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E McBean1
, Ai Li Yang2
, Huiyan Cheng2
, Yi Cheng Wu2
, Zheng Liu2
, Zhi Neng Dai2
, Haiyan Fu2
and Munir Bhatti1
*
1
School of Engineering, University of Guelph, Canada
2
School of Environmental Science and Engineering, Xiamen University of Technology, Xiamen, China
3
Department of Dryland Science, Graduate school of Sustainability Science, Tottori University, Japan
*Corresponding author: Munir A Bhatti, School of Engineering, University of Guelph, N1G 2W1 Guelph, Ontario, Canada, Tel: (1)519-591-0720;
Email:
Submission: May 26, 2018; Published: August 16, 2018
Evaluation of a Double Pipe Technology-
Performance for Sponge City
Research Article
1/2
Copyright © All rights are reserved by Kotaro Tagawa.
Volume - 1 Issue - 5
Introduction
China is a country with severe water problems including dimen-
sions of water scarcity, flooding, and water pollution, all of which
have been intensifying in urban areas and threatening socio-eco-
nomic development. In recent years, urban flooding has become
very frequent, pervasive, and severe. For example, it was reported
that 641 out of 654 Chinese cities have incurred frequent floods
in a survey conducted by the Ministry of Housing and Urban Rural
Development (MOHURD). This study showed that over the period
2008–2010, 62% of 351 cities surveyed suffered urban flooding,
and 39% experienced flooding on three or more occasions. Since
2008, the number of Chinese cities affected by floods has more than
doubled, and at least 130 cities have experienced flooding nearly
every year [1].
Making matters worse are also important issues of subsidence,
with consequences that will exacerbate urban flooding problems.
Land subsidence caused by extensive groundwater pumping has
become a factor which cannot be ignored in the sustainable ex-
ploitation of groundwater resources. The Hangzhou-Jiaxing-Hu-
zhou Plain is one of the locations with China’s most severe land
subsidence problems; the region has experienced dramatic land
subsidence since the 1960s. Historical records of groundwater ex-
traction, hydraulic head, and land subsidence show the latter to
be the result of continual and excessive extraction of groundwater
from deep confined aquifers [2].
For Beijing, almost two-thirds of the urban water supply comes
from groundwater [3]. In recent years, water consumption has
sharply increased due to the rapid expansion of Beijing’s population
[4]. Groundwater extraction was measured as 2.6 x 109m3
/yr., with
an overexploitation of approximately 1x106m3
/year [5]. This long-
term overexploitation of groundwater has caused a substantial de-
cline in groundwater and land subsidence. By the end of 2010, the
land subsidence area reached 4.2 x 103km2
and 66% of the Beijing
plain has been affected by land subsidence (>50mm), with a maxi-
mum sinking of 1.23m. As a consequence, attention is being given to
alleviate issues of both flooding and subsidence. In this context, the
double pipe technology described herein has particular merit since
it can assist with attenuating flooding while also decreasing land
subsidence by infiltrating surface water to groundwater. This paper
describes research results investigating the potential performance
of application of the double pipe technology in Beijing.
Abstract
Precipitation, evaporation and runoff patterns are changing, resulting in uncertainty about the security of water supply, the quality of drinking
water, flood management in urban environments and the long-term health of natural ecosystems. The particular aspects for China are described
where, with increasing urbanization, flooding has become a regular occurrence in response, China is developing “sponge cities” to attain resilience to
stormwater. This paper describes a novel technology with significant potential; the principle of the ‘double pipe technology’ which involves placement
of a perforated pipe below a stormwater pipe, encourages passage from the stormwater pipe down to a second pipe, a perforated pipe. This allows
temporary storage in the lower pipe and enhances exfiltration from the lower pipe to the underlying aquifer. A conceptual model of the double pipe
technology is provided, and the results show that the surcharge potential in the stormwater pipe is dramatically decreased. The lower pipe is able to
capture, store, and eventually infiltrate into the groundwater, storm water runoff where the exfiltrate water from the lower pipe 56% to 62% of the
total annual rainfall to be released to groundwater. This would truly enhance groundwater levels and decrease subsidence in areas where this is a major
concern (particularly related to coastal zone cities in China).
Advancements in Civil Engineering
& Technology
C CRIMSON PUBLISHERS
Wings to the Research
ISSN 2639-0574
Adv Civil Eng Tech Copyright © Munir A Bhatti
2/5
How to cite this article: E McBean, Ai Li Y, Huiyan C, Yi Cheng W, Zheng L, Zhi N D, et al. Evaluation of a Double Pipe Technology-Performance for Sponge
City. Adv Civil Eng Tech .1(5). ACET.000524.2018. DOI: 10.31031/ACET.2018.01.000524
Volume - 1 Issue - 5
Background
China began to focus on the pattern of urban construction a
decade ago, when continuous inland flooding shocked citizens.
From 2012 to 2014, 180 cities annually incurred inland flooding
caused by stormwater. In July 2012, the Chinese capital’s heaviest
rainstorm in six decades caused serious inland flooding and killed
79 people, with property damage of $1.8 billion. The frequent mis-
haps and disasters caused by inland flooding in large cities caused
authorities and citizens to be in favor of ‘green’ rather than ‘grey’
and unordered, urbanization. China’s 12th five-year plan proposed
to pay more attention to the storage and recycling of stormwater.
As China has become increasingly urbanized, flooding has become
a regular occurrence in its cities; 62% of Chinese cities surveyed
experienced floods and direct economic losses of up to $100 billion
between 2011 and 2014. The 2016 flooding affected more than 60
million people-more than 200 people were killed and $22 billion in
losses were suffered across China.
Hence, assessment of future changes in urban flooding is very
important for managing urban floods by designing new, and re-de-
signing existing, urban infrastructures to be more resilient in re-
sponse to the impacts of future climate change. While it is speculat-
ed that urban floods are speculated to increase in the future, their
magnitudes are hard to assess due to uncertainties associated with
future climate change scenarios, as well as the under-representa-
tion of plausible climate change mitigation and adaptation strate-
gies in the models [6]. Further, severe weather is likely to become
one of the greatest reasons for higher costs in the future delivery
of water services and managing infrastructure [7]. Precipitation,
evaporation and runoff patterns are changing, resulting in uncer-
tainty about the security of water supply, the quality of drinking
water, flood management in urban environments and the long-term
health of natural ecosystems [8].
Insofar as the issue of subsidence, groundwater over-extraction,
waterway degradation, and urban flooding are forcing China’s cities
to address this vicious cycle. The intent of the sponge city initiative
requires a holistic and sustained effort, including effective environ-
mental governance [9]. The optimal goals of the sponge city are that
the stormwater generated from rainfall events could be absorbed,
stored, infiltrated and cleaned with the natural and/or manmade
facilities and the rainfall and stormwater could be transformed into
water resources that could be utilized during drought [10]. The re-
cycled water can be used to improve sustainability of recharge-de-
pleted aquifers, offset potable water demand, and help to meet de-
mands of industry and irrigation of urban farmlands [10,11]. It is
of great importance, and there is urgency, to explore methods that
can minimize the impact of the urbanization process on the natural
environment.
In that context, as examples, important cities in northern Chi-
na experience arid and semi-arid climates, with an average annual
rainfall of less than 600mm with precipitation concentrated within
the rainy season from May to October. Major urban water problems
in these areas include severe water shortages. Therefore, urban
rainwater resource utilization continues to be the focus of sponge
city construction in northern China. However, the degree of ability
to decrease flooding by infiltration may be limited in some regions
due to the shallow vadose zone, hence negating the opportunity to
reduce urban runoff and waterlogging by employing some source
control measures [12]. The concept of sponge city/LID began to
be promoted in new development areas. A milestone of green con-
struction was December 2013, when China’s president proposed
to develop “sponge cities” with attained resilience to stormwater.
From this moment on, national and local policies and guidelines re-
lated to the sponge city initiative, including LID, have been issued.
As defined in the policy announcement, a sponge city should alle-
viate the adverse effects of urban construction and recycle 70% of
stormwater in-situ by combining five kinds of measures including
permeation, retention, storage, purification, and reuse before dis-
charge.
As Wang et al. [13] reported, China has developed 30 pi-
lot sponge cities, billions of Chinese Yuan have been invested in
sponge city introduction, and many projects are already in opera-
tion although the challenges of urban flooding continue. In the last
three years, more than 80% of China’s large cities experienced ur-
ban flooding; in fact, Beijing, as well as Wuhan and Guangzhou, are
flooded more than once a year. By implementing the sponge city
projects in cities, China hopes to mitigate urban flooding using dif-
ferent methods, including: minimizing the impacts of urban devel-
opment on the natural environment through LID; slowing the rate
of growth in impervious areas of cities; making an effort to imple-
ment green infrastructure; and developing drainage network sys-
tems. The sponge city strategy replaces a prior objective of “rapid
draining” in urban water management with preserving rainwater
as a resource. Accordingly, the Sponge City Project (SCP) advocates
for various forms of utilization of rainwater as water sources of cit-
ies. One objective of the SCP is to improve urban living experiences
that involve water issues by adjusting urban microclimates with
various approaches, such as maintaining and raising water areas
and enhancing the implementation of urban water landscapes and
green infrastructure in cities.
A technology that has significant potential to assist in enhanc-
ing green infrastructure is the principle of the ‘double pipe technol-
ogy’ which involves placement of a perforated pipe below a storm-
water pipe. The basis of the methodology is to encourage passage
from the stormwater pipe down to the perforated pipe, as illustrat-
ed in Figure 1. This allows temporary storage in the lower pipe and
enhances exfiltration from the lower pipe to the underlying aquifer.
To evaluate the performance potential, a computer simulation of
the response is described herein. The physical regime modelled is
defined in Section 3 below.
Case Study Subdivision
The test case (a hypothetical area but representative of Beijing)
is shown in Figure 2. It has three catch basins with a total contrib-
uting area of 1.44 hectares (ha), with sub-areas sizes contributing
from 0.54, 0.48 and 0.42ha each, respectively. The land use has
3/5
How to cite this article: E McBean, Ai Li Y, Huiyan C, Yi Cheng W, Zheng L, Zhi N D, et al. Evaluation of a Double Pipe Technology-Performance for Sponge
City. Adv Civil Eng Tech .1(5). ACET.000524.2018. DOI: 10.31031/ACET.2018.01.000524
Adv Civil Eng Tech Copyright © Munir A Bhatti
Volume - 1 Issue - 5
been assumed as typical urban areas with 75% impervious and
land slope of 0.5% towards each catch basin. It is also assumed that
infiltration in governed by the Horton equation. To design the size
of the storm sewer, a 5-year recurrence interval storm and rainfall
duration of two hours was utilized, and the rational method to se-
lect pipe sizes. The rainfall Intensity duration and return period re-
lationship for Beijing, China was utilized [14]:
I = 12.0 (1+0.811 LOG10 (Tr) / (D+8)0.711 for D <120 min
I = 13.9 (1+1.091 LOG10(Tr) / (D+10)0.759 for D from 120 to
360 min
Where I is rainfall intensity in mm/min, Tr is return period in
years and D is duration in minutes, as per Table 1.
Figure 1: Schematic of Double Pipe Technology Scenario.
Figure 2: Schematic of Test Case Area.
Table 1: Intensity of rainfall for various time durations and return periods [14].
Tr Yr 5 5 5 5 5 5 5 5
D minutes 5 10 15 30 60 120 180 360
I mm/minute 2.74 2.23 1.91 1.37 0.92 0.59 0.46 0.28
I mm/hour 164.50 134.07 114.40 81.90 55.02 35.43 27.62 16.59
Amount mm 13.71 22.35 28.60 40.95 55.02 70.86 82.86 99.54
The configuration of the lower pipe, to facilitate exfiltration
and thereby to replenish groundwater, while also preserving the
sediment accumulation to avoid clogging of the granular material
around the lower pipe (and hence, continued ability to continue
to recharge groundwater) is as depicted in Figure 3. The receiving
media of soil (using 15mm of clear stone) around the perforated
pipe is capable of absorbing the amount of water ex-filtrated from
perforated pipe. The results are shown in Table 2. To estimate the
capacity of flows through the perforations into the vadose zone sur-
rounding the lower pipe, orifice flow conditions were assumed, and
orifice equations used [15-17].
Adv Civil Eng Tech Copyright © Munir A Bhatti
4/5
How to cite this article: E McBean, Ai Li Y, Huiyan C, Yi Cheng W, Zheng L, Zhi N D, et al. Evaluation of a Double Pipe Technology-Performance for Sponge
City. Adv Civil Eng Tech .1(5). ACET.000524.2018. DOI: 10.31031/ACET.2018.01.000524
Volume - 1 Issue - 5
Table 2: Total Ex-filtration Volume from the Perforated Pipe for a
5-Year 2hr Storm.
Section Length (m) M3
% of Total Rainfall Ex-filtrated
A-D 240 560 56.1
Findings from calculation sequence
From computer modelling, the net result of the scenario of us-
ing the double pipe design, resulted in the following results:
a) The surcharge potential in the storm sewer is dramatical-
ly decreased. The lower pipes can capture, store, and eventually
infiltrate into the groundwater, storm water runoff from a two-
hour duration, 5-year recurrence interval storm [18,19].
b) Overall, over a 40-year time history, the potential exists to
exfiltrate water from the lower pipe, at levels varying from 56%
to 62% of the total annual rainfall. This would truly enhance
groundwater levels and decrease subsidence in areas where
this is a major concern (particularly related to coastal zone cit-
ies in China).
c) The findings indicate that so long as the groundwater is
>1m below the depth of the lower pipe, the exfiltration will oc-
cur.
d) Decreasing the flooding from heavy storms can be cap-
tured (the so-called heavy storms that occur several times a
year). For major events (e.g. the 25 to 100-year storms), there
is only a modest effect due to the magnitudes of the storms.
e) The costs of placement of placing the second pipe increase
the overall cost of the installation of this system are about 15%
extra and, given the magnitudes of flooding and the resulting
damages, this is a technology that has considerable merit.
Figure 1: Schematic of Double Pipe Technology Scenario.
Conclusion
There is widespread evidence of major flooding events in
urban cities in China. One option that warrants consideration is to
use a double pipe system where substantial portions of the storm
water can be transferred to the lower pipe where exfiltration will
take place. The extent to which this would assist in the lowering
of the flood damages could very well be substantial. The costs for
such additional implementation of the lower storm water pipe are
relatively modest (15 percent increase), if undertaken at the time of
the construction of the storm water system.
References
1. Jiang Y, Zevenbergen C, Ma Y (2018) Urban pluvial flooding and
stormwater management: A contemporary review of China’s challenges
and “sponge cities” strategy. Environmental Science and Policy 80: 132-
143.
2. Cao G, Han D, Moser J (2013) Groundwater exploitation management
under land subsidence constraint: empirical evidence from the
Hangzhou-Jiaxing-Huzhou plain, China. Environ Manage 51(6): 1109-
1125.
3. Gao M, Gong H, Chen B, Zhou C, Chen W, et al. (2016) InSAR time-series
investigation of long-term ground displacement at beijing capital
international airport, China. Tectonophysics 691: 271-281.
4. Wang H, Mei C, Liu J (2017) New strategy for integrated urban water
management in china: sponge city. Sci China Tech Sci 61(3): 317-329.
5. Singh RP, Wu J, Kumar AJ, Fu D (2017) Study on mercury distribution and
speciation in urban road runoff in Nanjing city, China. Water 9(10): 779.
6. Zhu L, Gong HL, Li XJ, Wang R, Chen BB, et al. (2015) Land subsidence
due to groundwater withdrawal in the northern Beijing plain, China. Eng
Geol 193: 243-255.
7. http://www.oecd.org/futures/infrastructureto2030/37182873.pdf
8. http://www.cwn-rce.ca/project-library/project/developing-
a - c a n a d i a n - wa t e r - s e c u r i t y - f r a m e w o r k- a s - a - t o o l - f o r -
assessing-cumulative-impacts-and-improving-watershed-
governance?u=keyword%3DMcBean%26category%3Dsecure-source-
water%26start%3D0
9. h t t p : / / w w w . c h i n a d a i l y . c o m . c n / a / 2 0 1 7 0 9 / 2 6 /
WS5a0bde03a31061a738404981.html
10. MOHURD (2014) Guide of Sponge City construction technology based
on the LID concept (Experiment), China architecture and Building Press.
5/5
How to cite this article: E McBean, Ai Li Y, Huiyan C, Yi Cheng W, Zheng L, Zhi N D, et al. Evaluation of a Double Pipe Technology-Performance for Sponge
City. Adv Civil Eng Tech .1(5). ACET.000524.2018. DOI: 10.31031/ACET.2018.01.000524
Adv Civil Eng Tech Copyright © Munir A Bhatti
Volume - 1 Issue - 5
Ministry of Housing and Urban-Rural Development (MOHURD), Beijing,
pp. 2-7.
11. https://www.foreground.com.au/environment/the-big-soak/
12. Zhang Y, Xue YQ, Wu JC, Wang HM, He JJ (2012) Mechanical modeling of
aquifer sands under long-term groundwater withdrawal. Eng Geol 125:
74-80.
13. Zhou C, Gong H, Chen B, Li J, Gao M, et al. (2017) InSAR time-series
analysis of land subsidence under different land use types in the eastern
Beijing plain, china. Remote Sens 9(4): 380.
14. Gong Y, Liang X, Li X, Li J, Fang X, et al. (2016) Influence of rainfall
characteristics on total suspended solids in urban runoff: a case study in
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15. Duchene M, McBean EA (1992) Discharge characteristics of perforated
pipe for use in infiltration trenches. American water resources
Association 28(3): 517-524.
16. http://www.ads-pipe.com
17. DPIWE (2012) Water sensitive urban design, wsud engineering
procedures for storm water management in Tasmania, EPA division of
the department of primary industries. Water and Environment.
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Mexico City subsidence observed with persistent scatterer, InSAR. Int J
Appl Earth Obs Geoinf 13(1): 1-12.
19. Zhou Q, Leng G, Huang M (2016) Impacts of future climate change on
urban flood volumes in Hohhot City in Northern China: benefits of
climate mitigation and adaptations. Hydrol Earth Syst Sci 22: 305-316.
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Evaluation of a Double Pipe TechnologyPerformance for Sponge City_Crimson publishers

  • 1. E McBean1 , Ai Li Yang2 , Huiyan Cheng2 , Yi Cheng Wu2 , Zheng Liu2 , Zhi Neng Dai2 , Haiyan Fu2 and Munir Bhatti1 * 1 School of Engineering, University of Guelph, Canada 2 School of Environmental Science and Engineering, Xiamen University of Technology, Xiamen, China 3 Department of Dryland Science, Graduate school of Sustainability Science, Tottori University, Japan *Corresponding author: Munir A Bhatti, School of Engineering, University of Guelph, N1G 2W1 Guelph, Ontario, Canada, Tel: (1)519-591-0720; Email: Submission: May 26, 2018; Published: August 16, 2018 Evaluation of a Double Pipe Technology- Performance for Sponge City Research Article 1/2 Copyright © All rights are reserved by Kotaro Tagawa. Volume - 1 Issue - 5 Introduction China is a country with severe water problems including dimen- sions of water scarcity, flooding, and water pollution, all of which have been intensifying in urban areas and threatening socio-eco- nomic development. In recent years, urban flooding has become very frequent, pervasive, and severe. For example, it was reported that 641 out of 654 Chinese cities have incurred frequent floods in a survey conducted by the Ministry of Housing and Urban Rural Development (MOHURD). This study showed that over the period 2008–2010, 62% of 351 cities surveyed suffered urban flooding, and 39% experienced flooding on three or more occasions. Since 2008, the number of Chinese cities affected by floods has more than doubled, and at least 130 cities have experienced flooding nearly every year [1]. Making matters worse are also important issues of subsidence, with consequences that will exacerbate urban flooding problems. Land subsidence caused by extensive groundwater pumping has become a factor which cannot be ignored in the sustainable ex- ploitation of groundwater resources. The Hangzhou-Jiaxing-Hu- zhou Plain is one of the locations with China’s most severe land subsidence problems; the region has experienced dramatic land subsidence since the 1960s. Historical records of groundwater ex- traction, hydraulic head, and land subsidence show the latter to be the result of continual and excessive extraction of groundwater from deep confined aquifers [2]. For Beijing, almost two-thirds of the urban water supply comes from groundwater [3]. In recent years, water consumption has sharply increased due to the rapid expansion of Beijing’s population [4]. Groundwater extraction was measured as 2.6 x 109m3 /yr., with an overexploitation of approximately 1x106m3 /year [5]. This long- term overexploitation of groundwater has caused a substantial de- cline in groundwater and land subsidence. By the end of 2010, the land subsidence area reached 4.2 x 103km2 and 66% of the Beijing plain has been affected by land subsidence (>50mm), with a maxi- mum sinking of 1.23m. As a consequence, attention is being given to alleviate issues of both flooding and subsidence. In this context, the double pipe technology described herein has particular merit since it can assist with attenuating flooding while also decreasing land subsidence by infiltrating surface water to groundwater. This paper describes research results investigating the potential performance of application of the double pipe technology in Beijing. Abstract Precipitation, evaporation and runoff patterns are changing, resulting in uncertainty about the security of water supply, the quality of drinking water, flood management in urban environments and the long-term health of natural ecosystems. The particular aspects for China are described where, with increasing urbanization, flooding has become a regular occurrence in response, China is developing “sponge cities” to attain resilience to stormwater. This paper describes a novel technology with significant potential; the principle of the ‘double pipe technology’ which involves placement of a perforated pipe below a stormwater pipe, encourages passage from the stormwater pipe down to a second pipe, a perforated pipe. This allows temporary storage in the lower pipe and enhances exfiltration from the lower pipe to the underlying aquifer. A conceptual model of the double pipe technology is provided, and the results show that the surcharge potential in the stormwater pipe is dramatically decreased. The lower pipe is able to capture, store, and eventually infiltrate into the groundwater, storm water runoff where the exfiltrate water from the lower pipe 56% to 62% of the total annual rainfall to be released to groundwater. This would truly enhance groundwater levels and decrease subsidence in areas where this is a major concern (particularly related to coastal zone cities in China). Advancements in Civil Engineering & Technology C CRIMSON PUBLISHERS Wings to the Research ISSN 2639-0574
  • 2. Adv Civil Eng Tech Copyright © Munir A Bhatti 2/5 How to cite this article: E McBean, Ai Li Y, Huiyan C, Yi Cheng W, Zheng L, Zhi N D, et al. Evaluation of a Double Pipe Technology-Performance for Sponge City. Adv Civil Eng Tech .1(5). ACET.000524.2018. DOI: 10.31031/ACET.2018.01.000524 Volume - 1 Issue - 5 Background China began to focus on the pattern of urban construction a decade ago, when continuous inland flooding shocked citizens. From 2012 to 2014, 180 cities annually incurred inland flooding caused by stormwater. In July 2012, the Chinese capital’s heaviest rainstorm in six decades caused serious inland flooding and killed 79 people, with property damage of $1.8 billion. The frequent mis- haps and disasters caused by inland flooding in large cities caused authorities and citizens to be in favor of ‘green’ rather than ‘grey’ and unordered, urbanization. China’s 12th five-year plan proposed to pay more attention to the storage and recycling of stormwater. As China has become increasingly urbanized, flooding has become a regular occurrence in its cities; 62% of Chinese cities surveyed experienced floods and direct economic losses of up to $100 billion between 2011 and 2014. The 2016 flooding affected more than 60 million people-more than 200 people were killed and $22 billion in losses were suffered across China. Hence, assessment of future changes in urban flooding is very important for managing urban floods by designing new, and re-de- signing existing, urban infrastructures to be more resilient in re- sponse to the impacts of future climate change. While it is speculat- ed that urban floods are speculated to increase in the future, their magnitudes are hard to assess due to uncertainties associated with future climate change scenarios, as well as the under-representa- tion of plausible climate change mitigation and adaptation strate- gies in the models [6]. Further, severe weather is likely to become one of the greatest reasons for higher costs in the future delivery of water services and managing infrastructure [7]. Precipitation, evaporation and runoff patterns are changing, resulting in uncer- tainty about the security of water supply, the quality of drinking water, flood management in urban environments and the long-term health of natural ecosystems [8]. Insofar as the issue of subsidence, groundwater over-extraction, waterway degradation, and urban flooding are forcing China’s cities to address this vicious cycle. The intent of the sponge city initiative requires a holistic and sustained effort, including effective environ- mental governance [9]. The optimal goals of the sponge city are that the stormwater generated from rainfall events could be absorbed, stored, infiltrated and cleaned with the natural and/or manmade facilities and the rainfall and stormwater could be transformed into water resources that could be utilized during drought [10]. The re- cycled water can be used to improve sustainability of recharge-de- pleted aquifers, offset potable water demand, and help to meet de- mands of industry and irrigation of urban farmlands [10,11]. It is of great importance, and there is urgency, to explore methods that can minimize the impact of the urbanization process on the natural environment. In that context, as examples, important cities in northern Chi- na experience arid and semi-arid climates, with an average annual rainfall of less than 600mm with precipitation concentrated within the rainy season from May to October. Major urban water problems in these areas include severe water shortages. Therefore, urban rainwater resource utilization continues to be the focus of sponge city construction in northern China. However, the degree of ability to decrease flooding by infiltration may be limited in some regions due to the shallow vadose zone, hence negating the opportunity to reduce urban runoff and waterlogging by employing some source control measures [12]. The concept of sponge city/LID began to be promoted in new development areas. A milestone of green con- struction was December 2013, when China’s president proposed to develop “sponge cities” with attained resilience to stormwater. From this moment on, national and local policies and guidelines re- lated to the sponge city initiative, including LID, have been issued. As defined in the policy announcement, a sponge city should alle- viate the adverse effects of urban construction and recycle 70% of stormwater in-situ by combining five kinds of measures including permeation, retention, storage, purification, and reuse before dis- charge. As Wang et al. [13] reported, China has developed 30 pi- lot sponge cities, billions of Chinese Yuan have been invested in sponge city introduction, and many projects are already in opera- tion although the challenges of urban flooding continue. In the last three years, more than 80% of China’s large cities experienced ur- ban flooding; in fact, Beijing, as well as Wuhan and Guangzhou, are flooded more than once a year. By implementing the sponge city projects in cities, China hopes to mitigate urban flooding using dif- ferent methods, including: minimizing the impacts of urban devel- opment on the natural environment through LID; slowing the rate of growth in impervious areas of cities; making an effort to imple- ment green infrastructure; and developing drainage network sys- tems. The sponge city strategy replaces a prior objective of “rapid draining” in urban water management with preserving rainwater as a resource. Accordingly, the Sponge City Project (SCP) advocates for various forms of utilization of rainwater as water sources of cit- ies. One objective of the SCP is to improve urban living experiences that involve water issues by adjusting urban microclimates with various approaches, such as maintaining and raising water areas and enhancing the implementation of urban water landscapes and green infrastructure in cities. A technology that has significant potential to assist in enhanc- ing green infrastructure is the principle of the ‘double pipe technol- ogy’ which involves placement of a perforated pipe below a storm- water pipe. The basis of the methodology is to encourage passage from the stormwater pipe down to the perforated pipe, as illustrat- ed in Figure 1. This allows temporary storage in the lower pipe and enhances exfiltration from the lower pipe to the underlying aquifer. To evaluate the performance potential, a computer simulation of the response is described herein. The physical regime modelled is defined in Section 3 below. Case Study Subdivision The test case (a hypothetical area but representative of Beijing) is shown in Figure 2. It has three catch basins with a total contrib- uting area of 1.44 hectares (ha), with sub-areas sizes contributing from 0.54, 0.48 and 0.42ha each, respectively. The land use has
  • 3. 3/5 How to cite this article: E McBean, Ai Li Y, Huiyan C, Yi Cheng W, Zheng L, Zhi N D, et al. Evaluation of a Double Pipe Technology-Performance for Sponge City. Adv Civil Eng Tech .1(5). ACET.000524.2018. DOI: 10.31031/ACET.2018.01.000524 Adv Civil Eng Tech Copyright © Munir A Bhatti Volume - 1 Issue - 5 been assumed as typical urban areas with 75% impervious and land slope of 0.5% towards each catch basin. It is also assumed that infiltration in governed by the Horton equation. To design the size of the storm sewer, a 5-year recurrence interval storm and rainfall duration of two hours was utilized, and the rational method to se- lect pipe sizes. The rainfall Intensity duration and return period re- lationship for Beijing, China was utilized [14]: I = 12.0 (1+0.811 LOG10 (Tr) / (D+8)0.711 for D <120 min I = 13.9 (1+1.091 LOG10(Tr) / (D+10)0.759 for D from 120 to 360 min Where I is rainfall intensity in mm/min, Tr is return period in years and D is duration in minutes, as per Table 1. Figure 1: Schematic of Double Pipe Technology Scenario. Figure 2: Schematic of Test Case Area. Table 1: Intensity of rainfall for various time durations and return periods [14]. Tr Yr 5 5 5 5 5 5 5 5 D minutes 5 10 15 30 60 120 180 360 I mm/minute 2.74 2.23 1.91 1.37 0.92 0.59 0.46 0.28 I mm/hour 164.50 134.07 114.40 81.90 55.02 35.43 27.62 16.59 Amount mm 13.71 22.35 28.60 40.95 55.02 70.86 82.86 99.54 The configuration of the lower pipe, to facilitate exfiltration and thereby to replenish groundwater, while also preserving the sediment accumulation to avoid clogging of the granular material around the lower pipe (and hence, continued ability to continue to recharge groundwater) is as depicted in Figure 3. The receiving media of soil (using 15mm of clear stone) around the perforated pipe is capable of absorbing the amount of water ex-filtrated from perforated pipe. The results are shown in Table 2. To estimate the capacity of flows through the perforations into the vadose zone sur- rounding the lower pipe, orifice flow conditions were assumed, and orifice equations used [15-17].
  • 4. Adv Civil Eng Tech Copyright © Munir A Bhatti 4/5 How to cite this article: E McBean, Ai Li Y, Huiyan C, Yi Cheng W, Zheng L, Zhi N D, et al. Evaluation of a Double Pipe Technology-Performance for Sponge City. Adv Civil Eng Tech .1(5). ACET.000524.2018. DOI: 10.31031/ACET.2018.01.000524 Volume - 1 Issue - 5 Table 2: Total Ex-filtration Volume from the Perforated Pipe for a 5-Year 2hr Storm. Section Length (m) M3 % of Total Rainfall Ex-filtrated A-D 240 560 56.1 Findings from calculation sequence From computer modelling, the net result of the scenario of us- ing the double pipe design, resulted in the following results: a) The surcharge potential in the storm sewer is dramatical- ly decreased. The lower pipes can capture, store, and eventually infiltrate into the groundwater, storm water runoff from a two- hour duration, 5-year recurrence interval storm [18,19]. b) Overall, over a 40-year time history, the potential exists to exfiltrate water from the lower pipe, at levels varying from 56% to 62% of the total annual rainfall. This would truly enhance groundwater levels and decrease subsidence in areas where this is a major concern (particularly related to coastal zone cit- ies in China). c) The findings indicate that so long as the groundwater is >1m below the depth of the lower pipe, the exfiltration will oc- cur. d) Decreasing the flooding from heavy storms can be cap- tured (the so-called heavy storms that occur several times a year). For major events (e.g. the 25 to 100-year storms), there is only a modest effect due to the magnitudes of the storms. e) The costs of placement of placing the second pipe increase the overall cost of the installation of this system are about 15% extra and, given the magnitudes of flooding and the resulting damages, this is a technology that has considerable merit. Figure 1: Schematic of Double Pipe Technology Scenario. Conclusion There is widespread evidence of major flooding events in urban cities in China. One option that warrants consideration is to use a double pipe system where substantial portions of the storm water can be transferred to the lower pipe where exfiltration will take place. The extent to which this would assist in the lowering of the flood damages could very well be substantial. The costs for such additional implementation of the lower storm water pipe are relatively modest (15 percent increase), if undertaken at the time of the construction of the storm water system. References 1. Jiang Y, Zevenbergen C, Ma Y (2018) Urban pluvial flooding and stormwater management: A contemporary review of China’s challenges and “sponge cities” strategy. Environmental Science and Policy 80: 132- 143. 2. Cao G, Han D, Moser J (2013) Groundwater exploitation management under land subsidence constraint: empirical evidence from the Hangzhou-Jiaxing-Huzhou plain, China. Environ Manage 51(6): 1109- 1125. 3. Gao M, Gong H, Chen B, Zhou C, Chen W, et al. (2016) InSAR time-series investigation of long-term ground displacement at beijing capital international airport, China. Tectonophysics 691: 271-281. 4. Wang H, Mei C, Liu J (2017) New strategy for integrated urban water management in china: sponge city. Sci China Tech Sci 61(3): 317-329. 5. Singh RP, Wu J, Kumar AJ, Fu D (2017) Study on mercury distribution and speciation in urban road runoff in Nanjing city, China. Water 9(10): 779. 6. Zhu L, Gong HL, Li XJ, Wang R, Chen BB, et al. (2015) Land subsidence due to groundwater withdrawal in the northern Beijing plain, China. Eng Geol 193: 243-255. 7. http://www.oecd.org/futures/infrastructureto2030/37182873.pdf 8. http://www.cwn-rce.ca/project-library/project/developing- a - c a n a d i a n - wa t e r - s e c u r i t y - f r a m e w o r k- a s - a - t o o l - f o r - assessing-cumulative-impacts-and-improving-watershed- governance?u=keyword%3DMcBean%26category%3Dsecure-source- water%26start%3D0 9. h t t p : / / w w w . c h i n a d a i l y . c o m . c n / a / 2 0 1 7 0 9 / 2 6 / WS5a0bde03a31061a738404981.html 10. MOHURD (2014) Guide of Sponge City construction technology based on the LID concept (Experiment), China architecture and Building Press.
  • 5. 5/5 How to cite this article: E McBean, Ai Li Y, Huiyan C, Yi Cheng W, Zheng L, Zhi N D, et al. Evaluation of a Double Pipe Technology-Performance for Sponge City. Adv Civil Eng Tech .1(5). ACET.000524.2018. DOI: 10.31031/ACET.2018.01.000524 Adv Civil Eng Tech Copyright © Munir A Bhatti Volume - 1 Issue - 5 Ministry of Housing and Urban-Rural Development (MOHURD), Beijing, pp. 2-7. 11. https://www.foreground.com.au/environment/the-big-soak/ 12. Zhang Y, Xue YQ, Wu JC, Wang HM, He JJ (2012) Mechanical modeling of aquifer sands under long-term groundwater withdrawal. Eng Geol 125: 74-80. 13. Zhou C, Gong H, Chen B, Li J, Gao M, et al. (2017) InSAR time-series analysis of land subsidence under different land use types in the eastern Beijing plain, china. Remote Sens 9(4): 380. 14. Gong Y, Liang X, Li X, Li J, Fang X, et al. (2016) Influence of rainfall characteristics on total suspended solids in urban runoff: a case study in Beijing, China. Water 8(7): 278. 15. Duchene M, McBean EA (1992) Discharge characteristics of perforated pipe for use in infiltration trenches. American water resources Association 28(3): 517-524. 16. http://www.ads-pipe.com 17. DPIWE (2012) Water sensitive urban design, wsud engineering procedures for storm water management in Tasmania, EPA division of the department of primary industries. Water and Environment. 18. Osmanoglu B, Dixon TH, Wdowinski S, Cabral-Cano E, Jiang Y (2011) Mexico City subsidence observed with persistent scatterer, InSAR. Int J Appl Earth Obs Geoinf 13(1): 1-12. 19. Zhou Q, Leng G, Huang M (2016) Impacts of future climate change on urban flood volumes in Hohhot City in Northern China: benefits of climate mitigation and adaptations. Hydrol Earth Syst Sci 22: 305-316. For possible submissions Click Here Submit Article Creative Commons Attribution 4.0 International License Advancements in Civil Engineering & Technology Benefits of Publishing with us • High-level peer review and editorial services • Freely accessible online immediately upon publication • Authors retain the copyright to their work • Licensing it under a Creative Commons license • Visibility through different online platforms