3.2. Analysis of Research Results
Analyzing research results is an essential step in validating formulated hypotheses and acquiring a comprehensive understanding of the phenomenon studied. In this research, specific statistical methods were applied, such as the t-test, ANOVA, the Chi-square test, Pearson correlation, and linear regression analysis, each selected according to the typology of the variables involved in the study and the objectives pursued. The results obtained were interpreted in the context of the specialized literature, providing a perspective on tourists’ perceptions of sustainable ecotourism post-COVID-19 pandemic in the South-West Oltenia region. These analyses highlight the significant relationships between the demographic, economic, and behavioral variables pertaining to the respondents and provide concrete answers to the research hypotheses.
H1. Gender influences the desire to practice ecotourism.
Our research hypothesis that gender influences the motivation to engage in ecotourism builds upon the established literature documenting gender-based variations in environmental attitudes and travel behaviors. Previous empirical studies indicate that women frequently demonstrate higher levels of environmental concern and a stronger inclination toward ecotourism activities than men. For instance, Balińska et al. (2024) [
52] observed that female Generation Z respondents exhibited significantly more favorable attitudes toward ecotourism and greater participation intent compared to their male counterparts. Grounded in these insights, this study hypothesizes that gender similarly shapes the desire to participate in ecotourism within the Oltenia Region.
The descriptive analysis indicated that women had a slightly higher mean score for the desire to practice ecotourism relative to men. To determine whether this difference was statistically significant, an independent-samples t-test was performed.
The
t-test analyzing the influence of gender on the desire to practice ecotourism indicated that the variability between groups was different, as shown by the Levene Test for equality of variances, with an F-value of 14.507 and a significance level of
p = 0.000, indicating that the hypothesis of equality of variances must be rejected (
Table 4).
For the
t-test, when equality of variances was assumed, the t-value was 1.683 with 493 degrees of freedom and a significance level of
p = 0.093. The mean difference between groups was 0.106, with a 95% confidence interval between −0.018 and 0.230. When inequality of variance was assumed, the t-value was 1.403 with 140.805 degrees of freedom, and the significance level
p = 0.163, with the same mean difference of 0.106 and a 95% confidence interval between −0.043 and 0.256 (
Table 4).
The results show that there are no statistically significant differences between genders in terms of willingness to practice ecotourism, as the p-values are greater than the significance threshold of 0.05.
H2. Age influences the duration of visits to protected areas.
Our research hypothesis that age influences the duration of visits to protected areas was formulated on the basis of observations reported in the literature, which indicate that tourism preferences and behavior differ significantly across generations. Previous studies have highlighted that young people, especially those from the Millennial generation, prefer shorter but more frequent visits, while people from older age groups tend to allocate more time to recreational activities, including ecotourism [
53].
Also, according to research conducted by Kolster et al. (2025), older visitors are more likely to appreciate nature-related activities and spend more time in protected areas [
54]. Based on this evidence, the research hypothesis was formulated to analyze whether there are significant age-based differences in the duration of visits.
To examine whether the duration of visits to protected areas differs across age groups, a one-way ANOVA was conducted. The assumption of homogeneity of variances was satisfied prior to testing (Levene’s test: F = 0.060, and p = 0.981), confirming that the dataset fulfilled the necessary requirements for standard ANOVA execution.
The ANOVA results show that there are statistically significant differences between age categories in terms of the duration of visits to protected areas, with an F value = 8.000 and a significance level
p = 0.000 (
p < 0.05). The variability between groups is represented by a sum of squares of 12.439 and a mean of squares of 4.146, and the variability within groups is represented by a sum of squares of 257.089 and a mean of squares of 0.518. The total variability is 269.528 (
Table 5). These results validate the hypothesis that age influences the duration of visits to protected areas.
H3. Tourists’ levels of education affect perceptions of the possibility of practicing ecotourism.
Our research hypothesis that tourists’ levels of education affect perceptions of the possibility of practicing ecotourism was substantiated by previous research showing that education plays a significant role in shaping attitudes towards sustainable tourism. Studies have shown that individuals with higher levels of education have a more comprehensive understanding of the positive impact of ecotourism on the environment and local communities [
55].
Education also increases awareness of the need to conserve natural resources and increases confidence in the benefits of ecotourism with respect to sustainable development [
56,
57]. This hypothesis was formulated to explore whether there are significant differences in perceptions of practicing ecotourism depending on tourists’ levels of education.
To examine whether perceptions of the possibility of practicing ecotourism differed according to the respondents’ education levels, a one-way ANOVA was performed. It showed no statistically significant differences in how the respondents rated the possibility of practicing ecotourism across education levels (F = 1.204,
p = 0.308) (
Table 6). With a
p > 0.05, we could not reject the null hypothesis. The data indicate that a tourist’s level of education has no real bearing on whether they see ecotourism as a viable option.
The F value obtained was 1.204, with a significance level of
p = 0.308. Since
p > 0.05 (
Table 6), the null hypothesis, which stated that there would be no significant differences between the education groups, could not be rejected. Thus, the results suggest that level of education does not influence perceptions of the possibility of practicing ecotourism.
H4. Labor market status influences post-pandemic travel frequency.
Our hypothesis that labor market status influences post-pandemic travel frequency was formulated on the basis of research indicating that professional involvement and financial stability are determinants of tourism behavior. Studies show that employees and entrepreneurs travel more frequently because they have more financial resources and opportunities to relax during vacations [
58]. In contrast, unemployed or retired people tend to have more restricted tourism behaviors, being constrained by limited income [
59].
The results of the Chi-square test show a significant association between labor market status and post-pandemic travel frequency. The Pearson Chi-Square value is 37.220, and the associated significance (
p = 0.005) indicates that the relationship between the two variables is statistically significant at a 95% confidence level. Also, the Likelihood Ratio result, with a value of 37.775 and
p = 0.004, supports this conclusion. The linear association between the two variables is marginally significant, with a value of 3.887 and
p = 0.049 (
Table 7).
The results of the symmetric association measures indicate that there is a significant relationship between labor market status and post-pandemic travel frequency.
The Phi value is 0.273, suggesting there is a moderate-intensity association between the two variables.
The Cramer’s V value is 0.158, indicating a moderately weak association.
Both values are statistically significant, with a significance level of p = 0.005, indicating that the association between the variables is not random.
The hypothesis that labor market status influences post-pandemic travel frequency can thus be confirmed.
H5. Residential environment influences preferences regarding means of transport in protected areas.
Our hypothesis that residential environments influence preferences regarding means of transport in protected areas was based on observations that rural and urban residents have different levels of access to means of transport as well as distinct priorities in their choices. Studies have revealed that urban residents prefer fast and convenient means of transport, such as personal cars or airplanes, because of their hectic lifestyles and greater access to infrastructure [
60].
In contrast, people in rural areas may opt for public transport or buses, especially because of financial limitations and reduced access to modern infrastructure [
61].
This hypothesis is important for understanding how residential environments influence tourist behaviors, especially in the context of ecotourism.
The results of the Chi-square test for the association between residential environments and transportation preferences yielded a Pearson Chi-Square value of 7.737, with 3 degrees of freedom (df) and an associated significance (Asymp. Sig.) of 0.052 (
Table 8). This value is very close to the significance threshold of 0.05, but does not exceed it, suggesting that there is no statistically significant association at the 95% confidence level between residential environments and transportation preferences.
The Likelihood Ratio test yielded a value of 9.637, with the same statistical significance of 0.022, which may suggest a weak but significant association between the variables. The Linear-by-Linear Association yielded a value of 4.194 and a significance level of 0.041, indicating a significant linear relationship. In total, 500 valid cases were analyzed, confirming that all available data were used in this analysis.
The results of the symmetric association measures for the relationship between residential environments and transportation preferences yielded a Phi coefficient value of 0.124, with a significance level of 0.052. This result indicates there is a weak association between the variables, and the p-value above the 0.05 threshold suggests that this association is not statistically significant at a 95% confidence level.
The Cramer’s V coefficient, which evaluates the strength of the relationship between the two variables, has the same value of 0.124 and a significance level of 0.052, confirming that the link between residential environments and transportation preferences is weak and statistically insignificant.
The hypothesis that residential environments influence preferences for means of transportation cannot be confirmed, as the results of the association measures (Phi and Cramer’s V) have significance values (p = 0.052) higher than the 0.05 threshold, indicating that the relationship between the two variables is not statistically significant.
H6. Region of residence influences the choice of tourist destination post-pandemic.
Our hypothesis that region of residence influences tourist-destination choice post-pandemic is based on the observation that regional factors, such as geographical proximity, accessibility, and cultural preferences, play essential roles in tourists’ decision to choose certain destinations. Previous research has shown that residents of regions close to mountains or the coast are more likely to prefer regional tourist destinations, while people from more remote regions frequently opt for foreign destinations [
62,
63].
The COVID-19 pandemic altered tourist preferences, driving interest toward closer and safer destinations from a health perspective—a trend that varies across regions of residence [
64,
65]. Testing this hypothesis helps clarify regional tourism dynamics and provides a foundation for adjusting local marketing strategies.
Overall, the Pearson Chi-Square test confirmed that region of residence significantly influences post-pandemic destination choices.
The symmetric association measures for the relationship between region of residence and post-pandemic tourist destinations yielded a Phi coefficient value of 0.340 and an associated
p-value of 0.001 (
Table 9), indicating a moderate association between the two variables and statistical significance.
The Cramer’s V coefficient value is 0.170, which is also statistically significant (p = 0.001), confirming the existence of a relationship between the variables analyzed. Thus, the results suggest that there is a significant association between region of residence and preferences regarding post-pandemic tourist destinations.
H7. Monthly net income influences the budget allocated for eco-tourism products.
Our hypothesis that monthly net income influences the budget allocated for eco-tourism products is based on observations indicating that income level plays a crucial role in shaping consumer behavior, including in the field of eco-tourism. Studies show that people with higher incomes are more willing to allocate more generous budgets for eco-tourism products, considering their quality and sustainability to be priorities [
66].
Eco-tourism products are often more expensive because of environmentally friendly practices and strict sustainability standards, making them more accessible to middle- and high-income groups [
67]. Following the pandemic, higher-income travelers have shown stronger interest in sustainable tourism, preferring high-quality experiences over mass travel [
68].
The Pearson Correlation results indicate that there is a very weak positive correlation between monthly net income and the budget allocated for ecological tourism products (r = 0.052). This correlation is statistically insignificant since the value associated with the probability (
p = 0.248) is higher than the conventional significance threshold of 0.05 (
Table 10). Thus, we cannot conclude that there is a significant relationship between monthly net income and the budget allocated for ecological tourism products.
H8. Practicing ecotourism in protected areas influences satisfaction with tourism resources.
Our hypothesis that practicing ecotourism in protected areas influences satisfaction with tourism resources is based on the premise that tourists’ involvement in ecotourism activities leads to a deeper appreciation of the value and quality of natural resources.
According to recent studies, ecotourism experiences favor the direct connection of visitors with natural and cultural environments, leading to a positive perception of them [
69,
70].
Also, practicing ecotourism involves tourists’ participation in activities that emphasize sustainability and conservation, thereby increasing levels of satisfaction with tourist facilities and resources [
71]. In addition, protected and preserved tourist resources within ecotourism create an authentic experience, improving visitors’ perceptions of the quality and uniqueness of these destinations [
72,
73].
The results of the
t-test indicate the following (
Table 11):
According to the Levene test, homogeneity of variances was not met, since the F value is 14.977 and the associated significance (Sig.) is 0.000 (less than 0.05). Therefore, the t-test results are used for the case where the variances are not equal.
The t-test for independent-samples shows a statistically significant difference between the two groups. The t-value is 7.968, with a degree of freedom (df) of 44.980, and the significance (Sig. 2-tailed) is 0.000, indicating a significant difference between the means at a confidence level of 95%.
The mean difference between the two groups is 1.0382, and the confidence interval for this difference is between 0.7757 and 1.3006, confirming the significance of the difference.
Our hypothesis that practicing ecotourism in protected areas influences satisfaction with tourism resources can be accepted because the difference between the groups that practice and do not practice ecotourism is statistically significant (p = 0.000).
H9. The desire to practice ecotourism influences the duration of visits to protected areas.
Our hypothesis that the desire to practice ecotourism influences the duration of visits to protected areas is based on the premise that a greater interest in ecotourism is associated with deeper involvement and a more extensive allocation of time for exploring natural resources. Studies show that tourists who show an increased desire to participate in ecotourism activities tend to plan longer visits to benefit from a complete experience in protected areas [
74,
75].
Also, the desire to understand and experience nature sustainably leads tourists to spend more time in locations that promote ecotourism, thus giving them the opportunity to interact more closely with its specific elements [
76,
77].
Research indicates that this correlation can be explained by the sustainability and conservation values associated with ecotourism, which require commitment and dedicated time [
78,
79].
The summary of the regression model shows that there is a positive, but weak, correlation between the desire to practice ecotourism and the duration of visits to protected areas, as indicated by the correlation coefficient R = 0.176. The R Squared coefficient (R2) value is 0.031, which means that only 3.1% of the variation in the duration of visits can be explained by the desire to practice ecotourism.
The Adjusted R Squared value, 0.029, confirms that the model explains a similar proportion of the variation, taking into account the adjustment for the number of variables.
The standard error of the estimate is 0.724, indicating the average deviation of the model predictions from the observed values. These results suggest that the relationship between the variables is significant, but of low intensity.
The results of the coefficients in the regression model indicate that the intercept has a value of −0.229, which suggests that when the willingness to practice ecotourism is 0, the duration of visits to protected areas would have this theoretical value. However, this value is not statistically significant (
p = 0.372), which means that the intercept does not contribute significantly to the model (
Table 12).
The regression coefficient for willingness to practice ecotourism is 0.220, indicating that a one-unit increase on the willingness scale corresponds to a 0.220-unit increase in visit duration. This coefficient reached statistical significance (p < 0.001), indicating that there is a real relationship between motivation to practice ecotourism and the length of visits. Meanwhile, the standardized Beta value of 0.176 points to a positive, though relatively weak, association between the two variables.
H10. The possibility of practicing ecotourism influences the frequency of post-pandemic travel.
Our hypothesis that the possibility of practicing ecotourism influences the frequency of post-pandemic travel is based on the premise that the accessibility of ecotourism activities and the specific infrastructure for ecotourism can influence tourists’ travel behavior.
Studies suggest that tourists are more likely to travel frequently to places that offer clear and attractive opportunities to practice ecotourism, especially in the context of post-pandemic concerns related to safety, sustainability, and social distancing [
80,
81].
Furthermore, perceptions of the possibility of carrying out ecotourism activities are often associated with overall satisfaction and the intention to repeat the tourist experience [
82,
83,
84]. In the context of the COVID-19 pandemic, the increased interest in nature-based tourism is considered an emerging trend, suggesting there is a direct link between the possibilities offered by ecotourism and the frequency of travel [
85,
86].
The regression model yielded a correlation coefficient (R) value of 0.055, which indicates an extremely weak relationship between the possibility of practicing ecotourism and the frequency of post-pandemic travel.
The value of the R Squared coefficient (0.003) shows that only 0.3% of the variation in travel frequency can be explained by the possibility of practicing ecotourism. The Adjusted R Squared value, 0.001, confirms that the model does not significantly improve the prediction of travel frequency.
The standard error of the estimate (0.903) suggests a high variability in travel frequency in relation to the predictor. Thus, the model cannot explain the relationship between the variables in a significant manner.
The model-constant value is 2.053, which indicates the average frequency of post-pandemic trips when the possibility of practicing ecotourism is zero.
The coefficient of the variable “possibility of practicing ecotourism” is −0.044, suggesting there is a weak inverse relationship between the possibility of practicing ecotourism and the frequency of engaging in post-pandemic trips. However, this coefficient is not statistically significant, with a
p-value of 0.217 (
p > 0.05), indicating that the independent variable does not have a significant impact on the dependent variable (
Table 13). The results suggest that our hypothesis that the possibility of practicing ecotourism influences the frequency of post-pandemic trips is not supported.
H11. Destination selection criteria influence satisfaction with tourist facilities.
Our hypothesis that destination selection criteria influence satisfaction with tourist facilities is based on the observation that tourists select destinations based on factors such as proximity, cost, service quality, and specific tourist offerings. Research shows that these criteria are correlated with perceptions of overall satisfaction, and choosing destinations that meet tourists’ expectations contributes to a positive experience [
87,
88].
Furthermore, the assessment of satisfaction with tourist facilities directly reflects the extent to which these expectations are met or exceeded [
89,
90]. The importance ascribed to selection criteria is also influenced by previous experiences, income level, and tourist typology [
91,
92].
In the context of the pandemic, factors such as safety and accessibility have become essential in making travel decisions, underlining the relevance of this hypothesis.
The summary results of the regression model show that the R Squared value is 0.010, which indicates that only 1% of the variation in satisfaction with tourist facilities is explained by the criteria for choosing destinations.
The adjusted R Squared value is 0.008, which confirms that this predictor has an almost insignificant influence on the dependent variable. The Std. Error of the Estimate, with a value of 0.8187, indicates considerable variability in the observed values that is not explained by the model.
The results of the regression model coefficients show that the intercept (constant) is 2.857, which represents the average value of satisfaction with tourist facilities when the criteria for choosing destinations are equal to zero.
The unadjusted coefficient for the criteria for choosing destinations is 0.095, indicating that for each unit of increase in this predictor, satisfaction with tourist facilities increases on average by 0.095 (
Table 14). The standardized value of the coefficient (Beta) is 0.101, suggesting a weak positive relationship between the variables.
The t-test associated with the predictor coefficient is 2.271, with a significance level (Sig.) of 0.024, indicating that this relationship is statistically significant at a threshold of 0.05.
H12. The importance of tourism services influences satisfaction with tourism resources.
Our hypothesis that the importance of tourism services shapes satisfaction with natural and cultural resources stems from past research showing that service quality drives overall destination appraisals. High-quality services—including accommodation, infrastructure, guided tours, and on-site facilities—play a direct role in delivering a positive visitor experience [
93,
94].
Furthermore, tourists’ satisfaction with an ecotourism destination’s natural and cultural assets depends heavily on the degree to which supporting services make these resources accessible and usable [
95,
96,
97]. In ecotourism settings, service quality also signals environmental responsibility and sustainability, reinforcing the relevance of this hypothesis [
98].
This coding allows direct interpretation of the relationship between the perceived importance of tourism services and the level of satisfaction with tourism resources, providing a solid basis for applying statistical analyses, such as Pearson correlation, to assess the direction and strength of the relationship between these variables.
The results of the Pearson correlation indicate that there is a weak but statistically significant positive relationship between the importance of tourism services and satisfaction with tourism facilities (r = 0.179,
p < 0.001) (
Table 15). This finding suggests that as respondents consider tourism services to be more important, their satisfaction with tourism facilities tends to increase slightly. The statistical significance (
p < 0.001) confirms that this relationship is not random. The total number of cases analyzed was 500.