Engineering Biology for Climate & Sustainability
Food & Agriculture Goal:

Lower greenhouse gas emissions from food production.

Current State-of-the-Art

Current food production and agricultural practices contribute significantly to global greenhouse gas (GHG) emissions. From 2000 to 2014, CO2 emissions from food production increased from 1 to 1.28 gigatonnes amongst 14 of the world’s top 20 agricultural producers.1Mrówczyńska-Kamińska, A., Bajan, B., Pawłowski, K. P., Genstwa, N., & Zmyślona, J. (2021). Greenhouse gas emissions intensity of food production systems and its determinants. PLOS ONE, 16(4), e0250995. View Publication. This production of GHGs includes nitrous oxide from synthetic fertilizer usage and agricultural production,2Davidson, E. A. (2009). The contribution of manure and fertilizer nitrogen to atmospheric nitrous oxide since 1860. Nature Geoscience, 2(9), 659–662. View Publication., 3Timilsina, A., Zhang, C., Pandey, B., Bizimana, F., Dong, W., & Hu, C. (2020). Potential Pathway of Nitrous Oxide Formation in Plants. Frontiers in Plant Science, 11, 1177. View Publication. and methane produced by livestock as part of their natural digestion process.4Tapio, I., Snelling, T. J., Strozzi, F., & Wallace, R. J. (2017). The ruminal microbiome associated with methane emissions from ruminant livestock. Journal of Animal Science and Biotechnology, 8(1), 7. View Publication., 5Lassey, K. R. (2008). Livestock methane emission and its perspective in the global methane cycle. Australian Journal of Experimental Agriculture, 48(2), 114–118. View Publication.

The Haber–Bosch process for manufacturing fertilizers is a cornerstone of industrial agriculture. However, the Haber process is energy intensive and generates large amounts of N2O, a potent and long-lived GHG with 300 times the warming potential of CO2.6Ghavam, S., Vahdati, M., Wilson, I. A. G., & Styring, P. (2021). Sustainable Ammonia Production Processes. Frontiers in Energy Research, 9. View Publication. Engineering biology is developing alternatives to decrease or eliminate the need for industrial fertilizers and chemical supplements. The rhizosphere, the soil zone where plant roots influence biological and chemical features of the soil, supports natural symbiosis with bacteria that help the plant with nitrogen fixation. This ability could be extended to more crops (i.e., non-legume plants) by engineering enhanced nitrogen fixation capabilities to crop plants and engineering bacteria associated with crops as fertilizers.7DeLisi, C., Patrinos, A., MacCracken, M., Drell, D., Annas, G., Arkin, A., Church, G., Cook-Deegan, R., Jacoby, H., Lidstrom, M., Melillo, J., Milo, R., Paustian, K., Reilly, J., Roberts, R. J., Segrè, D., Solomon, S., Woolf, D., Wullschleger, S. D., & Yang, X. (2020). The Role of Synthetic Biology in Atmospheric Greenhouse Gas Reduction: Prospects and Challenges. BioDesign Research, 2020, 1–8. View Publication., 8Bloch, S. E., Clark, R., Gottlieb, S. S., Wood, L. K., Shah, N., Mak, S.-M., Lorigan, J. G., Johnson, J., Davis-Richardson, A. G., Williams, L., McKellar, M., Soriano, D., Petersen, M., Horton, A., Smith, O., Wu, L., Tung, E., Broglie, R., Tamsir, A., & Temme, K. (2020). Biological nitrogen fixation in maize: Optimizing nitrogenase expression in a root-associated diazotroph. Journal of Experimental Botany, 71(15), 4591–4603. View Publication. Research is also underway to engineer microbial-plant interactions that enable lower use of phosphorus fertilization.9Cheng, Y. T., Zhang, L., & He, S. Y. (2019). Plant-Microbe Interactions Facing Environmental Challenge. Cell Host & Microbe, 26(2), 183–192. View Publication., 10Barea, J.-M., Pozo, M. J., Azcón, R., & Azcón-Aguilar, C. (2005). Microbial co-operation in the rhizosphere. Journal of Experimental Botany, 56(417), 1761–1778. View Publication., 11Ahmad, F., Uddin, S., Ahmad, N., & Islam, R. (2013). Phosphorus–microbes interaction on growth, yield and phosphorus-use efficiency of irrigated cotton. Archives of Agronomy and Soil Science, 59(3), 341–351. View Publication. Some of this is already practiced commercially by companies such as Pivot Bio, though most technologies are still at an early stage of development. These new biobased fertilizers can help reduce the need for water, enable the use of currently non-arable land for plant growth, and prevent ecological disruption caused by run-off of water-soluble nitrates and the eutrophication of marine environments.

Advances in genetic engineering (e.g., CRISPR) and precision agriculture will lead to more efficient crop production that generates fewer greenhouse gases. Genetically engineered crops have been grown successfully since 1996 with important impacts on carbon emissions.12Brookes, G., & Barfoot, P. (2020). Environmental impacts of genetically modified (GM) crop use 1996–2018: Impacts on pesticide use and carbon emissions. GM Crops & Food, 11(4), 215–241. View Publication. As an example of where engineering biology tools and technologies can impact the emissions from crop production, we can look at a world-wide staple crop: rice. Rice cultivation usually includes a period of time where fields are intentionally flooded, creating an environment where methanogens thrive. Methane from rice production accounts for approximately 11% of annual anthropogenic methane emission.13Jiang, Y., Qian, H., Huang, S., Zhang, X., Wang, L., Zhang, L., Shen, M., Xiao, X., Chen, F., Zhang, H., Lu, C., Li, C., Zhang, J., Deng, A., van Groenigen, K. J., & Zhang, W. (2019). Acclimation of methane emissions from rice paddy fields to straw addition. Science Advances, 5(1), eaau9038. View Publication. Rice engineered to maintain high yields with minimal flood time, or an engineered microbiome that suppresses methanogen activity during flooding, could lower total methane emissions (see Kumar et al., 201414Kumar, A., Dixit, S., Ram, T., Yadaw, R. B., Mishra, K. K., & Mandal, N. P. (2014). Breeding high-yielding drought-tolerant rice: Genetic variations and conventional and molecular approaches. Journal of Experimental Botany, 65(21), 6265–6278. View Publication.; Scholz et al., 202015Scholz, V. V., Meckenstock, R. U., Nielsen, L. P., & Risgaard-Petersen, N. (2020). Cable bacteria reduce methane emissions from rice-vegetated soils. Nature Communications, 11(1), 1878. View Publication.). As a specific example, a recent Science publication details the overexpression of a transcriptional regulator in rice, induced by light and low-nitrogen, resulting in increased photosynthesis and nitrogen utilization and higher yield.16Wei, S., Li, X., Lu, Z., Zhang, H., Ye, X., Zhou, Y., Li, J., Yan, Y., Pei, H., Duan, F., Wang, D., Chen, S., Wang, P., Zhang, C., Shang, L., Zhou, Y., Yan, P., Zhao, M., Huang, J., … Zhou, W. (2022). A transcriptional regulator that boosts grain yields and shortens the growth duration of rice. Science, 377(6604), eabi8455. View Publication. In addition to this example, the engineering of plant-incorporated protectants (PIPs) into more crop varieties could reduce emissions by decreasing the total production, transportation, and application of pesticides. Emissions caused by Conventional Tillage techniques can be reduced by engineering crops that enable transitions to Reduced Tillage or No Tillage,17Brookes, G., & Barfoot, P. (2020). Environmental impacts of genetically modified (GM) crop use 1996–2018: Impacts on pesticide use and carbon emissions. GM Crops & Food, 11(4), 215–241. View Publication. for example by engineering enhanced crop allelochemical production (see Mahé et al., 202218Mahé, I., Chauvel, B., Colbach, N., Cordeau, S., Gfeller, A., Reiss, A., & Moreau, D. (2022). Deciphering field-based evidences for crop allelopathy in weed regulation. A review. Agronomy for Sustainable Development, 42(3), 50. View Publication.). Crops that do not typically benefit from symbioses with nitrogen-fixing microbes could be engineered to do so. Plant biosensors could communicate phosphorus or nitrogen needs to enable their precise use, reducing overuse and runoff. Expanding the approaches, engineering goals, targeted crop species and varieties, accessibility, and general education about crop engineering will increase the ability to reduce emissions.

Food production from livestock is the largest anthropogenic source in the global methane budget, mostly from enteric fermentation of domestic ruminants.19Chang, J., Peng, S., Ciais, P., Saunois, M., Dangal, S. R. S., Herrero, M., Havlík, P., Tian, H., & Bousquet, P. (2019). Revisiting enteric methane emissions from domestic ruminants and their δ13CCH4 source signature. Nature Communications, 10(1), 3420. View Publication. Engineering biology could reduce methane in agriculture by producing more climate friendly diets for livestock. To prevent methane emissions, methanotrophs could be introduced through feed or inoculation to stably colonize the ruminant gut microbiome. Colonized microbes could be engineered to secrete small molecule inhibitors (see Duin et al., 201620Duin, E. C., Wagner, T., Shima, S., Prakash, D., Cronin, B., Yáñez-Ruiz, D. R., Duval, S., Rümbeli, R., Stemmler, R. T., Thauer, R. K., & Kindermann, M. (2016). Mode of action uncovered for the specific reduction of methane emissions from ruminants by the small molecule 3-nitrooxypropanol. Proceedings of the National Academy of Sciences, 113(22), 6172–6177. View Publication. and Patra et al., 201721Patra, A., Park, T., Kim, M., & Yu, Z. (2017). Rumen methanogens and mitigation of methane emission by anti-methanogenic compounds and substances. Journal of Animal Science and Biotechnology, 8(1), 13. View Publication., for examples) in ruminant guts to reduce methane formation or metabolize methane into non-gaseous compounds to enhance animal health (e.g., acetate, succinate, butyrate, amino acids, methanol).22Ungerfeld, E. M. (2020). Metabolic Hydrogen Flows in Rumen Fermentation: Principles and Possibilities of Interventions. Frontiers in Microbiology, 11. View Publication. Engineering biology could also be used to pretreat animal feed and increase animal feed efficiency. For example, engineered microbes could synthesize animal nutrients (e.g., essential amino acids, micronutrients, vitamins) not naturally found in unprocessed feed or maintain specific moisture content in hay, haylage, or silage to increase feed production efficiency.

Further development and expansion of the “cellular agriculture” sector, including current cultured/cultivated meat and algae food products, to produce a broader variety of meat alternatives would reduce climate change by providing substitutes for animal and crop use (agricultural footprint), and support resilience in the wake of the effects of climate change. Meat and protein alternatives enabled by engineering microbial, fungal, or plant production of proteins, fats, and flavorings offer another means to continue feeding a growing global population.23Linder, T. (2019). Making the case for edible microorganisms as an integral part of a more sustainable and resilient food production system. Food Security, 11(2), 265–278. View Publication. These technologies can also help to reduce the consumption of resources, including land, water, fertilizers, and pesticides. For instance, the milk protein market relies on animals and plants as a source for dairy and dairy alternatives (e.g., oat and nut milks); a recent modeling study concluded that microbes could be cultured to scalably produce Bovine Alpha Lactalbumin, one of the most prevalent whey proteins in the market and used for human infant formula among other products.24Vestergaard, M., Chan, S. H. J., & Jensen, P. R. (2016). Can microbes compete with cows for sustainable protein production—A feasibility study on high quality protein. Scientific Reports, 6, 36421. View Publication. Engineering biology to improve the taste, texture, and nutritional value of protein alternatives and lowering the cost of ingredients (e.g., flavorings, fatty acids, enzymes) will make these products more attractive and accessible to the global population. These proteins may ultimately be produced from CO2 or methane using photo- and chemoautotrophic organisms, similar to previously demonstrated production of single cell protein (SCP) from methane.25Marcellin, E., Angenent, L. T., Nielsen, L. K., & Molitor, B. (2022). Recycling carbon for sustainable protein production using gas fermentation. Current Opinion in Biotechnology, 76, 102723. View Publication., 26García Martínez, J. B., Pearce, J. M., Throup, J., Cates, J., Lackner, M., & Denkenberger, D. C. (2022). Methane Single Cell Protein: Potential to Secure a Global Protein Supply Against Catastrophic Food Shocks. Frontiers in Bioengineering and Biotechnology, 10. View Publication

Finally, the conversion or recycling of food and agricultural wastes into value-added products will help to circularize the sector, reducing greenhouse gas emissions, not just from the wastes themselves (e.g., emissions from rotting foods), but also waste management practices.27Nayak, A., & Bhushan, B. (2019). An overview of the recent trends on the waste valorization techniques for food wastes. Journal of Environmental Management, 233, 352–370. View Publication Engineered enzymatic pathways can be used to transform waste biomass into feedstocks, such as nutrients for biofertilizers or biomass for biofuels.28Liew, F. E., Nogle, R., Abdalla, T., Rasor, B. J., Canter, C., Jensen, R. O., Wang, L., Strutz, J., Chirania, P., De Tissera, S., Mueller, A. P., Ruan, Z., Gao, A., Tran, L., Engle, N. L., Bromley, J. C., Daniell, J., Conrado, R., Tschaplinski, T. J., … Köpke, M. (2022). Carbon-negative production of acetone and isopropanol by gas fermentation at industrial pilot scale. Nature Biotechnology, 40(3), 335–344. View Publication., 29Davis, K., & Moon, T. S. (2020). Tailoring microbes to upgrade lignin. Current Opinion in Chemical Biology, 59, 23–29. View Publication. To do so sustainably means ensuring that these systems can be implemented where wastes are generated and where the value-added products can be used or consumed locally.

Breakthrough Capabilities & Milestones

Enable sustainable, climate-friendly biobased fertilizers.

*Zurier, H. S., Duong, M. M., Goddard, J. M., & Nugen, S. R. (2020). Engineering Biorthogonal Phage-Based Nanobots for Ultrasensitive, In Situ Bacteria Detection. ACS Applied Bio Materials, 3(9), 5824–5831. https://doi.org/10.1021/acsabm.0c00546

Engineer agricultural crops that are less emission-intensive.

Reduce methane production through livestock and manure management.

Enable sustainable production of alternative meats and proteins.

* See for example https://multus.media/

Enable engineered biology to convert food and agricultural waste to value-added products.

*Pleissner, D., & Lin, C. S. K. (2013). Valorisation of food waste in biotechnological processes. Sustainable Chemical Processes, 1(1), 21. https://doi.org/10.1186/2043-7129-1-21

**Wang, J. Y., Stabnikova, O., Tay, S. T. L., Ivanov, V., & Tay, J. H. (2004). Biotechnology of intensive aerobic conversion of sewage sludge and food waste into fertilizer. Water Science and Technology: A Journal of the International Association on Water Pollution Research, 49(10), 147–154. Retrieved from https://pubmed.ncbi.nlm.nih.gov/15259949/

Footnotes

  1. Mrówczyńska-Kamińska, A., Bajan, B., Pawłowski, K. P., Genstwa, N., & Zmyślona, J. (2021). Greenhouse gas emissions intensity of food production systems and its determinants. PLOS ONE, 16(4), e0250995. https://doi.org/10.1371/journal.pone.0250995
  2. Davidson, E. A. (2009). The contribution of manure and fertilizer nitrogen to atmospheric nitrous oxide since 1860. Nature Geoscience, 2(9), 659–662. https://doi.org/10.1038/ngeo608
  3. Timilsina, A., Zhang, C., Pandey, B., Bizimana, F., Dong, W., & Hu, C. (2020). Potential Pathway of Nitrous Oxide Formation in Plants. Frontiers in Plant Science, 11, 1177. https://doi.org/10.3389/fpls.2020.01177
  4. Tapio, I., Snelling, T. J., Strozzi, F., & Wallace, R. J. (2017). The ruminal microbiome associated with methane emissions from ruminant livestock. Journal of Animal Science and Biotechnology, 8(1), 7. https://doi.org/10.1186/s40104-017-0141-0
  5. Lassey, K. R. (2008). Livestock methane emission and its perspective in the global methane cycle. Australian Journal of Experimental Agriculture, 48(2), 114–118. https://doi.org/10.1071/EA07220
  6. Ghavam, S., Vahdati, M., Wilson, I. A. G., & Styring, P. (2021). Sustainable Ammonia Production Processes. Frontiers in Energy Research, 9. https://doi.org/10.3389/fenrg.2021.580808
  7. DeLisi, C., Patrinos, A., MacCracken, M., Drell, D., Annas, G., Arkin, A., Church, G., Cook-Deegan, R., Jacoby, H., Lidstrom, M., Melillo, J., Milo, R., Paustian, K., Reilly, J., Roberts, R. J., Segrè, D., Solomon, S., Woolf, D., Wullschleger, S. D., & Yang, X. (2020). The Role of Synthetic Biology in Atmospheric Greenhouse Gas Reduction: Prospects and Challenges. BioDesign Research, 2020, 1–8. https://doi.org/10.34133/2020/1016207
  8. Bloch, S. E., Clark, R., Gottlieb, S. S., Wood, L. K., Shah, N., Mak, S.-M., Lorigan, J. G., Johnson, J., Davis-Richardson, A. G., Williams, L., McKellar, M., Soriano, D., Petersen, M., Horton, A., Smith, O., Wu, L., Tung, E., Broglie, R., Tamsir, A., & Temme, K. (2020). Biological nitrogen fixation in maize: Optimizing nitrogenase expression in a root-associated diazotroph. Journal of Experimental Botany, 71(15), 4591–4603. https://doi.org/10.1093/jxb/eraa176
  9. Cheng, Y. T., Zhang, L., & He, S. Y. (2019). Plant-Microbe Interactions Facing Environmental Challenge. Cell Host & Microbe, 26(2), 183–192. https://doi.org/10.1016/j.chom.2019.07.009
  10. Barea, J.-M., Pozo, M. J., Azcón, R., & Azcón-Aguilar, C. (2005). Microbial co-operation in the rhizosphere. Journal of Experimental Botany, 56(417), 1761–1778. https://doi.org/10.1093/jxb/eri197
  11. Ahmad, F., Uddin, S., Ahmad, N., & Islam, R. (2013). Phosphorus–microbes interaction on growth, yield and phosphorus-use efficiency of irrigated cotton. Archives of Agronomy and Soil Science, 59(3), 341–351. https://doi.org/10.1080/03650340.2011.646994
  12. Brookes, G., & Barfoot, P. (2020). Environmental impacts of genetically modified (GM) crop use 1996–2018: Impacts on pesticide use and carbon emissions. GM Crops & Food, 11(4), 215–241. https://doi.org/10.1080/21645698.2020.1773198
  13. Jiang, Y., Qian, H., Huang, S., Zhang, X., Wang, L., Zhang, L., Shen, M., Xiao, X., Chen, F., Zhang, H., Lu, C., Li, C., Zhang, J., Deng, A., van Groenigen, K. J., & Zhang, W. (2019). Acclimation of methane emissions from rice paddy fields to straw addition. Science Advances, 5(1), eaau9038. https://doi.org/10.1126/sciadv.aau9038
  14. Kumar, A., Dixit, S., Ram, T., Yadaw, R. B., Mishra, K. K., & Mandal, N. P. (2014). Breeding high-yielding drought-tolerant rice: Genetic variations and conventional and molecular approaches. Journal of Experimental Botany, 65(21), 6265–6278. https://doi.org/10.1093/jxb/eru363
  15. Scholz, V. V., Meckenstock, R. U., Nielsen, L. P., & Risgaard-Petersen, N. (2020). Cable bacteria reduce methane emissions from rice-vegetated soils. Nature Communications, 11(1), 1878. https://doi.org/10.1038/s41467-020-15812-w
  16. Wei, S., Li, X., Lu, Z., Zhang, H., Ye, X., Zhou, Y., Li, J., Yan, Y., Pei, H., Duan, F., Wang, D., Chen, S., Wang, P., Zhang, C., Shang, L., Zhou, Y., Yan, P., Zhao, M., Huang, J., … Zhou, W. (2022). A transcriptional regulator that boosts grain yields and shortens the growth duration of rice. Science, 377(6604), eabi8455. https://doi.org/10.1126/science.abi8455
  17. Brookes, G., & Barfoot, P. (2020). Environmental impacts of genetically modified (GM) crop use 1996–2018: Impacts on pesticide use and carbon emissions. GM Crops & Food, 11(4), 215–241. https://doi.org/10.1080/21645698.2020.1773198
  18. Mahé, I., Chauvel, B., Colbach, N., Cordeau, S., Gfeller, A., Reiss, A., & Moreau, D. (2022). Deciphering field-based evidences for crop allelopathy in weed regulation. A review. Agronomy for Sustainable Development, 42(3), 50. https://doi.org/10.1007/s13593-021-00749-1
  19. Chang, J., Peng, S., Ciais, P., Saunois, M., Dangal, S. R. S., Herrero, M., Havlík, P., Tian, H., & Bousquet, P. (2019). Revisiting enteric methane emissions from domestic ruminants and their δ13CCH4 source signature. Nature Communications, 10(1), 3420. https://doi.org/10.1038/s41467-019-11066-3
  20. Duin, E. C., Wagner, T., Shima, S., Prakash, D., Cronin, B., Yáñez-Ruiz, D. R., Duval, S., Rümbeli, R., Stemmler, R. T., Thauer, R. K., & Kindermann, M. (2016). Mode of action uncovered for the specific reduction of methane emissions from ruminants by the small molecule 3-nitrooxypropanol. Proceedings of the National Academy of Sciences, 113(22), 6172–6177. https://doi.org/10.1073/pnas.1600298113
  21. Patra, A., Park, T., Kim, M., & Yu, Z. (2017). Rumen methanogens and mitigation of methane emission by anti-methanogenic compounds and substances. Journal of Animal Science and Biotechnology, 8(1), 13. https://doi.org/10.1186/s40104-017-0145-9
  22. Ungerfeld, E. M. (2020). Metabolic Hydrogen Flows in Rumen Fermentation: Principles and Possibilities of Interventions. Frontiers in Microbiology, 11. https://doi.org/10.3389/fmicb.2020.00589
  23. Linder, T. (2019). Making the case for edible microorganisms as an integral part of a more sustainable and resilient food production system. Food Security, 11(2), 265–278. https://doi.org/10.1007/s12571-019-00912-3
  24. Vestergaard, M., Chan, S. H. J., & Jensen, P. R. (2016). Can microbes compete with cows for sustainable protein production—A feasibility study on high quality protein. Scientific Reports, 6, 36421. https://doi.org/10.1038/srep36421
  25. Marcellin, E., Angenent, L. T., Nielsen, L. K., & Molitor, B. (2022). Recycling carbon for sustainable protein production using gas fermentation. Current Opinion in Biotechnology, 76, 102723. https://doi.org/10.1016/j.copbio.2022.102723
  26. García Martínez, J. B., Pearce, J. M., Throup, J., Cates, J., Lackner, M., & Denkenberger, D. C. (2022). Methane Single Cell Protein: Potential to Secure a Global Protein Supply Against Catastrophic Food Shocks. Frontiers in Bioengineering and Biotechnology, 10. https://doi.org/10.3389/fbioe.2022.906704
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  28. Liew, F. E., Nogle, R., Abdalla, T., Rasor, B. J., Canter, C., Jensen, R. O., Wang, L., Strutz, J., Chirania, P., De Tissera, S., Mueller, A. P., Ruan, Z., Gao, A., Tran, L., Engle, N. L., Bromley, J. C., Daniell, J., Conrado, R., Tschaplinski, T. J., … Köpke, M. (2022). Carbon-negative production of acetone and isopropanol by gas fermentation at industrial pilot scale. Nature Biotechnology, 40(3), 335–344. https://doi.org/10.1038/s41587-021-01195-w
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Last updated: September 19, 2022 Back