초록
유해(有害) 중금속(重金屬)이 수도의 발아 및 묘대기(苗垈期)의 생육(生育)에 미치는 영향(影響)을 구명(究明)하기 위하여 중금속(重金屬) 원소별(元素別)로 농도(濃度)를 달리한 일정(一定)한 용액(溶液)을 계속(繼續) 공급(供給)하여 발아 및 묘(苗)의 생육(生育)에 미치는 영향(影響)을 조사(調査)한 결과(結果)는 다음과 같다. 1) 발아에 과잉(過剩)의 해(害)를 유발하는 중금속(重金屬)의 처리농도는 Cd; 0.05ppm 이하(以下), Cu; 0.05ppm 이하(以下), Ni; 0.5ppm 이하(以下), Co; 0.5~1.0 ppm, Cr; 0.5ppm~1.0ppm, Mn: 1.0ppm 이하(以下), Zn; 0.5~5.0ppm Pb; 0.5~5.0ppm으로 발아에 미치는 영향(影響)은 Cd>Cu>Ni>Co>Cr>Mn>Zn$$\geq_-$$Pb의 순(順)이었다. 2) 건물중(乾物重)의 감소(減少)를 유발하는 중금속(重金屬)의 처리 농도(濃度)는 Cd;0.05ppm 이하(以下), Ni, Cr, Co; 0.5ppm 이하(以下), Cu; 0.5~5ppm, Zn; 0.5~5ppm, Pb; 5~20ppm, Mn; 10~25ppm, 으로 건물중(乾物重)에 미치는 영향(影響)의 정도는 Ni>Cd>Cr>Co>Cu$$\geq_-$$Zn>Pb>Mn의 순(順)이었다. 3) 건물중(乾物重)의 감소(減少)를 유발하는 건물중(乾物中)의 중금속(重金屬)의 농도(濃度)는 Cd; 0.05~15.5ppm, Ni; 1.50~25.0ppm, Pb: 24.0~28.0ppm, Cu; 26.5~62.5ppm Zn; 470~645ppm, Mn; 231~500ppm, Co; 15.0ppm 이하(以下)였다. 4) 0.5ppm의 처리농도에서 각종(各種) 유해(有害) 중금속(重金屬)의 흡수(吸收) 축적(蓄積)은 Cr이 trace Co; 15ppm, Cd; 17.5ppm, Pb; 24.0ppm, Ni; 25. ppm, Cu; 84.5ppm, Zn; 470.0ppm으로 수도에 의(依)한 흡수정도(吸收程度)는 Zn>Cu>Ni>Pb>Cd>Co>Cr> 의 순(順)이었다. 5) 근활력(根活力)에 대해 과잉(過剩)의 해(害)를 유발하는 중금속(重金屬)의 농도(濃度)는 Ca;0.05ppm 이하(以下), Cu; 0.05~0.5ppm, Cr; 0.5ppm 이하(以下), Ni; 0.5~1.0ppm, Co; 0.5~1.0ppm, Zn; 0.5ppm 이상(以上), Pb; 0.5~5.0ppm, Mn; 1~10ppm으로 근활력(根活力)에 영향(影響)을 미치는 정도(程度)는 Cd>Cu>Cr>Zn>Ni>Co>Pb>Mn의 순(順)이었다.
Rice seeds, suweon 264, were germinated under 5 levels of toxic heavy metals, Cd(0, 0.05, 0.5, 5, 20ppm), Cu(0, 0.05, 0.5, 5, 20, ppm), Cr(0, 0.5, 1, 5, 10ppm), Ni(0, 0.5, 1, 5, 10ppm), Co(0, 0.5, 1, 5, 10ppm), Zn(0, 0.5, 5, 20, 40, ppm), Pb(0, 0.5, 5, 20, 40ppm) and Mn(0, 1, 10, 25, 50, ppm) in culture solution, and then grown with supplying culture solution contained respective concentrations. Germination and growth response to the toxic heavy metals were studied. Results obtained are as follows : 1) The germination injury of rice seeds by excess concentration of toxic heave metal in culture solution occured in Cd and Cu; below 0.05 ppm, Ni; below 0.5 ppm, Mn; below 1.0 ppm, Co and Cr; 0.5-1.0 ppm, and 0.5-5 ppm, Zn and Pb. Thereby, in the order of degrees of the elements toxicity to germination, they were arranged as follows : Cd>Cu>Ni>Co>Cr>Mn>Zn$$\geq_-$$Pb. 2) Toxic heavy metal concentrations in culture solution, which result in decreasing dry weight due to the injury of excess concentration of treated elements, were Cd: below 0.05 ppm, Ni, Cr and Co; below 0.5 ppm, Cu and Zn; 0.5-5 ppm, Pb; 5-20 ppm and Mn; 10-25 ppm. The order was Ni>Cd>Cr>Co>Cu$$\geq_-$$Zn>Pb>Mn. 3) The critical contents of Cd, Ni, Pb, Cu, Zn, Mn, and Co in dry matter, Which result in decreasing dry weight, were considered to be 0.05-15.5, 1.50-25.0, 24.0-28.0, 26.5-62.5, 470-645.0, 231.0-500.0 and below 15.0 ppm, respectively. 4) The contents of Cr, Co, Cd, Pb, Ni, Cu and Zn in dry matter by 0.5 ppm treatment concentration of each heavy metals was trace, 15.0, 17.5, 24.0, 25.0, 84.5 and 470.0 ppm, respectively. Thereby, in the order of each element to uptaked by rice seedlings, they were arranged as follow; Zn>Cu>Ni>Pb>Cd>Co>Cr. 5) The hazardous concentrations of root activity by toxic heavy metals in culture solution were Cd; below 0.05, Cu; 0.05-0.5, Cr; below 0.5, Ni; 0.5-1.0, Co; 0.5-1.0, Zn; above 0.5, Pb; 0.5-5.0 and Mn; 1.0-10.0 ppm. The hazardous degree of root activity by toxic heave metals was in the order of Cd>Cu>Cr>Zn>Ni>Co>Pb>Mn.