Research Article
Public Awareness About Native and Exotic Plants: An Approach to Develop Sustainable Urban Plantation Plan
Muhammad Umair Shafique1,2, Muhammad Muzamil Ijaz1,2*, Adnan Younis1, Arslan Tufail2, Syed Muhammad Hamayun Tahir2, Munawar Hussain Almas2, M. Saleem Akhtar Khan2, M. Abdul Salam Khan2 and Usama Bin Arif2
1Institute of Horticultural Sciences, University of Agriculture, Faisalabad, Pakistan; 2Directorate of Floriculture (Training and Research), Punjab, Lahore, Pakistan.
Abstract | Public attitudes toward urban trees, as well as an understanding of their ecological services and drawbacks, may significantly affect urban tree management decisions, with significant implications for urban plantation sustainability. The present study was conducted in Faisalabad city, Pakistan. A questionnaire survey of 300 respondents from the city’s roadside, urban parks, and residential areas was undertaken to assess their perspectives on the present state of the plantation, and their knowledge level about the sustainable plantation, native, and exotic trees were evaluated. Public involvement and their opinions on the future development of sustainable urban plantations were also studied. The majority of the public showed dissatisfaction with the present status of the plantation (50.3 %). Results also showed that the majority of the public has a low level of knowledge about native (54.7%) and exotic trees (80.6%). Understanding of sustainable plantation was also found low (85.3%). P-values of the chi-square test indicated that education has a strong significant relationship with the knowledge level about urban plantations. To improve public knowledge and understanding of the development of sustainable plantations, municipal departments related to urban plantation development should initiate public awareness campaigns about the knowledge and benefits of native and exotic trees. The local municipality should also improve the plantation and must initiate programs to encourage public participation in the sustainable development of the plantation soon.
Received | November 14, 2024; Accepted | January 23, 2025; Published | April 24, 2025
*Correspondence | Muhammad Muzamil Ijaz, Institute of Horticultural Sciences, University of Agriculture, Faisalabad, Pakistan; Email: [email protected]
Citation | Shafique, M.U., M.M. Ijaz, A. Younis, A. Tufail, S.M.H. Tahir, M.H. Almas, M.S.A. Khan, M.A.S. Khan and U.B. Arif. 2025. Public awareness about native and exotic plants: An approach to develop sustainable urban plantation plan. Sarhad Journal of Agriculture, 41(2): 567-578.
DOI | https://dx.doi.org/10.17582/journal.sja/2025/41.2.567.578
Keywords | Public knowledge, Awareness programs, Government planning, Public involvement and Future goals
Copyright: 2025 by the authors. Licensee ResearchersLinks Ltd, England, UK.
This article is an open access article distributed under the terms and conditions of the Creative Commons Attribution (CC BY) license (https://creativecommons.org/licenses/by/4.0/).
Introduction
Trees are the important component of urban green spaces as they are linked to the supply of a variety of ecosystem services (McBride, 2017). Pollution abatement, microclimatic management, water regulation, soil quality, and the production of edible fruits are all examples of these services (Escobedo et al., 2011). Trees differ in terms of their physical and biological properties (such as height, foliage, lifetime, and so on); they contribute differently in the supply of certain ecological services (Roy et al., 2012). Around the world, native and exotic plant species combine in unique combination to develop urban forests (Alvey, 2006; Aronson et al., 2015; Gaertner et al., 2017). According to Jaksic and Castro (2020) exotic plant species have taken over urban green spaces in various parts of the world. In this framework, a debate has erupted about the relative importance of native and exotic tree species (Dearnorn and Kark, 2010; Conway et al., 2019). Some research encourages the usage of native trees for ecological reasons (Oldfield et al., 2015), while some researchers advocate for utilizing the ecological services supplied by tree species regardless of their biogeographically origin (Vaz et al., 2018).
Pakistan is a country where scientific research related to the importance of ecosystem services is still in its initial stages, but it is essential to tackle the increasingly deteriorating status of urban ecological health (Larondelle and Lauf, 2016; Haase et al., 2014). It is critical to raise public awareness in order to protect ecosystems, combat biodiversity loss, and comprehend the impact of humans on nature (Jim and Shan, 2013). Natural ecosystems provide vital benefits to humans like climate regulation, food, medicine, water and soil cycles, pest control and pollination. Public understanding is required for responsible usage of these natural ecosystem services. Human perceptions of the natural environment and the desire to contribute to its long-term viability are influenced by cultural standards and awareness of environmental benefits (Ward Thompson et al., 2005). For ecological integrity and social sustainability, urban environmental deterioration necessitates the restoration, maintenance, and improvement of ecological resources (Kaczorowska et al., 2016; Green et al., 2016; Alavipanah et al., 2017).
Faisalabad is Pakistan’s major textile industry centre and the province’s third megacity. It is renowned as the Manchester of Pakistan because of its massive textile industry, which is the country’s major income source. Faisalabad, being an industrial city, is fast growing in population, resulting in pollution, health, and social problems (Younis et al., 2002). Despite, the efforts of Government and private sector to improve the greenery level of the city to cope with the ever-rising challenge of urban heat island, smog and pollution problems the residents of Faisalabad are still facing serious environmental issues. Thus, there is a dire need to develop a plantation system that helps to reduce the environmental problems. In the landscape of Faisalabad, a higher number of exotic tree species are growing which are disturbing the ecological functioning of the city. Dominance of exotic species and low diversity of tree species results in improper ecological functioning. To improve the ecological functioning of ecosystem there is need to revise the ongoing plantation strategy in Faisalabad. In order to design natural resource planning strategies, it is necessary to understand and account for public views (Younis et al., 2018). The public’s response to the cause of reduced biodiversity is influenced by their level of biodiversity understanding. Furthermore, research reveals that people’s perceptions of community species richness are generally erroneous (Dunning, 1997). Public knowledge about the role of native and exotic tree species is one of key factor for developing sustainable plantation in urban areas. The theme of this study was to check the knowledge of public about native, exotic trees and sustainable plantation, views about present status of plantation, public involvement and recommendations about the future plantation. The results of this study will help us to analyze the understanding of public about sustainable plantation as well as the knowledge of native and exotic tree species, which is key factor for developing sustainable plantation.
Materials and Methods
Study site
The present study was conducted in Faisalabad city which is located at 31° 25’ 7.3740’’ N and 73° 4’ 44.7924’’ E Faisalabad, Pakistan (Figure 1). According to the theme of our study we divided the city into 3 areas (Roadsides urban parks and street of residential areas).
Collection of data
To record data, in total 300 local respondents were interviewed, 100 each from roadsides, public parks and residential areas. The data was gathered using a questionnaire method. To collect information, an English version of a questionnaire with open-ended and closed-ended questions was prepared. The questions were asked in the respondents’ native language (Urdu, Punjabi) for their convenience. The general public in the city was among the respondents. To ensure the maximum availability of persons, the interviews were held from 8:00 am to 11:00 am and 3:00 pm to 6:00 pm.
Data analysis
The gathered data were evaluated by chi square with SPSS (Statistical Package for Social Sciences). To establish the statistical significance of non-parametric population and qualitative observation, the Chi-square test was applied.
Results and Discussion
The distribution of respondents from the three selected areas includes: “roadsides” (male 78% and female 22%), “urban parks” (male 58% and female 42%), and “streets of residential areas” (males 64% and female 36%). Among all respondents regarding age, 45.3% (21-30 years), 33.3% (31-40 years), 15.7% (41–50 years), and the remaining 5.7% (51-60% years) (Table 1). Results with respect to the education level of the respondents showed: (Below Matric, 30.7%), (Matric, 21.7%), (Graduation, 34.6%), and (post-Graduation, 13%). The distribution regarding profession showed that the proportion of respondents in different businesses was: (government job, 19%), (private job, 35.3%), (business, 18.3%), and others (27.4%) (Table 1).
Respondents perspectives on the status of plantation on the roadside/public park/street
About the current status of plantation on roadsides, the majority of respondents stated the status of plantation as “average” (57%), while (31%) stated the status of plantation as “poor”, and only (12%) considered the status of plantation as “good” (Table 2). The P- value showed that there is statistically significant relationship between respondent’s education and views about the present status of plantation along roadside (Table 14). Regarding urban parks, most of the
Table 1: Demographics characteristics of respondents.
|
Gender |
Roadside |
Public park |
Street |
Total |
||||
|
Frequency |
Percent |
Frequency |
Percent |
Frequency |
Percent |
Frequency |
Percent |
|
|
Male |
78 |
78 |
58 |
58 |
64 |
64 |
200 |
66.7 |
|
Female |
22 |
22 |
42 |
42 |
36 |
36 |
100 |
33.3 |
|
Total |
100 |
100 |
100 |
100 |
100 |
100 |
||
|
Age |
||||||||
|
20-30 |
60 |
60 |
50 |
50 |
26 |
26 |
136 |
45.3 |
|
31-40 |
26 |
26 |
26 |
26 |
48 |
48 |
100 |
33.3 |
|
41-50 |
8 |
8 |
18 |
18 |
21 |
21 |
47 |
15.7 |
|
51-60 |
6 |
6 |
6 |
6 |
5 |
5 |
17 |
5.7 |
|
Total |
100 |
100 |
100 |
100 |
100 |
100 |
||
|
Qualification |
||||||||
|
Below Matric |
33 |
33 |
25 |
25 |
34 |
34 |
92 |
30.7 |
|
Matric |
17 |
17 |
29 |
29 |
19 |
19 |
65 |
21.7 |
|
Graduation |
36 |
36 |
36 |
36 |
32 |
32 |
104 |
34.6 |
|
Post-graduation |
14 |
14 |
10 |
10 |
15 |
15 |
39 |
13 |
|
Total |
100 |
100 |
100 |
100 |
100 |
100 |
||
|
Profession |
||||||||
|
Government job |
16 |
16 |
26 |
26 |
15 |
15 |
57 |
19 |
|
Private job |
43 |
43 |
31 |
31 |
32 |
32 |
106 |
35.3 |
|
Business |
17 |
17 |
13 |
13 |
25 |
25 |
55 |
18.3 |
|
Other |
24 |
24 |
30 |
30 |
28 |
28 |
82 |
27.4 |
|
Total |
100 |
100 |
100 |
100 |
100 |
100 |
||
Table 2: Frequency distribution of the respondents according to the status of plantation of roadside/public park/street.
|
Response |
Roadside |
Urban parks |
Streets |
Total |
|
Good |
12 (12%) |
27 (27%) |
20 (20%) |
59 (19.6 %) |
|
Average |
57 (57%) |
53 (53%) |
60 (60%) |
170 (56.7%) |
|
Poor |
31 (31%) |
20 (20%) |
20 (20%) |
71 (23.7%) |
|
Total |
100 |
100 |
100 |
respondents stated the present status of plantations as “average” (53%), while (27%) respondents stated the status of plantations as “good”, and only (20%) considered the status of plantations as “poor”. The P- value showed that there is statistically significant relationship between respondent’s education, profession, age and views about the present status of plantation in urban parks (Table 14). Regarding the planation of streets, the majority of the respondents considered the status of plantation “average” (60%), while 20% of the respondents classified it as “good” and (20%) of the respondents considered the planation status of streets “poor”. The P- value showed that there is statistically significant relationship between respondent’s education, profession and views about the present status of plantation along streets of residential areas (Table 14). Overall, the majority (56.7%) of respondents considered the status of the plantation “average,” while (23.7%) stated “poor” and only (19.6%) stated “good” (Table 2).
Respondents level of satisfaction with the current roadside/public park/street conditions
The results of the satisfaction level with the planation of roadsides revealed that the majority of respondents (60%) were dissatisfied with the planation, and only 40% of the respondents were satisfied with the planation of roadsides (Table 3). The P- value showed that there is statistically non-significant relationship between respondent’s gender, education, profession, age and level of satisfaction about the present status of plantation along roadside (Table 14). The satisfaction level of respondents about the plantation of urban parks showed that the majority of the respondents (56%) were satisfied, while (44%) of the respondents showed dissatisfaction with the urban park’s plantations. The P- value showed that there is statistically significant relationship between respondent’s education, profession and level of satisfaction about the present status of plantation in urban parks (Table 14) Respondents from streets showed (55%) satisfaction with the planation of streets while (45%) were dissatisfied with the planation level of streets. The P- value showed that there is statistically non-significant relationship between respondent’s gender, education, profession, age and level of satisfaction about the present status of plantation along streets of residential areas (Table 14). Overall, (50.3%) respondents showed satisfaction and (49.7%) were not satisfied with the planation of roadside/urban park/street (Table 3).
Table 3: Frequency distribution of the respondents according to the satisfaction with the plantation status of roadside/public park/street.
|
Response |
Roadside |
Urban parks |
Streets |
Total |
|
Yes |
40 |
56 |
55 |
151 (50.3 %) |
|
No |
60 |
44 |
45 |
149 (49.7%) |
|
Total |
100 |
100 |
100 |
Table 4: Frequency distribution of the respondents according to the knowledge about the term sustainable plantation.
|
Response |
Roadside |
Urban parks |
Streets |
Total |
|
Yes |
10 |
20 |
14 |
44 (14.7%) |
|
No |
90 |
80 |
86 |
256 (85.3%) |
|
Total |
100 |
100 |
100 |
Knowledge of respondents about sustainable plantations
Results regarding the knowledge of the term “sustainable planation” showed that, at the roadsides, the majority of respondents (90%) had no knowledge of sustainable planation. Only 10%) of the respondents had knowledge about sustainable plantations (Table 4). The P- value showed that there is statistically significant relationship between roadside respondent’s gender, education, profession, and knowledge about sustainable plantation (Table 14). (80%) respondents of urban parks had no knowledge about sustainable plantations, while only (20%) had knowledge about sustainable plantations. The P- value showed that there is statistically significant relationship between urban park respondent’s gender, education, profession, age and knowledge about sustainable plantation (Table 14). On the streets, 86% of respondents were unaware of sustainable plantations, while 14% were. The P- value showed that there is statistically significant relationship between street respondent’s education, profession, and knowledge about sustainable plantation (Table 14). Overall, a major portion of the respondents (85.3%) had no knowledge about sustainable plantations, and only (14.7% had knowledge about sustainable plantations (Table 4).
Opinion of the respondents about the sustainable status of plantation of roadside/public park/street
The respondents were questioned about the sustainable status of plantations along roadsides/public park/street. The results of the roadside planation survey revealed that (71%) of respondents thought roadside planation was not sustainable; while only (29%) thought roadside planation was sustainable (Table 5). The P- value showed that there is statistically non-significant relationship between roadside respondent’s gender, education, profession, age and opinion about sustainable status of roadside plantation (Table 14). Regarding the sustainability of urban park plantations, (52%) of the respondents considered it sustainable and (48%) termed it not sustainable. The P- value showed that there is statistically significant relationship between urban park respondent’s gender, education, profession, and opinion about sustainable status of urban park plantation (Table 14). (55%) of respondents considered the planation of streets not sustainable, but according to (45%) respondents, streets have sustainable plantation. The P- value showed that there is statistically significant relationship between street respondent’s education, profession, and opinion about sustainable status of street plantation (Table 14). Overall results showed that (58%) of the respondents considered that plantation on the roadside/public park/street as not sustainable and only (42%) stated it as sustainable (Table 5).
Table 5: Frequency distribution of the respondents about the sustainable status of plantation of roadside/public park/street.
|
Response |
Roadside |
Urban Parks |
Streets |
Total |
|
Yes |
29 (29%) |
52 (52%) |
45 (45%) |
126 (42%) |
|
No |
71(71%) |
48(48%) |
55 (55%) |
174 (58%) |
|
Total |
100 |
100 |
100 |
Respondent’s level of knowledge about native trees
Different questions were asked of respondents related to native trees (definition of native trees, name of a few native trees). According to the answers of the respondents, their knowledge level was judged and rated in three categories (high, medium, and low). Results from roadside respondents revealed that the majority of the public (68%) have a low level of knowledge, (26%) respondents had a medium level of knowledge, and a high level of native tree knowledge was observed in only (6%) respondents (Table 6). The P- value showed that there is statistically significant relationship between roadside respondent’s gender, education, profession, and knowledge about native trees (Table 14). Results from urban park respondents revealed that most people have low levels of knowledge about native trees (49%), while (41%) have a medium level of knowledge and only (10%) have a high level of knowledge about native trees. The P- value showed that there is statistically significant relationship between urban park respondent’s genders, education, profession, age and knowledge about “native trees” (Table 14). Results from street respondents showed that the majority of the respondents have a medium level of knowledge (52%), while (47%) have a low level of knowledge and only (1%) have a high level of knowledge about native trees. The P- value showed that there is statistically significant relationship between street respondent’s gender, education, profession, and knowledge about “native trees” (Table 14). Overall, the majority of the respondents has a low level of knowledge (54.7%); followed by (39.7%) respondents with a medium level of knowledge, and only (5.6%) respondents have a high level of knowledge about native trees (Table 6).
Table 6: Frequency distribution of the respondents according to the knowledge level about native trees.
|
Response |
Roadside |
Urban parks |
Streets |
Total |
|
High |
6 (6%) |
10 (10%) |
1 (1%) |
17 (5.6%) |
|
Medium |
26 (26%) |
41 (41%) |
52 (52%) |
119 (39.7%) |
|
Low |
68 (68%) |
49 (49%) |
47 (47%) |
164 (54.7%) |
|
Total |
100 |
100 |
100 |
Respondents level of knowledge about exotic trees
Different questions were asked of respondents related to exotic trees (definition of exotic trees, and the names of a few exotic trees). According to the answers of the respondents, their knowledge level was judged and rated in three categories (High, Medium, and Low). Results from roadside respondents revealed that the majority of the public (86%) have a low level of knowledge. Only (8%) respondents had a medium level of knowledge, and a high level of exotic tree knowledge was observed in only (6%) respondents (Table 7). The P- value showed that there is statistically significant relationship between roadside respondent’s gender, education, profession, and knowledge about “exotic trees” (Table 14). Results from urban park respondents revealed that most people have low levels of knowledge about exotic trees (72%), while (24%) have a medium level of knowledge and only (4%) have a high level of knowledge about exotic trees. The P- value showed that there is statistically significant relationship between urban park respondent’s genders, education, profession, age and knowledge about “exotic trees” (Table 14). Results from street respondents showed that the majority of the respondents have a low level of knowledge (84%), while (15%) have a medium level of knowledge and only (1%) have a high level of knowledge about exotic trees. The P- value showed that there is statistically significant relationship between street respondent’s gender, education, profession, and knowledge about “exotic trees” (Table 14). Overall, the majority of the respondents has a low level of knowledge (80.6%); followed by (15.7%) respondents with a medium level of knowledge, and only (3.7%) respondents have a high level of knowledge about exotic trees (Table 7).
Table 7: Frequency distribution of the respondents according to the knowledge level about exotic trees.
|
Response |
Roadside |
Urban parks |
Streets |
Total |
|
High |
6 (6%) |
4 (4%) |
1 (1%) |
11 (3.7%) |
|
Medium |
8 (8%) |
24 (24%) |
15 (15%) |
47 (15.7%) |
|
Low |
86 (86%) |
72 (72%) |
84 (84%) |
242 (80.6%) |
|
Total |
100 |
100 |
100 |
Respondents preferences for similar or diverse trees in their surroundings
This question was asked to judge the public’s liking of plantation patterns in their surroundings. At roadsides, (68%) of respondents liked to see a variety of trees, and only (32%) wanted to see similar types of trees around (Table 8). The P- value showed that there is statistically significant relationship between roadside respondent’s education, and preferences for similar or diverse trees in their surroundings (Table 14). In urban parks, (58%) of respondents liked to see a variety of trees, while 42%) wanted to have similar types of trees around their surroundings. The P- value showed that there is statistically significant relationship between urban park respondent’s education, profession, age and preferences for similar or diverse trees in their surroundings (Table 14). (85%) respondents of streets wanted to see a variety of trees, and only (15%) wanted to see similar trees in their surroundings. The P- value showed that there is statistically significant relationship between street respondent’s gender, education, profession, and preferences for similar or diverse trees in their surroundings (Table 14). Overall, (70.3%) of respondents want to see a variety of trees, while only (29.7%) want similar trees in their surroundings (Table 8).
Table 8: Frequency distribution of the respondents according to their likeness about similar or variety of trees around them.
|
Response |
Roadside |
Urban parks |
Streets |
Total |
|
Similar trees |
32 (32%) |
42 (42%) |
15(15%) |
89(29.7%) |
|
Variety of trees |
68 (68%) |
58 (58%) |
85(885%) |
211(70.3%) |
|
Total |
100 |
100 |
100 |
Table 9: Frequency distribution of the respondents according to their opinion, about the responsibility of roadside/public park/street plantation.
|
Response |
Roadside |
Urban parks |
Streets |
Total |
|
Government |
55 (55%) |
45 (45%) |
36 (36%) |
136 (45.3%) |
|
Public |
6 (6%) |
7 (7%) |
23 (23%) |
36 (12.0%) |
|
Both |
39 (39%) |
48 (48%) |
41(41%) |
128 (42.7%) |
|
Total |
100 |
100 |
100 |
Opinion of respondents, according to their opinion, about the responsibility of roadside/urban park/street plantation
To evaluate the respondent’s perception regarding responsibility regarding the planation of roadside/urban park/street they were asked about their opinions. (55%) respondents from roadsides considered that roadside planation is the responsibility of the government, while, (39%) considered it the responsibility of both the public and the government, and only (6%) considered roadside planation as the public’s responsibility (Table 9). The P- value showed that there is statistically significant relationship between roadside respondent’s age and opinion about the responsibility of roadside plantation (Table 14). In urban parks, (48%) stated that the planation of urban parks is the responsibility of both the public and the government, while, (45%) respondents considered it the duty of the government and only (7%) considered the planation of urban parks a public responsibility. The P- value showed that there is statistically significant relationship between roadside respondent’s education, profession, age and opinion about the responsibility of urban park’s plantation (Table 14). Majority of street respondents (41%) considered street plantation as the responsibility of both public and government while, (36%) considered it government responsibility and only (23%) considered it public responsibility. The P- value showed that there is statistically significant relationship between street respondent’s education, profession, and opinion about the responsibility of street plantation (Table 14). Overall, (45.3%) respondents considered that planation of roadside/urban park/street as the responsibility of government while, (42.7%) opinioned that it should be the responsibility of both public and government and only (12%) considered it public responsibility (Table 9).
Table 10: Frequency distribution of the respondents according to their satisfaction with the efforts of government to improve greenery (plantation) level.
|
Response |
Roadside |
Urban parks |
Streets |
Total |
|
Yes |
48 (48%) |
58 (58%) |
62 (62%) |
168 (56.0%) |
|
No |
52 (52%) |
42 (42%) |
38 (38%) |
132 (44.0%) |
|
Total |
100 |
100 |
100 |
Opinions of respondents according to their satisfaction with the efforts of the government to improve greenery (plantation) level
Respondents were asked about their satisfaction level with the efforts of the government in improving roadside/urban park/street plantations. On roadside plantations, (52%) of respondents were dissatisfied, while (48%) were pleased with the government’s efforts to improve roadside plantations (Table 10). The P- value showed that there is statistically significant relationship between roadside respondent’s profession and satisfaction with the efforts of the government to improve greenery (plantation) level (Table 14). In urban parks, (58%) respondents showed satisfaction with government efforts, and (42%) were not satisfied with the efforts of the government in improving plantation of urban parks. The P- value showed that there is statistically significant relationship between urban park respondent’s profession and satisfaction with the efforts of the government to improve greenery (plantation) level (Table 14). (62%) respondents from streets showed satisfaction with the efforts of the government and (38%) were not satisfied with government efforts in improving the planation of streets. The P- value showed that there is statistically significant relationship between street respondent’s profession and satisfaction with the efforts of the government to improve greenery (plantation) level (Table 14). Overall, (56%) respondents were satisfied and (44%) were not satisfied with the government’s efforts in improving the roadside/urban park/street plantations (Table 10).
Opinions of respondents about the need to launch a plantation campaign
Respondents were questioned about the need to launch a plantation campaign on the roadside/urban park/street. Results showed that (90%) respondents from roadsides agreed and only (10% disagreed with the need to launch a plantation campaign along roadsides (Table 11). The P- value showed that there is statistically significant relationship between roadside respondent’s age and opinions about to launch a plantation campaign (Table 14). A majority of respondents (76%) from urban parks agreed with the need to launch a plantation campaign, while (24%) stated that there was no need to launch a plantation campaign. The P- value showed that there is statistically non-significant relationship between urban park respondent’s gender, education, profession, age and opinions about to launch a plantation campaign (Table 14). (95%) respondents want a plantation campaign in the streets, while (5%) suggested that there is no need to launch a plantation campaign in the streets. The P- value showed that there is statistically significant relationship between street respondent’s education, profession and opinions about to launch a plantation campaign (Table 14). Overall, (87%) respondents agreed and (13%) did not agree with the need to launch a plantation campaign on the roadside/urban park/street (Table 11).
Table 11: Frequency distribution of the respondents about the need of launching a plantation campaign.
|
Response |
Roadside |
Urban parks |
Streets |
Total |
|
Yes |
90 (90%) |
76 (76%) |
95 (95%) |
261(87.0%) |
|
No |
10 (10%) |
24 (24%) |
5 (5%) |
39 (13.0 %) |
|
Total |
100 |
100 |
100 |
Table 12: Frequency distribution of the respondents about their willingness of joining a planation campaign.
|
Response |
Roadside |
Urban parks |
Streets |
Total |
|
Yes |
72 (72%) |
48 (48%) |
80 (80%) |
200 (66.7%) |
|
No |
28 (28%) |
52 (52%) |
20 (20%) |
100 (33.3 %) |
|
Total |
100 |
100 |
100 |
Opinions of respondents about their willingness to join a planation campaign
Respondents were questioned about their willingness to join a plantation campaign on the roadside/urban park/street. Results showed that (72%) respondents from roadsides wanted to join, and only (28% did not want to join the plantation campaign along roadsides (Table 12). The P- value showed that there is statistically significant relationship between roadside respondent’s education, age and willingness to join a plantation campaign (Table 14). A majority of respondents (52%) from urban parks did not want to join the plantation campaign, while (48%) stated that, they wanted to join the plantation campaign. The P- value showed that there is statistically significant relationship between urban park respondent’s education, profession and willingness to join a plantation campaign (Table 14). (80%) of the respondents showed willingness to join, while (20%) showed no willingness to join a plantation campaign in the streets. The P- value showed that there is statistically significant relationship between street respondent’s education, profession and willingness to join a plantation campaign (Table 14). Overall, (66.7%) of respondents indicated a willingness to participate, while (33.3%) indicated a lack of interest in participating in a roadside/urban park/street plantation campaign (Table 12).
Opinions of respondents about the suggestions for the improvement of the roadside/urban park/street plantation
Suggestions were asked from respondents regarding the improvement of roadside/urban park/street plantations. On roadsides, (48%) respondents suggested plantation of trees, (26%) suggested proper care and maintenance, (16%) suggested ornamental trees and only (10%) suggested clean water availability for the improvement of roadside plantation (Table 13). The P- value showed that there is statistically significant relationship between roadside respondent’s gender, education, profession and suggestions for the improvement of roadside plantation (Table 14). In urban parks, (40%) suggested plantation of trees, (23%) suggested plantation of ornamental plants, (22%) recommended clean water availability, and only (15%) suggested proper care and maintenance for the improvement of urban park plantations. The P- value showed that there is statistically significant relationship between urban park respondent’s gender, education, profession, age and suggestions for the improvement of urban park’s plantation (Table 14). A majority of street respondents (49%) suggested tree plantation, (22%) suggested clean water availability, (21%) suggested proper care and maintenance, and only (8%) suggested the plantation of ornamental plants for the improvement of street plantation. The P- value showed that there is statistically significant relationship between street respondent’s gender, education, profession and suggestions for the improvement of street plantation (Table 14). Overall, (45.6%) suggested tree plantation, (20.6%) suggested proper care and maintenance, (18%) suggested clean water availability, and only (15.7%) suggested plantation of ornamental plants for the improvement of roadside/urban park/street plantation (Table 13).
Table 13: Frequency distribution of the respondents about the suggestions for the improvement of the urban plantation.
|
Response |
Roadside |
Urban parks |
Streets |
Total |
|
Tree plantation |
48 (48%) |
40 (40%) |
49 (49%) |
137(45.6%) |
|
Ornamental plants |
16 (16%) |
23 (23%) |
8 (8%) |
47 (15.7 %) |
|
Clean water availability |
10 (10) |
22 (22%) |
22 (22%) |
54 (18.0%) |
|
Proper care and maintenance |
26 (26%) |
15 (15%) |
21 (21%) |
62 (20.6%) |
|
Total |
100 |
100 |
100 |
This study investigates public perceptions of roadside, urban park, and street plantations, as well as knowledge of sustainable plantations, native trees, and exotic trees. Through this study, the public’s willingness to join the plantation campaign and suggestions for future recommendations and improvements to the roadside/urban park/street in Faisalabad were studied. In view of our survey results, the plantation status of Faisalabad is not good and almost half of the respondent showed dissatisfaction with the present plantation. There is a dire need to improve the plantation status of the city of Faisalabad. All the management responsible for plantations in Faisalabad must devise a plantation strategy to enhance the plantation level. According to Younis et al. (2018) the urban planners must establish a vision of the purpose and value of urban forests, and available resources must be appropriately targeted. In our study, respondents showed a greater willingness to be a part of the plantation campaign and also considered that, along with the government; the public must have to take part in plantation development and maintenance. For sustainable development of plantations in urban areas, during the planning process it is worthwhile considering the choice of local public (Younis et al., 2018). This depicts that, in order to properly manage the urban plantation, policymakers and practitioners must use
multiple types of interaction, such as education, to influence local people’s actions and views (Almas and Convey, 2016).
Unfortunately, our survey results revealed that the majority of the general public has very little knowledge and understanding of sustainable plantations, as well as native and exotic trees. The survey showed participant’s limited and inconsistent understanding reflects a larger issue of concern about how to interact with locals, especially those who aren’t already engaged in urban plantation issues. Participation of the community in the establishment and upkeep of urban green areas is essential (Younis et al., 2008). It has been stated by Riaz et al. (2012) that communities with a strong desire to contribute for the establishment of green spaces and tree planting are more sustainable than parks and green areas with no community involvement. Sarwar (2002) also reported that with the community involvement brings improvement in development and maintenance of urban green spaces. Lack of knowledge by the public about native and exotic tree species may leads to the choice of species for the landscape, which may disturb the ecological functioning of an ecosystem. Local residents are concerned about environmental issues and are willing to pay a higher price for ecologically friendly items (Russo and Fouts, 1997; Laroche et al., 2001; Yue et al., 2011). It is the need of the hour to encourage public for tree plantation but at the same time public awareness related to beneficial use of native trees and risks associated with the over use of exotic trees must be addressed via different campaigns on social media as well as electronic media. Locals should be educated on the usage of native flora, as proposed by Peppin et al. (2010). To raise public awareness of native plants, educational programmed should be launched, as well as technical and scientific information for landscape contractors through nursery catalogues, plant lists, and etc., (Alam et al., 2017). People who know about urban tree programmes and forestry services are more inclined to provide money and support the aims of tree planting programmes (Zhang and Zheng, 2011). Furthermore, awareness of common native species is associated with good opinions regarding urban biodiversity, native species, and overall environmental awareness (Kurz and Baudains, 2012). Public awareness related to environmental issues is essential because, if people’ behaviors are governed by their knowledge and attitudes, then teaching citizens about municipal urban forestry plans should assist accomplish the long-term goals outlined in such plans.
Respondents when inquired about the suggestions to improve the urban plantation. Most respondents suggested (45.6%) plantation of trees to improve the environmental functioning of the city. Keeping in view of our results, all the authorities responsible for plantation in Faisalabad must develop a proper plan to direct towards a sustainable plantation pattern. To successfully implement a plantation policy, public awareness campaigns and programs related to the use of native and exotic trees must be initiated at the local government level.
Conclusions and Recommendations
For developing the sustainable urban plantation, it is necessary that general public must have knowledge about native and exotic trees. Without community involvement it is not possible to develop and maintain plantation in urban areas. The local government should also have to work on sustainable plantation development which is only possible when local public have the awareness about the potential benefits and risks associated with native and exotic trees. Public awareness campaigns and programs about native and exotic trees must be initiated at government level. Electronic and print media may also play his part in providing general information about native and exotic tree uses in urban landscape. The government should also have to rethink about plantation strategy in order to develop city plantation on sustainable scale.
It is the need of the hour to enhance the plantation of urban areas to combat the problem of climate change. To enhance the plantation status, both local public and Government should play a positive role in term of plantation installation and management. Public awareness about the proper use of native and exotic plants should be carried out to improve public knowledge about the importance of native and exotic flora.
Acknowledgements
The authors are grateful to University of Agriculture Faisalabad and Directorate of Floriculture (T and R) Lahore, Pakistan for their invaluable support and contributions to this research experiment.
Novelty Statement
Knowledge about native and exotic trees is necessary for the sustainable development of plantation. Public awareness campaigns and programs about native and exotic trees must be initiated at government level.
Author’s Contribution
Muhammad Umair Shafique: Designed the experiment and questionaire.
Muhammad Muzamil Ijaz and Adnan Younis: Helped in data collection and manuscript write-up.
Arslan Tufail, Syed Muhammad Hamayun Tahir and M. Abdul Salam Khan: Data analysis and proofreading.
M. Saleem Akhtar Khan, Munawar Hussain Almas and Usama Bin Arif: Helped in relevant literature and format setting.
Conflict of interest
The authors have declared no conflict of interest.
References
Alam, H., J.Z.K. Khattak, S.B.T. Ppoyil, S.S. Kurup and T.S. Ksiksi. 2017. Landscaping with native plants in the UAE: A review. Emir. J. Food Agric., 3: 729-741. https://doi.org/10.9755/ejfa.2017.v29.i10.319
Alavipanah S., D. Haase, T. Lakes and S. Qureshi. 2017. Integrating the third dimension into the concept of urban ecosystem services: A review. Ecol. Indic., 72: 74-398. https://doi.org/10.1016/j.ecolind.2016.08.010
Almas, A.D. and T.M. Conway. 2016. The role of native species in urban forest planning and practice: A case study of carolinian Canada. Urban For. Urban Green., 17: 54-62. https://doi.org/10.1016/j.ufug.2016.01.015
Alvey, A.A., 2006. Promoting and preserving biodiversity in the urban forest. Urban for Urban Green., 5: 195-201. https://doi.org/10.1016/j.ufug.2006.09.003
Aronson, M.F.J., F.A. La Sorte, C.H. Nilon, M. Katti, M.A. Goddard, C.A. Lepczyk, P.S. Warren, N.S.G. Williams, S. Cilliers, B. Clarkson, C. Dobbs, C. Dolan, M. Hedblom, S. Klotz, J.L. Kooijmans, I. Kühn, I. MacGregor-Fors, M, McDonnell, U. Mörtberg, P. Pyšek, S. Siebert, J. Sushinsky, P. Werner and M. Winter. 2014. A global analysis of the impacts of urbanization on bird and plant diversity reveals key anthropogenic drivers. Proc. R. Soc. B, 281: 01-08. https://doi.org/10.1098/rspb.2013.3330
Conway, T.M., A.D. Almas and D. Coore. 2019. Ecosystem services, ecological integrity, and native species planting: How to balance these ideas in urban forest management. Urban For. Urban Green., 41: 1-5. https://doi.org/10.1016/j.ufug.2019.03.006
Dearnorn, D.G. and S. Kark. 2010. Motivations for conserving urban biodiversity. Conserv. Biol., 24: 432-440. https://doi.org/10.1111/j.1523-1739.2009.01328.x
Dunning, J.B., 1997. The missing awareness, part 2: Teaching students what a billion people looks like. Conserv. Biol., 11: 6-10. https://doi.org/10.1046/j.1523-1739.1997.96406.x
Escobedo, F.J., T. Kroeger and J.E. Wagner. 2011. Urban forest and pollution mitigation: Analyzing ecosystem services and disservices. Environ. Pollut., 159: 2078-2087. https://doi.org/10.1016/j.envpol.2011.01.010
Gaertner, M., J.R.U. Wilson, M.W. Cadotte, J.S. MacIvor, R.D. Zenni and D.M. Richardson. 2017. Non-native species in urban environments: patterns, processes, impacts and challenges. Biol. Invasions., 19: 3461-3469. https://doi.org/10.1007/s10530-017-1598-7
Green, T.L., J. Kronenberg, E. Andersson, T. Elmqvist and E. Gomez-Baggethun. 2016. Insurance value of green infrastructure in and around cities. Ecosystems., 19: 1051-1063. https://doi.org/10.1007/s10021-016-9986-x
Haase, D., N. Larondelle, E. Andersson, M. Artmann and S. Borgström. 2014. A quantitative review of urban ecosystem service assessments: Concepts, models, and implementation. Ambio. 43: 413-433. https://doi.org/10.1007/s13280-014-0504-0
Jaksic, F.M. and S.A. Castro. 2020. Biological invasions in the South American Anthropocene: Global causes and local impacts. Springer International Publishing. https://doi.org/10.1007/978-3-030-56379-0
Jim, C.Y. and X. Shan. 2013. Socio-economic effect on perception of urban green spaces in Guangzhou, China. Cities., 31: 123-131. https://doi.org/10.1016/j.cities.2012.06.017
Kaczorowska, A., J.H. Kain, J. Kronenberg and D. Haase. 2016. Ecosystem services in urban land use planning: integration challenges in complex urban settings-case of Stockholm. Ecosyst. Serv., 22: 204-212. https://doi.org/10.1016/j.ecoser.2015.04.006
Kurz, T. and C. Baudains. 2012. Biodiversity in the front yard: An investigation of landscape preference in a domestic urban context. Environ. Behav., 44: 166-196. https://doi.org/10.1177/0013916510385542
Laroche, M., J. Bergeron and G. Barbaro-Forleo. 2001. Targeting consumers who are willing to pay more for environmentally friendly products. J. Consum. Mark., 18: 503-520. https://doi.org/10.1108/EUM0000000006155
Larondelle, N. and S. Lauf. 2016. Balancing demand and supply of multiple urban ecosystem services on different spatial scales. Ecosyst. Serv., 22: 18-31. https://doi.org/10.1016/j.ecoser.2016.09.008
McBride, J.R., 2017. The world’s urban forest: History, composition, design, function and management. Springer. pp. 26-37. https://doi.org/10.1007/978-3-319-52108-4_7
Oldfield, E.E., S.A. Wood, C.A. Palm and M.A. Bradford. 2015. How much SOM is needed for sustainable agriculture? Front. Ecol. Environ., 13: 527-538. https://doi.org/10.1890/1540-9295-13.10.527
Peppin, D.L., P.Z. Fule, J.C. Lynn, A.L. Mottek-Lucas and C.H. Sieg. 2010. Market perceptions and opportunities for native plant production on the Southern Colorado Plateau. Restor. Ecol., 18: 113-124. https://doi.org/10.1111/j.1526-100X.2010.00656.x
Potgieter, L.J., M. Gaertner, C. Kueffer, B.M.H. Larson, S. Livingstone, P. O’Farrell and D.M. Richardson. 2017. Alien plants as mediators of ecosystem services and disservices in urban systems: A global review. Biol Invasions., 19: 3571-3588. https://doi.org/10.1007/s10530-017-1589-8
Riaz, A., A. Younis and S. Naveed. 2012. Impact analysis of urban and rural landscapes as perceived by respective communities: A case study of Faisalabad city, Pakistan. Acta Hortic., 954: 99-107. https://doi.org/10.17660/ActaHortic.2012.954.11
Roy, S., J. Byrne and C. Pickering. 2012. A systematic quantitative review of urban tree benefits, costs, and assessment methods across cities in different climatic zones. Urban For. Urban Green., 11: 351-363. https://doi.org/10.1016/j.ufug.2012.06.006
Russo, M.V. and P.A. Fouts. 1997. A resource based perspective on corporate environmental performance and profitability. Acad. Manage. J., 40: 534-559. https://doi.org/10.5465/257052
Sagoff, M., 2011. The quantification and valuation of ecosystem services. Ecol. Econ., 70: 497-502. https://doi.org/10.1016/j.ecolecon.2010.10.006
Santilli, L., S.A. Castro, J.A. Figueroa, N. Guerrero, C. Ray, M. Romero-Mieres, G. Rojas and N. Lavandero. 2018. Exotic species predominates in the urban woody flora of central Chile. Gayana Bot., 75: 568-588. https://doi.org/10.4067/S0717-66432018000200568
Sarwar, A., 2002. Planning green spaces in poverty line areas, Shadab colony, Noorpur and Chak no. 7, case study. M.Sc. (Hons.) Diss., Dept. Hort., Uni. of Agri., Faisalabad, Pakistan.
Vaz, A.S., P. Castro-Diez, O. Godoy, A. Alonso, M. Vila, A. Saldana, H. Marchante, A. Bayon, J.S. Silva, J.R. Vicente and J.R. Honrado. 2018. An indicator-based approach to analyses the effects of non-native tree species on multiple cultural ecosystem services. Ecol. Indic., 85: 48-56. https://doi.org/10.1016/j.ecolind.2017.10.009
Ward Thompson, C., P. Aspinall, S. Bell and C. Findlay. 2005. It gets you away from everyday life: Local woodlands and community use-what makes a difference. Landsc. Res., 30: 109-146. https://doi.org/10.1080/0142639042000324794
Younis, A., A. Riaz and M. Qasim. 2008. Case study: Impact of a well-planned landscape in delivering quality of life to city dwellers. Acta Hort., 775: 147-154. https://doi.org/10.17660/ActaHortic.2008.775.17
Younis, A., A. Riaz, M. Qasim and S. Akhtar. 2002. Development and management of green spaces on Sumundri road, Faisalabad: A case study. Pak. J. Agric. Sci., 39: 292-296.
Younis, A., M. Qasim, A. Riaz, M. Ishaq, F. Zulfiqar, A. Farooq and M.F. Hassan. 2018. Attitudes of citizens towards community involvement for development and maintenance of urban green spaces: A Faisalabad case study. Pak. J. Agric. Sci., 55: 1-12.
Yue, C., T.M. Hurley and N. Anderson. 2011. Do native and invasive labels affect consumer willingness to pay for plants? Evidence from experimental auctions. Agric. Econ., 42: 195-205. https://doi.org/10.1111/j.1574-0862.2010.00510.x
Zhang, Y. and B. Zheng. 2011. Assessments of citizen willingness to support urban forestry: An empirical study in Alabama. Arboric. Urban For., 37: 118-125. https://doi.org/10.48044/jauf.2011.016