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Journal of Integrative Agriculture  2020, Vol. 19 Issue (4): 1159-1161    DOI: 10.1016/S2095-3119(19)62880-7
Special Issue: Plant Protection—Entomolgy
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How does the arthropod–plant system respond to abrupt and gradual increases in atmospheric CO2?
ZHENG Xiao-xu, WU Gang
Hubei Insect Resources Utilization and Sustainable Pest Management Key Laboratory, College of Plant Science and Technology, Huazhong Agricultural University, Wuhan 430070, P.R.China
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Abstract  Global warming caused by elevated carbon dioxide (CO2) is a major environmental and policy issue.  The current global average temperature has been elevated by 1°C since the industrial revolution, and it is likely to reach a temperature increase of 1.5°C between 2030 and 2052 (IPCC 2018).  Human-caused emission of CO2 is responsible for the greenhouse effect and the atmospheric CO2 concentration is higher now than at any other time in the past 500 000 years, and it continues to rise (Lüthi et al. 2008).  Impacts of arthropod–plant interactions on carbon dynamics and the global climate are important but often ignored.  For example, outbreaks of the mountain pine beetle, Dendroctonus ponderosae, in British Columbia during 2000–2020 will cause the release of an estimated 270 Mt carbon and convert the forest from a small carbon sink to a large carbon source (Kurz et al. 2008).   The annual carbon release due to outbreaks of this beetle is almost equivalent to the annual carbon emission from all forest fires occurring in Canada over 1959–1999 (Kurz et al. 2008).
Most studies of arthropod–plant interactions have focused on the effects of ambient CO2 or abruptly increasing CO2 concentrations.  In general, these studies show that elevated CO2 has a positive direct effect on plant photosynthesis and photosynthate production (Bezemer and Jones 1998; Kim et al. 2015; Andresen et al. 2018; Thomey et al. 2019).  Most scientists expect C3 plants to benefit from this additional CO2 and outcompete C4 species, because the efficiency of C3 photosynthesis increases with increasing CO2 concentration to a far greater extent than it does in C4 photosynthesis (Hovenden and Newton 2018; Reich et al. 2018).  Yan et al. (2020) found that elevated CO2 increased photosynthetic rate, nodule number, yield and total phenolic content of Medicago truncatula.  Dong et al. (2018a) reported that elevated CO2 promoted the yield and nutritional quality of cucumber (Cucumis sativus L.).  After conducting a meta-analysis using 57 articles consisting of 1 015 observations, they found that elevated CO2 increased the concentrations of fructose, glucose, total phenols, and total flavonoids in the edible parts of vegetables by 14.2, 13.2, 8.9, and 45.5%, respectively, but decreased the concentrations of protein and nitrate, by 9.5 and 18.0%, respectively (Dong et al. 2018b).  Robinson et al. (2012) reviewed the evidence from 170 studies and concluded that plant biomass, C:N ratio, total phenolics and flavonoids increase under elevated CO2, while N-based secondary metabolites and plant terpenoid concentrations decrease.  Being an important limiting factor for phytophagous arthropods, changes in foliar C-based secondary metabolites (e.g., condensed tannins and phenolics) and N-based chemicals may have major effects on arthropod performance.
Numerous studies have found that elevated CO2 indirectly influences arthropod performance via the changes in plant chemical composition (Ge et al. 2010; Xu et al. 2013; Wu 2014; Sun et al. 2018).  Wen et al. (2019) observed a significantly longer larval duration and lower fecundity of Nilaparvata lugens in elevated CO2.  After analyzing 122 studies, Robinson et al. (2012) concluded that elevated CO2 increases arthropod survival, abundance and relative consumption rate, but it reduces fecundity, relative growth rate and adult weight.  Many chewing pests, such as cotton bollworm (Helicoverpa armigera) and gypsy moth, exhibited lower fecundity, consumption rate and finite rate under elevated CO2 (Foss et al. 2013; Liu et al. 2017).  The sucking pests, however, displayed varied responses to elevated CO2.  For example, in aphids, the responses to elevated CO2 in terms of fecundity, development and population growth varied between different species, different hosts or even different genotypes of the same host (Sudderth et al. 2005; Gao et al. 2008; Guo et al. 2013).  The studies documented above indicated that the chewing arthropods and sap feeders employ different strategies in response to elevated CO2
While it is clear that arthropod–plant interactions are affected by atmospheric CO2 concentrations, it is currently uncertain whether an abrupt increase in CO2 causes similar responses as the gradual increase has been observed since the industrial revolution.  A recent study of Bromus inermis (a perennial grass) and its associated arbuscular mycorrhizal fungi (AMF) shows that abrupt and gradual CO2 change regimes may not elicit the same response (Klironomos et al. 2005).  In a long-term 6-year experiment in which plants were exposed to three CO2 regimes (ambient CO2, gradual increase in CO2, and abrupt increase in CO2) for 21 successive generations, more AMF taxa were lost when CO2 was raised abruptly than when a gradual increase of the same magnitude was implemented.  The abrupt change in CO2 resulted in a significant change in mycorrhizal diversity in the first generation, although little change occurred in subsequent generations.  Species richness of AMF was similar in the gradual and ambient CO2 treatments but was significantly lower in the abrupt CO2 change treatment (Klironomos et al. 2005).  It is not known whether these effects would be similar in an intact field experiment where fungal meta-community dynamics may come into play and mediate any local species extinctions.  A comparable long-term 3-year experiment (Wu et al., unpublished data) investigating impacts of abrupt vs. gradual increases in CO2 on life-history traits of N. lugens feeding on rice over 16 successive generations, indicated that the gradual increase in CO2 treatment can promote the growth and physiological metabolism of N. lugens relative to the abrupt CO2 increase treatment.  So, the effects of abrupt and gradual CO2 change regimes on arthropods, plants and their associated organisms could differ because the changes affecting organisms are initially the greatest for the first subsequent generation in the abrupt regime, while the evolutionary responses of the interacting organisms differ between the two regimes.
Current generalizations about the effects of increasing atmospheric CO2 on arthropod–plant interactions are mainly based on experiments using the abrupt approach.  However, a major assumption of these approaches has not been tested, i.e., whether a single-step increase in CO2 yields similar responses in arthropod–plant systems as a gradual increase over several decades.  If a sudden increase in CO2 does not yield a response that is similar to a gradual increase of the same magnitude, some of these generalizations could be affected.  Hovenden and Newton (2018) considered that long-term experiments show unexpected plant responses to elevated CO2 concentrations.  Therefore, most current research may overestimate the impact of abrupt changes in CO2 concentrations on the arthropod–plant systems.  We must be cautious when designing experiments and explaining the effects of CO2 concentrations on the arthropod–plant system, because the magnitudes of responses to environmental changes that are significantly more abrupt may be different than those that would occur in nature.  Therefore, other model systems and intact ecosystems should be used to understand how an increase in atmospheric CO2 influences interactions between arthropods and their host plants.
Received: 15 October 2019   Accepted: 04 March 2020
Fund: This research was supported by the National Genetically Modified Organisms Breeding Major Project of China (2016ZX08012-005), the National Key R&D Program of China (2017YFD0200400), and the National Natural Science Foundation of China (31572003).
Corresponding Authors:  Correspondence WU Gang, Tel/Fax: +86-27-87282130, E-mail:    
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Cite this article: 

ZHENG Xiao-xu, WU Gang. 2020. How does the arthropod–plant system respond to abrupt and gradual increases in atmospheric CO2?. Journal of Integrative Agriculture, 19(4): 1159-1161.

Andresen L C, Yuan N M, Seibert R, Moser G, Kammann C I, Luterbacher J, Erbs M, Muller C. 2018. Biomass responses in a temperate European grassland through 17 years of elevated CO2. Global Change Biology, 24, 3875–3885.
Bezemer T M, Jones T H. 1998. Plant–insect herbivore interactions in elevated atmospheric CO2: Quantitative analysis and guild effects. Oikos, 82, 212–222.
Dong J L, Li X, Nazim G, Duan Z Q. 2018a. Interactive effects of elevated carbon dioxide and nitrogen availability on fruit quality of cucumber (Cucumis sativus L.). Journal of Integrative Agriculture, 17, 2438–2446.
Dong J L, Gruda N, Lam S K, Li X, Duan Z. 2018b. Effects of elevated CO2 on nutritional quality of vegetables - A review. Front Plant Science, 9, 924.
Foss A R, Mattson W J, Trier T M. 2013. Effects of elevated CO2 leaf diets on gypsy moth (Lepidoptera: Lymantriidae) respiration rates. Environmental Entomology, 42, 503–514.
Gao F, Zhu S R, Sun Y C, Du L, Parajulee M, Kang L, Ge F. 2008. Interactive effects of elevated CO2 and cotton cultivar on tri-trophic interaction of Gossypium hirsutum, Aphis gossyppii, and Propylaea japonica. Environmental Entomology, 37, 29–37.
Ge F, Chen F J, Wu G, Sun Y C. 2010. Response of Insects to Elevated Atmospheric CO2 Concentration. Science Press, Beijing. (in Chinese)
Guo H, Sun Y, Li Y, Tong B, Harris M, Zhu-Salzman K, Ge F. 2013. Pea aphid promotes amino acid metabolism both in Medicago truncatula and bacteriocytes to favor aphid population growth under elevated CO2. Global Change Biology, 19, 3210–3223.
Hovenden M, Newton P. 2018. Plant responses to CO2 are a question of time. Science, 360, 263–264.
IPCC (Intergovernmental Panel on Climate Change). 2018. Contribution of working group I to the sixth assessment report of the intergovernmental panel on climate change. [2019-09-10]. preparingreports/
Kim K, LabbeN, Warren J M, Elder T, Rials T G. 2015. Chemical and anatomical changes in Liquidambar styraciflua L. xylem after long term exposure to elevated CO2. Environmental Pollution, 198, 179–185.
Klironomos J N, Allen M F, Rillig M C, Piotrowski J, Nejad S M, Wolfe B E, Powell J R. 2005. Abrupt rise in atmospheric CO2 overestimates community response in a model plant–soil system. Nature, 433, 621–624.
Kurz W A, Dymond C C, Stinson G, Rampley G J, Neilson E T, Carroll L, Ebata T, Safranyik L. 2008. Mountain pine beetle and forest carbon feedback to climate change. Nature, 452, 987–990.
Liu J P, Huang W K, Wang C H, Hua H X, Wu G. 2017. Effect of elevated CO2 on the fitness and potential population damage of Helicoverpa armigera based on two-sex life table. Scientific Reports, 7, 1119.
Lüthi D, Le Floch M, Bereiter B, Blunier T, Barnola J M, Siegenthaler U, Raynaud D, Jouzel J, Fischer H, Kawamura K, Stocker T F. 2008. High-resolution carbon dioxide concentration record 650,000–800,000 years before present. Nature, 453, 379–382.
Reich P B, Hobbie S E, Lee T D, Pastore M A. 2018. Unexpected reversal of C3 versus C4 grass response to elevated CO2 during a 20-year field experiment. Science, 360, 317–320.
Robinson E A, Ryan G D, Newman J A. 2012. A meta-analytical review of the effects of elevated CO2 on plant-arthropod interactions highlights the importance of interacting environmental and biological variables. New Phytologist, 194, 321–336.
Sudderth E A, Stinson K A, Bazzaz F A. 2005. Host-specific aphid population responses to elevated CO2 and increased N availability. Global Change Biology, 11, 1997–2008.
Sun Y C, Guo H J, Yuan E Y, Ge F. 2018. Elevated CO2 increases R gene-dependent resistance of Medicago truncatula against the pea aphid by up-regulating a heat shock gene. New Phytologist, 217, 1697–1711.
Thomey M L, Slattery R A, Kohler I H, Bernacchi C J, Ort D R. 2019. Yield response of field-grown soybean exposed to heat waves under current and elevated CO2. Global Change Biology, 25, 4352–4368.
Wen D, Liu J P, Fan S, Zhang Z Y, Wu G. 2019. Evaluation on the fitness and population projection of Nilaparvata lugens in response to elevated CO2 using two-sex life table. International Journal of Pest Management,
doi: 10.1080/09670874.2019.1654146
Wu G. 2014. Study on the Response of Herbivorous Insects to the Ecological Environment. Hubei Science and Technology Press, China. (in Chinese)
Xu G L, Fu S L, Schleppi P, Li M H. 2013. Responses of soil Collembola to long-term atmospheric CO2 enrichment in a mature temperate forest. Environmental Pollution, 173, 23–28.
Yan H Y, Guo H G, Sun Y C, Ge F. 2020. Plant phenolics mediated bottom-up effects of elevated CO2 on Acyrthosiphon pisum and its parasitoid Aphidius avenae. Insect Science, 27, 170–184.
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