J. Microbiol. Biotechnol. (2012), 22(10), 1330–1335 http://dx.doi.org/10.4014/jmb.1205.05006 First published online July 24, 2012 pISSN 1017-7825 eISSN 1738-8872

Characterization of Microbial Community in the Leachate Associated with the Decomposition of Entombed Pigs

Yang, Seung-Hak1†, Sun Hwa Hong2†, Sung Back Cho1, Joung Soo Lim2, Sung Eun Bae3, Heekwon Ahn4, and Eun Young Lee2*

1Animal Environment Division, National Institute of Animal Science, R.D.A., Gyeonggi 441-706, Korea 2Department of Environmental and Energy Engineering, Suwon University, Gyeonggi 445-743, Korea 3Women’s Health, School of Medicine, Hodgkin Building, King’s College London, London SE1 1UL, United Kingdom 4Department of Animal Biosystems Science, Chungnam National University, Daejeon 305-764, Korea Received: May 4, 2012 / Revised: June 19, 2012 / Accepted: June 20, 2012

Foot and mouth disease (FMD) is one of the acute later stages. Therefore, these results indicate that the infectious diseases in hoofed and even-toed mammals, decomposition of pigs continues for a long period of time including pigs, and it occurs via acute infection by and leachate is created continuously during this process. It Aphthovirus. When FMD is suspected, animals around the is known that leachate can easily flow into the neighboring location of origin are typically slaughtered and buried. environment, so a long-term management plan is needed Other methods such as rendering, composting, and in burial locations for FMD-infected animals. incineration have not been verified in practice in Korea. Keywords: Denaturing gradient gel electrophoresis (DGGE), After the FMD incident, the regular monitoring of the foot and mouth disease (FMD), leachate, microbial community microbial community is required, as microorganisms greatly modify the characteristics of the ecosystem in which they live. This is the result of their metabolic activities causing chemical changes to take place in the Foot and mouth disease (FMD) is an acute infectious surrounding environment. In this study, we investigated disease caused by Aphthovirus, which belongs to the changes in the microbial community during a 24 week family Picornaviridae. The foot and mouth disease virus period with DNA extracts from leachate, formed by the (FMDV) is a prototypical member of the genus Aphthovirus. decomposition of buried pigs at a laboratory test site, using There are seven FMDV serotypes; A, O, C, SAT-1, SAT-2, denaturing gradient gel electrophoresis (DGGE) with a SAT-3, and Asia-1 [20]. FMD is highly contagious and can genomic DNA. Our results revealed that Bacteroides coprosuis, infect most types of Artiodactyla, including cattle, sheep, which is common in pig excreta, and Sporanaerobacter pigs, and even wild animals such as water buffalo [4]. The acetigenes, which is a sulfur-reduced microbe, were mortality rate of FMD is less than 5%, but it reduces the continuously observed. During the early stages (0~2 value of farm animals owing to consequential growth and weeks) of tissue decomposition, Clostridium cochlearium, movement disorders. In addition, it has been reported that Fusobacterium ulcerans, and Fusobacterium sp., which whereas adult animals typically may die as a result of the are involved in skin decomposition, were also observed. In infection, young animals normally die as a result of addition, various microbes such as Turicibacter sanguinis, myocardial damage [6, 21, 26]. There are several factors Clostridium haemolyticum, Bacteroides propionicifaciens, that make FMD a real and common threat to farmers and a and Comamonas sp. were seen during the later stages national food supply. The primary factors can be described (16~24 weeks). In particular, the number of existing as FMD’s high contagiousness, wide geographical microbial gradually increased during the early distribution, broad host range, ability to establish carrier stages, including the exponential phase, decreased during status, antigenic diversity leading to poor cross-immunity, the middle stages, and then increased again during the and the relatively short duration of immunity. It has been noted that, because of these factors, facilities and programs *Corresponding author are insufficient to adequately control an outbreak of FMD Phone: +82-31-220-2614; Fax: +82-31-220-2533; E-mail: [email protected] [22]. Therefore, when FMD is suspected, animals around †These two authors contributed equally to this work and should be the suspected locations have movement restrictions considered co-first authors. imposed and animals in the place of origin are slaughtered CHARACTERIZATION OF MICROBIAL COMMUNITY IN THE LEACHATE OF ENTOMBED PIGS 1331 and buried. These methods are utilized in the absence of MATERIALS AND METHODS effective treatment options. Large amounts of leachate and seriously unpleasant odors A Designed Lab-Scale Experiment are often generated in the burial areas by decomposing A laboratory pig carcass decomposition testing site was designed FMD-infected animals. Leachate starts to be produced based on animal mortality mass burial protocols developed by the approximately one week after burial. Leachate contains a Korean Ministry for Food, Agriculture, Forestry and Fisheries. In order to mimic the decomposition of pig carcasses at real burial large number of organisms, and contaminates soil and th sites, lab-scale systems scaled down to about 1/7 normal size were groundwater through the basement layer [23]. Contaminated used (Fig. 1). The area volume was around 0.67 m3 with a 1.4 m soil and underground water make for a serious environmental width, 0.54 m length, and 0.85 m height. A pig carcass of around issue with potential risks for the immediately local 115 kg in weight was placed on top of a soil and quick lime layer ecosystem as well as for neighboring areas. A large (7.5 cm soil + 0.75 cm quicklime + 7.5 cm soil). This was followed number of animal burials took place following a serious with additional layers of soil and quicklime (7.5 cm soil + 0.75 cm outbreak of FMD in Korea in November 2010. Serious quicklime + 7.5 cm soil). Approximately 120 kg of soil weight was problems resulting from leachate have not yet been laid on top of the upper layers of the soil and quicklime so as to reported; however, it would be prudent to prepare for the prevent the carcasses abdomen from swelling and distending. All three replicate containers were subjected to a constant-temperature possibility that contamination has already occurred and o may continue to occur from these, or future, burials. room at 35 C in order to increase the reaction rate of the decomposition of the pig carcass. Leachate samples were collected The regular environmental monitoring of burial areas from each of the three containers on a weekly basis for a month, importantly includes the monitoring of microbe changes and then monthly for five months. The collected leachate samples according to their correlation with pollution sources [18]. were analyzed using denaturing gradient gel electrophoresis (DGGE) Recently, various research techniques to study the microbial in order to examine microbial community variations during the community, but not the individual microbe, have been decomposition of the pig carcass. developed in the microbial ecosystem [14, 17, 25]. Amongst these, molecular biological methods are known to be Experimental Methods accurate, rapid, and well documented by previous researchers Total genomic DNA was extracted from the leachate of the [1,8,9,11,13-17, 24, 27]. In particular, denaturing gradient containers using a BIO101 kit (MB Bio, USA). Next, a fragment of gel electrophoresis (DGGE), using urea or formamide as a the variable V3 region of 16S rDNA was amplified by PCR primers denaturant, is a relatively simple method and it can compare 341f-GC (5'-CGC CCG CCG CGC GCG GCG GGC GGG GCG GGG GCA CGG GGG GCC TAC GGG AGG CAG CAG-3') and microbes numerically and quantitatively. 907r (5'-CCC CGT CAA TTC ATT TGA GTT-3'). The PCR reaction Therefore, in this study, we regularly monitored microbes was performed in a thermal cycler system (TaKaRa PCR Thermal using the DGGE method, with genomic DNA from Cycle, Japan) at 95oC for 5 min, followed by 28 denaturation cycles leachate formed by the decomposition of entombed pigs at at 95oC, annealing at 60oC for 30 s, and extension at 72oC for 30 s. a laboratory test site mimicking methods used for pig A final extension was performed at 72oC for 5 min. DGGE analysis slaughter and burial after FMD discovery, in order to better was conducted using a DCode system (Bio-Rad, USA). Samples of understand features of the microbial community in the PCR product (20 µl) were loaded onto 6% (w/v) polyacrylamide field. gels in 1× TAE buffer. The polyacrylamide gels were made with a

Fig. 1. Schematic diagram of animal mortality mass burial protocols (A) and photograph of the lab-scale system (B). 1332 Yang et al. linear denaturing gradient ranging from 35% denaturant at the top of the gel to 70% denaturant at the bottom. The electrophoresis was run at 50 V and 60oC for 14 h to get a clear image. The gel was analyzed with UVI-band pattern (UVI Soft, UVI-band version 12.14, UK). In addition, typically 19 bands were cut from the DGGE fingerprint to extract DNA and then PCR was conducted with 341f and 907r primers. The full-length sequence of amplified 16S rDNA genes was deposited in the GenBank database of the National Center for Biotechnology Information. The sequence was submitted to the Advanced Basic Local Alignment Search Tool (BLAST) search program to identify the sequences of any closely related organisms. The related sequences were preliminarily aligned with Clustal W, and manually adjusted with the aid of the Clustal X program. Phylogenetic analysis was performed using Bioedit, and the phylogenetic trees were determined using the neighbor-joining method. A phylogenetic tree was constructed with the MEGA4 program [1, 9].

RESULTS AND DISCUSSION

Phylogenetic features are shown in Fig. 2, and species in each period are illustrated in Table 1. A phylogenetic tree indicates whether microbes in the burial area are connected to other groups. Specifically, 19 bands on DGGE gel were cut and then isolated; however, three of the 19 bands were not isolated, with the rest shown in Fig. 2. The most clear band 1 (G1) was Bacteroides coprosuis and was close to band 10 (G10) and band 16 (G16) (UPGMA and maximum-parsimony with bootstrap values of 100% and 99%, respectively). Most bands, excluding bands 3 (G3), 4 (G4), and 17 (G17), were placed in similar locations. The microbes revealed in this study were divided into three groups depending on their existing stages, such as (i) present in all stages, (ii) present only in the early stages, and (iii) present only in a later stage. Our results showed that G1, G2, G4, G10, and G13 were detected in every sample after the event of pig burial. G1 and G10 were very similar to Bacteroides coprosuis, separated from the pig excreta hole with a 99% similarity. G2 was similar to Sporanaerobacter acetigenes known as a sulfur-reduced microbe that oxidizes acetate and succinates organic matter. A large amount of acetate (10,000 ppm) and succinate Fig. 2. Similarity analysis based on DGGE fingerprints (A) band pattern, and a phylogenetic tree illustrating the relationships (5,000 ppm) was produced in the leachate during the amongst the closest relatives in the GenBank database (B). decomposition, and malodorous substances affiliated with sulfur were formed in animal excreta, so Sporanaerobacter anaerobic environment. An artificial anaerobic environment acetigenes production seemed to be continuous. G4 was was maintained inside the reactor, so this could have isolated as an uncultured bacterium. G13 was observed in induced the appearance of Acidovorax sp. In addition, if a every sample but too blurred to be isolated on DGGE gel. large amount of ammonia is generated for 2 weeks during G3, G5, G6, and G11 were observed until 2 weeks after the decomposition, this could also have induced the burial. The bands were isolated as Acidovorax sp. (G3), appearance of nitrification germs in the early stages. In Tepidanaerobacter syntrophicus (G5, 6), and Clostridium addition, Tepidanaerobacter syntrophicus breaks down cochlearium (G11). Acidovorax sp. is a denitrifying into alcohol and lactate under anaerobic conditions [19]. bacterium known to convert nitric acid or nitrous acid to Lactate, succinate, and ethanol are generally generated nitrogen gas then released in the air [12] and it thrives in an when organic matter is used as the final electron acceptor CHARACTERIZATION OF MICROBIAL COMMUNITY IN THE LEACHATE OF ENTOMBED PIGS 1333

Table 1. Dominant species of leachate associated with the decomposition of entombed pigs based on 16S rDNA sequences. Band Incubation time (Week, W) Bacteria species name 0W 1W 2W 3W 4W 8W 12W 16W 24W G1 Bacteroides coprosuis (+) (+) (+) (+) (+) (+) (+) (+) (+) G2 Sporanaerobacter acetigenes (+) (+) (+) (+) (+) (+) (+) (+) G3 Acidovorax sp. (+) (+) (+) G4 Uncultured bacterium (+) (+) G5 Tepidanaerobacter syntrophicus (+) (+) G6 Tepidanaerobacter syntrophicus (+) (+) (+) (+) (+) G7 Fusobacterium ulcerans (+) G8 Fusobacterium sp. (+) G9 Fusobacterium ulcerans (+) (+) G10 Bacteroides coprosuis (+) (+) (+) (+) (+) (+) (+) (+) (+) G11 Clostridium cochlearium (+) (+) (+) G12 Tepidanaerobacter syntrophicus (+) (+) G13 NS (+) (+) (+) (+) (+) (+) (+) (+) (+) G14 Turicibacter sanguinis (+) (+) G15 Clostridium haemolyticum (+) (+) G16 Bacteroides propionicifaciens (+) (+) G17 Comamonas sp. (+) (+) G18 NS (+) (+) G19 NS (+) (+) Number of appearance bacteria 8 9 12 5 4 5 5 10 8 *NS, not sequenced. for fermentation. Therefore, Tepidanaerobacter syntrophicus to be involved in the early stages of the decomposition, seemed to appear in the early stages during the gravest with the nitrogen source considered to originate from decomposition. Clostridium cochlearium is a representative protein. Comamonas sp. was expected to participate in anaerobe of Clostridium sp. It is observed in septicemia denitrification in the burial area in the later stages. and able to cause skin necrosis. Clostridium cochlearium The number of microbe species in all samples increased also appeared in the early stages. continuously until the 2nd week and then decreased until In particular, the G7, G8, and G9 bands were very thick the 12th week, and then increased again in the 16th to the in the 2nd week’s sample, but very dim in the 12th, 16th, and 24th weeks with new species being observed. Acinetobacter 24th weeks. These were isolated as Fusobacterium ulcerans sp., Arthrobacter cumminsii, Bacillus sp., Brevibacterium and Fusobacterium sp., which are reported to be related to sp., Pseudomonas aeruginosa, and Serratia marcescens skin necrosis and septicemia [3]. Therefore, these latter were reported to be possibly present during the two seemed to participate in the decomposition of the skin, decomposition of pigs [11]. However, in the latter results, which was most active in the 2nd week of burial. it was considered that some microbes were derived from In the later stages (16th to 24th weeks), bands G14, G15, excreta (Bacteroides coprosuis, Turicibacter sanguinis, G16, G17, G18, and G19 were observed. G14 ~ G17 were and Comamonas sp.) and some from necrosed skin tissue isolated as Turicibacter sanguinis, Clostridium haemolyticum, (Clostridium cochlearium, Fusobacterium ulcerans, and Bacteroides propionicifaciens, and Comamonas sp., Fusobacterium sp.), whereas others were also related to a respectively, whereas G18 and G19 were not isolated. These foul smell (Sporanaerobacter acetigenes, Acidovorax sp., are also anaerobes and Turicibacter sanguinis is often found Bacteroides propionicifaciens, and Comamonas sp.). The in lagoons [16]. Clostridium haemolyticum is pathogenic results in the present paper seem to be different from and observed in dying animals. Bacteroides propionicifaciens previous studies. This is because in other studies the was previously isolated from the straw residues of methane microbes were collected from soil, whereas the microbes reactions to process farm waste [2] and seemed to appear in this study were collected from leachate. In addition, we as a result of the large amount of methane during the continuously observed microbes from pig excreta during decomposition. Comamonas sp. can be formed during an the experiment. In the case of a human, the body decomposes anaerobic process in pig excreta [27] and is known to from the first week after burial with the production of break down acetaldehydes [13]. In addition, Comamonas related microbes, followed by gases being generated by the sp. is a denitrifying bacterium [7]. Acidovorax sp. seemed decomposition of the organs expanding for three weeks. 1334 Yang et al.

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