Research Article |
Corresponding author: Emilio Di Gristina ( emilio.digristina@unipa.it ) Corresponding author: Fortunato Cirlincione ( fortunato.cirlincione@unipa.it ) Academic editor: Lorenzo Peruzzi
© 2023 Raimondo Pardi, Giuseppe Venturella, Gianniantonio Domina, Emilio Di Gristina, Fortunato Cirlincione, Maria Letizia Gargano.
This is an open access article distributed under the terms of the Creative Commons Attribution License (CC BY 4.0), which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.
Citation:
Pardi R, Venturella G, Domina G, Di Gristina E, Cirlincione F, Gargano ML (2023) Forest nurseries and the National Recovery and Resilience Plan: the case of Sicily and Apulia (Italy). Italian Botanist 15: 49-63. https://doi.org/10.3897/italianbotanist.15.102133
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In Italy, the National Recovery and Resilience Plan (NRRP) foresees the planting of ca. 6.6 million trees to establish urban and peri-urban forests in 14 metropolitan cities. This ambitious project requires a significant number of native trees and shrubs, currently unavailable in Italian public and private nurseries. This survey analyzes the state of forest nurseries in two administrative regions of southern Italy, i.e. the “Filici” forest nursery (province of Agrigento, Sicily) and the Gargano Mountain Reclamation Consortium (province of Foggia, Apulia), to evaluate the adequacy of Sicilian and Apulian forest nurseries as potential sources of plant material to meet the requirements of the NRRP. The census carried out at the “Filici” nursery revealed the presence of more than 22,000 seedlings in cultivation, comprising 55 species, 26 genera, and 26 families. The autochthonous species are 43 (78.2%), while the exotic ones are 12 (21.8%). The Gargano Mountain Reclamation Consortium forest nursery has 190,876 seedlings in cultivation. A total of 80 species are present, belonging to 59 genera and 32 families. Of these, 68 (85%) are native species, 12 (15%) are exotic. An analysis of the plant material being cultivated in these forest nurseries shows the presence of a share of autochthonous species of interest for urban reforestation initiatives, however these are still insufficient in number.
Mediterranean area, native species, shrubs, southern Italy, trees
The Italian National Recovery and Resilience Plan (NRRP), Mission 2, Component 4, Investment 3.1 “Protection and Enhancement of Urban and Suburban Green Areas” (approved by the EU Council of Ministers on 12 January 2021) foresees a series of widescale actions. The main objectives of the Plan are: a) improve the quality of life and well-being of citizens through the protection of existing green areas and the construction of new ones; b) preserve and enhance biodiversity and ecological processes related to the full functionality of ecosystems; c) preserve and enhance biodiversity, in line with the European Biodiversity Strategy; d) contribute to the reduction of air pollution in metropolitan areas; e) reduce the number of infringement procedures, related to air quality; f) curb land consumption and restore useful soils; g) restore man-made landscapes and improve protected areas contiguous to metropolitan areas. Besides, Article 4 of Decree-Law no. 111 of October 14, 2019, transposed with amendments into Law no. 141 of December 12, 2019, defines modalities for the design of tree planting in metropolitan cities. Specifically, the Urban and Suburban Forestation Plan establishes a series of actions, focused in the 14 Italian metropolitan cities, to fight air pollution and protect biodiversity. The goal is to establish and expand urban and peri-urban forests by planting about 6.6 million trees. All the initiatives that envisage the planting of trees and new reforestation, especially in urban and peri-urban areas, represent an important driving force for the relaunch of forest nurseries.
Starting in the 1930s, the main task of Italian foresters was to reforest vast degraded areas to counteract the widespread hydrogeological instability of the territory. This situation has favored the proliferation of many forest nurseries, which provided their product free of charge, as required by almost all subsequent Forest Laws until the 1960s (
The awareness that forest nursery activity is essential for the success of any intervention aimed at environmental requalification has stimulated interest in better understanding the state of this activity in southern Italy, especially in Apulia and Sicily. Currently, in Apulia, there are 20 forest nurseries distributed in the provinces of Foggia (3), Lecce (9), Bari (5), Taranto (2), and Brindisi (1). Seven regional forest nurseries are managed by the Regional Agency for Irrigation and Forestry Activities (ARIF), while the remaining 13 are private. In 1989, the Sicilian regional government , established the “Regional Nursery Center”. Currently, the Center includes 16 forest nurseries distributed in the provinces of Agrigento (4), Palermo (3), Catania (2), Enna (2), and one in each of the remaining five provinces. Each one is specialized in a specific production. In our study, for Apulia, the forestry nursery of the Gargano Mountain Reclamation Consortium of San Marco in Lamis (province of Foggia) was examined, as it is the most representative nursery in the Regional Register, both for the abundance of forest species produced and marketed and for its internal organization. As regards the Sicilian territory, we examined the “Filici” forest nursery of Cammarata (province of Agrigento).With the establishment of the Regional Nursery Center, it has become the largest forest nursery in terms of plant production in order to meet the needs of the Sicilian Forestry Administration (
The purpose of our survey was to analyze the plants growing in the “Filici” nursery and in that of the Gargano Mountain Reclamation Consortium and to evaluate their adequacy as a potential source of plant material to meet the needs of the NRRP.
The “Filici” forest nursery falls in the municipality of Cammarata (CW-Sicily) in the province of Agrigento (Fig.
The farm area covers a total of 2 ha and has an average slope of 20%. Because of the slope, the entire productive area of the nursery (1.5 ha, about 75% of the entire area) is organized in plots arranged in steps with retaining walls lined with local limestone. Irrigation is done manually or through an automated sprinkler system. The nursery’s main objective is to produce plants that have genetic, morphological, and health characteristics that can offer excellent guarantees of rooting, development, and adaptability, thus ensuring success for plantings from scratch or intended for eventual reforestation on state lands. The “Filici” nursery uses seeds collected in forests located in the neighboring areas that are included in the list of “Sicilian Seed Woods” established by the Sicilian Region, which lists the forests from where seeds can be taken for forest propagation. There are two cultivation practices: with a root ball, the most widely used as the use of containers guarantees planting, and bare-root cultivation, which, however, is little used. Average annual nursery production in the past reached 400,000 seedlings; currently, due to the significant decrease in funds assigned to the nursery, it does not exceed 50,000 seedlings. The average annual mortality is estimated at 10%.
The forest nursery belonging to the Gargano Mountain Reclamation Consortium is located in San Marco in Lamis, (Borgo Celano, province of Foggia) (Fig.
The census was carried out between spring 2021 and autumn 2022, on the basis of in situ surveys and observations. For each taxon, the number of cultivated seedlings was counted (Table
Taxa growing at the forest nurseries “Filici” (Nursery 1) and “Gargano Mountain Reclamation Consortium” (Nursery 2).
Taxon | No. Phytocells Nursery 1 | No. Phytocells Nursery 2 | Family | Biological form | Chorology | Native/exotic |
---|---|---|---|---|---|---|
Abies cephalonica Loudon | 1000 | – | Pinaceae | P scap | E-Medit. | Exotic |
Abies nebrodensis (Lojac.) Mattei | 10 | – | Pinaceae | P scap | Endemic Sicily | Native |
Acer campestre L. | 100 | 5544 | Sapindaceae | P scap | Europ.-Caucas. | Native |
Acer negundo L. | 10 | – | Sapindaceae | P scap | N-America | Exotic |
Acer opalus L. | – | 1419 | Sapindaceae | P caesp | W-Europ. | Native |
Acer pseudoplatanus L. | – | 2023 | Sapindaceae | P scap | Europ.-Caucas. | Native |
Anagyris foetida L. | – | 50 | Fabaceae | P caesp | S-Medit. | Native |
Arbutus unedo L. | 500 | 200 | Ericaceae | P caesp | Stenomedit. | Native |
Buxus sempervirens L. | 20 | – | Buxaceae | P caesp | Submedit.-subatl. | Native |
Carpinus betulus L. | – | 971 | Betulaceae | P caesp | Europ.-Caucas. | Native |
Carpinus orientalis Mill. | – | 245 | Betulaceae | P caesp | Pontic | Native |
Castanea sativa Mill. | 20 | 4501 | Fagaceae | P scap | SE-Europ. (?) | Native |
Cedrus atlantica (Endl.) Carrière | 50 | – | Pinaceae | P scap | N-Africa | Exotic |
Celtis australis L. | 300 | 2617 | Cannabaceae | P scap | Eurimedit. | Native |
Ceratonia siliqua L. | 20 | 1872 | Fabaceae | P scap | S-Stenomedit. | Exotic |
Cercis siliquastrum L. | 100 | – | Fabaceae | P scap | S-Europ. | Native |
Cistus creticus L. | – | 938 | Cistaceae | NP | Centromedit. | Native |
Citrus × aurantium L. | 50 | 120 | Rutaceae | P scap | Asia trop. | Exotic |
Colutea arborescens L. | – | 50 | Fabaceae | P caesp | Euri-Medit. | Native |
Cornus sanguinea L. | 10 | 1266 | Cornaceae | P scap | Eurasiat. | Native |
Colutea arborescens L. | – | 50 | Fabaceae | P caesp | Euri-Medit. | Native |
Cornus mas L. | – | 805 | Cornaceae | P caesp | SE-Europ.-Pontic | Native |
Corylus avellana L. | 10 | 533 | Betulaceae | P caesp | Europ.-Caucas. | Native |
Crataegus monogyna Jacq. | 500 | 2844 | Rosaceae | P caesp | Paleotemp. | Native |
Cupressus sempervirens L. | 2000 | 50 | Cupressaceae | P scap | E.-Medit. | Exotic |
Cydonia oblonga Mill. | 15 | 90 | Rosaceae | P scap | SW-Asia | Native |
Diospyros kaki Thunb. | – | 110 | Ebenaceae | P scap | E-Asiat. | Exotic |
Emerus major subsp. emeroides (Boiss. & Spruner) Soldano & F.Conti | – | 1817 | Fabaceae | NP | E-Medit.-Pontic | Native |
Erica multiflora L. | – | 67 | Ericaceae | NP | Steno-Medit. | Native |
Euonymus europaeus L. | – | 2634 | Celastraceae | P caesp | Eurasiat. | Native |
Fagus sylvatica L. | – | 3779 | Fagaceae | P scap | Europ. | Native |
Ficus carica L. | – | 28 | Moraceae | P scap | Medit.-Turan. | Native |
Fraxinus ornus L. | 500 | 18292 | Oleaceae | P scap | S-Europ.-Sudsib. | Native |
Ilex aquifolium L. | 20 | 420 | Aquifoliaceae | P caesp | Eurimedit. | Native |
Juglans regia L. | 100 | 1390 | Juglandaceae | P scap | SW-Asia | Native |
Juniperus macrocarpa Sm. | – | 802 | Cupressaceae | P caesp | Euri-Medit. | Native |
Juniperus turbinata Guss. | – | 408 | Cupressaceae | P caesp | W-Medit. | Native |
Laurus nobilis L. | 200 | 2050 | Lauraceae | P caesp | Stenomedit. | Native |
Lavandula angustifolia Mill. | 20 | 2001 | Lamiaceae | NP | Stenomedit. | Native |
Ligustrum lucidum W.T.Aiton | 100 | – | Oleaceae | P caesp | Asia or. | Exotic |
Ligustrum vulgare L. | – | 1000 | Oleaceae | NP | Eurasiat. | Native |
Matthiola incana W.T.Aiton | 20 | – | Brassicaceae | Ch suffr | Stenomedit. | Native |
Mespilus germanica L. | – | 254 | Rosaceae | P caesp | Europ. | Native |
Morus alba L. | – | 1 | Moraceae | P caesp | E-Asiat. | Exotic |
Myrtus communis L. | 200 | 1701 | Myrtaceae | P caesp | Stenomedit. | Native |
Olea europea var. sylvestris (Mill.) Lehr | 2000 | 262 | Oleaceae | P caesp | Stenomedit. | Native |
Ostrya carpinifolia Scop. | – | 3113 | Betulaceae | P scap | S-Europ. | Native |
Paliurus spina-christi Mill. | – | 40 | Rhamnaceae | P caesp | SE-Europ. | Native |
Phillyrea angustifolia L. | – | 472 | Oleaceae | P caesp | Stenomedit. | Native |
Phillyrea latifolia L. | 10 | 2000 | Oleaceae | P caesp | Stenomedit. | Native |
Pinus halepensis Mill. | 100 | 4690 | Pinaceae | P scap | Stenomedit. | Native |
Pinus pinea L. | 500 | – | Pinaceae | P scap | Eurimedit. | Exotic |
Pistacia lentiscus L. | 10 | 1563 | Anacardiaceae | P caesp | S-Stenomedit | Native |
Pistacia terebinthus L. | 500 | 2008 | Anacardiaceae | P caesp | Eurimedit. | Native |
Pistacia vera L. | – | 1322 | Anacardiaceae | P scap | E-Medit. | Exotic |
Populus alba L. | – | 17 | Salicaceae | P scap | Paleotemp. | Native |
Populus nigra L. | 50 | – | Salicaceae | P scap | Paleotemp. | Native |
Populus tremula L. | – | 26 | Salicaceae | P scap | Eurosib. | Native |
Prunus armeniaca L. | – | 24 | Rosaceae | P scap | Asiat. | Exotic |
Prunus avium L. | 10 | – | Rosaceae | P scap | Pontic (? Europ.-Caucas.) | Native |
Prunus cerasus L. | – | 18 | Rosaceae | P scap | Pontica | Exotic |
Prunus domestica L. | – | 218 | Rosaceae | P caesp | SW-Asiat. | Exotic |
Prunus dulcis (Mill.) D.A.Webb. | 200 | – | Rosaceae | P caesp | S-Europ.-Sudsib. | Exotic |
Prunus mahaleb L. | – | 2271 | Rosaceae | P caesp | S-Europ. | Native |
Prunus spinosa L. | 500 | 1398 | Rosaceae | P caesp | Europ.-Caucas. | Native |
Prunus webbii (Spach) Vierh. | – | 630 | Rosaceae | P caesp | E-Medit. | Native |
Punica granatum L. | 20 | 1941 | Lythraceae | P scap | SW-Asia | Exotic |
Pyracantha coccinea M. Roem. | 30 | – | Rosaceae | P caesp | Stenomedit. | Native |
Pyrus spinosa Forssk. | 1000 | 3116 | Rosaceae | P caesp | Stenomedit. | Native |
Quercus coccifera L. | 200 | – | Fagaceae | P caesp | W-Stenomedit. | Native |
Quercus cerris L. | – | 25968 | Fagaceae | P scap | Eurimedit. | Native |
Quercus ilex L. | 5000 | 28654 | Fagaceae | P scap | Stenomedit. | Native |
Quercus pubescens Willd. | 5000 | 17780 | Fagaceae | P scap | Europ.-Subpontic | Native |
Quercus suber L. | 100 | – | Fagaceae | P scap | W-Eurimedit. | Native |
Rhamnus alaternus L. | 200 | 320 | Rhamnaceae | P caesp | Stenomedit. | Native |
Rhamnus saxatilis Jacq. | – | 52 | Rhamnaceae | P caesp | SE-Europ. | Native |
Ribes uva-crispa L. | – | 76 | Grossulariaceae | NP | Eurasiat. | Native |
Robinia pseudoacacia L. | 100 | – | Fabaceae | P scap | N-America | Exotic |
Rosa canina L. | 50 | 402 | Rosaceae | NP | Paleotemp. | Native |
Rosa sempervirens L. | 50 | – | Rosaceae | NP | W.-Medit.-Mont. | Native |
Ruscus aculeatus L. | – | 85 | Asparagaceae | Ch frut (G rhiz) | Eurimedit. | Native |
Salix alba L. | – | 6611 | Salicaceae | P scap | Paleotemp. | Native |
Salix babylonica L. | 15 | – | Salicaceae | P scap | Subtrop.-Asiat. | Exotic |
Salix × fragilis L. | – | 117 | Salicaceae | P caesp | Eurisiber. | Exotic |
Salvia officinalis L. | – | 200 | Lamiaceae | Ch suffr | Stenomedit. | Native |
Salvia rosmarinus Spenn. | 20 | 1540 | Lamiaceae | NP | Steno-Medit. | Native |
Sambucus nigra L. | – | 1080 | Viburnaceae | P caesp | Europ-Caucas. | Native |
Smilax aspera L. | 50 | 130 | Smilacaceae | NP (G rhiz) | Paleosubtrop. | Native |
Sorbus aria (L.) Crantz | 500 | 17 | Rosaceae | P caesp | Paleotemp. | Native |
Sorbus domestica L. | 200 | 114 | Rosaceae | P scap | Eurimedit. | Native |
Sorbus torminalis (L.) Crantz | – | 442 | Rosaceae | P caesp | Paleotemp. | Native |
Spartium junceum L. | 30 | 13031 | Fabaceae | P caesp | Eurimedit. | Native |
Stachys major (L.) Bartolucci & Peruzzi | – | 30 | Lamiaceae | Ch frut | Stenomedit. | Native |
Tamarix africana Poir. | – | 2000 | Tamaricaceae | P scap | W-Medit. | Native |
Tamarix gallica L. | 10 | – | Tamaricaceae | P caesp | W-Stenomedit. | Native |
Teucrium fruticans L. | – | 1026 | Lamiaceae | NP | Stenomedit. | Native |
Thymus vulgaris L. | 20 | – | Lamiaceae | Ch frut | Stenomedit. | Native |
Tilia cordata Mill. | 10 | – | Malvaceae | P scap | Europ.-Caucas. | Native |
Tilia platyphyllos Scop. | – | 161 | Malvaceae | P caesp | Europ.-Caucas. | Native |
Ulmus minor Mill. | – | 26 | Ulmaceae | P caesp | Europ.-Caucas. | Native |
Viburnum tinus L. | – | 2905 | Viburnaceae | P caesp | Stenomedit. | Native |
Ziziphus jujuba Mill. | – | 88 | Rhamnaceae | P caesp | E-Asiat. | Exotic |
The census carried out at the “Filici” nursery revealed the presence of 22,360 seedlings in cultivation (Table
The Gargano Mountain Reclamation Consortium nursery has 190,876 seedlings in cultivation (Table
In both nurseries, native species clearly dominate over exotic ones. Most of the latter are not invasive and, indeed, have a long list of traditional uses of ethnobotanical interest (Citrus × aurantium, Diospyros kaki, Morus alba, Punica granatum, Ziziphus jujuba, etc.). However, alongside these taxa, there are others, such as Acer negundo, Ligustrum lucidum, and Robinia pseudoacacia capable of becoming invasive if planted in natural areas. It would be advisable to stop the production of these three species.
The age of the plants produced in the two forest nurseries range from 1 to 5 years old and, overall, the phytosanitary status of the plants is good.
A few decades after the first plantings, forest nursery production began to have difficulties in maintaining native forest biodiversity. The most important reason for these failures is the use of allochthonous genotypes of unproven adaptability (
These activities require the use of plant material adapted to the microclimatic and soil conditions of individual localities. This also helps to preserve biodiversity, enhance taxonomic entities and ecotypes of high genetic value, safeguard endangered species, and avoid genetic pollution. In this regard, forest nurseries play an important role as they should meet this requirement by supplying seedlings produced from seed of native origin.
Despite the awareness of the importance of forest nurseries, in recent years in Italy, there has been a progressive disinterest and abandonment of this activity as part of an ill-advised forestry policy undertaken by regional governments. Urban reforestation, within the actions of the Italian Recovery Fund, is the bet for the future of Italian cities and for the quality of life of the next generations. It will be necessary to overcome the difficulties in finding areas for reforestation in urban areas (lack of political sensitivity, constraints, etc.).
The number of native plants useful for reforestation kept in nursery stocks is still quite limited, partly due to the drastic reduction of regional nurseries and qualified personnel. It is, therefore, necessary to know the current stock of existing nurseries and implement the number of native species for more effective actions in the territory.
The analysis of the two forest nurseries in Sicily and Apulia showed that the available species meet the reforestation plan requirements. In fact, the propagated plant material comes entirely from local autochthonous populations, thus guaranteeing the availability of genotypes that are adapted to the environment in which they will be used and able to cope with the predicted climate change (
This study was carried out under Action IV.6 “Research Contracts on GREEN Themes – Ministerial Decree 1062/2021 and Ministerial Decree August 10, 2021, No. 1061, PON “Research and Innovation” Resources 2014-2020.