Diet and foraging behaviour of the semi-aquatic Varanus mertensi (Reptilia : Varanidae), Wildlife Research 32(1):67 74 | doi 10.1071/WR04040 [free] Beata Ujvari, Hee-chang Mun, Arthur D. Conigrave, Alessandra Bray, Jens Osterkamp, Petter Halling and Thomas Madsen (2013).
Finally, a WG on engineered nanoparticles (ENP) was officially established in October 2011 to address: 1) behaviour of ENPs in the aquatic environment (wastewater, storm water, surface water and sediment); 2) their effects on aquatic ecosystems and 3) analytical methods.
The first thoroughly experimented studies regard the health effects of airborne nanoparticles [ 8], while very few is known about the behaviour of nanoparticles in the aquatic medium, so that no databases are presently available about their presence in the aquatic environment.
So far, little is known about the occurrence and the behaviour of ENP in environmental aquatic systems.
In general, however, very little information is available on the temporal, spatial and diurnal behaviour of antibiotics in the aquatic environment.
The occurrence, fate and behaviour of carbon nanomaterials in the aquatic environment are dominated by their functionalization, association with organic material and aggregation behaviour.
The method described will also open the door to obtain reliable data on the occurrence and the behaviour of other ENP in environmental aquatic systems.
Adsorption of natural organic matter, aggregation and disaggregation have been identified as three of the main processes affecting the fate and behaviour of engineered nanoparticles (ENPs) in aquatic environments.
Water temperature greatly influences the physiology and behaviour of teleost fish as other aquatic organisms.
In some crustaceans, increased release of urine occurs during aggressive interactions between males [ 50- 52], suggesting that linking urine signals to aggressive behaviour may have evolved independently in different taxa of aquatic animals.
