Newsletter and Technical Publications
<International Source Book On Environmentally Sound Technologies
for Wastewater and Stormwater Management>
2. Wastewater and stormwater characteristics
(Topic a)
Household wastewater derives from a number of sources (Figure
2.1). Wastewater from the toilet is termed 'blackwater'. It has a high content
of solids and contributes a significant amount of nutrients (nitrogen, N and
phosphorus, P). Blackwater can be further separated into faecal materials and
urine. Each person on average excretes about 4 kg N and 0.4 kg P in urine, and
0.55 kg N and 0.18 kg P in faeces per year. In Sweden it has been estimated
that the nutrient value of urine from the total population is equivalent to
15 - 20 % of chemical fertiliser use in 1993 (Esrey et al., 1998). Table 2.1
shows characteristics of human excreta and a comparison with nutrient contents
of plant matter to indicate its value as a soil conditioner and fertiliser.

Figure 2.1: Sources of household wastewater, showing wastewater from toilet,
kitchen, bathroom, laundry and others
Greywater consists of water from washing of clothes, from
bathing/showering and from the kitchen. The latter may have a high content of
solids and grease, and depending on its intended reuse/treatment or disposal can
be combined with toilet wastes and form the blackwater. Both greywater and
blackwater may contain human pathogens, though concentrations are generally
higher in blackwater.
The volume of wastewater and concentration of pollutants
produced depend on the method of anal cleaning, volume of water used and water
conservation measures. Dry anal cleaning results in higher solids and fibre
content. The use of dry pit latrines and the practice of water conservation
produce low volume and high concentration wastewater, while use of flushing
toilets results in higher wastewater volumes and lower concentrations. The
characteristics of wastewater in the Regions are described in the Regional
Overviews under Topic a.
|
Table 2.1: Human excreta - per capita quantities
and their resource value (Strauss, 1985) |
|
|
Faeces |
Urine |
Excreta |
|
| Quantity and consistency |
|
|
|
| Gram/capita/day (wet) |
250 |
1,200 |
1,450 |
| Gram/capita/day (dry) |
50 |
60 |
110 |
| Chemical composition (% of dry solids) |
|
|
|
| Organic matter |
92 |
75 |
83 |
| Carbon C |
48 |
13 |
29 |
| Nitrogen N |
4-7 |
14-18 |
9-12 |
| Phosphorus (as P2O5) |
4 |
3.7 |
3.8 |
| Potassium (as K2O) |
1.6 |
3.7 |
2.7 |
|
| Comparison with other wastes (% of dry solids) |
N |
P2O5 |
K2O |
|
| Human excreta |
9-12 |
3.8 |
2.7 |
| Plant matter |
1-11 |
0.5-2.8 |
1.1-11 |
| Pig manure |
4-6 |
3-4 |
2.5-3 |
| Cow manure |
2.5 |
1.8 |
1.4 |
|
The flow of wastewater is generally variable with peak flows
coinciding with high household activities in the morning and evening, while in
the night minimal flow occurs. Pollutant loads vary in a similar manner.
Stormwater in a community settlement is produced from house
roofs, paved areas and from roads during rainfall events. In addition stormwater
is produced from the catchment of a stream or river upstream of the community
settlement. The amount of stormwater is therefore related to the amount of
rainfall precipitation, and the nature of surfaces, with impervious surfaces
producing more run-off. During a storm event the peakflow is higher and duration
shorter with an impervious surface, while the peakflow is lower and duration
longer with a vegetated surface (Figure 2.2).
Stormwater run-off may contain as much solids as household
wastewater depending on the debris and pollutants in the path of the stormwater
run-off, although in general the pollutant load of stormwater is lower than that
of wastewater. Table 2.2 shows a comparison of urban stormwater sources and
untreated sewage in North America.
| Table 2.2: Comparison of the characteristics of
stormwater sources and untreated sewage (Novotny and Olem, 1994; Novotny,
1995) |
| Type of wastewater |
BOD5
(mg/L)
|
Suspended solids
(mg/L)
|
Total N
(mg/L)
|
Total P
(mg/L)
|
Total Coliforms
(MPN/100mL)
|
| Urban stormwater |
10-250 (30)
|
3-11,000 (650)
|
3-10
|
0.2-1.7 (0.6)
|
103-108
|
| Construction site run-off |
NA
|
10,000-40,000
|
NA
|
NA
|
NA
|
| Combined sewer overflows |
60-200
|
100-1,100
|
3-24
|
1-11
|
105-107
|
| Light industrial area |
8-12
|
45-375
|
0.2-1.1
|
NA
|
10
|
| Roof run-off |
3-8
|
12-216
|
0.5-4
|
NA
|
102
|
| Untreated sewage |
(160)
|
(235)
|
(35)
|
(10)
|
107-109
|
| Wastewater treatment plant effluent (secondary treatment) |
(20)
|
(20)
|
(30)
|
(10)
|
104-106
|
| Figures in brackets = mean values; NA = not available; MPN
= most probable number |

Figure 2.2: Rainfall runoff relationship showing two different surfaces
(impervious and natural) (lager image)
|