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Peste des petits ruminants infection among cattle and wildlife in Northern Tanzania.

Peste des petits ruminants virus (PPRV) is a highly contagious morbillivirus (genus Morbillivirus, family Paramyxoviridae) that is closely related to rinderpest virus. PPRV primarily affects sheep and goats in Africa, Middle East, and Asia but can infect a wide range of other domestic and nondomestic species (1-4). For example, cattle have been found to be seropositive for the virus (1,2), and PPRV was isolated from subclinically infected cattle 3 weeks after virus transmission from experimentally infected goats (R.K. Singh, pers. comm.). This finding points to the need for further investigation of the role of cattle in peste des petits ruminants (PPR) disease outbreaks. In addition, little is known about natural patterns of PPR in free-ranging African wildlife. Morbilliviruses can switch hosts, and new ecologic niches created by the eradication of rinderpest may provide opportunities for PPR emergence in new hosts (4,5).

First identified in West Africa in the 1940s, PPR is now widespread across much of sub-Saharan Africa. High rates of death from PPR can have dramatic economic consequences, especially in rural African communities whose livelihoods rely on small ruminant livestock production (6). The potentially devastating effect of new introductions has raised considerable concerns for local and regional economies (6). PPR was first confirmed in Tanzania in 2008 in the country's northern regions. However, the virus, which was introduced into Tanzania by southward spread from neighboring countries, was probably in Tanzania long before official confirmation of the disease (7,8).

Capitalizing on the momentum resulting from the eradication of rinderpest, international agencies, including the Food and Agriculture Organization and the World Animal Health Organization, have focused attention on PPR; the disease has been identified as the next livestock disease candidate for eradication (9), and large-scale PPR interventions are being implemented in much of Africa. Epidemiologic surveillance is critical in global disease elimination and was considered key to the eradication of rinderpest (10). Although participatory surveillance was essential in assessing the levels and effect of cattle vaccination (10), wildlife serosurveillance was the primary tool for detecting the presence or absence of circulating rinderpest virus in the final stages of the eradication process (11). Grassroots-level surveillance is also likely to play a critical role in PPR control (7). However, critical questions remain about the role that species other than sheep and goats may play in PPRV persistence (2,3,12); the value of serosurveillance in control efforts; and, more specifically, whether cattle and wildlife species are useful indicators of virus circulation. To address these questions, we carried out serologic investigations for evidence of PPR infection in cattle and wildlife in northern Tanzania. The cattle lived in mixed cattle-small ruminant livestock systems in an area where a PPR outbreak had occurred in 2008, and the wildlife populations lived in protected-area ecosystems across a broader geographic area.

The Study

Serum samples from cattle living in close proximity to sheep and goats were available as part of epidemiologic studies involving randomly selected pastoralist households in Ngorongoro District, an area of the Serengeti ecosystem in northern Tanzania where the 2008 PPR outbreak had been confirmed (Figure) (7). The sampling was conducted in early to mid-2011 and included serum samples from cattle [greater than or equal to] 3 years of age (as determined on the basis of incisor tooth eruption) and from cattle [less than or equal to] years of age; the older cattle were alive during the 2008 outbreak, and the younger cattle were born after the outbreak (Table 1). In the area, large-scale PPR vaccination of sheep and goats was initiated in early 2011 but did not include cattle. The last rinderpest vaccination campaign in Tanzania was carried out in 1997 (13).

Serum samples from buffalo (Syncerus caffer) and gazelle (Eudorcas thomsonii and Nanger granti) came from an archived serum bank and were made available through the Tanzania Wildlife Research Institute-Messerli Foundation Wildlife Veterinary Programme in Seronera, Tanzania. The samples had been collected during wildlife immobilization operations conducted for rinderpest surveillance, research activities, and conservation management (Table 2). Wildlife samples originated from several ecosystems, including the Serengeti ecosystem (Figure). Age information based on incisor tooth eruption was available for a subset of buffalo sampled in the Serengeti National Park and Ngorongoro Conservation Area during 2011-2012 (Table 1).

PPRV antibodies were detected by using the antihemagglutinin PPRV C-ELISA (Biological Diagnostic Supplies Limited [BDSL], Dreghorn, UK; www.bdsl2000. com/diagnostic-kits/ppr.aspx). Samples with positive results (i.e., inhibition value >50%) were confirmed as positive by using the anti-nucleoprotein PPRV C-ELISA (IDvet, Grabels, France; The assays were performed and analyzed according to the manufacturers' instructions.

The screening for PPRV antibodies in cattle showed that 26.7% of the samples from cattle that were alive during the 2008 PPR outbreak were seropositive, and 5.9% of those from cattle born after the outbreak were seropositive. Seroprevalence in village cattle ranged from 7% to 48% (Figure). No detailed clinical information was available for the period of the outbreak.

Except for 1 borderline positive buffalo sample (inhibition value 56.6%), no seropositive samples were detected among samples from 266 buffalo, 59 Thomson's gazelles, and 6 Grant's gazelles. The borderline seropositive buffalo was from the Arusha ecosystem and would have been alive during the 2008 PPR outbreak. PPR-seronegative buffalo included older animals (i.e., [greater than or equal to] 4 years) from Serengeti National Park (n = 20) and Ngorongoro Conservation Area (n = 85) that were alive at the time of the 2008 outbreak and younger animals from Serengeti National Park (n = 10) and Ngorongoro Conservation Area (n = 35).


Our findings show higher rates of PPR seropositivity than found in previous studies and confirm that cattle are susceptible to PPR (1,2). These data support the view that in pastoral communities of northern Tanzania, where small ruminants and cattle co-exist, cross-species transmission of PPRV from small ruminants to cattle is likely to occur frequently.

Two broad conclusions can be drawn from these results. First, cattle are likely to be helpful indicators of PPRV circulation in mixed livestock communities and are therefore a useful population for surveillance. The study indicates that surveillance in cattle may also prove helpful in areas where PPR mass vaccination campaigns in sheep and goats have been implemented and would add value to existing syndromic surveillance networks. This conclusion is supported by the detection of seropositive young cattle (1-2 years of age) in more recent years at a time when no clinical cases were reported in small ruminants in the area.

Although transmission of the live attenuated PPR vaccine strain in the field cannot be completely ruled out, there is currently no evidence for vaccine strain transmission either in the field or through experimental infection studies (14). Second, the high potential for cross-species transmission of PPRV from small ruminants to cattle in areas where these species live in close proximity suggests that monitoring such livestock communities would be useful for detecting any changes in the apparent pathogenicity of PPRV, including the possible emergence of PPR as a disease in cattle populations.

This preliminary study provided no evidence for PPR infection of wild ruminants within northern Tanzanian ecosystems. However, wildlife are known to be susceptible to PPR (3,12), and seropositive African buffalo and antelopes have been found in other locations (15). This study had limitations that prevent us from drawing definitive conclusions about infection patterns in African wildlife: sampling was largely carried out within wildlife-protected areas where there is limited opportunity for contact with sheep and goats, and only a small number of potential wildlife hosts were sampled. Seroprevalence data from other African buffalo populations (R. Kock, pers. comm.) suggest that larger sample sizes may be required from each host population to detect seropositivity and for our conclusions to be more representative. Thus, we recommend further studies to monitor wildlife infection in populations living in closer proximity to livestock.


We thank the Tanzanian Ministry of Livestock and Fisheries Development, Tanzania National Parks, Tanzania Wildlife Research Institute, Ngorongoro Conservation Area Authority, and the Tanzania Commission for Science and Technology for permission and assistance with field activities.

Funding for this study was provided by the Biotechnology and Biological Sciences Research Council, the Department for International Development, and the Scottish Government through the Combating Infectious Diseases of Livestock for International Development initiative, which supported the collection of cattle and buffalo samples in Tanzania (project BB/H009302/1) and PPR serologic analyses at The Pirbright Institute (project BB/HH009485/1). The Messerli Foundation provided support for collection of additional buffalo and gazelle samples in Tanzania.


(1.) Abraham G, Sintayehu A, Libeau G, Albina E, Roger F, Laekemariam Y, et al. Antibody seroprevalences against peste des petits ruminants (PPR) virus in camels, cattle, goats and sheep in Ethiopia. Prev Vet Med. 2005;70:51-7. 2005.02.011

(2.) Balamurugan V, Krishnamoorthy P, Veeregowda B, Sen A, Rajak K, Bhanuprakash V, et al. Seroprevalence of Peste des petits ruminants in cattle and buffaloes from Southern Peninsular India. Trop Anim Health Prod. 2012;44:301-6. 0020-1

(3.) Gur S, Albayrak H. Seroprevalance of peste des petits ruminants (PPR) in goitered gazelle (Gazella subgutturosa subgutturosa) in Turkey. J Wildl Dis. 2010;46:673-7. 3558-46.2.673

(4.) Khalafalla AI, Saeed IK, Ali YH, Abdurrahman MB, Kwiatek O, Libeau G, et al. An outbreak of peste des petits ruminants (PPR) in camels in the Sudan. Acta Trop. 2010;116:161-5. http://dx.doi. org/10.1016/j.actatropica.2010.08.002

(5.) de Swart RL, Duprex WP, Osterhaus AD. Rinderpest eradication: lessons for measles eradication? Curr Opin Virol. 2012;2:330-4.

(6.) Republic of Kenya. Ministry of Livestock and Fisheries Development, Department of Veterinary Services. Emergency project for the control of peste des petits ruminants (PPR) in Kenya. Situation analysis and concept note. Republic of Kenya; June 2008 [cited 2013 Jun 10]. AID_EFFECTIVENESS/Donor_Sector_Groups/agriculture/ Situational_analysis_of_PPR_control.pdf

(7.) Karimuribo ED, Loomu PM, Mellau LSB, Swai ES. Retrospective study on sero-epidemiology of peste des petits ruminants before its official confirmation in northern Tanzania in 2008. Research Opinions in Animal & Veterinary Sciences. 2011;1:184-7 [cited 2013 Jun 7].

(8.) Swai ES, Kapaga A, Kivaria F, Tinuga D, Joshua G, Sanka P. Prevalence and distribution of peste des petits ruminants virus antibodies in various districts of Tanzania. Vet Res Commun. 2009;33:927-36.

(9.) Baron MD, Parida S, Oura CAL. Peste des petits ruminants: a suitable candidate for eradication? Vet Rec. 2011;169:16-21.

(10.) Mariner JC, House JA, Mebus CA, Sollod AE, Chibeu D, Jones BA, et al. Rinderpest eradication: appropriate technology and social innovations. Science. 2012;337:1309-12. science.1223805

(11.) Joint FAO/International Atomic Energy Agency Division of Nuclear Techniques in Food and Agriculture. Guidelines for the use of performance indicators in rinderpest surveillance programmes. A part of the Global Rinderpest Eradication Programme (GREP). IAEA-TECDOC-1161; 2000 [cited 2013 Jun 7]. http://www-pub.

(12.) Bao J, Wang Z, Li L, Wu X, Sang P, Wu G, et al. Detection and genetic characterization of peste des petits ruminants virus in free-living bharals (Pseudois nayaur) in Tibet, China. Res Vet Sci. 2011;90:238-40.

(13.) African Union-Interafrican Bureau for Animal Resources. The eradication of rinderpest from Africa: A great milestone. 2011 [cited 2013 Jun 3]. Eradication_of_Rinderpest_from_Africa_A_great_milestone.pdf

(14.) Mahapatra M, Parida S, Baron M, Barrett T. Matrix protein and glycoproteins F and H of peste-des-petits-ruminants virus function better as a homologous complex. J Gen Virol. 2006;87:2021-9.

(15.) Kock R. The role of wildlife in the epidemiology of rinderpest in East and Central Africa 1994-2004: a study based on serological surveillance and disease investigation [dissertation]. Cambridge (UK): University of Cambridge; 2008.

Tiziana Lembo, Christopher Oura, Satya Parida, Richard Hoare, Lorraine Frost, Robert Fyumagwa, Fredrick Kivaria, Chobi Chubwa, Richard Kock, Sarah Cleaveland, (1) and Carrie Batten (1)

Author affiliations: University of Glasgow, Glasgow, UK (T. Lembo, S. Cleaveland); School of Veterinary Medicine, The University of the West Indies at St. Augustine, Trinidad and Tobago, West Indies (C. Oura); The Pirbright Institute, Woking, UK (S. Parida, L. Frost, C. Batten); Tanzania Wildlife Research Institute, Arusha, Tanzania (R. Hoare, R. Fyumagwa); Ministry of Livestock and Fisheries Development, Dar es Salaam, Tanzania (F. Kivaria, C. Chubwa); and The Royal Veterinary College, University of London, London, UK (R. Kock).


Address for correspondence: Sarah Cleaveland, University of Glasgow, Institute of Biodiversity, Animal Health and Comparative Medicine, Graham Kerr Building, Glasgow, UK; email:

Dr Lembo is a postdoctoral research associate at the Boyd Orr Centre for Population and Ecosystem Health (Institute of Biodiversity, Animal Health and Comparative Medicine; College of Medical, Veterinary and Life Sciences), University of Glasgow. She is interested in applied infectious disease epidemiology with a specific focus on multihost pathogens in developing countries.

Table 1. Seroprevalence of peste des petits ruminants virus
antibodies in cattle and buffalo sampled in northern Tanzania

Animal, age, y                      No. positive (%)   No. sampled

Cattle *
  <1                                       0               41
  1-2                                   7 (9.0)            78
  3                                     8 (17.8            45
  4                                    12 (35.3)           34
  5                                     6 (17.6)           34
  6                                     9 (42.9)           21
  [greater than or equal to] 7          4 (33.3)           12
  Unknown                                  0                1
  Total                                46 (17.3)           266

Buffalo ([dagger])
  1                                        0                5
  2                                        0               17
  3                                        0               23
  4                                        0               10
  5                                        0               26
  6                                        0               11
  [greater than or equal to] 7             0               58
  Total                                    0               150

* Cattle in villages were sampled during 2011.

([dagger]) Syncerus caller. Buffalo in Serengeti National Park and
Ngorongoro Conservation Area were sampled during 2011-2012. Ages
were available only for a subset of buffalo.

Table 2. Number of wildlife samples from northern Tanzania tested
for peste des petits ruminants virus antibodies in northern
Tanzania, 2008-2012

                                           No. sampled per year

Ecosystem, species                      2008      2008      2010

Arusha, buffalo *                         0         0         0
Katavi, buffalo *                         0         0        23
Ngorongoro Conservation Area
  Buffalo *                               0         0         0
  Thomson's gazeiie ([dagger])            8         0         0
  Grant's gazeiie ([double dagger])       6         0         0
  Buffalo *                               2         3        14
  Thomson's gazeiie ([dagger])            7         0         2
Tarangire, buffalo *                      0         0         0
Total                                    23         3        39

                                         No. sampled
                                           per year         Total
Ecosystem, species                      2011      2012     sampled

Arusha, buffalo *                         0        24        24
Katavi, buffalo *                         0         0        23
Ngorongoro Conservation Area
  Buffalo *                              48        95        143
  Thomson's gazeiie ([dagger])            0        19        27
  Grant's gazeiie ([double dagger])       0         0         6
  Buffalo *                              22        10        51
  Thomson's gazeiie ([dagger])            0        23        32
Tarangire, buffalo *                     25         0        25
Total                                    95        171       331

* Syncerus caller.

([dagger]) Eudorcas thomsonii.

([double dagger]) Nanger granti.
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Article Details
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Title Annotation:DISPATCHES
Author:Lembo, Tiziana; Oura, Christopher; Parida, Satya; Hoare, Richard; Frost, Lorraine; Fyumagwa, Robert;
Publication:Emerging Infectious Diseases
Article Type:Report
Geographic Code:6TANZ
Date:Dec 1, 2013
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