首页> 外文会议>International conference on remediation of contaminated sediments >EFFECT OF SUPPLEMENTARY ORGANIC CARBON SOURCEAND ELECTRON ACCEPTOR ON THE REMOVAL OF2,4-DICHLOROPHENOXYACETIC ACID IN SLURRY BIOREACTORS
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EFFECT OF SUPPLEMENTARY ORGANIC CARBON SOURCEAND ELECTRON ACCEPTOR ON THE REMOVAL OF2,4-DICHLOROPHENOXYACETIC ACID IN SLURRY BIOREACTORS

机译:补充有机碳源和电子受体对污泥生物反应器中2,4-二氯苯氧乙酸的去除作用

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Ad situ remediation techniques appear as an interesting alternative for thetreatment of polluted solid matrices that are not amenable to in situ remediation techniques,such as sediments and soils characterized by high contents of clay and organicmatter coupled to low hydraulic conductivity and permeability. In this work, the removalof 2,4-D from a model, heavy solid matrix was evaluated in lab-scale slurry bioreactorsunder both aerobic and anaerobic (sulfate-reducing) conditions. Also, the effect of anadditional carbon source (sucrose) was assessed.A model solid matrix (48% clay, 4% organic matter) was sterilized and contaminatedwith a high dose of 300 mg 2,4-D/kg dry matrix. The polluted matrix was treated inboth aerobic and sulfate-reducing slurry bioreactors (SB-A and SB-SR, respectively),with and without 1 g/L sucrose. Each type of SB received a seed (20% v/v) acclimated to2,4-D from aerobic and sulfate-reducing continuous, complete mix reactors. In this study,aerobic conditions were more favourable for the degradation of 2,4-D in terms of theoverall removal efficiency (93%, 15 days treatment), compared to 25% under sulfatereducingconditions. However, the specific removal rate of SB-SR was significantlyhigher (ranging between 10-13 mg 2,4-D/(mg VSS seed.day)) than that in SB-A (2.7 mg2,4-D/(mg VSS seed.day)). This difference was ascribed to the fact that the VSS contentof the aerobic seed was much higher than the corresponding to the sulfate-reducinginoculum. The effect of the sucrose amendment on 2,4-D removal depended on theelectron acceptor used: aerobic removal was not affected by the sucrose supplementation,whereas the removal in SB-SR receiving sucrose was higher than in units withoutsucrose. These results could indicate different degradative pathways for aerobic andanaerobic conditions, as well as the existence of co-metabolism amongst a consortium ofmicroorganisms in the sulfate-reducing reactors. Yet, SB-SR without sucrose still showedan important 2,4-D removal (up to 18%) suggesting that 2,4-D could be used as substrate.The 2,4-D-clastic bacteria were present in all reactors dur ing the incubation: aerobic2,4-D-clastic bacteria ranged between 6 to 8 logs, whereas the sulfate-reducing 2,4-Dclasticpopulation ranged between 5 to 7 logs. Overall, the slurry bioreactor ex-situ bioremediationtechnique seems to be an effective alternative for the treatment of difficultsediments and soils (characterized by a fine texture and high contents of organic matter)polluted with agrochemicals.
机译:原位修复技术似乎是一种有趣的替代方法。 处理不适合原位修复技术的被污染的固体基质, 例如以高含量的粘土和有机物为特征的沉积物和土壤 物质与低水力传导性和渗透性有关。在这项工作中,去除 模型中2,4-D的浓度,在实验室规模的浆料生物反应器中评估了重固体基质 在有氧和厌氧(硫酸盐还原)条件下均可使用。另外, 评估了其他碳源(蔗糖)。 对模型固体基质(48%的粘土,4%的有机物)进行了灭菌和污染 高剂量的300 mg 2,4-D / kg干基质。被污染的基质在 需氧和减少硫酸盐的浆液生物反应器(分别为SB-A和SB-SR), 有和没有1 g / L蔗糖。每种类型的SB都接受了适应(20%v / v)的种子 来自需氧和硫酸盐还原的连续,完整混合反应器的2,4-D。在这项研究中, 有氧条件对2,4-D的降解更有利,因为 总体去除效率(93%,处理15天),相比之下,硫酸盐还原处理的去除效率为25% 情况。但是,SB-SR的比去除率显着 比SB-A(2.7 mg)高(介于10-13 mg 2,4-D /(mg VSS种子。天)之间) 2,4-D /(mg VSS种子。天)。这种差异归因于以下事实:VSS含量 好氧种子的含量比相应的硫酸盐还原剂要高得多 接种物。蔗糖修正剂对2,4-D去除的作用取决于 使用的电子受体:需氧去除不受蔗糖补充的影响, 而接受蔗糖的SB-SR的去除率高于没有蔗糖的单元 蔗糖。这些结果可能表明有氧和有氧运动的不同降解途径。 厌氧条件,以及在一个 硫酸盐还原反应器中的微生物。然而,不含蔗糖的SB-SR仍显示 重要的2,4-D去除率(高达18%)表明2,4-D可用作底物。 孵育过程中,所有反应器中均存在2,4-D碎屑细菌:好氧的 2,4-D碎屑细菌的范围在6至8个对数之间,而硫酸盐还原的2,4-D碎屑细菌 种群数量介于5到7个对数之间。总体而言,浆料生物反应器的异位生物修复 技术似乎是治疗困难的​​有效替代方法 沉积物和土壤(以质地优良,有机物含量高为特征) 被农药污染。

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