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Copyright © 2013 Jonathan M. Harris
Environmental and Natural Resource Economics 3rd ed. Jonathan M. Harris and Brian Roach Chapter 11 – Nonrenewable Resources: Scarcity and Abundance Copyright © 2013 Jonathan M. Harris
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Figure 11.1: Classification of Nonrenewable Resources
Subeconomic Economic Increasing Geologic Assurance Measured Indicated Demonstrated Inferred Identified Undiscovered Hypothetical (in known districts) Hypothetical (in un-discovered districts) Increasing Economic Feasibility Reserves The implication of this standard resource classification diagram is that reserves are not fixed but variable, and can be expanded in two ways: by new discovery or by new technology and changing market conditions. The currently identified economic reserves may be only a small portion of the ultimately recoverable reserves. Source: Adapted from U.S. Bureau of Mines and U.S. Geological Survey, 1976.
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Figure 11.2: Nonrenewable Resource Production Decisions
Price Quantity MC Qm Q* P A Figure 11.2: Nonrenewable Resource Production Decisions Unlike ordinary competitive firms, firms that produce non-renewable resources will not produce where P = MC, but will balance the resource rent available from producing today with the expected rent available from producing in the future. They forgo potential profits equal to area A in the expectation of greater future profits. High-quality resources, with high recoverable rents, will be exploited first, while lower-grade resources may be held in reserve. Source: Adapted from Hartwick and Olewiler, 1998, which provides a more advanced discussion of the economic theory of nonrenewable resource extraction.
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Figure 11.3: Hypothetical Nonrenewable Resource Use Profile
Time Price Quantity Extracted Stage I Stage III Stage II Stage IV Choke Price In theory, non-renewable resources should face eventual exhaustion. The price of the resource should rise over time (in accordance with Hotelling’s rule), while the quantity extracted should gradually decline, reaching zero when the “choke price”, or highest possible market price for the resource, is reached. The complete life cycle of a resource includes a period of declining prices and increasing consumption, followed eventually by rising prices and decreasing consumption. Until recently, it has appeared that we have been in Stage I or II, although recent evidence suggests that we may be moving into Phase III with rising prices for many resources. Source: Adapted from Hartwick and Olewiler, 1998,
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Figure 11.4: Prices for Selected Minerals, 1996-2011
Copper Lead Zinc Price per Pound After a long period of stable or declining prices, prices for key minerals rose rapidly in , though they fell back somewhat in Prices rose again in and have declined somewhat since then, but remain above previous levels. Source: U.S. Geological Survey, Minerals Commodities Summaries, various years.
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Figure 11.5: Global Economic Reserves for Selected Minerals, 1996-2012
Copper Zinc Lead Even though production has risen steadily since 1950, reserves for most minerals have increased, not decreased, due to new discovery and improved technology for resource recovery. Source: U.S. Geological Survey, Minerals Commodities Summaries, various years.
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Table 11.1: Expected Resource Lifetimes, Selected Minerals
2011 global production (thousand metric tons) Global reserves (thousand metric tons) Expected resource lifetime, years (static reserve index) Aluminum 220,000 29,000,000 132 Cadmium 22 640 29 Copper 16,100 690,000 43 Iron ore 2,800,000 80,000,000 Lead 4,500 85,000 19 Lithium 34 13,000 382 Mercury 2 93 47 Nickel 1,800 80,000 44 Tin 253 4,800 Tungsten 72 3,100 Zinc 12,400 250,000 20 Reserve base estimates indicate that shortages are not imminent, although higher-quality reserves may run short in the relatively near future. Source: U.S. Geological Survey, Minerals Commodities Summaries, various years. Note: Aluminum data for bauxite ore, the primary source of aluminum.
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Table 11.2: Potential Environmental Impacts of Mining
Activity Potential impacts Excavation and ore removal Destruction of plant and animal habitat, human settlements, and other features (surface mining) Land subsidence (underground mining) Increased erosion; silting of lakes and streams Waste generation Acid drainage and metal contamination of lakes, streams, and groundwater Ore concentration Waste generation (tailings) Organic chemical contamination Acid drainage and metal contamination Smelting/refining Air pollution (including sulfur dioxide, arsenic, lead, cadmium and other toxics) Waste generation (slag) Impacts of producing energy (most energy used for mineral production goes into smelting and refining). Mining has many negative environmental impacts on land, air, and water, with potential ecological and human health effects. Source: Young, 1992.
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Figure 11.6: Impact of Recycling on Virgin Resource Extraction Path
Stage III Stage IV Supply from Recycled Materials Supply from Virgin Resource Total Supply Extraction Path without Recycling Time Resource Supply Expansion of resource recycling and substitution of backstop (ideally renewable) resources can stretch out the lifetime of a non-renewable resource.
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Figure 11.7: Marginal Costs of Recycling
Proportion of Supply Obtained from Recycled Materials 40% 0% 60% 100% MCr MPCv MSCv Equilibrium levels of recycling can be identified based on marginal costs of virgin and recycled materials. Producers will tend to operate where these marginal costs are equalized, which will be at a higher level of recycling with internalization of environment costs.
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Figure 11. 8: Scrap Metal as a Percentage of Total U. S
Figure 11.8: Scrap Metal as a Percentage of Total U.S. Consumption, 2010 Scrap Metal (Percent) Metals in the U.S. are recycled at varying rates. The proportion recycled is highest for lead, a durable metal with high environmental impacts from mining. More than half of U.S. iron and steel, and over 50% of aluminum, are recycled. Source: USGS, 2012.
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