Integrating Natural Cycles and Engineered Processes for Ecosystem Resilience and Restoration

AUTHORS: Mohamed Z. Hatim, Juliette Kool, Farah Shishani, Eduardo Vias Torres, Gijs Bosman, Ties van der Hoeven
Published in Ecology & Evolution
Integrating Natural Cycles and Engineered Processes for Ecosystem Resilience and Restoration
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Ecosystem restoration efforts play a crucial role in fostering greater ecological complexity and addressing the limitations of conventional approaches1. While many restoration initiatives primarily focus on carbon sequestration through tree planting, it is imperative to consider the broader dynamics of energy and water fluxes within ecosystems2. Vegetation significantly influences the hydrological cycle, which involves the continuous circulation of water through the land, atmosphere, ocean, and surface water bodies. Particularly critical is the role of vegetation in land-atmospheric moisture transport through evapotranspiration3,4, as this directly affects terrestrial water availability through the infiltration and percolation of water into the soil4 and ultimately also local cloud formation and precipitation patterns3,5,6,7. On a global scale, it is shown that the majority of terrestrial precipitation depends on moisture derived from land8,9.

Neglecting these interactions when changing the landscape (e.g. through restoration, de- or afforestation programs) could lead to problematic ecohydrological outcomes10,11, such as decreased runoff and groundwater recharge due to an increase in plant root water uptake after afforestation12,13. Beyond the local effects, large-scale land cover change has shown to have strong atmospheric effects in empirical and modelling studies7. Particularly in coastal regions, where forest loss can, for example, lead to a drastic reduction in land-inward moisture flux, resulting in a decreasing precipitation trend downwind and the risk of shifting the inland regime from wet to dry14,15. In contrast, it has also been shown that desert plantations can be used to deliberately enhance rainfall locally16.

Numerous studies have utilized satellite data to examine the causal relationship between vegetation and precipitation and reveal diverse effects on local-to-regional water availability17,6. However, there is a consensus among researchers that vegetation holds potential as a strategy to modify local water availability18. Notably, Jiao19 demonstrated a positive correlation between vegetation and water availability, as illustrated in Figure 1.

Figure 1. a, b display the distribution of correlation coefficients between the normalized difference vegetation index (NDVI) anomaly and the 3-month Standardized Precipitation-Evapotranspiration Index (SPEI03) and Palmer Drought Severity Index (scPDSI ). The color legend represents the correlation coefficient values for the entire study period (horizontal axis) and the trend of correlation coefficient for 30 five-year moving windows (vertical axis), with unvegetated regions shown as no color. Chartreuse indicates decreasing water surplus in vegetation water surplus regions, navy represents increasing water surplus, magenta signifies increasing water deficit, and yellow indicates decreasing water deficit. c, d illustrate the temporal trends of significant changes in percentage areas associated with water deficit and water surplus responses, using 5-year moving windows. Blue represents water surplus response, and red represents water deficit response. All trends of water deficit and water surplus responses are statistically significant (p < 0.05) based on the linear and Mann–Kendall trend tests. The x-axes of figures (c, d) are binned using 5-year moving windows to smooth and highlight trends.

This finding supports the notion that vegetation can contribute to increased water availability in certain contexts. However, it is essential to recognize that the relationship between vegetation and water availability is not universally consistent and can exhibit location-specific variations17.

Overall, vegetation plays a crucial role in controlling local water availability through its influence on land-atmosphere fluxes, water infiltration, and soil percolation. Understanding these ecosystem dynamics and the role of vegetation in the water cycle is crucial for managing and conserving water resources20 and allows us to recognize the potential risks and adopt a more holistic, deliberate approach. Whereby restoration efforts can promote biodiversity, leverage excess nutrients in water bodies, and ensure sustainable ecological restoration outcomes21,22.

Blending Natural Cycles and Engineered Processes:

The remarkable aspect of ecosystem restoration lies in the harmonious integration of natural cycles with engineered processes23, also known as Bio-geoengineering16. By harnessing the inherent power of nature and incorporating carefully designed interventions, we can shape and direct ecosystem dynamics. The selection of specific algae, plant, and animal species plays a pivotal role in establishing diverse habitats, each contributing to the overall resilience of the ecosystem24,25. Moreover, the flexibility to set varying soil depths across different land ecosystems enables the creation of many habitats within a limited space, fostering greater biodiversity and ecological complexity26.

One of the leading examples of incorporating scientific knowledge of ecosystem dynamics and the integration of natural cycles and engineered processes, such as phytoremediation and ecohydrology, in ecosystem restoration is the Eco Oasis (Fig. 2). It is a dome-shaped greenhouse that integrates multiple interconnected habitats to establish a controlled environment for water, energy, and nutrient cycles. This synergy fosters accelerated biodiversity development, facilitating interactive and symbiotic processes among diverse life forms. Phytoremediation refers to the use of plants to mitigate environmental pollution27, while ecohydrology explores the interactions between ecological processes and hydrological systems28. By blending these natural cycles and engineered processes, the Eco Oasis project exemplifies a holistic approach to ecosystem restoration, ensuring the effective management of ecological resources and the restoration of vital ecosystem services. The Eco Oasis seeks to replicate and study these dynamics by mimicking natural ecosystems. This involves understanding and monitoring the flow of energy, nutrients, and matter among the various components of an ecosystem.

Figure 2. The Eco Oasis Laboratory from inside (left of the picture) and outside (right of the picture).

 

Nutrient Cycling:

Addressing nutrient imbalances in water and soil is crucial for achieving sustainable ecosystem restoration29. Excessive nutrient loadings of compounds based on nitrogen and phosphorus can lead to eutrophication and disrupt the delicate ecological balance of natural ecosystems25. Innovative approaches are being employed to remove these excess nutrients from ecosystems, restoring water quality and supporting the growth of diverse life forms. By utilizing natural processes such as phytoremediation, nutrient-rich waters can be purified as they interact with vegetation, effectively eliminating harmful substances and fostering ecological restoration30.

Nutrient cycling is an essential concept applied in the Eco Oasis. The system is designed to utilize surplus nutrients from the water to foster biodiversity31. As water passes through the different stages of the ecosystem, it supports the growth of various life forms, ranging from algae to higher organisms such as trees, reeds, microcrustaceans, molluscs, amphibians, and fish. This process contributes to rebalancing water quality and nutrient cycling, ultimately leading to increased biodiversity within the system31. By effectively managing and recycling nutrients, the Eco Oasis creates a self-sustaining environment that fosters the growth and development of diverse species, further enhancing the ecological dynamics and potential for harmonious coexistence with nature.

Monitoring Vegetation Dynamics:

Monitoring vegetation dynamics is essential for assessing the health and progress of ecosystem restoration efforts32. Through continuous observation, scientists gain valuable insights into the response of different plant species to changing environmental conditions, which in turn contributes to the preservation of biodiversity. By monitoring vegetation dynamics, researchers can identify shifts in species composition, detect changes in habitat suitability, and track the presence of rare or endangered plant species33. This knowledge allows for refining restoration strategies and optimising vegetation selection to maximize impact25. Furthermore, tracking vegetation dynamics enables the identification of invasive species, prompting the development of effective measures to mitigate their negative effects and preserve ecosystem integrity34.

Revitalizing the Soil:

Soil degradation significantly threatens ecosystem health and productivity through reduced nutrient availability, erosion and loss of topsoil, soil compaction, soil organic matter, and altered soil structure and function35. However, by implementing restoration techniques, we can revitalize the soil and create fertile environments for plant growth. Practices such as the application of organic matter, biochar and beneficial microbes can improve the soil structure, and increase nutrient availability and water retention capacity25. Soils are a vital natural resource that host vast biodiversity in terms of species, abundance and functions. These organisms and their interactions are essential to the processes and functions of the soil, and thus, enhance soil’s ability to decompose organic matter, regulate nutrients, pest regulation, and soil structure development36. The aggregate soil functions provide significant ecosystem services for society, such as climate regulation, food production, and provision of clean water37. By restoring the soil, ecosystem restoration efforts establish a solid foundation for sustained growth, biodiversity, and ecosystem services38. Therefore, the application of the Eco Oasis model catalyses soil revitalization and fosters quality soils through the promotion of higher biodiversity and providing ideal conditions for optimal soil functions in a comprehensive approach.

Conclusion:

Understanding ecosystem dynamics and the role of vegetation in the water cycle is crucial for managing water resources and maintaining ecosystem health. Successful ecosystem restoration requires monitoring vegetation dynamics, addressing nutrient imbalances, and revitalizing the soil. Restoring and preserving healthy ecosystems not only provides essential services such as clean water, air purification, and climate regulation but also enhances community resilience and sustainable livelihoods. To effectively tackle climate change and promote resilience, a holistic approach that empowers nature and harnesses ecosystem services is needed. It is important to invest in research and mainstream ecosystem-based solutions, while also understanding the local and downstream effects of ecosystems on weather and land-atmosphere processes. Integrating natural cycles and engineered processes is key to enhancing ecosystem resilience and achieving effective ecosystem restoration for long-term ecological health.

References:

  1. Palmer, M.A., et al. (2014). Ecological restoration of streams and rivers: Shifting strategies and shifting goals. Annual Review of Ecology, Evolution, and Systematics, 45, 247-269.
  2. Hobbs, R.J., et al. (2014). Managing the whole landscape: Historical, hybrid, and novel ecosystems. Frontiers in Ecology and the Environment, 12(10), 557-564.
  3. Falkowski, P., & Raven, J. A. (2007). Aquatic photosynthesis (2nd ed.). Princeton University Press.
  4. Mitsch, W. J., & Gosselink, J. G. (2015). Wetlands (5th ed.). Wiley.
  5. Falkowski, P. G., Fenchel, T., & Delong, E. F. (2008). The microbial engines that drive Earth's biogeochemical cycles. Science, 320(5879), 1034-1039.
  6. Cui, J., Lian, X. & Huntingford, C., Gimeno, L., Ding, J., He, M., & Xu, H., & Chen, A., Gentine, P., Piao, S. (2022). Global water availability boosted by vegetation-driven changes in atmospheric moisture transport. Nature Geoscience. 15. 1-7. 10.1038/s41561-022-01061-7.
  7. Mu, Y., & Jones, C. (2022). An observational analysis of precipitation and deforestation age in the Brazilian Legal Amazon. Atmospheric Research, 271, 106122. doi:10.1016/j.atmosres.2022.106122
  8. Sheil, D. Forests, atmospheric water and an uncertain future: the new biology of the global water cycle. For. Ecosyst. 5, 19 (2018). https://doi.org/10.1186/s40663-018-0138-y
  9. Tuinenburg, O. A., Theeuwen, J. J. E., & Staal, A. (2020). High-resolution global atmospheric moisture connections from evaporation to precipitation. Earth System Science Data, 12(4), 3177–3188. doi:10.5194/essd-12-3177-2020.
  10. Savenije, H. H. G. (1996). The runoff coefficient as the key to moisture recycling. Journal of Hydrology, 176(1–4), 219–225. https://doi.org/10.1016/0022-1694(95)02776-9
  11. Schaefli, B., van der Ent, R. J., Woods, R., & Savenije, H. H. G. (2012). An analytical model for soil-atmosphere feedback. Hydrology and Earth System Sciences, 16(7), 1863–1878. https://doi.org/10.5194/hess-16-1863-2012
  12. Palmer, M.A., et al. (2010). Mountaintop mining consequences. Science, 327(5962), 148-149.
  13. Ding, B., Zhang, Y., Yu, X., Jia, G., Wang, Y., Wang, Y., … Li, Z. (2022). Effects of forest cover type and ratio changes on runoff and its components. International Soil and Water Conservation Research, 10(3), 445–456. doi:10.1016/j.iswcr.2022.01.006
  14. Millán, M. M. (2014). Extreme hydrometeorological events and climate change predictions in Europe. Journal of Hydrology, 518(PB), 206–224. https://doi.org/10.1016/j.jhydrol.2013.12.041
  15. Sheil, D. (2014). How plants water our planet: Advances and imperatives. Trends in Plant Science, 19(4), 209– 211. https://doi.org/10.1016/j.tplants.2014.01.002
  16. Branch, O., & Wulfmeyer, V. (2019). Deliberate enhancement of rainfall using desert plantations. Proceedings of the National Academy of Sciences of the United States of America, 116(38), 18841–18847. https://doi.org/10.1073/pnas.1904754116
  17. Hoek van Dijke, A.J., Herold, M., Mallick, K. et al. Shifts in regional water availability due to global tree restoration. Nat. Geosci. 15, 363–368 (2022). https://doi.org/10.1038/s41561-022-00935-0
  18. te Wierik, S. A., Cammeraat, E. L., Gupta, J., & Artzy‐Randrup, Y. A. (2021). Reviewing the impact of land use and land‐use change on moisture recycling and precipitation patterns. Water Resources Research, 57(7), e2020WR029234.
  19. Jiao, W., Wang, L., Smith, W.K. et al. Observed increasing water constraint on vegetation growth over the last three decades. Nat Commun 12, 3777 (2021). https://doi.org/10.1038/s41467-021-24016-9
  20. Odum, E. P., & Barrett, G. W. (2004). Fundamentals of ecology. Cengage Learning.
  21. Suding, K.N., et al. (2015). Functional- and abundance-based mechanisms explain diversity loss due to N fertilization. Proceedings of the National Academy of Sciences, 112(18), 6100-6105.
  22. Allan, J.D., et al. (2013). Landscapes that work for biodiversity and people. Science, 342(6159), 803-805.
  23. Nassauer, J. I. (1995). Culture and changing landscape structure. Landscape Ecology, 10(4), 229-237.
  24. Chapin III, F. S., Walker, B. H., Hobbs, R. J., Hooper, D. U., Lawton, J. H., Sala, O. E., & Tilman, D. (1997). Biotic control over the functioning of ecosystems. Science, 277(5325), 500-504.
  25. Cardinale, B. J., Duffy, J. E., Gonzalez, A., et al. (2012). Biodiversity loss and its impact on humanity. Nature, 486(7401), 59-67.
  26. Wei, X., Shao, Q., Sun, Y., & Jiao, F. (2020). Influence of soil depths on vegetation patterns and soil moisture in a subtropical karst ecosystem. Ecological Indicators, 109, 105785.
  27. Salt, D. E., Smith, R. D., & Raskin, I. (1995). Phytoremediation. Annual Review of Plant Physiology and Plant Molecular Biology, 49, 643-668.
  28. D'Odorico, P., Caylor, K., Okin, G. S., & Scanlon, T. M. (2020). Ecohydrology: A mechanistic approach to understanding and restoring the structure and function of ecosystems. Ecological Engineering, 144, 105728.
  29. Vitousek, P. M., Aber, J. D., Howarth, R. W., Likens, G. E., Matson, P. A., Schindler, D. W., Schlesinger, W. H., & Tilman, D. G. (1997). Human alteration of the global nitrogen cycle: sources and consequences. Ecological Applications, 7(3), 737-750.
  30. Khan, S., Afzal, M., Iqbal, S., & Khan, Q. M. (2013). Plant–bacteria partnerships for the remediation of hydrocarbon contaminated soils. Chemosphere, 90(4), 1317-1332.
  31. Todd, J., H., van der Hoeven, M., L., E., B., & Bosman, G. (2023). NL Patent No. 2028987. Agricultural system and method of operating the same. The Netherlands, Ede: Netherlands Patent Office.
  32. Elzinga, C. L., Salzer, D. W., Willoughby, J. W., & Gibbs, J. P. (2001). Monitoring plant and animal populations: a handbook for field biologists. John Wiley & Sons.
  33. Gilliam, F. S. (2007). The ecological significance of the herbaceous layer in temperate forest ecosystems. Bioscience, 57(10), 845-858.
  34. Jourdan, F. J. C. B., Pilowsky, J., & Phillips, O. L. (2018). Tracking Plant Invasions: From Data to Models. Annual Review of Ecology, Evolution, and Systematics, 49.
  35. Montgomery, D. R. (2007). Soil erosion and agricultural sustainability. Proceedings of the National Academy of Sciences, 104(33), 13268-13272.
  36. Mirjam Pulleman, Rachel Creamer, Ute Hamer, Johannes Helder, Céline Pelosi, Guénola Pérès, Michiel Rutgers, Soil biodiversity, biological indicators and soil ecosystem services—an overview of European approaches, Current Opinion in Environmental Sustainability Volume 4, Issue 5, 2012, Pages 529-538, ISSN 1877-3435, https://doi.org/10.1016/j.cosust.2012.10.009.
  37. Mulder, C., Boit, A., Bonkowski, M., De Ruiter, P. C., Mancinelli, G., Van der Heijden, M. G., ... & Rutgers, M. (2011). A belowground perspective on Dutch agroecosystems: how soil organisms interact to support ecosystem services. In Advances in ecological research (Vol. 44, pp. 277-357). Academic Press.
  38. Ehrenfeld, J. G. (2003). Effects of exotic plant invasions on soil nutrient cycling processes. Ecosystems, 6(6), 503-523.

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