Urban humans and biodiversity-related concepts are interacting with each other in many negative and positive ways. The biodiversity provides a wide array of provision and cultural-ecological services to urban residents, but it is being overexploited to the point of crisis. The crisis is largely driven by the expanding illegal wildlife trade in developing countries with a high urbanization rate and biodiversity level like Vietnam. While supply-side measures are ineffective in reducing biodiversity loss, researchers have suggested demand-side measures as supplements, such as social marketing campaigns and law enforcement in urban areas. Moreover, urban residents are also potential visitors to urban public parks and national parks, which helps generate finance for biodiversity preservation and conservation in those places. Understanding how urban residents' perceptions towards biodiversity and biodiversity-related behaviors can help improve the effectiveness of conservation efforts and sustainable urban development. Thus, this article presents a data set of 535 urban residents' wildlife consumption behaviors, multifaceted perceptions and interactions with biodiversity-related concepts, and nature-based recreation demand. The data set is constructed with six major categories: 1) wildlife product consumption, 2) general biodiversity perceptions, 3) biodiversity at home and neighborhood, 4) public park visitation and motivations, 5) national park visitation and motivations, and 6) socio-demographic profiles. These resources are expected to support researchers in enriching the lax literature regarding the role of urban residents in biodiversity conservation and preservation, and help policymakers to find insights for building up an “eco-surplus culture” among urban residents through effective public communication and policymaking.

Biodiversity loss is happening at an unprecedented rate. Since 1970, the population sizes of mammals, fish, birds, amphibians, and reptiles have declined rapidly by 68% on average [1]. The Intergovernmental Science-Policy Platform on Biodiversity and Ecosystem Services (IPBES) reports that around 1 million species are threatened with extinction [2]. Among 35 biodiversity hotspots, the Indo-Burma hotspot is in the top five most threatened places, with only 5% of the natural habitat remaining and the highest human population compared to other hotspots [3]. Being located in the Indo-Burma, the disappearing rate of endemic species in Vietnam is also alarming. In particular, Vietnam Red List in 2007 identified 882 threatened and endangered species (418 animals and 464 plants), showing an increase of 22.33% (161 species) compared to the first published Vietnam Red List in 1992 [4].

The interactions between urban ecosystems and biodiversity are multiplex, so do the relationship between urban humans and biodiversity-related concepts. While urban residents' demand for wildlife products is one of the major causes of biodiversity loss, the associations between biodiversity-related concepts and humans urban ecosystem need further research to not only improve urban people's quality of life and education but also facilitate biodiversity preservation and conservation. The current data descriptor, thus, presents a data set of multifaceted interactions between urban residents and biodiversity-related concepts in Vietnam–a highly urbanized developing country with a rich biodiversity level. Specifically, the data set is valuable for studying urban people's wildlife product consumption behaviors, perceptions, and interactions with biodiversity across different levels (individual, home, neighborhood, and public park), and nature-based recreation demand.

To reduce the biodiversity loss rate, the Vietnamese government has demonstrated a great commitment to biodiversity protection and conservation by implementing national strategic plans, programs, and initiatives [5]. Conservation of ecosystems, endangered, rare, and precious species and genetics is one of the government's main objectives. In particular, the government released Decree 32/2006/ND-CP and Decree 82/2006/ND-CP to prohibit harvest, trade, use, and consumption of all protected species [6]. However, efforts controlling the supply side in the wildlife trade network seem to be ineffective due to several reasons [7, 8]: 1) slow and inadequate law enforcement and policy implementation, 2) lacking resources for monitoring and management, such as manpower, funding, and equipment, 3) corruption among influential people, 4) conflicts of conservation initiatives and programs with local livelihoods, and 5) the increasingly organized and expanded criminal networks.

Given these challenges, many scientists have suggested paying more attention to tackling the wildlife consumption demand, particularly among the middle class in urban areas. The consumption of wildlife products in Vietnamese urban areas is prevalent with multiple purposes, such as traditional medicines (tiger bones, bear bile, etc.) [9, 10], wildmeat [11, 12], and petting [13], but legal mechanisms are still missing [12]. Social marketing campaigns have also been suggested as a potential method to reduce the consumption demand of wildlife products or redirect it to herbal substitutes [6, 14, 15]. Understanding how biodiversity perceptions influence wildlife product consumption behaviors can help improve the effectiveness of public communication and law implementation in urban areas.

Biodiversity-friendly environments are inextricably associated with sustainable urban concepts and human well-being [16], as they provide a wide range of provision and cultural ecosystem services, maintain human's connection to nature, increase aesthetic appreciation and inspiration, and improve physical and mental health [17, 18, 19]. Given such benefits of biodiversity, international organizations and scholars call for the conservation and preservation of biodiversity in cities for the sake of sustainability. For example, the Intergovernmental Panel on Biodiversity and Ecosystem Services and the United Nations Habitat call to integrate biodiversity notions into human settlements [20, 21]. Opoku suggests that biodiversity conservation needs to be an integral component of the built environment's policies and strategies towards sustainable development [22]. Recognizing urban residents' perceptions and interactions with biodiversity is vital to gain public acceptance and support in developing biodiverse urban environments, specifically in residential areas and public parks [23, 24].

Nature-based recreation is another notion in which biodiversity-related concepts and urban residents can be closely linked together. Nature-based recreation is defined as “all forms of leisure that rely on the natural environment” [25]. As “nature” refers to any outdoor areas with greenery or natural features, the urban residents' demand for nature-based recreation can be met through urban green spaces (e.g., public parks, gardens, or neighborhood) and protected area visitations [26]. Urban public parks are cohabitation places between city dwellers and nature, whereas protected areas are designated for conservation and nature-based tourism. The high biodiversity levels in urban public parks and protected areas positively influence the visitors' psychological well-being [19, 26, 27, 28]. In return, the increasing demand for nature-based recreation might generate sustainable finance for biodiversity conservation in protected areas and preservation in urban public parks [29, 30]. In particular, it is reported that urban residents in Mekong Delta are willing to pay around $11 million per year for biodiversity conservation activities in the nearby protected area [31]. Comprehending how urban residents' perceptions of biodiversity are linked to their visitation behaviors, motivations, and financial contribution can enhance monitoring, management, and regulation effectiveness in urban green spaces and protected areas. Given the above reasons and the lack of related studies and resources in a developing country like Vietnam, data of urban residents' biodiversity perceptions and biodiversity-related behaviors are necessary. The current data descriptor provides a detailed explanation for the data set of wildlife consumption behaviors, multifaceted perceptions and interactions with biodiversity-related concepts, and nature-based recreation demand among urban Vietnamese residents. The data set comprises six major categories: 1) wildlife product consumption, 2) general biodiversity perceptions, 3) biodiversity at home and neighborhood, 4) public park visitation and motivations, 5) national park visitation and motivations, and 6) socio-demographic profiles. Such valuable resources are expected to enable studies about the human-biodiversity interactions in multiple aspects and provide insights for conservation and urban development policymaking, monitoring, management, and regulation. 2.1 Survey Design and Validation The survey was systematically designed with five major steps: (1) questionnaire design, (2) survey collection, (3) data check and validation, (4) data set generation, and (5) data analysis. First, as there is a lack of qualitative research on biodiversity perceptions among Vietnamese urban people, an in-depth semi-structured interview was conducted to set the stage for questionnaire design. Specifically, 38 urban residents at the two largest cities (Ho Chi Minh City and Hanoi Capital City) in Vietnam were interviewed from November 15 to December 26, 2020. The interviewees were purposively chosen to diversify opinions according to their gender, age, occupations, and prior experiences with nature. When the “theoretical saturation” point was met, the interview was stopped [32]. Based on the interviewed results, the questionnaire was constructed with the six major categories. 1. Wildlife product consumption 2. General biodiversity perceptions 3. Biodiversity at home and neighborhood 4. Public park visitation and motivations 5. National park visitation and motivations 6. Socio-demographic profiles The data were collected through a Web-based survey via Google Forms using a snowball sampling strategy. Google Forms was employed due to its user-friendly interfaces, confidentiality, and easy distribution [33]. The collection happened approximately two months, from June 18 to August 8, 2021. Even though the distribution was targeted at people living in Ho Chi Minh City and Hanoi Capital City, several respondents from other provinces and cities also participated in the survey. At the beginning of the questionnaire, respondents were required to read and agree with the consent form, which stipulates the research purposes, questionnaire contents, and confidentiality of participants. Two hundred random participants who completed the questionnaire were given a gift card with a value ranging from US$1 to US \$10 through their email addresses. Eventually, 581 people got involved in the data collection.

Next, to ensure the data set quality, a four-step quality check was performed. First of all, a certain number of questionnaire respondents were from other provinces that were not urban, so their responses were excluded from the data set based on the residency they reported. Secondly, children whose age was less than 18-year-old were also excluded from the data set as their agreement to the consent form was not legitimate without guardians' acceptance. Thirdly, based on the reported email addresses, duplicate responses were detected and removed afterwards.

Finally, “straightlining” and “select-all” behavior can distort the analysis results [34], so any respondents giving identical answers to a set of questions using the same response scale and selecting all answers of checkbox questions simultaneously were excluded. Although responses with solely “straightline” answers were not excluded, they were marked “warning” in the Quality Assessment column at the end of the data set. In detail, 27 responses were removed due to inappropriate residency; 13 were removed due to insufficient age; three were removed due to repeated reporting; three were removed due to their simultaneous “straightlining” and “select-all” behaviors. Eventually, 535 responses were included in the cleaned data set.

All four steps of the quality check were completed in the Microsoft Excel spreadsheet (xls.) file downloaded from Google Form. After cleaning the data, all the responses were encoded and saved under comma-separated value format for easing later uses. During this step, any missing data were coded as “NA” (a.k.a “Not Applicable”). The data set would be validated using Bayesian analysis in the later section.

2.2 Data Sample

Most respondents were from the two largest cities in Vietnam: 347 people from Ho Chi Minh City (accounting for 64.86%) and 107 people from Hanoi Capital City (accounting for 20%). The remaining respondents (15.14%) came from other urban areas, like Hue city, Vung Tau city, and Thanh Hoa city. Among 535 responses, female participants constituted a greater proportion than male participants (58.31% of females versus 41.12% of males). The average mean age of all participants was around 33.80. The educational level of participants was relatively high, as 85.05% of them acquired an undergraduate (63.18%) or post-graduate levels (21.87%).

The occupational backgrounds of participants were highly diverse, ranging from accountant, activist, actor to retiree and employee. The income of most participants (39.24%) fell into the range from 5 million to 15 million VNĐ monthly. No-income participants consisted of 4.11% of the total number, whereas the percentage of participants acquiring more than 30 million VNĐ monthly was 7.48%. Most of the participants reported spending the majority of their lifetime living in urban areas (84.86%). Only 54 and 26 participants spent most of their lifetime in sub-urban (10.09%) and rural areas (4.86%), respectively.

2.3 Response Coding

The current section presents how the responses of six major categories were coded according to the following order: 1) wildlife product consumption, 2) general biodiversity perceptions, 3) biodiversity at home and neighborhood, 4) public park visitation and motivations, 5) national park visitation and motivations, and 6) socio-demographic profiles. Two main types of responses are categorical (including binary variables) and numerical variables. In the next sub-sections, categorical variables are described using seven kinds of information corresponding with seven columns: “Variable”, “Name”, “Explanation”, “Level”, “Code”, “Frequency”, and “Proportion”. Meanwhile, for the description of numerical variables, the last three columns are replaced with “Range”, “Mean”, and “Standard deviation”.

2.3.1 Wildlife Product Consumption

The first sub-section of the data set comprises 12 categorical variables that demonstrate the wildlife product consumption behaviors among urban residents (Table 1). The variables were generated by questions about four ways of consuming wildlife products: bushmeat, traditional medicine, products made from animal skin/fur/leather, and uncommon pet. Variables A1 and A2 are used to present whether the respondent has ever consumed bushmeat and their consumption frequency.

Table 1.
Description of variables related to wildlife product consumption.
Categorical variables
VariableNameExplanationLevelCodeFrequencyProportion
A1 Bushmeat consumption Whether the respondent has ever consumed bushmeat Yes
No
1
202
333
37.76%
62.24%
A2 Bushmeat consumption frequency How often the respondent consumes bushmeat Never
Sometimes
Often
Very often
1
2
3
345
188
1
64.49%
35.14%
0.19%
0.19%
A3_1 Animal bone consumption Whether the respondent has ever consumed animal bone (monkey, tiger, horse, etc.) for traditional medicine Yes
No
1
77
458
14.39%
85.61%
A3_2 Bile bear consumption Whether the respondent has ever consumed bile bear for traditional medicine Yes
No
1
116
419
21.68%
78.32%
A3_3 Pangolin scale consumption Whether the respondent has ever consumed pangolin scale for traditional medicine Yes
No
1
11
524
2.06%
97.94%
A4 Information source of traditional medicine Information sources for traditional medicine Family and friends
Newspaper
Social media
Book
Doctor
Other
a
b
c
d
e
321
270
359
112
31
60.00%
50.47%
67.10%
20.93%
5.79%
1.31%
A5 Perceived effective medicine Perceived effective type of medicine Eastern medicine
Same
Western medicine
1
2
64
219
252
11.96%
40.93%
47.10%
A6 Skin/fur/leather product consumption Whether the respondent likes consuming animal skin/fur/leather No, I don't
Yes, a little
Yes, a lot
1
2
449
76
10
83.93%
14.21%
1.87%
A7 Number of skin/fur/leather product The number of products made from animal skin/fur/leather that the respondent owns Nothing
1-3 products
3–5 products
More than 5 products
1
2
3
429
95
4
80.19%
17.76%
0.75%
1.31%
A8 Skin/fur/leather product consumption Whether the respondent owns any products made from animal skin/fur/leather Yes
No
1
106
429
19.81%
80.19%
A9 Interest in uncommon pet Whether the respondent likes owning uncommon pet No, I don't
Yes, a little
Yes, a lot
1
2
363
142
30
67.85%
26.54%
5.61%
A10 Uncommon pet adoption Whether the respondent has ever adopted any uncommon pet No, never
Yes, in the past
1
2
401
116
18
74.95%
21.68%
3.36%
Categorical variables
VariableNameExplanationLevelCodeFrequencyProportion
A1 Bushmeat consumption Whether the respondent has ever consumed bushmeat Yes
No
1
202
333
37.76%
62.24%
A2 Bushmeat consumption frequency How often the respondent consumes bushmeat Never
Sometimes
Often
Very often
1
2
3
345
188
1
64.49%
35.14%
0.19%
0.19%
A3_1 Animal bone consumption Whether the respondent has ever consumed animal bone (monkey, tiger, horse, etc.) for traditional medicine Yes
No
1
77
458
14.39%
85.61%
A3_2 Bile bear consumption Whether the respondent has ever consumed bile bear for traditional medicine Yes
No
1
116
419
21.68%
78.32%
A3_3 Pangolin scale consumption Whether the respondent has ever consumed pangolin scale for traditional medicine Yes
No
1
11
524
2.06%
97.94%
A4 Information source of traditional medicine Information sources for traditional medicine Family and friends
Newspaper
Social media
Book
Doctor
Other
a
b
c
d
e
321
270
359
112
31
60.00%
50.47%
67.10%
20.93%
5.79%
1.31%
A5 Perceived effective medicine Perceived effective type of medicine Eastern medicine
Same
Western medicine
1
2
64
219
252
11.96%
40.93%
47.10%
A6 Skin/fur/leather product consumption Whether the respondent likes consuming animal skin/fur/leather No, I don't
Yes, a little
Yes, a lot
1
2
449
76
10
83.93%
14.21%
1.87%
A7 Number of skin/fur/leather product The number of products made from animal skin/fur/leather that the respondent owns Nothing
1-3 products
3–5 products
More than 5 products
1
2
3
429
95
4
80.19%
17.76%
0.75%
1.31%
A8 Skin/fur/leather product consumption Whether the respondent owns any products made from animal skin/fur/leather Yes
No
1
106
429
19.81%
80.19%
A9 Interest in uncommon pet Whether the respondent likes owning uncommon pet No, I don't
Yes, a little
Yes, a lot
1
2
363
142
30
67.85%
26.54%
5.61%
A10 Uncommon pet adoption Whether the respondent has ever adopted any uncommon pet No, never
Yes, in the past
1
2
401
116
18
74.95%
21.68%
3.36%

The behaviors of consuming traditional medicines made from wildlife are indicated by variables A3_1 to A5. While variables A3_1 to A3_3 are whether the respondent has ever consumed animal bones, bile bear, and pangolin scale for medical treatment, the other two variables (A4 and A5) are the respondent's information sources of traditional medicine and perception of effective medicine. Animal bones, bile bear, and pangolin scale are three frequently consumed materials for traditional medicines in Vietnam [9, 10, 35].

The consumption behaviors of products made from animal skin/fur/leather are indicated by variables A6 to A8. The remaining two variables are to demonstrate the uncommon pet adoption behaviors of the respondent. Uncommon pets are animals that are not dogs or cats.

2.3.2 General Biodiversity Perceptions

The second sub-section focuses on the urban residents' general perceptions towards biodiversity, like the self-assessment knowledge (variable B1), perceived importance of biodiversity loss (variable B2), perceived consequences of biodiversity loss (variables B3_1 to B3_13), perceived preventive measures of biodiversity loss (variables B4_1 to B4_9), perceived biodiversity-affected objects (variables B5_1 to B5_4), and perceived contributors to biodiversity loss prevention (variables B6_1 to B6_5). In total, 33 variables belong to this group (Table 2).

Table 2.
Description of variables related to general biodiversity perceptions.
Categorical variables
VariableNameExplanationLevelCodeFrequencyProportion
Poor
Good
1
2
3
64
189
243
39
11.96%
35.33%
45.42%
7.29%
B2 Biodiversity perception Perception about the importance of biodiversity loss Biodiversity loss is not real
Biodiversity loss is real but
only a small problem
Biodiversity loss is real and a major environmental problem
1
2
17
30
488
3.18%
5.61%
91.21%
Categorical variables
VariableNameExplanationLevelCodeFrequencyProportion
Poor
Good
1
2
3
64
189
243
39
11.96%
35.33%
45.42%
7.29%
B2 Biodiversity perception Perception about the importance of biodiversity loss Biodiversity loss is not real
Biodiversity loss is real but
only a small problem
Biodiversity loss is real and a major environmental problem
1
2
17
30
488
3.18%
5.61%
91.21%
Numerical variables
VariableNameExplanationRangeMeanSD
B3_1 Perceived impact [pollution] Agreement with that the following consequence is a result of biodiversity loss [Environmental pollution (air pollution, water pollution, etc.)] 1. Strongly disagree
2. Disagree
3. Agree
4. Strongly agree
3.34 0.74
B3_2 Perceived impact [climate change] Agreement with that the following consequence is a result of biodiversity loss [Climate change]  3.33 0.72
B3_3 Perceived impact [life imbalance] Agreement with that the following consequence is a result of biodiversity loss [Loss of life balance]  3.17 0.76
B3_4 Perceived impact [good's diversity loss] Agreement with that the following consequence is a result of biodiversity loss [Loss of daily product variety (food, medicine, etc.)]  2.95 0.84
B3_5 Perceived impact [economic growth] Agreement with that the following consequence is a result of biodiversity loss [Negative impacts on economic growth]  2.85 0.83
B3_6 Perceived impact [green space] Agreement with that the following consequence is a result of biodiversity loss [Loss of green space]  3.34 0.72
B3_7 Perceived impact [natural scenery] Agreement with that the following consequence is a result of biodiversity loss [Loss of natural aesthetics]  3.35 0.72
B3_8 Perceived impact [nature-based recreation] Agreement with that the following consequence is a result of biodiversity loss [Loss of opportunities for nature-based recreation]  3.02 0.80
B3_9 Perceived impact [knowledge loss] Agreement with that the following consequence is a result of biodiversity loss [Loss of knowledge about nature]  3.15 0.81
B3_10 Perceived impact [life quality loss] Agreement with that the following consequence is a result of biodiversity loss [Reduction of quality of life]  3.14 0.76
B3_11 Perceived impact [physical health loss] Agreement with that the following consequence is a result of biodiversity loss [Reduction of physical health]  3.00 0.81
B3_12 Perceived impact [mental health loss] Agreement with that the following consequence is a result of biodiversity loss [Reduction of mental health]  3.04 0.78
B3_13 Perceived impact [life expectancy loss] Agreement with that the following consequence is a result of biodiversity loss [Reduction of life expectancy]  2.95 0.82
B4_1 Perceived prevention method [conservation] Agreement with that the following measure is preventive of biodiversity loss [Species conservation in protected areas] 1. Strongly disagree
2. Disagree
3.36 0.72
B4_2 Perceived prevention method [reduction of deforestation and exploitation] Agreement with that the following measure is preventive of biodiversity loss [Reduction of deforestation and exploitation] 3. Agree
4. Strongly agree
3.60 0.67
B4_3 Perceived prevention method [environmental law] Agreement with that the following measure is preventive of biodiversity loss [Environmental law enactment]  3.54 0.65
B4_4 Perceived prevention method [research] Agreement with that the following measure is preventive of biodiversity loss [Scientific research]  3.30 0.68
B4_5 Perceived prevention method [public communication] Agreement with that the following measure is preventive of biodiversity loss [Public communication about biodiversity (loss)]  3.48 0.67
B4_6 Perceived prevention method [education] Agreement with that the following measure is preventive of biodiversity loss [Education about biodiversity (loss)]  3.48 0.67
B4_7 Perceived prevention method [wildlife consumption prohibition] Agreement with that the following measure is preventive of biodiversity loss [Prohibition of illegal wildlife consumption]  3.60 0.67
B4_8 Perceived prevention method [environmental tax] Agreement with that the following measure is preventive of biodiversity loss [Environmental tax]  3.24 0.77
B4_9 Perceived prevention method [donation] Agreement with that the following measure is preventive of biodiversity loss [Donation for biodiversity conservation]  3.25 0.73
B5_1 Affected object [my life] Agreement with that the following object is affected by biodiversity loss [My life] 1. Strongly disagree 2. Disagree
3. Agree
4. Strongly agree
3.06 0.69
B5_2 Affected object [my family] Agreement with that the following object is affected by biodiversity loss [My family]  3.03 0.70
B5_3 Affected object [my neighborhood] Agreement with that the following object is affected by biodiversity loss [My neighborhood]  3.14 0.67
B5_4 Affected object [my city] Agreement with that the following object is affected by biodiversity loss [My city]  3.23 0.67
B6_1 Contributor [myself] Agreement with that the following subject can contribute to biodiversity loss prevention [Myself] 1. Strongly disagree
2. Disagree
3. Agree
4. Strongly agree
3.30 0.62
B6_2 Contributor [my family] Agreement with that the following subject can contribute to biodiversity loss prevention [My family]  3.27 0.62
B6_3 Contributor [my neighbors] Agreement with that the following subject can contribute to biodiversity loss prevention [People in my neighborhood]  3.29 0.62
B6_4 Contributor [government] Agreement with that the following subject can contribute to biodiversity loss prevention [Government]  3.53 0.65
B6_5 Contributor [international organization] Agreement with that the following subject can contribute to biodiversity loss prevention [International organization]  3.55 0.64
Numerical variables
VariableNameExplanationRangeMeanSD
B3_1 Perceived impact [pollution] Agreement with that the following consequence is a result of biodiversity loss [Environmental pollution (air pollution, water pollution, etc.)] 1. Strongly disagree
2. Disagree
3. Agree
4. Strongly agree
3.34 0.74
B3_2 Perceived impact [climate change] Agreement with that the following consequence is a result of biodiversity loss [Climate change]  3.33 0.72
B3_3 Perceived impact [life imbalance] Agreement with that the following consequence is a result of biodiversity loss [Loss of life balance]  3.17 0.76
B3_4 Perceived impact [good's diversity loss] Agreement with that the following consequence is a result of biodiversity loss [Loss of daily product variety (food, medicine, etc.)]  2.95 0.84
B3_5 Perceived impact [economic growth] Agreement with that the following consequence is a result of biodiversity loss [Negative impacts on economic growth]  2.85 0.83
B3_6 Perceived impact [green space] Agreement with that the following consequence is a result of biodiversity loss [Loss of green space]  3.34 0.72
B3_7 Perceived impact [natural scenery] Agreement with that the following consequence is a result of biodiversity loss [Loss of natural aesthetics]  3.35 0.72
B3_8 Perceived impact [nature-based recreation] Agreement with that the following consequence is a result of biodiversity loss [Loss of opportunities for nature-based recreation]  3.02 0.80
B3_9 Perceived impact [knowledge loss] Agreement with that the following consequence is a result of biodiversity loss [Loss of knowledge about nature]  3.15 0.81
B3_10 Perceived impact [life quality loss] Agreement with that the following consequence is a result of biodiversity loss [Reduction of quality of life]  3.14 0.76
B3_11 Perceived impact [physical health loss] Agreement with that the following consequence is a result of biodiversity loss [Reduction of physical health]  3.00 0.81
B3_12 Perceived impact [mental health loss] Agreement with that the following consequence is a result of biodiversity loss [Reduction of mental health]  3.04 0.78
B3_13 Perceived impact [life expectancy loss] Agreement with that the following consequence is a result of biodiversity loss [Reduction of life expectancy]  2.95 0.82
B4_1 Perceived prevention method [conservation] Agreement with that the following measure is preventive of biodiversity loss [Species conservation in protected areas] 1. Strongly disagree
2. Disagree
3.36 0.72
B4_2 Perceived prevention method [reduction of deforestation and exploitation] Agreement with that the following measure is preventive of biodiversity loss [Reduction of deforestation and exploitation] 3. Agree
4. Strongly agree
3.60 0.67
B4_3 Perceived prevention method [environmental law] Agreement with that the following measure is preventive of biodiversity loss [Environmental law enactment]  3.54 0.65
B4_4 Perceived prevention method [research] Agreement with that the following measure is preventive of biodiversity loss [Scientific research]  3.30 0.68
B4_5 Perceived prevention method [public communication] Agreement with that the following measure is preventive of biodiversity loss [Public communication about biodiversity (loss)]  3.48 0.67
B4_6 Perceived prevention method [education] Agreement with that the following measure is preventive of biodiversity loss [Education about biodiversity (loss)]  3.48 0.67
B4_7 Perceived prevention method [wildlife consumption prohibition] Agreement with that the following measure is preventive of biodiversity loss [Prohibition of illegal wildlife consumption]  3.60 0.67
B4_8 Perceived prevention method [environmental tax] Agreement with that the following measure is preventive of biodiversity loss [Environmental tax]  3.24 0.77
B4_9 Perceived prevention method [donation] Agreement with that the following measure is preventive of biodiversity loss [Donation for biodiversity conservation]  3.25 0.73
B5_1 Affected object [my life] Agreement with that the following object is affected by biodiversity loss [My life] 1. Strongly disagree 2. Disagree
3. Agree
4. Strongly agree
3.06 0.69
B5_2 Affected object [my family] Agreement with that the following object is affected by biodiversity loss [My family]  3.03 0.70
B5_3 Affected object [my neighborhood] Agreement with that the following object is affected by biodiversity loss [My neighborhood]  3.14 0.67
B5_4 Affected object [my city] Agreement with that the following object is affected by biodiversity loss [My city]  3.23 0.67
B6_1 Contributor [myself] Agreement with that the following subject can contribute to biodiversity loss prevention [Myself] 1. Strongly disagree
2. Disagree
3. Agree
4. Strongly agree
3.30 0.62
B6_2 Contributor [my family] Agreement with that the following subject can contribute to biodiversity loss prevention [My family]  3.27 0.62
B6_3 Contributor [my neighbors] Agreement with that the following subject can contribute to biodiversity loss prevention [People in my neighborhood]  3.29 0.62
B6_4 Contributor [government] Agreement with that the following subject can contribute to biodiversity loss prevention [Government]  3.53 0.65
B6_5 Contributor [international organization] Agreement with that the following subject can contribute to biodiversity loss prevention [International organization]  3.55 0.64

2.3.3 Biodiversity at Home and Neighborhood

The third sub-section focuses on the interactions between humans and biodiversity at the respondent's home and neighborhood (Table 3). The first four variables (from C1_1 to C1_4) show the respondent's behaviors and willingness to plant varied types of plants in their houses, while the next four variables (from C2_1 to C2_4) present the respondent's behaviors and willingness of adopting varied types of pet in their houses. The respondent's feelings (e.g., comfortability and aesthetics) when being in the house are indicated by variables C3_1 to C3_4. The last three variables (C4_1, C4_2, and C4_3) are used to present the perceived availability of plants in the respondent's neighborhood, their willingness to donate to a planting project, and considered important aspects of the project, respectively.

Table 3.
Description of variables related to biodiversity at home and neighborhood.
Categorical variables
VariableNameExplanationLevelCodeFrequencyProportion
C1_1 In-house planting (scale) Whether the respondent plants plant in their house Not at all
Yes, but only a few
Yes, I plant many
1
2
31
292
212
5.79%
54.58%
39.63%
C1_2 In-house planting (binary) Whether the respondent plants plant in their house Yes
No
1
504
31
94.21%
5.79%
C1_3 Number of types of plants planted The number of types of plants planted in the house 0
1
2
3
4
5
More than 5
0
1
2
3
4
5
30
17
48
66
32
50
292
5.61%
3.18%
8.97%
12.34%
5.98%
9.35%
54.58%
C1_4 Willingness to plant more plants Whether the respondent is willing to plant more plants No, I wouldn't
Yes, I would plant more plants from the same type
Yes, I would plant more plants from various types
1
2
38
49
448
7.10%
9.16%
83.74%
C2_1 Petting Whether the respondent owns any pet Yes
No
1
254
281
47.48%
52.52%
C2_2 Type of pet Type of pet that the respondent owns Cat
Dog
Fish
Other
No pet
a
b
c
d
142
225
174
23
154
26.54%
42.06%
32.52%
4.30%
28.79%
C2_3 Number of pets Number of pet types that the respondent owns 0
1
2
More than 2
0
1
2
200
183
70
62
37.38%
34.21%
13.08%
11.59%
C2_4 Willingness to adopt more pet Whether the respondent is willing to adopt more pet No, I wouldn't
Yes, I would adopt more pets from the same type
Yes, I would adopt more pets from various types
1
2
347
78
110
64.86%
14.58%
20.56%
C3_1 Feeling comfortable at home (scale) How much comfortable the respondent feels in the house Very Uncomfortable
Uncomfortable
Comfortable
Very comfortable
1
2
3
25
33
258
219
4.67%
6.17%
48.22%
40.93%
C3_2 Feeling comfortable at home (binary) Whether the respondent feels comfortable when being in the house Comfortable
Uncomfortable
1
477
58
89.16%
10.84%
C3_3 Feeling aesthetic at home due to plant/animal (scale) How much aesthetic the respondent feels the house is due to plant/animal Very negative effect
Negative effect
Positive effect
Very positive effect
1
2
3
12
12
316
195
2.24%
2.24%
59.07%
36.45%
C3_4 Feeling aesthetic at home due to plant/animal (binary) Whether the respondent feels the house aesthetic due to plant/animal Positive effect
Negative effect
1
511
24
95.51%
4.49%
C3_3 Feeling aesthetic at home due to plant/animal (scale) How much aesthetic the respondent feels the house is due to plant/animal Very negative effect
Negative effect
Positive effect
Very positive effect
1
2
3
12
12
316
195
2.24%
2.24%
59.07%
36.45%
C4_2 Donation to planting project in the neighborhood Whether the respondent is willing to financially contribute to the planting project in the neighborhood Not at all
Not really
Willing
Very willing
1
2
3
5
60
284
186
0.93%
11.21%
53.08%
34.77%
C4_3 Favorable planting characteristics in the neighborhood Important aspects that should be considered in the planting project Amount
Variety
Aesthetics
Location
Other
a
b
c
d
e
248
267
388
323
365
46.36%
49.91%
72.52%
60.37%
68.22%
0.93%
Categorical variables
VariableNameExplanationLevelCodeFrequencyProportion
C1_1 In-house planting (scale) Whether the respondent plants plant in their house Not at all
Yes, but only a few
Yes, I plant many
1
2
31
292
212
5.79%
54.58%
39.63%
C1_2 In-house planting (binary) Whether the respondent plants plant in their house Yes
No
1
504
31
94.21%
5.79%
C1_3 Number of types of plants planted The number of types of plants planted in the house 0
1
2
3
4
5
More than 5
0
1
2
3
4
5
30
17
48
66
32
50
292
5.61%
3.18%
8.97%
12.34%
5.98%
9.35%
54.58%
C1_4 Willingness to plant more plants Whether the respondent is willing to plant more plants No, I wouldn't
Yes, I would plant more plants from the same type
Yes, I would plant more plants from various types
1
2
38
49
448
7.10%
9.16%
83.74%
C2_1 Petting Whether the respondent owns any pet Yes
No
1
254
281
47.48%
52.52%
C2_2 Type of pet Type of pet that the respondent owns Cat
Dog
Fish
Other
No pet
a
b
c
d
142
225
174
23
154
26.54%
42.06%
32.52%
4.30%
28.79%
C2_3 Number of pets Number of pet types that the respondent owns 0
1
2
More than 2
0
1
2
200
183
70
62
37.38%
34.21%
13.08%
11.59%
C2_4 Willingness to adopt more pet Whether the respondent is willing to adopt more pet No, I wouldn't
Yes, I would adopt more pets from the same type
Yes, I would adopt more pets from various types
1
2
347
78
110
64.86%
14.58%
20.56%
C3_1 Feeling comfortable at home (scale) How much comfortable the respondent feels in the house Very Uncomfortable
Uncomfortable
Comfortable
Very comfortable
1
2
3
25
33
258
219
4.67%
6.17%
48.22%
40.93%
C3_2 Feeling comfortable at home (binary) Whether the respondent feels comfortable when being in the house Comfortable
Uncomfortable
1
477
58
89.16%
10.84%
C3_3 Feeling aesthetic at home due to plant/animal (scale) How much aesthetic the respondent feels the house is due to plant/animal Very negative effect
Negative effect
Positive effect
Very positive effect
1
2
3
12
12
316
195
2.24%
2.24%
59.07%
36.45%
C3_4 Feeling aesthetic at home due to plant/animal (binary) Whether the respondent feels the house aesthetic due to plant/animal Positive effect
Negative effect
1
511
24
95.51%
4.49%
C3_3 Feeling aesthetic at home due to plant/animal (scale) How much aesthetic the respondent feels the house is due to plant/animal Very negative effect
Negative effect
Positive effect
Very positive effect
1
2
3
12
12
316
195
2.24%
2.24%
59.07%
36.45%
C4_2 Donation to planting project in the neighborhood Whether the respondent is willing to financially contribute to the planting project in the neighborhood Not at all
Not really
Willing
Very willing
1
2
3
5
60
284
186
0.93%
11.21%
53.08%
34.77%
C4_3 Favorable planting characteristics in the neighborhood Important aspects that should be considered in the planting project Amount
Variety
Aesthetics
Location
Other
a
b
c
d
e
248
267
388
323
365
46.36%
49.91%
72.52%
60.37%
68.22%
0.93%

2.3.4 Public Park Visitation and Motivations

Respondent's public park visitation and involvement in planting projects can be explored using the variables in the fourth sub-section (Table 4). At the beginning of the sub-section, the question, “is there any public park near your house?” was asked. If the respondent answered “yes”, other questions about their visitation to the public park and planting-project contribution willingness would be given. Otherwise, these questions would be skipped. In this sub-section, specific questions about the public park's biodiversity characteristics were not included to avoid respondent's recall bias, which downgrades the answers' reliability.

Table 4.
Description of variables related to public park visitation and motivations.
Categorical variables
VariableNameExplanationLevelCodeFrequencyProportion
D1 Availability of a nearby public park Whether there is a public park near where the respondent lives Yes
No
1
415
120
77.57%
22.43%
D2 Public park visitation frequency Frequency of going to the nearby public park Never
Almost never
Sometimes
Almost everyday
Everyday
1
2
3
4
21
38
281
55
20
3.93%
7.10%
52.52%
10.28%
3.74%
D3 Public park visitation reasons The respondent's reasons to visit the nearby public park Relaxation
Physical activities
Meeting with friends
Spending time with family
Educational activities for children
Enjoying nature
Community events
Other
a
b
c
d
e
f
g
260
238
96
107
101
220
70
48.60%
44.49%
17.94%
20.00%
18.88%
41.12%
13.08%
0.37%
D4 Donation to planting project in the public park Whether the respondent is willing to financially contribute to the planting project in the nearby public park Not at all
Not really
Willing
Very willing
1
2
3
8
58
244
105
1.50%
10.84%
45.61%
19.63%
D5 Favorable planting characteristics in the public park Important aspects that should be considered in the planting project Amount
Variety
Aesthetics
Location
Other
a
b
c
d
e
220
281
326
228
284
41.12%
52.52%
60.93%
42.62%
53.08%
1.31%
Categorical variables
VariableNameExplanationLevelCodeFrequencyProportion
D1 Availability of a nearby public park Whether there is a public park near where the respondent lives Yes
No
1
415
120
77.57%
22.43%
D2 Public park visitation frequency Frequency of going to the nearby public park Never
Almost never
Sometimes
Almost everyday
Everyday
1
2
3
4
21
38
281
55
20
3.93%
7.10%
52.52%
10.28%
3.74%
D3 Public park visitation reasons The respondent's reasons to visit the nearby public park Relaxation
Physical activities
Meeting with friends
Spending time with family
Educational activities for children
Enjoying nature
Community events
Other
a
b
c
d
e
f
g
260
238
96
107
101
220
70
48.60%
44.49%
17.94%
20.00%
18.88%
41.12%
13.08%
0.37%
D4 Donation to planting project in the public park Whether the respondent is willing to financially contribute to the planting project in the nearby public park Not at all
Not really
Willing
Very willing
1
2
3
8
58
244
105
1.50%
10.84%
45.61%
19.63%
D5 Favorable planting characteristics in the public park Important aspects that should be considered in the planting project Amount
Variety
Aesthetics
Location
Other
a
b
c
d
e
220
281
326
228
284
41.12%
52.52%
60.93%
42.62%
53.08%
1.31%

2.3.5 National Park Visitation and Motivations

The fifth sub-section is about the respondent's national park visitation (Table 5). Besides the visitation behaviors (variable E1) and motivations (variables E2 to E4), the respondent's willingness that might contribute to conservation finance in national parks was also measured by variable E5 (entrance fee payment willingness) and E6 (donation willingness). The questions in this sub-section were kept as general (or not context-based) as possible because urban residents in different cities had distinct impression with particular national parks, so their perceptions about national parks might be different accordingly. Moreover, recall bias also alleviates the reliability of responses to specific (or context-based) questions.

Table 5.
Description of variables related to national park visitation and motivations.
Categorical variables
VariableNameExplanationLevelCodeFrequencyProportion
E1 National Park visitation frequency Frequency of going to the national park Never
Less than once a year
Once a year
Twice a year
More than twice a year
1
2
3
4
114
259
111
27
24
21.31%
48.41%
20.75%
5.05%
4.49%
ENational park visitation reasons The respondent's reasons to visit the national park Escape and relaxation
Enjoying nature
Watching wild animals
Meeting with friends
Spending time with family
Educational activities for children
Seeking new knowledge (animals, plants, etc.)
Outdoor activities (hiking, trekking, etc.)
Other
a
b
c
d
e
f
g
h
300
342
290
107
223
182
244
233
56.07%
63.93%
54.21%
20.00%
41.68%
34.02%
45.61%
43.55%
1.31%
EWillingness to visit a national park (scale) Whether the respondent is willing to visit a national park in the next 12 months No, I don't even think about it
No, but maybe later
Yes, but I'm still not sure
Yes, certainly
1
2
3
30
36
232
237
5.61%
6.73%
43.36%
44.30%
E4 Willingness to visit a national park (binary) Whether the respondent is willing to visit a national park in the next 12 months Yes
No
1
469
66
87.66%
12.34%
E5 Entrance fee payment willingness Whether the respondent is willing to pay for the national park's entrance fee Yes
No
1
522
13
97.57%
2.43%
E6 Conservation project donation willingness Whether the respondent is willing to donate to the national park's conservation activities Yes
No
1
508
27
94.95%
5.05%
Categorical variables
VariableNameExplanationLevelCodeFrequencyProportion
E1 National Park visitation frequency Frequency of going to the national park Never
Less than once a year
Once a year
Twice a year
More than twice a year
1
2
3
4
114
259
111
27
24
21.31%
48.41%
20.75%
5.05%
4.49%
ENational park visitation reasons The respondent's reasons to visit the national park Escape and relaxation
Enjoying nature
Watching wild animals
Meeting with friends
Spending time with family
Educational activities for children
Seeking new knowledge (animals, plants, etc.)
Outdoor activities (hiking, trekking, etc.)
Other
a
b
c
d
e
f
g
h
300
342
290
107
223
182
244
233
56.07%
63.93%
54.21%
20.00%
41.68%
34.02%
45.61%
43.55%
1.31%
EWillingness to visit a national park (scale) Whether the respondent is willing to visit a national park in the next 12 months No, I don't even think about it
No, but maybe later
Yes, but I'm still not sure
Yes, certainly
1
2
3
30
36
232
237
5.61%
6.73%
43.36%
44.30%
E4 Willingness to visit a national park (binary) Whether the respondent is willing to visit a national park in the next 12 months Yes
No
1
469
66
87.66%
12.34%
E5 Entrance fee payment willingness Whether the respondent is willing to pay for the national park's entrance fee Yes
No
1
522
13
97.57%
2.43%
E6 Conservation project donation willingness Whether the respondent is willing to donate to the national park's conservation activities Yes
No
1
508
27
94.95%
5.05%

2.3.6 Socio-demographic Profile

The last sub-section consists of variables about the socio-demographic characteristics of the respondent, such as gender (variable F1), age (variables F2 and F3), occupation (variable F4), educational level (variable F5), and income (variables F6 and F7). Apart from basic information, the nearby landscape (variable F8), environmental information source (variable F9), most frequently lived area (variable F10), and current residency (variable F11) are also included in the sub-section (Table 6).

Table 6.
Description of variables related to respondents' socio-demographic profi les.
Categorical variables
VariableNameExplanationLevelCodeFrequencyProportion
F1 Gender Gender Female
Male
0
312
220
57.08%
42.92%
F3 Age group The age group in which the respondent belongs to 18–22
23–30
31–40
41–50
51–60
More than 60
1
2
3
4
5
120
132
140
87
36
20
13.95%
21.36%
25.75%
17.37%
7.58%
3.99%
F4 Occupation The current occupation of the respondent NA NA NA NA
F5 Education The highest educational level of the respondent Primary school
Secondary school
High school
1
2
3
4
1
9
70
338
117
0.2%
1.8%
13.77%
61.68%
22.55%
F7 Income group The income group in which the respondent belongs to No income
Less than 5 million VNĐ
10–15 million VNĐ 5–10 million VNĐ 15–20 VNĐ 20–30 million VNĐ More than 30 million
VNĐ
1
2
3
4
5
6
22
53
99
107
40
44
40
4.39%
10.58%
15.37%
20.16%
7.78%
9.38%
7.78%
F8 Nearby landscape The landscapes that the respondent has ever lived nearby Forest
Ocean
River
Cropland
Pond
Other
Not at all
a
b
c
d
e
f
121
133
201
205
203
143
23.15%
24.35%
36.73%
37.72%
37.92%
28.54%
0%
F9 Environmental information source The sources from which the respondent receives environment-related information Newspaper
Online newspaper
Social Media
Lecture
Word of mouth
Books
Textbooks
Documentary movies
Observations
Local government
Others
a
b
c
d
e
f
g
h
i
j
382
380
464
228
278
253
228
339
292
99
71.86%
71.46%
87.03%
43.91%
52.50%
47.90%
43.51%
64.27%
56.09%
19.56%
0.6%
F10 Area with most living time The area in which the respondent has spent a majority of their lifetime Urban Sub-urban Rural a
b
454
54
26
85.63%
10.38%
3.79%
F11 Current residency The current city in which the respondent is living NA NA NA NA
Categorical variables
VariableNameExplanationLevelCodeFrequencyProportion
F1 Gender Gender Female
Male
0
312
220
57.08%
42.92%
F3 Age group The age group in which the respondent belongs to 18–22
23–30
31–40
41–50
51–60
More than 60
1
2
3
4
5
120
132
140
87
36
20
13.95%
21.36%
25.75%
17.37%
7.58%
3.99%
F4 Occupation The current occupation of the respondent NA NA NA NA
F5 Education The highest educational level of the respondent Primary school
Secondary school
High school
1
2
3
4
1
9
70
338
117
0.2%
1.8%
13.77%
61.68%
22.55%
F7 Income group The income group in which the respondent belongs to No income
Less than 5 million VNĐ
10–15 million VNĐ 5–10 million VNĐ 15–20 VNĐ 20–30 million VNĐ More than 30 million
VNĐ
1
2
3
4
5
6
22
53
99
107
40
44
40
4.39%
10.58%
15.37%
20.16%
7.78%
9.38%
7.78%
F8 Nearby landscape The landscapes that the respondent has ever lived nearby Forest
Ocean
River
Cropland
Pond
Other
Not at all
a
b
c
d
e
f
121
133
201
205
203
143
23.15%
24.35%
36.73%
37.72%
37.92%
28.54%
0%
F9 Environmental information source The sources from which the respondent receives environment-related information Newspaper
Online newspaper
Social Media
Lecture
Word of mouth
Books
Textbooks
Documentary movies
Observations
Local government
Others
a
b
c
d
e
f
g
h
i
j
382
380
464
228
278
253
228
339
292
99
71.86%
71.46%
87.03%
43.91%
52.50%
47.90%
43.51%
64.27%
56.09%
19.56%
0.6%
F10 Area with most living time The area in which the respondent has spent a majority of their lifetime Urban Sub-urban Rural a
b
454
54
26
85.63%
10.38%
3.79%
F11 Current residency The current city in which the respondent is living NA NA NA NA
Numerical variable
VariableNameExplanationRangeMeanSD
F2 Age The reported age of the respondent 18–71 33.80 12.18
F5 Income The reported income of the respondent 0–100,000,000 13,708,971 16,646,862
Numerical variable
VariableNameExplanationRangeMeanSD
F2 Age The reported age of the respondent 18–71 33.80 12.18
F5 Income The reported income of the respondent 0–100,000,000 13,708,971 16,646,862

This section presents Bayesian linear analysis's results to validate the data set. I constructed the model using four socio-demographic factors (Gender, Age, Education, and Income) and two perceptions about perceived impacts of biodiversity loss (GoodDiversityLoss and EconomicGrowthLoss) as predictor variables. The Gender, Age, Education, and Income variables were illustrated by F1, F2, F5, and F7 variables in the data set. B3_4 and B3_5 variables correspondingly present the agreement level with that the loss results of daily product diversity and negative impacts on economic growth are consequences of biodiversity loss. Meanwhile, the respondents' agreement with prohibiting illegal wildlife consumption as a preventive measure was selected as the outcome variable, which variable WildConsProhibi exhibits. The variable was generated by modifying variable B4_7 from numerical data to dichotomous data, with “strongly disagree” and “disagree” being 0 and “agree” and “strongly agree” being 1. Eventually, the constructed model and its logical network can be presented as follows (Figure 1):

WildConsProhibi ∼ α + Gender + Age + Education + Income + GoodDiversityLoss + EconomicGrowthLoss

Logical network of the simulated model.

Figure 1.
Logical network of the simulated model.
Figure 1.
Logical network of the simulated model.

The bayesvl R package was utilized to perform the data analysis due to its user-friendly operation, eyecatching graphics, and integration of the Monte Carlo Markov Chain (MCMC) technique [36, 37]. All the parameters' prior distributions were set at normal distribution (0,10), or “uninformative” distribution. The simulation was operated on R Studio (version 4.1.0) using four Markov chains and 5,000 iterations, 2,000 of which were for the warm-up process. Before constructing and fitting the model in R, the following code snippet was employed to prepare necessary resources:

Then, we started to construct and fit the model:

The simulated results are shown in Table 7. When employing Bayesian analysis, diagnosing the convergence of Markov chains is one of the fundamental steps. The diagnosis can be performed using two basic statistics: effective number size (n_eff) and Gelman shrink factor (Rhat). If the n_eff value is larger than 1,000 and the Rhat value equals 1, the model's Markov chains can be deemed well-convergent, and the estimations are reliable. Here, all the parameters' n_eff and Rhat values meet the basic criteria.

Table 7.
Estimated posterior coefficients.
ParametersMean (μ)Standard deviation (σ)n_effRhat
Constant -4.36 2.11 6241
Gender 0.78 0.65 7921
Age 0.00 0.03 8647
Education 0.63 0.42 7153
Income 0.15 0.25 6942
GoodDiversityLoss 0.87 0.44 7121
EconomicGrowthLoss 0.98 0.46 7152
ParametersMean (μ)Standard deviation (σ)n_effRhat
Constant -4.36 2.11 6241
Gender 0.78 0.65 7921
Age 0.00 0.03 8647
Education 0.63 0.42 7153
Income 0.15 0.25 6942
GoodDiversityLoss 0.87 0.44 7121
EconomicGrowthLoss 0.98 0.46 7152

Using the diagnostic statistics solely is not sufficient, but visual diagnoses through trace plots, Gelman plots, and autocorrelation plots are also required. The trace plots in Figure 2 show “healthy” and stationary patterns of Markov chains, so the convergence can be confirmed. In the Gelman plots, the shrink factor values drop rapidly to 1 during the warm-up period (before the 2,000th iterations), while the autocorrelation levels in autocorrelation plots also decline to 0 after a certain lag (Figures A1 and A2). Both signals indicated by Gelman and autocorrelation plots imply that the Markov chain central limit theorem is held, so the simulated results are reliable for interpretation.

Trace plots.

Figure 2.
Trace plots.
Figure 2.
Trace plots.

The simulated results show that Gender, Education, and Income positively influenced the probability to agree that illegal wildlife consumption prohibition is a preventive measure of biodiversity loss (μGender = 0.78 and σGender = 0.65; μEducation = 0.63 and σEducation = 0.42; μIncome = 0.0.15 and σIncome = 0.25), but Age did not (μAge = 0.00 and μAge = 0.03). When plotting the probability distributions of parameters, we could see that almost entire distributions of Gender and Education are located on the positive side of the x-axis, indicating reliable positive associations among Gender, Education, and WildConsProhibi. As for Income, the certain proportion of the distribution still lies on the negative side, so its positive association with WildConsProhibi was less reliable than the other two.

Apart from socio-demographic factors, I also found positive associations between perceptions about the consequences of biodiversity loss and the agreement that wildlife consumption prohibition is a preventive measure. Specifically, respondents thinking that the loss of daily product variety and loss of economic growth are consequences of biodiversity loss were more likely to consider wildlife consumption prohibition a preventive measure (μGoodDiversityLoss = 0.87 and σGoodDiversityLoss = 0.44; μEconomicGrowthLoss = 0.98 and σEconomicGrowthLoss = 0.46). In Figures 3A and 3B, their probability distributions are almost completely located on the positive side of the x-axis, implying the high reliability of the associations.

Probability distributions of posterior coefficients (A–Interval plot, B–Density plot).

Figure 3.
Probability distributions of posterior coefficients (A–Interval plot, B–Density plot).
Figure 3.
Probability distributions of posterior coefficients (A–Interval plot, B–Density plot).

For plotting the above figures, the following code snippet was used:

The current data set provides resources for studying important aspects of the interactions between urban residents and biodiversity-related concepts, which are currently lacking in the literature.

Besides the stringent quality-check process, the data set was also employed to examine the associations between the agreement with illegal wildlife consumption and perceived negative impacts of biodiversity loss for further validation. The results show that respondents who perceived more negative effects of biodiversity on economic growth and their daily used product diversity would be more likely to agree with illegal wildlife consumption prohibition. This finding is aligned with the Mindsponge mechanism, which stipulates that an individual's perceptions towards a specific matter are influenced by their subjective cost-benefit judgement towards that matter [38, 39, 40]. Due to the consistency with the theoretical assumption, the data set can be deemed reliable to study the socio-psychological aspects of the relationship between urban humans and biodiversity-related concepts.

Some potential issues can be explored using the current data set. First of all, mitigating the demand for the wildlife product among urban residents is crucial for biodiversity loss reduction. Raising urban residents' awareness through social marketing campaigns is a potential measure to achieve such a target [6, 7]. Using the current data set to explore how biodiversity perceptions influence wildlife product consumption behaviors might help improve the effectiveness and efficiency of public communication campaigns and programs. Besides, insights generated from this data set might also contribute to the biodiversity conservation-related legislation and law enforcement in urban areas [12].

Secondly, based on the current data set, researchers can also investigate the interactions of urban residents with biodiversity-related concepts in multiple green spaces at home, neighborhood, urban public park, and national park. This can help enrich the literature in both sustainable urban development and biodiversity conservation. For example, planting and pet keeping behaviors might be associated with the willingness to support planting projects in the neighborhood and public parks. Moreover, the frequency of visiting national parks might be predicted by the biodiversity perceptions of urban residents, which provides more insights for social marketing campaigns to attract more visitors. The increasing influx of visitors might help generate sustainable finance for biodiversity conservation in national parks and preservation in urban public parks [29, 30].

Additionally, the current data set helps reduce the cost of doing science for researchers in developing countries with similar characteristics to Vietnam [41]: high urbanization rate and high level of biodiversity (e.g., being located in a biodiversity hotspot). Within an academic setting with high competition and limited resources, not only researchers from developing countries, but also young scholars in developed countries can capitalize on this data set to develop new hypotheses and test their assumptions regarding the relationships between urban humans and biodiversity-related concepts [42]. Making the data set open also enhances transparency and facilitates open review and dialogue among researchers [43].

In summary, the data set was systematically designed, collected, and validated to explore the interactions between urban residents and biodiversity-related concepts. Thus, researchers can make use of the data set to enrich the lax literature regarding the role of urban residents in biodiversity conservation and preservation; policymakers can find insights for building up an “eco-surplus culture” [44] among urban residents through effective public communication and policymaking.

I would like to send my gratitude to my family, and friends for assisting in collecting data, especially Prof. Vuong Quan Hoang (Phenikaa University) and Ms. Dam Thu Ha (Vuong & Associates). My most sincere appreciations also go on to Prof. Jones E. Thomas (Ritsumeikan Asia Pacific University), Mr. Le Tam Tri (Phenikaa University), and Mr. Khuc Van Quy (Vietkaplab) for providing me with comments and feedbacks on the questionnaire design.

The data set was designed and collected for the author's dissertation research project.

The responses of 535 participants on the multifaceted interactions between urban humans and biodiversity were saved as “Data_535 (cleaned).csv” and deposited in Science Data Bank repository, https://doi.org/10.11922/sciencedb.j00104.00097, under an Attribution 4.0 International (CC BY 4.0). Detailed data description, which was saved as “Data description.xlsx”, was also included in the same repository. All information related to participants' personal contacts was excluded for the sake of confidentiality.

[1]
World Wildlife Fund
.
Living Planet Report 2020 - Bending the curve of biodiversity loss
. Available at: http://environmentportal.in/content/468493/living-planet-report-2020-bending-the-curve-of-biodiversity-loss/. Accessed 24 June
2021
[2]
Intergovernmental Science-Policy Platform on Biodiversity and Ecosystem Services
.
Nature's dangerous decline ‘unprecedented’ species extinction rates ‘accelerating’
. Available at: https://www.unenvironment.org/news-and-stories/press-release/natures-dangerous-decline-unprecedented-species-extinction-rates. Accessed 24 June
2021
[3]
Tordoff
,
A.W.
, et al.:
Indo-Burma biodiversity hotspot
. Critical Ecosystem Partnership Fund. Available at: https://www.kfbg.org/en/conservation-by-site/indo-burma-biodiversity-hotspot. Accessed 24 June
2021
[4]
Ministry of Natural Resources and Environment
.
Vietnam fifth national report to the United Nations Convention on Biologival Diversity
. The Vietnamese Government, Hanoi (
2014
)
[5]
Ministry of Natural Resources and Environment
.
Vietnam national biodiversity strategy to 2020, vision to 2030
. The Vietnamese Government, Hanoi (
2014
)
[6]
Shairp
,
R.
, et al.:
Understanding urban demand for wild meat in Vietnam: Implications for conservation actions
.
PloS ONE
11
(
1
),
e0134787
(
2016
)
[7]
Challender
,
D.W.
,
MacMillan
,
D.C.
:
Poaching is more than an enforcement problem
.
Conservation Letters
7
(
5
),
484
494
(
2014
)
[8]
Van Song
,
N.
:
Wildlife trading in Vietnam: Situation, causes, and solutions
.
The Journal of Environment and Development
17
(
2
),
145
165
(
2008
)
[9]
Davis
,
E.O.
, et al.:
Consumer demand and traditional medicine prescription of bear products in Vietnam
.
Biological Conservation
235
,
119
127
(
2019
)
[10]
Davis
,
E.O.
, et al.:
An updated analysis of the consumption of tiger products in urban Vietnam
.
Global Ecology and Conservation
22
,
e00960
(
2020
)
[11]
Olmedo
,
A.
, et al.:
Who eats wild meat? Profiling consumers in Ho Chi Minh City, Vietnam
.
People and Nature
3
(
3
),
700
710
(
2021
)
[12]
Sandalj
,
M.
,
Treydte
,
A.C.
,
Ziegler
,
S.
:
Is wild meat luxury? Quantifying wild meat demand and availability in Hue, Vietnam
.
Biological Conservation
194
,
105
112
(
2016
)
[13]
Nguyen
,
N.H.
:
Bird play: Raising red-whiskered bulbuls and (re)inventing urban ‘nature’ in contemporary Vietnam
.
Contemporary Social Science
16
(
1
),
57
70
(
2021
)
[14]
Greenfield
,
S.
,
Veríssimo
,
D.
:
To what extent is social marketing used in demand reduction campaigns for illegal wildlife products? Insights from elephant ivory and rhino horn
.
Social Marketing Quarterly
25
(
1
),
152450041881354
(
2018
)
[15]
Moorhouse
,
T.P.
, et al.:
Reduce or redirect? Which social marketing interventions could influence demand for traditional medicines?
Biological Conservation
242
,
108391
(
2020
)
[16]
Kowarik
,
I.
,
Fischer
,
L.K.
,
Kendal
,
D.
:
Biodiversity conservation and sustainable urban development
.
Sustainability
12
(
12
),
1
8
(
2020
)
[17]
Schwarz
,
N.
, et al.:
Understanding biodiversity-ecosystem service relationships in urban areas: A comprehensive literature review
.
Ecosystem Services
27
,
161
171
(
2017
)
[18]
Fischer
,
L.K.
, et al.:
Beyond green: Broad support for biodiversity in multicultural European cities
.
Global Environmental Change
49
,
35
45
(
2018
)
[19]
Clark
,
N.E.
, et al.:
Biodiversity, cultural pathways, and human health: A framework
.
Trends in Ecology Evolution
29
(
4
),
198
204
(
2014
)
[20]
UN Habitat
.
Habitat III
:
New Urban Agenda
. Available at: https://habitat3.org/the-new-urban-agenda. Accessed 24 June
2021
[21]
IPBES
.
Summary for policymakers of the global assessment report on biodiversity and ecosystem services of the Intergovernmental Science-Policy Platform on Biodiversity and Ecosystem Services
. Available at: . Accessed 24 June 2021
[22]
Opoku
,
A.
:
Biodiversity and the built environment: Implications for the Sustainable Development Goals (SDGs)
.
Resources, Conservation and Recycling
141
,
1
7
(
2019
)
[23]
Ives
,
C.D.
,
Kendal
,
D.
:
The role of social values in the management of ecological systems
.
Journal of Environmental Management
144
,
67
72
(
2014
)
[24]
Alberti
,
M.
, et al.:
Integrating humans into ecology: Opportunities and challenges for studying urban ecosystems
.
BioScience
53
,
1169
1179
(
2003
)
[25]
Jenkins
,
J.
,
Pigram
,
J.
:
Encyclopedia of leisure and outdoor recreation
.
Routledge
:
Oxfordshire
(
2004
)
[26]
Lackey
,
N.Q.
, et al.:
Mental health benefits of nature-based recreation: A systematic review
.
Annals of Leisure Research
24
,
379
393
(
2021
)
[27]
Fuller
,
R.A.
, et al.:
Psychological benefits of greenspace increase with biodiversity
.
Biology Letters
3
(
4
),
390
394
(
2007
)
[28]
Shwartz
,
A.
, et al.:
Enhancing urban biodiversity and its influence on city-dwellers: An experiment
.
Biological Conservation
171
,
82
90
(
2014
)
[29]
Tapper
,
R.
:
Wildlife watching and tourism: A study on the benefits and risks of a fast growing tourism activity and its impacts on species
. UNEP/Earthprint, Bonn (
2006
)
[30]
Chung
,
M.G.
,
Dietz
,
T.
,
Liu
,
J.
:
Global relationships between biodiversity and nature-based tourism in protected areas
.
Ecosystem Services
34
,
11
23
(
2018
)
[31]
Khai
,
H.V.
,
Yabe
,
M.
:
The demand of urban residents for the biodiversity conservation in U Minh Thuong National Park, Vietnam
.
Agricultural and Food Economics
2
,
10
(
2014
)
[32]
Creswell
,
J.W.
,
Poth
,
C.N.
:
Qualitative inquiry and research design: Choosing among five approaches
.
SAGE
:
Los Angeles
(
2018
)
[33]
Nguyen
,
M.-H.
, et al.:
A data set of students' mental health and help-seeking behaviors in a multicultural environment
.
Data
4
,
124
(
2019
)
[34]
Kim
,
Y.
, et al.:
Straightlining: Overview of measurement, comparison of indicators, and effects in mail–web mixed-mode surveys
.
Social Science Computer Review
37
(
2
),
214
233
(
2019
)
[35]
Sexton
,
R.
,
Nguyen
,
T.
,
Roberts
,
D.L.
:
The use and prescription of pangolin in traditional Vietnamese medicine
.
Tropical Conservation Science
14
,
1
13
(
2021
)
[36]
Vuong
,
Q.-H.
, et al.:
Improving Bayesian statistics understanding in the age of Big Data with the bayesvl R package
.
Software Impacts
4
,
100016
(
2020
)
[37]
Vuong
,
Q.-H.
, et al.:
Bayesian analysis for social data: A step-by-step protocol and interpretation
.
MethodsX
7
,
100924
(
2020
)
[38]
Vuong
,
Q.-H.
,
Napier
,
N.K.
:
Acculturation and global mindsponge: An emerging market perspective
.
International Journal of Intercultural Relations
49
,
354
367
(
2015
)
[39]
Nguyen
,
M.-H.
, et al.:
Alice in suicideland: Exploring the suicidal ideation mechanism through the sense of connectedness and help-seeking behaviors
.
IJERPH
18
,
3681
(
2021
)
[40]
Vuong
,
Q.-H.
:
Global mindset as the integration of emerging socio-cultural values through mindsponge processes: A transition economy perspective
. In:
,
J.
, (ed.)
Global Mindsets: Exploration and Perspectives
, pp.
1
9–126
.
Routledge
,
Oxfordshire
(
2016
)
[41]
Vuong
,
Q.-H.
:
The (ir)rational consideration of the cost of science in transition economies
.
Nature Human Behaviour
2
,
5
(
2018
)
[42]
Vuong
,
Q.-H.
:
From children's literature to sustainability science, and young scientists for a more sustainable Earth
.
Journal of Sustainability Education
24
,
1
12
(
2020
)
[43]
Vuong
,
Q.-H.
:
Reform retractions to make them more transparent
.
Nature
582
,
149
(
2020
)
[44]
Vuong
,
Q.-H.
:
The semiconducting principle of monetary and environmental values exchange
.
10
,
284
290
(
2021
)

APPENDIX A

Figure A1.
Gelman plots.
Figure A1.
Gelman plots.

Autocorrelation plots.

Figure A2.
Autocorrelation plots.
Figure A2.
Autocorrelation plots.
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