Wastewater Collection Systems On completion of this module you should be able to: Discuss the sources of wastewater Understand the relevant.
Download ReportTranscript Wastewater Collection Systems On completion of this module you should be able to: Discuss the sources of wastewater Understand the relevant.
Wastewater Collection Systems On completion of this module you should be able to: Discuss the sources of wastewater Understand the relevant sections of the legislation relating to sewer collection systems and wastewater Plan and design a wastewater collection system Public Health Engineering 1 Wastewater Collection Systems Some definitions on wastewater systems Sewerage – a system comprising of collection and treatment facilities Sewage – spent water or wastewater Sewers – a collection system of pipes to convey wastewater to a central point of treatment Public Health Engineering 2 Wastewater Collection Systems Sources of wastewater Domestic flows Industrial and trade wastes Urban stormwater Infiltration/inflow Public Health Engineering 3 Wastewater Collection Systems Materials in wastewater Impurities 0.01% Physical form suspended Chemical Biological inorganic organic dissolved living Non-living Public Health Engineering bacteria, fungi, protozoa, algae 4 Wastewater Collection Systems Infiltration/inflow (I/I) Ingress of groundwater or rainwater from pipe defects, joints etc Ground condition also dictates I/I I/I peaks during and after storms and varies with season Extraneous water from illegal connections Qld’s guidelines allow 14 – 28 m3/d.km Public Health Engineering 5 Wastewater Collection Systems Wastewater presents a unique design problem Hydraulic loading (ML/d) Organic loading (kg/m3.d) Concept of equivalent person or population (ep) for design Public Health Engineering 6 Wastewater Collection Systems Relevant legislations Plumbing & Drainage Act 2002, and Standard Plumbing & Drainage Regulation 2003, that relate to licensing and assessing of work Environmental Protection Act 1994 that relates to quantity and quality of flows into the environment Public Health Engineering 7 Wastewater Collection Systems Discharge into sewers Governed by the local authority (trade officers) Industrial and trade effluent are considered on a case by case basis Land discharge is subject to the Environmental Protection Act 1994 Public Health Engineering 8 Wastewater Collection Systems Quality of treated effluent Subject to the Environmental Protection Act 1994 Administered by the Environmental Protection Agency Generally licence conditions of BOD5 < 20 mg/L; NFR < 30 mg/L; DO > 2 mg/L Public Health Engineering 9 Wastewater Collection Systems Types of wastewater systems Separate versus combined systems Gravity and pumped flows Small collection systems using pressure or vacuum Public Health Engineering 10 Wastewater Collection Systems Pressure system Public Health Engineering 11 Wastewater Collection Systems Vacuum system Public Health Engineering 12 Wastewater Collection Systems Sewer installation Sewer alignment Depth of sewer House connection Location of manholes Testing of sewers and house drains Public Health Engineering 13 Wastewater Collection Systems Sewer installation Public Health Engineering 14 Factors that control the depth of sewers Self-cleansing velocity ie. minimum slope Minimum cover to protect the sewer Required depth to drain properties serviced Sufficient depth to avoid other services Public Health Engineering 15 House drain and connection House drain is the property sewer pipe that adjoins council’s sewer Minimum house drain dia. is 100 mm with a min. slope of 1:60 allowing 0.5 invert depth at the head House drains must be vented at the head House connection is made at the lowest point Public Health Engineering 16 Wastewater Collection Systems Sewer installation Typical sewer and housedrain connection Public Health Engineering 17 Testing of sewers Water test - apply a pressure equal to 2 m head at the higher section of the length under test. Loss of water shall not exceed 1 L/m diameter. m length in 30 minutes Air test – apply a pressure of 30 kPa and hold for 3 mins. Time taken for a drop from 25 kPa to 20 kPa shall be not less than 90 secs for pipes less than 225 mm. Public Health Engineering 18 Use of manholes and location Inspection and maintenance Changes in vertical and horizontal alignment Intersections Spaced not greater than 90 m for 375 mm pipes Spaced not more than 150 m for larger pipes Public Health Engineering 19 Wastewater Collection Systems Typical manhole configuration Public Health Engineering 20 Wastewater Collection Systems Design parameters System must drain all points of the catchment Peak wet weather flow capacity Self-cleansing flow velocity gravity flow at minimum slope Pressure mains where necessary Public Health Engineering 21 Wastewater Collection Systems Design for maximum flow (Queensland Planning Guidelines for Water Supply and Sewerage Schemes) Average dry weather flow (ADWF) 275 L/c.d Peak dry weather flow, PDWF = C1 x ADWF Peak wet weather flow, PWWF = C1 .ADWF + I/I Maximum flow at 3/4 pipe depth 150 mm min. dia gravity flow & min. slope dependent on pipe dia. Public Health Engineering 22 Peaking factors for maximum flows Public Health Engineering 23 Proportional velocity and discharge Public Health Engineering 24 Proportional geometry elements sin 2 Ad D 8 Pd D d/D radian 0.015 0.4911 28 5.48648E-05 0.0368 0.1164 0.00036 0.016 0.5073 29 6.04235E-05 0.0380 0.1215 0.00042 0.017 0.5230 30 6.61557E-05 0.0392 0.1265 0.00047 Ad Pd v/V Public Health Engineering 2 q/Q 25 Wastewater Collection Systems About 60 – 80% of the daily water demand appears as spent water There is a diurnal pattern in the collection system Minimum 150 mm pipe with a minimum slope of 1:150 in the collection system Minimum slopes relate to self-cleansing velocity Public Health Engineering 26 Wastewater Collection Systems Owing to a mixture of solids and liquids, sewage flow velocities must be self-cleansing 0.75 PDWF at least once a day to promote selfcleansing flow Generally, self-cleansing velocity is achieved at 0.6 – 0.75 m/s Use of 0.15 kg/m2 shear stress for organic solids Public Health Engineering 27 Wastewater Collection Systems Effects of long detention times Owing to the high O2 demand of biodegradable organic matter, long HRT will deplete dissolved oxygen (DO) Slime growth under waterline will promote anaerobic bacteria and reduce sulfate to sulfides Downstream turbulence will release H2S into the air space Moist film above the waterline and aerobic bacteria will oxidise H2S to H2SO4 Public Health Engineering 28 Effects of long detention times Public Health Engineering 29 Effects of long detention times Public Health Engineering 30 Effects of detention times in rising mains Public Health Engineering 31 Wastewater Collection Systems Finally do we question: Is it still environmentally responsible to use 50 - 80 kg/day of drinking water to transport 1 - 1.5 kg/d of human waste to a treatment plant? Do we have to continue improving the wrong solution or do we have the intelligence for new solutions? Public Health Engineering 32 End of Module 6 Wastewater Collection Systems Public Health Engineering 33