Air, Water and Solubility

65 soru

Soru 21Soru

Calculate the solubility in mol/dm3\text{mol/dm}^3 of sodium nitrate (NaNO3\text{NaNO}_3) at 25C25^\circ\text{C}, if 17.0 g17.0\text{ g} of the salt dissolves in 100.0 g100.0\text{ g} of water to form a saturated solution. [Relative atomic masses: Na=23,N=14,O=16\text{Na} = 23, \text{N} = 14, \text{O} = 16; density of water =1.0 g/cm3= 1.0\text{ g/cm}^3]

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Cevap: 2

Cevap

The solubility of sodium nitrate at 25C25^\circ\text{C} is 2.0 mol/dm32.0\text{ mol/dm}^3.
To find solubility in mol/dm3\text{mol/dm}^3, first convert 17.0 g17.0\text{ g} of NaNO3\text{NaNO}_3 into moles by dividing by its molar mass (85.0 g/mol85.0\text{ g/mol}), obtaining 0.20 mol0.20\text{ mol}. Next, convert 100.0 g100.0\text{ g} of water into volume, which equals 0.100 dm30.100\text{ dm}^3. Dividing 0.20 mol0.20\text{ mol} by 0.100 dm30.100\text{ dm}^3 yields 2.0 mol/dm32.0\text{ mol/dm}^3.

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1
Determine the molar mass of the solute (NaNO3\text{NaNO}_3)
Molar mass of NaNO3=23+14+(3×16)=85.0 g/mol\text{NaNO}_3 = 23 + 14 + (3 \times 16) = 85.0\text{ g/mol}
Molar mass is required to convert mass of solute to amount in moles.
2
Calculate the amount of NaNO3\text{NaNO}_3 in moles
Moles=17.0 g85.0 g/mol=0.20 mol\text{Moles} = \frac{17.0\text{ g}}{85.0\text{ g/mol}} = 0.20\text{ mol}
Solubility in mol/dm3\text{mol/dm}^3 measures the amount of solute in moles per cubic decimeter of solvent.
3
Convert the mass of solvent (water) to volume in dm3\text{dm}^3
100.0 g of water=100.0 cm3=0.100 dm3100.0\text{ g of water} = 100.0\text{ cm}^3 = 0.100\text{ dm}^3
Density of water is 1.0 g/cm31.0\text{ g/cm}^3, and 1000 cm3=1 dm31000\text{ cm}^3 = 1\text{ dm}^3.
4
Calculate the solubility in mol/dm3\text{mol/dm}^3
Solubility=0.20 mol0.100 dm3=2.0 mol/dm3\text{Solubility} = \frac{0.20\text{ mol}}{0.100\text{ dm}^3} = 2.0\text{ mol/dm}^3
Dividing the moles of solute by the volume of solvent in dm3\text{dm}^3 gives the concentration in mol/dm3\text{mol/dm}^3.

Anahtar Kavram

Solubility expressed in molar concentration (mol/dm³)
Soru 22Soru

A municipal water treatment facility processes raw river water containing fine colloidal clay particles, dissolved hydrogen sulfide, soluble iron(II) compounds, and harmful microorganisms. During the treatment process, the water is subjected to aeration, addition of potash alum, sedimentation, sand filtration, and chlorination. Which of the following statements correctly distinguishes the primary chemical roles of aeration and potash alum in this treatment sequence?

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Cevap: Aeration oxidizes soluble iron(II) compounds and expels dissolved foul-smelling gases, whereas potash alum induces coagulation of fine colloidal clay particles.

Cevap

Aeration oxidizes soluble iron(II) compounds and expels dissolved foul-smelling gases, whereas potash alum induces coagulation of fine colloidal clay particles.
In municipal water purification, aeration serves to bubble air through raw water, oxidizing dissolved iron(II) salts to insoluble iron(III) precipitates and stripping out dissolved volatile gases (such as hydrogen sulfide and carbon(IV) oxide). Potash alum (hydrated potassium aluminium tetraoxosulfate(VI)) supplies aluminium ions that coagulate fine suspended colloidal particles into larger flocs that readily settle out during sedimentation.

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1
Analyze the primary chemical and physical effects of aeration in municipal water treatment.
Aeration increases dissolved oxygen, which oxidizes soluble Fe2+\text{Fe}^{2+} ions to insoluble Fe(OH)3\text{Fe(OH)}_3 precipitates, while simultaneously purging volatile dissolved gases such as H2S\text{H}_2\text{S} and excess CO2\text{CO}_2.
Aeration targets volatile odorous compounds and oxidizable dissolved inorganic species.
2
Analyze the role of potash alum (KAl(SO4)212H2O\text{KAl(SO}_4\text{)}_2 \cdot 12\text{H}_2\text{O}) during water purification.
Potash alum dissociates to yield Al3+\text{Al}^{3+} ions, which neutralize the negative surface charges on microscopic colloidal clay particles, allowing them to coagulate and settle during sedimentation.
Colloidal suspensions will not settle naturally under gravity without chemical coagulation.
3
Evaluate the choices to distinguish these functions from water softening and sterilization.
Sterilization is achieved by chlorination, and water softening requires removal of Ca2+\text{Ca}^{2+} or Mg2+\text{Mg}^{2+} ions via chemical precipitation or ion exchange, confirming the statement regarding oxidation/gas expulsion for aeration and coagulation for alum.
Distinguishing municipal water treatment for domestic supply (removal of turbidity and pathogens) from water softening avoids common conceptual confusion.

Anahtar Kavram

Distinct roles of aeration (gas removal and oxidation) and coagulation (potash alum flocculation) in municipal water treatment
Soru 23Soru

The solubility of a salt YY (molar mass = 160 g mol1160\text{ g mol}^{-1}) in water is 2.5 mol dm32.5\text{ mol dm}^{-3} at 70C70^\circ\text{C} and 1.2 mol dm31.2\text{ mol dm}^{-3} at 30C30^\circ\text{C}. If 300 cm3300\text{ cm}^3 of a saturated solution of YY at 70C70^\circ\text{C} is cooled to 30C30^\circ\text{C}, what mass of salt YY will crystallize out of solution?

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Cevap: 62.4 g62.4\text{ g}

Cevap

The mass of salt YY that crystallizes out of solution is 62.4 g62.4\text{ g}.
The mass of salt precipitated is determined by taking the difference in molar solubility (2.51.2=1.3 mol dm32.5 - 1.2 = 1.3\text{ mol dm}^{-3}), multiplying by the volume fraction (300/1000=0.3 dm3300/1000 = 0.3\text{ dm}^3) to find the number of moles (0.39 mol0.39\text{ mol}), and then multiplying by the molar mass (160 g mol1160\text{ g mol}^{-1}) to obtain 62.4 g62.4\text{ g}.

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1
Determine the change in molar solubility upon cooling
ΔS=2.5 mol dm31.2 mol dm3=1.3 mol dm3\Delta S = 2.5\text{ mol dm}^{-3} - 1.2\text{ mol dm}^{-3} = 1.3\text{ mol dm}^{-3}
Solubility decreases as temperature drops, causing the excess solute to precipitate.
2
Calculate the amount in moles precipitated in 300 cm3300\text{ cm}^3 of solution
n=1.3 mol dm3×300 cm31000 cm3 dm3=0.39 moln = 1.3\text{ mol dm}^{-3} \times \frac{300\text{ cm}^3}{1000\text{ cm}^3\text{ dm}^{-3}} = 0.39\text{ mol}
The solution volume is 300 cm3300\text{ cm}^3 (0.3 dm30.3\text{ dm}^3), so the moles precipitated must be scaled from 1 dm31\text{ dm}^3.
3
Convert the moles precipitated to mass in grams
Mass=0.39 mol×160 g mol1=62.4 g\text{Mass} = 0.39\text{ mol} \times 160\text{ g mol}^{-1} = 62.4\text{ g}
Mass is found by multiplying the mole quantity by the given molar mass of the salt.

Anahtar Kavram

Solubility and Crystallization Calculations
Soru 24Soru

A 24.6 g24.6\text{ g} sample of hydrated magnesium tetraoxosulfate(VI), MgSO4xH2O\text{MgSO}_4 \cdot x\text{H}_2\text{O}, was heated strongly until all the water of crystallization was driven off, leaving behind 12.0 g12.0\text{ g} of anhydrous MgSO4\text{MgSO}_4. What is the value of xx? [Mg=24,S=32,O=16,H=1][\text{Mg} = 24, \text{S} = 32, \text{O} = 16, \text{H} = 1]

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Cevap: 7

Cevap

The value of xx is 7.
Heating the sample evaporates 12.6 g12.6\text{ g} of water of crystallization (24.6 g12.0 g24.6\text{ g} - 12.0\text{ g}). Converting the masses to moles gives 0.1 mol0.1\text{ mol} of anhydrous MgSO4\text{MgSO}_4 (12.0 g/120 g/mol12.0\text{ g} / 120\text{ g/mol}) and 0.7 mol0.7\text{ mol} of H2O\text{H}_2\text{O} (12.6 g/18 g/mol12.6\text{ g} / 18\text{ g/mol}). The mole ratio of water to salt is 0.7/0.1=70.7 / 0.1 = 7, which means x=7x = 7.

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1
Calculate the mass of water of crystallization lost during heating.
Mass of water = 24.6 g12.0 g=12.6 g24.6\text{ g} - 12.0\text{ g} = 12.6\text{ g}.
The decrease in mass after heating represents the mass of water driven off from the hydrated salt.
2
Determine the molar masses of MgSO4\text{MgSO}_4 and H2O\text{H}_2\text{O}.
Molar mass of MgSO4=24+32+(4×16)=120 g/mol\text{MgSO}_4 = 24 + 32 + (4 \times 16) = 120\text{ g/mol}; Molar mass of H2O=(2×1)+16=18 g/mol\text{H}_2\text{O} = (2 \times 1) + 16 = 18\text{ g/mol}.
Molar masses are required to convert the measured masses into chemical amounts (moles).
3
Calculate the number of moles of anhydrous salt and water.
Moles of MgSO4=12.0 g120 g/mol=0.1 mol\text{MgSO}_4 = \frac{12.0\text{ g}}{120\text{ g/mol}} = 0.1\text{ mol}; Moles of H2O=12.6 g18 g/mol=0.7 mol\text{H}_2\text{O} = \frac{12.6\text{ g}}{18\text{ g/mol}} = 0.7\text{ mol}.
The chemical formula stoichiometry is determined by the molar ratio of components.
4
Determine the mole ratio of water to anhydrous salt (xx).
x=Moles of H2OMoles of MgSO4=0.7 mol0.1 mol=7x = \frac{\text{Moles of } \text{H}_2\text{O}}{\text{Moles of } \text{MgSO}_4} = \frac{0.7\text{ mol}}{0.1\text{ mol}} = 7.
The coefficient xx is the integer ratio of moles of water of crystallization per mole of anhydrous salt.

Anahtar Kavram

Water of Crystallization Stoichiometry
Soru 25Soru

In an industrial plant, dry air is cooled to 200C-200^\circ\text{C} to form liquid air after removing carbon dioxide and water vapor. When this liquid air undergoes fractional distillation in a fractionating column as its temperature is slowly raised, which statement correctly identifies the constituent that boils off first and the rationale behind its separation?

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Cevap: Nitrogen boils off first at 196C-196^\circ\text{C} because it has a lower boiling point than argon and oxygen.

Cevap

Nitrogen boils off first at 196C-196^\circ\text{C} because it has the lowest boiling point among the main liquefied atmospheric constituents.
During the fractional distillation of liquid air, components separate according to their boiling points. As the column temperature warms up from 200C-200^\circ\text{C}, nitrogen (boiling point 196C-196^\circ\text{C}) reaches its boiling point first, vaporizes, and is collected at the top of the fractionating column.

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1
Identify the main liquefied components of air after pre-purification
Purified liquid air consists primarily of liquid nitrogen, argon, and liquid oxygen. Water vapor and carbon dioxide are removed prior to liquefaction to prevent clogging the equipment.
Water freezes at 0°C and carbon dioxide sublimes at -78.5°C, making them solids well above the liquefaction temperature of air (-200°C).
2
Compare the boiling points of the liquefied components
Nitrogen boils at 196C-196^\circ\text{C} (77 K), Argon boils at 186C-186^\circ\text{C} (87 K), and Oxygen boils at 183C-183^\circ\text{C} (90 K).
Lower boiling point values on the Celsius scale correspond to colder temperatures (e.g., -196°C is colder than -183°C).
3
Determine the distillation sequence as temperature rises from 200C-200^\circ\text{C}
Nitrogen reaches its boiling point first at 196C-196^\circ\text{C} and turns into gas, leaving argon and oxygen behind until further warming.
In fractional distillation, the liquid with the lowest boiling point boils off first at the top of the column.

Anahtar Kavram

Fractional Distillation of Liquid Air
Tahmini Süre:1m 30s
Soru 26Soru

A 250 cm3250\text{ cm}^3 sample of dry air is passed over excess heated phosphorus in a closed tube to remove all the oxygen gas present. Assuming oxygen constitutes 21%21\% by volume of dry air, what is the volume of the remaining gas mixture in cm3\text{cm}^3?

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Cevap: 197.5

Cevap

The volume of the remaining gas mixture is 197.5 cm3197.5\text{ cm}^3.
Because oxygen makes up 21%21\% by volume of dry air, a 250 cm3250\text{ cm}^3 sample contains 0.21×250 cm3=52.5 cm30.21 \times 250\text{ cm}^3 = 52.5\text{ cm}^3 of oxygen. Heated phosphorus reacts with all the oxygen to form solid phosphorus oxide, leaving behind 250 cm352.5 cm3=197.5 cm3250\text{ cm}^3 - 52.5\text{ cm}^3 = 197.5\text{ cm}^3 of unreacted gases.

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1
Calculate the volume of oxygen gas in the initial sample
52.5 cm352.5\text{ cm}^3
Oxygen makes up 21%21\% by volume of dry air, so 0.21×250 cm3=52.5 cm30.21 \times 250\text{ cm}^3 = 52.5\text{ cm}^3.
2
Determine the remaining gas volume after complete removal of oxygen
197.5 cm3197.5\text{ cm}^3
Phosphorus reacts completely with oxygen, leaving the unreacted components of air: 250 cm352.5 cm3=197.5 cm3250\text{ cm}^3 - 52.5\text{ cm}^3 = 197.5\text{ cm}^3.

Anahtar Kavram

Percentage composition of air by volume
Soru 27Soru

Smoke consists of fine solid particles dispersed in a gaseous medium. Which of the following colloidal classifications correctly describes smoke?

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Cevap: Aerosol

Cevap

Smoke is classified as an aerosol because it consists of solid particles dispersed in a gas.
Smoke consists of microscopic solid carbon particles suspended in air (a gas). Any colloidal dispersion where a solid or liquid is dispersed in a gas is categorized as an aerosol.

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1
Identify the dispersed phase and the dispersion medium of smoke.
Dispersed phase = solid (carbon/ash particles), Dispersion medium = gas (air).
Classification of colloids depends on the physical states of the dispersed phase and dispersion medium.
2
Match the phase combination (solid in gas) to the standard colloidal nomenclature.
Solid dispersed in a gas is termed a solid aerosol.
Colloids with a gaseous dispersion medium are broadly categorized as aerosols.

Anahtar Kavram

Classification of Colloidal Systems based on Dispersed Phase and Dispersion Medium
Soru 28Soru

An industrial effluent contains suspended colloidal particles of clay carrying negative surface charges, with particle diameters ranging from 1 nm1\text{ nm} to 100 nm100\text{ nm}. To treat the effluent, equal volumes of four different 0.01 mol dm30.01\text{ mol dm}^{-3} electrolyte solutions—Al2(SO4)3Al_2(SO_4)_3, CaCl2CaCl_2, NaClNaCl, and Na3PO4Na_3PO_4—are evaluated for their ability to induce coagulation. Which electrolyte has the highest precipitating power (lowest coagulation value) for this clay colloid, and what is the physical mechanism causing coagulation?

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Cevap: Al2(SO4)3Al_2(SO_4)_3, because the trivalent cation (Al3+Al^{3+}) carries the highest positive charge to neutralize the negative charges on the colloidal particles, causing them to aggregate into particles larger than 100 nm100\text{ nm}.

Cevap

The electrolyte with the highest precipitating power is Al2(SO4)3Al_2(SO_4)_3 because the trivalent cation (Al3+Al^{3+}) effectively neutralizes the negative surface charge on the clay particles according to the Hardy-Schulze rule.
The clay colloidal particles are negatively charged with diameters between 1 nm1\text{ nm} and 100 nm100\text{ nm}. According to the Hardy-Schulze rule, the coagulating power of an electrolyte is determined by the ion bearing a charge opposite to that of the colloidal particles, and it increases rapidly with the valency of the active ion. For a negative sol, cations are active. The trivalent Al3+Al^{3+} ion from aluminium tetraoxosulfate(VI) has a significantly higher precipitating power than divalent Ca2+Ca^{2+} or monovalent Na+Na^{+}, neutralizing the charge and aggregating particles beyond 100 nm100\text{ nm}.

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1
Identify the charge carried by the colloidal clay particles.
The clay particles are negatively charged lyophobic colloidal particles in the size range 1 nm1\text{ nm} to 100 nm100\text{ nm}.
Coagulation requires neutralizing the electrostatic repulsion between colloidal particles using an oppositely charged ion.
2
Apply the Hardy-Schulze rule to determine which ion causes precipitation.
Positively charged cations (Al3+Al^{3+}, Ca2+Ca^{2+}, Na+Na^{+}) are responsible for coagulating the negative colloid.
Ions possessing a charge opposite to that of the colloidal sol are effective for coagulation.
3
Compare the valencies of the effective cations present in the electrolytes.
Al3+Al^{3+} has a valency of +3+3, Ca2+Ca^{2+} has +2+2, and Na+Na^{+} has +1+1.
Precipitating power increases exponentially with increasing valency of the active ion (Al3+>Ca2+>Na+Al^{3+} > Ca^{2+} > Na^{+}).
4
Relate charge neutralization to particle size change.
Neutralized particles coalesce into larger aggregates (>100 nm>100\text{ nm}) that precipitate out.
Removal of surface charge reduces electrostatic repulsion, allowing van der Waals forces to aggregate colloidal particles into suspension-sized precipitates.

Anahtar Kavram

Hardy-Schulze Rule and Coagulation of Colloidal Systems
Soru 29Soru

In a municipal water treatment plant, raw water undergoes several physical and chemical processing steps. What is the primary purpose of introducing activated charcoal during the purification of water for town supply?

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Cevap: To remove unpleasant odors, objectionable tastes, and colored organic compounds

Cevap

The primary purpose of activated charcoal in municipal water treatment is to remove unpleasant odors, objectionable tastes, and colored organic compounds.
Activated charcoal (carbon) has a micro-porous structure with an exceptionally high surface area. It physically adsorbs dissolved organic pollutants, pigments, and volatile substances that cause objectionable odors and tastes, thereby clarifying and improving the aesthetic quality of drinking water.

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1
Identify the chemical reagent or material specified in the question.
The specified material is activated charcoal (activated carbon).
Activated charcoal is an adsorbent material used in filtration beds during water treatment.
2
Recall the specific functional role of activated charcoal in water purification.
Activated charcoal physically adsorbs dissolved organic impurities, volatile organic compounds, pigments, and substances responsible for foul tastes and odors.
Its extremely porous structure provides a vast surface area suitable for physical adsorption.
3
Distinguish activated charcoal's role from other water treatment chemicals.
Chlorine sterilizes water, potash alum coagulates suspended particles, and slaked lime adjusts pH or precipitates hardness.
Each chemical reagent added during municipal water treatment has a distinct, specialized role.

Anahtar Kavram

Role of Activated Charcoal in Water Treatment
Soru 30Soru

A water sample contains both temporary hardness due to dissolved Ca(HCO3)2\text{Ca(HCO}_3)_2 and permanent hardness due to dissolved MgSO4\text{MgSO}_4. Which sequence correctly arranges the operational steps required to completely soften this water sample using slaked lime followed by washing soda?

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Cevap

The correct operational sequence is: first, adding slaked lime to precipitate calcium carbonate from temporary hardness; second, filtering off the solid precipitate; third, adding washing soda to precipitate magnesium carbonate from permanent hardness; and fourth, performing a final filtration to obtain clear, soft water.
The removal process follows a logically structured chemical workflow. Temporary hardness caused by Ca(HCO3)2\text{Ca(HCO}_3)_2 is treated first with a calculated amount of slaked lime (Clark's process), producing insoluble CaCO3\text{CaCO}_3, which is filtered out. The remaining filtrate contains permanent hardness from MgSO4\text{MgSO}_4, which is treated with washing soda (sodium trioxocarbonate(IV)) to precipitate MgCO3\text{MgCO}_3. A second filtration removes this precipitate, leaving pure soft water.

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1
Identify the chemical reaction for temporary hardness removal.
Adding Ca(OH)2\text{Ca(OH)}_2 precipitates temporary hardness: Ca(HCO3)2+Ca(OH)22CaCO3+2H2O\text{Ca(HCO}_3)_2 + \text{Ca(OH)}_2 \rightarrow 2\text{CaCO}_3\downarrow + 2\text{H}_2\text{O}.
Slaked lime specifically removes hydrogentrioxocarbonate(IV) salts causing temporary hardness.
2
Separate the solid calcium carbonate formed.
The solid CaCO3\text{CaCO}_3 is filtered out of the solution.
Precipitates must be removed so they do not redissolve or contaminate subsequent steps.
3
Identify the chemical reaction for permanent hardness removal.
Adding Na2CO3\text{Na}_2\text{CO}_3 precipitates permanent hardness: MgSO4+Na2CO3MgCO3+Na2SO4\text{MgSO}_4 + \text{Na}_2\text{CO}_3 \rightarrow \text{MgCO}_3\downarrow + \text{Na}_2\text{SO}_4.
Soluble carbonate ions from washing soda precipitate divalent magnesium cations as insoluble trioxocarbonate(IV) salts.
4
Conduct final liquid-solid separation.
Filtering removes insoluble MgCO3\text{MgCO}_3, producing soft water.
Soluble sodium tetraoxosulfate(VI) remaining in solution does not react with soap to form scum.

Anahtar Kavram

Sequential chemical removal of temporary and permanent hardness using Clark's process followed by precipitation with washing soda.
Soru 31Soru

Match each municipal water purification stage or chemical additive on the left with its precise operational mechanism on the right.

Soldaki öğeye tıklayın, sonra eşleşen sağdaki öğeye tıklayın

Öğeler

Aeration
Addition of Potash Alum
Sand Filtration
Addition of Slaked Lime

Eşleşmeler

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Cevap

Aeration matches with expelling volatile gases and oxidizing soluble iron(II); Addition of Potash Alum matches with neutralizing negative charges on clay colloids for flocculation; Sand Filtration matches with straining out fine suspended particles remaining after sedimentation; Addition of Slaked Lime matches with adjusting pH of acidic water post-coagulation.
Aeration oxidizes soluble iron and removes dissolved gases. Potash alum supplies trivalent cations to neutralize negative charges on colloidal clay. Sand filtration physically retains fine suspended particles. Slaked lime neutralizes acidity induced by alum coagulation.

Adım Adım Çözüm

1
Analyze the primary chemical and physical effects of Aeration.
Spraying raw water into air maximizes gas exchange, driving off dissolved volatile species (H2SH_2S) and converting soluble Fe2+Fe^{2+} ions to insoluble Fe(OH)3Fe(OH)_3 precipitate.
Aeration targets volatile odors/tastes and dissolved metals rather than solid particulate filtration.
2
Analyze the coagulating action of Potash Alum (KAl(SO4)212H2OKAl(SO_4)_2 \cdot 12H_2O).
Trivalent Al3+Al^{3+} ions neutralize negative charges on suspended clay colloids, causing them to coalesce into larger settleable flocs.
Fine clay particles do not settle spontaneously due to mutual electrostatic repulsion.
3
Determine the function of Sand Filtration.
Water percolating through sand layer beds leaves behind non-settled micro-particles.
Filtration serves as a final physical straining stage after bulk sedimentation.
4
Evaluate the requirement for Slaked Lime (Ca(OH)2Ca(OH)_2).
Neutralizes acidity produced during alum hydrolysis, raising the pH to safe alkaline levels.
Acidic water damages metal distribution pipes through corrosive action.

Anahtar Kavram

Operational mechanisms of chemical and physical processes in town water supply treatment
Soru 32Soru

Starch mucilage is classified as a colloidal system rather than a true solution. Which of the following physical properties distinguishes starch mucilage from a true solution of sodium chloride?

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Cevap: Ability to scatter a beam of light passing through the mixture

Cevap

The ability to scatter a beam of light passing through the mixture (the Tyndall effect)
Colloidal systems such as starch mucilage contain particles ranging from 1 nm1\text{ nm} to 100 nm100\text{ nm} which scatter light (the Tyndall effect). In contrast, true solutions like sodium chloride contain ions or molecules smaller than 1 nm1\text{ nm} that cannot scatter visible light.

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1
Compare particle size ranges of true solutions and colloidal systems.
True solutions have solute particles smaller than 1 nm1\text{ nm}, whereas colloidal systems have dispersed particles in the range of 1 nm1\text{ nm} to 100 nm100\text{ nm}.
Particle size dictates whether light scattering occurs.
2
Identify the optical phenomenon associated with colloidal particle sizes.
Particles between 1 nm1\text{ nm} and 100 nm100\text{ nm} scatter light rays, making the beam's path visible (Tyndall effect).
This property clearly differentiates colloids like starch mucilage from true solutions like sodium chloride in water.

Anahtar Kavram

Tyndall Effect and Particle Size Differences in Mixtures
Tahmini Süre:45s
Soru 33Soru

During domestic water treatment, a household adds a measured amount of calcium hypochlorite (bleaching powder) to clear well water before consumption. What is the primary chemical purpose of adding this substance?

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Cevap: To destroy pathogenic microorganisms present in the water

Cevap

Adding calcium hypochlorite serves to sterilize the water by killing pathogenic bacteria and microorganisms.
Calcium hypochlorite (Ca(ClO)2Ca(ClO)_2) releases hypochlorous acid and chlorine when added to water. This powerful oxidizing environment kills bacteria, viruses, and other disease-causing pathogens, fulfilling the sterilization stage of water treatment.

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1
Identify the chemical reagent and its functional group
Calcium hypochlorite, Ca(ClO)2Ca(ClO)_2, acts as a chlorine-releasing disinfecting agent.
Bleaching powder hydrolyzes in water to release active chlorine ions.
2
Distinguish municipal/domestic water treatment roles
Disinfection/sterilization kills microorganisms, whereas coagulation removes turbidity and precipitation removes hardness.
Each water treatment reagent plays a specific, distinct chemical role.

Anahtar Kavram

Chemical Sterilization in Water Purification
Tahmini Süre:1m 0s
Soru 34Soru

In a municipal water treatment plant, raw river water undergoes several sequential processing stages to ensure it is safe for domestic consumption. Arrange the following key stages of municipal water purification in the correct chronological order from first to last.

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Cevap

The correct sequence of municipal water treatment stages from start to finish is: Screening to remove large floating debris, followed by Coagulation using alum to clump fine particles, then Sand filtration to remove tiny remaining suspended solids, and finally Chlorination to kill disease-causing germs.
The correct sequence follows the standard municipal waterworks workflow: physical removal of large debris (Screening) \rightarrow chemical aggregation of clay suspensions (Coagulation) \rightarrow mechanical straining of micro-solids (Filtration) \rightarrow chemical destruction of disease-causing bacteria (Chlorination).

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1
Identify the primary intake step.
Screening is the initial physical process to filter out large objects like leaves and sticks.
Large debris must be removed first to protect pump machinery and piping.
2
Identify the chemical clumping step.
Coagulation involves adding chemical coagulants such as alum to bind fine suspended clay particles into larger flocs.
Fine particles will not settle or filter easily without prior coagulation.
3
Identify the physical clarification step.
Filtration passes water through sand and gravel layers to remove remaining micro-suspended matter.
Water must be visually clear before chemical disinfection so pathogens are fully exposed to chlorine.
4
Identify the final disinfection step.
Chlorination is carried out last to kill bacteria and ensure biological safety for drinking.
Adding chlorine last ensures residual disinfection in the municipal piping network.

Anahtar Kavram

Sequential Stages of Municipal Water Purification
Soru 35Soru

A river water sample collected for a township supply system is found to contain fine suspended clay particles, objectionable taste caused by decomposing organic matter, and pathogenic bacteria, but has negligible dissolved calcium and magnesium salts. Which combination of chemical reagents must be utilized during the treatment process to render this water clean, odorless, and biologically safe?

Cevabı ve açıklamayı göster

Cevap: Potash alum, activated charcoal, and chlorine

Cevap

Potash alum, activated charcoal, and chlorine form the correct combination of reagents for purifying soft, turbid, contaminated surface water for public distribution.
The correct answer combines potash alum, activated charcoal, and chlorine because each chemical directly addresses one of the identified raw water issues: potash alum coagulates colloidal clay particles into larger flocs during sedimentation; activated charcoal adsorbs dissolved organic matter causing unpleasant tastes and smells; and chlorine kills disease-causing bacteria during final disinfection.

Adım Adım Çözüm

1
Analyze the specific impurities present in the raw water sample
Impurities identified: fine suspended colloidal clay (requires coagulation), organic taste/odor compounds (requires adsorption), and pathogenic microbes (requires disinfection/sterilization). Hardness minerals are absent.
Different water treatment chemicals address distinct types of physical, chemical, and biological contamination.
2
Select the appropriate chemical reagent for colloidal suspension removal
Potash alum (KAl(SO4)212H2OKAl(SO_4)_2 \cdot 12H_2O) provides Al3+Al^{3+} ions to neutralize negative charges on clay particles, causing coagulation into settleable flocs.
Physical filtration alone cannot remove extremely fine colloidal clay without prior chemical coagulation.
3
Select the reagent for taste and odor removal
Activated charcoal (carbon) adsorbs volatile organic compounds responsible for objectionable smells and tastes.
Porous activated carbon has a very large surface area optimized for organic molecule adsorption.
4
Select the chemical required for biological safety
Chlorine (or chlorine compounds) acts as a powerful oxidizing disinfectant to destroy disease-causing bacteria.
Water for public distribution must undergo chemical sterilization to eliminate waterborne pathogens.

Anahtar Kavram

Municipal water treatment requires distinct functional reagents: coagulants (potash alum) for suspended particles, adsorbents (activated carbon) for taste/odor, and disinfectants (chlorine) for sterilization. Softening reagents (slaked lime/washing soda) are only needed when hardness ions (Ca2+Ca^{2+}, Mg2+Mg^{2+}) are present.
Soru 36Soru

Three unlabelled liquid mixtures, PP, QQ, and RR, are tested in a laboratory. Mixture PP passes completely through both filter paper and semi-permeable membranes without scattering light. Mixture QQ passes through filter paper but is retained by semi-permeable membranes and scatters a narrow beam of light. Mixture RR leaves a solid residue on filter paper upon gravity filtration. Which mixture will undergo precipitation upon the addition of an electrolyte, and what physical property accounts for this behavior?

Cevabı ve açıklamayı göster

Cevap: Mixture QQ, because its dispersed particles carry surface charges and have diameters between 1 nm1\text{ nm} and 100 nm100\text{ nm}.

Cevap

Mixture QQ, because its dispersed particles carry surface charges and have diameters between 1 nm1\text{ nm} and 100 nm100\text{ nm}.
The experimental observations identify Mixture QQ as a colloid because it passes through ordinary filter paper, is retained by a semi-permeable membrane, and displays light scattering (Tyndall effect). Colloidal particles range in size between 1 nm1\text{ nm} and 100 nm100\text{ nm} and carry surface electrical charges. Addition of an electrolyte neutralizes these charges, leading to coagulation.

Adım Adım Çözüm

1
Analyze the filtration and optical properties of each mixture to classify them.
Mixture PP is a true solution (particle size <1 nm< 1\text{ nm}). Mixture QQ is a colloidal system (particle size 1100 nm1\text{--}100\text{ nm}, exhibits Tyndall scattering, retained by semi-permeable membrane). Mixture RR is a suspension (particle size >100 nm> 100\text{ nm}, retained by filter paper).
Differentiation among true solutions, colloids, and suspensions is based on particle size and membrane permeability.
2
Determine which system undergoes coagulation upon adding an electrolyte.
Colloidal particles (Mixture QQ) carry electric charges that stabilize them. Adding an electrolyte supplies ions of opposite charge, neutralizing the colloidal particles and causing them to coagulate/precipitate.
True solutions do not coagulate on electrolyte addition, and suspensions settle naturally by gravity.

Anahtar Kavram

Classification and properties of true solutions, colloidal systems, and suspensions
Soru 37Soru

A liquid pharmaceutical preparation shows a distinct illuminated path when a beam of light passes through it in a dark room (Tyndall effect) and shows no settling of particles upon standing for several weeks. However, when poured through standard filter paper, it leaves no residue. Which of the following correctly classifies this liquid system and explains its observed behavior?

Cevabı ve açıklamayı göster

Cevap: It is a colloidal system because its dispersed particle diameters (1 nm1\text{ nm} to 100 nm100\text{ nm}) are large enough to scatter light but small enough to pass through standard filter paper pores.

Cevap

The liquid preparation is a colloidal system because its dispersed particles (diameters between 1 nm1\text{ nm} and 100 nm100\text{ nm}) are sufficiently large to cause the Tyndall effect by scattering light, yet small enough to pass unhindered through the pores of standard filter paper without settling.
The correct response identifies the mixture as a colloidal system. Colloidal particles range in diameter from 1 nm1\text{ nm} to 100 nm100\text{ nm}. This intermediate particle size makes them small enough to pass through the microscopic pores of standard laboratory filter paper while remaining large enough to scatter incident light beams (Tyndall effect) and stay suspended indefinitely via Brownian motion.

Adım Adım Çözüm

1
Analyze the light scattering observation.
The observation of a visible light path (Tyndall effect) rules out true solutions, which have particle sizes smaller than 1 nm1\text{ nm} and do not scatter light.
Particles must be comparable in size to the wavelength of light (1 nm1\text{ nm} to 100 nm100\text{ nm}) to scatter light effectively.
2
Analyze the filtration and stability observations.
Passage through standard filter paper without leaving a residue and absence of settling rules out suspensions.
Suspension particles exceed 100 nm100\text{ nm} (or 0.1 μm0.1\text{ }\mu\text{m}), causing them to be trapped by filter paper pores and to settle under gravity over time.
3
Synthesize particle size characteristics to classify the system.
The mixture exhibits properties unique to a colloidal dispersion.
Colloids uniquely combine stability against gravity, ability to pass through ordinary filter paper, and distinct scattering of light.

Anahtar Kavram

Physical distinction between true solutions, colloids, and suspensions based on particle size, filtration capability, and light scattering (Tyndall effect).
Soru 38Soru

During industrial water treatment, temporary hardness caused by dissolved calcium hydrogencarbonate is removed chemically via Clark's process by adding a controlled quantity of slaked lime, Ca(OH)2\text{Ca(OH)}_2. Which balanced chemical equation correctly represents this water-softening reaction?

Cevabı ve açıklamayı göster

Cevap: Ca(HCO3)2(aq)+Ca(OH)2(aq)2CaCO3(s)+2H2O(l)\text{Ca(HCO}_3)_2\text{(aq)} + \text{Ca(OH)}_2\text{(aq)} \rightarrow 2\text{CaCO}_3\text{(s)} + 2\text{H}_2\text{O(l)}

Cevap

Ca(HCO3)2(aq)+Ca(OH)2(aq)2CaCO3(s)+2H2O(l)\text{Ca(HCO}_3)_2\text{(aq)} + \text{Ca(OH)}_2\text{(aq)} \rightarrow 2\text{CaCO}_3\text{(s)} + 2\text{H}_2\text{O(l)}
The equation Ca(HCO3)2(aq)+Ca(OH)2(aq)2CaCO3(s)+2H2O(l)\text{Ca(HCO}_3)_2\text{(aq)} + \text{Ca(OH)}_2\text{(aq)} \rightarrow 2\text{CaCO}_3\text{(s)} + 2\text{H}_2\text{O(l)} represents Clark's process. Slaked lime provides hydroxide ions that neutralize the hydrogencarbonate ions in temporary hard water, precipitating all calcium as insoluble calcium trioxocarbonate(IV), leaving soft water.

Adım Adım Çözüm

1
Identify the chemical cause of temporary hardness in the water sample
Temporary hardness is caused by dissolved calcium hydrogencarbonate, Ca(HCO3)2(aq)\text{Ca(HCO}_3)_2\text{(aq)}.
Hydrogencarbonate salts of calcium and magnesium decompose or precipitate when treated with appropriate alkaline agents.
2
Apply the principles of Clark's process for temporary hardness removal
Clark's process involves adding a calculated amount of slaked lime, Ca(OH)2(aq)\text{Ca(OH)}_2\text{(aq)}, which supplies hydroxide ions to convert hydrogencarbonate ions into insoluble trioxocarbonate(IV) ions.
Adding excess lime would re-introduce calcium ions and cause artificial hardness, so a stoichiometric amount is used.
3
Balance the precipitation chemical equation
Ca(HCO3)2(aq)+Ca(OH)2(aq)2CaCO3(s)+2H2O(l)\text{Ca(HCO}_3)_2\text{(aq)} + \text{Ca(OH)}_2\text{(aq)} \rightarrow 2\text{CaCO}_3\text{(s)} + 2\text{H}_2\text{O(l)}
One mole of calcium hydrogencarbonate reacts with one mole of calcium hydroxide to produce two moles of insoluble calcium trioxocarbonate(IV) and two moles of water.

Anahtar Kavram

Clark's process (slaked lime precipitation) for removal of temporary water hardness
Soru 39Soru

Arrange the following sequential processing stages involved in the treatment of raw river water for municipal supply in the correct order from initial treatment to final distribution.

Öğeleri doğru sıraya koymak için sürükleyin

Cevabı ve açıklamayı göster

Cevap

The correct sequence for municipal water purification is: Aeration → Coagulation (addition of alum) → Sedimentation → Sand Filtration → Chlorination (Disinfection).
Municipal water treatment follows a logical progression designed to clear large and dissolved impurities first before fine physical filtering and final chemical disinfection. Aeration removes volatile gases and oxidizes metals; coagulation aggregates colloidal particles using alum; sedimentation settles the heavy flocs; sand filtration removes micro-particles; and chlorination destroys disease-causing microorganisms as the final safeguard before piping to households.

Adım Adım Çözüm

1
Identify the initial physical treatment step for raw water.
Aeration is performed first to remove volatile odors/gases and oxidize dissolved iron salts into insoluble forms.
Air exposure improves taste and prepares dissolved metals for precipitation.
2
Determine the step that precipitates fine colloidal particles.
Coagulation with potash alum follows aeration.
Alum causes fine, non-settling colloidal particles to aggregate into larger flocs.
3
Identify how the aggregated flocs are removed bulk-wise.
Sedimentation allows these heavy flocs to settle to the basin floor.
Gravity settling removes the bulk of suspended solids before filtration.
4
Identify the step that removes residual microscopic suspended solids.
Sand filtration passes clear water through sand and gravel beds.
Filtration traps any residual suspended particles that escaped sedimentation.
5
Identify the final biological safety step prior to distribution.
Chlorination is carried out as the final step.
Sterilization must occur after physical clarity is achieved so chlorine acts effectively on pathogenic bacteria.

Anahtar Kavram

Sequential Stages of Municipal Water Treatment
Soru 40Soru

Match each chemical species or substance involved in water chemistry with its primary role or behavior regarding water hardness.

Soldaki öğeye tıklayın, sonra eşleşen sağdaki öğeye tıklayın

Öğeler

Magnesium hydrogencarbonate, Mg(HCO3)2\text{Mg(HCO}_3)_2
Magnesium tetraoxosulfate(VI), MgSO4\text{MgSO}_4
Sodium trioxocarbonate(IV), Na2CO3\text{Na}_2\text{CO}_3
Sodium permutit / Zeolite, Na2Z\text{Na}_2\text{Z}

Eşleşmeler

Cevabı ve açıklamayı göster

Cevap

Magnesium hydrogencarbonate causes temporary hardness that decomposes on boiling; magnesium tetraoxosulfate(VI) causes permanent hardness unaffected by boiling; sodium trioxocarbonate(IV) removes all hardness via chemical precipitation; sodium permutit removes all hardness via ion exchange.
Magnesium hydrogencarbonate is a soluble hydrogencarbonate salt causing temporary hardness removed by boiling. Magnesium tetraoxosulfate(VI) is a soluble sulfate salt causing permanent hardness that cannot be removed by boiling. Sodium trioxocarbonate(IV) removes all hardness types by precipitating calcium/magnesium ions as insoluble carbonates. Permutit softened water by exchanging hardness cations for soluble sodium ions.

Adım Adım Çözüm

1
Identify the cause of temporary hardness.
Magnesium hydrogencarbonate, Mg(HCO3)2\text{Mg(HCO}_3)_2, dissolves in water to cause temporary hardness. Upon boiling, hydrogencarbonate ions decompose to insoluble carbonate precipitates: Mg(HCO3)2(aq)MgCO3(s)+H2O(l)+CO2(g)\text{Mg(HCO}_3)_2(aq) \rightarrow \text{MgCO}_3(s) + \text{H}_2\text{O}(l) + \text{CO}_2(g).
Temporary hardness is specifically caused by hydrogen carbonate salts of calcium and magnesium, which are thermally unstable.
2
Identify the cause of permanent hardness.
Magnesium tetraoxosulfate(VI), MgSO4\text{MgSO}_4, causes permanent hardness because sulfate salts do not undergo thermal decomposition upon boiling.
Permanent hardness is caused by soluble tetraoxosulfate(VI) or chloride salts of calcium and magnesium.
3
Analyze the action of washing soda (Na2CO3\text{Na}_2\text{CO}_3).
Adding washing soda introduces CO32\text{CO}_3^{2-} ions, which combine with dissolved Mg2+\text{Mg}^{2+} or Ca2+\text{Ca}^{2+} ions to precipitate them as MgCO3\text{MgCO}_3 or CaCO3\text{CaCO}_3.
Precipitation of divalent metallic cations as insoluble carbonates removes both temporary and permanent hardness.
4
Analyze the action of sodium permutit (zeolite).
Permutit acts as an ion exchanger: Na2Z(s)+Mg2+(aq)MgZ(s)+2Na+(aq)\text{Na}_2\text{Z}(s) + \text{Mg}^{2+}(aq) \rightarrow \text{MgZ}(s) + 2\text{Na}^+(aq).
Hardness-causing divalent cations are bound to the zeolite matrix while harmless sodium ions are released into solution.

Anahtar Kavram

Classification of water hardness causes (hydrogencarbonate vs sulfate salts) and chemical removal mechanisms (boiling, precipitation, ion exchange).
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