Our expert septic system design engineers have extensive experience in designing onsite septic systems and preparing septic permit drawings for municipal approval in Ontario, where properties in rural areas rely upon onsite septic systems for their sewage disposal.
Our experienced and competent professional engineers licensed in Ontario, specializing in designing septic systems, design a variety of advanced, innovative, predictable, permanent, robust, cost-effective, compact, low energy, low maintenance, visually subtle, and efficient onsite septic systems for off-sewer developments in rural Ontario.
Our stamped engineering septic system designs and the septic permit drawings meet the Ontario Building Code and the Ministry of Environment requirements and offer the most affordable, long-lasting site-specific septic system design. Inappropriate septic system design, bad construction practices, or poor maintenance can all lead to failure of septic systems.
The two main factors that dictate the septic system design are the maximum amount of sewage the building could produce daily (sewage/septic load), and soil/site conditions. Geotechnical investigation, including proper soil testing, ensures the septic system design meets the site-specific requirements. Enlisting the help of a qualified and registered professional engineering firm is a key element to the successful septic system design. Our licensed professional engineers design onsite septic systems that will work best for the property based on the specific site-specific characteristics, including
The Municipal Building Department or Health Unit, and if applicable, a Conservation Authority, examines septic system design and approves septic permit applications, issues septic permits for the construction of septic systems, and does inspections for septic systems regulated under Part 8 of the Ontario Building Code. The Municipal Officials regulate the design, construction, and approval of septic systems with a design capacity of less than 10,000 litres per day on one lot. The rate at which the wastewater will be absorbed into the soil is called a "T" time. "T" time is equal to the number of minutes it takes for the water level to drop per cm in a water-filled hole in the receiving soil. In sandy soil, a typical T time is less than 10 (meaning it took less than 10 minutes for the water level to drop 1 cm in the water-filled hole). But in sandy loam soil, the T time could be 20 or more because the smaller soil particles are slowing the rate of absorption. The worst soil, though, is clay, where the T time is typically well over 50 because clay particles are so fine and tightly packed. Once the maximum amount of wastewater that the building could produce daily (Daily Sewage Flow) and the "T" time are identified, we can design the septic system accordingly. Each type of septic system then has a different equation to be used to design the septic system.
Ontario Building Code Design Standards for Designing a Septic System
General Requirements for Septic System Design
Site Evaluation
(1) A site evaluation shall be conducted on every site where a new septic system is to be designed.
(2) The percolation time for the septic design shall be determined by,
(3) Where the soil percolation time is determined by a percolation test, there shall be a minimum of 3 locations selected, suitably spaced to accurately evaluate the leaching bed area, with the highest percolation time of the tests being used for the septic design.
Minimum Clearances Required for Septic System Design
Horizontal separation distances to wells, streams, property lines, and other features are regulated and are designed to minimize adverse environmental effects.
For Septic Treatment Units
For Septic Distribution Piping
Design of an on-site private septic system has two basic parts: a septic tank that receives the untreated sewage and in which solids settle out, and a leaching bed (tile bed) through which the liquid waste portion of the sewage is dispersed into the soil. The main function of the septic tank is to allow solids to settle and to let clear effluent flow to the septic tile bed. Biological reactions within the septic tank will break down some solids into liquids and gases, but the retained solids will eventually accumulate in the septic tank. Only clear liquid waste should be discharged from the septic tank to the septic tile bed. This liquid waste will then undergo further biological breakdown and treatment. To ensure the efficient operation of the entire septic system, it is important that the sludge, scum, and solids that can accumulate in the septic tank do not enter the leaching bed (tile bed). The septic tank should be inspected by a licensed professional at least once every two years and the septic tank pumped out when necessary. The design of an on-site septic system for new construction is always a challenge because of the very limited area available for the septic system due to the required minimum setbacks from the drinking water well, property lines, and the proposed structures. There are a number of different septic designs, configurations, and combinations associated with the choice of the septic tank, septic field, and overall septic system design.
Our licensed Professional engineers make sure that the septic system is properly designed to handle. Advanced septic treatment systems are very effective in treating septic sewage. With cleaner effluent leaving these advanced septic treatment systems, the size of the soil component (leaching bed) that is needed to complete the septic treatment is smaller than for those using septic tanks only. Advanced septic treatment systems could use one of two small leaching bed systems that are currently approved or authorized in Ontario: a shallow buried trench and an area bed. Advanced septic treatment systems can be used with a variety of above-ground and in-ground distribution options and offer several unique final distribution options. Advanced control panels, auto-dialer alarm systems, and remote monitoring services make the operation of the septic system simple and efficient.
Design of advanced septic treatment systems is required when:
Septic tanks do not use oxygen as part of the septic treatment. This is known as an anaerobic treatment. Advanced septic treatment units use oxygen to enhance septic treatment. This is known as an aerobic treatment. Aerobic septic treatment units treat septic sewage by adding air. Aerobic septic treatment units inject and circulate air so that oxygen-dependent bacteria can thrive. The bacteria break down organic matter, reduce pathogens, and transform nutrients (e.g., ammonia to nitrate). Aerobic septic treatment units often have a pre-treatment tank where the scum and solids are separated and stored before the effluent is passed to an aeration chamber. At the aeration chamber, the air is added to the effluent, which allows the bacteria to feed on the contaminants, thereby producing cleaner effluent. Generally, Aerobic septic treatment units are classified based on the status of bacteria in the wastewater within the treatment unit. Bacteria are either suspended in the liquid or attached to the media. Aerobic septic treatment units require air compressors and in most cases, pumps and use an area bed or shallow buried trench for final distribution and treatment.
In suspended growth septic treatment units, wastewater flows from the pre-treatment tank into the aeration chamber, where an air compressor and air diffuser supply oxygen and mix the liquid waste. The air keeps the bacteria “suspended” or floating in the liquid waste. It does not attach to any surface. The oxygen supports the growth of the bacteria and other microorganisms that break down the wastewater and solids. The effluent then flows into a shallow buried septic trench or an area bed. Suspended Growth Treatment Units presently used in Ontario include Whitewater, Aquarobic, Aqua Safe and Aqua Air, Biocycle, Clearstream, Norweco, and WSB.
The revolutionary Norweco Hydro-Kinetic septic system employs innovative Hydro-Kinetic filtration technology to produce the cleanest, most consistent effluent quality available. Developed to serve homes and small businesses outside of city sewers, the Norweco Hydro-Kinetic septic system uses extended aeration and attached growth processes to treat wastewater and features innovative nitrification-denitrification technology. The Hydro-Kinetic septic system is designed to meet or exceed stringent local regulations for septic design in areas where excessive nitrogen is a concern. In lakefront areas, nitrogen is a threat to aquatic life, wildlife, and recreational use. Nitrogen is reduced to less than 10 mg/L by the Norweco Hydro-Kinetic septic system, which is lower than the USEPA’s standard for drinking water. This demonstrates the Norweco Hydro-Kinetic septic system’s superb treatment performance.
Norweco Hydro-Kinetic septic system is compact, performant, and affordable to operate and maintain septic treatment solution providing a long-life expectancy and peace of mind. During its successful completion of both NSF/ANSI Standard 40 and 245 tests, the Norweco Hydro-Kinetic Flow Equalized Up Flow (FEU) system, became the only NSF/ANSI Standard 40 and 245 certified residential septic treatment system to pass two consecutive back-to-back tests without performing routine maintenance for a full 12 months and achieved unmatched effluent results of 2 mg/L CBOD (Carbonaceous Biochemical Oxygen Demand), 2 mg/L TSS (Total Suspended Solids) and 7.9 mg/L TN (Total Nitrogen).
Norweco Hydro Kinetic offers
In attached growth septic treatment units, wastewater from the pre-treatment septic tank flows into an aeration tank that contains pieces of plastic or other synthetic material. Attached growth septic treatment units rely on oxygen-dependent bacteria to break down wastewater and solids similar to suspended growth units. The difference is that attached growth septic treatment units let the bacteria attach, grow, and thrive on synthetic material (e.g., plastic shavings, balls, etc.). An air diffuser provides continuous aeration around the synthetic material to enhance bacterial activity and septic treatment. Some attached growth septic treatment units require an air compressor. The effluent then flows to a shallow buried trench or an area bed. The attached growth septic treatment units presently used in Ontario include Bionest, Bio-Microbics — FAST, Nayadic, and Rotordisk.
Filtration septic treatment units utilize trickling filter technology. Wastewater flows to a pre-treatment tank. The wastewater then flows from the pre-treatment tank into the septic filtration unit, which is filled with materials such as peat moss, sand, or a synthetic medium. As the wastewater trickles or percolates down through the septic filtration unit, a bacterial slime grows and thrives. Typically, trapped air fills the voids in the medium and encourages aerobic conditions where bacteria break down the septic waste as it slowly moves through the filter medium. The effluent then flows to a shallow buried trench or an area bed for final distribution and septic treatment in the soil.
Septic filter beds can be made verifiable by installing underdrains, which would keep the sand free-draining and aerobic. High-quality effluent from septic filter beds, peat, or foam filters can then be placed in a “shallow area bed” for low-risk disposal. The shallow area septic bed technology, used in Ontario since 1994, affords a two-stage filtration septic treatment train. The “roughing filter” of sand, peat, or foam removes ~95% of the organics and >99% of E. coli. The second “polishing filter” is the fine sand layer in the shallow area septic bed that removes the remaining E. coli for a total of 99.9993% removal before entering the natural environment. The soil and the groundwater are both protected, and health risks are minimized.
The double safeguard of septic filtration treatment followed by filtration disposal is similar to the preferred “multiple-barrier” approach to drinking water safety. The multi-barrier approach or defense in depth has been an approach that has long been used by the drinking water industry to provide safe and secure supplies of drinking water. The single bio-mat barrier in soil-based septic systems does not provide the safety of the multiple-barrier approach.
Synthetic Media Septic Filter Treatment Units presently used in Ontario include Waterloo Biofilter and Orenco AdvanTex. The Waterloo Biofilter is an aerobic trickling filter that uses an absorbent synthetic filter material developed by researchers at the University of Waterloo and first installed in Ontario in 1991. Septic tank effluent is applied intermittently to the top of the filter media. The synthetic media support microbiological growth, and these microorganisms are responsible for the aerobic breakdown of the wastewater. The core of the Waterloo Biofilter septic system is a synthetic, absorbent filter medium that is configured as a free-draining, attached-growth, biological trickling filter to treat sewage and process wastewater.
This patented, engineered Waterloo Biofilter medium is consistent in its physical properties and has been optimized to:
The absorbent Waterloo Biofilter filter medium creates an ideal environment for microbial attachment. Beneficial bacteria colonize the interior surfaces of the absorbent Waterloo Biofilter filter medium where they are protected from predators, desiccation, and freezing. These microbes degrade and oxidize organic pollutants, coliform bacteria, ammonium, and other contaminants as the wastewater is retained in the absorbent Waterloo Biofilter filter medium by capillarity. Air passively circulates throughout the absorbent Waterloo Biofilter filter medium, providing an aerobic septic treatment environment without the need for forced aeration. This attached growth process (also referred to as a fixed film process, intermittent filter, packed bed media filter, or percolating filter) outperforms activated sludge or suspended growth (suspended sludge) processes with lower energy requirements, fewer moving parts, simpler operation, less maintenance, and a better ability to handle shock loads of chemical addition or hydraulic overloads.
Waterloo Biofilter is proven in frigid -50°C temperatures, treating cold sewage with influent temperatures as low as 3°C. Compared to other media-based trickling filters, the Waterloo Biofilter does not slough off microbes in the form of aerobic sludge, maintains high septic treatment levels even in very cold climates, has longer retention times, and can accept much higher organic and hydraulic loads without plugging. Waterloo Biofilters consistently provide tertiary, sand filter quality effluent (< 10 mg/L cBOD & TSS) that is clear and odourless. Highly treated effluent is easily and safely dispersed back into the soil via small, shallow disposal beds or trenches, or can be reused onsite for purposes such as irrigation, truck washing, or toilet flushing.
Peat Filter Septic Treatment Units presently used in Ontario include Premier Tech Ecoflo and Puraflo. The Ecoflo Biofilter is a trickling filter that uses peat to treat wastewater. The Ecoflo Biofilter consists of an open-bottomed fibreglass shell full of harvested peat. Effluent from a septic tank is delivered by pump or by gravity (depending on relative elevations) to the top of the peat media. The wastewater percolates downward through the peat and then through the infiltration zone, which consists of 200 mm of clear stone & 300 mm of clean sand. After moving through this infiltrative zone, wastewater infiltrates into the native soils. The peat acts both as a place for aerobic bacteria to anchor and treat wastewater as it passes through the filter and as a physical filter. Some limited chemical reactions are also achieved. Aeration of the unit is passive, i.e., there are no blowers or fans to enhance air movement through the peat. The peat must be replaced approximately every 8 years.
Sand Filter Treatment Units presently used in Ontario include Orenco.
The minimum design capacity of a residential septic system is 1,600 L/ day. The septic tank is designed to store the wastewater for two days or more before discharging it to the disposal field or to further treatment. If you have a larger home, or if your home has fixtures that use additional water (such as hot tubs), or if you have a multi-residential building, you will need a septic system that is designed to receive more wastewater, or problems can result.
Effluent Filter for Septic System
Septic tank effluent filters are designed to intercept solids that might otherwise escape from the septic tank and clog the septic bed. An effluent filter installed at the outlet of the septic tank dramatically improves the quality of effluent being discharged to the leaching bed, effectively extending its life. The addition of an effluent filter to all systems is strongly recommended. Sewage enters the first chamber of the septic tank through an inlet baffle or tee. Most of the larger particles settle out, and the effluent enters the second chamber. The second chamber (much smaller than the first) further enhances the settling process. If flows are heavy at times, solids can pass through both compartments and enter the leaching bed. The effluent filter minimizes this. Effluent filters in accordance with NSF/ANSI 46, “Evaluation of Components and Devices Used in Septic Treatment Systems,” must now be sized to filter out particles of 1.6 mm [1/16”] and have a minimum area of 550cm² (85 in²), in addition to being installed in accordance with the manufacturer's requirements.
Effluent filters assist in the settling of both large and small particles, and help slow down the flow to further enhance particle settling before damage is done to the leaching bed. Effluent filters improve effluent quality and extend leaching bed life. Installation and maintenance of effluent filters are relatively simple and can be equipped with an alarm to warn that the filter needs cleaning.
Septic Pumps and Siphons
Where the total length of the distribution pipe required is 150 m or more, the septic system shall have at least one septic pump or a siphon contained in a dosing tank that may be a separate compartment within the septic tank structure, for distribution of the effluent.· Alternating siphons shall not be installed in a septic system.· Where 2 or more septic pumps are employed within a dosing tank, the septic pumps shall be designed such that the septic pump's alternate dosing and dosing shall continue in the event that one septic pump fails.· Where a septic pump or siphon is required, the septic pump or siphon shall be designed to discharge a dose of at least 75% of the internal volume of the distribution pipe within a time period not exceeding fifteen minutes. Septic systems dispose of sewage and rely on the soil to absorb and disperse wastewater. The Septic Systems are designed to keep effluent underground and to filter wastewater before it reaches groundwater, streams, or lakes. “Sewage” can include domestic wastewater from toilets, showers, bathtubs, and kitchen and laundry wastes.
There are various types of Septic Permit designs depending on site conditions. Our licensed professional engineers evaluate the site conditions when selecting or designing a septic system. Septic Systems are designed by our licensed professional engineers to ensure that effluent is properly treated in the septic field and natural soil, and that harmful bacteria are removed before it reaches the water table beneath the septic field. Drawing on our experience, our licensed engineers can supply information on the procedure for selecting/designing an on-site septic system.
Septic Area Bed
A septic area bed is an infiltrative zone similar to that of a septic filter bed. The septic area beds have very small footprints and are only allowed in conjunction with alternative septic treatment units providing tertiary-level septic treatment. Septic area bed generally consists of a clean stone layer 250 mm thick underlain by a sand layer 200 to 300 mm thick. The sand layer may vary in depth and size depending on the septic treatment unit being used.
Some advanced septic treatment systems have open bottoms that sit right on top of the stone layer while others have a septic distribution network of PVC laterals placed in the stone layer for effluent distribution. Typically, effluent from the advanced septic treatment system will flow by gravity to an area bed. However, some septic systems have a pump as an integral part of the septic system, and sometimes a pump is added to overcome an elevation difference between the advanced septic treatment system and the area bed.
The header and distribution pipes within area beds must be designed and built in such a way that they can be detected by one of the following:· Magnetic means.· 14-gauge TW solid copper light-coloured plastic-coated tracer wire.· Any other type of subsurface detection.· Landscape design should not interfere with the natural functioning of a septic system. A balanced combination of oxygen and organisms will maintain the healthy soils necessary for the septic system.
Shallow-Buried Trench
A shallow-buried trench is an alternative to a conventional leaching bed. Shallow-buried trenches may only be used when the wastewater has been treated to tertiary standards. A shallow-buried trench consists of small-diameter PVC laterals running through open-bottom plastic chambers. The laterals are perforated at regular intervals on the top of the pipe. Effluent from the advanced septic treatment system is pumped under pressure through distribution pipes at regular intervals (time-dosed).
When the dosing pump is activated, wastewater is forced along the entire length of the lateral and sprayed upwards where it hits the chamber and trickles down into the soil. By sizing the pump correctly, the entire footprint of the septic system is dosed at the same time, ensuring much more efficient septic distribution and use of the soil absorption system. This pressurized distribution allows for small doses to be evenly distributed along the entire length of the trench and greatly enhances the soil’s ability to receive and treat the effluent.
Shallow-buried trenches are typically installed in the natural soil close to the surface of the ground, allowing plant roots and bacteria in the soil to take up additional nutrients. Shallow buried trenches can be installed as one row or several rows to meet minimum trench length standards as required by the Ontario Building Code. This method is versatile because the septic trench can follow an irregular pattern (e.g., around trees).
The footprint of a shallow-buried trench system is much smaller than a conventional septic system because the soil is not relied upon to complete treatment. In addition, shallow-buried trenches may be installed in native soils with a T-time up to 125 min/cm. A shallow-buried trench system is appropriate for sites with a high water table, shallow depth to bedrock, or tight soils.
Ontario Building Code Requirements for Shallow Buried Trench Construction
MAINTENANCE OF SEPTIC SYSTEMS·
Don’t:
· Plant a vegetable garden on or near the septic drain field.
· Put plastic sheets, bark, gravel, or other fill over the septic drain field.
· Reshape or fill the ground surface over the septic drain field and reserve area. However, just adding topsoil is generally acceptable if it isn’t more than a 5cm (2”)
· Make ponds on or near the septic system and the reserve area.
Plant native, drought-tolerant plants as ground cover for septic drain fields.
The following shallow-root plants are some of the best for planting in your septic drain field:
Grass:
Groundcovers for the sun:
Groundcovers for shade:
Soil Compaction
Soil Compaction can bring serious consequences to septic system performance. Any soil treatment area whether it is below grade with trenches, a bed or drip distribution, or above grade with an at-grade or a mound — needs non-compacted soil. Half of a healthy soil’s makeup is pore space, with the other half composed of organic matter and mineral particles (sand, silt, and clay). Pore space provides room for air and water to circulate around the mineral particles, providing a healthy environment for plant roots and beneficial microorganisms. In compacted soils, the particles are pressed together so tightly that the space for air and water is greatly reduced.
Compaction is most likely to occur with heavier soils like clay and loam, but when heavy equipment is used, sandy soils can also become compacted. Reduced oxygen transfer to the soil treatment area can decrease the life of the septic system, as it needs oxygen to break down the wastewater. Reduced pore space decreases the pathways for wastewater to move through the soil. Lack of pore space translates into a lack of drainage. Reduced microbial community due to decreased oxygen levels. Lack of vegetative cover that is needed to protect components, use water and prevent erosion. In fact, it can be almost impossible to maintain plants in compacted soil because it interferes with the movement of water, air, nutrients, and roots in the pore spaces between soil particles. This makes root penetration and growth harder, leading to poor, shallow rooting; poor plant growth; and a greater need for irrigation and fertilizer. As a result, soil compaction can result in increased costs for the homeowner for water, fertilizer, and, in the end, plant replacement. Also, we do not want fertilizer or irrigation over a septic system drain field.
Causes of compaction
When construction is occurring near the septic system put up a temporary fence to prevent traffic over the septic system. Install barriers to prevent traffic. Avoid working the soil when it is too wet (this includes mowing). Educate all those on the property about the concerns and consider signage if it’s in a high-traffic area.
Use of Chemicals
Septic systems thrive on wastewater, but certain chemicals can cause major indigestion. Flushing even small amounts of paints, solvents, thinners, nail polish removers and other common household compounds (or pouring them down the drain) can poison the organisms that break down organic material.
Laundry bleaches, toilet bowl cleaners, and caustic drain openers can also slow the septic treatment process, allowing sewage to pass through without proper septic treatment. And often, the chemicals themselves seep into the ground, sometimes contaminating wells or surface waters.
Confirm household cleaning products are septic-safe, biodegradable, and not antibacterial. Vinegar and baking soda can clean about 70% of a home safely and economically, but there are also many biodegradable products in the market today, such as Nature Clean, Ecos, and Citra-Solv. Most retail stores, grocery stores, drug stores, and health food shops offer natural cleaning products. Liquid fabric softeners cause the most harm to a septic system and should be avoided. Dryer softener sheets, such as Bounce or a non-chemical dryer sheet, are recommended. Potassium Chloride salts are recommended for water softeners. Potassium Chloride is available through hardware stores including Canadian Tire and selected water softener suppliers.
Oil, Grease & Fat
Septic systems are not designed to digest oils, grease, and fat. Poured down the sink or toilet, they congeal in pipes sometimes plugging them. Grease can also combine with detergents and flow into the drainage field where it may clog the soil. Fats can form a blob in the top of the tank and interfere with the biological activities taking place. All oily waste should go out with the garbage.
Refuse & Garbage
Using your septic system to dispose of garbage is another no-no. In-sink garbage disposals (“Garburators”) are unwelcome strains on the septic system. Disposable diapers, tampons, and their holders, condoms, wrappers, and many other kinds of refuse can plug and impair septic systems. If something doesn’t break down naturally, don’t flush it into your septic tank.
Bath Bombs
Bath bombs are hard-packed mixtures of dry ingredients that effervesce when wet. They are used to add essential oils, scent, bubbles, and color to bathwater. They are a mixture of salts, colorants, oils, and solid items such as flower petals or glitter. When added to a bath, the sodium bicarbonate reacts with citric acid to release carbon dioxide gas (like Alka-Seltzer). As it is breaks down, it releases colorants, fragrances, salts, and oils.
Solid particles in bath bombs could include natural things like lavender buds and flower petals or synthetic materials such as glitter and confetti. None of these items will dissolve. Along with the other items present in the waste stream, these could plug up plumbing and negatively affect the septic system. It is best to use bath bombs that do not contain solid particles, or you could place a length of pantyhose or a fine mesh strainer over the tub drain to collect any solids. The natural products could contribute to the oxygen demand of the septic system and the synthetic ones could accumulate in the septic tank, clog effluent filters, and potentially harm downstream components.
There are fats and oil in most bath bombs. Oils are liquid at room temperature and will make their way to the septic tank where they will hopefully float to the top and accumulate in the scum layer. Fats or butter in bath bombs can be a problem as they have a variety of melting points and if they cool too fast while traveling through the drain pipes, they can solidify and create a blockage similar to grease in the kitchen. Typical bathwater is usually around 105°F. Cocoa butter has a melting point of around 97°F, but at the end of the bath, the water may have cooled to close to 98°F. When the drain is opened, the pipes will easily going to bring that temperature below the 97°F solidification point and potentially create a buildup in the interior plumbing.
Most bath bombs have such a low butter content that they should not create much of an issue in the plumbing, but if bombs are used frequently, they could accumulate in piping and the tanks outside the home. Bath “truffles” have a much higher butter content and should be avoided. These oils and greases can accumulate in the septic tank, clog effluent filters or exert an additional oxygen demand in the overall septic system. The salts used in some bath bombs may not totally dissolve. Partially dissolved bath salts can result in clogs as a few undissolved chunks can become caught in the drain, which will then catch hair and other pieces of debris. In high amounts, these added salts will harm the bacteria in the septic system. In general, bath bombs are not a product recommended for frequent use for those on septic systems. For those connected to septic treatment plants, care should be taken not to clog drains.
Backwash Water from Water Softener
We do not recommend that you discharge backwash water from water treatment devices like water softeners to the septic system unless the system has been designed by a licensed professional engineer to handle the specified water treatment system.
If you have municipal water service, your water meter will record your water use. You can compare water use with the design flow of the system and detect leaking plumbing fixtures.
Improperly designed, selected, installed, or maintained septic systems can fail. Problems related to the pipes, rock, or soil can result from a poorly designed septic system (inadequately sized for the soil conditions). Remember that if use is greater than the design flow rate, untreated effluent may surface down the gradient of the drain field. The average septic tank should be inspected every 1 to 2 years by a professional septic tank cleaner. If the cover is removed and the tank is full, this does not mean there is a malfunction. The tank is designed to have an outflow level of approximately 75 mm (3 in.) below the inflow level.
When properly designed, installed, used, and maintained, your septic system will be simple, economical, and effective, and will do its work reliably, safely, and efficiently for many years.
Here are a few examples of how homeowners have caused problems with their septic systems. None is covered by the TARION new home warranty.
“That large, flat piece of land was just sitting there, so we ...... built a driveway (patio, deck, tennis court) over it.”
Just covering the grass over the leaching bed will stop evapotranspiration and keep out the oxygen the system requires. Any weight can crush the pipes and make the leaching bed useless.
... used it for our above-ground pool.”
The weight of an above-ground pool will almost certainly crush the leaching bed.
.... used it for our in-ground pool.”
Don’t laugh. It really happened. They got the whole thing excavated, and then somebody flushed the toilet.
.... flooded it so the kids could have a skating rink.”
Leaching beds are carefully built to accept water -- even if it comes from a hose sprayed in the middle of winter. This family managed to freeze their entire leaching bed solid and ended up with water backing up into the house.
... rototilled it for a vegetable garden.”
Pipes can be as little as 375 mm below the ground surface. They can easily get damaged. Besides, vegetables don’t protect the soil from erosion like grass does.
.... made it look pretty with trees and nice landscaping.”
Perforated pipes don’t stand a chance against roots from trees and shrubs. They get clogged or crushed. Either way, the septic system doesn’t work properly.
That huge mound was really ugly, so we ... ... brought the rest of the ground up to match.”
Often, the reason the septic designer designed a septic system with a raised bed is that the site is clay. If owners fill in around the septic bed with more of that clay soil, they end up making a sort of large, almost impervious bathtub. Sooner or later, it will fill up. If they also put a layer of clay soil over top, it can fail within months. The only material that should be used to level the grade is good sand.
.... cut it off and built a nice-looking retaining wall.”
This family didn’t understand that the whole mantle area is used for filtering wastewater. When they cut it off, the liquid (which wasn’t completely filtered yet) seeped out through that pretty wall instead.
“Nobody ever told me I couldn’t ...... drain the downspouts, sump pump, etc. down the septic system.”
This is a common problem, which can make the actual water flow through the system many times the estimated design flow. It will drown the septic bed.
.... water the lawn over the leaching bed area.”
There have even been cases where people installed automatic lawn sprinklers over the leaching bed area and refused to turn them off. Again, this will drown the septic bed.
.... start a daycare centre, add an apartment in the basement, etc.”
Anything that increases the house water use - and both of these certainly did - can overload the septic system.
.... fill in those ugly ditches.”
“Swales” are used to direct rainwater and melting snow away from the leaching bed. Filling them in changes all that carefully thought-out drainage pattern.
Our Professional Engineers licensed in Ontario design a variety of advanced, innovative, predictable, permanent, robust, cost-effective, compact, low energy, low maintenance, visually subtle, and efficient onsite septic systems for off-sewer developments in Ontario.
Our septic system designs meet the requirements of the Ontario Building Code and the Ministry of the Environment, Conservation, and Parks and offer the most affordable, long-lasting site-specific septic system design. Inappropriate septic system design, bad construction practices, or poor maintenance can all lead to septic system failure.A small house with a maximum daily flow rate of about 1,000 L, and if that system is being installed in sandy soil (which has a high absorption rate) then the system could be quite small and be installed at a cost of a few thousand dollars. On the other hand, a big house with a maximum daily sewage flow rate of 9,000L and hard clay soil which can only absorb 4 L, per square meter, per day then the cost could be over $50,000 because the tertiary septic system may need to be installed.
Typical stamped engineering residential class 4 sewage system design complying with provisions of Division 8 Part 8 of O.B.C and if required, a design of a tertiary treatment unit, pump chamber, and a shallow buried trench would cost $1,695⁺ʰˢᵗ and upon the receipt of all the required information, could be completed in 5 to 8 business days.
If required, a new soil sampling and particle size distribution analysis by an accredited laboratory to find the Unified Soil Classification as described in MMAH Supplementary Standard SB-6 and the "T" time would cost $495⁺ʰˢᵗ for locations in the Greater Toronto Area. If Hydrometer Testing is required, it would cost an additional fee of $125⁺ʰˢᵗ.
If the client wishes to have two separate septic systems design of a separate system would cost an additional fee of $795⁺ʰˢᵗ.
If deemed necessary by the Municipality and/or the Conservation Authority, the applicant may be requested to provide supporting reports, assessments, plans, and analyses including the following:
· Seasonal High Groundwater Elevation and bedrock elevations
· General soil properties and conditions
· Geotechnical Report
· Hydrogeological Assessment
· Calculation of Nitrogen Concentration and/or Phosphorus Reduction· Nitrate-Nitrogen Dilution Calculation
Depending on the scope of work, the fee for preparing any of the above-mentioned reports/analyses may vary.
The septic contractor may have to contact the Municipal Officials to determine their requirements and if they need inspectors on site for the test pit investigation/assessment and arrange for septic test pit digging equipment based on site accessibility.
We need the following to prepare a Septic Design:
For Additional Information please contact one of our key design team members:
Land Line: 905 940 9937
After Hours / Text Messages: 647 877 8262
Email: landbuildex@gmail.com
County of Brant, City of Brantford, City of Chatham-Kent, Haldimand County, City of Hamilton, Norfolk County, City of Kawartha Lakes, City of Toronto
REGIONAL MUNICIPALITIES
City of Oshawa, City of Pickering, Municipality of Clarington, Town of Ajax, Town of Whitby, Township of Brock, Township of Scugog, Township of Uxbridge
Halton
City of Burlington, Town of Halton Hills, Town of Milton, Town of Oakville
Niagara
City of Niagara Falls, City of Port Colborne, City of St. Catharines, City of Thorold, City of Welland, Town of Fort Erie, Town of Grimsby, Town of Lincoln, Town of Niagara-on-the-Lake, Town of Pelham, Township of Wainfleet, Township of West Lincoln
Peel
City of Brampton, City of Mississauga, Town of Caledon
Waterloo
City of Cambridge, City of Kitchener, City of Waterloo, Township of North Dumfries, Township of Wellesley, Township of Wilmot, Township of Woolwich
York
City of Vaughan, Town of Aurora, Town of East Gwillimbury, Town of Georgina, City of Markham, Town of Newmarket, City of Richmond Hill, Town of Whitchurch-Stouffville, Township of King
Dufferin
Town of Grand Valley, Town of Mono, Town of Orangeville, Town of Shelburne, Township of Amaranth, Township of East Garafraxa, Township of Melancthon, Township of Mulmur
Elgin
City of St Thomas, Municipality of Bayham, Municipality of Central Elgin, Municipality of Dutton/Dunwich, Municipality of West Elgin, Town of Aylmer, Township of Malahide, Township of Southwold
Hastings
City of Belleville, City of Quinte West, Municipality of Centre Hastings, Municipality of Hastings Highlands, Municipality of Marmora and Lake, Municipality of Tweed, Town of Bancroft, Town of Deseronto, Township of Carlow/Mayo, Township of Faraday, Township of Limerick, Township of Madoc, Township of Stirling-Rawdon, Township of Tudor & Cashel, Township of Tyendinaga, Township of Wollaston
Northumberland
Municipality of Brighton, Town of Cobourg, Municipality of Port Hope, Municipality of Trent Hills, Township of Alnwick/Haldimand, Township of Cramahe, Township of Hamilton
Oxford
City of Woodstock, Town of Ingersoll, Town of Tillsonburg, Township of Blandford Blenheim, Township of East Zorra-Tavistock, Township of Norwich, Township of South-West Oxford, Township of Zorra
Peterborough
City of Peterborough, Township of Asphodel-Norwood, Township of Cavan Monaghan, Township of Douro-Dummer, Township of Havelock-Belmont-Methuen, Township of North Kawartha, Township of Otonabee-South Monaghan, Township of Selwyn, Municipality of Trent Lakes
Simcoe
City of Barrie, City of Orillia, Town of Bradford West Gwillimbury, Town of Collingwood, Town of Innisfil, Town of Midland, Town of New Tecumseth, Town of Penetanguishene, Town of Wasaga Beach, Township of Adjala-Tosorontio, Township of Clearview, Township of Essa, Township of Oro-Medonte, Township of Ramara, Township of Severn, Township of Springwater, Township of Tay, Township of Tiny
Wellington
City of Guelph, Town of Erin, Town of Minto, Township of Centre Wellington, Township of Guelph-Eramosa, Township of Mapleton, Township of Puslinch, Township of Wellington North
County of Perth
City of Stratford, Municipality of North Perth, Town of St. Marys, Township of Perth East, Township of Perth South, Municipality of West Perth
County of Middlesex
City of London, Municipality of North Middlesex, Municipality of Southwest Middlesex, Municipality of Thames Centre, Township of Adelaide Metcalfe, Township of Lucan Biddulph, Township of Middlesex Centre, Township of Strathroy - Caradoc, Village of Newbury
County of Huron
Municipality of Bluewater, Municipality of Central Huron, Municipality of Huron East, Municipality of Morris-Turnberry, Municipality of South Huron, Town of Goderich, Township of Ashfield-Colborne-Wawanosh, Township of Howick, Township of North Huron
County of Bruce
Municipality of Arran Elderslie, Municipality of Brockton, Municipality of Kincardine, Municipality of Northern Bruce Peninsula, Municipality of South Bruce, Town of Saugeen Shores, Town of South Bruce Peninsula, Township of Huron-Kinloss
County of Grey
City of Owen Sound, Town of The Blue Mountains, Town of Hanover, Municipality of Meaford, Township of Chatsworth, Township of Georgian Bluffs, Municipality of Grey Highlands, Township of Southgate, Municipality of West Grey
County of Haliburton
Township of Algonquin Highlands, Municipality of Dysart et al, Municipality of Highlands East, Township of Minden Hills
District of Muskoka
Town of Gravenhurst, Town of Bracebridge, Town of Huntsville, Township of Muskoka Lakes, Township of Lake of Bays, Township of Georgian Bay
The Durham Region Health Department is responsible for approving the design and installation of private septic systems in Durham Region. The City of Oshawa is an exception.
A Septic Permit from the Durham Region Health Department is required for
Applications for a Septic Permit from Durham Region Health Department must contain all 4 pages of the Ontario Ministry of Municipal Affairs and Housing Application for a Permit to Construct or Demolish, completed and signed by the applicant, 2 pages of Schedule A, and a sewage system design drawing.
The following locations accept drop-off applications for a Septic Permit from the Durham Region Health Department
605 Rossland Road East, Whitby
and
181 Perry Street, Port Perry (2nd floor)
Public health inspectors are available by phone at Health Department - Durham Health Connection Line 905-668-2020, should you have questions about septic systems, the septic permit application process, or your specific application.
Please note that applications for septic permits submitted without the applicable payment will not be processed.
Fees can be paid by sending an Interac payment e-transfer to healthpayments@durham.ca.
The optional "message" field of your e-transfer MUST contain the required application code. This is required to ensure the payment is linked to the correct application.
Fees can be paid by cheque made payable to "Durham Region Health Department".
The following municipalities have retained the services of the Region of Durham Health Department to issue septic permits.
Septic Flow Balancing - Balancing / Detention Tanks
When we design septic systems for hospitality, leisure, or tourism properties, we design the septic systems to accommodate variable sewage loads and times of peak demand to ensure that the septic system is environmentally compliant and futureproofed for maximum capacity without having to worry about sewage failures.
Some hospitality, leisure, or tourism sites frequently host events such as weddings, parties, or festivals, and there will be certain times when there will be peak septic sewage load. Summer is the peak season for many in the hospitality, leisure, and tourism sectors, and a high number of guests during peak seasons creates surges in wastewater generated. We design septic systems that need to manage these surges without failure.
We design the septic system to be adaptable and handle the surge with ease and consistency of treatment quality without disruptions or worrying about whether the septic system will be able to cope.
Flow balancing is a design approach for septic systems that stores predictable, short-term peak sewage flows and pumps them to the downstream components over the course of several days. Flow Equalization is typically achieved over 24 hours to reduce diurnal peaks, whereas Flow Balancing is intended to store and reduce peak flows over multiple days, perhaps over a weekend or other predictable high-use event.
When we incorporate Flow Balancing, septic system components installed downstream of the balancing/detention tank can be sized at less than the maximum daily flow, resulting in smaller unit components. Flow balancing evens out both the hydraulic and organic loadings to the treatment system (soil or treatment unit), resulting in better, more effective primary and secondary processes. This may result in better effluent quality on average over the long term.
Balancing/detention tanks should be sized in accordance with “good engineering practice” to ensure peak sewage flows can be accommodated. Appendix A, A-8.2.1.3 (1) and (2) of the 2024 Ontario Building Code outlines information for balancing/detention tanks. The 2024 Ontario Building Code also suggests that components downstream of the balancing tank may be sized on the average weekly flow.
The 2024 Ontario Building Code does require flow equalization when discharging highly treated effluent to a shallow buried trench or Type B dispersal bed. According to the 2024 Ontario Building Code, effluent must be discharged to the septic bed evenly over 24 hours on an hourly basis. This approach requires the use of a timer-controlled pump to ensure hourly dosing and to limit the amount that is dosed each hour to ensure even distribution over 24 hours.
The Ministry of Environment's Manual of Policy, Procedures and Guidelines for Onsite Sewage Systems as per Ontario Regulations 374/81 under Part VII of the Environmental Protection Act, notes that balancing/detention tanks may be needed where the peak day or peak hour flow is much higher than average flows (Section 9.3.3.b and 9.3.8.b), and balancing tanks are to be sized to accommodate the flows during peak periods and include pumps/controls to discharge an even daily flow to the sewage system (9.3.5.b). The Ministry of Environment's Manual of Policy, Procedures and Guidelines for Onsite Sewage Systems, notes that typically, it is variable daily sewage flows that give rise to balancing as opposed to variable hourly flows, such as a rural area restaurant which sees weekend flows far in excess of flows during the work week. The sizing of the balancing/detention tank pumping system and sewage system downstream of the balancing/detention tank should be at least equal to the average daily flow for the week (9.3.8.b). The Ministry of Environment’s Manual states that balancing tank size should be based on the peak volume of sewage that will accumulate during high flow days when the outgoing pumping rate is exceeded, plus some additional capacity to accommodate unexpected peaks higher than design or pump failure. Further, the manual notes that a high-level alarm should be installed to provide a warning of unexpected high flow, pump failure, or blockage.
The Canadian Standards Association's Installation Code for Decentralized Wastewater Systems, CSA B65-12, also includes a short section on flow balancing. Section 7.3 states that “if the daily flow is expected to vary substantially among the days of the week, a flow equalization and management method (e.g., a balancing tank, timer, and pump) to balance the flow over seven days may be used to allow the system design to be based on the averaged seven-day flow (i.e., the balanced daily flow).” This is consistent with the approach outlined in both the 2024 Ontario Building Code and the MECP design guidelines.
Our four qualified licensed professional engineers, specialized in septic design can rush your project through when you need us. Our qualified licensed professional engineers have deep experience working with municipalities and conservation authorities, which enables faster response to address their concerns. Our qualified licensed professional engineers collaborate with architects, arborists, and surveyors to respond to changes quickly whenever required.
Phosphorus Reduction
Reduce the use of phosphate-based detergents, soaps, and cleaners since phosphorus in detergents, soaps, and cleaners doesn’t break down in a septic system. When the phosphorus leaches into nearby bodies of water, it can promote algae growth and impair water quality and fish habitat.
Soil is an integral component of assessment criteria for site development because soil impacts the effectiveness of the onsite private septic system and is an important factor in the determination of buffer effectiveness, depending on soil depth, percolation rate, and resulting ability to retain phosphorus.
Fine-texture soils are better at phosphorus removal, but they have lower percolation rates. The Ontario Building Code accounts for the hydraulic loading rates of the receiving soil, and therefore, overland flow should not be a problem if septic systems are designed, constructed, and inspected correctly.
There are no definitive guidelines in Part 8 of the Ontario Building Code to account for the optimum sand/soil fill to be used to provide long-term attenuation of phosphorus, but in terms of determining general site suitability, moderately coarse soils are generally the most appropriate for buffering and the construction of septic leaching beds.
Mineral-rich soil containing high Iron and Aluminum, and non-calcareous (< 1% CaCO3) soil, provides very significant long-term phosphorus retention and mineralization of up to 95% of septic system phosphorus, and provides significant protection for phosphorus-sensitive lakes.
Iron-rich "B-horizon" soil is formed naturally by precipitation of oxides of iron leached from the overlying "A-horizon" soil. Reactive phosphorus dissolved in septic tank effluent passing through "B-horizon" soil adsorbs onto and binds chemically to surfaces of iron oxides and hydroxides.
As adsorption of phosphate on charged soil surfaces and mineralization of phosphate with iron and aluminum can immobilize septic phosphorus by formation of phosphate minerals such as vivianite and strengite, which have very low solubilities in aerobic and anoxic environments.
Vegetation improves the success of phosphorus and sediment attenuation through interception and infiltration of stormwater runoff and retention of septic phosphorus in the shoreline buffer, which is a very significant mitigation measure associated with the development of waterfront lots. development.
The Waterloo Biofilter's EC-P™ efficiently and permanently removes phosphorus from septic systems by the precipitation of iron-phosphate minerals. This process mimics the natural phosphorus removal of iron-rich "B-horizon" soils by introducing iron to any naturally iron-free filtration media. With the use of Biofilter's EC-P, up to 99% of total phosphorus can be removed from septic systems.
Since drilled wells are considered to be of superior construction and are less susceptible to contamination than other types of wells, drilled wells shall be provided on vacant subdivision lots and vacant lots created by consent where private water supplies are required. Wells shall be drilled on each proposed lot unless on-site testing demonstrated that underlying aquifers are unable to support a drilled well, in which case bored wells may be considered as long as they provide the water supply described in Section 3.3 and conform with Ontario Regulation 903 made under the OWRA.
Committee of Adjustment decisions to approve individual privately serviced residential severances are contingent upon compliance with the municipal requirements that:
The Ministry of the Environment’s Technical Guidelines (D-5-5) must be applied to assess water supplies through the use of individual private wells in order to establish that a sufficient quantity and quality of drinking water is present. The adequacy of a water supply well on each lot with respect to quantity shall be based on the result of the sustainable-yield pumping test conducted during the Preliminary Hydrogeological Investigation (Stage 1) and the Final Hydrogeological Investigation (Stage 2).
A water supply well is considered to be adequate with respect to quality, where the water:
As a condition of approval for all rural estate plans of subdivision, to be serviced by individual private services, the owner will be required to establish an adequate private well and to demonstrate acceptable quality impact on each draft approved lot before Final Approval. In the case that an adequate private well cannot be established on any draft-approved lot or unacceptable quality impact should be deduced, the said lot shall not be registered as a separate building lot, but will be either merged with an abutting lot or the subdivision will be redesigned.
All rural residential lots within plans of subdivision comprising three or more lots shall meet the minimum lot size recommendations of the site-specific Preliminary - Stage 1 and Final - Stage 2 Hydrogeological Investigations.
The Ontario Ministry of Municipal Affairs and Housing sets a minimum lot size of 0.9 hectares (9,000m²/2.22 acres) for installing a septic system. However, this can vary depending on factors such as soil conditions, the type of septic system, and municipal regulations.
All unserviced lands that are subdivided or severed are to be assessed, so consequently, the development shall not impact the environment or pose a public health risk. To prevent land development from potentially contaminating the environment or becoming a public health risk, for all new vacant lots being created, the septic system area will be based on a Class 4 conventional septic system, including a separate area for the replacement of a Class 4 conventional septic system. The Class 4 conventional septic system will be designed to process a minimum daily sewage flow of 3,000 L.
Each newly created vacant lot in a severance application or in a subdivision proposal must be suitable for the construction of a Class 4 conventional septic system, including a separate area for the replacement of a Class 4 conventional septic system, and also adhere to applicable provincial policies and guidelines.
Subdivision/severance applications shall be assessed for the installation of a conventional Class 4 septic system based on soil suitability, a prime and separate replacement area, topography, maximum groundwater elevation, surface drainage, flooding potential, and potential impact on groundwater quality and other applicable provincial policies and guidelines.
A proposed lot must conform with Part 8 Sewage Systems under the Ontario Building Code as it relates to soil percolation time, depth to high groundwater table elevation, depth to impermeable soil, maximum slopes, drainage characteristics, and horizontal clearances.
The area required for a conventional Class 4 septic system and the separate replacement area must be available for all new vacant lots. Each lot will be assessed on the assumption that a minimum daily sewage flow of 3,000 L/day will be generated from the proposed residence. Other proposals that will generate sewage flows in excess of 3,000 L/day (i.e., commercial/industrial or large residential dwellings) will be assessed on an individual basis.
Site constraints for the location of private septic systems may include, but are not limited to:
• Soil with a percolation time greater than 50 minutes per cm, or less than 1 minute per cm.
• Property is subject to flooding in the proposed septic system areas.
• A high water table in the proposed septic system areas or where the hydraulic loading of the sewage system may cause a saturated soil condition within 0.9 m of the bottom of the leaching bed.
• The topography of the lot or other site deficiencies may not be suitable for the installation of private septic systems. (i.e., an area that has an average slope that exceeds one unit vertically to four units horizontally (> 25%).
If a proposed development indicates major reshaping of the property, the municipal authorities may defer the subdivision/severance assessment until the re-grading has been completed and the municipality has approved the new drainage/grading plans. Extensive reshaping (cut and fill) of the property, particularly sites with fine-grained soils, should not be undertaken since re-moulded soils will have a reduced hydraulic conductivity or the permeability can be destroyed.
The 2024 Ontario Building Code restricts the installation of septic systems in areas where the natural slope in the proposed sewage system envelope exceeds 25%. Lot development involving proposed septic system envelopes in locations where the natural slope ranges between 10% and 25% will require very specific details relative to surface grading, drainage, tile field design, alignment, and depth of cover.
A hydrogeological report and/or a geotechnical report is required for any proposed subdivision development and may be required for lots created through the consent process where there is a potential impact on the environment. A hydrogeological report and/or a geotechnical report should consider the quality and quantity of drinking water on the proposed site and on adjacent groundwater conditions. This will require a current study of proposed and adjacent wells to determine the quality and quantity of drinking water.
The Ministry of the Environment’s Technical Guidelines (D-5-4) is to be applied to determine the impact of the proposed sewage systems on the immediate and adjacent groundwater supplies (bacterial and chemical quality), which will determine the maximum number of lots. The Ministry of the Environment’s Technical Guidelines (D-5-4) involve a three-step process, in which the proponent will review each step sequentially, and proceeding to the next step will depend on whether the previous step can be satisfied.
In most cases, total nitrogen (all species) converted to nitrate-nitrogen is considered the critical contaminant. For the purposes of predicting the potential for groundwater impact, a nitrate-nitrogen content of at least 40 mg/L in the sewage effluent shall normally be used in the impact assessment. A residential dwelling with up to 4 bedrooms shall be considered to generate a minimum of 1,000 L/day of sewage, resulting in a nitrate-nitrogen loading of 40 grams/day. For each additional bedroom in a residence, the sewage generation shall increase by 250 L/day or an additional loading of 10 grams/day nitrate-nitrogen.
Nitrate-nitrogen removal treatment may not be considered to decrease the interpreted nitrate-nitrogen loading, as the provision for such treatment is not included in the OBC standards.
In assessing the nitrate-nitrogen impact, only the on-site precipitation reaching the water table (groundwater recharge) will be accepted as a quantifiable dilution source. Mixing of the sewage discharge with groundwater flowing beneath the site (underflow) will not be allowed in the dilution calculations, as the current and future activities cannot be ascertained on the upgradient lands. The stringent requirement that the dilution availability shall only comprise the on-site groundwater recharge was established in consultation with the Ministry of the Environment, Conservation and Parks MECP.
The representative recharge rate for the property shall be the geometric mean of the rates determined for the individual soil samples collected throughout the property. Estimates of the on-site recharge shall consider the post-development impermeable areas (including roof tops and paved areas). Where precipitation is directed to a subsurface stormwater system, the rainfall occurring on rooftops, driveways, and access roads shall be deducted from the potential onsite infiltration in evaluating the development quality impact. Where roof top discharge to adjacent land and where access roads discharge to open ditching, the precipitation occurring on the impervious areas may be partially utilized in the dilution calculations.
Consideration is required in regard to the ambient nitrate-nitrogen detected in either the shallow saturation zone and/or the underlying aquifer intended as the development groundwater source.
Where the ambient nitrate-nitrogen has a geometric mean greater than 2 mg/L within the on-site wells due to antecedent on-site and upgradient land-use activities, we should provide a detailed interpretation regarding the source and the possibility that the nitrate-nitrogen content may be decreased by changing land use. If attributed to adjacent off-site uses, the observed nitrate-nitrogen content should be factored into the dilution calculations when determining the permissible residential density. Any individual well having a nitrate-nitrogen content exceeding 9 mg/L shall be abandoned as a dependable groundwater source, and any individual well having a nitrate-nitrogen content exceeding 5 mg/L shall be equipped with reverse-osmosis treatment equipment for the drinking water portion of the water supply.
Residential lot-area variations are recognized due to the development design/configuration; however, the minimum individual-lot area should be at least ¾ (0.75) of that for a self-sustaining lot area to maintain the on-site quality conditions. This standard only applies to residential subdivisions – not severances.
Step One: Lot Size Considerations involves reviewing the lot sizes for each lot that makes up the proposed subdivision. The average size when combining all the lots cannot be less than one hectare, with no individual lot being less than 0.8 hectares in size. If Step One is not satisfied, proceed to Step Two.
Step Two: System Isolation Considerations applies to lots that are less than one hectare in size and requires the proponent to assess the potential risk to groundwater. This step reviews the potential for the sewage effluent discharged from each on-site sewage system to be isolated from the existing supply aquifer that is used as the source for local private wells. Based on the borehole log information detailed in the Preliminary Nitrate Impact Assessment shall be completed.
If the subject site does not appear to have an effective isolation layer of low-permeable soils, and Step Two is not satisfied, then proceed to Step Three.
Step Three: Contaminant Attenuation Considerations applies where it cannot be demonstrated that the sewage effluent is hydrogeologically isolated from all existing or potential supply aquifers; therefore, a nitrate impact study is required to assess the risk that the development’s individual on-site septic systems will cause concentrations of nitrate in groundwater to exceed 10 mg/L (ODWS) at the property boundary.

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