| Literature DB >> 30711919 |
John Graham-Brown1, Diana J L Williams1, Philip Skuce2, Ruth N Zadoks2,3, Stuart Dawes2, Harry Swales4, Jan Van Dijk5.
Abstract
Options for diagnosing Fasciola hepatica infection in groups of cattle are limited. Increasing the opportunities for herd-level diagnosis is important for disease monitoring, making informed treatment decisions and for flukicide efficacy testing. The sensitivity of a simple sedimentation method based on composite faecal samples for the detection of fluke eggs in cattle was assessed through a combination of experimental and statistical modelling techniques. Initially, a composite sample method previously developed for sheep was used to investigate the sensitivity of composite sample testing compared with individual counts on the same samples in cattle. Following this, an optimised, validated, qualitative (presence-absence) composite sample field test was developed for cattle. Results showed that fluke egg counts obtained from a composite sample are representative of those expected from individual counts. The optimal sampling strategy was determined to be 10 individual 10 g samples (100 g composite sample) from which a 10 g subsample is taken for sedimentation. This method yielded a diagnostic sensitivity of 0.69 (95 per cent CI 0.5 to 0.85). These results demonstrate the validity and usefulness of a composite faecal egg sedimentation method for use in the diagnosis and control of F. hepatica in groups of cattle, with the caveat that a negative test should be followed up with a second test due to limitations relating to test sensitivity. © British Veterinary Association 2019. Re-use permitted under CC BY. Published by BMJ.Entities:
Keywords: cattle; diagnostics; herd health; liver fluke; parasitology
Mesh:
Year: 2019 PMID: 30711919 PMCID: PMC6583716 DOI: 10.1136/vr.105128
Source DB: PubMed Journal: Vet Rec ISSN: 0042-4900 Impact factor: 2.695
Parameters of fitted negative binomial distributions (NBDs) for farms A.1–A.7 and B.1–B.22
| Farm ID | |||
| A.1 | 1.048 | 14.750 | 0.194 |
| A.2 | 0.914 | 13.850 | 0.297 |
| A.3 | 3.905 | 10.150 | 0.276 |
| A.4 | 0.594 | 0.400 | 0.878 |
| A.5 | 2.053 | 48.667 | 0.262 |
| A.6 | 2.152 | 47.550 | 0.253 |
| A.7 | 0.488 | 2.500 | 0.878 |
| B.1 | 0.237 | 2.077 | 0.998 |
| B.2 | 100 | 0.083 | 0.925 |
| B.3 | 0.555 | 2.320 | 0.827 |
| B.4 | 0.825 | 2.071 | 0.319 |
| B.5 | 3.121 | 4.720 | 0.759 |
| B.6 | 1.352 | 1.640 | 0.852 |
| B.7 | 0.252 | 0.360 | 0.967 |
| B.8 | 0.891 | 2.920 | 0.834 |
| B.9 | 0.193 | 1.625 | 0.992 |
| B.10 | 0.811 | 0.550 | 0.614 |
| B.11 | 100 | 0.400 | 0.467 |
| B.12 | 0.240 | 1.250 | 0.350 |
| B.13 | 8.364 | 1.450 | 0.667 |
| B.14 | 0.307 | 0.950 | 0.754 |
| B.15 | 0.675 | 0.800 | 0.687 |
| B.16 | 0.867 | 2.350 | 0.676 |
| B.17 | 100 | 0.030 | 1.000 |
| B.18 | 100 | 0.150 | 0.349 |
| B.19 | 0.020 | 0.250 | 1 |
| B.20 | 0.044 | 0.100 | 1 |
| B.21 | 100 | 0.100 | 0.574 |
| B.22 | 1.097 | 2.000 | 0.707 |
k captures the degree of overdispersion and µ the mean egg count for each fitted NBD. X2 P values are the result of comparison between original fluke egg counts and NBD-predicted fluke egg counts.
Summary of multivariable linear regression analysis using egg count data from all 29 farms (A and B) in part 1
| Variable | Transformation | Intercept ( | Coefficient ( | P value |
| Response variable ( | ||||
| Coefficient of variation | log( | 0.779 | – | 0.0003 |
| Explanatory variables ( | ||||
| NBD-predicted FEC (50 g) | log( | – | −0.342 | 1.51×10−7 |
| Quantity of faeces (g) | log( | – | −0.261 | 0.0004 |
with fitted intercept (α), coefficients (β) and P values.
FEC, faecal egg counts; NBD, negative binomial distribution.
Summary of composite egg counts for farms A.1–A.7
| ID | % of egg positive samples* | Composite egg count (10×5 g) |
| A.1 | 95 | 96 |
| 82 | ||
| A.2 | 89 | 61 |
| 46 | ||
| A.3 | 100 | 68 |
| 57 | ||
| A.4 | 25 | 6 |
| 1 | ||
| A.5 | 100 | 167 |
| 341 | ||
| A.6 | 100 | 201 |
| 269 | ||
| A.7 | 53 | 0 |
| 12 |
Two composite counts are shown for each farm (n=14).
*Based on individual counts.
Figure 1Comparison of model generated 95% CIs from phase I to (a) sum of observed individual egg counts (per 50 g) based on individual counts for 1 and 10 g faecal samples and (b) observed composite egg counts for 10×5 g composite samples.
NBDs fitted to egg count data (≥40 cattle), the predicted numbers of eggs recovered and the probability of finding ≥2 eggs in a 10-sample composite in phase II
| Sampling | Parameters | Herd H | Herd M | Herd C | Herd I | Herd N | Herd D | Herd T |
| March/April | 1.00 | 0.37 | 0.41 | 0.33 | NEE | NS | NS | |
| 7.06 | 0.78 | 0.63 | 4.08 | |||||
| Mean rec | 71 (30– 123) | 7 (0–21) | 6 (1–15) | 42 (9–97) | 0 (0–2) | |||
| Probability | 1 | 0.96 | 0.92 | 0.99 | 0.09 | |||
| May/ June / July | 0.32 | NEE | 0.27 | 0.16 | NED | NS | NS | |
| 1.68 | 0.48 | 0.10 | ||||||
| Mean rec | 1 (0–3) | 5(0–14) | 1 (0–4) | 0 (0–0) | ||||
| Probability | 0.99 | 0.24 | 0.81 | 0.25 | 0 | |||
| August | NS | NS | NS | NS | NS | 0.35 | 0.29 | |
| 0.46 | 0.24 | |||||||
| Mean rec | 5 (0–13) | 2 (0–7) | ||||||
| Probability | 0.89 | 0.60 | ||||||
| September/ October/ November | 0.68 | NEE | 0.54 | 0.40 | 0.30 | NS | NS | |
| 1.00 | 0.73 | 2.48 | 0.39 | |||||
| Mean rec | 10 (3–21) | 1 (0–3) | 7 (1–17) | 24 (5–56) | 4 (0–11) | |||
| Probability | 0.99 | 0.25 | 0.95 | 0.99 | 0.77 |
k and µ give the degree of overdispersion and the mean of the fitted NBDs, respectively; ‘mean rec’=simulated mean recovery (95% CI) numbers of eggs in a 10-sample composite; ‘probability’=likelihood of finding ≥2 eggs in the composite sediment.
NBD, negative binomial distribution; NEE, not enough eggs detected to reliably fit an NBD; NED, no eggs detected; NS, not sampled.
Bootstrapped estimated egg recovery and likelihood of finding ≥2 eggs across all samplings in phase II
| Number of samples | 8+2 | 10 | 12 |
| Mean rec | 12 (4 to 22) | 13 (5 to 23) | 15 (7 to 27) |
| Probability | 0.68 (0.51 to 0.83) | 0.69 (0.50 to 0.85) | 0.72 (0.57 to 0.88) |
'8+2’=8 random samples and two of these (randomly chosen) contribute to the composite twice; ‘mean rec’=simulated mean recovery (95% CI) numbers of eggs in a 10-sample composite; ‘probability’=likelihood of finding ≥2 eggs in the composite sediment (95% CI), eg, the estimated overall sensitivity of the test.