Jessie George, Monica Dimson, Regan E. Dunn, Emily L. Lindsey, Aisling B. Farrell, Brenda Paola Aguilar, Glen M. MacDonald
{"title":"拉布雷亚牧场(美国加利福尼亚州)杜松种子化石的鉴定:晚更新世的干旱与灭绝","authors":"Jessie George, Monica Dimson, Regan E. Dunn, Emily L. Lindsey, Aisling B. Farrell, Brenda Paola Aguilar, Glen M. MacDonald","doi":"10.1111/nph.20324","DOIUrl":null,"url":null,"abstract":"<h2> Introduction</h2>\n<p>The asphaltic fossil deposits at the Rancho La Brea (RLB) locality in Los Angeles, California, USA (Fig. 1) are internationally known for the preservation of Pleistocene mega-mammals such as sabertoothed cats (<i>Smilodon fatalis</i>), dire wolves (<i>Aenocyon dirus</i>), and Columbian mammoths (<i>Mammuthus columbi</i>). What is less known is that the asphaltic seeps also captured and preserved an abundance of plant macrofossils, including seeds, leaves, and wood, over the site's <i>c</i>. 60 000 yr (60 ka) depositional history. This provides an exceptional opportunity for long-term and taxonomically highly resolved vegetation reconstructions to be made across the Late Pleistocene and Holocene for southern California. While plant material has been identified in the past with species aligning to a broad diversity of California plant communities such as closed-cone conifer forests, coastal sage scrub, oak woodland, and chaparral (Frost, <span>1927</span>; Templeton, <span>1956</span>, <span>1964</span>; Warter, <span>1976</span>), before the present study, no effort has been made to radiocarbon date plant fossils or place them into any chronological context across the 60 ka preservational window at RLB. Such a record is critical in understanding the ecology of the RLB fauna.</p>\n<figure><picture>\n<source media=\"(min-width: 1650px)\" srcset=\"/cms/asset/aecd2724-afb4-425e-8aae-3cabeb8d6b52/nph20324-fig-0001-m.jpg\"/><img alt=\"Details are in the caption following the image\" data-lg-src=\"/cms/asset/aecd2724-afb4-425e-8aae-3cabeb8d6b52/nph20324-fig-0001-m.jpg\" loading=\"lazy\" src=\"/cms/asset/74e1a49e-99a5-4769-98e5-bda29bc5afdb/nph20324-fig-0001-m.png\" title=\"Details are in the caption following the image\"/></picture><figcaption>\n<div><strong>Fig. 1<span style=\"font-weight:normal\"></span></strong><div>Open in figure viewer<i aria-hidden=\"true\"></i><span>PowerPoint</span></div>\n</div>\n<div>Map of the location of the La Brea Tar Pit (Rancho La Brea) fossil deposits (a) within the Los Angeles Basin, (b) California, and (c) United States.</div>\n</figcaption>\n</figure>\n<p>During the past 60 ka, covering marine isotope stages (MISs) 3-1, significant long-term shifts in global climate occurred with the growth and decline of continental ice sheets. Abrupt millennial-scale climatic events including 17 Dansgaard–Oeschger (D-O) warming events and five of the more extreme cold intervals known as Heinrich stadials punctuated the glacial and interglacial phases, culminating in the Bølling–Allerød and Younger Dryas at the start of Holocene warming (Asmerom <i>et al</i>., <span>2010</span>; Wagner <i>et al</i>., <span>2010</span>; Renssen <i>et al</i>., <span>2018</span>). The environmental upheaval occurring at this time includes the spread of humans in North America (Bennett <i>et al</i>., <span>2021</span>) and the disappearance of much of the world's megafauna (Barnosky <i>et al</i>., <span>2011</span>; O'Keefe <i>et al</i>., <span>2023</span>). Plant macrofossils recovered from RLB provide a unique opportunity to track species-level responses to the extreme climatic and environmental shifts of the Late Quaternary, which in turn can offer key insights into the climate and environment during past megafauna extinction and potential vegetation range shifts with future anthropogenic warming.</p>\n<p>Seeds, leaves, and wood of <i>Juniperus</i> spp. are among the most commonly found plant fossils at RLB. <i>Juniperus</i> is a geographically widespread genus (Adams, <span>2014</span>) whose species are considered keystone taxa in woodland habitats as they modulate hydrology, nitrogen cycling (Miller & Wigand, <span>1994</span>), and land surface temperatures (Wang <i>et al</i>., <span>2021</span>), and provide food and habitat for a diversity of wildlife (Miller <i>et al</i>., <span>2019</span>). Within fossil contexts, particularly in packrat middens (Betancourt <i>et al</i>., <span>2001</span>, <span>2016</span>; Holmgren <i>et al</i>., <span>2006</span>, <span>2010</span>; Inman <i>et al</i>., <span>2018</span>), <i>Juniperus</i> spp. remnants serve as important paleoecological and paleoenvironmental indicators as they are particularly sensitive to changes in temperature, winter precipitation, and fire (Stevens <i>et al</i>., <span>2020</span>; Loehman <i>et al</i>., <span>2023</span>).</p>\n<h3> Juniper on the run</h3>\n<p>Recent decades have witnessed dramatic changes to juniper populations in the Northern Hemisphere, from slowed recruitment, dramatic die off, and fragmentation in their current geographic range (Fisher, <span>1997</span>; Breshears <i>et al</i>., <span>2005</span>; Lloret & García, <span>2016</span>; Lu <i>et al</i>., <span>2019</span>; Kannenberg <i>et al</i>., <span>2021</span>; Baker <i>et al</i>., <span>2024</span>), to active encroachment as invasive plants (Jackson <i>et al</i>., <span>2002</span>; Mueller <i>et al</i>., <span>2005</span>; Willson <i>et al</i>., <span>2008</span>; Wang <i>et al</i>., <span>2021</span>). <i>Juniperus</i> as a genus is considered drought tolerant, since many species demonstrate substantial resistance to water stress-induced xylem cavitation and the leaves can withstand long periods of negative water potential (Linton <i>et al</i>., <span>1998</span>; Maherali <i>et al</i>., <span>2004</span>; Mueller <i>et al</i>., <span>2005</span>; Willson <i>et al</i>., <span>2008</span>; Long <i>et al</i>., <span>2023</span>).</p>\n<p>Yet, juniper's ability to tolerate drought has its limits: Today, significant mortality of Utah juniper (<i>J. osteosperma</i>) is occurring in the American southwest due to extreme drought coupled with increased summer and annual temperatures (MacDonald, <span>2010</span>; Kannenberg <i>et al</i>., <span>2021</span>), particularly at the lower elevations (< 2000 m) of its geographical range. This same pattern has occurred repeatedly in the lowlands of southern California throughout glacial/interglacial cycles of the Late Quaternary (Woolfenden, <span>1996</span>; Heusser, <span>1998</span>; Davis, <span>1999</span>; Mensing, <span>2001</span>; Koehler <i>et al</i>., <span>2005</span>; Heusser <i>et al</i>., <span>2015</span>; McGann, <span>2015</span>).</p>\n<p>Sometime between the Late Pleistocene and today, naturally growing <i>Juniperus</i> spp. disappeared completely from the lowlands of southern California (O'Keefe <i>et al</i>., <span>2023</span>). The nearest populations of established juniper are scattered stands of <i>J. californica</i> in mountainous areas and rocky washes outside the Los Angeles Basin <i>c</i>. 20 km north of RLB at elevations between 900 and 2700 m (Calflora, <span>2023</span>), though isolated stands have been observed at lower elevations (< 100 m) in the nearby Santa Monica Mountains (Rundel & Stürmer, <span>1998</span>; Calflora, <span>2023</span>). However, during the Late Pleistocene, dominance of Cupressaceae pollen, likely of <i>Juniperus</i> spp., indicates that juniper was the most prevalent tree species growing at elevations as low as 377 m across southern California during glacial periods (Heusser, <span>1998</span>; Davis, <span>1999</span>; Mensing, <span>2001</span>; Heusser <i>et al</i>., <span>2015</span>). The great abundance of macrofossils preserved at RLB confirm <i>Juniperus</i> spp. as the dominant tree of Late Pleistocene woodlands in the region at even lower elevations (<i>c</i>. 58 m). In contrast to pollen, the occurrence of juniper seeds and branchlets at RLB allows for species-level identifications to be made and is representative of vegetation growing in the immediate area. <i>Juniperus</i> as a genus demonstrates significant interspecific variation in environmental tolerances (Miller & Wigand, <span>1994</span>; Lyford <i>et al</i>., <span>2003</span>). Therefore, having species-level identifications from fossil assemblages is necessary to understand how climatic changes have impacted ecosystems in the past, and how they are likely to impact them in the future (Schupp <i>et al</i>., <span>1997</span>; Dimitri <i>et al</i>., <span>2017</span>).</p>\n<h3> Juniper of Rancho La Brea</h3>\n<p>RLB's exceptional fossil record is the product of the combined presence of surficial pooling of asphalt from buried, Miocene age, oil-bearing strata, and alluvial deposition from the surrounding Santa Monica Mountains (Quinn, <span>1992</span>). Throughout the Late Pleistocene and Holocene, sticky asphalt pools trapped flora and fauna at the surface of the northern Los Angeles Basin (Akersten <i>et al</i>., <span>1983</span>; Spencer <i>et al</i>., <span>2003</span>). In areas near to seasonal streams, flood deposits buried entrapped organic tissue, and with the aid of continued asphalt seepage, tissues such as bone, chitin, calcium carbonate, cellulose, and lignin were preserved. Renewed asphalt seepage to the surface would eventually start the entrapment process again. The resulting ‘pockets’ of fossil material have no easily discernable stratigraphy or temporal associations and may represent periods of tens of thousands of years (Friscia <i>et al</i>., <span>2008</span>; Holden <i>et al</i>., <span>2017</span>). As a result of this age-mixing, determining relative abundances of species at discrete time intervals is not possible, hence we use presence/absence data for our study.</p>\n<p>Plant fossils recovered from RLB include seeds of two species of <i>Juniperus</i>: the large-seeded <i>J. californica</i> and a small-seeded juniper of uncertain affinity. Previously, the small-seeded juniper was described as <i>J. hanseni</i> n. sp., an extinct species (Templeton, <span>1964</span>). This identification was based on seed size and a qualitative assessment of resin pit arrangement when compared to extant juniper species with cones containing one or two seeds. However, Templeton's <i>J. hanseni</i> n. sp. description was never officially published, and occurrences of this taxon have not been reported outside of RLB. Given that only one plant species extinction has been documented from Late Quaternary macrofossil records in North America (Jackson & Weng, <span>1999</span>), it may be more likely that the small-seeded juniper of La Brea is from an extant juniper species now extirpated from southern California.</p>\n<p>The goals of this study are to identify the small-seeded juniper to species and to track the two juniper species occurrences at RLB through time. To determine the taxonomic affinity of the unknown juniper species, we compared branchlet and seed morphology of the fossils to selected extant taxa and produced hindcasted species distribution models (SDMs) for the last glacial maximum (LGM) for morphologically similar <i>Juniperus</i> species using their respective modern climate envelopes. To develop a timeline for juniper occurrences at RLB, we radiocarbon dated individual <i>Juniperus</i> seeds. Combined, these data allow us to trace juniper's history in the basin and investigate potential causes of its disappearance.</p>","PeriodicalId":214,"journal":{"name":"New Phytologist","volume":"28 1","pages":""},"PeriodicalIF":8.3000,"publicationDate":"2024-12-10","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"","citationCount":"0","resultStr":"{\"title\":\"Identification of fossil juniper seeds from Rancho La Brea (California, USA): drought and extirpation in the Late Pleistocene\",\"authors\":\"Jessie George, Monica Dimson, Regan E. Dunn, Emily L. Lindsey, Aisling B. Farrell, Brenda Paola Aguilar, Glen M. MacDonald\",\"doi\":\"10.1111/nph.20324\",\"DOIUrl\":null,\"url\":null,\"abstract\":\"<h2> Introduction</h2>\\n<p>The asphaltic fossil deposits at the Rancho La Brea (RLB) locality in Los Angeles, California, USA (Fig. 1) are internationally known for the preservation of Pleistocene mega-mammals such as sabertoothed cats (<i>Smilodon fatalis</i>), dire wolves (<i>Aenocyon dirus</i>), and Columbian mammoths (<i>Mammuthus columbi</i>). What is less known is that the asphaltic seeps also captured and preserved an abundance of plant macrofossils, including seeds, leaves, and wood, over the site's <i>c</i>. 60 000 yr (60 ka) depositional history. This provides an exceptional opportunity for long-term and taxonomically highly resolved vegetation reconstructions to be made across the Late Pleistocene and Holocene for southern California. While plant material has been identified in the past with species aligning to a broad diversity of California plant communities such as closed-cone conifer forests, coastal sage scrub, oak woodland, and chaparral (Frost, <span>1927</span>; Templeton, <span>1956</span>, <span>1964</span>; Warter, <span>1976</span>), before the present study, no effort has been made to radiocarbon date plant fossils or place them into any chronological context across the 60 ka preservational window at RLB. Such a record is critical in understanding the ecology of the RLB fauna.</p>\\n<figure><picture>\\n<source media=\\\"(min-width: 1650px)\\\" srcset=\\\"/cms/asset/aecd2724-afb4-425e-8aae-3cabeb8d6b52/nph20324-fig-0001-m.jpg\\\"/><img alt=\\\"Details are in the caption following the image\\\" data-lg-src=\\\"/cms/asset/aecd2724-afb4-425e-8aae-3cabeb8d6b52/nph20324-fig-0001-m.jpg\\\" loading=\\\"lazy\\\" src=\\\"/cms/asset/74e1a49e-99a5-4769-98e5-bda29bc5afdb/nph20324-fig-0001-m.png\\\" title=\\\"Details are in the caption following the image\\\"/></picture><figcaption>\\n<div><strong>Fig. 1<span style=\\\"font-weight:normal\\\"></span></strong><div>Open in figure viewer<i aria-hidden=\\\"true\\\"></i><span>PowerPoint</span></div>\\n</div>\\n<div>Map of the location of the La Brea Tar Pit (Rancho La Brea) fossil deposits (a) within the Los Angeles Basin, (b) California, and (c) United States.</div>\\n</figcaption>\\n</figure>\\n<p>During the past 60 ka, covering marine isotope stages (MISs) 3-1, significant long-term shifts in global climate occurred with the growth and decline of continental ice sheets. Abrupt millennial-scale climatic events including 17 Dansgaard–Oeschger (D-O) warming events and five of the more extreme cold intervals known as Heinrich stadials punctuated the glacial and interglacial phases, culminating in the Bølling–Allerød and Younger Dryas at the start of Holocene warming (Asmerom <i>et al</i>., <span>2010</span>; Wagner <i>et al</i>., <span>2010</span>; Renssen <i>et al</i>., <span>2018</span>). The environmental upheaval occurring at this time includes the spread of humans in North America (Bennett <i>et al</i>., <span>2021</span>) and the disappearance of much of the world's megafauna (Barnosky <i>et al</i>., <span>2011</span>; O'Keefe <i>et al</i>., <span>2023</span>). Plant macrofossils recovered from RLB provide a unique opportunity to track species-level responses to the extreme climatic and environmental shifts of the Late Quaternary, which in turn can offer key insights into the climate and environment during past megafauna extinction and potential vegetation range shifts with future anthropogenic warming.</p>\\n<p>Seeds, leaves, and wood of <i>Juniperus</i> spp. are among the most commonly found plant fossils at RLB. <i>Juniperus</i> is a geographically widespread genus (Adams, <span>2014</span>) whose species are considered keystone taxa in woodland habitats as they modulate hydrology, nitrogen cycling (Miller & Wigand, <span>1994</span>), and land surface temperatures (Wang <i>et al</i>., <span>2021</span>), and provide food and habitat for a diversity of wildlife (Miller <i>et al</i>., <span>2019</span>). Within fossil contexts, particularly in packrat middens (Betancourt <i>et al</i>., <span>2001</span>, <span>2016</span>; Holmgren <i>et al</i>., <span>2006</span>, <span>2010</span>; Inman <i>et al</i>., <span>2018</span>), <i>Juniperus</i> spp. remnants serve as important paleoecological and paleoenvironmental indicators as they are particularly sensitive to changes in temperature, winter precipitation, and fire (Stevens <i>et al</i>., <span>2020</span>; Loehman <i>et al</i>., <span>2023</span>).</p>\\n<h3> Juniper on the run</h3>\\n<p>Recent decades have witnessed dramatic changes to juniper populations in the Northern Hemisphere, from slowed recruitment, dramatic die off, and fragmentation in their current geographic range (Fisher, <span>1997</span>; Breshears <i>et al</i>., <span>2005</span>; Lloret & García, <span>2016</span>; Lu <i>et al</i>., <span>2019</span>; Kannenberg <i>et al</i>., <span>2021</span>; Baker <i>et al</i>., <span>2024</span>), to active encroachment as invasive plants (Jackson <i>et al</i>., <span>2002</span>; Mueller <i>et al</i>., <span>2005</span>; Willson <i>et al</i>., <span>2008</span>; Wang <i>et al</i>., <span>2021</span>). <i>Juniperus</i> as a genus is considered drought tolerant, since many species demonstrate substantial resistance to water stress-induced xylem cavitation and the leaves can withstand long periods of negative water potential (Linton <i>et al</i>., <span>1998</span>; Maherali <i>et al</i>., <span>2004</span>; Mueller <i>et al</i>., <span>2005</span>; Willson <i>et al</i>., <span>2008</span>; Long <i>et al</i>., <span>2023</span>).</p>\\n<p>Yet, juniper's ability to tolerate drought has its limits: Today, significant mortality of Utah juniper (<i>J. osteosperma</i>) is occurring in the American southwest due to extreme drought coupled with increased summer and annual temperatures (MacDonald, <span>2010</span>; Kannenberg <i>et al</i>., <span>2021</span>), particularly at the lower elevations (< 2000 m) of its geographical range. This same pattern has occurred repeatedly in the lowlands of southern California throughout glacial/interglacial cycles of the Late Quaternary (Woolfenden, <span>1996</span>; Heusser, <span>1998</span>; Davis, <span>1999</span>; Mensing, <span>2001</span>; Koehler <i>et al</i>., <span>2005</span>; Heusser <i>et al</i>., <span>2015</span>; McGann, <span>2015</span>).</p>\\n<p>Sometime between the Late Pleistocene and today, naturally growing <i>Juniperus</i> spp. disappeared completely from the lowlands of southern California (O'Keefe <i>et al</i>., <span>2023</span>). The nearest populations of established juniper are scattered stands of <i>J. californica</i> in mountainous areas and rocky washes outside the Los Angeles Basin <i>c</i>. 20 km north of RLB at elevations between 900 and 2700 m (Calflora, <span>2023</span>), though isolated stands have been observed at lower elevations (< 100 m) in the nearby Santa Monica Mountains (Rundel & Stürmer, <span>1998</span>; Calflora, <span>2023</span>). However, during the Late Pleistocene, dominance of Cupressaceae pollen, likely of <i>Juniperus</i> spp., indicates that juniper was the most prevalent tree species growing at elevations as low as 377 m across southern California during glacial periods (Heusser, <span>1998</span>; Davis, <span>1999</span>; Mensing, <span>2001</span>; Heusser <i>et al</i>., <span>2015</span>). The great abundance of macrofossils preserved at RLB confirm <i>Juniperus</i> spp. as the dominant tree of Late Pleistocene woodlands in the region at even lower elevations (<i>c</i>. 58 m). In contrast to pollen, the occurrence of juniper seeds and branchlets at RLB allows for species-level identifications to be made and is representative of vegetation growing in the immediate area. <i>Juniperus</i> as a genus demonstrates significant interspecific variation in environmental tolerances (Miller & Wigand, <span>1994</span>; Lyford <i>et al</i>., <span>2003</span>). Therefore, having species-level identifications from fossil assemblages is necessary to understand how climatic changes have impacted ecosystems in the past, and how they are likely to impact them in the future (Schupp <i>et al</i>., <span>1997</span>; Dimitri <i>et al</i>., <span>2017</span>).</p>\\n<h3> Juniper of Rancho La Brea</h3>\\n<p>RLB's exceptional fossil record is the product of the combined presence of surficial pooling of asphalt from buried, Miocene age, oil-bearing strata, and alluvial deposition from the surrounding Santa Monica Mountains (Quinn, <span>1992</span>). Throughout the Late Pleistocene and Holocene, sticky asphalt pools trapped flora and fauna at the surface of the northern Los Angeles Basin (Akersten <i>et al</i>., <span>1983</span>; Spencer <i>et al</i>., <span>2003</span>). In areas near to seasonal streams, flood deposits buried entrapped organic tissue, and with the aid of continued asphalt seepage, tissues such as bone, chitin, calcium carbonate, cellulose, and lignin were preserved. Renewed asphalt seepage to the surface would eventually start the entrapment process again. The resulting ‘pockets’ of fossil material have no easily discernable stratigraphy or temporal associations and may represent periods of tens of thousands of years (Friscia <i>et al</i>., <span>2008</span>; Holden <i>et al</i>., <span>2017</span>). As a result of this age-mixing, determining relative abundances of species at discrete time intervals is not possible, hence we use presence/absence data for our study.</p>\\n<p>Plant fossils recovered from RLB include seeds of two species of <i>Juniperus</i>: the large-seeded <i>J. californica</i> and a small-seeded juniper of uncertain affinity. Previously, the small-seeded juniper was described as <i>J. hanseni</i> n. sp., an extinct species (Templeton, <span>1964</span>). This identification was based on seed size and a qualitative assessment of resin pit arrangement when compared to extant juniper species with cones containing one or two seeds. However, Templeton's <i>J. hanseni</i> n. sp. description was never officially published, and occurrences of this taxon have not been reported outside of RLB. Given that only one plant species extinction has been documented from Late Quaternary macrofossil records in North America (Jackson & Weng, <span>1999</span>), it may be more likely that the small-seeded juniper of La Brea is from an extant juniper species now extirpated from southern California.</p>\\n<p>The goals of this study are to identify the small-seeded juniper to species and to track the two juniper species occurrences at RLB through time. To determine the taxonomic affinity of the unknown juniper species, we compared branchlet and seed morphology of the fossils to selected extant taxa and produced hindcasted species distribution models (SDMs) for the last glacial maximum (LGM) for morphologically similar <i>Juniperus</i> species using their respective modern climate envelopes. To develop a timeline for juniper occurrences at RLB, we radiocarbon dated individual <i>Juniperus</i> seeds. Combined, these data allow us to trace juniper's history in the basin and investigate potential causes of its disappearance.</p>\",\"PeriodicalId\":214,\"journal\":{\"name\":\"New Phytologist\",\"volume\":\"28 1\",\"pages\":\"\"},\"PeriodicalIF\":8.3000,\"publicationDate\":\"2024-12-10\",\"publicationTypes\":\"Journal Article\",\"fieldsOfStudy\":null,\"isOpenAccess\":false,\"openAccessPdf\":\"\",\"citationCount\":\"0\",\"resultStr\":null,\"platform\":\"Semanticscholar\",\"paperid\":null,\"PeriodicalName\":\"New Phytologist\",\"FirstCategoryId\":\"99\",\"ListUrlMain\":\"https://doi.org/10.1111/nph.20324\",\"RegionNum\":1,\"RegionCategory\":\"生物学\",\"ArticlePicture\":[],\"TitleCN\":null,\"AbstractTextCN\":null,\"PMCID\":null,\"EPubDate\":\"\",\"PubModel\":\"\",\"JCR\":\"Q1\",\"JCRName\":\"PLANT SCIENCES\",\"Score\":null,\"Total\":0}","platform":"Semanticscholar","paperid":null,"PeriodicalName":"New Phytologist","FirstCategoryId":"99","ListUrlMain":"https://doi.org/10.1111/nph.20324","RegionNum":1,"RegionCategory":"生物学","ArticlePicture":[],"TitleCN":null,"AbstractTextCN":null,"PMCID":null,"EPubDate":"","PubModel":"","JCR":"Q1","JCRName":"PLANT SCIENCES","Score":null,"Total":0}
引用次数: 0
摘要
在海拔900米至2700米之间的RLB以北约20公里(Calflora, 2023),尽管在附近的圣莫尼卡山脉(Rundel &;)的较低海拔(<; 100米)观察到孤立的林分。斯特姆苹果,1998;Calflora, 2023)。然而,在晚更新世,柏科花粉的优势,可能是杜松属的,表明在冰河时期,杜松是最普遍的树种,生长在南加州低至377米的海拔(Heusser, 1998;戴维斯,1999;心,2001;Heusser et al., 2015)。在RLB保存的大量大型化石证实了Juniperus spp.是该地区晚更新世林地的优势树种,海拔更低(约58 m)。与花粉相比,在RLB上出现的杜松种子和小枝允许进行物种水平的鉴定,并代表了附近地区的植被生长。杜松属在环境耐受性方面表现出显著的种间差异(Miller &;Wigand, 1994;Lyford et al., 2003)。因此,有必要从化石组合中进行物种水平的鉴定,以了解气候变化在过去如何影响生态系统,以及它们在未来可能如何影响生态系统(Schupp et al., 1997;Dimitri等人,2017)。Rancho La BreaRLB的Juniper独特的化石记录是埋藏中新世含油地层的地表沥青池和周围圣莫尼卡山脉的冲积沉积共同作用的产物(Quinn, 1992)。在整个晚更新世和全新世,黏糊糊的沥青池将洛杉矶盆地北部表面的动植物困住(Akersten et al., 1983;Spencer et al., 2003)。在靠近季节性溪流的地区,洪水沉积物掩埋了被困的有机组织,在持续的沥青渗漏的帮助下,骨骼、几丁质、碳酸钙、纤维素和木质素等组织得以保存。重新渗漏到地表的沥青最终会再次启动截留过程。由此产生的化石材料“口袋”没有容易识别的地层或时间关联,可能代表数万年的时期(Friscia et al., 2008;Holden et al., 2017)。由于这种年龄混合,在离散的时间间隔内确定物种的相对丰度是不可能的,因此我们使用存在/缺失数据进行研究。从RLB中发现的植物化石包括两种杜松的种子:大种子加利福尼亚杜松和一种亲和力不确定的小种子杜松。以前,小种子杜松被描述为J. hanseni n. sp.,一种灭绝的物种(Templeton, 1964)。这种鉴定是基于种子大小和树脂坑排列的定性评价,并与现存的松果含有一个或两个种子的杜松物种进行比较。然而,Templeton对J. hanseni n. sp.的描述从未正式发表过,该分类群在RLB之外的出现也未见报道。考虑到北美晚第四纪大化石记录中只有一种植物物种灭绝(Jackson &;Weng, 1999),更有可能的是,La Brea的小种子杜松来自于现在已经从南加州灭绝的现存杜松物种。本研究的目的是鉴定小种子杜松的种类,并追踪两种杜松在RLB的发生情况。为了确定未知树种的分类亲缘性,我们将化石的小枝和种子形态与选定的现存类群进行了比较,并在各自的现代气候包层下,对形态相似的杜松种建立了末次冰期极大期(LGM)的后延物种分布模型(SDMs)。为了制定一个在RLB的杜松发生的时间表,我们对单个杜松种子进行了放射性碳测年。综合起来,这些数据使我们能够追踪盆地中杜松的历史,并调查其消失的潜在原因。
Identification of fossil juniper seeds from Rancho La Brea (California, USA): drought and extirpation in the Late Pleistocene
Introduction
The asphaltic fossil deposits at the Rancho La Brea (RLB) locality in Los Angeles, California, USA (Fig. 1) are internationally known for the preservation of Pleistocene mega-mammals such as sabertoothed cats (Smilodon fatalis), dire wolves (Aenocyon dirus), and Columbian mammoths (Mammuthus columbi). What is less known is that the asphaltic seeps also captured and preserved an abundance of plant macrofossils, including seeds, leaves, and wood, over the site's c. 60 000 yr (60 ka) depositional history. This provides an exceptional opportunity for long-term and taxonomically highly resolved vegetation reconstructions to be made across the Late Pleistocene and Holocene for southern California. While plant material has been identified in the past with species aligning to a broad diversity of California plant communities such as closed-cone conifer forests, coastal sage scrub, oak woodland, and chaparral (Frost, 1927; Templeton, 1956, 1964; Warter, 1976), before the present study, no effort has been made to radiocarbon date plant fossils or place them into any chronological context across the 60 ka preservational window at RLB. Such a record is critical in understanding the ecology of the RLB fauna.
During the past 60 ka, covering marine isotope stages (MISs) 3-1, significant long-term shifts in global climate occurred with the growth and decline of continental ice sheets. Abrupt millennial-scale climatic events including 17 Dansgaard–Oeschger (D-O) warming events and five of the more extreme cold intervals known as Heinrich stadials punctuated the glacial and interglacial phases, culminating in the Bølling–Allerød and Younger Dryas at the start of Holocene warming (Asmerom et al., 2010; Wagner et al., 2010; Renssen et al., 2018). The environmental upheaval occurring at this time includes the spread of humans in North America (Bennett et al., 2021) and the disappearance of much of the world's megafauna (Barnosky et al., 2011; O'Keefe et al., 2023). Plant macrofossils recovered from RLB provide a unique opportunity to track species-level responses to the extreme climatic and environmental shifts of the Late Quaternary, which in turn can offer key insights into the climate and environment during past megafauna extinction and potential vegetation range shifts with future anthropogenic warming.
Seeds, leaves, and wood of Juniperus spp. are among the most commonly found plant fossils at RLB. Juniperus is a geographically widespread genus (Adams, 2014) whose species are considered keystone taxa in woodland habitats as they modulate hydrology, nitrogen cycling (Miller & Wigand, 1994), and land surface temperatures (Wang et al., 2021), and provide food and habitat for a diversity of wildlife (Miller et al., 2019). Within fossil contexts, particularly in packrat middens (Betancourt et al., 2001, 2016; Holmgren et al., 2006, 2010; Inman et al., 2018), Juniperus spp. remnants serve as important paleoecological and paleoenvironmental indicators as they are particularly sensitive to changes in temperature, winter precipitation, and fire (Stevens et al., 2020; Loehman et al., 2023).
Juniper on the run
Recent decades have witnessed dramatic changes to juniper populations in the Northern Hemisphere, from slowed recruitment, dramatic die off, and fragmentation in their current geographic range (Fisher, 1997; Breshears et al., 2005; Lloret & García, 2016; Lu et al., 2019; Kannenberg et al., 2021; Baker et al., 2024), to active encroachment as invasive plants (Jackson et al., 2002; Mueller et al., 2005; Willson et al., 2008; Wang et al., 2021). Juniperus as a genus is considered drought tolerant, since many species demonstrate substantial resistance to water stress-induced xylem cavitation and the leaves can withstand long periods of negative water potential (Linton et al., 1998; Maherali et al., 2004; Mueller et al., 2005; Willson et al., 2008; Long et al., 2023).
Yet, juniper's ability to tolerate drought has its limits: Today, significant mortality of Utah juniper (J. osteosperma) is occurring in the American southwest due to extreme drought coupled with increased summer and annual temperatures (MacDonald, 2010; Kannenberg et al., 2021), particularly at the lower elevations (< 2000 m) of its geographical range. This same pattern has occurred repeatedly in the lowlands of southern California throughout glacial/interglacial cycles of the Late Quaternary (Woolfenden, 1996; Heusser, 1998; Davis, 1999; Mensing, 2001; Koehler et al., 2005; Heusser et al., 2015; McGann, 2015).
Sometime between the Late Pleistocene and today, naturally growing Juniperus spp. disappeared completely from the lowlands of southern California (O'Keefe et al., 2023). The nearest populations of established juniper are scattered stands of J. californica in mountainous areas and rocky washes outside the Los Angeles Basin c. 20 km north of RLB at elevations between 900 and 2700 m (Calflora, 2023), though isolated stands have been observed at lower elevations (< 100 m) in the nearby Santa Monica Mountains (Rundel & Stürmer, 1998; Calflora, 2023). However, during the Late Pleistocene, dominance of Cupressaceae pollen, likely of Juniperus spp., indicates that juniper was the most prevalent tree species growing at elevations as low as 377 m across southern California during glacial periods (Heusser, 1998; Davis, 1999; Mensing, 2001; Heusser et al., 2015). The great abundance of macrofossils preserved at RLB confirm Juniperus spp. as the dominant tree of Late Pleistocene woodlands in the region at even lower elevations (c. 58 m). In contrast to pollen, the occurrence of juniper seeds and branchlets at RLB allows for species-level identifications to be made and is representative of vegetation growing in the immediate area. Juniperus as a genus demonstrates significant interspecific variation in environmental tolerances (Miller & Wigand, 1994; Lyford et al., 2003). Therefore, having species-level identifications from fossil assemblages is necessary to understand how climatic changes have impacted ecosystems in the past, and how they are likely to impact them in the future (Schupp et al., 1997; Dimitri et al., 2017).
Juniper of Rancho La Brea
RLB's exceptional fossil record is the product of the combined presence of surficial pooling of asphalt from buried, Miocene age, oil-bearing strata, and alluvial deposition from the surrounding Santa Monica Mountains (Quinn, 1992). Throughout the Late Pleistocene and Holocene, sticky asphalt pools trapped flora and fauna at the surface of the northern Los Angeles Basin (Akersten et al., 1983; Spencer et al., 2003). In areas near to seasonal streams, flood deposits buried entrapped organic tissue, and with the aid of continued asphalt seepage, tissues such as bone, chitin, calcium carbonate, cellulose, and lignin were preserved. Renewed asphalt seepage to the surface would eventually start the entrapment process again. The resulting ‘pockets’ of fossil material have no easily discernable stratigraphy or temporal associations and may represent periods of tens of thousands of years (Friscia et al., 2008; Holden et al., 2017). As a result of this age-mixing, determining relative abundances of species at discrete time intervals is not possible, hence we use presence/absence data for our study.
Plant fossils recovered from RLB include seeds of two species of Juniperus: the large-seeded J. californica and a small-seeded juniper of uncertain affinity. Previously, the small-seeded juniper was described as J. hanseni n. sp., an extinct species (Templeton, 1964). This identification was based on seed size and a qualitative assessment of resin pit arrangement when compared to extant juniper species with cones containing one or two seeds. However, Templeton's J. hanseni n. sp. description was never officially published, and occurrences of this taxon have not been reported outside of RLB. Given that only one plant species extinction has been documented from Late Quaternary macrofossil records in North America (Jackson & Weng, 1999), it may be more likely that the small-seeded juniper of La Brea is from an extant juniper species now extirpated from southern California.
The goals of this study are to identify the small-seeded juniper to species and to track the two juniper species occurrences at RLB through time. To determine the taxonomic affinity of the unknown juniper species, we compared branchlet and seed morphology of the fossils to selected extant taxa and produced hindcasted species distribution models (SDMs) for the last glacial maximum (LGM) for morphologically similar Juniperus species using their respective modern climate envelopes. To develop a timeline for juniper occurrences at RLB, we radiocarbon dated individual Juniperus seeds. Combined, these data allow us to trace juniper's history in the basin and investigate potential causes of its disappearance.
期刊介绍:
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