「蓮」「環」密碼--環境因子對蓮花效應的影響
蓮花效應是指蓮葉表面具有奈米纖毛結構,因此只要葉面稍微傾斜,水珠就會滾離葉面,在我們生活週遭,許多植物具有蓮花效應。本實驗選擇彩葉山漆莖作為研究材料,因為我們發現在同一植株上,嫩葉的蓮花效應最佳,而老葉幾乎無蓮花效應。當彩葉山漆莖的新葉轉為老葉,蓮花效應會減弱,甚至消失。我們以不同水量、土壤酸鹼值及光照作為變因,來探討蓮花效應改變的原因,結果發現水量並非主要影響蓮花效應改變的變因;土壤過酸或過鹼,會減弱新葉及嫩葉的蓮花效應;置於暗室則使整株彩葉山漆莖所有葉面皆無蓮花效應。許多植物的性狀,在老化或面臨環境改變時,會將控制性狀的基因開啟或關閉。因此,我們推論,當環境因子改變時,植物的蓮花效應可能是經由基因層次的調控,藉以增強或減弱此性狀的表現。如果不是基因的開啟或關閉,則有可能僅是葉表面的結構發生些微的改變,真正詳細的機制仍有待進一步的確認。;We choose Breynia nivosa (Bull ex W. G. Smith) Small as a model plant to study the lotus effect on the leaves for the reason that on the same chosen plant the new-born leaves have the best lotus effect while the elder ones have little lotus effect. When the new leaves turns into elder ones, the lotus effect also turns weaker or even vanishes. To explore the exact mechanisms, we take water quantity、soil pH、and light density as the experimental factors. The results show that water quantity cannot affect the lotus effect on all leaves, change in soil pH can decrease the lotus effect on the new and new-born leaves, and dark treatments can eliminate the lotus effect on all leaves. When the environments change, the phenotypes of plants could also be changed to adapt to the new conditions by turning on or off genes. Therefore, we suggest that the lotus effect on the leaves is also controlled by genes to increase or decrease its phentype so as to adapt to the changing environments. If not, it may simply be a little change of the surface structure of the leaves. The detailed mechanism remains to be confirmed further.
咦?!田螺長毛了!探討石田螺及其螺殼上附生藻類與環境因子之關係
This research is about two ponds in the Behu park’s and the Dahu park’s snail(Square Mystery Snail:Sinotaia quadrata) in Taipei city of Nei-hu District for research object, carry out the study of the following research proceed: 1.Discriminate the algae species that are growth on the snail shell and which is a kind of interaction with the snail; 2.The influence of the snail and algae with difference of temperature, salinity, pH value and dark ; 3. The factors affect algae growth on snail shell; 4.Use the variation of snail and algae to be a biological incator. The result manifestation: the algae that are growth on snail shell have two kinds, one is Oscillatoriaceae and the other is Cladophora sp. The interaction between algae and snail belong to communalism, but under the condition of lacking of food, the snail then will eat the Cladophora sp. which grow on the shell of other snails. The temperature adapts aspect, upper limit of the feat existence of the snail should be low in 28℃. When over than 28℃, Cladophora sp. as the most strong, Oscillatoriaceae is secondly, and the snail then is most poor. For the maximum tolerance of the salinity, the snail is about 4.38?, Oscillatoriaceae is about 5.00?, Cladophora sp. is then about 5.83?; Under the different salinity for the tolerance , the Cladophora sp. still the most strong, Oscillatoriaceae is secondly, and the snail then is most poor. Under the dark environment, the speed of Oscillatoriaceae begin to be bleaching is very fast than the Cladophora sp.. In the tolerance of pH value range: The snail is about pH=5~10, Oscillatoriaceae is about pH=7~8, Cladophora sp. is about pH=6~8; When the pH value range is in the pH=5~8, the speed of the Oscillatoriaceae occur changing is very fast than Cladophora sp.. The algae are growing on snail shell very different between two ponds, the main reason is water pH value dissimilarly: When pH value over than 8.5, there is no Cladophora sp. to grow on the snail shell, after the pH value to decrease, Oscillatoriaceae then will compare early than Cladophora sp. to grow on the snail shell. Calculate by the classification of the freshwater biological incator : Two organic pollution degree of the ponds may be lain in theβ-mesosaprobic to theα-mesosaprobic, and the polluting degree of the Dahu pond is more seriously. As for two ponds, have already faced what level of eutrophication? Belong to actually which stage of pollution grade? Not only added the classification data of floating and fixative algea in two ponds, and also according to the parts of chemistry analysis method measure of the data makes the substantial evidence, then could carry out the more accurate and thorough study in the days to come steadily studying process.本研究是以臺北市內湖區兩個綠地公園(碧湖公園與大湖公園)池塘內的石田螺(Sinotaia quadrata)為研究對象,進行以下研究目的之探討:1.鑑別石田螺螺殼上藻類的種類及其與石田螺的互動關係;2.溫度、鹽度、酸鹼值及黑暗等環境因子的差異,對石田螺及螺殼上附生藻類的影響;3.影響藻類附生於石田螺螺殼上的因素;4.將石田螺及螺殼上附生藻類的變化作為監測環境因子或水質變異的指標現象。結果顯示:附生於石田螺螺殼上的藻類有顫藻(Oscillatoriaceae)與剛毛藻(Cladophora sp.)兩類;與石田螺的互動關係應屬於片利共生(communalism),但在缺乏食物的情況下,石田螺則會採食同伴殼上的剛毛藻。溫度適應方面,石田螺適宜生存的溫度上限應低於28℃,超過28℃水溫環境的耐受程度,是以剛毛藻為最強,其次是顫藻,而石田螺則為最差。對於環境鹽度最大耐受度方面:石田螺約為4.38?,顫藻約為5.00?,剛毛藻則約為5.83?;在不同鹽度環境下,鹽度的耐受程度,仍以剛毛藻為最強,其次是顫藻,而石田螺則是最差。在黑暗環境下,顫藻褪色產生白化現象的速度明顯地比剛毛藻要快了許多。在環境酸鹼值耐受的範圍方面:石田螺約在pH=5~10 之間,顫藻約在pH=7~8 之間,剛毛藻則約在pH=6~8之間;而酸鹼值範圍在pH=5~8 時,顫藻產生變化的速度明顯地比剛毛藻還要快。而兩樣區池塘水體酸鹼值的不同,應是造成石田螺螺殼藻類附生現象差異的主要原因:當酸鹼值超過8.5 時,螺殼上就無剛毛藻附生,當酸鹼值降下後,顫藻則會比剛毛藻早出現在螺殼上。藉由淡水生物指標的分類推測:兩樣區池塘水體有機污染程度,可能介於β-中腐水性(β-mesosaprobic,βm)至α-中腐水性(α-mesosaprobic,αm)的範圍之間,而D池塘受污染的程度應會比B池塘還要更嚴重些。至於兩樣區池塘水體,已面臨了何種優養化的程度?究竟是屬於哪一個階段的污染等級呢?除須補充水體中浮游性及附著性藻類分類的詳細觀察資料外,仍必須參照部分水質化學分析法所測得的數據作佐證,才能在日後持續地研究過程中進行更精確及深入的探討。
單細胞浮游藻類對紫外線防禦機制之探討
在先備知識中,我們知道在缺少營養鹽及紫外線傷害下,浮游藻類的葉綠體會因為過氧化物(R.O.S.)的增加而受到破壞,進而影響光合作用的進行,甚至導致死亡。所以確實了解常見浮游藻類生理狀態和環境的影響,以期待未來可利用大幅度提高浮游藻類生產力的方式有效降低溫室效應的影響為本實驗的主要目的。故實驗設計針對兩種常見的海洋種浮游藻類(Tetra、Ske),在不同紫外線光譜(UVAB、UVC)的照射下,觀察R.O.S.的產生量和T-T dimer的表現狀況,並對照兩者之間的關係。結果我們發現:綠藻(Tetra)和矽藻(Ske)在UVAB、UVC 的照射下皆會產生R.O.S.,且綠藻產生的量較少;但在UVC 照射下皆有DNA 損傷(產生T-T dimer)。故推估並不是綠藻(Tetra)擁有紫外線的特殊防禦機制,而是能較有效地代謝R.O.S.。As we know, under the condition of unorganized salt’s shortage and the harm of the ultraviolet ray, the phytoplankton’s chloroplast will be destroyed because of the increasing peroxide (R.O.S.). Furthermore, the ultraviolet ray will have an effect on the process of photosynthesis, and even result in the death of phytoplankton. So, we intend to promote the production of phytoplankton in order to lower the influence of greenhouse effect by probing into the environmental influence on the physiology of phytoplankton. The experimental is designed to observe two common marine phytoplankton: Tetra and Ske. By close observing Tetra and Ske exposed to different wavelength of ultraviolet way (UVAB and UVC ), we contrast the production of R.O.S. with the appearing of T-T dimer. We observe that both Tetra and Ske will produce R.O.S. after being exposed to UVAB and UVC , but Tetra produce less than Ske, and that UVC will do harm to both the DNA of Tetra and Ske (producing T-T dimer). Based on the result of the experiment we estimate that Tetra can catobolize R.O.S. efficiently instead of having a unique defensive mechanism against ultraviolet ray (UVAB and UVC under discussion in this experiment.)
超音波霧化降溫之研究探討
本研究(超音波霧化降溫研究)由二實驗組成。實驗一主要針對超音波霧化器(以下簡稱霧化器)之造霧性能進行探討;實驗二則為霧化器之降溫應用。實驗一以改良傳統造霧方式,進而維持最佳造霧效果為主。由於先前的霧化方式是直接放置霧化器於水面,致使最佳霧化水深因霧氣蒸散、水位下降而無法維持;所以在實驗一裡,我們針對霧化器的使用設計一套「漂浮造霧法」:本法運用浮體使霧化器懸於水面,和水面等起伏,使霧化器底部距水面高度不變,藉以維持最佳造霧水深、造霧效果。實驗二乃霧化降溫之探討。本實驗在相同的霧化量下,操縱風速和接觸表面積的差異;利用霧、氣接觸面積與蒸散速率呈正向關係的原理,找出最佳的降溫條件。同時,也期待在兼顧環保的前提下,將之應用於未來開放空間的降溫。The research(Heat Control by Supersonic Vaporization)includes two experiments. One is focused on atomized effect of Supersonic Vaporization(so-called Atomizer); the other is about applying atomizer to temperature decrease. Exp.1 adapts formal way of atomization. Since previous way of atomization is to put atomizer directly on the water, making the change of atomizer’s distance from water as water evaporates, Exp.1 creates a way called “Floating”. In Floating, atomizer is suspended in a float; constantly keeps the bottom of atomizer from same distance from surface of water. Thus, no matter how much volume of water is evaporated, the best depth of water for atomization and also, the best atomized condition, could stay. Exp2 inquires in relation between atomization and temperature decrease. In Exp2, the atomized volume is fixed, while wind speed and air-contact area are mastered elements. By the theory that, “the wider contact area is, the more efficiently water evaporates,” we could manage out the best condition in temperature decrease. In that way, with the theory practiced, this research, considering environmental case, is supposed to be applied to open-air area one day.
斑馬魚胚胎發育時期中樞神經系統與單羧基運輸蛋白之相關性
Astrocytes provide energy to neuron mainly with lactate, which is transported through monocarboxylate transporters (MCTs). Among 14 isoforms of MCTs reported in mammals, only MCT1, 2 and 4 are expressed in brain and the three isoforms are found to differentially expressed in neuron and astrocyte, respectively. Based on these, “astrocyte-neuron lactate shuttle” has been proposed. However, no in vivo evidence was available so far to support this hypothesis. In the present study, zebrafish was used as a model to provide in vivo molecular physiological evidence for the involvements of MCTs in the development and functioning of central nervous system (CNS). Full-length cDNAs of the zebrafish MCT1-4 were cloned from zebrafish. Based on RT-PCR results, zMCT1 and zGLUT4 expressed in brain were chosen for further experiment. Morpholino knockdown experiments provided for the 1st time the in vivo evidence to indicate that the zMCT1 and zMCT4 may be involved in energy translocation and functioning of the developing CNS. 於前人預備實驗中,發現斑馬魚胚胎時期肝醣訊號會於腦部與中樞神經系統區位出現。因此,醣類的分布與在細胞間的傳遞應可視為腦部發育的重要指標。我們以基因體資料庫為工具,研究斑馬魚腦部相關基因異構型分布。目前,我們選殖到數個葡萄糖運輸 (GLUT)、鈉離子/葡萄糖協同運輸(SGLT)與單羧基運輸(MCT)通道在斑馬魚腦部表現,其表現是否與胚胎初期中樞神經系統的發育相關仍未知。經過初步基因分析後,我們決定以MCT 中第一和四異構型作為研究對象,並用Anti-Hu,與PCNA 做神經觀測,將施打反股寡核?酸進行突變操作的斑馬魚,與對照組進行免疫染色分析,以螢光顯微鏡觀察發現:抑制MCT 表現,確實影響胚胎時期中樞神經細胞發育及鰓部細胞分裂;亦可能造成畸形出現。
人類粒腺體蘋果酸.活性中心輔.NAD(P) + 結合位置之探討
人類粒線體蘋果酸.可利用NAD+或NADP+為輔.,幫助腫瘤細胞獲得能量,但一般生理條件較傾向以NAD+為輔.。本研究將K346 修改成偏好NADP+之粒線體蘋果酸.家族中具有高度保留性的絲胺酸、及不具極性之丙胺酸,探討為何此酵素較偏好以NAD+為輔.。天然及突變株酵素的催化常數 (kcat)、基質Km 值、及抑制常數 (Ki) 測定結果顯示K346 之點突變不會影響基質Km 值,但K346S 之kcat明顯上升,繼而改變此酵素對NADP+之選擇性。本研究對於人類粒線體蘋果酸.催化機制的了解,有助設計具專一性的活性抑制劑,未來可應用於抑制腫瘤細胞能量來源,進而抑制腫瘤細胞生長。;Human mitochondrial NAD(P)+-dependent malic enzyme can help tumor cells gain energy, using either NAD+ or NADP+ as the cofactor, but prefers NAD+ as the coenzyme. By mutating the K346 to Ser, conserved in NADP+-dependent ME and to Ala with non-polar, we explore why human mitochondrial NAD(P)+-dependent malic enzyme prefers NAD+ as the coenzyme. We measured the proteins kcat, Km and the Ki values. The experiments showed that mutantions don’t affect the Km values, but K346S increased in the kcatvalue, transferring the coenzyme specificity to NADP+. If we develop deeper understanding of the human mitochondrial NAD(P)+-dependent malic enzyme, we can design a specific drag to inactivate the enzyme activity, and inhibit tumor cell growth.