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Debt-for-Nature Initiatives and the Tropical Forest Conservation Act (TFCA): Status and Implementation

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Debt-for-Nature Initiatives and the Tropical Forest Conservation Act: Status and Implementation

March 30, 2010 (RL31286)

Contents

Summary

In the late 1980s, extensive foreign debt and degraded natural resources in developing nations led to the creation of debt-for-nature initiatives that reduced debt obligations, allowed for debt repayments in local currency as opposed to hard currency, and generated funds for the environment. These initiatives, called debt-for-nature swaps, (hereinafter referred to as debt-for-nature transactions) typically involved restructuring, reducing, or buying a portion of a developing country's outstanding debt, with a percentage of proceeds (in local currency) being used to support conservation programs within the debtor country. Most early transactions involved debt owed to commercial banks and were administered by nongovernmental conservation organizations and referred to as three-party swapstransactions. Since 1987, three-party transactions involving countries all over the world have generated more than an estimated $140167 million in local currency for conservation projects, as a result of the purchase of approximately $170 million in debt (face value) for approximately $49 million. Other debt-for-nature initiatives involved official (public) debt and were administered by creditor governments directly with debtor governments (termed bilateral swaps).

transactions). In the early 1990s, the United States initiated a program called the Enterprise for the Americas Initiative (EAI), which involved debt-for-nature transactions. The United States restructured, and in one case sold, debt equivalent to a face value of nearlyover $1 billion owed by Latin American countries; these transactions were authorized by Congress as part of the Enterprise for the Americas Initiative (EAI)EAI, which broadened the scope of debt swapstransactions to include a number of social goals. Nearly $178177 million in local currency for environmental, natural resource, health protection, and child development projects within debtor countries was generated from these swapstransactions. The model for debt-for-nature initiativestransactions, outlined in the EAI, was expandedused in the Tropical Forest Conservation Act (TFCA; P.L. 105-214; 22 U.S.C. 2431) to include countries around the world with tropical forests. Under this program, debt can be restructured in eligible countries, and funds generated from the transactions are used to support programs to conserve tropical forests within the debtor country.

Since 1998, $124.8233.4 million has been used under the TFCA to restructure loan agreements in 1314 countries (1520 transactions), and nearly $218.4 million in local currency will be generated in the next 12-26 years for tropical forest conservation projects. The TFCA isover $339 million will be generated for tropical forest conservation at the conclusion of these agreements. The TFCA was authorized to receive appropriations through FY2007, but no funds have been appropriated for the program since FY2015 and no new deals are anticipated. The TFCA is being considered for reauthorization in the 111114th Congress.

(S. 566). Debt-for-nature transactions are generallygenerally are viewed as a success by conservation organizations and debtor governments because of the funds generated for conservation efforts. The appeal of debt-for-nature transactions has been tempered in recent years, however, by higher debt prices on secondary markets and lowerfewer or no appropriations. As a result, fewer transactions have taken place. This report provides a description of debt-for-nature transactions and a summary of the Tropical Forest Conservation Act.


TFCA.
Debt-for-Nature Initiatives and the Tropical Forest Conservation Act: Status and Implementation
(TFCA): Status and Implementation

Background Information

Debt-for-nature initiatives were conceived to address the rapid loss of resources and biodiversity in developing countries that were heavily indebted to foreign creditors. Conservationists had noted that the pressure to pay off foreign debts in hard currency was leading to increased levels of natural resource exports (i.e., timber, cattle, minerals, and agricultural products) at the expense of the environment. In many cases, indebted developing countries had difficulty meeting their hard currency debt obligations and defaulted. Reducing foreign debt and allowing for portions of it to be paid with local currency while increasing funds for the environment was thought to improve environmental conditions in developing countries and had the advantage of relieving the debtor country's difficulties in procuring sufficient hard currency to pay off its debts.1 Money generated from debt-for-nature transactions has been used to fund a variety of projects, ranging from national park protection in Costa Rica to supporting ecotourism in Ghana and conserving tropical forests in Bangladesh.

Since 1993, there has been a declining trend in the number of debt-for-nature transactions involving official (public) and private funds. Accounting changes requiring new appropriations to support official (public) debt transactions in creditor countries such as the United States, and a higher price of commercial debt on secondary markets, are two reasons suggested for the decline of debt-for-nature transactions. While Congress has periodically authorized U.S. participation in three-party debt-for-nature swapstransactions and has supported two bilateral debt-for-nature initiatives, appropriations to support these types of efforts have generally diminished over the years. Authority for Debt-for-Nature Initiatives Early debt-for-nature legislation concentrated on understanding and promoting third-party debt-for-nature transactions (see Appendix for legislation summaries and United States Code citations). Congress in 1989 directed the Secretary of the Treasury to ask the U.S. Executive Director of the World Bank to develop a pilot debt-for-nature program and other ways of reducing debt owed by foreign countries while generating funds for the environment. A subsequent law, the International Development and Finance Act of 1989, authorized the U.S. Agency for International Development (USAID) to make grants to nongovernmental organizations (NGOs) to purchase debt in three-party transactions. Official (public) P.L. 480 debt owed to the United States by eligible Latin American countries was authorized to be reduced by the 1990 farm bill (P.L. 101-624; 7 U.S.C. 1738b). The 102nd Congress authorized debt reduction for foreign assistance loans made by USAID (P.L. 102-549; 22 U.S.C. 2430 and 2421), the Export-Import Bank (Ex-Im Bank; P.L. 102-429; 12 U.S.C. 635i-6), and the Commodity Credit Corporation (CCC; P.L. 102-549; 22 U.S.C. 2430 and 2421). Together, the P.L. 480, USAID, Ex-Im, and CCC debt-reduction authorizations were undertaken as part of President George H. W. Bush's Enterprise for the Americas Initiative. In 1996, USAID was further authorized by Congress to conduct swaps, buybacks, and cancellations of debt owed to the United States by eligible Latin American and Caribbean countries (P.L. 104-107). In 1998, the Tropical Forest Conservation Act (TFCA; P.L. 105-214; 22 U.S.C. 2431) was passed, allowing debt swaps, buybacks, and restructuring to generate funds for tropical forest conservation worldwide.

Funding for the TFCA was reauthorized by Congress in 2004 (P.L. 108-323). In the 114th Congress, S. 566 would authorize appropriations for the TFCA of $20.0 million annually from FY2015 to FY2018. The bill also would expand the TFCA to include coral reefs and associated coastal marine ecosystems.2

and has supported two bilateral debt-for-nature initiatives, appropriations to support these types of efforts have generally diminished over the years.

Debt-for-Nature Initiatives and Their Mechanisms

Three-Party Swaps

Transactions Three-party debt-for-nature swapstransactions, involving nongovernmental organizations such as The Nature Conservancy and Conservation International, were the first debt-for-nature agreements to be formed. In a three-party swap, a conservation group purchases a hard currency debt owed to commercial banks on the secondary market or in some cases a public (official) debt owed to a creditor government at a discounted rate compared to the face value of the debt, and then renegotiates the debt obligation with the debtor country.23 The debt is generally sold back to the debtor country for more than it was purchased for by the NGO, yet less than what it was on the secondary market. The proceeds generated from the renegotiated debt, to be repaid in local currency, are typically put into a fund that often allocates grants to local environmental organizations for conservation projects (see Figure 1). In these cases, the fund is administered by the conservation organization, representatives from local environmental groups, and the debtor government. Money to buy the debt initially may come from the nongovernmental organization, governments, banks, or other private organizations.

Source: Congressional Research Service.

Figure 1. An Illustrative Example of a Three-Party Debt-for-Nature Swap Agreement

In 1989, Congress authorized the United States Agency for International Development (USAID) to provide assistance to nongovernmental organizations to purchase the commercial debt of foreign countries as part of a debt-for-nature agreementagreements (P.L. 101-240; 22 U.S.C. 2282-2286). Several nongovernmental organizations participated in debt-for-nature swapstransactions with financial assistance from USAID; however, specific information on funds given by USAID to support three-party debt-for-nature swaps istransactions was not available.

While debt initiatives conducted with three-party swapstransactions are numerous, they have resulted in less reduction in total debt than the debts swapped under bilateral agreements (government-to-government), and slightly less in conservation funds generated. In total, approximately $170200 million in debt (face value) has been reduced, restructured, or swapped using this mechanism, generating approximately $140167 million in local currency for conservation purposes (see Table 1).

Table 1. Selected Countries Participating in Three-Party Debt-for-Nature SwapsTransactions, 1987-Present (excluding TFCA transactions)

(U.S.$, in thousands)

Country

Year

Purchaser

Cost

Face Value of Debt

Conservation Funds Generated

BOLIVIA

1993

TNC/WWF

$0

$11,500

$2,860

 

1987

CI

100

650

250

Total Bolivia

 

 

100

12,150

3,110

BRAZIL

1992

TNC

748

2,200

2,200

COSTA RICA

1991

RA/MCL/
TNC

360

600

540

 

1990

SW/WWF/
TNC

1,953

10,574

9,603

 

1989

TNC

784

5,600

1,680

 

1989

Sweden

3,500

24,500

17,100

 

1988

Holland

5,000

33,000

9,900

 

1988

NPF

918

5,400

4,050

Total Costa Rica

 

 

12,515

79,674

42,873

DOMINICAN REP.

1990

PRCT/TNC

116

582

582

ECUADOR

1992

Japan

NA

NA

1,000

 

1989

WWF/FN

640

5,400

5,400

 

1987

WWF

354

1,000

1,000

Total Ecuador

 

 

994

6,400

7,400

GHANA

2000

CI

80

100

90

 

1991

CI/SI

250

1,000

1,000

Total Ghana

 

 

330

1,100

1,090

GUATEMALA

1992

CI/USAID

1,200

1,334

1,334

 

1991

TNC

75

100

90

Total Guatemala

 

 

1,275

1,434

1,424

JAMAICA

1991

TNC/USAID/
PRCT

300

437

437

MADAGASCAR

2008

WWF/France

n/a

n/a

20,000

 

1996

WWF/Netherlands Development Corporation

n/a

2,000

1,500

 

1994

WWF/JPM

0

1,341

1,072

 

1994

CI

50

200

160

 

1993

WWF

909

1,868

1,868

 

1993

CI

1,500

3,200

3,200

 

1991

CI/UNDP

59

118

119

 

1990

WWF

446

919

919

 

1989

WWF/USAID

950

2,111

2,111

Total Madagascar

 

 

3,914

11,757

30,949

MEXICO

1998

CI

256

550

318

 

1996

CI

192

391

254

 

1996

CI

327

496

443

 

1996

CI

440

671

561

 

1995

CI/USAID

246

488

337

 

1994

CI

399

480

480

 

1994

CI

236

280

280

 

1994

CI

248

290

290

 

1993

CI

208

252

252

 

1992

CI/USAID

355

441

441

 

1991

CI

0

250

250

 

1991

CI

183

250

250

Total Mexico

 

 

3,092

4,838

4,155

NIGERIA

1991

NCF

65

150

93

PERU

1993

WWF

n/a

2,860

1,573

 

2002

WWF, CI, TNC, U.S.

5,500

14,000

10,600

Total Peru

 

 

5,500

16,860

12,173

PHILIPPINES

1993

WWF

13,000

19,000

17,100

 

1992

WWF/USAID

5,000

10,000

9,000

 

1990

WWF/USAID

439

900

900

 

1989

WWF

200

390

390

Total Philippines

 

 

18,639

30,290

29,090

POLAND

1990

WWF

11

50

50

ZAMBIA

1989

WWF

454

2,270

2,500

 

 

 

 

 

 

Grand Total

 

 

60,501

170,192

139,127

Sources:
M. Moye, Commercial Debt-for-Nature Swaps: Summary Table (Washington, DC: World Wildlife Fund, 2003).

M. Guerin-McManaus, Ten Years of Debt for Nature Swaps 1987-1997 (Washington, DC: Conservation International, 2000).

The World Bank, World Debt Tables, 1996 (Washington, DC: The World Bank, 1996).

(in thousands of dollars)

Country

Year

Purchaser

Cost

Face Value of Debt

Conservation Funds Generated

Bolivia

1993

TNC/WWF

$0

$11,500

$2,860

 

1987

CI

100

650

250

Total Bolivia

   

100

12,150

3,110

Brazil

1992

TNC

748

2,200

2,200

Costa Rica

1991

RA/MCL/ TNC

360

600

540

 

1990

SW/WWF/ TNC

1,953

10,574

9,603

 

1989

TNC

784

5,600

1,680

 

1989

Sweden

3,500

24,500

17,100

 

1988

Holland

5,000

33,000

9,900

 

1988

NPF

918

5,400

4,050

Total Costa Rica

   

12,515

79,674

42,873

Dominican Republic

1990

PRCT/TNC

116

582

582

Ecuador

1992

Japan

NA

NA

1,000

 

1989

WWF/FN

640

5,400

5,400

 

1987

WWF

354

1,000

1,000

Total Ecuador

   

994

6,400

7,400

Ghana

2000

CI

80

100

90

 

1991

CI/SI

250

1,000

1,000

Total Ghana

   

330

1,100

1,090

Guatemala

1992

CI/USAID

1,200

1,334

1,334

 

1991

TNC

75

100

90

Total Guatemala

   

1,275

1,434

1,424

Jamaica

1991

TNC/USAID/ PRCT

300

437

437

Madagascar

2008

WWF/France

n/a

n/a

20,000

 

1996

WWF/Netherlands Development Corporation

n/a

2,000

1,500

 

1994

WWF/JPM

0

1,341

1,072

 

1994

CI

50

200

160

 

1993

WWF

909

1,868

1,868

 

1993

CI

1,500

3,200

3,200

 

1991

CI/UNDP

59

118

119

 

1990

WWF

446

919

919

 

1989

WWF/USAID

950

2,111

2,111

Total Madagascar

   

3,914

11,757

30,949

Mexico

1998

CI

256

550

318

 

1996

CI

192

391

254

 

1996

CI

327

496

443

 

1996

CI

440

671

561

 

1995

CI/USAID

246

488

337

 

1994

CI

399

480

480

 

1994

CI

236

280

280

 

1994

CI

248

290

290

 

1993

CI

208

252

252

 

1992

CI/USAID

355

441

441

 

1991

CI

0

250

250

 

1991

CI

183

250

250

Total Mexico

   

3,092

4,838

4,155

Nigeria

1991

NCF

65

150

93

Peru

1993

WWF

n/a

2,860

1,573

 

2002

WWF, CI, TNC, U.S.

5,500

14,000

10,600

Total Peru

   

5,500

16,860

12,173

Philippines

1993

WWF

13,000

19,000

17,100

 

1992

WWF/USAID

5,000

10,000

9,000

 

1990

WWF/USAID

439

900

900

 

1989

WWF

200

390

390

Total Philippines

   

18,639

30,290

29,090

Poland

1990

WWF

11

50

50

Seychelles

2015

TNC/PC

n/a

30,000

28,500

Zambia

1989

WWF

454

2,270

2,500

Sources: Several sources, including M. Moye, Commercial Debt-for-Nature Swaps: Summary Table (Washington, DC: World Wildlife Fund, 2003); M. Guerin-McManaus, Ten Years of Debt for Nature Swaps 1987-1997 (Washington, DC: Conservation International, 2000); and World Bank, World Debt Tables, 1996 (Washington, DC: The World Bank, 1996).

Notes: A cost of $0 indicates that funds were written off by the bank to restructure the debt.Funds generated may be cash or bonds. Figures given do not include interest earned over the life of the bonds. Full titles of abbreviations are given below. Grand total given is an estimate since some figures were not available. n/a = not available.Notes:
A cost of $0 indicates that funds were written off by the bank to restructure the debt.

Funds generated may be cash or bonds. Figures given do not include interest earned over the life of the bonds. Full titles of abbreviations are given below. Grand total given is an estimate since some figures were not available.

USAID = Agency for International Development

CABEI = Central American Bank for Economic Integration

CI = Conservation International

FN = Fundacion Natura

JPM = J. P. Morgan Chase and Co.

MBG = Missouri Botanical Garden

MCL = Monteverde Conservation League

NCF = Nigerian Conservation Foundation

NPF = National Parks Fdn. of Costa Rica

PC = Paris ClubPRCT = Puerto Rican Conservation Trust

RA = Rainforest Alliance

SI = Smithsonian Institution

TNC = The Nature Conservancy

UNDP = United Nations Development Prog.

U.S. = U.S. federal government

USAID = U.S. Agency for International DevelopmentWWF = World Wildlife Fund

Bilateral and Multilateral Debt-for-Nature Initiatives

Bilateral debt transactions are conducted with official (public) funds directly between the creditor and debtor governments. The creditor government determines the criteria for eligibility, which usually involve the existence of certain financial and political conditions in the debtor country. Debt agreements are usually cancelled and then restructured to extend payback periods, or in some cases, debt is bought back by the debtor country for a discounted price. Money for the environment can be generated through interest payments from the debtor country if the debt is restructured, or from a percentage of the buyback price (see Figure 2). Multilateral debt-for-nature agreements have also been conducted between more than one creditor country and a debtor country (see Table 2). Poland, for example, benefitted from a multilateral debt-for-nature agreement from 1991 to 1997. During this time, five countries restructured debt obligations with Poland, generating over $473 million in local currency for environmental projects. The United States was the primary participant in this deal, swapping 10% of Poland's debt to generate $367 million for environmental programs.3

(See Table 2.) Table 2. Countries Other than the U.S.United States Participating in
Bilateral and Multilateral Bilateral and Multilateral Debt-for-Nature Initiatives

(U.S.$, in thousands)

(in thousands of dollars, except where noted)

Creditor                                                                                                       SourcesValue of Debt Treated

Creditor

Debtor Country

Year

Debtor Country

Year

Face Value of Debt Treated

Conservation Funds Generated

Canada

Columbia

1993

$12,000

$12,000

El Salvador

1993

7,500

6,000

Honduras

1993

24,900

12,450

Nicaragua

1993

13,600

2,700

Peru

1994

11,250

3,800

Belgium

Bolivia

1992

13,000

n/a

Finland

Poland

1990

17,000

17,000

Peru

1995

18,900

8,100

France

Egypt

1992

n/a

11,600

Philippines

1992

n/a

4,000

Poland

1993

66,000

66,000

Cameroon

2006

n/a

25,000

Mozambique

2015

17,500 (in euros)

2,000 (in euros)

Germany

Peru

1994

16,079

6,100

Jordan

1995

13,400

6,700

Jordan

1995

22,700

11,300

Philippines

1996

5,800

1,800

Vietnam

1996

18,200

5,400

Bolivia

1997

3,700

1,150

Honduras

1999

1.068

534

Peru

1999

5,140

2,060

Vietnam

1999

16,400

5,000

Jordan

2000

43,600

21,800

Bolivia

2000

15,800

3,200

Jordan

2001

11,300

5,700

Vietnam

2001

7,000

n/a

Syria

2001

31,700

15,900

Ecuador

2002

9,500

3,081

Ecuador

2002

10,200

3,235

Madagascar

2003

25,092

14,843

Indonesia

2003

n/a

n/a

Indonesia

2004

29,250

n/a

Indonesia

2006

13.7 (in euros)

6.3 (in euros)

Indonesia

2006

13.7 (in euros)

6.3 (in euros)

Indonesia

2007

n/a

n/a

Mozambique

2014

n/a

10,000 (in euros)

Holland

Peru

1996

n/a

n/a

Costa Rica

1996

14,100

14,100

Costa Rica

1988

33,000

9,900

Italy

Poland

1998

32,000

32,000

Egypt

2001

n/a

n/a

Norway

Egypt

1993

17,300

n/a

Egypt

1993

6,200

n/a

Nigeria

1993

10,200

n/a

Poland

2000

27,000

27,000

Spain

Costa Rica

1999

5,222

2,180

Sweden

Costa Rica

1989

24,500

17,100

Tunisia

1992

1,100

1,100

Tunisia

1993

520

520

Bolivia

1993

35,400

3,900

Poland

1997 & 1999

13,000

13,000

Switzerland

Peru

1992

130,800

32,600

Tanzania

1993

22,200

3,300

Bolivia

1993

35,400

1,365

Poland

1993

48,000

48,000

Honduras

1993 &1997

42,030

8,430

Ecuador

1994

46,300

4,524

Bulgaria

1995

16,700

16,200

Egypt

1995

23,000

18,000

Guinea Bissau

1995

8,400

400

Philippines

1995

16,100

16,100

U.K.

Nigeria

1993

7,300

n/a

Tanzania

1993

15,400

15,400

Conservation Funds Generated

Canada

Columbia

1993

12,000

12,000

 

El Salvador

1993

7,500

6,000

 

Honduras

1993

24,900

12,450

 

Nicaragua

1993

13,600

2,700

 

Peru

1994

11,250

3,800

Belgium

Bolivia

1992

13,000

n/a

Finland

Poland

1990

17,000

17,000

 

Peru

1995

18,900

8,100

France

Egypt

1992

n/a

11,600

 

Philippines

1992

n/a

4,000

 

Poland

1993

66,000

66,000

 

Cameroon

2006

n/a

25,000

Germany

Peru

1994

16,079

6,100

 

Jordan

1995

13,400

6,700

 

Jordan

1995

22,700

11,300

 

Philippines

1996

5,800

1,800

 

Vietnam

1996

18,200

5,400

 

Bolivia

1997

3,700

1,150

 

Honduras

1999

1.068

534

 

Peru

1999

5,140

2,060

 

Vietnam

1999

16,400

5,000

 

Jordan

2000

43,600

21,800

 

Bolivia

2000

15,800

3,200

 

Jordan

2001

11,300

5,700

 

Vietnam

2001

7,000

n/a

 

Syria

2001

31,700

15,900

 

Ecuador

2002

9,500

3,081

 

Ecuador

2002

10,200

3,235

 

Madagascar

2002

25,092

14,843

 

Indonesia

2003

n/a

n/a

 

Indonesia

 

 

 

Holland

Peru

1996

n/a

n/a

 

Costa Rica

1996

14,100

14,100

 

Costa Rica

1988

33,000

9,900

Italy

Poland

1998

32,000

32,000

Norway

Egypt

1993

17,300

n/a

 

Egypt

1993

6,200

n/a

 

Nigeria

1993

10,200

n/a

 

Poland

2000

27,000

27,000

Spain

Costa Rica

1999

5,222

2,180

Sweden

Costa Rica

1989

24,500

17,100

 

Tunisia

1992

1,100

1,100

 

Tunisia

1993

520

520

 

Bolivia

1993

35,400

3,900

 

Poland

1997 & 1999

13,000

13,000

Switzerland

Peru

1992

130,800

32,600

 

Tanzania

1993

22,200

3,300

 

Bolivia

1993

35,400

1,365

 

Poland

1993

48,000

48,000

 

Honduras

1993 &1997

42,030

8,430

 

Ecuador

1994

46,300

4,524

 

Bulgaria

1995

16,700

16,200

 

Egypt

1995

23,000

18,000

 

Guinea Bissau

1995

8,400

400

 

Philippines

1995

16,100

16,100

U.K.

Nigeria

1993

7,300

n/a

 

Tanzania

1993

15,400

15,400

Source: Various sources and R. Curtis. "Bilateral Debt Conversions for the Environment, Peru: An Evolving Case Study," IUCN World Conservation Congress, Montreal (1996). n/a = information not available.

: Various sources and R. Curtis. "Bilateral Debt Conversions for the Environment, Peru: An Evolving Case Study," IUCN World Conservation Congress, Montreal (1996).

Note: n/a = information not available.

U.S. Bilateral Debt-for-Nature Initiatives

The model for bilateral debt-for-nature agreements conducted by the United States was first defined in 1990 by the Enterprise for the Americas Initiative (EAI; Title 15, Section 1512 of the Food, Agriculture Conservation and Trade Act of 1990, "1990 Farm Billfarm bill," P.L. 101-624; 7 U.S.C. 1738) and has since been expanded numerous times (see Appendix). It was last amended by the Tropical Forest Conservation Act (TFCA) in 1998 (P.L. 105-214; 22 U.S.C. 2431).

Figure 2. An Example of a Bilateral Debt-for-Nature Transaction
Modeled After the TFCA

The Enterprise for the Americas InitiativeModeled After the TFCA

Source: Congressional Research Service.

The EAI legislation authorizes the sale, reduction, cancellation, and country buyback of eligible debt of Latin American and Caribbean countries that meet certain criteria. The debt authorized to be treated include the following types:P.L. 480 debtP.L. 4804 (P.L. 101-624; 7 U.S.C. 1738m, p-r, etc.), AID AID debt5 (P.L. 102-549; 22 U.S.C. 2430 and 2421), CCC CCC debt6 (P.L. 102-549; 22 U.S.C. 2430 and 2421), and Exim Exim debt7 (P.L. 102-429; 12 U.S.C. 635i-6) debt of eligible Latin American and Caribbean countries.8 8 Debtor countries must meet certain political and macroeconomic criteria in order to be eligible. Eligible countries are required to (1) have a democratically elected government, (2) not support terrorism, (3) not fail to cooperate with the United States on drug control, and (4) not engage in gross violations of human rights. From an economic perspective, eligible countries are required to have (1) an IBRD (International Bank for Reconstruction and Development (IBRD) or ) or IDA (International Development Association (IDA) structural or sectoral adjustment loan or its equivalent, (2) a macroeconomic agreement with the International Monetary Fund or equivalent, and (3) instituted investment reforms, as evidenced by a bilateral investment treaty with the United States, an investment sector loan, or progress towards implementing an open investment regime. Each country that participates in the EAI must enter into an America'sAmericas Framework Agreement with the United States to establish an America'sAmericas Trust Fund and create enforcement mechanisms to insure payments into the fund and prompt disbursements out of the fund.9 Funds can be used to support environmental, natural resource, health protection, and child development programs within the debtor country.

Debt swaps, buybacks, and restructuring are three mechanisms usedauthorized to conduct debt-for-nature transactions under the EAI. Seven of the eight countries that have participated in debt-for-nature transactions under the EAI used the debt-restructuring mechanism to generate environmental funds (see Table 3); only Peru took advantage of the debt buyback option. In a debt-restructuring agreement, the original debt agreement is cancelled (i.ee.g., a percentage of the face value of the debt iscould be reduced) and a new debt agreement is created with a provision for an annual amount of money (in local currency) to be deposited into an environmental fund. In 1992, for example, the United States reduced 10% of a $310 million (face value) debt owed by Colombia by 10% in return for thea total deposit of $41.6 million in local currency into an environmental fund managed by the Colombian government over 10 years.10 In a debt buyback, the debtor country purchases its debt at a reduced price. The lesser of either 40% of the repurchase price or the difference between the face value of the debt and the repurchase price is deposited in local currency into an environmental trust to support environmental and child support programs in the debtor country (P.L. 104-107, Title V, Sec. 574). For example, in 1998 Peru took advantage of this program and bought back $177 million in debt for $57 million, generating nearly $23 million (40% of the repurchase price) in local currency funds for conservation and child development programs. For all eight debtor countries, nearlymore than $1 billion (face value) of debt was reduced from a total debt of $1.89 billion, and almost $180 million of conservation funds were generated under the guidelines of the EAI (see Table 3).

Six All deposits into EAI funds have stopped, and some countries continue to award grants from their funds. Five transactions under the EAI continued to operate in 20102015 (Chile, Uruguay, and Bolivia and Uruguay have been concluded). Argentina's program expired in 2015. These programs support small projects with grants and monitor existing projects that have been funded. Some examples of projects include coastal zone marine management and hurricane relief projects in Jamaica, environmentally based development projects in the Peruvian Andes, and community productionconservation grants in Bolivia.11

Table 3. U.S. Bilateral Debt-for-Nature Transactions Under EAI

(U.S.$, in thousands)

Country

Year

Face Value Reduction

Face Value of Debt

Conservation Funds Generated

Duration (years)

Bolivia

1991

30,700

38,400

21,800

15

El Salvador

1992

463,300

613,000

41,200

20

Uruguay

1992

3,700

34,400

7,030

12

Columbia

1992

31,000

310,000

41,600

10

Chile

1991 & 1992

31,000

186,000

18,700

10

Jamaica

1991 & 1993

311,000

406,000

21,500

19

Argentina

1993

3,800

38,100

3,100

14

Peru

1998

120,000

177,000

22,840

n/a

TOTAL

 

993,998

1,803,300

177,770

 

Source: The United States Department of Treasury. "The Operation of the Enterprise for the Americas Facility and the Tropical Forest Conservation Act, Report to Congress," March, 2001.

Tropical Forest Conservation Act

(in thousands of dollars)

Country

Year

Debt Reduction

Original Value of Debt

Conservation Funds Generated

Duration (years)

Bolivia

1991

$30,700

$38,400

$21,800

15

El Salvador

1992

469,900

614,000

41,200

20

Uruguay

1992

3,700

34,400

6,190

12

Columbia

1992

31,000

310,000

41,600

10

Chile

1991 & 1992

30,600

186,000

18,700

10

Jamaica

1991 & 1993

310,800

405,400

21,500

19

Argentina

1993

3,800

38,100

3,100

14

Peru

1998

177,000

350,000

22,840

n/a

TOTAL

 

1,057,500

1,976,300

176,930

 

Source: USAID, Enterprise for the Americas Initiative and the Tropical Forest Conservation Act: 2014 Financials Report, March 2015.

Note: EAI = Enterprise for the Americas Initiative (Title 15, Section 1512 of the Food, Agriculture Conservation and Trade Act of 1990, "1990 Farm Bill," P.L. 101-624; 7 U.S.C. 1738.)

Tropical Forest Conservation Act Acknowledging that tropical rainforests were valuable for preserving biodiversity, reducing atmospheric carbon dioxide, and regulating hydrological cycles, Congress sought to expand the EAI authorization to countries throughout the world with tropical forests. The result was the 1998 Tropical Forest Conservation Act (TFCA, P.L. 105-214; 22 U.S.C. 2431), which was established to generate funds to conserve tropical forests by reducing external debt in countries with such forests. TFCA is an extension of the Enterprise for the Americas Act, in that it allows debt swaps, debt restructuring, and debt buybacks to generate conservation funds. These funds, however, are specifically designated for the conservation of tropical forests and are not confined to Latin America. To date, 1314 countries have participated in this program, establishing 1520 agreements (Panama and Peruseveral countries have two agreements) that will reduce a total of at least $2090.0 million from the face value of their debts to the United States and generate $218.4310.2 million in local currency in the next 12-2613 years for tropical forest conservation projects (see Table 4). For 2009To date, the Republic of Indonesiathe Philippines completed the largest ever debt-for-nature swaptransaction under the TFCA.

Table 4. U.S. Bilateral Debt-for-Nature Transactions Under TFCA

(U.S.$, in thousands)

Countrya

Year

Budget Cost

Private Funds Leveragedb

Face Value Reduction of Debt

Conservation Funds Generated

Duration (years)

Bangladesh

2000

$6,000

$0.0

$600

$8,500

18

Belize

2001

5,500

1,300

1,400

9,000

26

El Salvador

2001

7,700

0.0

3,000

14,000

26

Peru I

2002

5,500

1,100

3,700

10,600

12

Philippines

2002

5,500

0.0

100

8,300

14

Panama I

2003

5,600

1,200

10,000

10,000

14

Columbia

2004

7,000

1,400

n/a

10,000

12

Panama II

2004

6,500

1,300

n/a

10,900

12

Jamaica

2004

6,500

1,300

n/a

16,000

20

Paraguay

2006

4,800

0.0

n/a

7,400

12

Guatemala

2006

15,000

2,000

n/a

24,400

15

Botswana

2006

7,000

0.0

n/a

8,300

10

Costa Rica

2007

12,600

2,500

n/a

26,000

16

Peru II

2008

19,600

0.0

n/a

25,000

7

Indonesia

2009

20,000

2.0

n/a

30,000

8

TOTAL

 

$124,800

$14,100

n/a

$218,400

n/a

Source: Email communications with Scott Lampman, 2004-2009, and U.S. Agency for International Development, Operation of the Enterprise of the Americas Facility and Tropical Forest Conservation Act, Annual Report to Congress (Washington, DC, March 2004-2009).

Note: In the transaction with Peru in 2002, $1.1 million was given by The in 2013.

Subsidized Debt Swap

In 2001, a different form of a debt-for-nature transaction emerged under the TFCA. The Nature Conservancy and the United States agreed to share costs to buy down a portion of debt that Belize owed to the United States. This partnership in debt-for-nature transactions is referred to as a subsidized debt swap. In a subsidized debt swap, an NGO generally matches a portion of the U.S. government contribution toward a debt-for-nature transaction. For example, in a transaction with Panama in 2003, the U.S. government provided $5.6 million and the Nature Conservancy provided $1.2 million to reduce Panama's debt by $10 million and generate $10 million in conservation funds. The transaction is completed when three agreements are signed: (1) the U.S. government and the beneficiary country sign a debt-restructuring agreement; (2) the U.S. government and the NGO sign an agreement to transfer NGO funds; and (3) the NGO and the beneficiary country sign a Forest Conservation Agreement.12 In a subsidized swap, the U.S. government is not a signatory to the Forest Conservation Agreement, yet it generally has representatives on the oversight committee.13

Table 4. U.S. Bilateral Debt-for-Nature Transactions Under TFCA

(in thousands of dollars)

Countrya

Year

Budget Costb Private Funds Leveragedc

Face Value Reduction of Debt

Conservation Funds Generated

Duration (years)

Bangladesh

2000

$6,000

$0.0

$600

$8,500

18

Belize

2001

5,500

1,300

1,400

9,000

26

El Salvador

2001

7,700

0.0

3,000

14,000

26

Peru I

2002

5,500

1,100

3,700

10,600

12

Philippines I

2002

5,500

0.0

100

8,300

14

Panama I

2003

5,600

1,200

10,000

10,000

14

Columbia

2004

7,000

1,400

n/a

10,000

12

Panama II

2004

6,500

1,300

n/a

10,900

12

Jamaica

2004

6,500

1,300

n/a

16,000

20

Paraguay

2006

4,800

0.0

n/a

7,400

12

Guatemala

2006

15,000

2,000

n/a

24,400

15

Botswana

2006

7,000

0.0

n/a

8,300

10

Costa Rica I

2007

12,600

2,500

n/a

26,000

16

Peru II

2008

19,600

0.0

n/a

25,000

7

Indonesia I

2009

20,000

2,000

n/a

30,000

8

Brazil

2010

19,500

0.0

20,800

21,000

5

Costa Rica II

2010

19,600

3,900

21,000

27,000

15

Indonesia II

2011

19,800

3,960

28,500

28,500

7

Philippines II

2013

28,200

0

n/a

31,800

10

Indonesia III

2014

11,200

560

n/a

12,700

7

TOTAL

 

310,200

22,520

n/a

339,400

n/a

Sources: Email communications with Office of the Tropical Forest Conservation Act Secretariat, USAID 2004-2009, and the USAID, Operation of the Enterprise of the Americas Facility and Tropical Forest Conservation Act, Annual Report to Congress (Washington, DC, March 2004-2009). USAID, Enterprise for the Americas Initiative and the Tropical Forest Conservation Act: 2014 Financials Report, March 2015.

Notes: In the transaction with Peru in 2002, a total of $1.1 million was given by the Nature Conservancy, World Wildlife Fund, and Conservation International, and $5.5 million was given by the U.S. government. n/a = not available.

a. The Republic a. The Kingdom of Thailand signed a debt -reduction agreement in September 2001. The signing of the second required agreement, the Tropical Forest Agreement (TFA), never took place. The Thai government annulled the agreement on January 30, 2003, amidst false media reports that warned that the U.S. government would retain control over forests involved in the agreement.

b. b. The budget cost of the debt is the funding provided by the U.S. government to reduce the face value of the original debt. c. In some debt-for-nature transactions, a third party is involved (generally a non-governmental organization or NGO) in the process and subsidizes a portion of the debt-reduction done by the United States. Non-governmental organizationsFor example, NGOs such as the World Wildlife Fund, Thethe Nature Conservancy, and Conservation International have subsidized these transactions.

To be eligible for this program, a developing country must contain at least one tropical forest with unique biodiversity, or a tropical forest tract that is representative of a larger tropical forest on a global, continental, or regional scale.1214 Political and macroeconomic criteria for eligibility are almost identical to those used for participation under the EAI.1315 Conservation funds (in local currency) from these transactions are deposited in a tropical forest fund for each country. The fund is overseen by an administrating body composed of one or more appointees chosen by the U.S. government and the government of the beneficiary country, and individuals who represent a broad range of environmental, academic, and scientific organizations in the beneficiary country (the majority of the board is represented by these individuals). This fund operates in the same manner as the America'sAmericas Fund: Local currency payments of interest accrued on restructured loans are deposited into a tropical forest fund and serve as the principal. Interest earned from this principal balance and the principal itself is usually given in the form of grants to fund tropical forest conservation projects. Eligible conservation projects include (1) the establishment, maintenance, and restoration of parks, protected reserves, and natural areas, and the plant and animal life within them; (2) training programs to increase the capacity of personnel to manage parks; (3) development and support for communities residing near or within tropical forests; (4) development of sustainable ecosystem and land management systems; and (5) research to identify the medicinal uses of tropical forest plants and their products.

The TFCA was reauthorized for appropriations in 2004, including $20 million for FY2005, $25 million for FY2006, and $30 million for FY2007. This law also authorizes funds to conduct audits and evaluations of debt-for-nature programs. A "TFCA Evaluation Sheet" has been created to evaluate the performance of TFCA country programs. The Evaluation Sheetevaluation sheet establishes criteria for TFCA program categories and functions and will beis completed each year by the U.S. government representative on the local TFCA board or oversight committee. Some of the programs under the TFCA are in beginning stages and have not disbursed grants to local non-government organizations. However, in Peru, El Salvador, and Belize, some grants have been disbursed for projects and project monitoring has begun. This law would also allow the principal of restructured loans to be used in debt-for-nature transactions. Currently, interest accrued on restructured loans are deposited into a tropical forest fund for disbursement.

Congressional Role in Debt-for-Nature Initiatives

Authority for Debt-for-Nature Initiatives

Early debt-for-nature legislation concentrated on understanding and promoting third-party debt-for-nature swaps (see Appendix for legislation summaries and United States Code citations). Congress in 1989 directed the Secretary of the Treasury to ask the U.S. Executive Director of the World Bank to develop a pilot debt-for-nature program and other ways of reducing debt owed by foreign countries while generating funds for the environment. A subsequent law, the International Development and Finance Act of 1989, authorizes USAID to make grants to nongovernmental organizations (NGOs) to purchase debt in three-party swaps. Official (public) P.L. 480 debt owed to the United States by eligible Latin American countries was authorized to be reduced by the 1990 farm bill (P.L. 101-624; 7 U.S.C. 1738b). The 102nd Congress authorized debt reduction for foreign assistance loans made by USAID (P.L. 102-549; 22 U.S.C. 2430 and 2421), the Export-Import Bank (P.L. 102-429; 12 U.S.C. 635i-6), and the Commodity Credit Corporation (P.L. 102-549; 22 U.S.C. 2430 and 2421). Together, the P.L. 480, USAID, CCC, and Ex-Im debt reduction authorizations were undertaken as part of President George H. W. Bush's Enterprise for the Americas Initiative. In 1996, USAID was further authorized by Congress to conduct swaps, buybacks, and cancellations of debt owed to the United States by eligible Latin American and Caribbean countries (P.L. 104-107). In 1998, the Tropical Forest Conservation Act (TFCA) was passed, allowing debt swaps, buybacks, and restructuring to generate funds for tropical forest conservation worldwide.

Funding for the TFCA was reauthorized by Congress in 2004 (P.L. 108-323) and is currently being considered for authorization in the 111th Congress under H.R. 52 and S. 345. Both bills would expand the TFCA to include coral reefs and associated coastal marine ecosystems.14 H.R. 52 would authorize $30 million annually in appropriations for the TFCA from FY2007 through FY2011; S. 345 would reauthorize $25 million in FY2009, and $30 million annually from FY2010 through FY2012.

This law also authorizes the use of the principal of restructured loans for debt-for-nature transactions. Issues for Congress Rationale for and Criticism of Debt-for-Nature Initiatives

Advocates of debt-for-nature initiatives argue that reducing debt in developing countries will help create free-market systems (as part of the reforms required for eligibility), stimulate economic growth and trade liberalization, provide incentives for foreign investment, and help protect the environment. Converting hard currency debts to local currency debts, advocates argue, will lower debt burdens on developing countries and in the long run may reduce resource extraction at the expense of the environment. Critics of debt-for-nature initiatives argue that only a small percentage of debt is reduced, thereby minimizing the positive benefits of debt reduction in developing countries. For example, in some transactions under the TFCA, the interest paid for the debt is used for conservation projects, while the principle of the debt remains. Supporters point out that whilealthough the percentage of debt reduced by debt-for-nature transactions is small, conservation funds generated for debtor countries arethe establishment of laws, programs, and funds dedicated to conservation that follows debt-for-nature initiatives in debtor countries is generally significant relative to what the country originally would have originally spent on conservation.1516 The relationship between debt reduction and lower resource extraction rates is controversial. Some analysts suggest that debt reduction has no direct relationship to lower extraction rates of minerals or timber in developing countries with foreign debt.16

17 Advocates of debt-for-nature initiatives note that the United States has a history of supporting debt reduction initiatives in developing countries and appropriating funds for environmental causes. Recent appropriations by the United States to supportFor example, the Heavily Indebted Poor Countries (HIPC) initiative (22 U.S.C. §262p-6) support the claim for reducingaims to reduce debt in developing countries.1718 HIPC was created by international creditors, the World Bank, and IMF to reduce debt of poor countries that have demonstrated social and economic policy reforms that enable fluid export revenues and capital inflows.1819 Funds generated for the environment in developing countries are argued toarguably improve local environmental conditions, promote sustainable resource use, and help to preserve global biodiversity and ecosystem services.

Critics argue that such benefits are limited in scope because conservation spending is unbalanced. The majority of conservation funds are often directed toward a few areas and specific projects that already feature work by organizations and researchers and do not address other areas that are equally rich in biodiversity.20 Advocates also suggest that debt-for-nature transactions that generate funds to support tropical forest conservation are especially appropriate to address climate change. Deforestation1921 is responsible for the largest share of additional carbon dioxide (CO2) released to the atmosphere due to land use changes, approximately 20% of total anthropogenic greenhouse gas (GHG) emissions annually.2022 Much of the deforestation responsible for CO2 releases occurs in tropical regions, specifically in developing countries such as Brazil, Peru, Indonesia, and the Democratic Republic of the Congo. MostSome of these tropical countries with high levels of total debt owed to the United States also have some of the largest areas of tropical forest cover. For example, Brazil and Peru have debts to the United States totaling over $1 billion each, and have two of the largest areas of tropical forest cover in the world.2123 Other countries, such as the Democratic Republic of Congo and Sudan, also fit this pattern; however, these countries may be ineligible for debt-for-nature transactions under the TFCA due to political and economic eligibility requirements.22

24 Those who oppose debt-for-nature transactions often argue that they are not adequately enforced by debtor countries, generate insufficient funds to improve environmental problems, and may infringe on national sovereignty.2325 Three-party debt swapstransactions have historically had weak enforcement mechanisms; however, bilateral debt swapstransactions such as those conducted under the EAI generally include safeguards and default provisions to protect the U.S. government from losing funds. National sovereignty became an issue with the first debt-for-nature swap in Bolivia when a conservation organization was reported to have obtained title to forested lands. There was a public outcry and ensuing political crisis when the Bolivian people thought a large part of their country had been given to a foreign organization. Consequently, conservation organizations involved in recent three-party swapstransactions have generally refrained from directly buying land in debtor countries with conservation funds earned from swaps.

debt-for-nature transactions. Decline of Debt-for-Nature Transactions

The number of debt-for-nature transactions has declined in recent years, perhaps due to accounting changes that require greater appropriations to fund debt-for-nature transactions with official (public) debt, and a higher price of commercial debt on the secondary market (see Figure 3). Before 1991, no appropriations were required for debt cancellations, and the United States cancelled between $11 billion and $12 billion in debt between 1988 and 1991. This changed with the Federal Credit Reform Act of 1990 (2 U.S.C. 661a et seq.). This law requires that the net present value (NPV) of debts owed to the United States of debts ofby foreign countries be used to reportcalculate the cost of debt restructuring, buybacks, swaps, and cancellations to the U.S. government. The NPV of the cash flow of the loan is calculated often giving consideration to projected default losses, fees, and interest subsidies. Therefore, appropriated funds for these programs must be used to cover the interest fee no longer coming to the United States (in the case of funds set up under EAI and TFCA) and the difference in the NPV of the loan that may result from restructuring.24

Funds appropriated by Congress for conducting debt-for-nature transactions cover the cost of loan modifications, which could include a face-value reduction in the amount of eligible debt owed to the United States. TFCA has not received appropriations since FY2014, and none are requested for FY2017. A decline in three-party commercial debt-for-nature swapstransactions may also be due to the conclusion of Brady Plan operations by Latin American countries. The Brady Plan allowed for partial debt forgiveness with a restructuring of the remaining debt into bonds that could be traded on the securities markets. When this program was concluded, the price of debt on the secondary market increased and financing leverage decreased, making it difficult and less attractive for environmental organizations to acquire debt for resale.2526 Further, debt relief for developing countries is available through other programs that allow for relatively greater amounts of debt to be cancelled (e.g., HIPC). These programs may be more desirable to developing countries with debt than debt-for-nature initiatives under the EAI or TFCA. Under the TFCA, there was an 18-month period from 2004 to 2006 when no transactions were made, largely due to the length of time needed to negotiate and create debt-restructuring agreements. Lastly, the political and economic requirements needed to be eligible for debt-for-nature transactions make it difficult for several countries to participate in EAI or TFCA programs.

Figure 3. Three Party and Bilateral U.S. Debt-for-Nature Transactions 1987-2007

Source: Created by CRS.

Emergence of Subsidized Debt-for-Nature Transactions

In 2001, a different form of a debt-for-nature transaction emerged under the TFCA. The Nature Conservancy and the United States joined to buy down a portion of debt that Belize owed to the United States. This partnership in debt-for-nature transactions is referred to as a subsidized debt swap. In a subsidized debt swap, an NGO generally matches 20% of the U.S. government contribution toward a debt-for-nature transaction. For example, in a recent transaction with Panama in 2003, the U.S. government provided $5.6 million and The Nature Conservancy provided $1.2 million to reduce Panama's debt by $10 million and generate $10 million in conservation funds. The transaction is completed when three agreements are signed: (1) the U.S. government and the beneficiary country sign a debt restructuring agreement; (2) the U.S. government and the NGO sign an agreement to transfer NGO funds; and (3) the NGO and the beneficiary country sign a Forest Conservation Agreement.26 In a subsidized swap, the U.S. government is not a signatory to the Forest Conservation Agreement, yet generally has representatives on the oversight committee.27 Subsidized swaps have been implemented in the last three out of four transactions under the TFCA (see Table 4).28

Appropriations

Appropriations for debt reduction activities authorized by the EAI have totaled $90 million. Forty million dollars was appropriated for P.L. 480 debt reduction for FY1993 (P.L. 102-341) and $50 millionFigure 3. Total Debt-for-Nature Transactions 1987-2015

Source: Congressional Research Service.

Note: Some debt transactions during this time period may not be represented in this figure due to limited data available from international sources and organizations.

Effectiveness of Debt-for-Nature Transactions

Few studies have analyzed the effectiveness of debt-for-nature transactions. Because most of the transactions are relatively new, it would be difficult to comprehensively analyze their effectiveness in preventing the destruction of tropical forests. A recent study on deforestation in poor countries found that poor nations that have implemented debt-for-nature transactions and have high levels of conservation funds tend to have lower rates of deforestation than countries that do not.27 Nevertheless, many conservation organizations support the framework of the TFCA and suggest that the TFCA should serve as a model for conserving other ecosystems, such as coral reefs and grasslands.

Appropriations Appropriations for debt reduction activities authorized by the EAI totaled $90 million; $40 million was appropriated for P.L. 480 debt reduction for FY1993 (P.L. 102-341) and $50 million was appropriated for other debt restructuring under EAI in FY1993 (P.L. 102-391). For debt reduction activities under TFCA, appropriations have totaled up to $117approximately $235.8 million from FY2000 to FY2006FY2014 (see Table 5). Appropriations are not authorized for FY2008 and beyond under TFCA.

Table 5. Appropriations Provided Under the
Tropical Forest Conservation Act of 1998

Fiscal Year

Appropriated Amount
($ in millions)

Annual Obligation
($ in millions)a

2000

$13.0

$7.0

2001

$13.0

$13.2

2002

Up to $25.0 ($11.0 was
given for the TFCA)b

$11.0

2003

Up to $40.0 ($20.0 was
given for the TFCA)

$5.6

2004

$19.8

$20.0

2005

$20.0

$0.0c

2006

$20.0

$20.0

2007

$20.0

$19.6

2008

$20.0

$19.6

2009

$20.0

$20.0

2010

$20.0

n/a

2011

(request is $20.0)

n/a

a. Cells with n/a indicate that funding totals are not available.

b. This figure consists of $5 million in direct funds and $6 million in funds transferred from unobligated balances.

c. No transactions under the TFCA were conducted in 2005.

Future Directions

Bilateral debt-for-nature initiatives implemented by the U.S. government have been supported with appropriations (e.g., under the EAI and now the TFCA authorization) for the last 10 years. Debt-for-nature transactions administered by the United States have focused on transactions under the TFCA. Since most of the transactions are relatively new, there have been no comprehensive analyses of their effectiveness in preventing the destruction of tropical forests. Some contend that a fair analysis might not be possible until 10 years after the implementation of a transaction. Nevertheless, many conservation organizations support the framework of the TFCA and suggest that it should serve as a model for conserving other ecosystems such as coral reefs and grasslands.

Transactions under the TFCA are expected to continue since it is included in strategies to address global climate change.29 Tropical forests make up the largest proportion of carbon stored in terrestrial land masses and are thought to be a carbon sink.30 Despite uncertainties on the part of some, it is generally thought that maintaining existing tropical forests will store carbon, and that preventing deforestation will reduce the entry of carbon into the atmosphere.31 Indeed, a recent debt-for-nature swap with Indonesia under the TFCA has been billed as a cooperative effort to deal with climate change by Indonesia.

Appendix. Authorization for appropriations under TFCA expired in FY2008, and Congress has not appropriated funding for the program since FY2013. Table 5. Appropriations for Debt-for-Nature Transactions Under TFCA

(in millions of dollars)

Fiscal Year

Appropriated Amount

Annual Obligation

2000

$13.0

$7.0

2001

13.0

13.2

2002

Up to 25.0 (11.0 was given for the TFCA)a

11.0

2003

Up to 40.0 (20.0 was given for the TFCA)

5.6

2004

19.8

20.0

2005

20.0

0.0

2006

20.0

20.0

2007

20.0

19.6

2008

20.0

19.6

2009

20.0

20.0

2010

20.0

39.1

2011

16.4

19.8

2012

12.0

0.0

2013

11.4

28.3

2014

0.0

11.2

2015

0.0

0.0

2016

0.0

0.0

Sources: Tropical Forest Conservation Act Secretariat, Enterprise for the Americas Initiative and Tropical Forest Conservation Act, 2014 Report, USAID, 2015, and federal appropriations laws. a. This figure consists of $5 million in direct funds and $6 million in funds transferred from unobligated balances. Future Directions

Bilateral debt-for-nature initiatives implemented by the U.S. government were supported through appropriations under programs such as the EAI and TFCA. Recently, appropriations for conducting debt-for-nature transactions under these programs have stopped. It is unclear why there is less interest in conducting debt-for-nature transactions. Some possibilities could include the following:

  • Eligible debt to conduct these transactions has decreased, making these transactions either insignificant or not allowed for some debtor countries.
  • The amount involved in the transactions is too small for some eligible countries to show interest in participating.
  • There is a lack of appropriations to support debt-for-nature transactions.
  • The focus on tropical forests (i.e., through TFCA) might be too narrow for many eligible countries.

Some Members of Congress contend that transactions under TFCA should continue because the program is included in strategies to address global climate change.28 Tropical forests make up the largest proportion of carbon stored in terrestrial land masses and are thought to be a carbon sink.29 Despite uncertainties on the part of some, it is generally thought that maintaining existing tropical forests will store carbon and that preventing deforestation will reduce the release of stored carbon into the atmosphere.30 The most recent debt-for-nature swap with Indonesia under the TFCA in 2014, for example, has been billed as a cooperative effort to deal with climate change.31However, no quantitative analyses have examined the amount of stored-carbon emissions reduced by TFCA efforts.

Appendix. List of Related Laws and Appropriations That Support Debt-for-Nature InitiativesContinuing Appropriations Act for 1988 (P.L. 100-202; Section 537(C)(1-
List of Related Laws and Appropriations That Support Debt-for-Nature Initiatives
  • Continuing Appropriations Act for 1988 (P.L. 100-202; Section 537(C)(1-3)). Directs Secretary of the Treasury to analyze initiatives that would enable developing countries to repay portions of their debt obligations through investments in conservation activities.
  • International Development and Finance Act of 1989 (P.L. 101-240; Title VII, Part A, Section 711) (22 U.S.C. 2282 - - 2286). Authorizes USAID to provide assistance to nongovernmental organizations to purchase debt of foreign countries as part of a debt-for-nature agreement (i.e., three-party swap). Authorizes USAID to conduct a pilot program for debt-for-nature swaps with eligible sub-Saharan African countries.
  • Support for East European Democracy (SEED) Act of 1989 (P.L. 101-179; Title I, Section 104) (22 U.S.C. 5414). Authorizes the President to undertake the discounted sale, to private purchasers, of U.S. government debt obligations from eligible Eastern European countries.
  • FY1990 Foreign Operations Appropriations Act (P.L. 101-167; Title V, Section 533(e)) (22 U.S.C. 262p-4i - 262p--4i - 262p-4j). Directs the Secretary of the Treasury to (1) support sustainable development and conservation projects when negotiating reduction of commercial debt and assisting with reduction of official (public) debt obligations, (2) encourage the World Bank to assist countries in reducing or restructuring private debt through environmental project and policy-based loans, and (3) encourage multilateral development banks to support lending portfolios that will allow debtor countries to restructure debt that may offer financial resources for conservation.
  • Enterprise for the AmericasAmericas Initiative (Title XV, Section 1512 of the Food, Agriculture Conservation and Trade Act of 1990) (P.L. 101-624; 104 Stat. 3658) (7 U.S.C. 1738b). Amends the Agriculture Development and Trade Act of 1954 to allow the President to reduce the amount of P.L. 480 sales credit debt owed to the United States by Latin American and Caribbean countries.
  • Export Enhancement Act of 1992 (P.L. 102-429; Title I, Section 108) (12 U.S.C. 635i--6). Authorizes the sale, reduction, cancellation, and buyback of outstanding Export-Import Bank (Exim) loans for EAI purposes.
  • Jobs Through Exports Act of 1992 (debt forgiveness authority under EAI) (P.L. 102-549; Title VI, Section 704) (22 U.S.C. 2430) and (22 U.S.C. 2421). Authorizes the sale, reduction, cancellation, and country buyback (through right of first refusal) of eligible Commodity Credit Corporation (CCC) debt. Also authorizes the reduction of foreign assistance (USAID) debt.
  • Enterprise for the AmericasAmericas Initiative Act of 1992 (P.L. 102-532) (7 U.S.C. 1738m, p--r, etc.). Establishes guidelines for debt-for-nature swaps for Latin American and Caribbean countries.
  • Agriculture Appropriations for FY1993 (P.L. 102-341). Provided $40 million for P.L. 480 debt reduction under EAI.
  • Foreign Operations Appropriations for FY1993 (P.L. 102-391). Provided $50 million for debt restructuring under EAI.
  • Foreign Operations Appropriations for FY1995 (P.L. 103-306; Title II, Section 534). Authorizes nongovernmental organizations associated with the Agency for International Development to place funds from economic assistance provided by USAID in interest-bearing accounts. Earned interest may be used for the purpose of the grants given.
  • Foreign Operations Appropriations for FY1996 (P.L. 104-107; Title V, Section 571). Provides authority to perform debt buybacks/swaps with eligible loans made before January 1, 1995. For buybacks, the lesser of either 40% of the price paid or the difference between price paid and face value must be used to support conservation, child development and survival, or community development programs (Title V, Section 574).
  • Tropical Forest Conservation Act of 1998 (P.L. 105-214) (22 U.S.C. 2431). Amends the Foreign Assistance Act of 1961 to facilitate the protection of tropical forests through debt restructuring, buybacks, and swaps in eligible developing countries with tropical forests.
  • Reauthorization of the Tropical Forest Conservation Act (P.L. 107-26). Authorizes the appropriation of $50 million, $75 million, and $100 million for FY2002, FY2003, and FY2004. Reduces the magnitude of investment reforms that must be in place for eligible countries.
  • Reauthorization of Appropriations under the Tropical Forest Conservation Act (P.L. 108-323). Authorizes the appropriation of $20 million, $25 million, and $30 million for FY2005, FY2006, and FY2007, respectively. Includes authorization for evaluating programs and allows for the principal on debt agreements to be treated by the debt-for-nature transaction.

Footnotes

Thomas E. Lovejoy III, "Aid Debtor Nations' Ecology," New York Times, October 4, 1984, secSec. A, p. 31.

2. U.S. Agency for International Development (USAID) foreign5. Commodity Credit Corporation (CCC) loans are given to developing countries to enable them to import U.S. agricultural products.

Developing country is defined as a "low-" or "middle- Instead of having in place major investment reforms in conjunction with an IADBInter-American Development Bank (IADB) loan or making progress toward implementing an open investment regime, the country must have in place a bilateral investment treaty with the United States, investment sector loans with the IADB, World Bank -supported reforms, or other measures as appropriate (22 U.S.C. 2431c).

For example, Ecuador reduced its external debt of $8.3 billion by only $1 million from a debt-for-nature swap, yet doubled its budget for parks and reserves with money received from the resulting conservation fund.

. . See CRS Report RL30214, Debt Reduction: Initiatives for the Most Heavily Indebted Poor Countries, by [author name scrubbed] (pdf).

Deforestation is the conversion of forests to pasture, cropland, urban areas, or other landscapes that have few or no trees. Afforestation is planting trees on lands that have not grown trees in recent years, such as abandoned cropland.

. Participation in three-party debt-for-nature swaps through USAID is not subject to the same economic and political criteria required for participation in TFCA and EAI debt-for-nature transactions. An eligible country must be committed to, plan for, and have a government or local nongovernmental organizationNGO responsible for the long-term viability of the programs under the swap agreement.

. For more information, see CRS Report R41144, Deforestation and Climate Change, by [author name scrubbed] and [author name scrubbed].

T. K. Rudel, Sequestering Carbon in Tropical Forests: Experiments, Policy Implications, and Climate Change, Society and Natural Resources, vol. 14 (2001), pp. 525-531.

1.

Author Contact Information

[author name scrubbed], Specialist in Natural Resources Policy ([email address scrubbed], [phone number scrubbed])

Footnotes

1.
2.

S. 566 defines associated coastal marine ecosystems as "any coastal marine ecosystem surrounding, or directly related to, a coral reef and important to maintaining the ecological integrity of that coral reef, such as seagrasses, mangroves, sandy seabed communities, and immediately adjacent coastal areas."

3.

Sometimes debt is donated to the nongovernmental organization (NGO) in the three-party swap.

4.

Sometimes debt is donated to the NGO in the three-party swap.

3.

Organization for Economic Cooperation and Development, "Swapping debt for the environment: The Polish EcoFund," Paris: EU Phare program (1996).

4.

P.L. 480 "Food for Peace" loans were low-interest loans given to developing countries to purchase U.S. agricultural products.

5.

USAID Foreign assistance loans.

6.

assistance loans.

6.
7.

Export-Import (Ex-Im) Bank loans are made to foreign importers of U.S. goods and services.

8.

Although debt under the P.L. 480 program was the first to be authorized for debt-for-nature transactions, authorization quickly followed for reduction of debt owed to the United States under three other programs: (1) Commodity Credit CorporationCCC programs, (2) Export-Import Bank loans, and (3) foreign aid loans administered by USAID.

9.

The America's The Americas Trust Fund can be either an endowed fund or a sinking fund depending on the agreement reached by the United States and the debtor country. Interest payments made by debtor countries on their new restructured loans are deposited into the fund. These payments form the principal of the fund, and interest earned on this principal and the principal itself can be used to fund environmental, community development, and child survival and development programs.

10.

R. Curtis, "Bilateral Debt Conversions for the Environment, Peru: An Evolving Case Study," IUCN World Conservation Congress, Montreal (1996).

11.

USAID, Enterprise for the Americas Initiative and the Tropical Forest Conservation Act: 2014 Financials Report, March 2015.

12.

In comparison, the U.S. government is a signatory on a Tropical Forest Agreement, which is used with debt-for-nature transactions that are not subsidized by an NGO.

13.

This agreement generally addresses the structure of the conservation fund, its administrative council, and the use of monies from the fund, among other things.

14.

Tropical Forest Conservation Act Secretariat, Operation of the Enterprise for the Americas Initiative and the Tropical Forest Conservation Act, 2006 Annual Report to Congress (Washington, DC: March 2007).

12.

Developing country is defined as a "low" or "middle" income country as determined by the International Bank for Reconstruction and Development in its World Development Report. In 2001According to 2013 data from the World Bank, the cutoff for low-income countries was a per capita annual income of $7451,045 or less. For middle-income countries, the range is $746-$9,205, and the cutoff is $9,205.

13.

for per capita annual income is more than $1,045 but less than $12,746.

15.
14.

S. 345 defines associated coastal marine ecosystems as "any coastal marine ecosystem surrounding, or directly related to, a coral reef and important to maintaining the ecological integrity of that coral reef, such as seagrasses, mangroves, sandy seabed communities, and immediately adjacent coastal areas." H.R. 52 does not have a definition for associated coastal marine ecosystems.

15.

16.
16 17.

Dal Didia, "Debt-for-Nature Swaps, Market Imperfections, and Policy Failures as Determinants of Sustainable Development and Environmental Quality," Journal of Economic Issues (2001), pp. 477-486; and Esben Brandi-Hanson and Kaspar Svarrer, "Debt-for-Nature Swaps: One or the Other, or Both?" Royal Veterinarian and Agricultural University of Denmark, Department of Economics, 1998, 17 pp.

17p. 17. 18.

Eligibility requirements for participating in the HIPCHeavily Indebted Poor Countries (HIPC) program include that a country must receive only concessional financing from the World Bank and IMFInternational Monetary Fund (IMF) (i.e., borrowing only from the World Bank's International Development Association (IDA)[IDA] and from the IMF's Enhanced Structural Adjustment Facility (ESAF)[ESAF]), establish a track record of economic reforms under IMF- and World Bank-sponsored programs, and hold a debt burden that is unsustainable under existing (Naples terms) relief arrangements.

18.

19.
19.

.

20.

John M. Shandra et al., "Do Commercial Debt-for-Nature Swaps Matter for Forests? A Cross National Test of World Polity Theory," Sociological Forum, vol. 26, no. 2 (June 2011), p. 387.

21.
20 22.

Intergovernmental Panel on Climate Change, "Working Group I Contribution to the Fourth Assessment Report of the Intergovernmental Panel on Climate Change," Climate Change 2007: The Physical Science Basis (2007). Available, at http://ipcc-wg1.ucar.edu/wg1/wg1-report.html. (HereafterHereinafter referred to as 2007 IPCC WG I Report.)

21 23.

U.S. Department of the Treasury and Office of Management and Budget, "United States Government Foreign Credit Exposure As of December 31st 1999," 2001;" (2001). Food and Agriculture Organization of the United Nations, "State of the World's Forests 2001," Rome (2001).

22.

2001.

24.
23 25.

R. T. Deacon and P. Murphy, "The Structure of an Environmental Transaction: The Debt-for-Nature Swap," Land Economics (1997), pp. 1-24.

24.

Stacy Warden, "The Tropical Forest Conservation Act," PowerPoint presentation, U.S. Department of Treasury, Washington, DC, 2001.

25.

The World Bank, "World Debt Tables, 1996," Washington, DC, 1996.

26.

The U.S. government is a signatory on a Tropical Forest Agreement, which is used with debt-for-nature transactions that are not subsidized.

27.

This agreement generally addresses the structure of the conservation fund, its administrative council, and the use of monies from the fund, among other things.

28.

Scott Lampman, "Debt Swaps Create New Conservation Opportunities,"Biodiversity 13 (2003), pp. 1-3.

29.

See http://www.whitehouse.gov/news/releases/2002/02/climatechange.html, last updated February 2002, and last accessed October 11, 2006. (Hereafter referred to as Climate Change Policy.)

30.

26.

The World Bank, "World Debt Tables, 1996," 1996.

27.

John M. Shandra et al., "Do Commercial Debt-for-Nature Swaps Matter for Forests? A Cross National Test of World Polity Theory," Sociological Forum, vol. 26, no. 2 (June 2011), pp. 401-402.

28.

Senator Rob Portman, "Portman Renews Efforts to Promote Conservation and Reduce Greenhouse Gas Emissions," press release, February 26, 2015, at http://www.portman.senate.gov/public/index.cfm/press-releases?ID=4E89FFE6-B315-460E-B3A3-6E5844619F9E.

29.
31.

.

30.
31. U.S. Embassy in Indonesia, "U.S. and Indonesia Award Grants to Promote Forest Conservation and Combat Climate Change," press release, April 29, 2014, at https://id.usembassy.gov/u-s-and-indonesia-award-grants-to-promote-forest-conservation-and-combat-climate-change-2/.