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Nigerian Journal of Microbiology, Vol. 25: 2243 – 2250 2011
ANTIBIOTIC RESISTANCE PROFILE OF WASTEWATER ISOLATES OBTAINED
FROM UNIVERSITY OF CALABAR TEACHING HOSPITAL AND GENERAL
HOSPITAL CALABAR, NIGERIA.
Akubuenyi F.C. 1, G.E. Arikpo1, C.J. Ogugbue2, J.F. Mfongeh1, E. V. Akpanumun1.
1 Department of Biological Sciences, Cross River University of Technology, Cross River
State, Nigeria.
2 Department of Microbiology, University of Port Harcourt, Rivers State, Nigeria.
Abstract
The antibiotic resistance profile of bacterial isolates obtained from the wastewaters of the
University of Calabar Teaching Hospital (UCTH) and the General Hospital Calabar (GHC),
Cross River State, Nigeria, was determined using the disc-diffusion method. A total of 125
bacterial isolates from both hospitals wastewater comprising of the following genera:
Escherichia;
Salmonella;
Shigella;
Klebsiella; Pseudomonas;
Streptococcus;
Bacillus;
Staphylococcus and
Proteus, were tested for their antibiotic resistance capability. Data
obtained showed that all the isolates from both hospitals had multiple antibiotic resistance
(MAR). Over fifty five percent of the isolates from UCTH and 12.5% of the isolates from
GHC exhibited resistance to the antibiotics tested (amoxycilin, gentamycin, augumetin,
chloramphenicol,
cotrimoxazole). Amongst the UCTH isolates, 5 different antibiotic patterns were observed
ranging from 6-12 MAR combinations while 8 different antibiotic resistance patterns ranging
from 4-12 MAR combinations were obtained from the GHC isolates. All the UCTH isolates
were resistant to the antibiotics commonly used in the hospital (amoxicillin, augumentin,
chloramphenicol, gentamycin, erythromycin, tetracycline, ciprofloxacin, streptomycin and
cotrimaxazole) except
Escherichia coli and
Pseudomonas which are sensitive to
ciprofloxacin. The same trend was obtained for the GHC isolates for the commonly used
antibiotics (chloramphenicol, erythromycin, tetracycline, streptomycin, cotrimaxazole) in
GHC. The lowest resistance of 25% was obtained for ofloxacin which was one of the
antibiotics rarely used in both hospitals. Results obtained show the important public health
hazard associated with the discharge of untreated hospital wastewater into the environment.
KEY WORDS: antibiotics, bacterial isolates, resistance, hospital
Path, 2001). The occurrence of strongly
A myriad of substances such as
selective environments such as hospitals,
antibiotics, synthetic drugs, radionuclide,
promotes, not only the growth of resistant
and solvents, etc. are used in hospitals for
bacteria, but also leads to an increase in
the frequency of resistance bacterial genes
and genetic elements such as plasmids.
application, many non-metabolized drugs
Hospital wastewater, even if it is
are excreted by the patients and enter the
treated, may contain pathogenic drug-
resistant bacteria, which constitute the
wastewater may be present at levels that
most dangerous single risk factor for
could not only alter the ecology of the
dissemination of pathogenic and drug-
environment but also give rise to antibiotic
resistant organisms in the environment
resistance (Raloof, 1998).
(Diab
et al., 2008). These resistant
Acquired resistance to antibiotics
bacterial species may be transmitted to
may arise by cellular mutation or by
acquisition of genetic elements in the form
infection that cannot be treated by
of plasmids or transposons (Russel and
conventional antibiotics (Khachatourians,
Akubuenyi
et al., 2011
Nig. J. Microbiol. Vol. 25: 2243 - 2250
1998). Hence, the hospital wastewater with
Isolation
culturable
its high content of multidrug resistant
heterotrophic bacteria (TCHB).
bacteria and the presence of enteric
Isolates of TCHB were obtained
pathogens could pose a grave problem for
through 10-fold serial dilution of the
the community receiving such wastewaters
(Cabrera
et al. 2004; Chitris, 2004;
physiological saline and pour plating of
Somwang
et al., 2005).
0.1ml aliquots in duplicates on Nutrient
Agar (Difco Lab). Discrete colonies that
untreated wastes of hospital and urban
developed after incubation at 30oC for 48h
sewage systems are released into rivers,
were subcultured to obtain pure cultures
lakes and other surface waters which also
which were stored at 40C and used
serve as sources of drinking water for local
communities and poor homes and could
characterization and biochemical analyses.
also help sources of water for the water
Isolation of enteric bacteria
treatment plants that provide drinking
One ml aliquots of appropriately
water for the cities. Despite this practice,
diluted samples were plated out (pour
characterizations
plate) in duplicates on MacConkey agar to
wastewaters have been carried out in
screen for coliform bacteria. To screen for
Nigeria to determine the antibiogram of
Salmonella spp. and
Shigella spp., the
the microbial diversity inherent in such
samples were enriched in Selenite F broth
discharges. The aim of this research
for 8h and then pour plated on
Salmonella-
therefore was to determine the antibiotic
Shigella agar and incubated for 24-48h.
The samples were also enriched on
wastewaters coming out of hospital drains
alkaline peptone water (pH 8.3) and then
in Calabar. The study was carried out on
plated out (pour plate) on thioglycholate
the wastewaters of the University of
citrate bile salt sucrose (TCBS) agar, to
Calabar Teaching Hospital (UCTH), and
isolate
Vibrio species. Pure cultures of
the General Hospital Calabar (GHC). Both
isolates were stored on nutrient agar slants
hospitals are public health centers located
characterization
in Calabar, Cross River State, Nigeria, that
identification (Krieg and Holt, 1994).
provide hospital services in a broad
Characterization and identification of
category of illnesses and injuries.
isolates
The isolates were characterized and
Materials and methods
procedures as described in Bergey s
Collection of samples
Manual of Systemic Bacteriology (Krieg
Wastewater samples were collected
and Holt, 1994).
from UCTH and GHC both located in
Antibiotic resistance studies
Calabar Metropolis, Nigeria. The sampling
The standardized disc diffusion
was performed according to the protocol
method (Bauer et al., 1999) and the zone-
of Nunez and Moretton (2007). Samples
size interpretation chart of Kirby-bauer
were collected over a 10h period taking
(1966) was used for the
in vitro
samples every 2h for 16 days using sterile
determination of the bacterial sensitivity to
500ml sample bottles. The same volume
the various antibiotics selected, selection
(250ml) of each partial sample was mixed
of antibiotics was based on their usage in
at the end of the day to obtain the
the hospitals. The antibiotics used were;
composite sample used for microbiological
analyses. A total of 76 samples were
collected from both hospital and all
chloramphenicol (30g/ml), erythromycin
samples were preserved in an icebox until
transported to the laboratory.
Akubuenyi
et al., 2011
Nig. J. Microbiol. Vol. 25: 2243 - 2250
(10g/ml), and cotrimoxazole (25g/ml).
samples were 7.80•3.6 x 106 and 9.50•4.5
x 106 CFU/ml for TCHB, and 3.30•2.1 x
(25g/ml), and pefloxacin (5g/ml) which
106 and 4.20•2.9 x 106 CFU/ml for
are rarely used antibiotics in both hospitals
coliforms respectively (Table 1). The
were also included in this study.
percentage of coliforms to total bacteria is
Commercially prepared paper discs
42.31% and 44.21% respectively. A total
impregnated with the various antibiotics
of 125 isolates comprising of 65 from
were mounted on Muller-Hinton agar
UCTH and 60 from GHC were identified
plates (Lab M) containing pure cultures of
based on their colonial morphology and
the various isolates. Each plate was
their biochemical characteristics. They
belonged to the following bacterial genera:
suspensions containing 107 to 108 cells
obtained using basic 0.5 Mcfarland
solution (NCCLS, 1990). A total of 125
Bacillus;
Staphylococcus and
Proteus. All
randomly selected isolates were tested and
these bacterial genera except
Proteus were
results obtained were classified as resistant
isolated from both hospital wastewaters.
or sensitive. Inhibition zone diameters
Proteus was isolated from only UCTH
were measured after 18-24h of incubation.
wastewater samples. Tables 2 and 3 show
the frequency of isolation of these
counts from UCTH and GHC wastewater
Table 1: Total bacterial and coliform counts of UCTH and GHC wastewaters
*Composite mean value of triplicate counts.
Table 2: Frequency of isolation of the different bacterial genera from the wastewaters
of UCTH.
Total number of No.
positive Frequency
Staphylococcus
Akubuenyi
et al., 2011
Nig. J. Microbiol. Vol. 25: 2243 - 2250
Table 3: Frequency of isolation of the different bacterial genera from the wastewater of
GHC
No. of positive Frequency
Staphylococcus
Resistance patterns of isolates from
(Table 4). Only one genus (
Salmonella)
both hospital wastewaters showed that all
isolated from the GHC
samples showed resistance to all the tested
antibiotic resistance (MAR). Five genera
antibiotics (Table 4). None of the bacteria
(
Salmonella,
Klebsiella,
Bacillus,
isolated from the wastewater samples of
Staphylococcus and
Proteus) from the
antibiotic resistance to all the antibiotics
resistance to all the antibiotics tested
Table 4: Antibacterial susceptibility profile of bacteria isolated from UCTH wastewater
Antibiotics tested
% Resistance of single
Akubuenyi
et al., 2011
Nig. J. Microbiol. Vol. 25: 2243 - 2250
Table 4: Antibacterial susceptibility profile of bacteria isolated from
Antibiotics tested
s.
igella.
lebsiella
% Resistance of single
All the isolates from the UCTH
only
Salmonella had developed resistance
wastewater samples showed resistant to all
to all twelve antibiotics used in this study
the antibiotics (amoxycillin, gentamycin,
(Table 5). It was also found that all the
chloramphenicol,
bacterial isolates from the GHC had
erythromycin, tetracycline, streptomycin
developed resistance to some of the
and cotrimaxazole) commonly used in the
(chloramphenicol,
hospital except Ciprofloxacin.
Escherichia
erythromycin, streptomycin, tetracycline
coli and
Pseudomonas from UCTH and
and cotrimaxazole)
alone from GHC were
hospital. Only
Salmonella and
Staphyloc
sensitive to Ciprofloxacin (Tables 4 & 5).
More organisms -
Shigella,
Escherichia
ofloxacin which was also rarely used in
and
Streptococcus showed sensitivity to
that hospital.
antibiotics).
Shigella and
Escherichia were
The TCHB and coliform counts in
sensitive to ceftriazone, another not
investigated were similar to counts
Streptococcus in UCTH and
Streptococcus
and
Escherichia
Argentina by Nunez and Moretton (2007).
sensitivity to Pefloxacin – third rarely used
Similar results were also obtained for the
antibiotic employed. Data obtained from
the GHC wastewater analyses showed that
wastewater, Brazil (Ortolan, 1999) and the
Akubuenyi
et al., 2011
Nig. J. Microbiol. Vol. 25: 2243 - 2250
University of Ilorin Teaching Hospital
ability/predisposition to develop resistance
wastewater (Olayemi and Opaleye, 1990).
under conditions of antibiotic selective
The counts obtained for the bacterial
pressure (e.g. hospital environments)
groups at the two studied sites indicated
might be responsible for the acquisition of
high pollution level. The safe discharge
the antibiotic resistance capacity of these
level of such wastewaters should not
bacteria. The spectrum of resistance
exceed 100CFU/ml for TCHB and
30CFU/ml for coliforms (EPA Guidelines,
Escherichia indicates that the multidrug
2003). Out of the 7.80•3.6 x 106 CFU/ml
resistance genes responsible for the unique
total bacteria count obtained in the UCTH
characteristics observed might also be
domiciled in some of these bacterial
coliforms while 44.21% of the 9.50•4.5 x
CFU/ml of total bacteria count
obtained from GHC were coliforms (Table
resistance among the bacterial isolates was
1).
Escherichia coli and
Streptococcus spp
shown for the most commonly used
were the most frequently isolated bacteria
antibiotics in both hospitals (Tables 3 &
(Table 2). All the isolates had multiple
4). This result thus lays credence to a
antibiotic resistance, with most of the
previous report by Islam
et al. (2008)
isolates from both
hospital samples
which claims that resistance development
(Tables 3 & 4) exhibiting resistance to at
was directly related to the use of
least 6 antibiotics. Resistance to all of 9
commonly used antibiotics was recorded
It is widely acknowledged that the
for 7 genera in UCTH namely:
Salmonella,
selection and dissemination of antibiotic
Shigella,
Streptococcus,
resistant bacteria in nature should be
Staphylococcus and
Proteus
order to maintain the
(Table 4)
, whereas 4 genera (
Salmonella,
ecological balance that favours the
Shigella,
Klebsiella and
Streptococcus)
predominance of a susceptible bacterial
showed resistance to the same nine
flora in the environment and to ensure
antibiotics in GHC (Table 5). Previous
effective treatment
against infectious
reports have implicated
E. coli strains as
diseases in humans and farm animals.
the main carrier of antimicrobial resistance
Thus, the indiscriminate use of antibiotics
in faecal flora, as resistance in other
and the discharge of untreated antibiotic-
species was rare especially in the absence
of antimicrobial selection (Osterblad, et al.
environment may disrupt the microbial
2000; Guardaasi,
et al., 1998). Results
balance in nature in favour of resistant
obtained in this study however have shown
that other genera can acquire multiple
important public health hazard that may be
antibiotic resistance capacity and could
surpass
E. coli in exhibiting resistance to
discharge of hospital effluent into the
environment without adequate treatment.
The authors wish to thank the
laboratory crew of the Department of
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C. and M. Turk, (1999). Antibiotic
University of Technology, Nigeria for
susceptibility testing by a standard
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