PCR METHOD FOR DETECTION OF mecA GENE IN METHICILLIN-RESISTANCE Staphylococcus aureus (MRSA) STRAINS ISOLATED FROM MILK AND MILKING SURROUNDING ENVIRONMENT

Document Type : Research article

Authors

1 Department of Food Hygiene, Faculty of Veterinary Medicine, Assiut University, Egypt.

2 Department of Animal Hygiene, Faculty of Veterinary Medicine, Assiut University, Assiut, Egypt.

Abstract

The aim of the present investigation was to run a protocol to detect mecA gene that characterizing methicillin-resistant Staphylococcus aureus (MRSA) using phenotypic and genotypic molecular techniques. Also, this study was designed to determine the prevalence of mecA-positive MRSA strains in milk and its surrounding milking environment from 60 dairy cattle houses including 30 for cows and 30 for buffalos. Therefore, 308 samples were collected including 150 samples from cows’ houses and 158 from buffalos’ houses. The samples from cows’ houses were 30 milk samples (5 of them were mastitic), 30 air samples, 30 floor samples of different soil types, 30 tap water samples and 30 pail water samples. The samples from buffalos’ houses were 38 milk samples (8 of them were mastitic), 30 air samples, 30 floor samples of different soil types, 30 tap water samples and 30 pail water samples. It was also recorded the floor type either muddy or dry and the rearing type either separate or mixed with farm animals. Thereafter, the collected samples were examined directly for identification of Staph. aureus and then MRSA using phenotypically and biochemically with API ID 32-STAPH. All the identified strains were tested genotypically for resistance to oxacillin by detection of the gene encoding methicillin-resistant that called mecA gene PBP2a (penicillin-binding protein) using PCR assay. The obtained results revealed that, 139 samples were positive for Staph. aureus including 75 samples were positive for MRSA which included 50 samples were found mecA-positive MRSA divided as 14 milk samples and 36 milking surrounding environmental samples. The mastitic milk samples of cows and buffalos were contaminated with mecA-positive MRSA in percentages of 60 and 37.5%, respectively. The statistical analysis results proved a significant correlation among the isolated strains in the milking surrounding environments of both dairy cows and buffalos; in which, a significant correlation between milk samples and also between soil and water in the cows’ environment. With attention to the buffalos’ environment, a significant correlation was found between clinically normal milk and both of air and water; also, a significant correlation among air, soil and water was noticed. According to the obtained results, the role of some ecological parameters on the distribution of mecA-positive MRSA strains was observed as a significant correlation between muddy floor and both types of rearing, and also between dry floor and mixed rearing in the milking surrounding environments of both dairy cows and buffalos.

Keywords


Department of Food Hygiene,

Faculty of Veterinary Medicine,

AssiutUniversity, Assiut, Egypt.

Corresponding author: dr.mohammedsayed@yahoo.com

 

PCR method for detection of mecA gene in methicillin-resistance Staphylococcus aureus (MRSA) strains isolated from milk and milking surrounding environment

(With 10 Tables and 2 Figures)

 

By

M. Sayed and S. Kotb*

* Department of Animal Hygiene, Faculty of Veterinary Medicine, AssiutUniversity, Assiut, Egypt.

(Received at 14/10/2010)

 

طريقة تفاعل البلمرة المتسلسل للکشف عن جين mecA في عترات المکور العنقودي الذهبي المقاوم للميثيسيللن (MRSA) المعزولة مناللبن وبيئة الحلب المحيطة

 

محمد سيد، صابر قطب

 

هدفت الدراسة الحالية إجراء برتوکول لتحديد جين mecA المميز للمکور العنقودي الذهبي المقاوم للميثيسيللن (MRSA) باستخدام التقنيات الظاهرية وتقنيات البيولوجيا الجزيئية. کما تم تصميم هذه الدراسة لتحديد نسب إنتشار عترات mecA-positive MRSA في اللبن وفي البيئة المحيطة لعملية الحلب وذلک من 60 مسکن لماشية الألبان الحلابة والمقسمة إلى 30 للأبقار وکذلک 30 للجاموس. وقد تم تجميع عدد 308 عينة شملت 150 عينة من مساکن الأبقار الحلابة و158 عينة من مساکن الجاموس الحلاب. وقد کانت عينات مساکن الأبقار متضمنة على 30 عينة لبن (وجد منها 5 مصابة بإلتهاب الضرع الظاهري)، 30 عينة من الهواء، 30 عينة من التربة، 30 عينة من ماء الصنبور، 30 عينة من أواني مياه الشرب. أما عينات مساکن الجاموس فقد شملت على 38 عينة لبن (وجد منها 8 مصابة بإلتهاب الضرع الظاهري)، 30 عينة من الهواء، 30 عينة من التربة، 30 عينة من ماء الصنبور، 30 عينة من أواني مياه الشرب. وقد تم تسجيل نوع التربة سواء طينية أو جافة وکذلک نوع التربية سواء منفردة أو مختلطة مع حيوانات المزرعة. ثم تلا ذلک مباشرة فحص العينات للتعرف على المکور العنقودي الذهبي ثم المقاوم للميثيسيللن بإستخدام التقنيات الظاهرية والبيوکيميائية بواسطة API ID 32-STAPH. وبعد ذلک تم فحص کل العترات باستخدام البيولوجيا الجزيئية للکشف عن الجين الخاص بمقاومة الميثيسيللن والذي يسمى جين mecA PBP2a (بروتين مرتبط البنيسيللين) وذلک بإستعمال تقنية تفاعل البلمرة المتسلسل PCR. وقد أوضحت النتائج المکتسبة أن 139 عينة کَانت إيجابية للمکور العنقودي الذهبي ومنها 75 عينة کانت إيجابية للمقاوم للميثيسيللن ومنها 50 عينة وجدت إيجابية للعترات mecA-positive MRSA ومقسمة إلى 14 عينة لبن و36 عينات بيئية. وکانت عينات اللبن لإلتهاب الضرع للبن البقري والجاموسي ملوثة mecA-positive MRSA بالنسب 60 و37.5%، على الترتيب. وقد برهنت نتائج التحليل الإحصائي على وجود إرتباط معنوي بين العترات في بيئات حلب اللبن لکل من الأبقار والجاموس الحلاب، حيث کان هناک إرتباط معنوي بين عينات اللبن وکذلک بين التربة والماء وذلک في بيئة الأبقار. وبالإشارة إلى بيئة الجاموس، فالإرتباط المعنوي وجد بين اللبن وکل من الهواء والماء، کما تم ملاحظة إرتباط معنوي بين الهواء والتربة والماء. وطبقا للنتائج المکتسبة، فإن دور بعض البارامترات البيئية على توزيع عترات mecA-positive MRSA قد تم ملاحظته حيث کان هناک إرتباط معنوي بين التربة الطينية وکل من نوعي التربية وکذلک بين التربة الجافة والتربية المختلطة وذلک لکل من بيئات حلب اللبن للأبقار والجاموس الحلاب.

 

الکلمات الکاشفة:جين mecA، المکور العنقودي الذهبي المقاوم للميثيسيللن (MRSA)، mecA-positive MRSA، اللبن، إلتهاب الضرع، الهواء، التربة، المياه، بارامترات بيئية،API ID 32-STAPH، تقنية تفاعل البلمرة المتسلسل PCR.

 

Summary

 

The aim of the present investigation was to run a protocol to detect mecA gene that characterizing methicillin-resistant Staphylococcus aureus (MRSA) using phenotypic and genotypic molecular techniques. Also, this study was designed to determine the prevalence of mecA-positive MRSA strains in milk and its surrounding milking environment from 60 dairy cattle houses including 30 for cows and 30 for buffalos. Therefore, 308 samples were collected including 150 samples from cows’ houses and 158 from buffalos’ houses. The samples from cows’ houses were 30 milk samples (5 of them were mastitic), 30 air samples, 30 floor samples of different soil types, 30 tap water samples and 30 pail water samples. The samples from buffalos’ houses were 38 milk samples (8 of them were mastitic), 30 air samples, 30 floor samples of different soil types, 30 tap water samples and 30 pail water samples. It was also recorded the floor type either muddy or dry and the rearing type either separate or mixed with farm animals. Thereafter, the collected samples were examined directly for identification of Staph. aureus and then MRSA using phenotypically and biochemically with API ID 32-STAPH. All the identified strains were tested genotypically for resistance to oxacillin by detection of the gene encoding methicillin-resistant that called mecA gene PBP2a (penicillin-binding protein) using PCR assay. The obtained results revealed that, 139 samples were positive for Staph. aureus including 75 samples were positive for MRSA which included 50 samples were found mecA-positive MRSA divided as 14 milk samples and 36 milking surrounding environmental samples. The mastitic milk samples of cows and buffalos were contaminated with mecA-positive MRSA in percentages of 60 and 37.5%, respectively. The statistical analysis results proved a significant correlation among the isolated strains in the milking surrounding environments of both dairy cows and buffalos; in which, a significant correlation between milk samples and also between soil and water in the cows’ environment. With attention to the buffalos’ environment, a significant correlation was found between clinically normal milk and both of air and water; also, a significant correlation among air, soil and water was noticed. According to the obtained results, the role of some ecological parameters on the distribution of mecA-positive MRSA strains was observed as a significant correlation between muddy floor and both types of rearing, and also between dry floor and mixed rearing in the milking surrounding environments of both dairy cows and buffalos.

 

Key words: mecA gene, methicillin-resistance Staphylococcus aureus (MRSA), mecA-positive MRSA, Milk, Mastitis, Air, Soil, Water, Ecological parameters, API ID 32-STAPH, PCR.

           

Introduction

 

Staphylococcus aureus is a common human pathogen capable of producing a wide range of diseases from skin and soft tissue infections to life-threatening endocarditis, bacteremia and necrotizing pneumonia (Gordon and Lowy, 2008). Infections due to Staph. aureus have assumed new public health importance due to emerging multiple antibiotic resistant strains, particularly methicillin-resistant Staph. aureus (MRSA) and its epidemic clones, increasingly being found in communities and hospitals (Moran et al., 2006; Pesavento et al., 2007; David et al., 2008).

The emergence of pathogenic microorganisms resistant to commonly used antibiotics is a worldwide concern of the 21st century. One of the most important bacteria in this regard is Staph. aureus, in particular its methicillin-resistant strains. The first MRSA strains were isolated from hospitalized patients in the United Kingdom in 1961, i.e. only 2 years after methicillin had started to be used for the treatment of staphylococcal infections (Barber, 1961; Jevons, 1961) and by the mid-1970s had become endemic in many countries (Voss and Doebbeling, 1995).

In the early 1990s, MRSA strains were isolated from the general population in USA (Naimi et al., 2001). However, detection of MRSA in animals, including also the farmed ones, was reported even much earlier in the bovine mastitis literatures, as the first case reported in an animal setting in 1972 following its detection in milk from Belgian dairy cows with mastitis (Devriese et al., 1972; Devriese and Hommez, 1975). Recently, there have been several reports of MRSA in both domestic and companion animals including dairy cows in a number of countries worldwide (Lee, 2003; Kaszanyitzky et al., 2004; Kwon et al., 2005; Voss et al., 2005). A comparison of human and farm animal isolates was carried out in some studies, MRSA from infected animals and asymptomatic carriers can be transmitted to humans (Scott et al., 1988; Manian, 2003; Duquette and Nuttall, 2004; Weese et al., 2005; Weese et al., 2006). Some studies strongly suggest that people working with livestock are at a potential risk of becoming MRSA carriers and hence are at an increased risk of infections caused by MRSA (Wulf et al., 2008). Additionally, isolates from cow’s milk appeared to be of human origin in a Korean study (Kwon et al., 2005). Transmission of antimicrobial-resistant Staph. aureus strains through foods including milk (da Silva et al., 2004), was involved in human outbreaks has been reported in sporadic cases (EFSA, 2008).

The surrounding environment (air, water, soil…etc) play an important role in transmission of microorganisms. Transmission of MRSA via inanimate objects such as floors, door knobs, switches, tables, etc., within environment has been well documented (Shiomori et al., 2002; Boyce, 2007). These inanimate objects play a role in transmission of disease when MRSA is shed by colonized carriers, or infected individuals, and deposited from direct contact or settled aerosols. In addition, airborne MRSA has been shown to play a significant role in the host-air-surface transmission triangle. For example, MRSA has been shown to not only survive on surfaces for days-to-months, but to maintain the capacity to transmit disease (Boyce et al., 1997; Huang et al., 2006).

The mecA gene is highly conserved in staphylococcal strains and thus is a useful marker of meticillin/oxacillin resistance (Ferreira et al., 2003). Its detection is considered the gold standard for detection of MRSA isolates. The mecA gene is found on a large mobile genetic element called the staphylococcal chromosomal cassette mec (SCCmec) (Van Duijkeren    et al., 2004; Weese et al., 2005). However, many laboratories throughout the world do not have the capacity to use molecular techniques to detect MRSA in routine clinical practice. However, such tests may not be widely available outside reference laboratories (Lee et al., 2004; van Duijkeren    et al., 2004; CDC, 2005).

The best method for MRSA verification still is PCR, detecting the mecA gene that codes for the resistance determinant. Resistance to methicillin and other β-lactam antibiotics in MRSA is conferred by the mecA gene, which is part of a 21 to 60-kb mobile genetic element, SCCmec. Expression of mecA yields PBP2a which has a low affinity for β-lactam rings, the primary active site of β-lactam antibiotics (Hanssen and Ericson Sollid, 2006).

According to the aforementioned public health hazard and the antimicrobial resistance of MRSA, there is a need to investigate the prevalence of MRSA in the milk of clinically normal and mastitic dairy cattle, in addition to, its incidence in the surrounding milking environment. Also, this study aimed to detect the gene determinant of methicillin-resistance (mecA gene) in the isolated MRSA strains as mecA-positive MRSA.

 

Materials and Methods

 

- Animal housing:

This study was conducted in 60 animal houses (30 for dairy cows and 30 for dairy buffalos). Each animal house (of an average area 15 m2) was being inside its owner’s farmer house (of an average area 135 m2) whom distributed in different locations sites in Manfalout city that faraway about 27 km north of Assiut city. The count of dairy animals was 30 cows as one inside each house; and 38 buffalos as one inside each one of 22 houses and the 8 rest houses had 16 buffalos as 2 for each. Other animal species were found as one donkey, 2-3 sheep and 2-5 goats in each house.

- Sampling:

A total of 308 samples were taken as 68 milk and 240 environmental samples. Each sample was taken under strictly hygienic conditions and labeled to indicate type, date, time…etc, and then carried with a minimum of delay for bacteriological examination.

 

I) Milk samples:

Firstly, the teat apices were cleaned and disinfected with a piece of cotton soaked in 70% ethyl alcohol, then the first stream of quarter was discarded, and about 20 ml of milk was aseptically drawn from each quarter into a sterile 250 ml capacity glass bottle. Milk sampling was done according to the recommendation of National Mastitis Council (1999).

1. Cows’ milk samples: 30 quarter milk samples were taken as one sample from each dairy cow. It was noticed that 5 dairy cows had clinical mastitis.

2. Buffalos’ milk samples: 38 quarter milk samples were taken as one sample from each dairy buffalos. It was noticed that 8 dairy buffalos had clinical mastitis.

 

 

II) Environmental samples:

1. Air samples: 60 air samples were collected as one sample from each animal house by means of liquid impinger as described by Cown et al. (1956). 20 ml of sterile normal saline was used for collecting airborne-dust particles. The liquid impinger was adjusted at a rate of 5 L/min. The amount of air sampled from each house was in ratio to the dimensions of the examined animal enclosure. The air samples were collected at a mid-day and during the ordinary activity of individuals. During air sampling, liquid impinger was moved inside the house in order to trap all the suspended dust particles to get a representative air samples.

2. Soil samples: 60 soil samples were collected as one sample from each house according to Clegg et al. (1983). Each sample was taken at a depth of 5 cm from different floor places of the houses and transferred to a clean sterile glass bottle, fitted with sterile ground glass stopper. After thorough mixing of each soil sample, 10 g was weighted on a sterile glass watch, and then sterile soy broth solution was added and aseptically strained through sterile gauze. The original soil filtrate was collected in a sterile flask for bacteriological examination.

3. Tap water samples: 60 tap water samples were taken as one sample from each house. Each tap water sample was collected in a clean sterile transparent 500 ml capacity glass bottle fitted tightly with ground glass stopper (according the recommendation of WHO, 1971). Before collection of samples, thoroughly cleaning and disinfection of the tap nozzles was done, then water was run for 3-4 min to rinse any accumulated dust and dirt.

4. Pail water samples: 60 pail water samples were taken as one sample from each house in a clean sterile transparent 500 ml capacity glass bottle fitted tightly with ground glass stopper (according the recommendation of WHO, 1971). The bottles were immersed several times in the collected water then filled with water sample.

- Phenotypic identification (Isolation and characterization of Staph. aureus): It was done according to Melter et al. (1999) and Lee (2003). The samples were immediately suspended in Tryptone Soya Broth (TSB, Oxoid) containing 10% NaCl and then incubated at 37°C for 24 h for selective enrichment of Staphylococci. Enrichment cultures were then streaked out on Baird-Parker agar and incubated at 35°C for 24 to 48 h. The colonies were tested (using conventional methods that included Gram staining, colonial morphology, coagulase test and urease assay) for Staph. aureus levels.

- API ID 32-STAPH: Some positive samples were also re-tested using API ID 32-STAPH (BioMe´rieux, Lyon, France, a commercial identification system for identification of Staphylococci) as confirmatory test for Staph. aureus. An API STAPH test strip was done following manufacturer’s protocol.

- Phenotypic identification (Isolation and characterization of MRSA):

The positive samples were re-streaked on mannitol salt agar (MSA, Oxoid) supplemented with 6 mg/L of oxacillin (Sigma, St. Louis, Mo.) for selective isolation of MRSA. A sample was recorded as positive for MRSA if one or more colonies were identified and one representative colony was chosen from each sample for further testing. MRSA isolates were stored at -70°C in freezer vials pending further PCR assay for the presence of the gene conferring methicillin-resistance (mecA gene).

- Preparation of whole-cell DNA extraction for PCR assay:

The method of Lee (2003) was used for whole-cell DNA extraction. Cells grown in 1.5 ml of Trypticase soy broth at 35°C for 20 h were harvested and centrifuged at 16,000 x g for 3 min. The pellet was washed with 1.0 ml of sterile distilled water, re-suspended in 50 µl of Triton X-100 lysis buffer (100 mM NaCl, 10 mM Tris-HCl [pH 8], 1 mM EDTA [pH 9], 1% Triton X-100), boiled for 10 min, and then centrifuged at 16,000 x g for 3 min. The suspension was cooled at room temperature for 5 min and centrifuged at 16,000 x g for 3 min. A total of 2 ml of the supernatant was used as the template.

- Genotypic identification (PCR assay for amplification of the mecA gene):

The presence of the mecA gene was verified for the oxacillin-resistant isolates by means of PCR. Amplification of the mecA gene was performed using the primers mecA1 and mecA2 (Table 1), yielding a PCR product of 533-bp. PCR was performed in a 25 µl volume with a PCR buffer containing 10 mM Tris-HCl [pH 8.3], 50 mM KCl, 1.5 mM MgCl2, a 200 µM concentration of each deoxynucleoside triphosphate (Promega, Madison, Wisconsin, USA), 2.5 U of Taq polymerase (Promega, Madison, Wisconsin, USA), and a 0.2 µM concentration of each primer. Amplification was carried out using 40 cycles of amplification at 94°C for 30 s, 55°C for 30 s, and 72°C for 1 min; this reaction was followed by 5 min of an additional extension at 72°C. PCR products were electrophoresed on a 1.5% agarose gel. A positive result was inferred by detection of a 533-bp band, which represented a part of the mecA gene.

 

Table 1. Primers used to type mecA of MRSA isolates.

 

Gene

Primer name

Primer sequence

Reference

mecA1

mecA1 primer

5'-AAAATCGATGGTAAAGGTTGGC

Murakami

et al. (1991)

mecA2

mecA2 primer

5'_AGTTCTGCAGTACCGGATTTGC

- Detection of PCR products:

The amplification products were identified by running 20 µl of the PCR reaction mixture in 2% agrose gel in Tris acid EDATA buffer. Gel was run at 100 V for 1 h, stained with ethodium bromide solution for 30 min and PCR product bands visualized under UV light. The expected PCR product is 533-bp.

- Ecological parameters:

Some ecological parameters were recorded during application of the study like rearing of dairy animals (either separate or mixed) and floor (either muddy or dry). After obtaining the results, the distribution of positive samples for mecA-positive MRSA strains were zoned according to the recorded observations.

- Statistical analysis:

The statistical analysis that represented in the correlation matrix of quantitative data was done with using SPSS version 11.0.

 

Results

 

533-bp→

   M     1       2       3      4      5      6       7      8       9     10

Figure 1. Sensitivity of PCR assay for detection of mecA-positive MRSA strains in the positive samples. M: 100 bp ladder, Lane 1: normal cow’s milk, Lane 2: mastitic cow’s milk, Lane 3: normal buffalo’s milk, Lane 4: mastitic buffalo’s milk, Lane 5: air of cows’ houses, Lane 6: air of buffalos’ houses, Lane 7: soil, Lane 8: tap water (negative), Lane 9: pail water of cows’ houses, Lane 10: pail water of buffalos’ houses.

 

533-bp→

    M     1       2       3      4      5      6

Figure 2. PCR assay showing the only negative samples for mecA gene MRSA in lane 3 (as negative) for tap water samples.

 

 

Table 2: Prevalence of positive samples for Staph. aureus, MRSA and mecA-positive MRSA.

Samples

Samples

No.

Staph. aureus

MRSA

mecA-positive

MRSA

+ve

No.

%

+ve

No.

%

+ve

No.

%

Cows’

milk

Normal

25

14

56

9

36

5

20

Mastitic

5

5

100

4

80

3

60

Buffalos’

milk

Normal

30

11

36.67

5

16.67

3

10

Mastitic

8

5

62.5

3

37.5

3

37.5

Air

Cows’ houses

30

14

46.67

8

26.67

5

16.67

Buffalos’ houses

30

16

53.33

7

23.33

3

10

Soil

Cows’ houses

30

20

66.67

10

33.33

8

26.67

Buffalos’ houses

30

17

56.67

9

30

5

16.67

Tap

water

Cows’ houses

30

6

20

1

3.33

0

0

Buffalos’houses

30

4

13.33

1

3.33

0

0

Pail

water

Cows’ houses

30

13

43.33

9

30

8

26.67

Buffalos’houses

30

14

46.67

9

30

7

23.33

Total

308

139

45.13

75

24.35

50

16.23

 

Table 3: Role of some ecological parameters on the distribution of mecA-positive MRSA.

mecA-positive MRSA

Related communities

Management area

Separate

rearing

Mixed

rearing

Muddy

floor

Dry

floor

Cows’

Milk

Normal

3

2

3

2

Mastitic

2

1

2

1

Buffalos’

Milk

Normal

2

1

2

1

Mastitic

1

2

1

2

Air

Cows’ houses

2

3

2

3

Buffalos’ houses

1

2

2

1

Soil

Cows’ houses

3

5

5

3

Buffalos’ houses

2

3

3

2

Tap

Water

Cows’ houses

0

0

0

0

Buffalos’ houses

0

0

0

0

Pail

Water

Cows’ houses

3

5

6

2

Buffalos’ houses

3

4

4

3

Total

22

28

30

20

50

50

 

Table 4: Some recorded studies about incidence of the isolated strains.

 

Samples

Staph. aureus

MRSA

mecA-positive MRSA

%

Country

Reference

%

Country

Reference

%

Country

Reference

Normal milk

28.93

Korea

Lee (2003)

0.9

Korea

Lee (2003)

0.34

Korea

Lee (2003)

15.9

Czech

Republic

Zouharova and

Rysanek (2008)

0

Switzerland

Huber

et al. (2010)

-

-

-

22.22

Czech

Republic

Stastkova

et al. (2009)

3.27

Czech

Republic

Stastkova

et al. (2009)

-

-

-

45.45

Egypt

Present

study

25.45

Egypt

Present

study

14.55

Egypt

Present

study

Mastitic milk

33.79

Egypt

Mokhbatly

et al. (2001)

13.73

Korea

Moon

et al. (2007)

-

-

-

40.5

Ethiopia

Workinen

et al. (2002)

5.56

Portugal

Pereira

et al. (2009)

-

-

-

100

Switzerland

Huber

et al. (2010)

1.41

Switzerland

Huber

et al. (2010)

-

-

-

76.92

Egypt

Present

study

53.85

Egypt

Present

study

46.15

Egypt

Present

study

Enviro-

nmental

0

Czech

Republic

Stastkova

et al. (2009)

0

Czech

Republic

Stastkova

et al. (2009)

0

Czech

Republic

Stastkova

et al. (2009)

43.33

Egypt

Present

study

22.5

Egypt

Present

study

15

Egypt

Present

study

Table 5: Correlation matrix among the isolated strains in milking surrounding environment of dairy cows.

 

Cows’ environment

Staph. aureus

MRSA

mecA-positive MRSA

Staph. aureus

1.000

 

 

MRSA

0.886*

1.000

 

mecA-positive MRSA

0.754

0.812*

1.000

 

    **Correlation is significant at the 0.01 level (2-tailed).

    *Correlation is significant at the 0.05 level (2-tailed).

 

Table 6: Correlation matrix among the examined samples in milking surrounding environment of dairy cows.

 

Cows’

environment

Normal

milk

Mastitic

milk

Air

Soil

Tap

water

Pail

water

Normal milk

1.000

 

 

 

 

 

Mastitic milk

0.998*

1.000

 

 

 

 

Air

0.992

0.982

1.000

 

 

 

Soil

0.954

0.933

0.984

1.000

 

 

Tap water

0.954

0.933

0.984

1.000**

1.000

 

Pail water

0.964

0.945

0.990

0.999*

0.999*

1.000

 

   **Correlation is significant at the 0.01 level (2-tailed).

    *Correlation is significant at the 0.05 level (2-tailed).

 

Table 7: Correlation matrix of some ecological parameters in milking surrounding environment of dairy cows.

 

Cows’

environment

Separate

rearing

Mixed

rearing

Muddy

floor

Dry

floor

Separate rearing

1.000

 

 

 

Mixed rearing

0.725

1.000

 

 

Muddy floor

0.886*

0.786*

1.000

 

Dry floor

0.502

0.741*

0.445

1.000

 

         **Correlation is significant at the 0.01 level (2-tailed).

          *Correlation is significant at the 0.05 level (2-tailed).

 

Table 8: Correlation matrix among the isolated strains in milking surrounding environment of dairy buffalos.

 

Buffalos’ environment

Staph. aureus

MRSA

mecA-positive MRSA

Staph. aureus

1.000

 

 

MRSA

0.899*

1.000

 

mecA-positive MRSA

0.783

0.971**

1.000

 

    **Correlation is significant at the 0.01 level (2-tailed).

     *Correlation is significant at the 0.05 level (2-tailed).

Table 9: Correlation matrix among the examined samples in milking surrounding environment of dairy buffalos.

 

Buffalos’

environment

Normal

milk

Mastitic

milk

Air

Soil

Tap

water

Pail

water

Normal milk

1.000

 

 

 

 

 

Mastitic milk

0.971

1.000

 

 

 

 

Air

0.998*

0.954

1.000

 

 

 

Soil

0.996

0.945

1.000*

1.000

 

 

Tap water

1.000*

0.971

0.998*

0.996

1.000

 

Pail water

0.999*

0.961

1.000*

0.999*

0.999*

1.000

 

  **Correlation is significant at the 0.01 level (2-tailed).

  *Correlation is significant at the 0.05 level (2-tailed).

 

Table 10: Correlation matrix of some ecological parameters in milking surrounding environment of dairy Buffalos.

 

Buffalos’

environment

Separate

rearing

Mixed

rearing

Muddy

floor

Dry

floor

Separate rearing

1.000

 

 

 

Mixed rearing

0.667

1.000

 

 

Muddy floor

0.889*

0.786*

1.000

 

Dry floor

0.692

0.889*

0.667

1.000

 

         **Correlation is significant at the 0.01 level (2-tailed).

          *Correlation is significant at the 0.05 level (2-tailed).

 

Discussion

 

It is obvious from the aforementioned results in Table 2 that, all the examined samples contained Staph. aureus with incidence in mastitic cows’ milk as 100%. It was hypothesized that Staph. aureus would be isolated from milk samples but the prevalence of MRSA would be low (Table 4), in agreement with Lee (2003); Stastkova et al. (2009); Virgin et al. (2009); Huber et al. (2010). Additionally, It was noticed that the prevalence of MRSA became lower than Staph. aureus not only in the examined milk samples but also in the surrounding environmental samples, with accordance to Stastkova et al. (2009).

Why the design study interested with the surrounding milking environment besides milk? The answer summarized in the fact that air and soil in the stables can play an important role in the spread of MRSA to the environment (Dewaele et al., 2008). As Staph. aureus is present in soil, water sources and air (Hamann, 1986) and the prevalence of MRSA in animals’ environment continues to rise, there is an inherent risk for new MRSA clones to evolve secondary to horizontal gene transfer and host selection pressure and then spread to human hosts (Lin et al., 2010). Thus, the presence of MRSA in animals is a concern not limited only to veterinarians and animal health care workers, but to the public health at large (Lin et al., 2010).

Here, accuracy and promptness in the detection of MRSA are of key importance in ensuring the correct antibiotic treatment in mastitic animals and control their spreading to the environment (Velasco et al., 2005). MRSA strains were isolated from mastitic milk in approximately double percentages more than normal milk (Table 2). MRSA has been detected in the milk of cows with mastitis in many studies (Lee, 2003; Leonard and Markey, 2006). Middleton et al. (2005) found all MRSA strains isolated from bovine species were from milk samples. Moreover, none of the MRSA isolates was recovered from environmental samples in the study of Stastkova et al. (2009).

Key question investigated is, why this study deals deeply with mecA gene-positive MRSA rather than just MRSA detection? Because mecA gene encodes resistance to methicillin (Bosgelmez-Tinaz et al., 2006); i.e. the definition of Staph. aureus isolates with phenotypic methicillin-resistance as MRSA requires demonstration of the mecA gene. The gene mecA has been reported to be responsible for methicillin-resistance (Zhang et al., 2004; Bagcigil et al., 2007; Zaraket et al., 2007; Zhang et al., 2008) that was determined during the genotypic identification step. If expressed, this gene confers resistance to all penicillins and cephalosporins (Brakstad and Maeland, 1997). The role of inappropriate antibiotic usage in the spread of antimicrobial resistance must also be considered. Exposure to broad spectrum antibiosis (notably 3rd generation cephalosporins and fluoroquinolones) has been associated with an increased risk of MRSA infection in several studies (Campillo et al., 2002; Hori et al., 2002).

The used PCR assay showed the sensitivity for detection of mecA-positive MRSA in the positive samples of clinically normal and mastitic milk, air, soil and pail water. While, tap water was found free from mecA-positive MRSA as shown in PCR gel photo as negative band of lane 8 (Figure 1) and of lane 3 (Figure 2).

The incidence of mecA-positive MRSA among the examined clinically mastitic milk (Table 2), emphasized the importance of detection of mecA gene in the isolated MRSA strains in order to ensure the appropriate antimicrobial chemotherapy of staphylococcal infections, particularly those from community associated infections (Palavecino, 2004; Kazakova et al., 2005). In a Korean dairy farms with livestock with mastitis problems, antibiotics (including members of the penicillin family such as ampicillin and penicillin) are largely used as a dry-cow treatment, although oxacillin and methicillin are rarely used in this veterinary field; this practice may contribute to increase incidence of MRSA strains in cows associated with mastitis (Lee, 2003).

It is clear from Table 2 that, the incidence of mecA-positive MRSA in mastitic milk was higher than clinically normal ones in both of cows’ and buffalos’ milk samples. Similarly, Lee (2003) found the all 12 mecA-positive MRSA isolates delivered from cattle specimens were originated from milk samples and 9 of them were from mastitic milk.

The correlation among the isolated strains in the milking surrounding environment of dairy cows was statistically analyzed in Table 5, showing a significant correlation (at 0.05 level) between Staph. aureus and MRSA and between MRSA and mecA-positive MRSA. A significant correlation between milk samples of cows’ milk was observed, in addition to a highly significant correlation between soil and water (Table 6). Also for the cows’ environment, mecA-positive MRSA strains were found distributed ecologically in muddy floor in a significant correlation with separate and mixed rearing with neighboring farm animals, and also between dry floor and mixed rearing (Table 7).

With forward to the buffalos’ environment, a high significant correlation (at 0.01 level) between MRSA and mecA-positive MRSA was recorded in Table 8, with possible contamination from air and water to milk samples as seen in the significant correlation between milk and air and water in Table 9. The significant correlation of ecological distribution of mecA-positive MRSA strains in the buffalos’ environment looked like of the cows’ environment (Table 10); concluding the role of dry floor incorporated with separate rearing in reducing the contamination to milk and considered as one of the good management.

MRSA may be present in milk as a result of contamination from udder or other environmental sources (air, soil, water). The significantly positive correlation between mecA-positive MRSA in milk and animal environment may be attributed to the high microbial contamination in dairy houses due to the long time spend by animals inside them (Schreinger and ruegg, 2003).

Regular audit of environmental cleaning should be carried out (Dancer, 2004). Otherwise, Lloyd et al. (2007) stated key points on dealing with MRSA in companion animal practice: 1) MRSA is prevalent in humans and animals and in their environment, 2) veterinary staff may be predisposed to MRSA carriage, 3) transfer of MRSA between people and animals can occur in both directions, 4) MRSA infection in animals usually has a good prognosis, 5) rigorous infection control policies and diligent hand washing can greatly reduce the spread of MRSA.

In conclusion, milk, air, soil and water from the milking environment of both dairy cows and buffalos were found contaminated with Staph. aureus, MRSA and mecA-positive MRSA strains with high incidences in the clinically mastitic milk of both dairy cows and buffalos. Significant correlations were observed between samples with highlighting the focus towards the possible contamination from environment into milk especially in the muddy floor incorporated with mixed rearing for both dairy cows and dairy buffalos.

 

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References
 
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Barber, M. (1961): Methicillin-resistant Staphylococci. J. Clin. Pathol. 14:385–393.
Bosgelmez-Tinaz, G.; Ulusoy, S.; Aridođan B. and Coskun-Ari, F. (2006): Evaluation of different methods to detect oxacillin resistance in Staphylococcus aureus and their clinical laboratory utility. Europ. J. Clin. Microbiol. Infect. Dis. 25:410–412.
Boyce, J.M. (2007): Environmental contamination makes an important contribution to hospital infection. J. Hosp. Infect. 65(2):50–54.
Boyce, J.M.; Potter-Bynoe, G.; Chenevert, C. and King, T. (1997): Environmental contamination due to methicillin-resistant Staphylococcus aureus: Possible infection control implications. InfectionControlHospital Epi. 18:622-627.
Brakstad, O.G. and Maeland, J.A. (1997): Mechanisms of methicillin resistance in Staphylococci. Apmis, 105:264-276.
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Clegg, F.G.; Chiejina, S.N.; Duncan, A.L.; Kay, R.N. and Wray, C. (1983): Outbreak of Salmonella Newport infection in dairy herds and their relationship to management and contamination of the environment. Vet. Rec. 112.
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