A.
Hakimian
,
S.
Kamarthi
,
S.
Erbis
,
K. M.
Abraham
,
T. P.
Cullinane
and
J. A.
Isaacs
*
Northeastern University, Department of Mechanical and Industrial Engineering, 360 Huntington Avenue, Boston, Massachusetts 02115, USA. E-mail: j.isaacs@neu.edu
First published on 4th August 2015
Development of safe, economically competitive, and environmentally responsible nano-enabled products is desirable to avoid unintended consequences. Given the environmental health and safety uncertainties associated with nanomaterials, additional precautions for exposure prevention may be required, although not regulated. Companies working with engineered nanomaterials may want to understand decision tradeoffs for the costs associated with increased levels of occupational safety and potential environmental impacts. Recent advances in nanotechnology have resulted in the development of advanced lithium nickel manganese cobalt (NMC) oxide batteries enhanced with multiwall carbon nanotubes (MWCNT). These batteries have a much greater energy density and product life than traditional lithium-ion batteries. A stochastic process-based cost model (PBCM) is developed to investigate the cost drivers for manufacture of MWCNT NMC batteries targeted for satellite and computer applications. Various levels of occupational safety protection (low, medium and high assumed) are analyzed to determine their effect on total manufacturing cost. The results show that MWCNT cost has the highest impact on total unit cost for production of satellite batteries, whereas cycle time has the highest impact on the unit cost of computer batteries. The mixing step contributes the most to the total unit cost for both satellite and computer MWCNT NMC lithium-ion batteries due to the inclusion of MWCNT costs in the mixing step. The process-based cost model developed in this work not only offers estimation of the economic drivers associated with the MWCNT NMC battery manufacturing, but also allows consideration of strategies to reduce costs. Results contribute to safer manufacturing practices for CNT lithium-ion batteries for low and high production volume applications (satellites and portable computers, respectively).
Nano impactThere is significant promise to realize improved properties of MWCNT batteries, but only when these products are responsibly manufactured, used and disposed throughout their product lifecycle. In this study a stochastic process-based cost model was developed to investigate the cost of occupational safety alternatives for manufacture of MWCNT lithium batteries. By combining PBCM with design of experiment based analysis, the effect of uncertainties in process yield, cycle time, cost of PPE waste, cost of energy, and cost of MWCNT on manufacturing unit costs can be analyzed. This approach allows exploration of ‘what if’ scenarios on the costs of exposure avoidance and allows comparisons with user costs on an annualized basis, considering the value-added longer product lifetimes with CNTs. This study represents a first exploration of cost tradeoffs for CNT batteries over the product lifetime. |
CNTs are nanoscale allotropes of carbon that have a cylindrical structure.7 Their structure, as well as their exclusive electrical, mechanical, thermal and magnetic properties place them in a special class of materials for many potential industrial and scientific applications.7,8 Produced as single-walled carbon nanotubes (SWCNTs) or multi-walled carbon nanotubes (MWCNTs), they are light-weight high-strength materials.8,9 Depending on their chirality, they can be either metallic or semiconducting.8–10 The market demand for CNTs is expected to increase considerably in the future.11,12 Global market demand for CNTs is anticipated to rise 40% to 50% in 2016 relative to 2011 (ref. 11) with demand for MWCNTs alone reaching 3728 MT by 2020 compared to 200 MT in 2011.12 Lux Research reports that the future demand of MWCNTs will result from two applications, namely, conductive polymer composites and lithium-ion battery electrodes12 (see Fig. 1).
Fig. 1 Anticipated MWCNT global market demand for use in battery and polymer composite applications.12 |
The growing use of CNTs has consequently raised concerns about their potential detrimental impact on human health and the environment. Depending on the application, release of CNTs could occur during their production, manufacture of nano-enabled products, their use, and/or product recycling/disposal.13–16 Although results are still under debate, existing studies indicate that CNTs have possible toxicity effects.17,18 As with other potentially hazardous materials, engineering principles can be utilized to design safer CNT manufacturing, use and disposal practices. To avoid exposures and releases during manufacture, a series of best practices has been recommended.19,20 Implementation of these additional safety measures will lead to more responsible manufacture.
That said, added safety measures incur costs. This study therefore focuses on CNT-enhanced lithium-ion batteries to estimate the changes in manufacturing costs for different levels of occupational safety. A stochastic process-based cost model (PBCM) that accounts for uncertain cost parameters is developed to investigate the cost drivers for production of MWCNT lithium nickel manganese cobalt oxide (NMC) batteries targeted for satellites and computer applications. Input parameters and assumptions for each process step (such as the amount of the raw materials, number of workers, and number of machines) are defined.21 Three scenarios are considered to analyze the effect of different occupational safety practices on total manufacturing cost. Each scenario reflects a different combination of additional protection such as ventilation, gloves, gowns, and respirators. The PBCM is built and validated with inputs from an actual process for manufacturing lithium-ion batteries (without CNTs). Manufacturing practices for MWCNT NMC batteries for both low and high production volume applications (satellites and computers, respectively) are investigated.
In lithium-based batteries, the choice of a cathode results in differing properties. Common cathode materials in lithium-ion batteries include lithium cobalt oxide (LCO), lithium manganese oxide (LMO), lithium iron phosphate (LFP), lithium nickel manganese cobalt oxide (NMC), and lithium nickel cobalt aluminum oxide (NCA). The anode for most lithium-ion batteries consists of graphite.23,26,27Table 1 summarizes the characteristics of the most commonly used lithium-ion batteries with different cathode materials. In addition, all battery types require a mechanism for circuit protection and cell balancing for safety. The global market of lithium-ion batteries has been growing significantly in recent years. The market forecast of lithium-ion batteries for specific applications is listed in Table 2.28Table 3 specifies the global market for different types of lithium-ion battery technologies.28 The satellite and portable computer applications selected for investigation in the present work utilize NMC batteries, which are forecasted at the highest volume.
Cathode composition | LiCoO2 (LCO) | LiMn2O4 (LMO) | LiFePO4 (LFP) | LiNiMnCoO2 (NMC) | LiNiCoAlO2 (NCA) |
---|---|---|---|---|---|
Voltage (V) | 3.6 | 3.7 | 3.3 | 3.6 | 3.6 |
Cycle life (h) | 500–1000 | 300–700 | 1000–2000 | 1000–2000 | 500 |
Specific energy (W h kg−1) | 150–200 | 100–150 | 90–120 | 150–220 | 200–260 |
Charge (C-rate) | 0.7–1 C | 0.7–1 C typical, 3 C maximum | 1 C | 0.7–1 C | 0.7 C |
Discharge (C-rate) | 1 C | 1 C recommended; 10 C possible, 30 C pulse | 1 C recommended, 20–25 C continuous | 1 C recommended; 2 C continuous possible | 1 C continuous |
Thermal runaway | 150 °C | 250 °C | 270 °C | 210 °C | 150 °C |
Cost | High | Moderate | Moderate | Moderate | High |
Characteristics | Very high specific energy; limited specific power | Good to high specific energy; high power | Moderate specific energy, high specific power, long life span, | Very high specific energy; high specific power | High specific energy and power, good life span |
Applications | Mobile phones, tablets, laptops, cameras | Power tools, medical, electric powertrain | Portable and stationary needing high load currents and endurance | E-bikes, medical devices, EVs, power tools, mobile devices | Medical devices, industrial, electric powertrain (Tesla) |
Applications | 2015 | 2020 |
---|---|---|
Hybrid electric vehicles | 6.2 | 13.8 |
Plug-in hybrid electric vehicles | 6.3 | 39.7 |
Electric vehicles | 25.3 | 31.7 |
Electric bikes | 0.3 | 3.2 |
Net-books | 11.3 | 24.1 |
Note-books | 29.4 | 42.0 |
Mobile phones | 22 | 39.0 |
Power tools | 5.9 | 8.8 |
Energy storage system | 4.2 | 18.7 |
Total | 110.9 | 220.9 |
Battery technology | 2015 | 2020 |
---|---|---|
NMC | 42.9 | 78.1 |
LMO | 18.0 | 36.3 |
LFP | 9.2 | 40.9 |
NCA | 7.9 | 12.8 |
LCO | 32.9 | 52.9 |
Total | 110.9 | 220.9 |
Fig. 2 Lithium-ion NMC battery with MWCNT manufacturing steps;32 all steps in the battery manufacturing process furnished with general ventilation to create healthy working conditions. When NMC is used as an active material, the protected environment encloses: cell assembly, filling, sealing & welding steps. When both NMC and MWCNTs are used as active materials, the protected environment is extended to cover all the steps except the forming & testing and final assembly steps. |
The economic analyses presented here address scale-up production of CNT lithium-ion batteries that are currently at the research and development stage. These batteries use MWCNT lithium nickel manganese cobalt cathodes. The batteries are designed for satellite and portable computer applications. The anode is made of graphite similar to anode electrodes of traditional lithium-ion batteries.27,37–39 The materials used to make the different components of selected CNT NMC battery are listed in Table 4.
Lithium-ion cell/battery part | Material used |
---|---|
Anode active material | Graphite |
Anode substrate | Copper |
Cathode active material | MWCNT NMC |
Cathode substrate | Aluminum |
Separator | Polyethylene |
Electrolyte solvent | Organic carbonate and lithium salt |
The property improvements in the performance of lithium-ion cells with MWCNTs compared to that of the conventional lithium-ion cells in satellites and computers are listed in Table 5. The inclusion of CNTs in the battery cells improves many parameters including: nominal rate, nominal capacity, specific energy, specific power, and battery life.
The impact of CNTs on battery performance varies depending on the percentage of CNT content in the battery's active material. The main improvement occurs in the maximum power density of battery cells, which is about 800% in satellite batteries. The battery life for both satellite and computer battery cells is expected to double. Other battery cell parameters (see Table 5) are expected to improve by about 25%.40–42
Battery cell parameter | Satellites batteries without CNTs | Satellites batteries with CNTs | Computers batteries without CNTs | Computers batteries with CNTs |
---|---|---|---|---|
Cell type | Prismatic | Prismatic | Cylindrical | Cylindrical |
Cathode material | NMC | MWCNT NMC | NMC | MWCNT NMC |
Anode material | Graphite | Graphite | Graphite | Graphite |
Nominal rate (C-rate) | 2C | 2C | 1C | 1C |
Nominal capacity (A h) | 25 | 30 | 1.8 | 2.5 |
Specific energy (W h kg−1) | 105 | 120 | 190 | 220 |
Maximum specific power (W kg−1) | 200 | 1800 | 160 | 200 |
Battery life (years) | 2 | 4 | 3 | 6 |
In the following section, development of a process-based technical cost model is described for manufacture of NMC batteries. To construct the model, the manufacturing process steps, model inputs, physical parameters and assumptions are defined to calculate total manufacturing costs based on annual production volumes. Process data were collected from a lithium-ion battery manufacturer located in southern New England. Three occupational safety scenarios are considered. The model is designed to account for stochastic input parameters to represent an input range or distribution, which results in manufacturing cost distributions for total battery cost.
The fixed and variable cost items considered for model development are shown in Fig. 3. The variable cost parameters include those cost elements that vary proportionally with production volume. Fixed costs are one-time capital investments that can be distributed across the entire production volume. Variable costs include material, energy, and labor costs, while fixed costs include the cost of equipment, maintenance, building, overhead, and tools.47,49
After entering process inputs for a specific battery application and assumptions for its annual production volume, the model calculates the required number of production lines, machines, materials, labors, and associated amount of energy. The total manufacturing cost per unit is calculated according to the following formula:
(1) |
(2) |
(3) |
(4) |
(5) |
Operation data assumptions | |
---|---|
a Assumed as a percentage (%) of capital cost (main equipment cost). b Assumed as a percentage (%) of direct labor cost. | |
Scheduled downtime per day | 1.5 h |
Hours per day | 24 h |
Days per year | 250 days |
Building life | 30 years |
Interest rate | 10% |
Auxiliary equipment ratea | 10% |
Fixed overhead rateb | 40% |
Maintenance ratea | 5% |
Installation equipment ratea | 2% |
Tool ratea | 25% |
Main cost parameter assumptions | |
---|---|
Direct labor cost | $25 per h |
Indirect labor cost | $20 per h |
Building cost | $73 per ft2 |
Operational and cost data assumptions used for calculating the total cost of MWCNT NMC batteries are provided in Tables 6 and 7. Table 6 shows the operating assumptions for battery fabrication for three work shifts.45,52Table 7 provides assumed cost parameters for: labor, energy, and building.
As in most manufacturing processes, there will be some defective cells/batteries, so the yield will not always be 100%. Based on the assumed conversion rates and the desired production volume, it is possible to calculate the total amount of scrap generated during battery manufacture. Defective units can be collected and sold to recycling companies. Battery manufacturing companies can use the scrap materials as a source of revenue and credit it against the total unit cost. The recycling companies recover metals such as aluminum, copper, and lithium. It is assumed that there is 5% scrap generated during the electrode manufacturing and cell assembly, 10% scrap during the forming process, and 2% during the final assembly. Therefore, a conservative lower limit for overall process yield is 95% × 90% × 98 = 84%.
As described earlier, there is no clear understanding regarding the impact of nanomanufacturing and engineered nanomaterials on human health and the environment.54 Hence, the National Institute for Occupational Safety and Health (NIOSH) suggests handling CNTs and nanoparticles with a hazard-based approach (e.g., avoiding exposures).19 The U.S. Environmental Protection Agency (EPA) also lists CNTs in the Toxic Substances Control Act (TSCA) inventory.20,51 In 2013, NIOSH announced the 8 hour time-weighted average (TWA) exposure limit to 1 μg m−1 (ref. 3) elemental carbon and described the strategies for controlling workplace exposures.19,55 To achieve these low levels, three different EHS scenarios are modeled to compare the costs of low, medium, and higher levels of occupational safety. The assumptions for each scenario are presented in Table 8. The low level EHS scenario is assumed to include moderate engineering controls (with general exhaust ventilation), administrative controls (monthly monitoring), and average Personal Protective Equipment (PPE) requirements (such as latex gloves, disposable respirators, and Tyvek suits). The medium EHS scenario includes local exhaust ventilation as well as general exhaust. Local exhaust ventilation includes blowers, and ductwork, with one hood and one filter assumed for each line. In this scenario, the workplace is monitored more frequently (weekly) for potential exposure to nanoparticles. For PPE, workers use nitrile gloves, disposable respirators, and Tyvek suits. For the high EHS scenario, again general and local ventilation is assumed. High EHS considers higher levels of PPE (e.g., HEPA filter masks instead of disposable respirators; with disposal of PPE considered as hazardous waste), and implements biweekly workplace monitoring and medical monitoring. In the high scenario, local ventilation is assumed to consist of one blower and two sets of hoods and filters for each line. Ventilation for the protective environment is calculated based on the air-change method, which is a product of the manufacturing space volume (ft3) and the number of total air changes per hour. The rate of air changes for the manufacturing area is assumed to be 20 changes per hour.56
EHS instruments to avoid exposures and releases | |||
---|---|---|---|
Type of EHS control | Low | Medium | High |
Engineering controls | |||
General ventilation | General exhaust ventilation | General exhaust ventilation | General exhaust ventilation |
Local exhaust ventilation | - Fume hood - HEPA filter | - Fume hood - HEPA filter | |
Enclosure of processes | Extra equipment | ||
Air monitoring | |||
Administrative controls | Monthly monitoring | Weekly monitoring | Biweekly monitoring |
Medical monitoring | |||
Personal protective equipment | |||
Gloves | Latex gloves | Nitrile gloves | Nitrile gloves |
Respirators | Disposable respirators | Disposable respirators | HEPA filters |
Suits | Tyvek suits | Tyvek suits | |
Disposal of PPE hazardous waste |
The simulation model is run (R = 1000 times) to calculate cost averages and confidence intervals. In each run, the Monte Carlo model generates numbers for the stochastic parameters by using the specified distributions above, and uses these values in the PCBM model to calculate the manufacturing unit cost of the batteries. After running the model 1000 times, the model calculates the average manufacturing unit cost and 95% confidence intervals. In the following sections, the results for the modified PBCM model are illustrated for batteries for satellite and portable computer case studies.
Cell specification | Value |
---|---|
Anode active material | Graphite |
Anode substrate | Copper |
Cathode active material | MWCNT NMC |
Cathode substrate | Aluminum |
Separator | Polyethylene |
Electrolyte solvent | Organic carbonate & lithium salt |
Cell number | 100 cells in 5 modules |
Cell type | Prismatic |
Cell dimension | 95 mm width × 140 mm ht × 28 mm thickness |
Nominal cell weight | 0.908 kg |
Life cycle | >800 cycles |
Nominal cell capacity | 30 A h |
Nominal voltage | 3.6 VDC |
Specific energy | 125 W h kg−1 |
Maximum specific power | 1800 W kg−1 |
CNT Li-ion battery | Ranges for (%) part weight37,57,58 | Model input assumptions |
---|---|---|
Anode material | 12–18% | 15% |
Anode current collector | 2–5% | 3% |
Cathode material | 20–25% | 22% |
Cathode current collector | 1–3% | 1% |
Electrolyte | 8–12% | 10% |
Separator | 2–4% | 2% |
Cell container | 1–3% | 1% |
Module container | 8–12% | 10% |
Pack container and battery management systems | 30–40% | 36% |
The results obtained from the PBCM with Monte Carlo simulation with the low EHS scenario as a base case are presented for satellite batteries. The main cost drivers for manufacture of MWCNT NMC batteries include all stochastic parameters: process yield, the cycle time of the forming step, the cost of hazardous waste disposal for PPE, energy cost, and MWCNT cost. Fig. 5a illustrates the average cost breakdown by fixed and variable cost and Fig. 5b illustrates average cost breakdown by manufacturing process step for MWCNT NMC satellite batteries. The fabrication cost of MWCNT lithium-ion batteries is dominated by variable costs: material cost (84%), followed by labor cost (9%) and energy cost (1%). The mixing step has the highest impact on the manufacturing unit cost (58% of the manufacturing unit cost) due to the cost of MWCNTs and other raw materials used in the mixing step (Fig. 5b). For an annual production volume of 300000 battery cells (3000 batteries), assuming a 10% defective rate after forming and testing, the average annual base case satellite battery cost is approximated at $3945 per battery without considering revenue from manufacturing scrap.
Fig. 5 Manufacturing cost breakdowns of low EHS base case for satellite batteries for mean value; (a) fixed and variable cost breakdown; (b) cost by production step. |
The manufacturing waste is assumed to be collected and sold to the recycling companies. The revenues from scrap produced during the electrode manufacturing processes of CNT lithium-ion batteries are calculated based on the total production volume. As mentioned earlier, 5% scrap generation is assumed during the electrode manufacturing step with 10% and 2% scrap generation during the forming process and final assembly step, respectively. If companies recover revenue from scrap, the total unit cost is reduced to $3891, albeit only a small reduction in the total cost. The result reported here reflects the manufacturing costs without annualizing over the life of the product.
Using the specifications assumed in Tables 9 and 10, and costs for three EHS scenarios assumed in Table 8, along with revenues from scrap generation, the manufacturing unit costs of MWCNT NMC satellite batteries are calculated. The manufacturing unit costs along with confidence intervals for three EHS scenarios are shown in Fig. 6. To calculate the average values and intervals for manufacturing unit cost, the simulation model (Fig. 4) is run 1000 times by generating numbers for the stochastic parameters. The 95% confidence interval for manufacturing unit cost for different EHS scenarios is determined. The results indicate that if high EHS standards are preferred or become mandatory in the future, the manufacturing unit cost of satellite batteries increases by 9% compared to that of low EHS standards or increases by 5% over that of medium EHS standards.
Fig. 6 Unit cost and confidence intervals of alternative EHS scenarios for manufacturing MWCNT NMC satellite batteries. |
Cell specification | Value |
---|---|
Anode active material | Graphite |
Anode substrate | Copper |
Cathode active material | MWCNT NMC |
Cathode substrate | Aluminum |
Separator | Polyethylene |
Electrolyte solvent | Organic carbonate & lithium salt |
Cell number | 6 cells and 1 module |
Cell type | Cylindrical |
Cell dimension | 65.1 mm height × 18.5 mm diameter |
Nominal cell weight | 0.041 kg |
Life cycle | >800 cycles |
Nominal cell capacity | 2.5 Ah |
Nominal voltage | 3.6 VDC |
Specific energy | 220 W h kg−1 |
Maximum specific power | 200 W kg−1 |
CNT Li-ion battery | Ranges for (%) part weight37,57,58 | Model input assumptions |
---|---|---|
Anode material | 14–19% | 17% |
Anode current collector | 5–9% | 8% |
Cathode material | 25–30% | 25% |
Cathode current collector | 5–7% | 5% |
Electrolyte | 10–15% | 10% |
Separator | 2–6% | 4% |
Cell container | 1–3% | 1% |
Module container | 5–10% | 5% |
Pack container and battery management systems | 20–25% | 25% |
Just as in case of the satellite batteries, the amount of raw materials, number of machines, and number of workers change proportionally with the total production volume. The forecasted demand for lithium-ion portable computer batteries in 2018 is 1000000 battery units;59 this value is assumed as the annual total production volume for this case study. The cost breakdown by variable and fixed costs in computer battery manufacturing is shown in Fig. 7a, with the cost breakdown by process step in Fig. 7b. Again, material costs dominate at 62% of the manufacturing unit cost, followed by labor cost (17%) and EHS cost (10%). Because computer batteries are much smaller than satellite batteries, the percentage of material cost is lower for computer batteries, though labor costs remain similar. Fig. 7b indicates that among the battery production steps, the mixing step dominates with 36% of the total manufacturing unit cost. The average manufacturing unit cost of MWCNT NMC batteries for computers (for the low EHS base case scenario) is expected to be ~$27 for an annual production volume of 1000000 batteries, with an assumed 10% defective rate after the forming and testing step. The manufacturing unit cost decreases minimally (by $1) with credits gained through scrap collection. The result reported here reflects the manufacturing costs without annualizing over the life of the product.
Fig. 7 Manufacturing cost breakdowns of low EHS base case for portable computer batteries for mean value; (a) fixed and variable cost breakdown; (b) cost by production step. |
Fig. 8 shows the manufacturing unit cost and confidence intervals of MWCNTs lithium-ion batteries for portable computers. Using the manufacturing assumptions listed in Tables 11 and 12 and the EHS scenarios in Table 8, the average manufacturing unit cost for batteries in portable computers increases when higher levels of EHS are implemented. An increase of nearly $4.1 per unit (about 15% cost increase) results from shifting from low EHS practices to high EHS standards. The percentage increase in the manufacturing unit cost for computer batteries is about the same as that for the satellite batteries (10% cost increase). However the absolute dollar numbers will be smaller for computer batteries due to design differences between computer and satellite batteries.
Fig. 8 Unit cost and confidence intervals of alternative EHS scenarios for manufacturing MWCNT NMC portable computer battery modules. |
Factor level | Process yield Tri(a, c, b) | Cycle time Tri(a, c, b) | PPE waste cost Tri(a, c, b) | Energy cost N(μ, σ) | MWCNT cost N(μ, σ) |
---|---|---|---|---|---|
1 | (0.9, 0.95, 1) | (60, 72, 84) | (8, 16, 24) | (0.2, 0.01) | (800, 100) |
0 | (0.8, 0.85, 0.9) | (24, 48, 72) | (0, 8, 16) | (0.15, 0.01) | (600, 100) |
−1 | (0.7, 0.75, 0.8) | (12, 24, 36) | (0, 4, 8) | (0.1, 0.01) | (400, 100) |
Main and interaction effects of the factors on manufacturing unit cost of lithium-ion batteries with CNTs are investigated using a full factorial design. A three-level design with 5 factors has 243 possible combination treatments. The PBCM model was executed 1000 times for each run (treatment), and the average manufacturing unit cost of 1000 replications was taken as the response value for that run. MINITAB was used to analyze the results.
The main effects of process variables on manufacturing unit cost satellite batteries (for the high EHS scenario) are depicted in Fig. 9. Each plot in the figure shows the variation in manufacturing unit cost as a process variable that is varied from its low value to its high value, while keeping all other process variables at their midlevel. These plots are called marginal mean plots. The steep slope of the variation of total manufacturing cost with respect to MWCNT cost indicates that MWNT cost has the strongest effect on the satellite battery unit cost. Process yield has the second strongest effect on manufacturing unit cost. If process yield is poor, then the manufacturing unit cost will increase significantly due to high consumption of MWCNTs and other materials for the satellite battery manufacturing. Cycle time also exerts a non-negligible influence on the manufacturing cost. Longer cycle time means higher energy consumption and more labor hours. Although PPE disposal cost was one of the main contributors to the cost of maintaining high EHS standards, changes to hazardous waste costs do not appear to significantly affect the manufacturing unit cost. Similarly, the influence of energy cost on manufacturing unit cost is dwarfed by the influence of MWCNT cost and process yield.
Fig. 10 shows the interaction effects of factor-pairs on manufacturing unit cost of a satellite battery for the high EHS scenario. The middle line of each plot in the matrix is the same as the marginal mean plot of the corresponding variable in Fig. 9. Parallel lines in a plot indicate that two parameters associated with the plot do not interact, as is the case of PPE disposal cost and MWCNTs, although individually each of them may affect the cost. If the lines in the plot coincide or almost coincide with one another but with a non-horizontal slope, then only one of the variables has influence on the response variable. This is the case with the process yield-PPE disposal cost pair; only process yield has an effect on the unit cost, whereas PPE disposal cost has no effect on the unit cost. If the lines in the plot coincide or almost coincide with one another but with a close-to-horizontal slope, then neither of the two variables has influence on the response variable. This is the case with the PPE disposal cost-energy cost pair; neither of these two has an effect on the unit cost. When the lines are non-parallel as in the case of process yield and MWCNT cost, then each of these parameters affect the cost individually as well as interactively; at low MWCNT cost, process yield has a lower effect than at high MWCNT cost (i.e., the slope is steeper when MWCNT cost is high).
In Fig. 11 the response surface graph for satellite MWCNT batteries illustrates the effect of the two most influential parameters on the manufacturing unit cost: MWCNT cost and process yield. If high process yield is achieved through process improvements and MWCNT cost decreases over time due to advancements in nanomanufacturing, then the manufacturing unit cost will decrease significantly. Because both the process yield and the MWCNT cost have significant effects on the manufacturing unit cost of satellite MWCNT batteries, they both should be scrutinized to minimize the manufacturing unit cost.
The main and interaction effects of process variables on manufacturing unit cost of computer batteries differ from those of satellite batteries. Both cycle time and process yield have a significant effect on the manufacturing unit cost of computer batteries with MWCNTs; however, process yield has higher effect because of high-volume production of computer batteries. Cost of MWCNTs has a lesser effect on the manufacturing unit cost of computer batteries than on the unit cost of satellite batteries due to the fact that computer batteries require lower quantities of MWCNTs. The cost of disposal of PPE hazardous waste has the least effect on total manufacturing unit cost of computer batteries. Similarly, energy cost shows a negligible effect on total unit cost of computer batteries. The interaction between the cycle time and process yield shows the highest effect on the manufacturing unit cost of computer batteries, while the interaction between PPE disposal cost and energy cost shows the least effect. When the cycle time is long and process yield is poor, the manufacturing unit cost is high, as shown in the response surface graph for portable computer batteries (Fig. 12).
The economic analysis indicates that MWCNT cost and process yield have the greatest effect on manufacturing unit cost for satellite batteries, while process yield and cycle time have the greatest effect on the unit cost of computer battery modules. The cost of MWCNTs is likely to continue to come down as CNT manufacturing technologies improve, with significant reductions expected for large volume customers. Prices on the order of $100 per kg MWCNT or less are anticipated. Similarly the process yield of battery manufacturing is likely to improve with advancement in related technologies. As the price of MWCNTs goes down and process yields increase with time, manufacturing unit costs of satellite batteries are likely to become lower than current costs. If improvements to the existing technologies reduce cycle time, then future manufacturing unit costs of computers will also decrease. Currently, the duration of the forming and testing step is the largest contributor to the cycle time; it is a bottle-neck for high throughput production. Because CNTs have been shown to improve the charge and discharge rates of batteries, it is likely that the required cycle time for the forming step will decrease for CNT-enabled batteries. Other technologies could be explored to compress the forming and testing cycle time.
Energy cost has only a small effect on manufacturing unit cost of batteries compared to the effect of process yield, MWCNT cost, and cycle time. However there is still an opportunity to lower energy consumption by recapturing the discharge energy during the forming and testing step to utilize elsewhere in the battery manufacturing facility. For example this approach can mitigate the energy demand required to maintain high EHS standards for CNT-enabled batteries. In addition, the use of renewable energy could also be explored to determine the effects on unit cost as well as on related environmental impacts.
The use of MWCNTs in batteries results in significant enhancements (e.g., increased specific energy by 20%, battery life by 100%, and run time by 25%), but overall costs increase with inclusion of MWCNTs. When low EHS standards are maintained, the manufacturing unit cost of computer MWCNT batteries increases by 39% (from $19.78 to $27.46) relative to that of non-MWCNT battery modules; it is 55% (from $2520 to $3891) in the case of satellite batteries. This cost differential increases if high EHS standards are implemented: 60% higher (from $19.78 to $31.59) for computer MWCNT batteries and 70% higher (from $2520 to $4284) for satellite MWCNT battery modules compared with non-MWCNT batteries. There are several ways to assess whether these increases are worthwhile to stakeholders, which are discussed below.
For end users or manufacturers, it is notable that the cost of one unit of specific energy decreases when MWCNTs are added to batteries. For computer batteries, the relative cost of specific energy decreases from $0.142 per W h for batteries without MWCNTs to $0.118 per W h for MWCNT-enhanced batteries. Similarly these numbers drop from $37.57 per W h to $31.56 per W h for satellite batteries. Further, technical experimentation shows that the life of MWCNT NMC computer batteries will increase by 100% compared with the life of traditional NMC batteries. Given a doubled product life, it is useful to compare annualized costs of batteries with and without MWCNTs. Just as LED light bulbs cost more but last longer, MWCNT-enabled batteries cost more but provide longer operating life. The annualized cost for MWCNT-enabled computer batteries is expected to be spread over a 6 year life (compared to a 3 year period for computer batteries without MWCNTs). Considering 10% interest rate on initial investment, the annualized cost of a MWCNT-enabled computer battery is $6.20 (compared with $10.86 for a computer battery without MWCNTs). Similarly the enhanced battery life with MWCNTs in satellite applications is expected to be 4 years (compared to 2 years for its counterpart without MWCNTs), and annualized unit costs drop to $1244 from $2273. Although the MWCNT-enabled batteries are more expensive, they are less expensive on an annualized basis, considering their value-added properties for their longer product lifetimes.
The costs associated with implementing higher levels of EHS standards during manufacture may also outweigh the costs of potential future liabilities. This study shows that the manufacturing unit cost increases by ~15% for computer applications and ~10% for satellite applications from the base case (low EHS) compared with the high EHS scenario. The liability costs, if MWCNT regulations were imposed or made retroactive, could be higher than the cost of implementing more responsible industrial hygiene practices from the start. As such, taking preventative action to avoid the potential health and environmental consequences of MWCNTs in the manufacturing stage is likely to result in lower economic risk, particularly given a still uncertain future regulatory climate for CNTs.
There are ample means to avoid human exposures during occupational settings during manufacture or end-of-life (EOL), and as noted in this analysis, it is a question of cost. As new nano-enabled products emerge, costs to cover potential liabilities would also need to be assessed. As the knowledge-base grows for any potential risks, the insurance industry would offer coverage to manufacturers. Though premiums might be high as first, costs would decrease with time as risks become more certain.60 Firms could then explore these cost tradeoffs to determine whether to proceed. Some companies are currently willing to embrace the higher costs to afford the enhanced properties, because there is a market for their product. In the case of MWCNT batteries, the technical advantages result in longer lifetimes and lower energy footprints, and for some applications this makes good sense.
While this analysis has focused on the manufacturing phase of the life cycle, it is important for designers and manufacturers to consider the end-of-life alternatives for CNT-enabled batteries. Given the uncertain EHS effects or hazards associated with CNTs, it is useful to consider development or expansion of recycling infrastructures that avoid exposures and releases. Labeling systems for these batteries could help prevent inadvertent exposures during disposal or recycling especially for workers in recycling industries – and help protect the environment from possible CNT contamination. For powering satellites in orbit, MWCNT batteries would offer advantages in reduced weight, and would not affect humans during use or EOL, with complete burn up designed upon re-entry for newer satellites (hence no EOL disposal exposures). For powering laptops, consumers are not likely to be exposed, but laptop EOL battery disposal would be problematic if not addressed prior to production and broad distribution. Similarly, for powering electric or hybrid vehicles, consumers would not generally be exposed to CNTs, but if EOL practices are not thoughtfully designed, EOL workers could be at risk for exposures. If manufacturers are using CNT-enhanced materials, they should consider a plan for some level of product stewardship to allow responsible disposal of CNT-enabled batteries, just as automotive lead acid batteries are required to be handled with effective pollution control systems that also minimize worker exposure. There is significant promise to realize the improved properties of MWCNT batteries, but only when these products are responsibly manufactured, used and disposed throughout their product lifecycle.
For policymakers, uncertainty about risk poses dilemmas. On one hand, they do not want to over-regulate and undercut commercialization of potentially innovative technologies. On the other hand, they do not want to expose workers and nearby communities to potential risk from nanoparticles. Given such uncertainties, the prudent action may be to enable manufacturers to install the best possible occupational and environmental safety systems, perhaps through grant programs and tax incentives. Given past experience with risks that became more apparent over time, taking such precautions at the manufacturing stage seems a most prudent and cost-effective path.
Footnote |
† Electronic supplementary information (ESI) available. See DOI: 10.1039/c5en00078e |
This journal is © The Royal Society of Chemistry 2015 |