Annals of
Burns and Fire Disasters - vol. XIII - n. 3 - September 2000
PREVENTION OF
HOSPITAL-ACQUIRED INFECTIONS IN THE PALERMO BURNS CENTRE*
Torregrossa M.V.,1 Valentino L.,1
Cucchiara P.,2 Masellis M.,2 Sucameli M.2
1 Department of Hygiene and Microbiology,
Palermo University, Palermo, Italy
2 Department of Plastic Surgery and Burns Therapy, Palermo Civic
Hospital, Palermo
SUMMARY. This paper reports on an
extensive epidemiological survey of the microbiological monitoring of the environment,
staff, and patients in the Intensive Care Unit of the Palermo Bums Centre (Italy). The aim
of the survey was to evaluate the presence and distribution of environmental sources of
pathogens and opportunistic bacterial agents of nosocomial infection in immunocompromised
hosts. Strains collected from air, tap water, and medical and nursing staff were compared
with strains isolated from burn patients in order to study the potential transmission
route of bacteria. The results showed environmental strains presenting a profile identical
to that of the clinical strains, suggesting a link between the environment, staff, and the
patients. A programme of routine microbiological monitoring proved to be effective as a
surveillance programme for the reduction of nosocomial infection.
Introduction
Hospital-acquired infections are a considerable problem for health
services in all countries, with serious effects on the survival of high-risk patients,
such as burn patients. In a burns centre, primary bloodstream infections, pneumonia, and
infection of burn sites are very dangerous complications that can compromise the patients
survival and the outcome of reconstructive treatment. We stress the importance of emerging
pathologies involving opportunistic micro-organisms. In many patients we have detected
infections caused by Pseudomonas spp. The isolation of Pseudomonas spp., Bacillus cereus,
Achromobacter, Acinetobacter, and Proleus spp. in some patients in the Palermo Burns
Centre was the warning signal that prompted an investigation for the presence of
opportunistic bacteria in the environment (water, air, supplies) as a
"reservoir" of bacteria. Our research team is engaged in identifying the risk
factors linked to hospital infection and is carrying out procedures to control infection
as well as programmes to guarantee "safe treatment" in the hospital. We also
observed staff behaviour during ward activities (e.g., changes in medical and health
procedures) and on the basis of these observations we suggested a microbiological
surveillance programme for patients, medical and nursing staff, and the environment
regarding all the factors that contribute to the circulation of germs around the patient.
Materials and methods
Environmental water sampling
The Palermo Burns Centre (Fig. 1) receives municipal chlorinated water
and water from private wells. The survey of the level of microbiological environmental
pollution was carried out for water supplies, heating-tanks, tap water, tap mixers, bath
water, running water, and surface sanitary areas.

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Fig. 1 - Plan of Palermo Burns Centre. |
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When chlorine was < 0.2 mg/1, water samples (tap
water, tank water, and bath water) were collected in sterile glass bottle and analysed to
assess the concentration of heterotrophic opportunist bacteria. For quantitative analysis,
appropriate dilutions and 10, 50, 100, and 200 ml water
samples were filtered through sterile cellulose acetate filters (0.45 nm). The filters
were placed on agar nutrient, McConkey agar, and cetrimide agar (agar containing 3%
anionic detergent cetyltrimethyl ammonium bromide) and incubated at 22 and 36 °C. The
isolated strains were identified using "Standard methods of water and waste water
guidelines" (APHA, 1985).
Environment air sampling
Microbial contamination of the air was assessed by determining the air
microbe index (AMI). A total number of 396 AMI measurements were performed in the
intensive care unit rooms in the patients absence and in the course of routine department
activities. Three 10-cm petri dishes containing nutrient agar, blood agar, and Sabouraud's
agar were exposed in every room for 1 h at a distance of 1 m from every obstacle
(Fischer's 1-1-1 scheme). The dishes were incubated at 36 °C for 48 h and for every room
the mean dish values were taken as the colony forming unit (CFU). A further determination
of the bacterial charge in the air was made by the RCS-Biotest sampler: in each room 160 1
of air were removed and examined and the results calculated in CFU/cubic m.
Clinical sampling
Monitoring of the patients was performed on hospitalized subjects with
deep burns in 10-70% body surface area by means of surface swabs from burned and
immediately adjacent areas, biopsies, and haemocultures inoculated into culture media:
blood agar, simple and tryptose agar, bromothymol blue lactosate agar, and Pseudomonas
agar plates and incubated at 36 °C for 48 h.
Staff sampling
With regard to the health personnel, monitoring was carried out every
three months by a culture test of nasal and pharyngeal swabs to test for pathogens and by
examination of surgical gloves before and after contact with patients and the patients
environment.
Results
Some methicillin-resistant Staphylococcus aureus (MRSA) strains were
found in patients in our burns centre: this was the warning signal that prompted a survey
of the environment and staff. Three hundred and ninety-six AMI measurements were performed
in the intensive care unit rooms; during the study, strains of multi-resistant
Staphylococcus aureus were isolated in the nurses' room, the doctors' meeting room, and
the laboratory. Many of the strains were MRSA and one of them, which showed the same
biochemical characteristics and sensitivity to antibiotics, was isolated from the blood of
a young patient with primary blood stream infection (Table I). During the study period the
same micro-organisms were found in four staff members by means of nasal and oropharyngeal
swabs.
|
Nurses'
room |
Corridor |
Laboratory
|
Kitchen |
Young
patient |
Nurses'
WC |
Doctors'
WC |
Meeting
doctor |
Penicillin |
R |
R |
R |
R |
R |
R |
R |
R |
Ampicillin |
R |
R |
R |
R |
R |
R |
R |
R |
Methicillin |
R |
R |
R |
R |
R |
R |
R |
R |
Piperacillin |
R |
R |
R |
R |
R |
R |
R |
R |
Co-himozazole |
S |
S |
S |
S |
S |
S |
S |
S |
Cephalothin |
R |
R |
R |
R |
R |
R |
R |
R |
Genuamicin |
R |
R |
R |
R |
R |
R |
R |
R |
Erythomycin |
R |
R |
R |
R |
R |
R |
R |
R |
Clindamycin |
R |
R |
R |
R |
R |
R |
R |
R |
Tetracycline |
R |
R |
R |
R |
R |
R |
R |
R |
Vancomycin |
S |
S |
S |
S |
S |
S |
S |
S |
Fusidic acid |
S |
S |
S |
S |
S |
S |
S |
S |
Ciprdozacin |
R |
R |
R |
R |
R |
R |
R |
R |
R = resistant |
S = sensitive |
|
Table I - Staphylococcus aureus
strains isolated in the environment and in a young patient in the burns centre |
|
Environmental sampling was performed on water from taps,
baths, and the heating tank.
Thirty-five strains of opportunistic bacteria were isolated from skin lesions and blood
cultures on burn patients: 24 strains of Pseudomonas aeruginosa, 5 of Acinetobacter spp.,
3 of Bacillus cereus, 2 of Achromobacterium spp., and one of Alcaligenes spp. Tap and tank
water were always negative for faecal indicators (Table II) but strains of Pseudomonas
aeruginosa, Alcaligenes, Pseudomonas stutzeri, and Bacillus cereus (Table III) were
isolated from unchlorinated waters. The same strain of Bacillus cereus was isolated from
the skin lesions and the blood of two burn patients and in the hot water tank serving the
ward.
Sample
Free residual Cl |
1
0.2 ppm |
2
0.1 ppm |
3
0 |
4
< 0.1 ppm |
5
0 |
Total E. coli |
0 |
0 |
0 |
0
|
0 |
E. coli faecalis |
0 |
0 |
0 |
0 |
0 |
Streptococcus
faecalis |
0 |
0 |
0 |
0 |
0 |
Others |
0 |
2 |
12 |
4 |
14 |
Table II - Results of water system sampling |
|
Gram-negative
non-fermentative rods |
Gram-positive rods |
Pseudomonas aeruginosa |
Bacillus spp. |
Pseudomonas stutzeri |
Bacillus cereus |
Pseudomonas vesicularis |
|
Achromatobacter spp. |
|
Sphingomonas paucimobilis |
|
Alcalmigenes spp. |
|
Table III - Opportunistic bacteria isolated
from water samples
in the Palermo Burns Centre |
|
Pseudomonas aeruginosa strains were isolated in
thePseudomonas aeruginosa strains were isolated in the sanitary services of the patients
and medical staff rooms, hydrotherapy, and the swilling tank.
Strains of serotype 0:11 Pseudomonas aeruginosa were isolated from patient A. The same
strains were found after 24 h in bath water, with water and acqueous quaternary ammonium
compound, after the patient's hydrotherapy. Other strains of 0:6 serotype Pseudomonas
aeruginosa were isolated from patient B. 0:6-0:11 serotype strains were found in the bath
water and later in the blood culture from patient A, after a new bath (Table IV).
Antibiotics |
Patient A
before bath |
Bath water after 24 h |
Patient B before bath |
Bath water
after 24 h |
Patient A
after bath |
Ticarcillin |
R |
R |
S |
R S |
R S |
Tic. clavul. ac. |
R |
R |
S |
R S |
R S |
Piperacillin |
R |
R |
S |
R S |
R S |
Ceftazidime |
R |
R |
S |
R S |
R S |
Aztreonam |
R |
R |
S |
R S |
R I |
Imipenem |
R |
R |
S |
R S |
R S |
Tobramycin |
R |
R |
R |
R R |
R R |
Amikacin |
R |
R |
I |
R I |
R I |
Gentamicin |
R |
R |
S |
R S |
R S |
Netilmicin |
R |
R |
R |
R R |
R R |
Colistin |
S |
S |
S |
S S |
S S |
Pefloxacin |
R |
R |
R |
R R |
R R |
Ciprofloxacin |
S |
S |
S |
S S |
S S |
Sulph.-Trim. |
R |
R |
R |
R R |
R R |
Serotype |
0:11 |
0:11 |
0:6 |
0:11 0:6 |
0:11 0:6 |
R = resistant |
S = sensitive |
I = intermediate |
|
Table IV - Antibiotic resistance profiles
of Pseudomonas aeruginosa strains in patient and hydrotherapy pool |
|
Considerations and conclusions
The investigation gave rise to a number of considerations. There is
certainly a circulation of selected, multiresistant strains capable of causing pathologies
in patients who have been undergone invasive manoeuvres and in severely burned patients in
whom the damaged skin barrier allows the entry of any micro-organism in circulation.
Most of the cases of sepsis occurring in our burns centre were due to the circulation of
strains of MRSA in patients subjected to continuous infusion therapy using intravenous
catheters. The observation of sediment germs in the culture dishes of a strain that had
good resistance to the air and was always present in different periods of the survey
prompted us to perform a mapping in time of the air-person-patient system involved in the
re-circulation of the micro-organism, without underestimating the importance of
"alerting" germs even in the absence of a high environmental microbic charge.
A large number of gram-negative bacteria and emerging pathogens such as Pseudomonas,
Klebsiella, and Enterobacter species may also show the comparative resistance to some
disinfectants and antiseptic solutions.
Pseudomonas aeruginosa can cause sepsis, pneumonia, and infection in burned skin.
Pseudomonas aeruginosa occupies multiple ecological niches in nature by virtue of its
minimal growth requirements and its ability to produce a large number of extracellular
protective and toxic substances. Some of these substances, such as slime glycoliprotein,
haemolysis, fibrinolysin, lecithinase, elastase, Dnase, and phospholinase, may contribute
to the pathogenicity of this opportunistic micro-organism, which is multi-resistant to the
most commonly used antiseptics, disinfectants, and antibiotics.
Despite the large amount of information that is available regarding the distribution of
Pseudomonas aeruginosa and other micro-organisms in the hospital environment, the routes
of infection and transmission remain controversial.
Many investigators have suggested that these opportunistic micro-organisms, especially
Pseudomonas aeruginosa, can readily contaminate the hands of personnel, presumably by
water splashed from sinks during washing procedures. Other researchers deny this
transmission route and believe that a pre-existing colonization of patients leading to
endogenous infection is the major source of Pseudomonas aeruginosa.
Our results confirm that water taps in the hospital environment can represent a reservoir
of micro-organisms with low nutritional requirements, such as Pseudomonas aeruginosa. This
micro-organism can colonize water supply systems, especially when the tap water is
particularly rich in calcium and magnesium carbonate, and can spread from this source to
the patient environment. Our results showed environmental strains presenting a profile
identical to that of clinical strains, suggesting a link between bath water and the
patients.
A programme of routine microbiological monitoring effectively minimized the risk in
particular patients.
Appropriate nursing techniques are of particular importance for burn patients. There is an
increasing awareness of the importance of personal factors in preventing hospital
infection and of the need of proper understanding of the facts by all members of the
hospital staff. Although the issue is complex and involves many disciplines, the basic
ideas are simple, and many of the details of asepsis can be made easier by forms of
standardization based on the evidence of effectiveness and practicability.
RESUME. Les Auteurs
présentent les résultats d'une enquête approfondie épidémiologique sur le monitorage
microbiologique de l'environnement, du personnel, et des patients dans le Service de
Réanimation du Centre des Brûlés à Palerme (Italie). Le but de l'enquête était
d'évaluer la présence et la distribution des sources environnementales des pathogènes
et des agents bactériens opportunistes de l'infection nosocomiale dans les hôtes
immunocompromis. Des souches prélevées sur fair, l'eau de robinet et le personnel
médical et paramédical ont été comparées à des souches isolées dans les patients
brûlés pour étudier les routes possibles de transmission des bactéries. Les résultats
de l'enquête ont indiqué la présence de souches environnementales qui possédaient un
profil identique à celui des souches cliniques, ce qui suggérait un rapport entre
l'environnement, le personnel et les patients. Un programme de monitorage microbien de
routine s'est révélé efficace comme système de contrôle pour la réduction de
l'infection nosocomiale.
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This paper was received on 18 January 2000.Address correspondence
to: Dr MN Torregrossa, Dipartimento di Igiene a Microbiologia, Università di Palermo, Via
del Vespro 133, 90100 Palermo, Italy. |
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