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Commercial refrigeration is a broad equipment category that includes:
While the category is broad, the essentials can be represented by two commonplace configurations:
Focusing on central supermarket systems, the prototypical system includes various refrigerated and frozen food display cases, connected to a central refrigeration system, typically located in a mechanical equipment room or a rooftop enclosure. The typical direct expansion (DX) central refrigeration system consists of several sets of rack mounted compressors that independently serve a portion of the refrigeration load in the store. Often there are two racks for medium temperature, fresh food loads and two racks for low temperature, frozen food loads, but the exact configuration varies depending on the store size and other factors. Traditionally, the long runs of liquid and suction vapor lines connecting the display cases with the central compressor system in the DX configuration have been a source of refrigerant leaks, due to the large number of tubing joints and the significant movement caused by thermal expansion during hot gas defrosts. Pre-Montreal Protocol, CFC-12, CFC-502, and HCFC-22 were the refrigerants used; as the CFC phase-out date has passed, a complicated transitional regime of refrigerants is in use that still includes CFC-12 and CFC-502 from some existing equipment, along with HCFC-22, HCFC-22 based blends, and HFC blends that replace CFC-502, including R404A and R507. In the post-ODS phase-out context of this study, the relevant baseline refrigerants are the HFC blends, most commonly R404A or R507. Alternate refrigerants include ammonia and carbon dioxide, although modified system configurations are needed:
A major part of the rationale for the two alternate vapor cycle systems is to significantly reduce the refrigerant inventory, and to minimize the length of refrigerant tubing and number of fittings that are installed in the field.
While not subject to efficiency regulation, common practice in supermarket system design has been to design for high efficiency. This is an economically driven practice, owing to the high duty cycle of the equipment and the fact that supermarket energy costs are comparable to bottom line profits.
Recent developments in the rapidly evolving food retailing business have obsoleted many of the underlying assumptions of the TEWI-3 study. This subsection provides an updated estimate of typical energy use, based on input supplied by Hussmann [Thomas, 1999]. The most significant change, that began about ten years ago, is the increase in the size of the average supermarket that is being built. From the average size of 25,000 square feet for existing supermarkets cited in the TEWI-3 study, the average size of newly constructed supermarkets today is approaching 60,000 square feet. Given the 8-10 year remodeling/renewal cycle of the industry, this will be the average store by the mid to later part of the next decade. Based on an average of six recent Hussmann installations throughout the U.S., a "typical" U.S. supermarket and its refrigeration system can be characterized by the following assumptions [Thomas, 1999]:
On the basis of the preceding, representative refrigeration energy consumption in a typical, newly constructed supermarket is:
This is a representative level of energy consumption for comparing these alternatives as applied in a particular store. Obviously many variables influence actual energy consumption.
Refrigerant emissions are a more significant contribution to the LCCP in conventional DX systems in supermarkets than in smaller, factory assembled self-contained equipment, so the assumed charge sizes and emission rates have a significant impact on the calculated LCCP.
The GWP and manufacturing impact for the refrigerants of interest are summarized in Table 8-1.
| Refrigerant | GWP 100 yr. ITH | Refrigerant Manufacturing | Total |
| R404A | 3,260 | 18 | 3,278 |
| R507 | 3,300 | 18 | 3,318 |
| R410A | 1,725 | 14 | 1,739 |
| R717 | 0 | 2 | 2 |
LCCP estimates for U.S. supermarkets have been prepared based on the energy consumption discussed in 8.2 and the following assumptions about refrigerant charge size and emissions [Thomas, 1999].
100% EOL refrigerant recovery is assumed and an average system life of 15 years is assumed. Table 8-2 summarizes the resulting LCCP for four configurations:
| Configuration | Refrigerant | LCCP Million Kg CO2 | ||
| Indirect* | Direct** | Total | ||
| DX | R404A/R507 | 11.7 | 12.1 | 23.8 |
| Distributed | R404A/R507 | 10.7 | 0.8 | 11.5 |
| Secondary Loop |
R404A/R507 | 13.6 | 0.18 | 13.8 |
| Ammonia | 13.6 | 0.0001 | 13.6 | |
For direct expansion and distributed systems, that place the refrigerant charge throughout the store, the amount of refrigerant charge that could potentially be released into the store is large and the use of flammable or high toxicity refrigerants is not feasible. Store operators in the U.S. and some other countries will not accept the safety and legal risks and safety codes prohibit such large quantities of flammable refrigerant to be used in a publicly occupied space.
With secondary loop systems, potentially hazardous refrigerants such as ammonia and hydrocarbons could be used, but additional costs of safety precautions will be incurred.
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