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Environmental factors affect the spatial arrangement of survival and damage of outplanted Nothofagus dombeyi seedlings in the Chilean Andes/Factores ambientales afectan el arreglo espacial de la sobrevida y dano en plantas transplantadas de Nothofagus dombeyi en los Andes Chilenos/Fatores ambientais afetam o arranjo espacial da sobrevida e dano em plantas transplantadas de Nothofagus dombeyi nos Andes Chilenos.

SUMMARY

Mortality patterns were analyzed in a one-year old Nothofagus dombeyi plantation at mid-elevation in the Chilean Andes. Ripley's univariate function was used to detect spatial patterns of mortality and damage (as reflected in crown dieback) of seedlings by assigning them into four categories: no crown damage, 1/3 of the crown damaged, 2/3 of the crown damaged and dead. Through correspondence analysis, variables (plant attributes, topography, weed competition, neighboring vegetation and fertilization) that could affect mortality were tested. At the end of the first growing season 67% of the seedlings survived, and by the end of the following dormant season only 37% were alive. Mortality patterns were random for seedlings with 1/3 of the crown damaged, and clustered for all other categories. Environmental variables with the greatest influence on mortality were increasing distance to a neighboring 10m tall plantation, absence of tall vegetation cover and convex micro-topography. Results suggest that large temperature oscillations with events of freezing temperatures (defined as the reported lethal temperature for 50% of its leaves) during the growing season, and severe frost during the dormant season, were the main causes of mortality and damage. The convenience of providing seedlings with some shelter when outplanted, or with an appropriate cold-acclimation treatment to resist low freezing temperatures when outplanted in open fields in harsh cold regions of the south-central Andes is discussed.

KEYWORDS / Abiotic Stress / Border Effects / Freezing Temperatures / Ripley's Function / Regeneration / Vegetation Cover /

RESUMEN

Se analizaron los patrones de mortandad en una plantacion de Nothofagus dombeyi de un ano de edad a altura media en los Andes chilenos. La funcion univariada de Ripley fue utilizada para detectar patrones espaciales de mortalidad y dano de las plantas asumiendo cuatro categorias: sin dano en la copa, 1/3 de copa danada, 2/3 de copa danada y muerte. Las variables (atributos de la planta, topografia, competencia de realeza, vegetacion vecina y fertilizacion) fueron probadas por analisis de correspondencia. Al final de la primera estacion de crecimiento 67% de las plantas sobrevivieron y al final del siguiente periodo solo 37% sobrevivian. Los patrones de mortalidad fueron aleatorios en plantas con 1/3 de la copa danada, y agrupados en las otras tres categorias. Las variables ambientales con la mayor influencia en mortalidad fueron: distancia a una plantacion vecina de 10m de altura, ausencia de cobertura vegetal alta y microtopografia convexa. Los resultados sugieren que grandes variaciones de temperatura con eventos de congelamiento (definido como la temperatura reportada como letal para 50% de las hojas) en la estacion de crecimiento y congelamiento severo en la estacion de latencia fueron las causas principales de mortalidad y dano. Se discute la conveniencia de proteger las plantaciones transplantadas o de una aclimatacion apropiada para resistir las bajas temperaturas en plantas transplantadas a campo abierto en zonas frias de los Andes chilenos sur-centrales.

RESUMO

Analisaram-se os padroes de mortalidade em uma plantacao de Nothofagus dombeyi de um ano de idade a altura media nos Andes chilenos. A funcao univariada de Ripley foi utilizada para detectar padroes espaciais de mortalidade e dano das plantas assumindo quatro categorias: sem dano na coroa, 1/3 de coroa danificada, 2/3 de coroa danificada e morte. As variaveis (atributos da planta, topografia, competencia de maleza, vegetacao vizinha e fertilizacao) foram provadas por analise de correspondencia. No final da primeira estacao de crescimento 67% das plantas sobreviveram e no final do seguinte periodo latente somente 37% sobreviviam. Os padroes de mortalidade foram aleatorios em plantas com 1/3 da coroa danificada, e agrupados nas outras tres categorias. As variaveis ambientais com a maior influencia em mortalidade foram: distancia a uma plantacao vizinha de 10m de altura, ausencia de cobertura vegetal alta e microtopografia convexa. Os resultados sugerem que grandes variacoes de temperatura com momentos de congelamento (definido como a temperatura relatada como letal para 50% das folhas) na estacao de crescimento e, congelamento severo na estacao de latencia, foram as causas principais de mortalidade e dano. Discutese a conveniencia de proteger as plantacoes transplantadas ou de uma aclimatacao apropriada para resistir as baixas temperaturas em plantas transplantadas a campo aberto em zonas frias dos Andes chilenos sul-centrais.

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Plantations with native tree species in Chile are scarce, despite the fact that the Forest Service has promoted them for more than a decade. The three most widely planted trees are exotic (Pinus radiata [D. Don], Eucalyptus globulus [Labill], and E. nitens [Deane & Maiden]). Among native trees, several Nothofagus species seem to be the most promising. According to the last agricultural census there are ~4000ha of Nothofagus plantations in Chile, a rather small area that can be the result of a lack of high-quality seedlings, a poor knowledge about the plantation silviculture for these species, and/or a general belief that native species have low productivity. The technology to produce high-quality bare root and containerized seedlings is available (Donoso et al., 1999; 2006; Bustos et al., 2008), and there is increasing knowledge about the silvicultural treatments to be applied to Nothofagus plantations. It was shown that low elevation Nothofagus plantations can achieve high productivity rates (Donoso et al., 1993, 1999, 2005, 2006). Unfortunately, transference and adaptation of this knowledge has been poor, and there are many questions about the fate of the plantations established at mid- and high elevations, where only few results have been reported (Donoso et al., 1993). Mean growth rates of 16-29[m.sup.3] x [ha.sup.-1] per year have been reported for some Nothofagus dombeyi ([Mirb.] (Oerst)) plantations (Donoso et al., 1993, 1999, 2006), although these have been established without special site preparation treatments (tillage, herbicide, fertilization).

N. dombeyi is a pioneer tree species that colonizes sites that have been affected by large-scale disturbances such as fire, landslides or wind (Donoso, 1993; Veblen et al., 1995; Donoso et al., 2006). In general, the species has been reported as highly resistant to abiotic stress such as low temperatures, high light intensity, and drought (Alberdi, 1995; Reyes-Diaz et al., 2005; Piper et al., 2007), which allow it to grow in areas exposed to full sunlight, where periods of summer drought and extreme temperatures can occur (Alberdi et al., 1985; Weinberger, 1973). The good adaptation of N. dombeyi growing in natural conditions that are marginal for most other native tree species (500-1000masl), allow to expect that plantations with this species and under these conditions should have good rates of growth and survival. However, the more severe climatic conditions at these elevations suggest that the behavior of these plantations can differ from that seen at lower elevations, especially in the direction of having lower growth and survival rates when established in the open field. To test this, a plantation was established in a site considered as marginal (>600masl in the Chilean Andes) for forest production of rapid growth species. It was established in a south-aspect open field where herbicide was applied in the plantation tines and plants were fertilized with different doses. After one growing season this plantation suffered high mortality rates. One aim of the present work was to study the spatial pattern of mortality and crown damage that took place in the plantation; another aim was to explore the causes for low survival and crown damage by studying the effects of local (low) and surrounding (tall) vegetation, micro- and macro-topography, fertilization and seedling morphology on seedling mortality.

[FIGURE 1 OMITTED]

Study site

The study was carried out in the Valdivian Andes of Chile (39[degrees]35'S, 72[degrees]05'W) at 620masl in San Pablo de Tregua, an experimental forest belonging to the Universidad Austral of Chile. The plantation was established on a south facing slope of an abandoned open field with a 10m tall Nothofagus nervosa plantation and shrubby vegetation on its northern side. The region has a coastal oceanic climate according to Krppen and a Mediterranean influence, with short and dry summers (Dec-Mar) and humid winters (JunSept). The annual precipitation, mostly rainfall, ranges between 4000 and 5000mm (Neira, 2005) and is associated with westerly and northerly winds (Schlatter et al., 1995). Mean annual temperature is ll[degrees]C, that of the coldest month (August) is 5[degrees]C and that of the warmest one (February) is 16[degrees]C. The number of annual frosts is 30-50, concentrated from August through September. A Datalogger DIVER (Eijelkamp[R]) was installed to record temperatures in the perimeter of the plantation at 1,5m above ground. Data points were recorded every hour from 10/1/2005 to 01/13/2007.

[FIGURE 2 OMITTED]

Soils at the plantation site are derived from modern volcanic ashes (Acrudoxic hapludand), well structured, with a Pumice horizon over basaltic-andesitic rocks (CIREN, 1999). The texture is medium through the entire profile, rich in thin sand on the surface and clay in the lower profile. In terms of fertility the most important characteristics are a high water retention capacity (>250mm in lm depth), good infiltrarion, high organic matter content and total N (0.97 [+ or -] 0.07%), and a suitable C/N relation of 11.6 [+ or -] 0.3. However, these soils are poor in bases and P (3.5 [+ or -] 0.6mg x [kg.sup.-1]; Donoso et al., 2007). The main limitations are rapid superficial moisture loss, high P retention, high A1 levels (49 [+ or -] 6%) due to the presence of alophan, and wind erosion (Schlatter et al., 1995).

Methods

Characteristics of the seedlings and the plantation

The Nothofagus dombeyi ([Mirb.] (Oerst)) seedlings were grown in 130[cm.sup.3] polyethylene containers using composted Pinus radiata bark as the substratum, and were fertilized with a slow-release (18-6-12) fertilizer (Osmocote[R]; 5kg per [m.sup.-3]). The seed source was local, from San Pablo de Tregua. The containers were sown during the first week of September in a greenhouse and moved outdoors, under a 50% mesh, at the end of November, when N-based fertilization was initiated, and finally hardened during the last month of the growing season (February) by taking the mesh away and eliminating fertilization with N in favor of K. The seedlings selected for the study were 35-45cm tall with a 3-4mm root collar diameter when outplanted at the end of October of the following year (see Bustos et al. (2008) for further seedling characteristics). A spacing of ~2x2.5m was used throughout the 1ha plantation. Weeds were controlled by applying 41 of glyphosfate and 3.51 of Simazine per ha on 1m wide strips immediately after planting.

Sampling

One growing season after planting, and past the first winter and the first half of the second year spring, a 2000[m.sup.2] (40x50m) area was sampled. In this area height, root collar diameter and the X and Y coordinates of each one of 410 seedlings were recorded. Between outplanting and sampling, freezing temperatures occurred several rimes; just for a few hours a small number of days during the first growing season and even for entire days numerous rimes during the dormant season (Figure 1).

At the end of the first growing season (May) 67% of the seedlings were atice; they had reached an average collar diameter of 7.3cm and an average height of 75cm. At the beginning of the following spring (October) only 37% of the outplanted seedlings had survived; that is, 55% of the seedlings that were alive at the end of the first growing season (Figure 2). Therefore, it was decided to divide seedlings into four categories related to their survival and damage status: undamaged (the whole crown undamaged), slightly damaged (1/3 of its crown dead), seriously damaged (2/3 of its crown damaged) and dead.

Statistical analyses

The X and Y coordinates of each seedling in the sampled area were incorporated into the SpPack software (Perry, 2004) to use Ripley's K(t) function (Ripley, 1977) to represent the categories of seedling conditions. The interpretation was made according to L(d)-d against the d distance, which fits to the zero value. Therefore, the spatial pattern is grouped when L (d)-d is significantly (P<0.05) >0, and regular if L (d)-d is significantly <0 (Rozas and Camarero, 2005; Salas et al., 2006).

Each of the five factors that can have an effect on seedling conditions have different levels (Table I). The seedling variables (Rock et al., 2004) considered were crown form, height, and fertilization (high, medium and no fertilization, as reported in Donoso et al., 2007). The environmental variables were micro-topography (!m around the seedling), macro-topography (4m uphill and downhill from the seedling), weed cover (vegetation 1: <25% of the plant height; vegetation 2: 25-75% of the plant height; vegetation 3: >75% of the plant height). In addition, the type of vegetation (10m tall N. nervosa trees or 3m tall shrubs) in the north side of the plantation and the distance of individual plants to the edge were recorded. The five factors with their different levels were analyzed using correspondence analysis (CA) to represent spatial ordination (ter Braak, 1985). CA is a unimodal technique to organize series of categorical variables and non continuous data, allows detection of differences between two variables in a space of small dimensions and the interpretation of similarities and relations between categories. This allows the detection of dependences among variables (ter Braak, 1985; Jongman et al., 1995).

[FIGURE 3 OMITTED]

Results

Distribution of seedling damage

Seedlings with no crown damage, with 2/3 of the crown damaged and dead had a clustered distribution, except for the first 2-4m (Figure 3a, c, and d), as opposed to trees with 1/3 of the crown damaged, which showed a random distribution (Figure 3b).

Factors associated with seedling damage

The first three dimensions of the CA accumulated 53.9% of the overall variation. Dimension 1 represented 22.1% of the variation, and illustrates (Figure 4 and Table II) that plants with a poor crown form (highest values) are in the opposite side of fertilization and macro-topography (lower values), i.e. plants with a poor form were mainly those with least fertilization, in a rather flat macro-topography. Dimension 2 represented 18.8% of the variation and illustrates that plants with more crown damage are more strongly opposed to high values of macro-topography and of tall competing vegetation (Figure 4 and Table II), i,e, severely damaged plants were in flat macro-topography, and had low levels of surrounding tall competition, Also, the most damaged plants were those farther away from the neighboring N. nervosa plantation. Vegetation 1 and 2 and height had a low value in Dimensions 1 and 2. and thus they had no important effect on the variables of interest, i.e. crown, form and damage. Figure 4 also shows that seedlings of poorer crown form were close to the border of the shrubby vegetation rather than the neighboring N. nervosa plantation and seedlings with less crown damage were those closer to the plantation border. Also, seedlings with poor crown form were associated with low damage.

Discussion

Low temperatures affect N. dombeyi survival

In this study two-thirds of the original plantation was dead one year after being planted, when one growing and one dormant season had already gone by. This resulted in a final clustered distribution for most plants and spatial separation (repulsion) of dead and live plants. We suggest that the severe mortality was mainly caused by 1) the large temperature oscillations and some freezing events during the growing season that affected seedlings without a proper cold-acclimation period once outplanted, and 2) severe frosts during the dormant season that are likely to have affected plants that entered the dormant season with low vigor. We discard the possibility that mortality was due to poor seedling quality (except for the lack of cold acclimation) or improper seedling handling, since these type of seedlings (from the same nursery) have had high survival and growth rates in other areas, and this plantation was a highly supervised experiment. During the year of evaluation, daily temperature oscillations during summer were as high as 20[degrees]C, and 15[degrees]C during spring, while during the dormant season there were multiple frost events (Figure 1). The mortality was tempered in some parts of the plantation for several reasons, eventually causing the observed clustered distribution.

Seasonal changes highly influence cold resistance in many species (Oquist and Huner, 2003; Gonzalez-Rodriguez et al., 2005; Bannister, 2006). N. dombeyi is reported to be highly resistant to low temperatures, with a [LT.sub.50] (lethal temperature for 50% of its tissue) between -8 and -10.5[degrees]C during winter and between -1 and -3[degrees]C during summer (Alberdi et al., 1985; Alberdi, 1995). These values are lower than the usual [LT.sub.50] of tree species in the temperate regions of the southern hemisphere, which vary between -4.9 and -8.4[degrees]C (Read and Hope, 1989; Bannister, 2006) but higher than those for other Nothofagus species that distribute to higher latitudes than N. dombeyi in Chile (Alberdi, 1995). Figure 1 shows that freezing temperatures were recorded throughout the year. During the first spring and summer, after seedlings had been outplanted in October, there were few moments with temperatures <-3[degrees]C, the [LT.sub.50] for leaves from natural seedlings (Alberdi et al., 1985; Alberdi, 1995). These temperatures likely had an effect on the death of 1/3 of the plants registered immediately following the end of the first growing season. During the following fall and winter only in few occasions temperatures were found to be <-8[degrees]C, the LTso for winter leaves from natural seedlings (Alberdi et al., 1985; Alberdi, 1995). This suggests that seedlings used for the plantation had a higher [LT.sub.50]. The hardening treatment applied to the seedlings in the nursery was aimed to have more lignified seedlings, but that seemed not to be sufficient for seedlings to resist freezing conditions, since this was not a cold-acclimation treatment. Laboratory cold-acclimation treatments can be an option so as to be more successful in outplanting N. dombeyi seedlings under these conditions, allowing an increase of their frost resistance (Reyes-Diaz et al., 2005). For instance, Read and Hope (1989) were able to increase the frost resistance of N. cunninghammi (a species from temperate rainforests of Southern Australia) through artificial hardening from an [LT.sub.50] of -7.8[degrees]C in unhardened seedlings to -11.4[degrees]C in hardened seedlings. Inthe present study seedlings did not have the possibility to go through neither an efficient natural acclimation period nor an artificial cold-acclimation treatment. In addition, high growth rates exhibited by the seedlings in the nursery during early spring (Sept-Oct) could have caused a lower accumulation of soluble carbohydrates, reducing the resistance of seedlings to the frosts they had to withstand during late spring and summer (sensu Alberdi, 1995; Reyes-Diaz et al., 2005).

[FIGURE 4 OMITTED]

Positive effects of shelter and topography on survival of N. dombeyi seedlings

Protection from the vegetation or weed cover and a 10m tall N. nervosa plantation in the northern edge of the plantation were the variables that explained most part of the variation in plant survival. Also, the accompanying vegetation (Vegetation 3>2>1) and micro-topography explained an important portion of survival variation. Less damage was associated with a greater cover of relatively tall accompanying vegetation (similar or taller than N. dombeyi seedlings). These results demonstrate that accompanying vegetation, which is usually considered to be competitive (Albaugh et al., 2003; Nilsson and Orlander, 2003; Rubilar et al., 2008), in some cases can have beneficial effects on the plantation, like ameliorating extreme temperatures (Bashant et al., 2005; Donoso and Nyland, 2006). Seedlings showed less damage in concave surfaces. This kind of surface maintains a great amount of snow in the winter, preventing temperatures from falling below 0[degrees]C around the plant and on the soil surface (Donoso et ai., 2007). On the other side, fertilization caused a greater mortality probably for two reasons, toxicity in the case of the treatment with the highest doses (160g/pl; Donoso et al., 2007) and decline in the richness of mycorrhizal fungi due to the increase in plant nutrients (sensu Godoy et al., 1994). Therefore, outplanted seedlings could have reduced their resistance to drought stress (Fernandez, 2005) and their tolerance to stressful initial conditions. Macro-topography was also related to a greater mortality, because concave areas presented higher mortality, probably due to the slow flow of cold winds through the gentle slopes.

Management and restoration implications

The shade-intolerant character of N. dombeyi (Veblen, 1985; Donoso, 1993; Donoso et al., 2006; Donoso and Lusk, 2007) suggests that this species would tend to establish itself successfully in open fields lacking herbaceous or tree vegetation, like most pioneer fast-growing species (Bormann and Likens, 1979; Veblen and Alaback, 1996). This is the case at lower elevation, where survival rates are ~95% and growth rates are high (Donoso et al., 1999, 2005, 2007), even on low-fertility sites (unpublished data). However, this does not seem to happen under more severe environmental conditions such as flat areas, pockets of cold air, and south-facing slopes with poor wind drainage at mid and high elevations in the Andean range. The results of the present study, although limited to one plantation, may bring up a warning about what to expect when outplanting N. dombeyi seedlings under difficult environmental conditions, especially considering that the magnitude and frequency of temperature oscillations at 400-600masl in the Andes have increased during the last 15 years (Villalba et al., 2005), a condition that has caused massive mortality in N. dombeyi forests.

Landowners are becoming increasingly interested in planting Nothofagus trees because they are a promising option for management and restoration purposes, mainly at elevations >50masl. Knowledge of the critical factors to be taken into consideration for a successful reforestation program is important to decrease the current uncertainty about planting native species, one of the main reasons that explain the small area currently planted with Nothofagus trees in Chile. Establishing N. dombeyi plantations under environmental conditions similar to those in the present study has been more successful when conducted in the middle of vegetation strips (Alvarez and Lara, 2008), in gaps (unpublished data) or with lateral protection (like in this study). When planting in open fields like abandoned grasslands, we suggest maintaining the existing herbaceous or shrubby vegetation cover and, in the case of fertilizer application, to use moderate doses. It also seems necessary to provide seedlings with a cold-acclimation treatment and plant them at the end of the fali or during early winter, rather than in spring, as we did for this study. Professionals and landowners need to pay increasing attention on plant selection, date of planting, appropriate vegetation management and site preparation when embarked in plantation or restoration programs including Nothofagus trees at mid and high elevations in the south-central Andes of Chile.

ACKNOWLEDGMENTS

The authors thank Oscar Thiers, Victor Gerding, Carlos Oyarzun and Heriberto Figueroa (Universidad Austral of Chile), Jonathan Barichivich (graduate student at University of East Anglia, UK), Christian Salas (PhD candidate at Yale University, USA), and the support received from FONDEF-CONICYT (Grant D0411271).

Received: 08/27/2008. Modified: 01/17/2009. Accepted: 01/21/2009.

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Veblen TT, Kitzberger T, Burs BR, Rebertus AJ (1995) Perturbaciones y dinamica de regeneracion en bosques andinos del sur de Chile y Argentina. In Armesto JJ, Villagran C, Arroyo MK (Eds.) Ecologia de los Bosques Andinos del Sur de Chile y Argentina. Universitaria. Santiago, Chile. pp. 169-198.

Villalba R, Masiokas MH, Kitzberger T, Boninsegna JA (2005) Biogeographical consequences of recent Climate Change in the Southern Andes of Argentina. In Huber UM, Bugmann HKM, Reasoner MA (Eds.) Global Change and Mountain Regions: An Overview of Current Knowledge. Springer. New York, USA. pp. 145-157.

Weinberger P (1973) Bezeihungen zwischen mikroklimatischen faktoren und naturlicher Verjungung araukanopatgonischer Nothofagus-Arten. Flora 162: 157-179.

Daniel P. Soto. Forest Engineer, Universidad Austral de Chile (UACh), Chile. Researcher, UACh, Chile. Address: Institute of Silviculture, Universidad Austral de Chile, PO Box 567, Valdivia, Chile. e-mail: danielsoto@uach.cl

Pablo J. Donoso. Forest Engineer, UACh, Chile. Ph.D. in Forest Resources Management, State University of New York, USA. Professor, UACh, Chile. e-mail: pdonoso@uach.cl

Daniel Uteau. Forest Engineer, UACh, Chile. Researcher, Institute of Silviculture, UACh, Chile. e-mail: danieluteau@uach.cl

Alejandra Zuniga-Feest. Biologist and Ph.D. in Biological Sciences, Universidad de Concepcion, Chile. Professor, UACh, Chile. e-mail: alejandrazuniga@uach.cl
ABLE I
VARIABLES STUDIED AS POTENTIALLY ASSOCIATED WITH
TREE DAMAGE, AND NUMBER OF SEEDLINGS BY
CATEGORY AND VARIABLE

Group type         Variable        Category      Seedlings       %
                                                    Per         Per
                                                 category    category

Plant           Crown damage     1. no               84         20.4
                                 2. 1/3              21          5.1
                                 3. 2/3              48         11.7
                                 4. Dead            257         62.7

                Crown Form *     1. Monopodic       193         47.0
                                 2. Fork            127         30.9
                                 3. Multi-fork       74         18.1
                                 4. Dissolved        16          3.8

                Height class     1. 0-50             60         14.5
                (cm)             2. 51-89           278         67.5
                                 3. 90-125           73         17.8

Topography      Macro-           1. Flat            150         36.6
                topography       2. Convex           20          4.7
                                 3. Concave         240         58.6

                Macro-           l. Flat            204         49.7
                topography       2. Convex           73         17.8
                                 3. Concave         133         32.4

Weed            Vegetation       1. 0-5              12          2.9
competition     cover (%) 1 **   2. 5-25             15          3.5
                                 3. 25-50            56         13.6
                                 4. 50-75           148         36.0
                                 5, 75-100            l79       43.7

                Vegetation       1. 0-5             381         92.8
                cover {%) 2 **   2. 5-25             26          6.2
                                 3. 25-50             2          0.5
                                 4. 50-75             1          0.2

                Vegetation       1. 0-5             354         86.3
                cover (%) 3 **   2. 5-25             38          9.2
                                 3. 25-50            16          3.8
                                 4. 50-75             1          0.2
                                 5. 75-100            1          0.2

Neighbor        Type of Border   1. Plantation      317         77.3
vegetation                       2. Shrub            93         22.6

                Distance to      1. 0-12            174         34.8
                border {m)       2. 12-24            59         39.3
                                 3.24-36             39         25.8

Fertilization   Fertilization    1. 0               216         52.6
                (g per plant)    2. 110              67         16.3
                                 3. 160             127         30.9

For details see Methods. * From Rock et al. (2004).
** Categories from Braun-Blanquet (Knapp, 1984).

ABLE II
COORDINATES AND WEIGHTS OF THE STUDIED VARIABLES AND
VARIATION EXPLAINED BY THE CORRESPONDENCE ANALYSES

Group type            Variables            Weight   Dimension 1

Plant                 Crown damage         0.143      -0.166
                      Crown form           0.079       0.203
                      Height class         0.090       0.061

Topography            Macro-topography     0.081      -0.169
                      Micro-topography     0.099       0.232

Weed competition      Vegetation 1         0.184       0.038
                      Vegetation 2         0.048       0.111
                      Vegetation 3         0.053       0.201

Neighbor plantation   Type of border       0.054       0.170
                      Distance to border   0.085      -0.187

Fertilization         Fertilization        0.079      -0.296

Partial variation explained (%)                        22.07
Cumulative variation explained (%)                     22.07

Group type            Variables            Dimension 2   Dimension 3

Plant                 Crown damage            0.226        -0.034
                      Crown form              0.153         0.381
                      Height class           -0.094        -0.063

Topography            Macro-topography       -0.328         0.145
                      Micro-topography       -0.079        -0.173

Weed competition      Vegetation 1            0.008        -0.037
                      Vegetation 2           -0.028        -0.030
                      Vegetation 3           -0.169         0.012

Neighbor plantation   Type of border          0.136        -0.073
                      Distance to border      0.136        -0.052

Fertilization         Fertilization          -0.150         0.022

Partial variation explained (%)              18.79         13.09
Cumulative variation explained (%)           40.86         53.96
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Author:Soto, Daniel P.; Donoso, Pablo J.; Uteau, Daniel; Zuniga-Feest, Alejandra
Publication:Interciencia
Date:Feb 1, 2009
Words:5646
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