CHEMICAL ENGINEERING TRANSACTIONS  
 

VOL. 62, 2017 

A publication of 

 
The Italian Association 

of Chemical Engineering 
Online at www.aidic.it/cet 

Guest Editors: Fei Song, Haibo Wang, Fang He 
Copyright © 2017, AIDIC Servizi S.r.l. 
ISBN 978-88-95608- 60-0; ISSN 2283-9216 

Analysis of Pollution Control on the Construction of Garden 
Green Space in Petrochemical Enterprises 

Yihan Zhao 
Pingdingshan University, Pingdingshan 467000, China 
yihanzhao1984@126.com 

According to the production characteristics of petrochemical enterprises, this paper puts forward the control 
ability and the reduction ability of the environmental pollution of the plant area. It is the important goal of the 
construction of the garden green space for the petrochemical enterprise. It is also the key content of the 
research on the construction plan of the petrochemical enterprise garden green space. The latest plant 
ecological restoration theory and related technology are the direction for the aspects of pollution control, water 
pollution control, soil pollution control and air pollution and noise pollution control. The use of plants combined 
with the engineering design examples. 

1. Introduction 
The petrochemical production is the industrial production of petroleum raw materials. The production process 
produces a variety of pollutants (Qian et al., 2010; Liu et al., 2010). The main air pollutants are sulfur oxides, 
nitrogen oxides, hydrocarbons, CO and odor substances, followed by dust, ammonia and organic acids, etc. In 
this process it also produces waste water, alkali, waste acid, waste water in the main pollutants from the 
residue products. And it also produces organic matter, oil, suspended solids, acidity, suspended solids. Waste 
residue mainly from the cold water tower and water treatment sludge and dehydrated waste residue. These 
pollution sources have a wide distribution and complex emissions. The impact of all-round, comprehensive 
and dual on the ecological environment cannot be ignored. Figure 1 shows the production of petrochemical 
enterprises in the process of a series of problem, which seriously restricts the construction of petrochemical 
enterprises and sustainable development (Zhou, 2012; Cong et al., 2012). 
 

 

Figure 1: The influence of environmental protection on the production process of petrochemical enterprises 

                                

 
 

 

 
   

                                                  
DOI: 10.3303/CET1762236 

 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 

Please cite this article as: Yihan Zhao, 2017, Analysis of pollution control on the construction of garden green space in petrochemical 
enterprises, Chemical Engineering Transactions, 62, 1411-1416  DOI:10.3303/CET1762236   

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In order to eliminate and reduce environmental pollution, people generally take three measures (Yamamoto et 
al., 2013;): (1) Improve the production process, installation of purification, filtration, recycling equipment to 
protect the environment; (2) In the industrial enterprise planning and layout, according to the local wind 
direction, terrain, water flow we need to deal with industrial production land and other land location relationship; 
(3) According to the production characteristics of industrial enterprises, we choose anti-pollution tree green 
plant to build health protection forest. 

2. Theoretical basis of ecological green space system construction in petrochemical city 
The theoretical basis of ecological green space system construction in petrochemical city is ecology. Ecology 
also includes the following: 
(1) Ecosystem theory (Müller, 2012) 
According to Ehaekcel's definition, ecology is a science that studies the interrelationships between the 
creatures and the environment. And the ecosystem (Ecosysetm) is the habitat of all living creatures (ie, 
biological communities) and their environment. The unity of material circulation and energy flow is considered 
to be the most important concept in ecology.  
(2) The principle of ecological balance 
Ecological balance means that the energy flow and the material circulation in the ecosystem are always 
carried out smoothly under normal circumstances (without severe interference from external forces). While the 
structure of the ecosystem remains relatively stable (Klijn and Haes, 1994; Bergkamp, 1995). It is a kind of 
dynamic equilibrium. In the ecological construction of green space, the leading role of ecological balance 
principle should be emphasized. It pay attention to the relationship between urban functional zoning and it 
focuses on the ecology of the whole city environment and rational layout. As a result, the urban green space is 
not only around the city, but also the introduction of natural into the city maintain the ecological balance of the 
city. In recent years, many cities in China, such as Beijing, Tianjin, Hefei, Nanjing, Shenzhen and other cities 
have begun to combine the combination of forest gardens, urban green area. It expands the three-dimensional 
ecological construction approach. 
(3) Principles of biodiversity 
Biodiversity refers to the combination of various organisms. And their ecological complexes with the 
environment and their various ecological processes are the basis of the survival and sustainable development 
of human society. Due to unreasonable development and utilization, especially the ecological damage and 
pollution of habitats, biodiversity has continued to decline. Urban landscapes are one of the last bastions of 
native plants and native biodiversity conservation. Biodiversity is the basis for improving the greenland 
ecosystem function and greenland ecosystem health. 
(4) Niche theory (Kylafis et al., 2011; Kylafis and Loreau, 2011) 
The concept of niche is the function of a species in the ecosystem and its position in time and space. It reflects 
the relationship between species and species, species and the environment. In the construction of urban 
green space system, the selection and arrangement of green plants is very important, which is directly related 
to the ecological function of green space system and the value of landscape aesthetics. In the construction of 
urban green space system, we should fully consider the niche characteristics of the species. And we choose 
the type of plants rationally. It avoids the direct competition between species, which is the form a reasonable 
structure and functional and stable community structure. In order to complement each other, both the full use 
of environmental resources. However, the formation of beautiful landscape is also used. 

3. Results and discussion 
3.1 Water pollution control actuator selection  

In the serious pollution natural waters refinery establishes artificial wetlands. The artificial wetlands designs a 
regulating pool and five units in series. The design area is 500 square meters and the artificial wetland bed 
design depth is 1 meter. The substrate design depth is 50 cm. The substrate is the fine sand. Wetland plants 
is the main body. Artificial wetland sewage treatment process is shown in Figure 2. 
The results are shown in Table 1. The results showed that the wetland plants could remove the pollutants in 
the sewage through absorption, adsorption and enrichment. The nitrogen in the wastewater is in the form of 
organic nitrogen and inorganic nitrogen, in which inorganic nitrogen is used as a nutrient for plant growth. And 
it is absorbed by plants in the form of ions. Some organic nitrogen is decomposed by microorganisms. It is 
absorbed by plants. As a result, synthetic plant organisms are removed in the form of harvest. Inorganic 
phosphorus in wastewater is also absorbed by plants. Plants can directly absorb water-soluble heavy metals 
through the roots.  
 

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Figure 2: Technological process chart of artificial wetland 

Table 1: the change of water quality at a capacity 

Index Water in Water out Removal rate 
NO3- 1.536±0.341 0.605±0.043 60.57 
NH4+ 0.026±0.005 0.013±0.001 51.26 
TN 2.412±0.866 0.889±0.133 63.12 
TP 0.067±0.003 0.040±0.014 40.74 
SS 27.000±4.240 not detected 100 
KMnO4 4.369±1.126 1.282±0.055 70.67 
BOD5 2.810±0.795 0.746±0.029 73.45 
COD 29.572±3.217 5.005±1.930 83.07 

3.2 Soil pollution control 

Planting soils are resistant to petroleum substances on contaminated soils. They combine with fertilizers and 
they can significantly accelerate the degradation of petroleum substances in the soil. Plant bioremediation is 
the most economical. Plant-microbial co-repair is achieved by synergistic action of plants with specific 
mycorrhizal fungi or rhizosphere bacteria. Which increases the absorption and degradation of contaminants 
and it is shown in Figure 3. 

 

Figure 3: Sketch chart of microbial-phytoremediation system 

It has been found that more than 400 species of As, Cd, Co, Cu, Mn, Ni, Pb, Se, Zn and other elements are 
more than 400 species (Table 2). Super-rich plants are characterized by over-absorption of heavy metals. And 
they can be transported to the plant part of the ground. It mainly considers two factors, one is the plant part of 
the enrichment of heavy metals and the other is the plant part of the heavy metal content. They should be 
higher than the roots. Because of the concentration of various heavy metals in the soil and the background 
value in soil and plant, there are different enrichment limits for enrichment of different heavy metals. 
It is an easy and cost-effective method to strengthen phytoremediation through cultivation measures. This 
method is indeed an easy and cost-effective method. The following measures are shown in Figure 4. 

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Table 2: Species concentration of hyperaccumulators 

Heavy 
metals 

Plant species Content(mg/kg) 

Cd Solanum nigtrum L. 114 
Cd Thlaspi caerulescens 3000 
Pb Thlaspi rotundifolium Subsp. 820 
Co Haumaniastrum robertii 10200 
Cu Haumaniastrum robertii 2070 
Au Brassica juncea 10 
Mn Macadamia neurophylla 55000 
Mn Phytolacca acinosa Roxb. 19300 
Se Astragalus racemosus 14900 
Zn Cardaminossis balleri 13600 
Zn Sedum alferdii Hance. 4515 
U Atriplex confertifolia 100 
Ni Alyssum bertolonii 13400 
Ni Psychotria doarrei 47500 
T1 Iberis intermedia 3070 
AS Pteris vittata L. 7500 

 

 

Figure 4: Application of enhancing technology for phytoremediation 

3.3 Air pollution control 

Phytoremediation is the science and technology that utilizes the interaction between plants and their symbiotic 
microorganisms. Plant remediation includes direct repairs and indirect repairs. Direct repair refers to the 
absorption and assimilation of air pollutants. Indirect repair refers to the removal of dry. The removal process 
includes plant absorption, degradation, transformation and assimilation. The ability of common plants to 
absorb fluorine and chloride ions is shown in Table 3 and Table 4. 

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Table 3: The comparision of fluorine absorpive capacity of different plant’s leaves (g/kg) 

Plant leave Fluorine absorpive capacity Plant leave Fluorine absorpive capacity 
Grape plants 0.636 Side cypress 0.253 
peach 0.580 Pine 0.190 
Apple tree 0.108 peanut 0.736 
Poplar 0.792 Cynodon 0.056 
Populus×canadensi
s

1.700 locust 1.150 
Ash tree 1.258   

Table 4: The comparision of chloride absorpive capacity of different plant’s leaves (g/kg) 

Plant leave chloride absorpive capacity Plant leave chloride absorpive capacity 
Hibiscus 27.7 Oleander 7.7 
Buxus boxwood 24.8 Coral tree 6.9 
Cockscomb 16.5 Peach 6.3 
Canna 12.4 Palm 3.6 
Weeping willow 11.9 Bauhinia 3.6 
Privet 10.7 Heather 2.8 
Dragon claws 8.2 Camellia 1.6 
Euonymus japonicus 8.0 Green onion 1.8 

3.4 Noise pollution control 

The weakening effect of the same community on the noise in different growth stages is different. The 
weakening effect of the plant community on the noise is excellent. Therefore, when the green plant 
configuration is carried out, it should be used to reduce the noise pollution. Common plant noise reduction 
effect can be seen in Table 5. 

Tabel 5: Afforest effect that forest belt either hedge abate the buzz 

Forest type 
Sound source 
to forest belt 
distance (m) 

Forest 
width 
(m) 

Noise through the 
attenuation of the 
forest (dB) 

The amount of 
attenuation of the 
corresponding space 
(dB)

The net loss 
of the forest 
(dB) 

Blackberry 
pure forest 

8 34 16 11 5 

Cedar, 
cypress 
forest belt 

6 18 16 6 10 

Trees, Pittite 
Green 
Fence 

11 4 8.5 2.5 6 

4. Conclusion 
Through the study of the construction of garden green space, it is found that the plant and plant combination 
methods are different in the aspects of water pollution control, soil pollution control and air pollution and noise 
pollution control. For water pollution, the main way is to build artificial wetlands. For soil pollution, it is mainly 
with the cultivation of plants. For air pollution and noise pollution control, the main way is to use evergreen tree 
species and deciduous tree species. And under the forest configuration of a variety levels and ground cover 
plants, it increases the thickness of the forest. 
 
 

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