Skip to main content

ORIGINAL RESEARCH article

Front. Vet. Sci., 30 June 2023
Sec. Veterinary Epidemiology and Economics

Quantifying antimicrobial use on Canadian dairy farms using garbage can audits

  • 1Department of Health Management, Atlantic Veterinary College, University of Prince Edward Island, Charlottetown, PE, Canada
  • 2Public Health Agency of Canada, Guelph, ON, Canada
  • 3Faculty of Veterinary Medicine, University of Calgary, Calgary, AB, Canada
  • 4Department of Population Medicine, Ontario Veterinary College, University of Guelph, Guelph, ON, Canada
  • 5Faculty of Veterinary Medicine, Université de Montréal, Montréal, QC, Canada

Antimicrobial resistance in pathogenic bacteria is one of the preeminent concerns for the future of global health. There is a dose-dependent relationship between antimicrobial use (AMU) and the prevalence of antimicrobial-resistant pathogens. As most AMU in Canada is related to animal agriculture, there is a need to reduce overall AMU, which could be accomplished through surveillance of AMU in animal agriculture, including the dairy industry. The objective of this study was to quantify AMU on dairy farms across Canada. This study had two parts: a description of data collected in 2019–2020, and a meta-analysis comparing this data to previous estimates of AMU in the Canadian dairy industry. The first included a garbage can audit (GCA) on 107 farms in four Canadian provinces (British Columbia, Alberta, Ontario, and Nova Scotia) in 2020; AMU data were converted to the dose-based metrics of defined course doses (DCD) and defined daily doses (DDD). Mixed-effect linear models were fit to determine the relationship between province and use of different classes of antimicrobials. On average, for every 100 animals on the farm, 117 DCD of antimicrobials were administered per year (IQR: 55, 158). These treatments amounted to 623 DDD / 100 animal-yr (IQR: 302, 677 DDD/100 animal-years). Penicillins were the most used class of antimicrobials, followed by first-and third-generation cephalosporins. Farms in Ontario used more third-generation cephalosporins than other provinces. The second part of this study compared AMU in 2020 to previously reported Canadian studies through a meta-analysis. A GCA was conducted in 2007–2008 in Alberta, Ontario, Québec, and the Maritime provinces (Prince Edward Island, New Brunswick and Nova Scotia); another GCA was conducted in Québec in 2018. Overall, AMU was lower in 2018–2020 than in 2007–2008, with the exception of third-generation cephalosporin use, which increased.

1. Introduction

Antimicrobial resistance (AMR) is one of the most significant threats to global health (1). The Government of Canada has identified antimicrobial use (AMU) in animals as a target to reduce the development of resistance in zoonotic, pathogenic bacteria (2). To promote this, the Canadian government has encouraged prudent AMU in livestock and increased antimicrobial oversight of pharmaceuticals for veterinary use (Government of Canada, 2019). Addressing AMR in the Canadian dairy industry requires expressing and comparing AMU within the industry and across countries and industries (3, 4) to develop benchmarks for assessing future interventions.

Farm-level AMU information can be retrieved using different data sources (5). For instance, it can be obtained using treatment records, the most straightforward source of AMU because they directly measure the amount used (6). However, it has been observed that dairy farmers do not keep complete records of all the treatments, and therefore they underestimate AMUs (710).

Another approach to estimating AMU is the garbage can audit (GCA). This method consists of placing a receptacle in convenient locations on a farm, and farmworkers are instructed to discard all drug containers into the receptacle for a defined period (10). Discarded containers are then counted to measure the disappearance rate of antimicrobials on the farm and to estimate AMU. A GCA tends to correlate well with AMU quantified through veterinary dispensing records, but may report somewhat lower usage (11). The main advantage of a GCA is that it is simple and requires little logistical development compared to other methods. They also circumvent issues derived from farms obtaining antimicrobials from multiple vendors.

A GCA can give the amount of products used, but converting these to dose-based metrics (DBM) is useful so that AMU can be compared regarding therapeutic potential. Conversion factors are established so that a specific mass confers a single course of treatment or day of effect. Conversion factors must be calculated for each active ingredient (AI) for a given route of administration [ESVAC (12)]. Lardé et al. (13) computed the defined daily dose (DDD) and defined course dose (DCD) conversion factors for every antimicrobial approved for use in cattle in Canada, specified as DDDbovCA and DCDbovCA (13).

To account for variation in farm size and duration of observation, an antimicrobial drug use rate (ADUR) is used to express the DBM in terms of the amount of animal time exposed (10). ADURs can be computed for any type of DBM denoted by a subscript, such as ADURDDD or ADURDCD.

The objective of this study was to assess AMU in Canadian dairy farms. Firstly the relationship between AMU, management practices and farm characteristics will be summarized. Then, a meta-analysis was used to compare AMU between 2007–2008 and 2017–2020, using the GCA methodology.

2. Materials and methods

2.1. Data sources

Three GCA studies were used for this study. Two have been previously reported in the literature (10, 11). Saini et al. (10) provided the baseline while Lardé et al. (11) and the current study, as outlined in Fonseca et al. (14), provided a follow up. Many of the farms were the same in the baseline and follow-ups. The inclusion and exclusion criteria were very similar in all three studies and all aimed to be representative of commercial dairy farms in each province assessed.

The first study was from 2007 to 2008, when a GCA was conducted on 89 dairy farms in Alberta, Ontario, Québec, and the Maritime provinces of Canada (10). The average herd size was 84 cows with an average per cow daily milk production was 32 kg. The median SCC was 220,000 cells/mL and 61% used tie-stalls. For further information, refer to Saini et al. (10). Raw count data from the 2007 to 2008 GCA were obtained and processed using the same methods for all GCAs.

The second study was conducted in 2017–2018 on 101 dairy farms in Québec as described by Lardé et al. (11). The mean herd had 67 cows with a per cow butterfat production of 1.2 kg/day. The garbage cans were left on the farm for over 1 year. Data for comparison to the 2019–2020 GCA were retrieved from the Supplementary material of Lardé et al. (11).

The third study was conducted in 2019–2020 on 106 dairy farms in British Columbia, Alberta, Ontario, and Nova Scotia (14). Farms were a convenience sample recruited through their local veterinarian, and receptacles were placed in convenient locations on the farm.

The average herd size was 135 cows with a daily milk and butterfat output of 35 kg/cow and 1.4 kg/cow. The median somatic cell count (SCC) was 175,000 cells/mL. 13% of farms used tie stalls for their lactating herd. Tie-stalls are more common on smaller herds and in Québec, so this proportion is close to what would be expected of commercial dairy farms in the studied regions (15). The Code of Practice has been encouraging the reduction of tie stalls in Canada, so a marked reduction in their popularity is to be expected (16). Farm personnel were asked to discard all medications into the receptacle, whether they had an antimicrobial activity or not. At the start of the observation period, a farm pharmacy inventory was conducted to determine what antimicrobials the farms already had in stock. At this time, a questionnaire was completed to gather herd demographic information. Three times over the next six to 12 months, the garbage can was emptied, and the contents were counted. A second pharmacy inventory was conducted at the last visit. For more details, refer to Fonseca et al. (14).

2.2. Data base metrics

All data processing involved in computing DBMs was done using Python 3.9 in the integrated development environment PyCharm 2021.2 (JetBrains s.r.o, Prague, Czechia). A program was written to convert the GCA data into a standardized format. A diagram of the flow of data is presented in Figure 1.

FIGURE 1
www.frontiersin.org

Figure 1. A flow diagram to demonstrate the flow of data from the garbage can audit to dose based metrics. Orange represents primary AMU data, green represents herd metadata, black represents external reference data, light blue represents data processing steps, and dark blue represents AMU metrics.

The equation used to convert the number of drug containers found into the DBM of a single active ingredient in a product is expressed as:

D B M A I P r o d u c t F o r m a t = N P r o d u c t F o r m a t . F o r m a t . C o n c . A I P r o d u c t C o n v e r s i o n F a c t o r D B M A I R O A

Where the DBM for an active ingredient (AI) in a product for a given product size (format) can be expressed in terms of either DCD or DDD. N P r o d u c t F o r m a t is the number of items of a given product in a particular size. The format is the size of the product. The concentration is specific to each active ingredient in the product and taken from Health Canada’s drug product database. The product of these three variables equals the mass of the active ingredient. The mass is then converted to a DBM, be it DCD or DDD, with a conversion factor that is specific for an active ingredient and route of administration (13).

These metrics allow for fair product comparisons, but, in order to compare farms, the metrics should be corrected by the number of animals and time between the initial and end visits (duration). This can be calculated for either DDDs or DCDs using the equation:

A D U R D B M = D B M A I P r o d u c t F o r m a t N a n i m a l s . D u r a t i o n

Where the ADUR for a farm is the sum of DDDs or DCDs for every AI used on the farm during the observation period, divided by the number of animals and the amount of time for which the animals were exposed. This equation gives results in the number of courses of treatment (DCD) or the number of days of effect of those courses (DDD) per 100 animal-years. 100 animals-years was chosen to indicate AMU in terms of a 100-animal herd for a year.

2.3. Statistical analyses

Dose-based metrics were also expressed for chemical class and each category of importance. The Health Canada drug product database was used to determine both the chemical class of the antimicrobial and its category of importance (17). The chemical class refers to the chemical family of antimicrobial, such as penicillin or tetracycline. Health Canada ascribed a category of importance, from 1 (very high importance) to 4 (low importance), to each class of antimicrobials to indicate their importance to human medicine. Only Categories 1, 2, and 3 are considered medically important.

Statistical analyses were done in STATA16 (StataCorp., College Station, Texas, United States). Averages and interquartile ranges (IQR) were computed from the ADURDDD and ADURDCD. AMU was stratified by route of administration, category of importance, and the chemical class of the active ingredient. All statistical models were assessed for homoscedasticity with the Breusch-Pagan/Cook-Weisberg method. Deletion residuals were used to assess models of third-generation cephalosporins, for normality and outliers. Standardized residuals and BLUPs were used to assess models of all chemical classes.

2.3.1. AMU and herd-level characteristics

For the 2019–2020 GCA, data were obtained from each farm regarding cow-level somatic cell count (SCC), milk production per 305-day lactation, and herd size through their dairy herd improvement program. The SCC and 305-day milk production were averaged for all cows lactating at the sampling time closest to January 1, 2020, which was the approximate middle of the observation period. The herd size included animals in all production phases.

Linear regression models were assessed to evaluate the relationship between each of these three variables and the total ADURDDD, as well as the ADURDDD of third-generation cephalosporins. Separate multivariable mixed-effect linear regression models for total ADURDDD were built with SCC, milk production, and herd size, including a term for the chemical class of antimicrobial, and clustered on the farm. The relationship between AMU and third-generation cephalosporins used a simple, univariable linear regression for each of the three herd metrics. The total and third-generation cephalosporin ADURDDD was log-transformed to fit model assumptions. These models do not infer causality, so each association was considered to be of interest individually.

2.3.2. Comparison of AMU in 2007–2008 to 2017–2020

Modeling with all three data sets investigated how the data from 2007–2008 differed from that of the more recent studies, completed in 2017–2018 and 2019–2020. All three studies had the same target population of Canadian commercial dairy farms to provide surveillance of antimicrobial use at each time point. This provided follow-ups for Alberta, Ontario, Québec, and the Maritime provinces. Many farms were included in the original study and the follow ups, but were kept anonymized because of data privacy concerns. The 2007–2008 study only recorded the number of dry and lactating animals on the farm, so all ADURDDDs used the population correction unit of 100 cow-years. Only parenteral use was assessed due to differences in how studies approached medicated feed. There are no medically important antimicrobials approved for feed in lactating dairy cows in Canada (11).

Two sets of models were built to assess the shifts in AMU between the study by Saini et al. (10) and the later studies. Each province was modeled separately to determine how pervasive observed associations were. When significance was evaluated, α was set at 0.05. All assessments were determined a priori. A mixed-effects linear model was built to predict the amount of each class of antimicrobial that was used on a farm, given that it was above zero. Predictors were the time point, the chemical class of the antimicrobial, and the interaction between the two. Models were clustered on the farm.

3. Results

The most recent study, conducted in 2019–2020, collected data from 106 farms across British Columbia, Alberta, Ontario, and Québec. The ADURDDD was 623 DDD/100 animal-yr (IQR: 302, 677), and the ADURDCD was 117 DCD/100 animal-yr (IQR: 55, 158). Table 1 displays the ADURDDD and ADURDCD for each category of importance. One farm used a partial bag of chlortetracycline premix, which accounted for more than 10% of all of the DDDs in the study. Exclusion of this farm resulted in the ADURDDD of 514 DDD/100 animal-yr (IQR: 302, 666), and the ADURDCD was 115 DCD/100 animal-yr (IQR: 55, 157), a reduction of 17 and 1.7%, respectively.

TABLE 1
www.frontiersin.org

Table 1. Mean and interquartile range ADURDDD and ADURDCD by category of importance to human medicine in DDD/100 animal-years and DCD/100 animal-years for the CaDNetASR project (2019–2020).

3.1. AMU by chemical class in 2019–2020

Fluoroquinolones and third-generation cephalosporins are the two classes of Category I antimicrobial active ingredients available for use in Canadian dairy cattle. Fluoroquinolones were rarely used on study farms (n = 11), with a maximum ADURDCD of 7 DCD per 100 animal-yr. Ceftiofur, a third-generation cephalosporin, was the most used Category I antimicrobial, and it was used on all but five (95%) farms in the 2019–2020 study. The ADURDCD was 22 DCD/100 animal-yr (IQR: 5, 28) and the ADURDDD was 105 (IQR: 19, 110).

The most used chemical class of antimicrobial was penicillins, which are Category II. Penicillins accounted for 163 DDD/100 animal-years and 31 DCD/100 animal-yr, which is 26% of total use for both metrics.

3.2. AMU by route of administration in 2019–2020

Every farm used at least one product labeled for systemic administration. Systemic administration accounted for 31% of total usage, ranging from 0.6% to 100%. One hundred and one farms (95%) used intramammary (IMM) antimicrobials. IMM use contributed 66% of total AMU, ranging from 0% to 99%. Only 33 farms used products designated for oral, topical, or intrauterine use, averaging 3% of usage, ranging from 0% to 94%.

By ADURDDD, first-generation cephalosporins were the most used IMM antimicrobials (111 DDD/100 animal-yr). Penicillins were used at a similar level (105 DDD/100 animal-yr), with third-generation cephalosporins (70 DDD/100 animal-yr) and lincosamides (4 DDD/100 animal-yr) being used less commonly. By ADURDCD, penicillins were the most used at 19 DCD/100 animal-yr (IQR: 0.2, 34). This was followed by third-generation cephalosporins (15 DCD/100 animal-yr), first-generation cephalosporins (14 DCD/100 animal-yr), and lincosamides (0.7 DCD/100 animal-yr).

With respect to third-generation cephalosporins, most of their usage was due to intramammary products. Out of the 105 days/100 animal-years (IQR: 16, 92) of third-generation cephalosporins by all ROAs, 70 (IQR: 0, 43) were given by the intramammary route. Similarly, out of the 22 courses/100 animal-year total, 15 (IQR: 0, 15) were from intramammary products.

The preferred IMM antimicrobial differed by province. Ontario farms used the most third-generation cephalosporin IMM products, whereas Alberta and Nova Scotia farms had higher ADURDCD for penicillins. With respect to British Columbia, no difference was found in IMM treatment between third-generation cephalosporins and penicillins.

3.3. AMU by region in 2019–2020

Overall, linear regression showed that AMU differed between regions (ADURDDD: p = 0.015; ADURDCD: p = 0.011) (Supplementary material). There was insufficient evidence that systemic use of antimicrobials differed significantly across regions (ADURDDD: p = 0.28; ADURDCD: p = 0.22). Intramammary use differed significantly by ADURDCD (p = 0.019), though ADURDDD did not reach significance (p = 0.15). Usage in each province, by ADURDDD and ADURDCD for both of these routes, as well as overall use, can be seen in Tables 2, 3, respectively.

TABLE 2
www.frontiersin.org

Table 2. The ADURDDD for each region is presented for all parenteral use, as well as for systemic use and intramammary use.

TABLE 3
www.frontiersin.org

Table 3. The ADURDCD for each region is presented for all parenteral use, as well as for systemic use and intramammary use.

3.4. Association between AMU and herd-averaged cow-level metrics in 2019–2020

Herd size was significantly (p < 0.001) and negatively correlated (r = −0.17) with the total ADURDDD. Average 305-day milk production (p = 0.678) and SCC (p = 0.969) did not demonstrate a significant relationship with total ADURDDD (Supplementary material). The ADURDDD of third-generation cephalosporins was significantly associated with SCC (p = 0.025) and 305-day milk production (p = 0.029), but not herd size (p = 0.177). SCC (r = −0.24) was negatively correlated with the ADURDDD of third-generation cephalosporins, while milk production (r = 0.23) was positively associated. Tables 4, 5 describe the results of these models for the overall ADURDDD and third-generation cephalosporins ADURDDD.

TABLE 4
www.frontiersin.org

Table 4. Herd-level factors associated with the natural logarithm of the ADURDDD for each class of antimicrobial after mixed-effects linear regression clustered on farm.

TABLE 5
www.frontiersin.org

Table 5. Herd-level factors associated with the natural logarithm of the ADURDDD for third-generation cephalosporins after linear regression.

3.5. Comparison of AMU between 2007–2008 and 2019–2020

There were changes in AMU between the study by Saini et al. (10) and those conducted by Lardé et al. (11) and Fonseca et al. (14). Total AMU decreased from 284 to 161 DCD/100 cow-years (p < 0.001) as assessed through univariable mixed effect linear regression. There was a shift from polymyxin use to third-generation cephalosporins among Category I antimicrobials, likely attributable to the introduction of IMM ceftiofur in 2008 and the withdrawal of polymyxin-containing products from the Canadian market in 2020. New regulations regarding Category I antimicrobials came into effect in Québec in 2019, which Millar et al. (18) showed caused a profound reduction in the use of these products. However, this occurred after this study’s second assessment of AMU in Québec. Tables 6, 7 show the ADURDCD and ADURDDD, respectively, for each chemical class of antimicrobial at both time points. Beyond the amount used, the number of farms using each chemical class changed. Table 8 demonstrates the number and percentage of farms at each time point using at least one product containing each chemical class of antimicrobial.

TABLE 6
www.frontiersin.org

Table 6. The interquartile range and average parenteral ADURDCD (DCD/100 adult cow-years) of farms by class and timepoint, as well as the number of herds that used the products containing the drug class.

TABLE 7
www.frontiersin.org

Table 7. The interquartile range and average parenteral ADURDDD (DDD/100 adult cow-years) of farms by class and timepoint, as well as the number of herds that used the products containing the drug class.

TABLE 8
www.frontiersin.org

Table 8. The percentage of farms in each province that used each chemical class of antimicrobial at each time point.

As seen in Table 9, though there was a drop in both systemic and intramammary use, the drop in intramammary use was far greater than in systemic use. Table 10 shows that the change in the use of intramammary antimicrobials. The drop in IMM administration is largest in penicillins, while the use of third-generation cephalosporin increased dramatically, due to the introduction of IMM ceftiofur products in 2008.

TABLE 9
www.frontiersin.org

Table 9. The mean parenteral ADURDCD (DCD/100 adult cow-years) and ADURDDD (DDD/100 adult cow-years) of systemic and intramammary use are presented for the two timepoint observed, as well as the number of herds that used any product through the given route of administration.

TABLE 10
www.frontiersin.org

Table 10. The mean parenteral ADURDCD (DCD/100 adult cow-years) and ADURDDD (DDD/100 adult cow-years) of intramammary antimicrobials for the four main chemical classes for the route of administration, as well as the number of farms that used each chemical class in an intramammary product.

A drop in ADURDCD and ADURDDD was observed in each region observed at both time points. Table 11 shows the ADURDCD and ADURDDD for each region at each time point. British Columbia was only evaluated in 2019–2020, but had lower use than any other region at that time. In multivariable mixed-effect linear regression, the timepoint remained significant (p < 0.001), though there was a significant interaction between the timepoint and chemical class on the ADURDDD, indicating changes in preferred classes. Table 12 displays the coefficients for this mixed-effects model in each province evaluated at both times.

TABLE 11
www.frontiersin.org

Table 11. The mean parenteral ADURDCD (DCD/100 adult cow-years) and ADURDDD (DDD/100 adult cow-years) for each region at each time point.

TABLE 12
www.frontiersin.org

Table 12. Mixed-effects linear model for natural logarithm of ADURDDD for each chemical class in provinces observed at each time point, with the interaction between the chemical class and time.

4. Discussion

Overall, antimicrobial use decreased substantially and pervasively from 2007 to 2008 (10, 11). In multivariable models, the time point the data were collected at was the most important explanatory variable for the reduction in ADURDDD. The only noteworthy increase was in third-generation cephalosporins, which is attributable to the introduction of IMM ceftiofur products to the industry (19). This drop in overall AMU is likely due to a combination of the transition to selective dry cow therapy from blanket protocols, changes in producer priorities, industry group standards, veterinary guidelines, government intervention, and consumer preferences.

There are several differences in the context of AMU in the Canadian dairy industry between the previous effort by Saini et al. (10) in 2007–2008 and more recent projects (10). The primary difference was legislative changes, the most prominent being federal regulations that went into effect in August of 2018, which indicated all antimicrobials for use in animals now require a veterinary prescription (20). This change presented a layer of friction and oversight in antimicrobial acquisition, as it became less convenient for farms to procure antimicrobials and necessitated veterinary approval. Further regulations came into effect in Québec in 2019, directed at reducing the use of Category I. Millar et al. (18) found that these regulations were extremely effective and may provide a further intervention to address ceftiofur usage (18).

Another change was the introduction of new drugs and the removal of others from 2007 until 2020. A polymyxin combination (Special Formula 17,900-Forte, Zoetis Canada, Kirkland, QC, Canada) was widely used as an IMM treatment or, extralabelly, for keratoconjunctivitis. This product had three medically important antimicrobial agents. However, this product went off the market in Canada in July 2021, after years of supply issues coinciding with the later GCAs of this study. As time goes on, change in the market necessitates new decisions and protocols at the farm and veterinary clinic levels. Therefore, producers may have made a switch to cephalosporin products after Special Formula became unavailable.

Other AMU quantification studies have been conducted in the dairy industries of different parts of the world. Using a GCA, AMU was comparable in Flanders (759 DDD per 100 cow-yr) than the 623 d per 100 animal-yr reported in this study (21). More recently, using treatment records in large Wisconsin dairy farms was reported to be 628 DDD per 100 animal-yr (6), similar to our study. Notably, these studies were performed in different populations and used different data collection methods, so comparisons are made with caution.

In Saini et al. (10), IMM penicillin use was driven by Special Formula Forte-17,900. This udder injector contained several active ingredients, including the antimicrobials penicillin G procaine, polymyxin B sulfate, and dihydrostreptomycin. Polymyxins and aminoglycosides were rarely, if ever, used outside of this product. This formulation led to a high correlation between polymyxin use and aminoglycoside use, as well as a moderate correlation between polymyxin and penicillin use. It is worth noting that many medications used to treat calf diarrhea contain many medically important antimicrobial AIs, primarily sulfonamides, but are infrequently used, so they present less of a challenge to AMU quantification.

Systemic (intramuscular, intravenous, or subcutaneous) use of antimicrobials occurred on every farm evaluated in 2019–2020. Intramammary administration was nearly as common, but not used by every farm (101/107 farms). IMM use accounted for two-thirds of total AMU. This highlights that bacterial mastitis is still the most important infectious condition in the Canadian dairy industry (22).

In the 2019–2020 data set, farms with higher milk yields had a higher use of third-generation cephalosporins. This may be due to aggressive treatment leading to faster resolution of clinical mastitis cases with less of a lasting effect on milk production (23). This explanation may also apply for the negative correlation between the ADURDDD of third-generation cephalosporins and SCC. Farms that are aggressively trying to reduce their SCC or maintain a low SCC may establish more aggressive protocols for treating and preventing mastitis during lactation and at dry-off.

The negative correlation between herd size and total ADURDDD is unclear. This relationship indicates that larger herds use lower volumes of antimicrobials per animal per year than smaller herds. This could simply be due to expired products being more common on smaller farms because the drug turnover is lower, causing an outsized impact when looking at discarded products. It could also be due to increased resources and specialization in larger herds. It appears unlikely that an AMU reduction strategy should include increasing herd size, but, rather, AMU quantification programs should choose population correction units carefully and provide benchmarking to similar farms on multiple dimensions.

One problem with GCAs for quantifying AMU is rounding partly used quantities of large format drugs. For example, one farm in this study used half of a bag of a chlortetracycline feed premix during the observation period. This half bag accounted for 15,278 DDD. The farm with the second-highest usage had 5,441 DDD for all drugs on the farm. Since the fraction of the bag remaining was estimated visually, the fraction can be off by what would amount to the total use of another high-AMU farm. To account for this, an option would be to exclude this drug from this farm’s metrics. However, this fails to account for the large amount of chlortetracycline used by this farm, and we believe this use should be accounted for. The high DDD from this farm and others like it is due to the outsized contribution of feed additives to the DDD count. This farm had an ADURDCD of 331 DCD/100 animal-yr, which is high relative to the average of farms in that collection effort of 117 DCD/100 animal-yr, but much lower than the maximum of 499 DCD/100 animal-yr.

Another potential measurement issue could be an insufficient length of observation to encapsulate usage patterns. A GCA measures AMU through discreet, discarded items. This study intended to leave the garbage cans for 6 months, which is shorter than what has been done in other projects using GCAs (10, 21). This length may not reflect year-round AMU, due to seasonality of infection pressure and incidence of conditions like mastitis. However, most were left far longer, some over a year, which is more in line with standard efforts. Once a GCA lasts longer than a year, it should provide a valid snapshot of use, with reduced impact of seasonality.

When quantifying AMU in any production system, an important question to consider is how long the observation period must be to determine the ADUR properly. Veterinary dispensing records have the advantages of providing sales dates and containing much longer periods of retrospective data much of the time. However, using veterinary dispensing records requires building the infrastructure to process the data and relationships with producers and veterinary clinics to provide the dispensing data. These data could determine the dispersion in ADUR as a function of time to determine the necessary sample period for a given effect size. The implicit assumption in most of this research is that these estimates are consistent over reasonable periods, and future research should evaluate this assumption by measuring AMU on farms over extended periods.

5. Conclusion

There was a significant and ubiquitous drop in AMU across the Canadian dairy industry since 2008. The notable exception being third-generation cephalosporins, which is mostly attributable to the introduction of intramammary ceftiofur products. Intramammary administration accounts for most AMU in the Canadian dairy industry. The finding that milk production and SCC are associated with AMU provides opportunities for the industry to improve production and antimicrobial stewardship together. The Canadian dairy industry is well-positioned to continue improving antimicrobial stewardship.

Data availability statement

The original contributions presented in the study are included in the article/Supplementary material, further inquiries can be directed to the corresponding author.

Ethics statement

Ethics review and approval/written informed consent was not required as per local legislation and institutional requirements.

Author contributions

LW developed the data processing system, analyzed the data, and wrote and edited the manuscript. LH, DL, DRi, and JS planned the data collection, set up logistics, helped with analysis, and edited the manuscript. DK, DRe, SD, HB, and J-PR designed the sampling, set up logistics, and edited the manuscript. All authors contributed to the article and approved the submitted version.

Funding

This research was funded by the Dairy Research Cluster 3 (Dairy Farmers of Canada and Agriculture and Agri-Food Canada) under the Canadian Agricultural Partnership AgriScience Program and the Public Health Agency of Canada.

Publisher’s note

All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors and the reviewers. Any product that may be evaluated in this article, or claim that may be made by its manufacturer, is not guaranteed or endorsed by the publisher.

Conflict of interest

The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.

Supplementary material

The Supplementary material for this article can be found online at: https://www.frontiersin.org/articles/10.3389/fvets.2023.1185628/full#supplementary-material

References

1. WHO–World Health Organization (2020). Antibiotic resistance. Available at: https://www.who.int/news-room/fact-sheets/detail/antibiotic-resistance#:~:text=Key%20facts,animals%20is%20accelerating%20the%20process (Accessed August 3, 2022).

Google Scholar

2. Government of Canada (2020). Antimicrobial resistance and animals – actions. Available at: https://www.canada.ca/en/public-health/services/antibiotic-antimicrobial-resistance/animals/actions.html (Accessed May 30, 2021).

Google Scholar

3. IACG – International Coordination Group on Antimicrobial Resistance (2018). Surveillance and monitoring for antimicrobial use and resistance. Available at: https://www.who.int/docs/default-source/antimicrobial-resistance/amr-gcp-tjs/iacg-surveillance-and-monitoring-for-amu-and-amr-110618.pdf?sfvrsn=8a07c166_4 (Accessed June 22, 2022).

Google Scholar

4. Sanders, P, Vanderhaeghen, W, Fertner, M, Fuchs, K, Obritzhauser, W, Agunos, A, et al. Monitoring of farm-level antimicrobial use to guide stewardship: overview of existing systems and analysis of key components and processes. Front Vet Sci. (2020) 7:540. doi: 10.3389/fvets.2020.00540

PubMed Abstract | CrossRef Full Text | Google Scholar

5. Pucken, V-B, Bodmer, M, Lovis, B, Pont, J, Savioli, G, Sousa, FM, et al. Antimicrobial consumption: comparison of three different data collection methods. Prev Vet Med. (2021) 186:105221. doi: 10.1016/j.prevetmed.2020.105221

PubMed Abstract | CrossRef Full Text | Google Scholar

6. de Campos, J, Kates, A, Steinberger, A, Sethi, A, Suen, G, Shutske, J, et al. Quantification of antimicrobial usage in adult cows and preweaned calves on 40 large Wisconsin dairy farms using dose-based and mass-based metrics. J Dairy Sci. (2021) 104:4727–45. doi: 10.3168/jds.2020-19315

PubMed Abstract | CrossRef Full Text | Google Scholar

7. Menéndez González, S, Steiner, A, Gassner, B, and Regula, G. Antimicrobial use in Swiss dairy farms: quantification and evaluation of data quality. Prev Vet Med. (2010) 95:50–63. doi: 10.1016/j.prevetmed.2010.03.004

PubMed Abstract | CrossRef Full Text | Google Scholar

8. Nobrega, DB, De Buck, J, Naqvi, SA, Gang, L, Naushad, S, Saini, V, et al. Comparison of treatment records and inventory of empty drug containers to quantify antimicrobial usage in dairy herds. J Dairy Sci. (2017) 100:9736–45. doi: 10.3168/jds.2017-13116

PubMed Abstract | CrossRef Full Text | Google Scholar

9. Redding, LE, Bender, J, and Baker, L. Quantification of antibiotic use on dairy farms in Pennsylvania. J Dairy Sci. (2019) 102:1494–507. doi: 10.3168/jds.2018-15224

PubMed Abstract | CrossRef Full Text | Google Scholar

10. Saini, V, McClure, JT, Léger, D, Dufour, S, Sheldon, AG, Scholl, DT, et al. Antimicrobial use on Canadian dairy farms. J Dairy Sci. (2012) 95:1209–21. doi: 10.3168/jds.2011-4527

CrossRef Full Text | Google Scholar

11. Lardé, H, Francoz, D, Roy, J-P, Massé, J, Archambault, M, Paradis, M-È, et al. Comparison of quantification methods to estimate farm-level usage of antimicrobials other than in medicated feed in dairy farms from Québec, Canada. Microorgansisms. (2021) 9:1106. doi: 10.3390/microorganisms9051106

PubMed Abstract | CrossRef Full Text | Google Scholar

12. ESVAC – European Medicines Agency European Surveillance of Veterinary Antimicrobial Consumption (2015). Principles on assignment of defined daily dose for animals (DDDvet) and defined course dose for animals (DCDvet). Available at: https://www.ema.europa.eu/en/documents/scientific-guideline/principles-assignment-defined-daily-dose-animals-dddvet-defined-course-dose-animals-dcdvet_en.pdf (Accessed May 30, 2021).

Google Scholar

13. Lardé, H, Dufour, S, Archamault, M, Leger, D, Loest, D, Roy, J-P, et al. Assignment of Canadian defined daily doses and Canadian defined course doses for quantification of antimicrobial usage in cattle. Front Vet Sci. (2020) 7:10. doi: 10.3389/fvets.2020.00010

PubMed Abstract | CrossRef Full Text | Google Scholar

14. Fonseca, M, Heider, LC, Léger, D, McClure, JT, Rizzo, D, Dufour, S, et al. Canadian dairy network for antimicrobial stewardship and resistance (CaDNetASR): an on-farm surveillance system. Front Vet Sci. (2022) 8:799622. doi: 10.3389/fvets.2021.799622

PubMed Abstract | CrossRef Full Text | Google Scholar

16. NFACC – National Farm Animal Care Council (2023). Code of practice for the care and handling of dairy cattle. Available at: https://www.nfacc.ca/codes-of-practice/dairy-cattle/code2023#section2 (Accessed May 17, 2023).

Google Scholar

17. Health Canada (2009). Categorization of antimicrobial drugs based on importance in human medicine. Available at: https://www.canada.ca/en/health-canada/services/drugs-health-products/veterinary-drugs/antimicrobial-resistance/categorization-antimicrobial-drugs-based-importance-human-medicine.html (Accessed May 30, 2021).

Google Scholar

18. Millar, N, Aenishaenslin, C, Lardé, H, Roy, J-P, Fourichon, C, Francoz, D, et al. Evidence of a decrease in sales of antimicrobials of very high importance for humans in dairy herds after a new regulation restricting their use in Quebec. Canada Zoonoses Public Health. (2021) 69:370–81. doi: 10.1111/zph.12929

PubMed Abstract | CrossRef Full Text | Google Scholar

19. Health Canada – Government of Canada (2022). Product information – Spectramast LC. Available at: https://health-products.canada.ca/dpd-bdpp/dispatch-repartition.do;jsessionid=476D2DE49EA59BCE6936C4D95295845D (Accessed September 30, 2022).

Google Scholar

20. Health Canada (2021). Responsible use of medically important antimicrobials in animals. Available at: https://www.canada.ca/en/public-health/services/antibiotic-antimicrobial-resistance/animals/actions/responsible-use-antimicrobials.html (Accessed March 7, 2023).

Google Scholar

21. Stevens, M, Piepers, S, Supre, K, Dewulf, J, and De Vliegher, S. Quantification of antimicrobial consumption in adult cattle on dairy herds in Flanders, Belgium, and associations with udder health, milk quality, and production performance. J Dairy Sci. (2016) 99:2118–30. doi: 10.3168/jds.2015-10199

PubMed Abstract | CrossRef Full Text | Google Scholar

22. Jamali, H, Barkema, HW, Jacques, M, Lavallée-Bourget, E-M, Malouin, F, Saini, V, et al. Invited review: incidence, risk factors, and effects of clinical mastitis recurrence in dairy cows. J Dairy Sci. (2018) 101:4729–46. doi: 10.3168/jds.2017-13730

PubMed Abstract | CrossRef Full Text | Google Scholar

23. Adriaens, I, Van Den Brulle, I, Geerinckx, K, D’Anvers, L, De Vliegher, S, and Aernouts, B. Milk losses linked to mastitis treatments at dairy farms with automatic milking systems. Prev Vet Med. (2021) 194:105420. doi: 10.1016/j.prevetmed.2021.105420

CrossRef Full Text | Google Scholar

Keywords: antimicrobial use (AMU), dairy, garbage can audit, antimicrobial stewardship (AMS), meta-analysis, temporal change, Canada

Citation: Warder LMC, Heider LC, Léger DF, Rizzo D, McClure JT, de Jong E, McCubbin KD, Uyama T, Fonseca M, Jaramillo AS, Kelton DF, Renaud D, Barkema HW, Dufour S, Roy J-P and Sánchez J (2023) Quantifying antimicrobial use on Canadian dairy farms using garbage can audits. Front. Vet. Sci. 10:1185628. doi: 10.3389/fvets.2023.1185628

Received: 13 March 2023; Accepted: 16 June 2023;
Published: 30 June 2023.

Edited by:

Om P. Dhungyel, The University of Sydney, Australia

Reviewed by:

Andrew P. Woodward, University of Canberra, Australia
John I. Alawneh, Murdoch University, Australia

Copyright © 2023 Warder, Heider, Léger, Rizzo, McClure, de Jong, McCubbin, Uyama, Fonseca, Jaramillo, Kelton, Renaud, Barkema, Dufour, Roy and Sánchez. This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY). The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner(s) are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.

*Correspondence: Landon M. C. Warder, lmwarder@upei.ca

Disclaimer: All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors and the reviewers. Any product that may be evaluated in this article or claim that may be made by its manufacturer is not guaranteed or endorsed by the publisher.