Peak BMP Responses in the Drosophila Embryo Are Dependent on the Activation of Integrin Signaling
外文翻译 水性涂料

Progress in Organic Coatings 77 (2014) 315–321Contents lists available at ScienceDirectProgress in Organic Coatingsjou rn a l ho m e p ag e: www.el se vie r.co m/lo cat e/po rgco a tPreparation and properties of waterborne polyurethane/epoxy resincomposite coating from anionic terpene-based polyol dispersionGuo-min Wu a,b,∗, Zhen-wu Kong a,b,∗, Jian Chen a , Shu-ping Huo a , Gui-feng Liu a,ba Institute of Chemical Industry of Forest Products, Chinese Academy of Forestry, Key Laboratory of Biomass Energy and Material of Jiangsu Province, Keyand Open Laboratory on Forest Chemical Engineering, State Forestry Administration, National Engineering Laboratory for Biomass Chemical Utilization,Nanjing 210042, Chinab Research Institute of New Technology, Chinese Academy of Forestry, Beijing 10091, Chinaa r t i c l e i n f o ab s t r ac tArticle history:Received 22 July 2013Received in revised form 9 September 2013Accepted 20 October 2013Available online 14 November 2013Keywords:PolyolWaterborne polyurethaneEpoxy resinCompositeTerpeneAn anionic polyol (T-PABA) dispersion was prepared by modifying terpene-based epoxy resin with para-aminobenzoic acid. Then T-PABA dispersion was crosslinked with a hexamethylene diisocyanate (HDI)tripolymer to prepare waterborne polyurethane/epoxy resin composite coating. The rheological proper-ties and particle size distribution of the composite system were characterized by rotary rheometer andlaser particle size analyzer. The crosslinked composite product has good thermal resistant properties,with glass-transition temperatures (T g ) about 40% and 50% weight loss temperatures (T) in the rangeof 400–420. The smooth and transparent film obtained from the composite product has good flexibility,adhesion, impact strength, antifouling and blocking resistance properties. The impact strength, pencilhardness, water-resistant and thermal-resistant properties of the composite products increased with themolar ratio of isocyanate group to active hydrogen of T-PABA.© 2013 Elsevier B.V. All rights reserved.1.IntroductionConventional solvent-based polyurethanes, with their excel-lent outdoor durability, outstanding chemical resistance and verygood mechanical properties, are successfully used in variousapplications, such as original equipment manufacturer (OEM)coats, automotive repair coatings, industrial paints, furniture lac-quers, plastic coatings and adhesives [1,2]. Recently, controllingthe emission of volatile organic compounds (VOCs) is becomingthe important driving force for resin developments. The substi-tution of solvent-based coatings with water-dispersed coatingsis a major approach to reduce VOC emission. Two-componentwaterborne polyurethanes (2K-WPUs) coatings which integratethe environment-friendly property of water-dispersed coatingswith the high performance of two-component polyurethanes, aregaining extensive research attention [3–6]. 2K-WPUs comprisea polyisocyanate component and a waterborne polyol compo-nent which results in various performances of the 2K-WPUsdue to the various structures of the polyols. The most com-monly used waterborne polyol is polyacrylate polyol whichhas been applied widely in the field of coatings and adhesive∗Corresponding author at: No. 16, Suojin Wucun, Nanjing 210042, PR China.E-mail addresses: woogm@ (G.-m. Wu), kongzw@(Z.-w. Kong).[7–9]. However, the polyacrylate polymer has some shortcomingssuch as bad temperature adapt property and organic solventresistibility. Polyurethane polyol is another promising hydroxylgroup component for 2K-WPUs with its high comprehensiveproperties, while the use-cost of polyurethane polyol is quiteexpensive [10,11].Most of these polyol components for 2K-WPUs originate fromthe unrenewable fossil resource. With the fossil resource beingexhausted, the utilization of biomass resource for preparing poly-mer materials has been paid more attention to by many scholarsall over the world [12,13]. Terpene-based epoxy resin (TME), analicyclic epoxy resin with endocyclic structure, was synthesizedfrom the raw material turpentine [14,15]. Recent investigationsshowed that it could also serve as precursors for the synthesis ofTME-based polyols which could be crosslinked with polyisocyanateto prepare polyurethane/epoxy resin composite polymers [16]. Inthis article, an anionic polyol (T-PABA) dispersion was synthesizedby reacting TME with para-aminobenzoic acid (PABA). Then a newtwo-component waterborne polyurethane–epoxy resin compos-ite coating was prepared by crosslinking T-PABA dispersion withpolyisocyanate. The purpose of this study was in order to obtaina wonderful composite polymer product from the bioresource tur-pentine, which could combine the rigidity and heat resistance of theepoxy resin (TME), the flexibility and tenacity of the polyurethaneand the environmental friendliness and safety of the waterbornesystems together.0300-9440/$ – see front matter © 2013 Elsevier B.V. All rights reserved./10.1016/j.porgcoat.2013.10.005316G.-m. Wu et al. / Progress in Organic Coatings 77 (2014) 315–321Table 1Physicochemical parameters of T-PABA and T-PABA dispersionT-PABA (solid resin)Appearance Yellow transparent solidHydroxyl value (mg g-1 ) 168.9Amine value (mg g-1 ) 125.9Active hydrogen content (mmol g-1 ) 5.254T-PABA dispersionAppearance Yellow transparent liquidSolid content (%) 30Viscosity (mPa s, 25 ◦C) 400Average particle size (nm) 40Stability No delaminating after 6 months 2.Materials and methods2.1.MaterialsThe base material was the terpene-maleic ester-type epoxy resin (TME) with epoxy value of 0.34–0.38 mol 100 g−1, which was synthesized form turpentine [14]. Para-aminobenzoic acid (PABA), technical grade, was purchased from Changzhou Sunlight Pharmacy Industry Co., Ltd., China. N,N-dimethyl ethanolamine and 2-butanone, chemically pure, were purchased from Shanghai Lingfeng Chemical Reagent Co., Ltd., China. The hydrophilically modified hexamethylene diisocyanate (HDI) tripolymer (Fig. 1) with isocyanate (NCO) group content of 14 wt% and solid content of 85 wt%, technical grade, was supplied by Shanghai Sisheng Polymer Materials Co., Ltd., China.2.2.Synthesis of T-PABA and T-PAB dispersionA 500 ml four-necked flask equipped with stirrer, thermometer, condenser and heating mantle was charged with 30.6 g TME, 10.6 g PABA, and 16.5 g 2-butanone. After the PABA was all resolved in the 2-butanone under heating and stired, the reaction was contin-ued for 4 h at 80–90 ◦C. The 2-butanone was removed with vacuum distillation after reaction. The product (T-PABA) was neutralized with 4.8 g N,N-dimethyl ethanolamine, then dispersed with 96.0 g distilled water by churning at 500–1000 rpm, at 50–70 ◦C. A yel-low transparent anionic dispersion (T-PABA dispersion) with solid content of 30% was obtained (Scheme 1). The physicochemical parameters of T-PABA and T-PABA dispersion were described in Table 1.2.3.Preparation of the composite coatingA composite dispersion was prepared by mixing T-PABA disper- sion with the hydrophilically modified HDI tripolymer at the molar ratio of active hydrogen to isocyanate group ranging from 0.8 to 1.4. The solid content of the blending was about 32% (by mass) as applied in this work. After mixed, the blending was cast on tin-plates or glass slides to form 40 μm (±3 μm) thick dry films. The crosslinked product of the composite dispersion was obtained by keeping the films in the room temperature for 24 h and then curing them in an oven at 70 ◦C for 6 h.2.4. MeasurementsNicolet IS10 infrared spectrometric analyzer (Nicolet Instru-ment Co., U.S.A) was used to record the FT-IR spectra of polyol and composite product samples in the range of 400–4000 cm−1.13C NMR spectra were recorded on Bruker AV-300 NMR spec- trometer at 300 MHz. Deuteroacetone was used as a solvent and tetramethylsilane (TMS) was served as internal standard.Rheological properties of the T-PABA dispersion (30% solid content) and the composite dispersion (32% solid content) were performed with a Haake Mars-III rotational rheometer using coaxial cylinder technique.Particle size analysis was carried out on a Nano-ZS ZEN3600 Zeta-sizer (Malvern Instrument Co., UK). The T-PABA dispersion and the composite dispersion were diluted with distilled water to 0.5% solid content.The morphology of the composite product was characterized by atomic force microscope (AFM) performed on a SPM9600 AFM (Shimadzu, Japan). To prepare AFM sample, the composite sample was cast a film on silicon substrate.Mechanical properties of the composite product were evaluated according to standard test methods (impact strength GB/T 1732-93 [17], adhesion GB/T 1720-89 [18], flexibility GB/T 1731-93 [19], pencil hardness GB/T 6739-96 [20]). Water resistance, antifoul-ing and blocking resistance properties are measured according to standard test method GB/T 23999-2009 [21].PerkinElmer Diamond differential scanning calorimeter (U.S.A) was used to record the differential scanning calorimetry (DSC) ther-mograms of the composite products at a heating rate of 20 ◦C min−1 under a nitrogen gas flow of 20 ml min−1.NETZSCH STA 409 PC/PG thermogravimetric analyzer (Germany) was used to perform thermogravimetric analysis (TGA) of the composite products at a heating rate of 10 ◦C min−1 under a nitrogen atmosphere.3.Results and discussion3.1.Characterization of T-PABAThe synthesis of T-PABA was carried out with the addition reac-tion between oxirane group and primary amine group (Scheme 1). The chemical structure of T-PABA was characterized with FT-IR (Fig. 2) and 13C NMR (Fig. 3) spectra. Compared with the spectra of TME, the significant enhancement of O H stretch-ing peak at 3480 cm−1 and the disappearance of the absorption peak at 908 cm−1 in the spectra of T-PABA denoted the occur-rence of addition reaction of oxirane ring and amine group [22]. FT-IR spectra of T-PABA show signification absorption peaks at 3200–3700 cm−1 (N H and O H stretching), 2400–2800 cm−1 and 1680 cm−1 (COOH stretching), 1605 and 1530 cm−1 (benzeneFig. 1. Chemical structure of the hydrophilically modified HDI tripolymer.G.-m. Wu et al. / Progress in Organic Coatings 77 (2014) 315–321 317Scheme 1. Preparation of T-PABA and T-PABA dispersion.ring stretching), 1730 cm −1 (C O stretching), 1273 cm −1 (C N stretching of aromatic amine), and 1117 cm −1 (C O stretching of secondary hydroxyl group), which match the chemical structure characteristic of T-PABA correctly.13C NMR spectra were used to further demonstrate the chemical structure of T-PABA. The characteristic single peaks of the oxi- rane ring (C1 and C2 in TME) at about ı = 43.5 ppm and 48.5 ppm were disappeared in the 13C NMR spectra of T-PABA [23]. After the reaction between oxirane group and primary amine group, the ı of C1 and C2 shifted the low frequency region, and appeared at about ı = 46.9 ppm and 63.9 ppm (C1I and C2I in T-PABA). Thepeaks at about 112 ppm, 113.5 ppm, 118.4 ppm, 132 ppm, and154 ppm show the typical benzene ring absorptions, and the peak at 168.4 ppm exhibits the absorption of the carboxyl group.3.2. Rheological properties of the T-PABA dispersion and the composite dispersionRheological properties are important for the use and storage of dispersions when applied as coatings and adhesives. Rheological behavior can be characterized by power-law equation [24]:τ = Ky n or η˛Kyn −1(1)Fig. 2. FT-IR spectra of T-PABA and TME.318G.-m. Wu et al. / Progress in Organic Coatings 77 (2014) 315–321Fig. 3. 13 C NMR spectra of T-PABA and TME.where τ is shear stress, K is viscosity coefficient, y is shear rate, n is flow behavior index, and ηα is apparent viscosity.The logarithmic form of power-law equation can be written, log τ = log K + n log y(2)The factor n can be obtained graphically from the slope of the log τ − log y line from linear regression. Fig. 4 shows the rheologi- cal curves of the T-PABA dispersion and the composite dispersion at 25 ◦C, and correspondingly Fig. 5 shows the log τ − log y lines. It can be seen from Fig. 4, the apparent viscosity of the T-PABA dispersion and the composite dispersion remained constant with the increas- ing of shear rate. Because the particles of the T-PABA dispersion and the composite dispersion are both charged particles, interac- tion force among particles is strong enough to stand against the shear stress in our measurement. As shown in Fig. 5, the obtained log τ has good linear correlation with log y , and the values of theFig. 4. Rheological curves of T-PABA and the composite dispersions.flow behavior index n equals approximately 1, which indicates the dispersions are Newton fluids.3.3. Particle size analysis of the dispersionsThe film formation process of waterborne resin contains floccu -lationa nd merging phenomena of the dispersion particles. Well dispersion of the resin is important to the performance of the crosslinked product. According to Stokes’ law, separating rate of the dispersion particles, which directly affects the stability of dis- persion, is directly proportional to the density difference of oil phase and water phase, the size of the particles, and inversely proportional to the viscosity of continuous phase [25]. When the density difference of oil phase and water phase and the viscosity of continuous phase are invariableness, the size of the particles can characterize the stability of waterborne dispersion. Fig. 6 shows theFig. 5. Log τ − log y line of T-PABA and the composite dispersions.G.-m. Wu et al. / Progress in Organic Coatings 77 (2014) 315–321 319Fig. 6. Particle size distributions of T-PABA and the composite dispersions.laser particle size analysis of the T-PABA and the composite disper- sions. The HDI tripolymer used to crosslink with T-PABA cannot disperse well in water, although it has been hydrophilically modi- fied. The average particle size of the HDI tripolymer is large, about 6120 nm. T-PABA can be dispersed stably in water and does not delaminate after storing for 6 months. Its average particle size is about 40 nm. After mixing these two components completely, the composite dispersion obtained has a unimodal distribution of the particle size with the average value of about 89 nm, bigger than that of T-PABA dispersion. This result indicates that when the two components are mixed, T-PABA dispersion can emulsify the HDI tripolymer and rebuild new particles.3.4. CharacterizationofthecompositeproductThe film formation process of the composite dispersion is as fol- lows: (1) solvent, water volatilizing, (2) particles merging together, (3) isocyanate (NCO) group of HDI reacting with hydroxyl (OH) group and amine (NH) group. The results of the particles merging and the chemical reaction were characterized by AFM and FT-IR, respectively. The 3-D surface micro topography of the compos- ite product obtained from AFM is shown in Fig. 7. The surface of the product is quite rough, containing many cone-shaped hillocks. When particles of the dispersion overlap with each other, only the edge parts of the particles can merge together, and then the unmerged parts of the particles exposed on the surface of the film are observed as cone-shaped hillocks. The “hillock topography” found on the surface of the film is the trace of merged particles of the dispersion, which indicates indirectly that there are lots of particle traces in the body of the film. This result validates theFig. 7. AFM image of the composite product.particle merging mechanism of the film formation of waterborne resin [26].Urethane ( NH CO O ) and urea ( NH CO NH ) are formed after NCO group of HDI reacting with OH group and NH group of T-PABA, respectively. The chemical structure of the composite product was characterized by FT-IR spectra (Fig. 8). The signi- fication absorption peaks at about 3360 cm −1 (N H stretching), 1680 cm −1 (C O stretching), 1536 cm −1 ( NH CO stretching), and 1240 cm −1 ( CO O C stretching) show the typical absorp- tions of urethane ( NH CO O ) and urea ( NH CO NH ) group [27]. The disappearance of the absorption peak at 2270 cm −1 (NCO stretching) denotes the occurrence of addition reaction of the NCO group with active hydrogen. The other absorption peaks in the spectra assign to stretching vibration of methyl and methylene (2850–2990 cm −1), benzene ring stretching (1605 and 1530 cm −1), bending vibration of methyl and methylene (1458 cm −1), isopropyl group stretching (1370 cm −1), C N stretching (1173 cm −1), and C O stretching of secondary hydroxyl group (1117 cm −1), respec- tively.3.5. PropertiesofthecompositeproductThe properties of the composite product of T-PABA are showed in Table 2. Due to the high activity of the NH group reacting with NCO group, the film of the composite product dried faster than the commercial product. The film obtained from the composite prod - uct has excellent impact strength, adhesion, flexibility, antifouling and blocking resistance properties. Impact strength, pencil hard- ness and water resistance of the composite product were enhanced by increasing NCO/NH (OH) ratio. Because the superfluous NCO groups can react with H 2O to form urea and biurea, it will increaseFig. 8. FT-IR spectra of the composite product.320G.-m. Wu et al. / Progress in Organic Coatings 77 (2014) 315–321Table 2Properties of the composite product.Item n NCO :n NH(OH)Crosslinked products of T-PABA Commercial product a0.8:11:1 1.2:1 1.4:1 1.4:1Drying time (min 25 ◦C)4045455090Gloss (60◦)94.895.495.895.590.5Impact strength (kg cm)60657070>50Adhesion (grade)21111Flexibility (mm)110.50.51Pencil h ardness H H2H2H HWater resistance Water (24 h)Whitening Unchanged Unchanged UnchangedBoiling water (15 m in)Whitening Unchanged Unchanged UnchangedPollution resistance (1 h)Vinegar Polluted Unchanged Unchanged UnchangedTea Unchanged Unchanged Unchanged UnchangedBlocking resistance (4 h, 500 g, 50 ◦C)b MM:A-0MB:A-0MM:A-0MB:A-0MM:A-0MB:A-0MM:A-0MB:A-0MM:A-0MB:A-0a Blocking resistance: MM means front to front. MB means spoon-fashion. A means free-fall separation. 0 means no damage.b The commercial product and its data are supplied by Shanghai Sisheng Polymer Materials Co., Ltd., China.the crosslinking density and rigidity of the products. The gloss and pencil hardness of the composite product are superior to the commercial product we applied, as a result of the presence of the alicyclic structure and the benzene ring in the T-PABA.The glass transition of the composite product was examined with DSC (Fig. 9). In the range of scanning temperature from −40 ◦C to 120 ◦C, there is only one glass transition temperature (T g) in each DSC curve, which indicates the composite product is homo- geneous phase system, no major bulk phase separation occurs, and the T-PABA is well compatible with the HDI tripolymer. T g of the product does not change significantly with the increase of NCO/NH (OH) molar ratio. When NCO/NH (OH) molar ratio is more than 1, the superfluous NCO will reacted with H2O to form urea ( NH CO NH ), and then enhance crosslinking density of the products and lead to higher T g. On the other hand, compared with the chemical structure of HDI tripolymer, T-PABA containing benzene ring and alicyclic structure is the hard segment in the com- posite product. Increasing NCO/NH (OH) molar ratio means using more H DI t ripolymer, a nd w ill d ecrease t he c ontent o f T-PABA (hard segment) in the composite product, which leads to lower T g of the composite product. The above two opposite factors result little change of T g values with the increase of NCO/NH (OH) molar ratio.Thermal stability of the composite products was investigated by TGA (Fig. 10). The temperatures at 50% weight loss (T d) of the products are all above 400 ◦C. As shown in DTG curves, there are two weight loss stages of the composite product. The first stagedegradation (peak temperature at about 320 ◦C) is correlated with the decomposition of HDI tripolymer and the formed urethane (urea) due to the low breaking energy of C N bond [28]. The second stage (peak temperature at about 460 ◦C) is attributed to the thermal decomposition of epoxy resin (TME) structure [16]. Increasing NCO/NH (OH) molar ratio of the composite system can enhance the crosslinking density of the product, and leads to higher T d of the composite product. When the NCO/NH (OH) molar ratio increased from 0.8/1 to 1.4/1, T d of the composite products rose from 400 ◦C to 420 ◦C. Additionally, the temperature and the residue weight at the maximum degradation rate in the first stage rose from 316 to 321and from 58% to 64%, respectively, while in the second stage the temperature and the residue weight at the maximum degradation rate both kept constant, with an increase of NCO/NH (OH) molar ratio from 0.8/1 to 1.4/1. These results indicate the first stage degradation is related to the decomposition of the formed urethane (urea) but the second stage degradation is not. More urethane (urea) will be formed when increasing the molar ratio of NCO/NH (OH), which can enhance the thermal resistance of the first stage degradation but cannot affect the decomposition of the second stage degradation assigning to epoxy resin (TME) structure.Fig. 9. DSC curves of the composite product.Fig. 10. TG curves of the composite product.G.-m. Wu et al. / Progress in Organic Coatings 77 (2014) 315–3213214.ConclusionA waterborne polyurethane/epoxy resin composite coating was prepared by crosslinking a HDI tripolymer with an anionic polyol (T-PABA) dispersion, which was prepared from bio-resin TME and para-aminobenzoic acid. The T-PABA dispersion and the compos- ite dispersion are both Newton liquid whose viscosity remains constant with the increasing of shear rate. T-PABA dispersion can emulsify the HDI tripolymer in the mixing process and rebuild the composite dispersion particles, which merged with each other in the film formation process. The composite product has high gloss, excellent impact strength, adhesion, flexibility, thermal stability, and antifouling, blocking resistance properties. Impact strength, pencil hardness and water resistance can be enhanced by increasing NCO/NH (OH) molar ratio.AcknowledgmentThe authors gratefully acknowledge the financial support from the National Natural Science Foundation of China (contract grant number: 31100428).References[1] L.M. Zhu, Polyurethane Synthetic Material, Phoenix Science Press, Nanjing,China, 2002.[2] J.R. Zhang, W.P. Tu, Z.L. Dai, Prog. Org. Coat. 75 (2012) 579–583.[3] C.W. Chang, K.T. Lu, Prog. Org. Coat. 75 (2012) 435–443.[4] D. Otts, K. Pereira, M. Urban, Polymer 46 (2005) 4776–4788.[5] M. Melchiors, M. Sonntag, C. Kobusch, Prog. Org. Coat. 40 (2000) 99–109.[6] Z. Wicks, D. Wicks, J. Rosthauser, Prog. Org. Coat. 44 (2002) 161–183.[7] X. Kong, S.M. Li, J.Q. Qu, J. Macromol. Sci. Pure 47 (2010) 368–374.[8] C. Suzana, L. Caslav, S. Jakov, Sensors 7 (2007) 308–318.[9] J. Huybrechts, P. Bruylants, A. Vaes, Prog. Org. Coat. 38 (2000) 67–77.[10] J.Q. Qu, W.P. Tu, H.Q. Chen, J. Chem. Eng. Chin. Univ. 16 (2002)212–216.[11] D.E. Fiori, Prog. Org. Coat. 32 (1997) 65–71.[12] F.X. Chu, Biomass Chem. Eng. 40 (2006) 21–23.[13] J. Karger-Kocsis, Express Polym. Lett. 3 (2009) 676.[14] G.M. Wu, Z.W. Kong, F.X. Chu, Chem. Ind. Forest Prod. 27 (2007) 57–62.[15] G.M. Wu, Z.W. Kong, F.X. Chu, Chem. Ind. Forest Prod. 27 (2007) 21–26.[16] G.M. Wu, Z.W. Kong, H. Huang, J. Chen, F.X. Chu, J. Appl. Polym. Sci. 113 (2009)2894–2901.[17] GB/T 1732-93, Determination of Impact Resistance of Film.[18] GB/T 1720-89, Determination of Adhesion of Film.[19] GB/T 1731-93, Determination of Flexibility of Film.[20] GB/T 6739-96, Paints and Varnishes –Determination of Film Hardness by PencilTest.[21] GB/T 23999-2009, Water Based Coatings for Woodenware for Indoor Decorat-ing and Refurbishing.[22] Y.L. Liu, Y.J. Chen, Polymer 45 (2004) 1797–1804.[23] K.J. Ji, Y.J. Liu, Y.S. Zhang, Acta. Mater. Compos. Sinica 17 (2000) 15–18.[24] J. Jiao, W.Y. Lei, Structures, Performances, Tests of the Polymers, ChemicalIndustry Press, Beijing, China, 2003.[25] C.A. Black, D.D. Evans, L.E. Ensminger, J.L. White, F.E. Clark, Methods of SoilAnalysis, American Society of Agronomy, Madison, WI, 1965.[26] W. Zeno, N. Frank, S. Peter, Organic Coatings Science and Technology, JohnWiley & Sons, New York, 1999.[27] Y.M. Dong, Macromolecule Analytical Handbook, Petrachemical Press, Beijing,China, 2004.[28] L. Li, B. Li, X.S. Ji, Chin. Coat. 23 (2008) 28–31.。
重组牛碱性成纤维细胞生长因子联合Q开关NdYAG激光对玫瑰痤疮患者面部皮损及瘢痕修复的影响

Defects Rese, 2017, 109(11):809-815.[2]Bota M,Popa G,Blag CL,et al.Infantile hemangiomas: a 7-yearexperience of a single-center[J].Clujul Med,2017,90(4):396-400. [3]林晓,钱秋芳,黄迎,等.外用噻吗洛尔和激光治疗婴幼儿血管瘤疗效比较[J]. 中国麻风皮肤病杂志,2018,34(4):215-218.[4]马志兵,金培生,张爱君,等.普萘洛尔和595nm脉冲染料激光治疗婴儿血管瘤的疗效[J].中华医学美学美容杂志,2018,24(5):350-353.[5]李邻峰,赵俊英,王美芳.长脉冲1 064nm Nd∶YAG激光治疗化脓性肉芽肿临床观察[J].中国美容医学,2017,26(6):88-91.[6]李垣君,陈谨萍,李军,等.双波长Cynergy激光治疗婴幼儿血管瘤疗效评估[J].中华医学美学美容杂志,2013,19(6):437-440.[7]宫贺,徐大朋,李越霄,等.0.5%马来酸噻吗洛尔滴眼液联合普萘洛尔治疗婴幼儿血管瘤疗效分析[J].中国口腔颌面外科杂志,2014,12(5):441-445.[8]张凯驰,徐大朋,程沫沙,等.马来酸噻吗洛尔和普萘洛尔治疗婴幼儿表浅型血管瘤的疗效分析[J].中国口腔颌面外科杂志,2017,15(6):529-533.[9]Tollefson MM, Frieden IJ.Early growth of infantile hemangiomas: whatparents’ photographs tell us[J].Pediatrics,2012,130(2):e314-e320. [10]陈玉兰.马来酸噻吗洛尔治疗婴幼儿浅表性血管瘤的临床观察[J].中国医疗美容,2015,5(5):89-90.[11]Danarti R,Ariwibowo L,Radiono S,et al. Topical timolol maleate0.5% for infantile hemangioma: its effectiveness compared toultrapotent topical corticosteroids-a single-center experience of 278 cases[J]. Dermatology,2016,232(5):566-571.[12]Hunzeker CM,Geronemus RG.Treatment of superficial infantilehemangiomas of the eyelid using the 595‐nm pulsed dye laser[J].Dermatol Surg,2010,36(5):590-597.[13]苏海辉,佘庭宇,贾冬梅,等.Cynergy双波长激光治疗儿童皮肤血管瘤的临床疗效分析[J].临床皮肤科杂志,2014,43(7):437-440. [14]Püttgen K,Lucky A,Adams D,et al.Topical timolol maleate treatmentof infantile hemangiomas[J].Pediatrics,2016,138(3):e20160355. [15]Costa RD,Prindaville B,Wiss K.Doing the math: A simple approachto topical timolol dosing for infantile hemangiomas[J].Pediatr Dermatol, 2018,35(2):276.[16]Chan H,Mckay C,Adams S,et al.RCT of timolol maleate gelfor superficial infantile hemangiomas in 5- to 24-week-olds[J].Pediatrics, 2013,131(6):e1739.[收稿日期]2019-11-20本文引用格式: 何洛芸,韦妮波,马瑗,等.Cynergy双波长激光联合马来酸噻吗洛尔治疗婴儿浅表性血管瘤疗效评价[J].中国美容医学,2021,30(1):49-53.•论 著•重组牛碱性成纤维细胞生长因子联合Q开关Nd:YAG激光对玫瑰痤疮患者面部皮损及瘢痕修复的影响徐祥宇,王 俊,汪柳芬(安庆市第一人民医院皮肤科 安徽 安庆 246000)[摘要]目的:探究重组牛碱性成纤维细胞生长因子联合Q开关Nd:YAG激光对玫瑰痤疮患者面部皮损及瘢痕修复的影响。
极谱值英文专业表达

极谱值英文专业表达Polarographic Values: A Technical Overview.Polarography, often referred to as voltammetry, is an electrochemical analytical technique used to determine the concentration of various substances in a solution. Itrelies on the measurement of the current-voltagerelationship as a working electrode is scanned through a range of potentials in the presence of the analyte. The resulting polarogram, which is a plot of current against potential, provides information about the electrochemical behavior of the analyte and can be used to quantify its concentration.Polarographic values, or more specifically, the peak current and peak potential values obtained from polarograms, are crucial parameters in the analysis of substances using this technique. These values are directly related to the electrochemical properties of the analyte and can be usedto identify and quantify different compounds in a sample.Peak Current in Polarography.Peak current, denoted as Ip, is the maximum current value observed in a polarogram when the working electrode passes through the potential at which the analyte undergoes an electrochemical reaction. The magnitude of the peak current is dependent on several factors, including the concentration of the analyte, the nature of the electrochemical reaction, and the rate of electron transfer at the electrode surface.The peak current is proportional to the concentration of the analyte, assuming that other conditions such as temperature, electrode surface area, and solution composition remain constant. This relationship can be expressed as:Ip = nFAvC.where:Ip is the peak current.n is the number of electrons transferred in the electrochemical reaction.F is Faraday's constant (96,485 C/mol)。
Waters Protein-Pak Hi Res Q Column 分离 Low Range ss

Size and Purity Assessment of Single-Guide RNAs by Anion-Exchange Chromatography (AEX)Hua Yang,Stephan M. Koza,Ying Qing YuWaters CorporationAbstractSingle-guide RNA (sgRNA) is a critical element in the CRISPR/Cas9 Technology for gene editing, the size of which usually ranges from 100 to 150 bases. In this application note, we show that the size of several sgRNAs could be estimated by comparison to a Low Range ssRNA Ladder (50–500 bases) using an optimized anion-exchange method developed on a Waters Protein-Pak Hi Res Q Column. In addition, the purity of the sgRNA samples can be assessed using the same anion exchange method, providing an informative and non-complex method for sgRNA product consistency.BenefitsWaters Protein-Pak Hi Res Q Column separation of a Low Range ssRNA Ladder with the size ranging from ■50 to 500 basesWaters Protein-Pak Hi Res Q Column separation of ssRNAs and their impurities■Size and purity estimation of ssRNAs having a size range of 100–150 mer under the same gradient conditions ■using the AEX method on Waters Protein-Pak Hi Res Q ColumnIntroductionThe discovery of clustered regularly interspaced short palindromic repeats (CRISPR)/CRISPR associated (Cas) bacterial immunity systems and the rapid adaptation of RNA guided CRISPR/CRISPR Associated Protein 9 (Cas9) Technology to mammalian cells have had a significant impact in the field of gene editing.1–3 The Cas9 protein, a non-specific endonuclease, is directed to a specific DNA site by a guide RNA (gRNA), where it makes a double-strand break of the DNA of interest. The gRNA consists of two parts: CRISPR RNA (crRNA) and trans-activating crRNA (tracrRNA). The crRNA is usually a 17–20 nucleotide sequence complementary to the target DNA, and the tracrRNA serves as a binding scaffold for the Cas9 nuclease. While crRNAs and tracrRNAs exist as two separate RNA molecules in nature, the single-guide RNA (sgRNA), which combines both the crRNA sequence and the tracrRNA sequence into a single RNA molecule, has become a commonly used format. The length of a sgRNA is in the range of 100–150 nucleotides. It is critical to characterize the sgRNA, as it is the core of the CRISPR/Cas9 technology.Anion-exchange chromatography (AEX) separates molecules based on their differences in negative surface charges. This analytical technique can be robust, reproducible, and quantitative. It is also easy to automate, requires small amounts of sample, and allows for the isolation of fractions for further analysis. AEX has been utilized in multiple areas related to gene therapy, including adeno-associated virus empty and full capsid separation, plasmid isoform separation, and dsDNA fragment separation.4–6 Since the sgRNAs are negatively charged due to the phosphate groups on the backbone, we investigated AEX for size and purity assessment of sgRNAs.In this application note, we show that using a Waters Protein-Pak Hi Res Q strong Anion-Exchange Column on an ACQUITY UPLC H-Class Bio System, a single-stranded RNA (ssRNA) ladder ranging from 50 to 500 bases can be separated and used for estimating the size of ssRNAs in the approximate range of 100–150 bases, including the sgRNAs for CRISPR/Cas9 System. Moreover, the purity of these ssRNAs can be estimated with the same gradient conditions.ExperimentalSample DescriptionHPRT (purified and crude) is a pre-designed CRISPR/Cas9 sgRNA (Hs.Cas9.HPRT1.1AA, 100 mer). GUAC is acustomized ssRNA (150 mer), which contains repeats of GUAC sequence. HPRT sgRNA and GUAC ssRNA were purchased from Integrated DNA Technologies (IDT). Rosa26 and Scrambled #2 are both pre-designedCRISPR/Cas9 sgRNAs purchased from Synthego (100 mer). Low Range ssRNA Ladder was purchased from New England Biolabs (N0364S).Method ConditionsLC ConditionsLC system:ACQUITY UPLC H-Class BioDetection:ACQUITY UPLC TUV Detector with 5 mm titaniumflow cellWavelength:260 nmVials:Polypropylene 12 x 32 mm Screw Neck Vial, withCap and Pre-slit PTFE/Silicone Septum, 300 µLVolume, 100/pk (P/N 186002639)Column(s):Protein-Pak Hi Res Q Column, 5 µm, 4.6 x 100 mm(P/N 186004931)Column temp.:60 °CSample temp.:10 °CInjection volume:1–10 µLFlow rate:0.4 mL/minMobile phase A:100 mM Tris-HClMobile phase B:100 mM Tris baseMobile phase C: 3 M Tetramethylammonium chloride (TMAC)Mobile phase D:WaterBuffer conc. to deliver:20 mMGradient Table (an AutoBlend Plus Method, Henderson-Hasselbalch derived).In the above gradient table, the buffer is 20 mM Tris pH 9.0. The initial salt concentration is set to 0 mM to ensure all the analytes are strongly bound onto the column. After 5 mins, the salt concentration is increased to 1400 mM where most of the impurities will elute, based on prior investigation. After 4 mins equilibration, the separation gradient starts. The salt concentration increases linearly from 1400 m to 2100 mM in 20 mins for the Low Range ssRNA Ladder separation, as well as individual ssRNAs. Then it is ramped up to 2400 mM to strip off any remaining bound molecules. Finally, an equilibration step to the initial condition takes place, preparing for the next injection.An equivalent gradient table for a generic quaternary LC system is shown above.Data ManagementChromatography software:Empower 3 (FR 4)Results and DiscussionSize AssessmentVarious mobile phase conditions were tested using a Low Range ssRNA Ladder for size assessment of the ssRNAs, including pH (7.4 and 9.0), column temperature (30 °C and 60 °C) and salt (NaCl and TMAC).The results from the optimal conditions are shown in Figure 1B. Using a pH 9.0 Tris buffer with 60 °C column temperature and a TMAC salt gradient, the Low Range ssRNA Ladder (50–500 bases) along with four pre-made sgRNAs (100 mer), and one customized ssRNA (150 mer) were separated on a Waters Protein-Pak Hi Res Q Column. The separation for the Low Range ssRNA Ladder on this strong anion exchange column was very similar to that on an agarose gel, as shown in Figure 1A. A calibration curve was constructed based on the retention time and the logarithm of the number of bases of each ssRNA in the ladder (Figure 1C, blue dots). Thelinear fit from the Low Range ssRNA Ladder indicates a strong correlation between the logarithm of the size andthe retention time (R2=0.993). Using this plot, the size of the ssRNAs was calculated from their individual retention time. The percent error is calculated using the formula {(calculated size – theoretical size)/theoretical size}. The percent error was less than 6% for all the RNAs tested (Figure 1d), as evidenced by the orange data points residing on or very closely to the trendline of the calibration curve. Notice that small percent error was obtained from four pre-made sgRNAs from two different manufacturers and a customized ssRNA with an artificial sequence. Although ssRNAs with shorter than 100 bases and larger than 150 bases were not tested, it is possible that this method can be used for the ssRNAs size assessment in the range of 50–500 bases.Figure 1A.Agarose gel separation of Low Range ssRNA Ladder (Reprinted from (2021) with permission from New England Biolabs); 1B. Anion-exchange separation of Low Range ssRNA Ladder and ssRNAs on a Waters Protein-Pak Hi Res Q Column; 1C. A plot of log(size) vs. retention time of Low Range ssRNA Ladder (blue dots) and individual ssRNAs (orange dots); 1D. Size estimation of individual ssRNAs based on retention time and calibration curve. Small percent error was obtained for all ssRNAs.It is noteworthy that a mobile phase condition with pH 7.4 Tris buffer, 60 °C column temperature and a TMAC salt gradient also resulted in good size estimation with percent error <5% for all pre-made sgRNAs (100 mer) and ~12% for the artificially made GUAC ssRNA (150 mer). Overall, 60 °C column temperature resulted in one singlepeak for each ssRNA which is needed to determine the retention time of the peak for size assessment. 30 °C column temperature resulted in more than one major peaks, which are presumably the isomers of the ssRNAs. Multiple peaks were also observed when using NaCl as the salt, regardless of the pH and column temperature.Purity AssessmentPurified and crude HPRT sgRNA was separated on the Protein-Pak Hi Res Q Column (Figure 2) using the same gradient conditions for size assessment. The relative purities of the crude and purified samples were measured as 37.4% and 88.0%, respectively, based on the peak areas indicated. The majority of the impurities eluted prior to 50 bases although lower abundance impurities appear to be present up to the size of the HPRT sgRNA.Figure 2. Crude and purified HPRT sgRNA for CRISPR/Cas 9 System were separated on a Waters Protein-Pak Hi Res Q Column using the same conditions as in Figure 1B (see Experimental for details).ConclusionAnion-exchange chromatography is robust, reproducible, easy to automate, yields quantitative information, andrequires a small amount of sample. We demonstrate here that the components of a Low Range ssRNA Ladder, ranging from 50 to 500 bases, can be separated on a Waters Protein-Pak Hi Res Q Column with a linear correlation between the log of base-number and observed retention time when TMAC is used as an elution salt. The size of ssRNAs ranging from 100 to 150 bases can be estimated by comparing the retention time of the ssRNAs with that of the Low Range ssRNA Ladder. In addition, the purity of a sgRNAs may also be observed from the same chromatographic separation. This method can potentially be applied to the analysis of sgRNAs which are the key element for CRISPR/Cas9 gene editing technology.ReferencesDunbar C E, High K A, J. Joung K, Kohn D B, Ozawa K, Sadelain M. Gene Therapy Comes of Age. Science 1.2018; 359: 175.2.Rath D, Amlinger L, Rath A, Lundgren M. The CRISPR-Cas Immune System: Biology, Mechanisms and Applications. Biochimie 2015; 117: 119–128.3.Patrick D. Hsu P D, Eric S. Lander E S, and Zhang F. Development and Applications of CRISPR-Cas9 for Genome Engineering. Cell 2014; 157: 1262–1278.Yang H, Koza S and Chen W. Anion-Exchange Chromatography for Determining Empty and Full Capsid4.5.Yang H, Koza S and Chen W. Plasmid Isoform Separation and Quantification by Anion-Exchange6.Yang H, Koza S and Chen W. Separation and Size Assessment of dsDNA Fragments by Anion-ExchangeFeatured Products■■720007428, November 2021© 2021 Waters Corporation. All Rights Reserved.。
A review of the species of protozoan epibionts on crustaceans-11

A REVIEW OF THE SPECIES OF PROTOZOAN EPIBIONTS ONCRUSTACEANS.I.PERITRICH CILIATESBYGREGORIO FERNANDEZ-LEBORANS and MARIA LUISA TATO-PORTODepartamento de Biologia Animal I(Zoologia),Facultad de Biologia,Pnta9a,Universidad Complutense,E-28040Madrid,SpainABSTRACTAn updated inventory of the peritrich(Protozoa,Ciliophora)epibiont species on crustaceans has been carried out.Data concerning268epibiont species,their taxonomic position,and the various crustacean basibionts were considered.The overview comprised in this study may be of use in further surveys of protozoan-crustacean epibiosis.RESUMENSe ha realizado un inventario actualizado de las especies de peritricos(Protozoa,Ciliophora) epibiontes en crustáceos.Se han considerado los datos concernientes a268especies epibiontes,su posición taxonómica,y los diferentes crustáceos visión general que comprende este estudio puede ser utilizada en futuras investigaciones sobre la epibiosis protozoos-crustáceos.INTRODUCTIONEpibiosis is a facultative association of two organisms:the epibiont and the basibiont(Wahl,1989).The term“epibiont”includes organisms that,during the sessile phase of their life cycle,are attached to the surface of a living substratum, while the basibiont lodges and constitutes a support for the epibiont(Threlkeld et al.,1993).Both concepts describe ecological functions(Wahl,1989).Several crustacean groups,cladocerans,copepods,cirripedes,isopods,amphi-pods,and decapods,include forms that are hosts for macroepibiont invertebrates (Ross,1983),and for protozoan microepibionts of the phylum Ciliophora:apos-tomatids,chonotrichids,suctorians,peritrichs,and heterotrichs(Corliss,1979; Small&Lynn,1985).The study of ciliate epibionts on crustaceans began in the last century.Bütschli(1887-89)made a compilation from former publications.After-wards,other authors(Keiser,1921;Kahl,1934,1935;Precht,1935;Raabe,1947; c®Koninklijke Brill NV,Leiden,2000Crustaceana73(6):643-683644G.FERNANDEZ-LEBORANS&M.L.TATO-PORTONenninger,1948)not only described epibiont species,but proposed explanations for the processes of epibiosis.A review of the protozoan epibionts found on de-capod crustaceans was carried out by Sprague&Couch(1971).Green(1974), in a study of the epibionts living on cladocerans,pays considerable attention to protozoan species.Ho&Perkins(1985)have focused on the epibionts found on copepods.In other contemporary and also earlier works,the following aspects have been taken into account:(1)speci city between ciliates and their crustacean basi-bionts(Evans et al.,1981;Batisse,1986,1992;Clamp,1991);(2)the morpholog-ical and physiological adaptations of the epibionts(D’Eliscu,1975;Batisse,1986, 1994;Fenchel,1987;Clamp,1991;Lom&De Puytorac,1994);(3)the effects pro-duced by the epibionts on the crustaceans(Herman et al.,1971;Turner et al.,1979; Kankaala&Eloranta,1987;Nagasawa,1988);(4)the possible use of epibionts for the assessment of water quality(Antipa,1977;Henebry&Ridgeway,1979;Scott &Thune,1986);(5)the implications of protozoan epibionts on cultures of vari-ous species of crustaceans(Overstreet,1973;Johnson,1977,1978;Lightner,1977, 1988;Couch,1978;Scott&Thune,1986;V ogelbein&Thune,1988;Camacho& Chinchilla,1989);and(6)the organization of the epibiont communities on plank-tonic crustaceans(Threlkeld et al.,1993).Despite the fact that there is a considerable amount of information about the protozoan epibionts on crustaceans,since the works of Sprague&Couch(1971), Green(1974),and Ho&Perkins(1985),which relate to speci c crustacean groups, no further general reviews have appeared.Several new species of protozoan ciliate epibionts have recently been described(Dovgal,1985;Batisse,1992;Fernandez-Leborans&Gomez del Arco,1996;Zhadan&Mikrjukov,1996;Fernandez-Leborans et al.,1996,1997),and some of these are peritrich ciliates(Matthes& Guhl,1973;Bierhof&Roos,1977;Jankowski,1986;Dale&Blom,1987;Clamp, 1990,1991;Threlkeld&Willey,1993;Hudson&Lester,1994;Stoukal&Matis, 1994;Foissner,1996).The purpose of this work is to provide an up-to-date review of the peritrich ciliates living as epibionts on crustaceans:268species have been considered in this compilation,which may contribute data for studies of epibiosis in crustaceans.CRUSTACEAN PROTOZOAN EPIBIONTS,I.PERITRICH CILIATES645RESULTS1)Phylum CILIOPHORA Do ein,1901Class OLIGOHYMENOPHOREA De Puytorac,Batisse,Bohatier,Corliss, Deroux,Didier,Dragesco,Fryd-Versavel,Grain,Grolière,Hovasse,Iftode,Laval,Roque,Savoie&Tuffrau,1974Subclass P ERITRICHIA Calkins,1933Order S ESSILIDA Kahl,1933Family Epistylididae Kahl,1935Genus Rhabdostyla Kent,1880( g.1)R.bosminae Levander,1907.On the cladoceran Bosmina sp.R.conipes Kahl,1935.On the cladoceran Daphnia sp.Fresh water.On the cladocerans Daphnia magna,D.longispina and Scapholeberis mucronata (cf.Green,1957,1974).R.cyclopis Kahl,1935.On the copepod Cyclops sp.Fresh water.R.cylindrica Stiller,1935.On the cladoceran Leptodora ke Balaton (Hungary).On the cladoceran Leptodora kindtii.Denmark(Green,1974).R.hungarica Stiller,1931.On the cladoceran Leptodora ke Balaton (Hungary).R.globularis Stokes,1890.On the cladoceran Bosmina longirostris and on Diaphanosoma brachyurum.Germany(Nenninger,1948).R.invaginata Stokes,1886.On the ostracod Cypris sp.R.sessilis Penard,1922.On the copepod Cyclops sp.Fresh water.R.pyriformis Perty,1852(cf.Kahl,1935;on Entomostraca).On the clado-ceran Daphnia longispina(cf.Nenninger,1948).On the cladoceran Daph-nia hyalina(cf.Sommer,1950).On Daphnia pulex and Ceriodaphnia reticu-lata(cf.Hamman,1952).On Daphnia magna,D.pulex,D.cucullata,Simo-cephalus vetulus,Ceriodaphnia reticulata,and Leptodora kindtii(cf.Green, 1953).On Daphnia magna(cf.Green,1955).On Daphnia magna andD.longispina(cf.Green,1957).On Daphnia atkinsoni,D.hyalina,D.lon-gispina,D.curvirostris,D.obtusa,Ceriodaphnia laticaudata,and C.pulchel-la(cf.Green,1974).R.vernalis Stokes,1887.On the copepod Eucyclops agilis(cf.Henebry& Ridgeway,1979).1)For authors and dates of species of Crustacea mentioned herein,see separate section,below.646G.FERNANDEZ-LEBORANS&M.L.TATO-PORTOFigs.1-2.1,Rhabdostyla(R.pyriformis,after Green,1957);2,Epistylis(E.gammari,after Precht,1935).Rhabdostyla sp.Bierhof&Roos,1977.Between the spines at the end of the telson on Gammarus tigrinus.Germany.Rhabdostyla sp.Weissman et al.,1993.On the copepod Acartia hudsonica. Genus Epistylis Ehrenberg,1832( g.2)E.anastatica(Linnaeus,1767)(cf.Kent,1881).Syn.:Vorticella anastatica L.,1767.On Entomostraca and freshwater plants.On cyclopoid copepods and Daphnia pulex(cf.Green,1974).E.astaci Nenninger,1948.Fresh water.On the gills of the decapod Astacusastacus(as A. uviatilis)(Germany).On A.leptodactylus(cf.Stiller,1971).On the gills of Austropotamobius torrentium(cf.Matthes&Guhl,1973).E.bimarginata Nenninger,1948.Fresh water.On the appendages of Astacusastacus(as A. uviatilis).Germany.E.branchiophila Perty,1852.Syn.:E.formosa Nenninger,1948.On theparasitic copepod Lernaea cyprinacea,in freshwater environments of South Africa(Van As&Viljoen,1984).E.breviramosa Stiller,1931.On the antennal lament of the cladoceran Daph-nia ke Balaton(Hungary).On the copepod Cyclops sp.,Czechoslovakia (Srámek-Husek,1948).On the cladocerans Bosmina longirostris and Alona af nis(cf.Green,1974).E.cambari Kellicott,1885.On the gills of the decapod Cambarus sp.(NE ofU.S.A.).On the maxillae of the cray sh Astacus leptodactylus(fresh water) (cf.Matthes&Guhl,1973).E.crassicollis Stein,1867.On freshwater Entomostraca and on the pleopodsand gills of cray sh.On the gills of Astacus astacus(as A. uviatilis),andCRUSTACEAN PROTOZOAN EPIBIONTS,I.PERITRICH CILIATES647 the maxillae,maxillipeds,and gills of A.leptodactylus,in Europe(Matthes& Guhl,1973).E.cyprinaceae Van As&Viljoen,1984.On the parasitic copepod Lernaea cyprinacea(fresh water,South Africa).E.daphniae Fauré-Fremiet,1905.On the cladoceran Daphnia sp.On Daphnia magna(cf.Nenninger,1948).On the copepod Boeckella triarticulata(New Zealand)(Xu&Burns,1990).On the cladoceran Moina macrocopa in an urban stream.E.diaptomi Fauré-Fremiet,1905.On the copepod Diaptomus sp.E.digitalis Ehrenberg,1838.On the copepod Cyclops sp.E.epibarnimiana Van As&Viljoen,1984.On the parasitic copepod Lernaea barnimiana(fresh water,South Africa).E.fugitans Kellicott,1887.On the cladoceran Sida crystallina.North America.E.gammari Precht,1935.On the antennae of the gammarid Gammarus sp. (Kiel channel).On the proximal part of the rst antenna and,less commonly, on the second antenna of Gammarus oceanicus and G.salinus.In the Baltic Sea and areas of Norway(Fenchel,1965).On the rst antenna of Gammarus tigrinus(cf.Stiller,1971).E.halophila Stiller,1942.On the cladocerans Daphnia longispina and D.pulex (Lake Cserepeser,Hungary).E.harpacticola Kahl,1933.On harpacticoid copepods in the Kiel channel. E.helenae Green,1957.On the cladocerans Daphnia pulex,D.magna,D.ob-tusa,D.longispina,D.curvirostris,Ceriodaphnia pulchella,C.reticulata, ticaudata,Moina macrocopa,M.micrura,Chydorus sphaericus,Simo-cephalus serrulatus,and S.vetulus(cf.Green,1957,1974).On Daphnia magna(cf.Nenninger,1948).On Ceriodaphnia reticulata and Simocephalus vetulus(cf.Matthes,1950).E.humilis Kellicott,1887.On the gammarid Gammarus sp.and other Ento-mostraca.custris Imhoff,1884.On the pelagic copepod Cyclops sp.On the buccal appendages of the branchiopod Lepidurus apus(freshwater areas near Vienna, Austria)(Foissner,1996).E.magna V an As&Viljoen,1984.On the parasitic copepod Lernaea cypri-nacea(fresh water,South Africa).E.niagarae Kellicott,1883.On the body surface of cray sh(Niagara River, U.S.A.).On the antennae and body of the European cray sh Astacus lep-todactylus,on Austropotamobius torrentium,and on Orconectes limosus(as Cambarus af nis)(cf.Matthes&Guhl,1973).On the surface of the copepod648G.FERNANDEZ-LEBORANS&M.L.TATO-PORTOEucyclops serrulatus,and on the cladocerans Daphnia pulex,D.rosea,Cerio-daphnia reticulata,and Scapholeberis mucronata(lakes of Colorado,U.S.A.) (Willey&Threlkeld,1993).E.nitocrae Precht,1935.On the third pereiopod of Gammarus tigrinus(cf.Bierhof&Roos,1977).E.nympharum Engelman,1862.On cladocerans(Nenninger,1948).On Cy-clops sp.(cf.Foissner&Schiffman,1974).On the branchiuran Dolops ra-narum(cf.Van As&Viljoen,1984).E.ovalis Biegel,1954.On the gnathopods of Gammarus tigrinus.On the thirdpereiopod of the gammarid Gammarus pulex,and on the spines at the end of the third uropod of Gammarus tigrinus(cf.Bierhof&Roos,1977).E.plicatilis Ehrenberg,1838.On the copepods Eucyclops agilis,Cyclopsvernalis,and C.bicuspidatus(Ashmore Lake,Illinois,U.S.A.)(Henebry& Ridgeway,1979).E.salina Stiller,1941.On the rst and second antennae,coxae,and gills of thegammarid Gammarus pulex(cf.Bierhof&Roos,1977).E.thienemanni Sommer,1951.On the gills of Gammarus tigrinus(cf.Bierhof&Roos,1977).E.zschokkei(Keiser,1921).Syn.:Opercularia zschokkei Keiser,1921.On thegnathopods of the gammarid Gammarus tigrinus and on other Entomostraca.On the cladoceran Acantholeberis curvirostris(cf.Nenninger,1948).Epistylis sp.Hutton,1964.On the decapod Penaeus duorarum(Florida,U.S.A.).Between the setae of the rst antenna of Gammarus tigrinus(cf.Bierhof& Roos,1977).Epistylis sp.Hutton,1964.On the decapod Ploeticus robustus(Daytona Beach, Florida,U.S.A.).Epistylis sp.Viljoen&Van As,1983.Two species on the thoracic appendages of a freshwater brachyuran,apparently erroneously identi ed as“Potamon sp.”(South Africa)[the genus Potamon does not occur in southern Africa].Epistylis sp.Pearse,1932.On the gills of the decapods Coenobita clypeatus, Geograpsus lividus,and Pachygrapsus transversus(Florida,U.S.A.).Epistylis sp.Hudson&Lester,1994.On the gills of the decapod Scylla serrata (Moreton Bay,Queensland,Australia).Epistylis sp.Turner et al.,1979.On the estuarine copepods Acartia tonsa andA.clausi(Escambia Bay,Florida,U.S.A.).Epistylis sp.Villarreal&Hutchings,1986.Fresh water.On the maxillipeds, pereiopods,and ventral portion of the abdomen of the decapod Cherax tenuimanus(Australia).CRUSTACEAN PROTOZOAN EPIBIONTS,I.PERITRICH CILIATES649 Family Lagenophryidae Bütschli,1889Genus Lagenophrys Stein,1852( g.3)L.aegleae Mouchet-Bennati,1932.Fresh water.On the branchial laments of the anomurans Aegla sp.,Aegla castro,and Aegla franca.Arroyo Miguelete, (Uruguay)and Parana River(Brazil).L.ampulla Stein,1851.Fresh water.On the gills of species of the genus Gammarus.L.andos(Jankowski,1986)(cf.Clamp,1991).Syn.:Circolagenophrys andos Jankowski,1986.Fresh water.On the decapod Parastacus chilensis(Chile).L.anticthos Clamp,1988.Fresh water.On the branchial laments of the decapods Parastacus pugnax,P.defossus,and P.saffordi(Chile,Brazil, Uruguay).L.aselli Plate,1886.On the branchial surface of the isopod Asellus aquaticus (Hamburg,Germany).L.awerinzewi Abonyi,1928.On the gills of the decapod Potamon uviatilis(as Telphusa uviatilis)(Africa).L.bipartita Stokes,1890.On the cladoceran Daphnia sp.(fresh water,U.S.A.).L.branchiarum Nie&Ho,1943.Fresh water.On the gills of the caridean shrimp Macrobrachium nipponense(as Palaemon nipponense)(Japan).L.callinectes Couch,1967.Marine and in estuaries.On the gills of the decapods Callinectes sapidus,C.bocourti,and C.maracaiboensis(Chesapeake Bay, Maryland,Virginia,and Gulf of Mexico).mensalis Swarczewsky,1930.Fresh water.On gammarids(Lake Baikal).L.darwini Kane,1965.On the branchial laments of the decapod Cherax quadricarinatus(stream near Darwin,Australia).L.dennisi Clamp,1987.Fresh water.On the decapods Orconectes illinoiensis, Cambarus bartonii bartonii,and C.chasmodactylus(North America).L.deserti Kane,1965.Fresh water.On the gills of the decapods Cherax tenuimanus and C.quinquecarinatus(SW rivers,Australia).L.diogenes(Jankowski,1986).Syns.:Circolagenophrys diogenes Jankowski, 1986,Lagenophrys incompta Clamp,1987.Fresh water.On the gills of the decapods Orconectes illinoiensis and Cambarus diogenes(Illinois,U.S.A.).L.discoidea Kellicott,1887(cf.Clamp,1990).Syns.:Lagenophrys labiata Wallengren,1900(a junior homonym of biata Stokes,1887(cf.Clamp, 1990));L.wallengreni Abonyi,1928;Circolagenophrys entocytheris Jankow-ski,1986.Fresh water.On ostracods.On the cray sh Cambarus sp.,C.chas-modactylus,C.bartonii bartonii,and Orconectes illinoiensis(Ontario,Canada and U.S.A.).650G.FERNANDEZ-LEBORANS&M.L.TATO-PORTOFigs.3-7.3,Lagenophrys(L.eupagurus,after Clamp,1989);4,Clistolagenophrys(C.primitiva, after Swarczewsky,1930);5,Setonophrys(munis,after Clamp,1991);6,Operculigera (O.asymmetrica,after Clamp,1991);7,Usconophrys(U.aperta,after Clamp,1991).L.dungogi Kane,1965.On the branchial laments of the decapod Euastacus sp.(stream near Dungog,Australia).L.engaei Kane,1965.On the branchial laments,basal areas of the gills, branchiostegite membrane and,more rarely,on the pleopods of the decapods Engaeus victoriensis and Austroastacus hemicirratulus(Victoria,Tasmania, and Melbourne,Australia).L.eupagurus Kellicott,1893(cf.Clamp,1989).Syns.:Lagenophrys lunatus Imamura,1940;Lagenophrys articularis Nie&Ho,1943.Marine,in estu-arine areas and fresh water.On the decapods Litopenaeus setiferus(as Pe-CRUSTACEAN PROTOZOAN EPIBIONTS,I.PERITRICH CILIATES651 naeus s.)(Penaeidea,Penaeidae),on the surface of the body,Litopenaeus van-namei(as Penaeus v.),on the surface of the body,Macrobrachium nipponense (Caridea,Palaemonidae)on antennae and pleopods,Macrobrachium ohione, on the surface of the middle of the pleura,Macrobrachium rosenbergii,on the gills,Palaemon paucidens(Caridea,Palaemonidae),Palaemonetes inter-medius(Caridea,Palaemonidae),Palaemonetes kadiakensis,Palaemonetes paludosus,Palaemonetes pugio,Palaemonetes varians,on the whole body, except on the gills,Palaemonetes vulgaris,Upogebia af nis(Thalassinidea, Upogebiidae),and Pagurus longicarpus(Anomura,Paguridae),on the gills (U.S.A.,Japan,Venezuela,Thailand).L.foxi Clamp,1987.Fresh water.On the gills of the gammarids Gammarus pseudolimnaeus,G.troglophilus,G.minus,and Gammarus sp.(Missouri, U.S.A.).L.in ata Swarczewsky,1930.On the distal areas of pleopods of the gammarid Gmelinoides fasciata(Lake Baikal).L.jacobi(Kane,1969).Syn.:Stylohedra jacobi Kane,1969.On freshwater decapods in Australia.L.johnsoni Clamp,1990.Syn.:Lagenophrys labiata Stokes,1887(partim). Fresh water.On the appendages and the surface of the carapace of the gammarids Gammarus fasciatus,G.daiberi,G.tigrinus,and Crangonyx gracilis(New Jersey,Michigan,and North Carolina,U.S.A.).biata Stokes,1887(cf.Clamp,1990).Fresh water.On the appendages and on the surface of the carapace of the gammarids Gammarus fasciatus, G.daiberi,G.tigrinus,and Cangronyx gracilis(New Jersey,Michigan,and North Carolina,U.S.A.).L.leniusculus(Jankowski,1986).Syns.:Circolagenophrys leniusculus Jan-kowski,1986;L.oregonensis Clamp,1987.Fresh water.On the carapace, gills,ventral surface of the abdomen,uropods,pereiopods,and pleopods of the decapod Pacifastacus leniusculus leniusculus,and on the gills of P.leniusculus trowbridgii and P.connectens(North America).L.lenticula(Kellicott,1885)(cf.Clamp,1991).Syns.:Stylohedra lenticula Kellicott,1885;S.lenticulata Kahl,1935;Lagenophrys lenticulata(Kahl, 1935)(cf.Thomsen,1945).Fresh water.Setae of the sixth and seventh pereiopods of the gammarids Hyalella azteca and H.curvispina(U.S.A., Canada,Mexico,and Uruguay).L.limnoria Clamp,1988.Syn.:Circolagenophrys circularis Jankowski,1986 (cf.Clamp,1991).On the isopod Limnoria lignorum.L.macrostoma Swarczewsky,1930.Fresh water.On gammarids(Lake Baikal). L.matthesi Schödel,1983.On the maxillipeds of the gammarids Gammarus pulex and Carinogammarus roeselii.652G.FERNANDEZ-LEBORANS&M.L.TATO-PORTOL.metopauliadis Corliss&Brough,1965.Fresh water.On the gills of the brachyuran Metopaulias depressus(endemic on Jamaica).L.monolistrae Stammer,1935.On the pleopods of the isopod Monolistra sp.L.nassa Stein,1852.Fresh water.On the pleopods of the gammarid Gammarus pulex.L.oblonga Swarczewsky,1930.On the antennae of the gammarid Gammarus hyacinthinus(Lake Baikal).L.orchestiae Abonyi,1928.On the amphipod Orchestia cavimana(Lake Balaton,Hungary).L.ornata Swarczewsky,1930.Fresh water.On ke Baikal.L.ovalis Swarczewsky,1930.Fresh water.On the thoracic appendages of ke Baikal.L.parva Swarczewsky,1930.On ke Baikal.L.patina Stokes,1887(cf.Clamp,1990).Syn.:Lagenophrys labiata Stokes, 1887(cf.Shomay,1955).(Corliss&Brough,1965;Clamp,1973).Fresh water.On the pereiopods and gills of the gammarids Gammarus sp.and Hyalella azteca.American continent.L.rugosa Kane,1965.Fresh water.On the gills of the decapod Geocharax falcata(Victoria,Australia).L.similis Swarczewsky,1930.On ke Baikal.L.simplex Swarczewsky,1930.On ke Baikal.L.solida Swarczewsky,1930.On ke Baikal.L.stammeri Lust,1950.On ostracods.Germany.(Lust,1950a).L.stokesi Swarczewsky,1930.On ke Baikal.L.stygia Clamp,1990.Syn.:Lagenophrys labiata Stokes,1887(cf.Jakschik, 1967).Subterranean water.On the gills of the cave-dwelling amphipod Bactrurus mucronatus(Illinois,U.S.A.).L.tattersalli Willis,1942.On European copepods.L.turneri Kane,1969.On freshwater decapods in Australia.L.vaginicola Stein,1852.Syn.:Lagenophrys obovata Stokes,1887.On the genital setae and thoracopods of the copepods Cyclops miniatus and Cantho-camptus sp.L.verecunda Felgenhauer,1982.On the decapod Palaemonetes kadiakensis (Illinois,U.S.A.).L.willisi Kane,1965.Fresh water.On the gills of the decapods Cherax destructor,C.albidus,and C.rotundus(Melbourne,New South Wales(e.g., Newcastle),and NW Australia).Genus Clistolagenophrys Clamp,1991( g.4)C.primitiva(Swarczewsky,1930)(cf.Clamp,1991).Syn.:Lagenophrys primi-tiva Swarczewsky,1930.On pereiopods and pleopods of the gammarid Pallasea cancellus(Lake Baikal).Genus Setonophrys Jankowski,1986(cf.Clamp,1991)( g.5)S.bispinosa(Kane,1965)(cf.Clamp,1991).Syn.:Lagenophrys bispinosa Kane,1965.On pereiopods of the decapod Cherax rotundus setosus.Stream near Newcastle(N.S.W.,Australia).munis(Kane,1965)(cf.Clamp,1991).Syn.:Lagenophrys communis Kane,1965.On the body surface(telson,pleopods,pereiopods,carapace...) of the decapod Cherax destructor.On the gills of the decapods C.rotundus,C.albidus,C.quadricarinatus,Euastacus armatus,and Engaeus marmoratus(Victoria,Melbourne,and Tasmania,Australia).S.lingulata(Kane,1965)(cf.Clamp,1991).Syn.:Lagenophrys lingulata Kane,1965.On the branchial laments and branchiostegite membrane of the decapods Cherax destructor, C.albidus,and C.rotundus(Victoria, Melbourne,and coastal and central areas of Australia).S.nivalis(Kane,1969)(cf.Clamp,1991).Syn.:Lagenophrys nivalis Kane, 1969.On freshwater decapods in Australia.S.occlusa(Kane,1965)(cf.Clamp,1991).Syn.:Lagenophrys occlusa Kane, 1965.On the anterior zone of the branchial cavity of the decapods Cherax destructor,C.albidus,and C.rotundus(Victoria and New South Wales, Australia).S.seticola(Kane,1965)(cf.Clamp,1991).Syn.:Lagenophrys seticola Kane, 1965.On the setae of the decapods Engaeus fultoni and Geocharax falcata (Victoria,Melbourne,and Templestowe,Australia).S.spinosa(Kane,1965)(cf.Clamp,1991).Syn.:Lagenophrys spinosa Kane, 1965.On the pleopods,carapace,and telson of the decapod Cherax destructor (Victoria,Melbourne,and Heathcote,Australia).S.tricorniculata Clamp,1991.On the pleopods of the decapod Geocharax falcata(Victoria,Grampian Mountains,and Wannon River,Australia). Genus Operculigera Kane,1969( g.6)O.asymmetrica Clamp,1991.On the base of the gills of the freshwater decapods Parastacus pugnax and Samastacus spinifrons(Concepción and Talcahuano,Chile).O.insolita Clamp,1991.On the base of the gills of the freshwater decapod Parastacus pugnax(Concepción,Talcahuano,Malleco,and Puren,Chile).O.montanea Kane,1969.On the freshwater decapod Colubotelson sp.(Aus-tralia).O.obstipa Clamp,1991.Pleopods of the isopod Metaphreatoicus australis (New South Wales,Australia).O.parastacis Jankowski,1986.On the base of the gills of the decapod Parastacus nicoleti(Isla Teja,Valdivia,Chile).O.seticola Clamp,1991.On the setae at the base of gills of the decapod Parastacus pugnax(Concepción,Chile).O.striata Jankowski,1986.On the decapod Parastacus chilensis.Chile.O.taura Clamp,1991.On the branchial laments of the freshwater decapod Parastacus pugnax(Concepción,Malleco,and Puren,Chile).O.velata Jankowski,1986.On the gills of the anomuran Aegla laevis.Chile.O.zeenahensis Kane,1969.On freshwater decapods in Australia.Family Usconophryidae Clamp,1991Genus Usconophrys Jankowski,1985(cf.Clamp,1991)( g.7)U.aperta(Plate,1889)(cf.Clamp,1991).Syns.:Lagenophrys aperta Plate, 1889;Usconophrys dauricus Jankowski,1986.On the gills and pleopods of the isopod Asellus aquaticus(Marburg and Hessen,Germany;North Carolina, U.S.A.;Brittany,Finisterre,Plougarneau,Pont-Menou,and Douron River, France).U.rotunda(Precht,1935)(cf.Clamp,1991).Syn.:Lagenophrys rotunda Precht,1935.On ostracods.Germany.Family Operculariidae Fauré-Fremiet,1979(in Corliss,1979)Genus Opercularia Stein,1854( g.8)O.allensi Stokes,1887.Syn.:O.ramosa Stokes,1887.On several living and inert substrata.On the body of the cray sh Astacus leptodactylus(cf.Matthes &Guhl,1973).O.asellicola Kahl,1935.On the isopod Asellus sp.Germany.O.coarctata Claparède&Lachmann,1858.On crabs(Buck,1961).O.crustaceorum Biegel,1954.On the gills of the cray sh Astacus astacus(asA. uviatilis).On the maxillae,maxillipeds,and pleopods of Austropotamo-bius torrentium(cf.Matthes&Guhl,1973).O.cylindrata Wrzesniowski,1807.On the copepod Cyclops sp.O.gammari Fauré-Fremiet,1905.Pereiopods of the gammarid amphipod Gammarus sp.O.lichtensteini Stein,1868.On various crabs and molluscs.O.nutans Ehrenberg,1838.Syn.:O.microstoma Stein,1854.On Entomostraca.On the cladoceran Alona af nis(cf.Matthes,1950).On the maxillipeds of the European cray sh Astacus leptodactylus(cf.Matthes&Guhl,1973).O.protecta Penard,1922.On the setae of pereiopods of the gammarid amphi-pod Gammarus pulex.O.reichelei Matthes&Guhl,1973.Found exclusively on the maxillipeds of the cray sh Astacus leptodactylus.O.stenostoma Stein,1868.On the isopod Asellus aquaticus.Genus Orbopercularia Lust,1950(cf.Lust,1950b)( g.9)O.astacicola(Matthes,1950)(cf.Matthes&Guhl,1973).Syn.:Opercularia astacicola Matthes,1950.Maxillipeds and pleopods of the cray sh Aus-tropotamobius torrentium.Genus Propyxidium Corliss,1979( g.10)P.aselli Penard,1922.On the isopod Asellus sp.P.asymmetrica Matthes&Guhl,1973.On the European cray sh Astacus astacus(as A. uviatilis).P.bosminae Kahl,1935.On the cladoceran Bosmina sp.P.canthocampti Penard,1922.On the pereiopods of the harpacticoid copepod Canthocamptus sp.Fresh water.P.cothurnioide Kent,1880.On the ostracod Cypris sp.P.hebes Kellicott,1888.On the pereiopods of the isopod Asellus aquaticus.P.henneguyi(Fauré-Fremiet,1905)(cf.Kahl,1935).Syn.:Opercularia hen-neguyi Fauré-Fremiet,1905.On the rst abdominal segment of the copepod Cyclops sp.Genus Ballodora Dogiel&Furssenko,1921( g.11)B.dimorpha Dogiel&Furssenko,1921.On Porcellio sp.and other terrestrialisopods.Genus Nuechterleinella Matthes,1990( g.12)N.corneliae Matthes,1990.On the ostracod Cypria ophthalmica.Genus Bezedniella Stoukal&Matis,1994( g.13)B.prima Stoukal&Matis,1994.Fresh water.On the ostracod Cypria sp.(Slovakia).Figs.8-14.8,Opercularia(O.nutans,after Foissner et al.,1992);9,Orbopercularia(O.astacicola, after Matthes&Guhl,1973);10,Propyxidium(P.canthocampti,after Penard,1922);11,Ballodora (B.dimorpha,after Dogiel&Furssenko,1921);12,Nuechterleinella(N.corneliae,after Matthes, 1990);13,Bezedniella(B.prima,after Stoukal&Matis,1994);14,Rovinjella(R.spheromae,afterMatthes,1972).Family Rovinjellidae Matthes,1972Genus Rovinjella Matthes,1972( g.14)R.spheromae Matthes,1972.On the marine isopod Sphaeroma serratum. Family Scyphidiidae Kahl,1933Genus Scyphidia Dujardin,1841( g.15)Scyphidia sp.Henebry&Ridgeway,1979.On the cladocerans Scapholeberis kingi,Alona costata,and Pleuroxus denticulatus(Ashmore Lake,Illinois, U.S.A.).Family Vaginicolidae De Fromentel,1874Genus Platycola Kent,1881( g.16)P.baikalica(Swarczewsky,1930).Syn.:Vaginicola baicalica Swarczewsky, 1930.Fresh water.On the gills of the gammarids Brandtia lata,Pallasea grubei,and Echinogammarus fuscus(Lake Baikal).P.callistoma Hadzi,1940.Fresh water.On the cave-dwelling isopod Microlis-tra spinosissima(former Yugoslavia).P.circularis Dons,1940.Marine.On the uropods of the isopod Limnoria sp.P.decumbens(Ehrenberg,1830).Syns.:Vaginicola decumbens Ehrenberg, 1830;Platycola ampulla De Fromentel,1874;P.regularis De Fromentel, 1874;P.striata De Fromentel,1874;P.truncata De Fromentel,1874;P.longicollis Kent,1882;P.intermedia Kahl,1935;P.re exa Kahl,1935;P.amphora Swarcezwsky,1930;P.amphoroides Sommer,1951.Fresh water.On several vegetable and animal substrata.On the gills of the gammarid Brachiuropus sp.(Lake Baikal)(Swarczewsky,1930).geniformis Hadzi,1940.Fresh water.On the cave-dwelling isopod Micro-listra spinosissima(former Yugoslavia).P.pala Swarczewsky,1930.Syn.:Vaginicola pala Swarczewsky,1930.On the gills of the gammarid Palicarinus puzyllii(as Parapallesa pazill)(Lake Baikal).Genus Cothurnia Ehrenberg,1831(cf.Claparède&Lachmann,1858)( g.17)C.angusta Kahl,1933.Brackish or fresh water.On ostracods(Kiel,Germany).C.anomala Stiller,1951.Fresh water.On the amphipod Corophium curvispi-num(Lake Balaton,Hungary).C.antarctica(Daday,1911)(cf.Warren&Paynter,1991).Syn.:Cothurniopsisantarctica Daday,1911.Marine.Epibiont on the ostracod Philomedes lae-vipes(Antarctic areas).C.astaci Stein,1854.Fresh water.On the pleopods and gills of cray sh.On the maxillae,maxillipeds,and pleopods of the cray sh Astacus astacus。
animalsignalsand...

1160᭧2005The Society for the Study of Evolution.All rights reserved.1161 BOOK REVIEWSrisk to casting sounds,odors,and reflected light upon the environment with no assurance that anyone is listening, smelling,or watching.Although often viewed as handicaps, perhaps these investments are efficacy and not strategic costs. The discrimination will not always be clear.For instance,the authors suggest that courtship vigor in fruitflies(Maynard Smith1956)is an index of overall male health and thus a reliable indicator of male genetic quality to females(pp.51–52).Although possible,vigorous signaling might only in-dicate that the male is a good signaler.A frog’s metabolic rate increases manifold when he calls,thus the notion that the male is advertising his physicalfitness does not seem farfetched(see e.g.Welch et al.1998).But Taigen and Wells (1984)found no relationship between calling effort and total aerobic capacity in American toads.Are female toads being fooled by cheating males,or are we the ones being fooled by assigning the wrong function to signaling?Of the many lasting contributions of John Maynard Smith, the use of game theory to model animal behavior is most prominent(e.g.,Bradbury and Vehrencamp2000).The au-thors have used these models like a surgeon’s tool to dissect the assumptions and consequences of the handicap principle in general,and reliable signals in particular.The conclusion, as we note above,is that the handicap principle is one,but only one,of several scenarios that can achieve reliable sig-nals.But the authors also note that game theory is not an ideal approach for analyzing communication systems in-volved in sexual selection in which there cannot be a single optimum(p.12).Where simple economic models fall short in addressing the important factors in sexual signaling evo-lution,Maynard Smith previously(1982)offered quantitative genetic models such as Lande’s(1981)as a more appropriate alternative,and here the authors suggest that Enquist et al.’s (2002)artificial neural network model demonstrating the in-fluence of sensory exploitation on signal evolution may be a more informative alternative.That segue into alternative models highlights a more gen-eral weakness in the use of economic models to analyze an-imal communication.For us,it is hard to imagine a deep understanding of how and why animals use and respond to signals as they do without detailed attention to the contin-gencies of the animal’s external environment,internal phys-iology,and evolutionary history.The authors address these issues in their chapter on signal form.Several phenomena such as peak shift displacement and supernormal responses can result in the evolution of signals and responses that can never be predicted by economic models.Add to that other phenomena such as stimulus categorization,generalization, and historical contingencies of the brain,and we see that the economics approach by itself is left somewhat wanting(En-quist and Arak1998;Ryan et al.2001).The costs and benefits of signaling are critical to understanding signal evolution, but so are the other factors.Game theory by itself will never tell us why birds sing,frogs croak,crickets chirp,andfish flash,although on afiner scale it might reveal which song, croak,chirp,orflash works better.Game theory results in explicit statements about underlying assumptions,a refresh-ing contrast to some arguments for the handicap principle in which the elegance of the metaphor substitutes for the sig-nificance of the data.It has made critical contributions to signal evolution,but,as the authors themselves insinuate,it is time to move on to a more integrative biology of animal communication.This book is typical of several previous books by Maynard Smith,such as those on sex(1978)and game theory(1982): it is engaging,short,to the point,and emphasizes arguments fromfirst principles rather than exhaustive documentation. Anything that Maynard Smith says is worthy of our undivided attention,and this volume co-authored with Harper is no ex-ception.Sadly,this is our last opportunity to have our attention engaged by a new work from this incredible intellect,as John, a dear friend,passed away as wefinished chapter2.L ITERATURE C ITEDBradbury,J.,and S.L.Vehrencamp.2000.Economic models of animal communication.Anim.Behav.59:259–268.Borgia,G.,and U.Mueller.1992.Bower destruction,decoration stealing and female choice in the spotted bowerbird Chlamydera maculata.Emu92:11–18.Conner,W.E.,R.Boada,F.C.Schroeder,A.Gonzalez,J.Mein-wald,and T.Eisner.2000.Chemical defense:bestowal of a nuptial alkaloidal garment by a male moth on its mate.Proc.A97:14406–14411.Endler,J.A.1992.Signals,signal conditions,and the direction of evolution.Am.Nat.139:S125–S153.Enquist,munication during aggressive interactions with particular reference to variation in choice of behaviour.Anim.Behav.33:1152–1161.Enquist,M.,and A.Arak.1998.Neural representation and the evo-lution of signal form.Pp.21–87in R.Dukas,ed.Cognitive ethology.Univ.of Chicago Press,Chicago.Enquist,M.,A.Arak,S.Ghirlanda,and C.-A.Wachtmeister.2002.Spectacular phenomena and limits to rationality in genetic and cultural evolution.Philos.Trans.R.Soc.Lond.B357: 1585–1594.Grafen,A.1990.Biological signals as handicaps.J.Theor.Biol.144:475–518.Kirkpatrick,M.1986.The handicap mechanism of sexual selection does not work.Am.Natl.127:223–240.Lande,R.1981.Models of speciation by sexual selection on poly-genic A78:3721–3725. Maynard Smith,J.1956.Fertility,mating behaviour and sexual selection in Drosophila subobscura.J.Genet.54:261–279.———.1976.Sexual selection and the handicap principle.J.Theor.Biol.57:239–242.———.1982.Evolution and the theory of games.Cambridge Univ.Press,Cambridge,U.K.———.1978.The evolution of sex.Cambridge Univ.Press,Cam-bridge,U.K.Morton,E.S.1975.Ecological sources of selection on avian sounds.Am.Nat.109:17–34.Pomiankowski,A.1987.Sexual selection:the handicap principle does not work—sometimes.Proc.R.Soc.Lond.B231:123–145. Ryan,M.J.1998a.Principle with a handicap.Q.Rev.Biol.73: 477–479.———.1998b.Receiver biases,sexual selection and the evolution of sex differences.Science281:1999–2003.Ryan,M.J.,S.M.Phelps,and A.S.Rand.2001.How evolutionary history shapes recognition mechanisms.Trends Cog.Sci.5: 143–148.Taigen,T.,and K.D.Wells.1984.Reproductive behavior and aer-obic capacities of male American toads(Bufo americanus):Is behavior constrained by physiology?Herpetologica40:292–298. Welch,A.M.,R.D.Semlitsch,and H.C.Gerhardt.1998.Call duration as an indicator of genetic quality in male gray tree frogs.Science280:1928–1930.Book Review Editor:D.FutuymaBelow is given annual work summary, do not need friends can download after editor deleted Welcome to visit againXXXX annual work summaryDear every leader, colleagues:Look back end of XXXX, XXXX years of work, have the joy of success in your work, have a collaboration with colleagues, working hard, also have disappointed when encountered difficulties and setbacks. Imperceptible in tense and orderly to be over a year, a year, under the loving care and guidance of the leadership of the company, under the support and help of colleagues, through their own efforts, various aspects have made certain progress, better to complete the job. For better work, sum up experience and lessons, will now work a brief summary.To continuously strengthen learning, improve their comprehensive quality. With good comprehensive quality is the precondition of completes the labor of duty and conditions. A year always put learning in the important position, trying to improve their comprehensive quality. Continuous learning professional skills, learn from surrounding colleagues with rich work experience, equip themselves with knowledge, the expanded aspect of knowledge, efforts to improve their comprehensive quality.The second Do best, strictly perform their responsibilities. Set up the company, to maximize the customer to the satisfaction of the company's products, do a good job in technical services and product promotion to the company. And collected on the properties of the products of the company, in order to make improvement in time, make the products better meet the using demand of the scene.Three to learn to be good at communication, coordinating assistance. On‐site technical service personnel should not only have strong professional technology, should also have good communication ability, a lot of a product due to improper operation to appear problem, but often not customers reflect the quality of no, so this time we need to find out the crux, and customer communication, standardized operation, to avoid customer's mistrust of the products and even the damage of the company's image. Some experiences in the past work, mentality is very important in the work, work to have passion, keep the smile of sunshine, can close the distance between people, easy to communicate with the customer. Do better in the daily work to communicate with customers and achieve customer satisfaction, excellent technical service every time, on behalf of the customer on our products much a understanding and trust.Fourth, we need to continue to learn professional knowledge, do practical grasp skilled operation. Over the past year, through continuous learning and fumble, studied the gas generation, collection and methods, gradually familiar with and master the company introduced the working principle, operation method of gas machine. With the help of the department leaders and colleagues, familiar with and master the launch of the division principle, debugging method of the control system, and to wuhan Chen Guchong garbage power plant of gas machine control system transformation, learn to debug, accumulated some experience. All in all, over the past year, did some work, have also made some achievements, but the results can only represent the past, there are some problems to work, can't meet the higher requirements. In the future work, I must develop the oneself advantage, lack of correct, foster strengths and circumvent weaknesses, for greater achievements. Looking forward to XXXX years of work, I'll be more efforts, constant progress in their jobs, make greater achievements. Every year I have progress, the growth of believe will get greater returns, I will my biggest contribution to the development of the company, believe inyourself do better next year!I wish you all work study progress in the year to come.。
干旱对藻造成的氧化应激
Environmental and Experimental Botany 72 (2011) 194–201Contents lists available at ScienceDirectEnvironmental and ExperimentalBotanyj o u r n a l h o m e p a g e :w w w.e l s e v i e r.c o m /l o c a t e /e n v e x p b otDesiccation induced oxidative stress and its biochemical responses in intertidal red alga Gracilaria corticata (Gracilariales,Rhodophyta)Manoj Kumar,Vishal Gupta,Nitin Trivedi,Puja Kumari,A.J.Bijo,C.R.K.Reddy ∗,Bhavanath JhaDiscipline of Marine Biotechnology and Ecology,Central Salt and Marine Chemicals Research Institute,Council of Scientific and Industrial Research (CSIR),Bhavnagar 364021,Indiaa r t i c l e i n f o Article history:Received 9July 2010Received in revised form 4March 2011Accepted 11March 2011Keywords:Antioxidative enzymes DesiccationGracilaria corticata Polyamines PUFAsReactive oxygen speciesa b s t r a c tIntertidal alga Gracilaria corticata growing in natural environment experiences various abiotic stresses during the low tides.The aim of this study was to determine whether desiccation exposure would lead to oxidative stress and its effect varies with exposure periods.This study gives an account of various biochemical changes in G.corticata following the exposure to desiccation for a period of 0(control),1,2,3and 4h under controlled conditions.During desiccation,G.corticata thalli showed dramatic loss of water by almost 47%when desiccated for 4h.The enhanced production of reactive oxygen species (ROS)and increased lipid peroxidation observed during the exposure of 3–4h were chiefly contributed by higher lipoxygenase (LOX)activity with the induction of two new LOX isoforms (LOX-2,∼85kDa;LOX-3,∼65kDa).The chlorophyll,carotenoids and phycobiliproteins (phycoerythrin and phycocyanin)were increased during initial 2h exposure compared to control and thereafter declined in the succeeding exposure.The antioxidative enzymes such as superoxide dismutase (SOD),ascorbate peroxidase (APX),glutathione reductase (GR),glutathione peroxidase (GPX)and the regeneration rate of reduced ascorbate (AsA)and glutathione (GSH)increased during desiccation up to 2–3h.Further,the isoforms of antiox-idant enzymes Mn-SOD (∼150kDa),APX-4(∼110kDa),APX-5(∼45kDa),GPX-1(∼80kDa)and GPX-2(∼65kDa)responded specifically to the desiccation pared to control,a relative higher con-tent of both free and bound insoluble putrescine and spermine together with enhanced n-6PUFAs namely C20:4(n-6)and C20:3(n-6)fatty acids found during 2h exposure reveals their involvement in defence reactions against the desiccation induced oxidative stress.© 2011 Elsevier B.V. All rights reserved.1.IntroductionThe red alga Gracilaria corticata (J.Agardh)J.Agardh occurs extensively in intertidal zone of the Indian coast and regularly experiences the desiccation during low tide periods.The organ-isms living in the intertidal zone of tropical shores are subjected to various types of abiotic stresses due to periodic exposure to a wide range of fluctuating environmental factors such as desic-cation,salinity,radiation,temperature and pollutants (Apel and Hirt,2004;Liu and Pang,2010;Kumar et al.,2010a ).The environ-mental exposure during low tide condition,demands the intertidal macroalgae to prepare early for the desiccation followed by rehy-dration and associated cellular damage (Burritt et al.,2002).This constant state of readiness requires a great deal of energy budget and could be a contributing factor to the slow growth rates of algae dwelling at the upper littoral zone as compared to those at lower littoral zone (Stengal and Dring,1997).The possible explanation∗Corresponding author.Tel.:+912782565801/3805x614;fax:+912782566970/7562.E-mail address:crk@ (C.R.K.Reddy).for the success of an alga exposed to drought could be either being physiologically more tolerant or better at resisting the water loss (Ji and Tanaka,2002).During desiccation many of the intertidal seaweeds experience extreme drying rates,reaching air dryness within hours (Schonbeck and Norton,1979;Nelson et al.,2010),generally depends on the cli-matic conditions as well as the evaporating surface-to-volume ratio of the thallus (Lobban et al.,1985).Also,desiccation causes cellu-lar dehydration,which increases the concentration of electrolyte within the cell,causing changes to membrane-bound structures including the thylakoid (Kim and Garbary,2007).It has been sug-gested that instant responses of marine plants to adverse milieu involve excess production of reactive oxygen species (ROS)such as hydrogen peroxide (H 2O 2),singlet oxygen (1O 2),superoxide (O 2•−)and hydroxyl radical (OH −)(Burritt et al.,2002).The abil-ity to withstand the oxidative assault imposed by ROS depends on the enzymatic and non enzymatic oxidants of the cell.This antioxidant system functions in a coordinated manner to alle-viate the cellular hypo/hyper osmolarity,ion disequilibrium and detoxification of ROS which otherwise cause oxidative destruc-tion to cell (Wu and Lee,2008;Liu and Pang,2010;Kumar et al.,2010a,b ).0098-8472/$–see front matter © 2011 Elsevier B.V. All rights reserved.doi:10.1016/j.envexpbot.2011.03.007M.Kumar et al./Environmental and Experimental Botany72 (2011) 194–201195Conversely,in the recent years ROS have shown to have the mul-tifaceted roles in signalling and stress responses(Foyer and Noctor, 2005)as it can also generate oxygenated polyunsaturated fatty acids(Ox-PUFAs)defending the oxidative stress.A great deal of information supporting the involvement of Ox-PUFAs in abiotic and biotic stresses has also recently implicated the function of lipoxy-genase(LOX)enzyme in the stress physiology(Maksymiec and Krupa,2006;Rucinska and Gwozdz,2005).Ritter et al.(2008)also reported the synthesis of octadecanoid and eicosanoid oxygenated derivatives in Laminaria digitata following the exposure to Cu stress. Further,polyamines(PAs)–aliphatic amines with relatively low molecular mass have been studied in macroalgae for the matu-ration of reproductive structure in Grateloupia(Sacramento et al., 2007)and Gracilaria cornea(Guzman-Uriostegui et al.,2002).Most recently,Kumar et al.(2010a)explained the potential defensive role of polyamines particularly putrescine and of PUFAs especially n-6PUFAs(C18:3(n-6)and C18:2(n-6))under oxidative stress con-ditions.It is thus conceivable that polyamines and PUFAs could be the robust effectors for scavenging the ROS and thus counteract the desiccation stress.Although,the recovery of physiological processes(photosyn-thesis and nutrient uptake)following the desiccation has been studied extensively(Kim et al.,2009;Abe et al.,2001;Ji and Tanaka,2002),little information is available on the cellular mech-anisms that operate within the intertidal seaweeds to mitigate the oxidative stress arising from desiccation(Burritt et al.,2002; Sampath-Wiley et al.,2008).In view of this,we hypothesized that enzymatic and non enzymatic antioxidants,PUFAs and endogenous polyamines may play a crucial role in minimizing the ROS gener-ation under desiccation stress.Thus,wefirstly estimated the lipid peroxidation,ROS generation and their subsequent histochemical localization as an evidence of cellular damage as function of des-iccation exposure.Subsequently,the changes in the isoforms of major antioxidative enzymes,LOX and endogenous accumulation of polyamines were examined to understand how these different systems regulate in a coherent manner as a means of desiccation tolerance.2.Materials and methods2.1.Algal cultureThe vegetative thalli of G.corticata were collected from inter-tidal region during low tide periods from Veraval Coast(20◦54 N, 70◦22 E),Gujarat,India.Selected clean and young thalli were then brought to the laboratory in a cool pack.In order to ini-tiate unialgal culture,the fronds were cleaned manually with brush in autoclaved seawater to remove epiphytic foreign mat-ters.The fronds thus cleaned were acclimatized to laboratory conditions in aerated cultures in PES medium(Provasoli,1968) supplemented with germanium dioxide(5mg L−1)for10d.Dur-ing the acclimatization period,the medium was replenished twice at5d interval and maintained under white coolfluorescent tube lights at50mol photons m−2s−1with a12:12h light:dark cycle at22±1◦C.2.2.Desiccation treatment and determination of relative water contentIn the control treatment,the thalli were maintained under submerged conditions in seawater at the culture conditions as described above.For desiccation treatment the thalli were exposed to the air while keeping their bottom ends(∼1cm)in the wet sand spread on a propylene plastic tray at25±2◦C with relative humid-ity65±2%in culture room.The experiments were set up with three replicates and were measured at0(control),1,2,3,4and5h for all biochemical parameters.The relative water content(RWC)after the exposure was calcu-lated as follows:RWC=(LW t−DW)/(FW−DW)×100,where LW t is the weight of the thalli subjected to the desiccation treatment for t hours,dry weight(DW)is the weight of the thalli oven dried for 48h at80◦C,and FW is the weight of the thalli before desiccation.2.3.Determination of lipid peroxidation and ROSThe level of lipid peroxidation in the thallus was determined as described by Heath and Packer(1968).Tissue(0.2g)was extracted in2mL of0.5%thiobarbituric acid(TBA)prepared in20%trichloro acetic acid(TCA).Extract was heated at95◦C for30min and then quickly cooled on ice.After centrifugation at10,000×g for10min, the absorbance of the supernatant was measured at532nm.Cor-rection of non-specific turbidity was made by subtracting the absorbance value taken at600nm.The level of lipid peroxidation was expressed as nmol of malondialdehyde(MDA)formed using an extinction coefficient of155mM cm−1.ROS were determined according to the procedure described by Contreras et al.(2005). Individuals of G.corticata(1g FW)incubated for1h at15◦C in 100mL of5M2,4-dichlorofluoresceine diacetate(Calbiochem, San Diego,CA,USA)dissolved infiltered seawater.After incuba-tion,the tissue was rinsed in seawater,blotted dry,weighed,and frozen in liquid nitrogen.The tissue was then ground in liquid nitrogen,suspended in5mL of40mM Tris–HCl buffer,pH7.0,and centrifuged at15,000×g for25min.Fluorescence was determined using LS-5spectro-fluorometer(Perkin-Elmer,Norwalk,CT,USA)at an excitation wavelength of488nm and at an emission wavelength of525nm.Fluorescence values were obtained using a standard curve of2,4-dichlorofluoresceine(DCF;Sigma,St.Louis,MO,USA).2.4.Histochemical detection of O2•−and H2O2The production of O2•−and H2O2in response to desiccation was analysed according to Castro-Mercado et al.(2009).For the detection of O2•−radicals the hand cut sections of control and des-iccated thalli(20in number)were immersed in5mL detection solution containing0.05%nitroblue tetrazolium(NBT)in50mM potassium phosphate buffer(pH6.4)and10mM NaN3.The sec-tions were infiltrated under vacuum for3min in the same solution and illuminated for2h until appearance of dark spots,character-istic of blue formazan precipitates.Stained sections were cleared by boiling in acetic:glycerol:ethanol(1:1:3,v/v/v)solution before photographs were taken.H2O2production was visually detected by an endogenous peroxidase-dependent staining procedure using 3,3 -diaminobenzidine(DAB).Hand cut sections of control and des-iccated thalli(20in number each)were immersed in DAB solution 1mg/mL(pH5.0),vacuum-infiltrated for5min and then incubated at room temperature for8h in the presence of light till brown spots appeared.Sectioned were bleached by immersing in boiling ethanol to visualize the brown spots and photographs were taken.To ver-ify the specificity of precipitates,before staining with DAB some sections were immersed for2h in solution containing the H2O2 scavenger1mM ascorbate(data not shown).2.5.Determination of photosynthetic pigmentsThe photosynthetic pigments were estimated by following the method of Dawes et al.(1999).Chlorophyll,carotenoids(80% acetone)and phycobiliproteins(100mM phosphate buffer,pH 6.5)were extracted by grinding the sample(1g FW)in respec-tive solutions(1:3,w/v)in the dark and cold conditions followed by centrifugation at3000×g at4◦C for15min.Absorbance was recorded at662and645for chlorophyll,470nm for carotenoids196M.Kumar et al./Environmental and Experimental Botany72 (2011) 194–201and620,650,and565nm for phycobiliproteins by using Shi-madzu UV spectrophotometer(UV-160,Shimadzu,Japan).The amount of chlorophyll and carotenoids pigments was calculated according to Lichtentaler and Wellburn(1985).Phycoerythrin(PE), phycocyanin(PC)and allophycocyanin(APC)contents were esti-mated using the equations described by Tandeau and Houmard (1988).2.6.Determination of antioxidative enzymes,water soluble antioxidants,lipoxygenase and polyaminesThe activities of antioxidant enzymes namely superoxide dis-mutase(SOD),ascorbate peroxidase(APX),glutathione reductase (GR)and glutathione peroxidase(GPX)and water soluble antiox-idants were determined as described by Contreras et al.(2005). Extract for LOX was prepared according to the method of Tsai et al. (2008)and assayed by measuring the increase in absorbance at 234nm with substrate linolenic acid(100M)prepared in ethanol. The increase in absorbance due to the accumulation of conjugate dienes was monitored at234nm for10min.The activity was cal-culated using the extinction coefficient of conjugated dienes(ε, 25mM−1cm−1).Polyamines were extracted in5%TCA following the method described by Guzman-Uriostegui et al.(2002).TCA extracts were analysed for free polyamines following dansylation in a mixture consisted of200L TCA extract,400L dansyl chloride (Sigma,5mg mL−1in acetone),and200L saturated Na2CO3.After incubation at70C for1h,100L proline(100mg mL−1)was added to remove excess dansyl chloride and extracted in0.5mL of ethyl acetate by vortexing for15–30s.The organic layer containing the polyamines was separated by low speed centrifugation(3000×g), removed and dried under nitrogen.An aliquote of50L was used for spotting onto LK60Whatman silica gel thin layer chromatog-raphy(TLC)plates.Identification of polyamines was accomplished by comparison of R f values with authentic polyamine standards (Put,Spd and Spm obtained from Sigma as hydrochlorides)on TLC using the solvent system:cyclohexane:ethylacetate(5:4,v/v) and chloroform:triethylamine(25:2,v/v).Dansyl-polyamines were scrapped off from the TLC plates and redissolved in600L ace-tone.The samples thus obtained were shaken and centrifuged at6000×g for3min,and500L of this solution was quan-tified using high-resolution spectro-fluorometer(Perkin-Elmer, Norwalk,CT,USA)with excitation at365nm and emission at 510nm.2.7.Activity staining of antioxidative enzymes and lipoxygenaseThe isoenzyme profile of antioxidative enzyme and lipoxy-genase was determined using10%or12%non-denaturating polyacrylamide gels using their specific activity staining proce-dures for SOD(Beauchamp and Fridovich,1971),APX(Mittler and Zilinskas,1994),GPX(Lin et al.,2002)and LOX(Heinisch et al., 1996).The molecular mass of enzyme isoforms was evaluated comparing with the standard molecular weight marker contain-ing myosin,210kDa;-galactosidase,135kDa;bovine serum albumin,80kDa;soyabean trypsin inhibitor,31.5kDa;lysozyme, 18.2kDa.2.8.Determination of fatty acidsFatty acids from lipids were converted to respective methyl esters according to Kumar et al.(2010b)by trans-methylation using 1%NaOH in methanol and heated for15min at55◦C,followed by the addition of5%methanolic HCl and again heated for15min at 55◦C.Fatty acid methyl esters(FAMEs)were extracted in hexane and analysed by GC-2010coupled with GCMS-QP2010.3.Statistical analysisResults are expressed as mean of three replicates with standard deviation.Statistical analyses were performed by one way analysis of variance(ANOVA).Significant differences between means were tested by the least significant difference(LSD)at0.05probability levels.4.Results4.1.Relative water content,lipid peroxidation and ROSDesiccation exposure caused a significant decrease in the RWC that was contingent to exposure duration and decreased by almost 47%and58%(p<0.05)in the thalli desiccated for4h and5h respec-tively compared to control.The thalli desiccated for5h were not able to survive when rehydrated back in natural seawater for24h. Therefore,the thalli were exposed for a maximum of4h for sub-sequent experiments.The decrease in the RWC observed in the present study was accompanied with the accumulation of TBARS and ROS generation in the thalli(Table1).A threefold increase (p<0.05)in their content was found in the thalli exposed for3–4h. In view of this,a histochemical staining was employed to detect in situ accumulation of O2•−and H2O2radicals(two important representatives for ROS)using NBT and DAB respectively as the staining reagents(supplementary Fig.1).A blue formazone formed by reduction of NBT by O2•−is clearly evident for the generation of superoxide radical that appearedfirst in the epidermal cells (2h)then gradually progressed to cortical cells(3h)and later dis-tributed all over the tissue with the advancement of desiccation (4h)(supplementary Fig.1A).Similarly,the formation of H2O2 dependent brown precipitates was contingent with the exposure duration(supplementary Fig.1B)and accumulated maximum in the thalli exposed for longer duration(4h)where it drenched completely in to the epidermal as well as cortical cells.However, a short term desiccation did not produce detectable differences between control and thalli exposed for1h.Further,we also mea-sured the activity of LOX to ascertain its possible involvement in lipid peroxidation and generation of ROS.Desiccation exposure markedly enhanced the LOX activity(>3fold,p<0.05)in thalli exposed for3–4h(Table2)compared with the control activity (8.1nkatal min−1mg−1protein).In addition,prolonged exposure of 3–4h induced two new isoforms of LOX such as LOX-2(∼85kDa) and LOX-3(∼65kDa)in addition to LOX-1(∼110kDA)with a con-sistent increase in their intensity as the desiccation progress.4.2.Photosynthetic pigments,water soluble antioxidants and polyaminesA significant increase in chlorophyll and carotenoid concen-tration was observed during the initial exposure of2h with values80.48±3.44and38.93±4.49g g−1FW corresponded to an increase of almost1.5and1.75fold(p<0.05)respectively over the control values with53.32±3.94and22.32±4.38g g−1FW respectively.However,in the prolonged exposure of3–4h the con-tents of both were decreased gradually.Phycobiliproteins such as phycoerythrin(PE),phycocyanin(PC)and allophycocyanin(APC) showed varied responses with the desiccation exposure.The concentration of both PE and PC increased gradually with the des-iccation exposure and attained the peak values with565.81±19.88 and283.07±22.95g g−1FW after2h exposure.This corresponds to an increase of40%from the control amount with386.23±23.35 and201.33±11.56g g−1FW respectively.The degree of increase for APC following desiccation exposure was considerably low when compared with control.M.Kumar et al./Environmental and Experimental Botany72 (2011) 194–201197Table1Effect of desiccation exposure on relative water content,lipid peroxidation,reactive oxygen species and photosynthetic pigments of G.corticata(mean±SD,n=3). Parameter Desiccation hours(h)01234LSD(5%)RWC(%)100a82.64±2.76b70.66±3.09c58.90±2.09d52.69±2.59e 3.47 MDA(nmol g−1FW) 3.20±0.56d 4.63±0.57d 6.43±0.47c8.90±0.70b10.77±0.48a 2.10 ROS(mol g−1FW)0.17±0.03e0.32±0.04d0.47±0.05c0.66±0.07b0.80±0.05a0.08 Photosynthetic pigments( g g−1FW)Chlorophyll53.32±3.94c68.97±8.49b80.48±3.44a52.60±5.02c43.13±3.74d9.33 Carotenoids22.32±4.38cd30.17±2.21b38.93±4.49a24.61±2.73bc16.94±2.58d 6.21 Phycoerythrin386.23±23.35c475.50±15.87b565.81±19.88a412.38±34.85c315.18±8.39d40.53 Phycocyanin201.33±11.56b266.39±7.06a283.07±22.95a206.54±17.92b168.47±14.27c28.61 Allophycocyanin133.47±12.51b154.21±9.60a155.07±14.33134.10±7.77b127.56±13.84b15.89RWC,relative water content;MDA,malondialdehyde;ROS,reactive oxygen species;different superscript letters within row indicate significant differences at p<0.05 according to one way ANOVA.The contents of reduced(AsA),oxidized(DHA)and total (AsA+DHA)ascorbate were greatly influenced by desiccation expo-sure(Table2).The AsA showed a consistent higher amount throughout the experiment with the peak value2.41nmol g−1FW (2h)that correspond to an increase of2.4fold over the control value with1.04nmol g−1FW.DHA also gradually accumulated as the desiccation progress and increased to>2fold(p<0.05)after 4h when compared with control0.71nmol g−1FW.A significant accumulation of both AsA and DHA led to a remarkable increase in total ascorbate content with a maximum of3.87nmol g−1FW (2h)and was chiefly contributed by AsA.To determine the regen-eration of AsA,the ratio of AsA/DHA was calculated and found to increase only during the initial hours of exposure with peak ratio1.66(2h)compared to1.48(control)and decreased there-after till the end of experiment.The contents of reduced(GSH),total (GSH+GSSG)glutathione and their regeneration rate(GSH/GSSG) were quite higher(2.5–3fold,p<0.05)in the extended exposure of3h with values7.33,10.96and2.02nmol g−1FW respectively (Table2).The corresponding values in the control thalli were2.37, 4.32and1.22nmol g−1FW respectively.Among the polyamines such as putrescine(Put),spermidine (Spd)and spermine(Spm)investigated,Put was the predominant polyamine in all its three forms viz.free(F),bound soluble(BS) and bound insoluble(BI)followed by spermine and spermidine. In the control thalli,the accumulation of Put and Spm followed in the order of BS>BI>F and F>BS>BI respectively.Following the2h desiccation,the level of F-Put(43.01),BI-Put(41.05),F-Spm(22.04) and BI-Spm(7.61,1h)increased significantly(p<0.05)over the control values of14.02,33.42,12.10and1.07mol g−1FW respec-tively,and thereafter declined in the extended exposure(Table2). The content of BS-Spm increased by almost70%in short term des-iccation of less than2h over the control with9.30mol g−1FW, whereas BS-Put exhibited a constant decrease with the exposure duration.Table2Effect of desiccation exposure on enzymatic,water soluble antioxidants and polyamines in G.corticata(mean±SD,n=3).Parameter Desiccation hours(h)01234LSD(5%)Enzymes activity(U mg−1protein)SOD119.67±5.13c174.33±5.86b202.33±9.61a215.33±7.37a104.33±9.61d14.09 APX0.33±0.04d0.46±0.05c0.58±0.05b0.71±0.06a0.48±0.06c0.09GR0.52±0.03cd0.69±0.05c0.81±0.07b0.98±0.08a0.48±0.06d0.10 GPX0.63±0.06c0.60±0.04c0.92±0.06a0.76±0.05b0.53±0.06c0.09 LOX a8.10±0.62e12.81±1.22d18.74±1.45c25.12±3.22b31.02±3.11a 3.99 Antioxidants(nmol g−1FW)AsA 1.04±0.16c 1.61±0.12b 2.41±0.23a 1.87±0.22b 1.53±0.10b0.31 DHA0.71±0.08c 1.03±0.18c 1.46±0.13b 1.82±0.15ab 2.07±0.17a0.26AsA+DHA 1.76±0.15b 2.64±0.30b 3.87±0.34a 3.69±0.09a 3.60±0.12a0.40AsA/DHA 1.48±0.34ab 1.59±0.15a 1.66±0.08a 1.04±0.22bc0.74±0.10c0.30 GSH 2.37±0.25d 3.78±0.31c 5.51±0.30b7.33±0.30a 4.90±0.26b0.51 GSSG 1.95±0.03c 2.40±0.11c 2.76±0.50bc 3.63±0.24b 6.51±0.52a0.62 GSH+GSSG 4.32±0.27d 6.17±0.23c8.27±0.36b10.96±0.45a11.41±0.44a0.65 GSH/GSSG 1.22±0.11bc 1.58±0.20ab 2.05±0.49a 2.02±0.12a0.76±0.09c0.46 Polyamines( mol g−1FW)PutrescineF14.02±2.29d23.60±3.16c43.01±3.19a31.86±2.24b7.66±2.13d 4.81 BS46.85±6.01a13.73±2.97b36.98±3.58a17.14±2.01b9.19±1.67b 6.54 BI33.42±4.63bc55.47±3.72a41.05±3.65b26.95±3.07c 5.35±1.22d 6.28 SpermineF12.10±.18cd16.83±1.32b22.04±1.92a14.42±1.72bc9.55±1.65d 2.87 BS9.30±1.12bc15.78±1.94a13.30±1.06a9.85±1.04b 6.14±0.73c0.94 BI 1.07±0.10c7.61±1.01a 3.69±0.54b0.85±0.10d0.68±0.07d 2.26 SpermidineF 3.05±0.23b 2.13±0.26c 1.71±0.14cd 1.20±0.12d 6.10±0.36a0.43BS 3.94±0.28a 1.24±0.17b 1.12±0.07bc0.75±0.08c0.72±0.09c0.28 BI7.88±0.93a 6.08±0.43b7.02±0.39ab 4.28±0.56c 4.47±0.13c 1.00SOD,superoxide dismutase;APX,ascorbate peroxidase;GR,glutathione reductase;GPX,glutathione peroxidase;LOX,lipoxygenase;AsA and GSH,reduced ascorbate and glutathione respectively;DHA and GSSG,oxidized ascorbate and glutathione respectively;F,free;BI,bound soluble;BI,bound insoluble;different letters within row indicate significant differences at p<0.05according to one way ANOVA.a The unit of LOX is nkatal mg−1protein.198M.Kumar et al./Environmental and Experimental Botany72 (2011) 194–2014.3.Antioxidative enzymes and their isoformsSOD,APX,GR and GPX were selected as biomarkers to deter-mine the oxidative stress resulted from desiccation.All the studied enzymes exhibited enhanced activities duringfirst3h of exposure and thereafter reduced markedly.The specific activities of SOD,APX and GR increased by1.5–2.5fold(3h)with values215,0.71and 0.98U mg−1protein respectively over the control activities with 119,0.33and0.52U mg−1protein respectively(Table2).Thalli exposed for1h did not show any significant increase in GPX activ-ity,although gained the peak activity(0.92U mg−1protein)when exposed for2–3h and declined subsequently.Native PAGE sup-ported the spectrophotometric measurements of these enzymes (supplementary Fig.2).Apparent higher activity of SOD observed in the thalli throughout the experiment was solely attributed to Mn-SOD(∼150kDa)(supplementary Fig.2B)confirmed by using H2O2/KCN as inhibitors.APX in particular revealed the specific response to the desiccation exposure and exhibited three isoforms APX-1(∼125kDa),APX-2(∼85kDa),APX-3(∼60kDa)in control and1h desiccated thalli(supplementary Fig.2A).An additional isoform APX-4(∼110)exhibited in the samples exposed for2–4h. Further,the prolong exposure of3–4h is evident for the induction of APX-5(∼45kDa)with the complete inhibition of APX-3.The activ-ity gel of GPX(supplementary Fig.2C)displayed three GPX isoforms (GPX-1,2and3)with higher activity of GPX-3(∼35kDa)particu-larly in the control samples.The other isoforms GPX-1(∼80kDa) and GPX-2(∼65kDa)showed higher activity in the thalli exposed for2–3h while diminished in the samples desiccated for4h.4.4.Fatty acidsTable3summarizes the variation in fatty acid composition of G. corticata in response to desiccation stress.Palmitic(C16:0),stearic (C18:0),palmitoleic(C16:1,n-7),oleic(C18:1,n-9cis),linoleic (C18:2,n-6),dihomo-␥-linolenic(C20-3,n-6)and arachidonic acids (C20:4,n-6)were the foremost fatty acids that showed majorfluc-tuations following desiccation.The palmitic and arachidonic acid showed a reverse trend for their accumulation with the advance-ment of desiccation.The content of palmitic acid when decreased to minimum value19.88%TFA(2h)and corresponded to a signif-icant reduction of43%(p<0.01)over the control(34.83%TFA),a parallel increase of28%(2h)in the content of arachidonic acid was observed over the control52.54%TFA.During the prolong expo-sure a dramatic increase in palmitic acid(40.11%TFA,4h)was accompanied with a significant decline in arachidonic acid(46.98% TFA,4h).Among the other fatty acids,a substantial decrease in C18:0,C16:1(n-7),C18:1(n-9)trans and C20:5(n-3)fatty acids was analogized by a constant increase in C18:1(n-9)cis acid through-out the experiment.Interestingly,fatty acid C20:2(n-6)showed its existence only after an exposure of2h.The arachidonic and dihomo-␥-linolenic were the major polyunsaturated fatty acids contributed to almost58%TFA in control,while their level elevated to74%after an exposure of2h followed by a considerable decrease till the last sampling.Also,with the advancement of desiccation the ratio of UFA/SFA varied with a maximum of3.72(2h)and minimum 1.37(4h)compared with the control1.68.5.DiscussionAmong the variety of physical and biological factors determining algal zonation in intertidal region,desiccation tolerance/resistance also plays a decisive role in species distribution.The data obtained in the present study are clearly evident for the narrow tolerance competency of G.corticata and can tolerate the water loss of only 25–35%before it succumbs to desiccation stress.The water loss beyond35%(3–4h exposure)caused greater lipid peroxidation and accumulation of O2•−and H2O2radicals is evidenced by histochem-ical studies(supplementary Fig.1),confirming the state of oxidative stress.Superoxide radicals inactivate several enzymes important in energy production and amino acid metabolism.These enzymes have iron–sulfur clusters and their inactivation is caused by oxida-tion of the cluster,leading to release of iron,followed by Fenton chemistry.If O2•−levels rise(e.g.during desiccation),inactivation rates accelerate,repair cannot keep up and metabolic pathways are inhibited(Halliwell,2006).The role of H2O2in stress-induced dam-age has long been recognized,but it is now also generally accepted that H2O2is an integral component of cell signalling cascades and an indispensable secondary messenger in biotic and abiotic stress situations(Foyer and Noctor,2005).The results of ourfindings for desiccation tolerance are similar to Kim and Garbary(2007)who reported20–24%of water loss in Codium fragile.In contrary,Ji and Tanaka(2002)observed only13%water loss in Hizikia fusiformis and Gloipeltis furcata under2h of controlled desiccation.The intertidal Porphyra haitanensis could withstand a30%loss of water before major reduction in photosynthetic activity occurs(Zou and Gao, 2002).The water loss from thallus generally depends on the plant cell wall matrix composition,and surface texture(Moore et al., 2008).The volatile aldehyde like MDA and specific LOX isoen-zymes are suitable markers for membrane lipid peroxidation.As compared with control,the thalli desiccated for3–4h showed con-siderably higher lipid peroxidation and has positively correlated with enhanced activity of LOX.This enzyme generates singlet oxy-gen and superoxide anions while incorporating molecular oxygen in to linoleic and linolenic fatty acids,to form lipid hydroper-oxides.In the present study,the enhanced LOX activity together with the induction of two new isoform LOX-2and LOX-3in the thalli desiccated for3–4h could be attributed to the decreased arachidonic level which had been utilized as the substrate for its catalytic reaction.Moreover,the induced LOX isoforms could also be categorized in to type II lipoxygenases,as these isoforms were induced in the later hours of desiccation exposure when both chlorophyll and carotenoids got diminished.The type II lipoxyge-nases are widespread in plants,have a neutral pH-optimum and a strong tendency to show co-oxidation reactions(e.g.of chloro-phyll,carotenoids,and lipophilic vitamins)caused by free radicals liberated during the catalytic process(Siedow,1991).Recently, Contreras et al.(2009)described the induction of an arachidonic acid dependent LOX activity and its role in lipoperoxide produc-tion in Lessonia nigrecens and Scytosiphon lomentaria under copper exposure.The initial rise in the photosynthetic pigments during short term desiccation of2h suggests the greater demand for increased ATP (formed via cyclic photophosphorylation)for desiccation tolerance mechanism.Apparently,during this short term desiccation when the surface waterfilm gets evaporated,the atmospheric CO2can penetrate the cell and may enhance the photosynthesis(Zou and Gao,2002).But with the extended desiccation and more loss of water the electron system operating between photosystem II(PSII) and photosystem I(PSI)may get interrupted due to decreased photosynthetic pigments coupled with enhanced ROS.Moreover, a parallel increase in carotenoids during initial2h further sug-gests their role as an antioxidant by acting as physical quenchers of electronically exited molecules,in addition to functioning as photoreceptors(Woodall et al.,1997).Further,the increased phy-cobiliproteins particularly PE and PC evidenced their protective role under oxidative stress conditions.In red algae,phycobilipro-teins are synthesized in phycobilisomes and are associated with light harvesting centre(LHC)of PSII(Sampath-Wiley et al.,2008). Their increased level could be a possible acclamatory mechanism for G.corticata in response to desiccation induced oxidative stress as these proteins function as storage proteins for biosynthesis dur-。
数字信号处理—基于计算机的方法答案
3-2 (a)Sketch the naturally sampled PAM waveform that results from sampling a 1—kHz sine wave at a 4—kHz rate.(b) Repeat part (a) for the case of a flat-topped PAM waveform.Solution:3—4 (a)Show that an analog output waveform (which is proportional to the original input analog waveform)may be recovered from a naturally sampled PAM waveform by using the demodulation technique showed in Fig.3-4.(b) Find the constant of proportionality C, that is obtained with this demodulation technique , where w (t) is the oriqinal waveform and Cw(t) is the recovered waveform. Note that C is a function of n ,where the oscillator frequency is nfs.Solution :()()()()()()1111sin sin 2cos sin 2cos cos sin [cos 2cos cos sin 2cos s s jk ts k k k jk t s k k s sk s s s s s k n kt kT s t c ek d k d d e d d k tk d k dk d w t w t d d k t k d v t w t n tk dw t d n t n dd d k t n tn k d d ωωτππωπππωπωππωππωω∞∞-=-∞=-∞∞∞-=-∞=∞=∞=≠-⎡⎤=∏=⎢⎥⎣⎦==+⎡⎤=+⎢⎥⎣⎦==++∑∑∑∑∑∑2]s n t ω211cos cos 222s s n t n t ωω=+ after LPF: ()()()sin sin o w t w t n d d n d n d d n dcw t c ππππ==∴= 3-7 In a binary PCM system, if the quantizing noise is not to exceed P ± percent of the peak-to-peak analog level, show that the number of bits in each PCM word needs to be⎪⎭⎫ ⎝⎛=⎥⎦⎤⎢⎣⎡⎪⎪⎭⎫ ⎝⎛≥P p n 50log 32.350log 10] [log 10102(Hint : Look at Fig. 3-8c.)Solution:Binary PCM M=n2levelsfor PP q V P n 100||≤We need)50(log )10(log 50log 5025011002 size step 1022p P n PM P M V P M V n PP PP ≥⎪⎭⎫ ⎝⎛≥≥=≤≤==δ)(log )(log )(log )(log )(log x b a x x b a b b a ==3—8 The information in an analog voltage waveform is to be transmitted over a PCM system with a ±0。
无定形磷酸钛处理铅
Journal of Colloid and Interface Science318(2008)160–166/locate/jcisAdsorption of Pb2+,Zn2+,and Cd2+from watersby amorphous titanium phosphateKun Jia,Bingcai Pan∗,Qingrui Zhang,Weiming Zhang,Peijuan Jiang,Changhong Hong,Bingjun Pan,Quanxing ZhangState Key Laboratory of Pollution Control and Resource Reuse,School of the Environment,Nanjing University,Nanjing210093,People’s Republic of ChinaReceived24August2007;accepted16October2007Available online26November2007AbstractIn the current study,amorphous titanium phosphate(TiP)was prepared as an adsorbent for heavy metals from waters.Uptake of Pb2+,Zn2+, and Cd2+onto TiP was assayed by batch tests;a polystyrene–sulfonic acid exchanger D-001was selected for comparison and Ca2+was chosen as a competing cation due to its ubiquitous occurrence in waters.The pH-titration curve of TiP implied that uptake of heavy metals onto TiP is essentially an ion-exchange pared to D-001,TiP exhibits more preferable adsorption toward Pb2+over Zn2+and Cd2+even in the presence of Ca2+at different levels.FT-IR analysis of the TiP samples laden with heavy metals indicated that the uptake of Zn2+and Cd2+ions onto TiP is mainly driven by electrostatic interaction,while that of Pb2+ions is possibly dependent upon inner-sphere complex formation,except for the electrostatic interaction.Moreover,uptake of heavy metals onto TiP approaches equilibrium quickly and the exhausted TiP particles could be readily regenerated by HCl solution.©2007Elsevier Inc.All rights reserved.Keywords:Titanium phosphate;Heavy metals;Adsorption;Mechanism1.IntroductionWater pollution by heavy metals remains an important envi-ronmental issue associated negatively with health and the econ-omy[1],and more stringent regulations have been established to restrict their random discharge.Accordingly,various tech-nologies,including chemical precipitation[2],adsorption[3], membrane processes[4],electrolytic methods[5],and ion ex-change[6–9],have been proposed for their remediation from waste streams.Ion exchange is one of the most frequently studied and widely applied techniques for the treatment of metal-contaminated wastewater[6,7],and polymeric cation or anion exchangers are always employed for this specific pur-pose[6,7].*Corresponding author.E-mail address:bcpan@(B.Pan).As a family of inorganic cation exchangers,zeolite or zeolite-based adsorbents have been studied extensively for se-lective removal of heavy metals from industrial and natural waters[10,11].Unfortunately,we have less knowledge of stud-ies involving adsorption of heavy metals onto another important group of inorganic cation exchangers,M(HPO4)2(M=Zr,Ti, Sn).M(HPO4)2compounds are good ion-exchange materials and exhibit remarkable thermal and radiolytic stability[12,13]. There are numerous reports on ion-exchange properties of dif-ferent M(HPO4)2with alkali or alkaline earth metal ions in aqueous solution[13,14].However,little is known about their ion-exchange properties in the presence of aqueous heavy metal ions[15,16].In our previous study we demonstrated the applicability of Zr(HPO4)2as an adsorbent for heavy metals[17,18].Here we attempt to explore the adsorption behavior and mechanism of heavy metals onto another important M(HPO4)2,Ti(HPO4)2. D-001,a widely used polystyrenesulfone cation exchanger,was chosen for comparison.0021-9797/$–see front matter©2007Elsevier Inc.All rights reserved. doi:10.1016/j.jcis.2007.10.043K.Jia et al./Journal of Colloid and Interface Science318(2008)160–1661612.Materials and methods2.1.MaterialsLead nitrate,zinc nitrate,and cadmium nitrate were used as heavy metal sources in this study by dissolving them in the double-deionized water.All chemicals,including titanium chlo-ride(liquid,purity>98%),are of analytical grade and were purchased from Shanghai Reagent Station(Shanghai,China). D-001,a macroreticular polystyrenesulfone exchanger(of H-type)with total capacity of4.30meq/g and cross-linking den-sity of8%,was kindly provided by Langfang Electrical Resin Co.,Ltd.(Hebei Province,China).It was obtained in spheri-cal bead form with sizes ranging from0.6to1.0mm.Prior to use,D-001was subjected toflushing with deionized water to remove residual impurities until neutral pH(6.8–7.2)and then vacuum-desiccated at348K for24h until it reached a constant weight.2.2.Preparation and characterization of titanium phosphateFor preparation of TiP(titanium phosphate)particles,40ml of titanium chloride wasfirst dissolved into60ml of4M HCl solution.At the ambient temperature,the above solution was gradually added into aflask containing250ml of5M H3PO4and shaken at120rpm overnight.Then the mixture was subjected tofiltration,and the resulting solid particles(TiP) were rinsed with double-deionized water till neutral pH.Sub-sequently,the TiP particles were vacuum-desiccated at323K for24h for further study.X-ray diffraction(XRD)spectra of the TiP particles were recorded by an XTRA X-ray diffrac-tometer(Switzerland).XPS analysis of the TiP samples was performed with a spectrometer(ESCALAB-2,Great British) equipped with an Mg KαX-ray source(1253.6-eV protons). The software package Scalab was used tofit the spectra peaks. FT-IR spectra of TiP particles before and after metal adsorp-tion were taken from a Nexus870FT-IR spectrometer(USA) with a pellet of powered potassium bromide and adsorbent in the range of500–4000cm−1.2.3.pH titrationpH titration of TiP particles was performed according to the reference[13,19].Portions(500mg)of each exchanger were mixed with100ml of0.1M NaCl.This mixture was kept for 6h and titrated against0.15M NaOH solution.The pH of the solution was recorded after each addition of1.0ml of the titrant till the pH became constant.From the solution pH values before and after the exchange process,the milliequivalents of OH−ion consumed were liequivalents of OH−ions consumed by the exchanger were then plotted against the cor-responding pH values to get the pH-titration curves.2.4.Batch adsorption and regeneration experimentsBatch adsorption tests were determined by contacting TiP particles or D-001beads with a range of different concentra-tions of heavy metal solution in250-ml glassflasks,maintainedFig.1.XRD spectra of the TiP particles prepared in the current study.at desired pH and temperature.To start the experiment,known amounts of the individual adsorbents(TiP or D-001)were intro-duced into a100-ml solution containing each individual metal (50–500mg/l).Theflasks were then transferred to a G25 model incubator shaker with thermostat(New Brunswick Sci-entific Co.,Inc.)and shaken at200rpm for24h at303K to ensure that the adsorption process reaches equilibrium.HNO3 solution(0.5M)was used to adjust the solution pH throughout the experiment when necessary.A quantity of0.5ml of solution at various time intervals was sampled from theflasks to deter-mine adsorption kinetics.The amount of each metal loaded onto the adsorbent is calculated by conducting a mass balance before and after the test.The TiP samples from adsorption runs were transferred to anotherflask afterfiltering and10.0ml of0.5M HCl solution was used for extraction of the loaded metals.2.5.AnalysesConcentrations of all the heavy metals were determined by atomic absorption spectroscope(Z-8100,Hitachi,Japan)ex-cept for those less than1mg/l,which were determined by an atomicfluorescence spectrophotometer with an online reducing unit(AF-610A,China)with NaBH4and HCl solution[20].3.Results and discussion3.1.Characterization of TiP particlesTiP particles with sizes ranging from1to100µm generally were prepared according to the following equation:TiCl4+2H3PO4→Ti(HPO4)2↓+4HCl.(1) The Ti/P ratio in the TiP phase,determined as1:2by XPS analysis,further ensured its structure of Ti(HPO4)2.As indi-cated by XRD spectra(Fig.1),the TiP particles are amorphous in nature[21,22].To elucidate the nature and numbers of ex-changeable sites in TiP,pH titration of the TiP sample was carried out by comparison with D-001.The total number of hy-drogen ions in TiP deduced from Fig.2is about8.25mmol/g,162K.Jia et al./Journal of Colloid and Interface Science318(2008)160–166Fig.2.pH-titration curves of D-001and TiP using0.15M NaOH solution at 303K(0.50g of each adsorbent was used for titration test).which is consistent with the value calculated from its molecu-lar formula(8.34mmol/g).Similarly to ZrP[17],the hydrogen ion within TiP is also released in a stepwise manner because the acid groups within TiP are weakly dissociated and it is reluc-tant to exchange its H+ion for Na+,so that the ion exchange remains incomplete.Only about4.11meq/g of hydrogen ion (about half of the total amount)can be released to solution for ion exchange below the neutral pH.In contrast,as a strong acid cation exchanger,all the hydrogen ions in D-001parti-cles are readily released for ion exchange with Na+and then neutralization by the added OH−.Hence,the pH of the super-natant aqueous solution remains essentially unchanged.Note that heavy metals can always be effectively trapped by ion ex-change in weakly acidic solution because most of the heavy metal ions are precipitated in alkaline solution.Thus,it can be assumed that the conceptual mechanism of heavy metal adsorp-tion by TiP may be presented asTi(HPO4)2+(1/2)M2+ TiM1/2H(PO4)2+H+,(2) where M represents the corresponding heavy metal element. 3.2.Effect of solution pH on adsorptionThe effect of solution pH on metal extraction by TiP was examined and the results are presented in Fig.3.The uptake capacity of each metal was increased with the increasing so-lution pH,and the optimum solution pH for lead,zinc,and cadmium is about3,4.5,and5,respectively.According to the pH-titration curve and our previous study of heavy metal re-moval onto zirconium phosphate(ZrP)particles[17,18],the pH-dependent trend is assumed to result from ion exchange between metal ions and TiP.In addition,negligible uptake at pH less than0.5suggested that the metal-laden TiP particles might be regenerated by strong acid solutions,which was fur-ther demonstrated in the desorption experimentsbelow.Fig.3.Effect of solution pH on heavy metal adsorption onto TiP at303K (0.050g TiP particles were added into100ml solution containing1.10mmol/l of each metal,respectively).3.3.Adsorption isotherms and kineticsAdsorption isotherm experiments on heavy metals onto TiP were performed at303K and the results are illustrated in Fig.4 and correlated by the traditional Langmuir and Freundlich mod-els[15],(3)C eq e=1K L q m+C eq m,(4) q e=K F C1/n e,where C e is the concentration of each target species in equilib-rium,q e is adsorption capacity in equilibrium,q m is the max-imum amount of solute exchanged per gram of the exchanger, and K L is a constant that can indicate the capability of adsorp-tion.K F and n are constants to be determined.All the constants are listed in Table1.Results indicated that lead removal by TiP can be represented by the Langmuir model more reasonably, while zinc and cadmium adsorption can be well correlated by both models.Adsorption kinetic experiments of three metals on TiP were also performed and the results are presented in Fig.5.It can be seen that initial adsorption of heavy metals is very quick,fol-lowed by a gradual adsorption approaching equilibrium within 1h.The kinetic data are not correlated by any mathematic mod-els,mainly because we cannot define the size ranges of TiP particles due to their ultrafine nature,which is necessary before properly modeling the kinetic performance of a given sorbent.3.4.Effect of Ca2+on removal of heavy metalsTaking into account the fact that a relatively high level of common cations such as Na+,Ca2+,and Mg2+is ubiquitous in waste streams laden with heavy metals,adsorption selectivity of a specific exchanger toward heavy metals is a key factor in ensuring its technical applicability.In the current study,Ca2+ was selected as a model competing cation and its effect on theK.Jia et al./Journal of Colloid and Interface Science318(2008)160–166163Fig.4.Adsorption isotherms of(a)Pb2+(pH3.0–3.2);(b)Cd2+(pH4.5–5.0);(c)Zn2+(pH4.5–5.0)onto TiP particles at303K.Table1Isotherm constants for heavy metals adsorption onto TiP at303KHeavy metals Langmuir model Freundlich modelK L q m(mmol/g)R2K f n R2Pb2+0.0946 1.890.9600.0809 2.000.859 Cd2+0.02820.5580.9930.0704 2.620.961 Zn2+0.01870.7190.9920.0606 2.320.986Fig.5.Adsorption kinetics of heavy metals onto TiP at303K(0.40g TiP and 1000ml solution containing0.5mmol/l of each metal were selected for the study).removal of heavy metals was examined as compared to D-001 of sulfonic acid functionality.As seen in Fig.6,increasing Ca2+/M2+ratio inevitably results in decreasing uptake capacity of target species of both D-001and TiP due to the competi-tive effect.However,compared to D-001,TiP displays a high preference toward lead over other two metals.To compare the selectivity of the two adsorbents,the distribution ratio K d was quantified by the equation[23](5) K d=(C0−C e)/C0V/m,where C0is the initial concentration of the solute,V is the vol-ume of the solution,and m is the mass of the solute.The K d values listed in Table2further elucidate the preferable sequence toward different heavy metals,and the competitive effect of Ca2+was also demonstrated by the variation of K d values with the Ca/M ratios.In general,ion-exchange preference of a given exchanger for target ions follows the principle of hard and soft acids and bases(HSAB)[24,25].Therefore,TiP and similar compounds with hard Lewis basic oxygen-rich functional groups would be more likely to undergo ion exchange with hard Lewis acids. Therefore,Pb2+,grouped as a harder Lewis acid than Cd2+ and Zn2+[25],can be trapped by TiP particles more effectively than the other two metals.However,as a harder Lewis acid, Ca2+does not display an adverse effect on Pb2+removal by TiP as compared to the other two metals,which seems incon-sistent with the HASB principles.The underlying mechanism will be further elucidated in the following section.On the other hand,stronger adsorption affinity always oc-curs when thefixed ionic groups are similar in structure to precipitating or complexing agents that react with the counte-rions[13].Table3lists the log K sp values of some metal phos-phates or sulfates.Apparently,the absolute log K sp values of metal phosphates also follow the same sequence as their selec-tivity behavior,i.e.,Pb2+>Zn2+≈Cd2+>Ca2+.In contrast, calcium ions are preferred by sulfate ions,which are hard bases, over other cations and result in a great decrease in selectivity of heavy metals onto D-001accordingly.164K.Jia et al./Journal of Colloid and Interface Science318(2008)160–166Fig.6.Effect of Ca2+on(a)Pb2+(pH3.0–3.2);(b)Cd2+(pH4.5–5.0);(c) Zn2+(pH4.5–5.0)removal by TiP and D-001at303K(0.025g TiP particles or D-001beads were introduced in solution with each metal at initial concentration of0.25mmol/l,respectively).3.5.FT-IR analysisTo gain insight into the adsorption mechanism of different heavy metals onto TiP,FT-IR analysis of TiP samples laden with different metals was performed by comparison with the fresh ones.As seen from the IR spectra(Fig.7),the pres-Table2Effect of Ca2+on the distribution coefficients(K d)of heavy metals(M)ad-sorption onto TiP and D-001at303KHeavymetals(M2+)Adsorbent K d(l/g)at different initial Ca2+/M2+ratiosin solution2481632 Pb2+TiP12411610486.364.9 D-00116.87.05 3.30 1.680.84 Zn2+TiP 1.45 1.000.410.550.29 D-001 3.25 1.170.610.270.21 Cd2+TiP 1.75 1.400.780.700 D-001 3.64 1.310.2800Table3log K sp values of some metal phosphates and sulfates aMetal phosphates Ca3(PO4)2Cd3(PO4)2Zn3(PO4)2Pb3(PO4)2 log K sp−27.70−31.44−32.04−42.09 Metal sulfates CaSO4CdSO4ZnSO4PbSO4 log K sp−7.80NA NA−6.50a The corresponding values of CdSO4and ZnSO4are not available(NA) because they are soluble in water.ence of external water within the TiP particles in addition to the strongly hydrogen-bonded OH or extremely strongly co-ordinated H2O is confirmed by the sharp peaks at3500and 1650cm−1[19,26].The band from1000to1020cm−1repre-sents asymmetric stretching vibration of Ti–P–OH[27,28],and the weak band at605–615cm−1is assigned to the deforma-tion vibration for the Ti–O bond[29].Detailed band variation data of TiP samples before and after uptake of metals are listed in Table4.The bands of Ti–P–OH in all the TiP samples were shifted to higher frequency in the sequence Pb Zn≈Cd, which is consistent with their selectivity sequence.Note that negligible variation for Ca2+-laden TiP was observed in the band.This shift of the P–OH band reflects different electrostatic interactions between the orthophosphate group and metals af-ter replacement of hydrogen ion.Meanwhile,the obvious shift of the Ti–O band after uptake of Pb2+and Ca2+implies the presence of Pb–O or Ca–O interaction,which may result from inner-sphere complex formation of both metals with TiP.This is not the case for Zn2+and Cd2+,and the corresponding shifts are negligible.Therefore,adverse effects of Ca2+on Cd2+and Zn2+adsorption by TiP mainly result from the possible forma-tion of inner-sphere complexes between Ca2+and TiP,and TiP prefers Pb2+adsorption over the other three metals,mainly be-cause of the synergistic effect of the electrostatic interaction and possible inner-sphere complex formation[17].Further study should be performed to elucidate the mechanism of adsorption of heavy metals onto titanium phosphate.3.6.Environmental implicationsOther preliminary results also indicated that other common cations,including Na+and Mg2+ions,play a less significant role than Ca2+ions in uptake of heavy metals onto TiP,which also follows the HSAB principles.Following several trials,HClK.Jia et al./Journal of Colloid and Interface Science318(2008)160–166165Fig.7.FT-IR spectra of TiP samples loaded with different metal ions(the capacity of each metal ranges from0.7to0.8mmol/g).Table4Absorption peaks of TiP samples loaded with different heavy metals in FT-IR spectra aTiP TiP/Pb TiP/Zn TiP/Cd TiP/Ca A(cm)1019.91002.71016.91017.51020.3 B(cm−1)615.3607.1613.7614.4610.3 a A and B refer to Fig.7.solution was proved to be an efficient regenerant for TiP loaded with heavy metals.Batch desorption runs indicated that more than92%of Pb2+,95%of Zn2+,and80%of Cd2+preloaded on the TiP particles can be trapped by10ml0.5M HCl solution at303K.All the above results indicated that TiP is a potential candidate for removal of heavy metals,particularly for Pb2+. However,like other functional inorganic compounds,such as hydrated ferric oxide and ZrP,TiP as ultrafine particles in nature cannot be directly used for removal of heavy metals,due to the excessive pressure drop in anyflow-through systems[30,31]. An effective approach is to immobilize TiP particles on porous materials to obtain hybrid adsorbents,and the relevant study is under the way in our laboratory.4.ConclusionsAmorphous titanium phosphate(TiP)was proved to be an ef-fective adsorbent for Pb2+,Cd2+,and Zn2+from water through an ion-exchange mechanism.High preference of TiP for Pb2+ over Cd2+and Zn2+was observed even in the presence of Ca2+at relatively high levels,which can be explained by hard and soft acids and bases(HASB)principles.FT-IR analysis in-dicated that Cd2+and Zn2+adsorption onto TiP was mainly driven through electrostatic interaction,while Pb2+extraction by TiP was enhanced due to the synergetic effect of electrostatic interaction and inner-sphere complex formation.Additionally, the metal-laden TiP can be effectively regenerated by HCl so-lution.AcknowledgmentsThis study was partially supported by the NSFC of China (20504012)and Jiangsu NSF(BK2007717/2006129). References[1]J.O.Nriagu,J.M.Pacyna,Nature333(1988)134.[2]M.M.Matlock,B.S.Howerton,D.A.Atwood,Ind.Eng.Chem.Res.41(2002)1579.[3]C.J.Moon,J.H.Lee,Process Biochem.40(2005)1279.[4]J.J.Hong,S.M.Yang,C.H.Lee,Y.K.Choi,T.Kajiuchi,J.Colloid Inter-face Sci.202(1998)63.[5]N.Meunier,P.Drogui,C.Gourvenec,G.Mercier,R.Hausler,J.F.Blais,Environ.Technol.25(2004)235.[6]A.Dabrowski,Z.Hubicki,P.Podkošcielny,E.Robens,Chemosphere56(2004)91.[7]T.A.Kurniawan,G.Y.S.Chan,W.H.Lo,S.Babel,Chem.Eng.J.118(2006)83.[8]P.Woodberry,G.Stevens,I.Snape,Solvent Extr.Ion Exch.24(2006)603.[9]M.Perez-Collado,C.Molero,rrondo,React.Funct.Polym.64(2005)139.[10]L.Lv,G.Tsoi,X.S.Zhao,Ind.Eng.Chem.Res.43(2004)7900.[11]U.Wingenfelder,C.Hansen,G.Furrer,R.Schulin,Environ.Sci.Tech-nol.39(2005)4606.[12]F.Helfferich,Ion Exchange,McGraw–Hill,New York,1962.[13]A.Clearfield,Chem.Rev.88(1988)125.[14]C.A.Borgo,Y.Gushikem,J.Colloid Interface Sci.246(2002)343.[15]B.B.Sahu,K.Parida,J.Colloid Interface Sci.248(2002)221.[16]K.M.Parida,B.B.Sahu,D.P.Das,J.Colloid Interface Sci.270(2004)436.[17]B.C.Pan,Q.R.Zhang,W.Du,W.M.Zhang,Q.J.Zhang,Water Res.41(2007)3103.[18]B.C.Pan,Q.R.Zhang,W.M.Zhang,B.J.Pan,W.Du,L.Lv,Q.J.Zhang,Q.X.Zhang,J.Colloid Interface Sci.310(2007)99.[19]K.G.Varshney,A.H.Pandith,U.Gupta,Langmuir14(1998)7353.[20]F.Yu,T.L.Yu,Spectrosc.Spectr.Anal.20(2000)898.[21]G.L.Zhao,Z.Y.Yuan,T.H.Chen,Mater.Res.Bull.40(2005)1922.[22]C.Trobajo,S.A.Khainakov,A.Espina,J.R.Garcí,Chem.Mater.12(2000)1987.[23]B.C.Pan,Q.X.Zhang,F.W.Meng,X.T.Li,Environ.Sci.Technol.39(2005)3308.166K.Jia et al./Journal of Colloid and Interface Science318(2008)160–166[24]S.D.Alexandratos,X.P.Zhu,Macromolecules38(2005)5981.[25]M.Misono,E.Ochiai,Y.Saito,Y.Yoneda,J.Inorg.Nucl.Chem.29(1967)2685.[26]H.N.Kim,S.W.Keller,T.E.Mallouk,Chem.Mater.9(1997)1414.[27]M.Kawahara,J.Morita,M.Rikukawa,K.Sanui,N.Ogata,Electrochim.Acta45(2000)1395.[28]M.Yamada,I.Honma,Electrochim.Acta48(2003)2411.[29]A.I.Bortun,S.A.Khainakov,L.N.Bortun,D.M.Poojary,Chem.Mater.9(1997)1805.[30]B.C.Pan,B.J.Pan,X.Q.Chen,W.M.Zhang,X.Zhang,Water Res.40(2006)2938.[31]L.Cumbal,A.K.Sengupta,Environ.Sci.Technol.39(2005)6508.。
寄生黑腹果蝇的日本开臂反颚茧蜂生物学特性及其寄生对寄主发育及免疫反应的影响
http : ! www. insect. org. cndoi : 10.16380/L kcxb. 2021.01.0081 月 Janua/2021, 64(1): 70-79昆虫学报ACTAENTOMOLOGICASINICA寄生黑腹果蝇的日本开臂反"茧蜂生物:性其寄生对寄主 免疫反应的 丨张 显,周思聪,陈佳妮,庞 兰,张启超,王莹,时敏,陈学新,黄健华"(浙江大学昆虫科学研究所,农业部作物病虫分子生物学重点实验室,杭州310058)摘要:【目的】调查寄生黑腹果蝇Drosophila melanogastes 的日本开臂反P 茧蜂AsoPara japonica 的生物 ,明确其寄生对寄主生长发育及 的影响。
【方法】运用解剖成像和 光定量PCR.查分析了日本开臂反P 茧蜂的各发育 发育历期、形态特征,以及日本开臂反P 茧蜂寄生黑腹果蝇2龄幼'后的寄生率、出蜂率及寄主化蛹时间和 路15个主要基因'ToT通路中的 SPE , Tol l , Myd88 , Dp 和 Drosomycix , Imd 通路中的 PGRP-LE , PGRP-LC , iod , Relisp 和Diptericin 及PO 通路中的Spn27A , MP2 , yellow-f2 , DoxP2和PPO1 )转录水平的变化$【结果"在25 ±1f ,相对湿度50% ±1%和光周期16L :8D 条件下,日本开臂反P 茧蜂的卵期平均为2.38 ± 0.01 d ,'期为5.36 ±0.07 d ,蛹期为8.30 ±0.04 d o 日本开臂反P 茧蜂寄生黑腹果蝇2龄幼', 生率为94.9% ±4.0%,出蜂率为64. 3% ±7.1%$另外,日本开臂反P 茧蜂寄生使黑腹果蝇幼'50%化蛹时的化蛹时间比未被寄生对照显著延缓约0.5 d ;寄生后黑腹果蝇抗菌肽基因Drosomycix 和Di.pteri.ci.x 转录水平显著上调,而原酚氧化酶基因PPO1转录水平则显著下调$【结 论】延缓 发育和抑制寄主的黑化 ,日本开臂反P 茧蜂能够在黑腹果蝇幼'上成生。
- 1、下载文档前请自行甄别文档内容的完整性,平台不提供额外的编辑、内容补充、找答案等附加服务。
- 2、"仅部分预览"的文档,不可在线预览部分如存在完整性等问题,可反馈申请退款(可完整预览的文档不适用该条件!)。
- 3、如文档侵犯您的权益,请联系客服反馈,我们会尽快为您处理(人工客服工作时间:9:00-18:30)。
Report Peak BMP Responses in the Drosophila Embryo Are Dependent on the Activation of Integrin SignalingGraphical AbstractHighlightsd Drosophila embryos lacking integrin function have disruptedBMP responsesd Collagen IV activates integrin signaling to enhance levels ofthe pMad transducerd Integrins bind BMP receptors and promote pMad levels afterBMP receptor activationd BMP activates expression of an a-integrin,representing apositive feedback loop AuthorsAnnick Sawala,Margherita Scarcia, Catherine Sutcliffe,Scott G.Wilcockson, Hilary L.AsheCorrespondencehilary.ashe@In BriefDuring development,cells receive information from the extracellular matrix via integrin receptors,in addition to growth factor signals from other cells. Sawala et al.show that BMP-responsive transcription in the Drosophila embryo is not simply a readout of the BMP concentration but also requires integrin-mediated enhancement of BMP signaltransduction. Sawala et al.,2015,Cell Reports12,1584–1593September8,2015ª2015The Authors/10.1016/j.celrep.2015.08.012Cell ReportsReportPeak BMP Responses in the Drosophila Embryo Are Dependent on the Activation of Integrin SignalingAnnick Sawala,1,2Margherita Scarcia,1Catherine Sutcliffe,1Scott G.Wilcockson,1and Hilary L.Ashe1,*1Faculty of Life Sciences,University of Manchester,Manchester M139PT,UK2Present address:The Francis Crick Institute,Mill Hill Laboratory,The Ridgeway,London NW71AA,UK*Correspondence:hilary.ashe@/10.1016/j.celrep.2015.08.012This is an open access article under the CC BY-NC-ND license(/licenses/by-nc-nd/4.0/).SUMMARYWithin a3D tissue,cells need to integrate signals from growth factors,such as BMPs,and the extracellular matrix(ECM)to coordinate growth and differentia-tion.Here,we use the Drosophila embryo as a model to investigate how BMP responses are influenced by a cell’s local ECM environment.We show that in-tegrins,which are ECM receptors,are absolutely required for peak BMP signaling.This stimulatory effect of integrins requires their intracellular signaling function,which is activated by the ECM protein collagen IV.Mechanistically,integrins interact with the BMP receptor and stimulate phosphorylation of the downstream Mad transcription factor.The BMP-pathway-enhancing function of integrins is inde-pendent of focal adhesion kinase,but it requires conserved NPXY motifs in the b-integrin cytoplasmic tail.Furthermore,we show that an a-integrin subunit is a BMP target gene,identifying positive feedback between integrin signaling and BMP pathway activity that may contribute to robust cell fate decisions. INTRODUCTIONTwo key requirements for the success of multicellular life are the ability of cells to adhere to each other,via a secreted protein network called the extracellular matrix(ECM),and to communi-cate with each other,sometimes over long distances,through the release of signaling molecules.In addition to providing struc-tural support to tissues,the ECM has evolved to regulate inter-cellular signaling pathways,for example by binding to growth factors and regulating their distribution or activity in the extracel-lular space(Hynes,2009).The ECM can also signal through its own adhesion receptors,primarily integrins,to initiate intracel-lular signaling events that converge with growth factor signaling pathways,thus allowing cells to integrate information about ECM composition and mechanical properties with biochemical signals(Giancotti and Ruoslahti,1999).Although crosstalk between integrin signaling and growth-fac-tor-activated receptor tyrosine kinase signaling has been studied in some detail(Alam et al.,2007),comparably little is known about how the ECM influences intracellular signaling through bone morphogenetic proteins(BMPs),a highly conserved family of growth factors with diverse roles during development and disease(Wu and Hill,2009).In the canonical signaling pathway, BMPs assemble complexes of type I and type II receptors, leading to activation of the type I receptor Ser/Thr kinase domain and phosphorylation of a Smad transcription factor (Mad in Drosophila)(Wu and Hill,2009).Phospho-Mad(pMad) associates with a second Smad transcription factor(Medea in Drosophila),and the pMad/Medea complex accumulates in the nucleus to regulate transcription of BMP target ing the Drosophila model,we have recently shown that the ECM molecule collagen IV directly binds BMPs and regulates their movement across tissues(Sawala et al.,2012;Wang et al., 2008).Severalfindings indicate that collagen IV may also act locally to enhance BMP signal reception.For example,collagen IV is required for local activation of BMP signaling at the tip of developing renal tubules(Bunt et al.,2010).Furthermore, collagen IV can enhance the effect of BMPs in tissue culture, where long-range movement is unlikely to be important(Paralkar et al.,1992).To understand how the local ECM environment impacts BMP responses,we investigated a role for integrins,which are collagen IV receptors(Khoshnoodi et al.,2008).Wefind that maximal levels of BMP pathway activation in vivo are only achieved in the presence of integrin signaling,which functions downstream of collagen IV to potentiate signaling through the canonical Smad pathway.RESULTSIntegrins Are Required for Peak Levels of BMP Signaling in the Early Drosophila EmbryoWe examined a role for integrins in BMP pathway activation in the early Drosophila embryo,where a BMP activity gradient specifies cell fates along the dorsoventral axis(Figure1A). Integrin receptors are expressed on the cell surface as a/b heterodimers(Leptin et al.,1989).As b PS is the only b-integrin expressed in the early blastoderm embryo(Figure S1A),we induced homozygous germline clones for a null allele of b PS, mys XG43(Leptin et al.,1989),and analyzed BMP target gene expression in embryos lacking maternal and zygotic b PS expres-sion and therefore all integrin function(from now on referred to as b PSÀembryos).In wild-type embryos,the high threshold BMP target genes Race(Ance in FlyBase)and hindsight(hnt)are ex-pressed in a narrow stripe along the dorsal midline(presumptive1584Cell Reports12,1584–1593,September8,2015ª2015The Authorsamnioserosa),where peak signaling occurs,while the lower threshold gene u-shaped(ush)is expressed in a broader dorsal domain(Figure1B).By contrast,in b PSÀembryos,Race and hnt expression is lost in the presumptive amnioserosa,and ush expression is significantly(p<0.0001)narrower(Figure1B), characteristic of embryos with reduced levels of BMP signaling. The BMP defect is rescued by a paternal wild-type copy of b PS (data not shown).Expression of the major BMP ligand in the early embryo,dpp,and of sog,which encodes a critical extracel-lular BMP regulator(Wu and Hill,2009),is unaffected in b PSÀembryos(Figure S2A).Together,these data indicate that integ-rins are required for normal levels of BMP signaling in the early embryo.As b PS can form receptors with several a-integrins(Brown, 2000),we examined BMP phenotypes in a-integrin mutant em-bryos.Out of thefive a-integrin genes,we found that multiple edematous wings(mew)and scab(scb)are expressed in partially overlapping domains in the dorsal ectoderm(Figures S1B and S1C),where BMP signaling is active.In addition,mew expres-sion extends ventrally into the neuroectoderm,overlapping with the expression domain of sog(Figure S1D).Embryos mutant for mew or scb exhibit defects in the expression of BMP target genes(Figure1C),with differences in the phenotypes for mew and scb mutants reflecting their different expression patterns in the embryo.For Race,the expression is preferentially lost in the posterior in scb mutant embryos,whereas it is lost uniformly along the anterior-posterior axis in mew mutants(compare em-bryos classified as‘‘weak’’in Figure1C).These results suggest that integrin receptors involving both mew and scb gene prod-ucts enhance BMP signaling in the early embryo.The posteriorly expressed target gene hnt,like Race,is partially or fully lost in the scb mutant but infrequently lost in mew mutants(Figure1C). Also,in a subset of mew mutants,Race,hnt,or ush expression is broadened,in extreme cases resembling embryos that lack Sog(Figures1C and S2C).This likely represents a function of mew in regulating Sog distribution,as previously described in the developing wing(Araujo et al.,2003),in addition to its integrin signaling function described below.This second function may lead to a slightlyflatter BMP gradient in mew mutants,thus explaining the broader hnt expression observed(Figure1C),in contrast to the loss of Race,a gene that is absolutely dependent on the highest BMP levels.We next quantified the pMad gradient in b PSÀembryos(Umu-lis et al.,2010)To circumvent staining variability between samples,we only compared b PSÀembryos to siblings that were maternal b PSÀzygotic b PS+,as these embryos could be processed together throughout.Maternal b PSÀzygotic b PS+ embryos show no defect in BMP target gene expression or pMad activation(Figure1D;data not shown),making them a valid control.In both b PSÀand control embryos,peak pMad levels increase markedly between stage5and stage6(Fig-ure1E),consistent with previous reports of pMad gradient dynamics(Rushlow et al.,2001).At stage5,pMad levels are considerably lower in b PSÀembryos than controls,resulting in a narrower gradient and a reduced peak(Figure1E).At stage 6,peak pMad levels at the dorsal midline reach similar levels in b PSÀand control embryos(Figure1E);however,the dorsal domains over which the gradient reaches a threshold of0.4and0.6are significantly narrower(Figures1F and1G).In wild-type embryos,these thresholds correspond to the width of ush($14cells;see Figure1A)and Race/hnt(four to six cells;see Fig-ure3D)expression,respectively,consistent with the reduction inpMad levels leading to disrupted BMP target gene expression in b PSÀembryos.Although we cannot rule out additional effects on non-canonical BMP signal transduction or BMP-independenteffects,our data demonstrate that integrins are required forthe timely and robust formation of the pMad gradient in theearly embryo.The Signaling Function of Integrins Is Sufficient for Their Role in BMP Pathway ActivationTo test if integrins exert their effect on BMP signaling throughtheir extracellular ligand binding activity or by activating intracel-lular signaling pathways,we made use of a chimeric receptor,Torso D b PS cyt,in which the cytoplasmic domain of b PS is fused to the transmembrane and extracellular domains of a constitu-tively active form of the Torso receptor(Martin-Bermudo andBrown,1999).This integrin signaling construct is unable tobind integrin ligands,but it is capable of signaling due toTorso D-mediated clustering of the b PS cytoplasmic domain(Fig-ure2A).We used the Gal4/UAS-system to express wild-type b PS or Torso D b PS cyt transgenes in b PSÀembryos and tested for their ability to rescue the BMP phenotype.Zygotic expression of wild-type b PS restores Race expression in$50%of em-bryos(Figure2B).Rescue in only half of the embryos likely reflects the proportion expressing the Gal4transcription factor maternally and zygotically,as opposed to maternally only.The Torso D b PS cyt integrin signaling construct was also able to rescue Race and hnt induction in b PSÀembryos(Figures2B and2C),demonstrating that the signaling function of integrins is sufficient for their role in promoting BMP signaling.Overex-pression of b PS or Torso D b PS cyt in a wild-type background does not broaden Race or hnt expression(Figure S3),suggesting that whereas integrin signaling is required to augment BMP signaling,it is not limiting with respect to this function in a wild-type context.We conclude that integrin signaling is permissive for generating peak levels of BMP pathway activation.Integrin Signaling Acts Downstream of Collagen IV to Enhance BMP ActivityWe have shown previously that collagen IV mutant embryos have disrupted BMP signaling due to an altered extracellular BMP dis-tribution(Wang et al.,2008).If collagen IV acts as an integrin ligand,a loss of integrin signaling may contribute to the defect in BMP signaling observed in collagen IV mutant embryos(Fig-ure3A).To test this,we examined whether Torso D b PS cyt,which induces integrin signaling independent of ECM ligands,can rescue BMP target gene expression in embryos with reduced levels of collagen IV(Figure3A),due to a mutation in viking, one of two collagen IV genes in Drosophila(Wang et al.,2008). As shown in Figure3B,overexpression of Torso D b PS cyt restores Race induction in$50%of embryos,whereas wild-type b PS, which requires an ECM ligand for activation of signaling,has no effect.This result suggests that integrin signaling may act downstream of collagen IV to enhance BMP activity.The partial rescue of Race expression observed with Torso D b PS cyt inCell Reports12,1584–1593,September8,2015ª2015The Authors1585A EF GFigure 1.Loss of Integrin Expression Causes Defects in BMP Signaling Responses in the Early Embryo(A)Early Drosophila embryo showing patterning of the dorsal ectoderm by a gradient of BMP activity.(B)RNA in situ hybridizations of wild-type or maternal/zygotic mys XG43mutant (b PS À)embryos showing expression of the BMP target genes Race ,hnt ,and ush .For Race and hnt quantification,n =3,>15embryos per genotype in each experiment;error bars represent SEM.For ush width,individual measurements are shown with mean ±SD (n =92for wild-type and n =69for b PS À).****p <0.0001(unpaired t test).(C)RNA in situ hybridizations for Race and hnt in mew (mew M6)and scb (scb 5J38)mutant embryos.Phenotypes were classified as ‘‘lost,’’‘‘weak,’’or ‘‘broad’’(see Supplemental Experimental Procedures and Figure S2B for details)and were counted on embryo samples collected from heterozygous mutant stocks (n =3,>60embryos counted per genotype in each experiment;error bars represent SEM).(D)pMad immunostaining of wild-type,maternal b PS Àzygotic b PS +(mat b PS Àzyg b PS +)and maternal/zygotic b PS À(b PS À)embryos.All scale bars represent 50m m.(legend continued on next page)1586Cell Reports 12,1584–1593,September 8,2015ª2015The Authorscollagen IV mutant embryos,as compared to b PS Àembryos (Figure 2B),is consistent with a dual role for collagen IV in pro-moting BMP signaling in the early embryo:to activate integrin signaling and promote extracellular BMP gradient formation(Sawala et al.,2012;Wang et al.,2008).In agreement with this,a reduction in collagen IV leads to a more severe decrease in BMP signaling than the loss of integrins,based on the width of ush expression (Figure 3C).To exclude the possibility that the loss of integrin signaling in collagen IV mutants is due to a general loss of ECM integrity,we examined BMP signaling in embryos lacking expression of laminin,an ECM protein that interacts with the collagen IV network and can act as an integrin ligand in Drosophila (Brown,2000).In contrast to integrin and collagen IV mutants,embryos lacking b -laminin show a variable expansion of the Race expres-sion domain (Figure 3D).We speculate that this expanded Race expression is due to competition between collagen IV and lami-nin for binding to integrins,with only collagen IV interactions leading to BMP-promoting signaling events.In support of this,we find that addition of laminin to Drosophila cells plated on a collagen IV substrate,but not when plated on plastic,inhibits pMad accumulation in a dose-dependent manner following pathway stimulation,and this effect is reduced by co-transfect-ing additional b PS (Figure 3E,right panel).Together,these results suggest that engagement of integrin receptors by collagen IV,but not laminin,promotes BMP responses in the early Drosophila embryo.Integrin Signaling Acts Downstream of BMP Receptor Activation to Enhance pMad AccumulationWe next investigated the molecular link between integrin signaling and enhanced BMP signal transduction.A key signaling protein linking integrin to growth factor pathways is focal adhesion kinase (FAK)(Giancotti and Ruoslahti,1999).However,we did not detect any defect in BMP signaling in embryos lacking Drosophila FAK (Figure S4A),suggesting that integrin signaling enhances BMP signal transduction through an FAK-independent mechanism.To further dissect this mechanism,we developed a Drosophila tissue culture assay.Treatment of S2R+cells with the BMP ligand Dpp induces pMad,and this is enhanced when cells are plated on collagen IV (Figure 4A).RNAi-medi-ated knockdown of b PS abolishes the stimulatory effect of collagen IV on pMad induction,whereas it has no effect on pMad levels in plastic-plated cells (Figures 4A and 4C).As shown in Figures 4B and 4C,b PS RNAi in collagen IV-plated cells also reduces pMad induction by a constitutively active form of the BMP receptor Thickveins (Tkv),Tkv QD ,indicating that collagen IV/integrin signaling acts downstream of Tkv acti-vation.The effects of collagen IV/integrins on pMad levels do not coincide with changes in the levels of total Mad (transfected Flag-Mad)(Figures 4A and 4B),suggesting that they are not mediated via an effect on Mad stability.In terms of the a -integ-rin requirement,knockdown of both mew and scb together,but not either subunit alone,also reduces pMad accumulation (Fig-ure 4D),suggesting that both a -integrins can function with b PS to stimulate pMad.(E–G)Quantification of the pMad gradient in mat b PS À,zyg b PS +,and b PS Àembryos.(E)Mean pMad intensity along the dorsal-ventral axis at 0.5embryo length.Threshold lines indicate the width of the pMad gradient plotted in (C)and (D).(F and G)Mean width of the pMad gradient at thresholds 0.4(C)and 0.6(D)along the anterior-posterior axis for stage 6embryos.Black dots indicate significant differences (p <0.05)between maternal b PS Àzyg b PS +and b PS À.All embryo images show dorsal views of stage 6embryos,anterior to the left.See also Figures S1and S2.AFigure 2.Integrin Signaling Is Sufficient to Rescue the BMP Phenotype in b PS ÀIntegrin Mutant Embryos(A)Torso D b PS cyt construct,which can mimic integrin signaling in the absence of ligand binding.(B and C)Overexpression of b PS and of Torso D b PS cyt in maternal/zygotic mys XG43mutant (b PS À)embryos can rescue expression of the peak threshold BMP target genes Race (B)and hnt (C).Rescue was quantified as the per-centage increase in embryos with a wild-type expression pattern relative to a no transgene control (n =3,>50embryos counted per genotype in each experiment;error bars are SEM).For details,see Supplemental Experimental Procedures .Asterisks denote significant difference from no transgene control (i.e.,0%rescue);**p <0.01,***p <0.001(t test).Scale bars represent 50m m.See also Figure S3.Cell Reports 12,1584–1593,September 8,2015ª2015The Authors 1587Consistent with our in vivo rescue experiments (Figures 2and 3),the positive effect of collagen IV/integrins on both Dpp-or Tkv QD -induced pMad accumulation can be mimicked by expression of Torso D b PS cyt (Figures 4E and 4F),confirming that integrin signaling mediates the effect on pMad observed in S2R+cells and demonstrating that integrin signaling acts cell autonomously to enhance BMP responses.We next used the Torso D b PS cyt construct to identify residues in the b PS cyto-plasmic domain required for integrin-enhanced pMad accumula-tion.Two conserved NPXY motifs in the b -integrin cytoplasmic tail are important for the recruitment of a variety of integrin-bind-ing proteins (Legate et al.,2009).Mutation of tyrosine in the first (Y831)or second (Y843)NPXY motif to alanine,either alone or in combination,did not affect expression levels of Torso D b PS cyt (Figure 4F)but compromised its ability to promote pMad phos-phorylation (Figure 4F).These results suggest that both NPXY motifs in the b PS cytoplasmic tail are important for its enhance-ment of BMP signaling.To gain further mechanistic insight,we tested if integrin re-ceptors interact with Tkv.Indeed,we found that Tkv,but notaA C DEFigure 3.Activation of Integrin Signaling Can Partially Restore BMP Signaling Defects in Collagen IV Mutant Embryos(A)Diagram showing how a potential loss of integrin signaling in collagen IV mutant embryos may reduce BMP signaling (left),which would be predicted to be rescued by constitutively active integrin signaling (right).(B)Expression of Torso D b PS cyt ,but not wild-type b PS,can partially restore expression of Race in collagen IV (viking )mutant embryos.Race expression patterns were classified as normal,weak,or lost (n =3,>70embryos counted per genotype in each experiment;error bars represent SEM).Asterisks denote significant difference from no transgene control (i.e.,0%rescue);*p <0.05(t test).See Supplemental Experimental Procedures for details of rescue quantification.(C)The ush expression pattern is narrower in collagen IV (viking )mutant embryos than in embryos lacking b integrin (b PS À).ush width shown as individual measurements and mean ±SD,n >45for each genotype;****p <0.0001(ordinary one-way ANOVA).(D)Maternal/zygotic LanB11B1mutant embryos show a broadened Race expression pattern.Race width shown as individual measurements and mean ±SD,n >35for each genotype;****p <0.0001(Welch’s test).Scale bars represent 50m m.(E)Western blot of pMad and transfected Flag-Mad (total Mad),Flag-Tkv QD ,and Myc-b PS in S2R+cells which were plated on either plastic or collagen IV and treated with increasing levels of laminin,as indicated.1588Cell Reports 12,1584–1593,September 8,2015ª2015The Authorscontrol transmembrane protein(Frizzled),can co-immunopre-cipitate with b PS,mew(a PS1)and scb(a PS3)(Figures4G–4I). The interaction between a PS1or a PS3and Tkv is abrogated by b PS RNAi(Figures4H and4I),consistent with integrin surface presentation being dependent on functional integrin receptors (Leptin et al.,1989).We next truncated the b PS cytoplasmic tail after residues involved in stabilization of the integrin a-b het-erodimer(Figure S4B).A similar truncation in mammalian b3in-tegrin does not disrupt cell-surface expression(O’Toole et al., 1991),a result we confirmed for our b PS-trunc construct(Fig-ure S4C).As shown in Figure4J,truncation of the b PS cyto-plasmic tail abrogates the interaction with Tkv,suggesting that the integrin-Tkv interaction is mediated intracellularly and there-fore could be relevant for the integrin-mediated enhancement of Tkv-mediated Mad phosphorylation.By contrast,mutation of the NPXY motifs in the b PS did not impair its binding to Tkv(Fig-ure4J).As the NPXY motifs are required for integrin-signaling mediated enhancement of pMad(Figure4F),this suggests that binding of integrins to Tkv alone is not sufficient to enhance pMad accumulation(see Discussion).Together,our data sug-gest that integrin receptors can form complexes with BMP receptors,enhancing their ability to phosphorylate Mad.The a-Integrin Subunit scb/a PS3Is Itself a BMP Target GeneThe spatial and temporal expression pattern of scb is consistent with this a-integrin encoding gene being positively regulated by BMP signaling.Therefore we examined the scb expression pattern in embryos with increased and decreased levels of BMP signaling.We found that scb expression is expanded ventrally in embryos with four copies of dpp or overexpressing the activated BMP receptor,tkv QD,and lost in dpp Hin37mutant embryos(Figure5A).The lack of scb expression in the central re-gion of the embryo can be explained at least in part by a repres-sive input from the gap gene transcription factor Kru¨ppel,as scb expression expands into the central region in Kru¨ppel mutant embryos(Figure S5).Overall,these data demonstrate that scb is indeed a BMP target gene and identify a positive feedback loop in which BMP-dependent induction of scb expression further enhances BMP signal transduction via the activation of integrin signaling.DISCUSSIONOur study reveals that BMP-responsive transcription during Drosophila embryonic dorsal-ventral axis patterning is not sim-ply a readout of the BMP signal but instead requires synergy between BMP and integrin signaling.Our data support a model whereby collagen IV activation of integrin signaling augments pMad levels(Figure5B).Consistent with collagen IV acting as an integrin ligand,which is well documented in vertebrates (Khoshnoodi et al.,2008),collagen-IV-directed rotations of folli-cle epithelia during Drosophila oogenesis also require integrins (Haigo and Bilder,2011).Thus,we envisage two functions for collagen IV in regulating BMP signaling(Figure5B):(1)collagen IV shapes the BMP gradient through a direct collagen IV-Dpp interaction,as we have described previously(Sawala et al., 2012;Wang et al.,2008);and(2)collagen IV activates integrin signaling,which amplifies the BMP signal by forming com-plexes with BMP receptors and enhancing induction of pMad.In addition,we show specificity for collagen-IV-induced integrinactivation,as laminin,which can bind both a PS1-and a PS3-containing integrin receptors(Brown,2000;Scho¨ck and Perri-mon,2003),does not promote BMP responses,possibly dueto activation of a distinct signaling complex that does notincrease pMad.Instead,our data support competition betweencollagen IV and laminin for integrin binding,suggesting that therelative levels of laminin,collagen IV,and integrins in a particulardevelopmental context will impact the extent of BMP pathwayactivation.Mechanism of Integrin-Enhanced BMP Signal TransductionOur data indicate that collagen IV/integrin signaling in the earlyembryo promotes activation of canonical Smad-dependent sig-nal transduction in a mechanism that is independent of FAKbut may involve an association of integrins and BMP recep-tors.Several recent studies have also reported interactionsbetween integrins and BMP receptors,leading to inhibition ofSmad phosphorylation(North et al.,2015)or enhanced Smadphosphorylation either via a BMP-ligand-independent,shear-stress-induced activation of FAK/ERK MAPK signaling(Zhouet al.,2013)or via extracellular domain interactions that increasethe ligand binding affinity of the BMP receptor(Tian et al.,2012).Our data show that collagen IV/integrin signaling enhancespMad levels via a distinct mechanism,as it is independent ofFAK and involves intracellular domain interactions downstreamof BMP receptor activation.We identify two conserved NPXY motifs in the b PS cyto-plasmic domain as important sites for integrin-BMP synergy,but these motifs are not required for b PS binding to Tkv,suggesting that binding of integrins to BMP receptors is notsufficient for promoting Mad phosphorylation.One possibilityis that the NPXY motifs are required for the recruitment of factorsthat facilitate or stabilize Mad phosphorylation.NPXY motifs arealso involved in regulating the endocytosis and recycling of in-tegrin receptors(Margadant et al.,2012).As some evidence sug-gests that Smad phosphorylation by BMP receptors occurspreferentially on endosomes(Shi et al.,2007),integrin-facilitatedendocytosis and/or recycling of BMP receptors could enhanceMad phosphorylation.Roles of a PS1/mew and a PS3/scb in Integrin-Mediated Enhancement of BMP SignalingPreviously,integrins have been implicated in regulating Sog dis-tribution in ovarian follicle cells and the pupal wing(Araujo et al.,2003;Negreiros et al.,2010).Although the low penetrance sogmutant-like phenotype we observed in mew mutant embryosis also consistent with a function of mew/a PS1in modulatingSog levels(Figure5B),the major role of integrins in the earlyembryo appears to involve their signaling function,as we canrescue the integrin-null phenotype with the Torso D b PS cyt signaling-activated transgene.Consistent with this,our RNAiknockdown data suggest that integrin signaling through both a PS1and a PS3can promote Tkv-mediated Mad phosphoryla-tion and both a PS1and a PS3bind Tkv.In the early embryo,Cell Reports12,1584–1593,September8,2015ª2015The Authors1589。