INTRODUCTION
Johne's disease, or paratuberculosis, is a chronic granulomatous enteritis predominantly found in ruminants, which is caused by Mycobacterium avium subspecies paratuberculosis (MAP). MAP infection is believed to happen in the first year of life, although initial clinical symptoms can only be observed months or even years after infection. Animals suffer from therapy-resistant profuse diarrhoea, meaning that cachexia and the development of oedema due to hypoproteinaemia are typical symptoms in the late stage of the disease [Reference Tiwari1]. Economic losses are caused by reduced slaughter weight [Reference Whitlock2], increased susceptibility to other diseases [Reference Raizman3], premature culling [Reference Smith4] and, with regard to the dairy industry, reduced lactation performance even in cows with no clinical symptoms [Reference Gonda5–Reference Smith8]. Furthermore, many authors discuss the zoonotic potential of MAP in the pathogenesis of Crohn's disease, a form of granulomatous enteritis in humans [Reference Feller9, Reference Uzoigwe10].
With respect to the economic impact of Johne's disease and the presumed zoonotic potential of MAP, effective measures to control the disease should be implemented in MAP-positive herds in order to limit prevalence and thus shedding of the agent into the environment as well as to prevent it from being carried over into the food chain. The first step towards implementing control measures within a herd is the identification of a herd as being MAP positive.
Sampling individual animals in order to identify infected herds has its limitations. While faecal culture applied on individual faecal samples is still considered the most sensitive method, it is labour-intensive, time-consuming and costly [Reference Collins11]. Applying polymerase chain reaction (PCR) on faecal samples allows the detection of MAP in a relatively short time, but it is also expensive. Sensitivity and specificity vary according to the method applied [Reference Sweeney12]. Both depend on the DNA extraction procedures, which must ensure an effective removal of PCR inhibitors like phytic acid, polysaccharides, phenols or bile salts [Reference Pozzato13]. ELISA testing for MAP antibodies on selected animals is hampered by limited diagnostic sensitivity and specificity compared to detecting organisms, and also by the resulting difficulties when interpreting results with low numbers of reactors [Reference Donat14, Reference Lavers15].
Environmental sampling protocols have been developed and evaluated over several years [Reference Raizman16–Reference Sweeney22]. The herd-level sensitivity of environmental sampling depends on the number of samples and within-herd prevalence (WHP), and varies widely from ~30% to ~90% [Reference Lombard23]. It was estimated to be ~70% when sampling one set of six environmental samples in low-prevalence herds [Reference Lavers24]. A recent study calculated thresholds of MAP shedders' apparent within-herd prevalence (WHPapp) that allow the detection of a MAP-positive herd at different probabilities (P d) (~3% at 50% P d), which demonstrates that environmental sampling is capable of identifying herds with a low prevalence but has limitations in herds with very low WHPapp [Reference Donat25].
As one option, sampling socks as known from Salmonella testing (boot swabs) have been suggested as an easily accessible matrix for MAP detection in dairy herds [Reference Eisenberg26, Reference Wolf27], and have been studied in a longitudinal approach. It was possible to detect high-prevalence herds with a high degree of accuracy by repeatedly taking one sample per herd [Reference Eisenberg26]. Performance in herds with low prevalence has yet to be clarified. As such, data regarding the sensitivity of this approach is necessary in order to assess its applicability in the field.
Various authors emphasize bacterial culture of environmental samples as a suitable tool for MAP detection in dairy herds with moderate to high WHP [Reference Raizman16–Reference Donat20]. This approach utilizes the lengthy survival of MAP under environmental conditions [Reference Lovel28, Reference Jørgensen29]. Recently, quantitative real-time PCR protocols for the detection of MAP combined with high-efficiency DNA extraction were evaluated, identifying more individual faecal samples [Reference Logar30] and more environmental samples [Reference Dressel31] as MAP positive than with faecal culture on Herrold's egg yolk medium. Although these results also suggest an acceptable test performance of a PCR using boot swabs, this matrix has not yet been evaluated.
First, we hypothesize that sampling boot swabs and liquid manure is sufficient to detect MAP-positive herds when faecal culture as well as PCR are applied; and second, that the environmental sampling approach is suitable to identify MAP-positive dairy herds at an acceptable probability level even if the WHPapp is low and only one or two environmental samples are collected. Therefore, our study aimed to estimate WHPapp thresholds of this approach at different probability levels, applying both PCR and faecal culture simultaneously or separately.
MATERIALS AND METHODS
Study population
A total of 77 dairy herds in Thuringia, Hesse and Saxony, all federal states of Germany, with an average herd size of 356 cows per herd (27–1170) were selected for this study. All herds were housed in free stalls. The herds in Thuringia and Saxony had been enrolled in voluntary control programmes of bovine Johne's disease for several years; these are organized by Thuringia and Saxony's respective animal health services [32, 33]. Among other measures, the programmes include annual screenings of all lactating and dry cows, including breeding bulls, for MAP by faecal culture. Depending on herd size and herd management aspects, these animals are all sampled for testing either on one day per year or in a continuous manner in connection with other management measures (e.g. puerperal controls, pregnancy tests, drying off). Herds which never had a faecal culture-positive test result in the annual herd screenings over three consecutive years are certified as ‘herds not suspected of having paratuberculosis'. The rigour of this certification corresponds to level 6 of the Uniform Program Standards for the Voluntary Bovine Johne's Disease Control Program of the United States Department for Agriculture [34]. In the present study, herds were selected whose owners had agreed to take part in this project (n = 67). In Hesse, all herds included in the present study were found to contain at least one MAP shedder during a previous regional MAP survey conducted in 2007, which was based on individual serological testing with subsequent faecal culture. Several subsequent studies examined these herds during the following years [Reference Eisenberg26], but effective control measures were never implemented and the herds remained MAP positive. The Hessian herds were subjected to ad hoc WHPapp determination at the time of environmental sampling (n = 10).
Individual faecal sampling and determination of herd prevalence
Individual faecal samples were taken directly from the rectum and immediately transported to the laboratory for further processing. WHPapp of MAP shedders was calculated as the proportion of faecal culture-positive cows in the total cows sampled from the herd. In Hesse, individual as well as environmental samplings were conducted at the same time since no previous data on individual faecal culture existed. By contrast, in Thuringia and Saxony the latest individual cows' faecal culture results obtained during the preceding year were used in order to estimate WHPapp. A list of individuals that were kept in the herd on the day of environmental sampling was taken from the German database of animal origin (HI-Tier) and adjusted to the data in the laboratory database, extracting the test results for all cows after first calving and bulls aged >24 months.
Boot swabs and liquid manure sampling
Boot swab samples were collected as described by Eisenberg et al. [Reference Eisenberg26] during September and December 2012. Two samplers walked around, mainly in areas with high cow traffic, collecting four boot swab samples in parallel. Sampling involved manure concentration areas where most of the cows commingled and which had proven suitable for environmental sampling in previous studies [Reference Raizman16, Reference Pillars19, Reference Donat20]: main cow alleyways, travel routes, crossovers, waiting pen, lactating cow pens. To achieve rough standardization, walking was limited to at least 100 and not more than 200 steps. Basically, walking involved the normal route of a lactating cow to the milking parlour, starting in the lactating cows' pen and ending in the waiting pen. After sampling, the boot swabs were removed; three boot swabs coated well in manure were placed in the inner of two nested aseptic plastic bags, of which the outermost was labelled to ensure correct identification.
Additionally, samples from liquid manure storage areas (tanks, lagoons, pits or pre-flooders) were obtained at the same time by submerging a sampling container up to 10 cm beneath the surface of the manure. At least 50 ml manure was decanted into a sterile 125 ml plastic cup with screw cap. All the samples were transported in a cooler to the laboratory within 3 h. All samples were stored at −20 °C. For further processing, boot swabs were cut into small pieces and handled as described by Eisenberg et al. [Reference Eisenberg26].
Bacterial culture
The faecal culture of individual liquid manure as well as prepared boot swab samples was done on Herrold's egg yolk medium according to the official manual of diagnostic procedures published by the Friedrich-Loeffler-Institut, the German Federal Research Institute of Animal Health [35]. Differentiation of characteristic colonies was performed by Ziehl–Neelsen staining and PCR [Reference Englund36]. Samples were characterized as faecal culture-positive or faecal culture-negative. The amount of colony-forming units (c.f.u.) on the surface of the culture medium was scored semi-quantitatively, with 1–10 c.f.u. as ‘+’, 11–50 c.f.u. as ‘++’ and 51–100 c.f.u. as ‘+++’. If there were >100 c.f.u. on the surface, growth was characterized as ‘++++’.
DNA isolation from faeces, DNA amplification and PCR
Since different methods for DNA preparation and PCR were used by each laboratory, the respective methodologies are presented separately with the following abbreviations: Hessian State Laboratory (laboratory A): PCR A; Thuringian Animal Health Service (laboratory B): PCR B; Friedrich-Loeffler-Institut (laboratory C): PCR C.
PCR A
The liquid manure and prepared boot swab samples were processed according to the established bacterial culture protocol as an enrichment step. After 4 weeks of incubation at 37 °C, culture surface runoffs were harvested from each of the tubes and investigated by F57/IC real-time PCR. Duplex F57/IC real-time PCR was developed as a modification of a method published previously [Reference Schönenbrücher37, Reference Fawzy38]. The modified 20 μl PCR mixture for the duplex real-time PCR assay contained 1 μl of the primers F57-F (5′-TAC GAG CAC GCA GGC ATTC-3′) and F57-R (5′-CGG TCC AGT TCG CTG TCAT-3′) (10 pmol/μl), 0·63 μl F57 TaqMan probe (5′-CY5-CCT GAC CCT TC-BHQ1-3′) (10 pmol/μl), 125 copies of internal amplification control (IAC) DNA, 0·5 μl EGFP 4(5) mix [Reference Hoffmann39], 10·0 μl 2 × Quantitect Multiplex Master Mix No Rox (Qiagen, Germany), and a 5 μl aliquot of the DNA sample. EGFP 4(5) mix contains 2·5 pmol/μl of each primer EGFP-11-F (5′-CAG CCA CAA CGT CTA TAT CAT G-3′), EGFP-10-R (5′-CTT GTA CAG CTC GTC CAT GC-3′) and 1·25 pmol/μl EGFP-1HEX probe (5′-HEX-AGC ACC CAG TCC GCC CTG AGC A-BHQ1-3′).
The PCR tubes were then placed in a thermocycler (Mx3005 P, Stratagene, Germany) with a pre-heated lid and subjected to initial denaturation at 95 °C for 15 min followed by 50 cycles of denaturation at 94 °C for 1 min each and annealing and extension at 60 °C for 90 s each. Analysis of fluorescence was performed using Mx3000 P software (Stratagene). Amplification curves were carefully analysed after checking raw fluorescence values, baseline settings and the threshold as recommended by the manufacturer. Positive signals were recorded as cycle threshold (Ct) values.
PCR B
The general protocol utilized represented a commercially available integrated work flow including DNA isolation from faeces, DNA amplification and qPCR that was licensed in Germany for the detection of MAP from individual faecal samples and environmental faecal samples (Life Technologies GmbH, Germany). The DNA was extracted from faeces using the MagMax™ Total Nucleic Acid Isolation kit, using the MagMax™ Express 96 instrument (Life Technologies GmbH) according to the manufacturer's instructions; it uses magnetic beads to separate the DNA from the faeces. To detect MAP DNA, the VetMAX™ MAP Real-Time PCR Screening kit, performed on a 7500 fast real-time PCR cycler (Life Technologies GmbH), was applied according to the manufacturer's instructions. A sample was identified as positive if Ct values were ⩽37·0, and negative if Ct values were >37·0.
PCR C
A commercially available qPCR protocol was used. The DNA was extracted from faeces using a commercial nucleic acid isolation kit (QIAamp DNA Mini kit, Qiagen) after pre-concentration of samples using Adiafilter (Adifil 100, Adiagene, France) according to the manufacturer's instructions. The filter system performed the centrifiltration of 10 ml faecal supernatant to concentrate bacteria, enabling an increase in the sensitivity of the global PCR method. In order to detect MAP DNA, a commercial IS900-based real-time PCR method (Adiavet Paratb, Adiagene) was used according to the manufacturer's instructions. A sample was identified as positive if Ct values were <38·0, and inconclusive for Ct values between 38·0 and 40·0.
Statistical data analysis
Data recording and editing as well as descriptive statistics and WHPapp computation were performed using a Microsoft Excel spreadsheet (Microsoft Corporation, USA). The statistical software package BMDP/Dynamic (Release 8.1; W. J. Dixon, Statistical Solutions Ltd, Ireland) was used for all other statistical analyses [Reference Dixon40]. A statistical significance level of α = 0·05 was used in general.
In the first step of the data analysis, Spearman's rank correlation coefficient (r s ) was calculated for each matrix in order to analyse the relationship between WHPapp on the one hand and the semi-quantitative colony growth score or the Ct values (qPCR) of boot swabs and liquid manure samples on the other.
Concerning WHPapp of a certain herd as an influencing factor of interest (n = 77), its relation to the dichotomized MAP findings (negative or positive; MAP status) in the samples (boot swabs or liquid manure or combination of both), each determined by faecal culture and PCR in each of three laboratories was assessed using a logistic regression model analysed using the asymptotic logistic regression procedure BMDPLR [Reference Dixon40]. The applicability of the underlying logistic model was tested with the goodness-of-fit χ 2 test and the Hosmer–Lemeshow goodness-of-fit test to verify that the model fitted the data adequately. Additionally, the linear associations between the logit of the outcomes and WHPapp as the numeric predictor were examined by scattergrams. This assumption in particular is important for the reversibility of the logistic equation to estimate WHPapp thresholds to given probabilities (see below).
The findings of the boot swab and liquid manure samples were presented for three outcomes: PCR, faecal culture and both tests applied simultaneously.
The findings of the boot swab and liquid manure samples were combined to a single binary outcome (MAP status), being positive if at least one of these matrices showed a positive result, and negative if both matrices tested negatively.
Inversion of the logistic function yields an estimate of WHPapp related to a given P d of a herd as MAP positive. For practical reasons, a high P d (e.g. = 0·9) is desirable in control programmes or for prevalence estimation. At P d = 0·9 the slope of the logistic function is still rising steeply enough, thus limiting the uncertainty of WHPapp estimation. Additionally, the point of maximal slope (P d = 0·5) was selected in the analysis, because this is the point of inflection of the sigmoid logistic function. This minimizes the inaccuracy of the WHPapp estimation when dropping the perpendicular at the WHPapp axis.
By means of maximum-likelihood techniques [Reference Dixon40], WHPapp thresholds as well as asymptotic standard errors for these detection thresholds were estimated from the data using the program BMDPLE [Reference Dixon40]. Approximate 95% confidence intervals (CIs) for the thresholds of interest were computed using the asymptotic standard errors.
The formula of the logistic model used is
$$\eqalign{{P_{\rm d}} & = {\rm probability}\left( {{\rm herd} = +} \right) \cr & = {\rm exp}\left( {a + b\cdot {\rm WH}{{\rm P}_{{\rm app}}}} \right)/\left( {1 + {\rm exp}\left( {a + b\cdot {\rm WH}{{\rm P}_{{\rm app}}}} \right)} \right)},$$
leading to the WHPapp threshold formula:
$${\rm WH}{{\rm P}_{{\rm app}}}\left( {{P_{\rm d}}} \right){\rm} = {\rm} \left( {{\rm ln}\left( {{P_{\rm d}}/\left( {1-{P_{\rm d}}} \right)} \right)-a} \right)/b,$$
where P d = desired probability of detection (absolute number, not in per cent); WHPapp(P) = apparent within-herd prevalence with detection probability P; a = constant parameter in the logistic function; b = model coefficient relating to WHPapp in the logistic regression; ln = natural logarithm.
RESULTS
WHPapp
A total of 22 057 faecal culture test results (883 MAP positive and 21 174 MAP negative) were used to calculate WHPapp. The average sample size was 272 (minimum 11, maximum 916) cows per herd. On average, 86·8% of the cows kept in the herd at the time of environmental sampling had valid individual faecal culture test results allowing estimation of WHPapp (Table 1). Cows that were introduced into the herd between the date of environmental sampling and individual sampling diminished the percentage of cows with valid test results, as shown in Table 1. Samples from one herd with 27 cows showed an unexpectedly high percentage of bacterial and fungal contamination which resulted in 17 non-analysable samples. Since one sample was MAP positive and the calculated WHPapp of 9·1% was found to be in the expected range, the herd was not excluded from the study.
Table 1. Herd size, sample size and estimated apparent within-herd prevalence (WHPapp) of 77 herds
MAP, Mycobacterium avium ssp. paratuberculosis.
* Number of cows kept in the herd on the day of environmental sampling and which tested positively or negatively for MAP.
† Relation of sample size to herd size on the day of environmental sampling.
‡ Apparent within-herd prevalence on the day of environmental sampling.
Environmental samples
Apart from one boot swab (laboratory C), all 77 boot swab and 75 liquid manure samples were analysable with faecal culture in each laboratory. Positive and negative results of the PCR tests and the corresponding faecal culture results are given in Table 2. Out of 77 boot swabs, three or four were not analysable in PCR B or PCR C, while none were not analysable in PCR A. Because of solid dung systems, two herds did not supply liquid manure samples, which is why 75 samples were tested. Of these, seven samples in PCR B and five in PCR C were not analysable because of inconclusive Ct values.
Table 2. Number of boot swabs and liquid manure samples which tested negatively or positively by FC in three different laboratories and using three different PCR methods (A, B, C) for MAP
FC, Faecal culture; PCR, quantitative real-time polymerase chain reaction; MAP, Mycobacterium avium ssp. paratuberculosis; Pos., MAP-positive; Neg., MAP-negative.
Association between WHPapp and faecal culture or qPCR results
Spearman's rank correlation coefficients for the relationship between WHPapp and colony growth score in faecal culture or the Ct values of each qPCR are given in Table 3. All test methods showed a significant correlation with WHPapp (P < 0·0001), with the best association between WHPapp and the Ct values seen in PCR B.
Table 3. Spearman's rank correlation coefficient for the correlation between within-herd prevalence and colony growth score of the faecal culture in three laboratories (A, B and C) or Ct values of three PCR methods (A, B and C) for boot swabs and liquid manure samples from 77 dairy herds
PCR, Polymerase chain reaction; MAP, Mycobacterium avium ssp. paratuberculosis; FC, faecal culture; Ct, cycle threshold; r s , Spearman's rank correlation coefficient.
* Colony score of samples' faecal culture test (c.f.u.): +, 1–10; ++, 11–50; +++, 51–100; ++++, >100.
† Ct value of environmental samples' PCR.
Association between WHPapp and herds' MAP status as determined by faecal culture or PCR
Shown by logistic regression, the MAP status as determined by each faecal culture or each PCR was significantly associated with WHPapp (Table 4). An adequate model fit was verified by the goodness-of-fit χ 2 test as well as the Hosmer–Lemeshow goodness-of-fit test and by the inspection of an approximate linear association between the logit of the outcome and the WHPapp. The regression coefficients resulting from the logistic regression model were all statistically significantly positive, indicating increasing MAP detection probabilities with increasing WHPapp. The corresponding odds ratios (OR) ranged between 1·31 and 1·83 (2·23 in one case), showing a corresponding mean rise of the odds of detection of MAP when WHP increases by 1%. Applying both the faecal culture and the PCR methods simultaneously in the same laboratory resulted in slightly increased median OR in the range of 1·63 and 1·89.
Table 4. Results of the different logistic regressions to analyse the associations between MAP status of herds (n = 77) determined by different methods (FC or PCR or the combination of both) applied to boot swabs and liquid manure samples in three different laboratories (outcomes of interest) and the WHPapp as the predictor
MAP, Mycobacterium avium ssp. paratuberculosis; FC, faecal culture; PCR, polymerase chain reaction; WHPapp, apparent within-herd prevalence; s.e., standard error; OR, odds ratio.
* P value for odds ratio.
Estimates of the WHPapp relating to a given P d
For boot swabs, the lowest thresholds were estimated when faecal culture C was applied (P d 50%: 2·54 ± 0·49%; P d 90%: 5·29 ± 1·05%) (Tables 5 and 6). If liquid manure samples were used alone, analysing faecal culture A as well as all PCR test outcomes resulted in comparable estimates for P d 50% and slightly higher estimates for P d 90%. The outcomes for faecal culture C were considerably higher, which is caused by a markedly lower number of positive test results, obviously because cultivation was performed 9 months later than in laboratories A and B and storage at −20 °C did not completely prevent degradation of viable bacteria. The distinctly higher estimates for PCR A indicate a lower sensitivity of this method compared to PCR B and PCR C.
Table 5. Estimates of WHPapp threshold value ± asymptotic s.e. and 95% CIapp for the detection of a MAP-positive herd using a boot swab or a liquid manure sample or the combination of both applying FC (three different laboratories A, B, C), PCR (three different methods A, B, C) or the combination of each PCR with FC in the same laboratory at 50% probability of detection
WHPapp, Apparent within-herd prevalence; s.e., standard error; CIapp, approximate confidence interval; MAP, Mycobacterium avium ssp. paratuberculosis; FC, faecal culture; PCR, polymerase chain reaction.
Table 6. Estimates of WHPapp threshold value ± asymptotic s.e. and 95% CIapp for the detection of a MAP-positive herd using a boot swab or a liquid manure sample or the combination of both applying FC (three different laboratories A, B, C), PCR (three different methods A, B, C) or the combination of each PCR with FC in the same laboratory at 90% probability of detection
WHPapp, Apparent within-herd prevalence; s.e., standard error; CIapp, approximate confidence interval; MAP, Mycobacterium avium ssp. paratuberculosis; FC, faecal culture; PCR, polymerase chain reaction.
Simultaneous testing by faecal culture together with PCR methods led to slightly lower WHPapp thresholds in each laboratory compared to faecal culture results. PCR C together with faecal culture C applied on boot swabs (P d 50%: 2·39 ± 0·54%; P d 90%: 5·85 ± 1·24%) and PCR B together with faecal culture B applied on liquid manure samples (P d 50%: 2·57 ± 0·56%; P d 90%: 6·08 ± 1·28%) showed the lowest estimates for a single sample. The best results were obtained when the results of both samples were included in the model. Again, the lowest WHPapp thresholds were estimated for PCR C and faecal culture C applied on a combined set of boot swab and liquid manure samples (P d 50%: 1·49 ± 0·39%; P d 90%: 3·99 ± 0·90%; Fig. 1).
Fig. 1. Logistic functions of the probability of detection using boot swabs and liquid manure samples combined (results from laboratory C).
DISCUSSION
In order to control paratuberculosis in cattle herds, it is necessary to identify MAP-positive herds, to focus on these herds, and to persuade farmers to enrol in voluntary control programmes and implement control measures in their herds. As sampling individual animals in order to identify infected herds has its limitations, testing environmental samples by faecal culture is not only an alternative for herd diagnosis in low-prevalence herds, but actually shows test characteristics [Reference Sweeney22, Reference Donat25] better than those demonstrated for milk ELISA testing at the herd level [Reference Lavers15].
Our study aimed to demonstrate that even two samples – one boot swab and one liquid manure sample – are sufficient to identify MAP-positive herds. This study was performed in dairy herds well characterized with regard to their disease status according to the control programme regulations, with either herds not suspected of having paratuberculosis or MAP-positive herds with WHPapp known from individual faecal culture testing in previous years. This enabled us to calculate thresholds for identifying a herd as MAP-positive from a representative number of 77 study herds with a median WHPapp of 2·4%. The number of herds involved is one strength of our study compared to previous faecal culture-based studies, which applied environmental sampling of seven [Reference Pillars19] and 46 herds [Reference Donat20], respectively.
Compared to previous studies [Reference Raizman16–Reference Lombard18, Reference Lavers24], another strength of our study design is that we used the most sensitive method currently available for the diagnosis of Johne's disease in living animals for the estimation of WHPapp, i.e. individual faecal culture. Due to the higher sensitivity and specificity of faecal culture, studies that estimated WHPapp by direct detection of the organism in individual samples from each animal [Reference Pillars19–Reference Smith21] are less susceptible to misclassification bias than those using identification based on the detection of antibodies against MAP or pooled samples. Therefore, our WHPapp estimation was not influenced by any bias as can be anticipated after pooling, resulting in more precise data. This is particularly important in herds with low prevalence. Nonetheless, some uncertainty remains as a result of the suboptimal sensitivity of faecal culture, which is estimated to be approximately 60% relative to tissue culture [Reference Sweeney22]. We decided to refer to the faecal culture-based WHPapp because necropsy followed by tissue culture is not a realistic option for diagnosis in the framework of control programmes or field studies. Furthermore, the estimation of WHPapp was animal-based, and it cannot be ruled out that intermittent shedding by low shedders may cause some variability in the faecal culture outcome. In addition, at least in Thuringia, not all cows present in the herd on the day of environmental sampling had been tested; only those that had been sampled previously had, resulting in an average proportion of tested cows of 86·8% (Table 1). This may have led to an underestimation of WHPapp in herds with more shedders among the non-tested cows compared to the tested ones, or vice versa. We accepted this potential misclassification bias, as the percentage of non-tested cows was far smaller than the percentage of those tested. As such, this uncertainty cannot be excluded from the WHPapp estimation.
As the measured values of both MAP detection tests (Ct values for PCR, colony growth score for faecal culture) showed a highly significant association with WHPapp (Table 3), we calculated a logistic regression for both methods separately and for the combination of the faecal culture with PCR applied on boot swab or liquid manure samples for each laboratory (Table 4). As expected, the use of two test methods simultaneously increased the OR resulting from the logistic regression model, demonstrating a higher chance of identifying a herd as MAP positive when WHPapp increases. Consequently, the outcome of the WHPapp threshold estimation by the logistic model showed the same effect. Applying two tests resulted in lower WHPapp estimates in boot swabs, liquid manure samples and the combination of both matrices, respectively. Applying faecal culture (all laboratories) or PCR C to a combined boot swab and liquid manure sample, the estimate was lower compared to the use of only one matrix, apart from boot swabs tested by faecal culture in laboratory C (Tables 5 and 6). These markedly good results may be explained by the laboratory's many years of experience with faecal culture as Germany's national reference laboratory for paratuberculosis. This result may encourage the application of faecal culture on boot swabs alone, if the laboratory ensures a high standard for this test method.
The lowest estimates were calculated for the combination of faecal culture and PCR in laboratory C for a combined boot swab and a liquid manure sample with 1·5% at 50% Pd and 4·0% at the 90% Pd level. These values clearly demonstrate that using a combination of one boot swab and one liquid manure sample is sufficiently sensitive to identify dairy herds with a low prevalence of MAP shedders at an acceptable probability level. Even boot swabs alone performed rather satisfactorily, with estimated thresholds of about 2·4% at 50% P d and 5·8% at 90% P d. This is of considerable practical value as boot swabs are very easy to sample, pack and ship. Nonetheless, our results show that the combination of both matrices, one sample collected in cow concentration areas and the other one representing manure storage areas, leads to the most reliable outcome. Although the application of two methods on one sample appears to be elaborative and expensive, it is worthwhile as part of control programmes because it enhances the application options of environmental sampling. The detection limit of about 4% at 90% P d enables the use of environmental sampling as a reliable screening tool. The 90% P d WHPapp threshold gives an indication of what can be expected from the use of single sampling in voluntary control programmes or prevalence studies. It is important to identify herds with a high WHPapp because these herds represent the highest risk of MAP shedding into the food chain and the environment. In voluntary control programmes, these farms should be identified and given priority by consultants in order to enable the immediate introduction of control measures.
The reduction to 1·5% at 50% P d may allow herds not suspected of having paratuberculosis to be monitored in certification programmes, at least for herds with fewer than 50 cows, taking into account the following: In those herds, one shedder will cause a WHPapp of ⩾2%, which means that, theoretically, environmental sampling has the potential to detect all herds of this size in which there is one MAP shedder. Repeated sampling will not further reduce the WHPapp threshold, but it enhances the P d at a certain WHPapp level. Assuming, for example, five statistically independent observations of boot swab and liquid manure samplings with the calculated WHPapp threshold of 1·5% at P d of 50%, the resulting P d would be 96·9% and, therefore, acceptable. Despite concerns with respect to the misclassification of low-prevalence MAP-positive herds as ‘false MAP-negative’ by using solely environmental samples [Reference Pillars19–Reference Smith21], our results encourage the application of environmental sampling to monitor herds certified as not suspected of having paratuberculosis under certain conditions. Serious limitations remain for the use of environmental sampling to monitor large herds, especially in multi-site housing systems.
Taken together, these results confirm the hypothesis that boot swabs and liquid manure samples are an efficient means of identifying MAP-positive dairy herds. We favour a combination of one boot swab and one liquid manure sample tested simultaneously by faecal culture and PCR. This approach is suitable for identifying MAP-positive dairy herds at an acceptable probability level even if the WHPapp is low.
The use of one boot swab sample alone impairs the detectable WHPapp threshold to a certain degree, but is still a useful approach. Further research is required in a longitudinal study to evaluate the repeated use of boot swabs and liquid manure samples in herds previously certified as not suspected of having paratuberculosis, particularly in order to detect a reintroduction of the infectious agent.
ACKNOWLEDGEMENTS
This joint research project was undertaken and financed by the animal health services of three German federal states (organizing institutions: Hessian State Laboratory, Hesse State Council, Saxon Animal Disease Fund, Thuringian Animal Disease Fund). The authors thank all institutions for their support. Furthermore, the authors gratefully acknowledge the financial support by the Thuringian Dairy Industry Association (Landesvereinigung Thüringer Milch e.V.) and the Hessian Animal Disease Fund. Above all, the authors would like to thank the dairy farmers who participated, the laboratory staff, all veterinarians who collected samples, and Matthew Rockey for improving the English.
DECLARATION OF INTEREST
None.
