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Frontiers of Environmental Science & Engineering

ISSN 2095-2201

ISSN 2095-221X(Online)

CN 10-1013/X

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2018 Impact Factor: 3.883

Front.Environ.Sci.Eng.    0, Vol. Issue () : 747-756    https://doi.org/10.1007/s11783-014-0644-2
RESEARCH ARTICLE
Impacts of de-icing salt pollution on urban road greenspace: a case study of Beijing
Zhouyuan LI1,2,Yingmei LIANG3,*(),Junhui ZHOU4,Xiao SUN1,5
1. College of Environmental Science and Engineering, Beijing Forestry University, Beijing 100083, China
2. School of Environment, Tsinghua University, Beijing 100084, China
3. Museum of Beijing Forestry University, Beijing 100083, China
4. College of Biological Sciences and Technology, Beijing Forestry University, Beijing 100083, China
5. Warwick Business School, University of Warwick, Coventry CV4 7ES, United Kingdom
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Abstract

De-icing salt contamination of urban soil and greenspace has been a common issue of concern in many countries for years. In the 2009/2010 winter, Beijing experienced a contamination accident resulting from the overuse of de-icing salt, reported as almost 30000 tons, which severely damaged urban vegetation alongside roadways. The methods of sampling and rating for both soil contamination and response of the plant populations were developed to rapidly assess this emergency environmental event. Results showed that the shrubs were more severely damaged than the arbors in terms of both degree and extent, as almost all of the surveyed shrubs were severely damaged from the salt contamination, while only about 1/4 of the recorded arbors were rated as “severely injured” according to the integral plant injury index. The rating of the injury level showed that the trees like Pinus bungeana, Sophora japonica, and the shrubs like Euonymus japonicus, Sabina vulgaris showed less tolerance to de-icing salt pollution. The patterns of vegetation damage demonstrated that the ever-green shrubs alongside roads and the deciduous arbors in the center of roads were most vulnerable to the salt damage.

Keywords de-icing salt      environmental impact assessment      urban ecology      greenspace     
Corresponding Author(s): Yingmei LIANG   
Issue Date: 20 June 2014
 Cite this article:   
Zhouyuan LI,Yingmei LIANG,Junhui ZHOU, et al. Impacts of de-icing salt pollution on urban road greenspace: a case study of Beijing[J]. Front.Environ.Sci.Eng., 0, (): 747-756.
 URL:  
https://academic.hep.com.cn/fese/EN/10.1007/s11783-014-0644-2
https://academic.hep.com.cn/fese/EN/Y0/V/I/747
Fig.1  Meterological records of Beijing in the 2009/2010 winter (The triangle marks mean the time of the de-icing salt using) (a); Downtown of Beijing as the study area and the sampled lines in the survey (b)
salinity / %salinized degreevisual criterionphotos of the typical soils*rating for LSC
<0.1non-salinized soilno the white scalded patches<InlineMediaObject OutputMedium="Online"><ImageObject FileRef="fse-13062-lzy.doc_images/fse-13062-lzy-tb1fig1.jpg" ScaleToFitWidth="84.0pt" ScaleToFit="1"/></InlineMediaObject><InlineMediaObject OutputMedium="All"><ImageObject FileRef="fse-13062-lzy.doc_images/fse-13062-lzy-tb1fig1.tif" Format="TIFF" OrigFileRef="FSE-13062-LZY-tb1fig1" ScaleToFitHeight="86.9pt" ScaleToFitWidth="84.0pt" ScaleToFit="1"/></InlineMediaObject>0
0.1-0.3salinized soilwith the light white scalded patches<InlineMediaObject OutputMedium="Online"><ImageObject FileRef="fse-13062-lzy.doc_images/fse-13062-lzy-tb1fig2.jpg" ScaleToFitWidth="84.0pt" ScaleToFit="1"/></InlineMediaObject><InlineMediaObject OutputMedium="All"><ImageObject FileRef="fse-13062-lzy.doc_images/fse-13062-lzy-tb1fig2.tif" Format="TIFF" OrigFileRef="FSE-13062-LZY-tb1fig2" ScaleToFitHeight="86.9pt" ScaleToFitWidth="84.0pt" ScaleToFit="1"/></InlineMediaObject>1
0.3-0.5mid-salinized soilwith the white scalded patches and the land cracking<InlineMediaObject OutputMedium="Online"><ImageObject FileRef="fse-13062-lzy.doc_images/fse-13062-lzy-tb1fig3.jpg" ScaleToFitWidth="84.0pt" ScaleToFit="1"/></InlineMediaObject><InlineMediaObject OutputMedium="All"><ImageObject FileRef="fse-13062-lzy.doc_images/fse-13062-lzy-tb1fig3.tif" Format="TIFF" OrigFileRef="FSE-13062-LZY-tb1fig3" ScaleToFitHeight="86.9pt" ScaleToFitWidth="84.0pt" ScaleToFit="1"/></InlineMediaObject>2
0.5-1.0heavily-salinized soilwith the white scalded patches and the severe land cracking<InlineMediaObject OutputMedium="Online"><ImageObject FileRef="fse-13062-lzy.doc_images/fse-13062-lzy-tb1fig4.jpg" ScaleToFitWidth="84.0pt" ScaleToFit="1"/></InlineMediaObject><InlineMediaObject OutputMedium="All"><ImageObject FileRef="fse-13062-lzy.doc_images/fse-13062-lzy-tb1fig4.tif" Format="TIFF" OrigFileRef="FSE-13062-LZY-tb1fig4" ScaleToFitHeight="86.9pt" ScaleToFitWidth="84.0pt" ScaleToFit="1"/></InlineMediaObject>3
Tab.1  Rating for levels of soil contamination (LSC) with the salinity classification and the visual criterion (Modified from the Ref. [9] and [22])
itemindicestypes or levelsgrades
plant informationlife-formsarbors; shrubs; herbals or vines; others-
growth-formsneedle leaves; broad leaves; evergreen; deciduous-
landscape usagecentral belts; side belts; pavement; bridges-
injury levelslevels of degree(D)none, in good healthsuspected, in related symptoms *slight, mild and common symptomsmiddle, obvious symptomssever, seasonal phase changed01234
levels of scale(S)none, no obvious symptomssmall scale, several injurious plantsmiddle scale, continuous or patch-like damaged pots but under 1/5 of the whole observed sections wide scale, 1/5-1/3 of the whole observed sectionswider scale, over 1/3 of the whole observed sections01234
Tab.2  Recording and rating list for the vegetation injury during the contamination event
Fig.2  Typical symptoms of the road plants at the different levels of injury degree caused by the de-icing salt pollution (an example of E. japonicas, the lightest to the most severe symptoms from left to right, during the survey in the roads of Beijing, in April, 2010)
Fig.3  Modified coefficient K to differentiate (a) the discrete (K = 0.3) and (b) continuous (K = 1.0) hedgerow landscape
Fig.4  Single-side symptoms of the injured hedge plants along the severely contaminated roads: the examples of (a) E. japonicus and (b) S.vulgalis
Fig.5  Average value of IPIij (the integral plant injury index) for arbors and shrubs (a); index IPISi for arbors (b) and shrubs (c); correlation analysis between the level of soil contamination and the average integral plant injury index (LSC-IPIi¯) for arbors and shrubs (d)
typesindicesplant growth typelandscape usage
deciduous broad-leavedevergreen needle-leavedevergreen broad-leavedcentral roadside road
arborsdistance/km10.380.430.008.212.60
proportion/%96.04.00.075.924.1
shrubsdistance/km12.0530.6823.826.5040.03
proportion/%18.146.135.839.860.2
Tab.3  Life style and landscape usage for severely damaged plants (IPIij¯≥3.00) on roads
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