1. Introduction
Mycotoxins are low molecular weight secondary metabolites, produced by toxigenic fungi during their morphological and chemical differentiation, and are highly prevalent in many foods and feedstuffs [
1]. Currently, of over three hundred types of mycotoxins uncovered, aflatoxin is the most potent carcinogenic agent, threatening humans, and animal health, and primarily produced by
Aspergillus flavus and
Aspergillus parasiticus [
2,
3]. Specifically, four types of aflatoxins: B
1, B
2, G
1, and G
2, are known to be produced by Aspergillus species [
4,
5]. However, aflatoxin M
1 (AFM
1) is the hydroxylation byproduct of aflatoxin B
1 in the liver of lactating dairy cows that ingested the contaminated feedstuffs [
3,
6].
Milk is the main food in many countries, due to its valuable source of nutrients, where milk from dairy cows shares a significant contribution. Globally, 81 percent or 746 million tons of milk has been produced by dairy cows in 2021 [
7]. Similarly in Africa, 77% of the total milk were come from dairy cows [
8]. Specifically, of a total of 7.12 billion liters of milk produced in Ethiopia in 2020/21, 65.84% or 4.69 billion liters of milk were accounted as dairy cow’s milk [
9]. However, the presence of AFM
1 in the milk of dairy cows raises serious concerns of food safety and is usually, linked to cancer diseases, hepatotoxins, and others in humans and animals [
3,
10]. Subsequently, the International Agency for Research on Cancer [
11], has classified AFM
1 as Group 2B carcinogenic agent. Moreover, the association of a lasting adverse health condition (like child stunting) with children consuming AFM
1-containing milk, elevates its public health importance, where milk is widely regarded as a complementary diet for them [
10,
12]. The primary animal exposure route of aflatoxins is through ingestion of frequently contaminated crops, such as cereal grains, oilseeds, nuts, or others that are integral parts of feed ingredients [
13,
14]. While, human exposure to AFM
1, is mainly, through the consumption of contaminated milk and milk products [
14].
The proliferation of Aspergillus fungi and associated aflatoxins are determined by the host, fungus, and environmental stresses interaction [
1]. Thus, Medina et al., [
15] indicated that hot temperature and high moisture/humidity increase aflatoxin excretion, by modulating aflatoxin synthesizing genes. The hot and humid climates, with mean annual rainfalls >700 mm and relative humidity >60% in tropical and subtropical climates provide a conducive environment for Aspergillus proliferation, and concomitant aflatoxin M
1 in milk [
3]. Additionally, pre- and postharvest management practices such as cropping system, time of harvest, stage of dryness, storage conditions, and transportation have significantly contributed to fungal development in feeds and ultimately, lead to aflatoxins contamination in feed and milk [
16,
17,
18].
Thus numerous studies in sub-Saharan African countries with warm-humid tropics and subtropics climates were highly prevalent with AFM
1 in the raw milk of dairy cows. Accordingly, Kagera et al., [
19] reported, 98.8% (N=84) prevalence and 83.66±64.68 ng/L mean of AFM
1 in raw milk collected from the smallholder dairy farmers in the Kasarani sub-county of Kenya. In the same country, a higher prevalence of 100%, (N=150) was reported with 58% of the sample exceeding the EU tolerable limit [
20]. However, Anyango et al., [
21] reported, a comparably lower occurrence of AFM
1 (37.5%, N=72) in raw milk collected from the urban and peri-urban areas of Kisumu county in Kenya, which 26.4% exceed the tolerable limit of EU standard.
Similarly, a 100% (N=112) prevalence and 0.55±0.18 µg/L level of AFM
1 was reported in raw milk of dairy cows collected from three agro-ecological zones in Malawi, which 98% and 22% of the sample exceeded the tolerable limit of EU and FDA, respectively [
22]. Of 25 milk samples collected from Dairy Farms in Khartoum, 92% contain AFM
1 [
23]. Likewise, Nishimwe et al., [
24] reported, a 91.8% (N=170) prevalence, and 0.89±1.64µg/L mean of AFM
1 with a 38.8% sample exceeding the EU tolerable limit in Rwanda. Also, a high prevalence of AFM
1 (83.8%, N=37) was reported in milk collected from smallholder dairy farmers in Tanzania, where 100% and 16.1% exceeded the EU and FDA tolerable limits, respectively [
25]. While in a recent finding by Kitigwa et al., [
26], a lower prevalence of 30.7% with 27.9% exceeding the EU limit, was reported in milk samples collected from the smallholder dairy farmers in Tanzania.
Like in many East African countries, research revealed that AFM
1 posed a critical challenge for the dairy industry, with the significant prevalence in raw milk of dairy cows in Ethiopia. Accordingly, Dawit et al., [
27] reported, a 100% prevalence and 4.91 µg/L average of AFM
1 in 110 raw milk collected from the greater Addis Ababa milk sheds, which 97.8% of the sample exceeded the EU tolerable limit of 0.05 µg/L, and 26.3% surpassed the FDA limit of 0.5 µg/L. A year later, a study conducted by Abenet [
28] revealed that 93% (N=42) of milk samples from Dairy Farms in Addis Ababa and nearby districts had been contaminated by AFM
1, with 86% of the samples exceeding the EU tolerable limit. In another study conducted in the Guraghe zone of the SNNP region, 80% (N=10) of occurrence and 0.31 µg/L level of AFM
1 in milk samples was reported, where 68% of the samples exceeded the EU tolerable limit of 0.05 µg/L [
29].
Furthermore, among 64 milk samples collected from different urban and peri-urban areas of Oromia, Amhara, and SNNP regions all samples were contaminated by AFM
1, with 50% and 14% exceeding the EU and FDA limit respectively [
30]. Similarly, a 100% (N=108) prevalence and level of 0.69±0.505 µg/L of AFM
1, in which 96% and 82% of the samples exceeded the EU and FDA limits respectively, was reported in raw milk collected from Bishoftu town in Ethiopia [
31].
In Ethiopia, the urban population has been projected to be 23.20% by 2023, signifying rapid urbanization [
32], with a 4.8% rate of urbanization increase annually [
33]. Derived by rapid urbanization, then, the demand for milk and milk products has been increasing in the major Urban Centers [
33]. Thus, to address these demand-supply gaps for milk and milk products in urban areas, the roles played by urban and peri-urban dairy and specialized dairy production systems (SD) are remarkable [
33]. Thus, Shapiro et al., [
34] reported, a 125% increase in milk production by the SD from 2014/15 to 2019/20, where these specialized dairy and most urban and peri-urban dairy, primarily rely on concentrate supplementation [
35,
36,
37].
Likewise, in this study, the three selected Urban Centers of Eastern Ethiopia, the rapidly increasing urban dwellers, contributed to the demands for milk and milk products [
38,
39,
40]. Consequently, substantial indoor dairy operations, where wheat bran, maize feeds, total mixed rations, and brewer’s yeast byproducts were commonly supplemented to the dairy cows to increase milk yield [
41,
42]. However, the high susceptibility of these feeds to the Aspergillus species and associated aflatoxins [
27], and consequent led to contamination of milk, poses a critical challenge to the dairy industry as well as public health [
43]. Therefore, this study aimed to investigate the prevalence and level of AFM
1 in raw milk collected from indoor Dairy Farms and local Milk Vendors across the three selected Urban Centers in Eastern Ethiopia.
4. Discussion
Milk is widely regarded as a source of essential nutrients, that are consumed globally across different age groups, particularly, by infantry, children, pregnant women, and the elderly [
20,
56]. However, it could be a potential source of toxic compounds like aflatoxin M
1, which poses serious health risks, including liver cancer [
57]. This study assessed the prevalence and level of AFM
1 in milk collected from indoor Dairy Farms and local Milk Vendors in three Urban Centers and compared it with the different findings from several countries (
Table 5). Thus, to the best of our knowledge, a study has not been published yet, pertaining to the AFM
1 in raw milk of dairy cows from the current study areas. Therefore, in this study, aflatoxin M
1 was detected in 115/180 (63.9%) milk samples with an overall average concentration of 0.179±0.48 µg/L, which ranges from LOD (0.008 µg/L) to 3.85 µg/L. Thus, in the present study higher occurrence and level of AFM
1 in raw milk indicates that lactating cows have been exposed to concentrate feeds or feed ingredients that are prone to AFB
1 contamination [
58,
59], despite the determination of AFB
1 in feeds has not been the scope of this study.
Our study revealed a considerable variation in AFM
1 prevalence and concentration in milk from different regions in Ethiopia. Thus, compared to the present study, higher contamination of AFM
1 with 100% (N=110) prevalence and 4.98 µg/L average concentration in greater Addis Ababa milk sheds [
27], 100% (N=108) prevalence and 0.69±0.505 µg/L average concentration in Bishoftu town [
31], 100% (N=64) prevalence and 0.319±0.5 µg/L mean level in different Urban Centers of Oromia, Amhara and former SNNP region [
60], and 99% (N=100) prevalence and 0.47±0.73 µg/L mean level in South Gonder Zone [
61] were reported in raw milk from various locations in Ethiopia. Additionally, a higher occurrence, but relatively lower level of AFM
1 in raw milk from Addis Ababa and nearby towns (93%; average: 0.029 µg/L) and milk from different sites of Central Highland (71%; average: 0.054 µg/L) were reported in Ethiopia [
28,
62].
Furthermore, in some East African countries, higher occurrences of AFM
1 in raw milk of dairy cows, with a contamination rate of 95.45% (N=44; mean=2.07 µg/L) in Sudan [
63], prevalence of 100% (N=96; mean: 0.290.3 µg/L) in Kenya [
64] and occurrence of 83.8% (N=37) in Tanzania were reported [
25]. However, consistent with this finding, the prevalence rate of AFM
1 of 68.42% (N=38), 64.2% (N=38), and 58.8% (N=701) in Yemen, Pakistan, and Lebanon were reported respectively [
50,
65,
66]. Similarly, the average concentration of 0.183 µg/L (N=38), and 156.71 ng/L (N=84) of AFM
1 were reported in the raw milk of dairy cows of Algeria and Yemen respectively [
50,
67]. However, the variation in AFM
1 prevalence within different reports may be associated with different methods for toxin detection, geographical locations, agro-climatic variations, feed sources or feed ingredients, and feed storage conditions [
17,
48,
59].
In the present study, out of the contaminated milk samples (N=115), the levels of AFM
1 in 45 (39.13%) and 30 (26.08%) samples were higher than the threshold limits of ESA/EU and FDA respectively. Compared to the current study, a higher level of AFM
1 exceeding the tolerable limit of ESA/EU (97.8%), but comparable with FDA (26.5%) was reported in the greater Addis Ababa milk shed in Ethiopia [
27]. Likewise, 58% and 42% of milk samples from different sites of Central Highland and 96% and 82% of milk from Bishoftu town contain the concentration of AFM
1 exceeding the threshold limit of ESA/EU and FDA in Ethiopia [
31,
62]. However, Iqbal et al. [
65] and Daou et al. [
66] reported that 25% and 28% of the milk samples exceeded the tolerable limit of ESA/EU (0.05 µg/L) of AFM
1, which is relatively lower compared to the present finding.
Furthermore, data obtained in the present study indicates that Dire Dawa city, a relatively hotter Urban Center, was the origin of milk samples containing significantly higher prevalence (40.0%) as well as mean level (0.344±0.72 µg/L) of AFM
1 than in the milk samples from the Chiro town and Harar city. However, a 30.43% prevalence and 0.055±±0.13 µg/L mean level of AFM
1 in milk samples from Chiro town was not significant compared to a 29.57% prevalence and 0.140±0.33 µg/L average level in the milk samples collected from the Harar city. In agreement with the present finding, Njombwa et al., [
22] reported, a significantly higher level of AFM
1 in raw milk from the hotter Lakeshore Agro-ecological Zone, compared to the Mid and Highland Agro-ecological Zones in Malawi. This notion supports that, AFB
1 is more frequently produced in the areas with high environmental temperatures and humidity, where Aspergillus fungi thrive much better than in relatively less hot and dry environments. Thus, the level of AFB
1 produced is metabolized into AFM
1 by mammals and subsequently secreted into milk [
68].
Likewise, a finding in another study revealed, a considerable variation in AFM
1 contamination rate and mean level recovered from raw milk samples collected from different regions in Algeria [
67]. Thus, the highest contamination of 77.27% and mean of 152.46±44.14 ng/L in milk samples from the Center North region than in the milk samples from the Northeast region (prevalence: 30.43% and mean: 32.94±11.87 ng/L) and Northwest region (prevalence: 38.64% and mean: 57.05±21.67 ng/L). In support of our finding, the authors in this study have noted that the variations of AFM
1 level or contamination in raw milk between different regions in Algeria were linked to geographical and climatic differences.
Additionally, the prevalence of 57.39% and concentration level of 0.252±0.64 µg/L of AFM
1 in milk samples collected from the specialized Dairy Farms was found significant, compared to 42.61% prevalence and 0.107±0.21 µg/L mean in the milk samples collected from the local Milk Vendors. Similar to the current study, Zebib et al., [
60] reported, a higher mean concentration of AFM
1 in milk from producers/farmers (0.132 µg/L) than that of the milk from the farm gate markets (0.022 µg/L) in the former SNNP region in Ethiopia. In agreement with this finding, a study conducted in Nairobi Kenya revealed, a significantly higher level of AFM
1 in the milk samples from the Dairy Farms (627.5±238.19 µg/L) than in the samples collected from milk shops (28.8±0.0 µg/L) [
64]. Similarly, the study conducted by Kirino et al., [
69] concluded that AFM
1 levels in milk samples from the individual Dairy Farms were higher than in the milk samples collected from dairy shops, kiosks, vendors, and groceries.
Moreover, as shown in
Table 5, the level of AFM
1 recovered from the raw milk samples among large-scale herd size (0.720±0.975 µg/L) and large-scale milk producing Dairy Farms (0.763±0.974 µg/L) were found significant compared to the Dairy Farm with medium and low-scale herd size and milk production. Similarly, despite comparable occurrence of AFM
1 in milk obtained from small (46.8%, N=47) and large (45.94%, N=37) herd size, the mean level of AFM
1 in milk samples corresponding to the large herd size Dairy Farm (90.16±43.02 ng/L) was found significantly higher than the mean level of AFM
1 recovered from the milk samples corresponding to small herd size Dairy Farm (58.59±27.44 ng/L) in Algeria [
67]. This may be related that the large herd size Dairy Farms as well as large-scale milk producing Dairy Farms, the animals are mainly fed from different concentrate feeds [
33], which are more prone to Aspergillus fungus and subsequent aflatoxin contamination.
Table 5.
Level of AFM1 in raw milk of dairy cows across different countries.
Table 5.
Level of AFM1 in raw milk of dairy cows across different countries.
Countries |
Methods |
N |
+ (%) |
>EU (%) |
>FDA (%) |
Mean |
Ref. |
Ethiopia |
HPLC |
180 |
63.9 |
39.13 |
26.08 |
0.179±0.48 µg/L |
This study |
Sudan |
HPLC |
44 |
95.45 |
100 |
83.33 |
2.070 µg/L |
[63] |
Iran |
HPLC |
204 |
80.3 |
56.7 |
- |
0.660 µg/L |
[70] |
Egypt |
HPLC |
10 |
6 |
- |
- |
0.061 ng/L |
[71] |
Ethiopia |
HPLC |
42 |
93 |
86 |
- |
0.029 µg/L |
[28] |
Yemen |
HPLC |
38 |
68.42 |
36.84 |
- |
0.183 µg/L |
[50] |
Pakistan |
HPLC |
38 |
64.2 |
25 |
- |
0.082 µg/L |
[65] |
Algeria |
HPLC |
84 |
46.42 |
- |
1.19 |
156.71 ng/L |
[67] |
Lebanon |
HPLC |
701 |
58.8 |
28.0 |
- |
0.035±0.051 µg/L |
[66] |
Kenya |
HPLC |
96 |
100 |
66.4 |
7.5 |
290.3±66.3 ng/L |
[64] |
Ethiopia |
ELISA |
45 |
71 |
58 |
42 |
0.054 µg/L |
[62] |
Ethiopia |
ELISA |
110 |
100 |
97.8 |
26.3 |
4.980 µg/L |
[27] |
Ethiopia |
ELISA |
108 |
100 |
96 |
82 |
0.69±0.505 µg/L |
[31] |
Ethiopia |
ELISA |
100 |
99 |
41 |
- |
0.47±0.73 µg/L |
[61] |
Kenya |
ELISA |
72 |
37.5 |
26.4 |
- |
- |
[21] |
Malawi |
VICAM |
112 |
100 |
98 |
22 |
0.55±0.18 µg/L |
[22] |
Pakistan |
ELISA |
340 |
86.66 |
- |
34.45 |
0.520 µg/L |
[48] |
Kenya |
ELISA |
96 |
- |
- |
- |
627.5±238.19 ng/L |
[64] |
Kenya |
ELISA |
150 |
100 |
58 |
- |
- |
[20] |
Kenya |
ELISA |
84 |
98.8 |
64 |
- |
83.66±64.68 ng/L |
[19] |
Pakistan |
HPLC |
28 |
64.2 |
25 |
- |
82.4 ± 7.8 ng/L |
[65] |
Algeria |
ELISA |
84 |
46.42 |
- |
1.19 |
71.92±28.48 ng/L |
[67] |
Iran |
ELISA |
180 |
77.2 |
22.7 |
- |
56.32 ± 74.37 ng/L |
[56] |
Sudan |
VICAM |
25 |
92 |
- |
- |
- |
[23] |
Rwanda |
VICAM |
170 |
- |
91.8 |
38.8 |
0.89±1.64 µg/L |
[24] |
Tanzania |
HPLC |
- |
30.7 |
27.9 |
- |
- |
[26] |
Tanzania |
HPLC |
37 |
83.8 |
100 |
16.1 |
- |
[25] |