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A new noteworthy tool for improving forest
            biodiversity in reforested areas: the
         effectiveness of Miyawaki method in
       Mediterranean reforestation programs

                                               Federico Vessella

Department of Forest and Environment (D.A.F.), Università degli Studi della Tuscia, via S. Camillo de Lellis, 01100 Viterbo, Italy.


                                        Thessaloniki, March 22-24 2011
Miyawaki method
Applications and results
Miyawaki has been succesfully
applied in several Far East
countries, (e.g. Japan, China,
Malaysia, Thailand) and in South
America (Brazil and Chile).
Experimented      in    thousands
hectares, Miyawaki always allows
climax vegetation achievement.
Advantages compared to traditional methods




   After planting, any human care is not required, such
    as weeding or thinning;
   Undergrowth with late-successional species is
    immediately on site;
   Forest stand becomes quickly part of natural
    ecosystem
Method limits


   Accurate botanical and ecological analysis of sites
    is need, thus specialists are required for
    environmental investigations;

   Manpower need is high;

   Planting costs are quite expensive
Method restrictions – adaptability to Mediterranean climate
                                                  Some Mediterranean climate patterns

Sites where Miyawaki successed
Method involvement in Mediterranean environment


   Miyawaki method was never tested in Mediterranean
environment, mainly because is unknown

   Difficulties   are    linked     to     Mediterranean   climate
characterized by summer aridity, in several cases by winter
cold, and by thin soils

   Nevertheless, it could be interesting for the Mediterranean
context,     because     in   this   area   complete   environment
restoration takes long time

   Maintenance planting cost are reduced to the first year
Our experiment
Site location



                                                                   A




   Sardinia - Italy


                                               B




                           I.G.M. 1:25000 of       Aerial view (2006)
                          experimental field




Municipality of Pattada
Project description
                   Site A               Site B
Surface            4500 m2 c.a.         1000 m2 c.a.
Altitude a.s.l.    760 m                885 m
Slope              4°                   0°
Aspect             North-East           Flat
Geology            Granite              Granite
Soil               Lithic and Dystric   Lithic and Dystric
                    Xerorthents          Xerorthents
Plant number       1759                 1828
Density            4000 plants/ha       18000 plants/ha
N. of species      32                   17
Climatic features
   of the area
Site A:
List of spontaneous species
Site B:
List of spontaneous species
Potential vegetation (climax)

Mixed forest with Quercus ilex, Q. suber,
   Q. pubescens and Ilex aquifolium
Our changements to the original method

   No new soil addition (20 cm labour of first pre-
    existent soil)
   Use of some local pioneer species (Pinus
    pinaster) together with late successional ones
    to improve plant community resilience
   Test of different types of mulching
Planting scheme
List of species used for
      the plantation
Planting scheme
Mulching Map
Straw mulching
Saw mill residuals
Planting results after 11 years
Quantitative analysis
 Site A
 Planted species: 28                          Qualitatively                                    37%



                                                                                   Survived
                                              all survived
 Native species in not worked strips: 4
                                                                      63%




                                        Test Area closed to Site A
                                        in a 30 years old                     10 species (31,25%)
                                        reforested zone

                                        Test Area in a coeval
Traditional reforestation technique
                                        reforested zone lightly               7 species (21,88%)
                                        far from Site A

                                        Test Area in a gradoni
                                        reforested site                       7 species (21,88%)


                                                                      Quantitative analysis
  Site B                                                                              19.69%


  Total planted species: 23           Qualitatively                              Survived
  Forest species: 17                  7 forest sp. survived


                                                                     80.31%
Plant survived     Plant survived


Site A            Site B
pioneers
                         Specific survival percentage
Acer monspessulanum                                     M.S.
       Ilex aquifolium
       Laurus nobilis                                   L.S.
      Celtis australis

      Castanea sativa

        Cedrus libani

    Sorbus torminalis
       Arbutus unedo

    Spartium junceum

         Quercus ilex

   Ligustrum vulgaris
     Malus domestica

    Myrtus communis

       Fraxinus ornus
     Pyrus communis

       Pinus pinaster

Rosmarinus officinalis

  Quercus pubescens

       Quercus suber

       Taxus baccata
      Viburnum tinus
Site A
Site A
Quercus suber




         Site A
Natural
regeneration of
Pinus pinaster




    Site A
Site B
Site B
Quercus suber




                Site B
Pyrus pyraster




                 Site B
Juniperus oxycedrus




                Site B
Comparison with traditional methods of reforestation


   More rapid development of trees, in particular of
    pioneer species
   Greater richness in species, also climatic
    species (Quercus ilex, Q. suber, Q. pubescens
    and Ilex aquifolium are present)
30 years reforested area outside SITE A
20 years
Max height = 4 m
                   gradoni
                   reforestation
Improvement opportunities and conclusions

      Improve soil characteristics adding compost or local
       vegetal material
      Reducing pioneers species without excluding at all
      Test for the optimal plant density
      Use high quality seedlings
      Reduce planting costs


Pre-Forest cultivation approach should help solving those
problems and Miyawaki method should be applied as interesting
tool for forest restoration programmes in Mediterranean countries
• introduce a new technology build on pre-cultivation (in mini-plugs) of
                                      forest regeneration materials (FRM) in a cost efficient and
                                      environmental friendly production unit not affected by outdoor climate;
                                    • integrate these technologies into a functional system for large scale
                                      production of pre-cultivated forest regeneration materials adapted to
                                      transplanting and further growth at forest nurseries all over Europe




The mobile pre-cultivation unit,
adapted to a standardised
container size for transportation
on a lorry, train or boat to any
optional forest nursery.

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Miyawaki greece

  • 1. A new noteworthy tool for improving forest biodiversity in reforested areas: the effectiveness of Miyawaki method in Mediterranean reforestation programs Federico Vessella Department of Forest and Environment (D.A.F.), Università degli Studi della Tuscia, via S. Camillo de Lellis, 01100 Viterbo, Italy. Thessaloniki, March 22-24 2011
  • 3.
  • 4.
  • 5.
  • 6.
  • 7.
  • 8. Applications and results Miyawaki has been succesfully applied in several Far East countries, (e.g. Japan, China, Malaysia, Thailand) and in South America (Brazil and Chile). Experimented in thousands hectares, Miyawaki always allows climax vegetation achievement.
  • 9. Advantages compared to traditional methods  After planting, any human care is not required, such as weeding or thinning;  Undergrowth with late-successional species is immediately on site;  Forest stand becomes quickly part of natural ecosystem
  • 10. Method limits  Accurate botanical and ecological analysis of sites is need, thus specialists are required for environmental investigations;  Manpower need is high;  Planting costs are quite expensive
  • 11. Method restrictions – adaptability to Mediterranean climate Some Mediterranean climate patterns Sites where Miyawaki successed
  • 12. Method involvement in Mediterranean environment  Miyawaki method was never tested in Mediterranean environment, mainly because is unknown  Difficulties are linked to Mediterranean climate characterized by summer aridity, in several cases by winter cold, and by thin soils  Nevertheless, it could be interesting for the Mediterranean context, because in this area complete environment restoration takes long time  Maintenance planting cost are reduced to the first year
  • 14. Site location A Sardinia - Italy B I.G.M. 1:25000 of Aerial view (2006) experimental field Municipality of Pattada
  • 15. Project description Site A Site B Surface 4500 m2 c.a. 1000 m2 c.a. Altitude a.s.l. 760 m 885 m Slope 4° 0° Aspect North-East Flat Geology Granite Granite Soil Lithic and Dystric Lithic and Dystric Xerorthents Xerorthents Plant number 1759 1828 Density 4000 plants/ha 18000 plants/ha N. of species 32 17
  • 16. Climatic features of the area
  • 17. Site A: List of spontaneous species
  • 18. Site B: List of spontaneous species
  • 19. Potential vegetation (climax) Mixed forest with Quercus ilex, Q. suber, Q. pubescens and Ilex aquifolium
  • 20. Our changements to the original method  No new soil addition (20 cm labour of first pre- existent soil)  Use of some local pioneer species (Pinus pinaster) together with late successional ones to improve plant community resilience  Test of different types of mulching
  • 22. List of species used for the plantation
  • 27.
  • 29. Quantitative analysis Site A Planted species: 28 Qualitatively 37% Survived all survived Native species in not worked strips: 4 63% Test Area closed to Site A in a 30 years old 10 species (31,25%) reforested zone Test Area in a coeval Traditional reforestation technique reforested zone lightly 7 species (21,88%) far from Site A Test Area in a gradoni reforested site 7 species (21,88%) Quantitative analysis Site B 19.69% Total planted species: 23 Qualitatively Survived Forest species: 17 7 forest sp. survived 80.31%
  • 30. Plant survived Plant survived Site A Site B
  • 31. pioneers Specific survival percentage Acer monspessulanum M.S. Ilex aquifolium Laurus nobilis L.S. Celtis australis Castanea sativa Cedrus libani Sorbus torminalis Arbutus unedo Spartium junceum Quercus ilex Ligustrum vulgaris Malus domestica Myrtus communis Fraxinus ornus Pyrus communis Pinus pinaster Rosmarinus officinalis Quercus pubescens Quercus suber Taxus baccata Viburnum tinus
  • 34. Quercus suber Site A
  • 38. Quercus suber Site B
  • 39. Pyrus pyraster Site B
  • 41. Comparison with traditional methods of reforestation  More rapid development of trees, in particular of pioneer species  Greater richness in species, also climatic species (Quercus ilex, Q. suber, Q. pubescens and Ilex aquifolium are present)
  • 42. 30 years reforested area outside SITE A
  • 43. 20 years Max height = 4 m gradoni reforestation
  • 44. Improvement opportunities and conclusions  Improve soil characteristics adding compost or local vegetal material  Reducing pioneers species without excluding at all  Test for the optimal plant density  Use high quality seedlings  Reduce planting costs Pre-Forest cultivation approach should help solving those problems and Miyawaki method should be applied as interesting tool for forest restoration programmes in Mediterranean countries
  • 45. • introduce a new technology build on pre-cultivation (in mini-plugs) of forest regeneration materials (FRM) in a cost efficient and environmental friendly production unit not affected by outdoor climate; • integrate these technologies into a functional system for large scale production of pre-cultivated forest regeneration materials adapted to transplanting and further growth at forest nurseries all over Europe The mobile pre-cultivation unit, adapted to a standardised container size for transportation on a lorry, train or boat to any optional forest nursery.