key: cord-0000564-daheoyro
authors: Friberg, Ida M.; Lowe, Ann; Ralli, Catriona; Bradley, Janette E.; Jackson, Joseph A.
title: Temporal Anomalies in Immunological Gene Expression in a Time Series of Wild Mice: Signature of an Epidemic?
date: 2011-05-23
journal: PLoS One
DOI: 10.1371/journal.pone.0020070
sha: aec923adf0e16d218315a3083aaa71fb9ddb8b39
doc_id: 564
cord_uid: daheoyro

Although the ecological importance of coinfection is increasingly recognized, analyses of microbial pathogen dynamics in wildlife usually focus on an ad hoc subset of the species present due to technological limitations on detection. Here we demonstrate the use of expression profiles for immunological genes (pattern recognition receptors, cytokines and transcription factors) as a means to identify, without preconception, the likelihood of important acute microbial infections in wildlife. Using a wood mouse population in the UK as a model we identified significant temporal clusters of individuals with extreme expression of immunological mediators across multiple loci, typical of an acute microbial infection. These clusters were circumstantially associated with demographic perturbation in the summertime wood mouse population. Animals in one cluster also had significantly higher individual macroparasite burdens than contemporaries with “normal” expression patterns. If the extreme transcriptional profiles observed are induced by an infectious agent then this implicates macroparasites as a possible player in mediating individual susceptibility or resilience to infection. The form of survey described here, combined with next generation nucleic acids sequencing methods for the broad detection of microbial infectious agents in individuals with anomalous immunological transcriptional profiles, could be a powerful tool for revealing unrecognized, ecologically important infectious agents circulating in wildlife populations.

The role of infectious agents in the dynamics of natural vertebrate populations has been a growing interest for ecologists. Endemic infections have been shown to have important effects on survival [1, 2] and reproduction [3, 4, 5, 6, 7] and the theoretical potential to regulate populations and drive abundance cycles [8, 9] . At the same time there are many documented instances of epidemics associated with catastrophic mortality in nature [10, 11, 12] , although the observation of such events may often be serendipitous or depend on the focus of the researcher. Increasingly it is also appreciated that co-occurring pathogens should be regarded as a potential community [13, 14] , whose interactions may define the consequences of infection for the individual host and host population [15] . In general, however, ecological studies of microbial infectious disease in nature are constrained to the analysis of a single pathogen or an ad hoc panel of pathogens for which there is a priori knowledge, a preconception of possible importance and specific diagnostic reagents.

An alternative is to focus on non-pathogen-specific aspects of the host's immune response [16] , detecting the presence of significant microbial infections through perturbations caused in the expression of immunological genes in the host [17] . In the present study we present an example of such an approach, revealing spatio-temporal patterns of immunological expression in a summertime wood mouse population in the UK that may point to epidemic infections with an unknown microbial infectious agent.

We sampled wood mice (Apodemus sylvaticus) on 12 occasions through May-December 2008 at Cotgrave Forest (+52.891, 21.041242) a ,135 ha area of coniferous and mixed forestry plantation in Nottinghamshire, UK (total n = 141). Mice were caught by overnight live-trapping using Longworth traps. The traps were placed at permanently marked stations located at 20 m intervals (1 trap/station) along a 1600 m curvilinear transect that traced the margins of contiguous forestry blocks. These blocks were separated along their edges by narrow clear areas ,10-40 m wide. The use of an extended trapping line was intended to distribute trapping effort over a very large area and avoid local demographic effects. Traps were set in the afternoon (16.00 h BST) and collected the following morning (08.00 h) throughout the study period. Females that were lactating or heavily pregnant at the time of capture were released. At the last two sampling points, where numbers of mice captured exceeded the capacity to process them, some randomly selected individuals were also released. Other individuals were processed and infection variables quantified as previously described [18] . This was with the exception that in the present study lice were recorded in different infection categories (absent, ,50 egg cases present, $50 egg cases present). Additionally, in the present study, thin blood smears were prepared from cardiac blood and examined for the presence of Bartonella spp. and Babesia microti (counts of infected cells in one hundred 1006 microscope fields). Eyes from each specimen were stored in 4% formalin and then lenses were removed and dried in an oven at 80uC for 72 h and weighed for use as an index of age (combined weight, g) [19] . In the present study the same set of macroparasites was found as in a previous study along the same transect in 2007 [18] , with the exception that Heterakis spumosa was absent.

Use of animals in the present study complied with relevant UK legislation. Mice were killed by a listed competent person using a Home Office approved method as detailed in schedule 1 of the Animal (Scientific Procedures) Act 1986 (ASPA). In consultation with the Home Office ASPA inspectorate, the work was not considered to involve any scientific procedures on living animals (merely housing for a short period before killing [18] ) and was therefore not subject to regulation by ASPA.

For each mouse we established five sets of splenocyte cultures. One of these was left unstimulated, to provide ''constitutive'' measurements and three others were respectively stimulated with agonists for toll-like receptor (TLR) 2, TLR4 and TLR9, which are receptors involved in the innate recognition of, and the triggering of immune responses against, invading microorganisms [20] . Cells and supernatants harvested from these cultures at 24 h were used to measure mRNA and protein expression of the proinflammatory cytokine tumour necrosis factor alpha (TNF-a) [18, 21] , mRNA expression of TLR2, TLR4 and TLR9, and mRNA expression of TGF-b1 and IL-10, which are antiinflammatory cytokines involved in the regulation of immune responses [22, 23, 24] . In the unstimulated cultures alone we measured mRNA expression of FoxP3, a transcription factor associated with the anti-inflammatory regulatory T-helper cell (T reg ) subset [25, 26] . TNF-a protein expression was also measured in 96 h supernatants from a further set of cultures stimulated with Heligmosomoides bakeri somatic antigen (HbAg).

Spleens were disaggregated through a 70 mm cell strainer into RPMI 1640. Following erythrocytic lysis (Sigma R7757), leucocytes were washed three times in RPMI 1640 and then cultured (37uC, 5% CO 2 ) on 96 well plates at 2610 6 cells/ml in RPMI 1640 supplemented with 24 mM Na HCO 3 , 10% heat inactivated foetal calf serum, 2 mM L-glutamine, 100 u/ml penicillin, 100 mg/ml streptomycin and 60 mM monothioglycerol. Triplicate sets of individual cultures (150 ml volume) were assigned to each experimental condition. Three cultures sets were stimulated with different TLR agonists: heat-killed endotoxin-free Listeria monocytogenes (TLR2 agonist) at 0.6610 8 cells/ml, or a 50:50 mix of Ultrapure Escherichia coli K12 lipopolysaccharide and Ultrapure Salmonella minnesota lipopolysaccharide (TLR4 agonists) at 3 mg/ml, or oligonucleotide ODN2006 (TLR9 agonist) at 6 mg/ml. All TLR agonist reagents utilized were tested for functional induction of the target TLR and for endotoxin contamination by the manufacturer (InvivoGen) and were used at concentrations previously determined to be optimal [18] . Further culture sets were stimulated with HbAg antigen at 50 mg/ml (pretreated with 500 U/ml polymyxin B for 4 h at 4uC) or left unstimulated. Culture supernatants and cells were harvested after 24 h for the unstimulated and TLR cultures and after 96 h for the HbAg cultures. Supernatants were immediately stored at 280uC and cells were placed overnight at 4uC in RNAlaterH (Ambion) and then stored at 280uC.

Accumulated TNF-a protein was measured in 24 h culture supernatants by ELISA (R&D, DY410) as previously described [18] , except that all samples were analysed in triplicate wells.

Relative mRNA accumulations in cells harvested at 24 h were measured by two-step reverse transcription quantitative real-time PCR (Q-PCR) using SYBR Green chemistry. Total RNA was extracted from cells stored in RNAlaterH using an Ambion RNAqueousH-Micro kit (AM1931) and converted to cDNA using an Applied Biosystems High capacity RNA-to-cDNA kit (4387406). All samples were DNase-treated and periodic controls lacking a reverse transcriptase enzymatic step indicated that DNA contamination was negligible. Real-time PCR primers for the cytokines, transcription factor and endogenous control genes were designed from conserved regions identified in multiple alignments of rodent sequences in the NCBI database. For TLR genes de novo amplification and sequencing of a larger (300-500 bp) fragment was first carried out using conserved primers (designed as above). Real-time PCR primers were then designed from the resulting Apodemus sylvaticus TLR sequence. All primers were designed with Primer 3 v. 0.4.0. For each target and endogenous control gene 2-6 primer pairs were designed and trialled and the optimal set selected for further use. All selected primers (Table 1) were confirmed to be specific by re-sequencing of the target fragment, did not produce confounding primer dimers under assay conditions and had approximately equal efficiencies close to 100%, based on the average of 5-fold dilution series repeated on multiple different plates. Target genes were normalized against the endogenous control gene b-actin. This was the most stable endogenous control gene amongst a set of 9 candidates considered (including c-actin, G6PDH, GAPDH, HPRT1, Tubulin, YWHAZ, 18 s and Albumin) as determined by stepwise exclusion of those with low stability estimated by the M statistic [27] . This procedure was conducted separately for 10 LPS-, HKLM-or ODN 2006-stimulated cultures randomly selected out of a pool of 300 culture samples. In all three cases b-actin was identified as the joint most stably expressed gene. The primers used for b-actin were sense 59-AGATCAAGATCATTGCTCCTCCT -39 and antisense 59-TCCTGCTTGCTGATCCACATC -39 which gave a 102 bp amplicon. The 96-well real-time PCR assay was designed so that all target genes for one animal were run on a single plate, except for Foxp3 amplifications which were all run on a separate plate. Each target gene reaction and the endogenous control gene reaction were run in duplicate for samples and in triplicate for a reference cDNA that was included on each plate. A no-templatecontrol was included in duplicate for each primer pair. Real-time PCR assays were run using default settings and the manufacturerrecommended enzyme, buffer and SYBR Green reagents on an ABI 7500 Fast machine (Applied Biosystems). ABI 7500 v 2.0.4 software was used to calculate the expression of each target in each sample as a fold difference relative to the reference cDNA by the DDCt method [28] .

In total 30 immunological expression values were measured per individual. Initial examination of the data indicated a small number of individuals in which most or all of the readings were extremely high. In order to characterize this group each variable was log transformed (log10 [x+1]) and standardized ([x2mean]/ standard deviation) and then outlying observations in each variable were determined as those occurring .1.56 the interquartile range above the third data quartile. Individual mice with $10 such outlying values were classified as part of an ''extreme expression'' group. Examining the subset of 22 variables in which there were few missing values and considering animals with a full set of observations for these, we also used hierarchical cluster analysis (HCA) (average link) and ordinations against the principal axes derived from principal co-ordinates analysis (PCO) and principal components analysis (PCA) to assess the distribution of individuals in phenotypic space. Data were log-transformed and standardized prior to HCA and PCO and log-transformed prior to PCA on the correlation matrix.

To analyze clustering in the occurrence of ''extreme expression'' status we coded extreme (1) vs non-extreme (0) expression as a binary variable and carried out retrospective spatial, temporal and spatio-temporal scans [29] with the software SaTScan TM v9.1.0, specifying a Bernoulli model. Following identification of a most significant cluster, subsequent clusters were identified by adjusting for the presence of more significant clusters.

Variations in the macroparasite community were summarised by a PCA of individual parasite variables on the correlation matrix [18] . This was based on data for the common macroparasite species at Cotgrave Forest [18] : Skrjabinotaenia lobata, Brachylaemus recurvum, Calodium hepaticum, Syphacia nigeriana, Heligmosomoides polygyrus, Ixodes ricinus, laelapid mites and Polyplax serrata. As the PCA of macroparasite variables produced a significant (P,0.001) first component with coefficients of the same sign for most species, scores for this component (PC1 P ) were taken as an overall indicator of macroparasite infection.

An estimator of body condition was produced by taking residuals (BW resid ) from a regression of body weight (BW) on SVL, incorporating different slopes for males and females and quadratic terms to allow for a curvilinear association.

We used variations in trapping catch rate as a measure of demographic fluctuation in the host population as this rate would be expected to reflect either changes in population density or changes in spatial behaviour that relate, in some way, to the condition of individuals. Initial pairwise comparisons between trap success on different sampling occasions were based on contingency table analysis (Fisher exact tests). Overall variation in capture rates was then analysed by a linear mixed model (LMM) allowing for correlation between successive trapping intervals (AR1 covariance model).

Variations in body condition and PC1 P were assessed with general linear models (LMs) initially including terms for cluster membership, body size (SVL) and host stage (classified as in Jackson et al. [18] ), with deletion of non-significant terms. For analyses of individual macroparasite species, LMs with normal errors or equivalent generalized linear models (GLMs) with Poisson errors or negative binomial errors were used as appropriate (again with deletion of non-significant terms). A Poisson distribution was used as a surrogate distribution in the case of ordinal data for P. serrata. In the case of negative binomial errors, the dispersion parameter k was estimated from that of the entire host population and any significant results reported are also consistent with an analysis of log-transformed data in an LM.

We analysed splenocyte expression of immunological genes (TLR2, TLR4, TLR9, TNF-a, TGF-b1, IL-10, FoxP3) in a time series of A. sylvaticus at Cotgrave Forest, UK from May to December 2008. Preliminary analyses of individual variation indicated that a small proportion of individuals were associated with very extreme expression values for most or all of the measurements taken (Figure 1 ). In order to categorize this variation we initially identified outlier values in log-transformed, standardized data as occurring above the third data quartile cutoff by more than 1.56 the interquartile range. Individuals with .10 outlier readings from the 30 variables measured were considered as an ''extreme expression'' group ( Figure 2) . The individual composition of this group was broadly supported by HCA, PCA and PCO for the subset of 22 expression variables without missing data values (Figure 3) .

It was not possible to identify a candidate infectious aetiological agent for the extreme immunological expression syndrome described above amongst the microparasites (Eimeria spp., Babesia microti and Bartonella spp.) and macroparasites whose presence we 

We categorized individuals into ''extreme'' and ''normal'' expression groups (as above) and scanned for temporal clusters of extreme expression using a Bernoulli model in the programme SaTScan TM . A significant temporal cluster (cluster 1) was detected in late June 2008 (log likelihood ratio = 20.37, P = 0.001). Adjusting for the occurrence of the most significant cluster, a significant secondary temporal cluster (cluster 2) occurred in early September 2008 (log likelihood ratio = 13.10, P = 0.001). Analyses for spatial clusters and spatial-temporal clusters failed to detect any purely spatial clustering, but did find two significant space-time clusters (P = 0.014) within the time frame of the most significant temporal cluster. The areas included and not included in these clusters appeared to broadly correspond to distinct forestry blocks.

Against a background of apparent demographic increase during May-December 2008, significant decreases in trapping rate with respect the immediately preceding trapping occasions (either 1 or 2 intervals distant) were only recorded immediately after the detection of extreme expression clusters (Figure 2 ). LMM analysis of trapping success data against time (days), allowing for positive autocorrelation between successive trapping sessions, suggested a highly significant increasing trend across May to December (LMM, P,0.001; parameter estimate = 0.0013060.00035 catch rate day 21 ). A 2-level factor coding the two time intervals following the first detection of each extreme expression cluster (vs Using eye lens weight as an index of age, plots of lens weight with respect to time allowed unambiguous identification of overwintered (1 + ) and young-of-the-year (0 + ) cohorts in 2008 and also in a retrospective analysis of animals sampled at Cotgrave Forest by Jackson et al. [18] in 2007 ( Figure 4 ). Cohort dynamics differed in 2008 compared to 2007 by an abrupt earlier disappearance of 1 + animals, in late June, that was followed by a very large proportional contribution to the population by new recruits (0 + individuals with the lightest eye lenses, ,0.014 g) (Figure 4 ).

Although a small number of divergent individuals occurred within cluster 1 (Figure 3 ), significant overall variation in expression patterns occurred between cluster 1 and cluster 2 ( Figure 5 ). Most individuals in cluster 1 could be characterized by comparatively very elevated constitutive and LPS-stimulated TNF-a expression. Individuals in cluster 2 were characterized by relatively high levels of constitutive and LPS-stimulated expression of TLR4, TLR9 and FoxP3.

A comparison of contemporaneous cluster 1 and non-cluster animals was not possible (insufficient individuals occurred in the same time intervals) but cluster 2 individuals had significantly greater body condition (BW resid ) (LM, P = 0.036) and grouped macroparasite infection (PC1 p ) (LM, P = 0.048) than non-cluster individuals from the same sampling points ( Figure 6 ). For individual macroparasite species, there were significantly greater infections in cluster 2 animals for the louse, P. serrata (GLM, Poisson errors, P = 0.048) and the catenotaeniid cestode, S. lobata (GLM, negative binomial errors, P = 0.035).

The analysis of immunological expression profiles may provide an unbiased strategy for identifying important microbial infection pressures acting on a natural population. In this study we attempted to demonstrate such an approach using a time series of wood mice from a habitat in the east midlands, UK.

Acute infections with highly pathogenic viruses, bacteria or protozoa are often associated with extreme expression of cytokines and TLRs [30, 31, 32, 33] . We discovered significant temporal clusters of individuals with extreme expression of immunologicallyrelevant genes, including cytokines and TLRs, in late June (cluster 1) and early September 2008 (cluster 2). This is consistent with the presence of an acute, highly immunogenic microbial infection in the mouse population at these times. Other possible causes for the ''extreme expression'' clusters are considered less likely. Thus, autoimmunity, allergy or malignancy not involving infection does not well explain the clustered temporal epidemiological pattern and poisoning is unlikely because the habitat is managed for pheasant shooting (pheasants would be likely to take poisoned bait placed for rodents) . The pattern seen is also difficult to attribute to handling stress or to ontogenetic or genetic variation. Compared to the non-cluster animals in the present study and to hundreds of other ''normal'' wild rodents (A. sylvaticus and Microtus agrestis) recently analysed in our laboratory in a similar way [16, 18] , the relative mRNA expression ratios for immunological genes and the amount of constitutive TNF-a protein secretion in some cluster animals are unprecedentedly high. The variation in expression between cluster and non-cluster animals also seems to be much greater than constitutive variation in expression reported amongst wild-derived Mus inbred laboratory lines [34, 35] .

The occurrence of the clusters in time was circumstantially associated with significant reductions in A. sylvaticus trapping rate that were contrary to a prevailing trend of demographic increase during the period of study. An additional, circumstantial, corollary was that an abrupt turnover between 1 + and 0 + A. sylvaticus cohorts occurred in the weeks following cluster 1, consistent with a perturbation affecting the population at this time. Over an equivalent time interval in the preceding year (2007), clusters of individuals with extreme TNF-a protein expression did not occur ( [18] ; unpublished data) and the turnover between 1 + and 0 + cohorts proceeded much more gradually (Figure 4) .

Whilst the identity of any putative aetiological pathogen(s) is unknown, the two ''epidemic'' clusters differed in the nature of the immune responses observed. Members of both clusters expressed high levels of all immunological genes studied, but cluster 1 was characterized by relatively higher expression of TNF-a at the protein and mRNA level and cluster 2 by higher expression of TLR4 and TLR9 and the regulatory T-helper cell-associated transcription factor FoxP3. These differences may be indicative of more than one infectious agent stimulating different immune responses. Alternatively, different immune responses to the same pathogen may have occurred because the animals involved in the respective clusters were themselves different. Cluster 1 individuals were exclusively over-wintered (1 + ) animals, whilst cluster 2 animals were exclusively young-of-the-year (0 + ) individuals. Phenotypic differences might therefore have arisen from ontogenetic stage variation, or from a different history of programming by environmental cues in the respective cohorts. A further possibility is that animals in the second cluster might have had some level of acquired immunity, following the outbreak earlier in the year, and produced more highly regulated responses indicative of a degree of immunological tolerance. This latter possibility is supported by the fact that some atypical individuals occurred in cluster 1 that were either phenotypically intermediate, or, more similar to cluster 2 individuals (Figure 3 ).

Given the highly focussed temporal occurrence of the clusters (appearing and disappearing over the timescale of a few weeks), it might be inferred that if a putative infectious agent is involved this is highly transmissible and produces acute infections that rapidly result in death or recovery and the development of resistance. It is likely such a pathogen could only be maintained by rapid spatial movement through the wider population, via locally unstable dynamics, or by inactive latent infections in some hosts acting as a reservoir and intermittent source of infection through time. One possibility consistent with some of these considerations is cowpox virus, infections with which can show fine-scale temporal clustering in wood mouse populations [36] . However, cowpox virus is known to suppress TNF-a responses [37] , which were expressed at very high levels in cluster 1 mice. Furthermore, field studies of cowpox in UK wild rodents [38, 39] generally indicate that infection levels within populations persist with a much coarser temporal grain than was the case for the tightly focussed episodes of infection recorded here.

A further interesting characteristic of the second cluster is that cluster members, controlling for life history stage and size, showed significantly better body condition and greater macroparasite infection than non-cluster individuals from the same time interval. This indicates that healthier individuals with more macroparasites might either be more susceptible to any putative infection or more resilient to the effects of infection. Increased susceptibility could arise because individuals in better condition eat more and range farther, exposing themselves to greater infection risks from macroparasites and microbial infections. Macroparasites might also contribute to susceptibility due to their anti-inflammatory activities [18] . Increased resilience could occur because animals in better starting condition might be more likely to survive infection, thus raising their representation in infected classes by differential mortality. The immunoregulatory influence of macroparasites might also be important in this context: dampening potentially lethal immunopathogenic inflammatory responses. A further possibility is that individual mice respond to infection by adjusting life history traits in a way that produces an overcompensatory response in body condition. For example, A. sylvaticus infected with cowpox virus in summer may show positive effects on survival due to a diversion of resources from reproduction [3] .

We have shown here that very distinct anomalies in immunological gene expression patterns can be detected in wild mammal populations if these are surveyed over time. We suggest that such patterns will often be caused by infectious agents and can be used to monitor important infection influences operating on a natural host population. The general approach used here is technically accessible to a wide range of researchers. An obvious extension would also be to combine the present methods with next generation sequencing techniques for the broad detection of microbial pathogens [40, 41] in animals with anomalous immunological transcriptional profiles compared to ''normal'' animals. In the present example, we focussed on a population of wood mice and were able to detect the probable signatures of epidemic infectious disease outbreaks and their demographic and individual correlates. Given the long standing interest in the dynamics of A. sylvaticus populations in the UK [42, 43, 44, 45] , in particular the apparent slow growth during the earlier part of the breeding season, this study might point towards a possible, destabilizing, role for microbial infectious disease in addition to the factors identified by other authors. There is also a wider significance for the ability of ecologists to analyze the dynamic interaction between pathogen communities and their wildlife hosts and, particularly, to identify unsuspected acute microbial infectious disease outbreaks, whose effects might otherwise be dismissed as generalized environmental noise.

We are very grateful to Till Hill Ltd for allowing access to the study site. . Differences in body condition and macroparasite burden between cluster 2 and non-cluster animals captured at the same time. A. Cluster 2 animals (dark bar) had significantly better body condition (BW resid ) than non-cluster animals, adjusting for size and stage. B. Cluster 2 animals (dark bar) had greater grouped macroparasite burdens (PC1 P ) than non-cluster animals, adjusting for size and stage. PC1 P represents first principal component scores from a principal components analysis of common macroparasite species at Cotgrave Forest. This principal component accounted for 23% of total variation and showed high loadings of the same sign for most species. It was thus taken to represent the major pattern of positive covariation within the assemblage. Variable coefficients on PC1 P were: Skrjabinotaenia lobata 0.25, Brachylaemus recurvum 0.28, Calodium hepaticum 0.24, Syphacia nigeriana 0.52, Heligmosomoides polygyrus 0.50, Ixodes ricinus 20.040, laelapid mites 0.102, Polyplax serrata 0.52. There were individually significant associations with cluster 2 membership, in the same direction as PC1 P , for P. serrata and S. lobata, adjusting for host size and stage. doi:10.1371/journal.pone.0020070.g006

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