• 헤리티지:역사와 과학
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• 제43권1호
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• pp.190-211
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• 2010

본 조사연구는 경상북도지역의 천연기념물 노거수 34개소의, 생육상태와 입지환경 및 주변환경 실태, 보호관리실태 등을 조사하고 분석함으로써, 향후 천연기념물 노거수의 관리방안 및 보호사업 수립에 기초자료로 제공하기 위한 목적으로 실시되었다. 조사대상지의 수형 수관 주간 건강 엽량 상태를 조사분석한 결과, 안동 송사동 소태나무와 청송 홍원리 개오동나무의 생육상태가 아주 불량한 것으로 조사되었다. 울진 수산리 굴참나무, 울진 후정리 향나무, 울진 쌍전리 산돌배나무, 청도 덕촌리 털왕버들, 문경 화산리 반송, 문경 대하리 소나무 등 6개소의 노거수도 생육상태가 불량하여 지속적인 보호사업과 관찰이 요구되는 대상지로 분류되었다. 입지별 생육현황을 분석한 결과 사람의 내왕이 잦고 뿌리생육공간이 협소한 인문 입지환경에서 자라는 노거수가 생육상태가 불량 것으로 조사 되었다. 따라서 사람의 내왕이 잦은 입지환경의 노거수는 생육공간 확보와 토양 환경개선에 역점을 두어야 할 것으로 사료된다. 수종별 생육현황을 조사한 결과 종합적인 생육상태는 느티나무, 참나무, 소나무 수종이 생육상태가 양호하였으며, 버드나무와 대상지가 1개소인 기타수종은 불량하였다. 향후 개체수가 적은 기타수종은 보호관리에 있어 세심한 관리가 필요하다. 주간의 생부비율을 조사한 결과 소나무, 은행나무, 느티나무가 양호하였으며, 향나무, 굴참나무, 버드나무, 기타수종은 불량하였다. 보호관리사업에 있어서는 외과수술은 점차 감소하고 있는 추세로서 대부분 유지관리가 이루어지지 않고 있어 파손된 곳이 많았으며, 지주관리나 쇠당김시설도 시급한 보수가 요구되는 곳이 여러군데 조사되었다. 향후 지자체 등 관리단체는 마을주민의 일상적인 보호관리방법이 아닌 전문가에 의한 체계적인 관리와 보호계획을 수립한 후 실시하는 세심한 보호사업이 필요하다. 생육공간 확보를 위한 토지매입이 필요한 곳이 11개소로 조사되었는데, 대체로 토지매입이 가능한 지역이므로 예산확보와 해당 주민 설득을 통한 토지 매입 추진이 요구된다.

• Journal of Preventive Medicine and Public Health
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• 제3권1호
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• pp.1-16
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• 1970

우리나라에서 공중보건상(公衆保健上) 중요(重要)한 연충류감염에 대(對)하여 1969년(年) 현재(現在) 실시(實施)한 관리(管理) 현황(現況)을 조사(調査)하였으며, 그 결과(結果)를 보면 1966년(年)부터 1969년(年)까지의 학생기생충검사 및 회충구충 사업(事業)에 있어서 그 간(間) 회충감염률의 저하(低下)를 별(別)로 가져오지 못하였음이 나타났으며 따라서 앞으로 본(本) 사업(事業)의 개선(改善) 또는 보다 적극적인 사업(事業)의 추진(推進)이 요망(要望)된다. 보건사회부(保健社會部)에서 지정(指定)한 지역(地域)에서 $1965{\sim}1968$년(年)의 4년간(年間)에 실시(實施)한 폐(肺) 및 간(肝) 디스토마 집단치료사업(集團治療事業)에 있어서는 추정환자수(推定患者數)의 감소(減少)를 크게 가져오지 못하여 사업(事業)의 부진(不振)함을 나타내었다. 구충제제조에 있어서 너무 많은 제조회사(製造會社)에서 많은 종류(種類)의 상품(商品)이 제조(製造)되어 난맥(亂脈)을 이루고 있었으며 따라서 구충제 제조허가(製造許可)에 있어서의 재고(再考)가 요구(要求)된다. 인분처리(人糞處理) 상황(狀況)에 있어서 도시지역(都市地域)에 있어서는 위생적(衛生的)인 하수도(下水道)가 미비(未備)되고 하수종말처리장(下水終末處理場)이 전연(全然) 없고 수거처리(收去處理)되고 있으며 한편 농촌지역(農村地域)의 인분처리(人糞處理)는 거의 수임상태(收任狀態)로 비위생적(非衛生的)이어서 기생충 전파(傳播)의 가장 큰 요인(要因)의 하나가 된다. 인분사용금지구역(人糞使用禁止區域)으로 지정된 전국(全國) 55개(個) 지역중(地域中) 34개(個) 지역(地域)에서 총(總) 170건(件)의 토양(土壤)(밭흙)을 채취하여 검사(檢査)한바 그중(中) 44%에서 회충난이 검출(檢出)되었다. 청정채소보급소(淸淨菜蔬補給所)와 일반시장(一般市場)에서 판매하는 각종 채소(菜蔬) 각(各) 64건(件)씩을 구입하여 검사(檢査)한바 회충난검출률은 보급소(補給所)의 것이 25%, 일반시장(一般市場)의 것이 36%로 나타났다. 전국(全國) 보건소(保建所)에서의 기생충병관리사업 실적(實績)과 기생충 검사능력(檢査能力)은 저조(低調)하였다. 보건사회부(保健社會部)의 기생충병 관리(管理) 예산(豫算)은 아주 적으며, 세로판후층도말법(厚層塗抹法)에 소요(所要)되는 실비(實費)를 산출(算出)한바 1건당(件當) 8원이었다. 기생충병 관리원칙(管理原則)은 기생충 자체(自體)의 생활사(生活史)를 중심(中心)으로 하는 요인(要因)과 이에 영향을 주는 제환경적(諸環境的) 요인(要因), 그리고 감염(感染)과 관계되는 인간숙주측(人間宿主側) 요인(要因)등의 여러가지 요인(要因)에 의(依)해서 발생(發生)되는 기생충감염의 생성과정중(生成過程中)의 어느 한 부분(部分) 또는 그 이상(以上)을 제거하는 방향으로 이루어지며, 그 방법에는 다음과 같은 사항들을 들수 있다. (1) 감염자(感染者)에 대(對)한 집단치료(集團治療)로서 감염(感染)의 근원(根源)이 되는 병원소(病原巢)를 제거(除去)한다. (2) 보충동물을 제거(除去)함으로써 인체감염(人體感染)과 관계되는 동물병원소(動物病原巢)를 제거(除去)한다. (3) 보충숙주의 배설물(排泄物)에 대(對)한 위생적(衛生的) 처리(處理)인바 여기에서 주요(主要)한 것은 도시지역(都市地域)에서의 완비(完備)된 하수도(下水道)와 하수종말처리장(下水終末處理場), 그리고 농촌지역(農村地域)에서의 비흡취식(非吸取式)인 위생적편소(衛生的便所)의 설치(設置) 등이며 이것은 우리나라에서의 인분비료사용(人糞肥料使用)의 폐지(廢止)와 국가경제(國家經濟)의 향상(向上)으로서 그 목적(目的)을 달성(達成)할 수 있게 된다. (4) 매개체(媒介體) 및 중간숙주(中間宿主)의 관리(管理)로서 토양(土壤)의 기생충오염방지, 식품위생(食品衛生), 곤충관리 그리고 패류관리(貝類管理) 등을 들 수 있다. (5) 비위생적(非衛生的) 태도(態度)와 폐습(弊習)의 개선(改善)으로서 기생충감염과 관계 있는 입분비료(入糞肥料)의 사용(使用), 식습관(食習慣) 및 개인위생(個人衛生) 등이 문제된다. (6) 화학예방(化學豫防) 및 예방접종(豫防接種)은 전술(前述)한 바와같은 전파예방(傳播豫防) 조치(措置)가 실패(失敗)하는 경우 체내(體內)에 침입(侵入)되는 기생충체를 체내(體內)의 방어력(防禦力)에 의(依)하여 그 감염(感染)의 성립(成立)과 성충에의 발육(發育)을 방지(防止)하려는 조치(措置)로서 이에 대(對)한 앞으로의 보다 적극적인 연구(硏究) 개발(開發)이 요망(要望)된다.

• 한국식품위생안전성학회지
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• 제34권1호
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• pp.40-51
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• 2019

인삼은 인삼산업법이라는 독립된 법률의 적용을 받으며 4~6년간의 장기 재배기간과 이동경작이라는 독특한 재배특성이 있고 타 작물도 생산하는 복합영농의 형태를 가지고 있는 농가가 많은 점 등 일반 작물과는 생산과정과 관리방법이 다르다. 따라서 GAP기준에 적합한 인삼 생산을 위해서는 GAP인증기준 항목별로 인삼농가의 실천수준을 파악하여 미흡한 점에 대해서 실천방안을 제시할 필요가 있다. 인삼에 대하여 GAP인증을 신청한 농가의 인증 취득률은 77.6%으로 기타 농산물의 94.1% 보다 낮았다. 미등록농약의 사용이나 토양 중금속 기준치 초과 등 서류심사 단계에서 13.7%가 부적합으로 판정되었으며, 현장심사결과 관리미흡으로 인증을 취득하지 못한 경우는 8.7% 이었다. 이는 기타 농산물에서 서류심사 부적합율 5.3%와 현장심사 부적합율 0.6%에 비하여 상당히 높은 것으로 인삼에 있어서 부적합율이 높은 원인을 분석하여 부적합율을 낮추는 방안 모색이 필요하다. 전체 72개 평가항목 중 10가지 주요 필수항목인 필수+ 기준에 대해 인삼은 2.65점으로 평가되어 기타 농산물의 2.81점 보다 다소 낮게 평가되었다. 특히 인삼농가에서는 토양 및 작물 병해충관리용 농약의 안전사용기준 준수가 각각 2.01점과 1.92점으로 평가받아 기타 농산물의 2.96점과 2.94점에 비하여 상대적으로 낮아 인삼농가의 농약사용에 좀 더 많은 주의가 필요하다. 일반 필수기준인 필수기준에서도 인삼은 2.33점으로 기타 농산물의 2.58점 보다 낮게 평가되었다. 인삼이 기타 농산물에 비하여 상대적으로 낮게 평가된 항목은 영농기록의 1년 이상 보관 항목(1.98점), 품질보증 종자 사용 항목(1.31점), 토양 및 작물 병해충 관리용 농약 사용 기록 항목(1.38점과 177점), 농약보관장소 표시물(1.69점), 수확후저장장소 관리 항목(1.67점), 작업 전 후 손 세척 항목(1.00점), 작업자 위생복장 착용(1.50점) 작업자 안전위생교육 항목(0.82점), 위해요소관리계획서(1.96점) 등으로 이 항목들은 인삼농가들이 앞으로 개선을 해야 할 필요가 있다. 또한 전체 72개 항목 중 인삼에 적용되지 않는 항목이 12개 항목(필수 10개, 권장 2개)에 달한다. 따라서 기존의 인증기준으로는 인삼 생산과정에 대해 실효성 있는 평가를 하기에는 부적절한 것으로 판단된다. 결론적으로 인삼에 대한 GAP인증의 확대를 위해서는 차별화된 인증기준이 필요하며, 인삼 농가에 대한 GAP관리교육이 보다 체계적이고 현장중심으로 수행될 수 있는 프로그램의 개발이 필요하다.

• Journal of the Korean Wood Science and Technology
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• 제2권4호
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• pp.4-14
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• 1974

The total forest land area in Korea accounts for some 67 percent of the nation's land total. Its productivity, however, is very low. Consequently, forest production accounts for only about 2 percent of the gross national product and a minor proportion of no more than about 5 percent versus primary industry. In this case, however, only the direct income from forestry is taken into account, making no reference to the forestry output induced by other industrial sectors. The value added Or the induced forestry output in manufacturing the primary wood products into higher quality products, makes a larger contribution to the economy than direct contribution. So, this author has tried to analyze the structure of forestry and compute the repercussion effect and the induced output of primary forest products when utilized by other industries for their raw materials, Hsing the input-output table and attached tables for 1963 and 1966 issued by the Bank of Korea. 1. Analysis of forestry structure A. Changes in total output Durng the nine-year period, 1961-1969, the real gross national product in Korea increased 2.1 times, while that of primary industries went up about 1. 4 times. Forestry which was valued at 9,380 million won in 1961, was picked up about 2. 1 times to 20, 120 million won in 1969. The rate of the forestry income in the GNP, accordingly, was no more than 1.5 percent both in 1961 and 1962, whereas its rate in primary industries increased 3.5 to 5.4 percent. Such increase in forestry income is attributable to increased forest production and rise in timber prices. The rate of forestry income, nonetheless, was on the decrease on a gradual basis. B. Changes in input coefficient The input coefficient which indicates the inputs of the forest products into other sectors were up in general in 1966 over 1963. It is noted that the input coefficient indicating the amount of forest products supplied to such industries closely related with forestry as lumber and plywood, and wood products and furniture, showed a downward trend for the period 1963-1966. On the other hand, the forest input into other sectors was generally on the increase. Meanwhile, the input coefficient representing the yolume of the forest products supplied to the forestry sector itself showed an upward tendency, which meant more and more decrease in input from other sectors. Generally speaking, in direct proportion to the higher input coefficient in any industrial sector, the reinput coefficient which denotes the use of its products by the same sector becomes higher and higher. C. Changes in ratio of intermediate input The intermediate input ratio showing the dependency on raw materials went up to 15.43 percent m 1966 from 11. 37 percent in 1963. The dependency of forestry on raw materials was no more than 15.43 percent, accounting for a high 83.57 percent of value added. If the intermediate input ratio increases in any given sector, the input coefficient which represents the fe-use of its products by the same sector becomes large. D. Changes in the ratio of intermediate demand The ratio of the intermediate demand represents the characteristics of the intermediary production in each industry, the intermediate demand ratio in forestry which accunted for 69.7 percent in 1963 went up to 75.2 percent in 1966. In other words, forestry is a remarkable industry in that there is characteristics of the intermediary production. E. Changes in import coefficient The import coefficient which denotes the relation between the production activities and imports, recorded at 4.4 percent in 1963, decreased to 2.4 percent in 1966. The ratio of import to total output is not so high. F. Changes in market composition of imported goods One of the major imported goods in the forestry sector is lumber. The import value increased by 60 percent to 667 million won in 1966 from 407 million won in 1963. The sales of imported forest products to two major outlets-lumber and plywood, and wood products and furniture-increased to 343 million won and 31 million won in 1966 from 240million won and 30 million won in 1963 respectively. On the other hand, imported goods valued at 66 million won were sold to the paper products sector in 1963; however, no supply to this sector was recorded in 1963. Besides these major markets, primary industries such as the fishery, coal and agriculture sectors purchase materials from forestry. 2. Analysis of repercussion effect on production The repercussion effect of final demand in any given sector upon the expansion of the production of other sectors was analyzed, using the inverse matrix coefficient tables attached to the the I.O. Table. A. Changes in intra-sector transaction value of inverse matrix coefficient. The intra-sector transaction value of an inverse matrix coefficient represents the extent of an induced increase in the production of self-support products of the same sector, when it is generated directly and indirectly by one unit of final demand in any given sector. The intra-sector transaction value of the forestry sector rose from 1.04 in 1963 to 1, 11 in 1966. It may well be said, therefore, that forestry induces much more self-supporting products in the production of one unit of final demand for forest products. B. Changes in column total of inverse matrix coefficient It should be noted that the column total indicates the degree of effect of the output of the corresponding and related sectors generated by one unit of final demand in each sector. No changes in the column total of the forestry sector were recorded between the 1963 and 1966 figures, both being the same 1. 19. C. Changes in difference between column total and intra-sector transaction amount. The difference between the column total and intra-sector transaction amount by sector reveals the extent of effect of output of related industrial sector induced indirectly by one unit of final demand in corresponding sector. This change in forestry dropped remarkable to 0.08 in 1966 from 0.15 in 1963. Accordingly, the effect of inducement of indirect output of other forestry-related sectors has decreased; this is a really natural phenomenon, as compared with an increasing input coefficient generated by the re-use of forest products by the forestry sector. 3. Induced output of forestry A. Forest products, wood in particular, are supplied to other industries as their raw materials, increasng their value added. In this connection the primary dependency rate on forestry for 1963 and 1966 was compared, i. e., an increase or decrease in each sector, from 7.71 percent in 1963 to 11.91 percent in 1966 in agriculture, 10.32 to 6.11 in fishery, 16.24 to 19.90 in mining, 0.76 to 0.70 in the manufacturing sector and 2.79 to 4.77 percent in the construction sector. Generally speaking, on the average the dependency on forestry during the period 1963-1966 increased from 5.92 percent to 8.03 percent. Accordingly, it may easily be known that the primary forestry output induced by primary and secondary industries increased from 16, 109 million won in 1963 to 48, 842 million won in 1966. B. The forest products are supplied to other industries as their raw materials. The products are processed further into higher quality products. thus indirectly increasing the value of the forest products. The ratio of the increased value added or the secondary dependency on forestry for 1963 and 1966 showed an increase or decrease, from 5.98 percent to 7.87 percent in agriculture, 9.06 to 5.74 in fishery, 13.56 to 15.81 in mining, 0.68 to 0.61 in the manufacturing sector and 2.71 to 4.54 in the construction sector. The average ratio in this connection increased from 4.69 percent to 5.60 percent. In the meantime, the secondary forestry output induced by primary and secondary industries rose from 12,779 million Wall in 1963 to 34,084 million won in 1966. C. The dependency of tertiary industries on forestry showed very minor ratios of 0.46 percent and 0.04 percent in 1963 and 1966 respectively. The forestry output induced by tertiary industry also decreased from 685 million won to 123 million won during the same period. D. Generally speaking, the ratio of dependency on forestry increased from 17.68 percent in 1963 to 24.28 percent in 1966 in primary industries, from 4.69 percent to 5.70 percent in secondary industries, while, as mentioned above, the ratio in the case of tertiary industry decreased from 0.46 to 0.04 percent during the period 1963-66. The mining industry reveals the heaviest rate of dependency on forestry with 29.80 percent in 1963 and 35.71 percent in 1966. As it result, the direct forestry income, valued at 8,172 million won in 1963, shot up to 22,724 million won in 1966. Its composition ratio lo the national income rose from 1.9 percent in 1963 to 2.3 per cent in 1966. If the induced outcome is taken into account, the total forestry production which was estimated at 37,744 million won in 1963 picked up to 105,773 million won in 1966, about 4.5 times its direct income. It is further noted that the ratio of the gross forestry product to the gross national product. rose significantly from 8.8 percent in 1963 to 10.7 percent in 1966. E. In computing the above mentioned ratio not taken into consideration were such intangible, indirect effects as the drought and flood prevention, check of soil run-off, watershed and land conservation, improvement of the people's recreational and emotional living, and maintenance and increase in the national health and sanitation. F. In conclusion, I would like to emphasize that the forestry sector exercices an important effect upon the national economy and that the effect of induced forestry output is greater than its direct income.

• 한국농공학회지
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• 제16권1호
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• pp.3225-3262
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• 1974

The purposes of this thesis are to clarify experimentally the variation of ground water temperature in tube wells during the irrigation period of paddy rice, and the effect of ground water irrigation on the growth, grain yield and yield components of the rice plant, and, furthermore, when and why the plant is most liable to be damaged by ground water, and also to find out the effective ground water irrigation methods. The results obtained in this experiment are as follows; 1. The temperature of ground water in tube wells varies according to the location, year, and the depth of the well. The average temperatures of ground water in a tubewells, 6.3m, 8.0m deep are $14.5^{\circ}C$ and $13.1^{\circ}C$, respercively, during the irrigation period of paddy rice (From the middle of June to the end of September). In the former the temperature rises continuously from $12.3^{\circ}C$ to 16.4$^{\circ}C$ and in the latter from $12.4^{\circ}C$ to $13.8^{\circ}C$ during the same period. These temperatures are approximately the same value as the estimated temperatures. The temperature difference between the ground water and the surface water is approximately $11^{\circ}C$. 2. The results obtained from the analysis of the water quality of the "Seoho" reservoir and that of water from the tube well show that the pH values of the ground water and the surface water are 6.35 and 6.00, respectively, and inorganic components such as N, PO4, Na, Cl, SiO2 and Ca are contained more in the ground water than in the surface water while K, SO4, Fe and Mg are contained less in the ground water. 3. The response of growth, yield and yield components of paddy rice to ground water irrigation are as follows; (l) Using ground water irrigation during the watered rice nursery period(seeding date: 30 April, 1970), the chracteristics of a young rice plant, such as plant height, number of leaves, and number of tillers are inferior to those of young rice plants irrigated with surface water during the same period. (2) In cases where ground water and surface water are supplied separately by the gravity flow method, it is found that ground water irrigation to the rice plant delays the stage at which there is a maximum increase in the number of tillers by 6 days. (3) At the tillering stage of rice plant just after transplanting, the effect of ground water irrigation on the increase in the number of tillers is better, compared with the method of supplying surface water throughout the whole irrigation period. Conversely, the number of tillers is decreased by ground water irrigation at the reproductive stage. Plant height is extremely restrained by ground water irrigation. (4) Heading date is clearly delayed by the ground water irrigation when it is practised during the growth stages or at the reproductive stage only. (5) The heading date of rice plants is slightly delayed by irrigation with the gravity flow method as compared with the standing water method. (6) The response of yield and of yield components of rice to ground water irrigation are as follows: \circled1 When ground water irrigation is practised during the growth stages and the reproductive stage, the culm length of the rice plant is reduced by 11 percent and 8 percent, respectively, when compared with the surface water irrigation used throughout all the growth stages. \circled2 Panicle length is found to be the longest on the test plot in which ground water irrigation is practised at the tillering stage. A similar tendency as that seen in the culm length is observed on other test plots. \circled3 The number of panicles is found to be the least on the plot in which ground water irrigation is practised by the gravity flow method throughout all the growth stages of the rice plant. No significant difference is found between the other plots. \circled4 The number of spikelets per panicle at the various stages of rice growth at which_ surface or ground water is supplied by gravity flow method are as follows; surface water at all growth stages‥‥‥‥‥ 98.5. Ground water at all growth stages‥‥‥‥‥‥62.2 Ground water at the tillering stage‥‥‥‥‥ 82.6. Ground water at the reproductive stage ‥‥‥‥‥ 74.1. \circled5 Ripening percentage is about 70 percent on the test plot in which ground water irrigation is practised during all the growth stages and at the tillering stage only. However, when ground water irrigation is practised, at the reproductive stage, the ripening percentage is reduced to 50 percent. This means that 20 percent reduction in the ripening percentage by using ground water irrigation at the reproductive stage. \circled6 The weight of 1,000 kernels is found to show a similar tendency as in the case of ripening percentage i. e. the ground water irrigation during all the growth stages and at the reproductive stage results in a decreased weight of the 1,000 kernels. \circled7 The yield of brown rice from the various treatments are as follows; Gravity flow; Surface water at all growth stages‥‥‥‥‥‥514kg/10a. Ground water at all growth stages‥‥‥‥‥‥428kg/10a. Ground water at the reproductive stage‥‥‥‥‥‥430kg/10a. Standing water; Surface water at all growh stages‥‥‥‥‥‥556kg/10a. Ground water at all growth stages‥‥‥‥‥‥441kg/10a. Ground water at the reproductive stage‥‥‥‥‥‥450kg/10a. The above figures show that ground water irrigation by the gravity flow and by the standing water method during all the growth stages resulted in an 18 percent and a 21 percent decrease in the yield of brown rice, respectively, when compared with surface water irrigation. Also ground water irrigation by gravity flow and by standing water resulted in respective decreases in yield of 16 percent and 19 percent, compared with the surface irrigation method. 4. Results obtained from the experiments on the improvement of ground water irrigation efficiency to paddy rice are as follows; (1) When the standing water irrigation with surface water is practised, the daily average water temperature in a paddy field is 25.2$^{\circ}C$, but, when the gravity flow method is practised with the same irrigation water, the daily average water temperature is 24.5$^{\circ}C$. This means that the former is 0.7$^{\circ}C$ higher than the latter. On the other hand, when ground water is used, the daily water temperatures in a paddy field are respectively 21.$0^{\circ}C$ and 19.3$^{\circ}C$ by practising standing water and the gravity flow method. It can be seen that the former is approximately 1.$0^{\circ}C$ higher than the latter. (2) When the non-water-logged cultivation is practised, the yield of brown rice is 516.3kg/10a, while the yield of brown rice from ground water irrigation plot throughout the whole irrigation period and surface water irrigation plot are 446.3kg/10a and 556.4kg/10a, respectivelely. This means that there is no significant difference in yields between surface water irrigation practice and non-water-logged cultivation, and also means that non-water-logged cultivation results in a 12.6 percent increase in yield compared with the yield from the ground water irrigation plot. (3) The black and white coloring on the inside surface of the water warming ponds has no substantial effect on the temperature of the water. The average daily water temperatures of the various water warming ponds, having different depths, are expressed as Y=aX+b, while the daily average water temperatures at various depths in a water warming pond are expressed as Y=a(b)x (where Y: the daily average water temperature, a,b: constants depending on the type of water warming pond, X; water depth). As the depth of water warning pond is increased, the diurnal difference of the highest and the lowest water temperature is decreased, and also, the time at which the highest water temperature occurs, is delayed. (4) The degree of warming by using a polyethylene tube, 100m in length and 10cm in diameter, is 4~9$^{\circ}C$. Heat exchange rate of a polyethylene tube is 1.5 times higher than that or a water warming channel. The following equation expresses the water warming mechanism of a polyethylene tube where distance from the tube inlet, time in day and several climatic factors are given: {{{{ theta omega (dwt)= { a}_{0 } (1-e- { x} over { PHI v })+ { 2} atop { SUM from { { n}=1} { { a}_{n } } over { SQRT { 1+ {( n omega PHI) }^{2 } } } } LEFT { sin(n omega t+ { b}_{n }+ { tan}^{-1 }n omega PHI )-e- { x} over { PHI v }sin(n omega LEFT ( t- { x} over {v } RIGHT ) + { b}_{n }+ { tan}^{-1 }n omega PHI ) RIGHT } +e- { x} over { PHI v } theta i}}}}{{{{ { theta }_{$\infty$ }(t)= { { alpha theta }_{a }+ { theta }_{ w'} +(S- { B}_{s } ) { U}_{w } } over { beta } , PHI = { { cpDU}_{ omega } } over {4 beta } }}}} where $\theta$$\omega$; discharged water temperature($^{\circ}C$) $\theta$a; air temperature ($^{\circ}C$) $\theta$$\omega$';ponded water temperature($^{\circ}C$) s ; net solar radiation(ly/min) t ; time(tadian) x; tube length(cm) D; diameter(cm) ao,an,bn;constants determined from $\theta$$\omega$(t) varitation. cp; heat capacity of water(cal/$^{\circ}C$ ㎥) U,Ua; overall heat transfer coefficient(cal/$^{\circ}C$ $\textrm{cm}^2$ min-1) $\omega$;1 velocity of water in a polyethylene tube(cm/min) Bs ; heat exchange rate between water and soil(ly/min)