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Review Plant Biotechnology, 16(1), 15-25 (1999) Creative Ecology: Restoration of Native Forests by Native Trees Akira Miyawaki


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Review Plant Biotechnology, 16(1), 15-25 (1999)
Creative Ecology: Restoration of Native Forests by Native Trees

Akira Miyawaki
Japanese Center for International Studies in Ecology (JISE) and Nagano Nature Conservation Research Institute (NA CRI), Japan (Correspondence; Fax, 81-45-651-7692; E-mail, miyawaki@jise.or.jp )
Ecological devastation is becoming a serious problem locally to globally, in proportion as people seek affluent living circumstances. Environmental devastation originated mainly from nature exploita­tion and construction of cities and industrial institutions with non-biological materials. Humans have ignored the rules of nature, biodiversity and coexistence.

One of the best measures we can take anywhere, in order to restore ecosystems indigenous to each region and to maintain global environments, including disaster prevention and CO2 absorption, is to restore native, multi-stratal forests following an ecological method.

I would like to refer to the experimental reforestation projects based on ecological studies and their results at about 550 locations throughout Japan and in Southeast Asia, South America, and China. We have proved that it is possible to restore quasi-natural multi-stratal forest ecosystems in 20 to 30 years if we take the ecological method.


1. Introduction

Until recently there were two kinds of tree planting. One involves monocultures of needle-leaved trees or fast­growing exotic species for the purpose of producing lum­ber. Of course producing lurnber is an important business, but monocultures of species unsuited to the habitat, soil and climate will need maintenance, such as weeding and cutting off lower branches, for at least 20 years. Those conifers and exotic species are generally shallow-rooted and highly vulnerable to strong winds, beavy rain and dry air [1]. What is worse, many pine woods throughout Japan are damaged by forest fires and so called pive worms, and cedars (Cryptomeria japonica) cause pollen allergies which many people are suffering from every spring [2].

The other kind of planting is tree planting for beau­tification. Some examples of this are Japanese gardens, miniature gardens, and bon-sai, dwarf trees, which can be said to be enhanced to the most typical Japanese culture. In the Edo era, the Emperor's domains were covered with fine nearly-natural forests, and common people who en­vied them began to imitate and enjoy nature in and around their own small houses. They were apparently beautiful but cost a lot for maintenance. Recently decorative tree­and flower-planting campaigns are popular in towns and cities [3]. We see many parks dotted with adult trees planted on the lawn. These plantings may be good to delight citizens' eyes. They not only need a lot of main­tenance, however, but also are insufficient to protect en­vironments and prevent disasters [2].

It will be a third planting method based on ecological studies that is indispensable to restore green environments, to prevent disasters, and to sustain local to global en­vironments [4-6]. Through thorough vegetation-ecological field surveys, we grasp the potential natural vegetation of the area. Following the results of field surveys, we carry out what we can, restoration of "native forests by native trees" [7]. This reforestation is one of the most solid



measures to restore environments of the earth locally to globally, with our gaze fixed upon the coming 21st and 22nd centuries [8, 9].

The green surface of a multi-stratal forest of the potential natural vegetation is about thirty times as large as that of a mono-stratal lawn, which needs periodical maintenance. As for absorbing and accumulating CO2 multi-stratal native forests have a much larger capacity than do lawns.

When colonies, villages and towns were constructed in Japan, our ancestors usually grew forests indigenous to the region around shrines or temples, which are called Chinju-no-mori. Our method of reforestation "Native forests by native trees" is based on this traditional Japanese "Chinju-no-mori" and ecology, a new synthetic science that integrates biocoenoses and environment [1, 2].

In the 1960s we started determination and sys­tematization of phytosociological community units through steady ecological field investigations throughout Japan. Then we made maps of the actual vegetation of Japan, which can be used as diagnoses of natural en­vironments, and middle-scaled (1/500,000) potential natural vegetation maps of Japan, which can be used as ecological scenerios for restoration of green environments [10].

We choose the main tree species and their companion species from the potential natural vegetation of the area, collect acorns of those species, grow the seedlings in pots until the root system fully develops, and mix and plant them closely together following the system of natural forests. This is the way we succeeded in restoring forests at about 550 locations in Japan.

We applied this ecological method to reforestation in Malaysia in Southeast Asia, in Brazil and Chile in South America, and in some parts of China, and found each of them successful. We believe that to continue carrying out reforestation projects based on ecology on a global scale must be essential for our future wholesome environments.


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2. Method
The tree species must be chosen from the forest com­munities of the region in order to restore multi-stratal natural or quasi-natural forests. If the main tree species are badly chosen, it will be difficult to regenerate native forests which develop as time goes by. In the plant com­munities, if the top is authentic, the followers are also real, just like in human society.

For the proper choice of species, we first make a through field vegetation investigation of the area, espe­cially in shrine and temple forests, old house forests, natural forests remaining on slopes, and substitute vege­tation changed by various human impacts. The results of the investigations obtained in this way are called relevés, which are equivalent to a census of green enviornments [3, 4, 11].


Next, we decide local community units by tablework comparing relevés and grouping similar species combina­tions. Then we compare them with community units in­vestigated and systematized in other parts of the world and see the species combinations. When we see species combi­nations, we find high-fidelity species for particular corn­munities. These species are called character species. We decide phytosociological units based on the character spe­cies. We compare phytosociological units widely from natural forests to secondary communities, and decide "as­sociations", basic units of a plant community system, which can be applied to worldwide vegetation science. Likewise, we group the units into alliances, orders and classes by species combinations. In this way the hierarchi­cal vegetation community system is decided [7].

Vegetation maps are drawn so that even non-experts in vegetation can understand the vegetation community units and their distribution. The present distributions of vegetation communities are drawn onto actual vegetation maps, which work as vegetation-ecological diagnoses not only for pure scientific purposes but also for the purpose of new utilization of land and decisions whether reforestation is needed [12].

There is another concept of vegetation, i.e. the potential natural vegetation [13]. Without any human im­pact, what vegetation could the land hold as the sum total of natural environments? The potential natural vegetation indicates the potential capacity of the land, theoretically considered, as to what vegetation it can sustain. To decide the potential natural vegetation, we investigate remaining natural vegetation and compare it with various secondary vegetation types from the factors of time and space. We also investigate the soil profile, topography and land utilization and put these together to grasp the potential natural vegetation [14].

Potential natural vegetation maps are essential for each ecological study field and are significant as ecological diagnoses for restoration of green environments. We found it possible to restore native green environments, multi-stratal forests, by choosing the main species from the potential natural vegetation of the area and planting them mixed and densely with as many companion species as possible [8].



The main tree species from the potential natural vegetation are generally deep- and straight-rooted and have been said to be difficult to transplant. We solved the problem by planting potted seedlings. We first collect seeds, that is, acorns. We germinate the seeds, move the seedlings to pots when two or three leaves have sprouted, and cultivate them until the root groups fill the containers and seedlings grow 30 to 50 centimeters high. It takes one-and-a-half years to two years in the temperate climate zone where most cities of Japan and the United States are located. In the tropical rain forest zone, where Borneo and Brazil lie, it takes only six to eight months to complete the growth of the potted seedlings [15].
Then we adjust the soil conditions of the planting site. Topsoil is usually washed away both in Japanese urban areas and on tropical barren land, from shifting cultiva­tion and forest felling Therefore it is necesarry to recover 20 to 30 centimeter-deep topsoil by mixing the soil of the region and compost from organic materials such as fallen leaves, mowed grass and so on.

Next we plant potted seedlings of the main tree species from the potential natural vegetation along with compan­ion species according to the system of natural forests. Dense and mixed planting of two or three seedlings per square meter will be appropriate.


Mulching with organic materials such as rice straw is needed in order to prevent soil erosion and moisture loss after planting. For two or three years after planting, we have to cut or pull weeds and utilize them as mulching material by leaving them around the young trees. In about three years the trees grow 2 to 3 meters high, and the crown covering the forest floor cornes to keep the sunlight from coming in. Consequently very few weeds can grow. This is how nature manages itself through natural selection. Three years after planting, the site basically becomes maintenance free.

Dense and mixed planting of community species of indegenous forests will need no watering, insecticides or herbicides, with some exceptions. Natural management is the best management [7].


3. Experiments and Results
3.1 Internal reforestation
Since 1973 we have been forming environment pro­tection forests around newly built ironworks and power stations in cooperation with farsighted Japanese corpora­tions such as Nippon Steel Corp., Tokyo Electric Power Co., Kansai Electric Power Co., Honda Engineering Co., Toray Textile Co., Mitsui Estate Co., Mitsubishi Corp., JUSCO EAON Group, and so on. In the latter half of the 1970s municipalities like Kanagawa Pref., Okayama Pref., Nagano Pref., Nara Pref., Yokohama City, Mikawa City, and Nagoya City, as well as the central government in­cluding the Ministry of Construction, began to ask us to regenerate native forests with native trees. The planting sites range 3,000 kms from Hokkaido in the north to Okinawa in the south. As of August 1998, we have re­stored native forests at about 550 locations, each of which is successful (Fig. 2, Color plates 1, 2, 5-8).

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Fig. 1 Flow chart for the restoration and creation of native forests [12].


Why is it indispensable to plant trees in so many places around the infrastructure? To this question the Great Hanshin Earthquake on January 17, 1995, gave us a definite answer.
We made field investigations right after the earth­quake. Structures built of iron and cernent, including modern buildings and some parts of elevated highways

and Shinkansen railways, were destroyed easily, and some of them burst into flames. They had cost tens of billions of yen and involved the latest techniques. We believed they were the strongest structures, but non-biological materials showed weakness against such disasters, which hit us once in some hundred years (Color plate 3).

On the other hand, not a tree of the main component



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Fig. 2 Planting locations of native forests by native trees based on the vegetation ecological scenario as of Oct. 1998.

The number represent the planting locations (place names omitted).




of the potential natural vegetation fell. Where evergreen broad-leaved trees from laurel forests were planted in a fine, fire was stopped. They proved to have a fire preven­tion function in many places (Color plate 4).

In the earthquake many houses were destroyed and



levelled to the ground. Many of the nearly 6,000 victims were crushed to death under their houses. Some houses had evergreen trees aound them in spite of their shade and falling leaves. These trees stopped the falling roofs and pillars, and made openings in the rubble. The people living

Photo 1 Ecological planting around Gobo thermal power plant of Kansai Electric Power Co. on a manmade island in the Pacific

Ocean (July, 1983).

Photo 2 Same place after 12 years (December, 1995). The trees have now grown much higher.

Photo 3 Disastrous earthquake hit Hanshin District (January 17, 1995).

Photo 4 A fire was stopped by a line of evergreen Oak trees (Quercus glauca), main species from the potential nautral vegetation.

Photo 5 Planting along Shin-shonan Bypass by primary school students.

Photo 6 1,200 primary school children planting seedlings along the Kashihara Bypass (March, 1982).

Photo 7 Same place after 14 years (July, 1996).

Photo 8 20,000 seedlings planted by 2,000 people around the Shirakawa Dam, Nara Prefecture. Prof. H. Sano (right) and Madame

Elisabeth Sano (center), participating in the planting festival (author left) (April, 1996).

Photo 9 The first planting festival at the site in Bintulu, Sarawak, Malaysia. 6,000 seedlings planted by 2000 people (July 15, 1991).

Photo 10 Same place after 4 years (January 16, 1995). At present the trees have grown higher.

Photo 11 The first planting festival to regenerate tropical lowland forests near Belém, Brazilian Amazon (May 18, 1992).

Photo 12 Same place after 4 years.

Photo 13 Planting 14 species of seedlings from native tree species including Nothofagus trees in Concepciôn, Chile (May 26, 1992).

Photo 14 Same place after 4 years (February 2, 1996).

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there could probably escape from the dread of death through the openings.

Lately the Ministry of Construction is beginning to plant seedlings from the potential natural vegetation along expressways, under the so-called Miyawaki Method based on the ecological scenario (Color plate 5). School child­ren led by their teachers plant seedlings as a part of the regular curriculum [1].

If these programs had started in Kobe ten years before the earthquake, the planted seedlings would have grown to form a forest belt about 10 m high. Then the drivers might not have lost their lives when the expressway was des­troyed, through softer landing on the forest.

This is another example of reforestation along the expressway. In Nara Prefecture construction of the Kashihara Bypass met with opposition of the inhabitants and was suspended for ten years. Some adovocated a greenery campaign to plant seedlings along the expressway as a way out. On March 13, 1982, school children planted seedlings following the ecological method (Color plate 6). Sixteen years have passed since then. Many of those children graduated from school and got married during the period. When they corne back to their home town, they proudly see the forest belt (Color plate 7). When their own children become primary school students, they will surely take them to the forest and say, "The seedlings I planted with my hands when I was as old as you are now have grown to this great forest."

The staff in the civil engineering bureau in Nara Prefectural Government knew the case of Kashihara By-pass and held a planting festival around Ohta Dam. 2,000 people, including the Governor of Nara Prefecture, planted 20,000 seedlings from the potential natural vege­tation. Prof. Sano and his wife as well as many students of Nara Institute of Science and Technology took part in the festival and planted with sweat on their brows (Color plate 8). I would like people in Nara Prefecture to keep watching the growth of the seedlings with a scientific eye and love towards life.

3.2 Restoration of tropical raie forests in Southeast Asia

In 1978 we began vegetation field investigations in Indonesia (Borneo), Thailand, and Malaysia, from man­grove forests along the seacoast to tropical rainforests, tropical dry forests and laurel forests in the mountains in Thailand [16, 17]. Based on the results of the investiga­tions, we began a joint restoration project with Mitsubishi Corp. and the University of Agriculture, Malaysia in 1990. The planting site was 800 ha of barren land on the Bintulu campus of the university, Sarawak State (northeast Bor­neo) [15].

Restoration of tropical rainforests has been consi­dered to be quite difficult, and it was usual to plant rapid-growing speices such as Eucalyptus from Australia, and long-leaf pine, Pinus taeder from America, and Aca­cia mangium. These exotic rapid-growing species grow very fast at the beginning. Since they grow in a mono­stratum, however, they are highly vulnerable to dry air, strong wind and insect damage. Reforestation with these


species is not always successful.

We chose the main tree species from the potential natural vegetation of the area, Dipterocarpaceae, includ­ing Hopea, Shorea, and Dipterocarpus. We also planted as many companion species of the tropical rainforest com­munities as possible, in order to follow the natural bio­diversity. This may be the newest method of refore­station in the world. We have planted 91 species from the potential natural vegetation in all (Table 1) [18].

I would like to show the case of Plot 203 of the Bin­tulu reforestation as one example. There we had a lot of difficulty in the first stage of growth.

On July 15, 1991, we and 2,000 participants dug 6,000 small holes with our hands and planted 6,000 seedling. The record of their growth is represented in Fig. 3 and Color plates 9 and 10. The survival rates of the individuals and the groups in six years are shown in Fig. 4. During the first few years tenacious grass weeds came out and we cut them and covered the forest floor with them for supplementary mulching. After three years the plantation basically re­quired no maintenace. It is six years since the planting, and the trees have grown steadily to reach 6 m to 10 m high. Every year after the first planting 30-80 volunteers from Japan and people from Malaysia participate in the plant­ing festival in Bintulu. Until now 330,000 seedlings have been planted on 50 ha of land. We can see them developing into quasi-natural forests [19].

Adopting the same method, we have succeeded in restoring disaster-preventing, environment-protecting forests around newly built shopping centers backed by JUSCO in Kuala Lumpur, Melaka, Ippo (Malaysia), and Bangkok (Thailand). The forests restored in urban and peri-urban areas are highly valued by local people.

The royal family of Thailand had a lot of interest in ecological reforestation, and we started planting dry Dip­terocarpus and other species from the potential natural vegetation along the boundary between western Thailand and Myanmar. We named the joint work the Royal Prin­cess Sirindhorn Project.



3.3 Examples in South America

In December 1990 we started an experimental regeneration project for lowland tropical forests in col­laboration with Parà Agricultural University in Belém, northern Brazil. We collected 92 species mostly from the potential natural vegetation, including the main species Virola, and made potted seedlings with fully developed root systems. This project was backed by EIDAI do Brazil Madeiras S.A. and Mitsubishi Corp. The first planting festival was held on May 18, 1992, attended by the Mayor of Belém, Mr. and Mrs. Murazumi, Japanese Ambassador extraodinary and plenipotentiary to Brazil, President of Parà Agricultural University, and many other people (Color plate 11). After that every year we continually plant seedlings at planting festivals. They grow steadily and some individuals reach 10 m to 15 m high in five years (Color plate 12).

At this site we made haste in planting and intention­ally mixed indegenous species and rapid-growing pioneer species. Rapid-growing species, including Barsa, grew very

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Table 1 The species list of planted trees for reforestation in Malaysia



No.

Species Name

Family Name

Local Name

1

Shorea atrinervosa

Dipterocarpaceae

Selangan batu hitam

2

Shorea balanocarpoides

Dipterocarpaceae

Meranti lun

3

Shorea beccariana

Dipterocarpaceae

Meranti langgai

4

Shorea brunnescens

Dipterocarpaceae

Selangan batu tinteng

5

Shorea crassa

Dipterocarpaceae

Selangan batu daun tebal

6

Shorea dasyphylla

Dipterocarpaceae

Meranti batu

7

Shorea domatiosa

Dipterocarpaceae

Selangan batu lubang idon

8

Shorea gibbosa

Dipterocarpaceae

Meranti lun gajah

9

Shorea glaucescens

Dipterocarpaceae

Selangan batu daun nips

10

Shorea laxa

Dipterocarpaceae

Lun timbul

11

Shorea leprosula

Dipterocarpaceae

Meranti tembaga

12

Shorea macrophylla

Dipterocarpaceae

Engkabang jantung

13

Shorea macroptera

Dipterocarpaceae

Meranti melantai

14

Shorea maxwelliana

Dipterocarpaceae

Kumus hitam

15

Shorea mecistopteryx

Dipterocarpaceae

Meranti kawang burung

16

Shorea multera

Dipterocarpaceae

Lun jantan

17

Shorea ovata

Dipterocarpaceae

Meranti phis

18

Shorea parvifolia

Dipterocarpaceae

Meranti sarang punai

19

Shorea pauciflora

Dipterocarpaceae

Nemesu

20

Shorea rubella

Dipterocarpaceae

Meranti laut putih

21

Shorea scaberrima

Dipterocarpaceae

Meranti paya bersisik

22

Shorea scabrida

Dipterocarpaceae

Meranti lop

23

Shorea venulosa

Dipterocarpaceae

Meranti tangkai panjang pa

24

Hopea beccariana

Dipterocarpaceae

Merawan/Chengal pasir

25

Hopea bracteata

Dipterocarpaceae

Luis

26

Hopea kerangasensis

Dipterocarpaceae

Luis kerengas

27

Hopea pentanervia

Dipterocarpaceae

Chengal paya

28

Parashorea parvifolia

Dipterocarpaceae

Urat mata bukit

29

Parashorea smythiesii

Dipterocarpaceae

Urat mata daun puteh

30

Dryobalanops aromatica

Dipterocarpaceae

Kapur peringgi

31

Dryobalanops beccarii

Dipterocarpaceae

Kapur Bukit

32

Dipterocarpus rigidus

Dipterocarpaceae

Keruing utap

33

Dipterocarpus stellatus

Dipterocarpaceae

Keruing

34

Cotylelobium burckii

Dipterocarpaceae

Resak durian

35

Cotylelobium malayanum

Dipterocarpaceae

Resak batu

36

Cotylelobium melanoxylon

Dipterocarpaceae

Resak hitam

37

Upuna borneensis

Dipterocarpaceae

Upun

38

Vatica cuspidata

Dipterocarpaceae

Resak

39

Vatica mangachapoi

Dipterocarpaceae

Resak

40

Vatica nitens

Dipterocarpaceae

Resak daun panjang

41

Vatica venulosa

Dipterocarpaceae

Resak

42

Dracontomelon dao

Anacardiaceae

Sengkuang

43

Gluta wallichii

Anacardiaceae

Rengas

44

Mangifera pajang

Anacardiaceae

Embang

45

Parishia insignis

Anacardiaceae

Upi bung

46

Parishia maingayi

Anacardiaceae

Upi paya

47

Pentaspadon motleyi

Anacardiaceae

Pelajau

48

Neouvaria acuminatissima

Annonaceae

Karai

49

Alstonia angustifolia

Apocynaceae

Pelai

50

Alstonia angustiloba

Apocynaceae

Pelai

51

Alstonia scholaris

Apocynaceae

Pelai lilin

52

Durio carinatus

Bombacaceae

Durian burong

53

Durio zibethinus

Bombacaceae

Durian

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Table 1 (continued)



No.

Species Name

Family Name

Local Name

54

Dacryodes costata

Burseraceae

Kedondong

55

Santiria megaphylla

Burseraceae

Seladah

56

Diospyros sarawakana

Ebenaceae

Kaya malam

57

Baccaurea angulata

Euphorbiaceae

Ocong

58

Baccaurea bracteata

Euphorbiaceae

Tampoi paya

59

Baccaurea lanceolata

Euphorbiaceae

Tapus/Empaon(u)g

60

Elateriospermum tapos

Euphorbiaceae

Kelampai/Perah

61

Calophyllum ferrugineum

Guttiferae

Bintangor

62

Calophyllum macropodum

Guttiferae

Bintangor daun besar

63

Calophyllum nodosum

Guttiferae

Bintangor daun halus

64

Calophyllum sclerophyllum

Guttiferae

Bintangor jangkar

65

Garcinia cuspidata

Guttiferae

Knadis daun kechil

66

Stemonurus scorpioides

lcacinaceae

Semburuk

67

Eusideroxylon zwagerri

Lauraceae

Belian

68

Litsea sp.

Lauraceae

Medang

69

Barringtonia sp.

Lecythidaceae

Putat

70

Archidendron ellipticum

Leguminosae

Pet ai belalang/kedaung

71

Dialium sp.

Leguminosae

Keranji

72

Koompasia malaccensis

Leguminosae

Kampas

73

Sandoricum koetjape

Meliaceae

Kelampuk

74

Artocarpus integer

Moraceae

Cempedak

75

Artocarpus rigidus

Moraceae

Terap

76

Parartocarpus venunosus

Moraceae

Minggi

77

Engenia castanea

Myrtaceae

Ubah

78

Engenia chrysantha

Myrtaceae

Ubah

79

Engenia grandis

Myrtaceae

Ubah jambu

80

Engenia hoseana

Myrtaceae

Ubah

81

Engenia lineata

Myrtaceae

Ubah daun kecil

82

Engenia ochnecarpa

Myrtaceae

Ubah parit

83

Tristania beccarii

Myrtaceae

Selunsur

84

Whiteodendron mountonianum

Myrtaceae

Kawi

85

Sarcotheca glauca

Oxalidaceae

Tulang payong

86

Pometia pinnata

Sapindaceae

Kasai/Selan

87

Ganua pierrei

Sapotaceae

Ketiau putih

88

Palaquium gutta

Sapotaceae

Nyatoh riau

89

Scaphium macropodum

Sapotaceae

Kembang semangkuk

90

Eurycoma longifolia

Simaroubaceae

Tongkat ali

91

Gonystylus maingayi

Thymelaeaceae

Ramin batu air




Fig. 3 Growth curve in height on PQ 203 in Bintulu, Sarawak, Malaysia.



Fig. 4 Survival rate with passage time on PQ 203 in Bintulu, Sarawak, Malaysia.


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fast, but because of their shallow root systems some of them fell in the strong wind and received some other damage. They also made shade over the indegenous species like Virola, which were growing more slowly. In conclu­sion it is the best and the most secure method to mix and plant spcecies from the potential natural vegetation fol­lowing the system of natural forests, just as we did in Japan and Southeast Asia.

In Concepción, Chile, we practiced reforestation by mixed, dense planting of 14 species of Nothofagus. Though it was said to be difficult to restore native forests in the area because of dry air in summer and overgrazing, we have found that native forests can be restored if we take sufficient care for the first several years after planting (Color plates 13 and 14).



3.4 Reforestation in China

Forest devastation is quite serious around the Great Wall, the more than 2000-year-old structure stretching 2,600 km, which is called the symbol of the civilization of Great China. Several projects have been tried but were not necessarily successful.

We began field investigations to understand the potential natural vegetation around the Great Wall, in cooperation with the People's Government of Beijing and AEON Environment Foundation of Japan. We collected 80,000-1,000,000 acorns of indegenous species, including Quercus mongolica, and germinated them to grow see­dlings in pots. On July 4, 1998, the first planting festival was held, with the help of 1,400 volunteers from Japan and about 1,200 volunteers from China. Chinese people took the trouble of digging 175,000 60 cm' holes in the



Fig. 5 Comparison between our new succession theory and classical theory (Laurel forest area in Japan) [14].

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Fig. 6 Comparison between our new succession theory and classical theory (Case in Bintulu, Sarawak, Malaysia).
rocky surface with no topsoil, and we could plant seedlings with the view to an international green wall of native forests. This project is a three-year program, and 390,000 seedlings are planned to be planted in total.
4. Discussion and Conclusion

As Clements mentioned [20], annual plants on barren land are succeeded by perennial grass, sun shrubs, light­demanding fast-growing trees, and finally indegenous natural forests. It was said that it would take 150-200 years in Japan to reach the final indegenous natural forests [4] by secondary progressive succession and 300-500 years in Southeast Asia (Figs.5 and 6).



Several hundred years for reforestation is too long for us, however, because we live in a world where industry and urbanization are developing very rapidly. We tried eco­logical reforestation by recovering topsoil and planting seedlings in pots with fully developed root systems directly from the terminal vegetation in succession, that is, the potential natural vegetation. It is proved here that multi­stratal quasi-natural forests can be built in 15-20 years in Japan and 40-50 years in Southeast Asia by ecological reforestation based on the system of natural forests. Among 550 locations of our planting throughout Japan we don't see a single failure. We succeeded in restoration of native forests from in cold-temperate zone to in tropical forest zone.

550 locations is far from enough when we consider the whole 380,000 km2 land of Japan, much more on a global scale. We all should set to restoration and recreation of global environments in every place in the world by the ecotechnological method. We can start at once, following the rules of biocoenoses. Farsighted top managers of ad­ministrations, corporations, and communities can be general directors. Scientists write ecological scenarios for environment restoration. Citizens are the main characters on the stage. All the people on the earth share the work in a sweat for the sound future of human beings.

Ecology was originally viewed as a science of discov­ery and played the role of critic when environmental pol­lution occurred in the 1970s. Now ecology should be creative in order to restore environments and build better living conditions, We expect all scientists in the world to see our results positively and to begin to help make new affluent circumstances for the future in their own area. We hope to struggle together for creative ecology.
Acknowledgements

I had learned the concept of the potential natural vegetation for two and a half years since 1958, from Prof. Reinhold Tüxen, the then Director of Bundesamstalt für Vegetationskartierung in then West Germany. After com­ing back to Japan I began vegetation field investigations with the knowhow in the 1970s when the Japanese economy rapidly grew. Since then many farsighted inter­national and domestic corporations, Ministries including the Ministry of Education, governers and mayors of local public bodies, and so many citizens have been working with us. I would like to express my gratitude to every one of them.
References

[1] Miyawaki, A., Fujiwara, K., Ozawa, M., 1993. Bull. Inst.

Environ. Sci. Technol. Yokohama Nati. Univ. 19: 73-107.

[2] Miyawaki, A., 1997. Green Environments and Vegetation Science Chinjuno-mori (native forests with native trees in shrines and temples) to World Forests. NTT Publisher, Tokyo, 239 pp.

[3] Miyawaki, A., 1982. Bull. Inst. Environ. Sci. Technol. Yokohama Natl. Univ., 11: 107-120.

[4] Miyawaki, A., 1975. Entwicklung der Unweltschutz-Pflan­zungen und Ansaaten in Japan. In: Tüxen, R. (Ed.) Sukuzessionsforschung. Bericht über das Internationale



25

Symposium der Intemationalen Vereinigung für Vegetations­kunde. Vaduz, Cramer, 237-254.

  1. Miyawaki, A., Fujiwara, K., Box, E.O., 1987. Bull. Inst. Environ. Sci. Tech., Yokohama Natl. Univ. 14: 67-82.

  2. Miyawaki, A., Golley, F.B., 1993. Forest reconstruction as ecological engineering. Ecological Engineering. Elsevier, Amsterdam, 2: 333-345.

  3. Miyawaki, A., 1989. Restoration of evergreen broad-leaved forest (laure! forest') in Japan. In: Academy, Ch. (Ed.). The World Community in Post Industrial Society. The Human Encounter with Nature: Destruction and Reconstruction. Wooseok Publishing Co., Seoul, 5: 130-147.

  4. Miyawaki, A., 1998. Vegetation ecological study for resto­ration of forest ecosystems. Fujiwara, K. (Ed.), A vegetation ecological study for the restoration and rehabilitation of green environnent based on the creation of environmental protection forests in Japanese Archipelago. Inst. Veget. Sci., Inst. Environ. Sci. Technol. Yokohama Natl. Univ., 267­298.

  5. Miyawaki, A., 1998. Ecological Engineering. (in press).

  6. Miyawaki, A., et al., 1980-1988. Vegetation of Japan. vol. 1-10,1. Yakushima 376 pp., 2. Kyushu 484 pp., 3. Shikoku 539 pp., 4. Chugoku 540 pp., 5. Kinki 596 pp., 6. Chubu 604 pp., 7. Kanto 641 pp., 8. Tohoku 605 pp., 9. Hokkaido 563 pp., 10. Okinawa and Ogasawara 676 pp. Each vol. with color vegetation maps and tables.

  7. Miyawaki, A., 1981. Energy policy and green environnent on the base of ecology. In: Fazzolare, R.A., Smith, C.B. (Eds.), Beyond the Energy Crisis Opportunity and Challenge. Oxford and New York, 581-587.

  8. Miyawaki, A., 1996. Restoration of biodiversity in urban and peri-urban environments with native forests. In: di Castri, F., Younes, T. (Eds.). Biodiversity, Science and De 

velopment, Towards a New Partnership. CAB Inter­national, 558-565. Printed and bound at the University Press, Cambridge, UK.

  1. Tüxen, R., 1956. Die heutige potentielle natürliche Vegeta­tion als Gegenstand der Vegetationskartierung. Angew. Pflanzensoziologie 13: 5-42. Stolzenau/Weser.

  2. Miyawaki, A., 1992. Restoration of evergreen broad-leaved forests in the Pacific region. In: Wali, M.K. (Ed.), Ecosys­tem Rehabilitation, Ecosystem analysis and synthesis. SPB Academic Publishing, The Hague, Netherlands, 2: 233-245.

  3. Miyawaki, A., 1993. Restoration of native forests from Japan to Malaysia. In: Lieth, H., Lahmann, M. (Eds.), Restoration of Tropical Forest Ecosystems. Kluwer Aca­demic Publishers, Netherlands, 5-24.

  4. Miyawaki, A., 1982. Phytosociological study of East Kalimantan, Indonesia. Bull. Inst. Environ. Sci. Technol. Yokohama Natl. Univ., 8: 219-232.

  5. Miyawaki, A., 1992. Ecological perspectives for sustainable development of Southeast Asian forests. Proceedings of International Seminar on Agricultural Change and Develop­ment in Southeast Asia (SACOESA-III), Tokyo Univ. of Agriculture, 97-106.

  6. Megro, S., Miyawaki, A., 1997. Tropical Ecology. 38: 237­245.

  7. Miyawaki, A., Meguro, S., 1998. Restoraton of tropical rain forests in Sarawak, Malaysia. In: Sjligren, E., Maarel, E., Pokarzhevskaya, G., (Eds.), Studies in Plant Ecology, Vegetation science in retrospect and perspective, Uppsala, 20: p. 60.

Clements, F.E., 1916. Plant succession: An analysis of the development of vegetation. Carbegie Institution of Washington Publ., Washington, 242, 1-512.



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