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Newsletter and Technical Publications
<Proceedings of the International Symposium on Efficient Water Use in Urban
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- Innovative Ways of Finding Water for Cities ->
Trace Organics Removal. The regulations intend to control the
concentration of organics of municipal wastewater origin as well as
anthropogenic chemicals that have an impact on health when present in trace
amounts. Thus, the dilution requirements and the organics removal specified in
Project Categories I and IV in Table 4 are to limit average concentration of
unregulated organics in extracted groundwater affected by the groundwater
recharge operation. The concentration of unregulated and unidentified trace
organics is of great concern since other constituents and specific organics are
dealt with through the established maximum contaminant levels and action levels
developed by the California Department of Health Services (CDHS).
Approximately 90 percent by weight of the organics comprising the total
organic carbon (TOC) in treated municipal wastewater are unidentified (State of
California, 1987). One of the health concerns related to the unidentified
organics is that an unknown but small fraction of them are mutagenic. Regulation
of the presence of trace amount of organics in reclaimed water can be
accomplished by dilution using surface water or groundwater of less contaminated
source. When reclaimed water makes up more than 20 percent of the water reaching
any extraction well for potable water supply, treatment to remove organics must
be provided. Because of lack of an ideal measure for trace amount of organics in
reclaimed water as well as in the affected groundwater, total organic carbon
(TOC) was chosen, as a surrogate, to represent the unregulated organics of
concern. Although TOC is not a measure of specific organic compounds, it is
considered at present to be a suitable measure of gross organics content of
reclaimed water as well as groundwater for the purpose of determining organics
removal efficiency in practice. However, there is insufficient basis for the
establishment of a gross organics standard for the recharge water that protects
public health.
Table 4. Estimated log virus removal by wastewater treatment in
different project category1
|
| Project category 2 |
Treatment requirements |
Log virus removal3 |
|
| I |
Primary/secondary/filtration/
Organics removal/disinfection |
7 |
| II |
Primary/secondary/filtration/
Disinfection |
6 |
| III |
Primary/secondary/disinfection |
3 |
| IV |
Primary/secondary/filtration/
Organics removal/disinfection |
6 |
|
1 Adapted from State of
California, 1992 and Hultquist, et al., 1991.
2 Refer to Table 3 for the Project category.
3 Log removal is the negative log of the fraction remaining. Thus,
the fraction remaining is 0.10, it is equivalent to one log removal. Conversely,
99.999% removal or 0.00001 remaining is the equivalent of 5 logs removal. |
Inorganic Chemicals. Inorganic chemicals, with the exception of
nitrogen in its various forms, are adequately under control if all maximum
contaminant limits (MCLs) regulated by CDHS are met. By limiting the
concentration of total nitrogen in the reclaimed water, detrimental health
effects such as methemoglobinemia can be prevented. In those recharge operations
where adequate nitrogen removal cannot be achieved by treatment processes or
passage through an unsaturated zone, the criteria provide the alternative method
such as well head treatment to reduce the total nitrogen concentration to below
the allowable concentration of 10 mg/L as N.
Table 5. Estimate of overall removal of enteric viruses in groundwater
recharge systems due to the combined effects of treatment processes, soil
systems, and retention in groundwater1 2
|
| Project category |
Treatment requirements |
Log virus removal3 |
|
| I |
Primary/secondary/filtration/
Organics removal/disinfection |
17 |
| II |
Primary/secondary/filtration/
Disinfection |
16 |
| III |
Primary/secondary/disinfection |
14 |
| IV |
Primary/secondary/filtration/
organics removal/disinfection |
13 |
|
1Adapted from State of California,
1992 and Hultquist, et al., 1991.
2Infiltration rate of 7.3 m/day was assumed for virus removal with
soils in unsaturated zone. |
SUMMARY AND CONCLUSIONS
To increase the natural supply of groundwater, artificial recharge of
groundwater basins is becoming increasingly important in groundwater management
and particularly in situations where the conjunctive use of surface water and
groundwater resources is considered.
Several constraints limit expanding use of reclaimed municipal wastewater for
groundwater recharge. The lack of specific criteria and guidelines governing the
artificial recharge of groundwater with reclaimed municipal wastewater is
currently hampering the implementation of large-scale groundwater recharge
operations; thus, the establishment of policy and regulations for the planning
and implementing new groundwater recharge projects has been proposed. The
rational basis and other background information for the proposed groundwater
recharge regulations are presented in this paper. These regulations will serve
as a basis with which future groundwater recharge projects are evaluated. Two
case histories are presented for the soil aquifer treatment and non-potable
water reuse with less stringent water quality requirements.
ACKNOWLEDGEMENTS
Information contained in this paper was updated and revised with case
histories. However, portions of the material in this paper were previously
presented at various places which included the NATO Advanced Study Institute,
Acquafredda di Maratea, Italy, May 24-June 5, 1992, and Water Down Under 94,
Adelaide, South Australia, Australia, November 21-25, 1994.
REFERENCES
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operations in California,” Journal American Water Works Assoc. 72, 7, 380-385 |
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| Asano, T. (ed.) (1985). Artificial Recharge of Groundwater,
Butterworth Publishers, Boston, MA. |
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| Bennani, A.C., Lary, J., Nrhira, A., Razouki, L., Bize, J., and
Nivault, N. (1992). “Wastewater treatment of greater Agadir (Morocco): an
original solution for protecting the bay of Agadir by using the dune sands,”
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by infiltration and percolation.” Advanced Wastewater Treatment, Recycling and
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Milan, Italy. |
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| Hultquist, R.H., Sakaji, R.H., Asano, T. (1991). “Proposed
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| National Research Council (1982). Quality Criteria for Water
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overview,” Journal American Water Works Assoc., 72, 7, 375. |
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Water Resources Control Board, Dept. of Water Resources, and Dept. of Health
Services, Sacramento CA. |
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| State of California (1992). Proposed guidelines for groundwater
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