Background : The use of the rain shelter facility gets more prevalent in the Ginseng cultivation area these days. This study is designed to establish a technique for the stable cultivation of Ginseng in the rain shelter facilities in high temperature (above 30 ℃) without the damage from high temperature Methods and Results : This study was carried out on 3-year Ginseng roots in 2016 in order to find out how to stably cultivate Ginseng in high temperature without suffering the high temperature damage during the cultivation of Ginseng under rain shelter facilities. The rain shading materials were coated with scattering film (scattering film + black shading net 90%), bluish white double-sided film (shading 85%) and PE film (PE film + black shading net 90%). The damage reduction by high temperature was made to the scattering film and bluish-white double-ended film only. An aluminum screen (shading rate: 40%) was installed when the high temperature (above 30℃) was reached while the isoprene (solution of 2000 times) was sprayed 4 times every 7 days from the full development stage. The light transmittance was 12.6 - 13.4% for the scattering film, 10.5 - 10.8% for the bluish-white double sided film and 7.1% for the PE film in the first coating while it was 7.3% for the scattering film and 7.1% for the bluish-white double-sided film when the aluminum screen was installed in high temperature. The high, average and low values in the relative humidity were higher inside the facility than in the outside during the survey period. The area of leaf was the largest under the scattering film. The area of leaf was the largest for the scattered film under the aluminum shade of 40% shading followed by that of spraying of isoprene 4 times, and that of the no-treatment. As for the growth under ground, the growth of underground shoots increased by 40% in aluminum screen, 53.7% in shading and 26.1% in the spraying of isoprene 4 times than non-shading while there was no difference among other rain shelter materials. Conclusion : The result of the research showed that when the scattering film is selected as the rain shelter material film for the cultivation of Ginseng, it is necessary to shade the sunlight as much as 40% by using the aluminum screen or the shading net to reduce the high temperature damage.

Emission rates of biogenic hydrocarbon emitted from broad-leaved trees grown at Jeju Island were estimated using a dynamic enclosure method. Leaf temperature, PAR and relative humidity were monitored during the sampling time. The emission rates of isoprene and monoterpene were measured for five plants(Carpinus laxiflora, Quercus serrata, Styrax japonicus, Quercus acutissima, Quercus crispula) during the sampling period at the Halla mountain sites. Among five tree species, the highest isoprene emission rate of 10.60 ㎍ gdw-1hr-1 was observed for Quercus serrata. The seasonal emission rates were the highest during summer and the emission of isoprene was highly affected by light and temperature variations. The highest emission rate of isoprene was occurred between 13:00 and 14:00, but isoprene was not emitted in nighttime because of the absence of light.

The estimation of a biogenic volatile organic compound (BVOC, especially isoprene) and the influence of isoprene emissions on ozone concentrations in the Greater Busan Area (GBA) were carried out based on a numerical modeling approach during a high ozone episode. The BVOC emissions were estimated using a biogenic emission information system (BEIS v3.14) with vegetation data provided by the forest geographical information system (FGIS), land use data provided by the environmental geographical information system (EGIS), and meteorological data simulated by the MM5. Ozone simulation was performed by two sets of simulation scenarios: (1) without (CASE1) and (2) with isoprene emissions (CASE2). The isoprene emission (82 ton day -1 ) in the GBA was estimated to be the most dominant BVOC followed by methanol (56) and carbon monoxide (28). Largest impacts of isoprene emissions on the ozone concentrations (CASE2-CASE1) were predicted to be about 4 ppb in inland locations where a high isoprene was emitted and to be about 2 ppb in the downwind and/or convergence regions of wind due to both the photochemical reaction of ozone precursors (e.g., high isoprene emissions) and meteorological conditions (e.g., local transport).

The cost of conventional cultivation of ginseng (Panax ginseng C.A. Meyer) is very expensive, because shadow condition should be maintained during cultivation periods owing to inherently weak plant for high-temperature. Therefore, application of plant biotechnology may be possible to overcome these difficulties caused by conventional breeding of ginseng. Transgenic plants were produced via Agrobacterium tumefaciens Gv3101, both carrying the binary plasmid pBI121 mLPISO with nptII and Iso (isoprene synthase) gene. Integration of the transgenes into the P. ginseng nuclear genome was confirmed by PCR analysis using nptII primers and Iso primers. RT-PCR result also demonstrated the foreign isoprene synthase gene in three transgenic plant lines (T1, T3, and T5) which was expressed at the transcriptional level. When whole plants of transgenic ginseng were exposed to high temperature at 46℃ for 1 h, a non-transformed plant was wilted from heat shock, whereas a transgenic plant appeared to remain healthy. We suggest that the introduction of exogenous isoprene synthase is considered as alternative methods far generating thermotolerance ginseng.

The standard emission rate(ERs) of isoprene was quantitatively measured in situ from Quercus mongolica Fischer that dominates more than about 85% of domestic oak trees. The ERs values in spring and summer were similar to 64.4 and 58.1 (㎍C/gdw/hr), respectively. The ERs in autumn, 7.06(㎍C/gdw/hr), was about 8～9 times lower than those in spring and summer. The coefficient of determination (r2) between ERs and CL․CT ranged from 0.593 to 0.836. The correlation coefficients between the ERs and PAR, the ER and temperature suggested that ERs have strong correlation with PAR(photosynthetically active radiation) and temperature. In addition, the high values of PAR, temperature, and ERs were found in the time zone of 15:00 ～17:00(spring), 15:00 ～ 16:00(summer), and 14:00 ～ 15:00(autumn).