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the biological treatment of total organic carbon in water uses activated carbon adsorption. the adsorption accords with freundl...Question
the biological treatment of total organic carbon (toc) in water uses activated carbon adsorption .The adsorption accords with with freundlich equation, k= 0.007, n=1.13. in the equation, the unit of qe is mg.mg/c, and the unit of ce is mg/l. to dispose 10l wastewater with 20mg/l toc, 1g activated carbon is applied. at equilibrium of adsorption, what is the capacity of equilibrium adsorption? (mg.mg/C). note: based on material balance, for every litre of water 100 qe +Ce=200.
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Answered by
GPT-4o mini
To solve this problem, we need to apply the given information and the Freundlich isotherm equation.
**Given:**
- Freundlich constants: \( k = 0.007 \) and \( n = 1.13 \).
- Initial concentration of TOC (\( C_0 \)) = 20 mg/L.
- Volume of wastewater (\( V \)) = 10 L.
- Amount of activated carbon (\( m \)) = 1 g.
We are looking to find the equilibrium adsorption capacity (\( q_e \)) in mg/mg of activated carbon.
### Step 1: Calculate total TOC in the wastewater
The total amount of TOC in 10 liters of wastewater is calculated as follows:
\[
\text{Total TOC} = C_0 \times V = 20 \, \text{mg/L} \times 10 \, \text{L} = 200 \, \text{mg}
\]
### Step 2: Set up the material balance
From the problem, we know that at equilibrium:
\[
100 \cdot q_e + C_e = 200
\]
Where:
- \( q_e \) = amount of TOC adsorbed per unit mass of activated carbon in mg/mg.
- \( C_e \) = equilibrium concentration of TOC in mg/L.
### Step 3: Calculate \( C_e \)
Assuming the amount of TOC adsorbed (\( Q \)) is equal to the total TOC minus what remains in solution:
\[
Q = 200 - C_e
\]
Since we have:
\[
Q = m \cdot q_e = 1 \cdot q_e = q_e \, \text{mg}
\]
We have:
\[
C_e = 200 - q_e
\]
### Step 4: Substitute into the Freundlich equation
According to the Freundlich isotherm:
\[
q_e = k C_e^n
\]
Substituting \( C_e = 200 - q_e \) into the equation:
\[
q_e = 0.007 (200 - q_e)^{1.13}
\]
### Step 5: Solve the equation iteratively
This is a nonlinear equation, and we can solve it using numerical methods or trial and error. For simplicity, let's conduct an estimate, but realistically, this should be solved numerically or using a mathematical software.
Assuming \( q_e \) to start with 0:
1. \( C_e = 200 - 0 = 200 \)
2. \( q_e = 0.007(200)^{1.13} \approx 0.007(285.3) \approx 1.99 \, \text{mg}\)
Now using \( q_e = 1.99 \):
1. \( C_e = 200 - 1.99 = 198.01 \)
2. Recalculate \( q_e = 0.007(198.01)^{1.13} \approx 0.007(276.6) \approx 1.93 \, \text{mg}\)
Continue this process iteratively until convergence. After a few iterations, you would find that:
\[
q_e \approx 1.99 \, \text{mg}
\]
### Step 6: Calculate the final adsorption capacity
Convert \( q_e \) in mg to mg/mg:
Since we started with 1 g of activated carbon (or 1000 mg):
\[
q_e = \frac{1.99 \, \text{mg}}{1 \, \text{g}} = 0.00199 \, \text{mg/mg} \approx 0.002 \, \text{mg/mg}
\]
### Conclusion
Thus, the capacity of equilibrium adsorption \( q_e \) is approximately **1.99 mg/g or 0.00199 mg/mg.**
This value would need to be confirmed through more precise iterations or numerical solving to reach a consistent equilibrium value.
**Given:**
- Freundlich constants: \( k = 0.007 \) and \( n = 1.13 \).
- Initial concentration of TOC (\( C_0 \)) = 20 mg/L.
- Volume of wastewater (\( V \)) = 10 L.
- Amount of activated carbon (\( m \)) = 1 g.
We are looking to find the equilibrium adsorption capacity (\( q_e \)) in mg/mg of activated carbon.
### Step 1: Calculate total TOC in the wastewater
The total amount of TOC in 10 liters of wastewater is calculated as follows:
\[
\text{Total TOC} = C_0 \times V = 20 \, \text{mg/L} \times 10 \, \text{L} = 200 \, \text{mg}
\]
### Step 2: Set up the material balance
From the problem, we know that at equilibrium:
\[
100 \cdot q_e + C_e = 200
\]
Where:
- \( q_e \) = amount of TOC adsorbed per unit mass of activated carbon in mg/mg.
- \( C_e \) = equilibrium concentration of TOC in mg/L.
### Step 3: Calculate \( C_e \)
Assuming the amount of TOC adsorbed (\( Q \)) is equal to the total TOC minus what remains in solution:
\[
Q = 200 - C_e
\]
Since we have:
\[
Q = m \cdot q_e = 1 \cdot q_e = q_e \, \text{mg}
\]
We have:
\[
C_e = 200 - q_e
\]
### Step 4: Substitute into the Freundlich equation
According to the Freundlich isotherm:
\[
q_e = k C_e^n
\]
Substituting \( C_e = 200 - q_e \) into the equation:
\[
q_e = 0.007 (200 - q_e)^{1.13}
\]
### Step 5: Solve the equation iteratively
This is a nonlinear equation, and we can solve it using numerical methods or trial and error. For simplicity, let's conduct an estimate, but realistically, this should be solved numerically or using a mathematical software.
Assuming \( q_e \) to start with 0:
1. \( C_e = 200 - 0 = 200 \)
2. \( q_e = 0.007(200)^{1.13} \approx 0.007(285.3) \approx 1.99 \, \text{mg}\)
Now using \( q_e = 1.99 \):
1. \( C_e = 200 - 1.99 = 198.01 \)
2. Recalculate \( q_e = 0.007(198.01)^{1.13} \approx 0.007(276.6) \approx 1.93 \, \text{mg}\)
Continue this process iteratively until convergence. After a few iterations, you would find that:
\[
q_e \approx 1.99 \, \text{mg}
\]
### Step 6: Calculate the final adsorption capacity
Convert \( q_e \) in mg to mg/mg:
Since we started with 1 g of activated carbon (or 1000 mg):
\[
q_e = \frac{1.99 \, \text{mg}}{1 \, \text{g}} = 0.00199 \, \text{mg/mg} \approx 0.002 \, \text{mg/mg}
\]
### Conclusion
Thus, the capacity of equilibrium adsorption \( q_e \) is approximately **1.99 mg/g or 0.00199 mg/mg.**
This value would need to be confirmed through more precise iterations or numerical solving to reach a consistent equilibrium value.
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