LATE GLACIAL AND HOLOCENE ENVIRONMENTAL CHANGE INFERRED FROM THE PÁRAMO OF CAJANUMA IN THE PODOCARPUS NATIONAL PARK, SOUTHERN ECUADOR
Cambios ambientales durante el Último Glacial y Holoceno inferidos del páramo de Cajanuma en el Parque Nacional Podocarpus, sur del Ecuador
DOI:
https://doi.org/10.15446/caldasia.v36n2.47491Palabras clave:
Palaeoecology, páramo, late Glacial, Holocene, climate and fire dynamics (en)Paleoecología, páramo, Último Glacial, Holoceno, dinámica del clima y el fuego (es)
Para reconstruir la historia ambiental, incluyendo la dinámica de la vegetación, el fuego y el clima, del área del valle de Cajanuma ( 3.285 m de altitud) en el Parque Nacional Podocarpus, sur del Ecuador, nos planteamos las siguientes preguntas de investigación: (1) ¿Cómo fue el desarrollo de la vegetación de montaña durante el último glacial y el Holoceno? (2) ¿Acaso el fuego jugó un control importante sobre el cambio de la vegetación y fue éste de tipo natural o de origen antropogénico? Se investigaron cambios paleoambientales mediante múltiples proxy tales como polen, esporas, los análisis de carbón y la datación por radiocarbono. Datos del polen resaltan que durante la parte final del último glacial y la transición al Holoceno temprano (ca. 16,000-10,500 cal yr BP) el páramo herbáceo fue el principal tipo de vegetación alrededor de la zona de estudio, mientras que el subpáramo y el bosque montano se encuentran con una baja representación. El Holoceno temprano y medio (ca. 10.500 a 5.600 años cal BP) se encuentran marcados por la alta abundancia de páramo, durante el Holoceno temprano, seguido de una ligera expansión del bosque montano, durante el Holoceno medio. Durante el Holoceno medio y tardío (ca. 5.600-1.200 años cal BP) hay una presencia significativa de páramo y subpáramo mientras que el bosque montano bajo disminuyó sustancialmente. Sin embargo, el bosque montano alto se mantuvo relativamente estable durante este período. El Holoceno tardío (ca. 1200 años AP hasta la actualidad) se caracterizó por vegetación de páramo, aunque, el bosque montano y el subpáramo presentaron una abundancia significativa en comparación con los períodos anteriores. Los incendios se hicieron frecuentes a partir del Holoceno tardío. El aumento marcado de la intensidad del fuego local y regional durante Holoceno tardío, período húmedo, sugiere fuertemente que eran de origen antropogénico. Durante el Último Glacial y Holoceno temprano, la línea superior del bosque se encontró en elevaciones bajas, ésta subió a elevaciones más altas durante el Holoceno medio.
ANDREA VILLOTA
HERMANN BEHLING
Herbario QCA, Escuela de Ciencias Biológicas, Pontificia Universidad Católica del Ecuador, Quito-Ecuador. Corresponding author: andrea.villota@biologie.uni-goettingen.de
Department of Palynology and Climate Dynamics, Albrecht-von-Haller Institute for Plant Sciences, University of Göttingen, Untere Karspüle 2, 37073 Göttingen, Germany
ABSTRACT
To reconstruct the environmental history including vegetation, fire and climate dynamics, from the Cajanuma valley area ( 3285 m elevation) in the Podocarpus National Park, southern Ecuador , we address the following major research question: (1) How did the mountain vegetation developed during the late Glacial and Holocene? (2) Did fire played an important control on the vegetation change and was it natural or of anthropogenic origin?. Palaeoenvironmental changes were investigated using multiple proxies such as pollen, spores, charcoal analyses and radiocarbon dating. Pollen data indicated that during the late Glacial and transition to the early Holocene (ca. 16 00010 500 cal yr BP) herb páramo was the main vegetation type around the study area, while subpáramo and mountain rainforest were scarcely represented. The early and mid-Holocene (ca. 10 500 to 5600 cal yr BP) is marked by high abundance of páramo during the early Holocene followed by a slight expansion of mountain forest during the mid-Holocene. During the mid- to late Holocene (ca. 56001200 cal yr BP) there is a significant presence of páramo and subpáramo while Lower Mountain Forest decreased substantially, although, Upper Mountain Forest remained relatively stable during this period. The late Holocene, from ca. 1200 cal yr BP to present, was characterized by páramo; however, mountain forest and subpáramo presented significantly abundance compared to the previous periods. Fires became frequent since the late Holocene. The marked increased local and regional fire intensity during the wetter late Holocene strongly suggests that were of anthropogenic origin. During the late Glacial and early Holocene, the upper forest line was located at low elevations; but shifted slightly upslope to higher elevations during the mid-Holocene.
Key words. Palaeoecology, páramo, late Glacial, Holocene, climate and fire dynamics.
RESUMEN
Para reconstruir la historia ambiental, incluyendo la dinámica de la vegetación, el fuego y el clima, del área del valle de Cajanuma ( 3.285 m de altitud) en el Parque Nacional Podocarpus, sur del Ecuador, nos planteamos las siguientes preguntas de investigación: (1) ¿Cómo fue el desarrollo de la vegetación de montaña durante el último glacial y el Holoceno? (2) ¿Acaso el fuego jugó un control importante sobre el cambio de la vegetación y fue éste de tipo natural o de origen antropogénico? Se investigaron cambios paleoambientales mediante múltiples proxy tales como polen, esporas, los análisis de carbón y la datación por radiocarbono. Datos del polen resaltan que durante la parte final del último glacial y la transición al Holoceno temprano (ca. 16,000-10,500 cal yr BP) el páramo herbáceo fue el principal tipo de vegetación alrededor de la zona de estudio, mientras que el subpáramo y el bosque montano se encuentran con una baja representación. El Holoceno temprano y medio (ca. 10.500 a 5.600 años cal BP) se encuentran marcados por la alta abundancia de páramo, durante el Holoceno temprano, seguido de una ligera expansión del bosque montano, durante el Holoceno medio. Durante el Holoceno medio y tardío (ca. 5.600-1.200 años cal BP) hay una presencia significativa de páramo y subpáramo mientras que el bosque montano bajo disminuyó sustancialmente. Sin embargo, el bosque montano alto se mantuvo relativamente estable durante este período. El Holoceno tardío (ca. 1200 años AP hasta la actualidad) se caracterizó por vegetación de páramo, aunque, el bosque montano y el subpáramo presentaron una abundancia significativa en comparación con los períodos anteriores. Los incendios se hicieron frecuentes a partir del Holoceno tardío. El aumento marcado de la intensidad del fuego local y regional durante Holoceno tardío, período húmedo, sugiere fuertemente que eran de origen antropogénico. Durante el Último Glacial y Holoceno temprano, la línea superior del bosque se encontró en elevaciones bajas, ésta subió a elevaciones más altas durante el Holoceno medio.
Palabras clave. Paleoecología, páramo, Último Glacial, Holoceno, dinámica del clima y el fuego.
Recibido: 02/05/2014
Aceptado: 27/10/2014
INTRODUCTION
The tropical northern Andes are among the hot spots of global vascular plant diversity due to their high structural and geological diversity. Especially, the Ecuadorian Andes harbour the most species rich ecosystems on earth (Barthlott et al. 2005; Rangel 2006). Among these bioma, the most characteristic one is páramo, due to its floristically unique, which is found above the upper forest line. The páramo is thought to have expanded downslope, while extensive burning and grazing prevented forest recovery. Some researchers suggest that the grass páramo below 4300 4100 m represents, at least partially, secondary vegetation in formerly forested areas (Lægaard 1992). It is especially subject to overgrazing, burning and cultivation, which leads to reduction of biodiversity (Podwojewski et al. 2002). Moreover, Ecuador currently suffers the highest deforestation rate of 198 000 ha year-1 between 1990 and 2005 (FAO 2006), because of the long occupation history and increasing human impact during last decades.
In this context, natural vegetation regeneration and sustainable management, as well as conservation of less degraded areas is urgently needed. The knowledge of palaeoecological conditions is very important to understand the natural composition and dynamics of modern ecosystems for proper management and conservation. Despite the need, of this knowledge only a limited number of palaeoecological studies are available from the Ecuadorian Andes (Bush et al. 2007). The available pollen records for the southeastern Andes, Andean Depression, were provided by the German-Ecuadorian Research Unit (www.tropicalmountainforest.org) focusing on the Podocarpus National Park (PNP) area and its surroundings (Niemann et al. 2013; Rodríguez & Behling 2012; Villota et al. 2012). Several investigations from sites between 2000 and 3300 m a.s.l. provide reconstructions of the environmental history, mostly of the northern PNP (Brunschön & Behling 2009; 2010; Jantz et al. 2013; Niemann & Behling 2008; 2009; 2010; Niemann et al. 2009; Rodríguez & Behling 2011).
In this paper, we present the investigation results of a core from the Cajanuma valley area in the western slope of the PNP, southern Ecuadorian Andes. Our main objective is the reconstruction of the local environmental history including vegetation, fire and climate dynamics in an attempt to identify mechanisms of past ecosystem change and human impact during the late Glacial. For that reason in this study we want to address the following main questions: (1) How did the vegetation develop at Cajanuma during the late Glacial and Holocene? (2) Did fire provide an important control over the vegetation and was it natural or anthropogenic? (3) How dynamic or stable were the UFL during the late Glacial and Holocene in the upper region of the PNP?
STUDY SITE
Location. The study area, Cajanuma, is located at the western slope of the eastern cordillera (Cordillera Real) in the Podocarpus National Park (PNP), southeastern Ecuadorian Andes (Fig. 1). The eastern Andean Cordillera is mainly formed by Paleozoic metamorphic rocks (Baldock 1982). The basin margins contain conglomerates of metamorphic debris, semipelites, quartzites and black phylites with some granitic intrusions (Litherland et al. 1994).
Particularly, the Andes of southern Ecuador are part of the Andean depression region (Depression of Giron-Cuenca in southern Ecuador and Huancabamba in northern Peru), where the highest peaks reach no more than 4000 m a.s.l., and active volcanoes and glaciers are absent (Schubert & Clapperton 1990). However, indications of Pleistocene glaciations are found. During the Last Glacial Maximum (LGM) lower moraine limits at 37503500 m a.s.l. in the eastern Ecuadorian Andes were estimated (Heine 2000), as well as, cirque lakes (remnants of the latest glaciations) between 2900 and 3400 m a.s.l. in the central PNP (Emck 2007).
The core analyzed Cajanuma valley(CV) was derived from a small peat bog, 30 m in diameter, located at 3285 m elevation (4°0859 South, 79°0925 West). The surrounding landscape is characterised by páramo with small forest patches at lower slopes. The area around the study site is not disturbed.
Climate. Inside the PNP at 3100 m a.s.l., rainfall up to 6000 mm a-1 was measured (Emck 2007; Bendix et al. 2008). The main rainy season lasts from April to August (austral winter), although rainfall is high throughout the year. On average, 9-10 humid months are recorded for the western slopes and temperature varies according to the time of day and season (Bendix et al. 2008). The coldest period of the year is generally the main rainy season. In the Cajanuma area the mean annual temperature registered is ca. 6.9 ºC and the annual precipitation rate is about 5700 mm (Emck 2007).
Vegetation. The most appropriate vegetation description by Homeier et al. (2008) classifies four different escarpment vegetation types in the PNP, which are relevant for our investigation area: lower and upper mountain rainforest, subpáramo and páramo. The coring site is situated in the páramo (including shrub and herb páramo) between ca. 3100-3700 m a.s.l.
According to Homeier et al. (2008) and additional information provided by Lozano et al. (2003), the lowest vegetation type is the lower mountain rainforest (LMF) between ca. 1300-2100 m a.s.l. with canopy heights of 30 m. Undisturbed communities of this type can be found particularly on steep slopes with 30º to 50º inclination, as well as up to ca. 2300 m at the bottom of wind-protected river valleys. Characteristic species are Alzetea verticillata, Cedrela montana, Graffenrieda miconioides, Heliocarpus americanus, Mikania sp., Morus insignis, Myrcianthes sp. and Piper sp. The upper mountain rainforest (UMF) is located between ca. 2100-2700 m a.s.l. and the canopy attains heights up to 25 m. Some of the main key species are Clethra revoluta, Clusia sp., Dioicodendron dioicum, Hedyosmum racemosum, Ilex rimbachii, Macrocarpaea revoluta, Myrica pubescens, Myrsine andina, Myrsine coriacea, Podocarpus oleifolius, Prumnopitys montana, Purdiaea nutans and species of Weinmannia At upper elevation between ca. 2700-3100 m a.s.l. the elfin-forest or subpáramo vegetation occurs. This vegetation type forms the upper forest line ecotone with a canopy height of 6-8 m. Characteristic species are, e.g. Brachyotum rotundifolium, Clethra ovalifolia, Gaultheria reticulata, Gaiadendron punctatum, Graffenrieda harlingii and Hesperomeles lanuginosa. The páramo (including shrub and herb páramo) occurs in the crest regions of the Cordillera Real above the upper forest line between ca. 3100 and 3700 m a.s.l. Páramo vegetation is characterised by plants with a maximum height of 2 m. Some key species are Arcytophyllum setosum, Blechnum cordatum, Calamagrostis macrophylla, Chusquea neurophylla, Gynoxis buxifolia, Halenia weddelliana, Huperzia kuesteri, Ilex andicola, Monnina arbuscula, Neurolepis nana, Niphogeton dissecta, Oxalis spiralis, Puya eryngioides, Puya maculate, Rhynchospora vulcani and Valeriana microphylla.
The present vegetation around the PNP is partially degraded due to deforestation and land conversion into pastures and cultivations (Beck et al. 2008). Currently, disturbance is primarily restricted to the surrounding areas and some border zones; a reason why the Podocarpus National Park still widely possesses well-protected natural vegetation including the study area of Cajanuma.
MATERIAL AND METHODS
The Cajanuma valley (CV) sediment core was taken with a Russian Corer. The total length of the recovered core is 180 cm. Sections of 50 cm length were placed in splitted PVC tubes covered with plastic film and stored under dark and cold (+4 °C) conditions at Georg-August-University of Göttingen before processing.
For accelerator mass spectrometer (AMS) radiocarbon dating, four subsamples containing organic material were submitted to the University of Erlangen-Nürnberg (Germany). The 14C dates were calibrated using the curve SHCal04. 14C SH terrestrial dataset of the Calib 6.0 software (Stuiver et al. 2005).
For palynological analysis, the CV core was sampled at four cm intervals along the core, resulting in 41 subsamples of 0.5 cm3 each. All subsamples were processed using the standard pollen analytical methods (Fægri & Iversen 1989). One tablet of exotic Lycopodium clavatum spores, containing 18 583 ± 762 spores, was added to each sample before treatment as a marker for calculation of pollen and charcoal concentration as well as influx. A minimum of 300 pollen grains was counted for each sample. The pollen sum includes pollen of herbs, shrubs, trees and indeterminate taxa and excludes fern spores and pollen of aquatic taxa. The spores of Pteridophyta, Isoëtes and Sphagnum were counted and quantified as percentages based on the pollen sum.
The identification of pollen and spores is based on the reference published by Hooghiemstra (1984), as well as electronic pollen keys of Ecuador, kept at the department of Palynology and Climate Dynamics, and the South American Pollen Database (Bush & Weng 2007). Reference collections of recent material, held at the Department of Palynology and Climate Dynamics in Göttingen, were also used. They contain about 3000 neotropical taxa (Behling 1993) and ca. 620 Ecuadorian taxa, respectively. Identified taxa were classified into ecological groups that correspond to the prevailing vegetation types: Lower Mountain Rainforest (LMF), Upper Mountain Rainforest (UMF), Subpáramo, Páramo and Pteridophyta. The pollen types that could not be identified were grouped in the indeterminate taxa. For charcoal analysis was used the technique developed by Finsinger et al. (2008), which estimated that charcoal particles correspond to the concentration of Lycopodium clavatum spores (marker). Charcoal particles were counted up to a total count of 100 Lycopodium clavatum spores. The counted charcoal particles were separated in two groups of different particle sizes (10 - 50 µm and 50 - >100 µm) to be able to give more detailed information about the fire history (Sadori & Giardini 2007). Fragments between 10 and 50 µm indicate regional fires, and fragments 50 - >100 µm local fire (Whitlock & Larsen 2001).
The software TILIA was used for data calculation of percentages, sums, as well as pollen and charcoal concentration and influx. TILIAGRAPH software was used to illustrate the data, as well as stratigraphy and the calibrated and uncalibrated dates (Grimm 1987). The program CONISS was used to conduct a cluster analysis of the pollen data which were included in the pollen sum to generate a dendrogram (Grimm 1987), helping to identify the pollen zones.
RESULTS
Stratigraphy. The 180 cm long peat bog sediment core from Cajanuma Valley (CV) consists of clay and organic material. Between 180 and 160 cm core depth clayey material is dominant with a dark/light greyish colour. From 160 to the top of the core the sediments are more compact and there is presence of organic material. Between 160 and 130 cm the organic material is highly decomposed and has a dark brown colour. Between 130 and 100 cm is found less decomposed organic material with presence of a few fine roots and has a light brownish colour. Between 100 and 35 cm the organic material is little decomposed with many plant remains and has a brown colour. Between 35 and 0 cm little decomposed organic material with humus layer is present and has a light brown colour. A detailed description of the stratigraphic units is given in Table 1.
Chronology and pollen zonation. Four AMS radiocarbon dates (Table 2) were performed at the AMS laboratory at the University of Erlangen/Nürnberg, Germany, providing the chronological control of the sediment core from Cajanuma valley (CV). Extrapolation of the dates suggests that the base of the core has an age of ca. 16 000 cal yr BP that probably reflects the beginning of sediment accumulation.
The series of four AMS dates shows a consistent age-depth model (Fig. 2), which indicates that sediments accumulated continuously without any gaps since the late Glacial. The average sediment accumulation rate is 0.69 mm yr-1. In detail it is 0.04 mm yr-1 (16 000 to 10 500 cal yr BP), 0.04 mm yr-1 (10 500 to 5600 cal yr BP), 0.11 mm yr-1 (5600 to 1200 cal yr BP), 0.71 mm yr-1 (1200 to 350 cal yr BP), 1.68 mm yr-1 (350 to 200 cal yr BP), 1.68 mm yr-1 (200 to 50 cal yr BP) and 1.68 mm yr-1 (50 to -59 cal yr BP). The CONISS cluster analysis and major changes in the pollen assemblages suggest five main pollen zones (CV-I to CV) with subzones (CV-Va-c).
Description of the pollen diagram. A detailed pollen percentage diagram displays 21 different pollen taxa with a representation of >2% out of 77 pollen types and two spores types with a representation of >2% out of eleven identified (Fig. 3).
The summary percentage diagram (Fig. 4) shows the pollen and spores grouped into the vegetation types: Lower Mountain Rainforest (LMF), Upper Mountain Rainforest (UMF), Subpáramo, Páramo and Pteridophyta (without Isoëtes), Sphagnum and concentration and influx of pollen and charcoal particles.
Pollen concentration and influx vary between 25 000530 000 grains/cm3 and between 25012 000 grains/cm2/yr, respectively. The charcoal concentration of the two counted fraction vary between 3 500 00014 000 000 particle/cm3 (small fraction) and 100 000600 000 particle/cm3 (large fraction). The charcoal influx for both counted fractions varies between 40 0001 200 000 particle/cm2/yr (small fractions) and between 10095 000 particle/cm2/yr (large fraction).
Zone CVI (180156 cm; ca. 16 00010 500 cal yr BP, six samples), is characterized by low proportion of LMF pollen taxa (10%) mainly due to low values of Moraceae/Urticaceae (7%) and Acalypha (1%). UMF taxa (1520%) are mainly represented by Hedyosmum (9%), which presents the highest value of the record in this zone, Myrsine, Podocarpaceae, Symplocos, Weinmannia and Alnus acuminata (23%). Subpáramo pollen taxa show stable values (20%), mainly by Asteraceae (10%) and Melastomataceae (5%). This zone is marked by relatively high values of páramo taxa (60%), especially by Poaceae (40%) and Cyperaceae pollen (10%). Also, pollen of Gentianaceae (5%) presents the highest values of the record. In this zone Pteridophyta spores (2025%) are mainly represented by Huperzia (1520%), which presents the highest value of the record in this zone. Isoëtes spores (up to 25%), which are not included in the sum of Pteridophyta, are very frequent in this zone.
Zone CVII (156136 cm; ca. 10 5005600 cal yr BP, five samples). LMF taxa show stable values (10%) by Moraceae/Urticaceae (7%) and the presence of Acalypha (2%). Proportions of UMF pollen taxa increase slightly (25%) by Myrsine and Podocarpaceae (23%). Symplocos pollen represents the highest values (610%) of the record in this zone. Alnus acuminata values decrease (0%). Pollen of subpáramo taxa increases slightly (20%) at the top of the zone mainly by Melastomataceae (10%). Páramo taxa decreased slightly from 60 to 50%, especially due to lower representation of Poaceae (30%). However, Plantago rigida pollen has higher values (8%) in this zone. Pteridophyta group strongly decrease (10%); mainly due to the low representation of Huperzia spores (3%). In this zone Isoëtes spores occur with lower values (5%).
Zone CVIII (13696 cm; ca. 56001200 cal yr BP, eleven samples), is characterized by low representation of LMF pollen (6%), due to the lowest values of Moraceae/Urticaceae pollen (3%). Proportion of UMF taxa decreased slightly (15%), mainly due to low percentages of Symplocos (4%). Subpáramo pollen taxa show a stable proportion (25%) such as Asteraceae (15%) and Melastomataceae (6%). Ericaceae are represented by higher values (5%) in this zone. Páramo pollen taxa are frequent and show highest values in this zone (65%), mainly due to Poaceae (35%) and Valeriana (10%). Compared to the previous zone, Pteridophyta show stable proportions (10%), mainly due to Huperzia (5%); also by spores of Cyatheaceae (3%) which present the highest value of the record. In this zone spores of Isoëtes are absent. Proportion of Sphagnum spores (5%) increases in this zone.
Zone CVIV (9672 cm; ca. 1200350 cal yr BP, six samples), is marked by a slightly higher representation of LMF pollen (11%), e.g. Moraceae/Urticaceae (6%) and Acalypha (2%) compared to the previous zone. UMF taxa increase slightly (20%) at the top of the zone; mainly by Weinmannia (4%) and Alnus acuminata (4%) at the top of the zone. A slight increase is found in pollen of Celtis (3%). However, Podocarpaceae pollen represents lower values (1%) in this zone. Subpáramo pollen taxa decreased from 25 to 15%, especially due to lower representation of Asteraceae (8%) and Ericaceae (3%). Páramo taxa vary between 65 and 55%, especially due to lower values of Poaceae pollen (30%) at the bottom of the zone. Valeriana pollen presents the highest values (10%) of the record at the bottom of this zone. Compared to the previous zone Pteridophyta decreased strongly (5%) and Sphagnum spores (35%) present the highest values of the record.
Subzone CVVa (7244 cm; ca. 350200 cal yr BP, seven samples), is characterized by a stable representation of LMF taxa, mainly due to Moraceae/Urticaceae (47%); also Acalypha and Piperaceae with (2%). UMF taxa reach highest values between 20 and 28% of the record, mainly due to pollen of Myrsine (4%) and Symplocos and Alnus acuminata with (5%). Percentages of subpáramo taxa increase slightly, such as Ericaceae (4%). Highest representation of pollen of Melastomataceae (15%) and Hypericum (4%) is found in this subzone. Compared to the precious zone proportion of páramo taxa decreased (45%), mainly due to Poaceae (20%) and Valeriana (4%). Pollen of Cyperaceae represents higher proportion (10%) at the bottom of this subzone. In this subzone Pteridophyta spores (2%) decreased mainly by the low presence of Huperzia spore (1%) and the absence of Cyatheaceae spores. Isoëtes values increase slightly (7%) at the top of this subzone. Spore of Sphagnum (15%) decrease at this subzone.
Subzone CVVb (4420 cm; ca. 20050 cal yr BP, three samples), shows a stable proportion of LMF pollen (11%). UMF taxa remain stable (20%); however Weinmannia show higher values (5%) in this subzone. Subpáramo pollen shows the highest amounts within this subzone, especially by Asteraceae (15%) and Ericaceae pollen (5%). Compared to the previous subzone, páramo taxa show stable percentage, especially by Poaceae (20%). In this subzone Pteridophyta show stable values (2%).
Zone CVVc (240 cm; ca. 50 cal yr BP to -59 cal yr BP, three samples), is characterized by slightly increase proportion of LMF pollen taxa; mainly Moraceae/Urticaceae taxa slightly increase (610%) at the top of this zone. UMF taxa remain stable between 20 and 25%; however Celtis show highest values (5%) of the record in this zone. Subpáramo taxa show the lowest values of the record (13%), mainly by Asteraceae, Melastomataceae (5%) and Ericaceae (1%). Compared to the previous subzone, pollen of páramo increase from 40 to 50%. This is mainly due to increasing values of Poaceae (25%), Cyperaceae (15%) and Valeriana (6%). Compared to the previous subzone Pteridophyta spores show stable values (2%). Isoëtes value increase slightly (14%). Proportion of Sphagnum spores (25%) slightly increased at the bottom of this zone.
INTERPRETATION AND DISCUSSION OF THE ENVIRONMENTAL RECORD
During the Last Glacial Maximum (LGM), most Andean glaciers moved down slope and reached their lowermost positions at about 3000 m in the eastern Andes of Colombia, Ecuador and northern Peru (Rodbell 1994). Lower glacier margins are estimated at ca. 3100 m for the PNP region, with glaciers terminating at elevations of ca. 27502800 m (Rozsypal 2000). At the end of the LGM, the volume of glaciers decreased creating moraines, lakes and bogs. The moraine frontier at the PNP is found between 2800 and 3350 m elevation, after the glacial retreat deposits accumulated at the study site at about 16 000 cal yr BP.
The pollen record from the Cajanuma valley (CV) at 3285 m elevation, in general reflects the local development and vegetation dynamics on the drier western slope of the Podocarpus National Park (PNP) in the Andean Depression. Pollen and spores data suggest that páramo vegetation, which today naturally covered the area, exists around the core site since the late Glacial from ca. 16 000 cal yr BP.
Late Glacial and transition to the early Holocene. The pollen record from Cajanuma valley (CV) indicates that herb páramo was the main vegetation type around the study area during the recorded period from ca. 16 000-10 500 cal yr BP (zone CVI), while the subpáramo and mountain rainforest were low represented. The low presence of mountain forest taxa is probably related to low temperatures at that time which did not allow the development of mountain forest near the study site.
During this period, is also recorded the low pollen input into the basin with presence of clayey material; which could reflect that the páramo vegetation was sparse and forest occurred in some distance to the coring site. Such conditions of low local productivity coupled with input from long distance dispersal serves to elevate a few anemophilous pollen types in the percentage data, yielding proportions that do not reflect local vegetation (Hansen et al. 1984).
Pollen of Lower Mountain Rainforest (LMF) taxa (e.g., Moraceae/Urticaceae, Alchornea and Acalypha) tends to be over-represented due to wind transport to higher elevations (Jantz et al. 2013). At Laguna Baja in northern Peru over representation of forest taxa (e.g., Moraceae/Urticaceae) in páramo samples is attributed to low pollen productivity of local plants at high elevations resulting in higher values of long distance wind transported pollen (Hansen & Rodbell 1995). Main components of the Upper Mountain Rainforest (UMF) were Hedyosmum, Podocarpaceae and Alnus acuminata. The occurrence of Hedyosmum, which is abundant during this period, indicates relatively wet conditions. Representation of Alnus acuminata pollen in páramo was observed also in the superpuna of the Junín area in central Peru and was assumed due to long distance transport (Hansen et al. 1984). The subpáramo at CV was dominated by shrubby vegetation composed of Asteraceae and Melastomataceae. The herb páramo was rich in Poaceae, Cyperaceae and Gentianaceae, reflecting cool conditions, associated with a high presence of Huperzia and Isoëtes. The occurrence of Pteridophyta and high values of Isoëtes suggest wetter conditions. Isoëtes mostly occurs submerged in páramo lakes and is sensitive to strong frosts (Bosman et al. 1994). It indicates that there must have been a shallow water body at the study site. Similarly, cooler climates are indicated by the occurrence of treeless vegetation during glacial times in the southern Ecuadorian Andes (Colinvaux et al. 1997). Also in southwestern Ecuadorian Andes (3700 m elevation), studies indicate for the late Glacial period (17 00011 000 cal yr BP), a herb páramo surrounded the area, reflecting colder and moister climatic conditions (Hansen et al. 2003).
During the late Glacial and transition to the early Holocene, the low charcoal influx indicates rare fire and suggests the absence of human activity in the study area.
Early to midHolocene. The early to the mid-Holocene period between ca. 10 500 to 5600 cal yr BP (zone CVII), is marked by gradual change indicated by high abundance of páramo vegetation during the early Holocene, followed by a slight expansion of mountain forest into higher elevations and a partial replacement of páramo during the mid-Holocene. Páramo vegetation began to decrease while subpáramo and mountain rainforest increased (90005600 cal yr BP).
During this period stable proportion of LMF was shown in the pollen record; but there is evidence of a slight increase of Acalypha, which probably reflects slow and continuous increasing temperatures. UMF vegetation increases slightly mainly by the strong increase of Symplocos taxa. Also by, Myrsine and Podocarpaceae. Nevertheless, Hedyosmum starts to decline in abundance ca. 10 500 cal yr BP. The stable proportion of LMF and the increase of UMF suggest an establishment of mountain rainforest vegetation and a rise in temperature during this period. Subpáramo was dominated mainly by Asteraceae and Melastomataceae. Relatively high proportion of páramo was reached during this period, mainly by high abundance of Cyperaceae and Plantago rigida. The frequent occurrences of P. rigida and Cyperaceae indicate locally humid conditions (Moscol Oliveira & Hooghiemstra 2010). In particular P. rigida constitutes cushion bogs at high elevation (30005200 m) in grass páramo (Bosman et al. 1994; Niemann & Behling 2008). Pteridophyta were rare during this period, Huperzia decreased during the transition from the late PleistoceneHolocene period (Hansen et al. 2003). However, abundance of Cyatheaceae slightly increased during this period. Also, Isoëtes became rare at the study site. In the Cajas National Park (western Ecuadorian Andes), the pattern was similar, the early Holocene showed warmer conditions than at present (Colinvaux et al. 1997; Hansen et al. 2003). At Fuquene Lake (eastern Colombian Andes), very humid conditions are suggested during the early Holocene (Vélez et al. 2006). At Laguna Chochos and Laguna Baja (eastern Peruvian Andes) a warm and wet condition is shown by the arrival of cloud forest taxa to both sites at 11 500 cal yr BP (Hansen & Rodbell 1995; Bush et al. 2005). Also, studies in the west and central Andes region of Ecuador, Peru and Bolivia in general show a trend of a relative warm and dry mid-Holocene (Hansen et al. 2003; Paduano et al. 2003; Weng et al. 2006).
Relatively low values of charcoal influx during the early and mid-Holocene suggest rare fires in the study area.
Mid- to late Holocene. During the mid- to late Holocene (ca. 56001200 cal yr BP, zone CVIII), the LMF decreased, in particular Moraceae/Urticaceae. Whereas the LMF decreased, the UMF presence remained relatively stable; with a particular high abundance of Weinmannia and Hedyosmum and a marked lower occurrence of Symplocos. However, it has to be considered that Weinmannia and Hedyosmum are anemophilous taxa (Hansen & Rodbell 1995; Weng et al. 2004). Anemophilus taxa are overrepresented in pollen spectra (Moscol Oliveira et al. 2009; Jantz et al. 2013). Subpáramo vegetation expanded due to the higher representation of Asteraceae, Ericaceae and Hypericum at the top of the zone; probably suggesting higher moisture conditions (Marchant et al. 2002). Hypericum is also a good proxy for the existence of landscape disturbance (Brunschön & Behling 2009). The páramo vegetation expanded, it was dominated mainly by Poaceae and Gentianaceae with increasing proportions of Valeriana; suggesting a change to cooler and wetter conditions. The marked decrease of Plantago rigida and increase of Poaceae might indicate that grass páramo surrounded the study site. In addition, the high presence of Huperzia and Cyatheaceae suggests wetter conditions.
Fires were slightly frequent during the mid- to late Holocene period. There is evidence of a slight increased influx of smaller charcoal fragments after 5600 cal yr BP. Studies from lake Titicaca and the surrounding altiplano as well as southern Ecuador suggest that once the mid-Holocene drought ends, human populations expand rapidly and are engaged in landscape modification (Brenner et al. 2001; Niemann & Behling 2008).
Late Holocene. The late Holocene since ca. 1200 cal yr BP (zone CVIV to CVV), was generally characterized by páramo vegetation, but mountain forest and subpáramo were similar or slightly stronger presented compared to the previous periods. Pteridophyta were almost absent during this period.
Between ca. 1200350 cal yr BP (zone CVIV) the LMF increased slightly, mainly by the increased proportion of Alchornea and Piperaceae. However, as mention before pollen of LMF taxa (e.g., Moraceae/Urticaceae, Alchornea, Acalypha and Piperaceae) tends to be over-represented due to wind transport to higher elevations. The UMF increased slightly and was represented mainly by high occurrence of Alnus acuminata and Celtis. Alnus acuminata grows along river beds and follows landslides as a pioneer (Marchant et al. 2002). The presence of A. acuminata can be a result of anthropogenic disturbances (Weng et al. 2004), rather than by climatic changes. A. acuminata and Celtis are also a component of successional forests after human disturbance (Marchant et al. 2002). The subpáramo remained relatively stable during this period. Páramo vegetation was still well represented with a high occurrence of Poaceae and Valeriana; suggesting cooler and wetter conditions. Higher abundance of Sphagnum appeared during this period. Sphagnum moss probably reflects the formation of the peat bog the study area.
Between ca. 35050 cal yr BP (subzone CVVa and CVVb), the LMF vegetation remain stable. Slightly higher presence of UMF vegetation is due to the slight increase of Symplocos, Weinmannia and Alnus acuminata. Subpáramo vegetation slightly increased, mainly by higher proportion of Asteraceae and Melastomataceae. Especially, Asteraceae may reflect landscape disturbance (Chepstow-Lusty et al. 2003). Slightly lower presence of páramo vegetation is due to the lower occurrence of Poaceae and Valeriana. However, Cyperaceae slightly increased; suggesting cooler and wetter conditions. Sphagnum presence remained stable. Also, high occurrence of Isoëtes is recorded. Persistent humid conditions are suggested by high occurrences of Cyperacae and Isoëtes.
Between ca. 50 cal yr BPto the present (subzone CVVc) LMF and UMF remained stable. Subpáramo vegetation decreased slightly due to lower presence of mainly Asteraceae and almost absence of Ericaceae. Poaceae together with Cyperaceae dominated in the herb páramo until modern times; reflecting cooler conditions where modern vegetation as well as modern climatic conditions became established.
In addition, there is evidence of a major influx of larger charcoal fragments after 1200 cal yr BP which may reflect local fires of anthropogenic origin. Since, the first stronger presence of human in this region was after 10 000 yr BP according to the Cubilán archaeological record, located about 100 km north of Loja at 3100 m of altitude (Valdez 2008). During the late Holocene human influence is reported throughout the Andes (Hansen et al. 2003; Bush et al. 2005; Weng et al. 2006). Nevertheless, it is important to point out that for the last years there is no evidence of local fires; as mention above disturbance is primarily restricted to the surrounding areas and the study site is since the last years well-protected.
Upper forest line (UFL) changes. The Upper Forest Line (UFL) dynamics is mainly reflected by fluctuations in the proportion of upper mountain rainforest (UMF) and subpáramo vegetation. During the late Glacial and transition to the early Holocene, from ca. 16 000-10 500 cal yr BP, the high proportion of páramo taxa comparably with the low presence of mountain rainforest and subpáramo indicate that páramo vegetation extensively covered the area and dominated the landscape. This probably reflects a downslope shift of UFL in the study area. During the LGM, the UFL position in the Podocarpus National Park (PNP) area was at least ca. 700 m lower in the northernmost PNP area compared to today (Brunschön & Behling 2010).
Likewise, the late Glacial period, during the early Holocene, (10 5009000 cal yr BP), herb páramo was the main vegetation type around the study area. Subpáramo vegetation and mountain rainforest were low represented. Suggesting that, the UFL position was still low. On the contrary, within the whole PNP area, the UFL seems to have shifted upslope in the range of ca. 100150 m (Brunschön & Behling 2010). During the mid- Holocene, (90005600 cal yr BP), a relatively high increase of mountain rainforest and subpáramo shrubs and trees is observed. Páramo vegetation was represented by a lower occurrence. This probably, suggests a shift of UFL to higher elevations. A ca. 400 m upslope is reconstructed for the PNP by Brunschön & Behling (2010).
During the mid- to late Holocene, (56001200 cal yr BP), the significant presence of páramo taxa comparably with the relatively low presence of mountain rainforest probably represents a downslope shift of UFL in the study area.
Between ca. 1200350 cal yr BP high proportion of páramo taxa comparably with the low presence of mountain rainforest and subpáramo indicate a downslope shift of UFL in the study area. However, the suggested lower UFL should be interpreted in the context of local fires. Higher frequency of fires probably lowered the UFL position.
Between ca. 350 cal yr BP to present, the páramo vegetation seems to have been slightly depressed, while the mountain forest and subpáramo vegetation slightly expanded; suggesting an upslope of the UFL. The UFL shifted upslope to the highest elevations of ca. 2800 m a.s.l. in the PNP (Brunschön & Behling 2010).
Comparison with other records from the Podocarpus National Park. The Cajanuma valley record, located at 3285 m elevation in the western slope of the PNP, will be compared to close by study sites: El Tiro Pass (2811 m a.s.l.; 15 km north of the site), Cocha Caranga (2710 m a.s.l., ca. 10 km north), Valle Pequeño (3244 m a.s.l., ca. 3 km), Laguna Rabadilla de Vaca (3312 m a.s.l., ca. 15 km south of the study site) and Cerro Toledo (3150 m a.s.l., ca. 30 km south) (Fig. 1).
During the late Glacial and transition to the early Holocene (16 00010 500 cal yr BP), a similar vegetation pattern as in Cajanuma valley is evident from the pollen record of El Tiro Pass which indicated grass páramo vegetation, mainly composed of Poaceae and Plantago reflecting cold and moist conditions (Niemann & Behling 2008). Nevertheless, a pollen record of Cocha Caranga suggests higher proportions of the UMF between ca. 14 500 to 9700 cal yr BP, indicating increased temperatures compared to earlier periods (Niemann & Behling 2009). Also the Cerro Toledo record suggests higher occurrence of subpáramo and mountain rainforest vegetation with relative wet conditions (Brunschön & Behling 2009).
A similar vegetation pattern, as in Cajanuma valley, during the early Holocene, (10 5009000 cal yr BP), was recorded in El Tiro Pass between, 11 200 to 8900 cal yr BP, which indicates slowly warming conditions with a relatively low increase in mountain rainforest and subpáramo shrubs and trees (Niemann & Behling 2008). In the Laguna Rabadilla de Vaca record, between ca. 11 7008990 cal yr BP, it is evident that herb páramo was the main vegetation type associated with a high number of ferns, reflecting cool and relatively wet climatic conditions (Niemann et al. 2009).
A drier mid-Holocene, as recorded in Cajanuma valley between ca. 9000 to 5600 cal yr BP, has been recorded throughout the PNP. As is the case of the El Tiro record in which, between ca. 8900 to 3300 cal yr BP, UMF was predominant and a succession of Hedyosmum and Podocarpaceae took place (Niemann & Behling 2008). The Laguna Cocha Caranga record indicates that the early to mid-Holocene was a drier period by the strong increase of Cyperaceae and Isoëtes and a marked increase of fire intensity (Niemann & Behling 2009). The strong increase of Weinmannia indicates warmer climatic conditions, between ca. 89903680 cal yr BP, at the Laguna Rabadilla de Vaca record (Niemann et al. 2009). The Cerro Toledo record between 6900 to 4700 cal yr BP shows a gradual change in the vegetation composition. The lower presence of páramo vegetation and high proportion of subpáramo; reflects warmer conditions (Brunschön & Behling 2009).
During the late Holocene (ca. 1200 cal yr BP to the present) the vegetation composition at the study area is somewhat similar to what has been found in the pollen records of the PNP. The Cocha Caranga record shows open grassy areas with forest after ca. 1300 cal yr BP (Niemann & Behling 2009). The record of Cerro Toledo after ca. 1800 cal yr BP shows a slight decrease in páramo and increase in subpáramo, UMF, and LMF suggesting warmer temperatures (Brunschön & Behling 2009). Also, the El Tiro record shows an increase of Melastomataceae, thus suggesting relatively stable subpáramo vegetation (Niemann & Behling 2008). Also, the Valle Pequeño record suggests a higher representation of mountain forest after ca. 1630 cal yr BP (Rodríguez & Behling 2011).
CONCLUSIONS
The Cajanuma valley sediment core at 3285 m a.s.l. present a detailed palaeoenviromental record from the late Glacial to the Holocene, on the western slope of Podocarpus National Park of the eastern Cordillera in southern Ecuador.
During the recorded late Glacial period and transition to the early Holocene, since ca. 16 000 to 10 500 cal yr BP, herb páramo, rich in Poaceae, Cyperaceae and Gentianaceae, associated with a high presence of Huperzia and Isoëtes, indicates cool and wet conditions.
During the early to mid-Holocene from ca. 10 500 to 5600 cal yr BP, there was a high abundance of páramo vegetation followed by a slight expansion of mountain forest into higher elevations and a partial replacement of treeless páramo. High proportion of páramo was reached, mainly by high abundance of Plantago rigida, suggesting relatively cold conditions. The upper mountain rainforest (UMF) developed slightly due to higher abundance of Symplocos taxa. The high occurrence of the UMF at the coring site and the stronger decomposition of the organic material suggest relatively warm and also somewhat drier conditions.
During the mid- to late Holocene (ca. 56001200 cal yr BP) there is a marked presence of páramo and subpáramo, while LMF decreased markedly. Even though, UMF presence remained relatively stable.
The late Holocene period since 1200 cal yr BP was generally characterized by páramo vegetation. Even though, mountain forest and subpáramo presented a high abundance compared to the previous periods.
Fires were rare during the late Glacial and became slightly frequent during the mid- late Holocene after 5600 cal yr BP. But since the late Holocene at about 1200 cal yr BP, fires became more common, reflecting fires of anthropogenic origin.
The Upper Forest Line (UFL) dynamics fluctuated since the late Glacial to the Holocene. During the late Glacial, the UFL occurred at much lower elevation than today. During the early Holocene, the UFL position remains low. However, at the mid- to late Holocene, the UFL shifted upslope to higher elevations where it is today.
ACKNOWLEDGMENTS
We thank the Deutsche Forschungsgemeinschaft (DFG) for financial support (BE 2116/8-2) within the research unit FOR 816 Biodiversity and sustainable management of a megadiverse mountain ecosystem in southern Ecuador. Corinna Brunschön and Fernando Rodríguez are thanked for their assistance in the fieldwork. The team of ESCF is thanked for logistical support.
LITERATURE CITED
1. Baldock, J.W. 1982. Geology of Ecuador-explanatory bulletin of the national geological map of the Republic of Ecuador, scale 1:1,000,000. Ministerio de Recursos Naturales y Energéticos, Dirección General de Geología y Minas, Quito, pp. 11.
2. Barthlott, W., J. Mutke, D. Rafiqpoor, G. Kier & H. Kreft. 2005. Global centers of vascular plant diversity. Nova Acta Leopold 92: 61-83
3. Beck, E., F. Makeschin, F. Haubrich, M. Richter, J. Bendix & C. Valerezo. 2008. The Ecosystem (Reserva Biológica San Francisco). In: Beck, E., Bendix, J., Kottke, I., Makeschin, F., Mosandl, R., (Eds.), 2008. Gradients in a Tropical Mountain Ecosystem of Ecuador. Ecological Studies 198. Springer, Berlin, Heidelberg, pp. 1-13.
4. Bendix, J., R. Rollenbeck, M. Richter, P. Fabian & P. Emck. 2008. Climate. In: Beck, E., Bendix, J., Kottke, I., Makeschin, F., Mosandl, R., (eds.), Gradients in a Tropical Mountain Ecosystem of Ecuador. Ecological Studies 198, Springer, Berlin, Heidelberg, pp. 63-73.
5. Behling, H. 1993. Untersuchungen zur spätpleistozänen und holozänen Vegetations- und Klimageschichte der tropischen Küstenwälder und der Araukarienwälder in Santa Catarina (Südbrasilien). Dissertationes Botanicae 206, J. Cramer, Berlin, Stuttgart.
6. Bosman, A., H. Hooghiemstra & A. Cleef. 1994. Holocene mire development and climatic change from a high Andean Plantago rigida cushion mire. The Holocene 43: 233-243.
7. Brenner, M., D.A. Hodell, J.H. Curtis, M.F. Rosenmeier, M.W. Binford & M.B. Abbott. 2001. Abrupt climate change and Pre-Columbian cultural collapse. In Interhemispheric Climate Linkages, Markgraf V (ed.). Academic Press: San Diego, California. 87104.
8. Brunschön, C. & H. Behling. 2009. Late Quaternary vegetation, fire and climate history reconstructed from two cores at Cerro Toledo, Podocarpus National Park, southeastern Ecuadorian Andes. Quaternary Research 72: 388-399.
9. Brunschön, C. & H. Behling. 2010. Reconstruction and visualization of upper forest line and vegetation changes in the Andean depression region of southeastern Ecuador since the last glacial maximum A multi-site synthesis. Review of Palaeobotany and Palynology 163: 139-152.
10. Bush, M.B., B.C.S. Hansen, D.T. Rodbell, G.O. Seltzer, K.R. Young, B. Leon, M.B. Abbott, M.R. Silman & W.D. Gosling. 2005. A 17 000-year history of Andean climate and vegetation change from Laguna de Chochos, Peru. Journal of Quaternary Science 20: 703-714.
11. Bush, M.B. & C. Weng. 2007. Introducing a new (freeware) tool for palynology. Journal of Biogeography 34: 377-380.
12. Bush, M.B., J.A. Hanselman & H. Hooghiemstra. 2007. Andean montane forests and climate change. In: Bush, M.B., Flenley, J.R. (Eds.), Tropical rainforest responses to climatic change. Springer, Praxis, pp. 33-54.
13. Chepstow-Lusty, A., M.R. Frogley, B.S. Bauer & M.B. Bush. 2003. A late Holocene record of arid events from the Cuzco region, Peru. Journal of Quaternary Science 18: 491-502.
14. Colinvaux, P.A., M.B. Bush, M. Steinitz-Kannan & M.C. Miller. 1997. Glacial and postglacial pollen records from the Ecuadorian Andes and Amazon. Quaternary Research 48: 69-78.
15. Emck, P. 2007. A Climatology of South Ecuador With Special Focus on the Major Andean Ridge as AtlanticPacific climate Divide. Dissertation, Universität Erlangen, Nürnberg.
16. FAO. 2006. Global forest resources assessment 2005, Progress towards sustainable forest management. Food and Agricultural Organization of the United Nations, Rome.
17. Fægri, K. & J. Iversen. 1989. Textbook of Pollen Analysis, 4th ed. Wiley, Chichester, pp. 328.
18. Finsinger W., W. Tinner & F. Hu. 2008. Rapid and accurate estimates of microcharcoal content in pollen slides. Pp. 121-124 in Charcoals from the past: cultural and palaeoenvironmental implications. Proceedings of the Third International Meeting of Anthracology, Cavallino-Lecce (Italy), June 28th-July 1st 2004. Archaeopress, Oxford, UK; available from Hadrian Press.
19. Grimm, E.C. 1987. CONISS: a Fortran 77 program for stratigraphically constrained cluster analysis by the method of the incremental sum of squares. Computer and Geosciences 13: 13-35.
20. Hansen, B.C.S., H.E. Wright & J.P. Bradbury. 1984. Pollen studies in the Junín area, central Peruvian Andes. Geological Society of America Bulletin 95: 1454-1465.
21. Hansen, B.C.S. & D.T. Rodbell. 1995. A Late-Glacial/Holocene pollen record from the eastern Andes of northern Peru. Quaternary Research 44: 216-227.
22. Hansen, B.C.S., D.T. Rodbell, G.O. Seltzer, B. León, K.R. Young & M. Abbott. 2003. Late-glacial and Holocene vegetation history from two sides in the western Cordillera of southwestern Ecuador. Palaeogeography, Palaeoclimatology, Palaeoecology 194: 79-108.
23. Heine, K. 2000. Tropical South America during the Last Glacial Maximum: evidence from glacial, periglacial and fluvial records. Quaternary International 72: 7-21.
24. Hooghiemstra, H. 1984. Vegetation and Climatic History of the High Plain of Bogota, Colombia., Vaduz: J. Cramer.
25. Homeier, J., F.A. Werner, S.R. Gradstein, S.W. Breckle & M. Richter. 2008. Potential vegetation and floristic composition of Andean forests in South Ecuador, with a focus on the RBSF. In: Beck, E., Bendix, J., Kottke, I., Makeschin, F., Mosandl, R., (Eds.), Gradients in a Tropical Mountain Ecosystem of Ecuador. Ecological Studies 198, Springer, Berlin, Heidelberg, pp. 87-100.
26. Jantz, N., J. Homeier, S. León-Yánez, A. Moscoso & H. Behling. 2013. Trapping pollen in the tropics-Comparing modern pollen rain spectra of different pollen traps and surface samples across Andean vegetation zones. Review of Palaeobotany and Palynology 193: 57-69
27. Lægaard, S. 1992. Influence of fire in the grass páramo vegetation of Ecuador. In: Balslev, H. & Luteyn, J.L. (eds.) Páramo - An Andean ecosystem under human influence. Academic Press, London. pp. 151-170.
28. Litherland, M., J.A. Aspen & R.A. Jemielita. 1994. The metamorphic belts of Ecuador. Overseas Memoir of the British Geological Survey 11: 1-147.
29. Lozano, P., T. Delgado & Z. Aguirre. 2003. Estado actual de la flora endémica exclusive y su distribucion en el Occidente del Parque Nacional Podocarpus. Funbotánica y Herbario y Jardín Botánico. Loja, Ecuador.
30. Marchant, R., L. Almeida, H. Behling, J.C. Berrio, M. Bush, A. Cleef, J. Duivenvoorden, M. Kappelle, P. De Oliveira, A.T. De Oliveira-Filho, S. Lozano-García, H. Hooghiemstra, M.P. Ledru, B. Ludlow-Wiechers, V. Markgraf, V. Mancini, M. Paez, A. Prieto, O. Rangel & M.L. Salgado-Labouriau. 2002. Distribution an ecology of parent taxa of pollen lodged within the Latin American Pollen Database. Review of Palaeobotany and Palynology 121: 1-75.
31. Moscol Oliveira, M., J.F. Duivenvoorden & H. Hooghiemstra. 2009. Pollen rain and pollen representation across a forest-páramo ecotone in northern Ecuador. Review of Palaeobotany and Palynology 157: 285-300.
32. Moscol Oliveira, M. & H. Hooghiemstra. 2010. Three millennia upper forest line changes in northern Ecuador: Pollen records and altitudinal vegetation distributions. Review of Palaeobotany and Palynology 163: 113-126.
33. Niemann, H. & H. Behling. 2008. Late Quaternary vegetation, climate and fire dynamics inferred from the El Tiro record in the southeastern Ecuadorian Andes. Journal of Quaternary Science 23: 203-212.
34. Niemann, H. & H. Behling. 2009. Late Pleistocene and Holocene environmental change inferred from the Cocha Caranga sediment and soil records in the southeastern Ecuadorian Andes. Palaeogeography, Palaeoclimatology, Palaeoecology 276: 1-14.
35. Niemann, H. & H. Behling. 2010. Late Holocene environmental change and human impact inferred from three soil monoliths and the Laguna Zurita multi-proxi record in the southeastern Ecuadorian Andes. Vegetation History and Archaeobotany 19: 1-15.
36. Niemann, H., T. Haberzettl & H. Behling. 2009. Holocene climate variability and vegetation dynamics inferred from the (11700 cal. yr BP) Laguna Rabadilla de Vaca sediment record, southeastern Ecuadorian Andes. The Holocene 19: 307-316.
37. Niemann, H., I. Matthias, B. Michalzik & H. Behling. 2013. Late Holocene human impact and environmental change inferred from a multi-proxy lake sediment record in the Loja region, southeastern Ecuador. Quaternary International 308: 253-264.
38. Paduano, G.M., M.B. Bush, P.A. Baker, P.A., Fritz, S.C. & G.O. Seltzer. 2003. A vegetation and fire history of Lake Titicaca since the Last Glacial Maximum. Palaeogeography, Palaeoclimatology, Palaeoecology 194: 259-279.
39. Podwojewski, P., J. Poulenard, T. Zambrana & R. Hofstede. 2002. Overgrazing effects on vegetation cover and properties of volcanic ash soil in the páramo of Llangahua and La Esperanza (Tungurahua, Ecuador). Soil Use Managemant 18: 45-55.
40. Rangel, O. 2006. Síntesis final: Visión integradora sobre la región del páramo. Diversidad Biótica III. La región de la vida paramuna. Universidad Nacional de Colombia. Bogotá D.C. Pp: 816-838.
41. Rodbell, D.T. 1994. The timing of the last deglaciation in Cordillera Oriental, Northern Peru based on glacial geology and lake sedimentology. Geological Society of America Bulletin 105: 923-934.
42. Rodríguez, F. & H. Behling. 2011. Late Holocene vegetation, fire, climate and upper forest line dynamics in the Podocarpus National Park, south-eastern Ecuador. Vegetation History and Archaeobotany 20: 1-14.
43. Rodríguez, F. & H. Behling. 2012. Late Quaternary vegetation, climate and fire dynamics, and evidence of early to mid-Holocene Polylepis forests in the Jimbura region of the southernmost Ecuadorian Andes. Palaeogeography, Palaeoclimatology, Palaeoecology 350-352: 247-257.
44. Sadori, L. & M. Giardini. 2007. Charcoal analysis, a method to study vegetation and climate of the Holocene: The case of Lago di Pergusa (Sicily, Italy). Geobios 40: 173-180.
45. Schubert, C. & C.M. Clapperton. 1990. Quaternary glaciations in the Northern Andes (Venezuela, Colombia and Ecuador). Quaternary Science Reviews 9: 123-135.
46. Stuiver, M., P.J. Reimer & R.W. Reimer. 2005. CALIB 6.0. Radiocarbon Calibration Program. URL: http://calib.qub.ac.uk/calib/calib.html
47. Valdez, F. 2008. Inter-zonal relationships in Ecuador. In: Silverman H, Isbell WH (eds) Handbook of South American archeology. Springer, New York, pp. 865-888.
48. Vélez M.I., H. Hooghiemstra, S. Metcalfe, M. Wille & J.C. Berrío. 2006. Late Glacial and Holocene environmental and climatic changes from a limnological transect through Colombia, northern South America. Palaeogeography, Palaeoclimatology, Palaeoecology 234: 81-96.
49. Villota, A., S. León-Yánez & H. Behling. 2012. Vegetation and environmental dynamics in the Páramo of Jimbura region in the southeastern Ecuadorian Andes during the late Quaternary. Journal of South American Earth Sciences 40: 85-93.
50. Weng, C., M.A. Bush, A.J. Chepstow-Lusty. 2004. Holocene changes of Andean alder (Alnus acuminata) in highland Ecuador and Peru. Journal of Quaternary Science 19: 685-691.
51. Weng, C., H. Hooghiemstra & J.F., Duivenvoorden. 2006. Challenges in estimating past plant diversity from fossil pollen data: statistical assessment, problems and possible solutions. Diversity and Distributions 12: 310-218.
52. Whitlock, C. & C. Larsen. 2001. Charcoal as a fire proxy. In: Smol, J.P., Birks, H.J.B., Last, W.M., (eds) Tracking environmental change using lake sediments. Kluwer, Dordrecht, pp 75-98.
Referencias
BALDOCK, J.W. 1982. Geology of Ecuador-explanatory bulletin of the national geological map of the Republic of Ecuador, scale 1:1,000,000. Ministerio de Recursos Naturales y Energéticos, Dirección General de Geología y Minas, Quito, pp. 11.
BARTHLOTT, W., J. MUTKE, D. RAFIQPOOR, G. KIER & H. KREFT. 2005. Global centers of vascular plant diversity. Nova Acta Leopold 92: 61-83
BECK, E., F. MAKESCHIN, F. HAUBRICH, M. RICHTER, J. BENDIX & C. VALEREZO. 2008. The Ecosystem (Reserva Biológica San Francisco). In: Beck, E., Bendix, J., Kottke, I., Makeschin, F., Mosandl, R., (Eds.), 2008. Gradients in a Tropical Mountain Ecosystem of Ecuador. Ecological Studies 198. Springer, Berlin, Heidelberg, pp. 1-13.
BENDIX, J., R. ROLLENBECK, M. RICHTER, P. FABIAN & P. EMCK. 2008. Climate. In: Beck, E., Bendix, J., Kottke, I., Makeschin, F., Mosandl, R., (eds.), Gradients in a Tropical Mountain Ecosystem of Ecuador. Ecological Studies 198, Springer, Berlin, Heidelberg, pp. 63-73.
BEHLING, H. 1993. Untersuchungen zur spätpleistozänen und holozänen Vegetations- und Klimageschichte der tropischen Küstenwälder und der Araukarienwälder in Santa Catarina (Südbrasilien). Dissertationes Botanicae 206, J. Cramer, Berlin, Stuttgart.
BOSMAN, A., H. HOOGHIEMSTRA & A. CLEEF. 1994. Holocene mire development and climatic change from a high Andean Plantago rigida cushion mire. The Holocene 43: 233-243.
BRENNER, M., D.A. HODELL, J.H. CURTIS, M.F. ROSENMEIER, M.W. BINFORD & M.B. ABBOTT. 2001. Abrupt climate change and Pre-Columbian cultural collapse. In Interhemispheric Climate Linkages, Markgraf V (ed.). Academic Press: San Diego, California. 87–104.
BRUNSCHÖN, C. & H. BEHLING. 2009. Late Quaternary vegetation, fire and climate history reconstructed from two cores at Cerro Toledo, Podocarpus National Park, southeastern Ecuadorian Andes. Quaternary Research 72: 388-399.
BRUNSCHÖN, C. & H. BEHLING. 2010. Reconstruction and visualization of upper forest line and vegetation changes in the Andean depression region of southeastern Ecuador since the last glacial maximum — A multi-site synthesis. Review of Palaeobotany and Palynology 163: 139-152.
BUSH, M.B., B.C.S. HANSEN, D.T. RODBELL, G.O. SELTZER, K.R. YOUNG, B. LEON, M.B. ABBOTT, M.R. SILMAN & W.D. GOSLING. 2005. A 17 000-year history of Andean climate and vegetation change from Laguna de Chochos, Peru. Journal of Quaternary Science 20: 703-714.
BUSH, M.B. & C. WENG. 2007. Introducing a new (freeware) tool for palynology. Journal of Biogeography 34: 377-380.
BUSH, M.B., J.A. HANSELMAN & H. HOOGHIEMSTRA. 2007. Andean montane forests and climate change. In: Bush, M.B., Flenley, J.R. (Eds.), Tropical rainforest responses to climatic change. Springer, Praxis, pp. 33-54.
CHEPSTOW-LUSTY, A., M.R. FROGLEY, B.S. BAUER & M.B. BUSH. 2003. A late Holocene record of arid events from the Cuzco region, Peru. Journal of Quaternary Science 18: 491-502.
COLINVAUX, P.A., M.B. BUSH, M. STEINITZ-KANNAN & M.C. MILLER. 1997. Glacial and postglacial pollen records from the Ecuadorian Andes and Amazon. Quaternary Research 48: 69-78.
EMCK, P. 2007. A Climatology of South Ecuador — With Special Focus on the Major Andean Ridge as Atlantic–Pacific climate Divide. Dissertation, Universität Erlangen, Nürnberg.
FAO. 2006. Global forest resources assessment 2005, Progress towards sustainable forest management. Food and Agricultural Organization of the United Nations, Rome.
FÆGRI, K. & J. IVERSEN. 1989. Textbook of Pollen Analysis, 4th ed. Wiley, Chichester, pp. 328.
FINSINGER W., W. TINNER & F. HU. 2008. Rapid and accurate estimates of microcharcoal content in pollen slides. Pp. 121-124 in Charcoals from the past: cultural and palaeoenvironmental implications. Proceedings of the Third International Meeting of Anthracology, Cavallino-Lecce (Italy), June 28th-July 1st 2004. Archaeopress, Oxford, UK; available from Hadrian Press.
GRIMM, E.C. 1987. CONISS: a Fortran 77 program for stratigraphically constrained cluster analysis by the method of the incremental sum of squares. Computer and Geosciences 13: 13-35.
HANSEN, B.C.S., H.E. WRIGHT & J.P. BRADBURY. 1984. Pollen studies in the Junín area, central Peruvian Andes. Geological Society of America Bulletin 95: 1454-1465.
HANSEN, B.C.S. & D.T. RODBELL. 1995. A Late-Glacial/Holocene pollen record from the eastern Andes of northern Peru. Quaternary Research 44: 216-227.
HANSEN, B.C.S., D.T. RODBELL, G.O. SELTZER, B. LEÓN, K.R. YOUNG & M. ABBOTT. 2003. Late-glacial and Holocene vegetation history from two sides in the western Cordillera of southwestern Ecuador. Palaeogeography, Palaeoclimatology, Palaeoecology 194: 79-108.
HEINE, K. 2000. Tropical South America during the Last Glacial Maximum: evidence from glacial, periglacial and fluvial records. Quaternary International 72: 7-21.
HOOGHIEMSTRA, H. 1984. Vegetation and Climatic History of the High Plain of Bogota, Colombia., Vaduz: J. Cramer.
HOMEIER, J., F.A. WERNER, S.R. GRADSTEIN, S.W. BRECKLE & M. RICHTER. 2008. Potential vegetation and floristic composition of Andean forests in South Ecuador, with a focus on the RBSF. In: Beck, E., Bendix, J., Kottke, I., Makeschin, F., Mosandl, R., (Eds.), Gradients in a Tropical Mountain Ecosystem of Ecuador. Ecological Studies 198, Springer, Berlin, Heidelberg, pp. 87-100.
JANTZ, N., J. HOMEIER, S. LEÓN-YÁNEZ, A. MOSCOSO & H. BEHLING. 2013. Trapping pollen in the tropics-Comparing modern pollen rain spectra of different pollen traps and surface samples across Andean vegetation zones. Review of Palaeobotany and Palynology 193: 57-69
LÆGAARD, S. 1992. Influence of fire in the grass páramo vegetation of Ecuador. In: Balslev, H. & Luteyn, J.L. (eds.) Páramo - An Andean ecosystem under human influence. Academic Press, London. pp. 151-170.
LITHERLAND, M., J.A. ASPEN & R.A. JEMIELITA. 1994. The metamorphic belts of Ecuador. Overseas Memoir of the British Geological Survey 11: 1-147.
LOZANO, P., T. DELGADO & Z. AGUIRRE. 2003. Estado actual de la flora endémica exclusive y su distribucion en el Occidente del Parque Nacional Podocarpus. Funbotánica y Herbario y Jardín Botánico. Loja, Ecuador.
MARCHANT, R., L. ALMEIDA, H. BEHLING, J.C. BERRIO, M. BUSH, A. CLEEF, J. DUIVENVOORDEN, M. KAPPELLE, P. DE OLIVEIRA, A.T. DE OLIVEIRA-FILHO, S. LOZANO-GARCÍA, H. HOOGHIEMSTRA, M.P. LEDRU, B. LUDLOW-WIECHERS, V. MARKGRAF, V. MANCINI, M. PAEZ, A. PRIETO, O. RANGEL & M.L. SALGADO-LABOURIAU. 2002. Distribution an ecology of parent taxa of pollen lodged within the Latin American Pollen Database. Review of Palaeobotany and Palynology 121: 1-75.
MOSCOL OLIVEIRA, M., J.F. DUIVENVOORDEN & H. HOOGHIEMSTRA. 2009. Pollen rain and pollen representation across a forest-páramo ecotone in northern Ecuador. Review of Palaeobotany and Palynology 157: 285-300.
MOSCOL OLIVEIRA, M. & H. HOOGHIEMSTRA. 2010. Three millennia upper forest line changes in northern Ecuador: Pollen records and altitudinal vegetation distributions. Review of Palaeobotany and Palynology 163: 113-126.
NIEMANN, H. & H. BEHLING. 2008. Late Quaternary vegetation, climate and fire dynamics inferred from the El Tiro record in the southeastern Ecuadorian Andes. Journal of Quaternary Science 23: 203-212.
NIEMANN, H. & H. BEHLING. 2009. Late Pleistocene and Holocene environmental change inferred from the Cocha Caranga sediment and soil records in the southeastern Ecuadorian Andes. Palaeogeography, Palaeoclimatology, Palaeoecology 276: 1-14.
NIEMANN, H. & H. BEHLING. 2010. Late Holocene environmental change and human impact inferred from three soil monoliths and the Laguna Zurita multi-proxi record in the southeastern Ecuadorian Andes. Vegetation History and Archaeobotany 19: 1-15.
NIEMANN, H., T. HABERZETTL & H. BEHLING. 2009. Holocene climate variability and vegetation dynamics inferred from the (11700 cal. yr BP) Laguna Rabadilla de Vaca sediment record, southeastern Ecuadorian Andes. The Holocene 19: 307-316.
NIEMANN, H., I. MATTHIAS, B. MICHALZIK & H. BEHLING. 2013. Late Holocene human impact and environmental change inferred from a multi-proxy lake sediment record in the Loja region, southeastern Ecuador. Quaternary International 308: 253-264.
PADUANO, G.M., M.B. BUSH, P.A. BAKER, P.A., FRITZ, S.C. & G.O. SELTZER. 2003. A vegetation and fire history of Lake Titicaca since the Last Glacial Maximum. Palaeogeography, Palaeoclimatology, Palaeoecology 194: 259-279.
PODWOJEWSKI, P., J. POULENARD, T. ZAMBRANA & R. HOFSTEDE. 2002. Overgrazing effects on vegetation cover and properties of volcanic ash soil in the páramo of Llangahua and La Esperanza (Tungurahua, Ecuador). Soil Use Managemant 18: 45-55.
RANGEL, O. 2006. Síntesis final: Visión integradora sobre la región del páramo. Diversidad Biótica III. La región de la vida paramuna. Universidad Nacional de Colombia. Bogotá D.C. Pp: 816-838.
RODBELL, D.T. 1994. The timing of the last deglaciation in Cordillera Oriental, Northern Peru based on glacial geology and lake sedimentology. Geological Society of America Bulletin 105: 923-934.
RODRÍGUEZ, F. & H. BEHLING. 2011. Late Holocene vegetation, fire, climate and upper forest line dynamics in the Podocarpus National Park, south-eastern Ecuador. Vegetation History and Archaeobotany 20: 1-14.
RODRÍGUEZ, F. & H. BEHLING. 2012. Late Quaternary vegetation, climate and fire dynamics, and evidence of early to mid-Holocene Polylepis forests in the Jimbura region of the southernmost Ecuadorian Andes. Palaeogeography, Palaeoclimatology, Palaeoecology 350-352: 247-257.
SADORI, L. & M. GIARDINI. 2007. Charcoal analysis, a method to study vegetation and climate of the Holocene: The case of Lago di Pergusa (Sicily, Italy). Geobios 40: 173-180.
SCHUBERT, C. & C.M. CLAPPERTON. 1990. Quaternary glaciations in the Northern Andes (Venezuela, Colombia and Ecuador). Quaternary Science Reviews 9: 123-135.
STUIVER, M., P.J. REIMER & R.W. REIMER. 2005. CALIB 6.0. Radiocarbon Calibration Program. URL: http://calib.qub.ac.uk/calib/calib.html
VALDEZ, F. 2008. Inter-zonal relationships in Ecuador. In: Silverman H, Isbell WH (eds) Handbook of South American archeology. Springer, New York, pp. 865-888.
VÉLEZ M.I., H. HOOGHIEMSTRA, S. METCALFE, M. WILLE & J.C. BERRÍO. 2006. Late Glacial and Holocene environmental and climatic changes from a limnological transect through Colombia, northern South America. Palaeogeography, Palaeoclimatology, Palaeoecology 234: 81-96.
VILLOTA, A., S. LEÓN-YÁNEZ & H. BEHLING. 2012. Vegetation and environmental dynamics in the Páramo of Jimbura region in the southeastern Ecuadorian Andes during the late Quaternary. Journal of South American Earth Sciences 40: 85-93.
WENG, C., M.A. BUSH, A.J. CHEPSTOW-LUSTY. 2004. Holocene changes of Andean alder (Alnus acuminata) in highland Ecuador and Peru. Journal of Quaternary Science 19: 685-691.
WENG, C., H. HOOGHIEMSTRA & J.F., DUIVENVOORDEN. 2006. Challenges in estimating past plant diversity from fossil pollen data: statistical assessment, problems and possible solutions. Diversity and Distributions 12: 310-218.
WHITLOCK, C. & C. LARSEN. 2001. Charcoal as a fire proxy. In: Smol, J.P., Birks, H.J.B., Last, W.M., (eds) Tracking environmental change using lake sediments. Kluwer, Dordrecht, pp 75-98.
Cómo citar
APA
ACM
ACS
ABNT
Chicago
Harvard
IEEE
MLA
Turabian
Vancouver
Descargar cita
CrossRef Cited-by
1. K. Hagemans, D.H. Urrego, W.D. Gosling, D.T. Rodbell, F. Wagner-Cremer, T.H. Donders. (2022). Intensification of ENSO frequency drives forest disturbance in the andes during the holocene. Quaternary Science Reviews, 294, p.107762. https://doi.org/10.1016/j.quascirev.2022.107762.
2. Sofía Muñoz-Tobar, Michael Caterino. (2020). Mountains as Islands: Species Delimitation and Evolutionary History of the Ant-Loving Beetle Genus Panabachia (Coleoptera, Staphylinidae) from the Northern Andes. Insects, 11(1), p.64. https://doi.org/10.3390/insects11010064.
3. Gonzalo R. Torres, Claudio F. Pérez, Liliana C. Lupo. (2019). Altitudinal patterns of wind transport and deposition of Yungas tree pollen in northwestern Argentina: Implications for interpreting the Quaternary fossil record. Palaeogeography, Palaeoclimatology, Palaeoecology, 520, p.66. https://doi.org/10.1016/j.palaeo.2019.01.013.
4. John All, Michael Medler, Sylvie Arques, Rebecca Cole, Tommy Woodall, Justin King, Jun Yan, Carl Schmitt. (2017). Fire Response to Local Climate Variability: Huascarán National Park, Peru. Fire Ecology, 13(2), p.85. https://doi.org/10.4996/fireecology.130288764.
Dimensions
PlumX
Visitas a la página del resumen del artículo
Descargas
Licencia
Derechos de autor 2014 Caldasia
Esta obra está bajo una licencia internacional Creative Commons Atribución 4.0.
Aquellos autores/as que tengan publicaciones con esta revista, aceptan los términos siguientes:
- Los autores/as conservarán sus derechos de autor y garantizarán a la revista el derecho de primera publicación de su obra, el cual estará simultáneamente sujeto a la Licencia de reconocimiento de Creative Commons que permite a terceros compartir la obra siempre que se indique su autor y su primera publicación esta revista.
- Los autores/as podrán adoptar otros acuerdos de licencia no exclusiva de distribución de la versión de la obra publicada (p. ej.: depositarla en un archivo telemático institucional o publicarla en un volumen monográfico) siempre que se indique la publicación inicial en esta revista.
- Se permite y recomienda a los autores/as difundir su obra a través de Internet (p. ej.: en archivos telemáticos institucionales o en su página web) antes y durante el proceso de envío, lo cual puede producir intercambios interesantes y aumentar las citas de la obra publicada. (Véase El efecto del acceso abierto).