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Article

Design and Performance Evaluation of a Heat Pump System Utilizing a Permanent Dewatering System

1
Department of Architectural Engineering, INHA University, Inha-ro 100, Michuhol-gu, Incheon 22212, Korea
2
GS E&C Research Institute, Baegok-daero 388, Cheoin-gu, Youngin, Gyeonggi-do 17130, Korea
*
Author to whom correspondence should be addressed.
Energies 2021, 14(8), 2273; https://doi.org/10.3390/en14082273
Submission received: 27 March 2021 / Revised: 12 April 2021 / Accepted: 15 April 2021 / Published: 18 April 2021
(This article belongs to the Special Issue Renewable Energy Systems in the Design of Energy-Efficient Buildings)

Abstract

:
The earth provides a vast resource of groundwater from aquifers a few meters beneath the surface. Thus, buildings that use underground space must be equipped with dewatering wells to drain the permeated groundwater to the sewage pipelines to ensure the structural stability of the building. Although the inflowing groundwater temperatures and flow rates are stable enough for groundwater to be used as an energy source, 79% of the permeated groundwater is discarded through the sewers, generating significant sewerage expenses. This study introduced a novel heat exchanger module to utilize the permeated groundwater as an unused energy source using heat pumps, and the performance of the system was evaluated by TRNSYS simulations. First, the sizing of the unit heat exchanger module was proposed according to the mean inflow rate of the permeated groundwater. Second, the heat pump system was configured using multiple modules in the source-side loop. Finally, the performance of the proposed heat pump system was compared with that of a conventional air source heat pump using realistic load and temperature profiles. This preliminary study demonstrated interesting performance results, with a coefficient of performance for heating that was higher than that of a conventional heat pump system by 0.79. The results show the potential utilization of the systems for a construction project requiring large-scale underground spaces, where abundant groundwater is available.

1. Introduction

Upon the adoption of the Paris Agreement by the United Nations Climate Change Conference (UNCCC) in 2015, countries worldwide agreed to limit the increase in the average atmospheric temperature to below 2 °C by cooperating to reduce their respective greenhouse gas emissions [1]. Korea, ranking seventh in greenhouse gas emissions, set a goal to reduce emissions by 37% of the current emissions by 2030 and has developed and implemented diverse regulations for industries, transportation, buildings, and the public sector. In particular, buildings, occupying 30% of the primary annual energy consumption, exhibit great potential for reducing emissions [2,3]. Thus, the Korean government has encouraged the installation of new and renewable energy systems to minimize the consumption of fossil fuels and intends to implement the mandatory installation of these systems for all types of buildings by 2030.
According to the regulation of the Seoul metropolitan government [4], 5–15% of the energy consumption of new buildings constructed before the year 2025 will be required to utilize alternative energy through new and renewable energy systems. Currently, new buildings frequently adopt new and renewable energy systems, instead of existing systems using fossil fuels, for the operation of public spaces, such as elevators or underground parking lots. However, under the governmental regulations that encourage the introduction of systems comprising solar energy, geothermal heat pumps, and fuel cells, which require a considerable initial investment, construction companies in the private sector have also attempted unprecedented approaches to secure unused and economical sources of energy.
The unused energy system application for buildings is now promising solutions to reduce greenhouse gas emissions. By combining water-source energy such as groundwater, wastewater, river, and lakes with existing heat pump systems, the system efficiency can be increased resulting in lower greenhouse effects [5,6]. The groundwater flowing into the dewatering well exhibits a stable annual temperature range of 15–20 °C, which is attributable to the high thermal capacity of the surrounding earth. Thus, if the underground inflow is secured, it could be exploited as a source of energy rather than contributing to the maintenance costs of the building.
Studies from the past 10 years regarding the exploitation of groundwater and sewage water are summarized in Table 1. These studies have proposed systems such as groundwater heat pumps (GWHPs), wastewater source heat pumps (WWHPs), and sewage water heat pump (SWHP) systems to take advantage of these untapped energy sources. The GWHP system is a type of ground source heat pump (GSHP) system, for which holes are drilled to a depth of 300–500 m underground to install wells that act as a heat source for the heat pump [7]. WWHP and SWHP systems utilize residential wastewater through heat exchanger loops that are installed on the sewage pipeline to recover the waste heat [8,9]. Water storage in reservoirs or ponds located near a building can be another potential source of unused energy [10,11].
The WWHP and SWHP systems exhibit higher temperatures due to the hot water from the sources of waste heat [12] and come with the disadvantage of heat exchanger fouling, which necessitates the installation of ancillary equipment for maintenance [19]. Conversely, heat pump systems with the heat exchanger attached to the dewatering wells require less initial investment and benefit from stable groundwater temperatures of approximately 15–20 °C, and it is also possible to avoid the fouling problem by using uncontaminated groundwater. The GWHP system can provide a better and more stable performance than an air source heat pump (ASHP) under equivalent conditions [20,21] and is more economical in terms of maintenance with a longer expected lifespan of the system [12]. The standing column well (SCW) ground heat exchanger coupled heat pump system is one of the well-known forms of the GWHP system. However, the system requires a high initial investment for underground drilling of more than 300 m to install a groundwater well.
In Korea, the demand for large-scale residential apartments is substantial, particularly in areas that are characterized by shallow groundwater aquifers at 5–20 m below the ground surface [22]. The underground spaces in buildings in urban areas are typically utilized for underground parking lots or commercial facilities, so, dewatering wells and drainage equipment (e.g., drain pump, level gauge) are added during the initial excavation phase of construction to reject the inflowing groundwater. These systems are expected to operate throughout the lifespan of the building, they are called permanent dewatering (PD) systems. Since the PD systems operate continuously, buildings with large amounts of groundwater inflow incur high managerial costs owing to sewage treatment.
To use the hydrothermal energy of the PD systems, thermal performance of the PD system should be defined. However, research regarding PD systems similar to the one proposed in the present study is yet to be reported. In the present study, a heat pump system to utilize the PD system was proposed and analyzed, named by permanent dewatering heat pump (PDHP) system. The cooling/heating performance of the system was analyzed through varying the inflow rate of the groundwater to take advantage of this unused source of energy.
The challenge and contribution of the present study is to figure out the thermal performance of PDHP system, to answer the following two questions:
  • How much energy can be transferred by PD modules under variable amounts of groundwater inflow?
  • To what extent can the COP of the PDHP be improved compared with that of an ASHP under equivalent conditions?
The TRNSYS, Transient system simulation program [23], which is a well-known energy analysis tool for building energy systems, was employed to analyze the PDHP system, and compare the PDHP system performance with conventional ASHP system. The review of groundwater resources to utilize the PDHP system and its detailed description were presented in Section 2. The simulation-based PDHP system design method was presented in Section 3. The results of the design capacity (kW) of a single PD module and PDHP system, and also the comparison with ASHP were presented in Section 4.

2. Permanent Dewatering Heat Pump System

Figure 1 represents the groundwater level data for each observed location in Seoul from 2016 to 2019 [24]. From data of the 6–13 observatories of each district, it was revealed that the deepest groundwater depth was approximately 18 m and the average value was 9.3 m for all locations, therefore, all buildings that utilize underground space must install a PD system. According to the statistics [25], on the use of the inflow of groundwater prepared by the city of Seoul, most of the groundwater flowing into the PD system is wasted as an unused source of energy.
As illustrated in Figure 2, the average daily amount of groundwater inflow, observed for 1650 independent buildings in 2018 in Seoul, was 52 tons per day, of which 79.1% was discharged into the sewerage system. Among the remaining 20.9%, 12.3% of the groundwater inflow was consumed within the building, with most of the water wasted except in buildings using a well-type borehole heat exchanger.
A large-scale apartment complex in an urban area would typically install several collecting wells, as shown on the left in Figure 3, to drain the groundwater seeping through the underground walls of the building. This groundwater could be used as a source of heat by installing additional equipment capable of collecting or discharging heat energy within the existing collection wells. On the right in Figure 3 is a visual design of the PD module proposed in the present study for the exploitation of groundwater as a heat source. The PD module comprises two containers separated by a baffle: a discharging container corresponding to the existing well and a heat exchanger (HX) container. This PD module prototype uses a coil-type heat exchanger, where the design of this type and mechanism of the heat exchanger is currently in progress.
The discharging container, installed to drain the groundwater, is a water tank of 1.2 × 1.2 × 1.5 m or 1.4 × 1.4 × 1.5 m, with a water gauge installed at the height of 1.2 m from the bottom to trigger the pump to drain the water when it exceeds the predetermined level. The HX container, which has the same size as the discharging container, comprises a pipe with an inlet and outlet installed on the side of the container into which the groundwater flows, with water level gauge and overflow outlet installed at the same level on the other side, through which the HX container is connected to the discharging container. Irrespective of the operation of the drainage pump, the HX container should be completely filled with water for better heat exchange rates.
The coil-type HX container has a bundle of dual coils that are connected to the inlet/outlet headers in parallel, with the coils equally spaced to attain more surface area for efficient heat exchange. The length of each coil varies according to the size of each module, and the coil pitch is 2 cm so that a total of 60 coils can be installed at the height of the overflow. Unlike the case of a standard thermal storage tank, a sufficient amount of continuously flowing groundwater is necessary for its exploitation as a heat source when collected in small water tanks of 1.2 × 1.2 × 1.5 m and 1.4 × 1.4 × 1.5 m. Thus, the utilization of a larger water tank for multiple buildings, such as apartment complexes, would be advantageous over utilization of individual tanks in each building. A detail size and specification of the PD modules are presented in Table 2.
The entire residential complex presented in Figure 3 shares the underground space for parking, securing a sufficient amount of groundwater because of its extensive border. Table 3 represents the inflow of groundwater into residential complexes within Seoul and the average amount flowing into a single collecting well, with a total of 20–22 collecting wells installed for the operation of each drainage system. The total inflow of groundwater is the sum of the average amount of water flowing into each collecting well, which was found to be 24.5 ton/day.

3. Simulation-Based PDHP System Analysis

In the present study, the PDHP system employing the PD module was simulated assuming a daily average inflow of groundwater of 24.5 ton/day (17 Lpm) flowing into the prototype PD modules of 1.2 × 1.2 × 1.5 m and 1.4 × 1.4 × 1.5 m. As previously discussed, the proposed prototype of the PD module was devised as a water-source heat pump system with the heat exchanger attached to the existing system built to drain the groundwater to the sewerage system. As presented in Figure 4, the PDHP system consists of a building, a heat pump, and a PD module, with the two-loop systems configured on both sides of the heat pump. The blue text in Figure 4 indicates an index representing the temperature and flow rate at each point of the system, with EST, LST, G. W, and PDHX signifying the entering source temperature, leaving source temperature, groundwater, and PD heat exchanger, respectively.
The analyses were carried out through simulations to design the PDHP system employing the PD module and appraise its performance. In the design, the building load profile consisted as the cooling dominant case, and the inflow of water was of high temperature, which were used to calculate the capacity of the PD module conservatively. In contrast, the building load profiles of the cooling and heating capacities were similar to each other, and the temperature of the original inflow of water was reflected to appraise the performance under ordinary conditions. The different conditions employed for the design and evaluation of performance are presented in Table 4.
The PD module was connected to the heat pump to determine the applicability of the PD module as a heat source. The system capacity was analyzed by varying the amount of groundwater inflow and the circulated flow rate of the heat pump under the building load conditions where the cooling was dominant. TRNSYS 17, a dynamic energy simulation program, was employed for the analyses, and Type-534 coiled-type HX tank in the TRNSYS TESS library was used for the simulation of the prototype PD module. The flow rate of the total circulation on the source side of the heat pump was assumed to be distributed to each PD module according to Equation (1), configuring multiple modules in parallel with varying inflow of groundwater.
m ˙ PDcoil = m ˙ HP , S N PD
where m ˙ PDcoil and m ˙ HP , S indicate the flow rate of the PDHX in each PD module and the total source-side flow rate of the heat pump, Lpm, respectively, and N PD represents the number of PD modules.
The design of the heat pump system should be configured such that the EST of the heat source side is kept within the temperature capacity of the heat pump. For a GSHP, the maximum extent of the designed EST (ESTset) on the heat source side, capable of being supported by the capacity of the heat pump, is generally set at 30 °C, which was also used for the PDHP system proposed in the present study.
Figure 5 represents the load profile of a building employed for the design of the PDHP system. The annual profile with the capacity of 100 kW for the operations of cooling and heating, with the cooling operation dominant 88.3% of the time, was used. The cooling and heating loads are expressed as (+) and (−), respectively. The building load on Figure 5 was converted into the heat pump load ( Q HP ) by the heat pump COPs, and the Δ T HP , S (=LST − EST) of the heat pump was set to vary according to the constant flow rate ( m ˙ HP , S ) (constant m ˙ HP , S cases), also the m ˙ HP , S was set, such that the Δ T HP , S would be maintained at approximately 5 °C (constant   Δ T HP , S cases) using Equation (2). A total of 10 heat pumps were installed to maintain the temperature difference at the interval of a partial load at Δ T HP , S ≈ 5 °C, by which the operation of each pump was assumed to correspond the partial building load of 10 kW.
Q HP = m ˙ HP , S c p ( LST EST )
Based on the tabulated data provided by a heat pump manufacturer, the coefficient of performance (COP) was determined according to EST, as expressed in Equation (3). The performance indicators such as α and β describe the COP variation as shown in Figure 6, and they are given in Table 5.
{ COP C = α 0 + α 1 EST + α 2 EST 2 COP H = β 0 + β 1 EST + β 2 EST 2
The source-side temperature of the PDHP system is much more stable and lower than the outdoor air temperature. The groundwater temperature remains at 15–20 °C annually, as shown in Figure 7, while the outdoor air temperature varies from −10 to 35 °C, as shown in Figure 8a. Thus, higher heat pump COPs for the PDHP are expected compared with those of a conventional ASHP system. The sinusoidal groundwater temperatures in Figure 7 were used for the comparison simulation between the PDHP and ASHP, as mentioned earlier.
The simulations of the present study aimed at comparing the system performances, particularly focusing on the heat pump COP. The α and β in Table 5 were substituted for the corresponding terms in Equation (3) to model the heat pump so that the ASHP and PDHP would use identical heat pumps, where the ASHP and PDHP were assumed to represent an outdoor unit and a PD unit of 1.4 × 1.4 × 1.5 m (1.4 PD module), respectively. The simulation of each pump was carried out to compare the pumps’ annual performance by varying the temperature differences on the side of the heat source.
Figure 8 shows the annual hourly outdoor temperatures extracted from the Seoul TRY weather data and the test building load of 6 kW. The pattern of the building load of a typical residential house in Korea, having a floor area of 124 m2 and set temperatures of 26 °C and 20 °C for cooling/heating, was used.

4. Simulation Results and Discussions

4.1. Design Capacity of a Single PD Module

The capacity of the prototype PD module was derived through the iterative procedure presented in Figure 9. As illustrated in Figure 4, the TRNSYS 17 template was modeled and simulated with a single PD module in the loop on the heat source side of the heat pump, and the cutoff range of the building load with a capacity of 100 kW was adjusted until the peak value of the maximum ESTPDHX (ESTpeak) reached the ‘Best fit’ for ESTset. Through such iterations equalizing ESTPDHX with ESTset, the peak value of the building load ( Q b , peak ), equivalent to the capacity of the PD module, could be obtained. The iterative procedure presented in Figure 9 was also applied to the simulation for design of multiple PDHP system. The method proposed by Park and Kim [26] was used for the detailed simulation-based iterative calculation.
Figure 10 and Table 6 and Table 7 present the capacity results of 1.2, and 1.4 PD modules. In order to investigate the sizing results of the PD modules, two different cases, such as a constant heat pump source-side temperature difference ( Δ T HP , S = LST − EST) and a constant flow rate ( m ˙ HP , S ) are tested. The results for the cases are given in Figure 10, and the details are also listed in Table 6 and Table 7. Table 6 presents the results for a constant heat pump Δ T HP , S = 5.4°C, while Table 7 presents the results for the constant heat pump source-side flow rates, m ˙ HP , S : 21.8 Lpm (1.2 PD module) and 23.2 Lpm (1.4 PD module). The sizing (kW) results for single 1.2 and 1.4 PD modules are presented according to the groundwater inflow variations, 5–60 Lpm, based on the sizing procedure presented in Figure 9 for both the constant Δ T HP , S and m ˙ HP , S   cases. All of the values that appear in this section were obtained at the peak building load.
As a result, capacities ( q PDHP ) of 6.05 and 6.44 kW were derived when an average groundwater inflow rate ( m ˙ GW , in ) of 17 Lpm was applied. The q PDHP listed in Table 6 and Table 7 represents a possible building load that could be covered by the unit modules while keeping the ESTPDHX peak under the ESTset of 30 °C. From Table 6, for example, the maximum building load should be lower than 6.44 kW for Δ T HP , S = 5.4 °C for a single 1.4 PD module with a groundwater inflow rate of 17 Lpm. As the container volume of the PD module is increased, the q PDHP increases as well. Thus, q PDHP of 1.4 PD module becomes 6.44 kW, which is 0.39 kW larger than q PDHP of 1.2 PD module. The single 1.2 PD module can cover a maximum of 12.46 kW, while the 1.4 PD module covers 13.80 kW with a groundwater inflow rate of up to 60 Lpm.
For Δ T HP , S = 5.4 °C, the m ˙ HP , S should be set at 21.8 and 23.2 Lpm for the 1.2 and 1.4 PD modules, respectively. The q PDHP would vary greatly depending on the variation of m ˙ GW , in rather than the setting of the Δ T HP , S or m ˙ HP , S , since the difference in q PDHP would remain small despite changing Δ T HP , S and m ˙ HP , S under the same m ˙ GW , in conditions. In the present study, the investigated average rate of groundwater inflow, presented in Table 3, was used for the set value, Δ T HP , S = 5.4 °C. However, the values of m ˙ HP , S and Δ T HP , S can be determined at the discretion of the designer.
The changes in the capacity of the PD module ( Δ q PDHP ) corresponding to changing the rate of groundwater inflow ( Δ m ˙ GW , in ) by 1 Lpm are presented on the right side of each table. With regard to the Δ q PDHP / Δ m ˙ GW , in presented in Table 6 and Table 7, the capacity of the 1.4 PD module would increase by an average of 0.34 kW according to the variation in Δ m ˙ GW , in by 1 Lpm in the interval of 5–10 Lpm, whereas the capacity of the 1.4 PD module increases by an average of 0.27 kW in the interval of 10–15 Lpm.

4.2. Design of Multiple PDHP System

Based on the results obtained from Section 4.1, the changes in the capacity of the PDHP system according to the number of modules that were connected in parallel to the source side of the heat pump were analyzed. The groundwater, with a temperature of 20 °C and flow rate of 17 Lpm, was assumed to be flowing into each installed module, while the flow rates on the source side of the heat pump were assumed to be 21.8 Lpm and 23.2 Lpm for the 1.2 module and 1.4 module, respectively.
Figure 11 presents the capacities of the PDHP system corresponding to variable numbers of installed modules (1.2 and 1.4 PD modules). In accordance with increasing the number of modules (NPD) and inflow of groundwater ( m ˙ GW , in ), the capacity of the PDHP system ( q PDHP ) increases linearly and proportionally. Thus, the respective PDHP systems could be designed by adjusting the capacities of the individual PD modules based this linear relationship and the results presented in Table 6 and Table 7.
For instance, the capacity of a single module of 4.5 kW can be set for a site with the inflow of groundwater of 10.7 Lpm for each PD module in Table 3, which lists the varied groundwater inflow rates at the different sites. Alternatively, a total of 12 PD modules, corresponding to a total inflow rate of 240 Lpm at the C site, can be installed by assuming that the capacity of each module could accommodate the inflow of 20 Lpm of groundwater. Nevertheless, by referring to the tendencies illustrated in Figure 10, and Table 6 and Table 7, the decrease in the increment of q PDHP according to an increase in Δ m ˙ GW , in in a single module needs to be taken into account for the combination of PD module designs pertinent to the respective sites.

4.3. Comparison with an Air Source Heat Pump (ASHP) System

The comparison results of the annual simulation between the PDHP system with the 1.4 PD module and an ASHP system are shown in Figure 12 and Figure 13 presents the minimum, maximum, and mean COP during June–August (cooling season) and Decemeber–February (heating season), obtained from Figure 12.
In Figure 12, the bottom graph shows the variation in the annual heat source temperatures for the PDHP and ASHP systems, and the top graph shows their COPs, where the heating COP (COPH) is shown in the lower part from mid-September to mid-March, and cooling COP (COPC) is shown in the upper portion. The ASHP heat source shows the outdoor air temperature of Seoul, and the PDHP heat source represents the water temperature in the PD container that was simulated in TRNSYS. The groundwater temperature in the PD container (PDHP heat source) is more stable than the outdoor air temperature (ASHP heat source) and is remarkably higher during the heating season. Because the heat pump extracts energy from the heat source during the heating operation, increased source temperatures can drive a higher heat pump COP. Furthermore, a lower source temperature leads to a higher cooling COP because the heat pump injects heat energy into the source. Thus, the heating COP of the PDHP is higher than that of the ASHP, while the cooling COPs are similar.
From Figure 13, the minimum, average, and maximum COP values are presented at the bottom, middle, and top of the boxes, respectively. The average COPs of PDHP are higher than ASHP for both the cooling and heating operations—the PDHP COPC is higher by only 0.1, while COPH is higher by 0.79. Furthermore, the temporal variation according to temperature of outdoor air appears greater than the variation in the temperature of the PD container, resulting in a more significant variation in the COP of heating/cooling of the ASHP system than that of PDHP system, which is attributed to the temperature conditions of the heat sources.
The temperature of the PDHP heat source, as shown in the lower portion of Figure 12, remains above 10 °C in winter, whereas the temperature of the ASHP heat source decreases to −10 °C, exhibiting a temperature difference of over 20 °C. On the contrary, in the summertime, the temperatures of both heat sources are relatively similar, and the outdoor air temperature occasionally drops below the temperature of the PD container. Thus, the COPC for the PDHP, presented in Figure 13, appears similar to that of the ASHP. However, when the system is in operation between 9 a.m. and 6 p.m., the values of COPC for the PDHP and ASHP are 5.24 and 4.95, respectively.
The COP of the PDHP system is comparable to that of the ASHP when the temperature of the heat source of the PDHP system is similar to that of the atmosphere. If the PDHP system is used for a building where either the heating load (wintertime) or the cooling load (summertime) is dominant, the performance of the PDHP system, which is superior to that of the ASHP system, could be beneficial. In the present study, the ASHP system and PDHP system were compared using the ‘Seoul TRY weather data’, however, the differences in both systems would vary according to the usage, design, operation scenarios, and the working fluid of the system [27,28].

5. Conclusions

Owing to the advancement in technologies of pertinent applications, new and renewable energy sources, such as geothermal energy used in buildings, have been applied to diverse fields worldwide. For example, environmentally friendly low-carbon policies developed for buildings support these applications. However, despite the potential of unrecognized heat sources, in the form of drained or wasted water that could be exploited effectively, in the buildings around us, the institutional devices to utilize these unused energies are yet to be supported by pertinent studies.
In the present study, a permanent dewatering module (PD module) was introduced for the utilization of the abundant water wasted by numerous buildings using underground space in Seoul, and a ‘permanent dewatering heat pump (PDHP)’ system, exploiting a prototype PD module, was proposed for the utilization of the wasted groundwater. The PD modules of sizes of 1.2 × 1.2 × 1.5 m and 1.4 × 1.4 × 1.5 m can cope with the building loads of 6.05 kW and 6.45 kW, respectively, at the groundwater inflow rate 17 Lpm. The capacity of multiple PD modules, to be exploited as a heat source of a PDHP, increased linearly with increase in the number of modules. Under equivalent conditions, a single PD module of 1.4 × 1.4 × 1.5 m exhibited cooling and heating COPs that were 0.1 and 0.79 higher than those of the ASHP, respectively, which were attributed to the stable temperatures of the heat source.
The results show the potential utilization of the systems for a construction project requiring large-scale underground spaces, where abundant groundwater is available. For such projects, zoning of the PD modules and planning of the heat pump system with adequate PD modules should be considered. Furthermore, the results of the present study can be used for the economic analyses of the PDHP system and the utilization of a hybrid ground source heat pump system.

Author Contributions

Conceptualization, Y.-S.J.; methodology, S.-H.P. and E.-J.K.; software, S.-H.P.; validation, S.-H.P. and E.-J.K.; formal analysis, S.-H.P.; investigation, Y.-S.J.; data curation, S.-H.P., Y.-S.J. and E.-J.K.; writing—original draft preparation, S.-H.P.; writing—review and editing, Y.-S.J. and E.-J.K.; Supervision, E.-J.K. All authors have read and agreed to the published version of the manuscript.

Funding

This work was supported by a National Research Foundation of Korea (NRF) grant funded by Korean government (MSIP) (No. 2021R1A2C4002936).

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

The data used to support the findings of this study are available from the corresponding author upon request.

Acknowledgments

Thanks to GS E&C for their technical support.

Conflicts of Interest

The authors declare no conflict of interest.

Abbreviations

ASHPAir-source heat pump
COPCoefficient of performance
ESTEntering source-side temperature to heat pump
GWGround water
GWHPGround water heat pump
HPHeat pump
HXHeat exchanger
LSTLeaving source-side temperature from heat pump
PDPermanent dewatering
PDHPPermanent dewatering heat pump
PDHXPermanent dewatering heat exchanger
SWHPSewage water heat pump
WWHPWastewater heat pump

Nomenclatures

COP C Cooling COP (-)
COP H Heating COP (-)
c p Specific heat (kJ/kg°C)
H effective effective height (m)
m ˙ GW , in Mass flow rate of ground water inlet (Lpm)
m ˙ HP , S Mass flow rate of heat pump source side (Lpm)
m ˙ PDcoil Mass flow rate of PDHX coil (Lpm)
N PD Number of PD modules (-)
Q b , peak Peak building load (kW)
Q HP Heat pump load (kW)
q PDHP Heat transfer rate of permanent dewatering heat pump (kW)
T GW , in Ground water inlet temperature (°C)
T GW , out Ground water outlet temperature (°C)
Δ m ˙ GW , in Difference in mass flow rate of ground water inlet
Δ q PDHP Difference in heat transfer rate of permanent dewatering heat pump
Δ T HP , S Temperature difference of heat pump source side, LST-EST

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Figure 1. The depth of the groundwater levels observed in the districts of Seoul, South Korea.
Figure 1. The depth of the groundwater levels observed in the districts of Seoul, South Korea.
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Figure 2. Utilization percentage of the inflowing groundwater in buildings (Seoul, South Korea).
Figure 2. Utilization percentage of the inflowing groundwater in buildings (Seoul, South Korea).
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Figure 3. Schematic of the permanent dewatering module (prototype).
Figure 3. Schematic of the permanent dewatering module (prototype).
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Figure 4. Source-side configuration of the permanent dewatering coupled heat pump (PDHP) system.
Figure 4. Source-side configuration of the permanent dewatering coupled heat pump (PDHP) system.
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Figure 5. Annual building load profile (cooling (+) and heating (−)).
Figure 5. Annual building load profile (cooling (+) and heating (−)).
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Figure 6. Heat pump EST-COP curve for heating and cooling operations.
Figure 6. Heat pump EST-COP curve for heating and cooling operations.
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Figure 7. Annual profile of the inlet groundwater temperatures of the flow to the PDHX container.
Figure 7. Annual profile of the inlet groundwater temperatures of the flow to the PDHX container.
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Figure 8. Seoul TRY outdoor weather data (a) and 6 kW building load (b).
Figure 8. Seoul TRY outdoor weather data (a) and 6 kW building load (b).
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Figure 9. Sizing procedure for simulation-based PDHP system design.
Figure 9. Sizing procedure for simulation-based PDHP system design.
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Figure 10. Sizing results for a single 1.2 (left), 1.4 (right) PD module capacity (kW).
Figure 10. Sizing results for a single 1.2 (left), 1.4 (right) PD module capacity (kW).
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Figure 11. PDHP system capacity according to the number of PD modules in parallel loop.
Figure 11. PDHP system capacity according to the number of PD modules in parallel loop.
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Figure 12. Simulation results of heat pump COPs and heat source temperatures for PDHP and ASHP.
Figure 12. Simulation results of heat pump COPs and heat source temperatures for PDHP and ASHP.
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Figure 13. Comparison of cooling and heating COPs of PDHP with ASHP.
Figure 13. Comparison of cooling and heating COPs of PDHP with ASHP.
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Table 1. Review of research on unused energy source heat pump systems.
Table 1. Review of research on unused energy source heat pump systems.
AuthorsHeat SourceSource Side Loop Type
Luo et al., 2020 [12]GroundwaterInjection and production well
Zhang et al., 2020 [10]Lake waterHeat exchanger
Hervás-Blasco et al., 2020 [8]GreywaterGreywater storage tank and heat exchanger
Song et al., 2019 [13]GroundwaterStanding column well (SCW), injection and production well, forced external circulation SCW
Kastrinos et al., 2019 [7]GroundwaterStanding column well
Qin & Hao, 2017 [9]Sewage waterFree-flow-channel heat exchanger
Zhou et al., 2013 [14]GroundwaterInjection and production well
Shen et al., 2012 [15]WastewaterWastewater storage tank and heat exchanger
Ferguson, 2012 [16]GroundwaterInjection and production well
Cho & Yun, 2011 [11] Lake waterBrine water loop heat exchanger
Russo et al., 2011 [17] GroundwaterInjection and production well
Nam & Ooka, 2010 [18] GroundwaterInjection and production well
Table 2. Specification of the prototype module pertaining to the HX container.
Table 2. Specification of the prototype module pertaining to the HX container.
PD Module1.2 × 1.2 × 1.5 m1.4 × 1.4 × 1.5 mUnit
Floor area1.441.96m2
Coil length7.2508.515m
Effective height1.2m
Coil diameter (inner/outer)0.012/0.016m
Coil pitch0.02m
Number of coils60-
Table 3. Measured groundwater inflow rates for eight apartment sites.
Table 3. Measured groundwater inflow rates for eight apartment sites.
SiteDistrictNumber of Apartment BuildingsTotal Groundwater Flow RateGroundwater Flow Rate per Dewatering Well
Ton/DayLpmTon/DayLpm
AMapo1225171.10.8
BEunpyeong32241569.96.9
CSeongbuk1734624015.410.7
DSeocho537025716.411.4
ESeocho772850632.322.4
FJung1476453133.923.5
GJongno1489862438.226.5
HHanam12110076448.833.9
Average55738724.517.0
Table 4. Different simulation conditions for PDHP system design and performance estimation.
Table 4. Different simulation conditions for PDHP system design and performance estimation.
PhasesDesignEvaluation
Building load Energies 14 02273 i001
Cooling dominant profile
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Balanced profile
Groundwater inlet temperature Energies 14 02273 i003
Annually constant
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Sinusoidal profile
Table 5. Comparison of the heat pump performance data for the ASHP-PDHP simulation.
Table 5. Comparison of the heat pump performance data for the ASHP-PDHP simulation.
i α i β i
07.3692.724
1−0.1140.074
20.0009−0.0008
Table 6. PD module sizing results for constant ΔTHP,S (= LST − EST) of 5.4 °C (marked by a square in Figure 10).
Table 6. PD module sizing results for constant ΔTHP,S (= LST − EST) of 5.4 °C (marked by a square in Figure 10).
Module Size
(m3)
m ˙ G W , i n T G W , i n T G W , o u t m ˙ H P , S Δ T H P , S q P D H P Δ q P D H P Δ m ˙ G W , i n
(Lpm)(°C)(Lpm)(°C)(kW)(kW/Lpm)
1.2 PD module
(1.2 × 1.2 × 1.5)
520–28.29.235.4–302.57
1020–27.415.135.4–304.190.32
1520–26.720.035.4–305.550.27
1720–26.521.835.4–306.050.25
2020–26.224.335.4–306.750.23
3020–25.331.435.4–308.720.20
4020–24.736.935.4–3010.250.15
5020–24.241.335.4–3011.500.12
1.4 PD module (1.4 × 1.4 × 1.5)520–28.310.135.4–302.82-
1020–27.616.235.4–304.510.34
1520–27.021.335.4–305.910.28
1720–26.823.235.4–306.440.26
2020–26.525.935.4–307.200.25
3020–25.733.735.4–309.380.22
4020–25.140.135.4–3011.140.18
5020–24.645.335.4–3012.580.14
Table 7. PD module sizing results for constant m ˙ HP , S of 21.8 Lpm (1.2 PD module, left), 23.2 Lpm (1.4 PD module, right) (marked by a circle in Figure 10).
Table 7. PD module sizing results for constant m ˙ HP , S of 21.8 Lpm (1.2 PD module, left), 23.2 Lpm (1.4 PD module, right) (marked by a circle in Figure 10).
Module Size
(m3)
m ˙ G W , i n T G W , i n T G W , o u t m ˙ H P , S Δ T H P , S q P D H P Δ q P D H P Δ m ˙ G W , i n
(Lpm)(°C)(Lpm)(°C)(kW)(kW/Lpm)
1.2 PD module
(1.2 × 1.2 × 1.5)
520–28.421.832.3–302.64-
1020–27.521.833.8–304.260.32
1520–26.721.834.9–305.580.26
1720–26.521.835.4–306.050.24
2020–26.121.836.0–306.700.22
3020–25.221.837.5–308.470.18
4020–24.521.838.8–309.800.13
5020–24.021.839.6–3010.810.10
1.4 PD module (1.4 × 1.4 × 1.5)520–28.523.232.4–302.89
1020–27.723.233.8–304.580.34
1520–27.023.234.9–305.940.27
1720–26.823.235.4–306.440.25
2020–26.523.236.0–307.150.24
3020–25.623.237.6–309.140.20
4020–24.923.238.9–3010.670.15
5020–24.423.239.9–3011.880.12
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Park, S.-H.; Jang, Y.-S.; Kim, E.-J. Design and Performance Evaluation of a Heat Pump System Utilizing a Permanent Dewatering System. Energies 2021, 14, 2273. https://doi.org/10.3390/en14082273

AMA Style

Park S-H, Jang Y-S, Kim E-J. Design and Performance Evaluation of a Heat Pump System Utilizing a Permanent Dewatering System. Energies. 2021; 14(8):2273. https://doi.org/10.3390/en14082273

Chicago/Turabian Style

Park, Seung-Hoon, Yong-Sung Jang, and Eui-Jong Kim. 2021. "Design and Performance Evaluation of a Heat Pump System Utilizing a Permanent Dewatering System" Energies 14, no. 8: 2273. https://doi.org/10.3390/en14082273

APA Style

Park, S. -H., Jang, Y. -S., & Kim, E. -J. (2021). Design and Performance Evaluation of a Heat Pump System Utilizing a Permanent Dewatering System. Energies, 14(8), 2273. https://doi.org/10.3390/en14082273

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