Holocene climatic and environmental change from pollen records of
Transcription
Holocene climatic and environmental change from pollen records of
Review of Palaeobotany and Palynology 136 (2005) 63 – 92 www.elsevier.com/locate/revpalbo Holocene climatic and environmental change from pollen records of lakes Zempoala and Quila, central Mexican highlands L. Almeida-Lenero a, H. Hooghiemstra b,*, A.M. Cleef b, B. van Geel b a Departamento de Ecologı́a y Recursos Naturales, Facultad de Ciencias, Universidad Nacional Autónoma de México, C.P. 04510, México D.F. México b Institute for Biodiversity and Ecosystem Dynamics (IBED), Paleoecology and Landscape ecology, University of Amsterdam, Kruislaan 318, 1098 SM Amsterdam, The Netherlands Received 22 April 2004; received in revised form 20 April 2005; accepted 12 May 2005 Abstract Pollen records of a 520-cm long core from Lake Zempoala (2800 m altitude) and a 884-cm long composite core from Lake Quila (3010 m altitude), both located 65 km SW of Mexico City, show changes in vegetation and climate. The Zempoala record covers the last c. 6320 cal yr BP, while the Quila record spans the last c. 11,610 cal yr BP. These lakes, with submerged aquatics and hydroseral shore vegetation, lie today in the Abies religiosa-dominated forest belt. From c. 6320 to 2530 cal yr BP Zempoala shows a mixed forest with mesophyllous taxa, indicating warmer and more humid conditions than at present. From c. 2530 to 160 cal yr BP Abies forest and Pinus hartwegii forest dominated, indicating a temperate climate. During the first part of this period, from c. 2530 to 1150 cal yr BP abundant Pinus forest is indicative of drier climate conditions. During the last c. 310 cal yr of this period Abies-dominated forest prevailed, with a floral composition resembling the modern Abies forests. This is indicative of temperate and humid climatic conditions. During the last c. 160 cal yr BP the presence of Zea mays and Plantago reflect human impact. From c. 11,610 to 10,650 cal yr BP Quila shows Alnus- and Pinus-dominated forest, reflecting humid climatic conditions. From 10,650 to 5000 cal yr BP Pinus and Arceuthobium are indicative of a Pinus hartwegii forest, suggesting slightly lower temperatures than at present. A 25-cm thick volcanic ash horizon at 380–355 cm core depth is the well-known dyellow ashT marker with a known age of c. 4200–4800 14C yr BP. This age is supported by our bracketing dates of 5620 and 4650 14C yr BP. From 4630 to 1000 cal yr BP mixed forest, including Pinus, Quercus, Carpinus, Hedyosmum, Juglans and Artemisia, is indicative of mesophytic conditions. From 4630 to 1010 cal yr BP Abies forest was abundant, reflecting colder and more humid conditions. From c. 1010 to 20 cal yr BP Pinus forest was very abundant suggesting, as in site Zempoala, dry climatic conditions. The pollen record from Quila documents four different types of forest: Pinus/Alnus forest (possibly Alnus jorullensis in zone QUI-I), Pinus forest (most likely Pinus hartwegii forest in zone QUI-II), mixed forest in zone QUI-III), and Abies forest (Abies religiosa forest in zone QUI-IV). The last c. 1000 years show a decline of mixed forest and increasing Abies forest, reflecting cooler and more humid conditions. Quila also shows, during the most recent past, human impact by crop cultivation (Zea mays) * Corresponding author. E-mail addresses: [email protected] (L. Almeida-Lenero), [email protected] (H. Hooghiemstra). 0034-6667/$ - see front matter D 2005 Elsevier B.V. All rights reserved. doi:10.1016/j.revpalbo.2005.05.001 64 L. Almeida-Lenero et al. / Review of Palaeobotany and Palynology 136 (2005) 63–92 and vegetation disturbance (Plantago) leading to erosion. Other microfossils, among which coprophilous fungi, were recorded and illustrated. D 2005 Elsevier B.V. All rights reserved. Keywords: Mexico; environmental change; pollen analysis; Holocene; coprophilous fungi 1. Introduction Pollen records from tropical mountains are sensitive recorders of climatic change as vertical migration of the main vegetation belts occurred over only hundreds of meters. Therefore, the source areas of the pollen grains stay at a close distance to the archiving lake sediments all the time. Fine examples of such pollen-based records of climate change come from Colombian lake sediments. The lacustrine sediments of Lake Fuquene (e.g. van Geel and van der Hammen, 1973; Mommersteeg, 1998) and the sediments of the high plain of Bogotá, formerly a lake that drained before the last glacial maximum (LGM) (e.g. Hooghiemstra, 1984; van ’t Veer et al., 2000) document environmental history with a centennial to millennial scale resolution. The site inventory of the Latin American Pollen Database (LAPD, 1996) provides a list of available pollen records in Latin America; several are close to our study area and relevant for comparison purposes (Fig. 1). The region northwest of our study area includes the sites Pátzcuaro (Michoacán State), Yuriria and La Hoya (Guanajuato State). Closest to our study area lies the Upper Lerma Basin, Texcoco and Chalco lakes (Caballero and Ortega, 1998), and the Tlaloc crater site. Relevant sites from the Yucatan Peninsula are sites Lake Chichancanab and Lake Punta Laguna. Bradbury (2000) documented environmental change on the basis of pollen, diatoms and geochemical records from Lake Pátzcuaro. In this lake, climatic conditions during the mid-Holocene were similar to the present conditions. Evidence of the start of agricultural activities was found from c. 4000 cal yr BP onwards. Based on the interpretation of magnetic, geochemical and palaeoecological data from Lake La Hoya, Lake Yuriria and Lake Pátzcuaro, Metcalfe et al. (1994) reconstructed long-term variations in water levels. Episodes with high water levels show evidence of accelerated erosion, indicative of a change in rainfall c. 3600 cal yr BP. Closest to the lakes described here, in the Upper Lerma Basin (Fig. 1) Metcalfe et al. (1991) documented climatic change and anthropogenic disturbance. Their study was based on sediment chemistry, losson-ignition (LOI), mineral magnetism, and fossil diatom assemblages, and provided evidence for environmental changes since 11,580 F 70 14C yr BP (c. 13,800–13,400 cal yr BP). They showed that freshwater lakes developed since this date alternating, during dry episodes, with acidic marshes. They attributed an important phase of accelerated erosion around 3100 cal yr BP to human disturbance, which culminated around 1400–700 cal yr BP. Caballero et al. (2002) studied site Sta. Cruz Atizapan in the Upper Lerma Basin and found, based on diatoms, a rise of the lake level at 7000 BP, while in the same basin site Almoloya Lake showed lowering water levels at 6200 14C yr BP. In the Basin of Mexico a reconstruction of late Quaternary lake level changes in Lake Texcoco and Lake Chalco (Fig. 1) was published by Bradbury (1971, 1989). These studies were based on diatoms and showed the development of marshes during the last 10,000 years. González-Quintero and FuentesMata (1980) analyzed pollen from the sediments of Lake Texcoco (Fig. 1) and from archaeological excavations. Evidence of human activity was recorded since 3000 14C yr BP. González-Quintero (1981, 1986) studied three archaeological profiles from the northern border of Lake Chalco. Lozano et al. (1993) and Lozano and Ortega (1994, 1998) used pollen, diatoms, palaeomagnetic properties and LOI records from sediments of lakes Chalco and Texcoco. They documented environmental change during the early and middle Holocene and, again, reported human disturbance since c. 3000 14C yr BP. In their pollen-based environmental reconstructions of the lakes Chalco and Texcoco, Lozano and Xelhuantzi-López (1997) reported a strong impact of volcanism on the vegetation (Caballero et al., 1999). Finally, historical records were used by O’Hara and Metcalfe (1995) to evaluate human impact during the late Holocene and its relationships 25o 19o05’ N L. Quila 20o 10 3 12 3 11 12 Temperate forest Guatemala 110o 15o 100o 90o Mexico City 7 V. Iztaccihuatl 5230 m 19o15’ 3000 Toluca City 2900 8 4000 3500 o 99 30’ o V. Popocatepetl 5465 m 99 00’ 3000 V. Nevado de Toluca 4590 m 19o00’ 98o30’ L. Zempoala 3000 2900 3500 3000 4000 3500 9 5 6 19o00’ 10 km 6 3000 4 99o18’ L. Almeida-Lenero et al. / Review of Palaeobotany and Palynology 136 (2005) 63–92 5 Gulf of Mexico Pacific Ocean Fig. 1. (A) Map showing the main vegetation types of central and southern Mexico and the location of relevant sites mentioned in the text. (B) Detailed geographical map of the area south of Mexico City showing the selected sites and the relevant part of the Trans-Mexican Volcanic Belt where the study area is located; (C) Map showing the geographical location of Lake Zempoala at 2800 m, and Lake Quila at 3010 m altitude in the National Park Lagunas de Zempoala, 65 km southwest of Mexico City. Explanation of the numbers: Michoacán State: 1 = Lake Pátzcuaro, 2 = Zacapu Basin. Guanajuato State: 3 = La Piscina de Yuriria. Estado de Mexico: 4 = Upper Lerma Basin, 5 = Lake Quila, 6 = Lake Zempoala. Basin of Mexico: 7 = Texcoco, 8 = Chalco. Tlaxcala State: 9 = Tlaloc crater. Yucatán: 10 = Lake Chichancanab, 11 = Lake Punta Laguna. Guatemala: 12 = Lake Peten–Itza. 65 66 L. Almeida-Lenero et al. / Review of Palaeobotany and Palynology 136 (2005) 63–92 with climatic change in central Mexico. They concluded climatic change starting some 4000 years ago had a considerable impact on sedentarism and agriculture. The late Quaternary lacustrine records from sites Tlaloc-I and Tlaloc-II, a crater of La Malinche volcano (Puebla-Tlaxcala; Fig. 1), also lie close to our sites. These records, although with poor time control, show the vegetation history from Lateglacial time to the present (Ohngemach and Straka, 1983; Straka and Ohngemach, 1989). During the last 5000 years in particular, temperature and precipitation changed repeatedly. On the Yucatán Peninsula, climate variability and its possible implications for the Mayan civilization were studied on the basis of proxies (oxygen isotopes of ostracods and gastropods) from Lake Punta Laguna (Fig. 1). The Punta Laguna record is indicative of multi-decadal and millennial scale changes in the oxygen isotope records during the late Holocene. These changes reflect successive wet and dry episodes that may have influenced the cultural evolution in Mesoamerica (Curtis et al., 1996; O’Hara and Metcalfe, 1997). At Lake Chichancanab (Fig. 1), a continuous record of Holocene climatic change was reconstructed by Hodell et al. (1995, 2001) using temporal variations in oxygen isotopes and sediment composition. During the middle and late Holocene the interval between 1300 and 1100 cal yr BP was driest and coincided with the collapse of the Maya civilization at the end of its dClassic PeriodT. In Central America, south of Mexico, there are pollen studies from Guatemala (Islebe et al., 1996a) and Curtis et al. (1998) of Lake Peten–Itza (Fig. 1) including pollen, stable isotope analyses of ostracods and gastropods, geochemistry, elemental composition, and magnetic susceptibility. Holocene climatic change as well as human influence on the regional environment were recorded. In Costa Rica, the bogs La Chonta (Hooghiemstra et al., 1992) and La Trinidad (Islebe and Hooghiemstra, 1995) were studied. The record of La Chonta (at 2310 m altitude) shows that the bog was successively situated in the paramo belt, in the subalpine rainforest belt, and finally in the upper montane forest belt, reflecting vertical shifts of the upper forest line (UFL) of c. 1400 m during the last c. 80,000 years. The pollen record of La Trinidad bog, at 2700 m altitude, shows the postglacial development of the montane oak forest belt from c. 9500 to 1500 14C yr BP. Based on the analysis of pollen and charcoal fragments, Horn (1993) studied the vegetation history in the Costa Rican Chirripó Mountains in relation to the fire history. Pollen, sediment and isotope data of Lake Quexil in Guatemala (Fig. 1) have demonstrated a change from dry climatic conditions during the late Pleistocene, to more mesic conditions with higher temperatures during the Holocene (Leyden, 1984; Leyden et al., 1993, 1994). Multi-site studies were successively carried out by Brown (1985), Markgraf (1993), Bradbury (1997, 2000), Metcalfe et al. (2000) and Marchant et al. (in review). For selected time windows since the LGM a synthesis of vegetation and climatic change is available for the Mexican area. The impact of humans and/or herbivores on the vegetation in the past can often be inferred from the presence of pollen grains of light-demanding plants indicative of open vegetation and taxa characteristic of eutrophic conditions. Eutrophication of lakes is often caused by the input of excrement and other settlement-related organic waste. Humans and herbivores may have been responsible for creating new habitats, or at least changing the natural environment. Selected taxa of fungal spores are good environmental indicators, such as the characteristic fungi on mammal dung, mainly from herbivores. The spores of coprophilous ascomycetes can be very common in sediments from archaeological sites (Buurman et al., 1995; van Geel et al., 1986a, 2003). Davis (1987) used records of the coprophilous fungus Sporormiella to document the abundance of large herbivores in North America. The increase of Sporormiella in sediments of historic age is indicative of the increasing grazing pressure after the introduction of domesticated herbivores (Davis, 1987). Not all fungal spores preserve as fossils. Preservation depends on the thickness of spore wall and mycelium. As a consequence, normally only spores of thick-walled ascomycetes and Dematiaceae (Fungi Imperfecti with dark, relatively thick spore walls) are preserved. The indicator value of non-pollen palynomorphs is not fully exploited by palynologists and it is our aim in this paper to attract attention to these palynomorphs (van Geel, 1978, 2001; van Geel et al., 1989, 1994, 1995, 2003). The aim of the present study is to document the pollen-based vegetation change from Zempoala and Quila, and to compare the inferred climate history L. Almeida-Lenero et al. / Review of Palaeobotany and Palynology 136 (2005) 63–92 with other relevant sites in the central Mexican mountains. We use pollen grains, spores and algae, and also other microfossils rarely documented in Latin American palaeoecological studies. The most relevant nonpollen palynomorphs are illustrated and described. We aim to assess the start of Mesoamerican agriculture and deforestation in the study area, and we will compare the palynological evidence for early civilizations with archeological records. 67 Tres Cumbres, Morelos, Mexico (2810 m alt.) o C (14-20) o 9.9 C 1724.6 mm. T-: 7 T+: 12 P-: 8.4 P+: 392 400 200 50 80 30 40 20 10 2. Environmental setting of the study area 2.1. Geography and climate The lakes of Zempoala (2800 m altitude, 19803VN, 99818VW) and Quila (3010 m altitude, 19804VN, 99819VW) are located in the central part of the TransMexican Volcanic Belt (TMVB) (SPP, 1979; Metcalfe, 1997) 65 km southwest of Mexico City (Fig. 1). Both lakes are located within the dParque Nacional Lagunas de ZempoalaT at the base of the Cerro Chalchihuites and are located in different endorheic basins (Bonilla, 1992). The surrounding mountains consist of volcanic rock (Fries, 1960) and the soils around the lakes are humid Andosols. Subterraneous discharge through volcanic ash layers in the valleys causes marked seasonal differences in water levels (Sosa, 1935). The climate of the study area is characterized by an average annual temperature of 5–12 8C and monthly precipitation of 1720 mm. Temperatures show a strong daily fluctuation (Fig. 2). The rainy season generally lasts from June to October and the dry season lasts from November to May (Garcı́a, 1988). As a consequence, the studied endorheic depressions experience significant annual lake level fluctuations (Sosa, 1935). During January and February the lakes of Zempoala and Quila are frequently covered with ice due to their high elevation. Based on a study along the slope of the volcano Pico de Orizaba, some 250 km west of our study area, we use a temperature gradient of 0.6 8C per 100 m displacement of the UFL (Lauer and Klaus, 1975; Wille et al., 2001). 2.2. Regional and local vegetation In the Zempoala National Park, forests are dominated by Quercus (oak), Pinus (pine) and Abies 0 J F M A M J J A S O N D 0 Fig. 2. Climate diagram of Tres Cumbres, located at 2810 m altitude and at 10 km distance from Lake Zempoala, Mexico. (fir) (Miranda and Hernández-X, 1963). Several vegetation belts, with distinct altitudinal distributions and characteristic arboreal composition, can be recognized in this area (Fig. 3). The lower montane forest belt (1800–2800 m) includes dmesophyllous forestT with Carpinus caroliniana, Garrya laurifolia, Tilia houghii and Acalypha phleoides (Luna et al., 1989). However, the same altitudinal interval on exposed mountain ridges and on drier slopes becomes a dmixed forestT (2400–2800 m) where Quercus laurina, Arbutus xalapensis and Pinus montezumae coexist with species of Salix and Viburnum. In the upper montane forest belt (2800– 3700 m) we can recognize two forest types at different altitudinal intervals. From 2800 to 3550 m Abies religiosa-dominated forest occurs, with Roldana angulifolia and Thuidium delicatulum in the understory (Miranda and Hernández-X, 1963). From 3550 to 3700 m Pinus hartwegii-dominated forest with Festuca tolucensis and Festuca amplissima is common (Lauer, 1978). In and around the lakes submerged aquatic vegetation, swamp vegetation and shore vegetation is present. Today the shores and nearby surroundings of lakes Zempoala and Quila are covered by grasslands, surrounded by Abies religiosa forest. Under natural conditions forest would probably reach very close to the lake shore. The present-day vegetation around Lake Zempoala includes representatives of 49 families, 107 genera and 153 species of vascular plants (Islebe and ter Weijden, 1988; Bonilla and Novelo, 1995). 68 L. Almeida-Lenero et al. / Review of Palaeobotany and Palynology 136 (2005) 63–92 Vegetation Types (m alt.) Alpine Zacatonal (3700 m alt.) Caryophyllaceae, Plantago Pinus hartwegii forest (3550-3700 m alt.) Arceuthobium, Brassicaceae, Eryngium, Upper montane forest Geraniaceae, Pinus, Poaceae 3500 Coniferous forest 2800-3700 m alt. 3000 Abies religiosa forest (2800-3550 m alt.) Abies religiosa, Asteraceae, Cupressus, Salvia, Symphoricarpos, Onagraceae Lake Quila Mixed forest (2400-2800 m alt.) Lake Zempoala Quercus, Alnus, Salix 2500 Lower montane forest 1800-2800 m alt. Mesophyllous forest (1800-2400 m alt.) Acalypha, Arbutus, Artemisia, Carpinus, Hedyosmum, Juglans, Leguminosae, Melastomataceae, Rubiaceae, Scrophulariaceae, Thalictrum, Viburnum 2000 Fig. 3. Schematic cross-section from south (left) to north (right) through the study area showing the position of Lakes Zempoala and Quila. The modern altitudinal distribution of the main forest types and the main taxa in each vegetation belt, as far as relevant for a palynological analysis, are indicated. The azonal swamp vegetation of Lake Quila is dominated by aquatic and semi-aquatic elements, such as Eleocharis densa, Cardamine flaccida, Isoetes mexicana and Typha latifolia (Bonilla, 1992; Bonilla and Novelo, 1995). At a short distance from the coring site, the submerged and heliophytic vegetation of Lake Quila was described by Islebe and ter Weijden (1988) and Islebe et al. (2003). At the coring site in Lake Zempoala we recognized four main vegetation types: 1) Agrostis bourgaei and Glyceria lurida, 2) Carex lurica, 3) Eleocharis acicularis and Polygonum punctatum, and 4) Potamogeton pusillus and Ranunculus trichophyllus (Bonilla and Novelo, 1995; Almeida-Leñero and Cleef, 1997). Aquatic communities occur in these lakes with mainly Myriophyllum aquaticum (hydrophytes with floating roots), Potamogeton illinoensis, Eleocharis densa (hydrophytes with submersed roots), and heliophytic vegetation with Arenaria paludicola, Ranunculus hydrocharoides and Juncus ebracteatus. Along the lake shore, grasses such as Polypogon viridis and Muhlenbergia repens occur, but also Rumex obtusifolia (Bonilla, 1992; Bonilla and Novelo, 1995; Islebe and ter Weijden, 1988; Islebe et al., 2003). 3. Material and methods The sediment cores were collected with a handoperated Dachnowsky corer using increments of 25cm length (Faegri and Iversen, 1989). Sediment cores were wrapped in plastic bags and protected by rigid pvc-tubing. An horizon with volcanic ash and sand at 355 cm core depth in Lake Quila meant that sediments had to be collected in two intervals. At some 25 cm from the first core we penetrated this horizon using an Edelman corer (Faegri and Iversen, 1989) and removed these coarse sediments. Subsequently, we collected the sediment from 410 to 884 cm core depth. As a consequence the Quila-I core represents the interval from 5 to 380 cm, and the Quila-II core includes the core interval from 411 to 884 cm. Sediment cores were transported to Amsterdam and kept in cool and dark conditions. Samples of a known volume of c. 2 cm3 were collected at 5-cm intervals along the core. For pollen analyses, 100 samples were obtained from core Zempoala and 101 from cores Quila. Radiocarbon dating of selected organic horizons provided time control. We dated 6 bulk samples from core Zempoala and 4 bulk samples from core Quila. The dates were calibrated using Calib 4.2 Botryococcus* Fungal spores* Moss (like) spores* Pediastrum* Spirogyra* Zygnema-type* 69 Cyperaceae* Hydrocotyle* Isoetes* Myriophyllum* Potamogeton* Typha* Other elements Cyatheaceae* Hymenophyllum* Lycopodium foveolate* Monolete psilate* Monolete verrucate* Aquatics Apiaceae Chenopodiaceae Dodonaea Polygonaceae Rumex Solanaceae Urticales Zea mays Pteridophytes Arceuthobium Brassicaceae Eryngium Pinus Poaceae Caryophyllaceae Plantago Taxa marked with an asterisk are not included in the pollen sum. Pinus hartwegii Abies religiosa Zacatonal Abies Alnus Asteraceae Quercus Cupressus Salix Lamiaceae Symphoricarpus Acalypha Anacardiaceae Arbutus Artemisia Carpinus Euphorbiaceae Hedyosmum Leguminoseae Melastomataceae Rubiaceae Scrophulariaceae Thalictrum Viburnum Mixed forest Mesophytic forest Human impact Fir forest Alpine bunch grassland Pine forest (Stuiver and Reimer, 1993) and the calibration curve INTCAL98 (Stuiver et al., 1998). We have not tried to calibrate dinterpolatedT or dextrapolatedT radiocarbon ages as substantial uncertainties make such a procedure meaningless. Prior to processing, one tablet of exotic Lycopodium spores was added to each sample for calculation of the pollen concentration values. All samples were prepared using standard pretreatment techniques including solution in sodium pyrophosphate, acetolysis, and heavy liquid separation by bromoform (Faegri and Iversen, 1989). Pollen residues were mounted in a glycerin gelatin medium, sealed with paraffin, and analyzed with a Zeiss microscope at 400 magnification. For identification of pollen grains and spores we used the pollen reference collection of the University of Amsterdam, in combination with the pollen morphological publications of Ohngemach and Straka (1983), Hooghiemstra (1984), and van der Hammen and González (1963). Results of the pollen analysis were graphed as a pollen percentage diagram. The pollen sum consists of all arboreal and herbaceous taxa of the regional vegetation. Most pollen spectra have a pollen sum of 400 grains. Pollen grains from aquatic taxa and spores of ferns, mosses, fungi, colonies of algae and other microfossils were excluded from the pollen sum. We arrived at the following ecological groups: (1) Pinus (representing the altitudinal zone of pine forests), (2) Abies (representing the altitudinal zone of fir forest), (3) mixed forest taxa, (4) mesophyllous forest taxa, (5) taxa characteristic of human impact, (6) aquatics, (7) pteridophytes, (8) algae, (9) other microfossils (Table 1). The group of other microfossils includes various fungal spores types, Rivularia-type (Cyanobacteria), charred epidermis fragments of grasses, leaf-spines of the hydrophyte Ceratophyllum (the pollen grains of this plant do not fossilize), and remains of Azolla. Horizons in which sediments showed abundant fragments of volcanic ash (tephra) under binocular analysis, also revealed fine ash fragments in the microscope slides. Pollen diagrams were plotted with the software TILIAGRAPH. For calculations we used TILIA and for the cluster analysis of terrestrial pollen taxa we used CONISS (Grimm, 1987). Important changes in the composition of the pollen spectra and/or significant changes in representation of the dominant taxa characterize the boundaries between pollen zones. Table 1 Identified pollen and spore taxa from the sediments from the cores of lakes Zempoala and Quila (central Mexico highlands) arranged according to present-day altitudinal and ecological affinity L. Almeida-Lenero et al. / Review of Palaeobotany and Palynology 136 (2005) 63–92 70 L. Almeida-Lenero et al. / Review of Palaeobotany and Palynology 136 (2005) 63–92 Table 2 Lithological sequence of core Zempoala, and composite core Quila-1/ Quila-2 Depth (cm) Description Zempoala 0–80 80–120 120–180 180–260 Red brown organic sediments Peat, suspected ash at 110–115 cm Clay Sandy peat (very fibrous macros in the bottom), ash at 260–243 cm 260–330 Clay 330–415 Peat 415–520 Dark clay, rich in organic material Quila-1 0–100 Clay, with a volcanic ash horizon at 70–75 cm 100–355 Peat, rich in organic material with a volcanic ash horizon at 110 cm 355–380 Volcanic ash Quila-2 411–530 Gray clay with dark horizons 530–830 Peat, with thin intercalations of sandy clay at 530 cm and 600 cm, and water-logged sediments at 730 cm 830–884 Dark sandy clay of the Pico de Orizaba, on the Nevado de Toluca from 2600 to 4200 m, and on the volcano Malinche from 3000 to 4000 m. We also used the results from the Central American Guatemalan highlands (Islebe and Hooghiemstra, 1995) where this relationship was studied along a transect from 2800 to 4200 m. The interpretation of the pollen records representing the local vegetation has been based on the studies of modern plant communities by Islebe and ter Weijden (1988) and Islebe et al. (2003). For ecological ranges of taxa we also used Marchant et al. (2002). 4. Results 4.1. Stratigraphy The main changes in the lithology of the sediment cores are described in Table 2 and are shown in the summary of pollen diagrams. 4.2. Chronological control The interpretation of the pollen records is supported by modern pollen rain studies along altitudinal gradients from comparable settings not farther than 200 km from our lakes, which show the relationship between pollen representation and vegetation cover. We used the results from Ohngemach and Straka (1983) in particular; they showed the relationship between vegetation and modern pollen rain along an altitudinal transect from 3000 to 4600 m on the slopes In the Zempoala core three depth intervals were selected for time control where the organic carbon content of the sediments was most promising. In each interval two bulk samples from a 3 cm core section were collected for dating (Table 3). The three sets of two samples revealed ages that differed by less than 200 radiocarbon years, and all 6 samples are in chronological sequence. We conclude Table 3 Radiocarbon dates, calibrated age ranges (at 1 S.D.), and type of dated sediment from the cores of lakes Zempoala and Quila Depth (cm) Age: 14 C yr BP Age: cal yr BP (1 S.D.) Sediments Lab. number Lake Zempoala 190–186 195–191 370–366 375–371 490–485 495–491 580 F 70 620 F 70 2110 F 200 2110 F 130 4460 F 100 4580 F 120 540–650 550–650 1870–2340 1930–2300 5290–4890 5460–5050 Peat Peat Peat Peat Clay Clay GrN-18727 GrN-18728 GrN-18729 GrN-18730 GrN-18731 GrN-18732 Lake Quila 324–321 430–427 780–777 860–857 4650 F 60 5620 F 38 8480 F 80 9713 F 45 5470–5310 6310–6440 9330–9540 11,090–11,200 Peat Peat Peat Clay UtC-5343 UtC-5344 UtC-5400 UtC-5401 y13CLake Zempoala 24.6 24.3 22.5 24.1 L. Almeida-Lenero et al. / Review of Palaeobotany and Palynology 136 (2005) 63–92 that sediment accumulation rate is close to linear (Fig. 4). Time control of the sediments from Lake Quila is based on four bulk radiocarbon dates collected between 860 and 320 cm depth. Obtained ages are in chronological sequence and the plot of the depth vs. age (Fig. 4) shows a more or less linear accumulation rate for the lower and upper parts of the Quila core, separated by a volcanic ash horizon. The age of 71 this well known volcanic ash marker bed is c. 4200– 4880 14C yr BP (Limbrey, 1986) and fits well the interpolated age based on our bracketing ages of 5620 F 38 14C yr BP and 4650 F 60 14C yr BP. On the basis of the pollen concentration record, 14C ages and lithology, intervals with different sediment accumulation rates can be recognized. These differences relate to clay accumulation in the lower part of the core, and accumulation of peat and clay, intercalated Fig. 4. Graph showing depth vs. calendar age of sediments from Lake Quila (top) and Lake Zempoala (bottom), central Mexico. Bars indicate the possible range in calendar age (1r). For core Quila, the interval in between dotted lines represents the volcanic ash horizon, which separates the upper and lower parts of the sequence. 72 L. Almeida-Lenero et al. / Review of Palaeobotany and Palynology 136 (2005) 63–92 with volcanic ash in the upper part (above 415 cm) of the core. 4.3. Records of other microfossils A number of microfossil types, rarely registered during routine analysis, have been documented in this study. These microfossils were very well preserved. Their descriptions are given in Appendix A and photographs are presented in Plates I and II. 4.4. Characterization of the pollen diagrams 4.4.1. Lake Zempoala The pollen diagrams from Lake Zempoala show the most important fossil pollen and spore taxa out of the 42 different types that have been identified (Figs. 5 and 6). Pollen concentration values vary mainly from 20.103 to 150.103 grains cm 3 of sediment. Based on the CONISS cluster analysis, two main zones could be recognized, each with subdivisions. The ages of the zones are given in calendar years and based on the calculated dcal yr BPT-scale shown in Fig. 6. Zone ZEM-IA 520–422.5 cm 20 samples Zone ZEM-IB 422.5–392.5 cm 6 samples Zone ZEM-IIA 392.5–282.5 cm 22 samples Zone ZEM-IIB 282.5–102.5 cm 37 samples Zone ZEM-IIC 102.5–27.5 cm 13 samples Zone ZEM-IID 27.5–10 cm 3 samples c. 6320–3140 cal yr BP c. 3140–2530 cal yr BP c. 2530–1150 cal yr BP c. 1150–310 cal yr BP c. 310–180 cal yr BP c. 180–160 cal yr BP Zone ZEM-I is characterized by Pinus (34–63%, max. 72%), Quercus (2–22%), Salix (0.6–14%, max. 20%), Alnus (0.5–15%), and by a low representation of Poaceae (0.6–9%), Abies (0–5%, max. 9%), Asteraceae (0.2–4%), and Rubiaceae (0–5%). Aquatic taxa have very low values. In zone ZEM-1 two subzones (ZEM-1A and ZEM-1B) were distinguished. In zone ZEM-IA Pinus shows lowest values compared to the remaining part of the record, whereas Quercus, Alnus and Salix show highest percentages, and Artemisia and Brassicaceae are also important. Zone ZEM-IA includes two radiocarbon dates of 4580 F 120 14C yr BP and 4460 F 100 14C yr BP. In zone ZEM-IB Cupressus is represented for the first time and temperate elements show higher percentages. Potamogeton is better represented than in ZEM-IA. Zone ZEM-II is characterized by Pinus (28–88%), Abies (0–17%, max. 29%), Salix (9–13%, max. 20%), Alnus (0–9%, max. 18%) and Quercus (0–16%) and by the consistent presence of Asteraceae and Poaceae. Taxa belonging to the local vegetation, such as Cyperaceae, Anthoceros–Hymenophyllum, bryophyte spores and fungal spores show marked fluctuations. Compared to zone ZEM-I, the most important change is the significant increase of Pinus and Abies, a minor increase of Arceuthobium, Melastomataceae and Euphorbiaceae, and a decrease in representation of Quercus, Alnus and Salix. In zone ZEM-II four subzones (ZEM-IIA, ZEM-IIB, ZEM-IIC and ZEM-IID) were distinguished. Zone ZEM-IIA shows a relatively high representation of Arceuthobium and Salix. Values of Alnus, Abies and Anthoceros–Hymenophyllum are low. This zone includes a radiocarbon age of 2110 F 130 14C yr BP. Zone ZEM-IIB shows higher representation of Abies, Melastomataceae, and Anthoceros–Hymenophyllum than in ZEM-IIA, and shows low values of Salix and Rubiaceae. The local vegetation is mainly characterized by Cyperaceae (3–120%, Plate I. 1–3: 4–7: 8: 9–11: 12–18: 19–20: 21–22: 23–25: 26–30: Ascospores of Podospora-type, 1000 (1, 2: LZ ; 3: LZ-I/90) Ascospores of Cercophora-type, 1000 (4, 5: LQ-II/60; 6, 7: LZ-I/43) Ascospore of Diporotheca spec., 1000 (LQ-II/290) Heterocysts of Rivularia-type, 1000 (LZ-I/54) Separate ascospore-cells of Sporormiella spec., 1000 (12: LZ-I/43; 13–18: LZ-I/250) Chlamydospores of Glomus spec., 1000 (19: LZ-I/50; 20: LZ-II/215) Hyphopodia of Gaeumannomyces spec., 1000 (LZ-I/250) Conidia of fungus type 200, 1000 (LQ-II/220) Charred epidermis fragments of Poaceae ( 500); 26, 27, 28 and 30 show characteristic alternating long and short epidermis cells. 28 and 30 show prickles and 29 shows a stoma, 500 (26 and 29: LQ-II/215; 27, 28, 30: LZ-I/215). L. Almeida-Lenero et al. / Review of Palaeobotany and Palynology 136 (2005) 63–92 73 74 L. Almeida-Lenero et al. / Review of Palaeobotany and Palynology 136 (2005) 63–92 Plate II. 1–2: 3–4: 5–8: leaf-spines of Ceratophyllum spec., 500 (LZ-I/380) Glochidia and massulae of Azolla spec., 500 (LQ-II/110) Volcanic ash particles (tephra), 500 (LQ-III/350). max. 175%), Hydrocotyle (0–2.5%) and Isoetes (0– 4%). The interval 260–243 cm includes volcanic ash. ZEM-IIB shows high percentages of Pinus (42–86%), moderate percentages of Salix (0–9%, max. 20%), Quercus (0–12%, max. 16%) and Abies (1–14%), and low percentages of Alnus (1–10%), Asteraceae (0.4–8%), Poaceae (0–7%), Rubiaceae (0–5%, max. 8%) and Melastomataceae (0–3%). There is a marked increase of Anthoceros–Hymenophyllum (0–14%, max. 200%). Percentages of fungal spores (60– 700%, max. 3500%) and bryophyte spores (0–9%, max. 48%) are high. The top of this zone is radiocarbon dated at 620 F 70 14C yr BP. Volcanic ash occurs in the intervals of 243 to 226 and 115 to 110 cm. Pollen zone ZEM-IIC is characterized by Pinus (37– 89%), Abies (0–22%, max. 30%), Asteraceae (0–9%, max. 22%), Alnus (0–6%, max. 17%), Quercus (0– 8%, max. 12%), and low percentages of Salix (0–5%, L. Almeida-Lenero et al. / Review of Palaeobotany and Palynology 136 (2005) 63–92 Fig. 5. Pollen percentage diagram of core Lake Zempoala (2800 m altitude), central Mexico. From left to right are shown: AMS 14C ages, depth, a selection of the most important pollen records arranged by ecological preference, and pollen zones. The estimated abundance of fungal spore types is shown as bars. 75 L. Almeida-Lenero et al. / Review of Palaeobotany and Palynology 136 (2005) 63–92 Fig. 5 (continued). 76 L. Almeida-Lenero et al. / Review of Palaeobotany and Palynology 136 (2005) 63–92 Fig. 6. Summary pollen diagram of core Lake Zempoala. From left to right: AMS 14C ages, age scale in dcal yr BPT, depth, lithology, summary records of the main ecological groups (mixed forest = Quercus, Alnus and Salix; mesophyllous forest = Hedyosmum, Carpinus, Juglans, Carya, Ilex, Tilia, Celtis, Arbutus, Rubiaceae and Eryngium), pollen sum values, pollen concentration record, pollen zones, and the CONISS dendrogram. 77 78 L. Almeida-Lenero et al. / Review of Palaeobotany and Palynology 136 (2005) 63–92 Fig. 7. Pollen percentage diagram of core Lake Quila (3010 m altitude) in central Mexico. From left to right are shown: AMS 14C ages, depth, a selection of the most important pollen records arranged by ecological preference, and pollen zones. Fig. 7 (continued). L. Almeida-Lenero et al. / Review of Palaeobotany and Palynology 136 (2005) 63–92 79 80 L. Almeida-Lenero et al. / Review of Palaeobotany and Palynology 136 (2005) 63–92 Fig. 8. Summary pollen diagram of core Lake Quila. From left to right: AMS 14C ages, age scale in dcal yr BPT, depth, lithology, summary records of the main ecological groups (mixed forest = Quercus, Alnus and Salix; mesophyllous forest = Hedyosmum, Carpinus, Juglans, Rubiaceae and Eryngium), pollen sum values, pollen concentration record, pollen zones, and the CONISS dendrogram. L. Almeida-Lenero et al. / Review of Palaeobotany and Palynology 136 (2005) 63–92 max. 10%), Apiaceae (0–6%, max. 10%), Melastomataceae (0–6%, max. 9%) and Poaceae (0–4%, max. 8%). Compared to the previous zone, this zone is marked by an increase of Abies and Asteraceae and by a decrease of Pinus and Quercus. The local vegetation is represented by Cyperaceae (60– 290%, max. 525%) and Isoetes (0–10%, max. 23%). In the middle part of this zone abundant spores of the coprophilous fungus Podospora occur. Zone ZEM-IID is characterized by the increase of Alnus and the start of the record of Zea mays (0–2%), Dodonaea (0–2%) and Eryngium (0–5%). There is also an increase in the representation of aquatic taxa, such as Hydrocotyle (0–3%) and Zygnema (0.5–2%). Compared to the previous zone, zone ZEM-IID is most marked by the presence of Zea mays, and by decreasing percentages of Pinus and Abies. 4.4.2. Lake Quila The composite pollen diagram of cores Quila-1 (on top of the volcanic ash horizon) and Quila-2 (below the volcanic ash horizon) shows the most important fossil pollen and spore taxa out of the 46 that have been identified (Figs. 7 and 8). Pollen concentration values vary mainly from 20.103 to 150.103 grains per cm 3 of sediment. Based on the CONISS cluster analysis, four main zones could be recognized. The ages of the zones are given in calendar years and based on the calculated dcal yr BPT-scale shown in Fig. 8. Zone QUI-I 884–811.5 cm 6 samples Zone QUI-II 811.5–383.5 cm 27 samples Zone QUI-III 383.5–80.5 cm 19 samples Zone QUI-IV 80.5–5 cm 12 samples c. 11,610–10,650 cal yr BP c. 10,650–5000 cal yr BP c. 5000–1010 cal yr BP c. 1010–20 cal yr BP Zone QUI-I is mainly characterized by high representation of Pinus (15–50%), Alnus (8–55%), Quercus (4–9%) and Poaceae (0–10%), and by low representation of Abies, aquatics and ferns. Local taxa show low percentages: Myriophyllum (0–1%) and Spirogyra (0–1%). Radiocarbon dating near the base yielded an age of 9713 F 45 14C yr BP. 81 Zone QUI-II is characterized by Pinus (35–80%), Quercus (with highest percentages in the core of 0– 16%, max. 25%), Alnus (2–23%), Abies (3–18%, max. 23%) and Arceuthobium (0–1.7%). Melastomataceae (0–9%, max. 21%) is recorded for the first time in the middle of this zone. There are marked percentages of Cyperaceae (0–20%, max. 30%) and Hydrocotyle (max. 10%). Compared to the previous zone the representation of Pinus and Abies is higher, Arceuthobium appears for the first time and Alnus is decreasing substantially. The base and the top of this zone have been radiocarbon dated at 8480 F 80 14C yr BP and 5620 F 38 14C yr BP, respectively. Zone QUI-III follows after the volcanic ash horizon of 380 to 355 cm and is dominated by Pinus which fluctuates between 46% and 96%. Abies also shows its highest percentages (1–36%). Moderate percentages occur for Quercus (0–13%, max. 19%), Alnus (0.7–9%), Poaceae (0–12%, max. 30%), and Arceuthobium (0.2–0.8%). Taxa of local significance are Cyperaceae (0–15%, max. 20% ). Compared to the previous zone, Pinus shows higher percentages, Abies shows marked fluctuations, and Asteraceae continuously show relatively high percentages. The lower part of this zone has been radiocarbon dated at 4650 F 60 14C yr BP. Zone QUI-IV is characterized by significant percentages of Pinus which decrease towards the top (58– 36%), Abies (7–15%), Quercus (4–12%), Alnus (1– 10%), Poaceae (5–17%, max. 23%) and Asteraceae (1–8%). In this zone the highest percentages of Eryngium are found (0.9–4%). Taxa related to human impact are significant: Plantago (0–0.3%), Rumex (0– 0.4%) and Zea mays (0–0.3%). Cyperaceae (9–70%, max. 95%) show the highest percentages of the record. Compared to the previous zone, increase of Cyperaceae and the abundance of aquatics such as Myriophyllum (0–0.3%), Potamogeton (0–5%), Typha (0–5%), and the alga Botryococcus (0–18%) is most significant. 5. Reconstruction of environmental changes from the Zempoala and Quila records 5.1. Lake Zempoala During the period c. 6320–2530 cal yr BP (zone ZEM-I) the basin first accumulated clay (zone ZEM- 82 L. Almeida-Lenero et al. / Review of Palaeobotany and Palynology 136 (2005) 63–92 IA). Low abundance of aquatics (mainly Potamogeton) and the presence of algae (Fig. 6) suggest open water in which fine grained sediments accumulated in a low energy regime. Around 3000 cal yr BP, open water disappeared (indicated by the absence of algae) and peat formation initiated in the basin, suggesting a lowered water table (zone ZEM-IB).On a regional scale, the presence of Quercus, Alnus, Salix, and the moderate values of Pinus indicate the existence of a mixed forest, including some elements from the mesophyllous forest, at the elevation of Lake Zempoala. Apparently, lower montane forest had a higher altitudinal position than today. This mid-Holocene oak forest represents the last phase of a temperate and dry period. During the following period c. 2530– 160 cal yr BP (zone ZEM-II) lithological changes suggest a variable water level. For several hundreds of years accumulation of peat continued (zone ZEMIIA), pointing to continuous low water levels. Around 1600 cal yr BP, a significant increase of cyperaceous reedswamp, and later an increase of algae, suggest higher water levels resulting in clay accumulation. Another period of peat formation occurred c. 1000 to 600 cal yr BP (in the middle of zone ZEM-IIB), with a sand component. Aquatics demonstrate low representation indicating low water levels. During the period sand was supplied to the peat bog, high representation of pioneer taxa with such as Salix and fern spores suggest local disturbance of the vegetation cover. The beginning and end of sandy peat accumulation is characterized by peaks of fungal spores indicative of the active decomposition of organic material during low water level stands. From c. 600 to 310 cal yr BP water levels rose again and clay accumulated in open and relatively deep water. During the period c. 310 to 160 cal yr BP (zones ZEMIIC and ZEM-IID) the water body changed into a shallower lake; the sediments became richer in organic material. The presence of Ceratophyllum spines, Cyperaceae and Typha are indicative of shallow water. Isoetes may have grown on dynamic shores in the drainage system, and/or at places with several meters of water. Such vegetation types indicate that the lake had developed a hydrosere along the shores which is comparable to the present-day situation (Bonilla and Novelo, 1995; Almeida-Leñero and Cleef, 1997). The entire zone ZEM-II is characterized by the presence of coprophilous fungi which suggests the frequent presence of cattle around the lake/bog. On a regional scale, during the full period from c. 2530 to 160 cal yr BP (zone ZEM-II), Abies-dominated forest prevailed in the surroundings of the lake, and the forested areas experienced altitudinal migrations. The presence of various types of mesophyllous forest and mixed forest are indicative of a temperate climate varying from humid to subhumid (McDonald, 1993; Almeida-Leñero, 1997). During the period c. 2530–1150 cal yr BP (zone ZEM-IIA) the abundance of Pinus, in combination with Arceuthobium, suggests the presence of a Pinus hartwegii forest close to the lake (Ohngemach and Straka, 1983). During this period the lake was situated in the Abies forest, close to its uppermost altitudinal limit where it is transitional to Pinus hartwegii forest. The altitudinal position of the forest belts was possibly some 400 m lower than today, indicative of a lower temperature. Using a temperature gradient of 0.6 8C/100 m we estimate average temperatures of c. 2.5 8C lower than today for this period. During the period from c. 1150 to 310 cal yr BP (zone ZEM-IIB) Pinus hartwegii forest dominated around the lake. Pinus forest is indicative of dry climatic conditions and this conclusion corroborates the reported dry period from 2200 to 1200 cal yr BP. The driest interval of this period was from 1300 to 1100 cal yr BP. In the last part of this period the lake was located in the Abies forest belt pointing to climatic conditions similar to today. During the period c. 310 to 160 cal yr BP (zones ZEM-IIC and ZEMIID) Abies forests predominated under conditions similar to the present. The increasing contribution of non-arboreal taxa reflects progressive deforestation. Taxa such as Zea mays and fungal spores of the coprophilous genus Podospora indicate human occupation of the study area. The lake had open and relatively deep water, but changed into a shallower lake during these two centuries; the sediments became richer in organic material. 5.2. Lake Quila During the period from c. 11,610 to 10,650 cal yr BP (zone QUI-I) the accumulation of organic rich clay, and an almost complete absence of aquatics (some Myriophyllum and Hydrocotyle), indicate the presence of an open water body. The supply of sand L. Almeida-Lenero et al. / Review of Palaeobotany and Palynology 136 (2005) 63–92 suggests erosion in the surroundings of the lake. At the end of this period the water table lowered and peat formation started. Presence of shallow water plants and algae did not increase before the end of this zone. The pollen spectra show the presence of montane Alnus and Pinus forest, similar to the type of forest occurring today in the central Mexico highlands (Almeida-Leñero et al., 1997). The presence of this type of forest suggests humid conditions. During the period c. 10,650 to 5000 cal yr BP (zone QUI-II) there was a relatively long interval with peat formation: aquatics and algae were common and the water table was lower. Around 7000 cal yr BP (530 cm core depth) clay started to accumulate suggesting a rise of the water table. At the end of this period a volcanic ash horizon was deposited, reflecting a volcanic eruption in or near the study area. In the surrounding area, temperate forest with Pinus, Alnus and Abies was present. Pollen grains of Pinus and Arceuthobium indicate that Pinus hartwegii forest may have been close to Lake Quila. Compared to the present-day situation, this altitudinal distribution reflects a downward shift of the Pinus/Abies transition of some 400 m. We therefore estimate a temperature depression of some 2.4 8C compared to today. The period c. 5000 to 1010 cal yr BP (zone QUIIII) was characterized mainly by peat formation, suggesting a low water table; aquatics and algae also occurred. In the surroundings of Quila, temperate forest with Pinus, Alnus and Abies was present. Pollen grains of Pinus and Arceuthobium are present at the same time and indicate that Pinus hartwegii forest continued to be present, pointing to continuing dry conditions. This is supported by the low water table. During the period of c. 1010 cal yr BP to the present (zone QUI-IV) aquatics and algae became abundant and clay was accumulated, pointing to higher water levels compared to the previous period. Cyperaceous reedswamp with Typha and Potamogeton was abundant at the shores of the lake. In the surroundings of the lake Abies religiosa forest dominated. According to a comparison with the modern ecological envelope of this forest type (Rzedowski, 1978), temperate subhumid climatic conditions prevailed. Lower representations of Pinus, Abies and Quercus indicate a downward shift to present-day conditions of the belt, with a mixed forest. For the 83 first time in the record, human occupation of areas close to Quila is indicated by the occurrence of Zea mays and Rumex (Almeida-Leñero et al., 1990). 6. Discussion Multi-event volcanic ash depositions may detract significantly from the quality of a pollen record, but our sites were not intensively affected. Pollen records from the Valley of Mexico suffer from frequent and irregular ash depositions that severely damage the vegetation cover in a large area, and from tectonically induced irregularities in the stratigraphic column (Lozano and Xelhuantzi-López, 1997). The sediment sequences of lakes Zempoala and Quila offered evidence on lithology, fossil pollen, spores and nonpollen palynomorphs, local changes in the lake basins, regional scale climate change, and human impact. Lakes Zempoala and Quila are altitudinally and latitudinally close together. In the pollen spectra we identified 27 taxa of vascular plants at the family-level, and 19 taxa at the generic level. In the fossil pollen spectra of both cores, as well as in the spectra of the recent pollen rain, the same arboreal taxa are dominant in decreasing order of abundance: Pinus, Alnus, Abies, and Quercus (Palacios Chávez, 1977; Tovar-González, 1987; Ohngemach and Straka, 1983). These studies also illustrate that Pinus and Alnus, and to a lesser degree Quercus, are over-represented in the pollen rain, but their pollen signals closely relate to the altitudinal interval where these forests occur. Pinus shows an optimal representation in the belt with Pinus hartwegii forest (Ohngemach and Straka, 1983). Abies is under-represented in the pollen rain, which was also reported from a Guatemalan study (Islebe and Hooghiemstra, 1995), and its maximum representation is in the Abies forest belt. Where Alnus is dominant in the vegetation, this might be considered to be an indication of disturbance. Alnus shows its maximum representation in the mixed forest. High percentages of Cupressus and Quercus in the pollen spectra are indicative of local presence of these taxa in the vegetation. The most important genera of Poaceae in our study area are Calamagrostis and Festuca and these taxa are under-represented in the pollen rain (Ohngemach and Straka, 1983). 84 L. Almeida-Lenero et al. / Review of Palaeobotany and Palynology 136 (2005) 63–92 According to the calibrated time scale, the pollen record of Lake Zempoala includes the last c. 6320 cal yr BP. The uncalibrated ages of the two samples close to the base of the Zempoala core differ by only a few hundreds of years from the age of the dyellow ash bedT (4880 F 120 14C yr BP). We therefore assume that the Lake Zempoala record probably started after deposition of this important marker. An alternative interpretation that the record started after deposition of the dupper fine pumiceT horizon of the Pomez volcanic ash, dated 4250 F 110 14C yr BP, is less plausible (Bloomfield and Valastro, 1977; Lorenzo, 1991; Lambert, 1986; Limbrey, 1986); both beds are associated with a dry period (Metcalfe et al., 1991; Metcalfe, 1995). According to Metcalfe et al. (1991) most important Holocene climatic change occurred above this marker bed and this corresponds with the Zempoala record. The Zempoala (2800 m) core records two types of forest: mixed forest (today occurring below the altitude of this lake) at the base of the record, later replaced by Abies forest (today occurring from 2800 to 3500 m at and above the altitude of the lakes). This is clear evidence of altitudinally shifting vegetation belts forced by climate change. Changes in the floristic composition within periods of dominance by particular vegetation belts, mainly reflect changes in humidity, but changes in the seasonality of precipitation makes the relationship between total precipitation, moisture availability and vegetation complex (Street-Perrott and Perrott, 1990; O’Hara and Metcalfe, 1995). The record of environmental change now available may be further improved by analysing additional proxies (e.g. diatoms), and by developing a pollen morphological key to the different species of Pinus. In the following section we compare the results of the records of Lake Zempoala and Lake Quila with reconstructions from other sites. A synthesis is shown in Table 4. With respect to Zempoala, the dry conditions during the period from c. 6320 to 2539 cal yr BP (zone ZEM-I) were also reported for the central Mexican region by González-Quintero and Fuentes-Mata (1980). They found an increase in Quercus, as well as the first appearance of Zea in Lake Texcoco. González-Quintero and Fuentes-Mata (in Niederberger, 1987) also showed the first occurrence of maize in this period. In Lake Chalco Watts and Bradbury (1982) showed the existence of shallow freshwater and marshes from 5000 years ago onward, also pointing to dry conditions. Lozano et al. (1993) and Lozano and Ortega (1994, 1998) documented similar environmental change during the early and middle Holocene and human disturbance from c. 3000 14C yr onward. In central region of Mexico Metcalfe et al. (1991) also reported a phase of accelerated erosion around 3100 cal yr BP. On the basis of diatom studies in the Zacapu Basin Metcalfe (1995) inferred dry periods between c. 6000 and 4500 14C yr BP, and around 1000 14C yr BP. During the last part of this period (zone ZEM-1B) in particular, water levels were low and peat formation started in the lower parts of the basin. The lower temperatures during the period from 2530 to 1150 cal yr BP (zone ZEM-IIA) are supported by Vázquez-Selem (1997), who described a terminal moraine at the northern part of Iztaccihuatl, dated at c. 2000 14C yr BP. The same study assumed that at La Malinche volcano climatic conditions during the development of La Morrena-M-IV were colder than at present. Based on geomorphology, palaeopedology and tephrastratigraphy of glacier advances on the volcano La Malinche, Heine (1988) inferred a cool period from c. 3000 to 2000 14C yr BP. Also the Mexican pollen and diatom records of Brown (1985), Straka and Ohngemach (1989), Metcalfe et al. (1991), and the records from Central American lakes (e.g. Hodell et al., 1995; 2001) show lower temperatures for this period. During the period from c. 1150 to 310 cal yr BP (zone ZEM-IIB) the interval from 1300 to 1100 cal yr BP was driest and represents an extreme since the midHolocene (Hodell et al., 1995; 2001). The latter interval of 200 years coincides with the collapse of the Maya civilization. The sequence of climatic change between 1800 and 1100 14C yr BP (assuming errors of 50 years this reflects the period of c. 1800–1600 to 1050–950 cal yr BP) has also been documented in marine records (Brown, 1985) and in a climate record from Michoacan State (Metcalfe, 1995). In the last part of the period, represented by zone ZEM-IIB, the lake was located in the Abies forest belt pointing to climatic conditions similar to today. In the Valley of Mexico and surroundings there is a well documented record of agricultural activities which started 3000 14C yr BP (Brown, 1985). There is little doubt that evidence Table 4 Synthesis of Holocene vegetation development in the Central Mexican highlands and inferred climatic conditions for the altitudinal interval from 2800 to 3000 m Time scale Cal yr BP 20 (QUI–IV) 1100 Lake zempoala, Mexico (3010 m alt.) (2800 m alt.) Actual vegetation (grassland and Abies religiosa forest) Actual vegetation (Abies religiosa forest) Abies forest and elements of human impact (Zea mays) Abies forest 2000 Dry high salinity 160 Forest and elements of human impact Yucatan, Central America and the Caribbean (ZEM–II) (Zea mays) Very dry significant anthropogenic impact Dryer; but variable saline lakes Significant local anthropogenic impacts 2530 Drying Mixed forest 5000 6000 Central Mexican Volcanic Belt (Ruter et al., 2004) Hiatus (QUI–III) 4000 Cal yr BP (ZEM–I) Pinus forest, few pollen and volcanic ash Variable regionally Short dry interval–wet; Generally lower lake levels but high variable Highest lake levels Brosimum decline Abies forest 6320 Drying begings high lake levels Wet, rising lake levels 8000 Rising lake levels (QUI–II) Glacial advances? L. Almeida-Lenero et al. / Review of Palaeobotany and Palynology 136 (2005) 63–92 0 Lake Quila, Mexico 10,000 Very arid and cold 10,650 (QUI–I) 11,610 Lowest lake levels Alnus forest 85 The sequence of environmental change from lakes Quila and Zempoala (with pollen zones) are compared with the synthesis study by Ruter et al. (2004) for central Mexico and Yucatan. 86 L. Almeida-Lenero et al. / Review of Palaeobotany and Palynology 136 (2005) 63–92 reflects the establishment of an indigenous civilization with a dense population for Mesoamerica (Niederberger, 1987; Metcalfe et al., 1989). Agricultural development was registered slightly later in the peripheral parts around the Valley of Mexico (Brown, 1985). With respect to Quila, the period from 11,610 to 10,650 cal yr BP (zone QUI-I) shows a dominance of Alnus and this period is likely to correlate with zone III in the sections Tlaloc-I and Tlaloc-II (3100 m altitude) from the area of volcano La Malinche, east of our study area (Fig 1). Ohngemach and Straka (1983) and Straka and Ohngemach (1989) assumed that Alnus forests found in this area resulted from local fires, but may also represent successional stages towards an Abies forest. Madrigal (1967) interpreted the present Alnus–Pinus forest in this way. High percentages of Alnus during the same period are also reported by Xelhuantzi-López (1994) and Watts and Bradbury (1982) for the area northwest of our study area, and by Lozano and Ortega (1994) for the area of the Valley of Mexico. For this period an increase in humidity, related to increased precipitation, was also reported by González-Quintero (1981, 1986). For the period from c. 10,650 to 5000 cal yr BP (zone QUI-II) Ohngemach and Straka (1983) and Straka and Ohngemach (1989) also report slightly cooler conditions than at present. High percentages of Pinus possibly correlate with zone IV of sites Tlaloc-I and Tlaloc-II (Straka and Ohngemach, 1989). Between 7000 and 5000 14C yr BP (assuming errors of 50 years this reflects the period of 7950– 7750 to 5850–5650 cal yr BP) changes in the extension of Pinus forest was also reported by Brown (1985). For the Upper Lerma Basin, Toluca, Metcalfe et al. (1991) registered an important episode characterized by environmental disturbance, desiccation of Almoloya Lake and accelerated erosion in the surrounding valleys. These events are plausible under dry climatic conditions. During the same time the dyellow ashT was deposited, an event that supposedly corresponds to the upper part of our zone QUI-II. Coinciding with our period from c. 5000 to 1010 cal yr BP (zone QUI-III) González-Quintero (1981, 1986) reported an arid period from c. 4850 to 4200 14C yr BP (assuming errors of 50 years this reflects the period of 5650–5500 to 4850–4650 cal yr BP) associated with significant erosion in the Basin of Mexico. Niederberger (1987) and Bradbury (1989) reported similar cli- matic conditions on the basis of diatoms in the Basin of Mexico, so did Watts and Bradbury (1982) in Lake Pátzcuaro. The expansion of Abies forest might correspond to zone VII of pollen record La Malinche (Ohngemach and Straka, 1983; Straka and Ohngemach, 1989). Significant climatic change during this period is also reported by Hodell et al. (1995; 2001) for Mexico, by Curtis et al. (1996; 1998) for the Maya Lowlands and for other Mesoamerican sites, and by Islebe et al. (1996b) for Costa Rica. Abundant Pinus forest during the last part of this period (uppermost part of zone QUI-III) reflects the widespread occurrence of Pinus hartwegii forest, indicative of the most arid period reported during the middle to late Holocene from c. 1300 to 1100 cal yr BP. Climatic aridity during this time was also noted by Metcalfe et al. (1991) for the Lerma Basin where lakes changed between 900 and 1400 AD. Dry climatic conditions were also reported from Lake Pátzcuaro, central Mexico by Watts and Bradbury (1982), who inferred low water levels based on archaeological and lacustrine features. Dry conditions were also reported for Zacapu Basin (Metcalfe, 1995) and for the Yucatán Peninsula (Curtis et al., 1996, 1998; Hodell et al., 1995, 2001). The presence of Abies forest since c. 1010 cal yr BP (zone QUI-IV) was reported earlier by GonzálezQuintero (1986) for the Basin of Mexico, by Metcalfe et al. (1991) for the Upper Lerma Basin. In conclusion, the results from the pollen records of Quila and Zempoala appear to reflect climatic change, evidenced by vertical migration of the main vegetation belts. The pollen records show local fluctuations in the basin of the lakes, reflecting changes in the hydrological balance, climate change on a regional scale, and human impact on the landscape. Environmental changes correspond to those reported for the central Mexican region and, as such, support the regional sequence of climate fluctuations. The composite record of environmental change start with a period of more humid and cooler conditions than at present. During the period of c. 6320– 2540 cal yr BP dry conditions are inferred, which supports the evidence from other central Mexican records, showing a general trend of increasing dryness from early to mid-Holocene time. This dry episode was widespread in central Mexico. During the mid and late Holocene there are indications of human impact, as is the case in other sites in the study area. L. Almeida-Lenero et al. / Review of Palaeobotany and Palynology 136 (2005) 63–92 Lower temperatures during the period from 2530 to 1150 cal yr BP are supported by moraine records. The period from 1300 to 1100 cal yr BP was driest and represents extreme conditions since mid-Holocene time; this period coincides with the collapse of the Maya civilization. We started to use non-pollen microfossils, rarely documented in Latin American palaeoecological studies, as an unexplored source of information. Acknowledgements Peter Kuhry is thanked for his assistance in the field. Elly Beglinger and Annemarie Philip (Amsterdam) are thanked for the preparation of the pollen samples. The late Gerald Noldus assisted with identification of pollen grains. Gerald Islebe and Sonia Salamanca are acknowledged for the constructive comments on an earlier draft of the manuscript. Maarten Blaauw is thanked for assistance with chronology. Juan Carlos Berrio supported with using TILIA software. Veronica Aguilar is thanked for continuous support. Financial support from the Universidad Nacional Autónoma de México (UNAM) and FUOS (University of Amsterdam) made this study possible. We thank Sarah Metcalfe and an anonymous reviewer for constructive comment on an earlier draft of this paper. Appendix A Morphological descriptions and ecological/environmental preferences of other microfossils recorded in the sediments of Lake Zempoala. Podospora-type (Type 368); Plate I, 1–3. Ascospores, 29–46 16–23 Am. One-celled, ellipsoidal, smooth, dark brown, with one protruding pore 2 Am in diameter, directly below the apex. Pore surrounded by an annulus. Basal end bluntly conical, and originally bearing a hyaline appendage (which does not fossilise). Fossil spores of the Podosporatype (Sordariaceae) were recorded and illustrated for the first time by van Geel et al. (1981) in a sediment deposited directly beside an Iron Age settlement in the Netherlands. In later studies Podospora-type spores were observed also in material from other archaeolog- 87 ical sites where it could be used as an additional indicator for (extra) dung and the presence of dense populations of herbivores. Lundqvist (1972) described and illustrated many species of Sordariaceae and his well-illustrated study can be used as a reference for identification of fossil spores of that family of predominantly coprophilous Ascomycetes. Cercophora-type (Type 112); Plate I, 4–7. Ascospores, 16–22 9–12 Am. One-celled, smooth, brown, truncate at the basal side (originally bearing a hyaline appendage, which does not fossilise) and tapering at the apical end. One sub-apical pore c. 0.7 Am in diameter. Sometimes Cercophora spores show one septum, and if so, there is no constriction at the septum (van Geel, 1978). According to Lundqvist (1972), representatives of the Sordariaceous genus Cercophora are coprophilous or occur on decaying wood, on herbaceous stems and leaves. Sporormiella-type (Type 113); Plate I, 12–18. Separate cells of ascospores, 12–20 9–11 Am. Cells smooth and brown, showing a slightly curved germ slit, extending the entire length of the cell. When Sporormiella-type is present in the fossil record, there are always two types of cells. There is a category showing two flattened ends (Plate I, 12–14) and a category of cells showing one flattened end, in combination with a rounded end (Plate I, 15–17). The reason is that complete ascospores of Sporormiella species are three to many septate. The septa are transverse and ripe ascospores split up in separate cells, each one being able to germinate and form a new individual fungus. In the fossil state no observations of complete ascospores can be made, but the presence of the two types of cells (dterminal cellsT and dmiddle cellsT) is an extra feature for identification. Identification to species level of Sporormiella-type is not possible because fruit bodies, asci and complete ascospores are not available (compare Ahmed and Cain, 1972). The representatives of the related, coprophilous genus Sporormia are without germ slits. However, the descriptions of Ahmed and Cain (1972) are based on non-germinated spores, and a slit may appear after germination. Therefore we cannot exclude that also Sporormia is among our fossil spores, and thus we refer to the fossil spores as Sporormiella-type instead of Sporormiella. Fossil spores of Sporormiella were distinguished by Davis et al. (1977), Davis and Turner (1986), Davis (1987), 88 L. Almeida-Lenero et al. / Review of Palaeobotany and Palynology 136 (2005) 63–92 and van Geel et al. (2003) they used the spores as indicators for dung produced by herbivores. Diporotheca spec. (Type 143); Plate I, 8. Ascospores 50–55 21–24 Am, biseptate (not visible in illustration), fusiform, both ends truncate with a germ pore c. 3 Am in diameter. Surface of brown spores showing dark brown anastomosing ribs. For a more complete fossil record (illustrations including fruit bodies) reference is made to van Geel et al. (1986b). Originally the genus Diporotheca was classified as a representative of the Meliolaceae by Gordon and Shaw (1960), but Mibey and Hawksworth (1995) introduced the family Diporothecaceae to accommodate the genus Diporotheca. Gordon and Shaw illustrated D. rhizophila and mentioned roots of Solanum species as the substrate of the parasitic fungus. Glomus spec. (Type 207); Plate I, 19 and 20. Chlamydospores globose to egg-shaped, 17–138 Am, light to dark brown, with hyphal attachment. Representatives of the genus Glomus are vesicular– arbuscular endomycorrhizal fungi and they occur on a variety of host plants. The presence of Glomus in lake deposits can be used as an indication for erosion of soils, because the spores are formed below the soil surface and normally not transported. For additional information about the fossil record of Glomus see van Geel et al. (1989). Gaeumannomyces spec. (Type 126), Plate I, 21 and 22. Hyphopodia dark brown, roughly circular to oval or irregular in outline, with blunt lobes. Greatest diameter 12–39 Am. A prominent clear spot 1.8–2.8 Am in diameter in the central area, representing the point of host penetration. In Europe the fossil hyphopodia of Gaeumannomyces appeared to be indicative for local Carex in the peat-forming vegetation (Pals et al., 1980; van Geel et al., 1989). Type 200; Plate I, 23–25. Fungal spore: coiled cluster of 5–10 globose cells; greatest diameter of the clusters 18–45 Am. Individual cells variable in size, the smaller cells concentrated at one side of the cluster. One of the smaller cells tapering into a hypha, broken off at the end (former connection with mycelium). van Geel et al. (1989) recorded Type 200 spores in a Lateglacial deposit from the Netherlands, where they were common in the terrestrialisation phase (with Equisetum, Phrag- mites and Carex) of a shallow pool. A direct relationship with certain host plants or specific ecological conditions could not be revealed yet. Rivularia-type (Type 170; Cyanobacteria); Plate I, 9–11. Heterocysts almond-shaped, 10–12 6–8 Am, with a c. 0.8 Am wide pore at the narrow end, which often bears an up to 2 Am long appendage (the sheath of the trichome which did not become fossilised). Similar heterocysts were recorded and illustrated by van Geel et al. (1983, 1989). Cyanobacteria can play a pioneer role in aquatic habitats thanks to their nitrogen-fixing ability. Gramineae, charred epidermis fragments; Plate I, 26–30. Grasses show a characteristic pattern of epidermis cells: adjacent cells have dzip-fastenerT connections with each other and, apart from long cells, there are also short cells. Some of the observed fragments showed prickles and stomata. A more complete record and the study of modern reference material might result in identification of genera or even species. Considering the fact that grass pollen has to be lumped (apart from Cerealia, like Zea), identification of the gramineous taxa would be most welcome. Ceratophyllum spec. (Type 137); Plate II, 1 and 2. Leaf spines, consisting of a single thickened cell, narrowly elongate and sharply pointed, bearing at its base the impression of attachment to adjacent cells. Records of the spines are important because the pollen of Ceratophyllum does not preserve. Azolla spec.; Plate II, 3 and 4. Glochidia and massulae of Azolla could be recognised at various levels in the cores. Volcanic ash fragments (tephra); Plate II, 5–8. 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