• 한국환경농학회지
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• 제18권3호
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• pp.287-291
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• 1999

Mycorrhizae가 형성된 식물에서 인광석이 인산급원으로 이용될 수 있는 지를 검토하기 위하여 온실 실험을 수행하였다. 멸균된 제주 화산회토에 인광석과 용성인비를 100및 200 mg P/kg 수준으로 처리하고 토마토를 재배하였는데 토마토는 mycorrhizae 접종구와 비접종구를 두고 3개월간 재배한 후 식물생육과 인을 비롯한 무기영양소 흡수를 조사하였다. 용성인비 처리구에 비하여 인광석 처리구에서 생육이 현저히 저해되었는데 이는 인광석처리에 따른 토양중의 유효인산 부족 때문일 것이다. 용성인비와 인광석 200 mg P/kg 처리구에스는 mycorrhizae균의 접종에 따라 건물량이 증가하였다. Mycorrhizae 형성율과 토양중의 포자밀도는 인광석 처리구에서 낮았다. 식물체중의 인 함량은 용성인비 처리구에서 높았으며, mycorrhizae 처리 효과는 없었다. N, K, Ca, Mg 등의 함량에서도 처리별로 차이는 없었다. 이상의 결과를 볼 때, 제주 화산회토양에서 $100{\sim}200\;mg\;P/kg$ 수준의 인광석 처리로는 mycorrhizae 형성 여부에 상관없이 적정 식물생육을 위한 인 공급이 될 수 없는 것으로 판단되었다.

• 한국환경과학회:학술대회논문집
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• 한국환경과학회 1999년도 임시총회 및 가을 학술발표회 초록집 The Korean Environmental Sciences Society
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• pp.221-223
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• 1999

The adsorption and leaching of organophosphorus pesticide, EPN are investigated in Namwon soil(black volcanic soil), Aewol soil(very dark brown volcanic soil) and Mureung soil(dark brown nonvolcanic soil) sampled in Cheju Island. The organic matter of Namwon soil, Aewol soil and Mureung soil is 19.8%, 6.2%, 2.4%, respectively. The cation exchange capacity of Namwon soil, Aewol soil and Mureung soil is 24.8 meq/100g, 13.0 meq/100g, 9.5 meq/100g, respectively. The Freundlich constant, K value, is 89.4, 26.9 and 9.25 for Namwon soil, Aewol soil and Mureung soil, respectively. The K value of Namwon soil with very high organic matter content and cation exchange capacity was the highest for Aewol soil and Mureung soil. The Freundlich constant, 1/n, show a high correlation with organic matter content, i.e., it is less than unity for organic matter rich soil of Namwon soil and greater than unity for organic matter poor soil of Mureung soil. The leaching of EPN is slower for Namwon soil with high K values, and faster for Mureung soil with low K values. The results of the study is demonstrated the potential of pollution for EPN have little leached into soil environment.

• 한국초지조사료학회지
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• 제21권4호
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• pp.181-190
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• 2001

This study was conducted to investigate the effect of swine liquid manure(SLM) and phosphorus fertilizer from September, 1998 to July, 1999 on the soil fertility on Italian ryegrass field, Cheju volcanic ash soil. pH(lst investigated), Mg (2nd investigated) and Cu content (2nd investigated) on soil grown by Italian ryegrass were significantly increased by an increase of fertilizer P(P

• 한국환경과학회지
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• 제8권3호
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• pp.379-386
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• 1999

The adsorption and leaching of organophosphorus pesticides (phenthoate, diazinon, methidathion) were investigated in Namwon soli(black volcanic soil), Aewol soil(very dark brown volcanic soil) and Mureung soil(dark brown nonvolcanic soil) sampled in Cheju Island. The Freundlich constant, K value, was 52.4, 31.3 and 27.7 for phenthoate, diazinon and methidathion in Namwonsoil, respectively and decreased in the order of phenthoate, diazinon and methidathion among the pesticides. The K value of phenthoate was 52.4, 15.9 and 5.9 for Namwon, Aewol and Mureung soil, respectively and was the highest for Namwon soil with very high organic matter content and cation exchange capacity(CEC). The Freundlich constant, 1/n, showed a high correlation with organic matter content, i.e., its value was less than unity for organic matter rich soil(Namwon soil) and greater than unity for organic matter poor soil(Mureung soil). Total recoveries of pesticides in soil and leachate with leaching in soil column, were in the range of about 74~86%. The leaching of pesticides was less for phenthate with high K values, and more for methidathion with low K values among the pesticides. It was slower for Namwon soil with high K values, and more for methidathion with low K values among the pesticides. It was slower for Namwon soil with high K values, and faster for Mureung soil with low K values among the soils.

• 한국토양비료학회지
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• 제16권1호
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• pp.20-27
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• 1983

제주도(濟州道) 화산회토양유기물(火山灰土壌有機物)의 화학성(化学性), 유기물(有機物) 성상(性狀) 및 부식산(腐植酸)의 광학적(光学的) 특성(特性)을 알고져 수종(数種)의 화산회토양(火山灰土壌)을 공시(供試)하여 실내시험(室內試験)한 결과(結果)를 요약(要約)하면 다음과 같다. 가. 토양(土壌)의 화학적(化学的) 성질(性質) 1) 화산회토양(火山灰土壌)은 비화산회토양(非火山灰土壌)에 비(比)하여 유기물(有機物)(4~27%), 유효규산(有効珪酸)(291~884ppm), 활성(活性) 알루미늄(150~478ppm) 및 활성철함량(活性鉄含量)(0.77~0.86%)이 많고 반대(反対)로 유효인산(有効燐酸)(4~15ppm) 함량(含量)이 현저(顕著)히 낮았다. 2) 가리(加里), 석화(石火), 고토등(苦土等)은 밭의 경우 화산회토양(火山灰土壌)에서 높은 편이나 삼림지(森林地) 및 유휴지토양(遊休地土壌)은 낮은 경향(傾向)을 보였다. 3) 화산회토양(火山灰土壌)은 규반비(珪礬比) 및 규산(珪酸)/유기물비(有機物比)가 낮은 반면(反面) K/Ca+Mg, Al/Fe(활성(活性)) 및 C/P비(比)가 현저(顕著)히 높았다. 나. 유기물(有機物) 및 질소분별정량(窒素分別定量) 1) 화산회토양(火山灰土壌)은 유기물(有機物)의 총탄소중(総炭素中) Humin-C의 비율(比率), 유기물중(有機物中) Humin산(酸) 그리고 Humin중(中) C/N율(率)이 비화산회토양(非火山灰土壌)보다 현저(顕著)히 높았다. 2) 화산회토양(火山灰土壌)은 비화산회토양(非火山灰土壌)에 비(比)하여 총질소(総窒素), 산(酸) 및 알카리가용성(可溶性) 질소함량(窒素含量)이 현저(顕著)히 높은 반면(反面) 총질소중(総窒素中) 무기태질소(無機態窒素)로 방출(放出)될 수 있는 무기화율(無機化率)은 높지 않았다. 다. 토양부식(土壌腐植)의 형태(形態) 1) 화산회토양(火山灰土壌)은 비화산회토양(非火山灰土壌)에 비(比)하여 광흡(光吸) 수능(收能)이 높고(K600, RF치(値), ${\delta}logK$) 부식화도(腐植化度)가 진전(進展)될수록 색농도(色濃度)가 짙은 것으로 나타났다. 2) 화산회토양(火山灰土壌)은 산화제(酸化劑)에 대(対)한 저항성(抵抗性)이 높고 산(酸) 및 알카리 가수분해성(加水分解性)이 강(强)하여 부식화도(腐植化度)가 높아 부식(腐植)의 자연분해(自然分解)가 극(極)히 어려운 것으로 나타났다. 라. Humin의 관능기조사(官能基調査) 화산회토양(火山灰土壌)의 유출부식산(油出腐植酸)의 관능기(官能基)는 phenolic-OH기(基), Alcoholic-OH기(基) 및 Carboxyl기(基)가 많고 비화산회토양(非火山灰土壌)은 Methoxyl기(基) 및 Carbonyl기(基)가 많았다. 마. 부식산(腐植酸)의 흡광도(吸光度) 1) 공시토양(供試土壌)의 가시광역(可視光域)은 200~500nm부근의 단파장영역(短波長領域)이었으며 주로 350, 420, 450 및 480nm 에서 4개(個)의 흡광곡선(吸光曲線)을 나타내었다. 2) 화산회토양(火山灰土壌)인 흑악통(黑岳統)은 362nm부근에서 단일(單一)의 높은 흡광도(吸光度)를 보였으며 비화산회토양(非火山灰土壌)인 영악통(永楽統)은 360nm와 390nm에서 2개(個)의 단순(單純)한 높은 흡광대(吸光帶)를 나타내었다. 마. 분해촉진제(分解促進剤) 처리효과(處理効果) 화산회토양(火山灰土壌)에 대(対)한 분해촉진효과(分解促進効果)는 이도통(統)은 역분해성(易分解性) 유기물(有機物) 첨가(添加)에 따른 "Priming Effect"가 증가(增加)되었으며 남원(南元)과 흑악통(黑岳統)은 Na-Pyrophosphate의 첨가효과(添加効果)가 있었다.

• 한국토양비료학회지
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• 제13권2호
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• pp.65-70
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• 1980

우리나라 토양(土壤)의 입도분석(粒度分析)에 적합(適合)한 분산제(分散劑)를 선정(選定)하기 위하여 대표토양(代表土壤) 18점(点)에 대(對)한 표토(表土) 및 심토(深土)의 입도분석(粒度分析) 결과(結果)는 다음과 같다. 1. 토양입자(土壤粒子)가 작을수록 분산제별(分散劑別) 분산능력(分散能力)의 차이(差異)가 커지는 경향(傾向)으로 점토입자(粘土粒子)(<0.002mm)의 분석치(分析値)에 있어서 분산제(分散劑)에 따라 차이(差異)가 컸었다. 2. 분산율(分散率)은 Sodium Pyrophosphate가 가장 높고 다음으로 Sodium Hexametaphophate, Ammonium Hydroxide, Sodium Hydroxide, Sodium Oxalate 순(順)이었다. 3. Sodium Hexametaphosphate는 Volcanic Ash Soil만을 제외(除外)하고 우리나라 모두 토양(土壤)의 입도분석(粒度分析)에 있어서 분산제(分散劑)로써 사용(使用)할 수 있을 것으로 본다. 4. Volcanic Ash Soil의 분산율(分散率)은 분산제(分散劑)를 사용(使用)하지 않은 경우보다 오히려 감소(減少)되는 경향(傾向)이 있으므로 이의 분산방법(分散方法)의 선정(選定)에는 특별(特別)한 주의(注意)가 요망(要望)된다.

• 한국토양비료학회지
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• 제9권2호
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• pp.93-98
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• 1976

본(本) 연구(硏究)는 제주도토양(濟州道土壤)의 특성(特性) 및 생성(生成)에 관(關)한 논문(論文)의 일환(一環)으로 수행(遂行)되었으며 화산활동(火山活動)의 영향(影響)으로 이루어진 두드러진 현상중(現象中)의 하나인 polysequum토양(土壤)의 특성(特性)을 구명(究明)하기 위(爲)하여 형태적(形態的), 이화학적(理化學的), 광물학적(鑛物學的) 토양미세형태학적(土壤微細形態學的)으로 조사(調査)한 결과(結果)는 다음과 같다. 1. 공시토양(供試土壤)의 기반(基盤)은 현무암잔적층(玄武岩殘積層)(III)이고 화산사탄층(火山砂炭層)(II)과 화산회층(火山灰層)이 쌓여서 이루어졌다. 2. 따라서 화산회(火山灰), 화산사암층(火山沙岩層), 현무암잔적층(玄武岩殘積層)의 암석학적(岩石學的) 불연속성(不連續性)이 현저(顯著)하여 화산회층(火山灰層)은 미사질양토(微砂質壤土), 화산사암층(火山砂岩層)은 사토현무암층(砂土玄武岩層)은 미사질식토(微砂質植土)이었다. 3. 화산사암층(火山砂岩層)은 아직 토양(土壤)으로 발달(發達)이 덜 되어있으며 그 특성(特性)은 현무암층(玄武岩層)보다 화산회(火山灰)에 유사(類似)하였다. 4. 주요(主要) 점토광물(粘土鑛物)은 화산회층(火山灰層)에서는 Allophane, 현무암잔적층(玄武岩殘積層)에서는 kaoline, vermiculite와 Illite이였다. 5. 공시토양(供試土壤)은 대체(大體)로 생성년대(生成年代)가 오래지 않은 것으로 판명(判明)되었다. 이와같은 사실(事實)은 화산회토(火山灰土)는 초기풍화상태(初期風化狀態)에 있었고 화산사암층(火山砂岩層) 역시(亦是) 풍화(風化)가 진행(進行)되는 중(中)이며 현무암잔적층(玄武岩殘積層)에는 점토(粘土)의 집적층(集積層)이 없다는 근거(根據)로 추리(推理)된다.

• 한국지하수토양환경학회:학술대회논문집
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• 한국지하수토양환경학회 2003년도 총회 및 춘계학술발표회
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• pp.397-400
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• 2003

In this study, humic and fulvic acids in soils at the vicinity of domestic atomic power plants(NPPs), located in Yungkwang(YK), Uljin(UJ), Kori(KR), Koseong(KS), Wolseong(WS) area, and in volcanic ash soils of the Cheju island(Mt. Hanla(HL), Manjanggul(MJ)) were isolated, and characterized using chemical(elemental analysis, proton exchange capacity, molecular size distribution) and spectroscopic(UV/Vis., IR, FL, $^{13}$ C NMR spectra) methods. The results were compared with one another and compiled for their DB establishments. The humic substances distribution (humic acid, fulvic acid, Humin) in the soils were also determined by IHSS standard method. Main purpose of this study was to provide a basic data needed to evaluate the effect of humic substances on the migrational behaviour of radioactive elements in contaminated surface soil.

• Journal of Forest and Environmental Science
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• 제33권2호
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• pp.136-146
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• 2017

We selected 6 plots ($100m^2$) located 2.2-3.8 km from Minamidake Crater on the north flank of Sakurajima Volcano. We conducted a field study to investigate the effects of volcanic activity on vegetation succession and surface erosion rate. The results showed that trees growing in plots further from the crater had a greater diameter at breast height (DBH), total height, and age. In addition, these plots had a greater number of woody plants and species, as well as a greater total cross-sectional area at breast height. The Fisher-Williams index of diversity (${\alpha}$) and the proportion of evergreen broad-leaved trees were higher in plots located further from the crater. Vegetation succession in these plots was not at the level of a climax forest. From 1972 to 2015, the timing for active volcano, the depth of volcanic ash layer, the dry density, and the pH of ground surface were lower for plots located further from the crater. Furthermore, the average annual sheet erosion from 1972 to 2015 was also lower for plots located further away from the crater. Overall, plots further away from the crater have a better environment for vegetation growth and a lower dry density of the volcanic ash surface layer. It is thought that lower dry density results in increased soil permeability, which impedes surface flow. In order to prevent debris-flow disasters, caused by mud and rock flow resulting from impaired soil penetrability, it is essential to promote soil development and restore penetrability by artificial vegetation restoration.

• 한국토양비료학회지
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• 제11권4호
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• pp.247-262
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• 1979

Majority of reclaimable soils in hillside lands in Korea are red yellow soils, with exception in Jeju island, where most of reclaimable hillside lands are composed of volcanic ash soils. Songjeong, Yesan and Samgag series are the major soil series of red yellow soils which are available for the reclamation. When observed in the fields, they are distinguished as reddish brown clay loam, red yellow sand loam and yellowish brown sand loam. They have moderately good physical properties but their chemical properties are generally poor for crop cultivations. The chemical properties of red yellow soils, as compared to long time cultivated (matured) soils, are characterized by very low pH, high in exchangeable Al content and phosphorus fixation capacity. Also extraodinary low available phosphorus and organic matter contents are generally observed. On the other, the chemical properties of volcanic ash soils are characterized by high armophous Fe and Al hydroxides and organic matter contents, which are the causative factors for the extremely high phosphorus fixation capacity of the soils. The phosphorus fixation capacity of volcanic acid soils are as high as 5-10 times of that of red yellow soils. Poor growth of crops on newly reclaimed red yellow soils are mainly caused by very low available P and pH and high exchangeable Al. Relatively high P fixation capacity renders the failure of effective use of applied P when the amount of application is not sufficient. Applications of lime to remove the exchangeable Al and relatively large quantity of P to lower the P fixation capacity and to increase the available P are the major recommendations for the increased crop production on red yellow hillside soils. Generally recommendable amounts of lime and P to meet the aforementioned requirements, are 200-250kg/10a of lime and $30-35kg\;P_2O_5/10a$. Over doses of lime. frequently induces the K, B, arid Zn deficiencies and lowers the uptake of P. In volcanic ash soils, it is difficult to alter the exchangeable Al and the P fixation capacity by liming and P application. This may be due to the peculiarity of volcanic ash soil in chemical properties. Because of this feature, the amelioration of volcanic ash soils is not as easy as in the case of red yellow soils. Application of P as high as $100kg\;P_2O_5/10a$ is needed to bring forth the significant yield response in barley. Combined applications of appropriate levels of P, lime, and organic matter, accompanied by deep plowing, results in around doubling of the yields of various crops on newly reclaimed red yellow soils.