No abstract

Aluminium, cadmium and lead concentrations in the spermatozoa and seminal plasma of 27 employees of two industrial companies, a refinery and a polyolefin factory, and 45 consecutive sperm donor candidates at a sperm bank were studied using atomic absorption measurements. The relationship between metal concentration and parameters of semen analysis was studied. A high concentration of aluminium in spermatozoa was correlated with decreased sperm motility. The concentrations of cadmium and lead were low and did not show any correlation with parameters of semen analysis. Aluminium may be one of the environmental pollutants causing impaired semen quality. The mean sperm concentrations were similar in the factory employees (96 x 10(6)/ml), in the sperm donor candidates of the comparison group (104 x 10(6)/ml) and in 352 donor candidates at the sperm bank of the Family Federation of Finland (107 x 10(6)/ml) between May 1993 and May 1995.

We evaluated total and inorganic arsenic levels in long grain rice and rice based baby foods on Finnish market. Inorganic arsenic was analysed with an HPLC-ICP-MS system. The total arsenic concentration was determined with an ICP-MS method. In this study, the inorganic arsenic levels in long grain rice varied from 0.09 to 0.28mg/kg (n=8) and the total arsenic levels from 0.11 to 0.65mg/kg. There was a good correlation between the total and inorganic arsenic levels in long grain rice at a confidence level of 95%. The total arsenic levels of rice-based baby foods were in the range 0.02 - 0.29mg/kg (n=10), however, the level of inorganic arsenic could only be quantitated in four samples, on average they were 0.11mg/kg. Our estimation of inorganic arsenic intake from long grain rice and rice-based baby food in Finland indicate that in every age group the intake is close to the lowest BMDL0.1 value 0.3μg/kg bw/day set by EFSA. According to our data, the intake of inorganic arsenic should be more extensively evaluated.

The white-tailed eagle (Haliaeetus albicilla) suffered a severe population decline due to environmental pollutants in the Baltic Sea area ca. 50 years ago but has since been recovering. The main threats for the white-tailed eagle in Finland are now often related to human activities. We examined the human impact on the white-tailed eagle by determining mortality factors of 123 carcasses collected during 2000-2014. Routine necropsy with chemical analyses for lead and mercury were done on all carcasses. We found human-related factors accounting for 60% of the causes of death. The most important of these was lead poisoning (31% of all cases) followed by human-related accidents (e.g. electric power lines and traffic) (24%). The temporal and regional patterns of occurrence of lead poisonings suggested spent lead ammunition as the source. Lead shot was found in the gizzards of some lead-poisoned birds. Scavenging behaviour exposes the white-tailed eagle to lead from spent ammunition.

The lead, cadmium and mercury concentrations in muscle, liver and kidney from Finnish pigs and cattle were determined. The average wet weight lead concentrations in pig muscle, liver and kidney were 15 micrograms/kg, 38 micrograms/kg and 40 micrograms/kg, respectively. The corresponding concentrations for cattle were 13 micrograms/kg, 57 micrograms/kg and 110 micrograms/kg. The average wet weight cadmium concentrations were 1.5 micrograms/kg, 28 micrograms/kg and 170 micrograms/kg (pigs) and 1.3 micrograms/kg, 61 micrograms/kg and 350 micrograms/kg (cattle). The corresponding mercury concentrations were 11 micrograms/kg, 12 micrograms/kg and 14 micrograms/kg (pigs) and 11 micrograms/kg, 12 micrograms/kg and 15 micrograms/kg (cattle). The average concentrations were at or above the detection limit of the metal in question. According to the results obtained by the National Veterinary Institute, the cadmium concentration in pigs and cattle has decreased during the period 1973-1988. The provisional tolerable daily intake of lead/person (60 kg), recommended by GEMS/Food, is 0.43 mg. According to the results for lead levels in these products in Finland, a daily intake of 29 kg pig muscle, 33 kg cattle muscle, 11 kg pig liver, 8 kg cattle liver, 11 kg pig kidney or 4 kg cattle kidney would be required to reach this norm. The corresponding provisional tolerable daily intake of cadmium/person (60 kg) is 0.06 mg and is equivalent to 40 kg pig muscle, 46 kg cattle muscle, 2 kg pig liver, 1 kg cattle liver, 0.4 kg pig kidney and 0.2 kg cattle kidney. The validity of the methods was tested four times a year using spiked check samples.