Executive Summary
Wastewater Flows from Single Family Dwellings
Study done for the Michigan
Technical Advisory Council for Onsite Wastewater Treatment
Danielle N. McEachin and Ted L. Loudon
Student Intern and Professor, respectively,
Agricultural Engineering Department
Michigan State University
The purpose of this study was to collect, organize and present what is known about the amount of wastewater that can be expected to flow from dwellings. The goal is to provide designers and regulators with an actual flow based data set from which to develop design flow numbers for sizing systems. The data in this document comes from a variety of sources. Most were found on the Internet, some were found in the library, and others were provided from file data collected by entities in Michigan. The study was restricted to data collected during the years 1980-2000, so that the values determined would be representative of life styles of the present generation. In fact, only two numbers in the data tables are from before 1987.
A group of studies providing metered home water use rates presented in units of gpd per capita from around the country were reviewed and summarized. When averages were weighted based on the number of homes per study, the overall weighted average per capita daily water use was just under 51 gpd (Table 1). The value of this data is limited by the fact that much of the data was total use, including outdoor water use, and had to have a correction factor applied. Numerous sources containing recommended per capita design flows were reviewed. Most recommendations are in the 50-70 gpd/c range (Table 4).
Perhaps the most valuable data is data gathered in Michigan. A study of metered data from 700 homes in southern Michigan showed an average daily use per home of 214.3 gallons. The three bedroom home average was 221.3 gpd (74 gpd/br) and the four bedroom average was 285.5 gpd (71 gpd/br). A study of measured flows from 66 homes in Jackson County showed flows of 56 gpd per bedroom.
Average per person flows, averaged over large numbers of people, appear to be in the 50-55 gpd/c range. Average flows expressed per bedroom, for 3-4 bedroom homes appear to be in the 70-75 gpd/br range. While bedrooms do not generate flow, people do, it is common to design on the basis of number of bedrooms since occupancy varies. For large clusters of homes, designing on the basis of 75 gpd/br would appear to be supported by the data available. For an individual home design, a significant safety or peaking factor must be applied. Many of the references consulted suggest a factor of 2 or even 2.5. Use of a high design flow for individual homes helps to compensate for the state of the art in site evaluation and the occasional high water use occupancy.
The Technical Advisory Council will produce a companion guidance document providing recommendations for applying this data in design recommendations.
Wastewater Flows from Single Family Dwellings
Study done for the Michigan Technical Advisory
Council for Onsite Wastewater Treatment
Danielle N. McEachin and Ted L. Loudon
Student Intern and Professor, respectively,
Agricultural Engineering Department
Michigan State University
Purpose: Rational design of wastewater treatment and dispersal systems is based on the flow that the system must be able to handle. This is usually expressed on a daily flow basis and typically includes a factor of safety which is large for individual home systems and may be reduced as systems are clustered together. The purpose of this study was to collect, organize and present what is known about the amount of wastewater that can be expected to flow from dwellings. The goal is to provide designers and regulators with an actual flow based data set from which to develop design flow numbers for sizing systems.
The data in this document comes from a variety of sources. Most were found on the Internet, some were found in the library, and others were provided from file data collected by entities in Michigan. Every effort was made to ensure that the data reflect indoor water use, which eliminates most consumptive uses and represents the flow that would be expected in the wastewater system. Because consumptive uses are hard to eliminate completely, particularly in arid climates, we restricted our data to the more humid states. One exception is that a study from Denver, CO is included in which a significant effort was made to eliminate outdoor consumptive uses in the design of the study. The numbers in the Colorado study are higher than those from more humid states but we cannot determine exactly what the reason for this might be. Wherever total water use numbers were encountered they were multiplied by a factor of 0.70 to give indoor water use only. These values are indicated by a *. This factor is based on the findings of multiple studies which measured both indoor and outdoor usage. We restricted our selection of data to include only data collected during the years 1980-2000, so that the values determined would be representative of life styles of the present generation. In fact, only two numbers in the data tables are from before 1987, and these are from a study deemed to be sufficiently reliable that we did not wish to exclude it.
The data are divided into four tables. Table 1 contains data from literature and internal sources that were obtained through actual measurement. This means that the numbers were derived from meter readings at occupied residences. These numbers are from studies where multiple homes were metered and the indoor water use was determined. Only some of these studies reported indoor water use only. For those where the reported values were total use, the 0.70 factor was used to obtain indoor water use numbers. See footnotes following the tabulated data for the basis of this factor. The study done by the American Water Works Association Research Foundation metered 1188 homes to obtain their data. The Denver Board of Water Commissioners metered 5649 homes in the city and county of Denver.
The U.S. Department of Housing and Urban Development has conducted many studies on residential water use. In some of their work, they designed studies to obtain as diverse a group of homes as possible by gathering data on each household through issuing a questionnaire to each resident. Their study entitled “Water Saved by Low-flow Fixtures” included water meter data from over 200 homes. They also conducted a study of flow from apartment buildings in which they collected data from 23 buildings. The apartments were noted to be especially leaky and they found unusually high per capita water use. The U.S. Geological Survey published a table with water use values for every state. We selected data from the more humid states and applied the 0.70 factor to obtain indoor water use values. Data were collected from homes where the water supply was from both self-supplied (SS) and public-supplied (PS) sources.
Table 2 contains data that was found through actual measurement but is presented as gallons per day per home. The Michigan study done by Equinox Inc. for use in the design of the Mill Valley Condominium Subdivision metered over 700 homes in Livingston and Oakland counties and determined average water use per dwelling. The first 7 entries in Table 2 represent flows averaged over multiple single family dwellings and would be representative of flows to be expected from a cluster of homes. The average flow equals 159 GPD/home over 640 homes. The Michigan Department of Environmental Quality study involved determination of metered flows from over 500 homes in Oakland County and Highland Township. Both of these Michigan studies are believed to be highly reliable but resulted in per home flows that were higher.
Table 3 contains data found through actual measurement but the values were presented in the original studies in units of gallons per day per bedroom. This data is from a study done by the Michigan Department of Environmental Quality. In this study, 66 homes were metered in Jackson County and the size of home determined so that the data could be presented in terms of a per bedroom water use average.
Table 4 contains data from publications which give representative numbers that are recommended for design of wastewater systems. These are not well referenced so it is unclear whether they originally came from actual use studies or are estimates, possibly including a safety factor, that are simply repeated from another publication. These sources were mostly found on the Internet.
After the tables are a set of statements and observations gleaned from literature. The effect of income level and household size on water use is analyzed. Our reasons for using the 0.70 factor are given, a comparison of self-supplied and public-supplied water use is given. Typical times of peak water use are analyzed as are the effects of metering and water pressure.
Conclusions that can be drawn:
From Table 1, the per capita metered indoor water use data from nationwide studies show an average value of 69 gallons per person per day. The per capita data obtained by applying the 0.70 factor to total water use data found in humid climates shows an average value of 55.2 gallons per day, with a self-supplied average of 50.5, a public-supplied average of 57.7 and a range of 35-86.8. The weighted average per capita water use data for all homes in Table 1 show an overall average use of 50.7 gallons per day, with a self-supplied use of 51.1 and a public-supplied use of 50.47.
The per home metered indoor data in Table 2 shows an average of 214.3, with a 3 bedroom average of 221.3, a 4 bedroom average of 285.5 and a range of 140-327. The first 7 entries in Table 2 represents measured flow data from 640 Michigan homes and shows an average of 159 GPD/home.
The nationwide data sets show somewhat higher per capita water use. Humid region data suggest that average per capita indoor water use averages between 50 and 70 gpd. Total water use per home averages between 160 and 285 GPD with the larger figure for larger homes.
This should be considered a work in progress. We would like to include additional data. If the reader has or is aware of additional data that could be included, we would like to receive it. This summary will be modified if additional data are received or otherwise located.
Table
1. Sources whose data was found by actual measurement, measured in GPD/Person
|
Sponsor |
Source |
Study |
Area
of Study |
Time
Period |
Indoor
use or Total use? |
Type
of Dwelling |
Per
capita daily water use |
|
AWWA
Research Foundation |
Residential
End Uses of Water [Project#241] |
12
study sites, across the U.S. |
Copyright1999
|
Indoor |
1,188
Single-family homes |
69.3,
Including Leakage |
|
|
Denver
Board of Water Commissioners |
Litke
and Kauffman, “Analysis of Residential Use of Water in the Denver
Metropolitan Area, CO, 1980-87 |
16
groups of homes in the city and county of Denver |
Data
From 1980-87 |
Indoor |
5,649
Single-family homes |
64-119
Mean = 85.6 |
|
|
Rhode
Island Governor’s Office of Housing, Energy, and Intergovernmental Relations |
M.
A. Horn, P.A. Craft & Lisa Bratton, “Estimation of Water Withdrawal and
Distribution, Water Use, and Wastewater Collection and Return Flow in
Cumberland, Rhode Island, 1988 |
Cumberland,
Rhode Island |
Data
From 1988 |
Indoor
and Total |
Single-family
homes |
70
SS (Total) 77
PS (Indoor)
& 90 PS (Total) |
|
|
U.S.
Department of Housing and Urban Development, Office of Policy Development and
Research |
Brown
and Caldwell, “Residential Water Conservation Projects, Summary Report”, 1984 |
Water
Saved by Low-flow Fixtures |
Nationwide |
Data
from 1983 |
Indoor
|
200
Single-family homes |
66.2 |
|
Retrofit
of Apartment Buildings |
Washington, D. C. |
Data
From 1981 |
Indoor |
23
Apartment buildings |
100**
Including Leakage |
||
Table
1. (cont.)
Sponsor |
Source |
Study |
Area
of Study |
Time
Period |
Indoor
use or Total use? |
Type
of Dwelling |
Per
capita daily water use |
|
United
States Geological Survey |
http://water.usgs.gov//watuse/tables/dotab.st.html |
Table12.
Domestic Freshwater Use by State
(States chosen with humidity similar to that of Michigan) |
Alabama |
Data
From 1990 |
Indoor |
Single-family
homes |
52.5*
SS 70*
PS |
|
Arkansas |
Data
From 1990 |
Indoor |
Single-family
homes |
61.6*
SS 74.2*
PS |
|||
|
Connecticut |
Data
From 1990 |
Indoor |
Single-family
homes |
52.5*
SS 49*
PS |
|||
|
Delaware |
Data
From 1990 |
Indoor |
Single-family
homes |
55.3*
SS 54.6*
PS |
|||
|
Georgia |
Data
From 1990 |
Indoor |
Single-family
homes |
52.5*
SS 80.5*
PS |
|||
|
Illinois |
Data
From 1990 |
Indoor |
Single-family
homes |
58.8*
SS 63*
PS |
|||
|
Indiana |
Data
From 1990 |
Indoor |
Single-family
homes |
53.2*
SS 53.2*
PS |
|||
|
Kentucky |
Data
From 1990 |
Indoor |
Single-family
homes |
35*
SS 49*
PS |
|||
|
Louisiana |
Data
From 1990 |
Indoor |
Single-family
homes |
58.1*
SS 86.8*
PS |
|||
|
Maine |
Data
From 1990 |
Indoor |
Single-family
homes |
63*
SS 40.6*
PS |
|||
|
Maryland |
Data
From 1990 |
Indoor |
Single-family
homes |
58.1*
SS 73.5*
PS |
|||
|
Massachusetts |
Data
From 1990 |
Indoor |
Single-family
homes |
50.4*
SS 46.2*
PS |
|||
|
Michigan |
Data
From 1990 |
Indoor |
Single-family
homes |
51.1*
SS 53.9*
PS |
|||
|
Mississippi |
Data
From 1990 |
Indoor |
Single-family
homes |
35*
SS 86.1*
PS |
Table
1. (cont.)
|
Sponsor |
Source |
Study |
Area
of Study |
Time
Period |
Indoor
use or Total use? |
Type
of Dwelling |
Per
capita daily water use |
|
United
States Geological Survey |
http://water.usgs.gov//watuse/tables/dotab.st.html |
Table12.
Domestic Freshwater Use by State
(States chosen with humidity similar to that of Michigan) (cont.) |
Missouri |
Data
From 1990 |
Indoor |
Single-family
homes |
42*
SS 59.5*
PS |
|
New
Hampshire |
Data
From 1990 |
Indoor |
Single-family
homes |
45.5*
SS 49.7*
PS |
|||
|
New
Jersey |
Data
From 1990 |
Indoor |
Single-family
homes |
52.5*
SS 52.5*
PS |
|||
|
New
York |
Data
From 1990 |
Indoor |
Single-family
homes |
40.6*
SS 83.3*
PS |
|||
|
North
Carolina |
Data
From 1990 |
Indoor |
Single-family
homes |
38.5*
SS 39.9*
PS |
|||
|
Ohio |
Data
From 1990 |
Indoor |
Single-family
homes |
52.5*
SS 37.5*
PS |
|||
|
Pennsylvania |
Data
From 1990 |
Indoor |
Single-family
homes |
36.4*
SS 43.4*
PS |
|||
|
Rhode
Island |
Data
From 1990 |
Indoor |
Single-family
homes |
49*
SS 46.9*
PS |
|||
|
South
Carolina |
Data
From 1990 |
Indoor |
Single-family
homes |
52.5*
SS 53.2*
PS |
|||
|
Tennessee |
Data
From 1990 |
Indoor |
Single-family
homes |
45.5*
SS 59.5*
PS |
|||
|
Vermont |
Data
From 1990 |
Indoor |
Single-family
homes |
50.4*
SS 56*
PS |
|||
|
Virginia |
Data
From 1990 |
Indoor |
Single-family
homes |
52.5*
SS 52.5*
PS |
|||
|
West
Virginia |
Data
From 1990 |
Indoor |
Single-family
homes |
56*
SS 51.8*
PS |
|||
|
Wisconsin |
Data
From 1990 |
Indoor |
Single-family
homes |
42.7*
SS 36.4*
PS |
Table
1. (cont.)
|
Sponsor |
Source |
Study |
Area of Study |
Time
Period |
Indoor
use or Total use? |
Type
of Dwelling |
Per
capita daily water use |
|
United
States Geological Survey |
Estimated
Water Use for Ohio, 1995, by Hydrologic Cataloging Unit |
Ohio |
Data
From 1995 |
Indoor |
Single-family
homes |
70
SS* 50 |