IB DP · Thinka 原創模擬試題

2024 IB DP Economics 模擬試題連答案詳解

Thinka May 2024 HL (TZ1) IB Diploma Programme-Style Mock — Economics

25 75 分鐘2024
An original Thinka practice paper modelled on the structure and difficulty of the May 2024 HL (TZ1) IB Diploma Programme Economics paper. Not affiliated with or reproduced from IB.

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Choose one question from a choice of three. Each question consists of a 10-mark explanatory sub-question and a 15-mark evaluative sub-question.
2 題目 · 25
題目 1 · essay
10
Explain, using a negative externality of consumption diagram, how the overconsumption of single-use plastics leads to market failure.
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解題

An effective response should include:

1. **Definitions of key terms**:
- **Market failure**: An inefficient allocation of resources by the free market where community surplus is not maximized, leading to a net welfare loss.
- **Negative externality of consumption**: A situation where the consumption of a good or service imposes external costs on third parties who are not involved in the economic transaction.
- **External costs**: The costs of an economic activity that are paid by third parties rather than the consumer or producer (e.g., plastic pollution in oceans, cost of waste disposal, harm to marine ecosystems).

2. **Diagrammatic analysis**:
- A correctly labeled negative externality of consumption diagram.
- The vertical axis labeled Price/Cost/Benefit (\(P\)) and the horizontal axis labeled Quantity (\(Q\)).
- An upward-sloping Marginal Private Cost (\(MPC\)) curve, which is assumed to equal Marginal Social Cost (\(MSC\)) in the absence of production externalities.
- A downward-sloping Marginal Private Benefit (\(MPB\)) curve.
- A downward-sloping Marginal Social Benefit (\(MSB\)) curve positioned below and to the left of the \(MPB\) curve.
- The difference between \(MPB\) and \(MSB\) labeled as external costs.
- The free market equilibrium point where \(MPB = MPC\), yielding quantity \(Q_m\) and price \(P_m\).
- The socially optimum point where \(MSB = MSC\), yielding quantity \(Q_{\text{opt}}\) and price \(P_{\text{opt}}\).
- A clearly shaded area of welfare loss (deadweight loss) pointing from the market quantity \(Q_m\) back to the socially optimum quantity \(Q_{\text{opt}}\).

3. **Detailed explanation**:
- Consumers of single-use plastics only consider their private benefits (\(MPB\)), such as convenience and low cost, and private costs (\(MPC\)), such as the retail price.
- They ignore the negative external effects on third parties, such as the long-term environmental degradation caused by plastic waste that persists in ecosystems for hundreds of years.
- Because of these external costs, the marginal social benefit of consuming single-use plastics is less than the private benefit (\(MSB < MPB\)), where \(MSB = MPB - \text{External Costs}\).
- Since individual consumers act in their self-interest, they consume up to the point where \(MPB = MPC\) (at \(Q_m\)).
- However, the allocatively efficient outcome for society occurs where the marginal benefit to society equals the marginal cost to society, which is where \(MSB = MSC\) (at \(Q_{\text{opt}}\)).
- Because \(Q_m > Q_{\text{opt}}\), there is an overconsumption and overallocation of resources to single-use plastics.
- For every unit consumed between \(Q_{\text{opt}}\) and \(Q_m\), the marginal social cost exceeds the marginal social benefit (\(MSC > MSB\)). This creates a deadweight loss (welfare loss) to society, represented by the triangular area, signifying that allocative efficiency is not achieved and market failure has occurred.

評分準則

**Markbands**

- **9–10 marks**: The response is well-structured, clear, and demonstrates a thorough understanding of the demands of the question. Essential economic terms are defined accurately. A fully labeled and correct negative externality of consumption diagram is provided, showing the divergence between MPB and MSB, the market and socially optimal quantities, and the deadweight loss. The explanation is logical and comprehensive, clearly showing how the external costs of plastic consumption lead to a divergence between private and social benefits, overconsumption (\(Q_m > Q_{\text{opt}}\)), and a welfare loss.
- **6–8 marks**: The response shows a good understanding of the question. Key terms are defined. A diagram is drawn, though there may be minor errors (e.g., missing axis labels or a slightly mislabeled welfare loss area). There is a clear explanation of how the external costs of single-use plastics lead to overconsumption and market failure, though some links or details may be less fully developed.
- **3–5 marks**: The response shows a limited understanding of the question. Some terms are defined, but definitions may be incomplete. A diagram is attempted, but it may contain significant errors (e.g., shifting the wrong curves or confusing production and consumption externalities). The explanation is descriptive and contains gaps in economic reasoning.
- **1–2 marks**: The response is very basic, demonstrating little or no understanding of externalities or market failure. Diagrams are either missing or entirely incorrect.
- **0 marks**: The response does not meet any of the standards described above.
題目 2 · essay
15
Using real-world examples, evaluate the effectiveness of carbon taxes compared to command-and-control regulation as a policy to reduce the negative externalities of production associated with fossil fuel combustion.
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解題

### 1. Introduction
- **Define key terms**:
- **Negative externality of production**: An adverse side effect suffered by a third party as a result of an economic activity (production), where the marginal social cost (\(MSC\)) exceeds the marginal private cost (\(MPC\)).
- **Carbon tax**: A market-based policy that places a direct price on greenhouse gas emissions, forcing producers to internalize the external cost.
- **Command-and-control (CAC) regulations**: Direct government intervention consisting of laws, targets, and standards that set limits on emissions, technology mandates, or outright bans on specific polluting activities.
- **Thesis**: While carbon taxes are theoretically superior due to their economic efficiency and ability to incentivize continuous green innovation, command-and-control regulations are often necessary to provide target certainty and address situations where market forces fail to react quickly enough.

### 2. Diagrammatic Analysis
- Students should describe a standard **Negative Externality of Production** diagram:
- The x-axis represents the quantity of fossil-fuel-based energy (\(Q\)) and the y-axis represents costs and benefits (Price, \(P\)).
- The marginal private benefit (\(MPB\)) is equal to the marginal social benefit (\(MSB\)), assuming no consumption externalities.
- The marginal private cost (\(MPC\)) curve represents the private costs of production.
- The marginal social cost (\(MSC\)) curve lies above the \(MPC\) curve due to the negative externality (marginal external cost, \(MEC\)), so \(MSC = MPC + MEC\).
- The free market equilibrium occurs where \(MPC = MPB\), yielding quantity \(Q_m\) and price \(P_m\).
- The socially optimal level of output occurs where \(MSC = MSB\), yielding quantity \(Q_{opt}\) and price \(P_{opt}\).
- Because \(Q_m > Q_{opt}\), there is overproduction of energy, resulting in a welfare loss (deadweight loss) shaded between \(MSC\) and \(MPC\) from \(Q_{opt}\) to \(Q_m\).
- **Applying the carbon tax**: Explain that imposing a tax equal to \(MEC\) shifts the private cost curve upwards from \(MPC\) to \(MPC + tax\) (which coincides with \(MSC\)). This forces the market equilibrium to align with the social optimum at \(Q_{opt}\), eliminating the welfare loss.

### 3. Analysis of Carbon Taxes (Market-Based Policy)
- **How it works**: Internalizes the externality by making polluters pay for the damage they cause, utilizing the price mechanism to reallocate resources.
- **Strengths**:
- **Allocative and Cost Efficiency (Least-Cost Principle)**: Firms with low abatement costs will reduce emissions to avoid the tax, while those with high abatement costs will pay the tax. This achieves the overall emission reduction target at the lowest possible cost to society.
- **Dynamic Efficiency**: Provides a continuous financial incentive for firms to invest in research and development (R&D) and adopt green technologies to further reduce tax liabilities.
- **Government Revenue**: Generates public funds that can be used to subsidize renewable energy initiatives, invest in green infrastructure, or mitigate the regressive nature of the tax by offering rebates to low-income households (revenue neutrality).
- **Weaknesses**:
- **Measurement Difficulties**: It is highly complex to measure the exact monetary value of environmental degradation and set the tax rate precisely equal to the \(MEC\).
- **Inelastic Demand**: In the short run, fossil fuel demand is highly price inelastic. Firms may simply pass the tax on to consumers in the form of higher prices without significantly reducing output.
- **Regressivity**: Energy costs constitute a larger proportion of low-income household budgets, meaning a flat carbon tax disproportionately impacts poorer segments of society.

### 4. Analysis of Command-and-Control (CAC) Regulations
- **How it works**: The government mandates specific standards (e.g., fuel efficiency standards for vehicles) or limits emissions directly.
- **Strengths**:
- **Certainty of Outcome**: Directly guarantees that emissions or harmful practices will not exceed a set legal limit, which is vital when dealing with highly toxic pollutants or critical ecological tipping points.
- **Clarity and Simplicity**: Rules are straightforward for companies to understand, and compliance can sometimes be easier to monitor than carbon footprints (e.g., a ban on coal-fired power plants vs. measuring exact carbon output from diverse industrial processes).
- **Weaknesses**:
- **Inefficiency**: Treats all firms identically, regardless of their individual costs of cutting pollution. This makes the overall cost of abatement much higher for society.
- **Lack of Continuous Incentive**: Once a firm meets the regulatory minimum standard, it has no financial incentive to reduce emissions further.
- **Regulatory Capture and Bureaucracy**: Highly susceptible to industry lobbying, which can dilute standards. Setting, monitoring, and enforcing regulations also require a large, expensive state apparatus.

### 5. Real-World Examples
- **Carbon Taxes**: Sweden's carbon tax (introduced in 1991) is often cited as a major success, helping the country decouple GDP growth from carbon emissions. British Columbia's revenue-neutral carbon tax is another example where tax revenues were successfully returned to citizens through income tax cuts, mitigating political resistance.
- **Command-and-Control**: The European Union's ban on the sale of new petrol and diesel cars by 2035, or the United States' Corporate Average Fuel Economy (CAFE) standards, which mandate minimum fuel efficiency levels for car manufacturers.

### 6. Evaluation and Synthesis
- **Comparing the policies**:
- **Efficiency**: Carbon taxes are superior as they minimize the total cost of abatement and foster innovation.
- **Equity**: Carbon taxes can be highly regressive, whereas regulations (such as building standards) can also raise costs but are often perceived as less punitive to low-income households if structured well.
- **Certainty**: Regulations offer higher physical emission certainty than taxes, which depend on price elasticities.
- **Conclusion**: An effective policy framework rarely relies on just one tool. A hybrid approach is ideal: command-and-control regulations should be used to phase out obsolete, highly dangerous technologies (such as coal power or single-use plastics) and set minimum baseline standards, while carbon taxes should be used to incentivize broad-based, long-term investments in green alternatives across the wider market.

評分準則

### Markbands
- **Level 1 (1–3 marks)**:
- Identifies some basic concepts of market failure or government policy.
- Lacks clear structure, definitions, or relevant diagrams.
- **Level 2 (4–6 marks)**:
- Explains either carbon taxes or regulations but lacks depth in comparing the two.
- The diagram is omitted, incomplete, or incorrectly labeled.
- Real-world examples are absent or merely listed without analysis.
- **Level 3 (7–9 marks)**:
- Explains both carbon taxes and command-and-control regulations.
- Includes an appropriate negative externality of production diagram, though there may be minor errors in labeling or explanation.
- Some attempts at evaluation are made, but they tend to be descriptive rather than critical.
- Includes basic real-world examples, but their integration is weak.
- **Level 4 (10–12 marks)**:
- Offers a clear and structured comparative analysis of both policies.
- Features an accurate, fully labeled negative externality diagram showing how a tax can restore allocative efficiency.
- Evaluates both policies across criteria such as efficiency, equity, and implementation feasibility.
- Integrates relevant real-world examples (e.g., Sweden, BC, or CAFE standards) to support economic arguments.
- **Level 5 (13–15 marks)**:
- Provides a highly sophisticated, balanced evaluation with precise economic terminology.
- Seamlessly integrates accurate diagrams and well-developed real-world examples throughout the text.
- Delivers a nuanced synthesis that discusses the benefits of a hybrid policy mix, demonstrating a deep understanding of the practical limitations of both market-based and regulatory tools.

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