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Article

A Sustainable Strategy for Gastrointestinal Nematode Control in Sheep

1
Department of Veterinary Sciences, University of Pisa, 56124 Pisa, Italy
2
Office for Hunting and Fishing Activities of Grosseto Regional Administration, Via C. Colombo 5, 58100 Grosseto, Italy
*
Author to whom correspondence should be addressed.
Vet. Sci. 2026, 13(1), 104; https://doi.org/10.3390/vetsci13010104
Submission received: 22 November 2025 / Revised: 14 January 2026 / Accepted: 17 January 2026 / Published: 21 January 2026
(This article belongs to the Section Veterinary Microbiology, Parasitology and Immunology)

Simple Summary

Sustainable parasite control in sheep must reconcile environmental protection with animal health and welfare. This study compared two gastrointestinal nematode management strategies in an endangered local sheep breed: routine anthelmintic treatments versus a long-term non-chemical approach based on rotational grazing and veterinary monitoring. Although treated animals showed a temporary reduction in parasite egg counts shortly after deworming, this effect was short-lived and disappeared within five months. Sheep managed without routine anthelmintics maintained moderate parasite burdens without clinical disease and displayed significantly better body condition scores throughout the study. Haematological parameters were largely comparable between groups, while treated animals showed higher liver enzyme activity and transient metabolic alterations following drug administration. Long-term stress indicators, assessed by hair cortisol, did not differ between strategies, suggesting similar welfare levels. Overall, the results indicate that non-chemical parasite management, when combined with careful monitoring, can maintain animal health and welfare while reducing drug use and potential environmental contamination. This approach represents a viable and sustainable alternative to routine anthelmintic treatments in extensive sheep farming systems.

Abstract

Gastrointestinal nematodes (GIN) represent a major constraint to sheep production, and sustainable alternatives to routine anthelmintic use are increasingly required. This study compared two parasite control strategies in Zerasca sheep: routine albendazole treatment administered twice yearly (T) and a long-term non-chemical approach based on rotational grazing (relocation to a new pasture when grass height fell below 10 cm) combined with quarterly veterinary monitoring (NT). Twenty-four adult ewes (n = 12 per group) were monitored over an eight-month period. Mean faecal egg counts (EPG) differed significantly between groups (T: 210 ± 78; NT: 529 ± 89; p = 0.0007). In group T, EPG values decreased markedly 7 days after treatment but increased again by 150 days, resulting in no persistent differences between groups over time. Despite higher parasite burdens, NT sheep showed significantly higher body condition scores compared with treated animals (3.00 ± 0.61 vs. 2.51 ± 0.53; p = 0.0014). Haematological parameters were largely comparable between groups, although mild reductions in RBC, HGB, and HCT were observed in both. Treated sheep exhibited higher AST activity (p < 0.0001) and transient increases in ALT and BUN following treatment. Hair cortisol concentrations did not differ significantly between groups. Overall, these findings suggest that a non-chemical parasite management strategy, when combined with controlled grazing and veterinary monitoring, may maintain acceptable parasite levels while supporting body condition and stable welfare indicators, potentially reducing reliance on routine anthelmintic treatments.

1. Introduction

Gastrointestinal nematodes (GIN) are recognized as some of the most prevalent and significant pathogens affecting the gastrointestinal tract in domestic ruminants globally [1]. In infected animals, these parasites can lead to severe clinical manifestations as well as notable declines in production in sub clinically infected subjects, resulting in significant economic losses [2]. GIN infections presently cause significant financial losses to the global small ruminant livestock sector, amounting to millions of dollars each year [3].
Decreased productivity can result from a combination of anorexia and diminished efficiency in resource utilization for production objectives [4]. GIN infections can result in significant alterations within the digestive tract of small ruminants, including heightened cell turnover, modifications in permeability, variations in pH, changes in secretory activities, and reduced gastric acid production [5]. As a result, GIN infections can lead to an imbalance of nutrients and adversely affect feed intake, growth and weight gain, fertility, as well as the quality and quantity of milk [6,7].
Historically, parasite control in livestock has predominantly relied on the use of antiparasitic drugs. While various anthelmintics possess distinct mechanisms of action, all function to either induce parasite death or impair motility through drug-induced paralysis [8]. The benzimidazole family represents the most extensive chemical group of anthelmintic drugs, featuring widely utilized derivatives such as fenbendazole, albendazole, and oxfendazole. The cytoskeleton is compromised by these drugs through a selective interaction with β-tubulin, impacting cellular structure and mitosis [8].
The extensive use of veterinary drugs in livestock therapy significantly impacts the environment and poses considerable risks to ecosystems [9]. These substances are introduced into the environment through excretions in pastures or via manure from treated animals. The application of dung, advocated for sustainable agriculture due to its role in mineral or nitrogen sequestration, poses the risk of disseminating veterinary pharmaceuticals onto agricultural land. Over 50% of unmetabolized drugs ultimately enter soil or water [10] and may be taken up by plants that can metabolize these compounds and accumulate them in their tissues [11,12]. Moreover, certain veterinary drugs can adversely impact plant physiology and endogenous metabolism [13,14,15]. Lastly, the aboveground parts of plants that contain accumulated drugs and their metabolites may be ingested by invertebrates, farm animals, and humans, thereby presenting significant risks to ecosystems [13].
Anthelmintics are specifically designed to be toxic to helminths, and their harmful effects on invertebrates have been well documented [16,17,18,19]. Regarding wild and farm animals, anthelmintics at low environmental concentrations do not exhibit acute toxicity; however, prolonged exposure, such as through the consumption of contaminated plants, may pose chronic toxicity risks. Moreover, the ingestion of contaminated plants by animals infected with helminths could promote the development of drug resistance due to interactions between residual anthelmintics and parasites [20].
The swift emergence of anthelmintic resistance is acknowledged as a worldwide threat to livestock production [21,22]. Resistance is defined as the heritable capacity of a parasite to withstand a typically effective dosage of anthelmintic agents. A parasite is deemed resistant if it endures exposure to the standard recommended dose of an anthelmintic, with this survival trait being inherited by its offspring [23]. Parasite resistance results from genetic mutations that enable parasites to withstand anthelmintic (dewormer) drugs, which are increasingly ineffective due to their frequent and indiscriminate application [24]. GIN parasite resistance is a complex issue that encompasses the parasite’s capacity to endure pharmacological treatments [25] as well as the host’s inherent genetic resilience to infection. This phenomenon raises sustainability concerns by undermining the long-term effectiveness of available drugs and increasing the environmental burden due to chemical residues and treatment frequency [26].
Sustainable nematode control in sheep requires an integrated approach that includes grazing management strategies such as rotation, rest periods, avoidance of overgrazing, and multi-species grazing. Additionally, genetic selection through breeding for parasite resistance [27], and alternative control methods, including bioactive plants with condensed tannins, copper oxide wire particles, and nematophagous fungi, can be components of this strategy [28,29,30,31,32,33,34].
Regarding grazing management, potential interventions include pasture rotation, which involves frequently moving sheep to new pastures to disrupt the parasite’s life cycle, and rest, which allows for sufficient recovery periods for pastures to eliminate larvae. In temperate climates, a rest period of 100 days or more can be effective [35]. Additionally, rotational multi-species grazing involves grazing a different species, such as cattle, on a pasture after it has been grazed by sheep [36]. Other animals will ingest the sheep-specific parasite larvae, and their own parasites will not develop in the sheep. It is important to avoid overgrazing [37], as most infective larvae are concentrated in the bottom four inches of grass. Moreover, ensure clean pastures for vulnerable animals by grazing young or low-immunity animals on areas that have not been recently grazed by contaminated adult animals [38].
Integrated management practices and selective treatment approaches are increasingly advocated as alternatives to diminish dependence on chemical interventions [39]. It is essential to emphasize that worms cannot be eliminated from the host or the environment. Infections can be mitigated through an understanding of parasite dynamics and prevalence. This knowledge is crucial for the implementation of integrated control strategies and for minimizing reliance on chemical treatments [40]. The concept of resilience is increasingly pertinent to sustainable livestock systems. Resilience denotes an animal’s capacity to sustain productivity and overall health in the presence of parasitic infections [41]. Resistance pertains to the reduction in parasite burden, whereas resilience emphasizes the animal’s ability to manage infection without a substantial decline in performance [42]. The promotion of resilient animals and systems enhances production sustainability by reducing drug dependency, minimizing costs, and bolstering the natural adaptive capacity of flocks. Research on host resistance is being conducted in animals such as sheep, utilizing breeding programs to select individuals and breeds with enhanced natural abilities to combat parasites, identifiable through traits such as low fecal egg counts [43].
Ultimately, the research seeks to provide insights into how sustainable and resilient parasite control practices can be implemented in modern sheep farming to enhance both environmental and economic sustainability [27].
This study fits within this line of research and aims to compare two farming systems in Zerasca sheep adopting contrasting parasite management strategies: one based on regular anthelmintic treatments and the other relying on a non-chemical approach.

2. Materials and Methods

The study was carried out in accordance with European Commission regulations and approved by the Ethics Committee of the University of Pisa (Italy), decision no. 31/2022. It took place between August 2022 and April 2023 and involved Zerasca sheep, a native breed classified as endangered. The research was conducted on two farms located in the Zeri district (Massa Carrara, Italy) at an altitude of 900 m above sea level (44°19′ N, 9°47′ E). Both farms were situated within the same valley and experienced comparable climatic conditions. No new animals had been introduced into the flocks during the 12 months preceding the study. Each flock comprised approximately 60 individuals and shared similar management practices, on approximately 14 ha of natural pasture (stocking density ≈ 4 ewes/ha). The primary source of nourishment for the sheep consisted of natural pasture, including polyphyte meadow grasses, shrubs, and bushes. In addition, animals were supplemented daily with polyphyte meadow hay and corn, according to pasture availability and physiological stage.
Both farms provided salt licks to ensure adequate mineral intake.
The first farm implemented a conventional gastrointestinal parasite control regimen, administering albendazole (Sverminator®-FATRO S.p.A., Ozzano dell’Emilia, Bologna, Italy) per os at a dose of 3.75 mg/kg of body weight twice annually, in autumn and spring, to control GIN. In contrast, the second farm had not administered any gastrointestinal anthelmintic treatments over the past ten years, adhering instead to a non-chemical parasite management approach. This strategy relies on rotational grazing and regular monitoring of GIN (every three months) under the supervision of a veterinarian.
Grazing rotation was implemented by moving the animals to a new grazing area when, following browsing, grass height was reduced to approximately 10 cm in height [44]. In fact, it has been demonstrated that infective third-stage larvae (L3) of trichostrongylid nematodes are unevenly distributed along the vertical profile of the herbage, with the highest concentrations occurring near the base of the sward [45].
In cases of increased egg per gram (EPG), the veterinarian assessed the need for targeted anthelmintic treatment of individual animals showing a reduction in Body Condition Score (BCS).
For this study, twenty-four adult ewes (n = 12 per group) were monitored over an eight-month period. The ewes were randomly selected from each flock to form two experimental groups: group T composed of animals treated with anthelmintic drug; and group NT composed of animals that did not usually receive a vermifuge, ensuring homogeneity in age (3–6 years) and parity (≥2) to minimize potential bias. The investigation was conducted from August 2022 to April 2023. A veterinarian assessed the general health status of all animals during each sampling session. The presence of ectoparasites is regularly monitored in the flock, with treatment of particularly infested animals, but no antiparasitic treatments were carried out during the research.
Over the study period, two anthelmintic treatments were administered to the Group T flock in June and November. Three sets of blood, faecal, and wool samples were collected simultaneously from both treated (T) and non-treated (NT) groups, according to the study timeline reported in Figure 1. Sampling was performed under different climatic conditions: June (temperature 22–28 °C; mean relative humidity, RH, 60%), November (7–12 °C; RH 80%), and April (12–18 °C; RH 70%). This sampling strategy allowed evaluation of the effects of anthelmintic treatment in the short, medium, and long term, as well as under varying climatic conditions.
Faecal samples were collected directly from the rectal ampulla and analyzed using the McMaster technique [46] to estimate the faecal egg count of gastrointestinal strongyles, expressed as EPG. Samples were processed within 24 h of collection and subsequently stored at 4 °C until analysis. EPG values were categorized into three levels following Ambrosi’s classification [47]: level 1 = 0–300 EPG, level 2 = 301–600 EPG, and level 3 = >600 EPG.
Pooled fecal samples were subjected to coproculture according to Henriksen and Korsholm [48,49], and third-stage larvae were identified morphologically. Moreover, the samples were examined by macroscopic inspection for the presence of cestode proglottids [50].
Blood samples were collected from the jugular vein using Vacutainer® tubes (Becton, Dickinson & Co., Milan, Italy) and stored in a refrigerated container (+5 °C) until delivery to the laboratory. Complete blood counts were performed at the Veterinary Clinical Pathology Unit, Department of Veterinary Sciences (University of Pisa, Italy), using a CELL-DYN 3500® automated haematology analyser (Abbott, Minneapolis, MN, USA). The following haematological parameters were assessed: red blood cell count (RBC), haematocrit (HCT), haemoglobin (HGB), mean corpuscular volume (MCV), mean corpuscular haemoglobin (MCH), mean corpuscular haemoglobin concentration (MCHC), reticulocytes (RETIC), white blood cells (WBC), neutrophils (NEU), lymphocytes (LYM), monocytes (MON), eosinophils (EOS), basophils (BAS), and platelets (PLT).
Serum was separated, frozen, and sent to the Istituto Zooprofilattico Sperimentale delle Regioni Lazio e Toscana (IZSLT) for the analysis of selected metabolic and immunological parameters. These included: alanine aminotransferase (ALT), aspartate aminotransferase (AST), blood urea nitrogen (BUN), β-hydroxybutyric acid (BHBA), non-esterified fatty acids (NEFA), total proteins (TP), creatinine (Creat), calcium (Ca), chloride (Cl), phosphorus (P) and potassium (K), analysed using an automatic biochemical analyser (Olympus AU 400, San Diego, CA, USA).
Oxygen free radicals (OFR) were quantified using a commercial colorimetric method (Diacron International S.r.l., 58100, Grosseto, Italy).
Wool samples were collected from the shoulder area, between the scapular bones, and as close as possible to the skin, using scissors. The wool samples were stored in aluminum foil and labelled envelopes at room temperature until analysis at the ETOVET Laboratory, Department of Veterinary Sciences, University of Pisa (Italy). Wool samples were processed using the ELISA method described by Mariti et al. [51] to evaluate hair cortisol.
Serum cortisol concentrations were measured according to the method previously described by Gazzano and colleagues [52].
BCS was evaluated by one of the authors (M.N.B.) who has extensive experience in the field, according to the scale of Russel et al. [53], ranging from one (emaciated) to five (obese). This parameter was chosen because it is considered one of the most reliable indicators of animal health, productive performance, and reproductive status, as reported by Roche and colleagues [54].
Statistical analysis of blood parameters and gastrointestinal strongyles was performed using ANOVA. Data regarding FECs were logarithmically transformed [y = log (EPG + 25)] to normalize error [55]. Statistical analyses were performed using GraphPad Prism 9 (Graph-Pad Software, San Diego, CA, USA). Statistical significance was set at p ≤ 0.05. All the data are also provided in the Supplementary Materials (Table S1).

3. Results

Mean EPG values (±S.E.), calculated across the three sampling time points, were 210 ± 78.10 for group T and 529.05 ± 88.92 for group NT, and differed significantly between the two groups (t = 3.55; p = 0.0007).
EPG values in the T group were significantly lower than those in the NT group at 7 days post-treatment. However, no significant difference was observed at 150 days. Furthermore, intra-group comparisons across the three time points revealed no statistically significant differences, likely due to high inter-individual variability (Figure 2).
Table 1 summarizes the median EPG values and the corresponding minimum–maximum ranges recorded at each sampling time point. Although a reduction in EPG was observed 7 days after treatment, marked inter-individual variability was evident.
The distribution of EPG levels in the two groups is reported in Table 2. Animals in group NT exhibited a higher level of infestation, particularly at EPG level 2. Moreover, a substantial proportion of animals in group NT showed level 3 infestation.
No cestode proglottids were observed on macroscopic examination. Coproculture revealed a predominance of Trichostrongylus spp. larvae in the examined fecal samples, while Chabertia ovina was detected at a lower frequency.
Regarding BCS, the mean values (±S.E.) calculated across the three sampling time points for the two groups were 2.51 ± 0.53 in T group and 3.00 ± 0.61 in NT group; a significant difference was observed between groups (t = 3.548, p = 0.0007), with animals in group NT exhibiting a better body condition.
BCS values remained stable in animals from group NT across the three sampling time points. In contrast, a statistically significant reduction in BCS was observed in group T at 7 and 150 days post-treatment (Figure 3).
The BCS mean value (±S.E.) of animals of group T (2.05 ± 0.09), assessed 7 days after the second anthelmintic treatment, was significantly lower than that of animals in group NT (3.25 ± 0.17) (p ≤ 0.0001).
During the study period, none of the animals in group NT exhibited a reduction in BCS sufficient to require veterinary evaluation or the administration of anthelmintic treatment.
Table 3 reports the mean hair cortisol concentrations (±S.E.) according to EPG level. The highest mean value was observed at EPG level 3; however, no statistically significant differences were detected among the three levels.
When comparing hair cortisol concentrations across the three sampling time points, values measured 150 days after treatment were significantly higher in both groups T and NT than those recorded at 7 and 50 days post-treatment (Figure 4).
A statistically significant difference in mean (±S.E.) hair cortisol concentrations was also observed between groups T (9.97±), and NT (20.08 ± 2.09), at 7 days post-treatment (U = 20; p ≤ 0.05).
Analysis of the haematochemical parameters reported in Table 4 reveal no statistically significant differences between groups. Although not statistically significant, mean RBC and HCT values in group T were slightly below the physiological reference range.
Table 5 reports the mean values of metabolic parameters of animals of the T and NT group.
ALT mean values (±S.E.) at 7 (25.60 IU ± 1.4) and 50 (24.55 IU ± 1.40) days are higher than those detected 150 days after deworming (18.00 ± 1.13). A repeated-measures one-way ANOVA showed a significant effect of sampling time on ALT values [F (1.56, 12.48) = 6.78, p = 0.0139]. Tukey’s multiple comparisons test indicated that ALT values at 150 days were significantly lower than those measured at 7 days (p = 0.0327) and 50 days (p = 0.0063), while no significant difference was observed between 7 and 50 days (p = 0.9723). Mean AST values differed significantly between groups (U = 286.5; p = 0.0003); moreover, AST concentrations in group T animals were elevated at 7 and 50 days, with a statistically significant difference compared to those detected 150 days after treatment, although remaining within the range considered physiological (Figure 5).
BUN concentrations in group T were significantly higher at 7 days post-treatment compared with those measured at 50 and 150 days after deworming, whereas an opposite trend was observed in group NT (Figure 6).
Analysis of potential correlations among cortisol levels (in blood and hair), BCS, EPG, and biochemical and haematological parameters revealed the significant associations reported in Table 6.

4. Discussion

The expansion of land use and the increasing prevalence of intensive livestock farming require a comprehensive evaluation of the sustainability of animal production systems, a concept that has broadened considerably compared with earlier interpretations. Traditionally, production systems were considered unsustainable when natural resources were depleted beyond their capacity for recovery or when by-products accumulated to levels that impaired system functioning [56]. The concept now encompasses a broader scope; for example, a production system may be considered unsustainable because of its negative impacts on human health, animal welfare, or the environment. Moreover, consumers increasingly take the ethical implications of food production into account when evaluating product quality [57]. A system or procedure can be defined as sustainable if it is acceptable under current conditions and if its projected future impacts are likewise acceptable, taking into account resource availability, operational performance, and ethical considerations [58,59]. Livestock farming poses substantial challenges to environmental sustainability, even under extensive management systems. Key concerns include animal health and welfare, pasture overgrazing, the spread of drug-resistant parasites, and residues of antiparasitic compounds in the environment. This study compared two parasite control strategies in sheep in order to evaluate the feasibility of environmentally sustainable flock management without routine pesticide use, while maintaining adequate standards of animal health and welfare. Analysis of the factors influencing animal welfare indicated marked inter-individual variability in parasite load and a limited duration of the antiparasitic treatment effect. In fact, 150 days after treatment, no differences were observed between animals in group T and those in group NT. Additionally, treated animals exhibited a negative correlation between EPG and MCV at 7 days post-treatment, although MCV values remained within the physiological range for the species. This transient effect highlights the need for repeated treatments, which in turn raises concerns regarding the development of anthelmintic resistance [21]. Recent studies have shown that the overuse of broad-spectrum anthelmintics can accelerate resistance even in small, closed flocks [60]. From a sustainability perspective, reliance on chemical parasite control not only compromises the long-term efficacy of treatments but also generates environmental and economic challenges for livestock production. By contrast, group NT maintained relatively stable and moderate EPG levels in the absence of pharmacological intervention. Although correlation does not necessarily imply causation, in this group EPG was significantly and positively correlated with blood cortisol concentrations and reticulocyte counts, suggesting a physiological stress response associated with increasing parasite burden. This interpretation is further supported by the observed negative correlations between EPG and HGB, NEFA, and Ca. Previous studies [61,62] have demonstrated that parasitic infestations can influence key hematological parameters; in particular, subclinical anaemia may occur as a consequence of micro-hemorrhages caused by nematode attachment and larval migration, and a slight reduction in HGB concentration may represent an early and subtle indicator of parasitic challenge. These findings represent a warning signal that deserves careful monitoring in flocks managed without routine anthelmintic treatment.
Coproculture of pooled fecal samples identified Chabertia ovina and Trichostrongylus spp. as the main gastrointestinal nematodes present in the monitored sheep flocks. The two parasites differ in their ecological dynamics, with Trichostrongylus spp. showing rapid development and early pasture contamination under favorable environmental conditions, whereas Chabertia ovina exhibits slower larval development but greater environmental persistence once established on pasture [63]. In both cases, larval availability on herbage is strongly moisture-dependent, with peak exposure following rainfall or heavy dew [64]. Despite their presence, EPG values remained quite low, and no severe clinical signs were observed, in line with the typically mild to moderate pathogenicity associated with these nematodes under conditions of low parasite burden [65]. The absence of hematophagous species such as Haemonchus contortus further supports the limited clinical impact recorded in the studied flocks.
Another important factor in the assessment of animal welfare is body condition score (BCS). Animals in group NT exhibited a significantly higher mean BCS than those in group T and the values remained stable in the NT flock throughout the study period, whereas a statistically significant reduction in BCS was observed in group T at 7 and 150 days post-treatment. In addition, the BCS of treated animals assessed 7 days after the second anthelmintic treatment was significantly lower than that of animals in group NT.
Resilience represents a key adaptive trait in sustainable livestock farming, particularly under conditions of parasitic challenge [66,67]. Moreover, in extensive production systems, BCS may be influenced more strongly by environmental, nutritional, and behavioral factors than by parasite burden alone, as noted by Kenyon and Jackson [68]. However, in the present study, these potential confounding factors can be reasonably excluded, as environmental and nutritional conditions, as well as management practices, were comparable between the two farms.
Haematological analyses revealed only mild differences between the two groups. Although RBC, HGB, and HCT values were slightly below the reference ranges in both flocks, these variations were not statistically significant and may reflect physiological adaptation to chronic parasitism. The reduced RBC, HCT, and HGB levels observed are consistent with the findings of Aziz et al. [69], who reported similar decreases associated with intestinal parasitic infections.
Thrombocytopenia in ruminants may be associated with blood loss, septicemia and inflammatory diseases such as mastitis and metritis [70]. However, in the present study, the lower platelet counts observed in group NT compared with group T were not associated with any clinical signs consistent with these conditions [71].
Serum biochemical analysis revealed notable differences in markers related to liver and kidney function, as well as energy metabolism. ALT values exceeded the physiological reference range in both experimental groups, although no significant differences were detected between groups. In sheep, ALT is not considered a specific marker of hepatic injury, unlike in dogs or humans; nevertheless, increased ALT activity has been reported following the administration of anthelmintic drugs such as albendazole, which undergoes hepatic metabolism. This interpretation is supported by the observation that ALT values exceeded the physiological range at 7 and 50 days after deworming.
By contrast, AST is regarded as a more sensitive indicator for the diagnosis of fatty liver in sheep [72]. This enzyme is localized in both the cytoplasm and mitochondria of various tissues, with the highest activity found in skeletal muscle, heart, and liver. Consequently, alterations in circulating AST activity may reflect damage to cellular structures, particularly within hepatic tissue [73]. AST concentrations were significantly higher in animals from group T, pointing to a greater degree of liver involvement, potentially associated with pharmacological metabolism. In fact, albendazole undergoes hepatic metabolism following oral administration through a sequential two-step sulphoxidation pathway [74]. This process initially produces albendazole sulphoxide via a rapid and reversible reaction, followed by further oxidation mediated by cytochrome P450 (CYP) enzymes, resulting in the inactive metabolite albendazole sulphone [75,76]. These CYP-driven reactions are accompanied by the generation of reactive oxygen and nitrogen species (ROS and RNS), and the transient release of reactive intermediates from the metabolic system has been documented [77]. Such biochemical events may underlie the elevated AST activity observed in treated animals.
In group T, BUN levels 7 days after treatment were statistically higher than those of the other 2 samples: one cause could be a reduction in renal blood flow due to dehydration resulting from diarrhea, a possible side effect of treatment with albendazole [78].
NEFA concentrations were below the physiological reference range in both groups and were more markedly reduced in group T. In sheep with chronic gastrointestinal nematode infections, alterations of energy metabolism have been reported, including normal or reduced circulating NEFA concentrations, likely reflecting reduced lipid mobilization and energy reallocation towards immune responses rather than acute negative energy balance [79].
Oxidative stress, assessed through OFR, was higher in group NT, although the difference did not reach statistical significance. Oxidative stress is a multifactorial phenomenon and should not be attributed solely to pharmacological treatment. Additional contributing factors may include chronic parasitic burden, nutritional imbalances, environmental stressors, as well as physiological or social influences [80].
With respect to hair cortisol, although the highest concentrations were observed in animals with EPG level 3, no statistically significant differences were detected among EPG categories. Likewise, hair cortisol concentrations did not differ significantly between groups T and NT (18.33 vs. 16.67 pg/mg), indicating comparable long-term cortisol levels: this finding could reflect an inherent resilience trait in the animals. However, when animals were stratified by EPG levels, hair cortisol increased with parasite load; moreover, hair cortisol levels were slightly higher in sheep with high EPG (25.01 pg/mg) compared to those with low EPG (22.30 pg/mg), but the difference was not statistically significant. These findings are consistent with those of Carlsson et al. [81], who observed that although cortisol levels may rise with parasitic burden, they are not reliable as a standalone indicator of parasite infection.

5. Conclusions

This study highlights the multifaceted effects of different gastrointestinal parasite management strategies on sheep health. Although the findings should be considered preliminary, given the limited number of animals, the short duration of the study, and the inclusion of a particularly resilient sheep breed, the results appear to support the sustainability of sheep farming systems that do not rely on routine anthelmintic treatments, both in terms of animal welfare and environmental impact.
Although the absence of anthelmintic treatment may expose animals to potential health and production losses associated with parasitic infection, careful and continuous monitoring, enabling timely intervention in response to declines in BCS or alterations in haematological and biochemical parameters, can effectively support animal health and welfare.
On the other hand, the use of anthelmintic drugs is not without risk. In addition to the environmental concerns associated with drug residues, anthelmintic administration may act as a stressor for animals, particularly in the period immediately following treatment. In the present study, animals evaluated 7 days post-treatment showed a reduction in BCS, increased BUN concentrations, elevated AST activity, and ALT values exceeding the physiological reference range.
Despite the absence of pharmacological treatment, animals in group NT exhibited higher BCS values and showed no significant indications of chronic stress, as reflected by hair cortisol concentrations. Overall, these findings suggest that the adoption of integrated, low-chemical parasite control strategies may enhance the sustainability of livestock systems by reducing reliance on drugs, limiting environmental contamination, and preserving the long-term efficacy of available anthelmintics. Promoting resilience within such systems supports both animal welfare and productivity, ensuring that parasite management is aligned with the broader environmental, economic, and ethical objectives of modern sheep farming. The results obtained are therefore relevant and may provide a basis for extending this approach to other sheep breeds and diverse climatic conditions.

Supplementary Materials

The following supporting information can be downloaded at https://www.mdpi.com/article/10.3390/vetsci13010104/s1. Table S1: Data sets.

Author Contributions

Conceptualization, L.G., M.N.B. and F.M.; methodology L.G., M.N.B. and F.M.; statistical analysis, M.N.B.; investigation, A.G. and M.N.B.; resources, G.R., F.M. and A.G.; writing—original draft preparation, L.G., M.N.B. and F.M.; writing—review and editing, L.G., M.N.B., F.M., A.G. and V.G.; supervision, A.G. and V.G. All authors have read and agreed to the published version of the manuscript.

Funding

This research received no external funding.

Institutional Review Board Statement

The animal study protocol was reviewed and approved by the local animal care committee, Ethics Committee of the University of Pisa, Italy, authorization No.31/2022.

Informed Consent Statement

Informed consent was obtained from the owners of all animals involved in the study.

Data Availability Statement

The original contributions presented in this study are included in the article. Further inquiries can be directed to the corresponding author.

Acknowledgments

The authors thank the farmers Patrizia Figaroli and Vera Bertoni for their availability, and Benedetta Sarno for her valuable collaboration. The authors would like also to thank Antonello Di Paolo.

Conflicts of Interest

The authors declare no conflicts of interest.

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Figure 1. Timeline of the two anthelmintic administrations in the treated group (T) and of the three blood, faecal, and wool sampling time points in both treated (T) and non-treated (NT) groups during the study period.
Figure 1. Timeline of the two anthelmintic administrations in the treated group (T) and of the three blood, faecal, and wool sampling time points in both treated (T) and non-treated (NT) groups during the study period.
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Figure 2. Comparison of the levels of parasitic infestation (log EPG) between animals of the treated (T) and non-treated (NT) groups in the three samplings. *** p ≤ 0.001; ** p ≤ 0.01; ns = not significant.
Figure 2. Comparison of the levels of parasitic infestation (log EPG) between animals of the treated (T) and non-treated (NT) groups in the three samplings. *** p ≤ 0.001; ** p ≤ 0.01; ns = not significant.
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Figure 3. Relative Body Condition Score (BCS) values in treated (T) and non-treated (NT) groups at the three sampling time points. * p ≤ 0.05; *** p ≤ 0.001; ns = not significant.
Figure 3. Relative Body Condition Score (BCS) values in treated (T) and non-treated (NT) groups at the three sampling time points. * p ≤ 0.05; *** p ≤ 0.001; ns = not significant.
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Figure 4. Hair cortisol concentrations (pg/mL) in treated (T) and non-treated (NT) groups at the three sampling time points. * p ≤ 0.05; ** p ≤ 0.01; *** p ≤ 0.001; ns = not significant.
Figure 4. Hair cortisol concentrations (pg/mL) in treated (T) and non-treated (NT) groups at the three sampling time points. * p ≤ 0.05; ** p ≤ 0.01; *** p ≤ 0.001; ns = not significant.
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Figure 5. Serum Aspartate Aminotransferase (AST) concentrations in treated (T) and non-treated (NT) groups at the three different samplings. ** p ≤ 0.01; *** p ≤ 0.001; ns = not significant.
Figure 5. Serum Aspartate Aminotransferase (AST) concentrations in treated (T) and non-treated (NT) groups at the three different samplings. ** p ≤ 0.01; *** p ≤ 0.001; ns = not significant.
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Figure 6. Blood Urea Nitrogen (BUN) concentrations in treated (T) and non-treated (NT) groups at the three sampling time points. * p ≤ 0.05; ** p ≤ 0.01; *** p ≤ 0.001; **** p ≤ 0.0001; ns = not significant.
Figure 6. Blood Urea Nitrogen (BUN) concentrations in treated (T) and non-treated (NT) groups at the three sampling time points. * p ≤ 0.05; ** p ≤ 0.01; *** p ≤ 0.001; **** p ≤ 0.0001; ns = not significant.
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Table 1. Median EPG values and corresponding minimum–maximum ranges recorded in the non-treated group (NT) and treated group (T) at each sampling time point.
Table 1. Median EPG values and corresponding minimum–maximum ranges recorded in the non-treated group (NT) and treated group (T) at each sampling time point.
GroupSamplingDays from
Drenching
Median
EPG
Min–Max
T150140.00–920
T270.00–160
T315040.00–1680
NT1-300.080–1680
NT2-440.040–1680
NT3-200.00–1880
Table 2. Distribution of EPG levels in the treated (T) and non-treated (NT) groups.
Table 2. Distribution of EPG levels in the treated (T) and non-treated (NT) groups.
Group
TNT
EPG Level% of Sampled Animals
180.937.50
2033.33
319.029.17
Table 3. Mean hair cortisol concentrations (±S.E.) according to Eggs Per Gram (EPG) level.
Table 3. Mean hair cortisol concentrations (±S.E.) according to Eggs Per Gram (EPG) level.
Hair Cortisol
EPG LevelMean (pg/mg)S.E.
122.301.793
219.094.009
325.013.472
Table 4. Haematochemical parameters in the treated (T) and non-treated (NT) groups.
Table 4. Haematochemical parameters in the treated (T) and non-treated (NT) groups.
TNT
MeanS.E.MeanS.E.pUMNormal Range *
Red Blood Cells8.79 ↓0.358.32 ↓0.350.347M/µL9.49–15.12
HCT26.83 ↓1.1526.24 ↓1.150.717%27.0–42.0
HGB9.69 ↓0.459.02 ↓0.450.297g/dL10.0–14.9
MCV30.560.6931.610.690.285fl24.4–32.5
MCH11.100.3810.880.380.692pg8.5–11.8
MCHC36.491.2934.440.290.268g/dL32.3–42.0
Reticulocytes3.071.813.981.810.722K/µL0–15.0
Leucocytes7.920.667.980.660.949K/µL5.06–14.12
Neutrophyls2.080.282.630.280.171K/µL1.17–6.11
Lymphocytes4.080.343.790.340.531K/µL2.54–9.60
Monocytes1.000.150.86 ↓0.140.483K/µL0.10–1.01
Eosinophils0.680.170.620.170.805K/µL0.05–0.95
Basophils0.14 ↑0.030.100.030.373K/µL0–0.12
Platelets447.2562.10265.83 ↓62.100.042K/µL301–922
MPV9.780.289.040.280.068fl5.0–7.5
HCT (haematocrit), HGB (haemoglobin), MCV (mean corpuscular volume), MCH (mean corpuscular haemoglobin), MCHC (mean corpuscular haemoglobin concentration), and MPV (Mean Platelet Volume). * Reference intervals were provided by the Veterinary Clinical Pathology Laboratory, Department of Veterinary Sciences, University of Pisa. ↑ Values over the threshold of the normal range; ↓ Values under the threshold of the normal range.
Table 5. Mean values (±S.E.) of metabolic parameters in the treated (T) and non-treated (NT) groups.
Table 5. Mean values (±S.E.) of metabolic parameters in the treated (T) and non-treated (NT) groups.
Group
TNT
MeanS.E.MeanS.E.pUMNormal Range *
ALT24.54 ↑1.52123.75 ↑1.4560.7068IU/L≤18
AST123.005.65590.505.4140.0001IU/L40–128
BUN9.271.30616.581.2510.0001mg/dL8–20
BHBA7.831.0446.040.9990.2203mmol/L5.7–20
Creatinine0.810.0290.800.0270.7415mg/dL1.2–1.9
Cortisol1.910.182.380.200.0859mg/dL-
NEFA91.09 ↓70.047 136.6467.0650.6403μmol/L102–450
TP7.080.1927.140.1840.8229g/dL6–7.90
Ca9.72 ↓0.1749.78 ↓0.1670.8147mg/dL11.5–13
Cl106.82 ↑0.698108.330.6680.1221Mmol/L90–110
P4.450.2594.070.2480.2919mg/dL4.5–7.5
K4.58 ↓0.1534.70 ↓0.1460.5790mmol/L4.8–7
OFR38.454.98948.924.7770.1350U. Carr.44–88
Hair cortisol18.332.60816.672.4970.6470pg/mg-
ALT (alanine aminotransferase), AST (aspartate aminotransferase), BUN (blood urea nitrogen), BHBA (β--hydroxybutyric acid), NEFA (non-esterified fatty acids), TP (total proteins), Ca (calcium), Cl (chloride), P (phosphorus) and K (potassium), OFR (Oxygen free radicals), Cortisol (serum cortisol). * Reference ranges were provided by the IZSLT laboratory. U. Carr. is an arbitrary unit; 1 U. Carr. is equivalent to 0.08 mg of H2O2/100 mL. ↑ Values over the threshold of the normal range; ↓ Values under the threshold of the normal range.
Table 6. Significant correlations among Eggs Per Gram (EPG), Body Condition Score (BCS), haematological, biochemical, and hormonal parameters in treated (T) and non-treated (NT) groups.
Table 6. Significant correlations among Eggs Per Gram (EPG), Body Condition Score (BCS), haematological, biochemical, and hormonal parameters in treated (T) and non-treated (NT) groups.
Animal GroupParametersType of CorrelationDays After TreatmentRho
TEPG-MCVNegative7−0.68; p = 0.04
THair cortisol-BCSNegative7−0.69; p = 0.02
THair Cortisol-CaNegative7−0.77; p = 0.01
THair cortisol-BCSNegative50−0.65; p = 0.02
THair cortisol-PNegative50−0.65; p = 0.03
THGB–CortisolNegative150−0.79; p = 0.003
NTHair Cortisol-CaNegative7−0.69; p = 0.03
NTBCS-HCTPositive70.85; p ≤ 0.001
NTBCS-HGBPositive70.77; p = 0.005
NTBCS-CaPositive70.62; p = 0.04
NTEPG-HGBNegative7−0.63; p = 0.03
NTEPG-ReticulocytesPositive500.60; p = 0.04
NTEPG-CortisolPositive 500.62; p = 0.04
NTEPG-NEFANegative50−0.64; p = 0.03
NTEPG-CaNegative150−0.59; p = 0.05
EPG = Eggs Per gram; MCV = mean corpuscular volume; BCS = Body Condition Score; Ca = Calcium; P = Phosphorus; HGB = Haemoglobin; Cortisol = serum cortisol; NEFA = Non-Esterified Fatty Acids.
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Giuliotti, L.; Benvenuti, M.N.; Gazzano, A.; Gazzano, V.; Romeo, G.; Macchioni, F. A Sustainable Strategy for Gastrointestinal Nematode Control in Sheep. Vet. Sci. 2026, 13, 104. https://doi.org/10.3390/vetsci13010104

AMA Style

Giuliotti L, Benvenuti MN, Gazzano A, Gazzano V, Romeo G, Macchioni F. A Sustainable Strategy for Gastrointestinal Nematode Control in Sheep. Veterinary Sciences. 2026; 13(1):104. https://doi.org/10.3390/vetsci13010104

Chicago/Turabian Style

Giuliotti, Lorella, Maria Novella Benvenuti, Angelo Gazzano, Valentina Gazzano, Giorgia Romeo, and Fabio Macchioni. 2026. "A Sustainable Strategy for Gastrointestinal Nematode Control in Sheep" Veterinary Sciences 13, no. 1: 104. https://doi.org/10.3390/vetsci13010104

APA Style

Giuliotti, L., Benvenuti, M. N., Gazzano, A., Gazzano, V., Romeo, G., & Macchioni, F. (2026). A Sustainable Strategy for Gastrointestinal Nematode Control in Sheep. Veterinary Sciences, 13(1), 104. https://doi.org/10.3390/vetsci13010104

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