iForest - Biogeosciences and Forestry

iForest - Biogeosciences and Forestry

Using field and nursery treatments to establish Quercus suber seedlings in Mediterranean degraded shrubland

iForest - Biogeosciences and Forestry, Volume 13, Issue 2, Pages 114-123 (2020)
doi: https://doi.org/10.3832/ifor3095-013
Published: Mar 26, 2020 - Copyright © 2020 SISEF

Research Articles

Cork oak (Quercus suber L.) is a suitable species for restoring Mediterranean ecosystems due to its capacity to resprout after wildfires and its economic importance for the use of cork. Several studies have focused on improving the seedling quality and abiotic conditions at the outplanting site to favour the field performance of Q. suber, however, most studies have been conducted by independently testing treatments. The aim of this study was to assess the combined effect of three techniques that focused on reforestation success with Q. suber in Mediterranean degraded shrubland: (i) a nursery technique to improve root system development, such as the use of deep containers to develop a longer tap root, combined with two field techniques such as (ii) the use of tree shelters to diminish solar radiation stress, and (iii) shrubland treatments to reduce competition for soil water and nutrients. For this purpose, 1-year-old Q. suber seedlings were grown in two containers types: a shallow container (CCS-18) and a deep container (CCL-30). Seedlings were established in a degraded shrubland at three experimental sites in the Calderona mountain range of Castellón, Spain. A factorial design was combined based on container type (CCS-18 and CCL-30), shrubland management (undisturbed shrubland and cleared shrubland in strips) and tree shelters (vegetable fibre tree shelters and no tree shelters). After 2 years of monitoring, the outplanting results indicated that using: (i) a deep container produced a longer taproot, but did not favour better survival or better field performance of seedlings; (ii) tree shelters improved the microweather conditions around seedlings, particularly by reducing excess incoming solar radiation; (iii) cleared shrubland strips reduced competition for soil water by favouring a higher water potential, better maximum photochemical PSII efficiency and higher survival rates for the seedlings established into cleared sites. The results indicate that the cleared shrubland treatment effects overlap the effects of using deep containers and tree shelters. This, in turn, reveals that shrubland clearing is the most suitable technique for favouring the introduction of a resprouter species like Q. suber into ecosystems characterized by predominantly degraded shrublands.

Deep Container, Tree Shelters, Cleared Shrubland, Ecological Restoration


Different biotic and abiotic factors constrain the success of reforestation projects in dry and semiarid degraded areas ([47], [30]). Stress conditions due to both intense solar radiation, and water and nutrient deficits in introduced seedlings, is one of the main factors to affect the success of forest restoration projects in dry ecosystems ([8]). Previous studies have analyzed several treatments aimed at reducing these stressful conditions during site outplanting. Some of these treatments have focused on improving root system structure and growth to increase water uptake and to avoid water stress ([7], [24]). Other studies have reduced incoming solar radiation stress ([3]) or competition with co-existing vegetation by shrubland management techniques ([36], [2]). However, in most studied cases, the different reforestation techniques followed to improve seedling introduction into degraded shrubland have been analyzed individually and have not been combined.

In Spain, species of the Quercus genus are very important for the forest restoration of Mediterranean ecosystems. Cork oak (Quercus suber L.) is a very interesting typical resprouter Mediterranean species for restoring fire-prone ecosystems ([20]). Like other Quercus species, cork oak develops a long taproot during early development in the nursery ([6], [34]). Therefore, using shallow containers and low volumes physically limits its root system growth ([13], [38]). Moreover, field conditions impose other limitations for seedlings to be established in the countryside. Tree shelters have been used to improve microclimatic conditions and protect against herbivory in outplanted seedlings ([38], [11], [23]). Photosynthetic photon flux density, air temperature and relative humidity are climate variables that are affected by the use of tree shelters ([12]). Previous studies have shown that tree shelters help improving seedling survival and growth ([46], [1]). Tree shelter design (height, ventilation and the materials used) determines the protective effect on seedlings ([3], [38], [14]). For this reason, the use of tree shelters built according to an unusual design of vegetable fibres was considered herein.

Degraded ecosystems are characterized by shrubland vegetation dominated by seeder species that well tolerate drought conditions and have a high degree of competitive characteristics ([32]). Under these conditions, shrubland management techniques to reduce the competitiveness of standing vegetation have been recommended in some studies ([36]), but the selected shrubland management technique (i.e., type, extension and width of clearing strips) must be carefully designed ([22]). The use of cleared shrubland strips in parallel with contour curves is a recommended technique for preventing soil erosion and facilitating the outplanting performance of seedlings. This technique is applied to strips no wider than a few metres. It is a selective treatment that helps to conserve juvenile or adult individuals of important species in cleared strips, thereby favouring wildlife feeding and sheltering ([41], [26]).

In this context, we hypothesize that the combined effects of several nursery and field techniques, all of which focus on reducing abiotic stress, would better improve the field performance of seedlings in restoration projects compared to each technique individually applied. To test this hypothesis, the objective of this study was to assess the combined effects of using deep containers for nursery culture, tree shelters and cleared shrubland strips with Quercus suber seedlings in early outplanting stages. For this purpose, the following effect were studied: (i) deep containers during nursery culture on seedling morphological characteristics; (ii) vegetable fibre tree shelters to improve the microclimatic conditions around seedlings and diminish solar radiation stress; (iii) cleared shrublands strips to reduce competition for soil water between the introduced seedlings and the co-existing vegetation in restoration areas.

  Material and Methods 

Study area and experimental sites

The experimental sites are located in the Calderona mountain range in Castellón, Spain, where altitude ranges between 576 and 727 m a.s.l., with predominantly west-facing slopes between 13-40%. Sandy soils have developed from rock acidic sandstone. The climate is dry subhumid thermo-Mediterranean, with an average annual rainfall of 485 mm and an average temperature of 15.2 °C (Segorbe HS weather station, data 1961-1990 - [35]). The dominant vegetation is degraded shrubland composed mainly of Cistus monspeliensis L., Cistus salviifolius L., and Ulex parviflorus Pourr. At the less degraded sites, individuals of Quercus coccifera L., Rhamnus alaternus L., Pistacia lentiscus L., and Arbutus unedo L. are also present. On the tree layer, some isolated individuals of Pinus halepensis M., and Quercus suber L., can be found. The herbaceous layer is dominated by Brachypodium retusum (Pers.) Beauv. In this study area, the three experimental sites were Puntal de la Bella, El Sapo and Tristán, which presented different geographical localizations, altitudes and west-facing slopes (Tab. 1).

Tab. 1 - Geographical coordinates, altitude, slope and slope-facing of the experimental sites.

Variable Experimental sites
de la Bella
El Sapo Tristán
Latitude 39° 41′ N 39° 43′ N 39° 44′ N
Longitude 00° 23′ W 00° 27′ W 00° 28′ W
Altitude (m a.s.l.) 576 722 727
Slope (%) 13 40 20
Slope-facing 270° W 340° NW 210° SW

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Experiment design

In order to assess the combined effect of several techniques that focus on reducing abiotic stress in outplanting, a three-factor experimental design was implemented whose factors were: container type (CTf), shrubland management (Smf) and tree shelters (Tf).

Factor container type (CTf): a CCS-18 container (shallow container: 18 cm deep; volume of 353 cm3) and a CCL-30 container (deep container: 30 cm deep; volume of 589 cm3). Both employed container types were made of high-density polyethylene were cylindrically shaped and open-bottomed, and had a 5 cm diameter and a cultivation density of 318 seedlings m-2 (Fig. S1 in Supplementary material). The shallow container represented the container widely used for culture in nurseries of the genus Quercus and other Mediterranean species, while the deep container represented a technological innovation ([7]). Both containers were manufactured by CETAP-Antonio Matos Lda. (Forestry Containers Manufacturer Company, Espinho, Portugal) and the CCL-30 deep container is patented by this company (Ref. no. 9976, Boletim Propiedade Industrial no. 11-2004, Portugal).

Factor tree shelters (Tf): vegetable fibre tree shelters (VFT). A panel of vegetable fibre was composed of wicker branches (Salix purpurea), 0.50 m wide and 1.00 m long. Wicker branches (length: 1.00 m; diameter: 0.3-0.8 cm) were woven with a wire at four height levels (20, 40, 60 and 80 cm) to guarantee a stable structure. To build tree shelters, the vegetable fibre panel was placed in an upright position, whose ends were joined to form a cylinder (20 cm diameter, 1.00 m high). A bamboo cane (height: 1.00 m, diameter: ~1.2 cm) was needed to close the panel and form a cylinder to provide vertical support. In the field, tree shelters were buried in soil at a depth of 10-15 cm, along with three other bamboo canes, to confer tree shelters more stability and to avoid the flag effect (Fig. S2, Supplementary material). The opposite experimental treatment was to not use tree shelters (NVFT).

Factor shrubland management (SMf): cleared shrubland strips (CSs), 3 m wide, were made running perpendicularly to the hillside’s main slope. CSs were alternated with undisturbed shrubland strips (USs), 5 m wide (Fig. S3, Supplementary material). The clearing of strips at the experimental sites was done with a STIHL FS410 C-E® brush cutter (Andreas Stihl Ltd., Stihl House, Surrey, UK) using bush knives and grinding. At each site, four 3-metre wide strips of CSs and four 5-metre strips of USs were prepared. In USs, a 1-metre diameter circle was cleared to plant Q. suber seedlings.

In each strip (USs and CSs), the other experimental treatments were performed according to the three-factor design. Twelve planting holes (60 × 60 × 60 cm) were made every 3 m on the centre line of each strip. Holes were made with the help of a pneumatic hammer. No soil was removed from holes to avoid inverting soil horizons. Ninety-six one-year old Quercus suber L. seedlings (12 seedlings × 2 container types × 2 shrubland management treatments × 2 tree shelters type as treatment) were planted at each experimental site in January 2011. Thus at each site, there were 48 seedlings per level of container type factor, 24 seedlings per level of shrubland management factor and 24 seedlings per level of tree shelters factor. Twelve seedlings were used to analyze the interactions between factors.

Plant material and nursery culture

Cork oak (Quercus suber L.) seedlings were grown for a 1-year period in two container types: CCS-18 and CCL-30. Cultivation was carried out at the Centro de Investigación y Experimentación Forestal (CIEF) in Quart de Poblet (Valencia, Spain - 39° 28′ N, 00° 31′ W; 70 m a.s.l), with a mean annual rainfall of 462 mm and a mean annual temperature of 16.9 °C ([35]). The cork oak acorns from the Calderona mountain range were supplied by the Regional Government Forest Service (Banc de Llavors, Quart de Poblet) and were seeded in January 2010. The substrate was a mixture of limed peat (60%) and coconut peat (40%). A slow-release fertilizer (Plantacote plus®, N-P-K: 14-8-14; approaches longevity of 12 months at a mean temperature of 21 °C) was mixed with the substrate at a substrate dose of 1 g L-1. The watering regime was weekly (2 days week-1), with 15 mm applied in autumn, winter and spring, and 25 mm in summer.

Seedling morphology and biomass

At the end of nursery culture after 12 months of cultivation, morphological characterization was carried out. Fifteen seedlings per treatment were randomly sampled, and stem height and basal diameter were measured. Seedlings were cut at the cotyledon insertion point and separated into four fractions: leaves, stem, fine roots (diameter < 2 mm) and taproot (diameter > 2 mm). The dry weight of each fraction was determined after oven drying at 65 °C for 48 h. Shoot dry weight (DWS), root dry weight (DWR), seedling dry weight (SMT) were calculated. Two morphological indices were also calculated: root/shoot ratio (DWR/DWS) and root weight ratio (DWR/ SMT).

Vegetable fibre tree shelters: inside and outside environmental conditions

In order to compare the environmental conditions inside and outside the vegetable fibre tree shelters (VFT), three climatic variables were monitored. In one set in the nursery, one H08-032-08 HOBO© sensor with a data-logger (Onset Computer Corporation, USA) was placed inside three VFT to measure air temperature (, °C) and relative humidity (RH, %). Photosynthetic photon flux density (PPFD, µmol m-2 s-1) was measured using a Ha-Li HOBO© sensor (Onset Computer Corporation, USA). Simultaneously under open site conditions, the same variables (Tª, RH and PPFD) were measured by similar sensors. Vapour pressure deficit (VPD, kPa) was determined from and HR. These measurements were taken in the nursery in August 2010 on 7 sunny days.

Rainfall, air temperature and relative humidity in the study area

The outplanting period lasted 2 years: 2011, the wetter year with an annual rainfall of 528.5 mm, a mean air temperature of 16.0 °C and 68.8% relative humidity (CEAMET data, the weather station in Alturas, Castellón). April (105.4 mm), March (101.2 mm) and November (85.7 mm) were the wettest months, while August (4 mm) was the driest month (Fig. S4, Supplementary material). In summer, accumulated rainfall came to 49.8 mm. There were 16 rainfall events, for which more than 5 mm were recorded (minimum: 7.9 mm and maximum: 11.7 mm). However, 2012 was a less rainy year (397.8 mm) given the 25% drop compared to the annual rainfall of 2011, and the 18% drop compared with the region’s average annual (485 mm). The average temperature was 16.1 °C, while relative humidity was 62.2%. February (0.2 mm), May (0.8 mm), December (2.5 mm), August (4.2 mm) and July (5.0 mm) were the least rainy months, when rainfall did not exceed 5 mm month-1. The wettest month was October (172.8 mm - Fig. S4, Supplementary material) due to extraordinary rainfall (84.5 mm). The summer of 2012 was very dry (14 mm). Although 10 rainy events were reported, none exceeded 4 mm. Consequently, there were 120 days (June 21 to September 20) with no significant rainfall (> 5 mm).

Seedling performance

Seedling survival and growth in stem height (Hs) and basal diameter (D) at the experimental sites were measured for 100% individuals in the experimental plots in January 2011 after plantation, and in June and November 2011 and 2012. The relative growth rate (RGR) was calculated by the differences in the average stem height (Hs) and basal diameter (D) of seedlings between the last measurement (t2) and the first measurement (t1) using RGR = [ln (Hs t2) - ln (Hs t1)] / (t2 - t1). To determine the effect of the experimental treatments on seedling water stress, soil moisture and several ecophysiology variables were measured during the first outplanting year (2011). One part of the measures was taken at the end of spring (June), and coincided with the high soil water content conditions (low water stress). The others were taken in summer (August) and coincided with the period with the lowest soil water content conditions (maximum water stress). Five seedlings per experimental treatment and site were randomly selected for this purpose. In each seedling, the following were measured: (1) water potential at midday (Ψmd, -MPa) using a Sholander pressure chamber (Soil Moisture 3005®, Soil moisture Equipment Corp., Santa Barbara, CA, USA); (2) leaf chlorophyll content (LCC, no units) with SPAD 502® (Spectrum Technology, Inc. Aurora, USA); (3) maximum quantum yield of Photosystem II (PSII; Fv/Fm under dark conditions) at predawn (Fv/Fmpd) and midday (Fv/Fmmd) by a fluorimeter PAM 2100® (Heinz Walz GmbH, Germany). Simultaneously, soil water content (SWC, %) at a 15- to 20-cm depth was measured in all the selected seedlings for ecophysiological measurements. For this purpose, an EC-5 probe and an instant reader ProCheck (both manufactured by Decagon Devices, Inc., USA) were used. The intention was to assess the effect of the experimental treatments shrubland management (CSs and USs) and tree shelters (VFT and NVFT) on the climate variables. Air temperature (, °C), relative humidity (RH, %) and photosynthetic photon flux density (PPFD, µmol m-2 s-1) were monitored in both CSs and USs, and in the seedlings with VFT and without vegetable fibre tree shelters (NVFT). For these measures, HOBO© sensors (Onset Computer Corporation, USA) model H08-032-08, with a datalogger for and HR, and Ha-Li for the PPFD measurements, were used.

Statistical analyses

The statistical analysis was carried out with the SPSS© statistical software, v. 21.0 (SPSS Inc. Chicago, Illinois, USA). The data on the seedling morphological characteristics at the end of the nursery culture were compared by a t-test, when the variables fulfilled theoretical assumptions. A non-parametric test (W by Wilcoxon) was run for the variables that did not match theoretical assumptions. To test the environmental conditions (Tª, RH, VPD, and PPFD) inside and outside the vegetable fibre tree shelters (VFT), an analysis of variance (one-way ANOVA, Tukey’s HSD post-hoc test) was carried out. The comparison of the Tª, RH, VPD, and PPFD data in the field was made by a two-factor ANOVA (Tukey’s HSD post-hoc test) using shrubland management (SMf) and tree shelters (Tf) as fixed factors. The data of relative growth ratio in stem height (Hs-RGR) and basal diameter (D-RGR), soil water content (SWC), water potential at midday (Ψmd), leaf chlorophyll content (LCC) and maximum quantum yield of Photosystem II (Fv/Fmpd and Fv/Fmmd) were compared by a GLM univariate (three-way ANOVA, Tukey’s HSD post-hoc test) at each site to analyze the effect of the experimental factors: container type (CTf), shrubland management (Smf), and tree shelters (Tf). Data were transformed whenever necessary to assure the assumptions of the ANOVA. The seedling survival data were analyzed by the Kaplan-Meier test (Log Rank-Mantel-Cox) to each experimental factor.


Morphological characteristics of seedlings

The analysis of the morphological characteristics of seedlings at the end of the culture period in the nursery indicated several differences between seedlings (Tab. 2). The seedlings grown in the deep CCL-30 container presented higher stem height (p = 0.009), longer taproot (p < 0.001), higher shoot dry weight (p = 0.016) and seedling dry weight (p = 0.019 - Tab. 2) values than the seedlings grown in CCS-18. Two tendencies were observed. The seedlings in CCL-30 tended to present higher taproot dry weight (root > 2 mm; p = 0.081) and root dry weight (p = 0.076 - Tab. 2) values than those grown in CCS-18. No significant differences between container types were found for the remaining analyzed morphological variables (p > 0.05 - Tab. 2).

Tab. 2 - Seedling morphological characteristics (mean ± standard error) at the end of the nursery culture. The results of t-test or Wilcoxon test for differences between container types are reported, along with their statistical significance. (DWS): Shoot dry weight; (DWR): root dry weight; (SMT): seedling dry weight; (***): p < 0.001; (**): p < 0.01; (*): p < 0.05; (ns): non-significant.

Variables Units Container types Test applied Significance
CCS-18 CCL-30
Stem height cm 51.26 ± 3.60 66.46 ± 4.91 W by Wilcoxon 170.0 **
Root collar diameter mm 6.70 ± 0.37 7.47 ± 0.48 W by Wilcoxon 194.0 ns
Taproot length cm 17.28 ± 0.14 29.01 ± 0.22 W by Wilcoxon 120.0 ***
Taproot dry weight (>2 mm) g 4.28 ± 0.51 5.95 ± 0.70 t-test -1.811 ns (1)
Shoot dry weight g 7.69 ± 0.94 12.66 ± 1.65 W by Wilcoxon 175.0 *
Root dry weight g 4.73 ± 0.53 6.51 ± 0.81 t-test -1.843 ns (1)
Seedling dry weight g 12.42 ± 1.37 19.18 ± 2.41 W by Wilcoxon 176.0 *
DWR/DWS ratio g g-1 0.64 ± 0.05 0.56 ± 0.04 W by Wilcoxon 202.0 ns
DWR/SMT ratio g g-1 0.38 ± 0.02 0.35 ± 0.02 t-test 1.290 ns

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Seedling survival and post-outplanting growth

The seedlings in the cleared shrubland strips (CSs), combined with vegetable fibre tree shelter (VFT) or without VFT (NVFT), and in container CCS-18 or CCL-30, maintained the highest survival values (Long Rank = 47.831; p < 0.001 - Fig. 1), with survival values ranging between 50-59%. A second analysis was run to consider only field treatments (i.e., shrubland management and use of tree shelters). It confirmed that CSs was the main treatment (Long Rank = 46.391; p < 0.001 - Fig. S5, Supplementary material) to affect seedling survival. This analysis demonstrated that using tree shelters did not affect seedling survival. The temporal seedling survival dynamics by the experimental factors at each site ratified that neither factor tree shelters (VFT vs. NVFT), nor factor container (CCS-18 vs. CCL-30) affected seedling survival. This analysis reported that, once again, the seedlings grown in CSs maintained the highest survival values (p < 0.01 - Fig. 2) at the three experimental sites. The seedlings grown in VFT only reflected a higher survival tendency (p = 0.053) at the Puntal de la Bella site. The factor container had no effect on seedling survival (Fig. 2). The differences among years associated with rainfall regimes showed that 2012 was less rainy (397.8 mm) than 2011 (528.5 mm), but this did not affect the differences between treatments, and the seedlings in CSs maintained the highest survival values (Fig. 2).

Fig. 1 - Seedling survival by the combined effect of the three experimental treatments. (Css): cleared shrubland strips; (USs): undisturbed shrubland strips; (VFT): vegetable fibre tree shelters; (NVFT): without vegetable fibre tree shelters; (CCS-18): shallow container; (CCL-30): deep container.

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Fig. 2 - Seedling survival by the experimental factors at each site. The results are shown per experimental site: Puntal de la Bella (above), El Sapo (middle) and Tristán (below). Data at 6, 11, 18 and 23 months after planting (mean ± standard error). Kaplan Meier test results (Log Rank, p-value). Abbreviations: cleared shrubland strips (CSs); undisturbed shrubland strips (USs); vegetable fibre tree shelters (VFT); without vegetable fiber tree shelters (NVFT); shallow container (CCS-18); deep container (CCL-30).

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The growth response of seedlings to experimental treatments differed per site. The seedlings grown in CSs at Puntal de la Bella presented a higher D-RGR than those grown in USs (p < 0.001 - Tab. 3). In contrast, the seedlings grown in USs (El Sapo) gave higher Hs-RGR values than those grown in CSs (p < 0.01 - Tab. 3). Regarding D-RGR, a tendency (p<0.1) was observed. The seedlings with VFT (Puntal de la Bella) had higher Hs-RGR (p = 0.05) and lower D-RGR (p < 0.05) values than those grown without VFT (Tab. 3). The factor container had no effect on the RGR (Hs and D) of seedlings. At Tristán, no treatment affected the RGR of seedlings (p > 0.05 - Tab. 3). An interaction between SMf and Tf was observed at the El Sapo site in H_RGR. A posterior analysis (one-way ANOVA) indicated that the seedlings grown in CSs had higher Hs-RGR values than those grown in USs (F = 8.067; p = 0.006). Tf did not affect this interaction.

Tab. 3 - Relative growth ratio (RGR) in stem height (Hs) and root collar diameter (D) of outplanted seedlings. Results per experimental site of the GLM univariate, three-way ANOVA. Factors: shrubland management (SMf), tree shelters (Tf), and container type (CTf). Mean ± SE, effect of the main factors and interactions between factors (F value). (***): p < 0.001; (**): p < 0.01; (*): p < 0.05; (ns): non-significant.

Factors Levels/
F values
Puntal de la Bella El Sapo Tristán
Shrubland management
CSs 0.057 ± 0.001 0.013 ± 0.001 0.035 ± 0.001 0.110 ± 0.002 0.010 ± 0.002 0.010 ± 0.03
USs 0.073 ± 0.001 0.007 ± 0.001 0.085 ± 0.001 0.005 ± 0.003 0.007 ± 0.002 0.005 ± 0.001
F value 1.177 ns 13.486 *** 7.349 ** 3.591 (1) 0.732 ns 1.607 ns
Tree shelters
VFT 0.084 ± 0.001 0.008 ± 0.001 0.006 ± 0.001 0.006 ± 0.001 0.009 ± 0.002 0.007 ± 0.002
NVFT 0.046 ± 0.001 0.012 ± 0.001 0.003 ± 0.001 0.010 ± 0.004 0.006 ± 0.001 0.010 ± 0.003
F value 6.267 * 5.275 * 0.820 ns 1.727 ns 0.403 1.111 ns
Container type
CCS-18 0.072 ± 0.001 0.009 ± 0.002 0.007 ± 0.001 0.007 ± 0.002 0.008 ± 0.002 0.009 ± 0.002
CCL-30 0.059 ± 0.001 0.011 ± 0.001 0.005 ± 0.001 0.009 ± 0.002 0.009 ± 0.002 0.006 ± 0.002
F value 0.740 ns 0.797 ns 0.590 ns 0.116 ns 0.008 ns 0.265 ns
SMf × Tf 0.003 ns 1.024 ns 8.864 * 1.861 ns 0.258 ns 1.228 ns
SMf × CTf 0.345 ns 1.363 ns 0.265 0.108 ns 0.052 ns 0.050 ns
Tf × CTf 0.034 ns 0.000 ns 1.316 0.086 ns 0.021 ns 0.023 ns
SMf × Tf × CTf 1.112 ns 0.014 ns 0.629 2.083 ns 0.211 ns 0.254 ns

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Effects of shrubland management and tree shelters on seedlings’ microclimatic conditions in the field

The measurements taken in the nursery indicated that VFT brought about no change in the inside tree shelter (p > 0.05 - Tab. 4), but a significant decrease in RH (about 7%) and a significant drop in PPFD (about 59% of external sunlight) were observed. VPD significantly increased by 15% in relation to the external environmental conditions (Tab. 4).

Tab. 4 - Comparison in the nursery of the environmental conditions inside and outside the vegetable fibre tree shelters (VFT). Data of air temperature (Tª), relative humidity (RH) and photosynthetic photon flux density (PPFD). The t-test results (mean ± standard error). (***): p < 0.001; (ns): non-significant.

Variable Units Outside
T a °C 26.91 ± 0.10 27.05 ± 0.10 -1.050 ns
RH % 72.61 ± 0.42 67.88 ± 0.43 8.752 ***
VPD kPa 1.10 ± 0.02 1.32 ± 0.02 -7.634 ***
PPFD µmol m2 s-1 1.07 ± 0.02 0.44 ± 0.02 -59.697 ***

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At the experimental sites, shrubland management affected only the PPFD values. The seedlings grown in CSs had higher PPFD values (43% in June and 25% in August) than those grown in USs (p < 0.001 - Tab. 5). The use of tree shelters (VFT) significantly lowered the RH values (5.3% in June and 4.0% in August) and PPFD (54% in June and 31% in August - Tab. 5) in relation to the NVFT treatment. An interaction between SMf and Tf was observed. A later analysis indicated that the seedlings under treatments CSs+NVFT had higher PPFD values than those subject to the other treatments in both June and August (p < 0.001 - Tab. 5). In June, USs+VFT had the lowest PPFD values, while CSs+VFT and USs+NVFT gave intermediate results. No significant differences were observed between them. In August, no significant differences in the three treatments were noted (CSs+VFT, USs+VFT and Uss+NVFT - Tab. 5).

Tab. 5 - Effect of the experimental treatments’ shrubland management (SMf) and tree shelters (Tf) on climatic variables air temperature (), relative humidity (RH), vapour pressure deficit (VPD) and photosynthetic photon flux density (PPFD). Measurements taken in June 2011 (above) and August 2011 (below). Results of the GLM univariate (two-way ANOVA). Factors: shrubland management and tree shelters; F value, Tukey’s HSD post hoc test. (***): p < 0.001; (**): p < 0.01; (*): p < 0.05; (ns): non-significant.

Period Factors Param. Tª RH VPD PPFD
June 2011 Shrubland management (SMf) CSs 22.6 ± 0.2 69.8 ± 0.6 1.08 ± 0.03 523.1 ± 23.3 a
USs 22.5 ± 0.2 70.1 ± 0.6 1.04 ± 0.02 298.5 ± 16.7 b
F value 0.37 ns 1.64 ns 0.68 ns 61.35 ***
Tree shelters (Tf) VFT 22.4 ± 0.1 68.1 ± 0.6 b 1.08 ± 0.02 258.1 ± 15.3 b
NVFT 22.6 ± 0.2 71.9 ± 0.7 a 1.04 ± 0.03 563.6 ± 23.6 a
F value 0.92 ns 18.48 *** 0.92 ns 118.05 ***
SMf × Tf interactions CSs × VFT 22.3 ± 0.2 68.2 ± 0.9 1.07 ± 0.03 351.9 ± 25.8 b
CSs × NVFT 22.9 ± 0.2 71.4 ± 1.0 1.10 ± 0.04 694.4 ± 36.6 a
USs × VFT 22.5 ± 0.2 68.0 ± 0.8 1.09 ± 0.03 164.7 ± 15.0 c
USs × NVFT 22.4 ± 0.2 72.3 ± 0.9 0.99 ± 0.03 432.8 ± 28.0 b
F value 3.20 ns 0.52 ns 3.98 ns 64.21 ***
Aug 2011 Shrubland management (SMf) CSs 22.9 ± 0.2 77.4 ± 0.9 0.9 ± 0.04 646.1 ± 30.1 a
USs 22.3 ± 0.3 80.2 ± 1.0 0.9 ± 0.05 483.3 ± 28.9 b
F value 0.38 ns 0.24 ns 1.68 ns 15.25 ***
Tree shelters
VFT 22.2 ± 0.3 80.0 ± 1.1 a 0.87 ± 0.05 461.1 ± 26.2 b
NVFT 22.9 ± 0.2 77.6 ± 0.9 b 0.85 ± 0.04 668.3 ± 32.0 a
F value 0.92 ns 10.17 ** 0.92 ns 25.12 ***
SMf × Tf interactions CSs × VFT 22.3 ± 0.4 80.5 ± 1.4 0.8 ± 0.07 472.5 ± 34.9 b
CSs × NVFT 23.5 ± 0.3 74.4 ± 1.0 0.9 ± 0.05 819.6 ± 44.7 a
USs × VFT 22.1 ± 0.2 79.6 ± 1.5 0.9 ± 0.08 449.7 ± 39.2 b
USs × NVFT 22.6 ± 0.4 80.8 ± 1.4 0.8 ± 0.06 517.0 ± 42.4 b
F value 3.20 ns 0.58 ns 3.98 ns 18.14 ***

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Soil water content and plant ecophysiology response

The analysis of the effect of experimental treatments (SMf, Tf and CTf) on soil water content (SWC), water potential at midday (Ψmd), leaf chlorophyll content (LCC), and maximum quantum yield of Photosystem II (Fv/Fm at predawn and midday) per experimental site gave different results across sites. When spring ended (June 2011), the shrubland management factor had less effect on the analyzed variables. Only at the Tristán site the seedlings grown in CSs had higher SWC that those in USs (p = 0.036 - Fig. 3C), which favoured less stress in the seedlings in CSs (Ψmd, p = 0.015 - Tab. S1, Supplementary material). A similar tendency (p<0.1 - Tab. S1) was observed at the El Sapo site for SWC regarding the shrubland management factor.

Fig. 3 - Measurements taken in spring of soil water content (SWC, %), water potential at midday (Ψmd, -MPa), leaf chlorophyll content (LCC, units SPAD), and maximum efficiency of photosystem PSII (Fv/Fm) at predawn per experimental site. Results of the GLM univariate, three-way ANOVA; factors: tree shelters (Tf), container type (CTf) and shrubland management (SMf). Mean ± standard error. Values followed by the same letter were not significantly different (p>0.05). Results shown by experimental sites: Puntal de la Bella (panels A, D and G), El Sapo (panels B, E and H) and Tristán (panels C, F and I).

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All the SWC values were higher than 17%, which did not directly limit seedlings’ physiological activity. Under these optimal soil moisture conditions, using vegetable fibre tree shelters or not, was the experimental factor with the stronger effect on water potential and Fv/Fm in seedlings. At the Puntal de la Bella site, the seedlings grown with VFT presented lower water stress than those in NVFT (p = 0.016 - Fig. 3D), expressed as higher Ψmd values. This result gave higher Fv/Fmpd values (p = 0.019 - Fig. 3G) in the seedlings with VFT. At the Tristán site, the seedlings with VFT gave higher Ψmd values (p = 0.014 - Fig. 3F) and higher Fv/ Fmpd; p = 0.018 - Fig. 3I) than those without VFT. A similar result for Fv/Fm pd (p = 0.003 - Fig. 3H) was observed at the El Sapo site.

The container type factor (CTf) had little effect on the analyzed variables. Only at the Puntal de la Bella did the seedlings cultivated in CCL30 have higher LCC values than those in CCS-18 (p = 0.041 - Tab. S1, Supplementary material). Two interactions between factors were observed: an interaction between SMf and CTf in LCC (p = 0.007 - Tab. S1) at Puntal de la Bella, and another interaction between factors Tf × CTf in Ψmd (p = 0.049 - Tab. S1) at Tristán. In both cases, the one-way ANOVA did not find any effects of these factors separately (p < 0.05). The results of the GLM univariate three-way ANOVA (factors: tree shelters, container type and shrubland management) are shown in Tab. S1 and Tab. S7 in the Supplementary material.

As expected, at mid-summer the SWC values notably lowered in relation to the June values. However, shrubland management was the factor that most affected the variables analyzed at all the sites. At Puntal de la Bella, the seedlings grown in CSs had higher SWC (p = 0.010 - Fig. 4A) and, consequently, presented less water stress (Ψmd, p = 0.001 - Fig. 4D) and higher Fv/ Fmmd values (p = 0.014 - Tab. S2, Supplementary material) than those in USs. Similar results were observed at El Sapo site in SWC (p<0.01 - Fig. 4B), Ψmd (p <0.001 - Fig. 4E), and Fv/Fm at predawn (p<0.01 - Fig. 4H). At the Tristán site, the seedlings grown in CSs had higher SWC (p < 0.001 - Fig. 4G), presented lower water stress (p < 0.001 - Fig. 4H) and higher Fv/Fm at both predawn (p < 0.001 - Fig. 4I) and midday (p < 0.001 - Tab. S2) than the seedlings in USs. At Puntal de la Bella, the seedlings grown in CCL-30 tended to show higher LCC (p = 0.071 - Tab. S2) than those grown in CCS-18. At El Sapo, an interaction between SMf and Tf was observed (p = 0.008 - Tab. S2). One-way ANOVA indicated that the seedlings grown in CSs+VFT had lower LCC values (p = 0.008) than for the other treatments, and no significant differences appeared among them. Another interaction between factors SMf × Tf was observed at Tristán (p = 0.022 - Tab. S2). The one-way ANOVA reported that the seedlings in USs had higher LCC (p = 0.043) than those in CSs.

Fig. 4 - Measurements taken in summer of soil water content (SWC, %), water potential at midday (Ψmd, -MPa), and maximum efficiency of photosystem PSII (Fv/Fm) at predawn and midday per experimental site. Results of the GLM univariate, three-way ANOVA; factors: tree shelters (Tf), container type (CTf) and shrubland management (SMf). Mean ± standard error. Values followed by the same letter are not significantly different (p>0.05). Results shown by the experimental site Puntal de la Bella (panels A, D and G), El Sapo (panels B, E and H) and Tristán (panels C, F and I).

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Effect of deep container on the morphological characteristics and seedling field performance

The effect of increasing container volume on seedling morphology development is widely documented ([37], [15]). However, the effect of increased container depth on seedling morphology may have different responses according to species characteristics ([6], [19], [9]). In this study, a deep container was used to produce seedlings with a longer taproot and a higher DWR/ DWS ratio to favour not only deep root system development, but also the rapid colonization of deeper soil layers before the first summer. At the end of the nursery culture, the seedlings cultivated in a deep container (CCL-30) presented a longer taproot and a tendency to have higher root dry weight values. They also showed longer stem height and higher shoot dry weight values. Consequently, no significant difference in the DWR/DWS ratio was observed (Tab. 2). Previous studies that employed containers with similar depths in Quercus coccifera, Q. ilex ([6]) and Q. suber ([7]) reported the production of seedlings with no significant differences in height and basal diameter compared to those grown in standard containers. This also allowed to produce seedlings destined to dry ecosystems with a higher DWR/DWS ratio in the seedlings grown in deep containers ([6], [7], [24]), which favours better root growth and greater resistance to Mediterranean water stress characteristics ([34], [9]). Other studies that have employed deep containers produced seed-lings with a longer taproot ([42]) and a higher stem height ([25]). However, effects on stem height, diameter and other morphological characteristics have not always been observed ([42], [9]).

Relative resources allocation to roots or leaves is considered a key factor in species strategies in relation to the use of water ([10]) and seedling survival in the field ([48]). In our study, we expected the seedlings grown in CCL-30 to develop a deeper root system over a shorter time period, which would promote higher survival rates, more growth (Hs-RGR, D-RGR) and a better physiological status than the seedlings grown in short CCS-18 containers. Our results did not meet the expected results because using deep containers did not lead to any differences in seedling survival (Fig. 2), growth (Tab. 3) or ecophysiological status (i.e., water potential and maximum quantum yield of Photosystem II - Tab. S1, Tab. S2 in Supplementary material) compared to the seedlings in CCS-18. This result may be due to the fact that both seedling types had a similar DWR/DWS ratio upon planting. Some previous studies have also reported no effects on water status in different container types ([29]).

Effect of vegetable fibre tree shelters on microclimatic conditions, seedling survival and growth

The design of tree shelters (height, ventilation and material used to build them) affects the micro-meteorological conditions inside tree shelters ([3], [38], [28]). Former studies have shown that using tree shelters in relation to external micro-meteorological conditions increases air temperature ([12], [33], [27]). In contrast, the VFT in our study did not increase temperature in relation to the external environmental conditions (Tab. 4). The used material and tree shelter design, i.e., built with small wicker shoots, allowed air to flow through lateral ribs, which favours good ventilation and avoids overheating. These results are consistent with those obtained by Bellot et al. ([3]), who used tree shelters made by a network of Stipa tenacissima L. leaves. Tree shelters also reduced the PPFD, which has been widely documented. For example, Bellot et al. ([3]) reported a reduction in PPFD of between 70% and 80%, Jiménez et al. ([18]) reported a 78% reduction, while Devine & Harrington ([12]) indicated one of 15-54% for radiation at an open site. In our study, VFT reduced PPFD by 59%.

Regarding survival, several studies have indicated that using tree shelters significantly increases seedling survival ([46], [11]). Although Valkonen ([44]) and Oliet et al. ([31]) observed only marginal improvement, other authors did not find this relation ([29]). The use of VFT in our study did not increase seedling survival, although a tendency (p = 0.053 - Fig. 2) was observed at Puntal de la Bella. Other studies have indicated that using tree shelters also favours an increased growth height ([11], [31], [27]). We report the effect of tree shelters (VFT) only at the Puntal de la Bella site, where Hs-RGR increased and D-RGR lowered (Tab. 3). For the ecophysiological seedling response, the effects of using VFT were observed only in spring, mainly on the Fv/Fmpd values at the three experimental sites. This last result agrees with Puértolas et al. ([38]) and Ceacero et al. ([5]), who reported that tree shelters improved the physiological characteristics of seedlings. However, other studies like that Pemán et al. ([33]) did not find any differences in Fv/Fm either with or without tree shelters.

Effect of shrubland management on seedling survival and field performance

Studies on the competitive or facilitative effect of some shrub species on seedling survival and field performance have been well-documented ([36], [39], [21], [40]). In summer, under lower SWC conditions, shrubland management (CSs treatment) was the factor that contributed more to diminish water stress, and gave better maximum quantum yields status of Photosystem II and seedling performance. Our study indicated that the seedlings grown in CSs had higher PPFD (Tab. 5) and also higher SWC (Tab. S1, Supplementary material), which favoured less water stress (expressed as higher Ψmd - Fig. 4), as well as higher Fv/Fm values at both predawn (Fig. 4) and midday (Tab. S1, Tab. S2, Supplementary material). This better water and physiological status probably led to higher seedling survival in CSs than for the seedlings grown in USs. Our results agree with those of Pérez-Devesa et al. ([36]), who reported that the seedlings planted in the middle line of CSs presented more soil moisture, their survival was 22% higher, they displayed better growth for height and root collar diameter, and had higher Fv/Fm values at both predawn and midday than those planted in USs (control treatment). However, differences in seedling survival have not always been observed with these treatments ([43], [17]). The seedlings in CSs presented a higher H-RGR at El Sapo, which is consistent with the results reported in Pistacia lentiscus by Valdecantos et al. ([43]) for Hs-RGR, and by Madrigal et al. ([22]) in Pinus halepensis growth in Guadalajara, Spain. Another effect of the CSs treatment was its higher PPFD (43% in June and 25% in August) than for the seedlings in USs. This result is consistent with Pérez-Devesa et al. ([36]), who obtained 30% higher PPFD, and also coincides with the increased chlorophyll content in Pinus reported by Cambrón-Sandoval et al. ([4]). It is very important to indicate that, for our experimental sites, high PPFD values at midday in summer can cause radiation stress for seedlings ([8], [16]). The year 2012 was relatively dry (Fig. S4, Supplementary material) as 120 days went by with no significant rainfall (< 5 mm). Thus, mortality of almost 100% was expected ([45]). However, the survival values of the seedlings planted in the CSs remained between 39% and 64%.

Overall, our study results indicated that in both spring and summer, at the Tristan site the CSs treatment (shrubland management factor) and the use of vegetable fibre tree shelters (tree shelters factor) had a stronger effect on the ecophysiological response of seedlings (Fig. 3, Fig. 4). Tristán was the only site that was SW slope-facing. This slope-facing type presents more solar exposure, higher water stress and more stress by PPDF. Under those most unfavourable conditions compared to the other sites, both the studied treatments contributed to a better seedling water status and to improved seedling performance. We speculate that a better response of both experimental treatments for sites with more unfavourable conditions could be expected.


According to our starting hypothesis, we expected the combined use of deep containers, vegetable fibre tree shelters and shrubland clearing to improve the field performance of Q. suber seedlings to a greater extent than when applying only one treatment. Our results did not ratify this hypothesis, but highlighted the fact that shrubland clearing was the main treatment to improve Q. suber performance. The effects of the cleared shrubland treatment overlapped the functional improvement of deep containers and tree shelters. Using deep containers and tree shelters had no significant effect on seedling survival, despite improvements in microclimatic conditions and differences in the root system developed by seedlings, as observed at the end of the nursery culture. Accordingly, we conclude that shrubland clearing is the most suitable technique to favour the introduction of Q. suber into ecosystems where shrublands dominate as a result of degraded forests.

  List of abbreviations 

The following abbreviations have been used throughout the text:

  • Ctf: Factor container type;
  • Tf: Factor tree shelters;
  • VFT: Vegetable fibre tree shelters;
  • NVFT: Without vegetable fibre tree shelters:
  • Smf: Factor shrubland management;
  • CSs: Cleared shrubland strips;
  • USs: Undisturbed shrubland strips;
  • : Air temperature;
  • RH: Relative humidity;
  • PPFD: Photosynthetic photon flux density;
  • VPD: Vapour pressure deficit;
  • Hs: Stem height;
  • D: Basal diameter;
  • Hs-RGR: Relative growth ratio in stem height;
  • D-RGR: Relative growth ratio in diameter;
  • DWS: Shoot dry weight;
  • DWR: Root dry weight;
  • SMT: Seedling dry weight;
  • DWR/DWS: Root/shoot ratio;
  • DWR/SMT: Root weight ratio;
  • Ψmd: Water potential at midday;
  • LCC: Leaf chlorophyll content;
  • Fv/Fmpd: Maximum quantum yield of Photosystem II at predawn;
  • Fv/Fmmd: Maximum quantum yield of Photosystem II at midday;
  • SWC: Soil water content.

  Author contributions 

JM-R, ECh, VC, JM and AV conceived and designed the experiment. JM-R, ECh, VC and JM performed the experiment and took field measurements. ECh and OF carried out the statistical analysis. JM-R, ECh, AV and OF contributed to the data analysis and data interpretation. JM-R, ECh and AV wrote and edited the manuscript.


This research was partially funded by the Centro para la Investigación y Experimentación Forestal (CIEF) and by the Fundación Centro de Estudios Ambientales del Mediterráneo (CEAM), both from Comunidad Valenciana (Spain). Author JCMR is grateful to the Instituto de Fomento al Talento Humano (IFTH) of the Government of Ecuador for the fellowship granted for postgraduate studies abroad. AV work was partially funded by Projects CGL-2011-30531-CO2-02 and CGL2015-69773-C2-2-P MINECO/FEDER from the Spanish Government. CEAM is supported by the Generalitat Valenciana and IMAGINA project (PROMETEU/2019/110 - Generalitat Valenciana).


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Authors’ Affiliation

Julio Muñoz-Rengifo
Department of Ecology, University of Alicante, Ap. 99 03080 Alicante (Spain)
Julio Muñoz-Rengifo
Departamento Ciencias de la Tierra, Universidad Estatal Amazónica, Km. 2.500 vía Napo, Puyo, Pastaza (Ecuador)
Esteban Chirino 0000-0002-3766-8595
Facultad de Ciencias Agropecuarias, Universidad Laica Eloy Alfaro de Manabí, Ciudadela Universitaria, Av. Circunvalación - Vía a San Mateo, 130802 Manta, Manabí (Ecuador)
Vicent Cerdán
Jesús Martínez
Centro para la Investigación y Experimentación Forestal (CIEF) de la Comunidad Valenciana, Av. Comarques del País Valencia, 46930 Quart de Poblet, Valencia (Spain)
Osvaldo Fosado
Instituto de Postgrado y Facultad de Ingeniería Agronómica, Universidad Técnica de Manabí, Av. José María Urbina y Che Guevara, Portoviejo, Manabí (Ecuador)
Alberto Vilagrosa 0000-0002-1432-1214
Fundación Centro de Estudios Ambientales del Mediterráneo (CEAM), Joint Research Unit University of Alicante - CEAM, Univ. Alicante, PO Box 99, 03080 Alicante (Spain)

Corresponding author

Esteban Chirino


Muñoz-Rengifo J, Chirino E, Cerdán V, Martínez J, Fosado O, Vilagrosa A (2020). Using field and nursery treatments to establish Quercus suber seedlings in Mediterranean degraded shrubland. iForest 13: 114-123. - doi: 10.3832/ifor3095-013

Academic Editor

Andrea Cutini

Paper history

Received: Mar 12, 2019
Accepted: Jan 23, 2020

First online: Mar 26, 2020
Publication Date: Apr 30, 2020
Publication Time: 2.10 months

© SISEF - The Italian Society of Silviculture and Forest Ecology 2020

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