Table 15.
Control option | Arguments for low effectiveness | Arguments for high effectiveness | General comment | Largest range of quantitative estimates (%)a | Source of quantitative estimates | Median consensus (90% Probability interval) (%) |
---|---|---|---|---|---|---|
Vaccination |
Doubts about inconsistencies in field conditions after upscaling Despite many efforts, there is no vaccine (proven to be effective in practice) currently available |
Model results confirm large potential of vaccination The results are more consistent than for feed or water additives |
It is generally agreed that the wide distribution reflects existing uncertainty and differences in judgement between experts | 9–92 | Concentration model | 27 (4–74) |
Feed and water additives |
Doubts about inconsistencies under field conditions; very little evidence of reproducibility Publication bias: negative results are not published |
Some additives show a large effect When effective, the risk reduction achieved is large |
Unclear which specific additive is chosen Large variability between additives and studies |
0–80 | Concentration model | 24 (4–60) |
Discontinued thinning | Discontinued thinning will not reduce prevalence under poor biosecurity conditions |
Data suggest that flocks are rarely Campylobacter negative after thinning (Koolman et al., 2014) It is very difficult to maintain high biosecurity during thinning; undermines the motivation to, and effect of, carrying out good biosecurity |
Different experiences in different countries Differences between countries will be large Unclear how often thinning is currently applied in EU MSs; CAMCON project found that majority of flocks (> 80%) were thinned in large producer countries: ES, UK and PL |
2–25 | EFSA Opinion 2011; van Wagenberg et al. (2016) | 18 (5–65) |
Employing few and well‐trained staff | Training and/or certification alone does not mean that good biosecurity is consistently implemented |
Key for good overall biosecurity Good biosecurity and husbandry are reliant on people knowing what they are doing and why |
Main peak reflects PAF results | 2.7–38.8 | PAF analysis | 16 (5–45) |
Avoiding drinkers that allow standing water | Not clear why nipple drinkers are associated with lower prevalence of Campylobacter in the flock |
Standing water may facilitate cross‐infection between birds using the same drinker. Drinker cups are quickly contaminated with bedding materials and possibly feed providing a niche in which Campylobacter may survive and cross‐infect other birds Cups on drinkers may allow spillage onto the bedding resulting in a higher moisture content that supports Campylobacter survival |
Experts agreed on average (linear pool) of distributions based on individual judgements, without detailed discussion | 0–78.5 | PAF analysis | 15 (4–53) |
Addition of disinfectants to drinking water | The birds may dislike the odour or taste of the water resulting in lower effectiveness |
Prevents water acting as a source of Campylobacter Effective way of administering anti‐Campylobacter agents ensuring all birds are treated |
Experts agreed on average (linear pool) of distributions based on individual judgements, without detailed discussion | 0.6–54.9 | PAF analysis | 14 (3–36) |
Hygienic anterooms at broiler house entrance | Requires motivation on the part of the farmers |
A key part of any biosecurity system ensuring Campylobacter are not transmitted form a contaminated farmyard into the broiler house Easy to implement |
Experts agreed on average (linear pool) of distributions based on individual judgements, without detailed discussion | 0–31.9 | PAF analysis | 12 (3–50) |
Designated tools per broiler house |
Will not be effective as stand‐alone measure Sharing tools indicates poor overall biosecurity |
There is evidence that it is effective, although the effect is small | 1–16 | CAMCON project | 7 (1–18) |
As presented in the opinion.