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<journal-meta>
<journal-id journal-id-type="publisher-id">Front. Ecol. Evol.</journal-id>
<journal-title>Frontiers in Ecology and Evolution</journal-title>
<abbrev-journal-title abbrev-type="pubmed">Front. Ecol. Evol.</abbrev-journal-title>
<issn pub-type="epub">2296-701X</issn>
<publisher>
<publisher-name>Frontiers Media S.A.</publisher-name>
</publisher>
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<article-meta>
<article-id pub-id-type="doi">10.3389/fevo.2023.1115784</article-id>
<article-categories>
<subj-group subj-group-type="heading">
<subject>Ecology and Evolution</subject>
<subj-group>
<subject>Systematic Review</subject>
</subj-group>
</subj-group>
</article-categories>
<title-group>
<article-title>Exploring spatio-temporal patterns of palynological changes in Asia during the Holocene</article-title>
</title-group>
<contrib-group>
<contrib contrib-type="author" corresp="yes">
<name><surname>Bhatta</surname> <given-names>Kuber P.</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
<xref ref-type="corresp" rid="c001"><sup>&#x002A;</sup></xref>
<xref ref-type="author-notes" rid="fn003"><sup>&#x2020;</sup></xref>
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</contrib>
<contrib contrib-type="author">
<name><surname>Mottl</surname> <given-names>Ond&#x0159;ej</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
<xref ref-type="aff" rid="aff2"><sup>2</sup></xref>
<xref ref-type="author-notes" rid="fn003"><sup>&#x2020;</sup></xref>
<uri xlink:href="http://loop.frontiersin.org/people/2130786/overview"/>
</contrib>
<contrib contrib-type="author">
<name><surname>Felde</surname> <given-names>Vivian A.</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
<xref ref-type="aff" rid="aff2"><sup>2</sup></xref>
<xref ref-type="author-notes" rid="fn003"><sup>&#x2020;</sup></xref>
</contrib>
<contrib contrib-type="author">
<name><surname>Flantua</surname> <given-names>Suzette G. A.</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
<xref ref-type="aff" rid="aff2"><sup>2</sup></xref>
<xref ref-type="author-notes" rid="fn003"><sup>&#x2020;</sup></xref>
</contrib>
<contrib contrib-type="author">
<name><surname>Birks</surname> <given-names>Hilary H.</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
<xref ref-type="aff" rid="aff2"><sup>2</sup></xref>
<xref ref-type="author-notes" rid="fn003"><sup>&#x2020;</sup></xref>
<uri xlink:href="http://loop.frontiersin.org/people/347816/overview"/>
</contrib>
<contrib contrib-type="author">
<name><surname>Cao</surname> <given-names>Xianyong</given-names></name>
<xref ref-type="aff" rid="aff3"><sup>3</sup></xref>
<xref ref-type="author-notes" rid="fn003"><sup>&#x2020;</sup></xref>
<uri xlink:href="http://loop.frontiersin.org/people/1097653/overview"/>
</contrib>
<contrib contrib-type="author">
<name><surname>Chen</surname> <given-names>Fahu</given-names></name>
<xref ref-type="aff" rid="aff3"><sup>3</sup></xref>
<xref ref-type="author-notes" rid="fn003"><sup>&#x2020;</sup></xref>
<uri xlink:href="http://loop.frontiersin.org/people/1466045/overview"/>
</contrib>
<contrib contrib-type="author">
<name><surname>Grytnes</surname> <given-names>John-Arvid</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
<xref ref-type="author-notes" rid="fn003"><sup>&#x2020;</sup></xref>
<uri xlink:href="http://loop.frontiersin.org/people/2016210/overview"/>
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<contrib contrib-type="author">
<name><surname>Seddon</surname> <given-names>Alistair W. R.</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
<xref ref-type="aff" rid="aff2"><sup>2</sup></xref>
<xref ref-type="author-notes" rid="fn003"><sup>&#x2020;</sup></xref>
</contrib>
<contrib contrib-type="author">
<name><surname>Birks</surname> <given-names>Harry John B.</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
<xref ref-type="aff" rid="aff2"><sup>2</sup></xref>
<xref ref-type="aff" rid="aff4"><sup>4</sup></xref>
<xref ref-type="author-notes" rid="fn003"><sup>&#x2020;</sup></xref>
</contrib>
</contrib-group>
<aff id="aff1"><sup>1</sup><institution>Department of Biological Sciences, University of Bergen</institution>, <addr-line>Bergen</addr-line>, <country>Norway</country></aff>
<aff id="aff2"><sup>2</sup><institution>Bjerknes Centre for Climate Research</institution>, <addr-line>Bergen</addr-line>, <country>Norway</country></aff>
<aff id="aff3"><sup>3</sup><institution>Alpine Paleoecology and Human Adaptation Group (ALPHA), State Key Laboratory of Tibetan Plateau Earth System, Environment and Resources (TPESER), Institute of Tibetan Plateau Research, Chinese Academy of Sciences</institution>, <addr-line>Beijing</addr-line>, <country>China</country></aff>
<aff id="aff4"><sup>4</sup><institution>Environmental Change Research Centre, University College London</institution>, <addr-line>London</addr-line>, <country>United Kingdom</country></aff>
<author-notes>
<fn fn-type="edited-by"><p>Edited by: Anna Maria Mercuri, University of Modena and Reggio Emilia, Italy</p></fn>
<fn fn-type="edited-by"><p>Reviewed by: Anneli Poska, Lund University, Sweden; Dafna Langgut, Tel Aviv University, Israel</p></fn>
<corresp id="c001">&#x002A;Correspondence: Kuber P. Bhatta, <email>kuber.bhatta@uib.no</email></corresp>
<fn fn-type="other" id="fn003"><p><sup>&#x2020;</sup>ORCID: Kuber P. Bhatta, <ext-link ext-link-type="uri" xlink:href="https://orcid.org/0000-0001-7837-1395">orcid.org/0000-0001-7837-1395</ext-link>; Ond&#x0159;ej Mottl, <ext-link ext-link-type="uri" xlink:href="https://orcid.org/0000-0002-9796-5081">orcid.org/0000-0002-9796-5081</ext-link>; Vivian A. Felde, <ext-link ext-link-type="uri" xlink:href="https://orcid.org/0000-0002-2855-0894">orcid.org/0000-0002-2855-0894</ext-link>; Suzette G. A. Flantua, <ext-link ext-link-type="uri" xlink:href="https://orcid.org/0000-0001-6526-3037">orcid.org/0000-0001-6526-3037</ext-link>; Hilary H. Birks, <ext-link ext-link-type="uri" xlink:href="https://orcid.org/0000-0001-6881-9133">orcid.org/0000-0001-6881-9133</ext-link>; Xianyong Cao, <ext-link ext-link-type="uri" xlink:href="https://orcid.org/0000-0001-5633-2256">orcid.org/0000-0001-5633-2256</ext-link>; Fahu Chen, <ext-link ext-link-type="uri" xlink:href="https://orcid.org/0000-0002-8874-1035">orcid.org/0000-0002-8874-1035</ext-link>; John-Arvid Grytnes, <ext-link ext-link-type="uri" xlink:href="https://orcid.org/0000-0002-6365-9676">orcid.org/0000-0002-6365-9676</ext-link>; Alistair W. R. Seddon, <ext-link ext-link-type="uri" xlink:href="https://orcid.org/0000-0002-8266-0947">orcid.org/0000-0002-8266-0947</ext-link>; Harry John B. Birks, <ext-link ext-link-type="uri" xlink:href="https://orcid.org/0000-0002-5891-9859">orcid.org/0000-0002-5891-9859</ext-link></p></fn>
</author-notes>
<pub-date pub-type="epub">
<day>05</day>
<month>05</month>
<year>2023</year>
</pub-date>
<pub-date pub-type="collection">
<year>2023</year>
</pub-date>
<volume>11</volume>
<elocation-id>1115784</elocation-id>
<history>
<date date-type="received">
<day>04</day>
<month>12</month>
<year>2022</year>
</date>
<date date-type="accepted">
<day>03</day>
<month>04</month>
<year>2023</year>
</date>
</history>
<permissions>
<copyright-statement>Copyright &#x00A9; 2023 Bhatta, Mottl, Felde, Flantua, Birks, Cao, Chen, Grytnes, Seddon and Birks.</copyright-statement>
<copyright-year>2023</copyright-year>
<copyright-holder>Bhatta, Mottl, Felde, Flantua, Birks, Cao, Chen, Grytnes, Seddon and Birks</copyright-holder>
<license xlink:href="http://creativecommons.org/licenses/by/4.0/"><p>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.</p></license>
</permissions>
<abstract>
<p>Historical legacies influence present-day ecosystem composition and dynamics. It is therefore important to understand the long-term dynamics of ecosystems and their properties. Analysis of ecosystem properties during the Holocene using fossil pollen assemblages provides valuable insights into past ecosystem dynamics by summarising so-called pollen-assemblage properties (PAPs). Using 205 fossil pollen data-sets (records), we quantify eight PAPs [pollen-taxonomic richness, diversity, evenness, pollen-compositional turnover, pollen-compositional change, and rate of pollen-compositional change (RoC)] for the Asian continent at different spatial scales (in individual records, within and across climate-zones, and within the continent) and time (temporal patterns over the past 12,000 years). Regression tree (RT) partitioning of the PAP-estimates using sample-age as a sole predictor revealed the &#x201C;change-point(s)&#x201D; (time or sample-age of major change in a PAP). We estimated the density of RT and multivariate regression tree (MRT) change-points in 1,000-year time bins during the Holocene. Pollen-compositional turnover (range of sample scores along the first DCCA axis) and change (number of MRT partitions) in each record reveal gradual spatial variation across latitude and a decline with longitude eastward. Temporally, compositional turnover declines linearly throughout the Holocene at all spatial scales. Other PAPs are heterogeneous across and within spatial scales, being more detectable at coarser scales. RT and MRT change-point density is broadly consistent in climate-zones and the continent, increasing from the early- to mid-Holocene, and mostly decrease from the mid-Holocene to the present for all PAPs. The heterogenous patterns in PAPs across the scales of study most likely reflect responses to variations in regional environmental conditions, anthropogenic land-use, and their interactions over space and time. Patterns at the climate-zone and continental scales indicate a gradual but congruent decline in major PAPs such as compositional turnover, rate of compositional change, and major temporal compositional changes (MRT) during the Holocene, especially during recent millennia, suggesting that vegetation in Asia has become progressively more homogenous. Data properties (e.g., spatial distribution of the records, distribution of samples within the records, and data-standardisation and analytical approaches) may also have partly influenced the results. It is critically important to evaluate the data properties and the approaches to data standardisation and summarisation.</p>
</abstract>
<kwd-group>
<kwd>climate change</kwd>
<kwd>pollen-compositional turnover</kwd>
<kwd>detrended canonical correspondence analysis (DCCA)</kwd>
<kwd>Hill indices</kwd>
<kwd>land-use change</kwd>
<kwd>multivariate regression tree (MRT)</kwd>
<kwd>pollen-assemblage property (PAP)</kwd>
<kwd>past vegetation dynamics</kwd>
</kwd-group>
<contract-sponsor id="cn001">H2020 European Research Council<named-content content-type="fundref-id">10.13039/100010663</named-content></contract-sponsor>
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<ref-count count="135"/>
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<custom-meta-wrap>
<custom-meta>
<meta-name>section-at-acceptance</meta-name>
<meta-value>Paleoecology</meta-value>
</custom-meta>
</custom-meta-wrap>
</article-meta>
</front>
<body>
<sec id="S1" sec-type="intro">
<title>Introduction</title>
<p>The Holocene (ca. the last 11,700 years) was previously thought to be an environmentally stable period compared to the last glacial period. However, a growing amount of evidence, from both terrestrial and marine sediments, suggests that there have been marked environmental variations throughout the Holocene. Most transformations of natural ecosystems throughout the globe started with human activities during the early- to mid- Holocene (e.g., <xref ref-type="bibr" rid="B45">Fuller et al., 2011</xref>; <xref ref-type="bibr" rid="B46">Fyfe et al., 2015</xref>; <xref ref-type="bibr" rid="B90">Pennisi, 2015</xref>; <xref ref-type="bibr" rid="B86">Nolan et al., 2018</xref>; <xref ref-type="bibr" rid="B68">Kune&#x0161; et al., 2019</xref>; <xref ref-type="bibr" rid="B107">Stephens et al., 2019</xref>; <xref ref-type="bibr" rid="B39">Ellis et al., 2021</xref>). A broad-scale study (<xref ref-type="bibr" rid="B81">Lyons et al., 2016</xref>) suggests that basic species-assemblage patterns remained relatively consistent for many millions of years, but then changed significantly in the mid-Holocene as a result of a dramatic increase in anthropogenic impacts. To test the ideas of changes in species-assemblage properties and to understand the long-term dynamics of ecosystems, ecosystem properties must be defined and studied through the entire Holocene. Major ecosystem properties such as taxonomic diversity, composition, and rate of change should be explored across space as well as time as the patterns may vary depending on the scale of the study. Such studies are important in the management of natural ecosystems and landscapes in the context of ever-increasing anthropogenic pressure because historical ecological legacies, such as land-use changes and disturbances, can play a significant role in influencing present-day ecosystem composition and dynamics (e.g., <xref ref-type="bibr" rid="B64">Jackson and Hobbs, 2009</xref>; <xref ref-type="bibr" rid="B63">Jackson and Blois, 2015</xref>; <xref ref-type="bibr" rid="B8">Birks, 2019</xref>; <xref ref-type="bibr" rid="B38">Div&#x00ED;&#x0161;ek et al., 2020</xref>; <xref ref-type="bibr" rid="B43">Fordham et al., 2020</xref>).</p>
<p>To look back in time we use palaeoecological records as informative archives of past ecosystem composition, biodiversity, climate, anthropogenic land-use, and human history (e.g., <xref ref-type="bibr" rid="B9">Birks and Birks, 1980</xref>; <xref ref-type="bibr" rid="B8">Birks, 2019</xref>; <xref ref-type="bibr" rid="B43">Fordham et al., 2020</xref>). Pollen assemblages preserved in stratigraphic records are the most commonly used terrestrial fossil group for the Holocene to elucidate past vegetation patterns at the landscape or regional scale (e.g., <xref ref-type="bibr" rid="B12">Birks and Gordon, 1985</xref>; <xref ref-type="bibr" rid="B6">Birks, 2007</xref>; <xref ref-type="bibr" rid="B11">Birks et al., 2016b</xref>; <xref ref-type="bibr" rid="B41">Felde et al., 2016</xref>, <xref ref-type="bibr" rid="B40">2020</xref>). However, pollen-based compositional data generated from stratigraphic records are multivariate, containing many samples and taxa, are closed (pollen counts for each taxon in a sample of a record are expressed relative to the pollen sum of that sample), and may reflect a complexity of patterns (<xref ref-type="bibr" rid="B5">Birks, 1994</xref>, <xref ref-type="bibr" rid="B6">2007</xref>). Therefore, such data for multiple records covering a wide geographical area and different temporal scales can be difficult to summarise and interpret using traditional pollen diagrams and qualitative analyses alone.</p>
<p>With the development of quantitative palaeoecology over recent decades (e.g., <xref ref-type="bibr" rid="B13">Birks et al., 2012</xref> and references therein), it is possible to quantify more precisely the past ecological properties of pollen-assemblages, so-called pollen-assemblage properties (PAPs). These include compositional turnover, changes in composition (zonation or partitioning), taxonomic richness, diversity, and evenness, and rates of compositional change over time. They can be used by careful inference to reconstruct past vegetation dynamics (<xref ref-type="bibr" rid="B8">Birks, 2019</xref>). Although there is no direct 1:1 relationship between pollen-assemblage richness and floristic richness, several studies have documented that differences in pollen-assemblage richness may reflect differences in floristic richness, if the data have a consistent and detailed taxonomy and the data are analysed appropriately using consistent methodology (see <xref ref-type="bibr" rid="B10">Birks et al., 2016a</xref> and references therein; <xref ref-type="bibr" rid="B114">V&#x00E4;li et al., 2022</xref>). Therefore, diversity estimates such as Hill numbers (<xref ref-type="bibr" rid="B56">Hill, 1973</xref>), which provide conceptually simple but robust estimates of taxonomic diversity, can also be applied to carefully processed pollen-assemblage data for estimating pollen richness, evenness, and diversity (<xref ref-type="bibr" rid="B10">Birks et al., 2016a</xref>). Such estimates can be useful to summarise pollen-assemblage patterns across time and space, depending upon the purpose of the study and the nature of the data. However, because of the scale-dependence of biodiversity patterns and diversity-environment relationships, patterns revealed at one spatial or temporal scale or for one vegetation type may not necessarily reflect those at other scales or for other vegetation types (<xref ref-type="bibr" rid="B82">McGill et al., 2015</xref>). Therefore, it is important to define the spatial and temporal scales when assessing PAPs.</p>
<p>Cross-scale studies are hampered by two limitations in palaeoecology. First, well-preserved and well-sampled palaeoecological records covering a range of habitats and landscapes are geographically scarce. Open-access palaeoecological databases, especially the European Pollen Database (EPD),<sup><xref ref-type="fn" rid="footnote1">1</xref></sup> Neotoma (<xref ref-type="bibr" rid="B124">Williams et al., 2018</xref>),<sup><xref ref-type="fn" rid="footnote2">2</xref></sup> and Pangaea (PANGAEA<sup>&#x00AE;</sup> -- Data Publisher for Earth and Environmental Science),<sup><xref ref-type="fn" rid="footnote3">3</xref></sup> and data repositories for open access publications (for example, DRYAD), are playing a major part in reducing this limitation in recent decades. However, these data repositories often still lack sufficient high-quality palaeoecological records from large regions of the globe, for example parts of Asia (<xref ref-type="bibr" rid="B20">Cao et al., 2020</xref>). Second, there are inconsistencies in palaeoecological data from different parts of the world. These are mostly due to methodological differences used in different palaeoecological studies, for example in field sampling, laboratory sampling (taking sediment samples from a core for pollen counting, radiocarbon dating, etc.), pollen/spore identifications and nomenclature, chronological techniques, etc. Palynological, palaeoecological, and taxonomic expertise are required to standardise pollen records compiled from large geographical areas (e.g., <xref ref-type="bibr" rid="B47">Giesecke et al., 2014</xref>; <xref ref-type="bibr" rid="B11">Birks et al., 2016b</xref>; <xref ref-type="bibr" rid="B84">Mottl et al., 2021a</xref>). These major limitations are most striking in palaeoecological data from the huge area of Asia which covers highly heterogeneous pollen data in quality and quantity from a wide range of climate and vegetation types.</p>
<p>Consequently, there are relatively few synthetic studies at regional or continental scales that attempt to explore comprehensively Asian vegetation patterns during the Holocene (but see <xref ref-type="bibr" rid="B130">Yu et al., 1998</xref>, <xref ref-type="bibr" rid="B129">2000</xref>; <xref ref-type="bibr" rid="B95">Ren, 2000</xref>; <xref ref-type="bibr" rid="B97">Ren and Beug, 2002</xref>; <xref ref-type="bibr" rid="B128">Yang et al., 2011</xref>; <xref ref-type="bibr" rid="B19">Cao et al., 2013</xref>, <xref ref-type="bibr" rid="B21">2019a</xref>,<xref ref-type="bibr" rid="B22">b</xref>; <xref ref-type="bibr" rid="B108">Sun and Feng, 2021</xref>). The Asian continent encompasses a vast territory with enormous variation in climatic and vegetation in space and time. Moreover, parts of south-west, south, and south-east Asia are thought to have experienced significant anthropogenic impacts during the Holocene as these were the centres for the origin of modern human civilization, and where agricultural practices, and domestication as well as the spread of horticultural trees such as olive might have started (<xref ref-type="bibr" rid="B127">Wright, 1976</xref>; <xref ref-type="bibr" rid="B116">Van Zeist, 1992</xref>; <xref ref-type="bibr" rid="B123">Willcox, 2005</xref>; <xref ref-type="bibr" rid="B44">Fuller and Qin, 2010</xref>; <xref ref-type="bibr" rid="B45">Fuller et al., 2011</xref>; <xref ref-type="bibr" rid="B134">Zohary et al., 2012</xref>; <xref ref-type="bibr" rid="B60">Huang et al., 2017</xref>; <xref ref-type="bibr" rid="B30">Cheng et al., 2018</xref>; <xref ref-type="bibr" rid="B71">Langgut et al., 2019</xref>; <xref ref-type="bibr" rid="B76">Leipe et al., 2019</xref>; <xref ref-type="bibr" rid="B87">Palmisano et al., 2019</xref>; <xref ref-type="bibr" rid="B101">Ruddiman et al., 2020</xref>; <xref ref-type="bibr" rid="B39">Ellis et al., 2021</xref>). A systematic but exploratory synthesis of the cross-scale spatio-temporal patterns in PAPs of Asian pollen data during the Holocene is attempted here.</p>
<p>We compile fossil pollen data from Asia and analyse the patterns of eight PAPs, namely pollen-compositional turnover, changes in pollen composition, <xref ref-type="bibr" rid="B56">Hill&#x2019;s (1973)</xref> richness, diversity, and evenness estimates (N0, N1, N2, N2/N1, and N1/N0), and rate of pollen-compositional change (RoC) across space and time. We apply conservative data-standardisation procedures before analysing the data with robust analytical methods. We ask: (1) What are the major spatial and temporal patterns of PAPs in Asia during the Holocene and how do the temporal patterns vary in space? (2) Do the major pollen-compositional changes occur at the same time across Asia and across different climate-zones within the continent?</p>
<p>To answer these basic questions, our study is, by necessity explorative (pattern detection) rather than causational (hypothesis testing). <xref ref-type="bibr" rid="B92">Proctor (2010)</xref> emphasizes that both approaches can be valuable as science proceeds not only by hypothesis testing but also by assembling and exploring systematic bodies of data that often initiate further, more detailed study. Here we explore the patterns of the PAPs at different spatial scales (individual record, latitude, longitude, climate-zones, and continent) through time (patterns of PAP estimates during the past 12,000 years). These patterns may be useful in subsequent causational studies for elucidating potential drivers of vegetation change in Asia during the Holocene. To the best of our knowledge, no quantitative palaeoecological synthesis from Asia has been published at the scales of this paper, possibly because of the problems involved in gathering records, developing consistent and robust age-depth models, and establishing a harmonised continental-scale pollen taxonomy for the vast and diverse Asian region.</p>
<p>We first summarise the methods and records used and then present the results as a series of figures of PAPs through time and space. To provide the background for the discussion and interpretation of the results we first summarise current knowledge of Holocene climate and vegetation history of Asia. We conclude by considering some of the problems in analysing and interpreting PAP estimates over broad spatial and temporal scales.</p>
</sec>
<sec id="S2">
<title>Methods</title>
<sec id="S2.SS1">
<title>Geography and modern climate</title>
<p>Based on current and historical phytogeography, climate, and geo-political and ecological distinctiveness, here we consider the &#x201C;Asia continent&#x201D; as the geographical territory between approximately longitude 29&#x00B0; E (western part of Russia) and 180&#x00B0; E (including eastern Siberia and Japan) and latitude 10&#x00B0; N (including the Gulf countries, southern India, and south-east Asia-Malaysia) and 80&#x00B0; N (including northern Siberia). We compiled fossil pollen records from this area (<xref ref-type="fig" rid="F1">Figures 1</xref>&#x2013;<xref ref-type="fig" rid="F3">3</xref>). We describe the climate and vegetation in Asia through space and time with reference to geographic regions as described in the existing literature: Siberia (ca. 29&#x00B0; E&#x2013;180&#x00B0; E and ca. 50&#x00B0; N&#x2013;75&#x00B0; N; eastern Siberia ca. 120&#x00B0; E eastward, central Siberia ca. 55&#x00B0; E&#x2013;120&#x00B0; E, and western Siberia ca. 55&#x00B0; E westward), eastern Asia (between ca. 95&#x00B0; E&#x2013;150&#x00B0; E and ca. 20&#x00B0; N&#x2013;50&#x00B0; N), central Asia (between ca. 70&#x00B0; E&#x2013;95&#x00B0; E and ca. 30&#x00B0; N&#x2013;50&#x00B0; N), and south-western Asia (between ca. 29&#x00B0; E&#x2013;70&#x00B0; E and ca. 20&#x00B0; N&#x2013;ca. 45&#x00B0; N) (<xref ref-type="fig" rid="F1">Figure 1A</xref>).</p>
<fig id="F1" position="float">
<label>FIGURE 1</label>
<caption><p><bold>(A)</bold> Map of the study area (Asia), with the locations of the 205 processed records (blue dots). The records are only distributed in six (out of total nine) modified K&#x00F6;ppen&#x2013;Geiger climate-zones in Asia (cf. <xref ref-type="bibr" rid="B3">Beck et al., 2018</xref>): &#x201C;Arid&#x201D;, &#x201C;Cold-seasonally dry&#x201D;, &#x201C;Cold without dry season&#x201D;, &#x201C;Polar&#x201D;, &#x201C;Temperate&#x201D;, and &#x201C;Tropical monsoon&#x201D;. The &#x201C;Tropical monsoon&#x201D; climate-zone has one record, and therefore was excluded from the data, giving a total of 205 records from the five modified climate-zones for our analyses. We used a raster from the geo-tiff file in <xref ref-type="bibr" rid="B3">Beck et al. (2018)</xref> for the climate zonation and adopted their 13 climate-zone (general zones cluster) scheme, which provides a realistic classification of climate at the continental scale. For simplicity of climatic zonation over space, we amalgamated the closely related climate-zones based on the five climate-zone scheme of <xref ref-type="bibr" rid="B3">Beck et al. (2018)</xref>. Size of the blue-dots in the map represents the total compositional turnover of the fossil pollen records across Asia. <bold>(B,C)</bold> Patterns of the total compositional turnover or gradient length [range of <italic>CaseR</italic> scores of the first axis of a detrended canonical correspondence analysis (DCCA1)] along the latitudinal and longitudinal gradients, where the blue trend-lines are plotted as the fitted values for a generalised additive model regression. The DCCA1 values are in standard deviation units of turnover (<xref ref-type="bibr" rid="B112">ter Braak and &#x0160;milauer, 2012</xref>).</p></caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fevo-11-1115784-g001.tif"/>
</fig>
<fig id="F2" position="float">
<label>FIGURE 2</label>
<caption><p><bold>(A)</bold> Compositional change (number of unique partitions or &#x201C;zones&#x201D; revealed by multivariate regression tree, MRT) in the pollen assemblages along the temporal gradient of each fossil pollen record across Asia. <bold>(B,C)</bold> Patterns in the number of MRT groups along the latitudinal and longitudinal gradient (blue lines) are plotted as the fitted values for a generalised additive model regression.</p></caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fevo-11-1115784-g002.tif"/>
</fig>
<fig id="F3" position="float">
<label>FIGURE 3</label>
<caption><p>Number of fossil pollen records analysed from the five climate-zones in Asia.</p></caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fevo-11-1115784-g003.tif"/>
</fig>
<p>The vast area and physiographic variation within Asia result in considerable climatic variation. Based on temperature and precipitation regimes, climatic conditions across Asia can be broadly grouped into nine K&#x00F6;ppen&#x2013;Geiger climate-zones or &#x201C;General zone cluster&#x201D; (cf. <xref ref-type="bibr" rid="B3">Beck et al., 2018</xref>; see <xref ref-type="fig" rid="F1">Figure 1A</xref>). They are &#x201C;Arid&#x201D; (Middle East or the Levant region, north-western parts of the Indian Subcontinent, parts of Mongolia including the Gobi desert, north-west China); &#x201C;Cold-seasonally dry&#x201D; (parts of north-east China and Mongolia and south-east Siberia); &#x201C;Cold without dry season&#x201D; (regions between 50&#x00B0; N and 70&#x00B0; N latitudes, i.e., most of Siberia); &#x201C;Temperate&#x201D; (northern and north-eastern parts of southern Asia and some parts of Levant); &#x201C;Tropical monsoon&#x201D; (south-western parts of Indian subcontinent and parts of south-eastern Asia); &#x201C;Tropical savannah&#x201D; (Southern part of Indian subcontinent, and south-eastern Asia), &#x201C;Tropical rainforest&#x201D; (parts of south-eastern Asia-Malaysia), &#x201C;Polar&#x201D; (northern parts of Siberia and high altitude locations in central and southern Asia), and &#x201C;Polar frost&#x201D; (northern extreme of Siberia under permafrost) (<xref ref-type="bibr" rid="B3">Beck et al., 2018</xref>). However, our compiled records cover only six of the climate-zones, namely, &#x201C;Arid,&#x201D; &#x201C;Cold-seasonally dry,&#x201D; &#x201C;Cold without dry season,&#x201D; &#x201C;Polar,&#x201D; &#x201C;Temperate,&#x201D; and &#x201C;Tropical monsoon&#x201D; (<xref ref-type="fig" rid="F1">Figure 1A</xref>). South-western Asia and central Asia experience an arid climate with influence from the Mediterranean climate system, whereas the monsoon climate system dominates across the southern and eastern regions (<xref ref-type="fig" rid="F1">Figure 1A</xref>, &#x201C;Arid&#x201D;) (<xref ref-type="bibr" rid="B25">Chen F. et al., 2019</xref>). The Siberian region is influenced by the polar climate system and the &#x201C;Siberian High&#x201D; (<xref ref-type="bibr" rid="B48">Gong and Ho, 2002</xref>). Therefore, southern Asia is mild to hot, the far northern and north-eastern areas are very cold and dry, and mid-latitude areas of eastern Asia experience a temperate climate.</p>
<p>There is considerable variation in precipitation across the continent. The eastern and central parts are affected by the Indian summer monsoon, the East Asian summer monsoon, and the westerly circulation (<xref ref-type="bibr" rid="B19">Cao et al., 2013</xref>), resulting in a marked precipitation gradient from monsoon-dominated south-eastern Asia (<xref ref-type="fig" rid="F1">Figure 1A</xref>, &#x201C;Temperate&#x201D;) to the desert areas of central Asia influenced by the westerlies (<xref ref-type="fig" rid="F1">Figure 1A</xref>, &#x201C;Arid&#x201D;) (<xref ref-type="bibr" rid="B19">Cao et al., 2013</xref>). The Indian subcontinent and surrounding regions are affected by the Indian summer monsoon, and the south-western summer monsoon, creating an east-west and south-west &#x2013; north precipitation gradient in southern Asia with tropical rainforest, savannah, and temperate zones (<xref ref-type="fig" rid="F1">Figure 1A</xref>). In western and south-western Asia, most precipitation falls during winter and summers are generally dry and hot, leading to a north-south precipitation gradient, with a semi-arid to humid climate in the north and an arid climate in the south (<xref ref-type="fig" rid="F1">Figure 1A</xref>, &#x201C;Cold without dry season&#x201D;) (<xref ref-type="bibr" rid="B98">Rohling et al., 2009</xref>; <xref ref-type="bibr" rid="B29">Cheng et al., 2015</xref>).</p>
</sec>
<sec id="S2.SS2">
<title>Data compilation and screening</title>
<p>We compiled a total of 552 raw fossil pollen records from Asia. Of these, 438 records were downloaded from the Pangaea database (PANGAEA<sup>&#x00AE;</sup> &#x2013; Data Publisher for Earth and Environmental Science) (see text footnote 3, accessed on 13.01.2020), the Neotoma palaeoecology database (<xref ref-type="bibr" rid="B124">Williams et al., 2018</xref>) (see text footnote 2, accessed on 28.02.2021), and publications (datasets published with research papers, reports, etc.). In addition, we obtained 114 records from individual researchers. We processed all records applying a robust and consistent data-screening procedure based on their metadata, chronological and pollen data, and taxonomic harmonisation. The full metadata information of all records used in study (including the source of data) can be found in <xref ref-type="supplementary-material" rid="DS1">Supplementary Table 1</xref>.</p>
<sec id="S2.SS2.SSS1">
<title>Metadata</title>
<p>For each record we compiled information about latitude, longitude, site name or location, country, sample depth, number of samples, depositional environment, current climate based on the climatic classification of <xref ref-type="bibr" rid="B3">Beck et al. (2018)</xref> (see above and <xref ref-type="fig" rid="F1">Figure 1</xref>), and relevant publications.</p>
</sec>
<sec id="S2.SS2.SSS2">
<title>Chronological data</title>
<p>We used chronology-control points for the construction of an age-depth model for each record. We selected only the chronology control-point types appropriate for estimating robust age-depth models (see <xref ref-type="supplementary-material" rid="DS2">Supplementary Table 2</xref>). We only used records with more than two chronology-control points of the selected chronology-control types including core-top age.</p>
</sec>
<sec id="S2.SS2.SSS3">
<title>Fossil pollen records</title>
<p>We preferred fossil pollen records with raw counts for further data processing and analysis. However, 48 records with pollen percentages originating from data-sparse regions were also considered. We only included records collected from selected sediment depositional environments (<xref ref-type="supplementary-material" rid="DS2">Supplementary Table 3</xref>), and pollen counts or percentages for terrestrial trees, shrubs, herbs, palms, succulents, and mangrove taxa. We subjected the records to taxonomic harmonisation (see below). We then processed the taxonomically harmonised pollen records based on age criteria. For this, we set the calibrated age of 12,000 cal year BP (calibrated years before present, where 0 year BP = 1950 common era CE) as the oldest age-limit (lower age-limit) for each record and discarded samples older than the lower age-limit. We also discarded records in which the calibrated age of the youngest sample (upper age-limit) was &#x003E;1,600 cal year BP or the age of the oldest sample was &#x003C;5,800 cal year BP. Thus, the lower age-limit of the selected records varies from 5,800 to 12,000 cal year BP, whereas the upper age-limit varies from 0 to 1,600 cal year BP. We then processed the record based on the number of taxa and samples. We only selected records with five or more samples and with five of more harmonised taxa. We then filtered the records based on the number of pollen grains in each sample of a record, where we discarded samples containing &#x003C;25 grains. We also discarded samples with 25&#x2013;150 grains if 50% of the samples in a record have more than 150 grains. This was done to avoid losing too many pollen records with only a few samples that consistently have a low pollen count. For a statistical summary of the pollen data, see <xref ref-type="supplementary-material" rid="DS2">Supplementary Table 4</xref>.</p>
</sec>
</sec>
<sec id="S2.SS3">
<title>Taxonomic harmonisation</title>
<p>For standardisation of the pollen taxonomy in the records, we followed a hierarchical nomenclature system of the pollen morpho-types, in which closely related morpho-types are merged into a higher accepted pollen taxon or morpho-type. Based on the present flora and hence the pollen taxonomy, and the traditions of identifying, naming, and classifying pollen morpho-types by different analysts, we harmonised pollen taxonomy and nomenclature for the three regions, the Levant, continental Asia, and Siberia, separately. We harmonised the pollen morpho-types in each region to the taxonomically highest-precision level of pollen morpho-types potentially identified by most palynologists. As a result, the harmonised pollen taxa in all three regions are robust enough to compare pollen composition across these regions. Altogether, we harmonised 2115 &#x201C;raw&#x201D; pollen morpho-types into 508 harmonised taxa for Asia. The harmonisation tables used in this study can be found at <ext-link ext-link-type="uri" xlink:href="https://github.com/HOPE-UIB-BIO/Asian_palynological_synthesis/blob/main/Data/Input/Hamonisation_tables/Asia_Main-2021-07-07.csv">https://github.com/HOPE-UIB-BIO/Asian_palynological_synthesis/blob/main/Data/Input/Hamonisation_tables/Asia_Main-2021-07-07.csv</ext-link>, <ext-link ext-link-type="uri" xlink:href="https://github.com/HOPE-UIB-BIO/Asian_palynological_synthesis/blob/main/Data/Input/Hamonisation_tables/Asia_Siberia-2021-06-16.csv">https://github.com/HOPE-UIB-BIO/Asian_palynological_synthesis/blob/main/Data/Input/Hamonisation_tables/Asia_Siberia-2021-06-16.csv</ext-link>, and <ext-link ext-link-type="uri" xlink:href="https://github.com/HOPE-UIB-BIO/Asian_palynological_synthesis/blob/main/Data/Input/Hamonisation_tables/Asia_Levant-2021-06-16.csv">https://github.com/HOPE-UIB-BIO/Asian_palynological_synthesis/blob/main/Data/Input/Hamonisation_tables/Asia_Levant-2021-06-16.csv</ext-link>.</p>
</sec>
<sec id="S2.SS4">
<title>Age-depth models</title>
<p>We estimated an age-chronology of each record using the Bchron (<xref ref-type="bibr" rid="B52">Haslett and Parnell, 2008</xref>) age-depth modelling approach. To develop age-depth models, we calibrated the dates of the selected chronology-control point types using IntCal20 (<xref ref-type="bibr" rid="B94">Reimer et al., 2020</xref>) or mixed or post-bomb calibration curves based on the geographical location of the records and the boundaries recommended by <xref ref-type="bibr" rid="B58">Hogg et al. (2020)</xref>. For each record, we constructed an age-depth model using the &#x201C;bchron&#x201D; R package (<xref ref-type="bibr" rid="B52">Haslett and Parnell, 2008</xref>) using 50,000 iterations, while discarding the first 10,000 (&#x201C;burn&#x201D;) and keeping each 40th (&#x201C;thin&#x201D;). This results in 1,000 draws to build posterior estimates of age uncertainty. We calculated the median age estimate for each sample depth to obtain the age used in these analyses. All ages are expressed in calibrated years before present (cal year BP). We selected the records based on our age-limit criteria (see section &#x201C;Fossil pollen records&#x201D;) and used only the median age of the samples for analysing the temporal patterns in the PAPs.</p>
<p>Screening of the records based on the above criteria resulted in 232 records. We then examined the pollen diagram and the age-depth model for each record. Of these, 25 records were found to be of poor quality and therefore unsuitable for numerical analysis. This resulted in 207 fully processed records for further analyses. However, we removed the single record from the &#x201C;Tropical monsoon&#x201D; climate-zone, and a record from far-east Siberia that is beyond the international dateline (&#x2212;179.75&#x00B0; W longitude) before numerical analysis to avoid a large discrepancy in the number of records per climate-zone and the geographical distribution of records.</p>
</sec>
<sec id="S2.SS5">
<title>Numerical analyses</title>
<p>Analyses are based on the 205 fully processed fossil pollen records covering the past 12,000 years (<xref ref-type="fig" rid="F1">Figures 1</xref>&#x2013;<xref ref-type="fig" rid="F3">3</xref>). We used R version 4.1.1 (<xref ref-type="bibr" rid="B93">R Core Team, 2022</xref>) for data acquisition, processing, age-depth modelling, and analysis.</p>
<sec id="S2.SS5.SSS1">
<title>Estimating pollen-assemblage properties</title>
<p>In each record we analysed the spatial patterns of the total pollen-compositional variation and temporal pattern of each PAP (except MRT partitions) along the temporal gradient of 12,000 years.</p>
<sec id="S2.SS5.SSS1.Px1">
<title>Hill&#x2019;s taxonomic richness, diversity, and evenness measures</title>
<p>We estimated pollen richness (the number of pollen types present in a pollen record) by <xref ref-type="bibr" rid="B56">Hill&#x2019;s (1973)</xref> N0 measure, pollen diversity by <xref ref-type="bibr" rid="B56">Hill&#x2019;s (1973)</xref> N1 and N2 measures, and pollen evenness by their ratios (N2/N1 and N1/N0). There are several advantages of using Hill numbers over other diversity indices (<xref ref-type="bibr" rid="B23">Chao et al., 2014</xref>; <xref ref-type="bibr" rid="B10">Birks et al., 2016a</xref>), and these indices are increasingly used as quantitative diversity metrics in ecology. The most important feature of Hill numbers is that they obey the intuitive <italic>replication principle or doubling property</italic> and are all expressed in units of effective number of taxa, i.e., the number of equally abundant taxa (species) in an assemblage (<xref ref-type="bibr" rid="B23">Chao et al., 2014</xref>). N0 is the number of taxa in an assemblage regardless of their abundances. N1 estimates the number of abundant taxa in an assemblage, where each taxon is weighted by its relative frequency and is the exponential of the commonly used Shannon diversity index. N2 estimates the number of very abundant taxa in an assemblage by giving most weight to the common and more abundant taxa with rare taxa making almost no contribution to the sum and is the inverse of Simpson&#x2019;s diversity or concentration measure (<xref ref-type="bibr" rid="B23">Chao et al., 2014</xref>; <xref ref-type="bibr" rid="B10">Birks et al., 2016a</xref>). Evenness is a measure of the variability in taxon abundances in a sample or assemblage, and can be estimated by a ratio of Hill numbers (E<sub>&#x03B1;,&#x03B2;</sub> = N<sub>&#x03B1;</sub>/N<sub>&#x03B2;</sub>, where E is evenness, N is a Hill number, and &#x03B1; and &#x03B2; are the orders of N, and &#x03B1; &#x2260; &#x03B2;) (<xref ref-type="bibr" rid="B10">Birks et al., 2016a</xref>). <xref ref-type="bibr" rid="B56">Hill (1973)</xref> proposed N2/N1 as an appropriate evenness measure as evenness should be independent of taxon richness. However, several alternative measures of evenness (Hill ratios) have also been proposed, each of which has its own strengths and weaknesses (see <xref ref-type="bibr" rid="B10">Birks et al., 2016a</xref>). Here, we used the two most widely used evenness measures based on Hill numbers: N2/N1 and N1/N0. Prior to estimating Hill indices, we used rarefaction (cf. <xref ref-type="bibr" rid="B23">Chao et al., 2014</xref>) to standardize the count size. Using &#x2018;&#x2018;diversity_estimate&#x2019;&#x2019; function in &#x2018;&#x2018;R-Ecopol&#x2019;&#x2019; package (v0.0.1) in R,<sup><xref ref-type="fn" rid="footnote4">4</xref></sup> we estimated Hill&#x2019;s richness, diversity, and evenness indices.</p>
</sec>
<sec id="S2.SS5.SSS1.Px2">
<title>Pollen-compositional turnover</title>
<p>We performed detrended canonical correspondence analysis (DCCA) (<xref ref-type="bibr" rid="B110">ter Braak, 1986</xref>; <xref ref-type="bibr" rid="B112">ter Braak and &#x0160;milauer, 2012</xref>) with Hill&#x2019;s detrending, non-linear rescaling, and no down-weighting of rare taxa (<xref ref-type="bibr" rid="B57">Hill and Gauch, 1980</xref>) to estimate the compositional turnover in each pollen record, where time (sample age) was used as the sole explanatory variable. Pollen records provide a basis for estimating biotic turnover along long temporal gradients (<xref ref-type="bibr" rid="B6">Birks, 2007</xref>; <xref ref-type="bibr" rid="B40">Felde et al., 2020</xref>). In DCCA, weighted average (WA) sample scores, i.e., &#x201C;<italic>CaseR</italic>,&#x201D; along ordination axes are scaled in ecologically interpretable standard deviation units of compositional turnover (<xref ref-type="bibr" rid="B112">ter Braak and &#x0160;milauer, 2012</xref>). In pollen records, samples are arranged in a known temporal order, and the DCCA is constrained by sample age. Hence, the total gradient length, i.e., range of the sample scores (<italic>CaseR</italic>), of the first DCCA axis gives an estimate of the total amount of compositional turnover along the temporal gradient, whereas the individual <italic>CaseR</italic> scores elucidate sample-to-sample compositional turnover based on all pollen taxa within the record (<xref ref-type="bibr" rid="B6">Birks, 2007</xref>; <xref ref-type="bibr" rid="B40">Felde et al., 2020</xref>). We performed DCCA analysis using CANOCO version 4.5 (<xref ref-type="bibr" rid="B111">ter Braak and &#x0160;milauer, 2002</xref>) via &#x201C;fit_ordination&#x201D; function in &#x201C;R-Ecopol&#x201D; package (v0.0.1) using a second-order polynomial predictor of age.</p>
</sec>
<sec id="S2.SS5.SSS1.Px3">
<title>Pollen-compositional change: multivariate regression tree</title>
<p>Multivariate regression tree (MRT) is a statistical technique that can be used to explore, describe, and predict relationships between multivariate response data and environmental predictor variables (<xref ref-type="bibr" rid="B35">De&#x2019;ath, 2002</xref>). It forms clusters of samples by repeated splitting of the data, with each split defined by a simple rule based on external predictor values. The splits are chosen to minimise the dissimilarity of samples within clusters, where each cluster represents an assemblage of samples and response variables. It is a robust technique well suited for analysing complex data that may include imbalance, missing values, non-linear relationships between variables, and high-order interactions (<xref ref-type="bibr" rid="B35">De&#x2019;ath, 2002</xref>; <xref ref-type="bibr" rid="B74">Legendre and Birks, 2012</xref>; <xref ref-type="bibr" rid="B105">Simpson and Birks, 2012</xref>). We performed MRT partitioning based on the 1-SE rule [from a series of trees, the smallest tree within one standard error (SE) of the best is often selected, see <xref ref-type="bibr" rid="B35">De&#x2019;ath, 2002</xref>], using the Chi-squared metric (<xref ref-type="bibr" rid="B91">Prentice, 1980</xref>) and sample age as the sole predictor variable to extract statistically significant partitions (pollen-assemblage zones) for each record. These are the points of significant compositional change along the temporal gradient (<xref ref-type="bibr" rid="B105">Simpson and Birks, 2012</xref>). We used the &#x201C;mvpart&#x201D; package in R (<xref ref-type="bibr" rid="B37">De&#x2019;ath, 2014</xref>) for performing MRT analysis in each record.</p>
</sec>
<sec id="S2.SS5.SSS1.Px4">
<title>Rate of pollen-compositional change</title>
<p>Estimating the magnitude of the rate of compositional change through a pollen record per unit time (RoC) is a useful tool for quantifying temporal patterns of compositional change in pollen-stratigraphic data per unit time (<xref ref-type="bibr" rid="B7">Birks, 2012</xref>; <xref ref-type="bibr" rid="B85">Mottl et al., 2021b</xref>). There are several methods for estimating RoC (see <xref ref-type="bibr" rid="B85">Mottl et al., 2021b</xref>), but earlier studies have shown that many methods do not circumvent the artefactual variations arising from irregular temporal sampling resolution (<xref ref-type="bibr" rid="B85">Mottl et al., 2021b</xref>). To avoid such issues in RoC, <xref ref-type="bibr" rid="B85">Mottl et al. (2021b)</xref> present an innovative approach that is a variant of a moving window. Here we estimated the rate of compositional change for each record using the authors&#x2019; &#x201C;R-Ratepol&#x201D; package (<xref ref-type="bibr" rid="B85">Mottl et al., 2021b</xref>). We used an age bin size of 500 years and 5 window shifts and estimated RoC using the Chi-squared metric (<xref ref-type="bibr" rid="B91">Prentice, 1980</xref>) between consecutive time intervals. We transformed pollen counts to proportions and applied the &#x201C;Age-weighted average&#x201D; smoothing method with maximal age range for 500 years for each pollen type. For RoC estimation, we selected the random sample in each bin as a representative of that bin and standardised each &#x201C;Working Unit&#x201D; to 150 individuals (otherwise, to the smallest number of pollen grains in record) using random resampling without replacement. We set the number of iterations to 1,000. A detailed procedure for RoC estimation, and reasons for estimating RoC over 500-year bins are described in <xref ref-type="bibr" rid="B85">Mottl et al. (2021b)</xref>.</p>
</sec>
</sec>
<sec id="S2.SS5.SSS2">
<title>Spatial patterns of compositional turnover and change</title>
<p>We fitted a generalised additive model (GAM) regression using &#x201C;mgcv 1.8-40&#x201D; package in R (<xref ref-type="bibr" rid="B125">Wood, 2022</xref>) for analysing latitudinal and longitudinal patterns of total compositional turnover and compositional change (MRT partitions), where we treated these estimates as a response variable against latitude and longitude of the records as predictor variables. We assumed a &#x201C;Tweedie&#x201D; error distribution (<italic>p</italic> = 1.1) for the models of compositional turnover and a &#x201C;Poisson&#x201D; error distribution for the MRT partition models.</p>
</sec>
<sec id="S2.SS5.SSS3">
<title>Cross-scale patterns of pollen-assemblage composition and diversity estimates</title>
<p>For cross spatial-scale comparison of the temporal patterns of PAPs during the last 12,000 years, we analysed the patterns of each PAP at three spatial scales (grains): &#x201C;Pollen record level&#x201D; (patterns for individual records), &#x201C;Climate-zone level&#x201D; (assembled the records into the five climate-zones and summarised the patterns of each PAPs within each climate-zone), and &#x201C;Continent level&#x201D; (summarised the temporal patterns of each PAPs for the entire continent).</p>
<p>For &#x201C;record level,&#x201D; we developed a single generalised linear model (GAM) for each record using &#x201C;mgcv 1.8-40&#x201D; package in R (<xref ref-type="bibr" rid="B125">Wood, 2022</xref>), in which we treated estimates of each PAP as a response variable and time (ka) as a predictor variable. However, for the &#x201C;climate-zone level,&#x201D; we developed one hierarchical generalised additive model (hGAM) for each climate-zone, and for the &#x201C;continent level,&#x201D; we developed a single hGAM for the whole continent using &#x201C;mgcv 1.8-40&#x201D; package in R (<xref ref-type="bibr" rid="B89">Pedersen et al., 2019</xref>).</p>
<p>We treated location (&#x201C;dataset_id&#x201D;) of each record as a random effect variable with a separate smoother and penalty for each record within the climate-zone, and a shared smoother and penalty for the overall (global) model of the climate-zone (similar to Model GI in <xref ref-type="bibr" rid="B89">Pedersen et al., 2019</xref>). For the temporal patterns at the &#x201C;continent level,&#x201D; we fitted a single hierarchical GAM model with a separate smoother and penalty for each &#x201C;dataset_id&#x201D; and a shared smoother and penalty for the overall (global) model for the whole continent (similar to Model GI in <xref ref-type="bibr" rid="B89">Pedersen et al., 2019</xref>). We assumed a &#x201C;Tweedie&#x201D; error distribution (<italic>p</italic> = 1.1) for models of N0, N1, N2, DCCA1, and RoC, and a &#x201C;beta&#x201D; error distribution for models of evenness measures (N2/N1 and N1/N0). For all models we predicted values for each 100 years but limited the prediction to only span the time period with data (i.e., we did not fore- or back-cast more than 100 years from the first and last data point, respectively). For &#x201C;records level&#x201D; patterns, we summarised the similarity between patterns of records using the root-mean-square error (RMSE), calculated for each 100 years. All figures of the spatial and temporal patterns are plotted using &#x201C;ggplot2&#x201D; (<xref ref-type="bibr" rid="B122">Wickham, 2016</xref>).</p>
</sec>
<sec id="S2.SS5.SSS4">
<title>Major temporal changes in the pollen-assemblage properties</title>
<sec id="S2.SS5.SSS4.Px1">
<title>Regression tree partitioning</title>
<p>To answer our second research question concerning synchronicity of temporal changes in PAPs among records, we performed regression tree (RT) partitioning of the estimates of compositional turnover (DCCA axis 1 sample or &#x201C;<italic>CaseR</italic>&#x201D; scores) and Hill&#x2019;s richness, diversity, and evenness estimates, with respect to the time (sample-age) predictor variable for each record. This gives us the time or age of each split in a RT of a PAP, which represents the time of major changes in that PAP, called the &#x201C;change-point.&#x201D; RT, like MRT, are a specific family of machine-learning techniques, in which the trees are used to partition a record by successively separating the response variable based on relative abundances with respect to a predictor variable (<xref ref-type="bibr" rid="B36">De&#x2019;ath, 2007</xref>). Classification and RTs (<xref ref-type="bibr" rid="B17">Breiman et al., 1984</xref>) are being widely used to explore, describe, and summarise ecological data (e.g., <xref ref-type="bibr" rid="B35">De&#x2019;ath, 2002</xref>; <xref ref-type="bibr" rid="B105">Simpson and Birks, 2012</xref>; <xref ref-type="bibr" rid="B31">Chevalier et al., 2020</xref>). A univariate RT is a useful tool to analyse variation in a single numeric response variable using numeric and/or categorical predictor variables. We used the &#x201C;mvpart&#x201D; package in R (<xref ref-type="bibr" rid="B37">De&#x2019;ath, 2014</xref>) to partition the PAP estimates.</p>
<p>To summarise the temporal trends of RT change-points of each PAP, we estimated the density of RT and MRT &#x201C;change-points&#x201D; per 1,000-year time bin for each PAP, using the &#x201C;reflecting technique&#x201D; of <xref ref-type="bibr" rid="B104">Silverman (1986)</xref>, which mitigates edge effects. For &#x201C;record level&#x201D; we estimated density from change-points of each record. However, for the &#x201C;climate-zone level,&#x201D; and &#x201C;continent level,&#x201D; we pooled the change-points within each climate-zone and the continent, respectively, and then estimated the density of the change-points for each PAP. For all spatial scales we rescaled the density values between 0 and 1.</p>
</sec>
</sec>
</sec>
</sec>
<sec id="S3" sec-type="results">
<title>Results</title>
<p>The great variation in climate, physiography, and spatial distribution of the records across the continent is reflected in the complex variation in the spatio-temporal patterns of the different PAPs (see <xref ref-type="fig" rid="F1">Figures 1</xref>&#x2013;<xref ref-type="fig" rid="F5">5</xref>).</p>
<fig id="F4" position="float">
<label>FIGURE 4</label>
<caption><p>Pollen record-, climate-zone-, and continent-scale temporal trends of <xref ref-type="bibr" rid="B56">Hill (1973)</xref> numbers: richness (N0); exponent of Shannon entropy (N1); inverse of Simpson&#x2019;s index of concentration (N2); evenness ratios (N1 divided by N0 or N1/N0; and N2 divided by N1 or N2/N1), compositional turnover [site <italic>CaseR</italic> scores of the first axis of a detrended canonical correspondence analysis (DCCA1)], and rate of change (RoC) estimated for 205 records across Asia. Record level <bold>(first column)</bold> is a trend line for each record (green) for each PAP-estimate fitted by a generalised additive model for each location (&#x201C;dataset_id&#x201D;). Climate-zone level <bold>(middle column)</bold> models are fitted by five (one for each climate-zone) hierarchical generalised additive model (hGAM), accounting for the random effect of location. The continent level <bold>(third column)</bold> models are fitted by a single hGAM for all data within the continent accounting for the random effect of location. Lines are values predicted for each 100 years and shading (only climate-zone and continental scales) is error measurement represented by 95% confidence interval. For &#x201C;record level&#x201D;, the gradient of colour of the trend lines from pale green to green reveals the similarity between patterns of records based on the root-mean-square error (RMSE), calculated for each 100 years. The <italic>X</italic>-axis of each panel represents time (calibrated years before present expressed as thousands of years) and the <italic>Y</italic>-axis represents the estimates of the pollen-assemblage properties.</p></caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fevo-11-1115784-g004.tif"/>
</fig>
<fig id="F5" position="float">
<label>FIGURE 5</label>
<caption><p>Pollen record-, climate-zone-, and continent-scale temporal trends of density of regression tree (RT) and multivariate regression tree (MRT) change-points (time/age of the major changes in a PAP) for each PAP of 205 datasets across Asia. Trends of the change-point density are presented for <xref ref-type="bibr" rid="B56">Hill (1973)</xref> numbers: richness (N0); exponent of Shannon entropy (N1); inverse of Simpson&#x2019;s index of concentration (N2); evenness ratios (N1 divided by N0 or N1/N0 and N2 divided by N1 or N2/N1), compositional turnover [site <italic>CaseR</italic> scores of the first axis of a detrended canonical correspondence analysis (DCCA1)], rate of change (RoC), and compositional change [multivariate regression tree (MRT) partitions]. For &#x201C;record level&#x201D;, the gradient of colour of the trend lines from pale green to green reveals similarity between patterns of the records based on the root-mean-square error (RMSE) calculated for each 100 years. The <italic>X</italic>-axis of each panel represents time (calibrated years before present expressed as thousands of years) and the <italic>Y</italic>-axis represents the standardised density of the regression tree change points for the pollen-assemblage properties.</p></caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fevo-11-1115784-g005.tif"/>
</fig>
<sec id="S3.SS1">
<title>Spatial patterns of compositional turnover and change</title>
<p>Total compositional turnover along the temporal gradient of each record &#x2013; as estimated by the DCCA axis 1 gradient length &#x2013; varies markedly (0.3&#x2013;2.1 SD units) across records (<xref ref-type="fig" rid="F1">Figure 1A</xref>). However, there is no noticeable pattern in total compositional turnover along the latitudinal gradient (predicted values range between 1.1 and 1.2 SD units, 95% confidence intervals &#x201C;CI&#x201D; range between 0.8 and 1.2; <xref ref-type="fig" rid="F1">Figure 1B</xref>). We observe a decline in compositional variation (total compositional turnover and change) eastward along the longitudinal gradient, but with an increase in compositional turnover between ca. 100&#x00B0; E and 150&#x00B0; E (<xref ref-type="fig" rid="F1">Figures 1C</xref>, <xref ref-type="fig" rid="F2">2C</xref>). Temporal variation in compositional change (number of MRT zones in each record) along the latitudinal gradient is slightly more pronounced and exhibits a weak curvilinear latitudinal pattern, which declines from mid- to high-latitudes (predicted values 3.2&#x2013;2.2 MRT groups or assemblages, CI 1.6&#x2013;4.9; <xref ref-type="fig" rid="F2">Figures 2A, B</xref>).</p>
</sec>
<sec id="S3.SS2">
<title>Cross-scale patterns of pollen-assemblage composition and diversity estimates</title>
<p>Temporal patterns of Hill&#x2019;s indices (N0, N1, N2, N2/N1, and N1/N0), compositional turnover, and RoC are presented at three different spatial scales (individual record, climate-zone, and whole continent) (<xref ref-type="fig" rid="F4">Figure 4</xref>), whereas the temporal pattern of compositional change (MRT partitions) at the same spatial scales is presented in the form of the density of RT change-points in each 1,000-year time-bin in the last 12 ka (<xref ref-type="fig" rid="F5">Figure 5</xref>, &#x201C;MRT&#x201D;).</p>
<sec id="S3.SS2.SSS1">
<title>Taxonomic richness, diversity, and evenness</title>
<p>Holocene-wide patterns of <xref ref-type="bibr" rid="B56">Hill&#x2019;s (1973)</xref> diversity estimates are rather heterogeneous across spatial scales. Pollen richness (N0) at the record level is highly heterogeneous and shows no general temporal pattern with predicted values ranging between 2.4 and 48.7 pollen-taxa (CI 1.4&#x2013;53.5; <xref ref-type="fig" rid="F4">Figure 4</xref>, &#x201C;N0: Pollen record&#x201D;). However, when N0 estimates are summarised at the climate-zone level (<xref ref-type="fig" rid="F4">Figure 4</xref>, &#x201C;N0: Climate-zone&#x201D;), there is less heterogeneity in the patterns across the climate-zones. All the climate-zones except the &#x201C;Temperate&#x201D; zone either reveal a gradual or no temporal variation in pollen richness (predicted values 11.5&#x2013;12.7, CI range 9.3&#x2013;5.0). Pollen richness in the &#x201C;Temperate zone&#x201D; shows an increasing trend during the early-Holocene and then it decreases gradually until the present (predicted values 13.6&#x2013;16.4, CI 10.5&#x2013;21.1; <xref ref-type="fig" rid="F4">Figure 4</xref>, &#x201C;N0: Climate-zone&#x201D;). At the continental-scale, a gradually declining pattern from the early- to mid-Holocene and then a gradual increase in N0 from the mid-Holocene to the present is evident (predicted values 12.2&#x2013;12.6, CI 11.4&#x2013;13.5; <xref ref-type="fig" rid="F4">Figure 4</xref>, &#x201C;N0: Continent&#x201D;).</p>
<p>Temporal patterns of <xref ref-type="bibr" rid="B56">Hill&#x2019;s (1973)</xref> N1 and N2 measures also vary across spatial scales. No general temporal patterns of N1 and N2 are observed at the record level (<xref ref-type="fig" rid="F4">Figure 4</xref>, &#x201C;N1, N2 Pollen record&#x201D;). At the climate-zone level, both PAPs in the &#x201C;Temperate&#x201D; climate-zone reveal a unique pattern, where both N1 and N2 reveal a gradual increase during the early-Holocene and then decrease linearly from the mid-Holocene to the present (predicted values 5.5&#x2013;6.6 and 3.9&#x2013;4.2; CI 4.5&#x2013;7.9 and 3.3&#x2013;5, respectively for N1 and N2; <xref ref-type="fig" rid="F4">Figure 4</xref>, &#x201C;N1, N2: Climate-zone&#x201D;). However, in the climate-zone of &#x201C;Cold without dry season,&#x201D; both diversity estimates decrease gradually during the early-Holocene and then increase from the late early- to mid-Holocene, followed by a slight decrease during the most recent period of the late-Holocene (predicted values 5.0&#x2013;5.6 and 3.4&#x2013;4; CI 4.6&#x2013;6 and 3.2&#x2013;4.3, respectively, for N1 and N2; <xref ref-type="fig" rid="F4">Figure 4</xref>, &#x201C;N1, N2: Climate-zone&#x201D;). There is a gradual linear increasing or no temporal pattern of N1 and N2 in other climate-zones. At the continental scale, a gradually increasing pattern in N1 and N2 from the early- to late-Holocene is evident (predicted values 5.2&#x2013;5.4 and 3.7&#x2013;3.8; CI 4.9&#x2013;5.7 and 3.5&#x2013;4, respectively, for N1 and N2; <xref ref-type="fig" rid="F4">Figure 4</xref>, &#x201C;N1, N2: Continent&#x201D;).</p>
<p>No general temporal patterns of Hill&#x2019;s evenness ratio estimates (N2/N1 and N1/N0) are evident at the record level (<xref ref-type="fig" rid="F4">Figure 4</xref>, &#x201C;Pollen record&#x201D;). At the scale of climate-zones, estimates of both evenness ratios in the majority of the climate-zones either decrease gradually or remain unchanged from the early- to late-Holocene (<xref ref-type="fig" rid="F4">Figure 4</xref>, &#x201C;N2/N1 and N1/N0: climate-zone&#x201D;). However, a gradual increase in the evenness ratios from the early- to mid-Holocene, followed by a decline in the estimates from the mid- to late-Holocene, is evident in the &#x201C;Arid&#x201D; zone (predicted values 0.70&#x2013;0.75 and 0.43&#x2013;0.47; CI 0.67&#x2013;0.77 and 0.38&#x2013;0.42, respectively for N2/N1 and N1/N0; <xref ref-type="fig" rid="F4">Figure 4</xref>, &#x201C;N2/N1 and N1/N0: Climate-zone&#x201D;). At the continental scale, both the evenness estimates reveal a gradual declining trend from the early-Holocene to the present (predicted values 0.70&#x2013;0.72 and 0.44&#x2013;0.46; CI 0.69&#x2013;0.73 and 0.42&#x2013;0.48, respectively, for N2/N1 and N1/N0; <xref ref-type="fig" rid="F4">Figure 4</xref>, &#x201C;N2/N1 and N1/N0: Climate-zone&#x201D;).</p>
</sec>
<sec id="S3.SS2.SSS2">
<title>Compositional turnover</title>
<p>Temporal pattern of compositional turnover (<italic>CaseR</italic> scores of DCCA axis 1) is relatively more consistent across the spatial scales of individual records, climate-zones, and the whole continent, which declines linearly from the onset of the Holocene to present (<xref ref-type="fig" rid="F4">Figure 4</xref>, &#x201C;DCCA1&#x201D;). However, turnover in the &#x201C;Temperate&#x201D; zone does not reveal a clear temporal pattern from the early- to mid-Holocene, whereas it declines linearly from the mid-Holocene to the present (predicted values 0.14&#x2013;0.81; CI 0.11&#x2013;1; <xref ref-type="fig" rid="F4">Figure 4</xref>, &#x201C;DCCA1: climate-zone&#x201D;). At the continental scale, a linear declining pattern in DCCA1 from the early-Holocene to the present is evident (predicted values 0.18&#x2013;0.97; CI 0.16&#x2013;1.1; <xref ref-type="fig" rid="F4">Figure 4</xref>, &#x201C;DCCA1: continent&#x201D;).</p>
</sec>
<sec id="S3.SS2.SSS3">
<title>Rate of change</title>
<p>Rates of pollen-compositional change per 500-years vary along the temporal gradient of Holocene as well as across the spatial scales of study (<xref ref-type="fig" rid="F4">Figure 4</xref>, &#x201C;RoC&#x201D;). No general temporal pattern in RoC is observed at the record level, whereas it decreases gradually from the early-Holocene to the present in most of the climate-zones. Notably, an increase in RoC during the early-Holocene, followed by a gradual decrease until the present time, is evident in the &#x201C;Temperate zone&#x201D; (predicted values 0.16&#x2013;0.20; CI 0.12&#x2013;0.25), whereas there is a linear increase in RoC from the early- to late-Holocene in the &#x201C;Arid zone&#x201D; (predicted values 0.14&#x2013;0.20; CI 0.10&#x2013;0.26) (<xref ref-type="fig" rid="F4">Figure 4</xref>, &#x201C;RoC: Climate-zone&#x201D;). At the continental scale, a very gradual linearly declining pattern of RoC from the early-Holocene to the present is evident (predicted values 0.167&#x2013;0.168; CI 0.15&#x2013;0.18; <xref ref-type="fig" rid="F4">Figure 4</xref>, &#x201C;RoC: Continent&#x201D;).</p>
</sec>
</sec>
<sec id="S3.SS3">
<title>Major temporal changes in the pollen-assemblage properties</title>
<p>Temporal patterns of major changes in PAPs (density of RT and MRT change-points of PAPs), especially for DCCA1, MRT, and RoC are broadly consistent across spatial scales (<xref ref-type="fig" rid="F5">Figure 5</xref>). Record level temporal patterns in the density of RT change-points are heterogeneous for the Hill&#x2019;s indices. However, there is a clearly increasing temporal pattern of the density of change-points from the early- to mid-Holocene for the record level trends of DCCA1, RoC, and MRT (<xref ref-type="fig" rid="F5">Figure 5</xref>, &#x201C;Pollen record&#x201D;). At the climate-zone- and continent-scales, the density of the RT change-points increases from the early- to mid-Holocene for all PAPs. However, from the mid-Holocene to recent times, temporal patterns are slightly less consistent across the spatial scales as well as across the PAPs (<xref ref-type="fig" rid="F5">Figure 5</xref>, &#x201C;Climate-zone&#x201D;). During this period, the density of RT change-points for most of the PAPs decreases during the mid-Holocene (ca. 4,000&#x2013;5,000 cal year BP), followed by an increase in change-point density during the mid- to late-Holocene transition, but again with a decrease in the density during the most recent time (<xref ref-type="fig" rid="F5">Figure 5</xref>, &#x201C;Climate-zone&#x201D;, &#x201C;Continent&#x201D;). Temporal patterns in the density of RT change-points for the majority of PAPs are rather erratic in the &#x201C;Arid&#x201D; climate-zone, where the patterns reveal a generally increasing trend from the early-Holocene to the recent times (<xref ref-type="fig" rid="F5">Figure 5</xref>, &#x201C;Climate-zone&#x201D;).</p>
</sec>
</sec>
<sec id="S4" sec-type="discussion">
<title>Discussion</title>
<p>Before discussing the spatial and temporal patterns of the PAPs, we briefly summarise the Holocene history of climate and vegetation in Asia to provide a background for interpreting the PAP patterns.</p>
<sec id="S4.SS1">
<title>Holocene climate and vegetation development</title>
<sec id="S4.SS1.SSS1">
<title>Climate</title>
<p>There is considerable debate about the fine-scale patterns and timing of Holocene climate change in Asia. However, there is a general consensus that humid and warmer conditions gradually increased in eastern and central Asia during the early-Holocene due to an increase in temperature and East Asian summer monsoon activity resulting in relatively wet conditions during the mid-Holocene, and a subsequent decline in precipitation (<xref ref-type="bibr" rid="B28">Chen F. et al., 2015</xref>, <xref ref-type="bibr" rid="B25">2019</xref>). Trends in temperature follow the general trend of precipitation but a steep increase in temperature trend has been observed over recent centuries (<xref ref-type="bibr" rid="B28">Chen F. et al., 2015</xref>). Arid central Asia experienced a cold dry climate during the early-Holocene, and possibly warmer climate conditions during the mid- to late-Holocene (<xref ref-type="bibr" rid="B119">Wang and Feng, 2013</xref>; <xref ref-type="bibr" rid="B25">Chen F. et al., 2019</xref>). Pollen-based climatic reconstructions for the Tibetan Plateau indicate progressively warmer and wetter conditions in the early- to mid-Holocene and a general trend of cooling and drying toward the present (<xref ref-type="bibr" rid="B55">Herzschuh et al., 2006</xref>; <xref ref-type="bibr" rid="B26">Chen et al., 2020</xref>; <xref ref-type="bibr" rid="B108">Sun and Feng, 2021</xref>). The Indian subcontinent experienced a rising trend in temperature and Indian summer monsoon rainfall during the early- to mid-Holocene. However, this trend was punctuated by a global cooling event around 8,000 cal year BP. Climate started to shift from warm humid to cool arid from the mid-Holocene and reached an arid phase during the late-Holocene (<xref ref-type="bibr" rid="B73">Laskar and Bohra, 2021</xref>). Inferences on palaeoclimate from various proxies (such as fossil pollen, diatom, and bio-chemical data) suggest that the early-Holocene in south-west Asia was characterised by dry and warm conditions, whereas the mid-Holocene was wetter and colder, and the late-Holocene was drier and warmer (<xref ref-type="bibr" rid="B78">Litt et al., 2012</xref>; <xref ref-type="bibr" rid="B29">Cheng et al., 2015</xref>). However, some regional palynological studies infer relatively humid conditions in the eastern Mediterranean region during and Levant the early-Holocene (e.g., <xref ref-type="bibr" rid="B24">Cheddadi and Rossignol-Strick, 1995</xref>; <xref ref-type="bibr" rid="B65">Kadosh et al., 2004</xref>; <xref ref-type="bibr" rid="B70">Langgut et al., 2011</xref>). This may be due to an extension of the monsoonal climate system combining with the Mediterranean climate system (<xref ref-type="bibr" rid="B99">Rossignol-Strick, 1985</xref>; <xref ref-type="bibr" rid="B100">Rossignol-strick, 1999</xref>; <xref ref-type="bibr" rid="B69">Langgut, 2018</xref>), where as only the latter now influences the present climate. Historically, Siberian climate varied broadly, being both warmer and colder than the present. However, during the past century, it became much warmer and winter precipitation north of 55&#x00B0; N increased (<xref ref-type="bibr" rid="B50">Groisman et al., 2013</xref>). The early-Holocene in Siberia was characterised by a warmer and wetter climate resulting in a change from severe continental climatic conditions to a milder climate. However, during this period, cooling was noted in southern Siberia. The thermal maximum was most strongly expressed in Siberia during the mid-Holocene, when conditions were warmer and wetter than the twentieth century climate (<xref ref-type="bibr" rid="B83">Monserud et al., 1995</xref>). The late-Holocene was characterised by dry and cool conditions, especially in western Siberia (<xref ref-type="bibr" rid="B67">Karpenko, 2006</xref>). Most of the present-day Siberian vegetation and ecosystems started to develop after ca. 3,000 cal year BP, when climatic conditions started to become cooler and drier.</p>
</sec>
<sec id="S4.SS1.SSS2">
<title>Vegetation development</title>
<p>In this section we summarise the modern vegetation and the Holocene vegetation development of the major areas in Asia from where pollen-stratigraphical data are used in our analyses. Southern Asia is not discussed because of a lack of any available palynological data. A summary of the area&#x2019;s vegetation and its vegetation history is given in the <xref ref-type="supplementary-material" rid="DS2">Supplementary Material 1</xref>.</p>
</sec>
<sec id="S4.SS1.SSS3">
<title>Eastern Asia</title>
<p>Natural vegetation here today changes from a moist coastal-forest zone to steppe/desert, following the south-east &#x2013; north-west precipitation gradient. Main vegetation types are broad-leaved, deciduous, and boreal coniferous forests. Alpine vegetation on the Tibetan Plateau consisting of montane forest, high meadow, steppe, semi-desert, and desert follows the south-east to north-west gradient of decreasing precipitation (<xref ref-type="bibr" rid="B59">Hou, 2001</xref>; <xref ref-type="bibr" rid="B18">Cao et al., 2015</xref>). During the early-Holocene, tropical and subtropical regions were colonised by thermophilous broad-leaved forest (dominant taxa <italic>Castanea, Castanopsis, Cyclobalanopsis, Fagus, Pterocarya</italic>, etc.). Forest expanded westward and achieved its maximum distribution and abundance during the early- or mid-Holocene, reflecting optimal regional conditions (<xref ref-type="bibr" rid="B18">Cao et al., 2015</xref>). Forest declined from the mid- to late-Holocene, probably in response to changes in regional climate and land-use (<xref ref-type="bibr" rid="B49">Gong et al., 2007</xref>; <xref ref-type="bibr" rid="B44">Fuller and Qin, 2010</xref>). Mixed broad-leaved forest (dominant taxa <italic>Juglans, Quercus, Tilia, Ulmus</italic>, etc.) was confined to the southern parts of eastern Asia and extended northward and increased in abundance during the early- to mid-Holocene. However, during the mid- to late-Holocene, mixed vegetation declined, and conifer taxa such as <italic>Abies, Picea</italic>, and <italic>Pinus</italic> increased in response to changes in regional climate, especially the weakening of the summer monsoon.</p>
<p>On the north-eastern border of the Tibetan Plateau, <italic>Picea</italic> together with <italic>Betula</italic> flourished during the early- to mid-Holocene, in response to increasingly humid conditions. However, <italic>Betula</italic> and <italic>Picea</italic> forests decreased regionally as conditions became drier during the mid- to late-Holocene and forest was replaced by alpine steppe vegetation (<xref ref-type="bibr" rid="B53">Herzschuh et al., 2010</xref>). Alpine steppe on the central and eastern Tibetan Plateau was relatively stable throughout the Holocene, with a gradual replacement of temperate steppe by high-alpine meadows during the mid- to late-Holocene. The northern and western parts were dominated by temperate desert through the Holocene (<xref ref-type="bibr" rid="B53">Herzschuh et al., 2010</xref>).</p>
</sec>
<sec id="S4.SS1.SSS4">
<title>Central Asia</title>
<p>Vegetation here consists of Irano-Turanian and Central-Asiatic floristic elements. The predominant ecosystems are desert, semi-desert, and steppe (<xref ref-type="bibr" rid="B131">Zhang Y. et al., 2020</xref>). The gravel-desert flora typically includes taxa in the genera <italic>Anabasis, Atraphaxis</italic>, <italic>Caragana, Halolachne, Salsola</italic>, and <italic>Seriphidium</italic>. Arid ecosystems prevail at low elevations and in the foothills. Grassland, shrub, and forest are widespread at mid-altitudes on mountain slopes. Meadow and tundra-like ecosystems are found at high elevations. <italic>Abies</italic> and <italic>Betula</italic> forests occur mainly in the Tian Shan Mountains, whereas old-growth <italic>Juniperus</italic> forests are more common in the Pamir-Altai Mountains. Patches of riverine woodland with <italic>Elaeagnus, Halostachys</italic>, <italic>Populus euphratica, Tamarix</italic>, and <italic>Ulmus</italic> occur along rivers and lake shores. Most of the area in the south and south-west is sandy desert, changing to steppe vegetation in the east. In the north, forests form a transition zone between Siberian taiga forest and central Asian steppe. Major elements of the taiga forest are <italic>Betula, Larix sibirica</italic>, <italic>Pinus sibirica</italic>, and <italic>Pinus sylvestris</italic> (<xref ref-type="bibr" rid="B131">Zhang Y. et al., 2020</xref>).</p>
<p>In lowland regions during the early-Holocene, there was low forest cover and a high representation of drought-tolerant species compared to the mid-Holocene. Forest in general increased after the mid-Holocene in the low-elevation basins and plains due to increased humidity (<xref ref-type="bibr" rid="B61">Huang et al., 2018</xref>; <xref ref-type="bibr" rid="B131">Zhang Y. et al., 2020</xref>). High-elevation valleys in the Altai were dominated by meadow-steppe vegetation during the early-Holocene, which was gradually replaced by taiga (dominated by <italic>Abies, Juniperus, Picea</italic>, and <italic>Pinus</italic>) from the early- to mid-Holocene. Trees decreased after the mid-Holocene (<xref ref-type="bibr" rid="B15">Blyakharchuk et al., 2007</xref>; <xref ref-type="bibr" rid="B61">Huang et al., 2018</xref>), and steppe-meadow expanded since the mid-Holocene (<xref ref-type="bibr" rid="B15">Blyakharchuk et al., 2007</xref>; <xref ref-type="bibr" rid="B131">Zhang Y. et al., 2020</xref>).</p>
</sec>
<sec id="S4.SS1.SSS5">
<title>South-west Asia (Levant region)</title>
<p>Vegetation here can be broadly grouped into five phytogeographic divisions: Mediterranean, Irano-Turanian, Saharo-Arabian, Sudano-Zambesian, and Euro-Siberian (<xref ref-type="bibr" rid="B103">Schiebel, 2013</xref>). Mediterranean vegetation, mainly distributed around the Mediterranean Sea is dominated by oaks (e.g., <italic>Quercus calliprinos</italic> and <italic>Q. ithaburensis</italic>), as well as olive (<italic>Olea europaea</italic>) and pistachio (<italic>Pistacia lentiscus</italic>) (<xref ref-type="bibr" rid="B103">Schiebel, 2013</xref>). Irano-Turanian vegetation in the Asian steppes of the Syrian Desert, Iran, Anatolia in Turkey, and Gobi Desert supports <italic>Achillea santolina</italic>, <italic>Artemisia herba-alba</italic>, <italic>Thymelaea hirsuta</italic>, and several Poaceae and Amaranthaceae taxa. Sudano-Arabian vegetation is distributed in the Sahara, Sinai, and Arabian deserts and is characterised by many Amaranthaceae and <italic>Tamarix</italic> taxa. Sudano-Zambesian vegetation is mainly distributed in the subtropical savannahs of Africa and in oases along the Jordan Valley. Major taxa include <italic>Acacia, Balanites aegyptiaca</italic>, and <italic>Phoenix dactylifera</italic> (<xref ref-type="bibr" rid="B135">Zohary, 1982</xref>; <xref ref-type="bibr" rid="B103">Schiebel, 2013</xref>). Euro-Siberian vegetation grows mainly in damp habitats, along the Mediterranean coasts, and to the north of Mount Hermon (south-eastern Turkey). This vegetation consists of broad-leaved (<italic>Carpinus betulus, Cornus mas, Fagus orientalis, Ilex aquifolium, Quercus</italic>, etc.), beech (<italic>Fagus, Alnus</italic>, <italic>Ulmus</italic>, etc.), chestnut (<italic>Castanea sativa</italic>), alder (<italic>Alnus barbata</italic>), coniferous (<italic>Picea orientalis, P. sylvestris</italic>, etc.), and dry (<italic>Juniperus oxycedrus</italic>) forests (<xref ref-type="bibr" rid="B1">Atalay, 1986</xref>).</p>
<p>Palynological studies suggest that at the onset of the Holocene, vegetation was dominated by steppe and grasslands with <italic>Artemisia</italic> and members of the Amaranthaceae, Apiaceae, and Poaceae. This was gradually replaced by open oak-pistachio forest-steppe vegetation and then by forest from the early- to mid-Holocene. Forest vegetation consisted of oaks (<italic>Quercus</italic> spp.), conifers (<italic>Pinus</italic> and <italic>Abies</italic>), and broad-leaved species such as <italic>Acer, Alnus, Carpinus, Corylus, Fagus, Pistacia</italic>, <italic>Tilia</italic>, and <italic>Ulmus</italic>. This forest started to decline from the mid-Holocene and modern vegetation developed during the mid- to late-Holocene (e.g., <xref ref-type="bibr" rid="B118">Van Zeist and Wright, 1963</xref>; <xref ref-type="bibr" rid="B127">Wright, 1976</xref>; <xref ref-type="bibr" rid="B117">Van Zeist and Bottema, 1991</xref>).</p>
</sec>
<sec id="S4.SS1.SSS6">
<title>Siberia</title>
<p>Siberian vegetation can be summarised in latitudinal vegetation zones (<xref ref-type="bibr" rid="B102">Safronova and Yurkovsksya, 2019</xref>). The tundra zone occupies the northern part. High Arctic tundra consists of herb-lichen-moss associations, with <italic>Alopecurus magellanicus</italic>, <italic>Papaver polare</italic>, and <italic>Saxifraga</italic> spp., whereas the central and southern tundra is dominated by low-shrub species such as <italic>Arctous alpina, Betula nana</italic>, and <italic>Cassiope tetragona</italic>. The taiga zone extends between ca. 52&#x00B0; N and 72&#x00B0; N latitude, mainly in western and central Siberia. It is dominated by conifers such as <italic>Larix gmelinii</italic>, <italic>L. sibirica, Picea obovata, Pinus sibirica</italic>, and <italic>P. sylvestris</italic>, and with scrub and woodlands of <italic>Betula pendula, B. pubescens, Populus tremula</italic>, and <italic>Salix</italic> spp. Almost half of this zone is occupied by mires. The forest-steppe zone occurs south of ca. 56&#x00B0; N in western Siberia and is dominated by birch-aspen (<italic>B. pendula</italic> and <italic>P. tremula</italic>) forest. The zone also contains meadow steppes, which are fragmentary and occur only in the southern region of western Siberia.</p>
<p>Pollen studies show that at the onset of the Holocene north-eastern Siberia supported cold and drought-resistant tundra and steppe plant communities with <italic>Artemisia</italic>, <italic>Betula</italic>, and members of the Poaceae and Amaranthaceae. <italic>Betula</italic> and <italic>Larix</italic> forests occupied flood plains. Warmer, humid climate during the early-Holocene favoured the replacement of tundra&#x2013;steppe vegetation by spruce and larch forest-tundra with a shrub understory. In north-eastern Siberia, warmer and drier conditions during the early-Holocene also resulted in the spread of <italic>Betula nana &#x2013; Duschekia fruticosa</italic> shrub-tundra. In southern Siberia, the Holocene onset is marked by an increase in woody cover in response to significant climate amelioration. In the southern taiga of Siberia, forests of <italic>Abies sibirica, Picea obovata, Pinus sibirica</italic>, and <italic>P. sylvestris</italic> spread. In the northern Arctic belt, <italic>Betula exilis, Duschekia fruticosa</italic>, and <italic>Larix dahurica</italic> forests dominated the area during the early- to mid-Holocene. After the mid-Holocene, when climate became cooler and drier, afforestation of forest-steppe by cold- and drought-tolerant birch forest, freezing of wet mires in the taiga, and the formation of palsa bogs occurred. During this period, relatively thermophilous <italic>Abies</italic> forests retreated southward to the position of the present southern taiga, widespread expansion of <italic>Pinus sibirica</italic> occurred, and forest vegetation retracted from the high mountain areas of the Altai. The late-Holocene is characterised by a continuous cold and dry phase, resulting in a southward retreat of the northern boundary of the forest zone to reach its present position (<xref ref-type="bibr" rid="B15">Blyakharchuk et al., 2007</xref>; <xref ref-type="bibr" rid="B14">Blyakharchuk, 2009</xref>; <xref ref-type="bibr" rid="B50">Groisman et al., 2013</xref>).</p>
</sec>
</sec>
<sec id="S4.SS2">
<title>Spatial patterns of pollen-compositional turnover and change</title>
<p>We observe considerable variation in total temporal compositional turnover (gradient length) and change (MRT partitions) across the records. However, there is only a gradual latitudinal variation in both the PAPs (<xref ref-type="fig" rid="F1">Figures 1</xref>, <xref ref-type="fig" rid="F2">2</xref>). Latitudinal variation in compositional change may be primarily due to the south-north gradient of major climatic factors, with southern Asia being warmer and wetter than the northern Siberian region, a pattern that likely persisted through the Holocene (<xref ref-type="bibr" rid="B98">Rohling et al., 2009</xref>; <xref ref-type="bibr" rid="B29">Cheng et al., 2015</xref>). Temporally consistent higher environmental stress toward the higher latitudes might have resulted in strong environmental filtering in these regions throughout the Holocene, thereby allowing only taxa with specialised environmental niches to coexist. Consequently compositional heterogeneity along the entire temporal gradient (age) of the records from high latitudes was lower than in the records from lower latitudes. Another potential factor for the higher number of MRT partitions in the records from low- to mid-latitudes is anthropogenic land-use change at these latitudes. Low- to mid-latitude regions in Asia, such as the Levant region, eastern China, and south-east Asia were settled extensively by humans in the early- to mid-Holocene who initiated agriculture and livestock farming (e.g., <xref ref-type="bibr" rid="B42">Flenley, 1988</xref>; <xref ref-type="bibr" rid="B16">Bottema, 1992</xref>; <xref ref-type="bibr" rid="B95">Ren, 2000</xref>; <xref ref-type="bibr" rid="B44">Fuller and Qin, 2010</xref>; <xref ref-type="bibr" rid="B45">Fuller et al., 2011</xref>; <xref ref-type="bibr" rid="B2">Bakker et al., 2012</xref>; <xref ref-type="bibr" rid="B60">Huang et al., 2017</xref>; <xref ref-type="bibr" rid="B30">Cheng et al., 2018</xref>; <xref ref-type="bibr" rid="B121">Whitlam et al., 2018</xref>) (see the Holocene climate and vegetation development sections for Levant and central Asia), thereby altering the natural ecosystems in various ways. This may have increased fine-scale habitat heterogeneity over time, and together with relatively mild climate conditions in the regions throughout the Holocene, may have allowed taxa of diverse niches to coexist via increasing dispersal and establishment, thereby increasing overall species heterogeneity. No clear latitudinal trend in compositional variation toward southern Asia may be due to the very low density of records south of ca. 25&#x00B0; N.</p>
<p>Longitudinal variation in compositional turnover (<xref ref-type="fig" rid="F1">Figure 1</xref>) and change (<xref ref-type="fig" rid="F2">Figure 2</xref>) possibly reflects the influence of climatic factors (especially precipitation regimes) and anthropogenic land-use change along the spatial and the temporal gradients. The Mediterranean climate system forms a prominent west-east winter precipitation gradient (<xref ref-type="bibr" rid="B25">Chen F. et al., 2019</xref>), where precipitation decreases from the western Levant region (Turkey) to arid central Asia. Moreover, there may also have been temporal variation in the precipitation (moisture) regime in South-western Asia, where environmental conditions were relatively humid during the early-Holocene (e.g., <xref ref-type="bibr" rid="B24">Cheddadi and Rossignol-Strick, 1995</xref>; <xref ref-type="bibr" rid="B65">Kadosh et al., 2004</xref>; <xref ref-type="bibr" rid="B70">Langgut et al., 2011</xref>). However, drier conditions prevailed since the mid-Holocene as the influence of the monsoon climate system faded leaving only the Mediterranean climate system active in the region. South-western Asia (Levant) is the region with one of the oldest human civilisations in Asia (<xref ref-type="bibr" rid="B62">Issar and Zohar, 2004</xref>), where agricultural practices most likely started during the early-Holocene with the domestication of important crop plants (<xref ref-type="bibr" rid="B126">Wright, 1968</xref>, <xref ref-type="bibr" rid="B127">1976</xref>; <xref ref-type="bibr" rid="B115">Van Zeist, 1976</xref>; <xref ref-type="bibr" rid="B16">Bottema, 1992</xref>) (see the Holocene climate and vegetation development sections for Levant and central Asia). The higher values of temporal turnover and compositional change probably reflect the anthropogenic modification of the natural ecosystems in this region from the beginning of the Holocene. On the other hand, south-west Asia is reported to have experienced profound climatic variations (especially moisture conditions) during the Holocene, resulting in a significant impact on regional vegetation and human societies (<xref ref-type="bibr" rid="B32">Cullen et al., 2000</xref>; <xref ref-type="bibr" rid="B106">Staubwasser and Weiss, 2006</xref>; <xref ref-type="bibr" rid="B66">Kaniewski et al., 2013</xref>; <xref ref-type="bibr" rid="B72">Langgut et al., 2014</xref>; <xref ref-type="bibr" rid="B75">Leipe et al., 2014</xref>; <xref ref-type="bibr" rid="B87">Palmisano et al., 2019</xref>; <xref ref-type="bibr" rid="B120">Watanabe et al., 2019</xref>). Such an interplay of the spatially as well as temporally varying climatic changes and human land-use change probably influenced the spatial variation in vegetation composition in the region. Indeed, we observe higher compositional turnover in areas with higher temporal variation in climate and land-use (variation in habitat heterogeneity) resulting in larger temporal changes in vegetation, whereas lower compositional turnover occurred in areas with consistent environmental stress throughout the period that may have prevented colonisation of species with different ecological niches. Similarly, the south-east &#x2013; west precipitation gradient formed by the East Asian summer monsoon (<xref ref-type="bibr" rid="B19">Cao et al., 2013</xref>), and anthropogenic land-use changes in south-eastern to central Asian region during the Holocene (<xref ref-type="bibr" rid="B95">Ren, 2000</xref>; <xref ref-type="bibr" rid="B44">Fuller and Qin, 2010</xref>; <xref ref-type="bibr" rid="B45">Fuller et al., 2011</xref>; <xref ref-type="bibr" rid="B109">Tan et al., 2015</xref>; <xref ref-type="bibr" rid="B30">Cheng et al., 2018</xref>) might have influenced the spatio-temporal variation in vegetation composition in the region (see the Holocene climate and vegetation development sections for eastern and central Asia). Hence, a gradual rise in compositional change in the eastern Asian region (<xref ref-type="fig" rid="F1">Figures 1C</xref>, <xref ref-type="fig" rid="F2">2C</xref>) may be a result of an interaction between regional climate (mostly spatio-temporal variations in precipitation), human land-use changes, and fine-scale ecological processes of successional changes in vegetation in the mid- and low-latitude regions of eastern Asia during the Holocene.</p>
<p>Despite the enormous environmental variation along the latitudinal and longitudinal gradient in Asia during the Holocene, observed variation in total temporal compositional turnover and change along these gradients is lower than that would be expected when dealing with real vegetation. This is probably because pollen analysis is limited by rather crude taxonomic identification and pollen representation, and therefore the actual magnitude of change is difficult to infer. There is low temporal variation in the composition of the most frequent pollen-types (&#x223C; major taxa or vegetation types) identified from the records. Compositional variation of less frequent pollen- or vegetation-types may not be represented well in sediments and hence is masked by the counts of the numerically dominant pollen-types. Moreover, there is considerable inconsistency in the nomenclature of pollen taxa (morpho-types) in the raw records, and therefore nomenclature of the pollen taxa is, by necessity, standardised to the taxonomically most robust pollen morpho-types identified by most palynologists. This is broadly equivalent to the plant family level. Hence, variations occurring at finer taxonomic levels (species and/or genus) are aggregated to a higher taxonomic level and thus only major ecological changes at a higher level are revealed in a synthetic study.</p>
</sec>
<sec id="S4.SS3">
<title>Cross-scale patterns of pollen-assemblage composition and diversity estimates</title>
<p>We observe considerable variation in the temporal patterns of the PAPs across the spatial scales of analyses. Finer-scale spatio-temporal variations in PAPs are mostly observed at the scale of individual records, likely in response to fine-scale climatic variations, land-use change, various disturbance events, and site-conditions. Consequently, there is enormous variation in the record-scale temporal patterns of all PAPs, and when these patterns are plotted together, a gradual common pattern exhibited by most of the records is potentially biased by the extreme patterns of a few records formed by extremely high or low values of PAP estimates along the <italic>Y</italic>-axis of the diagrams (<xref ref-type="fig" rid="F4">Figures 4</xref>, <xref ref-type="fig" rid="F5">5</xref>, &#x201C;record&#x201D;). However, these become smoothed as we aggregate the records within climate-zones because PAP estimates of most of the records in each climate-zone consistently exhibit only the major temporal pattern in response to the major underlying drivers, which also hold true for the continent-scale patterns.</p>
<sec id="S4.SS3.SSS1">
<title>Taxonomic richness, diversity, and evenness</title>
<p>Rather heterogeneous temporal variation in the observed record-scale patterns of Hill&#x2019;s indices (richness, diversity, and evenness) suggests a lack of synchronicity in the patterns (see above) (<xref ref-type="fig" rid="F4">Figure 4</xref>, &#x201C;N0, N1, N2, N2/N1, N1/N0: record&#x201D;). However, when we aggregate the estimates of records into different climate-zones and the whole continent, record-specific spatio-temporal variations are averaged or smoothed slightly, and only the minimal general temporal pattern exhibited by the majority of the records in each aggregation are observed.</p>
<p>Temporal patterns of Hill&#x2019;s indices at the level of climate-zone (<xref ref-type="fig" rid="F4">Figure 4</xref>) are likely to reflect the broad-scale vegetation successional development in response to climatic (temperature and precipitation) and human land-use drivers during the Holocene (see above). Mostly, major expansion in forest biomes at the onset of the Holocene (<xref ref-type="bibr" rid="B21">Cao et al., 2019a</xref>,<xref ref-type="bibr" rid="B22">b</xref>) driven by climate change (progressively developed warmer and humid conditions) (see the Holocene climate and vegetation development sections for eastern and central Asia) may have resulted in a reduced taxon (&#x223C; pollen) richness (N0) from the early- to mid-Holocene. A progressive cooling and drying in most parts of the continent during the mid-Holocene resulted in a marked decline in forests with a southward retreat of the forests at higher latitudes, retreat of scrub from arid central Asia, and a decline of total vegetation in subtropical Asia during the period (<xref ref-type="bibr" rid="B21">Cao et al., 2019a</xref>,<xref ref-type="bibr" rid="B22">b</xref>; <xref ref-type="bibr" rid="B33">Dallmeyer et al., 2021</xref>). Monodominant coniferous forests that developed during the early- to mid-Holocene in most of the climate-zones might also have negatively altered habitat conditions (increased aridity, formation of acidic soil, etc.) for the development of understorey (shrub and herb) plant diversity. Extensive anthropogenic land-use change in, for example, eastern (<xref ref-type="bibr" rid="B95">Ren, 2000</xref>; <xref ref-type="bibr" rid="B77">Li et al., 2009</xref>; <xref ref-type="bibr" rid="B30">Cheng et al., 2018</xref>) and south-west (e.g., <xref ref-type="bibr" rid="B2">Bakker et al., 2012</xref>) Asia (see the Holocene climate and vegetation development sections for eastern, central, and south-west Asia) might also have amplified the decrease in vegetation cover as well as taxon richness (Hill&#x2019;s N0) during the early- to mid-Holocene. However, the decrease in forest cover and subsequent increase in scrub and grasslands in some of the climate-zones (e.g., &#x201C;Cold without dry season,&#x201D; &#x201C;Arid&#x201D; zones) during the mid- to late-Holocene, may be a reflection of habitat diversification via changes in regional climate and anthropogenic disturbance regimes (grazing, fire, logging, agricultural activities, etc.). These resulted in a greater variety of habitats, including meadow development, thus increasing pollen diversity. This continent-scale temporal pattern of Hill&#x2019;s N0 is almost similar to the temporal pattern of plant taxa richness documented by a recent sedimentary-DNA based study from the Tibetan Plateau (<xref ref-type="bibr" rid="B80">Liu et al., 2021</xref>), which assigns the observed pattern to changes in regional climatic conditions and anthropogenic disturbances, especially livestock grazing. Consequently, the number of equally abundant taxa in the vegetation and thus in the pollen rain may have increased slightly from the early-Holocene to the present, resulting in a gradual temporal increase in Hill&#x2019;s diversity estimates in the majority of climate-zones (<xref ref-type="fig" rid="F4">Figure 4</xref>, &#x201C;N1 and N2: climate-zone&#x201D;). Abundance, and hence evenness, of forest or other major woody taxa was possibly maximal during the early- to mid-Holocene in response to progressively warmer and humid climatic conditions (see the Holocene climate and vegetation development section). However, as the regional climate started to become cooler and/or drier, and human pressure on the landscapes increased, dominant forest taxa in many of the climate-zones decreased resulting in a gradual decrease in evenness estimates from the mid- to late-Holocene (<xref ref-type="fig" rid="F4">Figure 4</xref>, N2 divided by N1 and N1 divided by N0: &#x201C;climate-zone&#x201D;).</p>
<p>Pollen richness (N0) and diversity (N1 and N2) in the &#x201C;Temperate zone&#x201D; (<xref ref-type="fig" rid="F4">Figure 4</xref>, &#x201C;N0, N1, and N2: climate-zone&#x201D;) show small but an opposite temporal trends. Optimal climate conditions for forest development in the present &#x201C;Temperate&#x201D; climate-zone (Asian monsoon climate-zone) that developed during the early- to mid-Holocene (see the Holocene climate and vegetation development section for the eastern Asia) favoured the expansion of broad-leaved forests and resulted in a significant reduction of arid vegetation (<xref ref-type="bibr" rid="B129">Yu et al., 2000</xref>; <xref ref-type="bibr" rid="B96">Ren, 2007</xref>; <xref ref-type="bibr" rid="B133">Zhao et al., 2009</xref>; <xref ref-type="bibr" rid="B18">Cao et al., 2015</xref>; <xref ref-type="bibr" rid="B113">Tian et al., 2016</xref>). A gradual replacement of steppe and steppe-savanna in the current Temperate zone by broad-leaved forests might have enhanced taxa richness as well as diversity initially. However, as the dense broad-leaved forests reached their mature stage, canopy closure may have resulted in unfavourable conditions for shade-intolerant understorey vegetation. Subsequently, changes in regional climatic conditions and increasing human land-use during the mid- to late-Holocene caused a decline in forests (<xref ref-type="bibr" rid="B49">Gong et al., 2007</xref>; <xref ref-type="bibr" rid="B44">Fuller and Qin, 2010</xref>), and may have negatively impacted richness and diversity of major forest taxa in this climate-zone.</p>
<p>The &#x201C;Cold without dry season&#x201D; climate-zone is represented by boreal vegetation, the temporal dynamics of which were likely driven by climatic changes. Pollen studies show that during the onset of the Holocene much of this zone was covered by cold, drought-resistant tundra and steppe plant communities with dwarf <italic>Betula, Artemisia</italic>, and members of the Poaceae and Amaranthaceae (<xref ref-type="bibr" rid="B50">Groisman et al., 2013</xref>). A warmer and humid climate during the early-Holocene favoured the replacement of tundra&#x2013;steppe vegetation by forest mainly dominated by <italic>Abies</italic>, <italic>Larix</italic>, <italic>Picea</italic>, <italic>Pinus</italic>, etc., which negatively impacted the diversity of the less dominant herbaceous and shrub taxa. The climate progressively became cooler and drier after the mid-Holocene which caused the southward retreat of the relatively thermophilous coniferous forests (see the Holocene climate and vegetation development section for Siberia, and central and eastern Asia). This would have favoured the development of steppe, tundra, and meadow vegetation with a higher diversity of herbaceous and shrub taxa, thus explaining the climate-zone level temporal pattern of N1 and N2 observed in <xref ref-type="fig" rid="F4">Figure 4</xref> (&#x201C;N1 and N2: climate-zone&#x201D;). Continental-scale temporal patterns in Hill&#x2019;s richness, diversity, and evenness estimates generally reflect the trends revealed in majority of the climate-zones (<xref ref-type="fig" rid="F4">Figure 4</xref>, &#x201C;N0, N1, N2, N2 divided by N1, and N1 divided by N0: continent&#x201D;).</p>
</sec>
<sec id="S4.SS3.SSS2">
<title>Pollen-compositional turnover and change</title>
<p>The higher heterogeneity in the temporal patterns of turnover at the record level (<xref ref-type="fig" rid="F4">Figure 4</xref>, &#x201C;DCCA1: record&#x201D;), but slightly smoothed and more pronounced DCCA1 temporal patterns at the climate-zone- and continent-scales (<xref ref-type="fig" rid="F4">Figure 4</xref>, &#x201C;DCCA1: record and continent&#x201D;), are likely a response to major underlying drivers (see above for possible explanations). However, of the temporal patterns analysed, those of temporal compositional turnover are relatively more consistent across the spatial scales of analysis. This indicates that pollen-compositional turnover has changed substantially and consistently from the beginning of the Holocene to the present throughout the whole of Asia. Based on studies on vegetation and climate history in Asia (see the Holocene climate and vegetation development section), this pattern suggests that temporal changes in turnover followed the major temporal climatic gradient of the Holocene at the continental scale, i.e., becoming progressively cooler and drier from the early- to late-Holocene (see the Holocene climate and vegetation development section for details). Progressively increasing environmental stress from the early- to late-Holocene probably increased environmental filtering in the regional assemblages, resulting in compositionally homogenous assemblages temporally. As a result, sample-to-sample compositional dissimilarity (turnover) decreased temporally throughout the analysed records. Broadly consistent with this trend, distributional as well as compositional changes in Holocene vegetation throughout the continent in response to temporal changes in climate have also been documented by recent broad-scale studies (e.g., <xref ref-type="bibr" rid="B21">Cao et al., 2019a</xref>,<xref ref-type="bibr" rid="B22">b</xref>; <xref ref-type="bibr" rid="B54">Herzschuh et al., 2019</xref>; <xref ref-type="bibr" rid="B33">Dallmeyer et al., 2021</xref>).</p>
</sec>
<sec id="S4.SS3.SSS3">
<title>Rate of pollen-compositional change</title>
<p>Rates of pollen-compositional change vary along the temporal gradient of Holocene as well as across the spatial scales (<xref ref-type="fig" rid="F4">Figure 4</xref>, &#x201C;RoC&#x201D;). Lack of a general temporal pattern in the RoC estimates at the record level is likely due to the heterogeneous record-specific patterns (see above for possible explanations). However, at the climate-zone scale (<xref ref-type="fig" rid="F4">Figure 4</xref>, &#x201C;RoC: climate-zone&#x201D;), a general pattern of slightly gradually declining RoC from the early-Holocene to the present is detectable. The Holocene-wide pattern of RoC in Asia is partly consistent with the global as well as continental RoC patterns presented by <xref ref-type="bibr" rid="B84">Mottl et al. (2021a)</xref>, despite the fact that the spatial density of the analysed records and the length of temporal gradient in our study differ from those used by <xref ref-type="bibr" rid="B84">Mottl et al. (2021a)</xref>. However, in contrast to the increasing late-Holocene RoC pattern in Asia revealed by <xref ref-type="bibr" rid="B84">Mottl et al. (2021a)</xref>, our study reveals a gradually linear-decreasing pattern of RoC in most of the climate-zones during the mid-Holocene to the present time. A pronounced rise in RoC in the &#x201C;Temperate&#x201D; climate-zone during the early- to mid-Holocene may be linked to climate change-driven vegetation changes in the region during the period (see the Holocene climate and vegetation development section for eastern Asia). Overall, a linear decline in RoC at the &#x201C;climate-zone&#x201D; scale is possibly driven by temporal variation in major regional climate and land-use changes during the Holocene, while an influence of shorter-term climatic fluctuations remains undetected in the RoC estimates at coarser spatial scales (see above for possible explanations). However, progressively increased aridity accompanied by divergent temporal temperature and land-use conditions in the different parts of &#x201C;Arid&#x201D; climate-zone in Asia, especially from the mid- to late-Holocene (see the Holocene climate and vegetation development section for south-west and central Asia), might have contributed to the temporal increase in RoC in the region (<xref ref-type="fig" rid="F4">Figure 4</xref>, &#x201C;RoC: climate-zone&#x201D;).</p>
</sec>
</sec>
<sec id="S4.SS4">
<title>Major temporal changes in the pollen-assemblage properties</title>
<p>Temporal patterns of major changes in PAPs (density of RT and MRT change-points), especially DCCA1, MRT, and RoC, are broadly consistent across spatial scales as well as across the PAPs (<xref ref-type="fig" rid="F5">Figure 5</xref>). An increase in the density of RT change-points for all PAPs from the early- to mid-Holocene, especially evident at the spatial scales of &#x201C;climate-zone&#x201D; and &#x201C;continent,&#x201D; implies that the greatest change in assemblage properties in all climate-zones was during the early- to mid-Holocene (12,000 to ca. 5,000&#x2013;7,000 cal year BP), probably in response to major temporal changes in climate, as suggested by the previous broad-scale studies from the region (<xref ref-type="bibr" rid="B21">Cao et al., 2019a</xref>,<xref ref-type="bibr" rid="B22">b</xref>). Fewer samples (less data) for the early-Holocene period may be another potential reason for the pattern (<xref ref-type="supplementary-material" rid="DS2">Supplementary Figure 1</xref>). From the mid-Holocene to recent times, temporal changes in PAPs are slightly less consistent across the spatial scales as well as across the properties (<xref ref-type="fig" rid="F5">Figure 5</xref>, &#x201C;climate-zone,&#x201D; &#x201C;continent&#x201D;). These patterns most likely indicate an influence of multiple interacting factors operating at various spatial and temporal scales, such as changes in climatic (e.g., <xref ref-type="bibr" rid="B79">Liu and Feng, 2012</xref>; <xref ref-type="bibr" rid="B75">Leipe et al., 2014</xref>; <xref ref-type="bibr" rid="B51">Gurjazkaite et al., 2018</xref>; <xref ref-type="bibr" rid="B120">Watanabe et al., 2019</xref>), and land-use changes including agriculture, fire, and livestock grazing, especially in the &#x201C;Arid&#x201D; (central and south-west Asia) and &#x201C;Temperate&#x201D; (eastern and south-east Asia) zones (e.g., <xref ref-type="bibr" rid="B95">Ren, 2000</xref>; <xref ref-type="bibr" rid="B77">Li et al., 2009</xref>; <xref ref-type="bibr" rid="B44">Fuller and Qin, 2010</xref>; <xref ref-type="bibr" rid="B45">Fuller et al., 2011</xref>; <xref ref-type="bibr" rid="B2">Bakker et al., 2012</xref>; <xref ref-type="bibr" rid="B4">Bhagwat et al., 2014</xref>; <xref ref-type="bibr" rid="B27">Chen F. H. et al., 2015</xref>; <xref ref-type="bibr" rid="B109">Tan et al., 2015</xref>; <xref ref-type="bibr" rid="B60">Huang et al., 2017</xref>; <xref ref-type="bibr" rid="B30">Cheng et al., 2018</xref>), combined with changes in local site conditions (see above). However, in general, a decrease in the density of RT and MRT change-points during the most recent period of the late-Holocene (ca. 0 to 3,000 cal year BP) (<xref ref-type="fig" rid="F5">Figure 5</xref>, &#x201C;climate-zone,&#x201D; &#x201C;continent&#x201D;) indicates that pollen assemblages and thus vegetation might have become more homogeneous during recent times, most likely in response to anthropogenic disturbances, as proposed by previous broad-scale studies (e.g., <xref ref-type="bibr" rid="B34">Daru et al., 2021</xref>).</p>
</sec>
</sec>
<sec id="S5" sec-type="conclusion">
<title>Conclusion</title>
<p>In our study, many of the PAPs revealed marked variation across space and time, responding to spatio-temporal changes in regional environmental conditions and land-use. Weakly pronounced spatial patterns and high heterogeneity in the temporal patterns across the records indicate the influence of fine-scale (record-specific) environmental drivers, site-conditions, and conservative data processing and standardisation procedures. Generally decreasing temporal trends in the major PAPs of compositional change (DCCA1, RoC, and MRT) at coarser spatial scales indicate that there may have been an overall gradual decline in pollen- (&#x223C; vegetation) compositional heterogeneity, especially during the most recent period of the late-Holocene. This implies that vegetation in many regions across Asia has become more homogenous during recent time. However, some of the observed patterns in PAPs have possibly revealed potential sensitivity to the density of high-quality pollen-data with uniform temporal resolution and data-standardisation procedures as well as the numerical approaches applied to summarise the PAPs.</p>
<p>Pollen-assemblage properties are &#x201C;hidden&#x201D; features within pollen-stratigraphic data. Exploration of the cross-scale spatial and temporal patterns in PAP throughout a continent is a novel and challenging approach and is potentially useful for summarising ecological features of pollen assemblages over time and space. Otherwise, qualitative studies of spatio-temporal variation in pollen-vegetation at the continent scale would require large numbers of pollen diagrams, maps, and taxon distribution models and it can become difficult to comprehend and interpret all the observed patterns. An ecological summary based on PAP analysis could be used to evaluate hypotheses of past vegetation and landscape dynamics using causational hypothesis-testing approaches. Multivariate analyses (e.g., ordinations) of pollen data or assessment of the spatio-temporal patterns of only selected taxa over a wide geographic extent with a large variation in climate, geography, and human-landscape interactions do not fully meet this objective. A future line of investigation could be to study PAPs over smaller areas such as climate or vegetation zones or areas with consistent amounts of human activity.</p>
<p>In future, our approach to spatio-temporal analysis of PAPs could be extended to other fields of palaeoecology, such as evolutionary palaeoecology to study the variation of pollen-based functional and phylogenetic diversity of co-occurring pollen-taxa at different temporal and spatial scales, and in biogeographical palaeoecology for comparing spatio-temporal patterns of PAPs in different phytogeographical areas or continents and in smaller selected areas. As this study highlights, PAP estimates vary considerably in both space and time. Resolving the causes of this variation is a challenge for future research.</p>
</sec>
<sec id="S6" sec-type="data-availability">
<title>Data availability statement</title>
<p>The majority of the datasets used in this study can be obtained via open-access resources: PANGAEA &#x2013; Data Publisher for Earth and Environmental Science and Neotoma Paleoecology Database. However, 63 datasets (dataset_id starts with &#x201C;PVT&#x201D;, see <xref ref-type="supplementary-material" rid="DS1">Supplementary Table 1</xref>) are obtained from data contributors and therefore, can only be obtained from data contributors. PAP estimates and R script used for data analyses, and visualization are available at GitHub (<ext-link ext-link-type="uri" xlink:href="https://github.com/HOPE-UIB-BIO/Asian_palynological_synthesis">https://github.com/HOPE-UIB-BIO/Asian_palynological_synthesis</ext-link>). The original contributions presented in this study are included in the article/<xref ref-type="supplementary-material" rid="DS2">Supplementary material</xref>, further inquiries can be directed to the corresponding author.</p>
</sec>
<sec id="S7" sec-type="author-contributions">
<title>Author contributions</title>
<p>KB: conception, data acquisition and assembly, data processing and analysis, and manuscript writing. OM: data processing, statistical analyses, visualisations, and manuscript reviewing. VF, SF, J-AG, and AS: data processing and manuscript reviewing. HHB: manuscript revision and editing, and overall support to the team. XC and FC: data acquisition, and manuscript reviewing and commenting. HJB: conception, data acquisition and pollen harmonisation, manuscript reviewing and editing, and funding. All authors contributed to the article and approved the submitted version.</p>
</sec>
</body>
<back>
<sec id="S8" sec-type="funding-information">
<title>Funding</title>
<p>KB, HHB, OM, VF, J-AG, AS, and SF were supported by the European Research Council (ERC) under the European Union&#x2019;s Horizon 2020 Research and Innovation Programme (grant agreement no. 741413) HOPE Humans on Planet Earth &#x2013; long-term impacts on biosphere dynamics awarded to HJB. This publication is a contribution to the HOPE project.</p>
</sec>
<ack><p>We are grateful to Ole R. Vetaas for providing valuable feedback during data processing, analysis, and manuscript writing. We are indebted to the many colleagues who have provided data directly or indirectly via their publications. Most of the data were obtained from the Neotoma Paleoecology Database (<ext-link ext-link-type="uri" xlink:href="http://www.neotomadb.org">http://www.neotomadb.org</ext-link>) and PANGAEA<sup>&#x00AE;</sup> &#x2013; Data Publisher for Earth and Environmental Science Database (<ext-link ext-link-type="uri" xlink:href="https://www.pangaea.de/">https://www.pangaea.de/</ext-link>). The work of data contributors, data stewards, and the Neotoma and Pangaea communities is gratefully acknowledged. We also appreciate the valuable comments from the reviewers. We thank Shonil Bhagwat, Jianhui Chen, and Feiya Lv for the data contribution.</p>
</ack>
<sec id="S9" sec-type="COI-statement">
<title>Conflict of interest</title>
<p>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.</p>
</sec>
<sec id="S10" sec-type="disclaimer">
<title>Publisher&#x2019;s note</title>
<p>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.</p>
</sec>
<sec id="S11" sec-type="supplementary-material">
<title>Supplementary material</title>
<p>The Supplementary Material for this article can be found online at: <ext-link ext-link-type="uri" xlink:href="https://www.frontiersin.org/articles/10.3389/fevo.2023.1115784/full#supplementary-material">https://www.frontiersin.org/articles/10.3389/fevo.2023.1115784/full#supplementary-material</ext-link></p>
<supplementary-material xlink:href="Data_Sheet_1.CSV" id="DS1" mimetype="text/csv" xmlns:xlink="http://www.w3.org/1999/xlink"/>
<supplementary-material xlink:href="Data_Sheet_2.docx" id="DS2" mimetype="application/vnd.openxmlformats-officedocument.wordprocessingml.document" xmlns:xlink="http://www.w3.org/1999/xlink"/>
</sec>
<fn-group>
<fn id="footnote1">
<label>1</label>
<p><ext-link ext-link-type="uri" xlink:href="http://www.europeanpollendatabase.net/">http://www.europeanpollendatabase.net/</ext-link></p></fn>
<fn id="footnote2">
<label>2</label>
<p><ext-link ext-link-type="uri" xlink:href="http://www.neotomadb.org">www.neotomadb.org</ext-link></p></fn>
<fn id="footnote3">
<label>3</label>
<p><ext-link ext-link-type="uri" xlink:href="https://www.pangaea.de/">https://www.pangaea.de/</ext-link></p></fn>
<fn id="footnote4">
<label>4</label>
<p><ext-link ext-link-type="uri" xlink:href="https://github.com/HOPE-UIB-BIO/R-Ecopol-package">https://github.com/HOPE-UIB-BIO/R-Ecopol-package</ext-link></p></fn>
</fn-group>
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