Occurrence and hygienic/allergological relevance of mould from point of view of the environmental medicine.

Allergic skin and respiratory diseases range among the most frequent afflictions in industrialized countries. Due to this fact the importance of indoor mold pollution based on dampness is discussed. In a sentinel health study of the State Health Agency (LGA) children attending of 4th grade of a primary school were tested by an in-vitro allergy screening (UniCap 100/Phadia) for the mold allergens mx1 (Penicillium chrysogenum m1, Cladosporium herbarum m2, Aspergillus fumigatus m3 and Alternaria alternata m6). Primarily about 5% of the children were sensitized against molds which are associated with the ambient air. The investigations showed that most of the children were sensitized against Alternaria alternata and concerning the IgE-concentration (kU/l) Alternaria alternata had the highest concentration among the tested allergens. Commonly children with sensitization against molds were polysensitized. It is unclear if the allergy screening against mold mx1 includes molds with indication for indoor mold pollution such as Acremonium spp., Aspergillus penicillioides, Aspergillus restrictus, Aspergillus versicolor, Chaetomium spp., Phialophora spp., Stachybotrys chartarum, Tritirachium (Engyodontium) album und Trichoderma spp. by means of crossreaction. Therefore, such investigations do not admit any conclusion about health problems as a result of indoor mold pollution. At the present state of knowledge exposure measurements of indoor mold pollutions are not possible, at most a semiquantitative assessment. Although it is generally accepted that dwellings with moisture and mold represent a health risk, knowledge about indoor mold pollution and the related health problems is lacking.

[Respiratory symptoms and sensitization to airborne pollen of ragweed and mugwort of adults in Southwest Germany]. / Atemwegsbeschwerden und Sensibilisierungen gegen Pollen von Ambrosia artemisiifolia und Beifuß bei Erwachsenen in Süd-West-Deutschland.

BACKGROUND AND OBJECTIVE: Allergic diseases of the respiratory tract are common atopic diseases in the population. Pollen of plants are one of their main causes. Pollen of trees, grasses, and weeds like mugwort are of particular importance in this context. The purpose of the present study was to determine the association between typical respiratory symptoms due to pollen allergens and the sensitization to pollen of ragweed and mugwort in adults. METHODS: 1039 participants (18 to 66 years) from Southwest Germany were included in this cross-sectional study. Complains typically for aeroallergens were recorded by questionnaire. In-vitro existing sensitizations were determined for grasses/early bloomer (gx1), trees (tx6), mugwort (w6 and Art-v1) and ragweed (w1 and Amb-a1) by testing for specific IgE-antibodies. RESULTS: In a screening test with a mixed allergen sample (sx1) 36.0 % of the participants showed an aeroallergen sensitization. Consecutive investigations of these 374 positive samples revealed a sensitization to grasses/early bloomer, trees, ragweed (w1), mugwort (w6) and the major allergens ragweed (Amb-a1) and mugwort (Art-v1) in 61.8 %, 54.5 %, 29.9 %, 24.3 %, 1.9 %, and 12.3 %, respectively. This corresponds to 22.2 %, 19.6 %, 10.8 %, 8.7 %, 0.7 % and 4.4 %, respectively, in the whole study population. The participants tested positively stated significantly more disorders. On average, 51.1 % had known hay fever, 65.2 % sneezing without cold and 41.5 % sneezing due to contact with grasses or flowers. In contrast, participants tested negatively stated disorders in only 4.4 %, 32.5 %, and 3.9 %, respectively. CONCLUSION: In Southwest Germany, sensitizations to plant pollen mainly are still caused by grasses, trees, and weeds like mugwort. A sensitization to pollen of ragweed alone is rare until now. However, in case of continuous allergic disorders of the respiratory tract in late summer, a sensitization to ragweed can be important for differential diagnostics.

Decrease of internal exposure to chlororganic compounds and heavy metals in children in Baden-Württemberg between 1996/1997 and 2008/2009.

From 1996/1997 to 2008/2009, blood and urine were sampled from 9- to 11-year-old pupils in the state of Baden-Württemberg, South-West Germany. In blood samples the chlororganics DDE, HCB, PCB-138, PCB-153 and PCB-180 were analysed by gas chromatography and ECD detection. PCDD/PCDF were measured in pooled blood samples using GC/MS. Lead concentrations in blood were quantified by graphite furnace atomic absorption spectrometry (AAS), mercury in urine by using cold vapour AAS. For all chlororganics and heavy metals a distinct decrease of the internal concentration could be shown within the 12-year investigation period. For DDE, the median decreased from 0.32 µg/l to 0.11 µg/l. The median of HCB fell from 0.19 µg/l to 0.07 µg/l. The median of the sum of the three PCB-congeners PCB-138, PCB-153 and PCB-180 decreased from 0.47 µg/l to 0.18 µg/l. The burden of PCDD/PCDF in pooled blood samples resulted in approximately half the concentration after the 12-year period. The internal concentrations of the chlororganics were distinctly higher in breastfed children than in non-breastfed children. In 2008/2009, these differences were strongest for PCB and DDE (2-fold), moderate for PCDD/PCDF (1.6-fold), and slight for HCB (1.2-fold). The median of lead concentrations in blood dropped from 23.6 µg/l to 15.9 µg/l. The median of mercury concentrations in urine decreased from 0.25 µg/l to a value below the limit of quantification of 0.2 µg/l; the 95th percentile was reduced from 3.1 µg/l to less than 0.2 µg/l. The decline of amalgam fillings in children during the investigation period had a strong influence on internal concentrations of mercury. The internal concentration of the persistent xenobiotics investigated here decreased to a low level not likely to be of concern for human health.

Polybrominated diphenyl ethers (PBDE) in blood of children in Baden-Württemberg between 2002/03 and 2008/09.

Polybrominated diphenyl ethers (PBDE) are used in high amounts as flame retardants in plastic materials and textiles. Due to their persistence, their accumulation in the food chain and their toxic properties they have been integrated in the human biomonitoring program of the Baden-Württemberg State Health Office since 2002. In repeated cross-sectional studies in winter 2002/03 (n=162), 2004/05 (n=194), 2005/06 (n=411) and 2008/09 (n=770) blood samples of 9-11-year-old pupils were taken, pooled and analysed for PBDE after extraction and purification by silica gel using HRGC/HRMS. Samples were pooled according to region, gender, and breast feeding. PBDE in the pooled samples ranged from 1.9 to 12.5 ng/g blood fat (sum of all PBDE). Mean concentrations of PBDE, calculated for the four investigation periods, were 6.2 ng/g (2002/03), 5.4 ng/g (2004/05), 7.8 ng/g (2005/06) and 6.7 ng/g (2008/09). While the concentration of the decabrominated diphenyl ether (BDE-209) increased, the concentration of other congeners (BDE-47, BDE-99, BDE-100, BDE-153, BDE-154, BDE-183) decreased slightly or remained at the same level. Consistent differences with respect to gender and breast-feeding were not recognizable. Concentrations of PBDE in children range on the same level as in adults and do not seem to be critical from the toxicological point of view. Because of the slight increase of BDE 209, the internal concentrations of BDE should be monitored in the future. The strong variations in PBDE concentration between the different pooled samples indicate that, apart from ingestion, other routes of exposure (dermal, inhalation) and additional sources (textiles, building materials) must be taken into consideration.

[Sensitization to airborne ragweed pollen--a cause of allergic respiratory diseases in Germany?]. / Sensibilisierung gegen Ambrosiapollen--Eine Ursache für allergische Atemwegserkrankungen in Deutschland?

BACKGROUND AND OBJECTIVE: Allergic skin and respiratory diseases show a high prevalence in most industrial countries. In addition, during the last years ragweed colonization has increased in Europe. Ambrosia pollen ( AMBROSIA ARTEMISIIFOLIA L. - common ragweed) are highly allergenic. Due to the late flowering time (august/September) of ragweed this can result in increasing health threats for allergic populations. This is of particular importance for those who already are sensitive to some grass or tree pollen. These individuals can then suffer from allergies during nearly the whole year. The present study examined the prevalence of sensitization to ragweed in German children and possible health implications. METHODS: Between 2004 and 2007 sera of 1323 10-years old children in Baden Württemberg were tested in-vitro for specific IgE-antibodies against common aeroallergens including ragweed pollen. RESULTS: Specific IgE-antibodies to extracts of common ragweed pollen were present in 10 - 17 % of the tested sera depending on the year of investigation. CONCLUSION: The determined specific IgE-antibodies may be the result of a direct sensitization to ragweed pollen or correspond to cross-reactivity to other plants of the asteraceae subfamily or some nutritional allergens. The detection of sensitization to ragweed pollen does not prove actual allergic disease. However, a ragweed derived allergy should be considered in the differential diagnosis when allergic symptoms are present in direct connection to the flowering-time of ragweed. Ragweed plants should be removed and the spread of the plant 'restricted', as experiences in other countries with already wide spreading show.

No increase in the prevalence of asthma, allergies, and atopic sensitisation among children in Germany: 1992-2001.

BACKGROUND: From 1970 to 1990 increasing rates of asthma and allergic sensitisation were observed in several countries. The aim of this study was to investigate time trends in the prevalence of asthma and allergic sensitisation among school children in Germany between 1992 and 2001. METHODS: Parental reports of asthma, hay fever, and wheezing and measurements of specific serum IgE antibodies were investigated in six serial cross sectional surveys of 9-11 year old school children in three study areas in south west Germany. RESULTS: A total of 6762 school children of mean age 10 years (mean participation rate 77.9%) took part in the investigation in the three study areas. Over the 9 year study period no increase in the prevalence of current wheezing and asthma was observed. In addition, the prevalence of atopic sensitisation remained unchanged during the observation period. CONCLUSIONS: These data, using parental reports and objective measures of allergy, suggest that there has been no further increase in the prevalence of asthma and atopy since 1992. The epidemic may thus have reached a plateau.

[Human biomonitoring investigations of organochlorine compounds -- PCB, DDE, HCB, beta- and gamma-HCH, PCDD/PCDF, Dioxin-like PCB's and polybrominated biphenyl ethers]. / Humanbiomonitoring-Untersuchungen von Organohalogenverbindungen -- PCB, DDE; HCB, beta- und gamma-HCH, PCDD/PCDF, koplanaren PCB sowie polybromierten Biphenylethern.

Although PCB and PCB-containing materials are not processed for a long time, PCB is under discussion again and again caused by the pollution of indoor environments. To objectify the discussion, the dates of the PCB-biomonitoring, the organochlorine-compounds (DDE, HCB, beta-/gamma -HCH, PCDD/PCDF) and the polybrominated biphenyl ethers concerning the investigations within the project "Sentinel Health Departments" in Baden-Wurttemberg are represented. Additionally results from children from Kazakhstan (Aral-Sea area) and from teachers which are working in PCB polluted schools as well as from a long term investigated test person are reported. Blood concentrations of the following compounds decreased from 1996/97 to 2002/03: the sum of the concentration of PCB 138,153 and 180 decreased from 0.46 microg/L to 0.20 microg/L, DDE from 0.32 microg/L to 0.17 microg/, HCB from 0.20 microg/L to 0.08 microg/L, beta-HCH below the level of detection, I-TEQ NATO to 4.8 pg/g blood fat, TEQ WHO (without PCB) to 5.5 pg/g blood fat, PCB 126 to 18,8,pg/g blood fat and PCB 169 to 12.8 pg/g blood fat. The influence of breast feeding and the gender on the level of the pollution is conspicious. No local correlations were found in Baden-Wurttemberg, but they were found in comparison with the results of Kazakhstan (Aral-Sea area). The difficulty to produce time series while the analyzing pollutants are more and more decreasing, as well as the change of the calculation base of the summation of parameters like I-TEQ NATO to TEQ WHO are discussed.

[Molds in air-sampling and detection. Validation of sampling methods to verify molds in air]. / Schimmelpilze in Luft-Probenahme und Bestimmung. Validierung von Probenahmeverfahren zur Bestimmung von Schimmelpilzen in Luft.

The assessment of mold concentrations in air samples requires generally accepted evaluation criteria. It is not possible to derive guideline values based on risk assessment. Background concentrations are therefore used as the basis for the assessment of measured concentrations. The assessment criteria established by the Federal Environmental Agency in Berlin and by the State Health Agency of Baden-Wurttemberg are founded on the experience of some laboratories. The general application of these criteria is only meaningful if validated and generally applied methods of analysis are used. Until now, laboratories have been using many different methods for sampling and detection of culturable molds and total spore counts in air. In this study, different steps for sampling by impaction or filtration are validated. The results presented will contribute to standardization of sampling and detection of molds in air.

[Background concentrations of molds in air. Determination of mold concentrations in dwellings without known mold infestations in three parts of Germany]. / Hintergrundkonzentrationen von Schimmelpilzen in Luft. Erhebung von Schimmelpilzkonzentrationen in Wohnungen ohne bekannte Schimmelpilzschäden in 3 Regionen Deutschlands.

The mold concentration of indoor air and outdoor air in three parts of Germany was investigated in both winter and summer. In total, air samples from 80 dwellings, reportedly free from mold infestations, were analysed with both the cultivation method and the total spore count method. With the cultivation method, 40 mold species and genera were differentiated, while with the total spore count method, 11 spore types were distinguished. The concentration of the genera Alternaria, Cladosporium, Fusarium and yeast increased in summertime. In contrast, the concentrations of Aspergillus and Penicillium measured in summer were nearly equal to those measured in winter. The majority of the various molds were only found in a small number of samples, too small for a reliable comparison of the winter and summer findings. The 95th percentile of the indoor mold concentrations is suggested as the upper limit of the background concentration. The results are discussed comparing the assessment proposals of various authors, and a new assessment proposal is described.

[Molds in house dust. Sampling and detection]. / Schimmelpilze im Hausstaub. Probenahme und Bestimmung.

Examination of dust samples is widely used to detect sources of mold growth in indoor environments. The advantage of this investigation is that house dust can be regarded as a passive sampler collecting mold spores over a long time period. No generally accepted method exists, however, for sampling and analysis of house dust for the detection of molds. Therefore, results obtained by different laboratories are not comparable. Measurements with standardized validated methods are a prerequisite to assess concentrations of molds in indoor environments. The method presented is based on sampling with a modified filter holder (in accordance with VDI 4300 page 8). Mini-sieves of different sizes are used for sample preparation. The fraction <63 microm is used for cultivation of molds after suspension. Problems of dust sampling and preparation are discussed. Criteria for the detection of sources of mold growth based on dust samples are presented elsewere.

[Background concentrations of molds in house dust. Determination of mold concentrations in dwellings without known mold infestations in three parts of Germany]. / Hintergrundkonzentrationen von Schimmelpilzen in Hausstaub. Erhebung von Schimmelpilzkonzentrationen in Wohnungen ohne bekannte Schimmelpilzschäden in 3 Regionen Deutschlands.

Mold concentrations of house dust samples from dwellings reportedly free from mold infestations were analysed to obtain background values. Samples from carpet floors were taken from 80 dwellings in three parts of Germany in winter and summer. Samples were analysed with the cultivation method (using suspension). This resulted in the detection of 35 mold species or genera. Concentrations of the genera Alternaria, Cladosporium, Fusarium and yeast increased in summer. In contrast concentrations of Aspergillus and Penicillium in the summer samples were nearly equal to those in the winter samples. The majority of the various molds were only found in a number of samples too small for a reliable comparison of the winter and summer findings to be made. The results were compared with findings of other authors. The authors propose the concentrations of the 95th percentile of each species (when representing over 10,000 KBE/g of dust) as background values, while a threefold higher value is regarded as an indication of mold presence. An exception should be made for the concentrations of molds which increase sharply in the outdoor air in summer. Because of the difficulty in estimating the outdoor influence, no evaluation proposals can be given for these species for the summer season.

[Quality assurance in the diagnosis of indoor fungi]. / Ringversuch "Innenraumrelevante Schimmelpilze".

In co-ordination with the Umweltbundesamt Berlin, the Landesgesundheitsamt Baden-Wurttemberg (LGA) initiated external quality assurance in the diagnosis of indoor fungi in autumn 2001. Four of six fungal strains commonly found indoors have to be fully identified (on the genus and species level). There are two distributions per year; the six distributions hitherto carried out resulted in correct identification by 46-89% of laboratories (40-71 participants, total 148). It is clear from the results that repeat participants were more successful. In addition to the pure cultures sent out we offered actual samples (two air samples, one wood material, one sample of house dust, hitherto); 43- 69% of participating laboratories also took part in this facultative investigation of actual samples and 29-62% were successful. Results that differed considerably revealed problems while treating and evaluating actual samples. Therefore, activities in this field should be enhanced. In conclusion, external quality assurance in the diagnosis of indoor fungi is a useful management aid in the maintenance and improvement of laboratory performance.

[Comparison of methods for quantification of MVOC in indoor environments]. / Vergleich der Messverfahren zur Bestimmung von MVOC in Innenräumen.

For several years now, MVOC have been regarded as indicators for microbial growth in indoor environments. Until now, a direct correlation between the occurrence of microfungi and MVOC could not be shown in scientific investigations. One reason may be that different analytical methods were applied, and moreover they were not validated sufficiently. The present investigation aimed to test the comparability of both methods (Tenax adsorption/thermal desorption; charcoal adsorption/elution). It turned out that with both methods comparable results can be achieved if the technical handling of the calibration is standardized to a wide extent. Thus, highest demands have to be made on quality assurance. Therefore, it is necessary to formulate technical regulations for the quantification of MVOC.

[Determination of mold concentrations in homes and schools in Baden-Württemberg]. / Bestimmung der Schimmelpilzkonzentration in Wohnungen und Schulen Baden-Württembergs.

So far there have been rather few reliable and comparable data available on indoor pollution with mould. Following the publication of the Federal Environmental Agency and the Health Agency Baden-Württemberg which supports the assessment of mould pollution of indoor air, it seemed advisable to investigate as to how far these criteria can be used for the assessing the mould pollution in daily practice. The results of investigations of 130 homes and 117 classrooms in Baden-Württemberg. will be represented.

Determination of carbonyl compounds in pool water with O-(2,3,4,5,6-pentafluorobenzyl)hydroxyamine hydrochloride and gas chromatographic-tandem mass spectrometric analysis.

To avoid microbiological decay pool water is disinfected, a procedure which results into a lot of disinfection by-products, like carbonyl compounds, as well as a large number of others. The carbonyl compounds dissolved in pool water were derivatisized with O-(2,3,4,5,6-pentafluorobenzyl)hydroxyamine hydrochloride (PFBHA) and extracted using n-hexane. Measuring with the help of GC-electron-capture detection is hardly possible because of interferents like halogenated organics. Another method to detect the PFBHA derivates is the use of tandem mass spectrometry. Calibration ranges and precision are applicable and sufficient to determine carbonyl compounds in pool water.

[Exposition and sensitisation to indoor allergens, house dust mite allergen and cat allergens]. / Exposition und Sensibilisierung gegenüber Milben- und Katzenallergenen bei Kindern in Baden-Württemberg.

The study examined the exposure to biological indoor air agents and their possible role for allergies and respiratory tract illnesses of children. It was conducted as a case control study (atopic vs non-atopic children) at the four surveillance public health departments in Baden-Württemberg in the winter season 1999/2000 and included 379 children of the fourth class. The concentrations of the house dust mite antigens Der F1, Der p1, and Der Gr2 as well as cat allergen Fel d1 were determined in the children's bedrooms on the ground and in the mattress. Specific IgE-antibodies against allergens from house dust, mites and cat were determined in the serum of the children. For mite allergens the following medians ( micro g/g) were estimated in floor dust: Der p1 = 0.6, Der f1 = 2.3, Gr2 = 0.1; in mattresses: Der p1 = 1.2, Der f1 = 3.4, Gr2 = 0.3. The median of Fel d1 in floor dust was 0.2 microg/g, in mattresses 0.1 microg/g. Sensitisation to dust mite allergen was found to be more prevalent than sensitisation to cat. The distribution of sensitisation among the cases and controls is different. Among the cases, more subjects were sensitised to dust mites (32.9 %) and cat (13.1 %). Among the controls, 17.1 % were sensitised to dust mites and 4.1 % to cat. The results showed no direct association between the prevalence of allergies or respiratory tract illnesses and the indoor concentrations of the allergens. Possible reasons for these findings are discussed.

[10 years of observation by public health offices in Baden-Württemberg--assessment of human biomonitoring for mercury due to dental amalgam fillings and other sources]. / 10 Jahre Beobachtungsgesundheitsämter in Baden-Württemberg--Beurteilung der Human-Biomonitoring-Untersuchungen bezüglich der Quecksilber-Belastung durch Amalgamfüllungen und andere Quellen.

Since 1992, in Baden-Württemberg, ten-year old children have been surveyed in the project "Sentinel Health Departments" to study their exposure to environmental pollutants and possible health effects. In the four study areas 1200 children have been investigated every year initially, since 1996 every second year. The data for mercury in body fluids are reported here. The decrease in the body burden of mercury as a result of the declining usage of dental amalgam fillings, was been verified. In 1992/93, of all the children who had been surveyed, the 95 percentile for the body burden of mercury was 3.1 microg/l and in 2000/01 1.35 microg/l. Also to be discussed is the reason why mercury-based cosmetic ointments seriously exceed the HBM-II-intervention-value. Because of using these ointments, concentrations of mercury in urine up to 1400 microg/l were found. A study within the project "Sentinel Health Departments" compared the concentrations of mercury in the urine of adults with those in blood and salvia. The results support the opinion that mercury in urine is appropriate for estimating the mercury uptake from dental amalgam fillings. It can be assumed that these results reflect the situation in the entire Federal Republic of Germany. The ten years' experience confirms that the concept of the "Sentinel Health Departments" is excellently suited to obtain data relevant for environmental health of children. Environmental health protection and the essential gathering of data for future health observation in Baden-Württemberg.

[Serum selenium levels in school children: results and health assessment]. / Serumselenkonzentrationen bei Schulkindern in Baden-Württemberg und ihre gesundheitliche Bewertung.

BACKGROUND: In Germany, where geogenic selenium concentrations are low, only few data on selenium status in children are available. Aim of the study was to investigate serum selenium concentrations of children in a population-based sample and to additionally investigate spatial and temporal differences. METHOD: In three consecutive cross sectional studies the selenium concentration in serum was determined in 1,918 children (mean age 10.3 years) from four study areas. Potential factors of influence were assessed by questionnaires filled in by parents and physicians, respectively. Selenium determination was done by hydride atomic absorption spectrometry after microwave digestion. RESULTS: Mean selenium concentrations for the subcollectives ranged from 54.5 +/- 10.5 micro g/l to 71.9 +/- 15.1 micro g/l. The minimum observed was 14 micro g/l, the maximum 216 micro g/l. Turkish children had lower selenium concentrations than German children and children of other nationality, respectively. Controlling for sex and year of investigation German children from Stuttgart had significantly lower selenium concentrations than children from Aulendorf/Bad Waldsee. In the same regression model for the period from 1995/96 to 1998/99 a decreasing trend was found to be significant. However, the regression model only explains a very small part of variance. CONCLUSIONS: The selenium concentrations determined in this study are in the range also found in other studies in children from Germany. They are far below the toxicologically relevant range, which starts at about 600 micro g/l. The 5 th percentile in nearly all subcollectives was below the threshold limit of the lower tolerable selenium concentration of 45 micro g/l. For children from south Germany deficiency of selenium is therefore more to be suspected than a burden relevant to health. Selenium supplementation should however be considered thoroughly. Balanced nutrition is also a main factor for an optimum selenial supply.

Human biomonitoring of polychlorinated biphenyls and polychlorinated dibenzodioxins and dibenzofuranes in teachers working in a PCB-contaminated school.

Eighteen teachers from a highly contaminated school and 11 teachers from a control school participated in this study. Total polychlorinated biphenyl (PCB) indoor air concentration (six indicator congeners x 5) was beyond 12000 ng/m3 in some rooms of the contaminated school. PCB 28 and PCB 52 were the prevailing congeners. Whole blood was taken from each participant by the local health authority, pooled in two groups and analysed for the six PCB indicator congeners, non-ortho PCBs and polychlorinated dibenzodioxins (PCDD)/polychlorinated dibenzofurans (PCDF). Blood analysis showed elevated mean PCB 28 and PCB 52 levels for the exposed group, however the two groups were almost identical with regard to PCB 101, 138, 153 and 180. Moreover no difference can be observed for the concentration of non-ortho PCBs and PCDD/PCDF. The data support the finding, that heavy indoor air contamination with low chlorinated PCBs causes an increase of PCB 28 and PCB 52 blood levels. However, this increment was small compared to their total PCB load.