• 한국작물학회지
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• 제68권3호
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• pp.147-166
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• 2023

Seed color is controlled by several genes and is a key trait in determining the metabolite content and biological activities of legume genotypes. In this study, 296 adzuki bean accessions, including 159 grey, 99 red, and 38 white adzuki beans, were grown in Korea. Variations in total phenolic content (TPC), total saponin content (TSC), DPPH^• scavenging activity, ABTS^•+ scavenging activity, and ferric reducing antioxidant power (FRAP) were assessed and were reported to be in the ranges of 1.52-8.24 mg GAE/g, 14.36-114.22 mg DE/g, 0.23-12.84 mg AAE/g, 1.05-17.66 mg TE/g, and 0.59-13.14 mg AAE/g, respectively, with a wide variation across adzuki beans. Except for DPPH^• scavenging activity, the average values declined in the order gray > red > white adzuki beans, each demonstrating a significant variation (p < 0.05). White adzuki beans, which showed low metabolite content and antioxidant activity, were clearly separated from the gray and red genotypes using principal component and hierarchical cluster analyses. Moreover, TPC, TSC, and antioxidant activities were strongly correlated, regardless of seed color. Overall, the diversity of the TPC, TSC, and antioxidant activity in a broad population of adzuki bean genotypes was determined. Furthermore, this study found that seed color variation in adzuki beans had a significant effect on the metabolite content and antioxidant activity. Superior accessions with high levels of TPC, TSC, and antioxidant activity were also discovered and could be used for functional plant breeding and human consumption. The findings of this study may be useful for understanding the relationship between seed coat color and metabolite concentration in adzuki beans, paving the way for molecular-level analyses.

• 한국양식학회지
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• 제2권2호
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• pp.53-90
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• 1989

식욕에 부합되는 적정양의 먹이 섭취는 잉어의 성장을 증가시키고, 동시에 먹이의 허비를 막으며, 그로 인해서 사육수질의 오염을 막는 부수적인 효과도 가지게 된다. 이 목적을 달성하기 위하여 식욕 유발과 그에 따른 빠른 성장의 중요한 요인으로서 용존산소에 관한 정밀한 연구가 필요하다. 수온 $25^{\circ}C$ 하에서 잉어(이스라엘계)의 미성어, 67g, 200g, 400g, 600g 및 800g 되는 실험군으로서, 용존산소를 2.0-6mg/$\iota$ 사이에서 사료를 체중의 $1\%$부터 먹을 수 있는 양까지에 걸쳐서 사육실험연구를 하였다. 어체가 작을수록 동일한 용존산소 조건에서는 보다 높은 식욕과 보다 많은 먹이 섭취량을 나타내었다. 어체가 클수록 낮은 용존산소양에서는 생활 능력이 약해지고, 먹이 섭취량이 증가하면 내성은 더욱 줄어졌다. 성장률(일간 성장률)은 낮은 용존산소에 의해서 영향을 받지 않는 한, 먹이의 섭취량이 많을수록 증가하였다. 최고성장률은 67 g 어에서는 D.O. 5.0 mg/$\iota$에서 1일 먹이 량이 체중의 $7\%$ 일때 일간성장률 $\5.05%$였고, 200g 어에서는 D.O. 5.5/$\iota$ 에서 먹이량 $6\%$일때 1일 성장률이 $3.75\%$였다. 400g 어에서는 D.O. 6.0 mg/$\iota$에서 먹이량이 $5\%$ 일때 1일 성장률 $3.37\%$ 였으며, 600g 어에서는 D.O. 5.5 mg/$\iota$에서 먹이량이 1일 $4\%$였을 때 1일 성장률 $2.82\%$였다. 800g 어에서는 D.O. 5.0mg/$\iota$에서 먹이량이 1일 $3\%$었을 때 1일 성장율이 $1.95\%$였다. 정상적인 생활 및 성장 기능발휘 가능 D.O. 농도로부터 최고 먹이 섭취가능양에 부합되는 D.O. 농도까지 사이에서 먹이 전환효율(사료가 어체로 바뀌는 효율)은 처음 D.O.가 증가함에 따라 높아지고, 최고치에 이른 뒤, D.O.가 더욱 더 높아짐 에 따라 먹이 전환효율은 다시 감소하기 시작한다. 이 최고 사료효율은 작은 어체에서는 큰 어체 보다 높은 먹이 섭취량에서 나타난다 (물론 먹이 섭취량에 부응하는 D.O.량이 갖춰졌을때). 즉 최고 먹이 전환효율은 67g 어에서 D.O. 3.0-4.0 mg/$\iota$에서 먹이 섭취량 $4\%$때 였으며, 200g 어에서는 D.O. 3.0-4.5mg/$\iota$에서 먹이 섭취량 $3\%$때였고, 400 g 어에서는 D.O. 4.0-4.5mg/$\iota$에서 먹이 섭취량 $2\%$때였다. 600g 및 800 g 어에서는 가장 낮은 D.O.에서 먹이 섭취량 $1\%$ 때였다. 적절하지 못한 낮은 D.O. 함량에서는 정상적인 조건하의 개체보다 먹이 섭취량이 감소하며, 또 먹이가 소화관을 빨리 통과하고, 똥의 양이 증가하는 것을 관찰할 수 있었다. 그리고, 견디지 못할 만큼 낮은 D.O.하에서는 먹이를 토하고, 체색이 옅은 황색으로 변하거나, 또는 회색의 얼국진 반점으로 변하기도 했다. 이 모든 현상들이 먹이 전환효율의 감소로 이어졌다. 반면에 아주 높은 D.O.하에서는 강한 활동을 하였으며, 어체 크기가 같고 먹이의 양도 같았지만 D.O.가 약간 낮은 상에 비교하여 먹이 전환효율이 떨어지는 경향이 나타났다. 모든 크기에서 먹이량을 체중의 $1\%$만 주었을 때는 D.O. 량이 2.0-2.5mg/$\iota$ 이면 적절하였다. 먹이량을 증가시키면 어체의 정상활동을 유지시키기 위하여 보다 높은 D.O.가 필요하였다. 67g 어에서는 D.O. 2.0-2.5mg/$\iota$이면 체중의 $2\%$이상 먹이량을 충분히 지탱할 수 있었으나, 먹이를 $5\%$로 증가시키면 D.O. 3.0-4.0 mg/$\iota$일 때 식욕이 보다 왕성하고 높은 성장을 가져 왔다. 먹이량이 $5-7\%$에서는 4.0 mg/$\iota$ 이상의 D.O.라야 식욕을 유지시킬수 있다. 200g 어에서는 먹이량이 체중의 $2-3\%$ 일때는 D.O. 3.5-4.5mg/$\iota$에서 가장 높은 성장률을 보였으나 먹이량이 체중의 $3-6\%$로 올라가면 D.O. 함량이 4.5mg/$\iota$을 넘어서야만 어류의 생활기능 발휘에 부응될 수 있었다. 400 g, 600 g 및 800 g 어에서는 먹이량이 체중의 $2\%$를 넘을 때는 ($4\%$ 및 $5\%$까지 실험) 모두 D.O. 함량이 4.5 mg/$\iota$를 넘어야 했다.

• 자원환경지질
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• 제30권5호
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• pp.417-431
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• 1997

Characteristics of sedimentary rocks and enrichment of toxic elements in shale and coal from the Chungnam coal field were investigated based upon geochemistry of major, trace and rare earth elements. Shale and coal of the area are interbedded along the Traissic to the Jurassic Daedong Supergroup, which can be subdivided into grey shale, black shale and coal. The coal had been mined, however all the mines are abandonded due to the economic problems. The shale and coal are characterized by relatively low contents of $SiO_2$, and $Al_2O_3$ and high levels of loss-on-ignition (LOI), CaO and $Na_2O$ in comparison with the North American Shale Composite (NASC). Light rare earth elements (La, Ce, Yb and Lu) are highly enriched with the coal. Ratios of $Al_2O_3/Na_2O$ and $K_2O/Na_2O$ in shale and coal range from 30.0 to 351.8 and from 4.2 to 106.8, which have partly negative correlations against $SiO_2/Al_2O_3$ (1.24 to 6.06), respectively. Those are suggested that controls of mineral compositions in shale and coal can be due to substitution and migration of those elements by diagenesis and metamorphism. Shale and coal of the area may be deposited in terrestrial basin deduced from high C/S (39 to 895) and variable composition of organic carbon (0.39 to 18.40 wt.%) and low contents of reduced sulfur (0.01 to 0.05 wt.%). These shale and coal were originated from the high grade metamorphic and/or igneous rocks, and the rare earth elements of those rocks are slightly influenced with diagenesis and metamorphism on the basis of $Al_2O_3$ versus La, La against Ce, Zr versus Yb, the ratios of La/Ce (0.38 to 0.85) and Th/U (3.6 to 14.6). Characteristics of trace and rare earth elements as Co/Th (0.07 to 0.86), La/Sc (0.31 to 11.05), Se/Th (0.28 to 1.06), V/Ni (1.14 to 3.97), Cr/V (1.4 to 28.3), Ni/Co (2.12 to 8.00) and Zr/Hf (22.6~45.1) in the shale and coal argue for inefficient mixing of the simple source lithologies during sedimentation. These rocks also show much variation in $La_N/Yb_N$ (1.36 to 21.68), Th/Yb (3.5 to 20.0) and La/Th (0.31 to 7.89), and their origin is explained by derivation from a mixture of mainly acidic igneous and metamorphic rocks. Average concentrations in the shale and coal are As=7.2 and 7.5, Ba=913 and 974, Cr=500 and 145, Cu=20 and 26, Ni=38 and 35, Pb=30 and 36, and Zn=77 and 92 ppm, respectively, which are similar to those in the NASC. Average enrichment indices for major elements in the shale (0.79) and coal (0.77) are lower than those in the NASC. In addition, average enrichment index for rare earth elements in coal (2.39) is enriched rather than the shale (1.55). On the basis of the NASC, concentrations of minor and/or environmental toxic elements in the shale and coal were depleted of all the elements examined, excepting Cr, Pb, Rb and Th. Average enrichment indices of trace and/or potentially toxic elements (As, Cr, Cu, Ni, Pb, U and Zn) are 1.23 to 1.24 for shale and 1.06 to 1.22 for coal, respectively.

• 한국수자원학회:학술대회논문집
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• 한국수자원학회 2011년도 학술발표회
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• pp.8-9
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• 2011

On 4 September 2010 an earthquake of magnitude 7.1 on the Richter scale occurred on the Canterbury Plains in the South Island of New Zealand. The Canterbury Plains are an area of extensive groundwater and spring fed surface water systems. Since the September earthquake there have been several thousand aftershocks (Fig. 1), the largest being a 6.3 magnitude quake which occurred close to the centre of Christchurch on 22February 2011. This second quake caused extensive damage to the city of Christchurch including the deaths of 189 people. Both of these quakes had marked hydrological impacts. Water is a vital natural resource for Canterburywith groundwater being extracted for potable supply and both ground and surface water being used extensively for agricultural and horticultural irrigation.The groundwater is of very high quality so that the city of Christchurch (population approx. 400,000) supplies untreated artesian water to the majority of households and businesses. Both earthquakes caused immediate hydrological effects, the most dramatic of which was the liquefaction of sediments and the release of shallow groundwater containing a fine grey silt-sand material. The liquefaction that occurred fitted within the empirical relationship between distance from epicentre and magnitude of quake described by Montgomery et al. (2003). . It appears that liquefaction resulted in development of discontinuities in confining layers. In some cases these appear to have been maintained by artesian pressure and continuing flow, and the springs are continuing to flow even now. In spring-fed streams there was an increase in flow that lasted for several days and in some cases flows remained high for several months afterwards although this could be linked to a very wet winter prior to the September earthquake. Analysis of the slope of baseflow recession for a spring-fed stream before and after the September earthquake shows no change, indicating no substantial change in the aquifer structure that feeds this stream.A complicating factor for consideration of river flows was that in some places the liquefaction of shallow sediments led to lateral spreading of river banks. The lateral spread lessened the channel cross section so water levels rose although the flow might not have risen accordingly. Groundwater level peaks moved both up and down, depending on the location of wells. Groundwater level changes for the two earthquakes were strongly related to the proximity to the epicentre. The February 2011 earthquake resulted in significantly larger groundwater level changes in eastern Christchurch than occurred in September 2010. In a well of similar distance from both epicentres the two events resulted in a similar sized increase in water level but the slightly slower rate of increase and the markedly slower recession recorded in the February event suggests that the well may have been partially blocked by sediment flowing into the well at depth. The effects of the February earthquake were more localised and in the area to the west of Christchurch it was the earlier earthquake that had greater impact. Many of the recorded responses have been compromised, or complicated, by damage or clogging and further inspections will need to be carried out to allow a more definitive interpretation. Nevertheless, it is reasonable to provisionally conclude that there is no clear evidence of significant change in aquifer pressures or properties. The different response of groundwater to earthquakes across the Canterbury Plains is the subject of a new research project about to start that uses the information to improve groundwater characterisation for the region. Montgomery D.R., Greenberg H.M., Smith D.T. (2003) Stream flow response to the Nisqually earthquake. Earth & Planetary Science Letters 209 19-28.