TEMPERATURE EFFECTS ON BIOCONCENTRATION OF DDE BY DAPHNIA

Authors
Citation
S. Nawaz et Kl. Kirk, TEMPERATURE EFFECTS ON BIOCONCENTRATION OF DDE BY DAPHNIA, Freshwater Biology, 35(1), 1996, pp. 173-178
Citations number
27
Categorie Soggetti
Zoology,"Marine & Freshwater Biology
Journal title
ISSN journal
00465070
Volume
35
Issue
1
Year of publication
1996
Pages
173 - 178
Database
ISI
SICI code
0046-5070(1996)35:1<173:TEOBOD>2.0.ZU;2-H
Abstract
1. Lake temperatures vary with season, latitude, elevation and as a re sult of thermal pollution. Ln addition, lake temperatures may increase with global warming. Radiotracer experiments were conducted to determ ine the effects of temperature on the bioaccumulation of lipophilic or ganic contaminants by zooplankton. Daphnia pulex were exposed to C-14- labelled DDE, a stable metabolite of the organochlorine pesticide DDT, in particle-free water for 24 h. An increase in temperature from 5 to 25 degrees C resulted in a 314% increase in bioconcentration factor ( the ratio of contaminant concentration in the organism to contaminant concentration in the water). 2. To mimic the fluctuating temperatures experienced by zooplankton during diel vertical migration, we conducte d experiments in which animals were exposed to 25 degrees C for 12 h i n the light, then 15 degrees C for 12 h in the dark. Exposure to this fluctuating temperature regime for 48h resulted in a 27-33% increase i n bioconcentration factor relative to a constant 20 degrees C control. 3. Live animals accumulated more than twice the amount of DDE than fr eshly killed animals, indicating that the activity of the organism is important in bioconcentration. This finding sheds light on the possibl e mechanisms for the increase in bioconcentration at higher constant t emperatures. Daphnia pump more water through their branchial chambers at higher temperatures. Thus, if the thoracic limbs are an important s ite of contaminant uptake, then animals are exposed to more contaminan t molecules at higher temperatures. Other possible mechanisms include changes in the thickness of the diffusive boundary layer and changes i n cell membrane permeability.