Population Dynamics of Azotobacter sp., Azospirillum sp., Bacillus
subtilis, Talaromyces pinophilus, Trichoderma asperellum, and
Syncephalastrum racemosum in the Medium with Various Earthworm
Applications
Nur Ulina Warnisyah Sebayang
1
, Tengku Sabrina
1
, Abdul Rauf
1
, Mariani Sembiring
1
, Asmarlaili
Sahar
1
, and Erman Munir
2
1
Department of Agriculture, Universitas Sumatera Utara Padang BulanMedan, Indonesia 20155
2
Department of Math and Science, Universitas Sumatera Utara Padang BulanMedan, Indonesia 20155
Keywords: Earthworm, microorganism, population, dynamics.
Abstract: The quality of the biological fertilizer was based on the population of inoculated microorganism. The
important efforts made to increase the population and maintain the population of microorganisms during
storage was using the best carrier. The aim of this study was to measure the population dynamics of some
microbes due to the application of various types of earthworms in producing biofertilizer. The study was
conducted in Biology and Biotechnology Soil Laboratory, Department of Agriculture, Universitas Sumatera
Utara. The design used was a Factorial Randomized Block Design consisting of 2 factors. The first factor
was a type of earthworm with 4 treatments viz; without earthworm, anecic earthworms, endogeic
earthworms, and epigeic earthworms. The second factor was a type of microorganism inoculants with
6treatments, viz; Azotobacter sp., Azospirillum sp., Bacillussubtilis, Trichodermapinophilus, Talaromyces
asperellum, and Syncephalastrum racemosum. The results showed that there was a significant interaction
between the types of earthworms in influencing the population of each microorganisms in the medium. The
highest alteration of microbial population was found in Azotobacter sp. and Trichodermaasperellum. The
best type of earthworm that could be used on the inoculum medium was the epigeic earthworm.
1 INTRODUCTION
The use of organic fertilizers has been used to
reduce the use of chemical fertilizers. Development
of biofertilizer technology is being actively
conducted to resolve the limitations of biofertilizer
that is a relatively short storability thus inhibiting its
commercialization. Many studies have been done to
get the best carrier. Fungus phosphate-solvent
growth of 2.0x10
7
after 7 days of storage can be
maintained from wheat skin mixed with 20% (w / w)
perlite when compared to peat carrier, corn cobs +
20% (weight / weight) perlite and cow manure
compost with 20% (weight / weight) perlite(Wang,
2015).Increased proportion of carrier material
vermicast in improving the survival of microbes.
The results also showed that vermicasts can be used
as alternative carriers for Azotobacter chroococcum,
Bacillus megaterium and Rhizobium leguminosarum
(Sekar and Karmegam, 2015).
Earthworms have the ability as a vector of
microorganisms and the vermicast have
highavailability nutrient and population
ofmicroorganisms. Earthworm is an
organismcapable of selecting and increasing
thepopulation of microorganisms through
peptidesderived from its excretion. Digestive fluid of
earthworms released amino acids, sugars and
organic molecules from organic residues. Cellulotic
bacteria are present in the digestive canal and casts
of earthworms indicating that they live in the
digestive canal of earthworms and actively degrade
food containing cellulose (Suhartanti, 2013).
By using the role of the earthworm, a new
innovation can be found in biofertilizerproduction
(enriched product of vermicompost and some
microbial inoculant). The biovermi to be produced
must be investigated in advance to identified the
quality through the parameters of microbial
population observed for some time.
26
Sebayang, N., Sabrina, T., Rauf, A., Sembiring, M., Sahar, A. and Munir, E.
Population Dynamics of Azotobacter sp., Azospirillum sp., Bacillus subtilis, Talaromyces pinophilus, Trichoderma asperellum, and Syncephalastrum racemosum in the Medium with Various
Earthworm Applications.
DOI: 10.5220/0010073900260030
In Proceedings of the International Conference of Science, Technology, Engineering, Environmental and Ramification Researches (ICOSTEERR 2018) - Research in Industry 4.0, pages
26-30
ISBN: 978-989-758-449-7
Copyright
c
2020 by SCITEPRESS Science and Technology Publications, Lda. All rights reserved
The observed microbial population dynamics
indicate that the quality of the biofertilizer to be
developed in terms of both variation of earthworm
and microorganism and to know the fertilizer's
storage capacity. Therefore, it is necessary to know
the effect of calibrationvariation of earthworms and
microorganisms in organic compost carrier to know
the dynamics of the microbial population in order to
produce qualified biofertilizers that can be utilized
as an innovation and environmentally technology.
2 MATERIALS AND METHODS
2.1 Experimental Design
The experiment was conducted in Laboratory of
Biology and Biotechnology Soil,
AgriculturalFaculty, Universitas Sumatera Utara,
Medan, Indonesia.
The experiment used Factorial
Random Block Design with 2 factors with 2
replications, so this study gets 48 treatments
. The
first factor is type of earthworms with 4 stage of
treatments that are; without
earthworm (C
0
),
anecic earthworm (C
1
), endogeic earthworm (C
2
),
and epigeic earthworm (C
3
). The second factor is
type of microorganismwith 6 stage of treatments that
are; Azotobactersp. (M
1
), Azospirillumsp. (M
2
),
Bacillus subtilis(M
3
), Talaromycespinophilus(M
4
),
Trichodermaasperellumstrain G (M
5
), and
Syncephalastrumracemosumisolate VPCI 1857/11
(M
6
). Data wereanalyzed statistically by using
Analysis ofVariance (ANOVA) and then
following by Duncan Multiple Range Test
(DMRT) at 5 % level.
2.2 Experimental Pot Preparation
The experimental pot used was made of plastic with
size 19cm x 13cm x 9cm as figure 1.
Figure 1 : The Sketch of Experimental Pot.
2.3 Earthworm Preparation
Identification of earthworm was based on Blakmore
identification (Blakmore, 2002). The same weight of
each type earthworms was chosen for further
experiment. All selected earthworms soaked in
sterile water in order to remove its sewage so the
microbes on the digestive canal. Then they were
acclimatized in the laboratory with culture media
compost that has been sterilized.
2.4 Preparation of Inoculant Microbial
Azotobacter sp. and Azospirillum sp. were obtained
from the AgriculturalFaculty, Universitas Sumatera
Utara, Medan, Universitas Padjadjaran, Bandung.
Bacillus subtiliswas obtained from the Laboratory of
Institut Pertanian Bogor Culture Collection, Bogor,
Indonesia. Talaromycespinophilus was obtained
from the collection of Soil Biology Laboratory of
AgriculturalFaculty, Universitas Sumatera Utara,
Medanfrom potato plant (Sembiring, 2015). T.
Asperellum strain strain G and
Syncephalastrumracemosum isolates VPCI 1857/11
were obtained from a previous study (Sabrina, 2017)
derived from oil palm trunkchips and have been
identified. Multiplication of each isolate was carried
out using specific media such as Jensen medium for
Azotobacter sp., Okonmedium for
Azospirillumsp.,Pikovskayamedium to
Talaromycespinophilusand Bacillus subtilis.Potato
Dextrose Broth medium for
Trichodermaasperellumand
Syncephalastrumracemosum. After each isolate was
inoculated then incubated for 3-5 days, then
microbial population was calculated using colony
counter with the Pour Platedilution technique.
2.5 Preparation of Culture Media
Pot experiment of earthworm culture medium filled
with compost sterile as much as 400 gram and
covered with cloth net. Culture media regulated
moisture by adding water using hand sprayer.
2.6 Application of Microbes and
Earthworm
Each microbial was applied to a sterile culture
medium (compost sterile) of 10 mL and mixed
evenly. After 1 week of microbial application, the
earthworm application was performed with the same
individual weights selected and fed into the
experimental pot in accordance with the treatment
and then covered with a net cloth.
Population Dynamics of Azotobacter sp., Azospirillum sp., Bacillus subtilis, Talaromyces pinophilus, Trichoderma asperellum, and
Syncephalastrum racemosum in the Medium with Various Earthworm Applications
27
Table 1: The average of microbialpopulation in differenttypes of earthwormapplication on the second observation.
2.7 Maintenance and Observation of
Microorganism Population
Maintenance of various types of earthworms by the
addition of sufficient water using hand sprayer into
each culture medium. Observations were made on
the number of microorganisms in the culture
medium. Observations and sampling were
performed at the start of the study, a week after
application the microbial and a week after
application the earthworm (it means that 2 weeks
after microbial application). Ten (10) g of media
using a spatula and dissolved in 90 mL of sterile
water and shaker until homogeneous (dilution 10
-1
).
3 RESULT
3.1 Microbial Population (CFU/ml)
The results showed thatapplication oftypes of
earthworms, various microbes and theinteractions of
both in compost have a significantly effect
onmicrobial population. The average population of
microbes after a week earthworm application
available in table 1.
The population of Azospirillum sp. on boxtreated
with endogeic earthworms was the (27.5 x 10
-8
CFU/mL), however was not significant different
with its population in treatment anecic earthworms
(26 x 10
-8
CFU/mL). The lowest microbial
population was at treatment anecic earthworms and
Trichodermaasperellum(0.2 x 10
-8
CFU/mL) which
is a fungal decomposers and has a value of the
average population of microbes similar to
earthworms anecic treatment with the microbial
Syncephalastrumracemosum (table 1).
3.2 The Microbial Population
Dynamics
The dynamics of microbial populations was
determined from the difference between early
microbial population (a week after the application of
microbial) with microbial populations after
application of earthworm (figure 2).
Treatments
Azotobacte
r
Azospirillu
m
B
acillus
subtilis
Talaro
mycespinophilu
s
Trichoder
maasperellum
Syncephalast
rumracemosu
m
Mean
10
-8
CFU/mL
Without
Earthwor
m
12,1cdefg 11,5defg
1
2,4cde
f
0,4defg 0,9defg 0,4efg 6,3
Anecic
Earthwor
m
23,7b 26,0a 22,5bc 0,3fg 0,2g 0,2g 12,1
Endogeic
Earthwor
m
22,5c
d
27,5a 21,4c
d
0,3fg 0,7defg 1,1defg 12,2
Epigeic
Earthwor
m
20,2c
d
10,7defg 12,7cde 0,3fg 4,9defg 0,5defg 8,2
Mean 19,6 18,9 17,2 0,3 1,7 0,6
ICOSTEERR 2018 - International Conference of Science, Technology, Engineering, Environmental and Ramification Researches
28
C
FU/
ml
Figure 2 : Dynamics of Microbial Population
The dynamics of microbial populations in biovermi
compost suistainthe increased and decreased. The
bacterial population increased from the first
observation to the second observation, but the
average of fungus population decreased from the
first observation to the second observation (figure
2). However, the treatment without earthworms was
the lowest population in the first observation,
whereas in the second observation the lowest
population was treated with anecic earthworms. In
this study, the application of earthworms in the
second week after the application of earthworms had
the percentage of live earthworms continued to
decline, indicating that earthworms are not able to
survive on the medium that used in this study. On
the second day after the application of earthworms,
the percentage of live anecic earthworms dropped
dramatically, so that all anecic earthworm were died.
Anecic earthworms did not survive on carrier media,
it may be due to anecic type earthworms usually live
in the soil and not live in waste habitats as
decomposer worms. The anecics earthworm (length
13-17 cm; diameter 10-15 mm) is larger than other
types and usually move vertically in soil. The same
thing happens withendogeic earthworms prefer live
on the soil with medium clay content for their
habitat. While the comparison of culture media used
may not be comparable, so that this endogeic cannot
survive. In this case the endogeic worm used is
Pontocolexcorethrurus. However, it is inversely
proportional to the epigeic earthworm that used
Eisenia Andrei that survive from application to
completion of observation. This happens because the
epigeic earthworm is an active earthworm as a
decomposer of organic matter in soil. Furthermore,
epigeic earthworms are also more relative tolerant to
pH and can tolerate pH levels and are relatively
tolerant of environmental conditions of organic
waste (
Dominguez and Edwards, 2011),
(
Neuhauser, 1988).
4 CONCLUSION
The interaction between the types of earthworms and
microorganisms influenced the population of
microorganisms. The type of earthworm that could
be used on the medium was the epigeic earthworm
(Eisenia andrei). The highest microbe population
were Azospirillum sp. (bactery) and Trichoderma
asperellum (fungus).
REFERENCES
Blakemore R J 2002 Cosmopolitan Earthworms : An Eco-
Taxonomic Guide to the Peregrine Species of the
WorldAustralia Published by VermEcology.
Dominguez J and C A Edwards 2011 Biology and Ecology
of Earthworm Species Used for Vermicomposting.
ResearchGateTaylor & Francis Group, LLC.
NeuhauserE F, Loehr R C, and Malecki M R 1988 The
potential of earthworms for managing sewage
sludge :Earthworms in Waste and Environmental
Management, ed.CA Edwards and E F Neuhauser,
9–20. SPB Academic Publishing, the Hague, The
Netherlands.
Sabrina T, Poltak dan A S Hanafiah 2017 5 Jamur Asal
Potongan Batang Sawit : Jenis dan Potensinya
Medan. USUPress.
SekarKR and N Karmegam2010 Earthworm Casts as an
Alternate Carrier Material for Biofertilizers:
C0 :Without Earthworm
C1 :Anecic Earthworm
C2 :Endogeic Earthworm
C3 :Epigeic Earthworm
M1 :Azotobacter sp.
M2 :Azospirillum sp.
M3 :Bacillus subtilis
M4 :Talaromycespinophilus
M5 :Trichodermaasperellum
M6 : Syncephalastrumracemosum
Population Dynamics of Azotobacter sp., Azospirillum sp., Bacillus subtilis, Talaromyces pinophilus, Trichoderma asperellum, and
Syncephalastrum racemosum in the Medium with Various Earthworm Applications
29
Assessmentof Endurance and Viability of
Azotobacterchroococcum, Bacillus megateriumand
Rhizobium leguminosarum IndiaVinayaka Missions
University124 : 286–289.
SembiringM, D Elfiati, E S Sutarta dan T Sabrina 2015
Peningkatan Ketersediaan Fosfat dan Produksi
Tanaman Kentang (Solanum tuberosum L.) dengan
Menggunakan Talaromyces pinophilus Indigenous
dan Pupuk Sp36 pada Andisol Terdampak Erupsi
Gunung Sinabung.J. Pertanian Tropik. 2 (38) : 323-
329.
SuhartantiD, E D Anggara, Susanti 2013
DeteksiBakteriSelulolitikdariUsusdanKascingCacin
g Tanah (Lumbricusterestris) Yogyakarta:
Universitas Ahmad Dahlan. J.Pasca.
WangH, Liu S, ZhaiL, Zhang J, Ren T, Fan B, and Liu H
2015Preparation and Utilization of Phosphate
Biofertilizers Using Agricultural Waste China. J.
I.Agr.14(1):158–16
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