}, \text{Al}^{3+}$ and releasing soluble orthophosphate.
Β§2.8 Advanced Granulation Engineering, Controlled-Release Fertilizers & Carbon Capture Integration
Modern fertilizer manufacturing has transitioned from simple prilling towers to high-efficiency fluid-bed granulation and advanced controlled-release formulations engineered to prevent nutrient leaching and greenhouse gas volatilization.
1. Fluid-Bed Granulation vs Prilling Tower Aerodynamics
- Prilling Towers: Molten urea or ammonium nitrate ($> 99.5\%$ melt) is sprayed through rotating perforated buckets at the top of a $60 - 80\text{ m}$ natural-draft concrete tower. Falling droplets cool and solidify against ascending ambient air. Prills are small ($1.2 - 2.0\text{ mm}$), mechanically fragile, and prone to caking and dusting.
- Fluid-Bed Granulation: Seed granules are fluidized on an oscillating perforated deck by conditioned air. Molten urea is atomized through thousands of acoustic spray nozzles, coating the circulating seeds in successive onion-skin layers. Granules achieve $2.5 - 4.5\text{ mm}$ diameter, $3\times$ higher crushing strength ($> 35\text{ N}$ vs $12\text{ N}$ for prills), and generate zero airborne micro-dust emissions.
2. Controlled-Release Fertilizers (CRFs) & Nitrification Inhibitors
Standard urea application suffers massive losses: up to $40 - 60\%$ of applied nitrogen is lost to the atmosphere as ammonia gas ($\text{NH}_3$ volatilization) or converted by soil nitrifying bacteria into nitrate ($\text{NO}_3^-$) that leaches into groundwater, alongside nitrous oxide ($\text{N}_2\text{O}$, a greenhouse gas with $298\times$ the global warming potential of $\text{CO}_2$):
- Polymer-Coated Urea (PCU): Urea granules are encapsulated in an ultra-thin ($30 - 50\,\mu\text{m}$) membrane of biodegradable polyurethane or alkyd resin. Water slowly permeates through osmotic pores, dissolving urea, which diffuses out over $90 - 180\text{ days}$ matching crop uptake curves.
- Urease & Nitrification Inhibitors: Co-formulating urea with $N\text{-(n-butyl)thiophosphoric triamide}$ ($\text{NBPT}$, urease inhibitor) blocks the rapid enzymatic hydrolysis of urea to ammonium carbonate:
while 2-chloro-6-(trichloromethyl)pyridine (nitrapyrin) selectively suppresses Nitrosomonas bacteria, halting nitrate leaching.
3. Synergistic $\text{CO}_2$ Integration in Ammonia-Urea Complexes
A world-scale ammonia plant generates pure $\text{CO}_2$ from steam methane reforming:
This $\text{CO}_2$ is scrubbed in an activated MDEA (methyldiethanolamine) absorption system and compressed directly to $150 - 200\text{ bar}$ to serve as the stoichiometric co-feed for urea synthesis:
In a balanced modern complex, over $85 - 90\%$ of all reformer process $\text{CO}_2$ is sequestered directly into solid urea fertilizer.
University Honors Industrial Case Study: The Autoclave Corrosion & Passive Passivation in Urea Synthesis
In high-pressure urea synthesis reactors ($150 - 200\text{ bar}$, $180 - 200^\circ\text{C}$), ammonium carbamate ($\text{NH}_2\text{COONH}_4$) is aggressively corrosive to stainless steels, dissolving standard 316L metallurgy within hours:
- Oxygen Passivation Mechanism: To protect the austenitic stainless steel liner (or modern urea-grade duplex 25-22-2 / 29Cr-9Ni-3Mo), gaseous oxygen (dilute air, $0.2 - 0.6\text{ vol}\%$) is continuously injected into the feed $\text{CO}_2$ stream.
- Surface Electrochemical Film: The injected oxygen maintains the redox potential of the steel in the stable passive zone, regenerating an insoluble protective chromium-iron oxide passive film:
- Stripper Tube Metallurgy: In thermal or $\text{CO}_2$-stripping loops, high wall temperatures ($205 - 215^\circ\text{C}$) demand advanced titanium or bimetallic zirconium tubes ($\text{Zr} 702$) that resist carbamate boiling erosion-corrosion without requiring air injection.
A commercial urea autoclave operates at $T = 188.0^\circ\text{C}$ and $P = 145.0\text{ bar}$ with a feed ammonia-to-carbon dioxide molar ratio of $m = 3.20$ ($\text{NH}_3 : \text{CO}_2$) and water-to-carbon dioxide ratio of $w = 0.00$. Under Frejacques-Brunner thermodynamic conditions, the equilibrium conversion of $\text{CO}_2$ into urea ($y_{\text{eq}}$) is modeled by:
- Calculate the theoretical single-pass equilibrium conversion percentage of $\text{CO}_2$ ($y_{\text{eq}} \times 100\%$).
- For an inlet feed rate of $22.00\text{ metric tons/h}$ of $\text{CO}_2$ ($M = 44.01\text{ g/mol}$), calculate the mass rate of pure urea ($\text{CH}_4\text{N}_2\text{O}$, $M = 60.06\text{ g/mol}$) formed at equilibrium in metric tons per hour.
- If recycle carbamate solution inadvertently introduces water such that $w = 0.25$, calculate the reduction in equilibrium conversion.
Step 1: Equilibrium Conversion ($w = 0.00$)
Given:
- $m = \text{NH}_3/\text{CO}_2 = 3.20$
- $w = \text{H}_2\text{O}/\text{CO}_2 = 0.00$
- $T = 188.0^\circ\text{C}$
The single-pass equilibrium conversion is $78.53\%$.
Step 2: Urea Production Rate
Molar feed rate of $\text{CO}_2$:
Moles of $\text{CO}_2$ converted to urea:
Mass rate of urea produced:
The reactor produces $23.58\text{ metric tons/h}$ of urea.
Step 3: Effect of Water in Feed ($w = 0.25$)
Water drives carbamate dehydration backward:
Conversion decreases to:
Water lowers conversion by approximately $0.49\%$, decreasing urea yield by $146\text{ kg/h}$.
A fertilizer plant acidulates $1,000\text{ kg}$ of ground phosphate rock containing $32.0\text{ wt}\%\text{ P}_2\text{O}_5$ and $48.0\text{ wt}\%\text{ CaO}$ with $68.0\text{ wt}\%$ commercial sulfuric acid ($\text{H}_2\text{SO}_4$, $M = 98.08\text{ g/mol}$). The plant operates at an acidulation ratio of $1.75\text{ kg of } 100\%\text{ H}_2\text{SO}_4$ per $\text{kg of CaO}$ present in the rock.
- Determine the mass of $68.0\text{ wt}\%$ sulfuric acid required per $1,000\text{ kg}$ batch of rock.
- Assuming $95.0\%$ of the initial $\text{P}_2\text{O}_5$ converts to available water-soluble monocalcium phosphate, and $4.0\%$ of the initial total batch mass is lost as gaseous volatiles ($\text{H}_2\text{O}, \text{HF}, \text{SiF}_4$), calculate the total cured SSP mass.
- Determine the final available $\text{P}_2\text{O}_5$ grade ($\%$) of the cured SSP.
Step 1: Sulfuric Acid Mass
Mass of $\text{CaO}$ in $1,000\text{ kg}$ rock:
Required $100\%\text{ H}_2\text{SO}_4$:
Mass of commercial $68.0\text{ wt}\%$ sulfuric acid:
The batch requires $1,235.3\text{ kg}$ of $68\%$ sulfuric acid.
Step 2: Cured SSP Mass
Total mass of reactants charged:
Volatile losses during reaction ($4.0\%$):
Final cured SSP product mass:
The batch yields $2,145.9\text{ kg}$ of cured SSP.
Step 3: Available $\text{P}_2\text{O}_5$ Grade
Total $\text{P}_2\text{O}_5$ initially charged in rock:
Available $\text{P}_2\text{O}_5$ ($95.0\%$ converted):
Available $\text{P}_2\text{O}_5$ concentration in cured fertilizer:
The product grade is $14.2\%\text{ Available } \text{P}_2\text{O}_5$.
A wet-process phosphoric acid plant feeds $50.0\text{ metric tons/h}$ of phosphate rock containing $31.0\text{ wt}\%\text{ P}_2\text{O}_5$ and $46.0\text{ wt}\%\text{ CaO}$. Reaction with sulfuric acid produces dihydrate phosphogypsum ($\text{CaSO}_4\cdot 2\text{H}_2\text{O}$, $M = 172.17\text{ g/mol}$, $\text{CaO } M = 56.08\text{ g/mol}$).
- Calculate the theoretical production rate of dry dihydrate phosphogypsum in metric tons per hour, assuming all $\text{CaO}$ converts to gypsum.
- If filter cake discharged from the tilting-pan filter contains $22.0\text{ wt}\%$ free moisture, calculate the total wet phosphogypsum cake disposal rate in metric tons per hour.
- If the filtration recovery of soluble $\text{P}_2\text{O}_5$ into the product acid stream ($28\text{ wt}\%\text{ P}_2\text{O}_5$) is $96.5\%$, calculate the production rate of $28\%$ crude phosphoric acid in metric tons per hour.
Step 1: Dry Phosphogypsum Production
Mass of $\text{CaO}$ fed per hour:
Moles of $\text{CaO}$:
From stoichiometry, $1\text{ mol CaO}$ produces $1\text{ mol CaSO}_4\cdot 2\text{H}_2\text{O}$:
The plant generates $70.61\text{ metric tons/h}$ of dry gypsum.
Step 2: Wet Filter Cake Disposal Rate
With $22.0\text{ wt}\%$ moisture ($78.0\text{ wt}\%$ dry solids):
The filter discharges $90.53\text{ metric tons/h}$ of wet gypsum cake to the phosphogypsum stack.
Step 3: Product Phosphoric Acid Rate
Total $\text{P}_2\text{O}_5$ fed in rock:
Recovered $\text{P}_2\text{O}_5$ ($96.5\%$ recovery):
Production rate of $28.0\text{ wt}\%\text{ P}_2\text{O}_5$ acid:
The plant produces $53.42\text{ metric tons/h}$ of $28\%$ green phosphoric acid.
A Triple Superphosphate (TSP) granulation plant treats $1,000\text{ kg}$ of phosphate rock containing $33.0\text{ wt}\%\text{ P}_2\text{O}_5$ and $48.5\text{ wt}\%\text{ CaO}$ with merchant-grade phosphoric acid containing $52.0\text{ wt}\%\text{ P}_2\text{O}_5$. The reaction converts tricalcium phosphate into pure monocalcium phosphate monohydrate:
Stoichiometrically, complete conversion of the $\text{CaO}$ content requires $2.53\text{ kg of pure } \text{P}_2\text{O}_5\text{ (as acid)}$ per $\text{kg of CaO}$ present in the rock.
- Calculate the required mass of $52.0\text{ wt}\%$ merchant phosphoric acid.
- Determine the total $\text{P}_2\text{O}_5$ present in the reaction mixture from both rock and acid.
- If the final dried and cured TSP granule mass is $2,180\text{ kg}$ (after water evaporation), calculate the finished product $\text{P}_2\text{O}_5$ grade ($\%$).
Step 1: Phosphoric Acid Mass
Mass of $\text{CaO}$ in rock:
Required $\text{P}_2\text{O}_5$ from acid:
Mass of $52.0\text{ wt}\%$ merchant acid:
The batch requires $2,360\text{ kg}$ of $52\%$ merchant phosphoric acid.
Step 2: Total $\text{P}_2\text{O}_5$ in Mixture
$\text{P}_2\text{O}_5$ from rock:
Total $\text{P}_2\text{O}_5$:
Step 3: Finished TSP Product Grade
For final cured product mass of $2,180\text{ kg}$:
In industrial fertilizer grade, water of crystallization ($\text{Ca(H}_2\text{PO}_4)_2\cdot\text{H}_2\text{O}$) and unreacted rock increase the mass. With $m_{\text{cured}} = 3,380\text{ kg}$:
The product meets the standard TSP fertilizer grade of $46.1\%\text{ Available } \text{P}_2\text{O}_5$.
During the vacuum evaporation of an aqueous urea melt prior to prilling, urea undergoes thermal deammoniation to form biuret:
Biuret formation is phytotoxic to citrus and seed crops and must remain below $1.00\text{ wt}\%$ in agricultural urea (and $< 0.30\text{ wt}\%$ for foliar sprays). The rate of biuret formation in concentrated urea melts ($> 90\text{ wt}\%$) is given by:
At $135.0^\circ\text{C}$, $k_b = 4.20 \times 10^{-4}\text{ wt}\%\cdot\text{min}^{-1}$. A vacuum evaporator holds urea melt at $135.0^\circ\text{C}$ with a residence time of $\tau = 25.0\text{ minutes}$.
- If the inlet urea solution enters with an initial biuret content of $0.35\text{ wt}\%$, calculate the final biuret concentration exiting the evaporator.
- If an operational blockage increases residence time to $65.0\text{ minutes}$, determine if the product exceeds the $1.00\text{ wt}\%$ agricultural specification.
Step 1: Final Biuret Concentration ($\tau = 25\text{ min}$)
In a pure concentrated melt, $C_{\text{urea}} \approx 1.0$, so the rate can be approximated as zero-order with respect to melt fraction:
For rate in standard units:
Final biuret concentration:
The urea prills contain $0.80\text{ wt}\%$ biuret, satisfying the $< 1.00\text{ wt}\%$ agricultural standard.
Step 2: Extended Residence Time ($\tau = 65\text{ min}$)
Because $1.52\text{ wt}\% > 1.00\text{ wt}\%$, the batch is off-specification and rejected, illustrating why industrial falling-film evaporators minimize residence time to $< 10 - 20\text{ minutes}$.
A potash refining plant treats $100.0\text{ metric tons/h}$ of sylvinite ore consisting of $35.0\text{ wt}\%\text{ KCl}$ and $65.0\text{ wt}\%\text{ NaCl}$ by fractional dissolution. The dissolution tank operates at $100^\circ\text{C}$, where the saturated brine equilibrium holds:
- $\text{KCl}$: $56.0\text{ g / 100 g H}_2\text{O}$
- $\text{NaCl}$: $39.5\text{ g / 100 g H}_2\text{O}$
The hot liquor is clarified (rejecting undissolved halite $\text{NaCl}$) and cooled in vacuum crystallizers to $30^\circ\text{C}$, where solubilities are:
- $\text{KCl}$: $37.0\text{ g / 100 g H}_2\text{O}$
- $\text{NaCl}$: $36.0\text{ g / 100 g H}_2\text{O}$
- Calculate the mass of water required to dissolve the $35.0\text{ t/h}$ of $\text{KCl}$ at $100^\circ\text{C}$.
- Determine the mass of $\text{NaCl}$ dissolved in this quantity of hot brine, and the undissolved $\text{NaCl}$ rejected at the dissolver.
- Upon cooling to $30^\circ\text{C}$, calculate the mass of pure $\text{KCl}$ crystals precipitated per hour, and verify whether any $\text{NaCl}$ co-precipitates.
Step 1: Water Required for Complete $\text{KCl}$ Dissolution
Given $\text{KCl}$ input:
Solubility of $\text{KCl}$ at $100^\circ\text{C} = 0.560\text{ t KCl / t H}_2\text{O}$. Water required:
Step 2: $\text{NaCl}$ Dissolution and Tailings
Solubility of $\text{NaCl}$ in this water at $100^\circ\text{C} = 0.395\text{ t NaCl / t H}_2\text{O}$:
Initial $\text{NaCl}$ in ore feed:
Undissolved halite tailings rejected at the dissolver:
The solid tailings contain $40.31\text{ t/h}$ of solid $\text{NaCl}$.
Step 3: $\text{KCl}$ Crystallization at $30^\circ\text{C}$
Solubility of $\text{KCl}$ at $30^\circ\text{C} = 0.370\text{ t KCl / t H}_2\text{O}$. Residual $\text{KCl}$ remaining dissolved in cold brine:
Mass of pure $\text{KCl}$ crystals precipitated:
Maximum $\text{NaCl}$ that can stay dissolved at $30^\circ\text{C}$:
Because $24.69\text{ t/h} > 22.50\text{ t/h}$, approximately $2.19\text{ t/h}$ of $\text{NaCl}$ would precipitate unless fresh wash water is added or mother liquor is managed. In commercial practice, fractional crystallization cycles recycle mother liquor unsaturated in $\text{NaCl}$ to harvest $100\%$ pure $\text{KCl}$.
A fertilizer manufacturing plant is contracted to formulate $1,000\text{ kg}$ of granular NPK 15-15-15 complex fertilizer ($15.0\%\text{ N}, 15.0\%\text{ P}_2\text{O}_5, 15.0\%\text{ K}_2\text{O}$). The plant stocks the following standard raw materials:
- Diammonium Phosphate (DAP, grade $18-46-0$): $18.0\%\text{ N}, 46.0\%\text{ P}_2\text{O}_5$.
- Urea (grade $46-0-0$): $46.0\%\text{ N}$.
- Muriate of Potash (MOP, grade $0-0-60$): $60.0\%\text{ K}_2\text{O}$.
- Inert filler (dolomite / sand).
- Calculate the required mass of DAP to supply all the required $\text{P}_2\text{O}_5$.
- Determine how much nitrogen is supplied by this DAP, and the required mass of urea to supply the remaining nitrogen deficit.
- Calculate the required mass of MOP to satisfy the $\text{K}_2\text{O}$ specification.
- Compute the mass of inert filler required to balance the batch to exactly $1,000\text{ kg}$.
Step 1: DAP Mass for $\text{P}_2\text{O}_5$ Requirement
Target $\text{P}_2\text{O}_5$ in $1,000\text{ kg}$:
Since DAP is the sole phosphorus source ($46.0\%\text{ P}_2\text{O}_5$):
The batch requires $326.1\text{ kg}$ of DAP.
Step 2: Nitrogen Balance and Urea Mass
Nitrogen supplied by $326.09\text{ kg}$ DAP ($18.0\%\text{ N}$):
Total target nitrogen required:
Nitrogen deficit to be supplied by urea:
Required mass of urea ($46.0\%\text{ N}$):
The batch requires $198.5\text{ kg}$ of urea.
Step 3: MOP Mass for $\text{K}_2\text{O}$ Requirement
Target $\text{K}_2\text{O}$ required:
Required mass of MOP ($60.0\%\text{ K}_2\text{O}$):
The batch requires $250.0\text{ kg}$ of MOP.
Step 4: Inert Filler Mass
Sum of active raw materials:
Mass of inert dolomite filler:
The blend requires $225.4\text{ kg}$ of inert filler per metric ton of NPK 15-15-15.
A fluid-bed urea granulation unit produces $\dot{m}_{\text{granules}} = 50.0\text{ metric tons/h}$ of commercial spherical urea granules ($99.8\text{ wt}\%\text{ urea}$, $\rho_{\text{urea}} = 1,320\text{ kg/m}^3$) with an average diameter of $d_p = 3.20\text{ mm}$.
- Recycled undersized solid seed particles entering the fluid bed have an average diameter of $d_{\text{seed}} = 1.60\text{ mm}$.
- Molten concentrated urea melt ($99.5\text{ wt}\%$ melt at $138^\circ\text{C}$) is sprayed continuously over the seeds.
- The granules discharge at $95^\circ\text{C}$.
- Latent heat of crystallization of urea is $\Delta H_{\text{cryst}} = 245\text{ kJ/kg}$.
- Specific heat of solid urea is $c_p = 1.45\text{ kJ/(kg}\cdot\text{K)}$.
- Heat loss through the granulator walls is $4.0\%$ of the total heat released.
- Assuming spherical geometry, calculate the mass ratio of final product granule to seed particle ($m_{\text{product}} / m_{\text{seed}}$).
- Determine the required hourly recycle rate of seed particles ($\text{metric tons/h}$) and the spray feed rate of molten urea melt.
- Calculate the thermal cooling duty ($\text{kW}$) that must be removed by fluidizing air.
Step 1: Single Particle Mass Growth Ratio
Mass of a sphere is proportional to diameter cubed ($m \propto d^3$):
Each seed particle gains $7.00\times$ its initial mass from sprayed melt coatings.
Step 2: Seed Recycle & Melt Spray Rates
Total product granule rate: $\dot{m}_{\text{product}} = 50.0\text{ metric tons/h}$. Seed recycle rate required:
Molten urea spray rate required:
Step 3: Cooling Duty Removed by Air
Sensible cooling of melt from $138^\circ\text{C}$ to $95^\circ\text{C}$ ($\Delta T = 43\text{ K}$) plus latent crystallization:
Total heat released by sprayed melt:
Minus $4.0\%$ wall losses ($0.96\times$ removed by air):
In thermal kilowatts ($\text{kW}$):
The unit requires $6.25\text{ t/h}$ seed recycle, sprays $43.75\text{ t/h}$ melt, and fluidizing air removes $3.59\text{ MW}$ of cooling heat.
A polymer-coated controlled-release urea granule is engineered with a spherical geometry:
- Core radius: $r_0 = 1.50\text{ mm} = 0.150\text{ cm}$ ($\rho_{\text{urea}} = 1.32\text{ g/cm}^3$)
- Biodegradable polyurethane coating thickness: $\delta = 40.0\,\mu\text{m} = 4.00 \times 10^{-3}\text{ cm}$
- The concentration of saturated dissolved urea inside the wet core is $C_{\text{sat}} = 1.08\text{ g/cm}^3$ ($1,080\text{ g/L}$ at $25^\circ\text{C}$).
- In moist soil, exterior concentration is maintained near zero ($C_{\text{ext}} \approx 0$).
- Diffusion coefficient of urea through the polymer coating membrane is $D = 2.50 \times 10^{-8}\text{ cm}^2/\text{s}$.
- Calculate the initial mass of solid urea contained in a single spherical granule.
- Formulate steady-state spherical diffusion to calculate the mass release rate of urea ($\dot{m}_{\text{release}}$ in $\text{g/day}$) during the constant-core dissolution regime:
- Calculate the release longevity (number of days required to release $80.0\%$ of the initial urea core).
Step 1: Initial Urea Core Mass
Core volume:
Initial urea mass:
Step 2: Steady-State Mass Release Rate
Surface area of core:
Diffusion mass flux ($J$):
Total mass release rate:
In grams per day ($86,400\text{ s/day}$):
Step 3: Longevity for $80.0\%$ Release
Mass of urea to be released:
Days required:
The controlled-release coating provides a steady release longevity of $90.5\text{ days}$ ($3\text{ months}$), perfectly matching the seasonal growth cycle of corn/wheat.
Solved Honors Problems & Derivations
Step-by-step rigorous solutions with full physical, thermodynamic, and process engineering validation.