ROADS TO RUIN: EXPANDING TRANSPORTATION NETWORKS IMPERIL GLOBAL BIODIVERSITY

WILLIAM F. LAURANCE

Is James Cook Distinguished Research Professor at James Cook University in Cairns, northern Queensland, Australia. His research focuses on the impact of intensive land-uses, such as habitat fragmentation, logging, and wildfires, on tropical ecosystems, and on global-change phenomena and conservation policy. He works extensively in Amazonia, Australasia, and Central Africa. Dr. Laurance received his PhD from the University of California, Berkeley, in 1989 and subsequently held research and science-leadership positions in tropical Australia. From 1996–2009 he spent 14 years as a Senior Scientist with the Smithsonian Institution, where he was based in Brazil and Panama. Dr. Laurance has published five books and over 300 scientific and popular articles. A leading voice for conservation, he firmly believes that scientists must engage policy makers and the general public, as well as other scientists. He has received numerous professional awards and is a fellow of the American Association of the Advancement of Science and former president of the Association for Tropical Biology and Conservation, the world’s largest scientific organization devoted to the study and preservation of tropical ecosystems.

“The best thing you could do for the Amazon

is to bomb all the roads.”

Dr. ENEAS SALATI,

Technical Director, Brazilian Institute for Sustainable Development, Rio de Janeiro, Brazil

“Highways are the seeds of tropical forest destruction.”

Dr. THOMAS E. LOVEJOY,

Biodiversity Chair, Thomas H. Heinz Center Washington, D.C., USA

“In the Congo, rapidly proliferating roads—and the ivory hunters they bring—are decimating the African forest elephant.”

Dr. STEPHEN BLAKE,

Former Inventory Coordinator of the MIKE

(Monitoring of Illegal Killing of Elephants)

Program in central Africa

VILIFYING ROADS

As the quotes above illustrate, environmental scientists often take a very dim view of roads and highways in the vicinity of natural ecosystems. This perspective is strikingly different from that of many economists and regional planners, who typically extol the “opening up” of frontier regions by new roads as a good thing (e.g., Simuyemba 2001; Duval 2008). Why such a dramatic difference in perception?

Here I evaluate the impacts of roads from a broad environmental standpoint. At the outset, I describe how and why economic globalization is promoting rapid road expansion in many previously road-free areas. I then highlight the manifold environmental impacts of roads on native ecosystems and wildlife. Finally, I consider some strategies to reduce the impacts and extent of roads. As will quickly become apparent, I hold a deeply ambivalent view of roads: they are a necessary part of contemporary life, but they are sometimes environmentally devastating.

Two caveats are needed before I proceed further. First, in a functional sense there can be a strong distinction between a “highway,” which is a major paved thoroughfare that provides year-round access to a region, and a “road,” which is generally smaller and may or may not be paved. For simplicity, however, I will use the term “road” for either. Both are examples of linear infrastructure, which also includes power lines, gas lines, railroads, and canals. Linear infrastructures are among the most ubiquitous features of human activity in the world today.

Secondly, I will focus here exclusively on tropical nations. These are the areas I know best, having spent the better part of three decades living and working in them. More importantly, tropical nations harbor much of the world’s biodiversity—

sustaining at least half of the planet’s species in just 7% of its land area (Primack 2006)—and are where roads are expanding most swiftly.

ROADS AND RAINFOREST BIODIVERSITY

Roads and other linear infrastructure have serious environmental impacts on natural habitats worldwide (Forman and Alexander 1998; Trombulak and Frissel 2000), but tropical rainforests seem specially vulnerable (Laurance et al., in press).

Firstly, from a biological perspective, rainforests have a complex architecture and uniquely humid, dark, stable microclimate. They sustain many animal species specialized for living in forest-interior and understory conditions [Figure 1], some of which strongly avoid abrupt forest edges along clearings and rarely cross even narrow forest openings. Other tropical species are vulnerable to hunting, road-kill from vehicles, elevated predation, and species invasions near roads. The net effect is that, by virtue of their unique characteristics and abundance of ecologically specialized species, rainforests and their wildlife are exceptionally vulnerable to roads and other linear clearings.

Secondly, from a socioeconomic perspective, tropical rainforests are strongly concentrated in developing nations, many of which are experiencing further population growth, rapid economic development, and intense natural-resource exploitation. As a result, roads are running riot. For example, Brazil has just punched a 1200-kilometer-long highway into the heart of the Amazon (the BR-163) and is in the process of constructing another, 900-kilometer-long highway (the BR-319) that will cut into nearly pristine forest. A triad of new highways is slicing across the Andes Mountains, from the Amazon to the Pacific. New road networks in Sumatra are opening up some of the island’s last remaining forests to predatory loggers and hunters. A recent study found 52,000 kilometers of new logging roads in the Congo Basin (LaPorte et al. 2007). These are but a small sampling of the new roads and highways penetrating into the world’s last tropical frontiers.

GLOBALIZATION AND ROADS

Economic globalization is playing an ever-bigger role in road expansion and tropical deforestation. Tropical forests are disappearing at an average rate of 10–13 million hectares a year (FAO 2005)—the equivalent of roughly 50 football fields per minute. While this rate has remained relatively constant over the past few decades, the underlying causes of deforestation have shifted dramatically—from mostly small-scale, subsistence-driven deforestation through the 1980s, to far more industrial-driven deforestation more recently (Geist and Lambin 2002; Rudel 2005).

Beginning around the end of the Second World War and continuing through the late 1980s, tropical deforestation was mostly a consequence of two factors. The first was explosive growth of the human population in developing nations (Myers 1993). From 1950 to 1990, for example, the populations of the three biggest tropical nations, Brazil, Indonesia, and the Democratic Republic of Congo, collectively rose by more than 250%, from 146 million to 368 million people (UN 2004). The second factor promoting deforestation was government policies for rural development, such as agricultural loans, tax incentives, forest-colonization programs, and rural-road construction (Rudel 2005). Such initiatives, especially evident in countries like Brazil and Indonesia (Fearnside 1997), promoted large influxes of colonists and shifting cultivators into frontier areas and caused alarming forest loss.

More recently, however, the impacts of rural peoples on tropical forests seem to be stabilizing. Although many tropical nations still have considerable population growth, strong urbanization trends (except in Sub-Saharan Africa) mean that rural populations are growing more slowly, and are even declining in some areas (UN 2004). The popularity of large-scale frontier-colonization programs has also waned (Fearnside 1997; Rudel 2005). If such trends continue, they could begin to alleviate some pressures on forests from small-scale farming, hunting, and fuel-wood gathering (Wright and Muller-Landau 2006).

At the same time, globalized financial markets and a worldwide commodity boom are creating a highly attractive environment for the private sector. Under these conditions, large-scale agriculture—crops, livestock, and tree plantations—by corporations and wealthy landowners is increasingly emerging as the biggest direct cause of tropical deforestation (Rudel 2005; Nepstad et al. 2006a). In Brazilian Amazonia, for instance, large-scale ranching has exploded, with the number of cattle quadrupling, from about 20 to 80 million head, since 1990 (Smeraldi and May 2008). Industrial soy farming has also grown dramatically in Amazonia (Fearnside 2001). In Southeast Asia, expansion of industrial oil palm and rubber plantations has become a major driver of deforestation (Koh and Wilcove 2008). Surging demands for grains and edible oils, driven by rising standards of living in developing countries and the global thirst for biofuels, are also spurring these trends (Von Braun 2007; Scharlemann and Laurance 2008).

Road expansion and demand for new agricultural land often go hand in hand. In Brazil, for example, the powerful soy lobby has been a major proponent for the construction of new paved highways into the unexploited heart the Amazon. The lobby wants these highways so they can easily transport millions of tons of soy to the Amazon River, where it can then be exported internationally (Fearnside 2001). Other industrial activities, especially logging, mining, and oil or gas development, are also providing a key economic impetus for road building in tropical frontiers (Laurance 2001; Laurance et al. 2001; Asner et al. 2005; Finer et al. 2008).

Globalization is having another important impact on tropical deforestation. Historically, it is the nations with the highest population densities that have tended to lose the most forest (Wright and Muller-Landau 2006) and have the most threatened species (Sodhi et al. 2009). However, this relationship may be weakening because of international trade (Laurance 2007a; Butler and Laurance 2008). For instance, even a nation like Gabon, with a population density of fewer than five people per square kilometer on average, could lose much of its forest as China aggressively buys up huge stocks of the country’s raw timber, mineral, and oil resources (Laurance et al. 2006a). Thus, globalization may increasingly de-link the relationship between local population density and environmental degradation, so that even sparsely populated nations can be rapidly exploited and deforested.

ROADS AND RAINFORESTS

Roads can have wide-ranging impacts on natural ecosystems. Some are a direct consequence of road building, maintenance, and vehicle traffic, whereas others—often the most devastating—are a result of greatly increased physical accessibility to the forest (see Laurance et al., in press). Here I briefly summarize some the main effect of roads on rainforests.

PHYSICAL DISTURBANCES AND POLLUTION

In the tropics, as elsewhere, roads can seriously affect local soils, streams, and water quality (Trombulak and Frissel 2000). Roads are typically constructed using a cut-and-fill approach to help level local topography. Unless culverts are installed at frequent intervals, the filled areas impede drainage, especially in regions that receive heavy wet-season rains. This can cause flooding on the upstream side of the road that kills rainforest vegetation [Figure 4a]. On the downstream side of roads, water flow is often greatly impeded, causing streams to fail.

Road-cuts and local sand- and gravel-quarrying operations are major sources of erosion, with each hectare bleeding from 35–500 metric tons of sediments into nearby streams each year (Bruijnzeel 2004). These sediments degrade water quality and clog up streambeds, killing many fish, aquatic insects, and other stream-dwelling wildlife.

Finally, roads and vehicles can be a chronic source of pollutants. Dust, heavy metals, nutrients, ozone, and organic molecules are elevated within 10–200 meters of roads (Trombulak and Frissel 2000; Pratt and Lottermoser 2007a). Chemical pollutants and nutrient runoff from roads are especially harmful to nearby streams and wetlands, with pulses of waterborne pollutants entering aquatic ecosystems when rainfall is heavy (Pratt and Lottermoser 2007b). Such contaminants can have wide-ranging effects; for example, many aquatic insects are acutely sensitive to water pollution, waterborne nutrients can promote blooms of algae that deplete the water of life-giving oxygen, and heavy metals are toxic to many animal species.

EDGE AND BARRIER EFFECTS

A road slicing through a rainforest is a highly artificial environment. Forests along road clearings are typically drier, hotter, and windier than are forest interiors. These changes can kill some trees near the clearing from heat stress or windthrow, and the higher light levels along roads promote a proliferation of disturbance-loving vines and weeds (Murcia 1995; Laurance et al. 2002b; S. G. Laurance 2004).

Being ecologically specialized for dark, humid conditions, many rainforest animals tend to avoid the foreign disturbance created by roads and their abrupt forest edges. Examples include strictly arboreal species, such as certain monkeys, sloths, and possums; understory bats specialized for flying in dense, cluttered environments; understory birds with a strong psychological avoidance of clearings; and larger mammals that shun humans or traffic noise near roads (Goosem 2001, 2007; Develey and Stouffer 2001; S. G. Laurance et al. 2004).

For rainforest specialists, roads can seriously impede their natural movements, dispersal, and gene flow, leading to population isolation and fragmentation (Laurance et al., in press). Such deleterious effects are likely to be compounded as road density increases, with road-dominated landscapes becoming increasingly hostile terrain for rainforest specialists. In concert with other impacts, such as hunting or road-kill, roads can have a serious impact on population survival.

ROAD-KILL AND HUNTING

Many animals are killed along roads from collisions with vehicles (Goosem 1997, 2007) or from human hunting or trapping near roads. In terms of population survival, chronically elevated mortality is most serious for species that are rare, range over large areas, or have low reproductive rates, such as predators and larger-bodied mammals and birds (Bennett and Robinson 2000).

Road-kill from vehicles is limited to the road surface itself. Hunting by humans, however, can create zones of elevated mortality and animal avoidance within at least 5–10 kilometers of roads, and possibly much further for wide-ranging species (Lahm et al. 1998; Laurance et al. 2006b, in press; Blake et al. 2007). Populations of the African forest elephant, for example, appear to be depressed up to 50 kilometers from roads (Blake et al. 2008). Notably, the traits that predispose a species to road-kill, such as slow movement, poor eyesight, and forest edge-favoring behavior, are very different from those, such as large body size, gregarious social systems, conspicuous calls or displays, and the use of regular pathways, that predispose them to hunting or trapping by humans (Laurance et al., in press). Thus, roads affect a broad spectrum of species with widely varying characteristics.

INVASIONS OF EXOTIC SPECIES

Many exotic species love roads, which provide avenues for invading forests. Among others, such invaders include little fire ants (Wasmannia auropunctuta), exotic earthworms, non-rainforest vertebrates, fungal die-back (Phytophthora species), and myriad weed species (Dawson and Weste 1985; Walsh et al. 2004; Brown et al. 2007). Some of these invaders are having major impacts on tropical ecosystems. Little fire ants, for instance, are proliferating throughout African rainforests around 60 times faster along logging roads than through undisturbed forest, and kill or blind native species such as monkeys, apes, leopards, and insects (Walsh et al. 2004). Invasions can occur with surprising rapidity; for example, non-rainforest frogs, leafcutter ants, lianas, and exotic weeds are already penetrating into remote areas of the Amazon, using the verges of recently constructed roads as invasion corridors (Gascon et al. 1999).

Road-borne invaders affect people too. In Ecuador, for example, human enteric pathogens are 2–8 times higher in villages near roads than in more remote areas (Eisenberg et al. 2006). Increased incidences of dengue fever (Dutta et al. 1998), malaria (Hayes and Ferraroni 1981), and HIV (Carswell 1987) have been reported in people living near roads in India, Brazil, and Uganda, respectively. By accelerating invasions of novel and potentially lethal pathogens, roads penetrating into remote frontiers also threaten indigenous groups attempting to live with limited or no contact with outsiders. The Surui Amerindians of Brazilian Amazonia, for instance, have been driven to the edge of extinction by roads and the new infectious diseases they bring (Butler 2009).

HUMAN INVASIONS

In the tropics, roads greatly facilitate invasions of hunters, miners, colonists, and land speculators—a phenomenon dubbed the “Pandora’s Box Effect” (Laurance 1998). In Brazilian Amazonia, for example, ~95% of all deforestation and fires occur within 50 kilometers of highways or roads (Laurance et al. 2001). In Suriname, most illegal gold-mining operations are located near roads (Laurance 2008), whereas in tropical Africa, hunting intensity increases so sharply near roads that it strongly affects the large-scale distribution of forest elephants, buffalo, duikers, primates, and other exploited species (Lahm et al. 1998; Laurance et al. 2006b; Blake et al. 2007, 2008). Roads can greatly increase trade in bushmeat and wildlife products; for example, eight killed mammals were transported per hour on average along a single highway in Sulawesi, Indonesia (Lee et al. 2005).

Many formerly remote tropical regions, such as the Amazon (Laurance et al. 2001), Congo Basin (LaPorte et al. 2007), New Guinea (Shearman et al. 2009), and Borneo (Curran et al. 2004), are now being assailed by expanding road networks, particularly from industrial timber operations and oil, gas, and mineral projects. Paved highways, which provide year-round access to forests, typically have much greater impacts on forests and wildlife than do unpaved roads (Laurance et al. 2002a; Fearnside 2007; Soares-Filho et al. 2006), which tend to become inaccessible in the wet season.

By opening up new lands for colonization, proliferating frontier roads can also depress land prices across a region (although land prices near the road itself will typically rise because of greater access to markets). Lower land prices create a disincentive for landowners to invest in more-sustainable land uses (Laurance et al. 2001). Agriculture in the Amazon, for instance, is overwhelmingly dominated by fire-based methods, such as slash-and-burn farming and forest burning for low-density cattle ranching and charcoal production. These fire-based methods deplete soil nutrients so badly that farmlands are often abandoned after a few years, and also promote wildfires during periodic El Niño droughts (Cochrane 2003). Were land not so cheap and readily available, landowners would have a greater incentive to invest in more sustainable and profitable farming methods, such as agroforestry, tree plantations, and fruit crops, which are not fire-based (Laurance et al. 2001).

REDUCING THE IMPACTS OF ROADS

Measures to diminish the environmental impacts of roads fall into two categories: local strategies to reduce road impacts, and regional efforts to limit the expansion of roads into ecologically sensitive areas.

LIMITING ROAD EXPANSION

In simplest terms, roads can be thought of as the enemies of rainforests. Although roads are often an integral part of economic development, poorly planned roads can lead to massive forest disruption. In particular, roads that penetrate into remote frontier regions shouldbe avoided wherever and whenever possible. Paved highways are particularly damaging as they tend to spawn networks of secondary roads that dramatically increase the spatial scale of their impact (Perz et al. 2008); for example, the Belem-Brasília Highway, completed duringthe early 1970s, has now evolved into a 400 kilometer-wide swath of forest destruction and secondary roads across the eastern Brazilian Amazon (Laurance 1998). In efforts to project the future of the Amazon ecosystem [Figure 8], the locations of roads are the greatest single factor influencing expected spatial patterns of forest loss, fragmentation, and degradation (Laurance et al. 2001; Soares-Filho et al. 2006).

Large-scale efforts to expand regional highway networks in South America, South and Southeast Asia, and Sub-Saharan Africa are cause for great concern. Across all of these regions, perhaps the most notable trend in recent years is growing investment by China in frontier roads that will sharply increase access to mineral, oil, and timber resources. Maintaining large, roadless areas of intact forest should be among the highest priorities for regional conservation managers.

MANAGING TIMBER OPERATIONS

Industrial logging is currently occurring in about 28% of the world’s tropical forests (Asner et al., in press), and is probably the greatest single driver of road expansion in forest frontiers. In the tropics, nearly all logging is selective, with loggers using bulldozers and other heavy equipment to extract a limited number of trees from the forest (typically 1–10 trees per hectare). However, depending on harvest intensity, anywhere from 20–80% of the overhead forest-canopy cover can be destroyed, with logging tracks and roads proliferating throughout the forest and causing substantial soil damage, erosion, and fragmentation of the understory vegetation (Fimbel et al. 2001).

Many forests in the Asia-Pacific region have already been severely depleted by loggers. Surviving forests in the Amazon, New Guinea, and Congo Basin are now experiencing explosive timber expansion, with the Congo alone having at least 52,000 kilometers of recently created logging roads (LaPorte et al. 2007). In the Amazon, forests penetrated by roads from logging operations are about 400% more likely to be deforested than are unlogged forests (Asner et al. 2006).

Most logging in the tropics suffers from poorly planned and excessive road building (Putz et al. 2000). Efforts to reduce logging damage focus strongly on roads, with measures such as minimizing road works via careful pre-harvest planning, restricting roads wherever possible to flatter slopes and ridgelines, limiting widths of logging roads, minimizing stream crossings to reduce damage to streamside vegetation, and prohibiting logging during wet periods to reduce soil erosion and stream sedimentation (Fimbel et al. 2001). In addition, greater attention should focus on closing logging roads after harvest operations (such as by destroying key bridges or otherwise rendering the road impassable) to reduce post-logging invasions of forests by illegal colonists, hunters, and miners.

From an environmental perspective, some schemes for logging expansion appear especially alarming. In Brazilian Amazonia, for example, plans are afoot to log dozens of widely scattered National Forests—many located in remote, largely pristine areas—that could ultimately span over 50 million hectares (Verissimo et al. 2002). The vast network of new roads required for such an enterprise dramatically increase forest invasions, hunting, and land speculation in frontier areas. Similarly, efforts are underway to open up some of the last surviving forests in northern Sumatra to industrial logging.

REDUCING HUMAN INVASIONS

When roads in frontier areas cannot be avoided, unplanned forest loss and invasions by illegal colonists can be reduced by creating protected areas along the road route in advance of road expansion (Fearnside 2006; Nepstad et al. 2006b). In the Brazilian Amazon, for example, forest destruction has been more severe along the Cuibá-Santarém Highway, which had few protected areas in place prior to road construction, than along the Porto Velho-Manaus Highway, where 13 protected areas were established before or during road construction (although the latter is still incompletely paved and could suffer further in the future; Butler 2008a). More generally, forest fires are far less frequent near roads in Amazonian protected areas and indigenous lands than near roads in unprotected forest (Adeney et al. 2009).

Another strategy to reduce human invasions is establishing railroads rather than roads in frontier areas. Incursions into forests can be partially controlled because trains stop only at designated locations, and these can be situated strategically to limit invasions of environmentally sensitive areas. In Brazil, for example, a railroad has been advocated instead of the Manaus-Porto Velho Highway, which could greatly increase forest colonization in central Amazonia (Butler 2008b).

PROPERLY ASSESSING ROAD IMPACTS

Among the most serious hindrances to effectively limiting and mitigating roads is that, in many developing nations, environmental-impact assessments (EIAs) of proposed roads focus solely on the road route itself, ignoring the impacts of roads on forest invasions, hunting, and secondary-road expansion (Laurance 2007b). In Brazil, for instance, EIAs of major new Amazonian highways were often confined to a narrow swath along the road route itself, sometimes recommending such paltry mitigation measures as “helping” animals to move from the planned route before road building (Fearnside 2006). In other cases, such as for certain mines, hydroelectric dams, and other large developments, the EIA focuses on the project itself but ignores the impact of the roads it will inevitably spawn (Reid and Souza 2005). New roads will continue to be major drivers of forest disruption so long as the EIA process is so fundamentally flawed.

ROAD-DESIGN STRATEGIES

In nature reserves and other areas of high conservation significance, various measures can be used to minimize road impacts. The most important principle is that road density should be minimized, and roadless core-areas maximized, to sustain disturbance- and hunting-sensitive wildlife and reduce exotic-species invasions (Peres and Lake 2003; Blake et al. 2008). Flooding from road works can be minimized by installing large culverts at regular intervals under roads. Edge and barrier effects can be limited by minimizing road widths so that some forest-canopy connectively is maintained and allowing secondary growth, which provides a partial buffer against harmful edge effects, to proliferate along forest margins (S. G. Laurance 2006). Bridges over watercourses that include both a corridor of unflooded vegetation and natural streambed are especially effective for allowing animal movements, but culverts can also provide avenues for movements of smaller animals (Goosem 2007).

CONCLUDING REMARKS

Efforts to promote road expansion in the tropics are perhaps the most striking example of how globalization and regional economic integration in developing nations can be directly at odds with nature conservation. Economists and infrastructure planners typically see frontier road expansion in a positive light, whereas those alarmed by rapid deforestation perceive it in opposite terms, given the logistical challenges, expense, and near-futility of frontier governance once the roads go in.

All is not hopeless, however. Because frontier roads play a key role in promoting tropical deforestation and global carbon emissions (see Lovejoy, this volume), forest carbon-trading initiatives could increasingly focus on limiting and mitigating such roads. For example, such funds could potentially be used to help plan and minimize regional road works, establish protected areas in advance of road establishment, regulate road access, promote railroads rather than roads where feasible, and close down the environmentally most destructive roads (Laurance et al., in press).

Globalization and rapid economic development are leading to a massive proliferation of destructive roads in the world’s last surviving tropical frontiers. Actively limiting these frontier roads, I assert, is by far the most realistic, cost-effective approach to promoting the conservation of tropical nature and its crucial ecosystem services. As Pandora quickly learned, it was far harder to thrust the evils of the world back into the box, than to simply not open it in the first place.

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