Growth overcompensation against O3 exposure in two Japanese oak species, Quercus mongolica var. crispula and Quercus serrata, grown under elevated CO2
Introduction
Tropospheric ozone (O3) levels have increased globally since preindustrial times (Stockwell et al., 1997, IPCC., 2001, IPCC., 2007) and continue to rise, particularly in the region of East Asia (Fowler et al., 1999, Fowler et al., 2008, Vingarzan, 2004, Ashmore, 2005, Dentener et al., 2006). Increased O3 levels have the potential of limiting the carbon sink strength of forest ecosystems (IPCC., 2007, Sitch et al., 2007, Wittig et al., 2009, Pretzsch et al., 2010) because of reduced net photosynthesis, accelerated leaf senescence, and increased dark respiration (for review see Matyssek and Sandermann, 2003, Matyssek et al., 2010). Atmospheric carbon dioxide (CO2) concentration is predicted to double during the next century (IPCC., 2001, IPCC., 2007). Elevated CO2 has been linked to increased plant growth via enhanced photosynthetic carbon assimilation (Tissue et al., 1997, Ainsworth and Long, 2005, Norby and Zak, 2011), although long-term exposure to elevated CO2 results in photosynthetic downregulation, typically a decrease in the carboxylation capacity of Rubisco (Vc,max) (Rogers and Ellsworth, 2002, Ainsworth and Long, 2005, Bernacchi et al., 2005).
Quercus mongolica var. crispula (Japanese oak) and Quercus serrata (konara oak) are representative deciduous broadleaf tree species found in Japan and throughout East Asia (Menitsky, 2005). The former is mainly distributed in the cool-temperate and the latter in the warm-temperate zone of deciduous broadleaf forests in East Asia. Both species have a high sprouting ability with well-developed tap roots as they are commonly used for coppicing in secondary forests in Japan (Sakai et al., 1997, Sakai and Sakai, 1998). Both have mid-successional traits, i.e., moderately shade-tolerant and need a gap formation for regeneration (Higo, 1994). Their shoot development pattern is categorized as a flush and succeeding-type leaf emergence (Kikuzawa, 1983); they flush shoots generally once in spring, sometimes flushing new shoots if environmental conditions are preferable, such as gap formation. According to Yamaguchi et al. (2011), both the oak species are relatively O3 tolerant among the Japanese tree species and are related to a noted capacity for isoprene emission (Loreto and Fares, 2007, Tani and Kawawata, 2008, Miyama et al., 2013). Although there have been several studies primarily investigating the effects of elevated CO2 and/or O3 on leaf physiological and morphological traits in oak species (e.g., Velikova et al., 2005, Paoletti et al., 2007, Watanabe et al., 2007, Watanabe et al., 2013), only a few studies have investigated the combined effects of elevated CO2 and O3 on the growth and carbon allocation in oak species (Quercus petraea, Broadmeadow and Jackson, 2000; cf. King et al., 2013). A thorough assessment of the effects of elevated O3 and CO2 on the growth of these oak species (Q. mongolica and Q. serrata) is necessary to predict the effects of global change on the carbon sequestering capacity of forest ecosystems, particularly in East Asia.
Plant growth is mainly regulated by two factors: leaf area-based carbon assimilation rate and leaf area ratio (Poorter, 1989). The former is involved in photosynthetic capacity and the latter in photosynthate allocation. O3 exposure is known to shift carbon allocation preferably into shoots (Pell et al., 1994, Selldén et al., 1997, Landolt et al., 2000, Oksanen and Rousi, 2001), which may promote plant growth in response to the O3-induced reduction in photosynthesis (Mooney et al., 1988, Pell et al., 1994, Yamaji et al., 2003). Conversely, carbon allocation in plants grown under elevated CO2 is reported to be relatively unresponsive when compared with that in plants under the effects of O3, which are dependent on species, resource supply, and environmental factors (Rogers et al., 1996, Poorter and Nagel, 2000). In previous studies, the root to shoot ratio of Japanese white birch seedlings was considerably changed according to water and nitrogen availability, whereas no significant response was triggered by elevated CO2 (Kitao et al., 2005, Kitao et al., 2007).
Elevated CO2 concentration may alleviate the toxicological impacts of elevated O3 if elevated CO2 level is accompanied by lower stomatal conductance (Ainsworth and Long, 2005, Ainsworth and Rogers, 2007) or by a greater quantity of carbohydrates available for detoxification and repair in elevated CO2 (Riikonen et al., 2004, Riikonen et al., 2005). If greater carbon allocation into shoots directly induced by O3 occurs as a defense mechanism (Kangasjärvi et al., 1994, Pell et al., 1994), the impact of O3 is alleviated and photosynthesis is enhanced under elevated CO2, particularly in the Quercus species that are generally less sensitive to the damaging effects of O3; this may ultimately increase plant growth as an overcompensation.
We hypothesized that the growth of the two O3-tolerant oak species (Q. mongolica var. crispula and Q. serrata) native to East Asia with a plastic shoot developmental pattern (Kikuzawa, 1983) was enhanced when grown under elevated O3 and CO2 through an O3-induced carbon allocation into shoots and CO2-enhanced photosynthesis exceeding O3 impacts. Furthermore, as a greater cumulative O3 uptake via higher stomatal conductance was observed in Q. mongolica than in Q. serrata (Kinose et al., 2014), O3 impact on photosynthesis would be greater in the former species leading to a less enhancement in the growth. To test this hypothesis, we investigated the growth and photosynthetic responses in the seedlings of Q. mongolica and Q. serrata grown under free-air fumigation of elevated O3 and CO2.
Section snippets
Plant materials, and carbon dioxide and ozone exposure
The experimental field is located at the nursery of Forestry and Forest Products Research Institute in Tsukuba, Japan (36°00′N, 140°08′E, 20 m a.s.l.). Twelve frames were installed for CO2 and O3 exposure. One-year-old seedlings of Japanese oak (Q. mongolica Fisch. ex Ledeb. var. crispula (Blume) H. Ohashi) and Konara oak (Q. serrata Murray) approximately 5 cm in height under dormancy were transplanted directly to the ground in the frames at the end of March in 2012. Before transplanting, the
Growth responses to elevated CO2 and O3 in Q. mongolica and Q. serrata
In the present study, it is noteworthy that root growth was not limited to direct planting into the soils, allowing oak seedlings to grow roots up to 1.5 m in depth and 2.0 m in width after two growth seasons. A significant increase in total biomass was observed only in the seedlings of Q. mongolica grown under elevated CO2 and O3, whereas total biomass of the seedlings of Q. serrata was enhanced both by CO2 and O3 treatments (Fig. 2, Table 2, Table 3). Root biomass was not significantly
Discussion
Generally, elevated CO2 would increase the total biomass of trees via enhanced photosynthesis (Tissue et al., 1997, Ainsworth and Long, 2005, Ainsworth and Rogers, 2007, Norby and Zak, 2011), whereas elevated O3 may decrease tree growth because of reduced photosynthesis (Matyssek and Sandermann, 2003, Matyssek et al., 2010, Pretzsch et al., 2010, Kitao et al., 2009, Kitao et al., 2012). Earlier studies showed that growth enhancement by elevated CO2 was consistently negated by elevated O3 in
Acknowledgments
We thank Dr. Morikawa for his valuable suggestions concerning the present study. This work was supported in part by the project on “Technology development for circulatory food production systems responsive to climate change” conducted by the Ministry of Agriculture, Forestry and Fisheries, Japan, the Grant-in-Aid for Scientific Research (B) (No. 25292092) and the Grant-in-Aid for Scientific Research on Innovative Areas (No. 22114514).
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