斑马鱼脑细胞中凋亡基因对蛇毒麻痹性贝类毒素的反应

Zhang De, Pr Chin
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research has been carried out on the toxin,in particular the effects on central nervous system(CNS) of animals and human.Thus the present research is to investigate abnormity of apoptotic gene expression,ultrastructural damage of brain induced by aphantoxin,to reveal mechanism of response of brain on zebrafish to aphantoxins.Virus-free male zebrafish(Danio rerio),110 days old or so,average bodyweight of(0.4±0.01) g,after 7—10 days of acclimatization,were randomly assigned into control and treated groups(45 fish per group).The two groups were received 30μL 0.01 mol/L acetic acid solution(control) and 30 μL 0.01 mol/L acetic acid solution contained aphantoxins(5.3 μg STXeq/kg bodyweight,treated) through intraperitoneal injections(i.p.).At each time point(1,3,6,9,12 and 24h),five zebrafish in each group were sacrificed by cold shock(embedding into crushed ice at -8℃),and cerebra were removed from whole brain and washed at once in 0.86% ice-cold physiological saline,prefixed in 2.5% 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引用次数: 5

摘要

幻影藻DC-1是云南滇池冬季和春季的优势种,在淡水中频繁出现。近20年来,由于污染严重和优势种过度生长,滇池内每年都发生幻生花DC-1型水华。在滇池的某些水域,花期一年持续六个月,甚至整年。这些花也会向空气中散发出难闻的气味。因此,今天的游客更有可能呼吸到难闻的空气而不是新鲜的空气,看到的是绿泥水而不是清澈的蓝色水的糟糕风景。特别是优势种可产生麻痹性贝类毒素,影响水生生态系统,损害动物和人的神经系统。然而,关于这种毒素的研究很少,特别是对动物和人类中枢神经系统的影响。因此,本研究旨在通过观察斑马鱼脑内凋亡基因的表达异常、脑内超微结构的损伤,揭示斑马鱼脑内对蛇毒的反应机制。试验选用110日龄左右、平均体重(0.4±0.01)g的无病毒雄性斑马鱼(Danio rerio),经过7 ~ 10 d的驯化,随机分为对照组和处理组(每组45尾)。两组大鼠分别腹腔注射30μL 0.01 mol/L醋酸溶液(对照组)和30μL 0.01 mol/L含隐毒素的醋酸溶液(治疗组为5.3 μg STXeq/kg体重)。在每个时间点(1、3、6、9、12、24h),每组取5尾斑马鱼进行冷休克(-8℃下包埋于碎冰中),取全脑脑组织,一次性用0.86%的冰冷生理盐水冲洗,2.5%戊二醛溶液浸泡电镜观察。在每个时间点的另外5条鱼中,按照上述方法取出全脑,在液氮中冷冻,并在-70℃保存,以供后续RNA分析。预处理后的大脑(9h)在分级乙醇和环氧丙烷中脱水,包埋在Epon 812中,在超微切片机(Leica,Germany)上用玻璃刀切成超薄切片。切片在电镜前用醋酸铀酰和柠檬酸铅染色(JEM-1230,日本)。取冷冻(-70℃)斑马鱼全脑45mg(每个时间点5条)(IKA Werke,德国),用冷冻TRIzoL试剂(w:v,1:20,30s)均质,提取总RNA。使用RT-PCR试剂盒(Promega,USA)根据制造商的方案检测基因特异性RNA水平。反应体系按50μL进行:反应中加入25μL 2xaccessquick TM Master Mix、5μL oligo-dT、10 μmol/L上下游引物、1 μg模板RNA和无rnase MilliQ water至50μL。加入AMV逆转录酶(1μL), 45℃孵育45 min进行逆转录。扩增条件为40个循环,分别为95℃30s、58℃30s、72℃45s,最后进行扩增(72℃10min)。RT-PCR扩增物在1.5%-2.0%琼脂糖凝胶(60-100 V,40 A,30min)上电泳,溴化乙啶染色,在生物成像系统(M-20X,UVP,美国)上可视化,并使用分析软件(Quantity One v4.62,Bio-Rad,美国)进行密度测定。所有统计分析均采用商业软件(SPSS 13.0,Chicago,IL,USA),采用单因素方差分析(ANOVA)结合最小显著性差异(LSD)事后检验来表达组间差异的显著性(P0.05和P0.01)。结果表明,表观毒素可诱导脑细胞在超微结构上发生凋亡,如膜泡、凋亡样体等。在分子水平上进一步分析,p53、bax、caspase-3和c-jun基因的表达增加并呈时间依赖性,表达上调量分别是对照组的1.92倍、1.55倍、1.6倍和1.55倍。这些结果表明,表观毒素可能通过增加基因的表达导致脑组织超微结构的凋亡损伤。脑细胞对隐性毒素的反应机制可通过线粒体途径激活,涉及p53→bax→caspase-3基因级联。因此,该毒素可通过凋亡的方式导致脑细胞死亡,并表现出损伤脑的神经毒性。这些发现提供了直接的证据,淡水蓝藻表观毒素可以发挥对脑组织的毒性作用。这也为在分子水平上发现脑细胞对淡水蓝藻神经毒素的反应机制提供了有力的证据。
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RESPONSE OF APOPTOTIC GENES TO APHANTOXIN-PARALYTIC SHELLFISH POISON IN FRESHWATER EXTRACTED FROM THE APHANIZOMENON FLOS-AQUAE DC-1 IN CELLS OF BRAIN ON ZEBRAFISH (DANIO RERIO)
The Aphanizomenon flos-aquae DC-1,frequently appeares in freshwater,is a dominant species in Dianchi Lake of Yunnan Province,China,in winter and spring.During the past 20 years,blooms of Aphanizomenon flos-aquae DC-1 have occurred in the Dianchi Lake per year because of heavy pollution and the dominant species overgrowth.The blooms always sustained for six months in a year,even throughout a year in some water of Dianchi Lake.And the blooms could also give off distasteful smell into the air.As a result,visitors are more likely to breathe the odorous air than fresh air today,and see a bad scenery of green-mud water than clear blue waters.Especially the dominant species can produce aphantoxins,which is attributed to the paralytic shellfish poisons(PSPs) and influences aquatic ecosystem and damages the nerve system of animals and human.However,little research has been carried out on the toxin,in particular the effects on central nervous system(CNS) of animals and human.Thus the present research is to investigate abnormity of apoptotic gene expression,ultrastructural damage of brain induced by aphantoxin,to reveal mechanism of response of brain on zebrafish to aphantoxins.Virus-free male zebrafish(Danio rerio),110 days old or so,average bodyweight of(0.4±0.01) g,after 7—10 days of acclimatization,were randomly assigned into control and treated groups(45 fish per group).The two groups were received 30μL 0.01 mol/L acetic acid solution(control) and 30 μL 0.01 mol/L acetic acid solution contained aphantoxins(5.3 μg STXeq/kg bodyweight,treated) through intraperitoneal injections(i.p.).At each time point(1,3,6,9,12 and 24h),five zebrafish in each group were sacrificed by cold shock(embedding into crushed ice at -8℃),and cerebra were removed from whole brain and washed at once in 0.86% ice-cold physiological saline,prefixed in 2.5% glutaraldehyde solution for electron microscopy.In another 5 fish at each timepoint,whole brains were removed as described above,frozen in liquid nitrogen,and stored at either -70℃ for subsequent RNA analysis.The prefixed cerebra(at 9h) were dehydrated in graded ethanol and propylene oxide,embedded in Epon 812,and cut into the ultra-thin sections using glass knives on an ultramicrotome(Leica,Germany).Sections were stained with uranyl acetate and lead citrate before electron microscopy(JEM-1230,Japan).The 45mg frozen(-70 ℃) whole brain(five fish each timepoint) of zebrafish were homogenized(IKA Werke,Germany) in ice-cold TRIzoL reagent(w:v,1:20,30s) to extract total RNA.Gene-specific RNA levels were measured using an RT-PCR kit(Promega,USA) according to the protocol of manufacturer.The system of reactions was carried out into 50μL as follows:Reactions contained 25μL of 2× AccessQuick TM Master Mix,5 μL oligo-dT,10 μmol/L upstream and downstream primers,1 μg template RNA,and RNase-free MilliQ water to 50μL.AMV reverse transcriptase(1μL) was added and incubated at 45℃ for 45 min for reverse transcription.Samples were then heated at 95℃ for 5min before PCR;amplification conditions were 40 cycles of 95℃ for 30s,58℃ for 30s,72℃ for 45s,followed by a final extension step(72℃ for 10min).RT-PCR amplicons were analyzed by elec-trophoresis on 1.5%—2.0% agarose gels(60—100 V,40 A,30min),ethidium bromide staining,visualization on a Bio-imaging System(M-20X,UVP,USA),and densitometry using analytical software(Quantity One v4.62,Bio-Rad,USA).All statistical analyses employed commercial software(SPSS 13.0,Chicago,IL,USA) and assessed by one-way analy-sis of variance(ANOVA) combined with least significant difference(LSD) post-hoc tests to express significances of differences between groups(P0.05 and P0.01).The results showed that aphantoxins could induce the apoptosis of brain cells in ultrastructure,such as the membrane blebbing and apoptotic-like body.And it was further analyzed on molecular level to reveal that the expressions of p53,bax,caspase-3 and c-jun genes were increased and followed with time-dependent manner whose level of expression upreguation were 1.92,1.55,1.6 and 1.55 times that of control respectively.These results displayed that aphantoxins could lead to apoptotic ultrastructural damage of brain tissues through increasing expression of genes.And the brain cells could activate the mechnism of response to aphantoxins through the mitochondrial route which was involved in the cascade of p53→bax→caspase-3 genes.Therefore the toxin could result in death of brain cells by apoptotic way and exhibited the neurotoxicity of damage brain.These findings provide direct evidence that freshwater cyanobacterial aphantoxins can exert toxic effects on brain tissue.This is also strong evidences that find the mechanism of response on molecular level from brain cells to cyanobacterial neurotoxins of freshwater.
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