| Back to Contents Page |Home Energy Index |About Home Energy |
| Home Energy Home Page| Back Issues of Home Energy |


Home Energy Magazine Online March/April 2000


field notes

Designing an Affordable Green Housing Project

by Nancy Malone

This site plan of the Emeryville Resourceful Building Project shows how a two-story duplex and a two-story single-family house all fit comfortably on a 5,500 ft2 lot.
Table 1. Exterior Wall Assemblies--Cost Comparisons
Standard $/Ft2 ERB $/Ft2
2 x 6 @ 16 in OC $3.30 Sustainable 2 x 6 @ 24 in OC $2.75
R-19 fiberglass batts $0.40 R-19 cellulose $0.55
1/2-in OSB $1.10 5/8-in OSB $1.20
Wood fiber cladding $4.50 Cement fiber cladding $5.00
Standard exterior paint $0.55 Recycled exterior paint $0.65
15# building paper $0.15 15# building paper $0.15
1/2-in gypsum board $1.15 5/8-in gypsum board $1.25
Standard interior paint $0.55 Low-VOC interior paint $0.75
Standard caulk $0.05 Low-VOC caulk $0.08
$/ft2 of wall $11.75 $12.38
Total cost this project $74,789 $78,799
Table 2. 50-Year Cost Savings on Siding
Hardboard Siding Cement Fiber Siding
Cost/ft2 $4.50 Cost/ft2 $5.00
Installed cost $28,642 Installed cost $31,825
Warranty  25 yr Warranty 50 yr
Replacement cost at 25 yr $28,642 Replacement cost at 25 yr $0
Replacement cost at 50 yr $57,284 Replacement cost at 50 yr $31,825
Simple expected savings over 50 yr $25,459
Note: These numbers are based on the cost estimate, not on the contractor's pricing. 
Table 3. Exterior Wall Assemblies--Gross Energy Requirements in Therms
Fuel Fuel Production Fuel Use Transport Feedstock Total Therms
Standard ERB Standard ERB Standard ERB Standard ERB Standard ERB
Electricity 400 115 203 52 4 3 0 0 607 170
Oil 69 38 193 48 168 113 75 162 508 362
Other 156 129 1,034 620 6 66 2,239 1,552 3,435 2,368
Total th. 625 282 1,429 720 178 182 2314 1,714 4,550 2,900
Savings 55% 343 50% 709 -2% -4 26% 600 36% 1,650
Note: Differences in electrical energy between the two systems result from two key factors: a) differences in energy requirements to manufacture different building products and their related raw materials, and b) differences in types of fuels used to generate electricity in various geographic locations where raw materials are aquired and building products are produced.
Cement fiber lap siding was used on the homes. This material is very durable and more cost-effective in the long run.
Framing in the ERB homes was 24-in on center. 
Figure 1. This wall, floor, and roof section shows the variety of green materials selected for the ERB project.
This comfortable, affordable housing project is environmentally sound and fits into the style of the neighborhood.
Table 4. Annual Savings Summary Compared to Title 24 Requirements--Averaged per Residence
Energy Efficiency Measures Annual Energy Savings Cost Savings
Therms kWh $
R-19 batt insulation 23 9 $16
R-20 spray insulation 61 24 $43
High-efficiency ductwork 23 9 $16
Second-floor mass: Gypcrete 9 4 $7
0.50 U-value windows 41 16 $27
0.35 U-value windows 67 26 $47
High-efficiency condensing furnace 49 0 $32
High-efficiency hydronic heating 90 67 $67
Selected fluorescent lighting 0 88 $11
High-efficiency appliances 0 359 $47
Water heater blanket, low-flow fixtures 50 0 $33
Total of selected measures 250 147 $182
Note: Shaded items are the ones we selected.
Table 5. Annual Emissions from Operating Energy, Averaged per Unit
Standard Title 24 Model ERB Model % Savings
CO2/unit (global warming) 7,300 kg/yr 5,700 kg/yr 23%
SOx/unit (acid rain) 36 kg/yr 30 kg/yr 14%
NOx/unit (acid rain) 16 kg/yr 14 kg/yr 18%

Green building principles have not been as widely applied to affordable housing as energy efficiency principles have. The reasons for this include perceived higher construction costs and a reluctance on the part of developers and funders to use new materials and methods for publicly funded projects. Recently my firm, Siegel & Strain Architects, designed a unique residential construction project in a moderately priced neighborhood in the San Francisco Bay Area. With this project, we sought to show how careful selection and installation of mainstream materials--along with judicious use of recent innovations, recycled materials, and alternate construction methods--can create cost-effective, environmentally sound, affordable housing. We also hoped to show that satisfying environmental goals would actually make the housing more affordable.

The Emeryville Resourceful Building (ERB) project consisted of infill housing built on an empty lot in an otherwise developed neighborhood of older homes and apartments. It was completed in February 1999. It consists of three units--a two-story duplex and a two-story single-family house--on a 5,500 ft2 lot. The overall massing (that is, the volumetric shape or form) and placement of the buildings was tightly constrained by the size and proportions of the site and the five parking spaces required by local zoning regulations. The project was designed to blend in with the modest surrounding neighborhood housing and to strengthen the urban fabric by using otherwise underutilized land. 

Project Goals

It was imperative that our design not substantially add to the construction cost, reduce the floor area, or lower the quality of the homes. In addition, the environmental measures had to give the occupants tangible benefits by reducing maintenance and operating costs and by providing a healthier place to live. Finally, because state law requires that the construction contract be awarded to the lowest bidder--probably a contractor without any specialized training or knowledge of green building--the project had to be built using conventional means that any contractor could apply. 

We set ourselves five specific environmental goals:

  1. Provide energy-efficient housing.
  2. Provide housing that is easy and inexpensive to operate and maintain.
  3. Reduce resource consumption.
  4. Create a healthy indoor environment.
  5. Provide a model for environmentally sound, affordable housing.
Although many green houses have been built in the last few years, most designers have approached the process qualitatively rather than quantitatively; that is, few designers have actually attempted to measure how much better their green homes are. We wanted to measure the environmental impacts and costs of green structural systems and assemblies and compare them to those of standard stuctural systems and assemblies. We examined and compared complete building assemblies such as walls, roofs, and floors rather than individual materials. This creates a more realistic profile, because a material's performance often depends on its relationship to other materials in a particular assembly. 

Project Components and Findings

After developing alternate building assemblies for the floors, walls, and roof, we analyzed each assembly on the basis of cost per ft2 per unit of floor area, as well as total project costs. We subjected selected materials to a life cycle cost analysis (described below). We studied environmental impacts, including inputs of energy and raw materials, and solid waste and air and water emissions. We worked with the structural engineer to design a resource-efficient structural system (described below). Energy efficiency measures were compared based on how much energy and money they saved on an annual basis. 

The results of these studies allowed us to make decisions based on environmental performance criteria, initial cost, and long-term costs; when we examined these together, we felt we could make sound decisions based on environmental goals--and stay within budget.

Estimating Construction Costs

Baker Pre-Construction, a construction cost-estimating firm, created comparative cost estimates for each building assembly, including itemized costs for all of the materials in each assembly. This enabled us to see where costs varied, and therefore where cost-effective choices could be made. Table 1 shows the costs for a standard wall assembly and the optimized wall assembly that we selected. Although the ERB assembly cost slightly more, the benefits exhibited in other studies of life cycle costs, life cycle assessment, and energy efficiency showed us that this was an environmentally sound, cost-effective choice. Ultimately, we were pleased to find out that the estimated costs were almost identical to the bid that came in. 

Life Cycle Costs

Many of the environmental benefits and cost savings offered by the materials we selected for the project result from the use of durable materials, or from reducing the amount of material used to do a job. Table 2 combines information from the cost estimate and from material warranties. Warranties offer the most accurate estimate of the life of each material, although many materials do last somewhat longer. The information in Table 2 shows how much can be saved by investing in durable materials. In this case, the cement fiber siding had slightly higher initial costs, but these were justified by the long-term savings.

Life Cycle Assessment

After the design team completed initial selections and cost estimating, all the materials in the building assemblies underwent life cycle assessment. Boustead Consulting & Associates created an objective comparison between the standard systems and the alternate systems, using a computer simulation program that they have developed to calculate air emissions, water emissions, solid-waste generation, and embodied energy for the entire assembly. The comparison was undertaken using a systems engineering approach. As the entire building was modeled, each of the possible materials to be used for a given element (such as insulation, for example) was programmed in, one at a time, to determine its effect on the performance of the building, as well as the cost savings that would be realized by using it. The comparison also examined the life cylce of each material, including resource extraction, manufacture, transport (during all phases), the useful life of the product, and disposal. 

The final analysis identified measurable environmental performance differences between products and assemblies and showed which materials have particular environmental benefits or disadvantages. This allowed the design team to make educated selections. Table 3 is representative of the many comparisons made in this study; it compares the gross energy requirements of the two exterior wall assemblies. The data in Table 3 show that there is a clear environmental advantage to using the ERB assembly.

Designing the Structural System

We selected stick frame construction because it is most often used for affordable housing on the West Coast. We optimized the material used in the buildings by utilizing an efficient framing technique, known as optimum value engineering (OVE), that was developed by the National Association of Home Builders Research Center. This saved money by reducing the amount of wood going into the buildings by placing studs at 24 inches on center. This in turn reduced costs, thus allowing us to specify certified lumber (that is, harvested from a environmentally managed forest), which costs about 5% than does standard lumber. 

With the help of the structural engineer, we specified the following measures: 

  • frame walls at 24 inches OC; 
  • use cut-off ends for blocking;
  • use precut studs and joists where feasible;
  • use built-up headers instead of solid lumber;
  • use the smallest headers allowed by structural drawings; and
  • use roof trusses instead of standard framing.
These methods generated savings throughout the project. We reduced the total use of wood in the project by 19%, which in turn reduced the initial material costs. 

Operating Energy

The energy analysis was conducted by the Davis Energy Group of Davis, California. The study considered the effects of various energy efficiency measures on energy consumption and looked at ways to improve comfort. It resulted in an economically feasible design that minimizes energy use and reduces operating costs and associated environmental impacts.

Components that affect energy consumption were computer modeled to compare efficient alternatives to the standard California Title 24 Energy Code requirements. We then selected a package of cost-effective energy-saving materials and systems. These included, among other things: 

  • sealed electrical boxes;
  • use of foam sill sealer (this was observed during construction to make sure it was used thoroughly);
  • high-efficiency ductwork (R-4.2, specified sealant, tested for air infiltration); 
  • 0.35 U-value windows with solar insect screens on north- and south-facing windows;
  • a high-efficiency condensing furnace;
  • a water heater blanket;
  • low-flow water fixtures; and
  • sprayed cellulose insulation to achieve maximum R-value and to avoid installation defects. 
Each building was modeled with the full set of energy-saving features to determine its overall efficiency. Table 4 lists some of the measures we considered; those we selected are shaded. The greatest savings were in items that reduce heating costs: $47 per year for improved windows; $32 per year for a high-efficiency furnace; and $43 per year for better insulation. Given the mild climate, no air conditioning was installed, but the improved windows and insulation will help to keep the buildings cool during our brief hot spells and we hope will deter the use of window-installed air conditioning. The savings shown translate directly into reduced air emissions, as shown in Table 5.

Final Materials and Systems Selection

A close working relationship between consultants was critical to the success of the project. We made design decisions using a circular process wherein data from each consultant were analyzed jointly with data from other consultants to determine the most cost-effective, resource-efficient materials, systems, and assemblies. In selecting systems and materials, the team gave priority to components that would have the greatest environmental benefit for the least amount of extra expense and would provide the greatest long-term cost savings. Each consultant played an important role in the decision process. 

Our goal was to minimize construction costs so that overall costs were still within an acceptable range for comparable affordable housing projects in the same region. Comparable two- to four- unit custom housing projects in the Bay Area typically run from $95 to $105 per ft2 for construction costs alone; the ERB project cost $100 per ft2. The greatest benefits and savings were found in: reducing use of resources with optimal framing systems, increasing the durability of materials such as roofing and siding, improving insulation, and saving operating energy with more efficient systems for space heating (the gas furnace was high- efficiency, variable capacity with a 96.6 AFUE, and was properly sized). Benefits also came from an R-11 water heater blanket, heat traps on the water heater, and low-flow fixtures in the homes. The systems or materials that contribute most to operating efficiency, or that far outlast standard materials, resulted in the greatest savings. Figure 1 illustrates the construction systems and finish materials we selected. 

Construction 

The ERB project was publicly funded, and was therefore advertised for public bids; the Redevelopment Agency was obligated to accept the lowest bid. The contractor who came in lowest may be considered a fair representative of the pool of contractors available to build affordable housing projects. This contractor had no particular interest in the environmental measures, and was skeptical of the feasibility of any methods and materials that were unfamiliar to him. But because we utilized mainstream materials and technologies, most of the environmental measures we specified were successfully implemented despite the contractor's lack of experience with some measures, especially those having to do with efficient framing. 

There were a few cases where the contractor's lack of experience did become a problem. In one case, we specified raised heel trusses in order to increase insulation at the edge of the roof; we also specified that these be made out of certified lumber. When the contractor submitted the shop drawings from the truss fabricator, neither of these specifications was shown. We asked for revised drawings showing both specs, but it turned out that the trusses had already been fabricated without our approval of their design. Faced with the prospect of throwing away the nonconforming trusses and using more wood to fabricate another set, we chose to keep the nonconforming trusses. It turned out that, in our mild climate, the improved energy efficiency from the raised heel trusses would have saved the homeowner just $6 per year. 

In another case, we specified formaldehyde-free particle board for the cabinetry. The cabinetmaker's shop drawings didn't indicate the formaldehyde-free product, but we didn't notice! Again, we were faced with sending something to landfill. As a compromise, the cabinets were sealed on all faces to help prevent off-gassing of VOCs.

The experience we gained during the construction phase of this project is not directly quantifiable, but it is extremely useful as a reference for future projects. The design, the products, and the documentation were applied in the most realistic setting possible. We designed the ERB to be built by a typical production house contractor in the affordable housing market, and this approach was largely successful. We did not have a budget allocation to perform postconstruction testing, although it would be very valuable to do so.

Conclusion

The incorporation of green building principles into current design and construction practice is still in its infancy and requires extra effort to implement. Although few significant problems arose during construction of this project, some considerations are worth noting. Any design that deviates from established conventions demands more vigilance, either through increased site supervision or through increased submission of documents to us to verify compliance with our specifications. The owner must be willing to accept delays in the schedule if nonconforming work is to be rejected. 

Finally, the contractor should be adequately compensated for time spent on tasks that fall outside the scope of standard work. For example, our contractor asked for more money because he had difficulty with the fiber cement siding, which he had never used before. It is heavier than similar wood products and requires different cutting tools, as it is much harder than wood. After the contractor learned some techniques from the manufacturer's representative, things went smoothly, but he requested an additional $6,700 to help offset the extra time he spent. 

Clearly, balancing environmental goals with budget constraints and schedule requires the commitment of the architect, contractor, and owner. However, our findings clearly demonstrate that a thoughtful, interdisciplinary approach can produce competitively priced, environmentally sound, affordable housing and reduce long-term costs to the homeowner or managing agency. We succeeded in the following:

  • reducing expected total operating energy (combined gas and electricity consumption) by approximately 33%; 
  • reducing emissions from operating energy that contribute to global warming by an estimated 23%; 
  • reducing emissions from operating energy that contribute to acid rain by an estimated 16%; 
  • reducing the amount of fuel used for materials production by an estimated 50%; and
  • reducing wood framing by an estimated 19%. 
Finally, the ERB cost no more than conventional affordable housing. Most of these benefits are the result of using durable materials, reducing the amount of material used, and employing energy-efficient systems. These measures translate directly into environmental advantages, such as preventing deforestation, minimizing landfill, and reducing fuel and resource consumption. They also translate into cost savings for occupants and, as we predicted, make affordable housing more affordable. 

Nancy Malone is an architect and researcher with Siegel & Strain Architects in Emeryville, California. She teaches ecological design at the University of California at Berkeley.

Siegel & Strain Architects designed the ERB project for the Emeryville Redevelopment Agency as part of the agency's first-time home buyer program. The project team included Larry Strain, Henry Siegel, and Jaqueline Lange. Additional funding was provided by the Alameda County Source Reduction and Recycling Board and the Alameda County Waste Management Authority. A complete report of the project findings is available from Siegel & Strain Architects. For more information, write to info@siegelstrain.com


 | Back to Contents Page |Home Energy Index |AboutHome Energy |
| Home Energy Home Page| Back Issues of Home Energy |

Home Energy can be reached at: contact@homeenergy.org
Home Energy magazine -- Please read our Copyright Notice