1. Introduction
The increase in rooftop photovoltaic systems (RPVs) penetration, mainly in residential buildings, has significantly decreased carbon footprints and has assisted governments in achieving clean energy targets. The RPVs in some of the utilities now represent the largest energy resources, with an output equivalent to as high as three times the largest dispatchable generator [
1]. Moreover, the generation from RPVs has satisfied almost half of the underlying energy demand for some trading intervals on some days [
1]. As a result of this, conventional generators are bidding at low prices during low demand to ensure they get dispatched and avoid shutting down. The wholesale electricity market has even started to experience negative prices at midday, which historically happened overnight [
2].
On the other hand, a cluster of moving clouds over a small region can significantly fluctuate the output power of the RPVs. Therefore, the conventional generators must run at the minimum stable level in order to be available to supply the load when demand abruptly increases in such cases. If the conventional generators are shut down, they usually have a minimum start-up of a couple of hours before they can supply the load. Hence, the conventional generators are not flexible enough to respond to such rapid load demand changes.
Figure 1 shows the average minimum monthly load demand of the South West Interconnected System in Western Australia. This figure shows that the minimum load demand has decreased by approximately 25% from the first quarter of 2016 to 2020 [
3]. However, before 2016, the lowest demand was usually observed overnight, which was a relatively suitable time for conventional generators to shut down temporarily and restart the next day. However, recently, as low demand periods started to occur during midday, as shown in
Figure 2, the generator usually does not have enough flexibility to shut down and restart to cover the evening peak in a short period. Suppose this trend of increased penetration of RPVs continues. In this case, it will not be an economically viable option for these generators to remain online during midday low-demand periods, presenting a real risk of blackout or extensive load-shedding. Moreover, the RPVs cannot contribute towards peak-shaving and improving self-sufficiency on their own.
The highly inexpensive market for RPV system installation and upfront subsidy provided by most governments has resulted in a further increase in the penetration of RPVs. Reference [
4] addresses the challenges of increased penetration of RPVs by proposing the employment of community solar projects with embedded residential battery energy storage systems (BES). This scheme can be utilised in some newly built strata complexes. However, the BES installation in residential households is minimal currently, primarily due to the high cost and long payback period [
5]. This means that challenges brought in by the increased unmanaged penetration of RPVs will further worsen and threaten the power system security and reliability.
One of the suggested technological solutions to address the challenges of high penetration of RPVs is the deployment of community BES (CBES) [
1], which is economical at the utility and commercial-scale level. A CBES can be important in peak-shaving to alleviate an unwanted duck curve profile in the network, thus achieving the desired level of self-sufficiency. The stored energy in a CBES can also be purchased by the neighbouring households in the community (that do not have an RPV) under a power purchase agreement (PPA), at an economical rate compared to the electricity unit charge rate [
6,
7]. A CBES provides a reasonable level of flexibility to get the maximum use of generation from the RPV and could avoid exporting a significant portion of that to the grid. In addition to this, the CBES has a sufficient design margin that can handle the uncertainty of solar generation during days of varying solar generation.
On the other hand, it is interesting to note that the electricity tariffs are significantly different at the rural and remote locations because of the financial and technical challenges associated with supplying electricity to such areas [
8]. The majority of remote locations rely on fossil fuel-based electricity generation, which is costly, and these costs can be significantly reduced by deploying RPVs integrated with CBES [
9]. In such a case, the CBES can enhance the self-sufficiency of such remote localities.
A significant amount of research on self-sufficiency aspects of residential and individual BESs, peak-shaving, and duck curve profile have been conducted. Klingler [
10] proposed that the customer’s load, base, and peak demand be considered for the system size’s design. On the other hand, [
11] outlined the importance of peak-shaving capabilities in integrating RPVs into the grid, while system design accomplishing maximum self-sufficiency may lead to BES oversizing [
12].
In terms of BES design criteria, [
13] outlines the fact that a BES low-energy capacity and significant power charge rate results in a rapid BES saturation, leading to the export of unwanted power to the utility feeder. Furthermore, a high discharge rate of BES can limit the potentiality of BES to address the demand at levels that are rational [
14]. The possibility of remotely controlling BES for communities where households have RPVs has been outlined by [
15], whilst the optimal sizing and placement of RPV and BES to reduce the total cost and improve reliability was discussed in [
16,
17]. Various real-time operation modes for BES design for households with RPVs operating under time-of-use tariffs were proposed in [
18]. Likewise, [
19] proposed a framework for optimal charge and discharge operation of BES for RPVs to gain the maximum cost-benefit. Similarly, [
20] developed a control approach for the optimal energy flow from RPVs with BES on the basis of its state of charge. Alternatively, another method was proposed in [
21] for the energy management and optimisation in smart households consisting of RPVs and BES in a controllable or uncontrollable load situation. Reference [
22] studied the optimal sitting and sizing of BES while minimising the cost incurred resulting from voltage fluctuation, losses, and peak demand. Reference [
23] studied how the BES models affect its state of charge and state of health estimation and how simplified models may lead to oversized BESs. Reference [
24] developed a BES model based on its charging and discharging characteristics, whereas [
25] conducted a review of current perspectives in the economic analysis of BES investment.
The majority of the reviewed literature has outlined the potential advantages of RPVs and discussed the BES design criteria for individual households. BES is significantly expensive on a small scale, and also there is less load profile flexibility to better utilise BES. However, the above literature has not comprehensively addressed how CBES can address RPVs’ unmanaged penetration and employ them to improve the community’s self-sufficiency and peak shaving. The above literature highlights some areas in which a new design criterion can be developed. On the basis of this background, this paper proposes a design criterion for CBESs based on the penetration level of RPVs in the community. The proposed design criterion can help improve the utilities’ technical issues, such as increasing the community’s self-sufficiency, mitigating duck curve profile, and enabling peak-shaving. The proposed design criteria formulate the design requirements to achieve each objective. The system designer can appropriately size the system based on the more preferential objectives than others. Thus, the significant contribution is formulating the parameters for the mitigation of duck curve, increasing peak-shaving, and enabling self-sufficiency on the basis of the size of the community with RPVs with the help of a CBES.
2. Proposed CBES Design Criteria
As discussed above, a CBES is more economical than individual residential-owned BESs [
1], especially when its costs are distributed over a community with several households. In this background, sooner or later, it will be inevitable for the utilities or aggregators to employ properly designed CBES to address technical challenges such as duck curve profile and peak-shaving, regardless of the imposed additional cost.
This study outlines a design for the CBES system based on self-sufficiency improvement, peak-shaving of the demand, and mitigation of the duck curve. This design is not location-specific and can be employed when a CBES is to be used at any location within the network. CBES’ design is influenced mainly by input parameters of the number of customers willing to purchase energy from the CBES under a PPA
and the number of households with RPVs (
). These input parameters are employed in the proposed CBES design for determining the CBES’s energy capacity (
) and power charge/discharge rate (
).
Table 1 lists and defines the proposed concept’s design indices. If
, the excess is fed to the grid. For load-balancing and peak-shaving, the CBES design should aim to recognise a peak load that is less than or equal to the annual average addressed by the CBES.
Table 2 presents the critical assumptions on timings used in this study; the assumptions made are valid for most of the year, but this can vary on the basis of the location, weather, and other parameters.
The CBES discharging/charging rate is supposed to be greater than the community’s RPVs peak generation for duck curve mitigation, i.e.,
Nonetheless, in order for it to be further improved, CBES discharging/charging rate is supposed to be greater than the community’s RPVs average of maximum daily excess generation, i.e.,
For the accuracy of conditions (2) and (3), the capacity of the CBES’s energy storage is supposed to be larger than or equal to the daily excess generation’s average over the year, i.e.,
However, the CBES discharging/charging rate is supposed to be greater than the peak demand, for peak-shaving, i.e.,
Additionally, the CBES’s energy storage capacity is supposed to be greater than the community’s energy consumption over the peak duration, i.e.,
Ultimately, for self-sufficiency, the average of maximum daily excess generation from the RPVs and the discharging/charging rate of CBES is supposed to be larger than the maximum daily excess consumption, i.e.,
Moreover, the CBES’s energy capacity and the mean of the daily excess generation over a year should be larger than the mean of the consumed daily excess energy over a year, i.e.,
Although (7) and (8) result in competitive self-sufficiency, for attaining maximum self-sufficiency, the discharge/charge rate of CBES is supposed to be larger than the maximum excess consumption observed in the year, i.e.,
Furthermore, the CBES’s energy capacity and the mean of the daily excess generation over a year should be larger than the maximum of the consumed daily excess energy over a year, i.e.,
To sum up, the optimum design criterion of the CBES to reduce the export to the grid and ensure power requirement satisfaction is expressed by
Once the CBES is designed, its performance in achieving the desired objectives can be reviewed on the basis of the following capability indices. The capability of the CBES’s discharge rate in terms of realising the improved duck curve profile can be expressed by
On the other hand, the capability of the CBES’s energy capacity in terms of realising the improved duck curve profile can be given by
Similarly, the capability index of the CBES’s charge/discharge rate in terms of realising the peak-shaving can be expressed by
while that capability of CBES’s energy capacity for the same purpose can be given by
Finally, the capability index of CBES’s charge/discharge rate for realising high self-sufficiency can be expressed by
while its energy capacity for the same objective can be given by
The capability indices close to unity show the CBES is adequately designed to achieve the respective objective. The following section presents the performance evaluation of the proposed design criteria.
It is to be noted that the internal information of the BES such as its model or controller do not need to be considered at this design stage, as far as some key parameters such as the roundtrip efficiency and charge/discharge rate are considered. It is also to be noted that the over- and under-generation issues were the focus of the above design criteria. Thus, its key aim is using the CBES for mitigating the fluctuations in power system by decreasing the exported power to the grid at midday and enhancing the network’s peak-shaving. Even though this over- and under-generation indirectly impacts the voltage, the voltage variations were not directly considered in this study.
3. System Performance Evaluation
For the proposed concept’s performance evaluation, a CBES consists of some (3 to 10) households with RPVs of 10 kWp each, and some (5 to 50) households within the same community that are willing to purchase energy from the CBES under a PPA contract, were considered. The CBES proposed for the system had a power charge/discharge rate of 5 to 200 kW, and its energy storage capacity was 20 to 600 kWh. The study considers the new BES with roundtrip efficiency of 89%. The example case consists of three households with RPVs of 10 kWp and five households within the community involved with this program, as shown schematically in
Figure 3. The RPV generation and residential consumption and data used in this study were retrieved from Ausgrid’s 2013 Solar Home Electricity Data [
26]. This data shows 30 min RPVs generation and electricity consumption of 300 households. Relevant number of households are picked up on the basis of the study requirement for each scenario. The RPVs installed in this community were of small size. Therefore, a suitable multiplier was applied to scale the RPVs generation output for 10 kWp system. MATLAB was employed used for performance evaluation.
The performance of the suggested design is discussed by observing the quantities for self-sufficiency, peak-shaving capability, and the duck curve profile during three different periods as the result of the designed CBES, as discussed below.
3.1. RPV-Equipped Households and Number of Customers
The impact of the number of customers purchasing energy from the CBES under a PPA and households with RPVs in the community is evaluated using a sensitivity analysis. In this study, the first was varied from 3 to 10, while the latter was varied from 5 to 50. It was given that the CBES’s energy capacity and power charge/discharge rate were 200 kWh and 50 kW, respectively, as displayed in
Table 3. The performance evaluation for self-sufficiency realisation, peak-shaving enhancement, and duck curve mitigation of the proposed design criterion is explained below.
The first scenario assumed three community households with RPVs, while customers who purchased electricity under a PPA increased from 5 to 15. In such a case, the CBES’s observed performance was as below:
In terms of power, condition (7) to achieve high self-sufficiency was met by having the average maximum daily excess consumption (
less than
and the average daily maximum daily excess RPVs generation
). The system design parameter can even satisfy the yearly highest excess consumption
in all studied three instances. A greater than unity self-sufficiency capability index for the CBES’s charge/discharge rate
of
Table 3 verified this.
In terms of energy, the high self-sufficiency condition of (8) was met by having the average daily excess energy consumption (
) less than
and the average daily excess generation
). A greater than unity self-sufficiency capability index of
in
Table 3 also verified this.
As seen from
Table 3 and
Figure 4,
Figure 5 and
Figure 6, these input design parameters for the specified size of CBES ticked all the boxes by mitigating duck curve profile and providing high self-sufficiency, which came with high peak-shaving capability.
The second scenario assumed five community households with RPVs, while the number of customers under a PPA increased from 5 to 25. In such a case, the CBES’s observed performance was as below:
In terms of power, condition (3) for the duck curve profile mitigation was unsatisfied as the RPVs’ average excess daily maximum generation
) was higher than
and
. Therefore, the duck curve profile would be observed, as seen from
Figure 5a, less than the unity duck curve profile improvement capability index of
;
Table 3 also verifies this.
In terms of energy, the self-sufficiency condition of (8) was met by having the average daily excess generation lower than and the average daily excess energy consumption over a year . However, due to the low , firstly the duck curve profile was observed.
Secondly, because of the CBES’s inability to store most of the excess generation, a medium SS was observed in the third time slot when the number of households under PPA was quite large (i.e., 25).
Likewise,
Figure 4,
Figure 5 and
Figure 6 show that the duck curve profile flattened with a slight reduction in self-sufficiency when
increased from 15 to 25.
Scenario 3 assumes seven community households with RPVs, while customers under a PPA increased from 20 to 50. In such a case, the CBES’s observed performance was as below:
In terms of power, the high self-sufficiency condition of (7) was not met as either both the RPVs’ average daily maximum excess generation (), and were lower than the average maximum daily excess consumption , resulting in low or medium self-sufficiency.
In terms of energy, the high self-sufficiency condition of (8) was also not met, as the yearly average daily excess energy consumption (
was greater than either or both of the average daily excess generation
and
. However, condition (6) of achieving peak-shaving was still met, resulting in achieving high peak-shaving capability. These results were also verified by the respective capability indices in
Table 3.
3.2. CBES’s Energy Capacity and Power Charge/Discharge Rate
In most of the scenarios, it is important to keep the CBES size based on the excess generation from the RPVs and size of the community. It is expected in most of the markets that CBES must be available during peak hours; therefore, for better grid integration, it is recommended that CBES sizing should be based on the proposed design criteria in this paper. A sensitivity analysis to evaluate the impact of the energy rating and power of the CBES while 10 customers were under a PPA and 50 community households had RPVs was conducted.
Figure 7a illustrates the presence of the duck curve profile, which was because of the excess power, which was neither consumed by customers nor stored by the CBES, and exported to the grid.
Figure 7b displays the exported power, which was equivalent to the excess generation above the CBES charge rate during CBES charging mode until it was fully saturated. According to
Table 3’s assumed parameters,
kW, became the minimum threshold of the BES power ratings to restrict majority power export to the grid; as displayed in
Figure 7a, significant improvement in the duck curve profile was seen by utilising a CBES charge rate equal to or greater than
of 139 kW.
In terms of peak-shaving,
Figure 8a displays the period that the CBES was fully discharged.
Figure 8b displays the times the demand was not addressed by the BES and RPVs, thus importing energy from the utility grid. The BES supplied a significant fraction of the peak hour duration when higher values of
were relatively higher than
. However, after 18:00, no peak-shaving was noticed, and a low peak-shaving capability was observed with small
ratings. The proposed design criteria of CBES suggests that the peak-shaving capability was smartly exploited by a combination of having the
equal to the peak demand
of 19 kW, defined by (1), and the
equal to 171 kW (i.e., the peak demand integrated over the peak period defined by (6)).
To restrict energy export to the grid due to having a BES fully saturated, the
should be equal to or greater than the yearly average excess daily generation
kWh, as shown in
Figure 9.
In terms of self-sufficiency, with a moderate
of 200 kWh, the community’s self-sufficiency was not affected by varying the
rate. However, the impacts were observed on the peak-shaving capabilities and duck curve flattening. For instance, a BES with a
of 50kW and an
of 200 kWh performed better in terms of peak-shaving capability and duck curve flattening than the other studied
ratings, as displayed in
Figure 7 and
Figure 8. Increasing the CBES’s energy capacity to 600 kWh matched with the proposed design criteria of (8), better in achieving high self-sufficiency, as observed in
Figure 9 and from
Table 3. Different
rates did not significantly affect the peak-shaving capability in the case of an
higher than 600 kWh. However,
Figure 9 shows that failure to meet condition (2) results in the export of energy to the grid, as seen when
kW. Furthermore, self-sufficiency was affected by lower
, as seen in
Figure 9b; the corresponding capability indices in
Table 3 also verify the above observations.
4. Discussion
This study focused on various design components of a CBES to achieve the desired technical objectives of peak-shaving capabilities, self-sufficiency, and duck curve profile improvements. The study introduced indices based on the input parameters of historical generation to define the CBES size, which can address the consumption at an appropriate level. The studies show that a larger portion of the households should have RPV in a community to increase self-sufficiency. This also needs to be accompanied by a proper capacity of the CBES, since an undersized CBES will increase the amount of exported energy to the utility feeder and worsen the duck curve profile. On the other hand, an oversized CBES may not be utilised optimally, thus making the CBES financially less justified. The studies show that a suitably sized CBES can store all or most of the excess generation from the RPVs and supply the community demand in a longer demand period, hence improving the peak-shaving capability.
Moreover, the studies show that the charge/discharge rate of the employed CBES in the community should be based on the average excess maximum daily generation from the RPVs and average highest excess daily consumption of the community, while its energy capacity should be based on the average daily excess generation and consumption over a year. A deviation between the employed BES capacity and these quantities will result in a larger portion of the RPVs’ excess generation being fed to the utility feeder, causing a duck curve profile. In terms of peak-shaving, the charge/discharge rate of the employed CBES should be equal to the difference between the average maximum excess daily consumption and the average hourly consumption over a year. Then, the BES’ energy capacity should also be such that the CBES can supply the community demand over the entire peak period. Under such a design objective, the charge/discharge rate and the energy capacity of CBES will be relatively lower.
Suppose the key design objective is realising high self-sufficiency for the community. In that case, the number and rating of the RPVs should be large enough such that the yearly average excess daily generation over a year from the RPVs on any day becomes at least equal to the yearly average excess daily energy consumption. Moreover, the CBES’s energy capacity and charge/discharge rate should be high enough to store the excess generation and address the demand at any interval. Moreover, employing a CBES with a larger capacity and charge/discharge rate increases self-sufficiency. However, the study also shows that realising high self-sufficiency requires significantly overdesigned CBES.
On the basis of the performance evaluation, we found that the proposed CBES design criteria provide an accurate forecast on the level of duck curve profile improvement, peak-shaving capability, and self-sufficiency. It should be noted that the proposed design criteria were evaluated on the basis of the historical data, as the real-time data may be above or below this threshold, resulting in the value of indices being defined slightly differently. Therefore, the CBES designer should place some tolerance to achieve the desired objectives. The proposed CBES design criteria can be used as a guideline for the utilities when employing CBES in existing communities to accomplish either or all of the discussed objectives.