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Policy Implications of Greenhouse Warming: Mitigation, Adaptation, and the Science Base (1992)
Committee on Science, Engineering, and Public Policy (COSEPUP)

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. "P Reforestation." Policy Implications of Greenhouse Warming: Mitigation, Adaptation, and the Science Base. Washington, DC: The National Academies Press, 1992.

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Page 814

Appendix P
Reforestation

The most comprehensive analysis of the potential for sequestering carbon in trees in the United States is that undertaken by Moulton and Richards (1990) of the U.S. Forest Service. This is a detailed analysis of the land available in the United States that could support trees, the carbon uptake that might be expected, and actual costs for each type of land to be managed. The analysis assumes that trees could be planted on economically marginal and environmentally sensitive pasture and croplands and that forest management programs could increase carbon uptake on many nonfederal forestlands. After analyzing the potential carbon uptake and cost per ton for 70 region and land-type classes, Moulton and Richards arrange these in order by cost per ton and assemble a supply curve for carbon sequestering. The analysis concludes that up to 56.4 percent of U.S. emissions could be sequestered in domestic trees at costs ranging from $5.80 to $47.75/t of carbon (C) (there is no adjustment for the small energy and CO2 cost of implementing such a program).1

The analysis has a 40-year time horizon and so does not confront the consequences of declining growth rates as trees approach maturity or of the long-term possibilities for tree maintenance or harvest. Two sets of numbers that heavily influence the numeric results but are likely to elicit some discussion are land rental rates and the ratio between carbon uptake in marketable timber and total ecosystem carbon uptake. Both sets of numbers are carefully laid out in the analysis and could be manipulated by an analyst with different notions. The ecosystem carbon ratios, for example, ranges from 1.8 to 8.4 and include considerable carbon accumulation in soils. The result of using high ecosystem carbon ratios is that average carbon accumulation for the full program amounts to 5.3 t/hectare(ha)/yr. Trexler (1990) suggests that values nearer 3.7 might be more within expectation for a

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814
Front Matter (R1-R26)
Part One: Synthesis (1-2)
1 Introduction (3-4)
2 Background (5-11)
3 The Greenhouse Gases and Their Effects (12-28)
4 Policy Framework (29-35)
5 Adaptation (36-47)
6 Mitigation (48-64)
7 International Considerations (65-67)
8 Findings and Conclusions (68-72)
9 Recommendations (73-83)
Individual Statement by a Member Of The Synthesis Panel (84-86)
Part Two: The Science Base (87-88)
10 Introduction (89-90)
11 Emission Rates and Concentrations Of Greenhouse Gases (91-99)
12 Radiative Forcing and Feedback (100-110)
13 Model Performance (111-116)
14 The Climate Record (117-134)
15 Hydrology (135-139)
16 Sea Level (140-144)
17 A Greenhouse Forcing and Temperature Rise Estimation Procedure (145-152)
18 Conclusions (153-154)
Part Three: Mitigation (155-156)
19 Introduction (157-170)
20 Framework for Evaluating Mitigation Options (171-200)
21 Residential and Commercial Energy Management (201-247)
22 Industrial Energy Management (248-285)
23 Transportation Energy Management (286-329)
24 Energy Supply Systems (330-375)
25 Nonenergy Emission Reduction (376-413)
26 Population (414-423)
27 Deforestation (424-432)
28 Geoengineering (433-464)
29 Findings and Recommendations (465-498)
Part Four: Adaptation (499-500)
30 Findings (501-507)
31 Recommendations (508-514)
32 Issues, Assumptions, and Values (515-524)
33 Methods and Tools (525-540)
34 Sesitivities, Impacts, and Adaptations (541-652)
35 Indices (653-656)
36 Final Words (657-658)
Individual Statement by a Member of the Adaptation Panel (659-660)
Appendixes (661-662)
A Questions and Answers About Greenhouse Warming (663-691)
B Thinking About Time in the Context of Global Climate Change (692-707)
C Conservation Supply Curves for Buildings (708-716)
D Conservation Supply Curves for Industrial Energy Use (717-726)
E Conservation Supply Data for Three Transportation Sectors (727-758)
F Transportation System Management (759-766)
G Nuclear Energy (767-774)
H A Solar Hydrogen System (775-778)
I Biomass (779-785)
J Cost-Effectiveness of Electrical Generation Technologies (786-791)
K Cost-Effectiveness of Chlorofluorocarbon Phaseout—United States and Worldwide (792-797)
L Agriculture (798-807)
M Landfill Methane Reduction (808-808)
N Population Growth and Greenhouse Gas Emissions (809-811)
O Deforestation Prevention (812-813)
P Reforestation (814-816)
Q Geoengineering Options (817-835)
R Description of Economic Estimates of the Cost of Reducing Greenhouse Emissions (836-839)
S Glossary (840-846)
T Conversion Tables (847-848)
U Prefaces from the Individual Panel Reports (849-854)
V Acknowledgments from the Individual Panel Reports (855-857)
W Background Information on Panel Members and Professional Staff (858-868)
Index (869-918)

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Page 814 Appendix P Reforestation The most comprehensive analysis of the potential for sequestering carbon in trees in the United States is that undertaken by Moulton and Richards (1990) of the U.S. Forest Service. This is a detailed analysis of the land available in the United States that could support trees, the carbon uptake that might be expected, and actual costs for each type of land to be managed. The analysis assumes that trees could be planted on economically marginal and environmentally sensitive pasture and croplands and that forest management programs could increase carbon uptake on many nonfederal forestlands. After analyzing the potential carbon uptake and cost per ton for 70 region and land-type classes, Moulton and Richards arrange these in order by cost per ton and assemble a supply curve for carbon sequestering. The analysis concludes that up to 56.4 percent of U.S. emissions could be sequestered in domestic trees at costs ranging from $5.80 to $47.75/t of carbon (C) (there is no adjustment for the small energy and CO2 cost of implementing such a program).1 The analysis has a 40-year time horizon and so does not confront the consequences of declining growth rates as trees approach maturity or of the long-term possibilities for tree maintenance or harvest. Two sets of numbers that heavily influence the numeric results but are likely to elicit some discussion are land rental rates and the ratio between carbon uptake in marketable timber and total ecosystem carbon uptake. Both sets of numbers are carefully laid out in the analysis and could be manipulated by an analyst with different notions. The ecosystem carbon ratios, for example, ranges from 1.8 to 8.4 and include considerable carbon accumulation in soils. The result of using high ecosystem carbon ratios is that average carbon accumulation for the full program amounts to 5.3 t/hectare(ha)/yr. Trexler (1990) suggests that values nearer 3.7 might be more within expectation for a

OCR for page 815
Page 815 program of this magnitude. Any comparison with current forest growth rates must acknowledge that most of the increased growth envisioned in the Moulton and Richards analysis would be on what is characterized as ''marginal cropland" but which would in fact be very good forestland. The analysis does not include a start-up period for tree planting and establishment but assumes "instant trees" with all establishment costs in the first year. The structure of the Moulton and Richards report is such that one can examine the program incrementally. Table P.1 shows the implications of planting enough trees—in order of increasing dollars per ton of carbon—to sequester carbon at rates of 10 percent, 20 percent, and 56.4 percent of current U.S. total CO2 emissions. The table shows that at the 10 percent level most of the uptake would be accomplished by changing forest management practices on current forestlands and planting on marginal pasturelands, but that in order to get very much of the maximum potential, large-scale inclusion of marginal croplands would be required. Recognizing that the Moulton and Richards analysis suggests that 56.4 percent of U.S. CO2 emissions could perhaps be offset with a massive commitment to a reforestation program, the Mitigation Panel adopts a very conservative approach to estimating the carbon offset that might be envisioned. This analysis accepts that the 10 percent objective described by Moulton and Richards is a reasonable initial target and that reforestation of economically marginal or environmentally sensitive pasture and croplands and nonfederal forestlands to a total 28.7 Mha could take place at costs as described in their analysis. The carbon sequestering rate is then divided by 2 to ensure that only carbon that is truly taken into long-term storage is counted. This baseline then suggests that 240 Mt CO2 could be sequestered at costs between $3 and $10/t CO2 (average cost is $7.20/t CO2). Demonstration projects could verify the lower costs and higher targets for total sequestration projected by some. TABLE P.1 Reforestation Program Costs by Percentage Reduction Annual CO2 Offset (%/M short tons) Land Requirement (M acres) Total Annual Cost (Billion $) Average Cost ($/t carbon) 5/72 36.9 0.7 9.72 10/143 70.9 1.7 12.02 20/286 138.4 4.5 15.73 30/429 197.6 7.7 17.91 SOURCE: Moulton and Richards (1990).

OCR for page 816
Page 816 Note 1. Tons (t) are metric; 1 Mt = 1 megaton = 1 million tons. References Moulton, R. J., and K. R. Richards. 1990. Costs of sequestering carbon through tree planting and forest management in the United States. U.S. Forest Service Report. Draft. U.S. Department of Agriculture, Washington, D.C. Trexler, M. C. 1990. Minding the carbon store: Weighing U.S. forest strategies to slow global warming. Draft. World Resources Institute, Washington, D.C.

Representative terms from entire chapter:

forest management