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Abstract and Figures

Soil balls containing the so-called effective microorganisms (EM) have been applied to improve water quality of small ponds, lakes, and streams worldwide. However, neither the physical conditions facilitating their proper application nor the diversity of microbial community in such soil balls have been investigated. In this study, the application of 0.75 % of hardener to the soil balls exerted almost neutral pH (pH 7.3) which caused up to a fourfold increased hardness of the soil ball. Moreover, the 0.75 % of hardener in the soil ball also improved the water quality due to a significant reduction in dissolved oxygen, total phosphorus, and total nitrogen contents. Metagenomic analysis of the microbial community in the soil ball with 0.75 % hardener was compared with control (traditional soil ball) through next-generation sequencing. The traditional soil ball microbial community comprised 96.1 % bacteria, 2.7 % eukaryota, and 1 % archaea, whereas the soil ball with 0.75 % hardener comprised 71.4 % bacteria, 27.9 % eukaryota, and 0.2 % viruses. Additionally, metagenomic profiles for both traditional and improved soil balls revealed that the various xenobiotic biodegradation, such as those for caprolactam, atrazine, xylene, toluene, styrene, bisphenol, and chlorocyclohexane might be responsible for organic waste cleanup.
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SELECTEDPAPERS FROMTHE 2ND CONTAMINATED LAND, ECOLOGICAL ASSESSMENTAND REMEDIATION(CLEAR 2014) CONFERENCE: ENVIRONMENTALPOLLUTION AND REMEDIATION
An improved effective microorganism (EM) soil ball-making
method for water quality restoration
Gun-Seok Park
1
&Abdur Rahim Khan
1
&Yunyoung Kwak
1
&Sung-Jun Hong
1
&
ByungKwon Jung
1
&Ihsan Ullah
2
&Jong-Guk Kim
3
&Jae-Ho Shin
1
Received: 9 June 2015 /Accepted: 15 October 2015 /Published online: 24 October 2015
#Springer-Verlag Berlin Heidelberg 2015
Abstract Soil balls containing the so-called effective micro-
organisms (EM) have been applied to improve water quality
of small ponds, lakes, and streams worldwide. However, nei-
ther the physical conditions facilitating their proper applica-
tion nor the diversity of microbial community in such soil
balls have been investigated. In this study, the application of
0.75 % of hardener to the soil balls exerted almost neutral pH
(pH 7.3) which caused up to a fourfold increased hardness of
the soil ball. Moreover, the 0.75 % of hardener in the soil ball
also improved the water quality due to a significant reduction
in dissolved oxygen, total phosphorus, and total nitrogen con-
tents. Metagenomic analysis of the microbial community in
the soil ball with 0.75 % hardener was compared with control
(traditional soil ball) through next-generation sequencing. The
traditional soil ball microbial community comprised 96.1 %
bacteria, 2.7 % eukaryota, and 1 % archaea, whereas the soil
ball with 0.75 % hardener comprised 71.4 % bacteria, 27.9 %
eukaryota, and 0.2 % viruses. Additionally, metagenomic pro-
files for both traditional and improved soil balls revealed that
the various xenobiotic biodegradation, such as those for cap-
rolactam, atrazine, xylene, toluene, styrene, bisphenol, and
chlorocyclohexane might be responsible for organic waste
cleanup.
Keywords Biodegradation .Effective microorganisms .
Metagenome .Microbial community .Soil ball .Water quali ty
Introduction
Microbial biotechnology is the most recent approach to waste-
water treatment and is essential for protecting human health
and the environment (Mielczarek et al. 2013). In order to
guarantee the optimal operation using the effective microor-
ganism technology, it is very important to understand the
structure, function, and microbial community dynamics in-
volved in these approaches (Zakaria et al. 2010). Soil balls
have been used as carrier to immobilize effective microorgan-
isms for the remediation of contaminated water environment
(Ekpeghere et al. 2012). The concept of Beffective
microorganisms^(EM) was introduced by Dr. Teruo Higa,
and since then, EMs became an important part of natural
farming (Higa 1998). Those microbes are selected based on
their functions as fixation of atmospheric nitrogen, decompo-
sition of organic wastes and residues, suppression of soil-
borne pathogens, recycling and increased availability of plant
nutrients, solubilization of insoluble nutrient sources, and deg-
radation of toxicants including pesticides (Higa and Parr
1994). EM is co-cultures of naturally occurring beneficial mi-
croorganisms, and it is widely applied as inoculants to soil,
water and plants for the improvement of soil and water quality,
as well as for plant growth and crop yield (Grover et al. 2011;
Javaid 2010). Soil balls with EM can be a good alternative for
stream water treatment in eco-friendly environments, but there
have been no report on their physicochemical properties and
Responsible editor: Robert Duran
Electronic supplementary material The online version of this article
(doi:10.1007/s11356-015-5617-x) contains supplementary material,
which is available to authorized users.
*Jae-Ho Shin
jhshin@knu.ac.kr
1
School of Applied Bioscience, Kyungpook National University,
Daegu 702-701, Republic of Korea
2
Institute of Biotechnology and Genetic Engineering, The University
of Agriculture, Peshawar, Pakistan
3
School of Life Sciences and Biotechnology, Kyungpook National
University, Daegu 702-701, Republic of Korea
Environ Sci Pollut Res (2016) 23:11001107
DOI 10.1007/s11356-015-5617-x
Content courtesy of Springer Nature, terms of use apply. Rights reserved.
... A study by Park et al. [31] also sought to improve the quality of water of streams by studying the physical conditions and the diversity of the microorganisms in the water. Park et al. [31] made use of soil balls that contained EM and found that the quality of water was improved by hardener soil balls as it significantly reduced the dissolved oxygen, total nitrogen, and total phosphorus components. ...
... A study by Park et al. [31] also sought to improve the quality of water of streams by studying the physical conditions and the diversity of the microorganisms in the water. Park et al. [31] made use of soil balls that contained EM and found that the quality of water was improved by hardener soil balls as it significantly reduced the dissolved oxygen, total nitrogen, and total phosphorus components. The composition of the hardener soil ball and traditional soil ball microbial community was found to differ with the hardener soil balls comprising 0.2% viruses, 27.9% eukaryote, and 71.4% bacteria while the traditional soil ball consisted of 1% archaea, 2.7% eukaryote, and 96.1% bacteria. ...
... An assessment of pathways that support the xenobiotic degradation was also performed. An examination at the metagenomic profiles for both the hardened soil and the Contaminated harbor sediments Loess balls containing EM Acetic acid, propionic acid, valeric acid [14] Artificial lake Solution COD, TN, TP, TSS, turbidity [47] Synthetic polluted water Solution NH 3 -N, TP, COD [19] Stream water Soil balls containing EM TP, TN, xenobiotic [31] Artificial river water Mudballs containing EM COD, TSS [23] Safwat and Matta Journal of Engineering and Applied Science (2021) 68:48 Page 4 of 12 traditional soils showed that a certain percentage of the organic waste cleanup was due to the xenobiotic biodegradation [31]. Mudballs containing EM were also applied by a study by Nugroho et al. [23] to examine the impact that temperature had on COD and TSS removal. ...
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... Studies have shown that EM can positively influence decomposing organic matter in the environment by facilitating nitrification, denitrification, ammonification, and other processes, improving water and soil quality and maintaining microbial ecological equilibrium (Safwat and Matta, 2021). As a probiotic, it has been widely applied in aquaculture (Abdel-Aziz et al., 2021), organic agriculture (Mwegoha, 2012), wastewater treatment (Park et al., 2016), and other fields and has been demonstrated to have no adverse effects on fish, humans, and environmental conditions (Abdel-Aziz et al., 2020). At present, EM has been adopted by over 100 countries worldwide, not on an experimentation basis but for commercial use as well as environmental management (Olle and Williams, 2013). ...
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The bacterial diversity assessed from clone libraries prepared from rRNA (two libraries) and ribosomal DNA (rDNA) (one library) from polychlorinated biphenyl (PCB)-polluted soil has been analyzed. A good correspondence of the community composition found in the two types of library was observed. Nearly 29% of the cloned sequences in the rDNA library were identical to sequences in the rRNA libraries. More than 60% of the total cloned sequence types analyzed were grouped in phylogenetic groups (a clone group with sequence similarity higher than 97% [98% for Burkholderia and Pseudomonas-type clones]) represented in both types of libraries. Some of those phylogenetic groups, mostly represented by a single (or pair) of cloned sequence type(s), were observed in only one of the types of library. An important difference between the libraries was the lack of clones representative of the Actinobacteria in the rDNA library. The PCB-polluted soil exhibited a high bacterial diversity which included representatives of two novel lineages. The apparent abundance of bacteria affiliated to the beta-subclass of the Proteobacteria, and to the genus Burkholderia in particular, was confirmed by fluorescence in situ hybridization analysis. The possible influence on apparent diversity of low template concentrations was assessed by dilution of the RNA template prior to amplification by reverse transcription-PCR. Although differences in the composition of the two rRNA libraries obtained from high and low RNA concentrations were observed, the main components of the bacterial community were represented in both libraries, and therefore their detection was not compromised by the lower concentrations of template used in this study.
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