The Effects of Population and Land Cover Change ... - UCSB Geography

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Jul 17, 2010 - [email protected] b. The University of California, Santa Barbara, 4638 Ellison Hall, Santa Barbara, CA 93106. Email: [email protected].
Tropentag 2010 ETH Zurich, September 14 - 16, 2010 Conference on International Research on Food Security, Natural Resource Management and Rural Development

The effects of population and land cover change on food security in Latin America from 1961 2001 Ervina, Daniel, David López-Carrb and Anna López-Carrc a

The University of California, Santa Barbara, 4640 Ellison Hall, Santa Barbara, CA 93106. Email: [email protected] b

The University of California, Santa Barbara, 4638 Ellison Hall, Santa Barbara, CA 93106. Email: [email protected] c

Department of Geography, San Diego State University. Email: [email protected]

Introduction Unprecedented population growth accompanied equally unprecedented land use and land cover changes in Latin America during the second half of the twentieth century, affecting the food security of thousands of agriculturally based communities. The more than doubling of the population of Latin America was accompanied by rural migration to urban areas and extensification, or expansion, of agricultural land at the expense of forest and natural environments (Carr, Lopez, and Bilsborrow 2009). We have previously found that when these processes were examined at a country scale, both Malthusian and Boserupian demographic factors were important in explaining rural out-migration and forest cover decreases (Carr, Lopez, and Bilsborrow 2009). Our results supported Bilsborrow’s application of the theory of multiphasic response: that these two different types of drivers can be simultaneously present, acting influentially at different spatial and demographic levels (Carr, Lopez, and Bilsborrow 2009). The process of agricultural extensification has obvious natural limits, as the remaining high-quality arable land is increasingly exploited in response to growing populations or market demands. In addition, much of the world’s undeveloped arable land is either protected by laws or is of poor soil or topographic quality (World Bank 1995). As extensification becomes more difficult the only viable option for continued increases in food production is agricultural intensification. Of course, the process is not linear and both extensification and intensification occur in areas simultaneously. In addition, a causal relationship between these processes is far from certain, with some

researchers positing that, for example, percentage of forest versus agricultural land is a result of economic development levels (Mather et al., 1999), rather than agricultural necessities. Regardless, for the purpose of this work it will be assumed that agricultural intensification is seen as the answer to increasing agricultural production as viable agricultural land becomes scarcer, or more expensive. Land intensification takes numerous forms, be it existing developed land changing from pasture to cropland, an increase in irrigation, increased use of fertilizers or pesticides, or an increase in active production time by growing multiple crops during one year or not allowing fields to lie fallow. The use of these methods causes environmental problems, including aquifer depletion, the flooding of soil tables, chemical contamination associated with the use of fertilizers and pesticides, and bacterial imbalances in natural water sources from excess nutrients (Carr et al 2006). This final problem is most commonly associated with the ocean dead zones surrounding many developed countries (NASA 2010). The net environmental effects by using less land more intensely is open to debate, but the increase in the byproducts of intensive agricultural practices seems inevitable. The purpose of this paper is to contrast the intensification of agricultural practices and food production in eight countries in Central America and thirteen in South America. This paper is not meant to test this complex and often site-specific relationship but merely to examine the statistics on a broad level to determine any general trends. Methods We use data gathered from the Food and Agriculture Organization of the United Nations’ (FAO) Agricultural Yearbooks, as well as FAO online statistical resources (www.fao.org). The results contain indices measuring kilogram (Kg) of fertilizer use per hectare (Ha), and total number of tractors, which includes all engine-driven agricultural machines like harvesters, threshers, or milkers. These capital-intensive inputs will be contrasted with production yield measures. Yield is expressed as hectogram of crops produced over hectare of cultivated land for two groups of crops: cereals, which include maize and rice, and oil cakes, which includes soybeans and oil palms. We chose these groups because we felt that they contain products that were likely to be cultivated in some significant level throughout the diverse nations of Latin America. Results and Discussion Table 1 contains statistics concerning the use of fertilizer and irrigation in Latin America. It indicates that for all of the nations in Central America fertilizer per hectare of cropland has steadily and dramatically increased since 1961. The least dramatic increase is in Belize where they use a mere 142% more fertilizer per hectare than in 1971, while Honduras uses 2701% more than they did 40 years prior. In most nations this has also been accompanied by an expansion of cropland, leading to a large increase into total fertilizer used (not shown). The results for the South American nations are much the same, with large increases in per hectare use of fertilizer more or less across the board. Table 1 also contains the number of ‘tractors’. The results are similar, if less dramatic, with steady increases in almost all countries.

Table 1 - Agricultural Intensification Measures Fertilizer Use (Kg/Ha. of Cropland) % Change 1961 1971 1981 1991 2001 1961-2001 27.3

64.2

47.5

Tractors (4umber) 1961

1971

1981

1991

2001

% Change 1961-2001 445%

Belize

8.6

22.9

454%

211

596

825

1100

1150

Costa Rica

38.9

115.2 142.2 226.0 239.1

514%

3800

5200

6000

6500

7000

84%

El Salvador

31.8

121.0 116.3 93.6

142%

1600

2642

3320

3420

3430

114%

77.0

Guatemala

9.8

15.9

50.8

80.2

102.7

946%

1950

3250

4020

4220

4300

121%

Honduras

3.8

17.8

16.1

19.3

106.1

2701%

304

1950

3440

4650

5200

1611%

Mexico

8.0

26.4

63.1

61.1

67.8

743%

Nicaragua

A

A

A

A

A

A

Panama

7.2

56000

92800

143078 317313

324890

480%

130

550

2250

2650

2900

2131%

5420

5047

48.0

107.3 52.6

27.8

286%

347

2693

8066

2224%

Central Americaa 8.8 Central Americab 15.5

29.2

61.3

61.0

69.8

696%

64342

109681 168353 344900

356936

455%

52.5

74.7

85.3

95.4

518%

Argentina

0.8

2.9

3.6

6.1

29.7

3464%

120000 171000 213000 274034

299608

Bolivia

0.6

2.4

3.3

3.4

3.6

555%

1300

2300

6000

362%

Brazil

9.5

25.9

51.8

57.4

102.9

982%

72000

183500 569000 730000

806000

1019%

Chile

12.1

30.9

29.0

104.1 223.7

1756%

33550

34050

34370

37570

54000

61%

Colombia

14.3

36.5

53.8

125.2 149.9

949%

18241

23469

29500

31000

21000

15%

Ecuador

4.4

7.2

27.7

27.6

2750%

1558

3400

6844

10919

14680

842% 1995%

124.9

901% 4200

5300

150%

French Guiana

A

A

150.5 108.3 75.0

A

20

39

106

303

419

Guyana

24.0

32.6

28.7

31.0

27.2

13%

3240

3340

3480

3620

3630

12%

Paraguay

6.2

25.6

16.3

11.5

9.1

48%

3900

4900

8035

15878

16500

323%

Peru

0.3

1.6

2.6

5.2

15.7

5024%

6950

11100

11900

12750

13191

90%

Suriname

31.7

63.4

75.0

33.8

60.0

89%

580

940

1120

1300

1330

129%

Uruguay

16.4

61.8

44.6

60.4

82.3

401%

24695

29910

33160

32800

33000

34%

Venezuela

5.5

19.1

41.1

109.8 88.3

1518%

11400

20700

39000

48500

49000

330%

South Americaa South Americab

8.1

19.3

35.2

46.3

82.8

918%

297484 488748 953832 1204101 1318475

10.5

25.8

40.6

52.6

76.3

629%

343% 412%

a Indicates that the bolded region has been treated as a whole. b The mean of the country rows for calculated measures, to avoid unduly large influence by Mexico and Brazil’s on their regions.

Although this country-level data is both broad in area and in to varying degrees estimated or inaccurate, its usage here is meant to outline the general trend of increasing intensification of agricultural land. This intensification should have a relationship with per-area agricultural production, which is displayed in Table 2. The results of these tables show that yield per acre is increasing along with intensification throughout Latin America but at a much lower rate.

Table 2 - Agricultural Production Measures Cereals Yield (Hg/Ha) Year

Oilcakes yield HG/HA

% Change 1961-2001

1961

1971

1981

1991

2001

15290 20714 22761 31012

420%

NA

NA

NA

3612

8354

NA

11535 18378 22763 32989 35496

208%

4546

4305

4685

3591

3490

-23%

16771 16913 16335 19096

104%

6837

7808

6014

4393

6397

-6%

11422 15240 18100 18254

122%

4074

6519

8328

8506

6957

71%

10511 12095 13769 13170 14469

38%

4335

4209

3038

2581

4018

-7%

11049 15299 22925 24269 28556

158%

5206

7207

7836

9077

6761

30%

4172

1961

1971

Belize

5963

Costa Rica El Salvador

9378

Guatemala

8221

Honduras Mexico

1981

1991

2001

% Change 1961-2001

Nicaragua

9397

10826 14712 14171 16928

80%

5121

6430

5623

12728

149%

Panama

9515

11988 16255 18829 18315

92%

99377

103254

85117 3732

2083

-98%

Central Americaa 10702 14850 21704 22839 26795

150%

5249

7129

7526

8238

6624

26%

Central Americab 9446

14009 17911 20078 22766

119%

18499

19962

17234

4958

6349

18%

14106 17835 24249 26661 32068

127%

3624

4247

9408

13237

17694

388% 150%

Argentina Bolivia

9543

11031 13005 13580 17849

87%

4809

5364

9114

14038

12001

Brazil

13463 12908 16110 18506 31485

134%

3426

4029

10208

10693

20864

509%

Chile

14413 19944 21204 40508 49356

242%

5933

9010

6762

11355

16113

172%

Colombia

12752 19045 24797 24507 35483

178%

4850

5921

6195

6483

6778

40%

Ecuador

10106 9619

88%

2354

2457

6103

8096

5690

142%

17679 16739 18994

French Guiana

23877 37142 10784 42722 37870

59%

NA

NA

NA

NA

2920

NA

Guyana

20137 18210 31163 31422 39478

96%

NA

NA

NA

3457

3642

NA

Paraguay

12517 12574 15277 17684 21602

73%

3068

6177

10619

12705

16743

446%

Peru

14877 17501 21349 22926 32413

118%

4708

5385

6178

4803

5782

23%

Suriname

27633 33915 39581 38134 37673

36%

3119

3139

2419

1914

4232

36%

Uruguay

8597

288%

2705

3047

5677

6111

7848

190%

10349 18041 24188 33381

Venezuela

11155 12348 18853 26214 33033

196%

2416

3079

3883

3675

3087

28%

South Americaa South Americab

13466 14985 19404 21446 31450

134%

3572

4177

9824

11520

18749

425%

14860 17879 20930 26445 32360

133%

3728

4714

6961

8779

11218

193%

Conclusions and Outlook Simple arithmetic comparisons of intensification and production figures for each country indicate that there is no linear relationship between agricultural input and output. For example, from 1961 to 2001 Honduras increased its fertilizer use per hectare by 2701 percent and its number of tractors by 1611 percent, yet its gains in yield are low or nonexistent. While other countries have had increases in production along with increases in intensification, the results point to inputs increasing exponentially, while outputs at best increase arithmetically, a familiar and worrisome relationship to those who are familiar with Malthusian theories. This perhaps calls into question the wisdom of Latin America following the agricultural path that the developed nations have taken, and certainly calls for further research into the relationship between intensification and production in Latin America.

References Carr, D.L. A. Barbieri, W. Pan, and H. Iravani, (2006). Agricultural land use and limits to deforestation in Central America. Chapter 6 in Agriculture and Climate Beyond 2015: A new perspective on future land use patterns. Eds. Floor Brouwer and Bruce McCarl. Dordrecht, The Netherlands: Springer. p. 98-107. Carr, D.L., A.C. Lopez, and R.E. Bilsborrow (2009). The population, agriculture, and environment nexus in Latin America: Country-level evidence from the latter half of the 20th century. Population and Environment. 30:222–246. Mather, A.S., C.L. Needle, J. Fairbairn (1999) Environmental Kuznets curves and forest trends. Geography, Vol. 84 (1), pp. 55-65. National Aeronautics and Space Administration (NASA). “Aquatic Dead Zones”. Last modified July 17, 2010. http://earthobservatory.nasa.gov/IOTD/view.php?id=44677.