|
|
||||||||
Physiology and Biochemistry |
School of Marine and Tropical Biology, James Cook University, Townsville, Queensland 4811, Australia; Smithsonian Tropical Research Institute, Balboa, Ancón, Republic of Panama
Received for publication February 5, 2007. Accepted for publication August 6, 2007.
ABSTRACT
Zamioculcas zamiifolia (Araceae), a terrestrial East African aroid, with two defining attributes of crassulacean acid metabolism (CAM) (net CO2 uptake in the dark and diel fluctuations of titratable acidity) is the only CAM plant described within the Araceae, a mainly tropical taxon that contains the second largest number of epiphytes of any vascular plant family. Within the Alismatales, the order to which the Araceae belong, Z. zamiifolia is the only documented nonaquatic CAM species. Zamioculcas zamiifolia has weak CAM that is upregulated in response to water stress. In well-watered plants, day–night fluctuations in titratable acidity were 2.5 µmol H+·(g fresh mass)–1, and net CO2 uptake in the dark contributed less than 1% to daily carbon gain. Following 10 d of water stress, net CO2 uptake in the light fell 94% and net CO2 uptake in the dark increased 7.5-fold, such that its contribution increased to 19% of daily carbon gain. Following rewatering, dark CO2 uptake returned to within 5% of prestressed levels. We postulate that CAM assists survival of Z. zamiifolia by reducing water loss and maintaining carbon gain during seasonal droughts characteristic of its natural habitat.
Key Words: Araceae CO2 exchange crassulacean acid metabolism drought stress photosynthesis Zamioculcas
Crassulacean acid metabolism (CAM) is the second most common pathway of photosynthesis in vascular plants (Winter and Smith, 1996
). CAM has evolved often, with species distributed in 29 families and 338 genera of flowering plants (Smith and Winter, 1996
; Silvera et al., 2005
; Liu and Wang, 2006
), two families of gymnosperms (Vovides et al., 2002
; von Willert et al., 2005
), two families of leptosporangiate ferns (Hew and Wong, 1974
; Carter and Martin, 1994
; Holtum and Winter, 1999
), and one family of lycophytes (Keeley, 1981
). Initially considered primarily a water-conserving adaptation of terrestrial succulent plants to hot, semi-arid environments, CAM assists species in a diverse range of habitats (Skillman et al., 2005
). The majority of CAM plants are probably epiphytes in tropical and subtropical forests (Crayn et al., 2004
; Holtum and Winter, 2005
; Silvera et al., 2005
), but CAM has also been reported in tropical trees (Gehrig et al., 2003
; Holtum et al., 2004
; Lüttge, 2006
), halophytes (Winter and Holtum, 2005
, 2007
), alpine succulents (Osmond et al., 1975
), aquatic plants of oligotrophic lakes or seasonal pools (Keeley, 1981
, 1996
), and in plants without stomata that obtain CO2 via their roots (Keeley et al., 1984
).
The CAM pathway, which enables plants to successfully live in such a range of environments, involves the ability to fix CO2 during the dark, storing the carbon as malic acid in vacuoles. In the light, the malic acid is decarboxylated, and the CO2 evolved is refixed by Rubisco and used for growth and maintenance (Holtum et al., 2005
). CAM species with functional stomata are highly water-use efficient because decarboxylation and CO2 refixation are accompanied by reduced stomatal aperture and, consequently, lower rates of transpiration (Winter et al., 2005
). In aquatic plants, CAM is an adaptation to CO2-limited environments in which the levels of dissolved CO2 are either permanently low or low during the light (Keeley, 1996
).
Unlike C3 or C4 photosynthesis, the phenotypic expression of CAM is not an all-or-nothing phenomenon. Some CAM species obtain virtually all of their CO2 during the dark, most species obtain CO2 during the dark and the light, and in some species dark CO2 fixation is restricted to the refixation of respiratory CO2. Such variety of expression increases the utilitarian nature of CAM (Osmond, 2007
). The ecological adaptability of CAM plants is often enhanced by an ability to modify, in response to environmental conditions, the relative amounts of CO2 assimilated in the light via the less water-use efficient C3 photosynthesis vs. CO2 assimilated in the dark by the more water-use efficient CAM process. The ability to express CAM may be constitutive or facultative, developmentally programmed, or induced in response to stress.
The majority (>90%) of epiphytes with CAM are in the monocotyledonous families Bromeliaceae (Poales) and Orchidaceae (Asparagales). In 1989, Kress
calculated that of an estimated 23 466 species of vascular plants that are epiphytes (16 610 monocots and magnoliids, 4253 eudicots, four gymnosperms, and 2599 ferns or fern allies; roughly 10% of vascular plants in toto), 74% of the species are in five families: the Orchidaceae (13 951 species), the Araceae (1349 species), the Bromeliaceae (1145 species), the Polypodiaceae (1029 species), and the Piperaceae (710 species). Though CAM is well represented in the Orchidaceae and the Bromeliaceae and moderately represented in the Piperaceae, few species have been described in the Polypodiaceae, and CAM has never been reported in the Araceae (Smith and Winter, 1996
), the family with the second highest number of epiphytic species. The absence of documented CAM species from the Araceae is surprising because it is large (at least 4025 species and 106 genera; Croat [2004]
; Stevens [2006]
), mainly tropical, and epiphyte-rich. Moreover, some epiphytes, particularly in the genus Anthurium, sport succulent leaves so characteristic of plants with CAM.
Here we report the presence of CAM in a terrestrial aroid, Zamioculcas zamiifolia Schott (Araceae). Apart from having CAM, Z. zamiifolia is an atypical aroid in several taxonomic and ecological respects. Within the Araceae, Zamioculcas is a monotypic genus in the Zamioculcadeae, a tribe basal to the subfamily Aroideae (Hesse et al., 2001
; Tam et al., 2004
; Bogner and Hesse, 2005
). Unique in the Araceae, the Zamioculcadeae can propagate vegetatively from fallen leaflets. Not a wet rainforest species like most aroids, Z. zamiifolia inhabits humid to seasonally dry forests, open bushland, and savannas in tropical east and subtropical southeast Africa (Peter, 1929
; Mayo et al., 1997
; Newton, 1997
), where it is seldom found above 800 m a.s.l. Its ability to tolerate water stress and low light has elevated Z. zamiifolia to international horticultural importance (the "ZZ plant"; Chen and Henny, 2003
). Belowground, plants consist of a large tuber and a short, thick underground stem from which arise compound leaves. Aboveground, each compound leaf consists of 4–8 pairs of oblong–elliptic, glabrous, coriaceous, slightly succulent leaflets borne on an elongate rachis attached to a succulent petiole (Mayo et al., 1997
).
MATERIALS AND METHODS
Plant material
Plants from the family Araceae and known CAM species from other plant families were cultivated in pots, with regular watering and periodic provision of slow-release complete fertilizer at the Smithsonian Tropical Research Institute, Panama City, Republic of Panama [Anthurium michelii Guillaumin (Araceae) and Z. zamiifolia]; the Department of Plant Sciences, Oxford, UK [A. harrisii (Graham) G. Don (Araceae), Kalanchoe daigremontiana Raym.-Hamet & H. Perrier (Crassulaceae) and Z. zamiifolia]; and the School of Marine and Tropical Biology, James Cook University, Australia [Agave attenuata Salm-Dyck (Agavaceae), Cissus rotundifolia Vahl (Vitaceae), Epipremnum aureum (Linden & André) G. S. Bunting (Araceae), Kalanchoe pinnata (Lam.) Pers. (Crassulaceae) and Z. zamiifolia].
Measurements of CO2 exchange
Net CO2 exchange by Z. zamiifolia was measured for distal sections of compound leaves containing eight leaflets and associated rachis. For A. michelii, a single attached fully expanded leaf was measured. Leaves, still attached to the parent plant, were sealed with Terostat VII (Henkel-Teroson, Düsseldorf, Germany), inside a gas-exchange cuvette (GWK-3M, Walz, Effeltrich, Germany) in a controlled-environment chamber operating under 12 h light (28°C, 350 µmol photon·m–2·s–1)/12 h dark (22°C) cycles. Dew point of air entering the chamber was 18°C. Net CO2 exchange was measured using a LI-6252 CO2 analyzer (LI-COR, Lincoln, Nebraska, USA) in a flow-through gas-exchange system (Holtum and Winter, 2003
) operating at 2.38 L air·min–1. Air was sourced 16 m above ground level and passed through a 1-m3 buffer.
The CO2 exchange of a succulent petiole of Z. zamiifolia was quantified for two day–night cycles in the gas-exchange system described. The petiole, 4.9 cm high and 1.9 cm diameter, was detached from the stem under water and was sealed into a beaker containing water. The detached petiole and beaker were placed in the gas-exchange system.
Extraction and assay of PEP carboxylase (PEPC)
Deacidified tissue, frozen in liquid N2, was extracted in 10 volumes of ice-cold buffer containing 200 mM tricine-KOH pH 8.0, 10% (v/v) ethanediol, 5 mM EGTA, 5 mM MgCl2, 1% (w/v) BSA, 5 mM dithiothreitol (DTT), 0.1% (v/v) Triton X-100, and insoluble polyvinylpolypyrrolidone (PVPP) of a mass equal to that of the tissue. The extracts were filtered through two layers of cheesecloth, centrifuged at 120 000 x g for 10 min, and desalted through Sephadex G-25 (PD-10 column; GE Life Sciences, NSW, Australia) with grinding medium minus Triton-100, PVPP, and BSA.
PEPC was assayed at 30°C according to Kluge et al. (1981)
.
Titratable acidity
Titratable acidity (µmol H+) was determined by measuring the volume of 5 or 10 mM NaOH required to neutralize to pH 7.0 extracts of leaves of known masses that had been frozen in liquid N2 and then boiled sequentially in 50% ethanol and water.
RESULTS
Zamioculcas zamiifolia has day–night fluctuations in titratable acidity
Well-watered Z. zamiifolia accumulated H+ in leaflets during the dark (Table 1). In comparison, leaves of E. aureum, a C3 aroid climber, and A. michelii, an epiphytic aroid with thick leaves, did not accumulate H+ during the dark. The day–night fluctuations of H+ of 2.5 µmol H+·(g fresh mass)–1 in Z. zamiifolia were small compared to those of three species with strongly expressed CAM in which maximal diel acidity changes ranged between 48 and 141 µmol H+·(g fresh mass)–1.
|
|
|
|
0.08 µmol·kg–1·s–1), whereas in the light the loss was 60% less, averaging approximately 0.2 µmol·m–2·s–1 (
0.03 µmol·kg–1·s–1).
Dark CO2 uptake is upregulated by water stress in Z. zamiifolia
Following the imposition of water stress, carbon gain during the dark increased and carbon gain during the light decreased, such that the proportion of carbon fixed during the dark rose relative to the light (Fig. 2). The reduction in CO2 uptake during the light was not uniform. Initially, the rate of CO2 uptake decreased late in the light period but not during the early light period. Subsequently, the rates of uptake in the early light period also decreased. During the imposition of stress, the enhanced carbon gain during the dark resulted from higher rates of dark CO2 uptake and longer periods during which CO2 exchange was positive. Net carbon exchange during the dark became positive after 1 d without watering and remained so for the 10 d without watering. Rewatering of drought-stressed plants was accompanied by a reduction in CO2 gain during the dark, which was initially observed during the first night after rewatering, and an increase in CO2 gain during the light (Figs. 1 and 2).
The increase in dark CO2 gain in response to drought was accompanied by a 56% increase in H+ accumulation in comparison to well-watered plants (Table 3).
|
|
Z. zamiifolia has CAM
The essential criteria that define CAM include an ability to fix CO2 during the dark and to store the carbon fixed in the vacuole as an organic acid, generally malic acid. Both well-watered and water-stressed Z. zamiifolia had net CO2 uptake during the dark and day–night fluctuations in titratable acidity (Fig. 1, Table 1). Thus, Z. zamiifolia can be classified as a CAM plant. Within the Araceae, it is the only CAM species yet reported, and within the Alismatales it is the only documented terrestrial species with CAM.
CAM in Z. zamiifolia is upregulated in response to water stress
The expression of CAM increased in response to water stress. After only 2 d without watering, both the rate and extent of dark CO2 uptake increased such that CO2 balance in the dark shifted from negative to positive. After 10 d without watering, net dark CO2 uptake increased 7.5-fold (Figs. 1 and 2).
Although CO2 uptake in the dark increased in response to water stress, the overall response to the 10 d drought treatment was a reduction by 93% of the total day–night CO2 gain (Figs. 1 and 2). This decrease in CO2 balance involved a 94% reduction in CO2 gain during the light that was offset by a small increase in CO2 uptake in the dark. Initially, the reduction in CO2 uptake in the light was confined to midday and afternoon CO2 fixation, but CO2 uptake during the morning began to decrease after 4 d of water stress.
The stimulation of CAM in response to water stress of Z. zamiifolia was reversible (Figs. 1 and 2). Upon rewatering, CO2 uptake during the light reverted to its prestress levels and dark CO2 uptake was reduced, with net CO2 uptake in the dark decreasing by 95% and CO2 balance in the dark changing from positive to negative.
The increase in net CO2 uptake in the dark that accompanied drought was most likely not solely due to an increase in PEPC-catalyzed uptake. The 56% greater diel fluctuation in titratable acidity in the water-stressed plants was consistent with an increase in net flux of carbon from CO2 to malic acid, but the rise was less than the 7.5-fold predicted from measurements of net dark CO2 uptake (Fig. 2; Table 3). Although fluctuations in titratable acidity were not measured for the leaves inside the gas-exchange cuvette (they were measured in leaves from a companion plant that grew in the growth chamber), it is probable that not all of the net increase in carbon flux into the plant was sequestered in organic acid. A component of the net increase in CO2 flux into the water-stressed tissue in the dark may have been the result of a reduction in respiratory carbon loss rather than increased assimilation per se. Stress-related decreases in CO2 uptake in the light are often accompanied by reductions in respiratory CO2 loss in the dark, a phenomenon exemplified by A. michelii, which has a 25% reduction in rates of CO2 loss in the dark after 4 d without water (Fig. 3). It is also possible that some of the CO2 fixed in the dark may have been converted to nonacidic metabolites. However, the major routes by which the early products of PEPC-mediated dark CO2 uptake are metabolized involve passage through the Krebs cycle, which results in the loss of the CO2 originally assimilated (Holtum et al., 2005
). We conclude that the net transfer of dark-fixed carbon to non-acid components is likely to be small.
Zamioculcas zamiifolia is a weak CAM plant. The fluctuations in titratable acidity of 3–5 µmol H+·(g fresh mass)–1, the extractable activity of PEPC, and the carbon gain in the dark were all low in comparison to levels in well-documented strong CAM species (Fig. 2; Tables 1–3). Why call Z. zamiifolia a CAM plant when, under well-watered conditions, it obtains 0.2% of its daily carbon during the dark, and even when stressed and CO2 uptake in the dark increased 7.5-fold in response to stress, dark CO2 uptake was only 1.5% of CO2 uptake in the light under well-watered conditions? Zamioculcas zamiifolia could be categorized as a C3 plant with a small capacity for CAM if the term CAM is applied in the narrow way that the terms C3 and C4 are generally employed, to simply describe the major pathway of photosynthesis by which the plant gains carbon throughout its lifetime. However, no plant species known is exclusively CAM, and the expression of CAM is rarely constant throughout the developmental and environmental lifetime of a plant. As a result of this flexibility of expression of CAM, the current, widely used definition of a CAM phenotype is a plant that, at any time during its lifecycle, irrespective of the amount of CO2 uptake in the light, assimilates CO2 in the dark and temporarily stores the carbon as organic acids in the vacuole, thus having diel fluctuations in titratable acidity. Ultimately, the presence or absence of the CAM cycle must be defined at the molecular level. There is, as yet, no consensus of what are the fundamental molecular markers of CAM. Because most components of the CAM cycle are also functionally present in C3 plants, the most promising candidates for markers are CAM-specific isogenes, the best studied of which is PEPC (Taybi et al., 2004
; Gehrig et al., 2005
). However, because CAM appears to have evolved often, it will be necessary to verify that marker isogenes are expressed in species across diverse taxa.
What is the advantage of CAM for Z. zamiifolia?
Although information on the ecology of Z. zamiifolia is scarce, it appears that in east Africa Z. zamiifolia is a plant of rocky, partially shaded sites in habitats subject to prolonged seasonal drought (Mayo et al., 1997
; Newton, 1997
). Zamioculcas zamiifolia in its natural habitat of high evaporative demand probably has a positive dark CO2 balance throughout much of the year as long as leaves are present. In situ water stress is likely to be more prolonged and severe than that imposed by us experimentally. In our experiments, the decrease in CO2 uptake during the light had not stabilized after 10 d of water stress (Figs. 1 and 2) and could be expected to fall further. At times, the contribution of CAM to 24-h carbon gain in Z. zamiifolia in its natural habitat is thus likely to exceed the 19% we observed. The role of CAM in the survival of Z. zamiifolia is that it contributes to the maintenance of a positive carbon balance while the plant reduces water loss by reducing CO2 uptake in the light. Water-use efficiency is thereby increased, and the period of net carbon gain is prolonged. Eventually, if stress persists, the rachis and leaflets abscise, reducing the aboveground plant to an apparently dormant cluster of erect, succulent, petiole bases (Newton, 1997
).
CAM is not the only water-conserving feature of Z. zamiifolia. Radiative load and transpirational water loss are reduced by erect, coriaceous, reflective, succulent leaflets with abaxial stomata, and by the erect, cylindrical, succulent petiole and rachis. The leaflets and tuber are rarely subject to herbivory, an observation consistent with the presence of chemical defenses, a feature common in the Araceae (Dring et al., 1995
).
Why is CAM apparently rare in the Araceae, particularly in epiphytes?
CAM is a derived condition that has evolved repeatedly in response to selection imposed by dry conditions and/or selection driven by low levels of dissolved carbon (Griffiths, 1989
; Keeley, 1998
). CAM is uncommon in the basal angiosperms, where it is present only in the most derived order, the Piperales (Peperomia spp.; Holthe et al., 1992
). Similarly, in the basal monocots, CAM is absent (Acorales, Petrosaviales) or rare (Alismatales). Many species in the basal monocots, particularly in the Alismatales, the order in which the Araceae are located, inhabit aquatic, marine, or mesic swampy areas. It is therefore perhaps not surprising that both known CAM species in the Alismatales, Sagittaria subulata (L.) Buchenau (Alismataceae) and Vallisneria americana Michx. (Hydrocharitaceae), are aquatic (Keeley, 1981
, 1996
; Webb et al., 1988
).
Fossil Araceae are associated with lacustrine deposits and generally moist habitats (Friis et al., 2004
; Wilde et al., 2005
). Indeed, the Araceae have not radiated extensively into water-limited environments (Mayo et al., 1997
). The few Araceae that inhabit deserts and semiarid regions, or grow at high altitude, tend to be geophytes that are characteristically deciduous or seasonally dormant. Modern Araceae are most abundant and diverse in the humid tropics. The epiphytic Araceae are principally wet forest species, generally inhabiting sites less exposed than those of most bromeliads and orchids. Benzing (1989)
notes that although many Araceae are secondary hemiepiphytes, a life form that might be expected to be well adapted to intermittent water stress, they characteristically exhibit fewer epiphytic specializations for coping with water stress than do bromeliads and orchids. As a result, they are typically restricted to more moist habitats where selection pressure for CAM may not be as pronounced.
If ancient Araceae and Isoetes, the oldest lineage of plants with CAM, were plants of wetlands, why is CAM common in extant Isoetes but not in the Araceae? A selection pressure for the retention of CAM in Isoetes may have been their poor ability to compete with faster-growing radiating flowering plants (Keeley, 1998
). Presumably by retaining CAM, Isoetes could reduce competition for inorganic carbon and thus could grow in the presence of more vigorous species in temporally carbon-infertile lakes. CAM also provided a mechanism for survival in permanently carbon-infertile waters and enabled them to utilize locally high concentrations of CO2 in muds. In contrast, the more rapid growth rates of the Araceae may have remained to be associated with C3 because they gleaned sufficient inorganic carbon in lacustrine environments. Presumably the lacustrine Araceae adopted amphibian habits that provided access to atmospheric CO2. The selection pressures for CAM in terrestrial plants living in extremely moist soils were unlikely to be strong. It may be relevant that many extant lacustrine Isoetes are amphibious species in which the submerged leaves express CAM but the emerged leaves are C3 (Keeley, 1996
, 1998
).
It is also possible that CAM may be more common in the Araceae than we are aware. Certainly, Araceae are often under-represented in isotopic surveys of epiphytes (Winter et al., 1983; Earnshaw et al., 1987
; Carter and Martin, 1994
), possibly because the surveyors tend to collect species that have recognizably succulent leaves and tend to ignore hemi-epiphytes. The most likely araceous candidates for CAM, on the basis of epiphytic habitat and succulence of leaves, are in the sections Leptanthurium and Porphyrochitonium of the genus Anthurium (subfamily Pothoideae), which contains over 800 species (Mayo et al., 1997
). To date, the few Anthurium spp. examined in carbon isotope surveys have C3-like
13C values, e.g., nine Anthurium species on Barro Colorado Island, Panama had
13C values between –28.1
and –33.7
(Zotz and Ziegler, 1997
). However, carbon isotope surveys that measure the integrated day–night carbon uptake signal over the life of the organ sampled rarely have the resolution required to detect weak CAM in plants that acquire only a small proportion of their carbon during the dark (Winter and Holtum, 2002
).
How prevalent is CAM in vascular plants?
The most recent estimate of the prevalence of CAM in vascular plants is that of Smith and Winter (1996)
, who documented CAM in 33 families and 328 genera containing about 16 000 species. The species number was based on the estimation that 50% of tropical epiphytic orchids and bromeliads are CAM. The 1996 census requires updating to accommodate reassessments of vascular plant taxonomy (e.g., Asclepiadaceae are now in the Apocynaceae, and Dracaenaceae are now in the Ruscaceae; Chase et al., 2000
; Stevens, 2006
), the report of CAM in a cycad (Vovides et al., 2002
), an extensive survey of bromeliad carbon isotope compositions (Crayn et al., 2004
), the discovery of new CAM genera in the Crassulaceae and Orchidaceae (Silvera et al., 2005
; Liu and Wang, 2006
), and this communication of CAM in the Araceae. We report that CAM is present in 34 families and 343 genera of vascular plants (Table 4). The great uncertainty is still the total number of CAM species. An improved estimate of the number of species requires extensive carbon isotope surveys of, in particular, the orchids. We suspect, however, that there are many species like Z. zamiifolia, in which the contribution of dark CO2 uptake to daily carbon gain is so small that it would not produce an identifiable isotopic signal (Winter and Holtum, 2002
; Silvera et al., 2005
). Discovery of these CAM species requires a more labor-intensive quantification of H+ fluctuations.
|
FOOTNOTES
1 The authors acknowledge the support of a Magdalen College Visiting Fellowship (J.A.M.H.); J.A.C. Smith and the Department of Plant Sciences, University of Oxford (J.A.M.H.); the Andrew W. Mellon Foundation (K.W.); and the Smithsonian Tropical Research Institute (K.W. and J.A.M.H.). C. Finney (James Cook University, Townsville) provided histological support and T. B. Croat (Missouri Botanical Garden) and C. Galdames (Smithsonian Tropical Research Institute) identified Anthurium michelii. ![]()
4 Author for correspondence (joseph.holtum{at}jcu.edu.au
) ![]()
LITERATURE CITED
Benzing D. H.. 1989. The evolution of epiphytism. In U. Lüttge, [ed.], Vascular plants as epiphytes, 15-41. Springer-Verlag, Berlin, Germany..
Bogner J. Hesse M.. 2005. Zamioculcadoideae, a new subfamily of Araceae. Aroideana 28: 3-20..
Carter J. P. Martin C. E.. 1994. The occurrence of crassulacean acid metabolism among epiphytes in a high-rainfall region of Costa Rica. Selbyana 15: 104-106..
Chase M. W. Soltis D. E. Soltis P. S. Rudall P. J. Fay M. F. Hahn W. H. Sullivan S. Joseph J. Givnish T. Sytsma K. J. Pires J. C.. 2000. Higher-level systematics of the monocotyledons: an assessment of current knowledge and a new classification. In K. L. Wilson, D. A. Morrison, [eds.], Monocots systematics and evolution, 3-16. CSIRO, Melbourne, Australia..
Chen J. J. Henny R. J.. 2003. ZZ: a unique tropical ornamental foliage plant. Horttechnology 13: 458-462..[Web of Science]
Crayn D. M. Winter K. Smith J. A. C.. 2004. Multiple origins of crassulacean acid metabolism and the epiphytic habit in the neotropical family Bromeliaceae. Proceedings of the National Academy of Sciences, USA 101: 3703-3708..
Croat T. B.. 2004. History and current status of systematic research with Araceae, 6th ed. Website http://www.aroid.org/literature/croat/history [accessed 27 January 2007]..
Dring J. V. Kite G. C. Nash R. J. Reynolds T.. 1995. Chemicals in aroids: a survey, including new results for polyhydroxy alkaloids and alkylresorcinols. Botanical Journal of the Linnean Society 117: 1-12..[CrossRef][Web of Science]
Earnshaw M. J. Winter K. Ziegler H. Stichler W. Cruttwell N. E. G. Kerenga K. Cribb P. J. Wood J. Croft J. R. Carver K. A. Gunn T. C.. 1987. Altitudinal changes in the incidence of crassulacean acid metabolism in vascular epiphytes and related life forms in Papua New Guinea. Oecologia 73: 566-572..[CrossRef][Web of Science]
Friis E. M. Pedersen K. R. Crane P. R.. 2004. Araceae from the Early Cretaceous of Portugal: evidence on the emergence of monocotyledons. Proceedings of the National Academy of Sciences, USA 101: 16565-16570..
Gehrig H. H. Aranda J. Cushman M. A. Virgo A. Cushman J. C. Hammel B. E. Winter K.. 2003. Cladogram of Panamanian Clusia based on nuclear DNA: implications for the origins of crassulacean acid metabolism. Plant Biology 5: 59-70..[Medline]
Gehrig H. H. Wood J. A. Cushman M. A. Virgo A. Cushman J. C. Winter K.. 2005. Large gene family of phosphoenolpyruvate carboxylase in the crassulacean acid metabolism plant Kalanchoe pinnata (Crassulaceae) characterized by partial cDNA sequence analysis. Functional Plant Biology 32: 467-472..[CrossRef][Web of Science]
Griffiths H.. 1989. Carbon dioxide concentrating mechanisms and the evolution of CAM in vascular epiphytes. In U. Lüttge, [ed.], Vascular plants as epiphytes, 42-86. Springer-Verlag, Berlin, Germany..
Hesse M. Bogner J. Halbritter H. Weber M.. 2001. Palynology of the perigoniate Aroideae: Zamioculcas, Gonatopus and Stylochaeton (Araceae). Grana 40: 26-34..[CrossRef][Web of Science]
Hew C. S. Wong Y. S.. 1974. Photosynthesis and respiration of ferns in relation to their habitat. American Fern Journal 64: 40-48..[CrossRef]
Hibberd J. M. Quick W. P.. 2002. Characteristics of C4 photosynthesis in stems and petioles of C3 flowering plants. Nature 415: 451-454..[CrossRef][Medline]
Holthe P. A. Patel A. Ting I. P.. 1992. The occurrence of CAM in Peperomia. Selbyana 13: 77-87..
Holtum J. A. M. Aranda J. Virgo A. Gehrig H. H. Winter K.. 2004.
13C values and crassulacean acid metabolism in Clusia species from Panama. Trees—Structure and Function 18: 658-668..
Holtum J. A. M. Smith J. A. C. Neuhaus H. E.. 2005. Intracellular transport and pathways of carbon flow in plants with crassulacean acid metabolism. Functional Plant Biology 32: 429-449..[CrossRef][Web of Science]
Holtum J. A. M. Winter K.. 1999. Degrees of crassulacean acid metabolism in tropical epiphytic and lithophytic ferns. Australian Journal of Plant Physiology 26: 749-757..[Web of Science]
Holtum J. A. M. Winter K.. 2003. Photosynthetic CO2 uptake in seedlings of two tropical tree species exposed to oscillating elevated concentrations of CO2. Planta 218: 152-158..[CrossRef][Web of Science][Medline]
Holtum J. A. M. Winter K.. 2005. Carbon isotope composition of canopy leaves in a tropical forest in Panama throughout a seasonal cycle. Trees—Structure and Function 26: 545-551..
Keeley J. E.. 1981. Isoetes howellii: a submerged aquatic CAM plant?. American Journal of Botany 68: 420-424..[CrossRef][Web of Science]
Keeley J. E.. 1996. Aquatic CAM photosynthesis. In K. Winter, J. A. C. Smith, [eds.], Crassulacean acid metabolism, 281-295. Springer-Verlag, Berlin, Germany..
Keeley J. E.. 1998. CAM photosynthesis in submerged aquatic plants. Botanical Review 64: 121-176..[CrossRef]
Keeley J. E. Osmond C. B. Raven J. A.. 1984. Stylites, a vascular land plant without stomata absorbs CO2 via its roots. Nature 310: 694-695..[CrossRef]
Kluge M. Brulfert J. Queiroz O.. 1981. Diurnal changes in the regulatory properties of PEP-carboxylase in crassulacean acid metabolism (CAM). Plant, Cell and Environment 4: 251-256..
Kress W. J.. 1989. The systematic distribution of vascular epiphytes. In U. Lüttge [ed.], Vascular plants as epiphytes, 234-261. Springer-Verlag, Berlin, Germany..
Liu X. Q. Wang R. Z.. 2006. Photosynthetic pathway and morphological functional types in the vegetation from North-Beijing agro-pastoral ecotone, China. Photosynthetica 44: 365-386..[CrossRef][Web of Science]
Lüttge U.. 2006. Photosynthetic flexibility and ecophysiological plasticity: questions and lessons from Clusia, the only CAM tree, in the neotropics. New Phytologist 171: 7-25..[CrossRef][Web of Science][Medline]
Mayo S. J. Bogner J. Boyce P. C.. 1997. The genera of the Araceae. Kew Publishing, Kew, UK..
Newton L.. 1997. Zamioculcas zamiifolia. Ballya 4: 68-69..
Osmond C. B.. 2007. Crassulacean acid metabolism: now and then. Progress in Botany 68: 3-32..
Osmond C. B. Ziegler H. Stichler W. Trimborn P.. 1975. Carbon isotope discrimination in alpine succulent plants supposed to be capable of crassulacean acid metabolism (CAM). Oecologia 18: 209-217..[CrossRef][Web of Science]
Peter A.. 1929. Die Araceae Deutsch-Ostafrikas. Nachrichten von der Gesellschaft der Wissenschaften zu Göttingen, Mathematisch-Physikalische Klasse 3: 185-225..
Silvera K. Santiago L. S. Winter K.. 2005. Distribution of crassulacean acid metabolism in orchids of Panama: evidence of selection for weak and strong modes. Functional Plant Biology 32: 397-407..[CrossRef][Web of Science]
Skillman J. B. Garcia M. Virgo A. Winter K.. 2005. Growth irradiance effects on photosynthesis and growth in two co-occurring shade-tolerant neotropical perennials of contrasting photosynthetic pathways. American Journal of Botany 92: 1811-1819..
Smith J. A. C. Winter K.. 1996. Taxonomic distribution of crassulacean acid metabolism. In K. Winter, J. A. C. Smith, [eds.], Crassulacean acid metabolism, 427-436. Springer-Verlag, Berlin, Germany..
Stevens P. F.. 2006. Angiosperm Phylogeny Website, version 7, May 2006. Website http://www.mobot.org/MOBOT/research/APweb/ [accessed 17 January 2007]..
Tam S.-M. Boyce P. C. Upson T. M. Barabé D. Bruneau A. Forest F. Parker J. S.. 2004. Intergeneric and infrafamilial phylogeny of subfamily Monsteroideae (Araceae) revealed by chloroplast trnL-F sequences. American Journal of Botany 91: 490-498..
Taybi T. Nimmo H. G. Borland A. M.. 2004. Expression of phosphoenolpyruvate carboxylase and phosphoenolpyruvate carboxylase kinase genes. Implications for genotypic capacity and phenotypic plasticity in the expression of crassulacean acid metabolism. Plant Physiology 135: 587-598..
Von Willert D. J. Armbrüster N. Drees T. Zaborowski M.. 2005. Welwitschia mirabilis: CAM or not CAM—what is the answer?. Functional Plant Biology 32: 389-395..[CrossRef][Web of Science]
Vovides A. P. Etherington J. R. Dresser P. Q. Groenhof A. Iglesias C. Ramirez J. F.. 2002. CAM-cycling in the cycad Dioon edule Lindl. in its natural tropical deciduous forest habitat in central Veracruz, Mexico. Botanical Journal of the Linnean Society 138: 155-161..[CrossRef][Web of Science]
Webb D. R. Rattray M. R. Brown J. M. A.. 1988. A preliminary survey for crassulacean acid metabolism (CAM) in submerged aquatic macrophytes in New Zealand. New Zealand Journal of Marine and Freshwater Research 22: 231-235..[Web of Science]
Wilde V. Kvacek Z. Bogner J.. 2005. Fossil leaves of the Araceae from the European Eocene and notes on other aroid fossils. International Journal of Plant Sciences 166: 157-183..[CrossRef][Web of Science]
Winter K. Aranda J. Holtum J. A. M.. 2005. Carbon isotope composition and water-use efficiency in plants with crassulacean acid metabolism. Functional Plant Biology 32: 381-388..[CrossRef][Web of Science]
Winter K. Holtum J. A. M.. 2002. How closely do the
13C values of CAM plants reflect the proportion of CO2 fixed during day and night?. Plant Physiology 129: 1843-1851..
Winter K. Holtum J. A. M.. 2005. The effects of salinity, crassulacean acid metabolism and plant age on the carbon isotope composition of Mesembryanthemum crystallinum L., a halophytic C3-CAM species. Planta 222: 201-209..[CrossRef][Web of Science][Medline]
Winter K. Holtum J. A. M.. 2007. Environment or development? Lifetime net CO2 exchange and control of the expression of crassulacean acid metabolism in Mesembryanthemum crystallinum. Plant Physiology 143: 98-107..
Winter K. Smith J. A. C.. 1996. An introduction to crassulacean acid metabolism. Biochemical principles and ecological diversity. In K. Winter, J. A. C. Smith, [eds.], Crassulacean acid metabolism, 1-13. Springer-Verlag, Berlin, Germany..
Zotz G. Ziegler H.. 1997. The occurrence of crassulacean acid metabolism among vascular epiphytes from central Panama. New Phytologist 137: 223-229..[CrossRef][Web of Science]
This article has been cited by other articles:
![]() |
K. Silvera, L. S. Santiago, J. C. Cushman, and K. Winter Crassulacean Acid Metabolism and Epiphytism Linked to Adaptive Radiations in the Orchidaceae Plant Physiology, April 1, 2009; 149(4): 1838 - 1847. [Abstract] [Full Text] [PDF] |
||||
![]() |
A. Herrera Crassulacean acid metabolism and fitness under water deficit stress: if not for carbon gain, what is facultative CAM good for? Ann. Bot., February 1, 2009; 103(4): 645 - 653. [Abstract] [Full Text] [PDF] |
||||
![]() |
J. Karbulkova, L. Schreiber, P. Macek, and J. Santrucek Differences between water permeability of astomatous and stomatous cuticular membranes: effects of air humidity in two species of contrasting drought-resistance strategy J. Exp. Bot., October 3, 2008; (2008) ern238v1. [Abstract] [Full Text] [PDF] |
||||
![]() |
K. Winter, M. Garcia, and J. A. M. Holtum On the nature of facultative and constitutive CAM: environmental and developmental control of CAM expression during early growth of Clusia, Kalanchoe, and Opuntia J. Exp. Bot., May 1, 2008; 59(7): 1829 - 1840. [Abstract] [Full Text] [PDF] |
||||
| ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
| HOME | HELP | FEEDBACK | SUBSCRIPTIONS | ARCHIVE | SEARCH | TABLE OF CONTENTS |