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ORIGINAL RESEARCH article

Front. Plant Sci., 08 June 2023
Sec. Plant Systematics and Evolution
This article is part of the Research Topic Plant Diversity Patterns and Drivers View all 33 articles

Geographic distribution of C4 species and its phylogenetic structure across China

Aiying Zhang*&#x;Aiying Zhang1*†Zhongjie YangZhongjie Yang1Yu ZuoYu Zuo1Liang MaLiang Ma2Hanyu ZhangHanyu Zhang1
  • 1College of Life Sciences, China Jiliang University, Hangzhou, China
  • 2Mineral Resources and Geological Survey Center, Shaanxi Institute of Geological Survey, Xi’an, China

Over the past fifty years, the distribution patterns of C4 species, across large spatial scales, are largely ignored. Here, we endeavored to examine patterns in the taxonomic and phylogenetic diversity of species with C4 photosynthetic pathways across the broad spatial extent of China and relate those to climatic gradients. We built a database of all plants with the C4 photosynthetic pathway in China. We analyzed the geographic distributions, taxonomic diversity, phylogenetic diversity, and phylogenetic structure of all C4 species, as well as the three families with the most C4 species (Poaceae, Amaranthaceae and Cyperaceae), and compared their values along temperature and precipitation gradients at two scales—the level of the province and at the 100 x 100 km grid cell. We found 644 C4 plants (belonging to 23 families 165 genera) in China, with Poaceae (57%), Amaranthaceae (17%), Cyperaceae (13%) accounting for the majority of species. Standardized effect size values of phylogenetic distances were negative overall, indicating that C4 species showed a phylogenetic clustering pattern. Southern China had the highest species richness and the highest degree of phylogenetic clustering. C4 tended to be more phylogenetically over-dispersed in regions with colder and/or drier climates, but more clustered in warmer and/or wetter climates. Patterns within individual families were more nuanced. The distribution of C4 species and its phylogenetic structure across China was constrained by temperature and precipitation. C4 species showed a phylogenetic clustering pattern across China, while different families showed more nuanced responses to climate variation, suggesting a role for evolutionary history.

1 Introduction

Although they represent a small percentage of vascular plant species on the earth (~0.005%) (Sieben et al., 2010), C4 plants have highly efficient photosynthesis and can play an important role in many ecosystems, such as during succession and recovery of degraded ecosystems (Wang, 2002a; Wang, 2002b). Moreover, the occurrences of C4 plants are good indicators of ecosystem variation because they tend to be more tolerant of stressful environments than C3 plants (Wang and Ma, 2016; Pardo and VanBuren, 2021; Zhang and Xie, 2021). Plants with C4 photosynthesis not only differ biochemically from species with other photosynthetic systems, but also in their evolutionary history and ecological interactions (Osborne et al., 2015; Sage, 2017). Therefore, exploring the patterns in the distribution of C4 plants and their phylogenetic relationships across large spatial scales provides basic biogeographic understanding of this important plant trait both ecologically and evolutionarily.

The geographic distribution of C4 plants also tends to be associated with different environmental conditions (Munson and Long, 2017). For example, C4 plants tend to be more prevalent and diverse in warmer tropical areas and are notably absent from cooler regions (Osborne et al., 2015). However, to date, most studies on the distribution and diversity of C4 plants have tended to focus only on relatively small geographic areas (Taylor et al., 2010), or have examined it only within a subset of the angiosperm phylogeny (e.g., in grasses) (Edwards and Still, 2008; Visser et al., 2012; Sonawane et al., 2021), while an exploration of patterns of species diversity, phylogenetic diversity and phylogenetic structure could provide insights into the interactions between ecological and evolutionary processes influencing the distribution and diversity of these species (Liu et al., 2012; Munroe et al., 2022).

By examining patterns of species richness of C4 plants, together with patterns of phylogenetic diversity (which incorporates evolutionary relationships) and patterns of phylogenetic structure (i.e., clustering of co-occurring species within the phylogeny), we can make progress in understanding the patterns, and potential processes influencing those patterns. For example, because C4 plants tend to have evolved in warmer, more tropical regions (Osborne et al., 2015), the tropical niche conservatism hypothesis (i.e., freezing-tolerance hypothesis) (Latham and Ricklefs, 1993; Wiens and Donoghue, 2004) may help to describe patterns of species richness if there is a strong latitudinal gradient in C4 species. Likewise, the phylogenetic structure of species assemblages, such as how clustered co-occurring species are within the phylogeny, can reflect their evolutionary history of adaptation and tolerance to environments (Qian et al., 2019). For example, the phylogenetic niche conservatism hypothesis predicts that closely related species have more similar niches and thus should share similar environmental conditions and geographic distributions (Pyron et al., 2015; Lu et al., 2018; Qian et al., 2022).

Here, we endeavored to more deeply understand the diversity, structure and distribution of species of species with C4 photosynthesis across broad geographic areas and among the entire angiosperm phylogeny, as well as within specific groups within angiosperms that had large numbers of C4 species. To do so, we took advantage of an extensive database of C4 species and their distributions from across China. China provides an important venue in which to examine patterns of diversity and structure within C4 species, because it is a geographically and climatically diverse country, ranging from cold temperate to tropical ecosystems, and from extremely wet rainforests to deserts, with a well-characterized flora. Using these data, we could examine patterns of the taxonomic (species) richness of C4 taxa and its relation to climatic variables. In addition, by combining species distribution and composition data with information on species phylogenies, we could examine patterns of phylogenetic diversity of species, as well as the phylogenetic structure (e.g., clustering) of co-occurring species within the phylogeny. Overall, we found that the distribution of C4 species richness, phylogenetic diversity phylogenetic structure across China was constrained by temperature and precipitation; C4 species showed a phylogenetic clustering pattern across China, while different families showed more nuanced responses to climate variation, suggesting a role for evolutionary history.

2 Materials and methods

2.1 Data compilation

We compiled a database of C4 plants in China from a number of published references (Supporting Information, Table S1). Specifically, we classified C4 species as such when their photosynthetic pathway was identified by stable carbon isotope ratios (10‰-15‰, Sage and Monson, 1999) and/or anatomy (Kranz anatomy, Osborne et al., 2015). When a species photosynthetic pathway was not known from stable carbon isotopes or anatomical type, we classified these unknown species as C4 species if we could find such information in other databases, and by assuming that all species within a genus should share the same photosynthetic pathway (Osborne et al., 2015) (though we recognize that this is a coarse approach and might misclassify some species). We standardized species names from published references according to the Flora of China (http://foc.iplant.cn/) and the World Flora Online (www.world.flora.online.org). We classified species into family based on the latest Angiosperm Phylogeny Group classification (The Angiosperm Phylogeny Group, 2016).

We obtained species distribution data within regions from the Flora of China (Table S1). Furthermore, we obtained occurrence records with coordinates (latitude and longitude) from multiple sources, including the Chinese Virtual Herbarium (https://www.cvh.ac.cn/), National Specimen Information Infrastructure (http://www.nsii.org.cn/2017/home.php) and the Global Biodiversity Information Facility (https://www.gbif.org/). We then integrated these species distribution data so that we could estimate patterns of diversity and co-occurrence of species at two scales—the province level and at the level of 100 km x 100 km grid cells. For the province level, we divided China into 29 provinces, by combing Beijing and Tianjin within the Hebei Province, Hong Kong and Macau within the Guangdong province, and Shanghai within the Jiangsu Province.

In order to compare patterns of C4 diversity and phylogenetic structure with climate variables, we extracted climate data from the WorldClim database (http://www.worldclim.com/version2). Specifically, we extracted annual mean temperature (hereafter temperature) and annual mean precipitation (hereafter precipitation), which are known to be the most important bioclimatic variables driving plant species distributions in China (Qian et al., 2022). We used ArcGIS 10.8 to extract the variables from each province and grid cell.

2.2 Indices of species richness and phylogenetic structure

For each index of diversity or structure, we calculated the value for the entire group of C4 species, as well as separately for C4 species in the three families that accounted for 87% of all C4 species—Poaceae, Amaranthaceae and Cyperaceae (Figure S1). We calculated species richness as the total number of species that co-occur within a given province or grid cell. In order to calculate patterns of phylogenetic diversity and structure, we first built a phylogenetic tree of all C4 species in our database, using the R package ‘V.PhyloMaker2’ (Jin and Qian, 2022). With this phylogeny in hand, we calculated three indices of phylogenetic structure. First, we calculated Faith’s phylogenetic diversity (PD), which calculates the sum of total phylogenetic branch lengths of species in an assemblage (Faith, 1992). Second, we calculated the mean pairwise phylogenetic distances (MPD) between all possible pairs of species in an assemblage, which quantifies overall clustering of taxa on a tree (Webb et al., 2002). Third, we calculated the mean phylogenetic distance to the nearest taxon (MNTD) for each taxon in an assemblage, which quantifies the extent of terminal clustering, independent of deep level clustering (Webb et al., 2002; Qian et al., 2019). For each phylogenetic index, we calculated its standardized effect size (SES) to quantify the degree to which phylogenetic diversity and phylogenetic relatedness between species differed from what would have been expected if species were randomly distributed across the geographical extent. The SES was calculated as X = (Xobserved-meanXrandomized)/(sdXrandomized), where Xobserved represents the observed PD, MPD and MNTD values in a species assemblage, while meanXrandomized and sdXrandomized represent the expected mean and standard deviation of the species from the randomized assemblages (Webb et al., 2002). We ran each null randomization 999 times with a fixed species richness. Higher values of the standardized effect size of phylogenetic diversity (SES.PD) indicate a higher phylogenetic diversity (Qian et al., 2019). For the standardized effect size of the mean phylogenetic distance (SES.MPD), negative values indicate that the observed MPD values were lower than randomized ones and that species are more closely related than expected from the entire species pool (i.e., species are phylogenetically clustered). Conversely, positive SES.MPD values indicate that species are phylogenetically over-dispersed. Likewise, negative values of the standardized effect size of the mean phylogenetic distance to the nearest taxon (SES.MNTD) indicate clustering within the terminal part of the phylogenetic tree, while positive values indicate overdispersion. All phylogenetic indices and their SES were calculated using the R package ‘picante’ (Kembel et al., 2010).

2.3 Statistical analysis

At both the level of the province and the grid level, we used Spearman’s rank correlation analysis to test the relationship between species richness, the indices of phylogenetic structure, and the two bioclimatic variables (temperature and precipitation). We also calculated phylogenetic differences (MPD and MNTD) between regions using the R package ‘picante’ with the function comdist and comdistnt (Kembel et al., 2010), which we visualized using Principal Coordinate Analysis (PCoA).

All statistical analyses and figure construction were conducted in R 4.2.0 (R Core Team, 2022).

3 Results

3.1 Overview of the C4 dataset

Overall, we identified 644 C4 vascular plant species (belonging to 23 families 165 genera, Table S1; Figure S1) distributed in China, including 371 where species were directly measured to be C4, and 273 of which we inferred to be C4 based on the literature or their congeners. The Poaceae accounted for more than half of all C4 species (57%), with 17% of C4 species in the Amaranthaceae and 13% in the Cyperaceae in the third (13%); the remaining 13% of species were spread among 20 other families. Most C4 plants were perennial (50%) and annual (42%) non-woody (herbaceous) species, while 9% of species were shrubs (Figure S2A). Finally, there were 65 (~10%) C4 species that were non-native to China, half of which were classified as invasive species (Figure S2B).

The distribution of C4 species was skewed across China, with most species occurring in the south: Yunnan and Guangdong provinces had more than 50% of all C4 species, while 40% were in Guangxi, Fujian, Taiwan, Hainan and Sichuan (Figure 1). There were 99 C4 species that were endemic to only one province, more than half of which were in Xinjiang (61%) (including 35 species in the Amaranthaceae) (Figure S3).

FIGURE 1
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Figure 1 Geographic patterns of species richness (SR) and the standardized effect size values of phylogenetic structure indices (SES.PD, SES.MPD and SES.MNTD) for C4 plants across the 29 Chinese provinces. Panels represent different metrics (columns) and different taxonomic groupings (all C4 species, Poaceae, Amaranthaceae and Cyperaceae). The map of China is incomplete, which only includes mainland, Taiwan Island and Hainan Island.

3.2 Distribution patterns of species richness and phylogenetic structure

Overall, we found that both species richness and PD varied greatly across China for all species, as well as the three most common families, across the 29 provinces, while MPD and MNTD varied less (Table S2). Among the different families, the C4 species in the Amaranthacea had the highest Coefficient of Variation (CV) for species richness (71.4%), PD (55.4%) and MPD (19.9%) among the provinces. The C4 species in the Cyperaceae had the highest CV for MNTD (74.3%).

We found that species richness was highest in the south for all C4 species (Figure 1A), as well as those in the Poaceae (Figure 1E) and Cyperaceae (Figure 1M). Meanwhile, the highest richness of C4 species in the Amaranthaceae species was in the northwestern part of China (Figure 1I). The regions with the highest PD and SES.PD for all C4 species (Figure 1B), as well as those in the Poaceae (Figure 1F), were in northern China. For C4 species in the Amaranthaceae, the highest SES.PD was located in the northwestern, southwestern and southeastern China (Figure 1J), while northwestern China had the highest SES.PD for C4 species in the Cyperaceae (Figure 1N).

For patterns of phylogenetic structure, we found that northeastern China had the highest positive SES.MPD and SES.MNTD (Figures 1C, G, K), as well as the lowest negative SES.MPD and SES.MNTD (Figures 1L, O, P), indicating that this region had the highest phylogenetic overdispersion. Meanwhile, northwestern China had the highest positive SES.MPD and SES.MNTD (Figures 1C, G), as well as the highest negative SES.MPD and SES.MNTD), consistent with the highest phylogenetic overdispersion (and lowest clustering). Southern China had the lowest negative SES.MPD and SES.MNTD (Figures 1C, D, G, K), indicated that it had the highest phylogenetic clustering.

We found that the mean values of SES.PD, SES.MPD and SES.MNTD of all C4 species were significantly less than zero at both the province and grid level (Figures 2A, B), indicating that C4 plants were phylogenetically clustered. The same was true when we analyzed each of the most common families separately, except for the SES.MPD of the C4 species in the Cyperaceae at the province level (Figures 2A, B).

FIGURE 2
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Figure 2 Variation in the standardized effect size values of phylogenetic structure indices at the province level (left column) and grid level (right colum). Values of significant differences from zero are shown by three asterisks (P < 0.001), two asterisks (0.001< P < 0.01), one asterisk (0.01< P < 0.05) and NS (P > 0.05).

3.3 Relationships between species richness, phylogenetic structure and bioclimatic variables

We found significant positive relationships between the all C4 species richness, as well as both the Poaceae and Cyperacae, and both temperature and precipitation at the province and grid level (Figures 3A–D). The species richness of C4 species in the Amaranthaceae had a negative relationship with precipitation at both the province and grid level, but with non-consistent relationships with temperate at the province level and grid level (Figures 3A–D). On the other hand, the SES.PD of all C4 species and the C4 species in the Poaceae had a significant negative relationship with temperature and precipitation at both the province and grid level (Figures 3E–H), as did the SES.PD of the C4 species in the Amaranthaceae had a significant negative relationship at the grid level (but not province level) and the C4 species in the Cyperaceae had a significant positive relationship at the grid level (but not province level) (Figures 3E–H). Patterns of SES.MPD were similar to those of SES.PD (Figures 3I–L). For SES.MNTD, we found that all C4 species decreased a significant negative relationship with temperature and precipitation at both the province and grid level and the C4 species of the Cyperaceae had no significant relationship with temperature and precipitation (Figures 3M–P).

FIGURE 3
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Figure 3 Relationships of species richness and SES values of phylogenetic structure indices (SES.PD, SES.MPD, and SES.MNTD) with temperature and precipitation, calculated by Spearman’s rank correlation. R is correlation coefficient, p indicates significance.

Finally, we found that the PCoA showed that phylogenetic distance (MNTD and MPD) between regions with high temperature (and/or lower precipitation) were smaller, and thus more phylogenetically similar (Figures 4A–P; S4–S6).

FIGURE 4
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Figure 4 Relative phylogenetic differences (MNTD) among the regions [province level (A–H) and grid level (I–P)], visualized using a PCoA ordination biplot, calculated using the Gower distance. The color of dots varied from green to red, meaning the Temperature/Precipitation increased from low to high. Similar results of MPD (whose first two axes explained much lower variance than MNTD) were showed in Figure S4.

4 Discussion

Overall, our study showed that there is considerable, but important, variation in the distribution, diversity and phylogenetic structure of plants with C4 photosynthesis across the broad geographical (and climatic) extent of China. More specifically, we found that C4 species accounted for about 2% of all angiosperms in China (644 C4 species out of 29716-30260 total angiosperm species, Wang et al., 2015; Qian et al., 2022). Furthermore, the C4 photosynthetic pathway was most prevalent among species in the Poaceae. About half of all Poaceae species are C4 (Osborne et al., 2015), and our study, like others (Sage and Monson, 1999), found that Poaceae with C4 photosynthesis accounted for about half of all C4 species.

Our main result was that C4 species had higher species richness in regions with warmer and/or wetter climates. This pattern also holds when we examined patterns of the C4 species within the Poaceae and Cyperaceae. This is consistent with ideas related to the tropical niche conservatism hypothesis (Wiens and Donoghue, 2004) and is also mirrored by patterns in the distribution of woody and seed plants in China (Wang et al., 2011; Qian et al., 2019). C4 species in the Amaranthaceae, however, had a higher species richness in northwestern China in regions with drier climates (see also Wang and Ma, 2016; Rudov et al., 2020; Munroe et al., 2022). This suggests that the evolutionary history of C4 species within the Amaranthaceae likely differs from the other families with C4 photosynthesis.

While we found that C4 species in the Cyperaceae were more phylogenetically clustered in regions with colder and/or drier climates, consistent with previous studies in China (Lu et al., 2018; Qian et al., 2019) and North America (Qian and Sandel, 2017), this pattern did not hold for the other groups. Instead, we found that all C4 species (as well as those within the Poaceae and Amaranthaceae) tended to be more phylogenetically over-dispersed in regions with colder and/or drier climates, but more clustered in warmer and/or wetter climates.

These results are also consistent with the phylogenetic niche conservatism hypothesis (Qian et al., 2019), where all C4 species in the warmer and wetter climates of southern China had the highest species richness, but relatively lower phylogenetic diversity and the higher phylogenetic clustering, suggesting that species here were highly closely related. However, patterns differed for the C4 species in the Amaranthaceae, where drier climates of the northwestern parts of China had the highest species richness and phylogenetic diversity, as well as low phylogenetic clustering, suggesting these species were relatively distantly related. On the other hand, C4 species in the Cyperaceae had lower species richness, highest phylogenetic diversity and high phylogenetic overdispersion in the colder climates of the northwest, indicating these species were relatively distantly related. Overall, this suggests that C4 species in different families respond different to geographic gradients, likely as a result of their different evolutionary histories (Munroe et al., 2022).

We should emphasize, however, that while ours is the most comprehensive analysis of the distribution and diversity of C4 species in China, there are still some improvements that can be made. For example, in our database, there are 273 species whose stable carbon isotope value or anatomical type were not given, but rather inferred based on other databases and the assumption that all species within one genus should share the same photosynthetic pathway (Osborne et al., 2015). However, it is possible that taxonomic changes could influence this assumption. For instance, species in the Potamogeton genus were identified with C4 photosynthetic pathway, except for Potamogeton pectinatus (Table S1), which was identified as a synonym of Stuckenia pectinata. Likewise, several genera within the Amaranthaceae family were formerly classified in the Chenopodiaceae (Alternanthera, Atriplex, Axyris, Bassia, Suaeda and Salsola) (Table S1), which could have influenced their classification. This suggests that there remains work to be done on the taxonomy of Amaranthaceae. There are also some genera in other families, such as Cyperus and Panicum, whose taxonomy is controversial (Table S1) and do not share the same photosynthetic pathway. Indeed, the photosynthetic pathway might be a good tool to explore species evolutionary history and taxonomy.

In all, our study, by identifying key patterns in the diversity and phylogenetic structure of C4 species across regions in China, provides an important advance in our understanding of their distributions. This provides basic information on consistent (across all taxa) and nuanced (different patterns within some families) patterns of diversity and phylogenetic clustering patterns in response to major climate gradients. Furthermore, understanding these patterns of distribution can provide an important foundation for the use of C4 species in restoration practices in degraded ecosystems.

Data availability statement

The original contributions presented in the study are included in the article/Supplementary Material. Further inquiries can be directed to the corresponding author.

Author contributions

AZ conceived the study. AZ, ZY, YZ, LM and HZ collected the data. AZ and LM analyzed the data. AZ wrote the manuscript. ZY, YZ, LM and HZ commented the manuscript. All authors gave final approval for publication. All authors contributed to the article.

Funding

This work was financially supported by the National Natural Science Foundation of China (grant no. 31901211) and the Zhejiang Provincial Natural Science Foundation of China (LY21C030006).

Acknowledgments

We are grateful for Shenhao Yao at Zhejiang Museum of Natural History for assistance with species classification. We are grateful to the reviewers for the valuable comments, English language and grammatical editing that contributed to improve the manuscript.

Conflict of interest

The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.

Publisher’s note

All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors and the reviewers. Any product that may be evaluated in this article, or claim that may be made by its manufacturer, is not guaranteed or endorsed by the publisher.

Supplementary material

The Supplementary Material for this article can be found online at: https://www.frontiersin.org/articles/10.3389/fpls.2023.1214980/full#supplementary-material

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Keywords: clustering, niche conservatism, phylogenetic distance, phylogenetic diversity, Poaceae, standardized effect size

Citation: Zhang A, Yang Z, Zuo Y, Ma L and Zhang H (2023) Geographic distribution of C4 species and its phylogenetic structure across China. Front. Plant Sci. 14:1214980. doi: 10.3389/fpls.2023.1214980

Received: 01 May 2023; Accepted: 24 May 2023;
Published: 08 June 2023.

Edited by:

Jinliang Liu, Wenzhou University, China

Reviewed by:

Lei Su, Henan University, China
Zhaojia Li, Chinese Academy of Forestry, China

Copyright © 2023 Zhang, Yang, Zuo, Ma and Zhang. This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY). The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner(s) are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.

*Correspondence: Aiying Zhang, ayzhang@foxmail.com

ORCID: Aiying Zhang, orcid.org/0000-0002-1343-7899

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