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iForest - Biogeosciences and Forestry
vol. 9, pp. 409-413
Copyright © 2016 by the Italian Society of Silviculture and Forest Ecology
doi: 10.3832/ifor1893-008

Short Communications

Differential adaptations in nursery seedlings from diverse Chilean provenances of Peumus boldus Mol.

Carlos R Magni (1), Sergio E Espinoza (2)Corresponding author, Emilio F Garrido (1), Rómulo E Santelices (2), Antonio M Cabrera (2)

Introduction 

In the last decades, several studies reported the increase of land degradation and desertification in Mediterranean ecosystems ([12], [23], [29]). Mediterranean plants are well adapted to summer drought, though such adaptation may not be sufficient to ensure plant regeneration under extreme land degradation scenarios (e.g., wildfires - [27]). Indeed, water stress is a major cause of failure in ecological restoration of Mediterranean ecosystems ([20]). According to climate change predictions, the frequency and intensity of drought is expected to increase in Mediterranean regions ([8], [14]). This calls for studies focused on the ecology of species and their intra-specific variability in order to better understand their adaptability to the predicted changes and their suitability for ecological restoration purposes.

Peumus boldus Mol. (Boldo) is a sclerophyllous evergreen shrub native to Chile between 30° to 41° S and growing in plant communities of the Mediterranean region in central Chile ([13]). This species has several characteristics that make it an interesting case study for ecological restoration protocols, namely, a higher resistance to drought compared with other Mediterranean species, surviving in sites with less than 200 mm of annual precipitation ([7]). Its perennial leaves are used in medicine for their digestive, choleretic, and liver-protection properties ([9]), and this has generated a high pressure over the native forests. Furthermore, Boldo seeds have low germination rates (19-44% - [7]) due to the dormancy imposed by the essential oils of the pericarp. Botti & Cabello ([6]) pointed out that if Boldo seeds are sown during fall or winter, they will only germinate during the winter of the next year, being the embryo still immature; therefore, seeds must be collected in spring and sown immediately.

Despite the strong geographical isolation of southern provenances from the northern ones ([7]), information about the genecological differentiation of Peumus boldus is scarce. Vogel et al. ([33]) analyzed alkaloid and essential oil production in three different Boldo populations from central Chile, finding that northern provenances had significantly higher essential oil content and alkaloid concentration. Moreover, the available information on the variability of germination and seedling growth among provenances is limited. Germination was reported to greatly vary among populations ([4]).

It is known that provenances growing in Mediterranean environments show reduced leaf area as one of the key traits to withstand water deficit ([1]). Contrastingly, provenances from more mesic environments have elongated and large leaves and are restricted to humid or subhumid sites mainly in mild coastal areas (e.g., the “ilex” morphotype of Quercus ilex - [19]). According to the theory of specialization ([18]), genotypes adapted to favorable environments present superior performances in these environments as compared with those adapted to drought, but this is reduced when conditions are limiting, which results in a high phenotypic plasticity. It is also known that germination requirements of different species are often related to specific adaptation to their habitat ([22]). As a consequence, seeds collected from different parts of the species’ range often vary in their germination requirements.

In Chile, a limited number of studies have been carried out in P. boldus on the effect of provenance and mother plant in seed germination and seedling development. The aim of the present study was to analyze the effect of seed provenance and mother plant on the germination and short-term development of P. boldus. The wide distribution of P. boldus and the heterogeneity of the environments colonized suggest a high phenotypic plasticity of the species in terms of morphology. We tested the hypothesis that seedlings from northern provenances are more adapted to xeric environments, while southern provenances have adaptation mechanisms suitable for more humid environments.

Material and methods 

Site selection

Four provenances of P. boldus were selected in mainland Chile, at distances of at least 150 km, along a latitudinal gradient (Fig. 1). Two seed sources from central Chile represented northern provenances (Quebrada de la Plata and Colorado), and two seed sources from the south represented southern provenances (Villarica and Llifén). A general description of the seed collection sites is given in Tab. 1. Ripe fruits of trees were harvested at the four collection sites between December 2006 and February 2007. The collection date varied since the rate of seed maturation differed between provenances (early December in the north, late February in the south). For each provenance, five dominant or co-dominant mother trees with clear bole, well developed crown, good health condition and abundant fruits were randomly selected at a minimum distance of 100 m. We harvested 500 fruits per mother tree, evenly distributed over the canopy. Fruits were then depulped, seeds were washed and sown immediately after collection, according to Botti & Cabello ([6]).

Fig. 1 - Location of the four provenances of Peumus boldus selected for seed collection (red circles).
Tab. 1 - Location, Köppen climate classification, mean annual temperature and mean total precipitation of the four collection sites.

Seed germination variability

Seeds were soaked in distilled water for 24-48 h and those floating were discarded. Seeds were set to germinate in 1-liter plastic pots containing a mixture of sand and topsoil 1:1 (v/v). Four plastic pots were used as replicates and a total of 100 seeds per mother plant were sown in each pot. Seeds were then placed under nursery conditions (average temperature 23.5 °C, 60-80% relative humidity). The nursery was located at the University of Chile, Santiago (33° 34′ 05″ S, 70° 37′ 55″ W, 611 m. a.s.l) with climatic conditions similar to those of the Quebrada de la Plata provenance. Germination was monitored two times per week and recorded when the radicle emerged from the testa. The germination capacity (GC) was expressed as the proportion of the total number of germinated seeds out of sown seeds. Seed weight (SW) was estimated according to ISTA ([15]) and expressed as the average weight of 1000 seeds. As P. boldus has germination difficulties due the pericarp, seeds were sown immediately after harvesting, which led to different sowing dates. To avoid possible biases due to differences in sowing date, the number of days elapsed since sowing until full germination (radicle > 5 mm showing geotropism - DG) was registered for every provenance.

Seedling growth

The germinated seeds were transferred to 130 mL containers (BASF®, Santiago, Chile) filled with a mixture of sand and topsoil 1:1 (v/v). No fertilizer was added to the substrate. The experimental setup comprised four provenances, five mother plants per provenance, five replicates of 7 seedlings per replicate, totaling 700 seedlings (4×5× 5×7 = 700 seedlings). The seedlings were watered to field capacity and grown under nursery conditions during one growing season. Seedlings were protected by a 50% shading plastic mesh (Raschel®, Santiago, Chile).

Total height (H, cm), root collar diameter (D, mm) and number of leaves (NL) of all seedlings were recorded, as well as their survival in percentage (SUR). Survival was measured according to a categorical scale (1 = alive, 0 = dead). At the end of the first year of growth, seedlings were cut and separated into three fractions: leaves, stems and roots. The dry weight of each fraction was determined after oven drying at 65 °C for 48 h. The relative biomass was then determined and the following variables were recorded: leaf dry weight (LDW), stem dry weight (SDW), root dry weight (RDW) and total dry weight (TDW). Root weight ratio (RWR = RDW/TDW) and leaf weight ratio (LWR = LDW/TDW) were also determined. Foliar area of seedlings (FA, cm2) was also measured using a common desk-top scanner (Hewlett-Packard®, Cupertino, CA), and the surface of all leaves measured using a digital planimeter (Tamaya®, Tokyo, Japan). Roots length (RL, cm) was also measured as the distance from the root collar to the top of the tap root.

Statistical analysis

All traits were analyzed by 2-Way ANOVA using a nested design, i.e., provenance as a fixed factor and the mother plant as the random nested factor within provenance. The general linear model approach (GLM) was used, with type III sum of squares. Comparisons between groups for categorical variables (i.e., SUR) were done using a Chi-square test. Tukey’s HDS post-hoc tests were carried out when significant provenance and mother plant differences were detected (α = 0.05). The SPSS® v.18 software (IBM, New York, USA) was used for all statistical analyses.

Results 

Variability in seed germination

The overall mean germination capacity (GC) of P. boldus seeds was low (Tab. 2). However, significant differences in GC among mother plants within provenances were found. For example, the mean germination capacity in the Colorado and Llifén provenances differed by more than 100%. Seed weight was different among both provenances and mother plant; however, the germination of small seeds (<650 mg) was similar to that of large seeds (>900 mg). Moreover, we found significant differences among provenances in the germination time (i.e., the number of days elapsed from sowing to the emergence of the radicle - DG). Indeed, northern provenances germinated 37 days later than southern provenances.

Tab. 2 - Main effects on seed parameters of P. boldus tested through 2-way ANOVA using provenance (Prov) as fixed factor and mother plant (MP) as a random factor nested within provenance. Means ± standard errors are reported. (GC): Germination capacity; (SW): average weight of 1000 seeds; (DG): days elapsed since sowing to radicle emergence. (*): p < 0.05; (ns): non-significant.

Seedling development

Morphological traits and survival were different at the provenance and mother plant levels for most traits under consideration (Tab. 3). Seedlings from the southern provenances (Villarrica and Llifén) were taller and with thicker diameters than those from the northern provenances; however, the highest survival rate was found in the latter provenances (Colorado). Significant differences in leaf number and morphology were also found. Northern provenances showed smaller leaves as compared with southern ones, which had a lesser number of larger leaves. Regarding root anatomy, significant differences were also observed at population and mother plant levels. Seedlings from northern provenances (Quebrada de la Plata) exhibited longer roots as compared to southern provenances (Villarica and Llifén).

Tab. 3 - Main effects in morphological traits and survival of P. boldus tested through 2-way ANOVA using provenance (Prov) as fixed factor and mother plant (MP) as a random factor nested within provenance. Means ± standard errors are reported. (H): total seedling height; (D): root collar diameter; (NL): number of leaves; (SUR): survival; (RL): root length; (FA): foliar area. (*): p < 0.05; (ns): non-significant.

Biomass allocation

In general, there was shift in biomass allocation from northern to southern provenances, with the northernmost provenance seedlings (Quebrada de la Plata) having less body mass (TDW) and allocating a higher proportion of the total mass to belowground organs (RWR). Contrastingly, the southernmost provenance seedlings (Llifén) were taller and allocated a larger proportion of the total mass to leaves (LWR - Tab. 4). No differences in SDW were observed among provenances.

Tab. 4 - Main effects in biomass traits of P. boldus tested through 2-Way Analysis of Variance (ANOVA) using provenance (Prov) as fixed factor and mother plant (MP) as a random factor nested within provenance. Mean ± standard errors are reported. (LDW): leaf dry weight; (SDW): shoot dry weight; (RDW): root dry weight; (TDW): total dry weight; (RSR): root to shoot ratio; (RWR): root weight ratio; (LWR): leaves weight ratio. (*): p < 0.05; (ns): non significant.

Discussion 

Seed germination

In this study, the germination of P. boldus seeds was highly variable among mother plants within provenances, while its variation among provenances was not significant. The variability of seed germination is often interpreted as reflecting adaptations to specific ecological conditions ([11], [25]). Obviously, the environmental characteristics of the microsite occupied by a seed may strongly influence its probability of germination; however, the environmental conditions experienced by mother trees in the previous generation may also affect the germination of seeds ([28], [2]). Small differences in local site conditions, such as substrate type, soil humidity etc., cannot be excluded even when seeds are collected in the neighborhood. Several studies have shown a small-scale adaptation to such local habitat differentiation ([17], [3]), which may reduce the correlation between population differentiation and geographical distance.

In this study, we found no differences in seed germination capacity among different P. boldus provenances from a wide latitude gradient, while all the variation was attributed to differences among individual mother trees. Intra-population variability in germination is common in forest tree populations ([2]) and might correspond to genetic factors ([31]) as well as environmental variability during seed ripening ([21]). In addition, seeds collected from different individuals of the same population also display large differences in germination, which supports the hypothesis that individual mother tree genotype also plays an important role in seed germination. Indeed, an attempt was made to minimize microsite-specific environmental differences by collecting seeds only from healthy individuals growing under similar conditions in the field. Nonetheless, the observed differences in germination capacity may be interpreted as mainly due to maternal effects, i.e., to genetic differences of the sampled trees. However, a complete ecological understanding of the variation in P. boldus seed germination requires a multiple generation study.

Another possible explanation of the large within-population variation observed in seed germination could be related to differences in fruit ripening among mother trees. As a general rule, fruits should be collected only after the seeds have reached the full maturity ([5]). This aspect has been poorly investigated in P. boldus. According to Muñoz ([24]) the germination capacity of this species diminishes when the fruit is overripe; however, full seed maturity is not easily detectable, as the fruit color is widely used as an indicator of seed maturity. As mentioned above, we sowed P. boldus seeds immediately after fruit collection to avoid changes in their germination responses due to dry storage at room temperatures ([2]). However, differences in seed dormancy due to their different maturity cannot be excluded.

Different seed dormancy levels may also reflect differences in germination length, in terms of days elapsed since sowing until the radicle emerge (DG). In our study, significant differences in DG were found among geographically distinct provenances of the species. The northern Colorado provenance had the higher DG, which could be related to the higher elevation and lower mean annual temperature of the site (700-800 m and 8.1 °C, respectively). A longer delay in seed germination with increasing altitude and decreasing temperature may be the result of the increased susceptibility to unfavorable conditions during flowering and seed development. Moreover, seeds from this provenance were the smallest, indicating a lower endosperm content and thus lesser source of nutrient available for the embryo, which may defer the initiation of germination. Indeed, it has been reported that small seeds usually emerge more slowly ([30]). It is noteworthy to mention that the northernmost provenance (Quebrada de la Plata), characterized by large seeds sown three months earlier than southern provenances, showed a slower germination and yielded smaller seedlings with less body mass at the end of the experiment. This provenance seems to be adapted to the harsh conditions of the collection site, characterized by a low annual precipitation. Thus, it could be hypothesized that a delayed seed germination might represent an adaptation strategy to escape unfavorable conditions.

Seedling development and biomass allocation

We found a strong differentiation in seedling growth and biomass (both above- and belowground) among all the four provenances tested. The northernmost provenance site (Quebrada de la Plata) is characterized by a Mediterranean climate with low precipitation; accordingly, its seedlings showed the lowest foliar area (FA), which suggests a higher growth potential under low water availability, as a smaller transpiration surface may reduce the desiccation risk. Results of the present study are in line with findings of Doll et al. ([10]) who analyzed three provenances of P. boldus in central Chile and found that the Mediterranean provenance had more leaf rolling than Coastal provenances. Leaf rolling has been proposed to be an effective mechanism in decreasing the transpiration rate of plants experiencing water deficit ([26], [16]).

On the other hand, southern provenances showed a lower survival rate when growing in a Mediterranean climate (as at the nursery in Quebrada de la Plata). According to the theory of specialization ([18]), genotypes adapted to favorable environmental conditions exhibit superior performances in these environments, but the opposite occurs when conditions become limiting. In this study, seedlings from southern provenances showed performances consistent with this theory. In the xeric environment of the nursery, they grew more (higher H and TDW) and likely had an overall higher transpiration (as inferred from the superior FA, LDW and LWR), which clearly reduced survival. These provenances grow well in sites with more than 2000 mm annual precipitation, while in Quebrada de la Plata rainfall was only 350 mm.

Although based on a nursery experiment with no field validation, our results revealed some important consequences in the field of restoration ecology. The introduction of P. boldus southern provenances in sites with a more Mediterranean climatic characteristics, as in the northern part of the species’ range, may result in poor adaptation. Native plant species are routinely planted or sown in ecological restoration projects, but successful establishment and survival often depend on where and how seeds are collected ([32]). Our results highlights the importance of using seeds from locally adapted individuals of P. boldus in Mediterranean restoration projects, as local populations often show better performances as compared with non-local genotypes. Southern provenances of P. boldus showed several characteristics typical of genotypes non-tolerant to drought (i.e., taller, with more body mass, larger leaf area and less root biomass), thus their use in restoration projects in drought-prone Mediterranean sites should be avoided. This is particularly important in regions such as Chile, where the Mediterranean environments are expected to shift southward as a consequence of the global climate change.

Conclusions 

Provenance played a significant role in the early development of seedlings of P. boldus, highlighting the importance of the choice of suitable seed sources in ecological restoration plans. Northern provenances showed higher survival in comparison with the southern provenances. In addition, seedlings of the provenance from the driest site allocated more biomass to roots and less leaf dry weight, which suggest their adaptation to drought-prone Mediterranean ecosystems. On the other hand, the southern provenance seems to be more adapted to humid environments.

Acknowledgements 

The authors gratefully acknowledge Dr. Anne Bliss from the University of Colorado at Boulder (CO, USA) who provided helpful criticism of the manuscript.

CR conceived the study, organized the seed collection and reviewed the final manuscript; SE carried out the data analysis, and wrote an earlier draft and the final version of the manuscript; EG carried out the seed collection and the nursery trial; RS contributed with ideas and comments on the methodology of an earlier draft of the manuscript; AC commented the final draft of the manuscript.

References

(1)
Baldocchi DD, Xu L (2007). What limits evaporation from Mediterranean oak woodlands - the supply of moisture in the soil, physiological control by plants or the demand by the atmosphere? Advances in Water Resources 30: 2113-2122.
::CrossRef::Google Scholar::
(2)
Baskin CC, Baskin JM (2014). Seeds ecology, biogeography, and evolution of dormancy and germination. Academic Press, San Diego, CA, USA, pp. 1600.
::Google Scholar::
(3)
Bischoff A, Crémieux L, Smilauerova M, Lawson C, Mortimer S, Dolezal J, Lanta V, Edwards AR, Brook AJ, Macel M, Leps J, Steinger T, Müller-Schärer H (2006a). Detecting local adaptation in widespread grassland species - the importance of scale and local plant community. Journal of Ecology 94: 1130-1142.
::CrossRef::Google Scholar::
(4)
Bischoff A, Vonlanthen B, Steinger T, Müller-Schärer H (2006b). Seed provenance matters - effects on germination of four plant species used for ecological restoration. Basic and Applied Ecology 7: 347-359.
::CrossRef::Google Scholar::
(5)
Bonner FT, Karrfalt RP (2008). The woody plant seed manual. Agriculture Handbook 727, USDA Forest Service, Government Printing Office, Washington, DC, USA, pp. 1228.
::Online::Google Scholar::
(6)
Botti CG, Cabello A (1990). Anatomía y desarrollo de flores, frutos y semillas de boldo (Peumus boldus Mol.) [Anatomy and development of flowers, fruits and seeds of Boldo (Peumus boldus Mol.)]. Ciencia e Investigación Agraria 4: 49-60. [in Spanish].
::Online::Google Scholar::
(7)
Cabello A, Donoso C (2013). Peumus boldus (Molina) Johnston. Boldo, Folo. Familia: Monimiaceae [Peumus boldus (Molina) Johnston. Boldo, Folo. Family: Monimiaceae]. In: “Las Especies Arbóreas de los Bosques Templados de Chile y Argentina. Autoecología” (Donoso C ed). Marisa Cuneo Ediciones, Valdivia, Chile, pp. 510-515. [in Spanish].
::Google Scholar::
(8)
CONAMA (2006). Estudio de la variabilidad climática en chile para el Siglo XXI. Informe Final Texto [Study of the climatic variability in Chile for the XXI Century. Final Report]. Departamento de Geofísica Facultad de Ciencias, Físicas y Matemáticas, Universidad de Chile, Santiago, Chile, pp. 71. [in Spanish].
::Google Scholar::
(9)
Del Valle JM, Rogalinski T, Zetzl C, Brunner G (2005). Extraction of boldo (Peumus boldus M.) leaves with supercritical CO2 and hot pressurized water. Food Research International 38: 203-213.
::CrossRef::Google Scholar::
(10)
Doll U, Aedo D, Lopez P (2005). Caracterización morfológica de tres procedencias de boldo (Peumus boldus) en una plantación joven de 6 años [Morphological characterization of three provenances of Boldo (Peumus boldus) in a 6-year-old plantation]. Bosque 26: 45-54. [in Spanish].
::Online::Google Scholar::
(11)
Grime JP, Mason G, Curtis AV, Rodman J, Band SR, Mowforth MAG, Neal AM, Shaw S (1981). A comparative study of germination characteristics in a local flora. Journal of Ecology 69: 1017-1059.
::CrossRef::Google Scholar::
(12)
Hill J, Stellmes M, Udelhoven T, Röder A, Sommer S (2008). Mediterranean desertification and land degradation: mapping related land use change syndromes based on satellite observations. Global and Planetary Change 64: 146-157.
::CrossRef::Google Scholar::
(13)
Hoffmann AJ, Alliende MC (1984). Interactions in the patterns of vegetative growth and reproduction in woody dioecious plants. Oecologia 61: 109-114.
::CrossRef::Google Scholar::
(14)
IPCC (2007). Climate change 2007: the physical science basis. Contribution of Working Group I to the fourth Assessment Report of the Inter-governmental Panel on Climate Change (Solomon S, Qin D, Manning M, Chen Z, Marquis M, Averyt KB, Tignor M, Miller HL eds). Cambridge University Press, New York, USA, pp. 996.
::Google Scholar::
(15)
ISTA (2006). International rules for seed testing (2006 edn). International Seed Testing Association - ISTA, Bassersdorf, Switzerland.
::Online::Google Scholar::
(16)
Kadioglu A, Terzi R (2007). A dehydration avoidance mechanism: leaf rolling. The Botanical Review 73: 290-302.
::CrossRef::Google Scholar::
(17)
Lenssen JPM, Van Kleunen M, Fischer M, De Kroon H (2004). Local adaptation of the clonal plant Ranunculus reptans to flooding along a small-scale gradient. Journal of Ecology 92: 696-706.
::CrossRef::Google Scholar::
(18)
Lortie CJ, Aarssen LW (1996). The specialization hypothesis for phenotypic plasticity in plants. International Journal of Plant Sciences 157: 484-487.
::CrossRef::Google Scholar::
(19)
Lumaret R, Mir C, Michaud H, Raynal V (2002). Phylogeographical variation of chloroplast DNA in holm oak (Quercus ilex L.). Molecular Ecology 11: 2327-2336.
::CrossRef::Google Scholar::
(20)
Mendoza I, Zamora R, Castro J (2009). A seeding experiment for testing tree-community recruitment under variable environments: implications for forest regeneration and conservation in Mediterranean habitats. Biological Conservation 142: 1491-1499.
::CrossRef::Google Scholar::
(21)
Meyer SE, Allen PS (1999). Ecological genetics of seed germination regulation in Bromus tectorum L. I. Phenotypic variance among and within populations. Oecologia 120: 27-34.
::CrossRef::Google Scholar::
(22)
Meyer SE, Kitchen SG, Carlson SL (1995). Seed germination timing patterns in intermountain Penstemon (Scrophulariaceae). American Journal of Botany 82: 377-389.
::CrossRef::Google Scholar::
(23)
Moreira F, Viedma O, Arianoutsou M, Curt T, Koutsias N, Rigolot E, Barbati A, Corona P, Vaz P, Xanthopoulos G, Mouillot F, Bilgili E (2011). Landscape-wildfire interactions in southern Europe: implications for landscape management. Journal of Environmental Management 92: 2389-2402.
::CrossRef::Google Scholar::
(24)
Muñoz M (1986). Cultivo de embriones y ensayo de germinación en boldo (Peumus boldus Mol.) [Embryo culture and germination essay in Boldo (Peumus boldus Mol.)]. Undergraduate thesis, Facultad de Ciencias Agrarias y Forestales, Universidad de Chile, Santiago, Chile, pp. 88. [in Spanish].
::Google Scholar::
(25)
Nishitani S, Masuzawa T (1996). Germination characteristics of two species of Polygonum in relation to their altitudinal distribution on Mt. Fuji, Japan. Arctic and Alpine Research 28: 104-110.
::CrossRef::Google Scholar::
(26)
O’Toole JC, Cruz RT (1979). Leaf rolling and transpiration. Plant Science Letters 16: 111-114.
::CrossRef::Google Scholar::
(27)
Pausas J, Llovet J, Rodrigo A, Vallejo R (2008). Are wildfires a disaster in the Mediterranean basin? A review. International Journal of Wildland Fire 17: 713-723.
::CrossRef::Google Scholar::
(28)
Roach DA, Wulff RD (1987). Maternal effects in plants. Annual Review of Ecology and Systematics 18: 209-235.
::CrossRef::Google Scholar::
(29)
Schulz JJ, Cayuela L, Echeverria C, Salas J, Benayas JMR (2010). Monitoring land cover change of the dryland forest landscape of Central Chile (1975-2008). Applied Geography 30: 436-447.
::CrossRef::Google Scholar::
(30)
Tripathi RS, Khan ML (1990). Effects of seed weight and microsite chraracteristics on germination and seedling fitness in two species of Quercus in a subtropical wet hill forest. Oikos 57: 289-296.
::Google Scholar::
(31)
Van Der Vegte FW (1978). Population differentiation and germination ecology in Stellaria media (L.) Vill. Oecologia 37 (2): 231-245.
::CrossRef::Google Scholar::
(32)
Vander Mijnsbrugge K, Bischoff A, Smith B (2010). A question of origin: where and how to collect seed for ecological restoration. Basic and Applied Ecology 11 (4): 300-311.
::CrossRef::Google Scholar::
(33)
Vogel H, Razmilic I, Doll U (1997). Essential oil and alkaloid contents of different populations in boldo (Peumus boldus Mol.). Ciencia e Investigación Agraria 24:1-6.
::Google Scholar::

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Magni CR, Espinoza SE, Garrido EF, Santelices RE, Cabrera AM (2016).
Differential adaptations in nursery seedlings from diverse Chilean provenances of Peumus boldus Mol.
iForest - Biogeosciences and Forestry 9: 409-413. - doi: 10.3832/ifor1893-008
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Paper ID# ifor1893-008
Title Differential adaptations in nursery seedlings from diverse Chilean provenances of Peumus boldus Mol.
Authors Magni CR, Espinoza SE, Garrido EF, Santelices RE, Cabrera AM
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