Hostname: page-component-78c5997874-ndw9j Total loading time: 0 Render date: 2024-11-13T07:01:58.667Z Has data issue: false hasContentIssue false

Lead concentrations in Hymenolepis diminuta adults and Taenia taeniaeformis larvae compared to their rat hosts (Rattus norvegicus) sampled from the city of Cairo, Egypt

Published online by Cambridge University Press:  17 October 2003

B. SURES
Affiliation:
Zoological Institute, Parasitology–Ecology, University of Karlsruhe, Geb. 07.01, D-76128, Karlsruhe, Germany
T. SCHEIBLE
Affiliation:
Zoological Institute, Parasitology–Ecology, University of Karlsruhe, Geb. 07.01, D-76128, Karlsruhe, Germany
A. R. BASHTAR
Affiliation:
Zoology Department, Faculty of Science, University of Cairo, Cairo, Egypt Present address: Zoology Department, College of Science, King Saud University, Riyadh, Saudi Arabia.
H. TARASCHEWSKI
Affiliation:
Zoological Institute, Parasitology–Ecology, University of Karlsruhe, Geb. 07.01, D-76128, Karlsruhe, Germany

Abstract

Concentrations of lead, determined by electrothermal atomic absorption spectrometry, were compared between the cestodes Hymenolepis diminuta and Taenia taeniaeformis and its host rat (Rattus norvegicus). Rats were sampled at 2 sites, which differed in respect to lead pollution as quantified from road dust, adjacent to the city of Cairo, Egypt. Comparing lead levels among host tissues and the parasites the significantly highest accumulation was found in H. diminuta, followed by rat kidney and larvae of T. taeniaeformis. Calculation of bioconcentration factors showed that H. diminuta contained 36-, 29-, 6- and 6-fold higher lead levels than intestinal wall, liver, kidney and larvae of T. taeniaeformis, at the more polluted site. At the less contaminated site lead bioconcentration factors for H. diminuta were found to be 87, 87 and 11 referred to intestine, liver and kidney of the host. Due to a high variability of the lead concentrations in H. diminuta it was not possible to indicate differences in metal pollution between both sampling sites. This variability may be influenced by different age structures of cestode infrapopulations. It is likely that younger worms contain lower metal levels than older worms due to a shorter exposure period. Thus, it is necessary to standardize the sampling of worms which should be used for indication purposes. Due to a lack of adequate sentinel species in terrestrial habitats more studies are required to validate and standardize the use of helminths as accumulation bioindicators in order to obtain mean values with low standard deviations. The host–parasite system rat–H. diminuta appears to be a useful and promising bioindication system at least for lead in urban ecosystems as rats as well as the tapeworm are globally distributed and easily accessible.

Type
Research Article
Copyright
2003 Cambridge University Press

Access options

Get access to the full version of this content by using one of the access options below. (Log in options will check for institutional or personal access. Content may require purchase if you do not have access.)

References

REFERENCES

BARUš, V., TENORA, F. & KRÁČMAR, S. (2000). Heavy metal (Pb, Cd) concentrations in adult tapeworms (Cestoda) parasitizing birds (Aves). Helminthologia 37, 131136.Google Scholar
BEEBY, A. (2001). What do sentinels stand for? Environmental Pollution 112, 285298.Google Scholar
DIN 19730, Ausgabe: 1997–06. Bodenbeschaffenheit – Extraktion von Spurenelementen mit Ammoniumnitratlösung.
FAULKNER, B. C. & LOCHMILLER, R. L. (2000). Ecotoxicity revealed in parasite communities of Sigmodon hispidus in terrestrial environments contaminated with petrochemicals. Environmental Pollution 110, 135145.CrossRefGoogle Scholar
GUNKEL, G. (1994). Bioindikation in aquatischen Ökosystemen. Gustav Fischer Verlag, Jena, Stuttgart.
KRAMAR, U. (1997). Advances in energy-dispersive X-ray fluorescence. Journal of Geochemical Exploration 58, 7380.CrossRefGoogle Scholar
MERIAN, E. (1991). Metals and their Compounds in Environment and Life. Occurence, Analysis and Biological Relevance. Verlag Chemie Weinheim, New York.
RIGGS, M. R., LEMLY, A. D. & ESCH, G. W. (1987). The growth, biomass and fecundity of Bothriocephalus acheilognathi in a North Carolina cooling reservoir. Journal of Parasitology 73, 893900.CrossRefGoogle Scholar
SCHEEF, G., SURES, B. & TARASCHEWSKI, H. (2000). Cadmium accumulation in Moniliformis moniliformis (Acanthocephala) from experimentally infected rats. Parasitology Research 86, 688691.CrossRefGoogle Scholar
SCHUBERT, R. (1991). Bioindikation in terrestrischen Ökosystemen. Fischer Verlag, Jena, Stuttgart.
SIDDALL, R. & SURES, B. (1998). Uptake of lead by Pomphorhynchus laevis cystacanths in Gammarus pulex and immature worms in chub (Leuciscus cephalus). Parasitology Research 84, 573577.CrossRefGoogle Scholar
SMYTH, J. D. (1994). Introduction to Animal Parasitology. Cambridge University Press, Cambridge.
SURES, B. (2001). The use of fish parasites as bioindicators of heavy metals in aquatic ecosystems: a review. Aquatic Ecology 35, 245255.CrossRefGoogle Scholar
SURES, B. (2003). Accumulation of heavy metals by intestinal helminths in fish: an overview and perspective. Parasitology (in the Press).CrossRefGoogle Scholar
SURES, B. & SIDDALL, R. (1999). Pomphorhynchus laevis: the intestinal acanthocephalan as a lead sink for its fish host, chub (Leuciscus cephalus). Experimental Parasitology 93, 6672.CrossRefGoogle Scholar
SURES, B. & TARASCHEWSKI, H. (1995). Cadmium concentrations of two adult acanthocephalans (Pomphorhynchus laevis, Acanthocephalus lucii) compared to their fish hosts and cadmium and lead levels in larvae of A. lucii compared to their crustacean host. Parasitology Research 81, 494497.Google Scholar
SURES, B., FRANKEN, M. & TARASCHEWSKI, H. (2000 a). Element concentrations in the archiacanthocephalan Macracanthorhynchus hirudinaceus compared with those in the porcine host from a slaughterhouse in La Paz, Bolivia. International Journal for Parasitology 30, 10711076.Google Scholar
SURES, B., GRUBE, K. & TARASCHEWSKI, H. (2002). Experimental studies on the lead accumulation in the cestode Hymenolepis diminuta and its final host, Rattus norvegicus. Ecotoxicology 11, 365368.CrossRefGoogle Scholar
SURES, B., JÜRGES, G. & TARASCHEWSKI, H. (2000 b). Accumulation and distribution of lead in the acanthocephalan Moniliformis moniliformis from experimental infected rats. Parasitology 121, 427433.Google Scholar
SURES, B., SIDDALL, R. & TARASCHEWSKI, H. (1999). Parasites as accumulation indicators of heavy metal pollution. Parasitology Today 15, 1621.CrossRefGoogle Scholar
SURES, B., TARASCHEWSKI, H. & HAUG, C. (1995). Determination of trace metals (Cd, Pb) in fish by electrothermal atomic absorption spectrometry after microwave digestion. Analytica Chimica Acta 311, 395399.CrossRefGoogle Scholar
SURES, B., TARASCHEWSKI, H. & ROKICKI, J. (1997). Lead and cadmium content of two cestodes Monobothrium wageneri and Bothriocephalus scorpii, and their fish hosts. Parasitology Research 83, 618623.CrossRefGoogle Scholar
TENORA, F., KRÁČMAR, S., PROKEš, M., BARUš, V. & SITKO, J. (2001). Heavy metal concentrations in tapeworms Diploposthe laevis and Microsomacanthus compressa parasitizing aquatic birds. Helminthologia 38, 6366.Google Scholar