Mutagenic Characteristics and Contribution of Polycyclic Aromatic Hydrocarbons to Mutagenicity of Concentrates from Municipal River Water by Blue Chitin Column

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Mutagenic Characteristics and Contribution of Polycyclic Aromatic Hydrocarbons to Mutagenicity of Concentrates from Municipal River Water by Blue Chitin Column 232 Journal of Health Science, 48(3) 232–241 (2002) Mutagenic Characteristics and Contribution of Polycyclic Aromatic Hydrocarbons to Mutagenicity of Concentrates from Municipal River Water by Blue Chitin Column Akira Nagai,*, a Yoshinao Kano,a Ryozo Funasaka,a and Katsuhiko Nakamurob aGifu Research Center for Public Health, 4–6 Akebono-cho, Gifu-shi, Gifu 500–8148, Japan and bFaculty of Pharmaceutical Sciences, Setsunan University, 45–1 Nagaotoge-cho, Hirakata-shi, Osaka 573–0101, Japan (Received January 9, 2002; Accepted February 26, 2002) The mutagenic characteristics of concentrates from environmental water such as the effluent from various treatment plants and river waters using a modified Blue Chitin column method were determined by Ames assay with Salmonella typhimurium TA98, YG1021 and YG1024. This was done to estimate the quantitative contribution rate of mutagenicity estimated from analyzed polycyclic aromatic hydrocarbons (PAHs) content in the same concen- trates to the mutagenicity of environmental water. Moreover, PAHs content and the mutagenicity of the river sedi- ment-extract were measured to elucidate the fate of PAHs in the river. Many kinds of environmental waters and river sediment possessed principally indirect frame-shift type mutagenicity. Concentrates from many kinds of environ- mental waters possibly contained aminoarenes assayed with YG1021 and YG1024. In many kinds of environmental waters, the contribution rates of mutagenic magnitude estimated from seventeen analyzed PAH contents to the mutagenic magnitude of these water concentrates in TA98 with S9 mix were recognized to be from 0.10 to 1.15%. However, the contribution rate of mutagenic magnitude estimated from ten analyzed PAHs contents to the mu- tagenic magnitude of the Arata River sediment extract in TA98 with S9 mix was 64.2%. The high concentration of PAHs in the river sediment suggested that hydrophobic PAHs in the water might easily accumulate in the river sediment after adsorbing to the suspended solid. Key words —–— polycyclic aromatic hydrocarbons, mutagenic magnitude, contribution rate, environmental water, Blue Chitin INTRODUCTION cd)perylene as possible carcinogenic pollution indi- cators of drinking-water.15) The surface water of municipal river water has In mutagenicity investigations on environmen- served as a source of supply water. This river water tal water, water samples need to be concentrated for contains a large amount of trace toxic organic pol- Ames assay. One of the concentration methods is lutants, because it receives a large quantity of waste that using a solid support able to trap selectively water drained from the activities of human life, sew- molecular type mutagenic materials. XAD-2 resin age treatment plants, industrial waste plants, agri- traps a wide range of spectra of soluble organic sub- culture and road runoff. Many studies have been re- stances in water. Blue Cotton, Blue Rayon and Blue ported in which municipal river water shows mu- Chitin which have ligand linked copper phthalocya- tagenicity1–14) and its character is derived from nine trisulphonate are capable of adsorbing PAHs polycyclic aromatic hydrocarbons (PAHs) including with three or more fused rings. These have been used nitro- and amino-derivatives.1–6) Recently, WHO as a preconcentration method in many mutagenicity established the guidelines for fluoranthene, investigations.1–14,16–21) benzo(b)fluoranthene, benzo(k)fluoranthene, benzo Yamauchi et al.2) and Sasaki et al.13) used the (a)pyrene, benzo(ghi)peryrene and indeno(1,2,3- Blue Cotton hanging method for concentration of *To whom correspondence should be addressed: Gifu Research organic substances in river water, measured the mu- Center for Public Health, 4–6 Akebono-cho, Gifu-shi, Gifu 500– tagenicity of concentrate and analyzed 10 kinds of 8148, Japan. Tel.: +81-58-247-1300; Fax: +81-58-248-0229; E- PAHs, Trp-P-1 and Trp-P-2, respectively. Ohe and mail: [email protected] Nukaya reported the genotoxicity and the content No. 3 233 of 1-nitropyrene in concentrates from river water The column (14 mm i.d. × 60 mm) was packed using the XAD-2 resin column.17) Mouri et al. re- with 200 mg of Blue Chitin (Funakoshi, Ltd., Ja- ported the genotoxicity and the content of 6 kinds pan) which was in a powdered form and contained of heterocyclic amines in concentrates not only from 40 µmol of copper phthalocyanine trisulfonate- river water, but also from the effluent from various chitin. treatment plants using the Blue Rayon column Sample —–— The effluents from a night soil treat- method.19) ment plant, sewage treatment plant and septic tanks These reports described the contribution of PAHs combined with aerobic treatment were sampled in or heterocyclic amines to the mutagenicity or the Gifu city on September 1998. genotoxicity of river water, however, few target com- The surface waters of the Katsura River, the Uji pounds contributing to the mutagenicity or the River and the Kizu River were sampled on Septem- genotoxicity have been reported, and recovery of ber 1997. The surface waters of the Nagara River, such compounds by preconcentration method was the Sakai River, the Arata River and the Kuwabara not quantitative. River were sampled on September 1998. In the previous paper20) we reported a quantita- These water samples were filtered through a tive preconcentration method for 26 kinds of PAHs glass-fiber filter as quickly as possible after collec- in water, and suggested that a modified Blue Chitin tion. column method was useful for 14 kinds of PAHs with The Arata River sediment was sampled on May 4 and 5 rings. Moreover, we indicated the occurrence 1999. The sample was dried in a dark place at room of PAHs surveyed by GC-MS in the effluent from temperature, and was screened through a 2 mm mesh various treatment plants and river water. sieve. In this paper we measured 17 kinds of PAHs in- Preconcentration Method by Modified Blue cluding 6 kinds of PAHs established as WHO’s Chitin Column Method20) —–— Five liters of efflu- guideline in the environmental water and investi- ents from various treatment plants and river waters gated the mutagenic characteristics of concentrates was passed through a Blue Chitin column, which obtained from the effluent from various treatment was washed11) at a flow rate of 20 ml/min with a peri- plants and river water using this same method. We staltic pump, and then the column was washed with evaluated in detail quantitative contribution of mu- 20 ml of water. The organics adsorbed to Blue Chitin tagenic magnitude estimated from analyzed PAH were consecutively eluted with 100 ml of contents in the same concentrates to the mutagenic CH3OH • NH4OH (50 : 1) and 20 ml of CH2Cl2 at magnitude of river water concentrates as well as the a flow rate of 5 ml/min. Fractions of both river sediment. CH3OH • NH4OH (50 : 1) and CH2Cl2 were com- bined and evaporated to dryness with a rotary evapo- rator in a water bath at about 40°C under vacuum. MATERIALS AND METHODS The residue was dissolved in 2 ml of DMSO for Ames assay. The concentrates from upstream and Chemicals —–— downstream of the Nagara River were dissolved in Chemical sources were as follows: acenaphthylene 1 ml of DMSO, respectively. (Anl), acenaphthene (An), fluorene (Fl), phenan- Fifty grams of the river sediment was extracted threne (Phe), anthracene (Ant), fluoranthene (FA), with 200 ml of CH2Cl2 •C2H5OH (4 : 1) twice un- pyrene (PY), benz[a]anthracene (BaA), chrysene der ultrasonic vibration (28 Hz) for 15 min and then (Chr), benzo[a]pyrene (BaP) and dibenz[a,h] an- centrifuged at 3000 rpm for 10 min. The extract was thracene (diBahA) were from Wako Pure Chemical concentrated to about 100 ml with a rotary evapora- Industries, Ltd.; benzo[ghi]perylene (BghiP), 2- tor in a water bath at about 40°C under vacuum, aminoanthracene (2-AAnt), 3-aminofluoranthene (3- washed with 300 ml of 5% NaCl solution, and evapo- AFA) and 1-aminopyrene (1-APY) were from rated to dryness with a rotary evaporator in a water Aldrich Chemical Co. Inc.; benzo[b]fluoranthene bath at about 40°C under vacuum.21) The residue was (BbFA) and benzo[k]fluoranthene (BkFA) were from dissolved in 10 ml of CH3OH and then 90 ml of H2O RK Chemical Co.; methanol (CH3OH), ammonia added. This solution was passed through a Blue (NH4OH), dichloromethane (CH2Cl2) and dimethyl Chitin column and the same condition as for water sulfoxide (DMSO) were also from Wako Pure sample was followed. Half amount of concentrate Chemical Industries, Ltd., Japan. was dissolved in 2 ml of DMSO for Ames assay and 234 Vol. 48 (2002) Fig. 1. Mutagenicity of Concentrates from Effluent from Various Treatment Plant in TA98, YG1021 and YG1024 The numbers of spontaneous revertants per plate 25 ± 6.0 (TA98-S9), 33 ± 3.9 (TA98+S9), 20 ± 3.3 (YG1021-S9), 32 ± 5.7 (YG1021+S9), 23 ± 5.0 (YG1024-S9) and 60 ± 12 (YG1024+S9) were subtracted. the other amount was dissolved in 1 ml of CH2Cl2 for GC-MS analysis. GC-MS Analysis —–— Seventeenkinds of PAHs were analyzed by GC-MS using a Thermoquest GCQ. The conditions of GC-MS were described previously.20) Ames Salmonella/Microsome Assay22) —–— T h e bacterial Salmonella typhimurium strains used in the Ames Salmonella/microsome assay were TA98 and derivatives of TA98 capable of detecting mutagenic nitroarenes or aminoarenes: YG1021 and YG1024, respectively.23,24) YG1021 is a nitroreductase-over- producing strain and is highly sensitive to the mu- tagenic action of typical nitroarenes. YG1024 is an O-acetyltransferase-overproducing strain and is also Fig. 2. Mutagenic Magnitude of Concentrates from Effluent from Various Treatment Plants in TA98, YG1021 and extremely sensitive to the mutagenic action of YG1024 nitroarenes and aminoarenes. Ames assay was carried out by the liquid prein- cubation procedure.
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