Georgaki I, Tsamoukas A, Sakkas N, Ververidis F, Trantas E, Kyriacou A, Lasaridi K E, Manios T
School of Agricultural Technology, Technological Educational Institute of Crete, Stavromenos, Heraklion, 71004, Crete, Greece.
Water Environ Res. 2009 Jan;81(1):5-12. doi: 10.2175/106143007x221229.
Wastewater sludge and wood chips were used as feedstock for the construction of two piles, Pile I ("PI") and Pile II ("PII"), at a ratio of 1:1 and 1:2 v/v, respectively. Each pile was originally 1.3-m high, 2.0-m wide, and approximately 9.0-m long. A mechanical turner was used to turn the two windrows every 1 to 2 weeks. Three 500-mL-volume glass funnels were inverted and introduced into each pile: one in the core (named, respectively, "PIC" and "PIIC"), one at the top ("PIT" and "PIIT"), and one at the side ("PIS" and "PIIS"). Every 2 to 3 days, gas samples were collected using gas-tight syringes and analyzed in a gas chromatograph determining carbon dioxide (CO2) and methane (CH4) concentrations. An average gas concentration value between turnings was calculated and a two-way analysis of variance test was used to determine the significance of the differences between piles and pile location, followed by a Post Hoc Tukey test. During the thermophilic period, the mean CO2 concentration in PIC was 103 mL/L, 65 mL/L in PIT, and 24 mL/L in PIS, whereas, for PII, these values were 102mL/L, 59 mL/L, and 24 mL/L, respectively. The mean CH4 concentration between turnings in PIC was 9.2 mL/L, 1.9 mL/L in PIT, and 0.9 mL/L in PIS, whereas, for PII, the corresponding values were 6.4 mL/L, 0.4 mL/L, and 0.1 mL/L. For methane, there were no significant differences between these mean values, not only between the same placement in different piles, but also between different placements and different piles. This is probably due to the relatively frequent turnings (10 turnings during a period of 100 days), which did not allow the development of more anaerobic pockets in PI than in PII, indicating that both piles had similar greenhouse gas impacts. Results for carbon dioxide were similar in both piles, with some differentiation appearing between the core and top placements compared to the side placement. Reduction of the decomposition rate further from the core and a typical windrow chimney effect (gases from the core flowing through the top) explain this similarity between placements. The similarity between piles can be explained by the similar amounts of easily decomposable organic matter found in both piles, indicating that the effect of the bulking agent ratio on the concentration of gases within the pile was not significant.
将污水污泥和木屑用作原料,分别以1:1和1:2的体积比构建了两堆,即堆I(“PI”)和堆II(“PII”)。每堆最初高1.3米、宽2.0米、长约9.0米。使用机械翻堆机每隔1至2周对两条堆肥条垛进行翻堆。将三个500毫升的玻璃漏斗倒置并插入每堆中:一个在堆芯(分别命名为“PIC”和“PIIC”),一个在顶部(“PIT”和“PIIT”),一个在侧面(“PIS”和“PIIS”)。每隔2至3天,使用气密注射器采集气体样本,并在气相色谱仪中分析,以测定二氧化碳(CO₂)和甲烷(CH₄)的浓度。计算翻堆期间的平均气体浓度值,并使用双向方差分析测试来确定堆与堆位置之间差异的显著性,随后进行事后Tukey检验。在嗜热期,PIC中的平均CO₂浓度为103毫升/升,PIT中为65毫升/升,PIS中为24毫升/升;而对于PII,这些值分别为102毫升/升、59毫升/升和24毫升/升。PIC中翻堆期间的平均CH₄浓度为9.2毫升/升,PIT中为1.9毫升/升,PIS中为0.9毫升/升;而对于PII,相应的值分别为6.4毫升/升、0.4毫升/升和0.1毫升/升。对于甲烷,这些平均值之间没有显著差异,不仅在不同堆中的相同位置之间,而且在不同位置和不同堆之间。这可能是由于翻堆相对频繁(在100天内翻堆10次),这使得PI中比PII中没有形成更多的厌氧区,表明两堆具有相似的温室气体影响。两堆中二氧化碳的结果相似,与侧面位置相比,堆芯和顶部位置之间出现了一些差异。从堆芯进一步降低分解速率以及典型的条垛烟囱效应(来自堆芯的气体流经顶部)解释了这些位置之间的这种相似性。堆之间的相似性可以通过两堆中发现的易分解有机物数量相似来解释,这表明膨松剂比例对堆内气体浓度的影响不显著。