Abstract
Objectives
Cats are susceptible to highly pathogenic avian influenza H5 clade 2.3.4.4 (HPAI H5) and human new pandemic H1N1 (H1N1pdm09) influenza A viruses. A simultaneous infection with multiple influenza A virus subtypes could potentially result in the generation of reassortant viruses with enhanced zoonotic potential. Previously, high seropositivity (11.8%) to HPAI H5 virus has been detected in rural stray cats in the Netherlands, presumably through contact with or feeding on infected birds. Seropositivity was much lower (0.46%) in concurrently sampled domestic cats with unknown outdoor access, which were frequently (4.6%) seropositive to H1N1pdm09 virus. As outdoor access is expected to increase the risk of HPAI H5 exposure, in this study we determined seropositivity to HPAI H5 as well as H1N1pdm09 in domestic cats with known outdoor access.
Methods
In 2024, sera from 254 outdoor cats were collected and screened for antibodies to HPAI H5 and H1N1pdm09 virus using in-house developed ELISAs and haemagglutination inhibition assays (HAIs).
Results
Antibodies to HPAI H5 virus were detected in seven (2.8%) cat sera (95% confidence interval [CI] 1.1–5.6) by ELISA, but not by HAI. Antibodies to H1N1pdm09 were detected in 14 (5.5%) sera (95% CI 3.1–9.1), of which seven (2.8%) were positive by HAI (95% CI 1.1–5.6). Two sera (0.79%) reacted in ELISA to both HPAI H5 and H1N1pdm09 (95% CI 0.1–2.8).
Conclusions and relevance
Antibodies to both HPAI H5 and H1N1pdm09 viruses were detected in outdoor domestic cats, with a higher seroprevalence for H1N1pdm09. Seropositivity for HPAI H5 was higher than was previously detected in domestic cats with unknown outdoor access, but lower than in stray cats. This warrants further investigation into the potential role of outdoor domestic cats as mixing vessels and as a source of (novel) zoonotic viruses.
Introduction
Highly pathogenic avian influenza H5 clade 2.3.4.4 viruses (referred to as HPAI H5) have been enzootic among wild birds worldwide, including the Netherlands, since 2020.1 –4 These avian-origin influenza A viruses (IAVs) have spilled over to carnivores,5 –7 including domestic cats.8 –14 In cats, HPAI H5 virus exposure may have occurred through direct and/or indirect (ie, contaminated faeces or feathers 15 ) contact with infected birds,8,13,16 –19 but also through consumption of contaminated raw meat or petfood10,12,20,21 or, in the USA, contaminated raw milk.22,23 The increasing number of HPAI H5-infected cats in the USA since 2022, 24 where cat-to-cat, 25 cat-to-human 26 and human-to-cat 27 transmission may have occurred, emphasises the importance of cats as hosts and sentinels of HPAI H5 viruses. Domestic cats can also be infected with currently circulating human pandemic H1N1 (H1N1pdm09) IAVs.28 –32
Although experimental HPAI H5 virus infection of cats resulted in clinical signs and death,33 –36 the detection of antibodies against HPAI H5 and H1N1pdm09 in apparently healthy domestic cats indicated that exposure of cats to IAVs may remain clinically unnoticed.11,14,16,18,37 Cat-to-cat transmission of both these viruses has been experimentally demonstrated,31,33,35 while transmission was suspected but not confirmed under natural conditions. 27 (Co)infection of cats with HPAI H5 and H1N1pdm09 viruses might result in the generation of novel viruses with zoonotic potential, through reassortment and/or adaptation. Reassorted viruses containing segments from different avian viruses have been isolated from cats,38 –40 including a triple reassortant H3N8 IAV that was simultaneously detected in a child from the same household, suggesting cross-species zoonotic transmission. 39
Previous studies in the Netherlands showed that shelter cats (consisting of 86.4% ex-stray cats) sampled in 2016, and rural living stray cats (either owned cats gone astray, community cats or feral cats, as described previously 41 ) sampled between 2020 and 2023, were more frequently HPAI H5 seropositive (7.3% and 11.8%, respectively) than domestic (owned) cats with unknown outdoor access sampled in 2019 or between 2020 and 2023 (1.5% and 0.46%, respectively).11,37 Antibodies to H1N1pdm09 virus were common (15.3% and 4.6%, respectively) in domestic cat cohorts.11,37 Of note, in these studies, ELISAs based on recombinant hemagglutinin (HA) protein were used, which were shown to be more sensitive for detection IAV antibodies in cat sera than an ELISA based on the IAV nucleoprotein 37 or than haemagglutination inhibition assays (HAIs),11,37 in agreement with other studies.42,43
Based on their lifestyle, domestic cats with outdoor access may be at higher risk for exposure to HPAI H5 through infected wild birds than indoor cats, while they are also at risk for H1N1pdm09 through infected caretakers.11,28,37 Outdoor domestic cats may therefore not only be a source of HPAI H5 (or H1N1pdm09) viruses to humans, but potentially also of novel zoonotic viruses resulting from reassortment after coinfection. The aim of the current study was to gain more insight into the exposure of domestic cats with known outdoor access in the Netherlands to both these viruses. We therefore determined the presence of HPAI H5 and H1N1pdm09 antibodies and compared the seroreactivity of the cohort sampled in this study with that of domestic cats and stray cats sampled previously, which we hypothesise to have lower and higher seroreactivity to HPAI H5, respectively.
Materials and methods
Sample collection
After obtaining owner-informed consent, 24 veterinary practices submitted surplus serum samples from domestic cats. The large majority of these samples (n = 254) were from cats with outdoor access (outdoor cats), while a limited number (n = 33) came from indoor cats. None of the cats sampled were fed raw meat. We initially planned to only include outdoor cats in the study; however, during the sampling phase we received indoor cat samples, so we included this indoor cat cohort as a control group in the study (Table 1). Outdoor cats had access to a garden or non-confined outdoor area. Indoor cats lived strictly indoors, or had access to an outdoor enclosure or balcony, but were restricted in direct bird contact. Data on cats’ age, sex and postal code of the home address accompanied the samples.
Sample description of collected domestic cat sera
Data are mean (median [interquartile range]) unless otherwise indicated
Antibody detection by ELISA and HAI
All cat sera were analysed simultaneously in three in-house developed ELISAs, as described previously, 11 based on the HA protein of HPAI H5N8 clade 2.3.4.4 virus (A/Chicken/NL/14015526/2014,11,37 referred to as HPAI H5), low pathogenic avian influenza (LPAI) H5N2 virus (A/Common Teal/NL/4/2022, 11 referred to as LPAI H5) and human H1N1pdm09 IAV (A/California/04/2009, referred to as H1).11,37 The ELISA cut-off (five times the optical density [OD] value measured at 450 nm of a negative specific pathogen free cat serum) was calculated per assay, and the ELISA results were depicted as OD ratios (OD value:cut-off). Specific binding of a single serum sample that reacted positively in all three ELISAs was confirmed by lack of binding above the cut-off to an uncoated but blocked well. Sera positive in at least one of the ELISAs, and 24 randomly selected ELISA-negative sera, were analysed in HAIs. In the HAIs, the same HA proteins used in the ELISAs were coupled to mi3 nanoparticles, as described previously.11,37
Data analysis
Data analysis and visualisation was conducted using SPSS version 28.0 (IBM), GraphPadPrism version 10 (GraphPad Software) and Datawrapper (https://www.datawrapper.de). To calculate seroproportions with confidence intervals (CIs), the exact binominal test was used. The association of age and sex with HPAI H5 or H1 seropositivity was explored in a univariable analysis using the χ2 or Fisher’s exact test (when expected count <5), and odds ratios with 95% CIs were calculated. A P value <0.05 was considered statistically significant. The indoor cat cohort was excluded from detailed statistical analyses owing to the low sample size.
Reuse of data
The seroreactivity and seroprevalence of the samples analysed in this study were compared with those of cohorts of domestic cats with unknown outdoor access and stray cats obtained previously (2020–2023) by us and that were analysed using the same HPAI H5 and H1 proteins and ELISA and HAI methodology as in the current study. 11 Global Initiative on Sharing All Influenza Data (GISAID) EpiFLu (https://gisaid.org, accessed on 5 March 2025) and European Food Safety Authority (EFSA; https://hpai.efsa.aus.vet, accessed on 12 December 2024) databases were used to obtain data on the presence of HPAI clade 2.3.4.4-infected wild birds in the Netherlands. 44 All data were reused with permission when applicable.
Results
Sample collection
Sera from 254 outdoor cats and 33 indoor cats (total n = 287 cats) were collected between January and September 2024 (mean number of samples per veterinary practice 11; median 17 [range 2–55]). Targeted sampling was performed for areas where previously HPAI H5 seropositive stray cats had been detected, 11 resulting in clustering of samples in the north and centre of the Netherlands (Figure 1a,b).

Geographic distribution of sampled domestic cats in the Netherlands, 2024: (a) 253/254 sampled outdoor cats and (b) 33 indoor cats. Circles correspond to home addresses of individual cat owners based on the four digits of the postal code. Red and yellow circles indicate positive and negative reactivity in the highly pathogenic avian influenza (HPAI) H5 ELISA, respectively. Municipalities and provinces are indicated by light and dark grey lines respectively (www.cbs.nl)
Seroreactivity
Seropositivity to HPAI H5 in ELISA was detected in 7/254 (2.8%) outdoor cat sera (95% CI 1.1–5.6) (Figure 2a,c) but not in HPAI H5-HAI (Figure 2d). Reactivity to LPAI H5 in ELISA was detected in 4/254 (1.6%) sera (95% CI 0.43–4.0), but not in LPAI H5-HAI. Reactivity to H1 in ELISA was detected in 14/254 (5.5%) sera (95% CI 3.1–9.1), of which seven (50.0%) were positive in H1-HAI (2.8%; 95% CI 1.1–5.6). Two outdoor cat sera reacted positively to both HPAI H5 and H1 in ELISA, with similar OD ratios (0.79%, 95% CI 0.1–2.8). Of 33 indoor cat sera, two (6.1%; 95% CI 0.74–20.2) displayed low reactivity to the HPAI H5 ELISA (Figure 2b) but not in HPAI H5-HAI. Two other indoor cat sera (6.1%; 95% CI 0.74–20.2) reacted positive in ELISA to H1, one of which was also positive in the H1-HAI (Figure 2d).

Reactivity in cat sera to influenza A viruses. Reactivity of serum samples from (a) 254 outdoor cats and (b) 33 indoor cats in ELISAs depicted as dot plots. The dotted line indicates the cut-off (ELISA optical density [OD] ratio = 1). Heatmaps of (c) ELISA and (d) haemagglutination inhibition assay (HAI) reactivity from 21 outdoor cats and four indoor cats positive for antibodies to highly pathogenic avian influenza (HPAI) H5 and/or low pathogenic avian influenza (LPAI) H5 and/or H1 in ELISA. The outdoor and indoor cat samples are presented above and below the black horizontal bar, respectively. The blue colour intensity corresponds with ELISA or HAI-binding reactivity of the sera based on OD ratio or HAI titre as indicated. The white colour depicts reactivity below the cut-off. HA = haemagglutinin protein
In our previous study, 11 although 79.3% of HPAI H5 ELISA positive stray cat sera were positive in HAI, none of the HPAI H5 ELISA positive cat sera in this study were positive in HAI. We therefore analysed the degree of seroreactivity of seropositive outdoor cats from this study and compared this with that of stray cats and domestic cats analysed previously using the same assays 11 and that were either HAI positive or negative (Figure 3). The range of HPAI H5 ELISA OD ratios of the positive outdoor cat sera observed in this study was comparable to ELISA-positive but HAI-negative stray cat sera, and was lower than stray cat sera that were both ELISA and HAI positive, and higher than domestic cat sera that were ELISA positive and HAI negative (Figure 3). We conclude that the absence of detectable HAI titres in the outdoor cat sera in this study can be explained by low antibody levels combined with a lower sensitivity of the HAI compared with the ELISA.11,37

Seroreactivity analysis of highly pathogenic avian influenza H5 ELISA-seropositive and haemagglutination inhibition assay (HAI)-negative cats. Optical density (OD) ratios of ELISA-positive, HAI-negative outdoor domestic cat sera (n = 7) were plotted. For comparison, similar ratios from ELISA-positive, HAI-negative (n = 4) domestic cat sera, ELISA-positive and HAI-positive (n = 66) and ELISA-positive, HAI-negative (n = 19) stray cat sera obtained using similar methods 11 are also plotted. The reactivity is depicted as dot plots and boxplots. The HAI cut-off was set at titre 40
Age and sex do not associate with HPAI H5 or H1 ELISA seropositivity in outdoor cats
Previously, we found that HPAI H5 seropositivity was significantly higher in stray cats aged 3 years or older compared with younger cats. 11 Age and sex were, however, not significantly associated with HPAI H5 or H1 ELISA seropositivity in the outdoor domestic cats analysed in this study (Table 2).
Associations of age and sex with seropositivity to highly pathogenic avian influenza (HPAI) H5 virus or human H1 virus in outdoor cats
Data are n (%) unless otherwise indicated
Age was unavailable for one cat
Firth correction applied to correct for categories with zero events
CI = confidence interval; OR = odds ratio; Ref = reference category
Discussion
We analysed HPAI H5 and H1N1pdm09 ELISA seropositivity in domestic cats with outdoor access. The proportion of HPAI H5-seropositive outdoor cats (2.8%) found in this study was higher than of domestic cats with unknown outdoor access (0.46%; but significance was not reached) and significantly lower than of stray cats (11.8%), sampled previously (2020–2023) by us in the Netherlands, and subjected to a similar serological analysis 11 (Table 3), which is in agreement with our hypothesis. The indoor cat cohort was excluded from this comparison because of the low sample size. A comparable HPAI H5 seropositivity (2.6%) was observed in a French cat cohort consisting of 642 (2.2%) outdoor cats and 86 (5.8%) stray cats sampled in 2023–2025. 14
Comparison of influenza A virus ELISA seropositivity in different cat cohorts in the Netherlands
Data are n (%) unless otherwise indicated
Domestic cats with unknown outdoor access
Cross-reactivity of highly pathogenic avian influenza (HPAI) H5 antibodies to H1 in ELISA was suspected in 30/35 samples. 11 H1N1pdm09 seropositivity found in stray cats may be an overestimation resulting from cross-reactivity between HPAI H5 and H1 in ELISA, as most of these cats displayed low reactivity to H1 (optical density [OD] ratio <4) and high reactivity to HPAI H5 (OD ratio >4), 11 which was not observed for the domestic cat cohorts analysed previously 11 and in this study
CI = confidence interval
Outdoor access is a presumed important prerequisite of HPAI H5 virus exposure.11,14,37 Direct or indirect contact with infected birds is more likely for permanent outdoor living stray cats than for outdoor domestic cats that spend part of their life indoors. Moreover, in contrast to domestic cats, 45 stray cats need to prey or scavenge on birds to survive,46,47 which adds to their exposure. In agreement herewith, absence of hunting behaviour was shown to be a significant protective factor. 14 In addition, whereas stray cats may scavenge on dead waterfowl that are highly susceptible to HPAI H5 virus,1,3,4,46 outdoor cats mostly prey on smaller songbirds or pigeons, 48 in which HPAI H5 virus infections were less frequently detected in the Netherlands. 4 The absence of a significant association of age with HPAI H5 seroprevalence in this study may have been due to the low number of HPAI H5 seropositive cats and lower sample size compared with the previous study (11). The lower HPAI H5 ELISA seropositivity in domestic cats with unknown outdoor access sampled previously 11 may be due to sampling a substantial proportion of strictly indoor cats (~40% cats in the Netherlands live strictly indoors).11,37,49 As secondary data, in this study we also found HPAI H5 antibodies in two indoor cats. These cats originate from the island Texel where very high numbers (25.9%) of HPAI H5 seropositive stray cats were reported previously. 11 One of these cats had limited outdoor access via an enclosure and may have been indirectly exposed. 15 The other cat was reported to strictly live indoors. However, historical information on the living condition of these two cats is unavailable, limiting further interpretation of these positive results. To conclude, frequency of (in)direct bird contact, contact with high-at-risk bird species and scavenging may partly explain differences in seropositivity among cat cohorts.
HPAI H5 virus exposure is obviously also affected by the presence of HPAI H5 virus-positive wild birds in the Netherlands, which may depend to some extent on the targeted geographical sampling (at areas where previously HPAI H5 seropositive stray cats had been detected 11 ) as well as the sampling periods. Limited numbers of HPAI H5 virus-infected birds were reported in the Netherlands in 2024 compared with 2020–2023. 4 To compare the presence of HPAI H5 virus-positive wild birds in the Netherlands during the sampling periods of the cohorts shown in Table 3 (this study and Duijvestijn et al 11 ), we graphed the number of HPAI H5-positive wild birds, based on the number of sequences reported to EFSA and GISAID (EpiFLu database), in a timeline together with the number of samples obtained (Figure 4). Domestic cats and stray cats in the previous study 11 were sampled when large numbers of HPAI H5-infected wild birds were reported in the Netherlands. In contrast, the outdoor cat samples in this study were collected when the number of reports of HPAI H5-infected birds were relatively low. The lower ELISA OD ratios in outdoor cat sera (sampled in 2024) compared with stray cat sera (sampled in 2020–2023) (Figure 3), appears in agreement herewith. The low antibody levels in outdoor cats in this study may be due to the waning of antibodies, which in these generally older (mean age 10.7 years) outdoor cats were induced after exposure in previous years. Studies on IAV antibody longevity in cats – to substantiate this hypothesis – have not been conducted; however, cats are known to produce long-lasting detectable antibodies after natural infection with, or vaccination against, different pathogens. 50 However, we cannot exclude that other differences (eg, in exposure) contribute to the different antibody levels between outdoor cats and stray cats.

Sampling period of cat cohorts (2020–2024) compared with the presence of highly pathogenic avian influenza (HPAI) H5 clade 2.3.4.4-positive wild birds in the Netherlands (2016–2024). The x-axis depicts the years (in quarters). The y-axis depicts the number of cats sampled and the number of HPAI H5 clade 2.3.4.4-positive wild birds, as reported to the European Food Safety Authority (EFSA) and Global Initiative on Sharing All Influenza Data (GISAID)
In addition to HPAI H5 exposure, we observed seropositivity in domestic cats with and without known outdoor access in this study and in our previous study 11 to H1N1pdm09, which remained at a constant high level (5.5% and 4.6%, respectively) (Table 3) over the years. This indicates frequent and continuous exposure of these cats to H1N1pdm09, presumably through human caretakers. 28 Seropositivity to both HPAI H5 and H1 was detected in two outdoor cat sera, but it remains unclear if these cats had dual or successive exposure, as the exposure moment cannot be extrapolated based on the presence of antibodies. Dual H1N1pdm09 and HPAI H5 virus exposure in the Netherlands is theoretically possible, given the temporal overlap in seasonal H1N1pdm09 virus circulation in humans – peaking from mid-November to mid-April, and a similar peak in HPAI H5 virus circulation in wild birds. 51 If cats are dually infected with different IAVs within the same cell, they may potentially act as a mixing vessel. Reassortants of HPAI H5 and H1 have so far not been detected. However, other reassortant viruses have been detected in cats, including a HPAI H5N6 virus containing genes from H5N6, H9N2 and H7N9 subtypes, 38 as well as a triple reassortant H3N8 IAV, which was also found in a child from the same household. 39
Conclusions
The results of our study emphasise the need to closely monitor exposure to avian and human IAVs in domestic cats with outdoor access, especially in areas with high numbers of birds infected with IAVs, including but not limited to HPAI H5.
Footnotes
Acknowledgements
We thank Wendy van Hoeyen, Sylvia Bruin, Danique Holthuijsen, Marian Broekhuizen and Feye de Rooij for their assistance with sample processing. We thank Mieke Matthijs, Andreas Papanikolaou and Jasper de Louwere for providing the red blood cells for HAIs. We thank all veterinarians for their assistance with the sample collection, and we thank all cat owners for participating in this study. We gratefully acknowledge all data contributors – that is, the authors and their originating laboratories responsible for obtaining the specimens, and their submitting laboratories for generating the genetic sequence and metadata and sharing via the GISAID initiative, on which this research is partly based.
Author note
For comparison, data from our previous study were included in this manuscript. Based on the editorial policy of Eurosurveillance, authors retain ownership of the copyright for their manuscript. Data on the presence of HPAI H5 clade 2.3.4.4-infected wild birds in the Netherlands were based on the GISAID EpiFLu Database Access Agreement. Reuse of EFSA data was authorised as EFSA was acknowledged as the source of the material. The data that support the findings of this study are available upon reasonable request from the corresponding authors.
Conflict of interest
The authors declared no potential conflicts of interest with respect to the research, authorship, and/or publication of this article.
Funding
The authors disclosed receipt of the following financial support for the research, authorship, and/or publication of this article: This study was conducted on behalf of the Directorate of Animal Agricultural Chains and Animal Welfare, part of the Dutch Ministry of Agriculture, Fisheries, Food Security and Nature (study number IUC202309050).
Ethical approval
The work described in this manuscript involved the use of non-experimental (owned or unowned) animals. Established internationally recognised high standards (‘best practice’) of veterinary clinical care for the individual patient were always followed and/or this work involved the use of cadavers. Ethical approval from a committee was therefore not specifically required for publication in JFMS. Although not required, where ethical approval was still obtained, it is stated in the manuscript.
Informed consent
Informed consent (verbal or written) was obtained from the owner or legal custodian of all animal(s) described in this work (experimental or non-experimental animals, including cadavers, tissues and samples) for all procedure(s) undertaken (prospective or retrospective studies). No animals or people are identifiable within this publication, and therefore additional informed consent for publication was not required.
