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Article

Exploring Awareness and Public Perception towards the Importance of Visual Aesthetics for Preservation of Permanent Forest Reserve (PFR) in Malaysia

1
Department of Landscape Architecture, Faculty of Design and Architecture, Universiti Putra Malaysia, Serdang 43400, Malaysia
2
Department of Resource Management and Consumer Studies, Faculty of Human Ecology, Universiti Putra Malaysia, Serdang 43400, Malaysia
3
Department of Architecture, Faculty of Built Environment, University of Malaya, Kuala Lumpur 50603, Malaysia
*
Author to whom correspondence should be addressed.
Land 2022, 11(8), 1280; https://doi.org/10.3390/land11081280
Submission received: 12 June 2022 / Revised: 8 July 2022 / Accepted: 11 July 2022 / Published: 10 August 2022

Abstract

:
Malaysia has suffered a significant loss of forest cover over the years, mainly due to logging and land clearance for agriculture activities. Although the forest legislation has long been established and continuously enforced, it was not inclusive enough to protect the local natural resources. This study aims to identify public perception and awareness regarding values and essential aspects that affect the preservation of permanent forest reserves (PFR) in Malaysia. In particular, this study investigated the values of visual aesthetics to promote the preservation of Malaysian PFR within the existing legal framework. Results from the survey revealed that the public strongly perceived ecology and research education as the two most important aspects of preserving Malaysian PFR. The study also confirmed that visual aesthetics are considered a crucial aspect of forest classification and preservation beyond people’s health, safety, recreational, and economy. Interm of PFR functions, aesthetic is aslo the third most important factors after protection and research/education.

1. Introduction

Deforestation is considered the main cause of climate change, reduced ecosystem services, biodiversity loss, soil degradation, and other problems affecting human health [1,2]. In addition to excessive logging and extensive agricultural activities, another main reason for the loss of forest areas is due to the sprawl of urbanization [2]. Driven by rapid population and economic growth, these factors have contributed to continuous land-use change leading to the loss of green spaces, especially in urban areas [3,4,5].
Factors that cause deforestation can be classified into five categories: economic, social, political, technological, and cultural [6]. It does not surprise that the absence of comprehensive policies and legislation to protect forest areas remains a complex issue that is still unsolved [7,8,9]. The severity of deforestation could also be associated with a lack of participation in forest management by local communities or the public [7]. Researchers have shown that community involvement can correspond to or provide methods and justifications to increase the protection of forests and biodiversity conservation [2,10].
In Malaysia, deforestation based on the above reasons is also significant. Continuous threats from various human activities have caused tremendous pressure among the decision-makers to balance the need to preserve the natural forest and generate economic revenues [11]. Unfortunately, although the Malaysian forest legislative policy has been established for more than 40 years, it can be considered less inclusive [12]. In particular, the policy only related to four main areas: ecology, the economy, recreation, and research. Other aspects of forest preservation, such as visual aesthetics, remained vague and were not fully emphasized as a valuable factor, even though they have long been considered a strong motivator for protecting natural areas [13]. This ambiguity may be the result of challenges in balancing aesthetic values and economic resource utilization and management [14]. This problem of appraising the visual and environmental aspects was evident in the forest management system.
Therefore, this study investigates aspects of forest preservation within the current Malaysian policy and legislation for permanent forest reserves. Using a bottom-up approach, this study explored identifying public perception towards existing values and aspects of forest preservation as well as including visual aesthetics as a potential factor that could affect the preservation of permanent forest reserves (PFR) in Malaysia (Figure 1). This formulates the basis of three objectives to determine the level of Malaysians’ awareness of the permanent forest reserve system:
  • RO1: To investigate the public awareness of the forest classification types within the Malaysian permanent forest reserve (PFR)
  • RO2: To identify the public perception of important aspects affecting the preservation of the Malaysian permanent forest reserve (PFR).
  • RO3: To verify the hypothesis that aesthetic function is a strong motivator and persuasive reason to increase the preservation of the permanent forest reserve (PFR).

1.1. The General Importance of Forest Preservation

It is essential to preserve natural forests because of their biodiversity richness, complex ecosystem services, and potential to improve human health and well-being [7,15,16]. In addition to ecological and social importance, the beauty of the forest environment can also be a significant motivation for forest preservation, particularly as a tourist attraction that serves social and economic objectives [17,18]. For instance, a natural forest reserve within the urban environment could protect wildlife habitat and natural landscape elements in addition to preserving local biodiversity [19,20]. It also promotes noise reduction, carbon sequestration, air purification, temperature management, healthy lifestyles, and flood control, which can lead to the creation of more sustainable cities [21,22].
Peoples’ roles in the transformation of land cover and deforestation has been one of the primary causes of land-use change [23,24,25,26]. Such changes contributed to existing environmental problems such as air pollution, flooding, landslides, and increasing temperatures. As an example, in the early 1990s, the Earth’s surface temperature increased by 17%, and this was attributed mainly to the loss of 16 million hectares of forest per year [27,28,29,30]. Consequently, these problems could threaten the future existence of human life as well as the extinction of flora and fauna. Without serious intervention, the forest ecosystem and its long-term survival could be jeopardized [7,31,32]. Despite many widespread consequences of forest degradation, natural forests are still being cleared to accommodate the needs of urban expansion and other human activities [33,34].

1.2. The Role of Local Communities in Forest Preservation

Understanding public oppinions towards protected areas is crucial because it could reveal essential aspects of preservation. Local concerns associated with forest ecosystems indicate that they have a vital role in the planning and execution of resource management activities, particularly if these activities are environmentally, socially, and economically sustainable [35]. It also enables proper documentation of local concerns that can be included in future forest management decisions and improve the preservation process’s efficiency [36,37]. Nevertheless, it is also important for the local public and communities to be exposed to other essential environmental issues in order to be actively involved in environmental management decisions [38]. In addition, preservation policies could not be effectively enforced or implemented without active participation by local communities through forest management initiatives [7].
Most conservationists agree that protected areas are doomed to failure unless local communities engage to some degree in conservation efforts [39]. Thus, it is not surprising that local community roles in managing forests and the surrounding areas have been recognized globally [35,40,41]. Such strategies of community engagement are known as “community conservation” or “participatory management” [36,42]. They aim to improve the relationship between protected areas and the local community by increasing the community’s involvement in resource management and, at the same time, improving their economic status [37]. It is crucial to note that such social issues significantly impact forest management decision-making. Hence, the preservation of forests based on ecological importance and the opinions of local communities provide a basis for decision-makers to develop more effective strategies for forest conservation and development [2,40,41].

1.3. Legislative Aspects of the Preservation of Permanent Forest Reserve (PFR) in Malaysia

In Malaysia, the National Forest Policy (NFP) was initiated in 1977 and approved by the National Land Council in 1978. One of the essential functions of the National Forest Policy is to identify permanent forest reserves in appropriate areas strategically located throughout Malaysia [43]. In 1992, amendments to the legislation were made to further highlight the conservation of forest biodiversity, the role of local communities in forest development, and genetic resource management.
Apart from the NFP, Malaysia’s state governments are allowed to reserve (gazette) any forest area under the National Forestry Act 1984 [43]. Nevertheless, this protection was limited and not large-scale, which has led to the loss of many forest areas [3]. Consequently, forests in Malaysia, particularly natural forests in urban areas (including gazetted areas), continuously receive threats from urban development [4]. Based on the 1990–2018 Malaysian Ministry of Energy and Natural Resources land area survey (Table 1), the loss of forested areas was found to be significant [44]. The results are similar to the Department of Forestry of Peninsular Malaysia’s annual reporting of statistics regarding types of permanent forest reserves [43]. It is worth mentioning, underscoring the concern expressed in this study, that the ministry reported a loss of 0.10 million hectares between 2011 and 2020, especially given that these lands are preserved under PFR, as shown in Table 2.

2. Materials and Methods

Using the online Qualtrics Survey tool, the questionnaire was distributed using a snowball sampling (non-random) approach through various social media platforms over 14 days. The survey was divided into two parts: (A) Questions that assess respondents’ understanding of permanent forest reserves (PFRs) and (B) questions about each respondent’s demographic.
Part A consisted of six questions designed to assess the public’s knowledge of the permanent forest reserve system based on policy used by the Department of Forestry of Peninsular Malaysia (FDPM). FDPM is responsible for the management, protection, planning, and development of PFRs. The PFR is typically classified into six types of forest: inland forest, peat swamp forest, mangrove forest, plantation forest, state land forest, or national and wildlife forest. The PFR is also classified into four categories depending on its function. Protection forests are forests for mitigating impacts of local/regional climatic conditions; water resource management; conservation of flora and fauna diversity; environmental quality; and flood damage mitigation. Work forests are industrial forests producing forest products and supplying raw materials for agriculture, industry, and exports. Amenity forests are intended to increase and attract tourists and provide recreational activities such as camping and mountain hiking. Research and education forests are areas of benefit for scientific research and education, especially to further knowledge of biodiversity and natural forest ecosystems. Based on these classifications, Malaysia’s permanent forest reserve can be structured as shown in Figure 2.
In this section, respondents were asked to which extent they understood the PFR system and how frequently they visited this kind of forest reserve. Furthermore, a question surveyed their understanding of different forest types classified under the PFR definitions. We also asked about the most important aspects of preserving PFRs and probed whether aesthetics should be included as crucial aspects and values toward permanent forest reserves in Malaysia. Details of the questionnaire used in the online survey are shown in Figure 3.
Part B contained seven general questions on citizenship, gender, age, ethnicity, educational level, marital status, and home address. Results from the survey were analyzed using SPSS for statistical analysis to determine the final mean and test the reliability of the selected aspects and values. In addition, the independent samples Kruskal–Wallis test was used to validate the aesthetic hypothesis and comprehend the variances in reactions among demographic groupings.

3. Results

3.1. Descriptive Statistics for Demographic Results

From the 219 people who participated in the study, only 204 respondents completed the survey, yielding a response rate of 93.15%. Based on the final number of the respondents, 97.04% were Malaysian citizens; of these, 59.31% identified as Malay ethnic origin, reflecting the demographic composition of the Malaysian community as a whole. It is worth noting that the proportion of female participants (58.82%) was slightly higher than that of male participants (41.18%). The majority of participants (62.25%) were single. Half of the respondents were younger than 30 years of age. Regarding the highest education level achieved, 85.29% of the participants had completed education at the bachelor’s degree or postgraduate level. Furthermore, about half (50.98%) of the respondents lived in urban areas. In general, this study found that most respondents were Malaysian citizens, most of whom had completed university studies, and their ages represented a mix between younger and older people, as shown in Table 3.

3.2. Descriptive Statistics for Public Perception towards Permanent Forest Reserves (PFRs)

The survey found that the level of awareness regarding PFR among the respondents can be considered high. To our surprise, 66.18% answered “yes”, 9.80% stated “no”, and 24.02% answered “maybe”, as shown in (Figure 4). Most of the respondents (refer to Table 4) identified wildlife forest, inland forest, mangrove forest, peat swamp forest, and forest plantations as major types of PFR. They also stated that botanical and public parks do not form types of permanent forest reserve (PFR), which confirmed our earlier assumption. The public is generally familiar with PFR and its forest classification and its types, though there was a slight difference in their understanding of timber production forests. One likely explanation is that they possibly believe PFRs are dedicated only to forest preservation rather than purposely preserving them to manufacture wood products.
Additionally, nearly two-thirds (66.18%) of the respondents confirmed that they had visited a PFR, more than half (58.33%) had visited a PFR two to three times a year, and 6.86% of respondents stated they visited at least one or more PFRs monthly. The results revealed that the respondents had good sense and vision to respond to important aspects of protecting permanent forest reserves. Although the survey respondents asserted that all aspects were significant in preserving forests, they prioritized the aspects of ecological importance, research/educational importance, aesthetic/natural beauty importance, and human health/well-being importance. While respondents generally underestimated the value of economic importance compared with other aspects, the overall rating of the last aspect scored higher than the average. The reliability of the statistical analysis on all aspects was tested using the Cronbach Alpha SPSS, and the results were >0.8, indicating high reliability. These results are shown in Table 5.
Respondents confirmed the validity of their important aspects of the preservation by assessing the importance of statements for the protection of permanent forest reserves. The highest values reported were “preserve forest biodiversity”, “source of freshwater”, “conserve large diversity of flora and fauna”, and “influence local/regional climatic conditions.” On the other hand, it was found that the lowest values were given to “provide raw materials for furniture products”, “timber supply for building materials”, and “a place for a picnic with the family”. The reliability statistics were measured for these aspects also, using Cronbach Alpha SPSS, and the results were >0.8, indicating the reliability of the statistical tests. These results are shown in Table 6.
Data were also collected based on groups that define the protection of the permanent forest reserve by function. These included the four functions already set out in the Malaysian PFR legislation (protection, research and education, amenity, work/economic forest) and the aesthetics function as a fifth protection aspect. The results from the survey responses confirmed the value of the existing classification of the important aspects mentioned above. These results are shown in Table 7.
Again, based on the findings of this survey, one of the most important aspects of preserving permanent forest reserves is aesthetic/natural beauty. As seen in Table 6 and Table 7, this was confirmed by adding the aesthetic function as an important aspect of enhancing the preservation of the permanent forest reserve. The results support our assertion that the hypothesis is reliable and suggests that adding the aesthetic/natural beauty aspect to the PFR evaluation criteria would enhance the PFR legislation.

3.3. Verification of the Hypothesis and Perceptual Differences between Demographic Groups

We investigated the premise that beauty is a powerful motivation and compelling cause to improve Malaysia’s conservation of permanent forest reserves (PFRs). From the analysis using the Shapiro–Wilk and Kolmogorov–Smirnov tests, the data deviated from the normal distribution, i.e., the null hypothesis for all demographic data was significant (p < 0.05). Thus, it could be concluded that the data were not normally distributed, and non-parametric analytical tests needed to be used. The same test was performed for Group C (Aesthetic), and the results were almost identical to the above, where all data were significant (p < 0.05) except for some of the sub-category data. Namely, in the division of ethnicity, the p-value was higher for the groups Indians and Others (Kolmogorov–Smirnov = 0.105, 0.200; Shapiro–Wilk test, W = 0.321, 0.113). Differences in the p-value were also found in the education level, specifically for those whose highest educational attainment was a high school certificate and those with a doctorate (Kolmogorov–Smirnov = 0.200, 0.186; Shapiro–Wilk = 0.539, 0.267). However, none of the demographic data indicated a total acceptance of the null hypothesis. As a result, we concluded that the data were not normally distributed and that a non-parametric analytical test was required.
For the non-parametric test, independent samples were conducted to investigate the statistical significance of perceptual differences between different demographic groups. Responses to questions were tested by grouping them into respondents’ demographic attributes based on gender and marital status, living area, education, age, and ethnic group.
The results were tested using the independent samples Kruskal–Wallis test, and descriptive statistics tables of responses pertaining to the survey questions were established (“How much do you agree that permanent forest reserves (PFRs) should be protected because of important aspects?”) We tested the aesthetic/natural beauty importance aspect. An analysis of the results indicated a statistical difference between the four ethnic groups (Malay, Chinese, Indian, and Other, which represents smaller groups of ethnicities in Malaysian) in their responses to aesthetic/natural beauty importance. A p-value of 0.004 indicated that the null hypothesis was rejected. A significant difference was found between the groups Others and Malay (p = 0.001) in their rating of aesthetic/natural beauty importance. This indicates that respondents in the Malay group agreed more strongly that PFRs should be protected based on the importance of their aesthetic/natural beauty, as shown in Table 8 and Figure 5.
Similarly, the independent samples Kruskal–Wallis test was conducted to understand perceptual differences between demographic groups’ responses to the questions (“How do you rate the importance of the statements regarding values of permanent forest reserve PFR in Malaysia, toward forest function?”). When we tested the aesthetic function, the analysis results indicated a statistical difference between the three living areas (urban area, semi-urban area, and rural areas) in the responses toward the aesthetic function; a p-value of 0.003 indicated that the null hypothesis should be rejected. The significance was found between urban area and semi-urban area (p = 0.018), and between urban area and rural area (p = 0.003), in the importance values for the aesthetic function. This indicates that people living in rural and semi-urban areas are more likely to agree on the importance of the aesthetic function in protecting PFRs than those living in urban areas, as illustrated in Table 9 and Figure 6.

4. Discussion

This research has revealed three major aspects that need to be considered in the discussion and should be explored in detail. First, data from previous research and government statistics on Malaysia’s permanent forest reserve have shown that forest reserve areas are declining despite being protected under the existing legislation. The same pattern can also be observed for forest areas not subject to the same legal protection as permanent forest reserves. Similar to the Sabah and Sarawak regions (East of Malaysia, Borneo Island), Peninsular Malaysia constantly suffers deforestation caused by urban expansions and other economic reasons. Ref. [45] stated that although one the main essences of PFRs are to limit the rate of forest loss, protection efforts are still being influenced by political decisions that prefer to maximize forest contributions towards the Malaysian economy. Statistics reported by the Forestry Department of Peninsular Malaysia (FDPM) indicated a shortage of 0.10 million hectares of permanent forest reserve area between 2011 and 2020. The decline in permanent forest reserves appears to be continuing for several reasons, the most important of which are the gap in forest protection laws and the difficulty of implementing these laws [3,4].
Second, the study proved there is awareness of PFRs in the community and that the public favors preserving PFRs in Malaysia. The results of this study show that the respondents understand and are aware of different types of forests classified under permanent forest protection laws in Malaysia. Their answers to the forest classification questions are identical to those provided by the Department of Forestry of Peninsular Malaysia. We also concluded that the respondents had two concerns. First, regarding forests being cleared and converted into consumer products, such as furniture and construction materials, which is the main reason for rating the economic aspect as being of lower importance than other aspects, this runs contrary to the preservation of the permanent forest reserve. The second explanation is the fear of visiting of family and of children. Their fear for children may be attributed to the nature of the terrain, which necessitates a significant deal of effort for a picnic, which reduces their social aspect perspective in the forest area. This indicates that Malaysians are generally aware of the issue of forest protection in Malaysia. This confirms the validity of the statement that the adoption of the views of local communities provides a basis for decision-makers to develop strategies for forest conservation and management [2,35,40,41].
Third, the natural beauty of forests offers motivation to protect the environment, while its quality gives pleasure to the senses. In some countries, aesthetic values are included in the decision-making process for forest management [17]. In this study, visual aesthetics was rated as one of the most important aspects of preserving a permanent forest reserve besides ecological function, research and education, and human health and well-being. Ref. [13] confirmed that the visual aesthetics aspect of natural forests is an important incentive for preserving permanent forest reserves. Visual aesthetics value plays an important role in the preservation and protection of forest areas deemed exceptionally beautiful, and this result corresponds to [13,17,46,47]. Finally, this study showed that aesthetics are an important aspect that can be added to the current legislation to enhance forest protection. To further preserve forest, there is a need to establish unique aesthetics assessment systems that reflect local awareness and perception.

5. Conclusions

The continuing shortfall in the permanent forest reserve in Malaysia can be attributed to a lack of inclusiveness in forest protection policies. This study revealed that aesthetics are important aspects of forest preservation in addition to the importance of ecological and research/educational and human health/well-being. On the other hand, respondents downplayed the economic aspect’s role in preserving forests. They believed that the economic needs caused deforestation, leading to other problems affecting various aspects of people’s lives. The findings of this research suggest that adding the aesthetics aspect to the classification of PFR functions in Malaysia could benefit the continued protection of these forest areas. Hopefully, it will enhance the preservation of the permanent forest reserves in Malaysia and aid the policymakers’ understanding of aesthetics as a catalyst for the protection of natural areas.

Author Contributions

Conceptualization, R.M. and S.A.B.; methodology, R.M. and A.A.-S.; software, S.O.; validation, M.J.M.Y. and S.M.; formal analysis, S.O. and H.G.; investigation, S.A.B.; writing—original draft preparation, R.M.; writing—review and editing, S.A.B.; visualization, R.M. and S.A.B.; supervision, M.J.M.Y. and S.M. All authors have read and agreed to the published version of the manuscript.

Funding

This research received no external funding. The APC was funded by Scenic America.

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

Not applicable.

Conflicts of Interest

The authors declare no conflict of interest.

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Figure 1. The framework of this study.
Figure 1. The framework of this study.
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Figure 2. Classification of PFR by forest type, function, and legislative aspect in Peninsular Malaysia.
Figure 2. Classification of PFR by forest type, function, and legislative aspect in Peninsular Malaysia.
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Figure 3. Formulation of survey questions based on the research objectives.
Figure 3. Formulation of survey questions based on the research objectives.
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Figure 4. Level of respondents’ knowledge about the permanent forest reserve system in Malaysia.
Figure 4. Level of respondents’ knowledge about the permanent forest reserve system in Malaysia.
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Figure 5. Independent samples Kruskal–Wallis test between aesthetic/natural beauty importance and ethnic groups.
Figure 5. Independent samples Kruskal–Wallis test between aesthetic/natural beauty importance and ethnic groups.
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Figure 6. Independent samples Kruskal–Wallis test between aesthetic function and living area groups.
Figure 6. Independent samples Kruskal–Wallis test between aesthetic function and living area groups.
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Table 1. Forest statistics collected by the Ministry of Energy and Natural Resources between 1990 and 2018 in Malaysia, by region.
Table 1. Forest statistics collected by the Ministry of Energy and Natural Resources between 1990 and 2018 in Malaysia, by region.
YearArea (Million Hectares)
Peninsular MalaysiaSabahSarawakTotal
19906.274.448.0718.78
20005.914.427.6217.95
20105.864.437.6817.97
20185.754.767.7418.25
Table 2. Forest statistics collected by the Department of Forestry of Peninsular Malaysia for 2011 and 2020.
Table 2. Forest statistics collected by the Department of Forestry of Peninsular Malaysia for 2011 and 2020.
Land Area of Peninsular MalaysiaArea (Million Hectares)
20112020
Forested Area5.815.69
Non-Forested Area7.377.53
Permanent Forest Reserve (PFR)4.914.81
Permanent forest reserved by forest type
Inland Forest4.394.34
Peat Swamp Forest0.240.25
Mangrove Forest0.100.09
Plantation Forest0.180.12
State Land Forest0.310.28
National and Wildlife Forest0.590.51
Permanent forest reserved by forest function
Protection Forest1.991.84
Production Forest2.922.97
Amenity Forest--
Research and Education Forest--
Table 3. Background of respondents.
Table 3. Background of respondents.
Category Sub-CategoryPercentage (%)Frequency (n)
Malaysian citizen1Yes97.06%198
2No2.94%6
Gender1Male41.18%84
2Female58.82%120
Age118–2950.00%102
230–3930.39%62
340 and above19.61%40
Ethnicity1Malay59.31%121
2Chinese24.51%50
3Indian7.84%16
4Others8.33%17
Education level completed1High school certificate5.88%12
2Diploma8.82%18
3Bachelor’s degree54.90%112
4Master’s degree25.00%51
5Doctorate5.39%11
Marital status1Single62.25%127
2Married37.75%77
Living area1Urban area50.98%104
2Semi-urban area38.73%79
3Rural area10.29%21
Table 4. Levels of knowledge about permanent reserved forests by type.
Table 4. Levels of knowledge about permanent reserved forests by type.
PFR by TypeYesQtyMaybeQtyNoQty
1Wildlife forest90.20%1846.37%133.43%7
2Inland forest87.75%17910.78%221.47%3
3Mangrove forest84.80%17311.27%233.92%8
4Peat swamp forest75.49%15416.67%347.84%16
5Forest plantation70.10%14315.20%3114.71%30
6Timber production forest44.12%9021.08%4334.80%71
7Botanical park36.76%7520.10%4143.14%88
8Public park16.67%3418.63%3864.71%132
Table 5. The opinions of the respondents on the important aspects of the preservation of PFRs in Malaysia.
Table 5. The opinions of the respondents on the important aspects of the preservation of PFRs in Malaysia.
Important Aspects of the Preservation of PFRs in MalaysiaMean *Reliability Statistic (Cronbach Alpha) **
1Ecological importance4.640.831
2Research/educational importance4.420.822
3Aesthetic/natural beauty importance4.390.826
4People’s health/well-being importance4.190.813
5National safety/security importance3.880.846
6Recreational/social importance3.780.832
7Economic importance3.600.857
Total 0.853
(*) The mean is between 1.00 and 5.00, where the minimum is 1.00 = strongly disagree, the middle is 3.00 = neither agree nor disagree, and the maximum is 5.00 = strongly agree. (**) Cronbach’s alpha reliability coefficient ranges typically between 0 and 1, where coefficients closer to 1 indicate the presence of higher reliability, and coefficients closer to 0 indicate lower reliability.
Table 6. Means and reliability statistics for values of the preservation of PFRs in Malaysia.
Table 6. Means and reliability statistics for values of the preservation of PFRs in Malaysia.
The Item on PFR Values in MalaysiaMean *Reliability Statistics (Cronbach Alpha) **
1Preserve forest biodiversity4.760.821
2Source of fresh water4.690.821
3Conserve large diversity of flora and fauna4.630.822
4Influence local/regional climatic conditions4.610.826
5Contain unique formation of forest species (e.g., size, shape)4.490.821
6Mitigate floods4.470.817
7Educate people about the natural biodiversity4.440.815
8Vast potential for scientific research4.420.818
9Field laboratory for teaching and learning4.260.814
10Various hierarchies of landforms (e.g., ridges, valleys)4.250.816
11Offer iconic natural viewpoints and features (e.g., waterfalls, cliffs)4.240.811
12Present varieties of natural color composition3.880.806
13Opportunity to conduct bird watching3.450.801
14Production of agriculture products3.450.813
15Provide jungle trekking or mountain hiking experience3.380.814
16It can be turned into a forest plantation3.200.816
17Conducive space for outdoor camping3.150.805
18Provide raw materials for furniture products2.720.810
19Timber supply for building materials2.700.808
20A place for a picnic with family2.560.818
Total 0.823
(*) The mean is between 1.00 and 5.00, where the minimum is 1.00 = not important, the middle is 3.00 = moderately important, and the maximum is 5.00 = highly important. (**) Cronbach’s alpha reliability coefficient ranges typically between 0 and 1, where coefficients closer to 1 indicate the presence of higher reliability, and coefficients closer to 0 indicate lower reliability.
Table 7. The preservation group of permanent forest reserves by function.
Table 7. The preservation group of permanent forest reserves by function.
PFR by FunctionThe Item on PFR Values in MalaysiaIndividual MeanAverage Mean *
1Group A
(Protection)
Source of fresh water4.694.60
Conserve large diversity of flora and fauna4.63
Influence local/regional climatic conditions4.61
Mitigate floods4.47
2Group B
(Research and Education)
Preserve forest biodiversity4.764.47
Educate people about the natural biodiversity4.44
Vast potential for scientific research4.42
Field laboratory for teaching and learning4.26
3Group C
(Aesthetic)
Contain unique formation of forest species (e.g., size, shape)4.494.22
Various hierarchies of landforms (e.g., ridges, valleys)4.25
Offer iconic natural viewpoints and features (e.g., waterfalls, cliffs)4.24
Present varieties of natural color composition3.88
4Group D
(Amenity/Recreational)
Opportunity to conduct bird watching3.453.14
Provide jungle trekking or mountain hiking experience3.38
Conducive space for camping3.15
A place for a picnic with family2.56
5Group E
(Work/Economic)
Production of agriculture products3.453.02
It can be turned into a forest plantation3.20
Provide raw materials for furniture products2.72
Timber supply for building materials2.70
(*) The mean is between 1.00 and 5.00, where the minimum is 1.00 = not important, the middle is 3.00 = moderately important, and the maximum is 5.00 = highly important.
Table 8. The difference in responses to aesthetic/natural beauty importance between ethnic groups.
Table 8. The difference in responses to aesthetic/natural beauty importance between ethnic groups.
Null HypothesisTestSignificanceDecision
The distribution of responses to Aesthetic/natural beauty importance is the same across categories of ethnicity.Independent samples Kruskal–Wallis test0.004 *Reject the null hypothesis
Pairwise Comparisons of Ethnic Groups
Dependent VariableSample 1–Sample 2Std. Test StatisticSignificance
Aesthetic/natural beauty importanceOthers–Malay3.2930.001 *
Note: (*) the asterisk indicates the significance level is 0.05. Each row tests the null hypothesis that the Sample 1 and Sample 2 distributions are the same.
Table 9. The difference in responses to aesthetic function between living area groups.
Table 9. The difference in responses to aesthetic function between living area groups.
Null HypothesisTestSignificanceDecision
Group C–Aesthetic Function distribution is the same across Living Area categories.Independent samples Kruskal–Wallis test0.003 *Reject the null hypothesis
Pairwise Comparisons of Ethnic Groups
Dependent VariableSample 1–Sample 2Std. Test StatisticSignificance
Group C Aesthetic FunctionUrban area–Semi-urban area−2.3760.018 *
Urban area–Rural area−2.9510.003 *
Note: (*) the asterisk indicates the significance level is 0.05. Each row tests the null hypothesis that the Sample 1 and Sample 2 distributions are the same.
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Mundher, R.; Abu Bakar, S.; Maulan, S.; Mohd Yusof, M.J.; Osman, S.; Al-Sharaa, A.; Gao, H. Exploring Awareness and Public Perception towards the Importance of Visual Aesthetics for Preservation of Permanent Forest Reserve (PFR) in Malaysia. Land 2022, 11, 1280. https://doi.org/10.3390/land11081280

AMA Style

Mundher R, Abu Bakar S, Maulan S, Mohd Yusof MJ, Osman S, Al-Sharaa A, Gao H. Exploring Awareness and Public Perception towards the Importance of Visual Aesthetics for Preservation of Permanent Forest Reserve (PFR) in Malaysia. Land. 2022; 11(8):1280. https://doi.org/10.3390/land11081280

Chicago/Turabian Style

Mundher, Riyadh, Shamsul Abu Bakar, Suhardi Maulan, Mohd Johari Mohd Yusof, Syuhaily Osman, Ammar Al-Sharaa, and Hangyu Gao. 2022. "Exploring Awareness and Public Perception towards the Importance of Visual Aesthetics for Preservation of Permanent Forest Reserve (PFR) in Malaysia" Land 11, no. 8: 1280. https://doi.org/10.3390/land11081280

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