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[Summary]

The reduction of forests due to environmental pollution has been marked in and Europe. In Japan, as well, expansion of visible damage to the forests has recently been reported. Forest vegetation fixes CO2 from the air. A decrease in vegetation leads to a decrease in CO2fixation and environment-cleaning function and thus may lead to a rise in the global temperature. Within the framework of global environmental problems, it is most urgent that steps are taken to protect forests from damage and to enhance the forest functions, in addition to facilitating the reforestation of tropical forests and converting deserts into vegetation areas. To this end, it is essential to develop strains resistant to environmental pollution and to develop technology for utilization of symbiotic microorganisms in plant root which play an essential role for the growth of the plant. This report has first presented the present status of forest damage and environmental pollution. We have then investigated systematically pollution-resistant , usable microbes and their gene analysis(basic research), and also breeding and planting technology(applied technology). Furthermore, we described an analysis of ways to combine the results of basic research with those of applied research, with the goal of contributing to the advancement of biological CO2 fixation.

Chapter 1 Present status of forest damage and environmental pollution At present, the area of forestation is decreasing on a global scale. Annually, more than 10 million ha of tropical forest have been lost due to the indiscriminate felling of trees and slash-and-bum agriculture. Forest damage has also been spreading in temperate and subarctic forests in the northern hemisphere. In Japan, blight of needle-leaf trees (pine and momi fir) and of Japanese oak has occurred in areas along the Sea of Japan and in the Kyushu district. In addition, blight of some other trees, such as wild cherry trees, Japanese apricot trees, birch, Japanese cedar, cypress and bamboo, has been reported from various regions of the country. Outside Japan, forest damage has become apparent in Central Europe, North America and East Asia (China). Decay is not confined to needle- leaf trees but has been extending to broadleaf trees. This global deforestation has been attributed to various factors, including soil souring, ozone, Mg deficiency and nitrogen excess. In the past, acid rain was studied as a possible cause of forest decay. However, since desulfurization of industrial gas exhaust has been put into practice in the developed countries, some investigators now consider climatic drying as a possible factor related to the increased failure of trees. In any event, the exact cause of deforestation has not yet been identified. In decaying forests, the growth of tree rootlets is less active, and mycorrhizal fungi have decreased or disappeared. Mycorrhizal fungi are indispensable for tree growth. It is unknown whether weakened rootlet growth or decrease of mycorrhizal fungi occurred first. The forest is the chief place on earth where CO2 is fixed and stored. Damage to forests, as mentioned above, results in a decrease of fixed CO2 , leading to global warming. According to a report made by the IPCC, the annual loss of tropical forest causes the release of CO2 which is the equivalent of about 1.6 billion tons of carbon into the ambient air per year.

- 1 - This amount of CO2 can be fixed by trees in the temperate and subarctic zones are left intact. However, because forests in these zone are also being damaged, it is estimated that ambient CO2 equivalent to about 100 million tons of carbon failed to be fixed in Europe due to forest damage. As a result, each year excess CO2 equivalent to 3 billion tons of carbon is left free in the atomosphere. This indicates the necessity of our taking further steps, including planting pollution-resistant trees.

Chapter 2 Search for pollution-resistant plants and analysis of their function Pollutants, released into ambient air, spread widely, causing environmental problems on a global scale. If coal, which is low in quality, is substituted for high quality oil as a source of energy, the release of sulfur oxides will increase. In addition to removal of sources of pollutants, cultivation of plants resistant to pollutants is important. This chapter lists plants reported to be resistant to pollutants and describes the physiological features of these plants. Furthermore, to develop pollution-resistant plants, this chapter reviews reports relating to clarification of the mechanism of resistance development and the genes involved. To facilitate the development of pollution-resistant plants, recent trends and advances in plant breeding technology have also been investigated. Pollutants are absorbed via the stomata and cuticle into the leaves. Heavy metals and aluminum are absorbed from the roots. If the stomata are closed to avoid invasion by the pollutants, the photosynthetic capacity will decrease. To protect trees from pollutants, it is therefore necessary to develop plants which are highly resistant to pollutants. In case where pollutants cause oxygen radicals or hydrogen peroxide to be formed, an increase in oxygen radical detoxifying enzyme activity or antioxidation is probably necessary for resistance to these pollutants to develop. Some herbaceous plants with a high NO2 assimilating were selected, and their mechanisms of resistance to pollutants have been analyzed. The findings from this analysis have been utilized for molecular plant breeding, making use of genes involved in resistance to pollutants. Genes reported to be involved in plant resistance to pollutants include genes encoding glutathion reductase, phytochelatin synthase and metallothionein. Because one generation of trees is relatively long, gene transfer provides a useful means of developing pollution-resistant trees. However, research on cell and tissue cultures, regeneration and gene transfer for trees lags considerably behind these techniques as applied to herbaceous plants. Even if pollution-resistant trees are developed, much time will be needed before forest composed of such trees are standing. It is, therefore, desirable to develop techniques for the direct introduction of pollution-resistant characteristics to forest trees by means of gene transfer.

Chapter 3 Utilization and functional analysis of soil microorganisms The role played by the root in absorbing and delivering nutrients and water is as important for plants as is photosynthesis. Microorganisms which symbioses for roots support these root functions. Symbiotic microorganisms attenuate environmental stresses such as drought and pollution and thus protect the roots. They also suppress the activity of pathogenic microorganisms and improve the

- 2 - environment around the roots, thus helping plants to grow normally. This chapter discusses the roles played by symbiotic microorganisms and how to utilize these organisms. Their functions in coping with acid rain and heavy metal pollution, and how to utilize such functions are also discussed. Rhizobia in leguminous plants and Frankia in alders are known to fix nitrogen. The total amount of nitrogen fixed by these microorganisms.is estimated at about 17.5 million tons, which is equivalent to more than double the amount of nonbiologically fixed nitrogen. These organisms greatly affect the growth of plants and the circulation of nitrogen-based nutrients on earth. Although a number of studies have been published concerning the genes involved in nitrogen fixation by Rhizobia, few such studies have been published for Frankia. All tree symbiose with mycorrhizal fungi. VA mycorrhizal fungi absorb phosphorus from the soil and supply it to the host plants to promote their growth. They also suppress the hazards to plants caused by pathogenic bacteria in the soil. Although ectomycorrhizal fungi can symbios only with limited hosts, plants carrying these fungi can absorb nutrients better than plants without these fungi. The fungi also help plants absorb water, thus making plants more resistant to drought Mycorrhiza formation elevates the efficiency of nutrient absorption and promotes plant growth, leading to higher photosynthetic activity. An increase sink promotes plant growth, elevates the CO2 assimilating ability of source organs and thus suppresses an increase in ambient air CO2 levels. It is desirable to search for more such useful symbiotic microorganisms which elevate the resistance of host plants to pollutants and to clarify their functions.

Chapter 4 Techniques of cultivating and maintaining plants resistant to pollution Our surveys revealed that both the underground roots and symbiotic microorganisms were disappearing in dying forests. The activity of symbiotic microorganisms around the roots of plants is indispensable for their growth. Therefore, to cultivate and maintain pollution-resistant plants, it is necessary not only to assess the features of such plants but also to develop techniques for the utilization of symbiotic microorganisms, including techniques to make elevate the affinity of symbiotic microorganisms for plants and techniques to inoculate plants with symbiotic microorganisms. In the past, few attempts to find or create pollution-resistant tree were made. In the present study, we took the development of trees resistant to pine wood nematodes as an example, and reviewed the current state of research and explored the direction of future possible advances concerning methods to evaluate the resistance to pollution, techniques to increase the affinity of symbiotic microorganisms, desirable plant cultivation techniques, and method to reinforce resistance to pollution. Since conventional cross-breeding is needed to reinforce the function of new strains of pollution-resistant trees, it is desirable to develop a technique to shorten the tree life cycles. To establish up and maintain forests, amidst environmental pollution, it is necessary to establish a systematic technology resting on a strong platform of basic and applied research relating to the selection of resistant plant, elucidation of their features, methods of efficient tree nutrition, methods for reinforcing resistance to pollution, and methods for plant cultivation tailored to the conditions of

- 3 - each area.

Chapter 5 Conclusion and Proposals Damage of forests on a global scale is continuing. It is not always attributable to two or more combined factors. To suppress the increase of CO2 release into the air, it is essential to plant trees and to preserve existing forests. To this end, elimination of pollutants and the development of pollution-resistant plants are essential. Pollution-resistant plants are able to be selected by screening, and also obtained by molecular plant breeding. The growth of plants is supported by microorganisms which symbioses with their roots. Symbiotic microorganisms elevate the resistance of plants to environmental stresses and promote their growth, resulting in suppression of an increase in ambient air CO2 levels. It remains to be clarify whether or not the resistance of plants carrying symbiotic organisms can be increased even in polluted environments, if appropriate microorganisms are selected for symbiosis. It is urgently needed to establish a molecular breeding system, especially in vitro culture system, for woody plants, and to develop a technique of gene transfer to plants, which can be called "gene therapy". Furthermore, we should clarify the physiology of symbiosis of plants and fungi which form mycorrhiza, which has not yet been clarified except for symbiosis between leguminous plants and rhizobia, and establish techniques of breeding, culturing and inoculating such organisms, with the goal of establishing a system for developing and maintaining better forest environment with the help of these microorganisms. At present, the course shown in Fig. 1 is turning in a negative direction. If the course is partially modified, the current negative direction of things will become positive.

- 4 - Current state Preservation of the Grobal Environment X Environmental pollution; Control of environmental pollution e. g. , Acid rain \ Inhibition of the growth Inhibition of Superior mycorrhizal of mycorrhizal fungi Pollution-res is tant plant growth fungi plants

Promotion of nycorrhiza formation * Reduction of Selection and Gene manipulation (gene therapy) breeding Promotion of nutrient absorption forests ^ Resistance to drought Enlargement of the sink

Aggravation of environments ;Increase of ambient air C02 Desirable steps and action

Fig.l Turn the environmental circuit from the negative to positive direction

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- 32 - 50) W. C. Shortle and K. T. Smith; Science Vol.240 (1988), P1017-1018 51) Ruhling and G. Tyler; Oikos Vol.24 (1973), P402-416 52) G. Tyler; Plenum Press, New York, "Effect of Acid Precipitation on Terrestrial Ecosystem" ed. by T. C. Hutchingson et al. (1975), P252-282 53) K. W. Burton, E. Morgan and A. Roig; Plant Soil Vol.78 (1984), P271-282 54) D. L. Godbold and A. Huttermann; Environ. Pollut. (Ser. A) Vol.38 (1985), P375-381 55) E.von Zezschwitz; Geol. Jb. Vol.F 21 (1986), P3-61 56) H. V. Meisch, M. Vessler, W. Reinle and A. Wagner; Experientia Vol.42 (1986), P537-542 57) G. Tyler; Water Air Soil Pollut. Vol.9 (1978), P137-148 58) T. S. Hutchinson and L. M. Whitby; Water Air Soil Pollut. Vol.7 (1977), P421-438 59) BSOTr, No. 10 (1991), P765-768 60) /JvflfM; #### Vol.25 (1996), P31-39

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1) A. Wild, V. Schmitt; Physiologia Plantarum Vol. 93(1995), P. 375-382. 2) A. Wild, P. Strobel, & U. Flammersfeld Z. Naturforsch. Vol.48 (1993), P.911- 922 3) H. Hohlfeld, C,Lutz, D.Strack; Z. Naturforsch. Vol. 46 (1991) P.502-505 4) M. Scalet, R. Federigo, M. G. Guido, F. Manes; Emviron. Exp. Bot. Vol.35 (1995), P. 417-425 5) T. A. McKeon, N. E. Hofinan, S. F. Young; Planta Vol. 115 (1982), P. 437-443 6) H. Mehlhom, B.J. Francis, A.R. Wellburn; New Phytol. Vol. 110 (1989) P. 525-534 7) K Asada; Physiol. Plant. Vol.85 (1992), P. 235-241 8) am^; 10# (1985), p. 729-743 9) N. Kondo, Y. Akiyama, M. Fujiwara; Res. Rep. Natl. Inst. Environ. Stud. Noll (1980), P, 137-150 10) J. Sekiya, L. G. Wilson, P. Filner; Plant Physiol. Vol. 70 (1982), P. 437-441 11) K Asada, K Kiso; Eur. J. Biochem. Vol. 33 (1973), P. 253-257 12) T. T. Kozlowski, H. A. Constantinidou; Forestry Abstracts Vol. 47 (1986), P. 6-51

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— 82 — 1) e, mmmn ; voi. 38 No. 2 (19%), p.15-19 2) #m#% ; lHU M 1350 -§• (1996), P.30-36 3) C.H. Foyer, N. Souriau, S. Perret, M. Lelandais, K.-J. Kunert, C. Pruvost, L. Jouanin; Plant Physiol. Vol. 109 (1995), P. 1047-1057 4) M. DeCleene, J. CeLey; Bot. Rev. Vol. 42 (1976), P. 389-466 5) I. Hay, D. Lachance, P. V. Aderkas, P. J. Charest; Can. J. For. Res. Vol. 24 (1994), P.2417-2423 6) D. Botstein, R.L. White, M. Skolnik, R. Davis; Am. J. Hum. Genet. Vol. 32 (1980), P.314-331 7) J.G.K. Williams, A.R. Kubelik, K.J. Livak et al. Nucl. Acids Res. Vol. 18 (1990) P.6531-6535 8) P. Vos, R. Hogers, M. Bleeker, M. Reijans, T. van de Lee, M. Homes, A. Frijters, J. Pot, J. Peleman, M. Kuiper, M. Zabeau; Nucl. Acids Res. Vol. 23 (1995), P.4407-4414 9) [nJ#M P.50-53 10) A. Groover, M. Devey, T. Fiddler et al. Genetics Vol. 138 (1994), P. 1293-1300 11) H. D. Bradshaw, R. F. Stettler; Genetics Vol. 139 (1995), P. 963-973 12) D. Grattapaglia, R. F. Sederoff; Theor. Appl. Genet. Vol. 91 (1995) P. 13) E. Paakkonen, S. Paasisalo, T. Holopainen, L. Karenlampi; New Phytol. Vol. 125 (1993), P615-623 14) D.F. Kamoski, Z.E. Gsgnon, D.D. Reed, J.A. Witter; Can. J. For. Res. Vol. 106 (1992), P. 1785-1788 15) S.A. Watmough, N. M. Dickinson; Envron. Exp. Bot. Vol. 36 (1996), P. 293-302 16) W. Prus-Glowacki, St. Godzik; Silvae Genet. Vol. 44 (1995), P. 62-65 17) F. Bergmann, F. Scholz; Silvae Genet. Vol. 36 (1987), P.80-83 18) T. H. Geburek, F. Scholz, W. Knabe, A. Vomweg; Silvae Genet. Vol. 36 (1987), P.49-53 19) W. Prus-Glowacki, St. Godzik; Silvae Genet. Vol. 40 (1991), P. 184-188 20) F. Bergmann, B. Hosius; Water, Air, and Soil Pollution Vol. 89 (1996), P.363-373 21) J. L. Hamrick, S. L. Sherman-Broyles; New Forests Vol. 6 (1992), P. 95-124

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- 85 - 1) T. Friedmann and R. Roblin, Science, Vol. 175 (1972), P 949-55 . 2) R. G. Crystal, Science, Vol. 270 (1995), P 404-410 . 3) K Roemer and T. Friedmann, Eur. J. Biochem, Vol. 208 (1992), P 211-225 . 4) J. R. MclachHn, K. Cornetta, M. A. Eglitis and W. F. Anderson, Prog. Nucleic Acid Res. Mol.Biol., Vol. 38 (1990), P 91-135 . 5) R. M. Blaese, K. W. Culver, A. D. Miller, C. S. Carter, T. Fleisher, M. Clerici, G. Shearer, L.Chang, Y. Chiang, P. Tolstoshev, J. J. Greenblatt, S. A. Rosenberg, H. Klein, M. Berger, C.A. Mullen, W. J. Ramsey, L. Muul, R. A. Morgan and W. F. Anderson, Science, Vol. 270 (1995), P 475-480 . 6) J. Zabner, L. A. Couture, R. J. Gregory, S. M. Graham, A. E. Smith and M. J. Welsh, Cell, Vol. 75 (1993), P 207-216 . 7) R. G. Crystal, N. G. McElvaney, M. A. Rosenfeld, C. S. Chu, A. Mastrangeli, J. G. Hay, S.L. Brody, H. A. Jaffe, N. T. Eissa and C. Danel, Nature Genetics, Vol. 8 (1994), P 42-51. 8) A. R. Mushegian and R. J. Shepherd, Microbiological Reviews, Vol. 59 (1995), P 548-578. 9) W. O. Dawson, D. J. Lewandowski, M. E. Hilf, P. Bubrick, A. J. Raffb, J. J. Shaw, G. L. Grantham andP. R. Desjardins, Virology, Vol. 172 (1989), P 285-292 . 10) S. Chapman, T. Kavanagh and D. Baulcombe, Plant J, Vol. 2 (1992), P 549-557 . 11) M. H. Kumagai, T. H. Turpen, N. Weinzettl, G. Della Cioppa, A. M. Turpen, J. Donson, M. E. Hilf, G. L. Grantham, W. O. Dawson and C. TP, Proc. Natl. Acad. Sci. USA, Vol. 90 (1993), P 427-430 . 12) X. H. Li and J. C. Carrington, Proc. Natl. Acad. Sci. USA, Vol. 92 (1995), P 457-461. 13) J. Henderson, M. J. Gibbs, M. L. Edwards, V. A. Clarke, K. A. Gardner and J. I. Cooper, Journal Of General Virology, Vol. 73 (1992), P 1887-1890 . 14) M. Nemeth, Bulletin OEPP, Vol. 24 (1994), P 525-536 .

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