Milk is nature’s most nutritious food comprising of appreciable amount of
essential nutrients and micronutrients, such as proteins, lipids, carbohydrates,
vitamins and enzymes, and plays an irreplaceable role and position in the human diet
(Abriouel et al., 2008; Thorning et al., 2016). Because of its
nutritional properties, milk is also a good culture medium for a variety of spoilage
and potentially pathogenic microorganisms which are harmful to human health. With
the rapid development of China economy, the increasing demand for dairy products,
milk safety problems become the focus of social attention (Gabriels et al., 2015). The quality and safety of raw milk,
which is the upstream of dairy supply chain, are the main factors that limit the
sustainable and healthy development of dairy industry (Coorevits et al., 2008). The quality of milk is affected by many
factors: health status of cows, milk handling and hygiene of milking. The pathogenic
microorganisms in raw milk are mainly bacteria, its spoilage causes significant
economic losses for the food industry also can affect the health of consumers and
even lead to death while lowering the quality of milk (De Silva et al., 2016; Salovuo
et al., 2005).A growing number of scientific studies indicated that the contamination of raw milk
before milking was very low, mainly during milking and milk storage. Milk is
considered to be sterile when secreted from a healthy udder, after which numerous
contamination sources increase its bacterial load (Vacheyrou et al., 2011). The raw milk secreted by healthy cows is in a
relatively sterile state, but the raw milk is inevitably contaminated by
microorganisms at every procedures down the production chain, such as being squeezed
out and transportation to dairy processing plants (Sørensen et al., 2016).The research on the source of raw milk microorganisms has been a hot spot in foreign
countries in recent years. In China, the research focuses on the studies of
pathogenic bacteria but there is little research on the microorganism pollution
source of raw milk (Garedew et al., 2012;
Marjan et al., 2014). In order to control
the microbial contamination and milk safety risk in raw milk, bacteria population
dwelling in the production chain and environment of dairy industry in China should
be strictly regulated and controlled. Therefore, it is important to characterize
bacterial population and its risk factor in raw milk.The advent of high-throughput sequencing technology facilitates the inquiries in the
field of micro-ecology that had been deterred due to technological limits. In this
study, high-throughput sequencing technology was used to study the bacteria
population structure and diversity in raw milking procedure and dairy farm
environment, predicting the source of bacterial contamination in raw milk. The
results of this study can be used to predict the possible bacteria species in raw
milk, provides the basis for good hygienic practices and standardized operation
procedures in the milk production to deliver high-quality milk products.
Material and Methods
Study area and description of different sampling sites
The study was conducted in a large dairy farm (more than 1,500 cows in the
stockade) in Tangshan City, Hebei Province, China (118.02°E,
39.63°N). The Milking Parlour, milk-storing hall and Sports Ground were
selected as sampling sites. The sampling sites were cleaned and rinsed daily
after milking, samples collected included pre-sterilized cow’s teats
(C1), post-sterilized cow’s teats (C2), milking cluster (E), milk in
storage tank (M1), milk in transport vehicle (M2), milk storage equipment (E2),
cow dung samples (F) and cow’s drinking water (W). The samples were
stored in liquid nitrogen tank for a short time after collection. Study was
performed in September of 2019, and samples were taken 3 times per day, for a
consecutive 5 days. The samples collected at the same day was mixed together and
serve as a replicate. For each site, 5 repeats were sequenced and analyzed.
Study design and sample collection
In this study, 8 typical sites in dairy farm in Hebei province of China were
selected, the bacterial population composition and diversity were studied by
high-throughput sequencing. Samples were collected in the experiment dairy farm.
Collection of samples C1.1–C1.6: six healthy cows were randomly selected,
samples were taken with sterile cotton swab from the area of 1 cm2
around the teats, and then placed in 10 mL sterile normal saline immediately;
collection of samples C2.1–C2.6: Samples were taken with sterile cotton
swab from the cows corresponds to C1 in the same way; samples collection of
E.1–E.6: according to the distribution of the milking cluster, 6 milking
cluster that can cover the whole milking parlor were selected, and the surface
of the clusters were smeared with sterile cotton swabs for 3 times and placed in
sterile saline solution immediately. Collection of M1.1–M1.6 and
M2.1–M2.6 samples: after proper blending, the liquid milk bucket was used
to collect milk from the surface, the middle and the bottom of the 3 points then
thoroughly mixed and evenly, respectively 15 mL milk was taken and divided into
6 sample collection tubes; collection of E2.1–E2.6 samples: wiping with
sterile cotton swab and placed in 10 mL sterile normal saline. Collection of
F.1–F.6 samples: 6 different directions of cow’s sports field were
selected, collect the excrement about 1g that does not have the impurity and put
it into aseptic test tube with aseptic medicine spoon. Collection of
W.1–W.6 samples: after each sampling site >10L breeding water was
filtered, the filter membrane (cut or removed) was transferred to a sterile
centrifuge tube for storage and inspection. All samples were stored in liquid
N2 for long-term preservation immediately after collection.
DNA extraction and libray construction
DNA was extracted from 48 samples of 8 groups. The V3–V4 hypervariable
region of 16S rRNA were amplified by PCR for barcoded pyrosequencing. The 16S
rRNA gene V3–V4 region of bacteria was amplified using the universal
Forward: 5’-ACTCCTACGGGAGGCAGCAGCAG-3’ and reverse
5’-GGACTACHVGGGTWTCTAAT-3’. The PCR amplification products were
purified and dissolved in Elution Buffer by Agencourt AMPure XP magnetic beads,
and then the library was constructed. Agilent 2100 Bioanalyzer was used to
detect the range and concentration of fragments in the library, the V3–V4
region of the 16S rDNA gene was amplified with the qualified sample DNA as the
template, and the magnetic beads were used to screen Amplicon fragments.
Finally, the qualified library was used for Cluster preparation and Paired-end
sequencing. The data obtained from the computer were used for the corresponding
bioinformatics analysis (Avershina et al.,
2013; Smith and Peay,
2014).
Data analysis
The data from Illumina platform was filtered to remove the low-quality sequences
and the remaining high-quality valid sequences, which can be used for subsequent
analysis (Fadrosh et al., 2014; Sørensen et al., 2016); FLASH
V1.2.11 software was used to assemble the paired sequences obtained by
paired-end sequencing into a sequence by overlapping relationship, and tag
sequences with high variable region were obtained. The minimum matching length
was set to 15 bp and the allowable mismatch rate of Overlap region was
10%. Sequences without overlapping relationship were removed (Cicconi-Hogan et al., 2013; Magoč and Salzberg, 2011); USEARCH
V9.1 was used to cluster the splice effective sequences with 97%
similarity, and then the OTU representative sequences were compared with the
Greengene database by RDP Classifer V2.2 software, and the species annotation of
OTU was carried out (Edgar, 2013; Edgar et al., 2011; Fouts et al., 2012; Wang et
al., 2007); based on the results of OTU and species annotation,
species complexity analysis and inter-group species difference analysis were
performed.
Abundance analysis, rarefaction analysis and significance analysis of
intergroup differences
The α-diversity of 8 groups was calculated using the VEGAN package in R
3.4.3, and the following indices were analyzed: observed species, Chao, Ace,
Shannon, Simpson, and Coverage. The α-diversity values of the samples
were calculated using the Mothur (v1.31.2) software, and the corresponding
rarefaction curves, Heatmap analysis β-Diversity heatmaps and Clustering
trees were generated using the R (v3.1.1) software. Principal component analysis
(PCA) was conducted to compare similarities among samples using R and the
corresponding rarefaction curves were generated using the R (V3.1.1). Intergroup
differences in alpha-diversity indices were presented as box plots. Histograms
were constructed for all taxa at the genus level. Cluster analysis was performed
using the QIIME (v1.80) software. An iterative algorithm was used to perform
sampling of 75% of the sequences in a sample with the least number of
sequences using weighted and unweighted taxon abundance data, respectively. The
final statistical results were obtained by analyzing the overall statistics
after 100 iterations. The clustering method used was the unweighted pair group
method with arithmetic mean (UPGMA). The significance of intergroup differences
was analyzed using the R software rank-sum test.
Results
Total viable count of 8 tested sites
The total viable count of the 8 tested sites varied substantially. Due to the
nature of samples, the total viable count is measured separately in F, which was
presented in different unit (CFU/g) and showed extraordinarily high Total viable
bacterial counts (TVC; Table 1). Overall,
E2 and W demonstrated the lowest TVC, C2, and E present moderate amount of TVC.
C1, M1, and M2 demonstrated similar TVC. We can see that the TVC increases
significantly from E to M1, and slightly from M1 to M2, indicating that
additional measures are desired for the storage and transportation of milk.
Table 1.
Total viable bacterial counts (TVC) of 8 sites
Site location
Total viable bacterial count of 8
test sites
Pre-sterilized cow’s teats
(C1)
3.2×106
CFU/mL
Post-sterilized cow’s teats
(C2)
0.89×105
CFU/mL
Milking cluster (E)
0.62×105
CFU/mL
Milk in storage tank (M1)
3.5×105
CFU/mL
Transport vehicle (M2)
4.2×105
CFU/mL
Storage equipment (E2)
0.21×105
CFU/mL
Cow’s dung samples (F)
42×107 CFU/g
Drinking water (W)
0.2×105
CFU/mL
Statistical analysis of sequencing results, verification of sampling depth,
and OTUs composition analysis
High-throughput sequencing of 16Sr RNA (V3–V4 region) of bacterial genome
was carried out on 48 samples from 8 different sampling sites, and the
composition of bacterial population was obtained. As shown in Fig. 1, the rarefaction curves of all samples
had reached plateaus with the current sequencing, and the species had no more
obvious increase as the sample number increased, which indicated that the
sequencing depth and coverage was sufficient and the sample volume in our study
was relatively large enough to reflect the species richness.
Fig. 1.
Rarefaction curves of the bacterial communities at different sampling
sites.
C1, pre-sterilized cow’s teats; C2, post-sterilized cow’s
teats; E, milking cluster; M1, milk in storage tank; M2, transport
vehicle; E2, storage equipment; F, cow dung samples; W, drinking
water.
Rarefaction curves of the bacterial communities at different sampling
sites.
C1, pre-sterilized cow’s teats; C2, post-sterilized cow’s
teats; E, milking cluster; M1, milk in storage tank; M2, transport
vehicle; E2, storage equipment; F, cow dung samples; W, drinking
water.A total of 2,624,955 original sequences and 2,181,981 quality control sequences
were obtained from the 48 samples at 8 different sampling sites. After
clustering the merged tags, 45,726 OTUs were obtained from the 16S rRNA data at
97% similarity. Among them, the OTUs in E group were the most, reaching
8,408 OTUs, while the OTUs in E2 group were the least, only 2, 108 OTUs (Table 2).
Table 2.
Sequence information of samples
Samples ID
Samples clean reads
Clean tags
Tags length (bp)
OTUs
C1
328,104
320,352
418
7,605
C2
328,427
320,149
416
7,502
E
328,883
318,290
415
8,408
M1
327,901
314,746
417
6,016
M2
327,824
317,880
417
5,871
E2
328,157
317,462
413
2,108
F
328,660
321,428
414
5,544
W
326,999
321,884
413
2,672
C1, pre-sterilized cow’s teats; C2, post-sterilized
cow’s teats; E, milking cluster; M1, milk in storage tank;
M2, transport vehicle; E2, storage equipment; F, cow dung samples;
W, drinking water.
C1, pre-sterilized cow’s teats; C2, post-sterilized
cow’s teats; E, milking cluster; M1, milk in storage tank;
M2, transport vehicle; E2, storage equipment; F, cow dung samples;
W, drinking water.
OTUs abundance analysis
Among the 48 samples in 8 sampling sites, the common number of OTUs in 8 groups
is 372, which accounted for 4.4%–17.6% of the total number
of OTUs in each group, of which C1 group has 69 unique OUTs, C2 has 78 unique
OTUs, E has 174 unique OUTs, M1 has 161 unique OTUs, M2 has 140 unique OTUs, E2
has 92 unique OTUs, F only has 6 unique OTUs and W has 69 unique OTUs, which
accounting for 0.91%, 1.04%, 2.07%, 2.68%,
2.38%, 5.69%, 0.11%, 2.58% of the total OUTs,
respectively (Fig. 2). In addition, the
results also showed that among the 8 groups, E (milking equipment) group had the
most unique OTUs, indicating that E group is most diverse in bacterial
populations and post a key factor influencing the quality of milk.
Fig. 2.
The picture of OTU Core-Pan of different sampling sites.
C1, pre-sterilized cow’s teats; C2, post-sterilized cow’s
teats; E, milking cluster; M1, milk in storage tank; M2, transport
vehicle; E2, storage equipment; F, cow dung samples; W, drinking
water.
The picture of OTU Core-Pan of different sampling sites.
C1, pre-sterilized cow’s teats; C2, post-sterilized cow’s
teats; E, milking cluster; M1, milk in storage tank; M2, transport
vehicle; E2, storage equipment; F, cow dung samples; W, drinking
water.
Diversity and composition of bacterial communities
The Alpha diversity indices of 8 groups were as shown in Table 3, and there were significant differences
(p<0.05, respectively). The bacterial population richness of C1 and E
group were the highest among all sampling sites, and Chao index, Ace index and
Shannon index of C2, M1, M2, F groups were significantly higher than E2 and W
groups, but Simpson index of C2, M1, M2, F groups was significantly lower than
that of E2 and W groups. The Shannon index of E, M1 and M2 was higher than that
of the other groups, which indicated that the bacterial population of the
milking cluster and raw milk samples had higher diversity, and the species
diversity of E2 and W was the lowest.
Table 3.
The Alpha diversity index of the samples
Sample/info
Sobs index
Chao index
Ace index
Shannon index
Simpson index
Coverage
C1
1,267.530±171.852
1,510.231±201.751
1,515.750±205.170
4.827±0.7345
0.041±0.043
0.993±0.002
C2
1,250.333±132.952
1,360.722±216.808
1,361.686±229.008
5.373±0.297
0.017±0.009
0.996±0.003
E
1,401.333±152.792
1,489.633±203.448
1,480.794±202.806
5.667±0.063
0.012±0.001
0.997±0.002
M1
1,002.667±51.259
1,018.735±50.420
1,011.785±52.527
5.779±0.092
0.008±0.001
0.999±0.000
E2
351.333±159.439
383.601±149.439
372.815±151.463
2.567±0.889
0.245±0.167
0.999±0.000
M2
978.566±18.328
998.733±33.006
986.595±21.047
5.772±0.0292
0.008±0.001
0.999±0.000
F
924.000±169.513
1,116.558±241.009
1,091.290±235.108
5.083±0.124
0.024±0.003
0.993±0.002
W
445.333±0.000
682.374±519.825
837.135±508.115
2.015±1.246
0.387±0.187
0.995±0.004
C1, pre-sterilized cow’s teats; C2, post-sterilized
cow’s teats; E, milking cluster; M1, milk in storage tank;
M2, transport vehicle; E2, storage equipment; F, cow dung samples;
W, drinking water.
C1, pre-sterilized cow’s teats; C2, post-sterilized
cow’s teats; E, milking cluster; M1, milk in storage tank;
M2, transport vehicle; E2, storage equipment; F, cow dung samples;
W, drinking water.
Analysis of taxonomic annotations
Comparison of OTUs against the database at the phylum, class, order, family,
genus, and species levels resulted in the annotation of the 16S rRNA
sequence-based OTUs to 36 phyla, 96 classes, 186 orders, 353 families, 766 genus
and 896 species.
Comparative analysis of bacterial composition in different sampling
sites
The NGS method was used for comparative analysis with Greengene database.
Approximately 36 phyla and 799 genera were detected. The predominant phylum was
Firmicutes which account for 32.36% (C1), 44.62% (C2),
44.71% (E), 41.10% (M1), 45.08% (M2), 8.08% (E2),
53.38% (F), 4.47% (W) in each group; proteobacteria was the
subdominant phylum, which account for 20.72% (C1), 16.01% (C2),
17.39% (E), 15.49% (M1), 13.06% (M2), 21.88% (E2),
3.98% (F). Proteobacteria was the absolute dominant phylum accounting for
81.79% in W group; actinobacteria accounts for 56.43% in E2 group.
Minor phyla in 8 groups including Bacteroidetes and Actinobacteria (Fig. 3A).
Fig. 3.
Relative abundance and diversity of bacteria phylum (A) and bacteria
genus (B) in different sampling sites.
The x-coordinate is the sample name, and the y-coordinate is the relative
abundance of the species annotated. The classification level was not
annotated were grouped at unclassified and with an abundance of less
than 20% in a sample were group at others. C1, pre-sterilized
cow’s teats; C2, post-sterilized cow’s teats; E, milking
cluster; M1, milk in storage tank; M2, transport vehicle; E2, storage
equipment; F, cow dung samples; W, drinking water.
Relative abundance and diversity of bacteria phylum (A) and bacteria
genus (B) in different sampling sites.
The x-coordinate is the sample name, and the y-coordinate is the relative
abundance of the species annotated. The classification level was not
annotated were grouped at unclassified and with an abundance of less
than 20% in a sample were group at others. C1, pre-sterilized
cow’s teats; C2, post-sterilized cow’s teats; E, milking
cluster; M1, milk in storage tank; M2, transport vehicle; E2, storage
equipment; F, cow dung samples; W, drinking water.The dominant genus in 8 groups were Acinetobacter,
Arthrobacter, Kocuria,
Chryseobacterium, Clostridium,
Corynebacterium, Enhydrobacter,
Microbacterium, Prevotella,
Macrococcus. Considerable difference was noted between the
bacterial compositions of the 8 groups. The bacterial composition in C1, C2, and
E is most similar, the most abundant genus were Acinetobacter,
Arthrobacter and Sphingobacterium. The
dominant bacterial genera were Kocuria,
Microbacterium and Chryseobacterium in E2
group, which account for 30.04%, 10.89% and 8.69%,
respectively; The predominant genera was Acinetobacter in 8
groups which accounted for 13.06% (C1), 6.31% (C2), 5.84%
(E), 5.04% (M1), 3.90% (M2), 6.96% (E2), F (0.81%),
W (7.56%) at each sampling sites. Arthrobacter was the
subdominant bacteria genera, which accounted for 7.43% (C1), 4.01%
(C2), 3.65% (E), 0.25% (E2), 0.86% (M1), 1.06% (M2),
F (0.01%), W (0.02%) at each sampling site, Ranking the third
dominant bacteria genera was Sphingobacterium, which accounted
for 2.69% (C1), 1.03% (C2), 0.49% (E), 0.14% (E2),
0.17% (M1), 0.18% (M2), F (0.02%), W (0.03%) in each
sampling site, respectively (Fig. 3B).
Heatmap analysis
Heatmap clustering analysis were performed at the genus level, and all taxa with
an abundance of less than 20% in a sample were group at others. The top
10 most abundant bacterial species, based on the 16S rRNA sequences, were in
descending order of Acinetobacter,
Arthrobacter, Sphingobacterium,
Macrococcus, Corynebacterium,
Knoellia, Psychrobacter,
Ruminobacter, Kocuria,
Chryseobacterium. The bacteria population of the collected
samples was vertically clustered into two large branches according to the
evolutionary relationship. Among the 8 group, C1, C2, and E were relatively
close to each other in the graph, which shows that the diversity of species
composition is small. The TOP3 bacteria population were
Acinetobacter C1 (13.06%), C2 (6.31%), E
(5.84%), Arthrobacter C1 (7.43%), C2
(4.01%), E(3.65%) and Corynebacterium C1
(1.57%), C2 (2.11%), E (2.36%). However,
Chryseobacterium was the predominant genus in M1 and M2
group, which account for M1 (1.96%), M2 (2.26%),
Staphylococcus was the subdominant genus in M1, M2 groups,
which account for M1 (1.91%), M2 (2.15%). The top 3 dominant genus
were Kocuria (30.04%), Microbacteria
(10.89%) and Rossia (6.92%) in E2 group, while
the predominant genus was Arcobacter (57.65%) in W
group, which indicated that the bacterial population composition in group E2 and
W was quite different from that in other groups (Fig. 4).
Fig. 4.
Realtive abundance heatmap of the bacteria in the level of
genus.
C1, pre-sterilized cow’s teats; C2, post-sterilized cow’s
teats; E, milking cluster; M1, milk in storage tank; M2, transport
vehicle; E2, storage equipment; F, cow dung samples; W, drinking
water.
Realtive abundance heatmap of the bacteria in the level of
genus.
C1, pre-sterilized cow’s teats; C2, post-sterilized cow’s
teats; E, milking cluster; M1, milk in storage tank; M2, transport
vehicle; E2, storage equipment; F, cow dung samples; W, drinking
water.
Cluster analysis of species compositions in different samples
Cluster analysis showed that the bacterial population compositions of the M1 and
M2 were quite similar, the bacterial population compositions of the C1, C2, and
E were quite similar, but E2 group and W group differs in species composition
from the other 6 groups (Fig. 5).
Fig. 5.
Samples clustering result (description,
weighted_unifrac).
The same color represents the samples in the same group. Short distance
between samples represents high similarity. C1, pre-sterilized
cow’s teats; C2, post-sterilized cow’s teats; E, milking
cluster; M1, milk in storage tank; M2, transport vehicle; E2, storage
equipment; F, cow dung samples; W, drinking water.
Samples clustering result (description,
weighted_unifrac).
The same color represents the samples in the same group. Short distance
between samples represents high similarity. C1, pre-sterilized
cow’s teats; C2, post-sterilized cow’s teats; E, milking
cluster; M1, milk in storage tank; M2, transport vehicle; E2, storage
equipment; F, cow dung samples; W, drinking water.
Significance analysis of intergroup differences
PCA was performed based on the OTUs abundance. The composition of bacteria
population in two raw milk (M1 and M2 group) were very close in the figure, and
some sites almost overlapped. In addition, the bacterial population in C1, C2,
and E were relatively similar. However, there were significant differences
between the W, E2 and other 6 groups in the bacterial population compositions
(Fig. 6). The bacterial population
structure of the 8 groups showed an obvious clustering phenomenon, with most of
them clustered to the left and only a few to the right.
Fig. 6.
Principle components analysis based on operational taxonomic units
abundance (description).
X-axis, 1st principle component and Y-axis, 2nd principal component.
Number in brackets represents contributions of principle components to
differences among samples. Each small shape in the figure above
represents a sample. The shapes of the same color are from the same
group. The closer the distance between the two shapes is the smaller,
the difference in community composition is high similarity. C1,
pre-sterilized cow’s teats; C2, post-sterilized cow’s
teats; E, milking cluster; M1, milk in storage tank; M2, transport
vehicle; E2, storage equipment; F, cow dung samples; W, drinking
water.
Principle components analysis based on operational taxonomic units
abundance (description).
X-axis, 1st principle component and Y-axis, 2nd principal component.
Number in brackets represents contributions of principle components to
differences among samples. Each small shape in the figure above
represents a sample. The shapes of the same color are from the same
group. The closer the distance between the two shapes is the smaller,
the difference in community composition is high similarity. C1,
pre-sterilized cow’s teats; C2, post-sterilized cow’s
teats; E, milking cluster; M1, milk in storage tank; M2, transport
vehicle; E2, storage equipment; F, cow dung samples; W, drinking
water.
Discussion
High-throughput next-generation sequencing, also known as “next
generation” or “deep” sequencing, which can sequence hundreds
of thousands to millions of DNA sequences in one time, so it is also called deep
sequencing (Ercolini et al., 2012; Quigley et al., 2012). In recent years,
high-throughput sequencing technology has been widely used in the study of dairy
products, gradually changing from the identification of dominant flora to the
studies on the overall diversity of microorganisms (Abriouel et al., 2008; Liu et al.,
2015). Due to the complexity of the dairy chain, microbial contamination
can occur in different steps of production, leading to the development of adequate
control plans for monitoring the microbial quality and safety of milk since
production to processing (Wouters et al.,
2002). Through high throughput sequencing technology, the key nodes of
whole milking procedure which affect raw milk quality were deduced, and the key
influencing factors of raw milk quality in the feeding environment of dairy farms
were clarified.Milk in healthy udder cells is thought to be sterile (Johnson et al., 2015), but there after becomes colonised by
microorganisms from a variety of sources, including the teat apex, milking
equipment, air, water, feed, grass, soil and other environments (Vacheyrou et al., 2011). Previous study found
several microbial groups in different milking sites, some groups were used to assess
the hygienic procedures and conditions during milking, such as Mesophilic
aerobes and Coliforms (Wouters et al., 2002), some groups were considered as relevant spoilage
agents, such as Sphingobacterium, Pseudomonas, and
Clostridium; many bacteria were researched due to their
pathogenic potential, such as Acinetobacter,
Arthrobacter, Staphylococcus,
Campylobacter and Arcobacter, and other
bacteria can possess beneficial features, like some Lactobacillus,
Lactococcus, Streptococcus and
Enterococcus (Vacheyrou et al.,
2011). This huge diversity is a challenge in the dairy industry,
addresses their sources in different production procedure, which can guide the raw
milk utilization by consumers and dairy industry.This study presented a novel investigation of the bacterial population in china dairy
farms. The predominant phylum was Firmicutes which account for 32.36% (C1),
44.62% (C2), 44.71% (E), 41.10% (M1), 45.08% (M2),
8.08% (E2), 53.38% (F), 4.47% (W) in each group, The
predominant genera was Acinetobacter in 8 groups which accounted
for 13.06% (C1), 6.31% (C2), 5.84% (E), 5.04% (M1),
3.90% (M2), 6.96% (E2), F (0.81%), W (7.56%) at each
sampling sites. Milking parlors as the very heart of every dairy and where milking
process are concerned, hygiene is key (Wouters et
al., 2002). Udder health is an essential component of quality milk,
mastitis is the common disease found in dairy herds in China. Cow teats surface can
contain a high diversity of bacteria, this study revealed that
Acinetobacter (13.06%) and Arthrobacter
(7.43%) were detected in C1 but Acinetobacter (6.31%)
and Arthrobacter (4.02%) in C2, there is a significant
decrease in bacterial richness. Notably, teats disinfection is very important before
milking which can reduce the diversity and richness of bacteria population. Previous
study also shown that the use of some disinfectant products for pre-milking teat dip
preparation can have beneficial effects on reducing the levels of staphylococcal and
streptococcal pathogens on teat skin (Gleeson et
al., 2009). Jones and Newburn
(2002) found the two basic principles of mastitis control are first,
elimination of existing infections and, secondly, prevention of new infections.
Milking cluster (E) which can direct touch cow’s udder, incomplete cleaning
can lead to a risk of mastitis, so, its cleanliness can directly affect the quality
of raw milk. According to the results of Samples Clustering (Description,
Weighted_Unifrac) and PCA, there was a notable clustering phenomenon toward
the C1, C2, and E which may have been caused by the bacterial population composition
of the C1, C2, and E were quite similar, it revealed that much of variance in
bacterial communities of above 3 groups was associated with cleanness of cow teats
and cleanness of milking cluster. The Top 3 dominant bacterial genus in F group were
Treponema (2.84%), Prevotella
(1.97%), Clostridium (1.60%), this study shows
composition of F group was similar to the C1, C2, E, M1, and M2 groups, which
further indicated that faeces could not be cleaned in time, microorganisms can
cross-contaminate the milking cluster by adhering to the cow’s body or by air
flow. The top 3 dominant genus in E2 group were Kocuria
(30.04%), Microbacteria (10.89%) and
Rossia (6.92%), while the predominant genus was
Arcobacter (57.65%) in W group, which indicated that the
bacterial population composition in group E2 and W was quite different from that in
other groups. Our study showed that Acinetobacter (5.04%),
Chryseobacterium (1.96%) and Treponema
(1.68%) were the dominant genus in M1. However,
Acinetobacter (3.90%), Lactobacillus
(2.62%), Chryseobacterium (2.26%) were the dominant
genus in M2. Cluster analysis showed that the bacterial population composition of M1
and M2 were quite similar, the results are partly consistent with previous studies,
Lafarge and Hagi believed that there were two main strains in the milk,
Lactobacillus and Staphylococcus (Hagi et al., 2010; Hagi et al., 2013). Delbès et al. (2007) detected that the dominant bacteria in milk
were Clostridium and Lactobacillus. Previous study
shows that the dominant bacteria detected in the commercial milk were
Acinetobacter and Pseudomonas. In addition,
cold-resistant bacteria are the main spoilage bacteria in milk, and
Gammaproteobacteria and BacillusI are also the
dominant bacteria with contents more than 1% in this study (Raats et al., 2011). Rasolofo et al. (2010) believed that the abundance of these two
bacteria would increase with the prolongation of refrigeration time, so the
processing time of raw milk into commercially available milk should be shortened.
Milk storage equipment (E2) can contain a reservoir of bacteria, this study detected
that Kocuria (30.04%), Chryseobacterium
(8.69%) and Enhydrobacter (6.64%) were the dominant
genus bacteria in E2. The bacterial population composition of E2 differs from other
7 groups, the reason for this difference may be caused by the tempe rature of the
milk storage equipment and the microorganisms in the environment.In conclusion, the difference of bacteria species diversity in different sampling
sites may be related to the environmental health status of each space, the timely
cleaning and wiping of bovine body, the sterilization of milking cluster and the
transmission of aerosol pollution. In this study, a variety of bacteria genera were
identified, including some pathogenic bacteria genera such as
Acinetobacter, Arthrobacter,
Sphingosinolium, Staphylococcus,
Pseudomonas and Corynebacterium which were the
main dominant bacteria genus in different milking sites.
Acinetobacter and Corynebacterium can cause
bovinemastitis, Sphingomonas can decompose milk fat and milk
protein and remove low milk protein activity. Pseudomonas
aeruginosa can also cause mastitis in cows. Bacillus
anthracis can produce enterotoxin, which is highly pathogenic to humans
and animals (Ercolini et al., 2012; Quigley et al., 2012).
Acinetobacter as a kind of conditional pathogenic bacteria
causing the cow’s mastitis, among 8 groups C1 (the cow teats before
disinfection) with the highest percentage (13.06%), followed by W
(7.56%), E2 (6.96%) and C2 (6.31%), the result suggests teats
disinfection before milking is crucial and the cleanliness of the milk storage
equipment also affects the quality of raw milk, the results also indicated that the
cleanliness of drinking water in the farm directly affected the quality of raw
milk.In summary, in the traditional dairy farms of China, there are two factors can affect
the quality of raw milk, one is the milking procedure, the other is the
environmental sanitation. Milking procedure includes cow’s teats, milking
cluster, milk storage equipment, milk from milk storage tanks and milk from
transportation vehicles, the sampling sites in this study were C1, C2, E, E2, M1,
and M2, while the farm environment mainly includes faeces and water, sampling sites
were F and W in this study, based on the results of our study, bacterial population
composition in different sampling sites of milking was significantly different,
therefore, we believe that there is a considerable correlation between the proper
milking procedure and raw milk quality. The timely disposal of excrement and the
cleanliness of drinking water also helpful to guarantee the quality of raw milk,
affect the quality of raw milk, pathogenic bacteria of messy environment in the
dairy farms will through the injured cow nipple cause mastitis, therefore, it is
necessary for the quality of raw milk to be ensured by the proper milking and the
hygienic condition in the course of dairy cow breeding.China has formulated and implemented a nationwide raw milk quality and safety testing
plan since 2008, but compared with the development needs of dairy industry, the
systematic research is still weak. This study from the perspective of industrial
chain, systematically analyzed the effect of milking behavior and environment on the
quality of raw milk in diary farm. About 90% of the bacterial communities
which cannot be isolated in lab were obtained through high-throughput sequencing,
this study gave a comprehensive and in-depth understanding of the bacterial
diversity and composition along milking in dairy farms. It is of great significance
to grasp the key nodes in the milk production process as a whole and provide a
strong scientific basis for the quality and safety supervision of raw milk.