Sustainability of Sugar-Derived Ethanol in Brazil

The case of the mostly widely applauded biofuel scheme to date, that of sugar­cane ethanol in Brazil, also has major doubts from the environmental perspective, although the first decade (1976-1985) of the program probably achieved a reason­able soil balance by recycling fermentor stillage as fertilizer, a valuable source of minerals, particularly potassium.20 36 With the great expansion of the industry sub­sequently, however, significant pollution problems have emerged. The volume of stillage that can be applied varies from location to location, and in regions with near-surface groundwater, much less stillage can be applied without contaminat­ing the water supply.36 In the case of the Ipojuca river in northeast Brazil, sugar cultivation and adjacent ethanol production plants use stillage extensively for both fertilization and irrigation, and this has led to water heating, acidification, increased turbidity, O2 imbalance, and increased coliform bacteria levels.98 The authors of this joint German-Brazilian study urged that a critical evaluation be made of the pres­ent environmental status of the sugar alcohol industry, focusing on developing more environmentally friendly cultivation methods, waste-reducing technologies, and water recycling to protect the region’s water resources.

The preservation of surface and groundwater in Brazil in general as a con­sequence of the sugar alcohol industry’s activities and development was ranked “uncertain, but probably possible” (table 5.17).99 Sugarcane plantations have been found to rank well for soil erosion and runoff criteria in some locations in Sao Paolo state, although the experimental results date from the 1950s (table 5.18). A much more recent study included in the second, Dutch-Brazilian report showed much poorer results for sugarcane in comparison with other monoculture crops (fig­ure 5.9). Nevertheless, although Brazilian sugarcane alcohol (viewed as an indus­trial process) makes massive demands on the water supply (21 m3/tonne of cane input), much of this water can (in principle) be recycled; in addition, Brazil enjoys such a large natural supply of freshwater from its eight major water basins (covering an area of 8.5 million km2) that the ratio of water extracted to supply is, on a global basis, exceedingly small: approximately 1%/annum, equivalent to 30-fold less than comparable data for Europe. Local seasonal shortages may, however, occur, and two of the four main sugar production regions have relatively low rainfalls (figure 5.10). Although sugar cultivation has mainly been rain-fed, irrigation is becoming more common.

TABLE 5.17

Selected Sustainability Criteria for Sugar Ethanol Production in Brazil

Criterion

Measurable parameter

Expected compliance

Greenhouse gas emissions

Net reduction 30% by 2007

Probable

Greenhouse gas emissions

Net reduction 50% by 2011

Probable

Competition with food supply

?

Uncertain

Biodiversity

No decline of protected areas in 2007 Active protection of local ecosystems by 2011

Very uncertain Very uncertain

Welfare

Compliance with treaties, declarations, etc.

Environment

Partial or unknown

Waste management

Compliance with existing laws

Uncertain

Use of agrochemicals

Compliance with existing laws

Partial

Use of agrochemicals

Compliance with EU legislation by 2011

Uncertain

Prevention of soil erosion and

Management plans

Unclear

nutrient depletion

Preservation of surface and

Water use and treatment

Probably possible

groundwater

Airborne emissions

Compliance with EU laws by 2011

Uncertain

Use of GMOs

Compliance with EU laws by 2011

Possible

Source: Modified from Smeets, E. et al.99

Подпись: Ш Latossolo roxo soil П Pdzolico vermelho soil FIGURE 5.9 Soil erosion for two types of Brazilian soils in the 1990s. (Data from Smeets et al.99)

Annual Soil Losses by Erosion and Runoff in Experimental Stations in Brazil

TABLE 5.18

Fertile soil, 9.4% slopea Red soil, 8.5% slopeb

Soil loss (tonne/

Runoff

Soil loss (tonne/

Runoff

Crop

hectare)

(mm)

Crop

hectare)

(mm)

Cassava

53

254

Castor beans

56.1

199

Cotton (in rotation)

38

250

Common beans

54.3

180

Soybean (continuous)

35

208

Cotton

51.4

183

Cotton (continuous)

33

228

Cassava

42.6

170

Soybean (in rotation)

26

146

Upland rice

36.6

143

Sugarcane

23

108

Maize (residues incorporated)

30.9

144

Maize (in rotation)

19

151

Peanut

30.6

134

Maize + common beans

14

128

Maize (residues burned)

29.0

131

Maize (continuous)

12

67

Maize + macuna bean (incorporated)

28.2

133

Maize + macuna bean (incorporated)

10

100

Sugarcane

21.0

88

Maize + manure

6.6

97

Maize + lime

19.1

96

Maize + macuna bean (mulched)

3.0

42

Maize + manure

8.9

62

Gordura grass 2.6 Source: Data from Smeets et al.99 a Average rainfall = 1,347 mm per year b Average rainfall = 1,286 mm per year

46

Jaragua grass

5.5

45

image170
Подпись: Amazon
Подпись: c о
Подпись: East Atlantic (sugar)
Подпись: San Francisco (sugar)

image101North and
northeast (sugar)

1.0 1.5

Rainfall (mm/km2/year)

FIGURE 5.10 Annual rainfall in main sugar-producing and other regions of Brazil. (Data from Smeets et al.99)

the enormous consumption levels of the Global North will not lead the Brazilian countryside out of poverty or help attain food sovereignty for its citizens.”100 On the other hand, to achieve poverty alleviation and the eradication of social exclusion and with support from environmentalists, Brazil proposed the Brazilian Energy Initiative at the 2002 World Summit on Sustainable Development (Johannesburg, South Africa) aiming at the establishment of global targets and timeframes of min­imum shares of energy from renewable sources.101 Headline figures for the global numbers of malnourished people known to international agencies are another datum point with a large uncertainty: from below 1 billion to 3.7 billion.3895 As an economist from the Earth Policy Institute was quoted as saying: “The competition for grain between the world’s 800 million motorists to maintain their mobility and its two billion poorest people who are simply trying to stay alive is emerging as an epic issue.”102

Brazil became the global leader in ethanol exports in 2006, exporting 19% (3 bil­lion liters) of its production — 1.7 billion liters of which were imported by the United States — and plans to export 200 billion liters annually by 2025, increasing sugar­cane planting to cover 30 million hectares.100 Sugar for ethanol will increasingly be viewed by nations without a strong industrial base but with suitable climatic condi­tions for sugarcane growth as a cash crop, in exactly the manner that Brazil regards coffee or soybeans; the example provided by Brazil in creating rural employment at low cost, reducing the economic burden of oil imports, and developing national industrial infrastructure will be one difficult to resist, especially if major sugar pro­ducers, including Brazil, India, Cuba, Thailand, South Africa, and Australia, unite to create an expanding alternative fuel market with sugar-derived ethanol.36 South Africa, for example, has a great and acknowledged need to improve its sugarcane

image102

FIGURE 5.11 Agricultural land efficiency in bioethanol production. (Data from von Blottnitz and Curran.105)

economy, where 97% of its sugarcane growers are small scale, achieving only a quarter of the productivity realized by commercial operators; sugar is produced in a surplus, most of which is exported, but a national plan to encourage biofuels usage is in place, and a first ethanol plant is planned for construction by a South African sugar producer[54] in neighboring Mozambique.103

Academic economists and agronomists are calling (and will continue to call) for an informed debate about land use in the context of increasingly large areas of highly fertile or marginal land being reallocated for energy crops.104 Although there is good evidence that sugarcane-derived ethanol in Brazil shows the highest agri­cultural land efficiency in both replacing fossil energy for transportation and avoid­ing greenhouse gas emissions (figure 5.11), impacts on acidification and human and ecological toxicity and deleterious environmental effects occurring mostly during the growing and processing of biomass are more often ranked as unfavorable than favorable in surveys.105

The principal economic drivers toward greater biofuel production in develop­ing economies are, however (and paradoxically), those widely accepted programs to reduce greenhouse gas emissions, increase energy security, and move to a scientifi­cally biobased economy by promoting the use of biofuels (table 5.19). If a new orga­nization of ethanol exporting countries, mostly in the Southern Hemisphere, arises to make up any shortfall in the production of endogenous biofuels in major OECD economies, only a sustained effort to require and enforce agronomically sound and environmentally safe practices on the part of those net importers will provide

TABLE 5.19

Support Measures and Targets for Biofuels

Target (% of biofuels

Country

in total road fuel consumption)

Target

deadline

Production

incentives?

Consumption

incentives?

United States

2.78a

Ethanol

2006

У

У

Brazil

(40% rise in production)

2010

У

У

Japan

(500 million liters)

2010

X

X

Canada

3.5

2010

X

У

European Union

5.75

Biofuels

2010

У

У

Sweden

3

2005

У

У

France

10

2015

У

У

Germany

2

2005

У

У

UK

5

2020

У

У

India

5

(unspecified)

У

У

China

15 (total renewables)

2020

У

X

Thailand

2

2010

У

У

Source: Modified from World Energy Outlook.66 a 4 billion gallons (2006) rising to 7.5 billion gallons by 2012

-°-E10-[55]-E20-*«-E85 -»-E100

image103Подпись: 25 50 75 100 Incremental Improvement in Mileage (%) 200

5.12 The impact of fuel economy on projected demand for ethanol in various gasoline blends. (Data from Morrow et al.76)

Selected Policies on Light-Duty Vehicle Fuel Economy

TABLE 5.20

Country

Target

Target deadline

Policy basis

United States

20.7 mpg to 22.2 mpg

2007

Mandatory

24 mpg

2011

Mandatory

Japan

23% reduction in fuel consumption (cars)

Progressive

Mandatory

13% reduction in fuel consumption (light trucks)

Progressive

Mandatory

China

10% reduction in fuel consumption

2005

Mandatory

20% reduction in fuel consumption

2008

Mandatory

Australia

18% reduction in fuel consumption (cars)

2010

Voluntary

Canada

Increase in corporate average fuel economy in line with U. S. standards

2007-2011

Voluntary

Source: Modified from World Energy Outlook.66

• Shifting our reliance on petroleum products to biobased products that gen­erally have fewer harmful environmental effects

When another principle is added — strengthening rural economies and increasing demand for agricultural commodities — the main issues of the political agenda that has emerged post-2000 in both the United States and OECD economies in general are clear. There is one final argument, however, and one that commenced in the 1950s, that, instead of rendering the question of economic price of biofuels irrel­evant, reformulates the question to ask: how will biofuels affect the cost of living and personal disposable income in the twenty-first century?