Annex 1 mandatory
General requirements for the composition and
water properties of water bodies
in control points and places of drinking, household and
recreational water use
№ |
Indicators |
Categories |
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For drinking and |
For recreational |
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1 |
2 |
3 |
4 |
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1 |
weighted |
At |
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0.25 mg/dm3 |
0.75 mg/dm3 |
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For suspension |
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2 |
floating |
On the |
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3 |
Coloring |
Should not appear in a column |
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20 cm |
10 cm |
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4 |
Smells |
Water should not acquire odors with an intensity of more than 2 |
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directly |
directly |
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5 |
Temperature |
Summer |
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6 |
Hydrogen |
Should not go beyond 6.5-8.5 |
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7 |
Mineralization |
Not more than 1000 mg/dm3, including: chlorides - 350; sulfates - 500 mg/dm3 |
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8 |
Dissolved |
Should not be less than 4 mg/dm3 in any period |
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9 |
Biochemical |
Should not exceed at a temperature of 20 ° C |
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2 mg 02/dm3 |
4 mg 02/dm3 |
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10 |
Chemical |
Should not exceed: |
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15 mg O2/dm3 |
30 mg 02/dm3 |
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11 |
Chemical |
Not |
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12 |
pathogens |
Water |
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13 |
Viable |
Should not be contained in 25 liters of water |
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14 |
thermotolerant |
Not more than 100CFU/100ml** |
Not more than 100 cfu/100ml |
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15 |
Are common |
No more |
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1000 cfu/100 ml** |
500 cfu/100 ml |
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16 |
coliphages |
No more |
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10PFU/100ml** |
10PFU/100ml |
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17 |
Total |
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Notes.
* The content of suspended solids in water of non-natural
origin (flakes of metal hydroxides formed during the treatment of waste
water, particles of asbestos, fiberglass, basalt, nylon, lavsan, etc.) do not
allowed.
** For centralized water supply; at
decentralized drinking water supply, water is subject to disinfection.
*** In case of exceeding the specified levels of radioactive
contamination of controlled water is carried out additional control
radionuclide contamination in accordance with the current standards of radiation
security;
AI-
specific activity of the 1st radionuclide in water;
YBi-
the corresponding intervention level for the 1st radionuclide (Appendix P-2 NRB-99).
Water supply and sewerage security zone
City water supply and sewerage facilities are objects of particular importance in the life support of the city. For network facilities of water supply and sewerage on street driveways, etc.
open territories, as well as subscribers located in the territories, the following security zone is established:
For network facilities of water supply and sewerage on street passages and other open areas, as well as subscribers located on the territories, the following security zone is established:
- for networks with a diameter of less than 600 mm - a 10-meter zone, 5 m each on both sides of the outer wall of the pipelines or from the protruding parts of the building, structure;
- for lines with a diameter of more than 1000 mm - a 20-50-meter zone on both sides of the pipeline wall or from the protruding parts of the building, structure, depending on the soil and the purpose of the pipeline. The water supply must run outside the facility at a distance of at least 5 m from the fence.
1 Calculation of concentrations of normatively permissible wastewater VAT discharge.
Concentration calculation
VAT and the choice of technological scheme
carried out taking into account the state
wastewater receiver - reservoir. In this
course project considers two
possible drainage schemes
industrial enterprises:
-
wastewater
industrial plants are cleaned
and discharged into a water body
domestic wastewater is directed
into the city sewerage networks and cleaned
together with city drains; -
if the quality
industrial wastewater matches
with the quality of domestic wastewater (according to weighted
substances, BOD, nitrogen and others), in this
case, the drains are combined and jointly
sent to treatment facilities
industrial enterprises, after which they are dumped
into the reservoir.
Average concentrations
wastewater for treatment, and
necessary data on the water body
are in the task.
-
Permissible
concentration weighted
substances v
wastewater discharged into the water
an object:
, mg/l
(3.2)
where
R
– allowable increase in weighted
substances in a water body, after discharge
waste water is 0.25 or 0.75 mg/l
depending on the category of the reservoir;
b
– content of suspended solids in water
water body before wastewater discharge
(background concentration by weighted
substances), mg/l;
γ
– coefficient
mixing, determined by ;
q–
wastewater consumption, m3/day;
Q–
river flow at 95% supply,
m3/day
-
Permissible
concentration on
BODfull
in wastewater discharged into water
an object:
, mg/l
(3.3)
where k–
average value of the coefficient
non-conservative organic
substances that cause BODfull
background and wastewater, 1/day; for BODfull
should be taken according to Appendix A;
LMPC–
maximum allowable
BOD concentrationfull
in the water of a water body, mg/l;
Lcm– BODfull,
caused by organic matter
atmospheric
precipitation from the catchment area on the site
path in front of the checkpoint length
0.5 daily run, mg/l:
- for flat
rivers flowing through the territory, soil
which is not too rich in organic
substances - 1.7 - 2 mg / l;
- for swamp rivers
supply or flowing through the territory
with which an increased amount is washed off
organic substances - 2.3 -2.5 mg / l;
- if the distance
from wastewater outlet to control
alignment less than 0.5 daily run -
is taken equal to zero.
Lf– background
BOD concentrationfull
in the water of a water body, mg/l (by order);
t– time
runaway from the place of wastewater discharge
to the settlement point, days;
n– multiplicity
total dilution in the watercourse, determined by
on .
-
Permissible
concentration on
petroleum products, surfactants, nitrogen and others
substances
in wastewater discharged into water
object is determined by the formula:
, mg/l (3.4)
where
— non-conservative coefficient
given substance, showing the speed
oxygen consumption, depending on
nature of organic substances, 1/day;
accepted depending on the substance
(Appendix A).
WITHMPC–
maximum allowable
the concentration of a given substance in water
water body, mg/l;
WITHf– background
the concentration of a given substance in water
water body, mg/l (by order);
-
Permissible
concentration on
various pollution v
wastewater, excluding coefficients
nonconservative, determined by
formula:
(3.5)
According to the results
calculation it is necessary to fill in the table,
an example is table 3.1, where Cin
– average concentration of pollution
after the averaging in the incoming
wastewater treatment, andexit
- estimated maximum allowable
concentration at their outlet after purification.
Table 3.1 - Example
calculation of allowable concentrations
pollutants
Indicator |
WITHin |
WITHf |
WITHMPC |
WITHVAT |
WITHexit |
weighted |
300 |
10 |
10,25 |
45 |
15* |
Oil products |
50 |
0,01 |
0,05 |
11,5 |
0,05** |
Copper |
4,5 |
0,002 |
0,001 |
-108 |
0,001*** |
Iron |
28 |
0,2 |
0,5 |
0,8 |
0,8**** |
* By weighted
substances of concentration CVAT
turned out to be much more than
WITHMPC
and Cf
, so we can take the calculated
concentration Cexit
at the exit
from VOC equal to 15 mg/l, which corresponds to
the level of technological
process.
** For oil products
WITHVAT
also far exceeds CMPC
and Cf
, so Cexit
can be taken equal toMPC
or in
compliance with the effects of the adopted
technologies.
*** By copper ions
background concentration Cf
already exceeds
WITHMPC,
those. the reservoir is polluted, in this case on
output accept Cexit=CMPC.
**** By iron ions
take the output concentration equal to
VAT concentration: Cexit=CVAT.
Desired Effects
cleaning for any kind of pollution
for VOC are determined by the formula:
(3.5)
Desired effect
cleaning for any kind of pollution
for a separate building is considered
similarly, taking into account the concentrations on
entering and exiting the building
(indicative effect values according to
various substances in tables B.4. and
B.5., Appendix B).