Reclaiming contaminated land through manipulating biodiversity

Contents of this post originally appeared on the Applied Ecologist, but with expanded thoughts here.

Five years ago I spent my sabbatical in China and worked closely with a lab in Guangzhou. While there, I built meaningful collaborations and friendships that have continued to advance the science I'm involved with. While in China, I accompanied my friend, Jin-tian Li to a biodiversity field experiment on contaminated post-mining lands in Hunan province, and our discussions led to the just-published paper (please e-mail me if you want a copy) in the Journal of Applied Ecology, first-authored by a former PhD student in my lab, Pu Jia.

Why do we care about degraded lands?

According to the IPBES report on land degradation, the degradation of productive lands and intact habitats is a major threat to sustainability, biodiversity and ecosystem functioning globally, which reduces the resiliency of ecological and economic systems. In many emerging economy countries, environmentally harmful practices that result in contamination render lands and habitats seriously degraded. In many circumstances, the restoration of contaminated habitats to original conditions is not an option because the capacity for these habitats to harbor intact native ecosystems is greatly compromised. In these cases, we need management options that allow us to reclaim contaminated and degraded lands (Nathanail & Bardos 2005), and preferably ones that increase biodiversity and ecosystem function (Rohr et al. 2016).

The potential role of biodiversity in reclaiming contaminated lands

While the ecological literature on the linkages between biodiversity and ecosystem function is vast and rich (e.g., Tilman, Isbell & Cowles 2014), the application of this field of research to reclaiming contaminated lands has been strangely depauperate, and so there’s little guidance on whether we should be planting diverse plant assemblages on contaminated lands, or if we ought to simply plant the most productive species or those that provide efficient phyto-removal of contaminants. This question is of fundamental importance to places like China, where rapid development and industrialization through the 1970s-1990s resulted in severe contamination of lands near mining and mineral processing facilities (Li et al. 2019), and now with China’s commitment to improving it’s environmental health, biodiversity research has the ability to impact policy and management at a national scale.

Our paper

We evaluated whether more diverse plantings increased reclamation and ecosystem functioning of a mine wasteland in Hunan Province, China, which had been severely contaminated with cadmium and zinc over decades. We sowed plots with 1-16 species and these were selected from the herbaceous species that grew around contaminated sites in the region, and more diverse assemblages produced more biomass and were more stable over time. Further, there was less heavy metal contamination of leaf tissues in the more diverse plantings, which reduces the impact on herbivores.

Importantly though, plant diversity spurred plant-soil feedbacks (PSFs) that appeared to drive the increased ecosystem functioning. Higher plant diversity supported higher soil bacterial and fungal diversity. Importantly, higher plant diversity was accompanied with more soil cellulolytic bacteria that exude enzymes that degrade cellulose and so drive decomposition and nutrient cycling, which are essential components of a functioning ecosystem. 




Furthermore, the multi-species assemblages also performed better because these high diversity treatments harboured fewer soil fungal pathogens (and by extension more beneficial soil fungi). This appeared to be driven by the fact that high plant diversity supported a greater diversity of soil chitinolytic bacteria that produce anti-fungal enzymes that degrade the chitin in cell walls of soil-borne plant-pathogenic fungi.

In the search for efficient ways to reclaim contaminated lands, sowing high-diversity plant assemblages appear to be an effective tool. The key for reclamation is to ensure that soil processes like decomposition and nutrient cycling are able to support a self-sustaining ecosystem, and higher plant diversity can ensure this. The next steps will be to field test this in real reclamation projects and to see this research work its way into best practices.

Li, T., Liu, Y., Lin, S., Liu, Y. & Xie, Y. (2019) Soil pollution management in China: a brief introduction. Sustainability, 11, 556.

Nathanail, C.P. & Bardos, R.P. (2005) Reclamation of contaminated land. John Wiley & Sons.

Rohr, J.R., Farag, A.M., Cadotte, M.W., Clements, W.H., Smith, J.R., Ulrich, C.P. & Woods, R. (2016) Transforming ecosystems: when, where, and how to restore contaminated sites. Integrated Environmental Assessment and Management, 12, 273-283.

Tilman, D., Isbell, F. & Cowles, J.M. (2014) Biodiversity and ecosystem functioning. Annual Review of Ecology, Evolution and Systematics, 45, 471-493.

---

Don't be Ranunculus... Little known plant behaviours

Guest post by Agneta Szabo, MEnvSci Candidate in the Professional Masters of Environmental Science program at the University of Toronto-Scarborough

Through the scientific study of plant behaviour, we continue to discover new ways in which plants interact with their environment in animal-like ways. Words like “listening”, “foraging”, and “parenting” may seem odd to associate with plants, and yet plants show evidence of all of these behaviours. Here are some of the many ways in which plants behave.

Listening

As it turns out, plants are listening! A study by Heidi Appel and Rex Cocroft published in 2014 describes their discovery that plants can detect their predators acoustically and ramp up their defenses as a response. Appel and Cocroft recorded the sound vibrations of caterpillars chewing on Mouse‑ear Cress leaves, and played these recorded vibrations to previously unaffected Mouse-ear Cress plants over several hours before allowing caterpillars to attack the plants. The researchers found that, compared to plants that were primed with recordings of silence, those who were primed with recordings of chewing produced much higher levels of the oils glucosinolate and anthocyanin, which are toxic to caterpillars. Furthermore, Appel and Cocroft found that the plants were able to distinguish the sound vibrations caused by chewing from recordings of wind or other insect noises.

In addition to listening for their predators, plants can also listen for water. In 2017, Monica Gagliano and her colleagues published a paper showing that the Garden Pea was able to locate water by sensing the vibrations generated by water moving inside pipes. Garden Pea seedlings were planted in pots shaped like an upside-down Y, and each arm of the pot was treated with different experimental conditions. When one arm was placed in a tray of water and the other was dry, plant roots grew towards the arm with water. Seems obvious enough. However, when one arm was placed above a tube with flowing water and the other was dry, the plant roots still grew towards the water, even though there was no moisture. When given a choice between a tray of water and the tube with flowing water, the Garden Pea seedlings chose the tray of water. This led Gagliano to hypothesize that plants may use sound vibrations to detect water at a distance, but that moisture gradients allow the plants to reach their target at close proximity.

Garden Pea water acoustics experimental set-up (Gagliano et al., 2017)

Foraging

Plant roots forage for food in a similar way to animals. In his 2011 review, James Cahill explores plant root responses to varying nutrient cues in the soil. Cahill explains that plant roots are responsive to both spatial and temporal nutrient availability. For example, when a nutrient patch is placed in the soil at a distance from the plant, there is a substantial acceleration in root growth in the following days. This growth is directed precisely towards the nutrient patch, and as the root approaches its target, the rate of growth slows as the nutrient patch is consumed. Furthermore, plants develop greater root biomass in richer nutrient patches, and they allocate more root biomass to patches with increasing nutrient levels.

Other foraging plants include the parasitic Dodder vine. This plant has no roots and lives off a host plant. In 2006, Consuelo De Moraes and her team published a study demonstrating that the Dodder plant uses scent, or volatile chemical cues, to locate and select its host plant. De Moraes experimentally planted Dodder seedlings between a Tomato and Common Wheat plant, the Tomato being its preferred host. Using a time lapse camera, De Moraes captured the circling movement of the Dodder plant as it approached both host options repeatedly, before settling on the Tomato plant 90% of the time. Through further experimentation by giving the Dodder seedlings a choice between the condensed chemical odour of the Tomato plant and a live Tomato that has been covered to prevent giving off odour, it was determined that the Dodder uses the chemical signals to select its host. Without being able to “smell” the live Tomato plant, the Dodder chose to attach to the vile containing the condensed chemical odour. 

Dodder vine attaching to a Tomato plant

(PBS, 2014: https://www-tc.pbs.org/wnet/nature/files/2014/09/Mezzanine_485.jpg)

Parenting

One of the most fascinating aspects of plant behaviour is parental care and kin recognition. Suzanne Simard’s work studying forests as a complex, interconnected organism has been featured on several popular media outlets including the TED Talk series and the Radiolab podcast. Through her research, Simard discovered that through a network of mycorrhizal fungi, adult trees were nurturing their young with a targeted exchange of nutrients such as carbon and nitrogen, as well as defense signals and hormones. Through experimental plantings of Douglas Fir seedlings that were directly related to the adult trees and unrelated Douglas Fir seedlings, she found that the “mother trees” recognized and colonized their kin with larger networks of mycorrhizal fungi, and sent more carbon to these seedlings. Furthermore, there was a reduction in root competition with the related seedlings. When injured, the adult trees sent large amounts of carbon and defense signals to their young, which increased the seedlings’ stress resistance.

Tree mycorrhizal network schematic 

(Medium, 2017: https://medium.com/ideo-colab/fungal-networks-connected-businesses-b38025ca7171)

Similar recognition of kin was observed by Susan Dudley and Amanda File in a 2007 paper. In this study, Dudley and File planted related “sibling” Sea Rocket plants together in pots, as well as unrelated “stranger” Sea Rocket plants together in pots. After several weeks, the roots were cleaned and assessed. The study found that kin groups allocated less biomass to their fine roots, while stranger groups grew larger roots in order to compete for resources. The same responses were not observed when kin and stranger groups were grown in isolated pots, which suggests that the mechanism for kin recognition was through root interactions.

Although we still don’t fully understand the mechanism by which plants process information, it is clear that the way plants interact with their environment is far more complicated than we previously thought. The concept of plants as inanimate organisms, blindly competing for resources is now outdated. Continued discoveries in plant behaviour demonstrate, once again, how little we understand about the natural environment—a humbling thought in an age when humankind thinks itself superior to our fellow species.

Bibliography

Appel, H.M. & Cocroft, R.B. (2014). Plants respond to leaf vibrations caused by insect herbivore chewing. Oecologia, (2014)175: 1257–1266.

Cahill, J.F. & McNickle, G.G. (2011). The behavioral ecology of nutrient foraging by plants. Annual Review of Ecology, Evolution, and Systematics, 2011(42): 289–311.

Dudley, S.A. & File, A.L. (2007). Kin recognition in an annual plant. Biology Letters (2007)3: 435–438.

Gagliano, M., Grimonprez, M., Depczynski, M. & Renton, M. (2017). Tuned in: plant roots use sound to locate water. Oecologia (2017)184: 151–160.

Runyon, J.B., Mescher, M.C. & De Moraes, C. (2006). Volatile chemical cues guide host location and host selection by parasitic plants. Science, 313(5795): 1964–1967.

Simard, S. (2016). Suzanne Simard: How trees talk to each other [Video file]. Retrieved from https://www.ted.com/talks/suzanne_simard_how_trees_talk_to_each_other#t-18444