ABSTRACT
Nitrogen (N) deposition has important negative impacts on natural and semi-natural ecosystems, impacting on biotic interactions across trophic levels. Low-nutrient systems are particularly sensitive to changes in N inputs and are therefore more vulnerable to N deposition. Carnivorous plants are often part of these ecosystems partly because of the additional nutrients obtained from prey. We studied the impact of N deposition on the nutrition of the carnivorous plant Drosera rotundifolia growing on 16 ombrotrophic bogs across Europe. We measured tissue N, phosphorus (P) and potassium (K) concentrations and prey and root N uptake using a natural abundance stable isotope approach. Our aim was to test the impact of N deposition on D. rotundifolia prey and root N uptake, and nutrient stoichiometry. D. rotundifolia root N uptake was strongly affected by N deposition, possibly resulting in reduced N limitation. The contribution of prey N to the N contained in D. rotundifolia ranged from 20 to 60%. N deposition reduced the maximum amount of N derived from prey, but this varied below this maximum. D. rotundifolia tissue N concentrations were a product of both root N availability and prey N uptake. Increased prey N uptake was correlated with increased tissue P concentrations indicating uptake of P from prey. N deposition therefore reduced the strength of a carnivorous plant-prey interaction, resulting in a reduction in nutrient transfer between trophic levels. We suggest that N deposition has a negative impact on D. rotundifolia and that responses to N deposition might be strongly site specific.
Subject(s)
Drosera/physiology , Nitrogen/analysis , Phosphorus/analysis , Wetlands , Drosera/chemistry , Ecosystem , Plant LeavesABSTRACT
⢠Carnivory in plants is presumed to be an adaptation to a low-nutrient environment. Nitrogen (N) from carnivory is expected to become a less important component of the N budget as root N availability increases. ⢠Here, we investigated the uptake of N via roots versus prey of the carnivorous plant Drosera rotundifolia growing in ombrotrophic bogs along a latitudinal N deposition gradient through Sweden, using a natural abundance stable isotope mass balance technique. ⢠Drosera rotundifolia plants receiving the lowest level of N deposition obtained a greater proportion of N from prey (57%) than did plants on bogs with higher N deposition (22% at intermediate and 33% at the highest deposition). When adjusted for differences in plant mass, this pattern was also present when considering total prey N uptake (66, 26 and 26 µg prey N per plant at the low, intermediate and high N deposition sites, respectively). The pattern of mass-adjusted root N uptake was opposite to this (47, 75 and 86 µg N per plant). ⢠Drosera rotundifolia plants in this study switched from reliance on prey N to reliance on root-derived N as a result of increasing N availability from atmospheric N deposition.
Subject(s)
Carnivory , Drosera/physiology , Nitrogen , Animals , Atmosphere , Nitrogen/pharmacokinetics , Nitrogen Isotopes , Plant Roots/metabolism , Predatory Behavior , Sweden , WetlandsABSTRACT
Artemia salina has, for the first time, been used as test organism for acute toxicity of leachate water from three landfills (the municipal landfills at Kristianstad, Sweden and Siauliai, Lithuania, and an industrial landfill at Stena fragmenting AB, Halmstad, as well as for leachate from Kristianstad treated in different ways in a pilot plan). Artemia can tolerate the high concentrations of chloride ions found in such waters. Large differences in toxicities were found, the leachate from Siauliai being the most toxic one. To increase the selectivity in the measurements, a fractionation was done by using ion exchange to separate ammonium/ammonia and metal ions from the leachate, and activated carbon adsorbents for organic pollutants. The influence of some metals and phenol compounds on the toxicity was investigated separately. It was found that most of the toxicity emanated from the ammonium/ammonia components in the leachate. However, there was also a significant contribution n from organic pollutants, other than phenol compounds, since separate experiments had in this latter case indicated negligible impact. The concentrations of metals were at a level, shown by separate experiments, where only small contribution to the toxicity could be expected.
Subject(s)
Artemia/drug effects , Refuse Disposal , Toxicity Tests, Acute , Water Movements , Water Pollutants, Chemical/toxicity , Ammonia/analysis , Ammonia/toxicity , Animals , Artemia/physiology , Copper/analysis , Copper/toxicity , Larva/drug effects , Larva/physiology , Lead/analysis , Lead/toxicity , Movement/drug effects , Phenols/analysis , Phenols/toxicity , Quaternary Ammonium Compounds/analysis , Quaternary Ammonium Compounds/toxicity , Water Pollutants, Chemical/analysis , Zinc/analysis , Zinc/toxicityABSTRACT
The hypothesis that carnivorous plants are less responsive to prey at high soil nutrient levels than at lower levels (Givnish et al. 1984) is tested on four plant species (Drosera rotundifolia, Pinguicula alpina, P. villosa and P. vulgaris) from a subarctic environment. The response, measured in terms of seven characteristics (winter bud weight, winter bud nitrogen and phosphorus content, flowering frequency, total seed weight, seed number and weight per seed), was analysed. Although all species responded to prey supply the response varied depending on the characteristic and species concerned. In 5 cases (out of 28 tests) the hypothesis was supported, whereas in 1 case it was refuted, i.e. the response to prey was higher for plants supplied with soil nutrients. In the remaining three-quarters of the tests, responses to prey were not significantly different between the two nutrient levels. Thus, the hypothesis that the response to prey diminishes as soil nutrient availability increases was not supported by our findings. A modification of the model presented by Givnish et al. (1984) is therefore suggested. This modified model measures the cost of carnivory as loss in growth rate and assumes that responses to prey remain unchanged as the soil nutrient content increases. Although the distribution of carnivorous plants is still predicted to be limited mainly to wet and sunny but nutrient-poor sites, the modified model also allows for their occurrence in richer habitats, provided competition is low.
ABSTRACT
The first recorded cases of the recent epizootic were harbour seals observed at the Danish island of Anholt, 12 April 1988. The disease then spread throughout the sea waters of north-western Europe. The total mortality in Europe up to November 1988, was estimated to be at least 17,000 seals. The mortality rate in Danish-Swedish waters was about 60%. Autopsies including sampling for histology of most organs were performed on 37 harbour seals and 12 grey seals, collected mainly at the Swedish west coast and in the southern Baltic. In most of the harbour seals and in three of the grey seals we found histological changes in the upper and lower respiratory tracts, in the lower urinary tract and in the lymphatic system consistent with those diagnostic of distemper viral infection in the canine. These diagnostic criteria were: presence of intracytoplasmic eosinophilic inclusion bodies of epithelial cells of the trachea and the urinary bladder, interstitial pneumonia, and atrophy of lymphatic organs due to depletion of lymphocytes. Our findings in pathology of a canine distemper-like disease in the seals were presented in late August 1988, together with the Dutch findings in virology by Dr. Osterhaus and collaborators.