Rewilding tropical forests: dung is the key

Rewilding means different things to different people. Basically, it involves restoring a species, or several species to an area from which they have been extirpated by humans. Conservation biologists might study the population size and distribution of the returned species, ecologists might focus on interactions between the returned species and other species, while anthropologists might investigate how humans in the area are adjusting to having a new species in their lives.  One of the most famous examples of rewilding is the return of gray wolves to the Greater Yellowstone Ecosystem in western U.S.A., which can be looked at from the perspective of how the wolf populations are doing numerically, how they affect their prey (elk) or their prey’s prey (willow and aspen in the case of elk), and how they affect ranchers in the surrounding areas.

Conservation ecologists have begun a major rewilding program in Tijuca National Park in Brazil, introducing agoutis in 2010 and brown howler monkeys (Alouatta guariba clamitans) in 2015. Howler monkeys were extirpated from this park over a century ago, so ecologists worried that the monkeys might interact with the remaining species in unexpected ways.  For example, this forest hosts several species of invasive fruit trees, such as the jackfruit (Artocarpus heterophyllus). Luisa Genes and her colleagues were concerned that howler monkeys might eat fruits from these trees, and poop out the seeds in new forest locations, causing the invasive species to spread more rapidly.

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Introduced howler monkey holding the second baby born to her in the forest. Credit: L. Genes.

Even a disturbed rainforest such as Tijuca National Park hosts a large number of plant species, so the interactions can be complex and difficult to study.  As is so often the case in ecology, one very important complex of interactions involves poop.  Specifically, howler monkeys eat fruit off of trees, and poop the seeds out, usually at a new location, effectively dispersing the seeds.  But there is a second link in this seed dispersal interaction.  Twenty-one species of dung beetles use howler monkey poop for food for themselves and their offspring, breaking off small sections into balls and rolling the balls to a new location.  This process of secondary dispersal is nice for the beetles, but also for the seeds within the balls, which can now germinate in a new location without competing with the large number of seeds in the original howler monkey pile.

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Two dung beetles battle over a dung ball. Credit: Rafael Brix.

Genes and her colleagues were interested in two basic questions.  First, were the howler monkeys eating fruit from a few select tree species, or were they eating from many different types of trees, thereby dispersing seeds from many species?  Before releasing the monkeys (two females and two males), they attached radio transmitters to the monkeys so they could easily track them, and note what they ate.  Based on 337 hours of observation, the howler monkeys ate fruit from 60 different tree species out of 330 possible species in the forest (18.2%).  This is an underestimation of actual howler monkey contribution to seed dispersal, because the researchers observed the monkeys for a relatively brief time, and fruit consumption by the monkeys should increase over time as the population of monkeys (and possibly tree diversity), continues to increase.

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Male howler monkey released in 2016.  Note the radio transmitter on its right rear leg. Credit: L. Genes.

The second question is whether secondary dispersal by dung beetles was reestablished following reintroduction of howler monkeys.  To answer this question quantitatively, Genes and her colleagues set up an experiment that used plastic beads of various sizes instead of seeds. The researchers set up circular plots of 1m diameter with 70 grams of howler monkey poop in the middle.  Each pile was mixed with seeds (actually beads) of four different sizes (3, 6, 10 and 14 mm diameters) to mimic the range of seed sizes. The researchers measured secondary seed dispersal by returning 24 hours later and counting the remaining beads, reasoning that the rest had been moved by dung beetles (along with the poop) to a new location.

Genes and her colleagues discovered that the median rate of seed dispersal (bead removal) was 69% with larger seeds being moved at a significantly lower rate than smaller seeds.  Thus secondary seed dispersal by dung beetles was still operating in this ecosystem even after howler monkeys had been absent for over 100 years.

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Removal rate of beads (seed mimics) from dung piles by dung beetles in relation to bead size.  Different letters above treatments indicate statistically significant differences between treatments. 

Overall, ecological interactions among howler monkeys, plants, and dung beetles were rapidly reestablished once howler monkeys were reintroduced to the community.  There are plans to introduce five more howler monkeys this year, which should further increase beneficial seed dispersal, and hopefully allow plant diversity to increase as well.  One problematic observation was that howler monkeys also ate invasive jackfruit, which could promote its dispersal within the community.

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Luisa Genes monitors howler monkeys in the forest. Despite its apparent lushness, the forest still lacks many species and interactions that you would expect to find in an intact forest. Credit: L. Candisani.

The researchers discovered only 21 species of dung beetles, which was somewhat lower than other studies have found.  It is probable that conversion of this land into farmland in the 19thcentury led to the decline and/or demise of some dung beetle species.  With reintroduction of howler monkeys, and the passage of time, Genes and her colleagues expect that this rewilding effort should lead to a more robust ecosystem, with increased howler monkey populations supporting high dung beetle abundance and diversity, and more effective dispersal of many plant species. To understand the overall impact on forests, the researchers recommend that future studies should compare seedling survival and forest regeneration in areas where howler monkeys were reintroduced to areas where howler monkeys are still missing.

note: the paper that describes this research is from the journal Conservation Biology. The reference is Genes, L. , Fernandez, F. A., Vaz‐de‐Mello, F. Z., da Rosa, P. , Fernandez, E. and Pires, A. S. (2019), Effects of howler monkey reintroduction on ecological interactions and processes. Conservation Biology, 33: 88-98. doi:10.1111/cobi.13188. Thanks to the Society for Conservation Biology for allowing me to use figures from the paper. Copyright © 2019 by the Society for Conservation Biology. All rights reserved.

Mustard musters its troops

North American forests are being invaded. The invading forces use chemical warfare to attack the native inhabitants and to repel counterattacks by hostile enemies. As it turns out, the invader is the humble garlic mustard, Alliaria petiolata, which releases toxic chemical compounds into the soil that reduce the growth rate of many native plant species, and has strong chemical defenses that makes it unpalatable to most herbivores.

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Garlic mustard invasion. Credit Pam Henderson

Lauren Smith-Ramesh wondered why garlic mustard was not even more successful as an invader. Its chemical arsenal should allow it to overrun an area, but she (and many other researchers before her) observed that garlic mustard invasions often decline after a while. As part of her investigations into garlic mustard’s use of chemicals to inhibit native plants, Smith-Ramesh collected seeds from plants from different populations. While shaking these seeds into bags, she noticed that web-building spiders often colonized the garlic mustard’s seed-bearing structure (silique). Were these spiders somehow behind the garlic mustard’s surprising lack-of-success?

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Garlic musard silique with web. Credit Lauren Smith-Ramesh

Spiders can benefit plants in several ways. As important predators in food webs, spiders can kill large numbers of herbivorous insects that might otherwise attack a plant. In addition the decaying corpses of their insect prey can add vital nutrients to soils. Garlic mustard does not enjoy these potential spider-associated benefits, because spiders colonize the garlic mustard after it has already gone into decline, and also because garlic mustard is already well-protected (chemically) against herbivorous insects.

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About 60% of the spiders were this species – Theriodiosoma gemmosum. Credit Tom Murray.

Smith-Ramesh first wanted to understand the relationship between seed structures (siliques) and spider abundance. She established three different types of plots that measured 2 X 2 meters: (1) S+, which had mustards with intact siliques, (2) S-, which had mustards with siliques removed, and (3) N, which had no garlic mustard plants at all in 2015. After several months, she collected all spiders from the middle square meter of each plot. Plots with garlic mustard with intact siliques (S+) had, by far, the highest spider density. S- plots had a somewhat higher spider density than N plots, which Smith-Ramesh attributes to spiders wandering in from just outside the S- plots (which tended to have more silique-bearing garlic mustard plants nearby than did the N plots). Based on this experiment Smith-Ramesh concluded that garlic mustard siliques were dramatically increasing spider density.

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But did increased spider density in S+ plots reduce the number of herbivorous insects, thereby benefiting nearby native plants? Smith-Ramesh set up insect traps that collected insects over two 48 hour time periods – once in August and again in September – in each of the S+, S- and N plots. Both surveys showed fewest herbivorous insects in the S+ plots. This supports Smith-Ramesh’s hypothesis that native plants are benefitting from higher spider density associated with garlic mustard siliques.

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Next, Smith-Ramesh wanted to know whether the decrease in herbivorous insects benefitted native plant growth. To test this directly, she transplanted three types of native plants into her S+, S- and N plots. One of the species, the Hairy Wood Mint Blephilia hirsuta, enjoyed a 50% biomass boost in S+ plots compared to S- plots. The other two native plants species showed very little effect.

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Smith-Ramesh collecting data with three siliques in the foreground. Credit: Lauren Smith-Ramesh.

Garlic mustard plants with intact siliques also benefitted the soils by increasing the amount of available phosphorus by approximately 60%. This phosphorus may have originated with insect carcasses that made their way into the soil and released their nutrients. In theory, soils with higher phosphorus availability could help support the growth of native plants. Smith-Ramesh plans to explore other plant communities that are suffering from different invasive plants, to see whether these invaders are also inadvertently providing resources or conditions that may undermine the success of their invasion.

note: the paper that describes this research is from the journal Ecology. The reference is Smith‐Ramesh, L. M. (2017). Invasive plant alters community and ecosystem dynamics by promoting native predators. Ecology98(3), 751-761. Thanks to the Ecological Society of America for allowing me to use figures from the paper. Copyright © 2017 by the Ecological Society of America. All rights reserved.