By analyzing the application situation of greening tree species in Liuzhou City,this study aimed to put forward several strategies and suggestions for garden tree species planning in Liuzhou City according to relevant...By analyzing the application situation of greening tree species in Liuzhou City,this study aimed to put forward several strategies and suggestions for garden tree species planning in Liuzhou City according to relevant theories and principles.展开更多
To figure out the disease occurrence of landscape plants in the main urban area of Lu'an City,the author investigated the disease occurrence of landscape plants in park green space,residential green space,unit att...To figure out the disease occurrence of landscape plants in the main urban area of Lu'an City,the author investigated the disease occurrence of landscape plants in park green space,residential green space,unit attached green space and main road in the area under administration.The survey results showed that there were 29 species of urban landscape plant diseases,mainly powdery mildew and spot diseases.According to the characteristics of the diseases,the causes and problems of the diseases were analyzed,and the corresponding prevention and control measures were put forward.展开更多
Species, application frequencies, habitat features and combination modes of Rhododendron species in Kunming City were studied through random sampling in different subareas of Kunming City. The results show that Rhodod...Species, application frequencies, habitat features and combination modes of Rhododendron species in Kunming City were studied through random sampling in different subareas of Kunming City. The results show that Rhododendron species were widely applied in parks, residential areas and street-side green spaces. Diversified application patterns presented excellent landscape effects, but only a few species were used, for example, Rhododendron pulchrum Sweet., R. hybridum, R. simsii var. simsii, while R. delavayi Franch. and R. simsii var. mesembrinum Rehd. were occasionally found. Landscaping features of Kunming were characterized by domination of Rhododendron species, advantages and problems of Rhododendron species in landscaping of Kunming City were analyzed. It was proposed that introduction and domestication of wild Rhododendron species should be enhanced, rich germplasm resources of Rhododendron species should be fully used, and more indigenous Rhododendron species applied.展开更多
By investigating species, characteristics and landscaping application of colored-leaf species in Guang'an City, this paper proposed suggestions for the application of colored-leaf species in the local area.
Air quality has been a major health issue in urban areas in recent decades.</span></span><span><span><span style="font-family:""> Human activities release a large number of...Air quality has been a major health issue in urban areas in recent decades.</span></span><span><span><span style="font-family:""> Human activities release a large number of pollutants into the atmosphere which ha</span></span></span><span><span><span style="font-family:"">s</span></span></span><span><span><span style="font-family:""> a direct impact on plant health and lead</span></span></span><span><span><span style="font-family:"">s</span></span></span><span><span><span style="font-family:""> to ecosystem degradation. The objective of this study is to contribute to a better evaluation of the impact of the air quality of the city of Togo on biological resources. The determination of pollutants was done on samples of plant species with a strong link with the source of pollution. The determination of Sulfur dioxide (SO<sub>2</sub>) was done by the ripper method. The determination of carbon and estimation of CO<sub>2</sub> and CO by the colorimetric method. The determination of nitrogen was done by <span>the Kjeldhal method. The results showed that at the industrial level the</span> amount of CO<sub>2</sub> in </span></span></span><span><span><span style="font-family:""><i></span></span></span><span><span><i><span style="font-family:"">Alternanthera r</span></i></span></span><span><span><i><span style="font-family:"">e</span></i></span></span><span><span><i><span style="font-family:"">pens</span></i></span></span><span><span><i><span style="font-family:""></i></span></i></span></span><span><span><span style="font-family:""> is high with a value of 53.3911 <span>mg/ml. On the other hand</span></span></span></span><span><span><span style="font-family:"">,</span></span></span><span><span><span style="font-family:""> the quantity of CO in </span></span></span><span><span><span style="font-family:""><i></span></span></span><span><span><i><span style="font-family:"">Senna occidentalis</span></i></span></span><span><span><i><span style="font-family:""></i></span></i></span></span><span><span><span style="font-family:""> is</span></span></span><span><span><span style="font-family:""> 44.3619 mg/ml. In </span></span></span><span><span><span style="font-family:""><i></span></span></span><span><span><i><span style="font-family:"">Pithecellobium dulce</span></i></span></span><span><span><i><span style="font-family:""></i></span></i></span></span><span><span><span style="font-family:"">,</span></span></span><span><span><span style="font-family:""> the quantity of SO<sub>2</sub> and NO<sub>2</sub> are evaluated respectively to 0</span></span></span><span><span><span style="font-family:"">.</span></span></span><span><span><span style="font-family:"">1588 mg/ml and 0</span></span></span><span><span><span style="font-family:"">.</span></span></span><span><span><span style="font-family:"">3696 mg/ml. Regarding to the dumps, the quantity of CO<sub>2</sub> in </span></span></span><span><span><span style="font-family:""><i></span></span></span><span><span><i><span style="font-family:"">Newbouldia laevis</span></i></span></span><span><span><i><span style="font-family:""></i></span></i></span></span><span><span><span style="font-family:""> is very high with a value of 65.8508 mg/ml. On the other hand the amount of CO in </span></span></span><span><span><span style="font-family:""><i></span></span></span><span><span><i><span style="font-family:"">Senna occidentalis</span></i></span></span><span><span><i><span style="font-family:""></i></span></i></span></span><span><span><i><span style="font-family:""> </span></i></span></span><span><span><span style="font-family:"">is 51.6106 mg/ml. The quantity of SO<sub>2</sub> in </span></span></span><span><span><span style="font-family:""><i></span></span></span><span><span><i><span style="font-family:"">Newbouldia laevis</span></i></span></span><span><span><i><span style="font-family:""></i></span></i></span></span><span><span><span style="font-family:""> is 0.2101 mg/ml and NO<sub>2</sub> in </span></span></span><span><span><span style="font-family:""><i></span></span></span><span><span><i><span style="font-family:"">Ocimum canum</span></i></span></span><span><span><i><span style="font-family:""></i></span></i></span></span><span><span><span style="font-family:""> is 0.2744 mg/ml. At the level of roads, the quantities of CO<sub>2</sub> and CO in </span></span></span><span><span><span style="font-family:""><i></span></span></span><span><span><i><span style="font-family:"">Eragrostis tenella</span></i></span></span><span><span><i><span style="font-family:""></i></span></i></span></span><span><span><span style="font-family:""> are very high with values respectively equal to 74.4092</span></span></span><span><span><span style="font-family:""> mg/ml and 62.2654 mg/ml. On the other hand</span></span></span><span><span><span style="font-family:"">,</span></span></span><span><span><span style="font-family:""> the amount of NO<sub>2</sub> in </span></span></span><span><span><span style="font-family:""><i></span></span></span><span><span><i><span style="font-family:"">Amaranthus</span></i></span></span><span><span><i><span style="font-family:""></i></span></i></span></span><span><span><span style="font-family:""> sp is 0.2304 mg/ml and that of SO<sub>2</sub> in </span></span></span><span><span><span style="font-family:""><i></span></span></span><span><span><i><span style="font-family:"">Eragrostis Tenella</span></i></span></span><span><span><i><span style="font-family:""></i></span></i></span></span><span><span><span style="font-family:""> is 0.1691 mg/ml. The use of a plant bioindicator sensitive to pollutants, allowed concluding that the air of the city of Lome is polluted. The concentration of <span>carbon dioxide and carbon monoxide is much more evident in return </span></span></span></span><span><span><span style="font-family:"">when </span></span></span><span><span><span style="font-family:"">the </span></span></span><span><span><span style="font-family:"">health of plant species is threatened.展开更多
Urban areas are a major source of anthropogenic carbon dioxide (CO<sub><span style="font-family:Verdana;">2</span></sub><span style="font-family:Verdana;">) emissions ...Urban areas are a major source of anthropogenic carbon dioxide (CO<sub><span style="font-family:Verdana;">2</span></sub><span style="font-family:Verdana;">) emissions because of road traffic and local heating with natural gas, oil or coal. Rome is among the largest European cities (129,000 ha) with a large volume of green areas (69.6% of the total Municipality area). The CO</span><sub><span style="font-family:Verdana;">2</span></sub><span style="font-family:Verdana;"> sequestration (CS) capability for the greenery extending for about 300 km</span><sup><span style="font-family:Verdana;">2</span></sup><span style="font-family:Verdana;"> inside the area delimited by the Great Ring Road (GRA) in Rome was calculated combining satellite data with CS data measured in the field. Data from Sentinel-2 were collected and the Normalized Difference Vegetation Index (NDVI) was computed on a pixel-base. Three plant classes homogeneous in terms of annual NDVI profile were identified: deciduous trees (DT), evergreen trees (ET) and meadows (M) covering an area of 14,142.027 ha within the GRA, of which M had the highest percentage (48%), followed by DT (27%) and ET (25%). CS ranged from 428,241</span><span style="font-family:Verdana;">,</span><span style="font-family:Verdana;">492.9 </span><span style="font-family:Verdana;">T</span><span style="font-family:;" "=""><span style="font-family:Verdana;">ons CO</span><sub><span style="font-family:Verdana;">2</span></sub><span style="font-family:Verdana;"> year</span><sup><span style="font-family:Verdana;">-1</span></sup><span style="font-family:Verdana;"> (ET) to 263,072</span></span><span style="font-family:Verdana;">,</span><span style="font-family:;" "=""><span style="font-family:Verdana;">460.6 Tons CO</span><sub><span style="font-family:Verdana;">2</span></sub><span style="font-family:Verdana;"> year</span><sup><span style="font-family:Verdana;">-1</span></sup><span style="font-family:Verdana;"> (M). The total CS of the greenery inside the GRA was 1049,490,355.4 Tons CO</span><sub><span style="font-family:Verdana;">2</span></sub><span style="font-family:Verdana;"> year</span><sup><span style="font-family:Verdana;">-1</span></sup><span style="font-family:Verdana;"> resulting in an annual economic value of $772,424,901.6/ha. The CO</span><sub><span style="font-family:Verdana;">2</span></sub><span style="font-family:Verdana;"> sequestration capability of the considered plant classes could be incorporated into the national greenhouse gas emission budget to calculate the contribution of CO</span><sub><span style="font-family:Verdana;">2</span></sub><span style="font-family:Verdana;"> sequestration to the economy of Rome.</span></span>展开更多
Located at the fringe of the western plain in Sichuan Province and the confluence of the Minjiang, Qingyijiang and Daduhe Rivers, Leshan is an historic city of major importance to tourism. As one of the earliest towns...Located at the fringe of the western plain in Sichuan Province and the confluence of the Minjiang, Qingyijiang and Daduhe Rivers, Leshan is an historic city of major importance to tourism. As one of the earliest towns originally under the jurisdiction of Kai Ming Shi, the king of Shu during the Western Zhou Dynasty (B.C. 1066—展开更多
针对如何通过预测未来土地利用结构的变化,以解决不合理的土地覆被类型造成的人地矛盾逐渐尖锐,以及生态、经济、社会发展失衡等问题,通过马尔可夫-斑块生成土地利用模拟(Markov-patch-generating land use simulation,Markov-PLUS)模型...针对如何通过预测未来土地利用结构的变化,以解决不合理的土地覆被类型造成的人地矛盾逐渐尖锐,以及生态、经济、社会发展失衡等问题,通过马尔可夫-斑块生成土地利用模拟(Markov-patch-generating land use simulation,Markov-PLUS)模型,以2000、2010、2020年乐山市土地覆被数据为基础,模拟2030年在自然惯性发展、生态保护、耕地保护3种不同情景下土地覆被的数量以及空间格局的变化,并对其转化情况进行分析。结果表明,Markov-PLUS模型模拟精度较高,可以较好地预测未来乐山市不同发展情景下土地覆被的数量以及空间格局的变化。土地覆被在3种情景中都有变化,耕地、草地、灌木地以及湿地面积在3种情景中均下降,水体、人造地表面积均上升,林地在生态保护情景下上升,其余2种情景下降。3种发展情景对比发现:生态保护情景下能较好保护乐山市生态环境;耕地保护情景下需要更严格的政策干预来保护耕地。该研究通过模拟预测不同情景下乐山市未来土地覆被变化,从而为该地区土地利用规划提供可能的参考。展开更多
文摘By analyzing the application situation of greening tree species in Liuzhou City,this study aimed to put forward several strategies and suggestions for garden tree species planning in Liuzhou City according to relevant theories and principles.
基金Supported by Youth Project of Natural Science Foundation of Anhui Province(2008085QC135)Postdoctoral Workstation Project of West Anhui University(WXBSH2020003)+4 种基金Key Program of Natural Science Research Project for Anhui Universities(KJ2021A0954)Forestry Carbon Sequestration Self-funded Science and Technology Project of Anhui Province(LJH[2022]267)Subject of Lu'an Forestry Bureau(0045021093)School-level Quality Engineering Project of West Anhui University(wxxy2021017)Provincial Quality Engineering Project of West Anhui University(2022jyxm1765).
文摘To figure out the disease occurrence of landscape plants in the main urban area of Lu'an City,the author investigated the disease occurrence of landscape plants in park green space,residential green space,unit attached green space and main road in the area under administration.The survey results showed that there were 29 species of urban landscape plant diseases,mainly powdery mildew and spot diseases.According to the characteristics of the diseases,the causes and problems of the diseases were analyzed,and the corresponding prevention and control measures were put forward.
基金Supported by Scientific Research Start-up Foundation(A2002160)Yunnan Province Natural Science Foundation(2009CD064)
文摘Species, application frequencies, habitat features and combination modes of Rhododendron species in Kunming City were studied through random sampling in different subareas of Kunming City. The results show that Rhododendron species were widely applied in parks, residential areas and street-side green spaces. Diversified application patterns presented excellent landscape effects, but only a few species were used, for example, Rhododendron pulchrum Sweet., R. hybridum, R. simsii var. simsii, while R. delavayi Franch. and R. simsii var. mesembrinum Rehd. were occasionally found. Landscaping features of Kunming were characterized by domination of Rhododendron species, advantages and problems of Rhododendron species in landscaping of Kunming City were analyzed. It was proposed that introduction and domestication of wild Rhododendron species should be enhanced, rich germplasm resources of Rhododendron species should be fully used, and more indigenous Rhododendron species applied.
基金Sponsored by Research Program of Sichuan Provincial Department of Education(14ZB0390)
文摘By investigating species, characteristics and landscaping application of colored-leaf species in Guang'an City, this paper proposed suggestions for the application of colored-leaf species in the local area.
文摘Air quality has been a major health issue in urban areas in recent decades.</span></span><span><span><span style="font-family:""> Human activities release a large number of pollutants into the atmosphere which ha</span></span></span><span><span><span style="font-family:"">s</span></span></span><span><span><span style="font-family:""> a direct impact on plant health and lead</span></span></span><span><span><span style="font-family:"">s</span></span></span><span><span><span style="font-family:""> to ecosystem degradation. The objective of this study is to contribute to a better evaluation of the impact of the air quality of the city of Togo on biological resources. The determination of pollutants was done on samples of plant species with a strong link with the source of pollution. The determination of Sulfur dioxide (SO<sub>2</sub>) was done by the ripper method. The determination of carbon and estimation of CO<sub>2</sub> and CO by the colorimetric method. The determination of nitrogen was done by <span>the Kjeldhal method. The results showed that at the industrial level the</span> amount of CO<sub>2</sub> in </span></span></span><span><span><span style="font-family:""><i></span></span></span><span><span><i><span style="font-family:"">Alternanthera r</span></i></span></span><span><span><i><span style="font-family:"">e</span></i></span></span><span><span><i><span style="font-family:"">pens</span></i></span></span><span><span><i><span style="font-family:""></i></span></i></span></span><span><span><span style="font-family:""> is high with a value of 53.3911 <span>mg/ml. On the other hand</span></span></span></span><span><span><span style="font-family:"">,</span></span></span><span><span><span style="font-family:""> the quantity of CO in </span></span></span><span><span><span style="font-family:""><i></span></span></span><span><span><i><span style="font-family:"">Senna occidentalis</span></i></span></span><span><span><i><span style="font-family:""></i></span></i></span></span><span><span><span style="font-family:""> is</span></span></span><span><span><span style="font-family:""> 44.3619 mg/ml. In </span></span></span><span><span><span style="font-family:""><i></span></span></span><span><span><i><span style="font-family:"">Pithecellobium dulce</span></i></span></span><span><span><i><span style="font-family:""></i></span></i></span></span><span><span><span style="font-family:"">,</span></span></span><span><span><span style="font-family:""> the quantity of SO<sub>2</sub> and NO<sub>2</sub> are evaluated respectively to 0</span></span></span><span><span><span style="font-family:"">.</span></span></span><span><span><span style="font-family:"">1588 mg/ml and 0</span></span></span><span><span><span style="font-family:"">.</span></span></span><span><span><span style="font-family:"">3696 mg/ml. Regarding to the dumps, the quantity of CO<sub>2</sub> in </span></span></span><span><span><span style="font-family:""><i></span></span></span><span><span><i><span style="font-family:"">Newbouldia laevis</span></i></span></span><span><span><i><span style="font-family:""></i></span></i></span></span><span><span><span style="font-family:""> is very high with a value of 65.8508 mg/ml. On the other hand the amount of CO in </span></span></span><span><span><span style="font-family:""><i></span></span></span><span><span><i><span style="font-family:"">Senna occidentalis</span></i></span></span><span><span><i><span style="font-family:""></i></span></i></span></span><span><span><i><span style="font-family:""> </span></i></span></span><span><span><span style="font-family:"">is 51.6106 mg/ml. The quantity of SO<sub>2</sub> in </span></span></span><span><span><span style="font-family:""><i></span></span></span><span><span><i><span style="font-family:"">Newbouldia laevis</span></i></span></span><span><span><i><span style="font-family:""></i></span></i></span></span><span><span><span style="font-family:""> is 0.2101 mg/ml and NO<sub>2</sub> in </span></span></span><span><span><span style="font-family:""><i></span></span></span><span><span><i><span style="font-family:"">Ocimum canum</span></i></span></span><span><span><i><span style="font-family:""></i></span></i></span></span><span><span><span style="font-family:""> is 0.2744 mg/ml. At the level of roads, the quantities of CO<sub>2</sub> and CO in </span></span></span><span><span><span style="font-family:""><i></span></span></span><span><span><i><span style="font-family:"">Eragrostis tenella</span></i></span></span><span><span><i><span style="font-family:""></i></span></i></span></span><span><span><span style="font-family:""> are very high with values respectively equal to 74.4092</span></span></span><span><span><span style="font-family:""> mg/ml and 62.2654 mg/ml. On the other hand</span></span></span><span><span><span style="font-family:"">,</span></span></span><span><span><span style="font-family:""> the amount of NO<sub>2</sub> in </span></span></span><span><span><span style="font-family:""><i></span></span></span><span><span><i><span style="font-family:"">Amaranthus</span></i></span></span><span><span><i><span style="font-family:""></i></span></i></span></span><span><span><span style="font-family:""> sp is 0.2304 mg/ml and that of SO<sub>2</sub> in </span></span></span><span><span><span style="font-family:""><i></span></span></span><span><span><i><span style="font-family:"">Eragrostis Tenella</span></i></span></span><span><span><i><span style="font-family:""></i></span></i></span></span><span><span><span style="font-family:""> is 0.1691 mg/ml. The use of a plant bioindicator sensitive to pollutants, allowed concluding that the air of the city of Lome is polluted. The concentration of <span>carbon dioxide and carbon monoxide is much more evident in return </span></span></span></span><span><span><span style="font-family:"">when </span></span></span><span><span><span style="font-family:"">the </span></span></span><span><span><span style="font-family:"">health of plant species is threatened.
文摘Urban areas are a major source of anthropogenic carbon dioxide (CO<sub><span style="font-family:Verdana;">2</span></sub><span style="font-family:Verdana;">) emissions because of road traffic and local heating with natural gas, oil or coal. Rome is among the largest European cities (129,000 ha) with a large volume of green areas (69.6% of the total Municipality area). The CO</span><sub><span style="font-family:Verdana;">2</span></sub><span style="font-family:Verdana;"> sequestration (CS) capability for the greenery extending for about 300 km</span><sup><span style="font-family:Verdana;">2</span></sup><span style="font-family:Verdana;"> inside the area delimited by the Great Ring Road (GRA) in Rome was calculated combining satellite data with CS data measured in the field. Data from Sentinel-2 were collected and the Normalized Difference Vegetation Index (NDVI) was computed on a pixel-base. Three plant classes homogeneous in terms of annual NDVI profile were identified: deciduous trees (DT), evergreen trees (ET) and meadows (M) covering an area of 14,142.027 ha within the GRA, of which M had the highest percentage (48%), followed by DT (27%) and ET (25%). CS ranged from 428,241</span><span style="font-family:Verdana;">,</span><span style="font-family:Verdana;">492.9 </span><span style="font-family:Verdana;">T</span><span style="font-family:;" "=""><span style="font-family:Verdana;">ons CO</span><sub><span style="font-family:Verdana;">2</span></sub><span style="font-family:Verdana;"> year</span><sup><span style="font-family:Verdana;">-1</span></sup><span style="font-family:Verdana;"> (ET) to 263,072</span></span><span style="font-family:Verdana;">,</span><span style="font-family:;" "=""><span style="font-family:Verdana;">460.6 Tons CO</span><sub><span style="font-family:Verdana;">2</span></sub><span style="font-family:Verdana;"> year</span><sup><span style="font-family:Verdana;">-1</span></sup><span style="font-family:Verdana;"> (M). The total CS of the greenery inside the GRA was 1049,490,355.4 Tons CO</span><sub><span style="font-family:Verdana;">2</span></sub><span style="font-family:Verdana;"> year</span><sup><span style="font-family:Verdana;">-1</span></sup><span style="font-family:Verdana;"> resulting in an annual economic value of $772,424,901.6/ha. The CO</span><sub><span style="font-family:Verdana;">2</span></sub><span style="font-family:Verdana;"> sequestration capability of the considered plant classes could be incorporated into the national greenhouse gas emission budget to calculate the contribution of CO</span><sub><span style="font-family:Verdana;">2</span></sub><span style="font-family:Verdana;"> sequestration to the economy of Rome.</span></span>
文摘Located at the fringe of the western plain in Sichuan Province and the confluence of the Minjiang, Qingyijiang and Daduhe Rivers, Leshan is an historic city of major importance to tourism. As one of the earliest towns originally under the jurisdiction of Kai Ming Shi, the king of Shu during the Western Zhou Dynasty (B.C. 1066—
文摘针对如何通过预测未来土地利用结构的变化,以解决不合理的土地覆被类型造成的人地矛盾逐渐尖锐,以及生态、经济、社会发展失衡等问题,通过马尔可夫-斑块生成土地利用模拟(Markov-patch-generating land use simulation,Markov-PLUS)模型,以2000、2010、2020年乐山市土地覆被数据为基础,模拟2030年在自然惯性发展、生态保护、耕地保护3种不同情景下土地覆被的数量以及空间格局的变化,并对其转化情况进行分析。结果表明,Markov-PLUS模型模拟精度较高,可以较好地预测未来乐山市不同发展情景下土地覆被的数量以及空间格局的变化。土地覆被在3种情景中都有变化,耕地、草地、灌木地以及湿地面积在3种情景中均下降,水体、人造地表面积均上升,林地在生态保护情景下上升,其余2种情景下降。3种发展情景对比发现:生态保护情景下能较好保护乐山市生态环境;耕地保护情景下需要更严格的政策干预来保护耕地。该研究通过模拟预测不同情景下乐山市未来土地覆被变化,从而为该地区土地利用规划提供可能的参考。