Abstract As a widely spread cyprinid fish species, the European chub ( Leuciscus cephalus ) has been used extensively in bio‐monitoring programs. However, no laboratory dose‐response and/or time course studies related to applied biomarkers have been reported on chub yet. In order to address this issue, specimens of juvenile chub caught in September 2005 in the Sava River, Croatia, were laboratory exposed to various (0.25–50 mg/kg) doses of either model polycyclic aromatic hydrocarbons (PAH) premutagen benzo[ a ]pyrene (B a P), or β‐naphthoflavone (β‐NF), a well‐known model cytochrome 1A (CYP1A) inducer, for 3 (B a P) or 5 d (β‐NF). The responses of several hepatic biomarkers were determined in the exposed fish: The hepatic 7‐ethoxyresorufin‐O‐deethylase activity, CYP1A content, glutathione S ‐transferase (GST) activity, liver bioactivation potential, and the amount of hydroxylated polycyclic aromatic hydrocarbon bile metabolites determined by the fixed wavelength fluorescence and the high‐performance liquid chromatography technique. The relevance of determined biomarker responses has been analyzed further and crosscorrelated with the same set of biomarkers, as well as with tissue concentrations of polycyclic aromatic hydrocarbons and polychlorinated biphenyls, determined in chub specimens collected in September 2005 at five different polluted locations along the Sava River. The species‐specific upper and lower limits in responses of studied biomarkers were determined and the obtained ranges successfully evaluated in real field situation. With the exception of the GST activity, all other biomarkers determined in chub proved to be valuable indicators of environmental pollution. Finally, the results of the present study demonstrated that the same strategy of laboratory characterization in combination with field evaluation should be used regularly in the selection of optimal biomarkers and indicator species.
Hrvatska je bogata vodom, ali zbog nedostatka postrojenja za njeno prociscavanje velike kolicine otpadnih voda iz gradova i industrijskih postrojenja uzrokuju degradaciju njene kakvoce. Sprecavanje gubitka naseg prirodnog bogatstva iziskuje razvoj i uspostavu specificnih monitoring programa za procjenu zdravlja bioloske komponente i kakvoce voda. Glavni cilj CROWAT je, suradnjom hrvatskih i norveskih istraživaca osmisliti, razviti i uspostaviti biomonitoring hrvatskih kopnenih voda i mora. U ovom interdisciplinarnom projektu upotrebljavaju se vecinom bioloske metode koje odražavaju promjene u organizmima uzrokovane djelovanjem oneciscivaca - biomarkere. Biomarkeri, kao mjera izlaganja oneciscenju i njegovog ucinka su od posebnog znacaja jer reagiraju samo na bioloski raspoložive koncentracije oneciscivaca i pružaju mogucnost rane detekcije promjena uzrokovanih oneciscenjem. Tijekom prve godine projekta (2002) za nasa istraživanja analizirali smo prirodne populacije organizama (skoljkase i ribe) kao i jedinke izlagane u kavezima. Istraživanja su provedena na tri postaje na Srednjem Jadranu (Kastelanski zaljev) i tri postaje u Istocnoj Slavoniji (rijeke Drava i Dunav). Ovaj projekt ukljucuje mjerenje slijedecih biomarkera: koncentracije metalotioneina, aktivnosti etoksirezorufin-O-deetilaze (EROD), aktivnosti benzo(a)piren monooksigenaze (BaPMO), aktivnosti acetilkolinesteraze (AChE), aktivnosti mehanizma multiksenobioticke otpornosti (MXR), koncentracije glutationa (GSH), koncentracije vitelogenina, ostecenja DNA (komet-test i mikronukleus-test), koncentracije policiklickih aromatskih ugljikovodika i njihovih metabolita, energetskog statusa organizama i destabilizacije lizosomalne membrane. Ovaj projekt (br. 150-463) financiran je od strane Norweigan Research Council-a.
Abstract Chloride/formate exchanger (CFEX; SLC26A6) mediates oxalate transport in various mammalian organs. Studies in Cfex knockout mice indicated its possible role in development of male-dominant hyperoxaluria and oxalate urolithiasis. Rats provide an important model for studying this pathophysiological condition, but data on Cfex (rCfex) localisation and regulation in their organs are limited. Here we applied the RT-PCR and immunochemical methods to investigate rCfex mRNA and protein expression and regulation by sex hormones in the pancreas, small intestine, liver, and kidneys from intact prepubertal and adult as well as gonadectomised adult rats treated with sex hormones. rCfex cDNA-transfected HEK293 cells were used to confirm the specificity of the commercial anti-CFEX antibody. Various biochemical parameters were measured in 24-h urine collected in metabolic cages. rCfex mRNA and related protein expression varied in all tested organs. Sex-independent expression of the rCfex protein was detected in pancreatic intercalated ducts (apical domain), small intestinal enterocytes (brush-border membrane; duodenum > jejunum > ileum), and hepatocytes (canalicular membrane). In kidneys, the rCfex protein was immunolocalised to the proximal tubule brush-border with segment-specific pattern (S1=S2<S3), and both rCfex mRNA and protein expression exhibited male-dominant sex differences driven by stimulatory effects of androgens after puberty. However, urinary oxalate excretion was unrelated to renal rCfex protein expression. While the effect of male-dominant expression of rCfex in renal proximal tubules on urine oxalate excretion remains unknown, its expression in the hepatocyte canalicular membrane may be a pathway of oxalate elimination via bile.