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F A de Haan

Publications and source records attributed to F A de Haan.

6 recordsLinked to original sources

Cu accumulation in Lumbricus rubellus under laboratory conditions compared with accumulation under field conditions.

Experiments were performed to determine Cu accumulation in earthworms under laboratory conditions using soil from a Cu-contaminated site, followed by field experiments in this contaminated site. The aims of the laboratory experiments were (a) to determine Cu accumulation rate, (b) to determine the effect of soil Cu content on the steady-state concentration, and (c) to evaluate the effect of soil moisture on accumulation. The field experiments were performed to evaluate the use of accumulation data obtained from laboratory experiments for prediction of accumulation under field conditions. In the laboratory experiment, earthworms (Lumbricus rubellus) were introduced into four homogeneously mixed Cu-contaminated soils and a reference soil. The total extractable Cu content in the soil (Cu(T)) varied from 10 to 130 mg kg-1, soil pH varied from 4.0 to 5.0, and soil moisture content was set to approximately 25, 35, and 45% of the dry weight for each treatment. The tissue Cu concentration (Cuw) was determined by sampling earthworms after 1, 7, 14, 28, and 56 days. In the field experiment, 500 earthworms were introduced at four different Cu-contaminated locations at a contaminated arable field. After 14, 28, and 70 days, earthworms were sampled to determine Cuw. In both experiments, soil Cu contents significantly affected Cuw. Soil moisture only significantly affected Cu accumulation for the wettest soil. Under laboratory conditions, a steady state did not seem to be achieved after 56 days; the Cu accumulation can be described by the toxicokinetic one-compartment model. The field experiment was considerably affected by variation in soil temperature resulting in significant fluctuations in tissue Cu concentrations. The tissue Cu accumulation was significantly correlated to the CuT, which is in agreement with the results from the laboratory experiments. Variance of Cuw at Day 14 in earthworms from the field experiments was significantly larger than in the worms from the laboratory experiment. At Day 28, the differences were not significant.

Analysis of Variance↗

Effect of Cd or Pb addition to Cu-contaminated soil on tissue Cu accumulation in the earthworm, Dendrobaena veneta.

Generally, soil heavy metal contamination consists of a mixture of heavy metals. Soil chemical properties and interaction with other pollutants in soil affect the external heavy metal bioavailability. Moreover, interaction with other pollutants accumulated in organisms may change the toxicity of each pollutant. Therefore, the hypotheses was tested that addition of Cd or Pb to Cu-contaminated soil would lead to an increase in tissue Cu accumulation in the earthworm, Dendrobaena veneta, caused by (i) induction of metallothionein by Cd, or (ii) an increase in Cu concentration in soil solution due to the exchange of adsorbed Cu for Pb. Tissue heavy metal concentrations were determined after exposure in contaminated soils for 3 or 21 days. Considerable amounts of Cu, Cd, and Pb were accumulated, indicating that these heavy metals were available for uptake by D. veneta. Both Cd and Pb, however, did not significantly affect tissue Cu accumulation.

Animals↗

Cu accumulation in the earthworm Dendrobaena veneta in a heavy metal (Cu, Pb, Zn) contaminated site compared to Cu accumulation in laboratory experiments.

Earthworms (Dendrobaena veneta) were exposed to heavy metal contaminated soil from a field site under both laboratory and field conditions. In the laboratory study, D. veneta were analysed for Cu after 2 weeks' exposure. The tissue Cu concentration (Cu(W)) increased proportionally with the total extractable soil Cu content (Cu(T)) in soils that contained less than 150 mg Cu kg(-1). In D. veneta exposed to soils containing more than Cu(T) = 150 mg kg(-1), however, we observed no further increase in Cu(W). In a 64-m(2) field plot at a contaminated site, 81 soil samples were taken and analysed for Cu, Pb, Zn and pH. In June 1994, 1000 D. veneta were homogeneously distributed in the plot and sampled after 1, 2 and 5 weeks to analyse for Cu. Additionally, 2000 D. veneta were introduced in September 1994 and sampled after 1, 2 and 4 weeks. At locations where earthworms were removed, the soil Cu content was estimated by disjunctive kriging. Cu concentration factors (ratio of Cu(W) to Cu(T)) in the field experiment were in excellent agreement with those of the laboratory experiment. This indicates that, with a sufficiently high sampling density, it may be feasible to predict earthworm Cu accumulation in the field using a concentration factor determined in the laboratory.

Journal Article↗

Soil quality in relation to soil pollution.

In comparison with the environmental compartments air and water, soil is an extremely complicated system, because properties of the soil and chemical, physical and biological characteristics vary greatly between different soil systems. This makes the development of general rules for quantitative evaluation of soil quality impossible. The large variation between the buffering capacities of various soils for different compounds also complicates the question. In The Netherlands, a system of reference values for various compounds has been developed, these reference values reflect situations in which there is a low degree of contamination. For heavy metals, these reference values consist of sliding scales incorporating the influence of a soil's clay and organic matter content. Examples for derivation of effect-based soil quality standards are briefly described.

Biological Availability↗