| Literature DB >> 30909452 |
Nantawan Yatbantoong1, Rattanawat Chaiyarat2.
Abstract
Leptospirosis found in cattle (Bos taurus indicus) has potentially increased in economic impact. The objective was to investigate the factors associated with leptospirosis in cattle in the protected area. We investigated the seroprevalence of leptospirosis in cattle in Salakphra Wildlife Sanctuary, Thailand. Serum was collected to investigate the seroprevalence by agglutination test and their associated factors. From a total of 513 samples, antibodies against Leptospira were detected in 92.2% of samples. Within a total of 42 herds, the serovar with the highest prevalence was L interrogans serovar Tarassovi (92.9%). Most leptospirosis was found in medium-sized herds with the highest concentrations in cattle farms close to cities (52.4%, p < 0.05). Seroprevalence was associated with herd size, raising pattern in the dry and wet seasons, grazing distance, number of years that cattle were kept in the farm, the introduction of new cattle into the farm, and keeping some pets in the farm. The results of the study suggest that keeping cattle in larger herds, raising pattern and distance, keeping period, and introducing new cattle and having pets impart potential risk of increasing leptospirosis exposure. These results indicate that cattle are important hosts of Leptospira in Thailand and may act as sentinels of Leptospira infection for wildlife and people in the protected areas.Entities:
Keywords: domestic cattle; leptospira; livestock production; protected area
Mesh:
Substances:
Year: 2019 PMID: 30909452 PMCID: PMC6466321 DOI: 10.3390/ijerph16061042
Source DB: PubMed Journal: Int J Environ Res Public Health ISSN: 1660-4601 Impact factor: 3.390
Figure 1The location of cattle and the seroprevalence along the Salakphra Wildlife Sanctuary.
Herd size, sample size, location and seroprevalence of Leptospira interrogans found in domestic cattle in Salakphra Wildlife Sanctuary.
| Herd ID | Herd Size (Individuals) | Sample Size (Individuals (%)) | Location | Seroprevalence of | |||||||||||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| aut | bal | bat | bra | can | cyn | dja | heb | ict | jav | lou | min | pom | pyr | ran | sar | sej | tar | ||||
| A | 70 | 7 (10) | 1 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 4 | 0 | 0 | 0 | 0 | 0 | 0 | 7 | 0 | 0 | 7 |
| B | 60 | 7 (11.7) | 1 | 0 | 0 | 0 | 1 | 0 | 0 | 0 | 3 | 0 | 0 | 0 | 0 | 0 | 0 | 7 | 0 | 0 | 7 |
| C | 30 | 5 (16.7) | 1 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 5 | 0 | 0 | 5 |
| D | 70 | 5 (7.1) | 1 | 0 | 0 | 0 | 3 | 0 | 0 | 0 | 2 | 0 | 0 | 0 | 0 | 0 | 0 | 5 | 0 | 0 | 5 |
| E | 14 | 9 (64.3) | 1 | 0 | 9 | 0 | 3 | 0 | 1 | 1 | 3 | 0 | 0 | 0 | 0 | 0 | 0 | 8 | 0 | 5 | 9 |
| F | 7 | 7 (100) | 1 | 0 | 6 | 1 | 2 | 0 | 0 | 0 | 2 | 0 | 0 | 0 | 0 | 1 | 0 | 6 | 0 | 5 | 6 |
| G | 9 | 2 (22.2) | 1 | 0 | 0 | 0 | 1 | 0 | 0 | 0 | 1 | 0 | 0 | 0 | 0 | 0 | 0 | 2 | 0 | 0 | 2 |
| H | 42 | 2 (4.8) | 2 | 0 | 0 | 0 | 2 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 2 | 0 | 0 | 2 |
| I | 44 | 9 (20.5) | 2 | 0 | 0 | 0 | 5 | 0 | 0 | 0 | 5 | 0 | 0 | 0 | 0 | 0 | 0 | 9 | 0 | 0 | 9 |
| J | 70 | 4 (5.7) | 2 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
| K | 37 | 3 (8.1) | 2 | 0 | 0 | 0 | 1 | 0 | 0 | 0 | 1 | 0 | 0 | 0 | 0 | 0 | 0 | 3 | 0 | 0 | 3 |
| L | 80 | 1 (1.3) | 2 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 1 | 0 | 0 | 1 |
| M | 120 | 2 (1.7) | 2 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 2 | 0 | 0 | 2 |
| N | 60 | 4 (6.7) | 2 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 1 | 0 | 0 | 0 | 0 | 0 | 0 | 4 | 0 | 0 | 4 |
| O | 24 | 3 (12.5) | 2 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 1 | 0 | 0 | 0 | 0 | 0 | 0 | 3 | 0 | 0 | 2 |
| P | 27 | 3 (11.1) | 1 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 3 | 0 | 0 | 3 |
| Q | 42 | 4 (9.5) | 1 | 0 | 0 | 0 | 1 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 4 | 0 | 0 | 4 |
| R | 59 | 6 (10.2) | 1 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 1 | 0 | 0 | 0 | 0 | 0 | 0 | 5 | 0 | 0 | 4 |
| S | 60 | 6 (10) | 3 | 0 | 0 | 0 | 1 | 0 | 0 | 0 | 1 | 0 | 0 | 0 | 0 | 0 | 0 | 6 | 0 | 0 | 6 |
| T | 60 | 2 (3.3) | 3 | 0 | 5 | 0 | 0 | 0 | 0 | 0 | 1 | 0 | 0 | 0 | 0 | 0 | 0 | 3 | - | - | 3 |
| U | 31 | 7 (22.6) | 3 | 0 | 5 | 0 | 0 | 0 | 0 | 0 | 1 | 0 | 0 | 0 | 0 | 0 | 1 | 5 | 1 | 2 | 7 |
| W | 70 | 7 (10) | 3 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
| X | 110 | 4 (3.6) | 3 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 1 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
| Y | 50 | 6 (12) | 3 | 0 | 2 | 0 | 0 | 0 | 0 | 0 | 1 | 0 | 0 | 0 | 0 | 0 | 0 | 1 | 0 | 1 | 2 |
| Z | 143 | 17 (11.9) | 3 | 0 | 14 | 1 | 1 | 0 | 0 | 0 | 2 | 0 | 0 | 0 | 0 | 0 | 0 | 11 | 0 | 2 | 13 |
| AA | 34 | 5 (14.7) | 3 | 0 | 2 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 4 | 0 | 0 | 4 |
| BB | 65 | 8 (12.3) | 3 | 0 | 6 | 0 | 0 | 0 | 0 | 0 | 3 | 0 | 0 | 0 | 0 | 0 | 0 | 6 | 0 | 0 | 6 |
| CC | 100 | 15 (15) | 3 | 0 | 9 | 0 | 2 | 0 | 0 | 0 | 5 | 0 | 0 | 0 | 0 | 0 | 1 | 14 | 0 | 0 | 15 |
| DD | 70 | 7 (10) | 1 | 0 | 1 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 6 | 0 | 0 | 6 |
| EE | 130 | 1 (0.8) | 1 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
| FF | 100 | 10 (10) | 1 | 0 | 4 | 0 | 1 | 0 | 0 | 0 | 2 | 0 | 0 | 0 | 0 | 0 | 0 | 9 | 0 | 0 | 1 |
| GG | 100 | 4 (4) | 1 | 0 | 2 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 2 | 0 | 0 | 3 |
| HH | 40 | 5 (12.5) | 1 | 0 | 2 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 5 | 0 | 2 | 5 |
| II | 57 | 8 (14) | 1 | 0 | 2 | 0 | 0 | 0 | 0 | 0 | 1 | 0 | 0 | 0 | 0 | 0 | 0 | 1 | 0 | 2 | 4 |
| JJ | 107 | 10 (9.3) | 1 | 0 | 4 | 0 | 1 | 0 | 0 | 0 | 4 | 0 | 0 | 0 | 0 | 0 | 0 | 4 | 0 | 5 | 9 |
| KK | 33 | 10 (30.3) | 1 | 0 | 10 | 0 | 0 | 0 | 0 | 0 | 1 | 0 | 0 | 1 | 0 | 0 | 0 | 10 | 0 | 9 | 9 |
| MM | 60 | 20 (33.3) | 1 | 2 | 12 | 0 | 0 | 9 | 0 | 0 | 2 | 0 | 0 | 0 | 1 | 1 | 13 | 13 | 2 | 3 | 13 |
| TT | 40 | 13 (32.5) | 3 | 5 | 5 | 0 | 0 | 1 | 0 | 1 | 1 | 0 | 0 | 0 | 0 | 1 | 0 | 1 | 2 | 0 | 7 |
| UU | 47 | 10 (21.3) | 3 | 4 | 4 | 0 | 0 | 0 | 0 | 0 | 1 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 7 |
| VV | 60 | 12 (20) | 3 | 12 | 12 | 0 | 3 | 1 | 1 | 2 | 3 | 0 | 1 | 0 | 1 | 0 | 3 | 0 | 0 | 4 | 12 |
| WW | 105 | 18 (17.1) | 3 | 13 | 13 | 0 | 1 | 0 | 0 | 0 | 2 | 2 | 0 | 0 | 0 | 0 | 1 | 2 | 2 | 4 | 18 |
| XX | 2,537 | 225 (8.9) | 1 | 36 | 129 | 2 | 29 | 11 | 2 | 4 | 56 | 2 | 1 | 1 | 2 | 3 | 19 | 179 | 7 | 44 | 225 |
| Seroprevalence (individuals (%)) | 72 (14) | 258 (50.3) | 4 (0.8) | 58 (11.3) | 22 (4.3) | 4 (0.8) | 8 (1.6) | 112 (21.8) | 4 (0.8) | 2 (0.4) | 2 (0.4) | 4 (0.8) | 6 (1.2) | 38 (7.4) | 358 (69.8) | 14 (2.7) | 88 (17.2) | 450 (87.7) | |||
Location 1 = Muang district, 2 = Sri Sawat district, 3 = Bo Phloi district, aut = Autumnalis, bal = Ballum, bat = Bataviae, bra = Bratislava, can = Canicola, cyn = Cynopteri, dja = Djasiman, heb = Hebdomadis, ict = Icterohaemorrhagica, jav = Javanica, lou = Louisiana, min = Mini, pom = Pomona, pyr = Pyrogenes, ran = Ranarum, sar = Sarmin, sej = Sejroe, Tar = Tarassovi.
Seroprevalence and the Shannon–Wiener diversity index of twenty Leptospira interrogans serovars found in domestic cattle herds (n = 42 herds) and red spiny rats (n = 70 sites) in Salakphra Wildlife Sanctuary.
| Serovars | Cattle Herd (% Prevalence) | Red Spiny Rat (% Prevalence) | Titer Range |
| df | |
|---|---|---|---|---|---|---|
|
| ||||||
| Tarassovi | 39 (92.9) | 4 (30.8) | 50–800 | 28.5 | 1 | <0.001 |
| Ranarum | 37 (88.1) | 4 (30.8) | 50–400 | 26.6 | 1 | <0.001 |
| Hebdomadis | 30 (71.4) | - | 5–800 | 30 | 1 | N/A |
| Ballum | 22 (52.4) | - | 50–400 | 22 | 1 | N/A |
| Bratislava | 17 (40.5) | - | 50–400 | 17 | 1 | N/A |
| Sejroe | 12 (28.6) | 1 (7.7) | 50–400 | 9.3 | 1 | 0.002 |
| Autumnalis | 6 (14.3) | - | 50–100 | 6 | 1 | N/A |
| Pyrogenes | 6 (14.3) | - | 50–400 | 2 | 1 | 0.153 |
| Bataviae | 5 (11.9) | 2 (15.4) | 50–100 | 5 | 1 | N/A |
| Sarmin | 5 (11.9) | 1 (7.7) | 50–100 | 2.7 | 1 | 0.098 |
| Canicola | 4 (9.5) | 4 (30.8) | 50–100 | 0 | 1 | N/A |
| Djasiman | 4 (9.5) | - | 50 | 4 | 1 | N/A |
| Icterohaemorrhagica | 3 (7.1) | - | 50–100 | 3 | 1 | N/A |
| Pomona | 3 (7.1) | 3 (23.1) | 50 | 0 | 1 | N/A |
| Cynopteri | 2 (4.8) | 1 (7.7) | 5–100 | 0.3 | 1 | 0.571 |
| Mini | 2 (4.8) | - | 50 | 2 | 1 | N/A |
| Javanica | 1 (2.4) | - | 100 | 1 | 1 | N/A |
| Louisiana | 1 (2.4) | - | 50 | 1 | 1 | N/A |
| Shermani | - | 9 (69.2) | 50 | 9 | 1 | N/A |
| Patoc I | - | 4 (30.8) | 50 | 4 | 1 | N/A |
| 1.027 | 0.905 | 173.4 | 40 | <0.001 |
Leptospires used for rabbit immunization.
The relationships between environmental factors and seroprevalence in domestic cattle in Salakphra Wildlife Sanctuary.
| Environmental Factor | Level | Seroprevalence |
| df | |
|---|---|---|---|---|---|
| Herd size (individuals) | 1 = small (<40) | 11 (26.2) | 7 | 2 | 0.03 * |
| Raising patterns | 1 = free grazing | 40 (95.2) | 42.9 | 1 | <0.001 *** |
| Raising distance (km/day) | 1 = <1 | 3 (7.1) | 18.8 | 3 | <0.001 *** |
| Water resource | 1 = natural source | 23 (54.8) | 1.5 | 1 | 0.22 ns |
| Number of years that livestock were kept (years) | 1 = <1 | 1 (2.4) | 32.5 | 4 | <0.001 *** |
| Raising in the same route with other herds | 0 = no | 26 (61.9) | 2.4 | 1 | 0.12 ns |
| Sharing feeding ground with other herds | 0 = no | 16 (38.1) | 2.4 | 1 | 0.12 ns |
| Introduced of new animal into herd | 0 = no | 31 (73.8) | 9.5 | 1 | 0.002 ** |
| Pets in the farm | 0 = no | 9 (21.42) | 18.7 | 1 | <0.001 *** |
| Abortion history | 0 = not aborted | 27 (64.3) | 3.4 | 1 | 0.06 ns |
a Significant level: ns = not significant, * = 0.05, ** = 0.01, *** = 0.001.
Figure 2Seroprevalence accumulation curves of cattle and red spiny rat in Salakphra Wildlife Sanctuary.
Factor loading eigenvalue, environmental factors, seroprevalence, and coordinates of sites of correlative coherence analysis (CCA) around the Salakphra Wildlife Sanctuary.
| Parameter | PC1 | PC2 | PC3 |
|---|---|---|---|
| Risk factor | |||
| Location of herd * | −0.265 | 0.062 | −0.165 |
| Herd size | −0.017 | −0.146 | −0.054 |
| Place | −0.100 | −0.031 | 0.098 |
| Raising distance (km/day) * | −0.076 | 0.111 | 0.081 |
| Together | −0.080 | −0.251 | 0.029 |
| Togeth_a | −0.061 | 0.069 | 0.088 |
| Number of years that domestic cattle were kept (years) * | 0.032 | 0.250 | −0.241 |
| Introduced of new animal into herd * | −0.257 | 0.052 | 0.015 |
| Abortion history * | −0.094 | −0.223 | −0.014 |
| Domestic cattle | 0.099 | 0.200 | 0.103 |
| Autumnalis | −2.948 | −0.884 | −0.673 |
| Ballum | −0.380 | −0.293 | 0.617 |
| Bataviae | 0.831 | −0.853 | 0.345 |
| Bratislava | 0.758 | −0.695 | −2.133 |
| Canicola | −0.770 | 4.907 | 0.283 |
| Cynopteri | −1.054 | −1.306 | 0.478 |
| Djasiman | −2.056 | −0.632 | −0.288 |
| Hebdomadis | 0.483 | −0.274 | −1.459 |
| Icterohaemorrhagica | −3.320 | −1.305 | −0.360 |
| Javanica | −4.350 | −0.279 | −2.689 |
| Louisiana | 0.982 | −3.859 | 7.542 |
| Mini | −2.176 | 3.175 | −0.534 |
| Pomona | −1.037 | 1.766 | −1.483 |
| Pyrogenes | −0.994 | 4.179 | 0.566 |
| Ranarum | 1.033 | 0.209 | −0.066 |
| Sarmin | −1.804 | 1.108 | −1.141 |
| Sejroe | 0.041 | −0.602 | 2.720 |
| Tarassovi | 0.129 | −0.160 | −0.142 |
* Denotes significant relationship at p < 0.05.
Figure 3Relationships of 18 seroprevalence and herd variables revealed of domesticated cattle by Correlative Coherence Analysis (CCA) in the Salakphra Wildlife Sanctuary, TIME = Number of years that livestock were kept in the farm (years), DISTANCE = Raising distance (km/day), NEW = Introduced of new animal into herd, LOCATION = Raising in the same route with other herds, ABORTION = Abortion history, L_aut = Autumnalis, L_bal = Ballum, L_bat = Bataviae, L_bra = Bratislava, L_can = Canicola, L_cyn = Cynopteri, L_dja = Djasiman, L_heb = Hebdomadis, L_ict = Icterohaemorrhagica, L_jav = Javanica, L_lou = Louisiana, L_min = Mini, L_pom = Pomona, L_pyr = Pyrogenes, L_ran = Ranarum, L_sar = Sarmin, L_sej = Sejroe.