香石竹的叶片培养及植株再生

１植物名称香石竹（Ｄｉａｎｔｈｕｓｃａｒｙｏｐｈｙ－ｌｌｕｓ）,别名康乃馨。２材料类别无菌苗叶片。３培养条件以ＭＳ为基本培养基。分化培养基附加：（１）６－ＢＡ１．０ｍｐ·Ｌ－１（单位下同）＋ＮＡＡ０．３;（２）６－ＢＡ１．０＋ＮＡＡ０．１;（３）６－ＢＡ１．０＋ＮＡＡ０．０５。增殖培养基附加６－ＢＡ０．５＋ＮＡＡ０．１。分化和增殖培养基均加蔗糖３％、琼脂０．７％,ｐＨ５．８。生根培养基为１／２ＭＳ附加ＮＡＡ０．１,蔗糖２％,琼脂０．６％,ｐＨ５．８。培养温度为（２５±１）℃,光照１２ｈ·ｄ－１,…     

5—羟色胺对肺动脉平滑肌细胞在缺氧条件下增殖的作用

本研究应用细胞培养、＾３Ｈ－ＴｄＲ掺入,核酸分子杂交、免疫组织化学染色技术,探讨无氧（０％Ｏ２＋９５％Ｎ２＋５％ＣＯ２）和／或低氧（２．５￣３％Ｏ２＋９２％Ｎ２＋５％ＣＯ２）对新生小牛肺动脉平滑肌细胞增殖和５－羟色胺转载体基因表达的影响。结果表明：无氧２４ｈ可刺激ＰＡＳＭ的ＤＮＡ合成,＾３Ｈ－ＴｄＲ的掺入增加（Ｐ〈０．０５）,加入５－羟色胺能非常显著地促进无氧ＰＡＳＭ增殖（Ｐ〈０．００１）,而对常     

芥蓝的组织培养和快速繁殖

１植物名称芥蓝（Ｂｒａｓｓｉｃａａｌｂｏｇｌａｂｒａ）优良种株,取自广东汕头白沙蔬菜原种研究所。２材料类别未开花的植株基部腋芽。３培养条件（１）诱导丛生芽培养基为Ｍ１：ＭＳ＋６－ＢＡ２ｍｇ·Ｌ‘（单位下同）＋ＮＡＡ０．２;Ｍ２：ＭＳ＋６－ＢＡ１＋ＮＡＡ０．１;Ｍ３：ＭＳ＋６．ＢＡ１＋ＮＡＡ０．２。上述培养基均含蔗糖３％,琼脂０．８％,ｐＨ５．８～６．０。（２）生根培养基：ＭＳ＋ＮＡＡ０．５＋２％蔗糖＋０．４５％卡拉胶（０．７％琼脂）。培养温度２０～２５℃,光照１２ｈ．ｄ－１,光照度２０００１ｘ４…     

刺五加在大鼠实验性肝癌诱发过程中作用的探讨

目的探讨大鼠实验性肝癌发病中刺五加对肌体免疫功能和抗氧化酶活性的影响。方法４６只ＳＤ雄性大鼠被随机分成对照组（喂普通饲料）、３－甲基４－双甲氨基偶氮苯（３－Ｍｅ－ＤＡＢ）组（喂含０．０６％３Ｍｅ－ＤＡＢ饲料 １０周）和刺五加组（饲喂同 ３－Ｍｅ－ＤＡＢ外、另加入刺五加 ４．５ｇ／ｋｇ饲料,用常规方法检测全血谷光甘肽过氧化物酶（ＧＳＨ－ＰＸ）、血清超氧化物歧化酶（ＳＯＤ）活性和丙二醛（ＭＤＡ）含量,用微量化学发光造检测吞噬细胞活性（ＰＭＮ－ＣＬ）。结果１．ＰＭＮ－ＣＬ检测峰值、积分值和吞噬细胞指数,３－ＭｅＤＡＢ组较正常组和刺五加组均有显著升高（Ｐ＜０．０５和Ｐ＜０．０１）２．全血ＧＳＨ－ＰＸ活性、ＳＯＤ活性,刺五加组较３－ＭｅＤＡＢ组均有显著升高（Ｐ＜０．０５）。ＭＤＡ含量刺五加组和３－ＭｅＤＡＢ组均较正常组升高（均Ｐ＜０．０５）。结论刺五加在大鼠实验性肝癌诱发过程中有提高抗氧化酶活性和对抗致癌剂引起的机体中性粒细胞吞噬功能代偿性增高的作用。     

刺槐宽叶和四倍体无性系的组织培养

１植物名称刺槐（Ｒｏｂｉｎｉａｐｓｅｕｄｏａｃａｃｉａ）优良无性系：Ｔｅｔｒａｐｌｏｉｄｌｏｃｕｓｔ、Ｇｌｇａｓｔｙｐｅｌｏｃｕｓｔ。２材料类别带腋芽的茎段。３培养条件（１）启动培养基：ＭＳ＋６－ＢＡ０．２５ｍｇ·Ｌ－１（单位下同）＋ＮＡＡ０．０５。（２）分化培养基和继代培养基：ＭＳ＋６－ＢＡ０．５＋ＮＡＡ０．１＋ＡｇＮＯ３１０,ＭＳ＋６ＢＡ０．５＋ＮＡＡ０．１。上述培养基均添加３％蔗糖、０．６％琼脂。（３）生根培养基：１／２ＭＳ＋ＩＢＡ０．２＋ＮＡＡ０．２,添加２％蔗糖０．６％琼脂。培养基ｐＨ…     

酸枣的组织培养和植株再生

１植物名称酸枣（Ｚｉｚｙｐｈｕｓ　ｊｕｊｕｂａｖａｒ．Ｓｐｉｎｏｓａ）。２材料类别沂河岸堤自然生长的野生植株上的嫩芽。３培养条件诱导愈伤组织培养基：（１）ＭＳ＋６－ＢＡ２ｍｇ·Ｌ’（单位下同）＋ＮＡＡ０．１;（２）ＭＳ＋６－ＢＡ２＋ＮＡＡ０．２;（３）ＭＳ＋６．ＢＡ２＋ＮＡＡ０．４;（４）ＭＳ＋６．ＢＡ２＋ＮＡＡ１;（５）ＭＳ＋６．ＢＡ２＋ＮＡＡ０．０１;（６）ＭＳ＋６．ＢＡ２＋ＮＡＡ０．０５;（７）ＭＳ＋６－ＢＡＩ＋ＮＡＡ０．５。芽分化培养基：（８）ＭＳ＋６－ＢＡＩ;（９）ＭＳ＋６－ＢＡ２;（…     

双歧杆菌活菌制剂对慢性乙肝病人细胞免疫功能影响的观察

在应用双歧杆菌活菌制剂治疗慢乙肝期间,重点观察了Ｔ细胞亚群（ＣＤ３,ＣＤ４,ＣＤ８）、ＮＫ细胞（ＣＤ（１６））、白细胞介素Ⅱ（ＩＬ－２）分泌细胞、肿瘤坏死因子（ＴＮＦ）等细胞免疫指标治疗前后的动态变化,同时观察了病人血内毒素水平的动态变化和乙肝病毒标志物（ＨＢＶＭ）的改变。结果表明：（１）与对照组比较,双歧杆菌活菌制剂可使慢乙肝病人ＣＤ３＋,ＣＤ４＋数目明显增多,而对ＣＤ８＋细胞数目无明显影响;（２）双歧杆菌活菌制剂可使ＣＡＨ组的ＣＤ１６＋细胞显著增多（ｐ＜０．０５）;使ＣＡＨ组和ＣＰＨ组的ＩＬ－２分泌细胞均有非常显著和显著增加（分别ｐ＜０．０１和ｐ＜０．０５）;（３）ＣＡＨ组病人血中内毒素和ＴＮＦ水平在双歧杆菌活菌制剂治疗后,匀出现非常显著降低（ｐ＜０．０１）;ＣＰＨ组ＴＮＦ水平较对照组无显著变化,但内毒素水平较对照组显著降低（ｐ＜０．０５）;（４）满疗程后（６０天）ＣＡＨ组有６例,ＣＰＨ组有５例ＨＢｅＡｇ阴转（分别为２６．０６％和２５．０％）,而对照组仅２例阴转（１３．３３％）,两治疗组与对照组比较有显著性差异（ｐ＜０．０５）。     

杜氏盐藻细胞质膜氧化还原系统

杜氏盐藻细胞质膜具的氧化ＮＡＤ（Ｐ）Ｈ,还原Ｆｅ（ＣＮ）＾３－６和Ｏ２的氧化还原系统。当Ｆｅ（ＣＮ）＾３－６浓度为０．６ｍｍｏｌ／Ｌ,氧化ＮＡＤＨ的Ｋｍ为９６μｍｏｌ／Ｌ,Ｖｍａｘ为１５９ｎｍｏｌ１０＾－８ｃｅｌｌｓｍｉｎ＾－１,最适ｐＨ为８．５。ＴｒｉｔｏｎＸ－１００可促进ＮＡＤＨ和Ｆｅ（ＣＮ）＾３－６的氧化还原活性。ＮＡＤＨ能促进藻细胞的氧吸收,最适ｐＨ为８．５。在无外源电子供体存在时,细胞质     

紫菀花序芽培养及植株再生

１植物名称紫菀（Ａｓｔｅｒｔａｔａｒｉｃｕｓ）。２材料类别花序芽。３培养条件愈伤组织、不定芽诱导及增殖培养基：（１）ＭＳ＋６－ＢＡ０．５～２．０ｍｇ·Ｌ－１（单位下同）;生根培养基：（２）ＭＳ＋ＮＡＡ０．５～２．０＋６－ＢＡ０．２,（３）１／２ＭＳ（大量元素减半）＋ＮＡＡ０．５～２．０＋６－ＢＡ０．２。上述培养基均加０．８％琼脂和３％蔗糖,高温高压灭菌前ｐＨ值调至５．８。培养温度为（２３１２）℃,每天光照１２ｈ,光照度为１５００～２０００ｌｘ４生长与分化情况４．１愈伤组织及不定芽的诱导剪取长约０…     

宫粉郁金的组织培养和快速繁殖

１植物名称宫粉郁金（Ｃｕｒｃｕｍａ　ｋｗａｎｇｓｉｅｎｓｉｓ）。２材料类别　块茎萌动芽。３培养条件　萌动芽生长培养基：（１）ＭＳ＋６－ＢＡ１ｍｇ·Ｌ－１（单位下同）＋ＮＡＡ０．２。不定芽增殖与愈伤组织诱导培养基：（２）ＭＳ＋６－ＢＡ１０＋ＫＴ５;（３）ＭＳ＋６．ＢＡ１０;（４）ＭＳ＋６－ＢＡ５＋ＫＴ２．５;（５）ＭＳ＋６－ＢＡ５;（６）ＭＳ＋６－ＢＡ２＋ＫＴ１。生根培养基：（７）ＭＳ＋ＮＡＡ０．５;（８）ＭＳ＋６－ＢＡ０．５＋ＮＡＡ０．５;（９）ＭＳ。以上培养基均加０．７％琼脂,３％蔗糖,ｐＨ５…     

ALGAE AS COMPETITORS FOR GLUCOSE WITH HETEROTROPHIC BACTERIA1

Dissolved organic carbon (DOC) constitutes the bulk of organic carbon in aquatic environments. The importance of DOC utilization by mixotrophic algae is unclear since heterotrophic bacteria are regarded as more efficient users. We tested the hypothesis that algae decrease the DOC concentration in the light to lower levels than in darkness resulting in competitive exclusion of heterotrophic bacteria according to the mechanistic competition theory. We investigated (a) the uptake kinetics of glucose as a model substrate by two cultured algae and mixed bacteria populations, (b) the competition for glucose between algae and bacteria in chemostats, (c) the effect of discontinuous glucose supply in chemostats, and (d) the minimum glucose concentrations achieved in cultures of algae and bacteria. Bacteria showed higher specific‐glucose‐uptake rates than algae. In chemostats, algae became extinct in the dark and coexisted in the light where they decreased bacteria to lower densities. Discontinuous glucose supply promoted the algae compared to continuous substrate addition. Several algae consumed glucose to lower concentrations in the dark than in the light and showed lower or equal residual glucose concentrations than bacteria. Residual concentrations were not related to allometric traits (cell volume) and photosynthetic potential (chl content). Overall, the hypothesis was not supported, and mechanisms of competition for DOC obviously differed from those for particulate prey. However, since some algae showed lower or equal residual glucose concentrations than bacteria, algal dark uptake of DOC may be important in deep layers of many waters.     

Influence of metazooplankton on interactions of bacteria and phytoplankton in an oligotrophic lake

Commensalism based on organic carbon supplied by phytoplanktonand competition for mineral nutrients are important interactionsbetween bacteria and phytoplankton in oligotrophic clear-watersystems. Both interactions are influenced by zooplankton activity.To examine the relation ship between algae and bacteria in LakeLa Caldera, we studied: the correlations among phyto plankton,bacteria and phosphorus (P) dynamics; the ratio of organic carbonsupplied by algae to organic carbon demand by bacteria; andthe importance of P remineralized by metazooplankton for bothcommunities. Phytoplankton and bacteria had a similar seasonaldynamics, and there was a sig nificant and positive relationshipbetween bacterial abundance and algal biomass (P<0.01). However,the release of organic carbon from phytoplankton was usuallyhigher than the bacterioplankton carbon requirement. P availablevia zooplankton remineralization satisfied between 74 and 316%of the minimum P demands of algae and bacteria. To elucidatewhether zooplankton operate similarly on algae and bacterialgrowth or indirectly influence bacterial growth through phytoplanktonmetab olism, we performed zooplankton manipulation experiments.High zooplankton biomass in these experiments stimulated bothprimary and bacterial production, but release of organic carbonfrom phytoplankton declined. These results suggest a directstimulus of bacterial growth, so algae and bac teria can balancegrazing losses by compensatory growth. Further, the algal decreaseof the organic carbon supply for bacteria could, over time,lead to a change in the algae-bacteria interaction from competitionto commensalism. This reduction in organic carbon excretioncould affect the balance of the competitive interaction.     

Studies on the purification of wastes from the nitrogen fertilizer industry by intensive algal cultures. IV. growth of Chlorella vulgaris in wastes with high nitrogen content in continuous and intermittent light.

The growth and utilization of nitrogen by intensive Chlorella vulgaris in wastes from production of urea, containing 1300 mg NH4+-N and 4000 mg urea-N/1, was investigated. In these conditions only Chlorella vulgaris AA strain, adapted to high concentrations of ammonia nitrogen, was able to grow. The elimination of nitrogen by continuous cultures was 750 mg urea-N/1 with 5-day flow rate. A considerable part of the urea was hydrolized by urease bacteria and removed in the form of NH3. The effect of intermittent light on the growth of algae was also studied. The better growth than in continuous light, was obtained with alternate one hour periods of light and darkness. Good results were also obtained with the use of 12 hour light and 12 hour darkness.     

In situ simultaneous organics and nitrogen removal from recycled landfill leachate using an anaerobic-aerobic process

An anaerobic-aerobic process including a fresh refuse landfill reactor as denitrifying reactor, a well-decomposed refuse reactor as methanogenesis reactor and an aerobic activated sludge reactor as nitrifying reactor was operated by leachate recirculation to remove organic and nitrogen simultaneously. The results indicated that denitrification and methanogenesis were carried out successfully in the fresh refuse and well-decomposed landfill reactors, respectively, while the nitrification of NH(4)(+)-N was performed in the aerobic reactor. The maximum organic removal rate was 1.78 kg COD/m(3)d in the well-decomposed refuse landfill reactor while the NH(4)(+)-N removal rate was 0.18 kg NH(4)(+)-N/m(3)d in the aerobic reactor. The biogas from fresh refuse reactors and well-decomposed refuse landfill reactors were consisted of mainly carbon dioxide and methane, respectively. The volume fraction of N(2) increased with the increase of NO(3)(-)-N concentration and decreased with the drop of NO(3)(-)-N concentration. The denitrifying bacteria mustered mainly in middle layer and the denitrifying bacteria population had a good correlation with NO(3)(-)-N concentration.     

Estimating Bacterioplankton Production by Measuring [H]thymidine Incorporation in a Eutrophic Swedish Lake

Bacterioplankton abundance, [H]thymidine incorporation, CO(2) uptake in the dark, and fractionated primary production were measured on several occasions between June and August 1982 in eutrophic Lake Norrviken, Sweden. Bacterioplankton abundance and carbon biomass ranged from 0.5 x 10 to 2.4 x 10 cells liter and 7 to 47 mug of C liter, respectively. The average bacterial cell volume was 0.185 mum. [H]thymidine incorporation into cold-trichloroacetic acid-insoluble material ranged from 12 x 10 to 200 x 10 mol liter h. Bacterial carbon production rates were estimated to be 0.2 to 7.1 mug of C liter h. Bacterial production estimates from [H]thymidine incorporation and CO(2) uptake in the dark agreed when activity was high but diverged when activity was low and when blue-green algae (cyanobacteria) dominated the phytoplankton. Size fractionation indicated negligible uptake of [H]thymidine in the >3-mum fraction during a chrysophycean bloom in early June. We found that >50% of the H activity was in the >3-mum fraction in late August; this phenomenon was most likely due to Microcystis spp., their associated bacteria, or both. Over 60% of the CO(2) uptake in the dark was attributed to algae on each sampling occasion. Algal exudate was an important carbon source for planktonic bacteria. Bacterial production was roughly 50% of primary production.     

海水中藻菌共培养体系对碳氮磷的吸收转化

海洋环境中,细菌和微藻之间的物质交换是生源要素在自然界中迁移转化的重要方式。为进一步了解生源要素的生物地球化学循环,在实验室模拟条件下,研究了共培养体系中营养盐和有机物在细菌和微藻之间的转换。通过纯培养中肋骨条藻(Skeletonema costatum)、东海原甲藻(Prorocentrum donghaiense)、天然海水中的细菌以及藻菌混合培养,分析了营养盐和有机物随藻菌生物量的变化情况,并计算了溶解有机碳(DOC)和溶解有机氮(DON)的浓度比值[(DOC/DON)a]。结果发现,在共培养体系中,细菌对中肋骨条藻的生长有抑制作用,对东海原甲藻影响不明显;中肋骨条藻有利于细菌生长,东海原甲藻抑制细菌生长,这种不同可能与微藻的粒径有关。海洋细菌在2种藻的指数生长均期均会促进微藻吸收氨氮(NH_4-N),但在生长末期NH_4-N以释放为主。硝氮(NO_3-N)的浓度与藻的生长呈负相关,但在衰亡期NO_3-N略有增加,表明NO_3-N再生所需时间较长。细菌对硝氮的吸收量较少,但对其再生有贡献。细菌和中肋骨条藻对磷酸盐(PO_4-P)的吸收存在竞争,但与东海原甲藻的竞争关系不明显。不同培养体系中DOC浓度变化不同,在藻菌共培养体系中增加较快,纯藻培养体系中增加缓慢,在纯菌培养体系中缓慢减少。通过对DOC与DON浓度比值的分析,发现用判断颗粒有机碳(POC)来源的方法可以分析DOC的来源。     

基于好氧反硝化及反硝化聚磷菌强化的低温低碳氮比生活污水生物处理中试研究

【背景】低碳氮比生活污水很难达标处理,多级A/O工艺、生物强化技术及生物膜技术的有机结合可有效解决这一问题。【目的】开发出一种泥膜共生多级A/O工艺并进行中试研究,驯化出高效脱氮除磷菌剂并对系统进行生物强化。【方法】通过测定中试设备出水及污水处理厂出水化学需氧量(Chemical oxygen demand,COD)、氨氮(NH_4~+-N)、硝氮(NO_3~--N)、总氮(Total nitrogen,TN)、总磷(Total phosphorus,TP)对比分析两种工艺的污染物去除效能,利用高通量测序技术对比生物强化技术对系统微生物群落结构的影响。【结果】中试设备对COD、NH_4~+-N、NO_3~--N、TN、TP的去除效果均优于污水处理厂的处理工艺;驯化的低温好氧反硝化菌TN去除率最大值可达84.21%,驯化的低温反硝化聚磷菌群对磷的去除率最高可达85.75%;利用驯化菌群对中试设备进行生物强化后较好地改善了系统NH_4~+-N、NO_3~--N、TN、TP的去除效果;经生物强化后,具有好氧反硝化和反硝化聚磷功能的Pseudomonas菌群明显增多。【结论】泥膜共生多级A/O工艺对于低碳氮比生活污水的处理具有很好的效果,利用生物强化技术可有效提高低温条件下系统污染物去除效能。     

氮肥形态对冬小麦根际土壤氮素生理群活性及无机氮含量的影响

采用大田盆栽方法研究了硝态氮肥、铵态氮肥、酰胺态氮肥3种氮肥形态对冬小麦品种豫麦50生育中后期(拔节期、开花期、花后14 d、花后28 d)根际土壤氮转化相关微生物活性、酶活性和根际土壤NH+4离子、NO-3离子含量的影响。结果表明:随着生育期的推进,除脲酶外,氨化细菌、硝化细菌、亚硝化细菌、反硝化细菌和蛋白酶活性变化的均为"倒V"型变化特征,以花后14 d活性最强;而脲酶活性在拔节期最强,并且其活性远大于其它微生物及酶。氮肥形态对根际土壤氮素生理群及无机氮的影响不同。酰胺态氮肥促进了根际氨化细菌、反硝化细菌、脲酶、蛋白酶的活性,而硝化细菌、亚硝化细菌在硝态氮肥条件下活性较强。除拔节期外,土壤中NH+4离子在铵态氮肥处理下含量较高,NO-3离子在酰氨态氮肥处理下含量较高。因此,酰胺态氮能够促进小麦根际土壤有机氮的分解,硝态氮肥可以促进土壤中氨的转化,以利于小麦根系的吸收与利用。氮肥形态主要是通过影响土壤中氮素生理类群及酶的活性,从而影响土壤中无机氮的含量。     

DETECTION OF LIMITING OR SURPLUS NITROGEN IN ALGAE AND AQUATIC WEEDS1

The rate of NH₄+-N absorption by algae and aquatic weeds in the dark has been shown to be 4-5 times greater for plants which are N-limited as compared to plants with sufficient available N. Eight species of green algae, 2 blue-green algae, 2 diatoms, and 3 aquatic weeds were used to demonstrate the usefulness of the test in determining if available N was in surplus or limited supply in a particular environment. The test was shown not to differentiate between blue-green algae capable of fixing N (4 species) from media with NO₃-N or without combined nitrogen. The factors influencing the results of NH4⁺-N absorption tests have been investigated. In order to differentiate between plants with sufficient available N and those which are N limited, the rate of NH₄⁺-N absorption (0.1 mg N) over 1-hr incubation in the dark by 10-20 mg of algae or aquatic weed tissues is measured. The relatively simple analysis for NH₄⁺-N in the samples makes it very easy to follow the changing N nutrition of plants in cultures with a limited N supply or in the presence of possible N sources.     

微藻-细菌共生体系在废水处理中的应用

在微藻-细菌协同共生的过程中,藻类光合作用释放的氧气被异养微生物利用来矿化水体中的污染物,细菌呼吸为藻类提供二氧化碳作为碳源。近年来,藻类-细菌协同共生体系在污水处理中的应用得到了广泛的研究。本文重点综述了菌藻协同共生体系中微藻与细菌之间的三种相互作用,以及菌藻协同共生体系在废水处理中的应用。菌藻协同共生体系中的微藻与细菌通过营养交换、信号转导及基因转移等相互作用实现共赢。该体系广泛用于处理富营养化、重金属、药物、多环芳烃(polycyclicaromatic hydrocarbons,PAHs)、石油烃化合物等难降解的有机污染的水体。对于氮、磷等营养物质的去除,其主要机理涉及同化作用、厌氧氨氧化作用、硝化与反硝化作用、磷酸化作用等。对重金属、药物、石油烃化合物及其他有机化合物的去除机制主要是生物吸附、生物富集及细胞内外的生物降解。