Residential Demand Module
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The NEMS Residential Demand Module projects future residential sector energy requirements based on
projections of the number of households and the stock, efficiency, and intensity of use of energy-consuming
equipment. The Residential Demand Module projections begin with a base year estimate of the housing
stock, the types and numbers of energy-consuming appliances servicing the stock, and the “unit energy
consumption” by appliance (or UEC—in million Btu per household per year). The projection process adds
new housing units to the stock, determines the equipment installed in new units, retires existing housing
units, and retires and replaces appliances. The primary exogenous drivers for the module are housing starts
by type (single-family, multifamily and mobile homes) and Census Division and prices for each energy
source for each of the nine Census Divisions (see Figure 5). The Residential Demand Module also requires
projections of available equipment and their installed costs over the projection horizon. Over time, equipment efficiency tends to increase because of general technological advances and also because of Federal and/or state efficiency standards. As energy prices and available equipment changes over the projection horizon, the module includes projected changes to the type and efficiency of equipment purchased as well as projected changes in the usage intensity of the equipment stock.
The end-use services for which equipment stocks are modeled include space conditioning (heating and
cooling), water heating, refrigeration, freezers, dishwashers, clothes washers, lighting, furnace fans, color
televisions, personal computers, cooking, clothes drying, ceiling fans, coffee makers, spas, home security
systems, microwave ovens, set-top boxes, home audio equipment, rechargeable electronics, and
VCR/DVDs. In addition to the major equipment-driven end-uses, the average energy consumption per
household is projected for other electric and nonelectric appliances. The module’s output includes number of households, equipment stock, average equipment efficiencies, and energy consumed by service, fuel, and geographic location. The fuels represented are distillate fuel oil, liquefied petroleum gas, natural gas, kerosene, electricity, wood, geothermal, coal, and solar energy.
One of the implicit assumptions embodied in the Residential Demand Module is that, through 2035, there will be no radical changes in technology or consumer behavior. No new regulations of efficiency beyond those currently embodied in law or new government programs fostering efficiency improvements are assumed. Technologies which have not gained widespread acceptance today will generally not achieve significant penetration by 2035. Currently available technologies will evolve in both efficiency and cost. In general, at the same efficiency level, future technologies will be less expensive than those available today in real dollar terms. When choosing new or replacement technologies, consumers will behave similarly to the way they now behave. The intensity of end-uses will change moderately in response to price changes. Electric end uses will continue to expand, but at a decreasing rate. [1]
Key Assumptions
Housing Stock Submodule
An important determinant of future energy consumption is the projected number of households. Base year
estimates for 2005 are derived from the Energy Information Administration’s (EIA) Residential Energy
Consumption Survey (RECS) (Table 4.1). The projection for occupied households is done separately for
each Census Division. It is based on the combination of the previous year’s surviving stock with projected
housing starts provided by the NEMS Macroeconomic Activity Module. The housing stock submodule
assumes a constant survival rate (the percentage of households which are present in the current projection
year, which were also present in the preceding year) for each type of housing unit; 99.6 percent for
single-family units, 99.9 percent for multifamily units, and 97.6 percent for mobile home units. Projected fuel
consumption is dependent not only on the projected number of housing units, but also on the type and
geographic distribution of the houses. The intensity of space heating energy use varies greatly across the
various climate zones in the United States. Also, fuel prevalence varies across the country—oil (distillate) is
more frequently used as a heating fuel in the New England and Middle Atlantic Census Divisions than in the
rest of the country, while natural gas dominates in the Midwest. An example of differences by housing type is
the more prevalent use of liquefied petroleum gas in mobile homes relative to other housing types.
Technology Choice Submodule
The key inputs for the Technology Choice Submodule are fuel prices by Census Division and characteristics
of available equipment (installed cost, maintenance cost, efficiency, and equipment life). Fuel prices are
determined by an equilibrium process which considers energy supplies and demands and are passed to this
submodule from the integrating module of NEMS. Energy price, combined with equipment UEC (which is a
function of efficiency), determines the operating costs of equipment. Equipment characteristics are exogenous to the model and are modified to reflect both Federal standards and anticipated changes in the
market place. Table 4.2 lists capital cost and efficiency for selected residential appliances for the years 2007
and 2020.
Table 4.3 provides the cost and performance parameters for representative distributed generation
technologies. The AEO2010 model also incorporates endogenous “learning” for the residential distributed
generation technologies, allowing for declining technology costs as shipments increase. For fuel cell and
photovoltaic systems, learning parameter assumptions for the AEO2010 reference case result in a 13
percent reduction in capital costs each time the number of units shipped to the buildings sectors (residential
and commercial) doubles.
The Residential Demand Module projects equipment purchases based on a nested choice methodology.
The first stage of the choice methodology determines the fuel and technology to be used, the second stage
determines the efficiency of the selected equipment type. The equipment choices for cooling, water heating,
and cooking are linked to the space heating choice for new construction. Technology and fuel choice for
replacement equipment uses a nested methodology similar to that for new construction, but includes (in
addition to the capital and installation costs of the equipment) explicit costs for technology switching (e.g.,
costs for installing gas lines if switching from electricity or oil to gas, or costs for adding ductwork if switching
from electric resistance heat to central heating types). Also, for replacements, there is no linking of fuel
choice for water heating and cooking as is done for new construction. Technology switching upon
replacement is allowed for space heating, air conditioning, water heating, cooking and clothes drying.
Once the fuel and technology choice for a particular end use is determined, the second stage of the choice methodology determines efficiency. In any given year, there are several available prototypes of varying efficiency (minimum standard, medium low, medium high and highest efficiency). Efficiency choice is based on a functional form and coefficients which give greater or lesser importance to the installed capital cost (first cost) versus the operating cost. Generally, within a technology class, the higher the first cost, the lower the operating cost. For new construction, efficiency choices are made based on the costs of both the heating and cooling equipment and the building shell characteristics.
The parameters for the second stage efficiency choice are calibrated to the most recently available shipment
data for the major residential appliances. Shipment efficiency data are obtained from industry associations
which monitor shipments such as the Association of Home Appliance Manufacturers. Because of this
calibration procedure, the model allows the relative importance of first cost versus operating cost to vary by general technology and fuel type (e.g., natural gas furnace, electric heat pump, electric central air conditioner, etc.). Once the model is calibrated, it is possible to calculate (approximately) the apparent discount rates based on the relative weight given to the operating cost savings versus the weight given to the higher cost of more efficient equipment. Hurdle rates in excess of 30 percent are common in the Residential Demand Module. The prevalence of such high apparent hurdle rates by consumers has led to the notion of the “efficiency gap”¾ that is, there are many investments that could be made that provide rates of return in excess of residential borrowing rates (10 to 20 percent for example). There are several studies which document instances of apparent high discount rates. [2] Once equipment efficiencies for a technology and fuel are determined, the installed efficiency for its entire stock is calculated.
Appliance Stock Submodule
The Appliance Stock Submodule is an accounting framework which tracks the quantity and average efficiency of equipment by end use, technology, and fuel. It separately tracks equipment requirements for new construction and existing housing units. For existing units, this module calculates equipment which survives from previous years, allows certain end uses to further penetrate into the existing housing stock and calculates the total number of units required for replacement and further penetration. Air conditioning and clothes drying are the two end uses not considered to be “fully penetrated.”
Once a piece of equipment enters into the stock, an accounting of its remaining life is begun. It is assumed
that all appliances survive a minimum number of years after installation. A fraction of appliances are
removed from the stock once they have survived for the minimum number of years. Between the minimum
and maximum life expectancy, all appliances retire based on a linear decay function. For example, if an
appliance has a minimum life of 5 years and a maximum life of 15 years, one tenth of the units (1 divided by
15 minus 5) are retired in each of years 6 through 15. It is further assumed that, when a house is retired from
the stock, all of the equipment contained in that house retires as well; i.e., there is no secondhand market for
this equipment. The assumptions concerning equipment lives are given in Table 4.4.
Fuel Consumption Submodule
Energy consumption is calculated by multiplying the vintage equipment stocks by their respective UECs. The UECs include adjustments for the average efficiency of the stock vintages, short term price elasticity of demand and “rebound” effects on usage (see discussion below), the size of new construction relative to the existing stock, people per household and shell efficiency and weather effects (space heating and cooling). The various levels of aggregated consumption (consumption by fuel, by service, etc.) are derived from these detailed equipment-specific calculations.
Equipment Efficiency
The average energy consumption of a particular technology is initially based on estimates derived from
RECS 2005. Appliance efficiency is either derived from a long history of shipment data (e.g., the efficiency of
conventional air-source heat pumps) or assumed based on engineering information concerning typical
installed equipment (e.g., the efficiency of ground-source heat pumps). When the average efficiency is
computed from shipment data, shipments going back as far as 20 to 30 years are combined with
assumptions concerning equipment lifetimes. This allows for not only an average efficiency to be
calculated, but also for equipment retirements to be vintaged—older equipment tends to be lower in
efficiency and also tends to get retired before newer, more efficient equipment. Once equipment is retired,
the Appliance Stock and Technology Choice Modules determine the efficiency of the replacement
equipment. It is often the case that the retired equipment is replaced by substantially more efficient
equipment.
As the stock efficiency changes over the simulation interval, energy consumption decreases in inverse proportion to efficiency. Also, as efficiency increases, the efficiency rebound effect (discussed below) will offset some of the reductions in energy consumption by increased demand for the end-use service. For example, if the stock average for electric heat pumps is now 10 percent more efficient than in 2005, then all else constant (weather, real energy prices, shell efficiency, etc.), energy consumption per heat pump would average about only 9 percent less.
Adjusting for the Size of Housing Units
Information derived from RECS 2005 indicates that new construction (post-1990) is on average roughly 26 percent larger than the existing stock of housing. Estimates for the size of each new home built in the projection period vary by type and region, and are determined by a log-trend projection based on historical data from the Bureau of the Census. [3] For existing structures, it is assumed that about 1 percent of households that existed in 2005 add about 600 square feet to the heated floor space in each year of the projection period. [4] The energy consumption for space heating, air conditioning, and lighting is assumed to increase with the square footage of the structure. This results in an increase in the average size of the housing stock from 1,632 to 1,934 square feet from 2005 through 2035.
Adjusting for Weather and Climate
Weather in any given year always includes short-term deviations from the expected longer-term average (or climate). Recognition of the effect of weather on space heating and air conditioning is necessary to avoid inadvertently projecting abnormal weather conditions into the future. In the residential module, adjustments are made to space heating and air conditioning UECs by Census Division by their respective heating and cooling degree-days (HDD and CDD). A 10 percent increase in HDD would increase space heating consumption by 10 percent over what it would have otherwise been. Over the projection period, the residential module uses a 10-year average for heating and cooling degree - days by Census Division, adjusted by projections in state population shifts.
Short-Term Price Effect and Efficiency Rebound
It is assumed that energy consumption for a given end-use service is affected by the marginal cost of
providing that service. That is, all else equal, a change in the price of a fuel will have an opposite, but less
than proportional, effect on fuel consumption. The current value for the short-term elasticity parameter for
non-electric fuels is -0.15. [5] This value implies that for a 1 percent increase in the price of a fuel, there will
be a corresponding decrease in energy consumption of -0.15 percent. Another way of affecting the marginal
cost of providing a service is through altered equipment efficiency. For example, a 10 percent increase in
efficiency will reduce the cost of providing the end-use service by 10 percent. Based on the short-term
efficiency rebound parameter, the demand for the service will rise by 1.5 percent (-10 percent multiplied by
-0.15). Only space heating, cooling, and lighting are assumed to be affected by both elasticities and the
efficiency rebound effect. For electricity, the short-term elasticity parameter is set to -0.30 to account for
successful deployment of smart grid projects funded under the American Recovery and Reinvestment Act of
2009 (ARRA09).
Shell Efficiency
The shell integrity of the building envelope is an important determinant of the heating and cooling load for
each type of household. In the NEMS Residential Demand Module, the shell integrity is represented by an
index, which changes over time to reflect improvements in the building shell. The shell integrity index is
dimensioned by vintage of house, type of house, fuel type, service (heating and cooling), and Census
Division. The age, type, location, and type of heating fuel are important factors in determining the level of
shell integrity. Housing units that heat with electricity tend to have less air infiltration rates than homes that
use other fuels. The age of homes are classified by new (post-2005) and existing. Existing homes are
characterized by the RECS 2005 survey and are assigned a shell index value based on the mix of homes
that exist in the base year (2005). The improvement over time in the shell integrity of these homes is a
function of two factors—an assumed annual efficiency improvement and improvements made when real fuel
prices increase (no price-related adjustment is made when fuel prices fall). For new construction, building
shell efficiency is determined by the relative costs and energy bill savings for several levels of heating and
cooling equipment, in conjunction with the building shell attributes. The packages represented in NEMS
range from homes that meet the International Energy Conservation Code (IECC) [6] to homes that are built
with the most efficient shell components. Shell efficiency in new homes would increase over time if energy
prices rise, or the cost of more efficient equipment falls, all else equal.
Legislation and Regulations
American Recovery and Reinvestment Act of 2009 (ARRA09)
The ARRAA09 legislation passed in February 2009 provides energy efficiency funding for Federal agencies, State Energy Programs, and block grants, as well as a sizable increase in funding for weatherization. To account for the impact of this funding, it is assumed that the total funding is aimed at increasing the efficiency of the existing housing stock. The assumptions regarding the energy savings for heating and cooling are based on evaluations of the impact of weatherization programs over time. [7] Further, it is assumed each house requires a $2,600 investment to achieve the heating and cooling energy savings cited in the Oak Ridge study, with a 20 year life expectancy of the measures.
The ARRA09 provisions remove the cap on the 30-percent tax credit for ground-source heat pumps, solar PV, solar thermal water heaters, and small wind turbines through 2016. Additionally, the cap for the tax credits for other energy efficiency improvements, such as windows and efficient furnaces, was increased to $1500 through the end of 2010.
Successful deployment of smart grid projects based on ARRA09 funding could stimulate more rapid
investment in smart grid technologies, especially smart meters on buildings and homes, which would make
consumers more responsive to electricity price changes. To represent this, the price elasticity of demand for
residential electricity was increased for the services that have the ability to alter energy intensity (e.g.,
lighting).
Energy Improvement and Extension Act of 2008 (EIEA 2008)
EIEA 2008 extends and amends many of the tax credits that were made available to residential consumers in EPACT 2005. The tax credits for energy efficient equipment can now be claimed through 2016, while the $2000 cap for solar technologies has been removed. Additionally, the tax credit for ground-source (geothermal) heat pumps was increased to $2000. The production tax credits for dishwashers, clothes washers, and refrigerators were extended by one to two years, depending on the efficiency level and product. See the EPACT 2005 section below for more details about product coverage.
Energy Independence and Security Act of 2007 (EISA 2007)
EISA 2007 contains several provisions that impact projections of residential energy use. Standards for
general service incandescent light bulbs are phased-in over 2012-2014, with a more restrictive standard
specified in 2020. It is estimated that these standards require 29 percent less watts per bulb in the first
phase-in, increasing to 67 percent in 2020. EISA also updates the dehumidifier standard specified in
EPACT 2005, resulting in 7 percent increase in electricity savings, relative to the EPACT 2005 requirement.
New efficiency standards for external power supplies are set for July 1, 2008, reducing electricity use in both
the active and no-load modes. Standards are also set for boilers (September 2012) and dishwashers
(January 2010). Lastly, DOE is instructed to create standards for manufactured housing, requiring
compliance to the latest International Energy Conservation Code (IECC) by the end of 2011.
Energy Policy Act of 2005 (EPACT05)
The passage of the EPACT05 in August 2005 provides additional minimum efficiency standards for
residential equipment and provides tax credits to producers and purchasers of energy efficient equipment
and builders of energy efficient homes. The standards contained in EPACT05 include: 190 watt maximum
for torchiere lamps in 2006; Dehumidifier standards for 2007 and 2012; and ceiling fan light kit standards in
2007. Manufactured homes that are 30 percent better than the latest code, a $1000 tax credit can be
claimed in 2006 and 2007. Likewise, builders of homes that are 50 percent better than code can claim a
$2000 credit over the same period. The builder tax credits and production tax credits are assumed to be
passed through to the consumer in the form of lower purchase cost. EPACT05 includes production tax
credits for energy efficient refrigerators, dishwashers, and clothes washers in 2006 and 2007, with dollar
amounts varying by type of appliance and level of efficiency met, subject to annual caps. Consumers can
claim a 10 percent tax credit in 2006 and 2007 for several types of appliances specified by EPACT05,
including: Energy efficient gas, propane, or oil furnaces or boilers, energy efficient central air conditioners,
air and ground source heat pumps, hot water heaters, and windows. Lastly, consumers can claim a 30
percent tax credit in 2006 and 2007 for purchases of solar PV, solar water heaters, and fuel cells, subject to a
cap.
National Appliance Energy Conservation Act of 1987
The Technology Choice Submodule incorporates equipment standards established by the National Appliance Energy Conservation Act of 1987 (NAECA). Some of the NAECA standards implemented in the module include: a Seasonal Energy Efficiency Rating (SEER) of 13.0 for central air conditioners and heat pumps; an Annual Fuel Utilization Efficiency (energy output over energy input) of 0.80 for oil and gas furnaces; an Efficiency Factor of 0.90 for electric water heaters; and refrigerator standards that set consumption limits to 510 kilowatt-hours per year in 2002.
Residential Alternative Cases
Technology Cases
In addition to the AEO2009 reference case, three side cases were developed to examine the effect of
equipment and building standards on residential energy use—a 2009 technology case, a best available
technology case, and a high technology case. These side cases were analyzed in stand-alone (not
integrated with the supply modules) NEMS runs and thus do not include supply-responses to the altered
residential consumption patterns of the two cases. AEO2009 also analyzed integrated 2009 technology and
high technology cases. The integrated 2009 technology case combines the 2009 technology cases of the
four end-use demand sectors, the electricity low fossil technology case, and the assumption of renewable
technologies fixed at 2009 levels. The integrated high technology case uses the same approach, but for high
technology.
The 2009 technology case assumes that all future equipment purchases are made based only on equipment
available in 2009. This case further assumes that existing building shell efficiencies will not improve beyond
2009 levels.
The high technology case assumes earlier availability, lower costs, and/or higher efficiencies for more advanced equipment than the reference case. Equipment assumptions were developed by engineering technology experts, considering the potential impact on technology given increased research and development into more advanced technologies.[8] In the high technology case, all new construction is assumed to meet Energy Star specifications after 2016. In addition, consumers are assumed to evaluate energy efficiency investments at 7 percent real.
The best available technology case assumes that all equipment purchases from 2010 forward are based on
the highest available efficiency in the high technology case in a particular simulation year, disregarding the
economic costs of such a case. This case is designed to show how much the choice of the highest-efficiency
equipment could affect energy consumption. In this case, all new construction is built to the most efficient
specifications after 2009. In addition, consumers are assumed to evaluate energy efficiency investments at
7 percent real.
Residential Tables 
Residential Demand Module Notes |