摘要

Energy Savings in Semiconductor Fabs

半導體廠房之節約能源策略

關鍵詞/ 節能23、耗能、耗電、碳足蹟、熱負荷、CDA壓力、製程冷卻水溫度
Keywords / Energy Saving17,Energy Consumption,Power Soumption,Carbon Footprint2,708,Heat Load,Cda Pressure,Pcw Temperature,708
文字設定:

INTRODUCTION

Energy and resource consumption in the semiconductor industry is causing increased attention since on one hand it increasingly impact the wafer cost due to continuously raising energy prices and on the other hand the energy consumption has an important environmental impact measured by the carbon footprint of the final product.

Also the size of the semiconductor industry attracts attention by regulatory bodies. So Samsung Electronics consumes already 1% of Korea’s overall power consumption [1].

This paper shall show, how semiconductor fabs consume power and resources, and shall identify opportunities how the overall power and resource consumption can be reduced.

Figure 1 shows a typical power consumption distribution by facility system of a 300 mm fab. Data have been taken from multiple sources [2] [3] [4] [5] and been integrated into a tool based equivalent energy consumption model.

Figure 1 : Energy consumption of a semiconductor fab by facility system (300 mm)

This diagram shows that the largest amount of power is consumed by the equipment, but approx. 55% is consumed by facility systems. Although also this consumption is mainly driven by process requirements, e.g. exhaust, need for cooling, consumption of nitrogen, compressed air and ultrapure water. The energy needed for facility systems can much higher but also lower between 35% and 65% of the total site power consumption.

The variation between fabs depends on climatic and operational conditions:

  • Need for cooling and for how long, raw water temperature cooling or use for heat recovery
  • Use of natural gas for boiler and local exhaust abatement
  • Water management system: chemical purity of raw water, need for high recycling rates due to cost, scarcity or regulations
  • Specific process requirements, e.g. quantity and temperature of hot ultrapure water
  • Special conditions, e.g. use of river water for cooling.

The diagram gives some ideas where energy can be saved, but it still does not differentiate enough.

ENERGY CONSUMPTION IN A FAB

Abetter model to determine actual energy and resource saving potentials is therefore shown in Figure 2 and 3. This model uses the equ ivalent energy consumption concept according to SEMI S23 [6] (direct and indirect energy consumption) and starts from the use itself in the process and considers the indirect energy consumption by the process utilities, such as UPW, nitrogen, compressed air, exhaust etc, but it can eb applied beyond that for all resource consumption. In a second layer it also considers the energy consumption of the infrastructure systems, such as the cleanroom, the make-up and recirculating air handling systems, the boilers and chillers. It differentiates between the consumption directly in the tool and the consumption of subfab equipment also called by-pack equipment, such as vacuum pumps, local exhaust abatement, chillers, RF generators etc.

Figure 2 : Direct and indirect power consumption in a fab (overview)

Figure 3 : Direct and indirect power consumption by system

Figure 3 is a more detailed visualization of the relationships

Figure 4 shows a breakdown of the equivalent energy. About 50% is consumed as power, but additional 50% of the equivalent energy is consumed as process utilities. This does not include the natural gas consumption for abatement.

Figure 4 : Equivalent equivalent energy consumption fabwide according to SEMI S23

Figure 4 shows the ratio between direct power consumption and the equivalent power consumption of the individual process facilities.

The power and utility consumption was then broken by process area again based on literature data.

Figure 5 summarizes the results. The first column shows the power consumption of the equipment, the second columns the indirect power consumption, by compressed air, nitrogen, hot and cold ultrapure water, exhaust (incl. required make-up air), heat emitted to te cleanroom and process cooling water incl. the energy needed for the chiller. This indirect energy consumption was converted into power consumption by using the energy conversion factors (ECF) defined in SEMI S23, which are listed in Table 1. The third column shows the total equivalent power as defined by SEMI S23.

Figure 5 : Power & equivalent energy consumption by process area according to SEMI S23

Table 1 : Standard energy conversion factors (ECF) by SEMI S23 [6]

 

Unit

 

ECF

Power

kW/

kW

1

Exhaust

kWh/

m3

0.004

Heat released to the cleanroom

kW/

kW

0.287

Ultrapure water (UPW)

kWh/

m3

9

Hot UPW

kWh/

m3

92.2

Process cooling water (PCW)

kWh/

m3

0.79

Nitrogen (N2)

kWh/

m3

0.25

Compressed air (CDA)

kWh/

m3

0.147

High temperature (HT) PCW

kWh/

m3

0.26

House Vacuum

kWh/

m3

0.06

To identify energy saving potentials another step is required. It needs to be understood, which equipment parts actually consume the energy. The results of a fabwide analysis are shown in Figure 6. It shows as an example the power consumption of a complete fab based on equipment categories. The local exhaust abatement is considered as part of the tool consumption.

Figure 6 : Power consumption of mainframe and subfab components, average over fab. ( calculation assumptions )

In this case that about one third of the tool power consumption is used by the mainfarme and two thirds by the bypack-equipment in the subfab.

HOW CAN THE ENERGY CONSUMPTION BE REDUCED?

Energy savings can be achieved in three main areas

a. In the facility and infrastructure system

b. In the process itself or

c. At the interface between facility and infrastructuresyszems

1 Improvements in the facility systems

Over years the focus has been on the facility systems since changes are supposed to have no or a lesser impact on process results.

General mechanical systems

The first step was to apply good piping engineering practices, i.e. to find the optimum between operational cost driven by the pressure drop and by the motor/pump/blower/fan efficiency. Success has been reported in many publications. [7] [8] [9]

The investment cost for variable frequency drives reduced over the years and therefore new fabs are using them extensively for pumps, compressors and large fans.

Cleanroom and air handling systems

The energy consumption of the cleanroom depends on many factors:

  • Cleanroom class/filter coverage
  • Cleanroom concept and associated pressure drop
  • Fan efficiency
  • Temperature and humidity specifications

300 mm fabs and 200 mm Standard Mechanical Interface (SMIF) fabs have typically much lower filter coverage than traditional fabs. This alone has reduced the power consumption of fabs drastically. Today the power consumption of the recirculation air handling system is hardly higher than the power consumption of the lighting system.

Compressed air and bulk gas systems

Large progress has been made over the years for the compressed air systems. Most manufacturers offer energy saving control systems which are optimizing the operation of the variable frequency drives. Besides that fabs are using more and more turbo compressors compared to oil free screw and similar compressors after smaller turbo units became available.

2 Improvements at the process

Process requirements are driving the overall energy and resource consumption. Naturally the equipment itself is under tight scrutiny. On one hand changes are difficult to implement since they require process re-qualifications on the other hand during process development optimization processes are used to drive down the cost of ownership or cost per layer. Therefore it is mandatory to use energy efficient equipment right from the beginning. Inefficient processes are replaced soon, so electroplating replaced ideas to deposit Copper layers with PVD or CMP replaced other planarization processes. And this is constantly changing and improving.

Equivalent energy consumption fabwide according to SEMI S23

Here is the main application of SEMI S23. It allows the characterization of tools with regard to their overall impact of the energy balance of a fab. Semiconductor companies and equipment suppliers are driving energy savings for manufacturing equipment with aggressive roadmaps. [10] [11]

It needs to be noted, that the technology scaling itself drives energy savings. Assuming that the same product is produced every two to three years the manufacturing output is doubled per wafer. However this is normally not counted in the energy saving roadmaps.

Another way to generate energy savings is the increase of the throughput of equipment. Many facility consumptions, such as exhaust, heating etc. are constant over the time. Therefore an increase in wafer throughput can reduce the specific energy consumption.

Another important driver for energy savings is the reduction of idle consumptions. This can range from optimized lamp configurations in RTP tools to modulating transfer chamber gas flows or UPW by-pass flows in wet equipment.

The reduction of idle consumptions is covered in more detail below.

Energy efficient components

There is a continuous drive to improve component efficiencies. In the last years dry vacuum pumps are improved dramatically with regard to energy reduction. Most pumps allow today to vary speed and nitrogen purge. But also new designs have been introduced which improve pumping efficiency under vacuum conditions without impacting reliability and lifetime of the vacuum pumps.

Solid state chillers have replaced only to a small extent traditionally refrigeration chillers due to high investment cost and availability only for small loads. But also traditional refrigeration chillers are much more efficient then before. They are equipped with variable frequency drives and many other energy saving features.

Resource reduction by tool/chamber matching

Resource consumption matching is one of the basic methods of eco efficiency engineering widely used in the chemical and pharmaceutical industry. Resource consumptions between similar tools and chambers running the same processes shall be equal. In the semiconductor industry this working methods gains more and more attraction. With state-of-the-art software and data mining techniques this can be achieved much more easily then previously. The detailed concept is explained in [12] and [13].

Reduction of idle consumptions

Many resources such as purge or cleaning gases are actually unproductive, but can also pose a certain risk to the process, if not used properly:

  • Purge gases prevent the intrusion of particles and oxygen
  • Gases such as Helium or mixtures are used to cool down wafers, variations may impact the temperature profile in the reactor/equipment
  • Heating to maintain temperature levels in reactors, since variations may cause particle bursts impact layer uniformity

The best known phenomenon is that dry vacuum pumps and abatement are running in a fab all the time independently from the status of the tool. During the idle state of the tool pumps cannot be switched off, but can run at a lower pump speed and with reduced Nitrogen purge rate and a burn/wet exhaust abatement could reduce fuel gas and oxygen.

Fab / subfab synchronization

This concept goes one step further than just using possible idle mode energy and resource reductions. Understanding all process steps enables a full synchronization of the subfab tool operation.

3 Improvements at the interface between process and facility systems

The biggest saving potentials besides the idle mode and fab/subfab synchronization can be found at the interface between facilities and process.

Several examples will be discussed below.

High temperature process cooling water ( HAT PCW )

The basic idea is to allow direct cooling from the cooling tower all year long as illustrated in Figure 7.. Historically the temperature level has been set to the strictest requirements in the fab (dehumidification in litho for environmental chamber). This drove the need for facility chillers to cool down the water. Many applications however can accept higher temperature, on contrary water is partly heated up again. In the meanwhile the needed process cooling water capacity is anyhow so high that a second cooling water loop would be economically viable, especially since the energy costs are continuously increasing.

Figure 7 : Current process cooling water system

This concept has been discussed multiple times [7] [15], but not implemented widely since requires a lot of detailed work.

Since not all users could be switched even if theoretically possible without extensive re-qualification, the idea is to install a second process cooling water system the so-called high temperature process cooling water system HT PCW.

So the current recommendation is to use the HT PCW only on the secondary site of local chillers and for applications where there is no impact on the process to minimize the need for a re-qualification of processes.

Exhaust recycling

Another major opportunity is the reuse of un-contaminated exhaust air. It is more energy effective to cool this air than to extract it to the outside and replace it with fresh make-up air since especially in summer this air needs to be to dehumidified, i.e. to cooled down to less than 10°C, which consumes a lot of energy. Opportunities have been discussed by many authors [9] [16]. TSMC has shown on their website in 2009 the most comprehensive program by using this uncontaminated air as make-up air for gas and chemical rooms.

Others

Other major improvement potentials can be found at interface specifications [7].

A good example can be found for compressed air where air is compressed partly to 10 bar g+, but used at this pressure only for very few applications. Most applications require a pressure regulator, destroying most of the energy, before it can be used.

Other examples are the humidity specification for compressed air or the pressure specification for Nitrogen [7].

The site water consumption is closely related to the energy consumption [17]. High reuse rates require typically energy extensive processes for recycling water treatment. If the consideration is gate-to-gate, i.e. only internal to the fab high recycling rates have a negative impact on equivalent power consumption, and thereby carbon footprint, If the balance area is changed to “cradle to gate” also the power of the raw water treatment and transport is considered and then the result is often changing.

ENERGY SAVING ROADMAP

The purpose of this chapter is to review, whether the energy reduction targets set by the ITRS [19] are realistic. Table 2 shows the targets set by ITRS in 2010 [19] in comparison with the 25% reduction target every year, which most companies follow.

Table 2 : ITRS Energy reduction targets set by ITRS in comparison with 25% reduction target over 5 years

 

 

2009

2010-2012

2013-2015

2016-2024

Power Eq/cm2 Si

kWh/cm2 Si

0.5

0.43

0.36

0.30...0.25

Power Total site/cm2 Si

kWh/cm2 Si

1

0.85

0.7

0.6...0.5

Reduction

25%/5 yr

2009

2012

2015

2020

Power Eq/cm2 Si

kWh/cm2 Si

0.5

0.43

0.36

0.27

Power Total site/cm2 Si

kWh/cm2 Si

1

0.85

0.72

0.54

The question is whether these targets are achievable. Table 3 shows the assumptions about implementation levels of the energy saving proposals explained in the previous chapter for a new 300 mm fab.

Table 3 : Energy saving measures by main user and implementation level (assumption)

 

Energy saving measure

2011

2012

2013

2014

2015

 

Proc. Equipment

 

 

 

 

 

 

 

Dry Pumps

Idle mode

25%

40%

75%

100%

100%

% of pumps with idle mode

Turbo pumps

 

5%

10%

20%

30%

30%

Efficiency improvement

Heaters

Efficiency, idle mode

5%

10%

20%

30%

30%

Efficiency improvement

Misc.

Efficiency

5%

10%

20%

30%

30%

Efficiency improvement

Non-Process Pumps

Efficiency

10%

10%

20%

30%

30%

Efficiency improvement

RF Generators

Efficiency improvement

10%

10%

20%

30%

30%

Efficiency improvement

UPS Control

Efficiency improvement

10%

10%

20%

30%

30%

Efficiency improvement

Remote Plasma Clean

Idle mode

10%

10%

20%

30%

30%

Efficiency improvement

Mini Environments

 

 

 

 

 

 

 

Others (Local abatement)

Idle mode

25%

40%

75%

100%

100%

% of abatement with idle mode

Chilled Water

 

 

 

 

 

 

 

Process equipment

HTPCW

40%

50%

70%

90%

90%

 

Others

 

 

 

 

 

 

 

Process Exhaust

Exhaust recycling

 

 

 

 

 

Central + local abatement

Scrubbed & general exhaust

Eco efficiency

10%

20%

30%

40%

40%

Exhaust reduction (e.g. by recycling)

VOC abatement

Eco efficiency

5%

10%

20%

30%

30%

 

Recirculating Air Handing

Reduce filer coverage

5%

5%

10%

15%

15%

 

Lighting

Efficiency

5%

10%

15%

15%

15%

High efficiency lamps

Make Up Air

See exhaust

 

 

 

 

 

 

Steam/Hot Water

 

 

 

 

 

 

 

Process Cooling Water

See HT PCW

 

 

 

 

 

 

DI/UPW

Eco efficiency

4%

6%

10%

15%

20%

Consumption reduction

UPW Hot

Eco efficiency

4%

6%

10%

15%

20%

Consumption reduction

Compressed Air

Eco efficiency

4%

6%

10%

15%

20%

Consumption reduction

Bulk Gases

Eco efficiency

4%

6%

10%

15%

20%

Consumption reduction

Process Vacuum

Eco efficiency

4%

6%

8%

8%

10%

Consumption reduction

Industrial Waste Collection & Treatment

Eco efficiency

4%

6%

10%

15%

20%

Consumption reduction

Chemical Dispense

Eco efficiency

4%

6%

10%

15%

20%

Consumption reduction

Automated Material Handling System AMHS

Eco efficiency

4%

6%

10%

15%

20%

Consumption reduction

Table 4 shows the results of the simulation. It can be clearly seen that the 25% energy saving level is achievable, but requires the implementation of multiple concepts. A single activity alone will not achieve the target.

Table 4 : Saving results for a 300 mm fab

 

300 mm

Power in kW

2011

2012

2013

2014

2015

Delta in kW

Proc. Equipment

47.2%

11,213

10,692

10,396

9,630

8,965

8,965

2,248

Dry Pumps

19.1%

4,535

4,308

4,172

3,855

3,628

3,628

907

Turbo pumps

4.3%

1,019

1,009

999

978

958

958

61

Heaters

5.9%

1,391

1,321

1,252

1,113

974

974

417

Misc.

5.4%

1,284

1,220

1,156

1,027

899

899

385

Non-Process Pumps

4.1%

963

867

867

770

674

674

289

RF Generators

2.7%

642

629

629

616

603

603

39

UPS Control

1.8%

428

419

419

411

402

402

26

Remote Plasma Clean

1.4%

321

315

315

308

302

302

19

Mini Environments

0.5%

107

107

107

107

107

107

0

Others (Local abatement)

2.2%

523

497

481

445

418

418

105

Chilled Water

20.0%

4,756

3,490

3,129

2,442

1,820

1,820

2,936

Process equipment

13.5%

3,210

1,926

1,605

963

321

321

2,889

Others

6.5%

1,546

1,546

1,546

1,546

1,546

1,546

0

Process Exhaust

2.3%

547

520

492

438

383

383

164

Scrubbed & general exhaust

1.9%

452

429

407

361

316

316

136

VOC abatement

0.4%

95

90

86

76

67

67

29

Recirculating Air Handing

4.0%

951

904

904

856

808

808

143

Lighting

2.2%

523

497

471

445

445

445

78

Make Up Air

3.0%

713

713

713

713

713

713

0

Steam/Hot Water

0.3%

71

71

71

71

71

71

0

Process Cooling Water

2.9%

690

690

690

690

690

690

0

DI/UPW

3.1%

737

708

693

663

627

590

147

UPW Hot

0.5%

119

114

112

107

101

95

24

Compressed Air

4.2%

999

959

939

899

849

799

200

Bulk Gases

7.9%

1,878

1,803

1,766

1,691

1,597

1,503

376

Process Vacuum

0.4%

95

91

89

88

88

86

10

Industrial Waste Collection & Treatment

1.6%

380

365

358

342

323

304

76

Chemical Dispense

0.0%

0

0

0

0

0

0

0

Automated Material Handling System AMHS

0.4%

95

91

89

86

81

76

19

 

 

 

 

 

 

 

 

 

Total

100.0%

23,768

21,708

20,912

19,160

17,560

17,348

6,420

Reduction

 

100%

91.3%

88.0%

80.6%

73.9%

73.0%

 

Power cost reduction in Mio US$

 

1.8

2.5

4.0

5.4

5.6

 

Additionally the savings achieved are in the 5 Mio. US$+ range for a 10000 m2 manufacturing area 300 mm fab.

Key activities to achieve the 25% target in 5 years time horizon are:

  • Reduction of resource consumption using eco efficiency engineering methods such as eliminating idle flows as much as possible and chamber & equipment matching of idle and operational flows
  • Application of smart idle operation of subfab components and fab/subfab synchronization of vacuum pump, heater and local abatement operation
  • Heat recovery from any source, such as hot UPW, compressor cooling water and others.
  • Exhaust recycling for uncontaminated exhaust, optimization of exhaust segregation
  • High temperature process cooling water (free cooling instead of facility chiller) all year long by optimization of process cooling water temperatures. Use of multiple temperature levels.

SUMMARY AND OUTLOOK

The return of investment of the alternatives proposed here are typically in the 2…3 years range for power rates of approx. 0.1 US$/kWh. Not all of them have been implemented widely, but no major obstacles can be seen for new fabs. In existing fabs not all of them can be implemented with reasonable return of investments, but sometimes government funding is available to improve existing fabs.

Savings beyond the current five years horizon will require a lot of effort beyond, what can be foreseen today, such as:

  • Implementation of high temperature PCW for all equipment [7]
  • Minimized inlet pressure e.g. for N2, CDA, UPW: system pressure at less than 4 bar g [15]
  • Reduction of heat load to cleanroom (at the same time use of high temperature process cooling water)
  • Use of green chemistries, which reduce required temperatures.

These changes will require major changes in the process equipment themselves and long process development time. Also since the return of investment is not as clear, it will require close cooperation between all stakeholders to make that happen in the future. This is the reason, why the ITRS has marked the expected energy savings in this time horizon as red.

Energy and resource saving will continue to be a major goal for fabs and suppliers in the semiconductor industry, but it requires a lot of cooperation and efforts to ensure, that it will not impact the process results.

參考文獻

  1. Taeho Kim: The study on efficient energy using of equipment for energy saving, IHTESH, Hsinchu, 2010.
  2. Michael O’Halloran: Fab Utility Cost Values for Cost of Ownership (COO) Calculations, International SEMATECH, 2002.
  3. Horst König: Organizational Energy Conservation at Texas Instruments Freising, Semicon Europe, 2005.
  4. B. Gopalokrishnan, Y. Mardikar, D. Korakakis: Energy Analysis in Semiconductor Manufacturing, Energy Engineering, 107 (2010) 2.
  5. Phil Naughton: Measurement of Conservation of Energy by Semiconductor Manufacturing Equipment and setting of targets for improvements, 2005 IEEE.
  6. SEMI S23: Guide for Conservation of Energy, Utilities and Materials Used By Semiconductor Manufacturing Equipment.
  7. Uehara Teruyoshi: Energy saving at 300mm Fab, Semicon Japan, 2009.
  8. Sarah Fister Gale, Energy costs drive innovation, Cleanrooms, September 2007.
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  10. Sangsun Ha: Climate Change Programs Samsung Electronics, Semicon Korea, Energy Workshop, 2009
  11. Norm Armour: Reducing Environmental & Energy Costs: A Equipment Supplier’s Perspective
  12. Andreas Neuber, Parth Sethia; Eco-Efficient Solutions Reduce Energy, Costs, Semiconductor International, 12/1/2008.
  13. Parris Hawkins, Andreas Neuber, Krishna Vepa: Reducing Semiconductor Process Tool Resource Usage – Pilot Project Results, ASMC San Francisco, 2010
  14. Phil Chandler, Paul Fisher, Andreas Neuber: Subfab sync increases energy savings, Solid State Technology, April 2010.
  15. Mitsuo Igarashi: JEITA Energy Saving Activities for Semiconductor Factory, Semicon Japan, 2007.
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  18. Vyacheslav Libman, Andreas Neuber: Water Conservation Challenges in the Electronics Industry, UPW conference, Austin 2007.
  19. International Technology Roadmap for Semiconductors, 2010, www.itrs.net.

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