본 연구는 염류집적 국화 재배지 토양적응성 인산분 해미생물 탐색하고 선발된 미생물 시용을 통한 염류집 적 국화 재배지 토양에서의 토양 화학성의 변화를 조 사하였으며 이를 통하여 염류 집적 국화 재배지 토양 환경 개선 기술을 개발하고자 수행되었다. 시험에 사용 된 인산분해미생물은 염류집적토양에서 분리된 Pseudomonas putida(KSJ11), Acinetobacter calcoaceticus (KSJ3) 및 Acinetobacter calcoaceticus (WP20) 3종류 이었으며 미생물의 제형은 버미큘라이트에 혼합되어 있 는 상용화된 제품을 이용하였다. 시험장소는 광주광역 시 광산구 소재 신우화훼농장의 15년간 작물이 재배되 어 염류집적현상이 나타나는 국화재배지에서 처리구 82 m2에 각각의 미생물 제재 250 L씩 시용하였다. 염 류집적이 이루어진 국화재배온실에 처리된 인산분해미 생물 Acinetobacter calcoaceticus(KSJ3; WP20)는 유 효인산을 효율적으로 분해하는 것으로 나타났으며, 특히 Acinetobacter calcoaceticus(WP20)는 염류의 분 해능력이 높았다. 인산분해미생물 시용에 따라 토양내 칼륨, 칼슘 및 마그네슘의 함량의 증가가 A. calcoaceticus(KSJ3; WP20)처리구에서 뚜렷하게 나타났 으며 이러한 변화의 영향으로 판단되는 토양내 전기전 도도도 증가되었다. 또한 인산분해미생물 시용은 선충 밀도의 감소효과를 나타내어 토양환경개선을 위한 재 료로 활용될 가능성을 나타내었다. 결과적으로 염류집 적이 이루어진 국화재배 온실에서의 인산분해미생물 시 용은 처리된 미생물의 종류에 따라 차이를 나타내었지 만 토양의 유효인산량 증가와 양이온의 유용화에는 분 명한 효과를 나타내었다. 따라서 염류집적 토양에서의 인산분해미생물 시용은 토양양분의 효율적인 사용을 가 능하게 할 수 있는 방안이 될 수 있기 때문에 시비량 절감 등의 방법으로 활용할 수 있다고 판단되었다.
본 연구는 토양 염도(EC)에 따른 토마토의 생육효과를 검토코자 토양 중 염류농도(EC)를 각각 1.0, 2.5, 5.0 및 7.5dS·m-1로 두어 폿트 실험을 수행하였다. 토마토의 초장, 생체중, 건물중 등 생육은 토양 중 염류농도가 높을수록 억제되었으며 특히 EC 5.0dS·m-1 이상의 염류농도에서 큰 차이를 나타내었다. 지상부의 생체중과 건물중은 초장과는 달리 EC 7.5dS·m-1에서 감소하였다. 반면 뿌리의 생체중과 건물중은 지상부와는 달리 EC 5.0dS·m-1까지는 차이가 없었으나 EC 7.5dS·m-1서는 매우 감소하였다. 평균과중은 EC 5.0dS·m-1에서 92g으로 EC 1.0dS·m-1 129g보다 37g이나 가벼웠고 착과수는 평균과중과는 달리 EC 7.5dS·m-1에서는 매우 감소하였다. 수량은 EC 5.0, EC 7.5dS·m-1에서 각각 3,810, 3,216kg/10a로 EC 1.0dS·m-1의 5,488kg/10a보다 각각 31%, 41% 감소하였다. 토마토 과실의 당도와 산도는 염류농도가 높을수록 증가하는 경향이었으며 토양 중 EC 5.0dS·m-1 이상에서 과실당도가 5.2% 이상 증가하였다. 잎의 수분퍼텐셜 및 엽록소, 기공전도도 및 광합성 함량은 염류농도가 높을수록 억제되었다. 총 T-N, P 및 Na 함량은 염 농도가 높아질수록 증가하는 경향이었으나, Ca, Mg 및 K 함량은 염류농도가 높을수록 감소하였다. Na 함량은 증가하였으며 다른 성분은 처리간에 차이가 없었다.
속리산 국립공원 내 용바위골 지역(a.s.1. 560∼640 m)의 신갈나무림에서 토양에 축적된 유기탄소, 질소, 인 및 칼륨의 함량을 측정하고 또 O1son(1963)의 부지수곡선 모델을 적용하여 낙엽의 분해상수(k)와 분해시간(t)를 측정하였다. 유기탄소량은 L층 231.25 g m-2, F층 291.50 g m-2, H층 166.91 g m-2, 그리고 A1층 174.51 g m-2, 로 L층과 F층에서 높
본 연구는 토양에의 고농도 Na 및 Cl 염류처리가 토마토의 생육과 무기성분 흡수, 광합성 속도 및 수분 포텐셜에 미치는 효과를 검토코자 수행되었다. 초장, 생체중, 건물중 등 생육은 대조구에 비해 모든 염 처리구에서 억제되었으나, 토양의 pH와 EC와는 관계가 없었다. 토마토의 생육억제 효과는 Na계열에서는 Cl, SO4, CO3, PO4, NO3 순으로, 그리고 Cl 계열에서는 Na, K, Mg, NH4, Ca순으로 컸으며, Na 계열이 Cl 계열보다 컸다. 토마토의 수량은 대조구보다 모든 염 처리구에서 30%~10%적었으며,특히 NaCl처리구에서 더욱 적었다. 엽록소 함량, 광합성 속도, 기공전도도는 대조구에 비해 염 처리구에서 낮았다. 무기양분 함량은 대조구보다 모든 염류에서 낮았다. N 함량은 NaNO3, NH4Cl 및 대조구가 11% 내외로 가장 높았으나 Na 계열에서는 NaCl 및 NaHCO3 처리구가, Cl 계열에서는 KCI 처리구가 5.5~6.0% 내외로 낮았다. K 함량은 Cl 계열보다 Na 계열이 적었으며, 특히 NaCl과 Na2SO4 처리구에서 더욱 낮았다. Mg 및 Ca 함량은 대조구보다 낮았으며, NaCl과 KCl 처리에서 매우 낮아 Na 및 K 이온과 상당한 길항관계를 보였다 전반적으로 각 이온의 흡수는 KCl및 NaCl처리구에서 가장 낮은 경향이었다.
This study was conducted to analyze seasonal variations of de-icing salt ions harvested from soils and plants according to salt damage of Pinus densiflora f. multicaulis, a evergreen conifer, on roadsides. Pinus densiflora f. multicaulis was divided into three groups referred to SD, ND, and WD (serious salt damage (SD) = 71 100%, normal salt damage (ND) = 31 70%, and weak salt damage (WD) = 0 30%) based on the degree of visible foliage damage, and measured acidity (pH), electrical conductivity(EC), and de-icing salt ions (K+, Ca2+, Na+, and Mg2+) harvested from soils and plants. The results indicated that acidity, electrical conductivity, and de-icing salt ions of soils and plants were significantly affected by seasonal variation and salt damage. In addition, a strong positive liner relationship was observed in plants between the concentration of de-icing salts and salt damage in spring, while the relationship among seasonal variation and salt damage in soil were not significant. The results from this study has important implications for the management of conifer species in relation to salinity and roadsides maintenance.
Background : This study examined EC in soil depending on leaking water rate of sun shading facilities and conducted experiments to establish the proper leaking water rate for ginseng depending on rainfall.
Methods and Results : For leakage examination, rainfall flowing into a ridge. As sun shading facilities of ginseng to examine leakage, four kinds such as Blue-Pe-sheet, Pe4 (four–layered polyethylene net) + Pe2 (two–layered polyethylene net), Pe4, Pe2 were installed. As for leakage, a plastic box (23 × 30 × 30 ㎝) was installed on the ridge of ginseng field and outside, rainfall into the box during precipitation was examined, and the leakage quantity was calculated as the ratio of the quantity into the ginseng field regarding rainfall outside. The leakage quantity was examined a total of six times on July 2, July 3, August 24, August 30, August 31, and September 4. Regarding EC in soil, WT–1000n (www.rfsenser.co) which is a EC measuring instrument was used, and the average was calculated through 3 repeated examinations. There are little differences in the leakage quantity depending on the sun shading with 0.1% of the Blue-Pe-sheet, 2.3% of Pe4 + Pe2, 4.3% of Pe4, and 30.7% of Pe2. At the leakage rate of 0.1%, EC decreased from 1.52 ds/m on July 3 to 1.04 ds/m on August 8, and increased again to 1.54 ds/m on September 3 At the leakage rate of 2.4%, EC changes were lower than that of the leakage quantity of 0.1%, and similar results depending on periods were found. At the leakage rate of 4.3%, salt concentration was measured at 0.92 ds/m on July 3, decreased since then, increased to 0.90 ds/m on September 3, and overall concentration was less than 1.0 ds/m. At the leakage rate of 30.7%, EC was the lowest at 0.46 ds/m and similar results were found since then.
Conclusion : The differences in leakage quantity depending on sun shading facilities of ginsengs affected EC in soil, and EC became lower with more leakage quantity. As for the leakage quantity to maintain the EC in soil proper for ginseng growth and development lower than 1.0 ds/m, it was found to be effective to control the leakage quantity at 30% in May - June, and September - October when there are less rainfall, and at 2 - 5% in July - August when there are heavy rainfall.
Background : Ginseng sometimes develops physiological disorders as EC of soil accumulates in sun shading facilities with no leaking water. In addition, it is difficult to make moisture content of soil and EC stably suitable for ginseng growth and development in the same sun shading facility. Accordingly, this study examined EC in soil depending on leaking water rate of sun shading facilities and conducted experiments to establish the proper leaking water rate for ginseng depending on rainfall.
Methods and Results : For leakage examination, rainfall flowing into a ridge. As sun shading facilities of ginseng to examine leakage, four kinds such as Blue-Pe-sheet, Pe4 (four–layered polyethylene net) + Pe2 (two–layered polyethylene net), Pe4 , Pe2 were installed. As for leakage, a plastic box (23 × 30 × 30 ㎝) was installed on the ridge of ginseng field and outside, rainfall into the box during precipitation was examined, and the leakage quantity was calculated as the ratio of the quantity into the ginseng field regarding rainfall outside. The leakage quantity was examined a total of six times on July 2, July 3, August 24, August 30, August 31, and September 4. Regarding EC in soil, WT-1000n which is a EC measuring instrument was used, and the average was calculated through 3 repeated examinations. There are little differences in the leakage quantity depending on the sun shading with 0.1% of the Blue-Pe-sheet, 2.3% of Pe4 + Pe2, 4.3% of Pe4, and 30.7% of Pe2. At the leakage rate of 0.1%, EC decreased from 1.52 ds/m on July 3 to 1.04 ds/m on August 8, and increased again to 1.54 ds/m on September 3 At the leakage rate of 2.4%, EC changes were lower than that of the leakage quantity of 0.1%, and similar results depending on periods were found. At the leakage rate of 4.3%, salt concentration was measured at 0.92 ds/m on July 3, decreased since then, increased to 0.90 ds/m on September 3, and overall concentration was less than 1.0 ds/m. At the leakage rate of 30.7%, EC was the lowest at 0.46 ds/m and similar results were found since then.
Conclusion : Differences in leakage quantity depending on sun shading facilities of ginseng affected EC in soil, and EC became lower with more leakage quantity. For the leakage quantity to maintain the EC in soil proper for ginseng growth and development lower than 1.0 ds/m, it was found to be effective to control the leakage quantity at 30% in May - June, and September - October when there are less rainfall, and at 2 - 5% in July - August when there are heavy rainfall.
기후변화에 따른 해수면 상승으로 인하여 해안지역의 지하수계에 해수침투가 가중된다. 지하수의 염분농도가 증가하면 지하수면 상부의 불포화 토양에서도 염분 농도가 증가할 수 있으며, 이는 농경지에서 작물피해를 일으킬 수 있다. 해수면이 상승함에 따라 내륙의 지하수위도 함께 상승한다. 이는 불포화 토양층의 두께를 감소시켜 해안 저지대의 경작에 피해를 끼칠 수 있다. 본 연구에서 지하수 해수침투는 3차원 모델, 토양 염류화 평가는 연직 1차원 모델을 합성 적용하여 해안 농경지에 대한 해수면 상승 피해를 평가하는 방법을 개발하였다. 3차원 해수침투 모델에서 지하수면의 수위 와 농도분포를 계산하고 최상부 절점 중에서 염분 농도가 기준 값 이상인 절점에서 지하수면과 지표면 사이의 토양층에서 연직 1차원 모델링으로 토양층의 염분 농도와 불포화대 두께를 계산하였다. 농경지의 토양 염류화는 작물의 뿌리 심도에서 보통 작물의 생육한계 염분농도를 기준으로 판 단하였다. 개발된 모델링 방법을 가상의 간척농경지에 적용하였다. 해수면 상승자료로 IPCC의 RCP 4.5와 8.5 시나리오를 사용하였다. 평가 결과 는 2050년과 2100년에 대하여 제시하였다. 연구결과 대상지역에서 기후변화 시나리오 RCP 8.5에서 2100년에는 지하수 염류화 피해 면적은 간 척지 육지면적 대비 7.8%, 염류화 토양 면적은 6.0%, 불포화층의 두께가 뿌리심도보다 적은 지역의 면적은 1.6% 증가하는 것으로 분석되었다.
Background : Excessively high concentration of sodium ion causednutrient deficiency and significantly decrease growth. This study was carried out to determine the limiting concentration range of sodium ion in the soil of ginseng field.
Methods and Results : The growth of the ginseng cultivar Chunpoong reduced with increase in salinity, and the rate of growth reduction was higher in shoots than that of roots. Particularly, ginseng plants cultivated at high level of nitrate nitrogen or sodium may suffer delayed development and stunted growth. Chlorophyll damage occurred on the leaves of ginseng planted in relatively high levels (> 0.2 c㏖+/㎏) of sodium ion, as determined by the fluorescence reaction. The incidence of physiological disorder in ginseng cultivated at 249 sites was correlated with the concentration of sodium ion in the soils. About 74% of ginseng fields in which physiological disorders occurred had concentrations of sodium ion in soil greater than 0.2 c㏖+/㎏. In contrast, the concentration of sodium ions at 51 of 85 sites where no damage occurred was relatively (0.05 c㏖+/㎏- 0.15 c +/㎏).
Conclusions : The concentration of sodium ion in soil of ginseng fields can be classified into three levels optimum (≤ 0.15), permissible allowance (0.15 - 0.2) and excessive (> 0.2).
After examining the difference in the photosynthesis rate of corn according to the planting distance, the distance of 40 × 40 cm showed the lowest rate by 23 days after transplanting (May 31); however, there was no significant difference in the photosynthesis rate due to increased salt tolerance in the plant as time went by. As for the difference in growth features of a plant, the planting distance of 40×40cm showed a growing disorder due to the influence of salt by 23 days after transplantation (May 31); however, there was a desirable growth as time went by. For the difference in the salt content within a plant, the planting distance of 40×40cm tended to be higher than other planting distances, and the K⁺ content is much higher than other kinds of salt after examining the difference in salt absorption. As for the correlation between saline components within a plant, there was a significant negative correlation among K⁺, Ca²⁺, and Na⁺ while there was a significant positive correlation among Mg²⁺, Ca²⁺, and Na⁺. After examining the effectiveness of salt removal from soil according to corn cultivation, the planting distance of 30×30㎝ showed a remarkable decrease by 37 days, compared with 23 days, after transplantation in K⁺ by 28%, Ca²⁺ by 36.6 %, Mg²⁺ by 30.6 %, and Na⁺ by 22.9 %. And the salt content is higher in surface soil than in subsoil.