ABSTRACT
BACKGROUND: Azobenzene disperse dyes (azo DDs) are well-known as textile allergens, but the knowledge of their occurrence in garments is low. The numerous azo DDs and dye components found in textiles constitute a potential health risk, but only seven azo DDs are included in the European baseline patch test series (EBS). OBJECTIVES: To investigate non-regulated azo DDs and dye components in synthetic garments on the Swedish market. METHODS: High-performance liquid chromatography/mass spectrometry, gas chromatography/mass spectrometry and computerized data mining. RESULTS: Sixty-two azo DDs were detected, with Disperse Red 167:1 occurring in 67%, and 14 other DDs each found in >20% of the garments. Notably, the EBS dyes were less common, three even not detected, while arylamines were frequently detected and exceeded 1 mg/g in several garments. Also, halogenated dinitrobenzenes were identified in 25% of the textiles. CONCLUSION: Azo DDs and dye components, in complex compositions and with large variations, occurred frequently in the synthetic garments. The arylamines were shown to occur at much higher levels compared to the azo DDs, suggesting the former constitute a potentially higher health risk. The role of arylamines and halogenated dinitrobenzenes in textile allergy has to be further investigated.
Subject(s)
Dermatitis, Allergic Contact , Allergens/adverse effects , Amines/adverse effects , Azo Compounds/adverse effects , Clothing , Coloring Agents/adverse effects , Dermatitis, Allergic Contact/epidemiology , Dermatitis, Allergic Contact/etiology , Dinitrobenzenes , Humans , Patch Tests/methods , Sweden , TextilesABSTRACT
Objective To establish an animal model for immunological contact urticaria in mice.Methods A total of 60 BALB/c mice were randomly and equally divided into 5 groups:anti-dinitrophenol IgE monoclonal antibody (anti-DNP IgE) + 2,4-dinitrofluorobenzene (DNFB) group and anti-DNP IgE + trimellitic anhydride (TMA) group both injected with anti-DNP IgE via tail veins firstly,followed by topical treatment with DNFB and TMA respectively on the ears at 24 hours after the injection,DNFB group,TMA group and normal saline (NS) group all injected with NS via the tail vein firstly,followed by topical treatment with DNFB,TMA and NS on the ears 24 hours after the injection.In the following 14 days,mice were observed daily for the appearance of wheals and for scratching behavior.All the mice were sacrificed at the end of the study followed by determination of the percentage of degranulated mast cells and spleen index as well as observation of pathological changes.Results Wheals were observed in all the mice (12/12) in the anti-DNP IgE + DNFB group,some mice (8/12) in the anti-DNP IgE + TMA group,but not observed in any mice in the other 3 groups.Compared with the NS group,both the anti-DNP IgE + DNFB group and anti-DNP IgE + TMA group showed a significant increase in the percentage of degranulated mast cells (70.21％ ± 26.01％ and 54.25％ ± 39.57％ vs.14.45％ ±6.79％,F=14.41,P=0.000),spleen index (7.54 ± 1.56 and 7.87 ± 1.18 vs.5.37 ± 1.16,F=4.29,P=0.004) and scratching frequency ((31.58 ± 3.58)/h and (22.17 ± 3.81)/h vs.(2.00 ± 0.85)/h at 30 minutes,F =437.86,P ＜ 0.01).Conclusion A stable mouse model for immunological contact urticaria can be established quickly by sensitization with anti-DNP IgE and challenge with DNFB.
ABSTRACT
Objective To establish an easy, rapid and sensitive method for determination of micro 2,4-dinitrotoluene in waste water. Methods Based on the fact that micro 2,4-dinitrotoluene could inhibit the discoloring oxidation reaction of methylene blue by KIO4 in the HC1 solution, micro 2,4-dinitrotoluene was determined using kinetic spectrophotometric method. Results A new kinetic spectrophotometric method for determination of micro 2,4-dinitrotoluene was established. The linear range of the method was 0.20?10~(-5)-1.8?10~(-5) mg/L, the detection limit was 1.7xlO'7 mg/L. When the method was applied to the determination of the 2,4-dinitrotoluene in waste water, its recovery rates in standard addition method were 95.6%-99.1% and the RSDs were 1.5%-2.6%. Conclusion The method was easier to operate and more rapid, which was suitable for the determination of micro 2,4-dinitrtoluene in wastewater.
