Natural organic matter (NOM), a complex mixture of organic compounds, influences drinking water quality and water treatment processes. The presence of NOM is unaesthetic in terms of colour, taste and odour, and may lead to the production of potentially carcinogenic disinfection by-products (DBPs), as well as biofilm formation in drinking water distribution systems. Some NOM removal processes such as coagulation, magnetic ion exchange resin (MIEXTM) and membrane filtration produce sludge and residuals. These concentrated NOM-containing sludges from alum precipitation, membrane treatment plants and MIEX regeneration must therefore be treated prior to disposal. The white-rot fungi possess a non-specific extracellular oxidative enzyme system composed of lignin peroxidase (LiP), manganese-dependent peroxidase (MnP) and laccase (Lac) that allows these organisms to mineralise lignin an d a broad range of intractable aromatic xenobiotics. Rojek (2003) has shown the capability of Phanerochaete chrysosporium ATCC 34541 to remove 40-50% NOM from solution, however, this was found to be mainly due to adsorption and to be a partially metabolically linked activity. Consequently, the bioremediation of NOM wastes by selected white-rot fungi was further investigated in the present study. The P. chrysosporium seemed to preferentially remove the very hydrophobic acid (VHA) fraction, and so was most effective for a NOM preparation with a high proportion of hydrophobic content (and so high in colour and specific UV absorbance (SUVA)). The extent of NOM decolourisation by P. chrysosporium in three growth media with different C:N ratios followed the trends: Waksman (C:N = 6) & Fahy (C:N = 76) & Fujita medium (C:N = 114), such that the lower the C:N ratio, the greater NOM removal. This was consistent with the findings of Rojek (2003), who used a different NOM preparation and demonstrated that the removal of NOM increased with decreased C:N ratio (1.58-15.81). As removals of NOM with P. chrysosporium ATCC 34541 were low, and little biodegradation occurred, this organism was compared with P. chrysosporium strain ATCC 24725, Trametes versicolor ATCC 7731, and three strains of yeast (Saccharomyces species arbitrarily denoted 1, 2 and 3). T. versicolor gave the greatest removal (59%) which was attributed largely to degradation, whereas the NOM removal by the two strains of P. chrysosporium (37%) and the yeast was predominantly due to adsorption as indicated by the deep brown colouration of the biomass. Saccharomyces sp. 1, 2 and 3 removed 12%, 61% and 23% of the colour, respectively. Although Saccharomyces sp. 2 had similar high colour reduction to T. versicolor, the specific removal values differed markedly: 0.055 compared to 0.089 mg NOM/mg biomass, respectively. The low level of the ligninolytic enzymes secreted by both strains of P. chrysosporium corresponded with the low degree of NOM removal by biodegrada tion as shown by high performance size exclusion chromatography (HPSEC). The high NOM removal attained by T. versicolor was attributed to the activities of the ligninolytic enzymes, especially laccase. The NOM removal was attributed to the breakdown of the high molecular weight compounds to form a pool of low molecular weight materials, which were then most likely utilised by the T. versicolor. Growth of T. versicolor cultures at 36oC caused inhibition or denaturation of the activity of the phenoloxidase enzymes compared to those grown at 30oC. The low activity of LiP in both cultures suggested that this enzyme may not play much of a role in NOM removal. The higher levels of MnP and Lac activities at 30oC were responsible for the greater NOM removal (73% vs. 59%) and thus the cleavage of aromatic rings, conjugated and C-Cβ αbonds in phenolic moieties, as well as catalysing alkyl-aryl cleavage in the NOM structures. T. versicolor cultured in Waksman medium with higher initial glucose (5 g/L cf. 2 g/ L) led to lower ligninolytic enzyme activities and a lower degree of NOM removal (25% less colour reduction), probably due to preferential use of glucose over NOM as carbon source. NOM removal (mg removed) increased linearly with NOM concentration up to 600 mg C/L (62 mg (A446); 31 mg (A254)), above which removal decreased markedly. This trend coincided with increasing total ligninolytic enzyme activity, where the level of Lac increased up to 600 mg C/L NOM although MnP decreased gradually across the range while LiP was only detected for 100 and 300 mg C/L NOM. Hence, the removal of NOM from solution by T. versicolor was associated with high oxidative enzyme activity, particularly of laccase. Laccase was the major extracellular enzyme secreted by T. versicolor and by deduction, played a major role in NOM removal. The optimum temperature for Lac activity secreted by T. versicolor cultured in Waksman medium supplemented with 4.5 g/L wheat bran plus 0.5% Tween 80 was determined to be 50oC. The optimum pH for th e Lac activity for guaiacol and NOM was identified as pH 4.0-4.5. Although the optimum enzyme activity occurred at 50oC, 30oC was recommended for enzymatic removal of NOM as the phenoloxidase enzyme activity may be denatured if the NOM removal process were considered to run for long period at high temperature. Although agitation led to apparent enzyme denaturation, fermentations with continuous agitation promoted enzyme activity faster than those with occasional agitation (agitated every 6 hours for 30 minutes at 130 rpm and 30oC) as it provides better mass transfer. However, it seemed that continuous agitation had an adverse effect on the fungal growth and enzyme production over extended fermentation periods. Addition of 4.5 g/L wheat bran to modified Waksman medium in the absence of NOM led to high production of Lac activity compared with LiP and MnP activities, showing its great potential as a laccase inducer. Addition of Tween 80 alone to the cultures led to a small improvement in Lac activity; however, with the presence of wheat bran it caused marked increases in LiP, MnP and Lac activities. When NOM was added to cultures of T. versicolor with the two supplements, it led to markedly reduced Lac activity, but increased LiP and MnP activities, and no improvement in NOM removal compared with the cultures in the absence of supplements (12 mg (or 61%) cf. 15 mg (or 73%) for 100 mg C/L after corrected for colour from and adsorption by wheat bran).
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机译:天然有机物(NOM)是有机化合物的复杂混合物,会影响饮用水质量和水处理过程。就颜色,味道和气味而言,NOM的存在是不美观的,并且可能导致潜在致癌的消毒副产物(DBP)的产生以及饮用水分配系统中生物膜的形成。某些NOM去除过程(例如凝结,磁性离子交换树脂(MIEXTM)和膜过滤)会产生污泥和残留物。因此,在处置之前,必须对来自明矾沉淀,膜处理厂和MIEX再生的浓缩的含NOM的污泥进行处理。白腐真菌具有由木质素过氧化物酶(LiP),锰依赖性过氧化物酶(MnP)和漆酶(Lac)组成的非特异性细胞外氧化酶系统,该系统可使这些生物使木质素矿化,并形成广泛的难治性芳香异种生物。 Rojek(2003)已证明,Phanerochaete chrysosporium ATCC 34541具有从溶液中去除40-50%NOM的能力,但是,这主要是由于吸附和部分与代谢相关的活性。因此,本研究进一步研究了通过选择的白腐真菌对NOM废物的生物修复。金黄色葡萄球菌似乎优先去除了非常疏水的酸(VHA)馏分,因此对于具有高比例的疏水性含量(以及如此高的颜色和特定的紫外线吸收率(SUVA))的NOM制剂最为有效。在三种具有不同C∶N比的生长培养基中,金黄色葡萄球菌对NOM的脱色程度遵循趋势:Waksman(C∶N = 6)> 1。 Fahy(C:N = 76)& Fujita培养基(C:N = 114),因此C:N比率越低,NOM去除量越大。这与Rojek(2003)的发现一致,后者使用了不同的NOM制剂,并证明NOM的去除随着C:N比的降低而增加(1.58-15.81)。由于用金黄色葡萄球菌ATCC 34541去除NOM的几率很低,并且几乎没有发生生物降解,因此将该生物与金黄色葡萄球菌ATCC 24725菌株,云芝Trametes ATCC 7731和三株酵母菌(任意命名为1、2和3的酵母菌种)进行了比较。 )。杂色锦葵(T. versicolor)去除率最高(59%),这在很大程度上归因于降解,而金黄色葡萄球菌(P. chrysosporium)和乳酸菌这两种菌株对NOM的去除主要是由于吸附所致,如棕褐色的深褐色所示。生物质。酿酒酵母1、2和3分别去除了12%,61%和23%的颜色。虽然酿酒酵母。 2号具有与杂色丁香相似的高减色性,具体去除值差异显着:0.055与0.089 mg NOM / mg生物质相比。如高性能尺寸排阻色谱法(HPSEC)所示,金黄色葡萄球菌两个菌株分泌的木质素分解酶水平低均与生物降解法去除NOM程度低相对应。杂色木霉获得的高NOM去除归因于木质素分解酶(特别是漆酶)的活性。 NOM的去除归因于高分子量化合物的分解,形成了一系列低分子量物质,然后极有可能被杂色丁香利用。与在30oC下生长的那些相比,在36oC下杂色云杉培养物的生长引起酚氧化酶活性的抑制或变性。两种培养物中LiP的活性均较低,表明该酶可能在NOM去除中没有太大作用。在30oC时,较高的MnP和Lac活性水平可导致NOM去除率更高(73%对59%),因此可裂解酚部分中的芳环,共轭和C-Cβα键,以及催化烷基芳基NOM结构中的断裂。在Waksman培养基中以较高的初始葡萄糖(5 g / L cf. 2 g / L)培养的杂色丁香导致木质素分解酶活性降低和NOM去除率降低(颜色减少减少25%),这可能是由于优先使用葡萄糖超过NOM作为碳源。 NOM去除量(去除的mg)随NOM浓度的增加而线性增加,最高达到600 mg C / L(62 mg(A446); 31 mg(A254)),在此之上去除量显着降低。这种趋势与总的木质素分解酶活性增加相吻合,其中Lac的水平增加至600 mg C / L NOM,尽管MnP在整个范围内逐渐降低,而LiP仅在100和300 mg C / L NOM时检测到。因此,通过杂色红锥菌从溶液中去除NOM与高氧化酶活性,特别是漆酶的氧化酶活性有关。漆酶是杂色丁香和演绎过程中分泌的主要细胞外酶。,在NOM移除中发挥了重要作用。确定在添加有4.5 g / L麦麸加0.5%Tween 80的Waksman培养基中培养的杂色丁香的分泌Lac活性的最佳温度为50oC。确定了愈创木酚和NOM的Lac活性的最佳pH为pH 4.0-4.5。尽管最佳酶活性发生在50oC,但是建议将30oC用于酶促去除NOM,因为如果认为NOM去除过程在高温下长时间运行,则酚氧化酶活性可能会降低。尽管搅拌导致明显的酶变性,但连续搅拌的发酵比偶尔搅拌的发酵(在130 rpm和30oC下每6小时搅拌30分钟)能更快地促进酶活性,因为它可以提供更好的传质效果。但是,在持续的发酵过程中,持续搅拌似乎对真菌的生长和酶的产生有不利影响。与LiP和MnP活性相比,在没有NOM的情况下在改良的Waksman培养基中添加4.5 g / L麦麸可导致Lac活性高产,显示出其作为漆酶诱导剂的巨大潜力。仅在培养基中添加吐温80会导致Lac活性略有改善;然而,由于麦麸的存在,导致LiP,MnP和Lac活性显着增加。与不添加补给品(12 mg(或)的培养物相比,将NOM与两种补品一起添加到杂色云杉培养物中时,其导致Lac活性显着降低,但LiP和MnP活性增加,并且NOM去除率没有改善。 61%)比照15 mg(或73%)的100 mg C / L,然后校正麦麸的颜色和吸附。
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