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Logging, tropical forests and biodiversity — what we don’t know

Holly Doremus, professor of law | March 11, 2013

A new paper in Conservation Biology (subscription required) from researchers at UC Berkeley and elsewhere provides an important reminder that we often don’t know as much as we think we do about ecological systems and the effects of human actions on those systems. Lead author Benjamin Ramage and colleagues evaluated all the studies they could find in the peer-reviewed literature for a ten-year period that made claims about the effects of logging in tropical forests on biodiversity.

The conventional story, of course, is that logging in these forests drastically reduces biodiversity. But Ramage et al. show that conclusion doesn’t necessarily follow from the available data. It turns out that there is substantial spatial variation in species composition in tropical forests, even over fairly small distances. Unless that variation is accounted for, either by baseline studies or by designing treatments so that logged areas are geographically interspersed with unlogged ones, it is impossible to know what to make of data finding differences in species diversity or composition between logged and unlogged sites. Those differences might have been there before logging, rather than being produced by logging. Ramage et al. find that “the probability of falsely inferring a treatment effect was as high as 0.45,” in other words that nearly half of the observed effects reported in the literature might be false positives.

They conclude that the possibility of false positives makes it especially difficult to interpret the inconsistent results in the literature from studies of selective logging, and that the resulting confusion and misinterpretation has inhibited useful learning and may have diverted policy efforts from the most effective paths:

Although the effects of intensive logging are relatively clear, the purported effects of selective logging (and other forms of minor to moderate habitat disturbance) are inconsistent in tropical forests. . . . [C]ollectively [the existing data] are exactly what should be expected given preexisting spatial variation, routine simple pseudoreplication, and no effects of selective logging. This argument in no way proves the absence of real logging effects; however, it does suggest that the compositional effects of logging have been exaggerated and demonstrates that the current body of literature provides little indication of the true nature of these effects. . . .

[Confusion in the literature] has likely inhibited widespread recognition of the conservation potential of tropical production forests. If more accurate knowledge had been available, efforts to stop all logging in tropical forests may have been reduced, allowing for a greater proportion of tropical conservation funds to focus on other objectives (e.g., preventing deforestation and developing strategies that optimally balance ecological concerns and economic pressures). Furthermore, by failing to isolate treatment effects, results of pseudoreplicated studies provide little guidance on the specific logging practices that best maintain communities characteristic of primary forests.

I take two key lessons from this study. First, the science community needs to better practice its institutional norm of skepticism in order to take advantage of its claimed ability to self-correct and learn over time. As the authors of this study acknowledge, it can be exceedingly difficult to do ideal studies of the effects of human interventions, like logging, on ecosystems. Baseline data are often not available, and the costs in time and money of performing carefully replicated experiments may make them infeasible. Necessarily, researchers are often following in the wake of logging and other impacts. But they need to be much more aware of possible confounding effects, and much more on the lookout for ways to deal with those effects or at least ways that those effects might undermine conclusions. Unless the scientific community notices the shortcomings of such studies, it can’t correct them.

Second, both the scientific and the policy community can be misled by the implicit assumption that all human intervention in nature is highly problematic. That assumption may lead us to see the available choices in too stark a light — in the tropical forest context, either we leave primary forest or we log intensively. It may be that there are other choices, that selective logging or carefully managed production forestry may be compatible with maintenance of relatively high levels of biodiversity. That’s not to say that we should always choose working landscapes, just that we should better understand both the costs and the benefits of a full range of landscape management choices.

Cross-posted from the environmental law and policy blog Legal Planet.

Comment to “Logging, tropical forests and biodiversity — what we don’t know

  1. The last paragraph is poignant. Where empirical evidence is clear enough in cases of blatant forest and habitat degradation no further studies should be needed. The plight of the Orang Utan on the island of Borneo does not need scrupulous scientific examination of the effect of human intervention.

    However, we face the conundrum of protecting the remaining forests and arguing for the reforestation of degraded forest land at a time when the pressure for land for food is great and will become greater. Our greatest chance of success under such pressure is to give these forests and forest lands real, non-stranded asset values and to do this we must consider their timber value together with other income potentials they can generate. It is here that we need good science to inform and advise on likelihood of minimum or zero negative effect on biodiversity in production areas and a good example is the work we at Retree Ltd are doing in Myanmar.

    The Myanmar selection system, designed in the 1850’s, still provides a sound method for sustainable Teak (and other) forests. Historically there is little evidence of this system of logging having a measurable detrimental effect on biodiversity unless and until the measures the system provides are exceeded (which has happened these past 20 years).

    Assumptions that human intervention equals negative effects will only ensure the forests are threatened more, not less, because their ability to pay for themselves will be severely restricted. Your final sentence sums this up perfectly.

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