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Environment intertidal

Bauer, J.E. and O.G. Capone. 1985. Degradation and mineralization of the polycyclic aromatic hydrocarbons anthracene and naphthalene in intertidal marine sediments. Appl. Environ. Microbiol. 50 81-90. [Pg.1396]

Collen J, Davison IR (1999c) Stress tolerance and reactive oxygen metabolism in the intertidal red seaweeds Mastocarpus stellatus and Chondrus crispus. Plant Cell Environ 22 1143-1151 Collen J, Pedersen M, Bornman CH (1994) A stress-induced oxidative burst in Eucheuma platycladum (Rhodophyta). Physiol Plant 92 417 122 Collen J, Roeder V, Rousvoal S, Collin O, Kloareg B, Boyen C (2006a) An expressed sequence tag analysis of thallus and regenerating protoplasts of Chondrus crispus (Gigartinales, Rhodophyceae). J Phycol 42 104-112... [Pg.265]

Johnson, B.T. Petty, J.D. Huckins, J.N. Lee, K. 2004, Hazard assessment of simulated oil spill on intertidal areas of the St. Lawrence River with SPMD-TOX. Environ. Toxicol 19 329-335. [Pg.136]

Short,]. W. Maselko, J. M. Llndeberg, M. R. Harris, P. M. Rice, S. D. Vertical Distribution and Probability of Encountering Intertidal Exxon Valdez Oil on Shorelines of Three Embayments within Prince William Sound, Alaska. Environ. Sci. Technol. 2006, 40, 3723-3729. [Pg.680]

Aston, S.R. and Stanners, DA. (1981) Observations on the deposition, mobility and chemical associations of plutonium in intertidal sediments. In Techniques for Identifying Transuranic Speciation in Aquatic Environments. IAEA, Vienna, pp. 209-218. [Pg.382]

One such difficulty is that, while it appears that [Sn2 ] levels may be as high as 400 /iM in some hypoxic environments, the precise number (n) of sulfur atoms in these polysulfide species, or even the range of n, is uncertain. Bouleague (16) discusses some of the thermodynamic equilibrium calculations which may be used to estimate the distribution of s[Sn2 ] among the various polysulfide species. Another difficulty with these data is that the structures of the thiols (RSH) detected are not well known. Mopper and Taylor (14) identified 13 different thiols in slurries of intertidal sediments from Biscayne Bay (FL), and found at least 20 more thiols whose structures could not be determined. Their observations (Table III) indicate that thiols encountered in natural waters will probably exhibit a broad variety of structures in any one location, but that a relatively small number of compounds may dominate the mixture. [Pg.103]

Bertness, M.D. and Leonard, G.H., The role of positive interactions in communities lessons from intertidal environments, Ecology, 78, 1976, 1997. [Pg.188]

Many intertidal and shallow subtidal habitats are highly variable over space or time. Consequently, the concentrations of chemical defenses that are appropriate at one place or time may be inappropriate at another. A strategy for dealing with this variability is the detection of an environmental cue that can be correlated with an appropriate level of defense for that environment at that time. One of the best examples of environmental cues causing changes in chemical defense concentrations are herbivore-induced defenses in which chemical levels are increased in response to an attack by a consumer.136 137 Induced defenses require that herbivory be variable and unpredictable, that the inducing cues produce effective increases in defenses, and that the induction is cost-effective and rapid enough to deter further consumption.140... [Pg.315]

A smaller percentage of the Phaeophyta (59% of taxa) contain MAAs and concentrations in thalli are relatively low (<300 nmol mg-1 protein). The Phaeophyta also excrete colored compounds with UV-absorbing properties.62 Some of these exudates are polyphenolic substances that are usually associated with alleopathy. However, in Ascophyllum nodosum, thallus concentrations are regulated by UV exposure and small herbivores are not deterred, rather they feed preferentially on irradiated algae.59 Since the Chlorophyta and Phaeophyta successfully inhabit intertidal and shallow subtidal areas, they have apparently evolved very efficient protective and repair mechanisms for dealing with UV exposure, but MAAs are probably not the key to their fitness in high light environments. [Pg.492]

Wilcock, R.J., Smith, T.J., Pridmore, R.D., Thrush, S.F., Cummings, V.J., Hewitt, J.E. (1993) Bioaccumulation and elimination of chlordane by selected intertidal benthic fauna. Environ. Toxicol. Chem. 12, 733-742. [Pg.833]

Fig. 6 Macromolecules are readily encapsulated in lipid vesicles in a single cycle of dehydration-hydration [53]. Such wetting-drying cycles would have commonly occurred in the prebiotic environment at intertidal zones... Fig. 6 Macromolecules are readily encapsulated in lipid vesicles in a single cycle of dehydration-hydration [53]. Such wetting-drying cycles would have commonly occurred in the prebiotic environment at intertidal zones...
Mountfort, D.O., Asher, R.A., Mays, E.L., and Tiedje, J.M. (1980) Carbon and electron flow in mud and sandflat intertidal sediments at Delaware Inlet, Nelson, New Zealand. Appl. Environ. Microbiol. 39, 686-694. [Pg.634]

S. A. Baldwin, W. A. Maher, Spatial and temporal variation of selenium concentration in five species of intertidal molluscs from Jervis bay, Australia, Mar. Environ. Res., 44 (1997), 243-262. [Pg.660]

Ward, B. B., and Cockroft, A. R. (1993). Immunofluorescence detection of the denitrifying strain Pseudomonas stutzeri (ATCC 14405) in seawater and intertidal sediment environments. Microb. Ecol. 25, 233-246. [Pg.1343]

Young, E. B., Dring, M. J., Savidge, G., Birkett, D. A., and Berges, J. A. (2007a). Seasonal variations in nitrate reductase activity and internal N pools in intertidal brown algae are correlated with ambient nitrate concentrations. Plant Cell Environ. 30, 764—774. [Pg.1443]


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See also in sourсe #XX -- [ Pg.73 , Pg.115 ]




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