Analysis of human plasma as an exposure level monitor for carcinogenic tryptophan pyrolysis products

A high-performance liquid chromatography method for detecting 3-amino-1,4- dimethyl-5H-pyrido[4,3-b]indole (Trp-P-1) and 3-amino-1-methyl-5H-pyrido[4,3-b]indole (Trp-P-2) in human plasma was developed. Plasma samples of 10 normal subjects were examined. Trp-P-1 and Trp-P-2, carcinogenic tryptophan pyrolysis products, were detected in all specimens, and the concentrations of Trp-P-1 and Trp-P-2 in plasma were 68.31 +/- 24.03 fmoles/ml (mean +/- S.D., n = 10) and 18.79 +/- 4.99 fmoles/ml, respectively. Our results suggest that plasma levels of carcinogenic tryptophan pyrolysis products may be useful indicators for estimating the exposure levels of the dietary carcinogens.     

Detection of Trp-P-1 and Trp-P-2, carcinogenic tryptophan pyrolysis products, in dialysis fluid of patients with uremia

In order to estimate the exposure levels of mutagenic and carcinogenic heterocyclic amines in humans, we developed a high-performance liquid chromatography method to detect 3-amino-1,4-dimethyl-5H-pyrido[4,3-b]indole (Trp-P-1) and 3-amino-1-methyl-5H-pyrido[4,3-b]indole (Trp-P-2) in dialysis fluid of patients with uremia. Using this methods, dialysis fluid of 12 patients who had received hemodialysis treatment or continuous ambulatory peritoneal dialysis was examined. Trp-P-1 was detected in dialysate of all uremic patients (727 +/- 282 pmoles, n = 12). In patients who had been treated with continuous ambulatory peritoneal dialysis, the average amount of Trp-P-1 found in whole dialysate (6 l) per day was 710 +/- 203 pmoles (mean +/- S.D., n = 8). Moreover, Trp-P-2 could be detected in 5 out of 12 patients (206 +/- 85 pmoles, n = 5). These results indicate that patients with uremia are actually exposed to carcinogenic tryptophan pyrolysis products. The average exposure level of Trp-P-1 in uremic patients apparently exceeded 710 pmoles (150 ng) per day.     

Localisation of allergens in ryegrass pollen and in airborne micronic particles

Summary In Melbourne, Australia, grass pollen allergens, especially from ryegrass, are a major cause of allergic hayfever and asthma. This review outlines recent developments in our understanding of how grass pollen allergens find their way into the atmosphere and how they are transported in particulate form. Much of this work has relied on antibody technology in immunological and immunocytochemical investigations. The localisation of allergens in situ has proved difficult due to their water-soluble character. Recently, allergens have been localised in developing ryegrass pollen by dryfixation, rapid-freeze and freeze-substitution techniques. This involved anthers being substituted in a mixture of aldehydes, organic solvents, and 2,2-dimethoxypropane. Incubation in dimethylsulfoxide prior to embedding in LR Gold resin provided good infiltration with freeze-substituted material. Immunogold-labelled sections show that the major allergens, Lol p 1 and Lol p 5, are synthesised in the pollen cytoplasm from the early bicellular stage, soon after the first starch granules are formed. From the early tricellular stage, Lol p 5 moves into the starch granules where it remains until maturity. Lol p 1 is localised in the cytoplasm of mature pollen grains. The incidence of airborne grass pollen, as measured in pollen traps, correlates with hayfever symptoms. Forecasting models which rely on rainfall and temperature data have been produced for the grass pollen (daily and seasonal) counts in Melbourne. Research over the past six years has shed light on the causes of grass-pollen-induced asthma. Micronic particles in the atmosphere may be starch granules originating from pollen grains osmotically ruptured by rainwater. Ultrastructural and immunological characterisation of micronic particles collected from outdoor air filters confirm the presence of airborne starch granules. These are loaded with grass pollen allergens, occur in the atmosphere especially after rainfall, and correlate significantly with instances of allergic asthma. Diesel particles might also play a role in the transmission of grass pollen allergens and thus become an extra asthma trigger. A variation in the mode of release of micronic particles occurs in other species, such as birch, where such particles are derived from burst birch pollen tubes. These particles are positive for Bet v 1 and are starch granules which are released into the atmosphere after light rain as a result of pollen germination on, e.g., leaves. After subsequent rupture of pollen tubes their contents are released when conditions become drier.Abbreviations DECP diesel exhaust carbon particles - DMP 2,2-dimethoxypropane - GPC grass pollen count - IgE immunoglobulin E - IgG immunoglobulin G - OGPS onset of the grass pollen season     

On the tryptophan determination in lysozyme and its photoxidation products

A comparative study was made of three techniques of tryptophan determination in lysozyme and its photoxidation products: mild acid hydrolysis (85–90°, 15 hr), pronase hydrolysis, and direct spectrophotometric determination.Satisfactory data have been obtained only after pronase hydrolysis. The technique for hydrolyzate treatment and its analysis have been worked out. This technique was used for tryptophan determination in three lysozyme photoxidation products.The mild acid hydrolysis has been found unsuitable owing to incomplete hydrolysis.The direct spectrophotometric determination has been modified as applied to lysozyme, and satisfactory results have been obtained. But this technique is unsuitable for tryptophan determination in photoxidized lysozymes as it does not permit differentiation of native from photoxidized tryptophan residues in protein.     

Filter efficiency of commercial face masks in capturing particles and airborne bacteria

The filter efficiency of seven kinds of commercial face mask for particles and airborne bacteria was tested in the wash room of a laboratory animal facility. The filter efficiency of the masks was 19 to 50%, as measured by the weight of particles with diameters below 10 micron, 22 to 71% for particles of the 0.3 micron level, 47 to 90% for the 1 micron level, and 90 to 99.6% for the 5 micron level. The filter efficiency for airborne bacteria was 35 to 81%. Among these even masks tested, glasswool surgery masks, three-sheet synthetic fiber masks with and without charcoal, and 28-sheet gauze masks with glass filter showed generally high efficiency, and single-sheet synthetic fiber masks, 18-sheet of gauze masks and gas masks showed low efficiency.     

Mutagenicity of airborne particles from four cities in Taiwan.

The mutagenicity of airborne particles from 8 urban and suburban locations in each of four cities, Taipei, Hsinchu, Taichung, and Kaohsiung, in Taiwan area were investigated with S. typhimurium strain TA98 by Ames Salmonella/microsomal test. The average mutagenic activity of airborne particulate samples from Taipei and Kaohsiung was higher than that from Hsinchu and Taichung with or without metabolic activation. The major direct-acting mutagenic compounds of airborne particulate samples from Taipei and Kaohsiung was similar to that of standard dinitropyrenes mixture (DNPs) in the retention time of HPLC. Moreover, the contents of DNPs of airborne particulate samples from Taipei and automobile exhaust partially purified through Sephadex LH-20 gel filtration and semipreparative HPLC were determined by HPLC. DNPs was major direct-acting mutagens of the urban air samples from Taipei and their major pollutants might be from automobile exhaust. However, the major mutagenic compounds of airborne particulate samples from Hsinchu and Taichung did not correspond to any of the standard compounds tested. The content of benzo[a]pyrene (B[a]P) of airborne particulate samples was also determined by HPLC. The concentration of B[a] P was 0.05-0.62 ng/m3 air sample. The B[a] P contents of airborne particulate samples from four cities in Taiwan did not show good correlation with their mutagenic activity. Thus, we concluded that B[a] P was not a major indirect-acting mutagenic compound in the tested air samples.     

Evidence that bacteria can form new cells in airborne particles.

Serratia marcescens incubated for 8 h at 31 degrees C in a chemically defined medium contained in shake flasks was aerosolized into rotating-drum aerosol chambers at 30 degrees C and saturated humidity. Cells furnished tryptone (Difco) and glycerol just before aerosolization increased (in viable numbers and countable cells) almost twofold within 1 to 2 h after becoming airborne, whereas cells not furnished additional tryptone decreased in viable numbers at a faster rate than the number of particles removed by gravitational settling. Limited tests with a Coulter Counter showed that cell volume changes occurred in growing cells that did not occur in the nongrowing population.     

Mutagenicity of amino-alpha-carbolines in pyrolysis products of soybean globulin.

The nuclear-cytoplasmic partition of newly synthesized C, D and 5 S RNAs of HeLa cells was studied with aqueous and non-aqueous methods of cell fractionation. The level of briefly labeled 5 S RNA in cytoplasmic fractions prepared by a non-aqueous method is lower than in cytoplasmic fractions obtained by an aqueous method. The reverse is true in nuclear fractions. At the same time, with both aqueous and non-aqueous cell fractionation, the level of briefly labeled precursors to RNAs C and D is similarly high in cytoplasmic fractions and low in nuclear preparations. This suggests that the previously reported finding that RNA species C and D are cytoplasmic during the first minutes of their lifetime, may represent an in vivo phenomenon, instead of an artifactual elution from nuclei during fractionation.     

Evidence that bacteria can form new cells in airborne particles.

Serratia marcescens incubated for 8 h at 31 degrees C in a chemically defined medium contained in shake flasks was aerosolized into rotating-drum aerosol chambers at 30 degrees C and saturated humidity. Cells furnished tryptone (Difco) and glycerol just before aerosolization increased (in viable numbers and countable cells) almost twofold within 1 to 2 h after becoming airborne, whereas cells not furnished additional tryptone decreased in viable numbers at a faster rate than the number of particles removed by gravitational settling. Limited tests with a Coulter Counter showed that cell volume changes occurred in growing cells that did not occur in the nongrowing population.     

Preliminary assessment of protein associated with airborne particles in Mexico City

The protein associated with airborne particles was measured during 1991 as an indicator of airborne biological material in different outdoor urban environments. Fifty air samples were collected simultaneously at three sampling sites, located in the north, south and downtown Mexico City, using a PM10 high-volume sampler (particles<10 μm). The air filters were weighed and protein extracted using a phosphate buffer. Protein concentrations were determined by Lowry assay. The extracts were also analysed by SDS electrophoresis and IEF using a Phastsystem. High concentrations of airborne particles were recorded at the sampling sites with a geometric mean of 70.2 μg/m³ in the south (residential area), 95.5 μg/m³ in the center (urban-commercial area), and with the highest value of 108.9 μg/m³ in the north (urban-industrial area). No statistically significant difference (P>0.05) was observed among the protein concentrations from the sampling sites and the concentrations ranged from non-detectable to 2.54 μg/m³. However, the protein concentrations presented significant difference (P<0.05) with respect to rainy and dry seasons. The Spearman correlation coefficient between protein concentration and airborne particles concentration was statistically significant (r=0.50). The molecular weights (MW) and isoelectric points (pI) for the proteins present in some of the extracts were determined. The values ranged from approximately 8000 to 106 000 Da and the pI values from nearly 4.0 to 5.85. This is important because the major allergens from inhalants are mostly acidic proteins with molecular weights in the range of 20 000–40 000 Da.     

Size distributions of total airborne particles and bioaerosols in a municipal composting facility

Size distributions of total airborne particles and bioaerosols were measured in a full-scale composting facility, using an optical particle counter and an agar-inserted six-stage impactor, respectively. Higher concentrations of total airborne particles and bioaerosols were detected at a sampling location near the screening process preceded by the composting process than at sampling locations in the composting process. At the sampling location near the screening process, the concentrations of total airborne particles were approximately 10(8)particles/m3 at the size of 0.3 microm and 10(5)particles/m3 at 6.2 microm. The concentration of bioaerosols was about 10(4)CFU/m3 in each stage of 7.0 microm (1st stage), 7.0-4.7 microm (2nd), 4.7-3.3 microm (3rd), 3.3-2.1 microm (4th), 2.1-1.1 microm (5th) and 1.1-0.65 microm (6th). Most of submicron particles smaller than 1 microm among the total airborne particles were believed to originate from the ambient air.     

Role of the uvr gene in the SOS function inducing activity of two tryptophan pyrolysis products, Trp-P-1 and Trp-P-2, in Escherichia coli K12

Two tryptophan pyrolysis products, Trp-P-1 and Trp-P-2 were assayed in the SOS-chromotest using PQ 37 (uvr A) and PQ 35 (uvr+) E. coli K12 strains, in the presence of S9 fraction from Aroclor-induced rats. Both compounds were able to induce the expression of SOS functions in uvr A bacteria, in the following order: Trp-P-1 less than Trp-P-2 less than aflatoxin B1, at low concentrations (less than 125 ng/assay). In this range, the induction of SOS functions was significantly decreased in the uvr+ strain. This implies that the uvr gene product plays an important role in the repair of genotoxic damage induced by Trp-P-1 and Trp-P-2. At higher concentrations (125-500 ng/assay), Trp-P-1 became more efficient in inducing SOS functions than Trp-P-2 and excision repair was less efficient than at low concentration.     

Short,medium and long range transported airborne particles in viability and antigenicity analyses

Summary It is no longer enough that aerobiologists identify pollen grains and fugal spores under the microscope. They are expected to serve as well allergologists, who want to known about the concentrations of various allergens in the air samples, as meteorologists, who need to know about the frequency of primary biological aerosols, which may act in radiative forcing of the atmosphere. Methods utilized by the aerobiologists vary from immunochemical analyses, culture and germination to infecting host plants with certain pathogens. Difficulties to separate between short, medium and long range transport of airborne particles on the basis of their viability are discussed.     

Quantification of airborne microorganisms and investigation of their interactions with non-living particles

A fluorescence method was developed for the direct counting of airborne microorganisms and for the examination of their interactions with other aerosol particles. The method is based on a combination of the aerosol sampling technique using a cascade impactor and the selective dyeing of the trapped microorganisms with ethidium bromide. The method enables both the total microorganism concentrations and their counts in clusters to be evaluated. The new method and the cultivation method, enabling the colony-forming units (CFU) to be determined, were compared. Based on the results obtained by the fluorescence technique, a procedure is suggested for the conversion of CFU data to bacteria and yeast concentrations.     

Effect of glutathione and uridine-5'-diphosphoglucuronic acid on the mutagenicity of tryptophan pyrolysis products (Trp-P-1 and Trp-P-2) by rat-liver and -intestine S9 fraction

In the Ames test, after the addition of glutathione (GSH) or uridine-5'-diphosphoglucuronic acid (UD-PGA), we observed for Trp-P-1 an unchanged or a reduced mutagenicity by both the liver and intestine S9 fraction. For Trp-P-2, the same was true when we used the intestine S9 fraction. In the presence of liver S9 fraction, Trp-P-2 mutagenicity was also decreased by the addition of UDPGA but was increased by the addition of GSH. These results show that cofactors for glucuronide and GSH conjugation may alter the metabolic activation of Trp-P-1 and Trp-P-2 and consequently their mutagenicity.     

The release of mutagens from airborne particles in the presence of physiological fluids

Airborne particulates collected indoors in residences and outdoors were extracted by soxhlet extraction and sonication with methanol. In a comparative study in which mutagenic activity was evaluated in the Salmonella typhimurium reversion assay both soxhlet extraction and sonication proved to be suitable extraction methods. First, the residue, obtained by sonication of loaded filters with methanol followed by evaporation to dryness (tar), was sonicated with newborn calf serum and lung lavage fluid from pigs. All serum extracts of the tar were mutagenic to Salmonella typhimurium TA98, and contained direct- and indirect-acting mutagens. However, the mutagenic activity recovered by serum was only about half of the total mutagenic activity of the tar. The other part of the mutagenic activity remained in the tar. Lung lavage fluid was only able to remove 5-10% of direct-acting mutagens from the tar of all samples. About 20% of indirect-acting mutagens from indoor air were recovered in lung lavage fluid, while the lung lavage fluid extract from outdoor air did not show indirect mutagenic activity. Second, mutagenic activity recovered by direct sonication of the filters with physiological fluids was comparable with the recovery obtained by sonication of the tar. However, after sonication of the filter with lung lavage fluid hardly any mutagenic activity remained on the filter, whereas after sonication of the tar a clear mutagenic activity was observed in the non-soluble residue.